Before the 

U.S. Environmental Protection Agency 

PETITION OF THE AMERICAN CHEMISTRY COUNCIL’S 

ETHYLENE GLYCOL ETHERS PANEL 

TO REMOVE ETHYLENE GLYCOL MONOBUTYL ETHER FROM 

THE TOXICS RELEASE INVENTORY UNDER SECTION 313 

OF THE EMERGENCY PLANNING AND COMMUNITY RIGHT-TO-KNOW ACT 

OF 1986 

Jonathon Busch 

Director, Ethylene Glycol Ethers Panel 

Technical Consultants: 

Miranda Henning 

Suzanne Persyn 

Duncan Turnbull, D.Phil. 

ENVIRON International Corporation 

136 Commercial Street, Suite 402 

Portland, ME 04101 

American Chemistry Council 

700 2nd Street, NE 

Washington, DC 20002 

(202) 249-6725 

December 29, 2014
Petition 

Pursuant to Section 313(d) & (e) of the Emergency Planning and Community Right-toKnow Act of 1986 (EPCRA), the Ethylene Glycol Ethers Panel of the American Chemistry 

Council hereby petitions the United States Environmental Protection Agency (EPA) to remove 

ethylene glycol monobutyl ether (EGBE) from the list of chemicals subject to the Toxics Release 

Inventory (TRI) reporting requirements of the EPCRA Section 313. 

As demonstrated below, available scientific data indicate that EGBE poses low potential 

hazards to human health and the environment, making an assessment of exposure appropriate 

under EPA’s policy for making TRI listing decisions under EPCRA. Conservative estimates of 

exposures resulting from plant emissions of EGBE are well below Integrated Risk Information 

System reference values for human inhalation and ingestion health risks and are also far below 

conservative benchmarks for acute human health effects and ecotoxicity. When the 

Administrator removed EGBE from the Clean Air Act’s list of Hazardous Air Pollutants in 

November 2004, he specifically determined, based on exposure assessments utilizing 1993 TRI 

data, that there is “reasonable assurance” that any potential adverse human health and 

environmental effects “will not occur” from EGBE facility releases (68 FR 65660). He concluded 

“with confidence” that releases of EGBE “may not reasonably be anticipated to cause any 

adverse effects to human health” or “adverse environmental effects” (69 FR 69322). 

As demonstrated in this petition, there is an even stronger basis for making essentially 

the same statutory findings under EPCRA and removing EGBE from the TRI reporting list. 

Based on the most recent TRI data available, EGBE releases and exposures are significantly 

lower than those that formed the basis for EPA’s Hazardous Air Pollutants (HAPs) 

determinations. Delisting under EPCRA would remove a significant disincentive to the use of 

EGBE, a solvent that has proven to be highly effective in a variety of important water-based 

coating formulations with demonstrable volatile organic compound (VOC)-reduction benefits. 

Delisting would also eliminate the potential for confusion and misdirected community priorities 

that currently exists because EGBE-using facilities are unfairly singled-out as significant sources 

of “toxics” despite the Administrator’s findings that EGBE releases may not reasonably be 

anticipated to cause adverse human health or environmental effects. Accordingly, for the 

reasons set forth in full in this petition, the EPCRA delisting criteria are satisfied and the Panel 

therefore respectfully requests that EPA remove EGBE from the TRI reporting list.
ii 

TABLE OF CONTENTS 

EXECUTIVE SUMMARY 1

1.0 INTRODUCTION 6

2.0 BACKGROUND 10

2.1 Synonyms 10

2.2 History of EGBE Regulation under EPCRA 10

2.3 Removal of EGBE from the Clean Air Act HAPs List 11

2.4 Regulatory Standards and Guidelines 13

2.5 Production and Use 13

3.0 HAZARD ASSESSMENT 16

3.1 Chemical and Physical Properties 16

3.2 Potential Human Health Hazards 17

3.2.1 Noncancer Toxicity 17

3.2.2 Potential Carcinogenicity 22

3.3 Ecotoxicity 26

3.4 Evaluation of Potential Hazards of EGBE and Implications for TRI 

Listing 27

3.4.1 Low Potential for Adverse Chronic Human Health Effects 27

3.4.2 Low Potential for Significant Adverse Ecological Effects 29

3.4.3 Conclusion 29

4.0 CRITERIA FOR EVALUATING ACUTE AND CHRONIC HUMAN EXPOSURES 31

4.1 Acute Toxicity 31

4.2 Chronic Toxicity 31

5.0 EMISSIONS INVENTORY 34

6.0 INHALATION EXPOSURE ASSESSMENT AND RISK CHARACTERIZATION 35

6.1 Overview of the Tiered Modeling Method for Assessing Risks from Air 

Exposures 37

6.2 Step A and B Prescreening 40

6.2.1 Step A Prescreening Methodology 40

6.2.2 Step A Results 41

6.2.3 Step B Prescreening Methodology 41

6.2.4 Step B Results 44

6.3 Chronic Inhalation Exposure Assessment for Individual Facilities 44

6.3.1 Tier 1 Screening for Individual Facilities 44

6.3.2 Tier 2 Screening for Individual Facilities 47

6.4 Chronic Inhalation Exposure Assessment for Clusters of Facilities 52

6.4.1 Facility Cluster Evaluation Tiered Screening Methodology 52

6.4.2 Step A Screening (Cluster Evaluation) 52

6.4.3 Step B Screening (Cluster Evaluation) 54

6.4.4 Tier 2 Screening (Cluster Evaluation) 56

6.5 Uncertainty Analysis 58
iii 

6.5.1 Conservatism of Step A through Tier 2 59

6.5.2 Tier 3 Modeling (Individual Facilities) 61

6.5.3 Tier 3 Modeling (Clusters of Facilities) 64

6.5.4 Conservatism of the Tiered Modeling Approach 65

6.6 Acute Exposure Margin of Exposure (MOE) Assessment 67

6.6.1 Acute Exposure Assessment for Individual Facilities 68

6.6.2 Acute Exposure Assessment for Clusters of Facilities 70

6.6.3 Acute Margin of Exposure (MOE) Assessment 71

6.7 Risk Characterization Conclusions for Potential EGBE Inhalation 

Exposures 72

7.0 SURFACE WATER EXPOSURES AND RISKS 73

7.1 Exposure Profiles 73

7.2 Exposure Equations 74

7.3 Exposure Assumptions 75

7.4 Results and Conclusions 77

8.0 ECOLOGICAL RISKS 79

8.1 HAPs Delisting Ecological Risk Assessments 79

8.1.1 The Panel’s ERA 79

8.1.2 EPA ERAs 80

8.1.3 Tier 1 ERA 81

8.1.4 Tier 2 ERA 82

8.2 Updated ERA 82

8.2.1 Problem Formulation 83

8.2.2 Exposure Assessment 83

8.2.3 Effects Assessment 84

8.2.4 Risk Characterization 87

8.3 Conclusions 88

9.0 SUMMARY AND RATIONALE FOR DELISTING EGBE 90

9.1 Delisting EGBE Is Fully Consistent with EPCRA’s TRI Listing Criteria as 

Interpreted by EPA 90

9.2 Substantial Conservatism is Incorporated into Every Primary Element of 

the Toxicological, Exposure, and Ecological Assessments Presented in 

this Petition 93

9.2.1 IRIS Reference Values 93

9.2.2 Exposure Assessments 94

9.2.3 Ecological Risk Assessment 95

9.3 In Light of the HAPs Delisting Decision, EPA’s Policy of Ensuring 

Consistency with Other Agency Decisions Supports Removal of EGBE 

from the TRI Reporting List 96

9.4 Removing EGBE from the TRI Would Promote the Local Risk 

Management and Pollution Prevention Objectives of EPCRA 97

10.0 REFERENCES 101
iv 

TABLES

Table ES-1 Key Findings of the Qualitative Hazard Evaluation 

Table ES-2 Key Findings of the Exposure and Risk Assessments 

Table ES-3 Sources of Uncertainty and Conservatism 

Table 2-1 Regulatory Standards and Guidelines Applicable to EGBE 

Table 3-1 Physical and Chemical Properties of EGBE 

Table 3-2 Aquatic Ecotoxicity Data for EGBE 

Table 5-1 Comparison of Glycol Ether TRI-Related Releases from 1993 through 2011 

Table 6-1 Screening Table Showing Threshold Emissions (tpy) 

for the Reference Concentration of 1.6 mg/m3 

Table 6-2 Number of Facilities with Total TRI-Reported Air Emissions of Certain Glycol 

Ethers Relative to 4.9 tpy (Step A) 

Table 6-3 Number of Facilities with Total Air Emissions of Certain Glycol Ethers 

Greater than Site-Specific Screening Values (Step B) 

Table 6-4 Long-Term (Chronic Exposure) Tier 1 Modeling Results 

Table 6-5 Long-Term (Chronic Exposure) Tier 2 Modeling Results (2009, 2010, and 

2011 TRI Data) 

Table 6-6 ZIP Codes with More than One Facility Reporting Air Emissions of Certain 

Glycol Ethers to the TRI in 2009 through 2011 

Table 6-7 ZIP Codes and Facilities Identified for Dispersion Modeling Following Step B 

Screening 

Table 6-8 Results of Chronic Tier 2 & Tier 3 Exposure Modeling for Facility Clusters 

Table 6-9 Uncertainty Analysis Long Term (Chronic Exposure) Tier 3 Modeling for 

Selected Facilities (2009, 2010, and 2011 TRI Data) 

Table 6-10 Comparison of Concentrations Using the Tiered Modeling Approach 

Table 6-11 Total TRI Air Emissions (Fugitive and Point-Source Air) by Year for Selected 

Facilities 

Table 6-12 Short-Term (Acute Exposure) Tier 1 Modeling Results 

Table 6-13 Results of Acute Tier 2 & 3 Modeling for Facility Clusters 

Table 6-14 Results of Short-Term Tier 2 & 3 Modeling and Acute MOE Analysis for 

Selected High Emitting Facilities 

Table 7-1 Hazards from Surface Water Exposure to EGBE, 

Residential Scenario: Ingestion of EGBE in Drinking Water 

Table 7-2 Hazards from Surface Water Exposure to EGBE, Residential Scenario: 

Dermal Contact with EGBE While Bathing and Showering 

Table 7-3 Hazards from Surface Water Exposure to EGBE, Recreational Scenario: 

Incidental Ingestion of EGBE in Surface Water While Swimming 

Table 7-4 Hazards from Surface Water Exposure to EGBE, Recreational Scenario: 

Dermal Contact with EGBE in Surface Water While Swimming 

Table 7-5 Summary of Hazards from Surface Water Exposures to EGBE 

Table 7-6 Comparison of Hazards from Surface Water Exposures 

Predicted in HAPs Petition and This Petition 
v 

TABLES 

Table 8-1 EGBE Emissions Rates Used in Level III Mackay Distribution Model (kg/hr) 

Table 8-2 Modeled EGBE Exposure Concentrations Used in This and Previous 

Ecological Risk Assessments 

Table 8-3 EQC Level III Input Parameter Values 

Table 8-4 Exposure Assumptions for Small Mammals 

Table 8-5 Chronic Species Sensitivity Distribution Calculations for EGBE 

Table 9-1 Key Findings of the Qualitative Hazard Evaluation 

Table 9-2 Key Findings of the Exposure and Risk Assessments 

Table 9-3 Sources of Uncertainty and Conservatism 

FIGURES 

Figure 1-1 Structure of Ethylene Glycol Monobutyl Ether (EGBE) 

Figure 2-1 Annual Production and Consumption of EGBE in the United States (1970 -

2009) 

Figure 5-1 Maximum Individual Facility Annual Certain Glycol Ether Releases to Air 

(2000 – 2011) 

Figure 8-1 Aquatic Organism Species Sensitivity Distribution Approach 

Figure 8-2 Aquatic Organism Species Sensitivity Distributions for EGBE 

APPENDICES 

Appendix A Toxicity Values in Laboratory Mammals 

Appendix B Emissions Inventory 

Appendix C Outcome of Screening Procedure for Long-Term Exposures 

Appendix D Outcome of Long-Term Tiered Modeling in Support of Uncertainty Analysis 

Appendix E Outcome of Short-Term Tiered Modeling 

Appendix F Tier 2 and Tier 3 Modeling Output Files (CDROM) 
vi 

ACRONYMS 

% percent

ACGHI American Conference of Governmental Industrial Hygienists 

ADI average daily intake 

AEGL Acute Exposure Guideline Level 

Ao oral absorption factor 

AT averaging time

ATSDR Agency for Toxic Substances and Disease Registry 

BAA 2-butoxyacetic acid

BAL 2-butoxyacetaldehyde

BCF bioconcentration factor

BHA butylated hydroxyanisole

BMC benchmark concentration

BOD biological oxygen demand 

BW body weight

CAA Clean Air Act 

CAS Chemical Abstracts Service 

Ci concentration of EGBE in diet item i

CICAD Concise International Chemical Assessment Document 

cm2 square centimeters

cm3 cubic centimeters

CMA Chemical Manufacturers Association

CMI Can Manufacturers Institute 

Cw concentration of EGBE in water 

DAevent absorbed dose per event 

DGBE diethylene glycol butyl ether 

DNA deoxyribonucleic acid

ECETOC 

EC50

European Centre for Ecotoxicology and Toxicology of Chemicals 

median effect concentration 

ED exposure duration

EF exposure frequency

EGBE ethylene glycol monobutyl ether 

EGBEA 2-butoxyethyl acetate

EGEE ethylene glycol monoethyl ether 

EGME ethylene glycol monomethyl ether 

EGPE ethylene glycol monopropyl ether 

EPA United States Environmental Protection Agency 

EPCRA Emergency Planning and Community Right-to-Know Act

ERA ecological risk assessment 

EU European Union

EV event frequency
vii 

ACRONYMS 

gps grams per second 

HAP hazardous air pollutant 

Hb hemoglobin

HQ hazard quotient

HSDB Hazardous Substance Data Bank 

IARC International Agency for Research on Cancer 

IR ingestion rate

IRa inhalation rate

IRdiet food ingestion rate 

IRIS Integrated Risk Information System 

IRw water ingestion rate 

kg kilograms

kg/hr kilograms per hour 

kg/kg BW-day kilograms per kilogram body weight per day 

km kilometers

km2 square kilometers

Kow octanol-water partition coefficient 

L/day liter per day 

LC50 lethal concentration for 50% of test organisms 

LD50 lethal dose for 50% of test organisms 

LOAEL lowest observed adverse effect level 

m meter

m3/kg BW-day cubic meters per kilogram body weight per day 

MCV mean corpuscular volume 

MEK methyl ethyl ketone 

mg/cm2 milligrams per square centimeter 

mg/kg milligrams per kilogram 

mg/kg BW-day milligrams per kilogram body weight per day 

mg/L milligrams per liter 

mg/m3 milligrams per cubic meter 

MIBK methyl isobutyl ketone 

mM millimolars

MOE Margin of Exposure 

μg/m3 micrograms per cubic meter 

NED National Elevation Dataset 

NEI National Emissions Inventory 

NIOSH National Institute of Occupational Safety and Health 

NOAEL no observed adverse effect level 

NOEC no observed effect concentration 
viii 

ACRONYMS 

NTP National Toxicology Program 

OEM original equipment manufacturing 

PBPK physiologically based pharmacokinetic 

Pi proportion of organism’s diet made up by diet item i

POTW publicly owned treatment works 

ppm parts per million 

RfC reference concentration

RfD reference dose

RME reasonable maximum exposure

ROS reactive oxygen species 

SA skin surface area exposed 

SARA Superfund Amendment and Reauthorization Act of 1986 

TDI total daily intake 

TGME triethylene glycol methyl ether 

TLV threshold limit value 

TNF∞ tumor necrosis factor alpha 

tpy tons per year 

TRI Toxics Release Inventory 

TRV toxicity reference value 

USGS U.S. Geological Survey 

UTM Universal Transverse Mercator 

VOC volatile organic compound 

WHO World Health Organization 
1 

EXECUTIVE SUMMARY 

Ethylene glycol monobutyl ether (EGBE) (Chemical Abstract Service [CAS] number 111-

76-2) is used primarily as a solvent in the manufacture of paints, coatings, metal cleaners, and 

household cleaners and as a chemical intermediate in the production of other chemicals. It has 

been used for more than 60 years because of its valuable and unique properties, especially its 

ability to make water-based, environmentally sound products work effectively. EGBE is 

regulated under Section 313 of the Emergency Planning and Community Right-to-Know Act 

(EPCRA) because it is a member of the “Certain Glycol Ethers” category of compounds as 

currently defined on the Toxics Release Inventory (TRI). 

Section 313(d) of EPCRA calls for the removal of a chemical from the TRI where “there 

is not sufficient evidence to establish” that the chemical “is known to cause or can reasonably 

be anticipated to cause” any of three types of effects: 

(A) significant adverse acute human health effects; 

(B) (i) cancer or teratogenic effects, or (ii) serious or irreversible 

reproductive dysfunctions, neurological disorders, heritable genetic 

mutations, or other chronic health effects; or 

(C) a significant adverse effect on the environment of sufficient 

seriousness, in the judgment of the Administrator, to warrant 

reporting of facility releases. 

As detailed in the human health and ecological hazard assessment presented in Section 

3 of this petition and summarized in Table ES-1, the available evidence indicates that EGBE 

presents low potential hazards to human health and the environment. The scientific data 

support the conclusions in the current Integrated Risk Information System (IRIS) assessment 

(EPA 2010)a that EGBE is not immunotoxic, genotoxic, or teratogenic, and does not cause 

adverse reproductive effects. The toxic effects of EGBE are secondary to its irritant and 

hemolytic effects, and United States Environmental Protection Agency (EPA) has determined 

that prevention of hemolytic effects in humans will also protect against all other potential toxic 

effects (EPA 2010, 68 FR 65656, 69 FR 69322). The data show, moreover, that humans are 

relatively insensitive to the hemolytic effects of EGBE. Even minor prehemolytic effects are 

expected to occur in humans, if they occur at all, only at exposure concentrations/doses far in 

excess of levels that might occur near EGBE-using facilities. The human-equivalent lowest 

observed adverse effect level (LOAEL) is significantly above 500 milligrams per kilogram body 

weight per day (mg/kg BW-day), and prehemolytic effects are not predicted in humans even in 

EGBE-saturated atmospheres (EPA 2010, Udden 2000, 2002). 

a Although the 1999 IRIS assessment is currently under review, the review is limited to updating the carcinogenicity 

evaluation to incorporate EPA’s recent cancer hazard evaluation for EGBE (EPA 2005a). See 71 Federal Register 

[FR] 77018 (EPA 2006).
2 

For similar reasons, the potential carcinogenicity of EGBE in humans is appropriately 

characterized under EPA’s TRI listing criteria as low to nonexistent based on a hazard 

evaluation. The IRIS assessment finds “limited” animal evidence of carcinogenicity and 

concludes that the human carcinogenic potential of EGBE “cannot be determined” (EPA 2010). 

Subsequent mechanistic studies led EPA to determine that that nonlinear, nongenotoxic modes 

of action are likely responsible for the increased incidence of tumors observed in rodent studies 

(EPA 2005a). Consequently, even if the limited rodent findings are relevant to humans, the 

relatively low sensitivity of humans (including subpopulations such as children) to the hemolytic 

effects of EGBE means that, as EPA has stated, “we would not expect to find these tumors in 

humans following environmental exposures” (69 FR 69322). 

EGBE likewise poses a very low potential ecological hazard judged by the criteria EPA 

has developed for making listing decisions under EPCRA. As summarized in Table ES-1, it has 

a relatively short residence time in the atmosphere, high water solubility, low octanol-water 

partition coefficient (Kow), low vapor pressure, and low bioconcentration factor. Thus, EGBE has 

very low potential for persistence or bioaccumulation. 

Consistent with the findings of a series of comprehensive ecotoxicity assessments— 

including the recently updated Concise International Chemical Assessment Document (CICAD) 

(WHO 2010), the European Union (EU) Risk Assessment (INERIS 2005); and Environment 

Canada (2002)—EPA determined in the Hazardous Air Pollutant (HAPs) proceeding that that 

EGBE causes only “very minor” effects that “are unlikely to be ecologically significant” (68 Fed. 

Reg. 65657). The updated ecological hazard evaluation in Section 3 of this petition supports 

that conclusion. Acute toxicity to most aquatic organisms has been found at concentrations in 

the vicinity of 1,000 milligrams per liter (mg/L) while chronic toxicity to most aquatic organisms 

has been found at concentrations above 100 mg/L. For the most sensitive species, acute and 

chronic aquatic toxicity likewise has been reported only at levels that are properly evaluated as 

high under EPA’s TRI listing criteria (Table ES-1). No data have been found indicating that 

EGBE is toxic to terrestrial mammals or birds. The data indicate, in short, that EGBE is 

“practically non-toxic” to fish and invertebrates under established EPA criteria and, therefore, 

presents “a low risk to the environment” (Staples 1998). 

For these reasons, the human health and ecological hazard evaluation presented here 

supports a determination that EGBE has “low toxicity and unrealistic exposures would be 

necessary for it to pose a risk to communities” (59 FR 61442). Under these circumstances, 

EPA’s interpretation of EPCRA Section 313(d)(2) calls for the consideration of exposure levels 

in determining whether to delete EGBE from the TRI reporting list. 

Significantly, this is an issue the Agency has addressed in a statutory setting that is 

virtually identical to Section 313(d) of EPCRA. On November 29, 2004, EPA Administrator 

Michael O. Leavitt granted the Panel’s petition to remove EGBE from the list of HAPs under 

Section 112 of the Clean Air Act (CAA) (EPA 2004a). Section 112 authorizes the removal of a 

listed HAP based on a determination that “the substance may not reasonably be anticipated to 

cause any adverse effects to the human health or any adverse environmental effects.” In 

assessing exposures to EGBE, EPA determined that the 1993 TRI data (on which our HAPs 
3 

petition was largely based) provided an “adequate” and “reasonable representation” of the 

sources and levels of EGBE emissions. Application of conservative exposure models led the 

Administrator to find that maximum estimated exposures from EGBE-emitting facilities are well 

below the IRIS reference concentration (RfC) and reference dose (RfD). He therefore 

concluded, “with confidence,” that releases of EGBE “may not reasonably be anticipated to 

cause any adverse effects to human health” (69 FR 69322). Relying on similar conservative 

modeling based on the 1993 TRI data, the Administrator likewise found that there are adequate 

data on environmental effects of EGBE to determine that ambient concentrations, 

bioaccumulation, or deposition of EGBE are not reasonably anticipated to cause any adverse 

environmental effects (68 FR 65657). 

This petition updates the hazard, exposure, and ecological assessments that EPA 

reviewed and prepared in the HAPs delisting proceeding, consistent with the assumptions and 

methodologies that EPA found to be “appropriate,” “acceptable,” and “conservative.” 

Section 4 reviews the bases for and substantial conservatism built into the IRIS RfC and 

RfD, which are used to evaluate the results of the exposure assessments prepared for this 

petition, as they were in the HAPs decision. 

Nationwide exposure potential is assessed in Section 5 by developing an inventory of 

Certain Glycol Ether releases using 2009, 2010, and 2011 TRI data. Because EGBE comprises 

52 percent (%) of the United States annual consumption of glycol ethers (SRI 2010), the 

inventory’s assumption that all releases of Certain Glycol Ether are EGBE (in the absence of 

facility-specific data to the contrary) generally overstates EGBE releases by a factor of two. 

As described in Section 6, every facility listed in the TRI database is subjected to a 

screening process very similar to that used in the HAPs proceeding to determine which facilities 

have the potential to have maximum annual average concentrations of EGBE at or beyond the 

fenceline greater than the IRIS RfC of 1.6 milligrams per cubic meter (mg/m3). In addition, an 

analysis of clusters of multiple facilities within the same zip code is used to evaluate the 

maximum potential combined exposures from closely located sources of EGBE. A comparison 

of annual emissions reported to TRI from 2000 through 2011 is used to demonstrate that 

interannual variability in reported emissions among high emitting facilities is relatively low and 

that the tiered modeling approach in this petition provides a sufficient margin of safety that 

encompasses reasonable interannual variability in facility EGBE emissions. Section 6 also 

includes a reasonable worst-case assessment of the potential for acute irritation effects from 

EGBE facility releases using the Margin of Exposure (MOE) methodology EPA has employed in 

prior TRI listing decisions. 

Section 7 evaluates the potential health effects of EGBE posed by human surface water 

ingestion and dermal exposures against the IRIS RfD of 0.1 mg/kg BW-day, based on 

essentially the same conservative assumptions and models that EPA characterized in the HAPs 

evaluation, with updates to reflect the estimated surface water concentration based on 2009, 

2010, and 2011 TRI data, the current RfD, and changes in EPA (2004b) guidance for dermal 

risk assessment. 
4 

Section 8 updates the three ecological risk assessments (ERAs) conducted in the HAPs 

proceeding by applying 2009, 2010, and 2011 TRI data to the Mackay Level III fugacity model, 

to yield updated estimates of the maximum surface water concentration. In addition, Section 7 

applies an updated toxicity reference value (TRV) for aquatic organisms that was identified in a 

supplemental review of the ecotoxicity literature for EGBE. 

The results, summarized in Table ES-2, reveal that EGBE exposures are well below the 

IRIS RfC and RfD for inhalation and dermal/ingestion exposures as well as appropriate 

ecotoxicity reference values. Consequently, the hazard quotients (HQs)—the ratio of maximum 

exposures to applicable health and environmental reference values—are also well below 1 

indicating, in accordance with the National Contingency Plan (EPA 1990a) and EPA (1989) risk 

assessment guidance, that adverse health and environmental effects are unlikely. Similarly, the 

acute MOE for the estimated maximum hourly concentration of EGBE is above 5, which 

indicates no significant concern for potential acute effects because, among other things, the no 

observed adverse effect level (NOAEL) is based on human data. 

As discussed in Section 9.2 and as summarized in Table ES-3, the exposure and risk 

estimates developed in this petition are likely overstated by wide margins, perhaps by as much 

as five orders of magnitude. EPA (2003) has acknowledged that substantial conservatism is 

incorporated into every primary element of the evaluation, including the IRIS and ecotoxicity 

reference values, the emissions inventory, and the models and assumptions used to estimate 

maximum exposures. The scientific evidence therefore supports a finding that “there is not 

sufficient evidence to establish” that EGBE satisfies any of the three listing criteria of EPCRA 

Section 313(d). 

Delisting EGBE is also consistent with the policies and goals of the TRI program as 

articulated by EPA. As developed in Section 9.3, the Agency has emphasized the need to 

ensure that TRI listing decisions are consistent with “other EPA decisions on the same 

chemical, to the extent that such decisions relate to the same basic criteria for human health 

and the environment” (52 FR 5481). That consideration is especially important here because, as 

summarized in Table ES-2, human and environmental exposures are consistent with or less 

than those that formed the basis of the Agency’s November 2004 HAPs findings that releases of 

EGBE “may not reasonably be anticipated to cause any adverse effects to the human health” or 

“adverse environmental effects” (EPA 2004a, 69 FR 69322). By their terms, these findings 

encompass the health and ecotoxicity listing criteria of EPCRA Section 313(d) and, therefore, 

should be accorded considerable weight here. 

Delisting EGBE also would promote the goals of the TRI program by focusing 

community risk management and pollution prevention efforts on other chemicals that EPA has 

determined present significant human health and environmental risks (see Section 9.4). Of 

special importance in this regard is the fact that delisting would remove the current disincentive 

to the use of EGBE in waterborne coating formulations that have demonstrable environmental 

benefits in the form of substantial reductions in volatile organic compound (VOC) emissions. 

Deleting EGBE from the TRI reporting list also would maintain the credibility of the program by 

eliminating the confusion that currently results because facilities are inappropriately singled out 
5 

as major sources of “toxics” on the basis of EGBE releases that, as EPA has found, may not 

reasonably be anticipated to cause adverse human health or environmental effects. 

The case for deleting EGBE from the TRI reporting list, in sum, is straightforward and 

compelling. Because the delisting criteria of EPCRA Section 313(d) as interpreted by EPA are 

met, and because the local risk management and pollution prevention purposes of the statute 

would be well served by delisting, the Panel respectfully asks EPA to grant this petition. 
6 

1.0 INTRODUCTION 

This petition, submitted by the American Chemistry Council’s Ethylene Glycol Ethers 

Panel (the Panel) under Section 313(d) & (e) of the Emergency Planning and Community Rightto-Know Act (EPCRA), seeks the removal of ethylene glycol monobutyl ether (EGBE) from the 

list of chemicals subject to the reporting requirements of the Emergency Planning and 

Community Right-to-Know Act (EPCRA) Toxics Release Inventory (TRI) program. The 

Chemical Abstracts Service (CAS) number for EGBE is 111-76-2, and its chemical structure is 

illustrated in Figure 1-1 below. 

The American Chemistry Council is a trade organization for chemical manufacturers. 

The American Chemistry Council’s contact is Mr. Jonathon Busch, Director of the Ethylene 

Glycol Ethers Panel. He can be reached at the mailing address listed on the cover of this 

petition, by phone at 202-249-6725, or by e-mail at jon_busch@americanchemistry.com.

b 

Members of the Ethylene Glycol Ethers Panel are The Dow Chemical 

Company, Eastman Chemical, and LyondellBasell. Panel members Dow, Eastman, along 

with LyondellBasell account for all domestic manufacture of EGBE (SRI 2010). 

Section 313(d) of EPCRA (42 U.S.C. §11023(d)(2)(A)-(C) & (d)(3)) calls for the delisting 

of a chemical where “there is not sufficient evidence to establish” that— 

(A) The chemical is known to cause or can reasonably be 

anticipated to cause significant adverse acute human 

health effects at concentrations expected to exist beyond 

facility site boundaries as result of continuous or frequently 

recurring releases; 

(B) The chemical is known to cause or can reasonably be 

anticipated to cause in humans— 

(i) cancer or teratogenic effects, or 

b There is an underscore symbol between Mr. Busch’s first and last names within his email address. 

C

C O

C

C

C

H C

H H H

H

H H H

H H H O H

H H

Figure 1-1. Structure of Ethylene Glycol Monobutyl Ether (EGBE)
7 

(ii) serious or irreversible— 

 (I) reproductive dysfunctions, 

 (II) neurological disorders, 

(III) heritable genetic mutations, or 

(IV) other chronic health effects. 

 (C) The chemical is known to cause or can reasonably be 

anticipated to cause, because of— 

(i) its toxicity, 

(ii) its toxicity and persistence in the environment, or 

(iii) its toxicity and tendency to bioaccumulate in the 

environment, 

a significant adverse effect on the environment of sufficient 

seriousness, in the judgment of the Administrator, to 

warrant reporting under this section. 

This petition evaluates EGBE based on these criteria. In accordance with United States 

Environmental Protection Agency’s (EPA’s) interpretation of the EPCRA listing criteria (59 Fed. 

Reg. 61432 [EPA 1994a]), the petition presents in Section 3 a qualitative assessment of the 

potential hazards EGBE poses to human health and the environment. Because the hazard 

assessment supports the conclusion that EGBE presents a low potential for adverse human 

health and ecological effects, we also present in Sections 4 through 8 conservative 

assessments of potential human and environmental exposures resulting from facility releases of 

EGBE and how such exposures compare to highly protective criteria for preventing adverse 

human health and ecological effects. Specifically, the petition is organized as follows: 

Section 2 presents background information on the chemical identity of EGBE, regulatory 

history, current standards and guidelines, production, and use. 

Section 3 presents a qualitative evaluation of the potential human health and ecological 

hazards posed by EGBE: 

The physical and chemical properties of EGBE are reviewed, focusing on properties 

relevant to potential health and environmental effects including persistence and 

bioaccumulation. 

The human health hazard evaluation reviews and updates the current Integrated Risk 

Information System (IRIS) toxicological assessment of EGBE (EPA 2010) and the reviews 

appearing in the 2004 Hazardous Air Pollutants (HAPs) delisting decision (68 Fed. Reg. 65648 

[EPA 2003], 69 FR 69320 [EPA 2004a]) and in EPA’s (2005a) report, An Evaluation of the 

Human Carcinogenic Potential of Ethylene Glycol Butyl Ether. Acute and chronic health effects 

are addressed separately in order to directly evaluate EGBE against the first two listing criteria 

set forth in EPCRA Section 313(d)(2)(A) & (B). 

The ecological hazard evaluation likewise builds on the ecotoxicity assessments 

developed or approved by EPA in the HAPs rulemaking as well as a series of recent 

comprehensive reviews by the World Health Organization (WHO), the European Union (EU), 

and Environment Canada, all of which have reached similar conclusions about the low potential 

ecotoxicity of EGBE. 
8 

Section 3 closes with a review and application of EPA’s criteria for considering exposure 

in making TRI listing decisions under EPCRA (59 Fed. Reg. 61432 [EPA 1994a). The next five 

sections of the petition evaluate potential human and environmental exposures resulting from 

EGBE facility releases based on conservative modeling and highly protective criteria for 

preventing potential health and ecological effects. 

Section 4 describes the criteria used in this petition for evaluating chronic human 

exposures to EGBE, viz. the IRIS reference concentration (RfC) and reference dose (RfD). 

Section 5 follows the general approach used in the HAPs delisting decision by 

constructing an inventory of EGBE releases based on the 2009, 2010, and 2011 TRI reports for 

Certain Glycol Ethers, which provide the most up-to-date data available (the HAPs assessment 

was based largely on 1993 TRI data). 

Section 6 presents the screening approach used to evaluate both chronic and acute 

exposures. 

Chronic exposures are assessed by applying EPA modeling guidance to develop 

conservative estimates of maximum annual average concentrations of EGBE at or beyond 

facility fencelines and comparing those estimates against the IRIS RfC. Because estimated 

maximum annual average concentrations for all facilities in the 2009, 2010 and 2011 inventories 

are below the RfC based on unrealistically conservative screening assumptions, application of 

more sophisticated tiered modeling is unnecessary in this case under EPA (1992a) modeling 

guidelines. Nevertheless, tiered modeling is used for a sample of the highest EGBE-emitting 

facilities in order to estimate the degree of conservatism incorporated into the screening results. 

It should be noted, an examination of trends in maximum TRI-reported Certain Glycol Ether 

emissions from for reporting years from 2000 to 2011 (see Figure 5-1) indicated there has been 

remarkably little variability in the Certain Glycol Ether emissions from the highest emitting 

facilities over the past decade. 

Similar to the HAPs assessment, cumulative exposures from closely located sources of 

EGBE (i.e., within the same zip code) are evaluated. 

Acute exposures are assessed by developing conservative estimates of maximum 

hourly average concentrations of EGBE at or beyond facility fencelines for the highest emitting 

facilities (i.e. those facilities that did not screen out in two highly conservative prescreening 

steps). The resulting estimates of the maximum hourly EGBE concentration in ambient air for 

the facilities are evaluated using the Margin of Exposure (MOE) methodology EPA has used in 

previous TRI listing decisions, using the no observed adverse effect level (NOAEL) derived from 

human data in Section 3 of the petition. 

Section 7 evaluates human health exposure and risks associated with EGBE in surface 

water against the IRIS RfD. Again, the same models and assumptions used in the HAPs 

assessment are employed here, updated to reflect the surface water concentration modeled 

from 2010 TRI release data, the most recent version of the Mackay fugacity model (EQC v2.02; 

CEMC 2003), and current EPA (2004b) guidance for dermal risk assessment. Potential 

exposures were evaluated based on 2009, 2010, and 2011 TRI release data but the human 

health exposure assessment was conducted with the 2010 TRI data because they represented 
9 

the worst-case scenario from the recent TRI data. The estimated exposures based on these 

data are well below the RfD. 

Section 8 presents an ecological risk assessment (ERA) for EGBE, based on the 

models and assumptions used in the HAPs assessment, EGBE releases to air, land, and water 

as reported in the 2009, 2010, and 2011 TRI, and a supplemental literature review to identify 

appropriate target species and toxicity reference values (TRVs). 

Section 9 presents a summary of the hazard, exposure, and risk assessments 

developed in the preceding sections, identifies the elements of conservatism built into these 

assessments, and evaluates the results under the listing/delisting criteria of EPCRA Section 

313(d)(2). In addition, EPA policies for the interpretation and administration of the TRI program 

are reviewed, and other considerations relevant to the question of whether to delist EGBE are 

discussed. 

References are listed in Section 10, and five appendices provide detailed data and 

analysis that form the basis for the hazard, release inventory and exposure assessments 

described in Sections 3 through 8. Appendix A tabulates laboratory bioassay studies of EGBE, 

including the compilation published in the 1998 Agency for Toxic Substances and Disease 

Registry (ATSDR) toxicological profile of EGBE, and a table of subsequent studies. Appendix B

is the emissions inventory. Appendix C presents the chronic screening results for airborne 

emissions. Appendix D provides results of a quantitative uncertainty analysis, which 

demonstrates the health protectiveness of the overall approach to evaluating inhalation 

exposures. Appendix E presents the acute screening results for airborne emissions. Finally, 

Appendix F, provided as electronic files on CDROM, are the model output files from both the 

Tier 2 and Tier 3 modeling. 
10 

2.0 BACKGROUND 

This section provides background information on EGBE (CAS 111-76-2), including a list 

of synonyms, history of EGBE regulation, regulatory standards and guidelines, chemical and 

physical properties, and production and use. 

2.1 Synonyms 

EGBE has many synonyms (NICNAS 1996, HSDB 1997, ECETOC 1994), including: 

 2-butoxyethanol

 2-butoxy-1-ethanol

 2-BE

 2-n-butoxyethanol

 3-oxa-1-heptanol

 beta-butoxyethanol

 butoxyethanol

 butyl glycol

 butyl glycol ether

 ethanol 2-butoxy

 ethylene glycol butyl ether

 ethylene glycol monobutyl ether

 ethylene glycol mono-n-butyl ether

 ethylene glycol n-butyl ether

 glycol butyl ether

 glycol monobutyl ether

 monobutyl ethylene glycol ether

 monobutyl glycol ether

 n-butoxyethanol

 o-butyl ethylene glycol

EGBE is marketed in the United States under various trade names, including: 

 Eastman® EB Solvent

 Butyl CELLOSOLVE® Solvent

 Butyl OXITOL®

 DOWANOL® EB

 Ektasolve EB

 Glycol Ether EB

 Poly-Solv EB

2.2 History of EGBE Regulation under EPCRA 

EGBE is regulated under EPCRA because it is a member of the “Certain Glycol Ethers” 

category of chemicals as currently defined in the TRI. Regulation of glycol ethers is an 

outgrowth of developmental studies conducted or sponsored by industry in the late 1970s and 

early 1980s. Subsequently, the National Institute of Occupational Safety and Health (NIOSH) 

concluded that two glycol ethers—ethylene glycol monomethyl ether (EGME) and ethylene 

glycol monoethyl ether (EGEE)—had the potential to cause adverse reproductive, embryotoxic, 

and teratogenic effects in laboratory animals (NIOSH 1983). Several state regulatory agencies 

assumed that the effects observed in EGME and EGEE were applicable to all glycol ethers. 

Thus, as a result of the 1983 NIOSH findings, the Maryland Department of Environmental 

Protection included glycol ethers in a list of chemicals for which it planned to collect use 

information (Maryland 1985). Maryland’s list of chemicals was subsequently incorporated into 
11 

the Section 313 list of Title III of the Superfund Amendment and Reauthorization Act of 1986 

(SARA), or EPCRA. Glycol ethers were initially defined as chemicals with the formula, 

R-(OCH2CH2)n-OR ́ Eqn. 1 

where: 

R = alkyl or aryl groups 

R ́ = R, H, or groups which, when removed, yield glycol ethers with the structure: 

 R-(OCH2CH2)n-OH 

n = 1, 2, or 3. 

In 1994, EPA redefined the glycol ether category to exclude compounds having alkyl 

chains of more than seven carbon members in length (59 FR 34386 [EPA 1994b]). The 

redefinition eliminated the need for nonionic surfactant manufacturers and users to report 

emissions of those chemicals to the TRI. As a result, the category, which is now called “Certain 

Glycol Ethers,” is defined as follows (http://www.epa.gov/ttn/atw/glycol2000.pdf): 

R-(OCH2CH2)n-OR ́ Eqn. 2 

where: 

n = 1, 2, or 3 

R = alkyl C7 or less; or 

R = phenyl or alkyl substituted phenyl; 

R ́ = H, or alkyl C7 or less; or 

OR ́ consisting of carboxylic acid ester, sulfate, phosphate, nitrate, or sulfonate. 

2.3 Removal of EGBE from the Clean Air Act HAPs List 

In the 1990 Amendments to Clean Air Act (CAA), Congress expanded the list of HAPs, 

based on the EPCRA Section 313 list and other compilations of chemicals, to include the glycol 

ether category. EGBE remained on the CAA HAPs list, as part of the glycol ethers category, 

until it was delisted on November 29, 2004 (69 FR 69320 [EPA 2004a]). The Administrator’s 

HAPs delisting decision granted our 1997 petition (CMA 1997),c which used 1993 TRI data (and 

other sources of information on potential sources) and exposure modeling adapted from EPA 

(1992a) modeling guidance to demonstrate that maximum EGBE exposures fall below IRIS 

reference values. Additionally, we prepared an ERA, also in accordance with EPA guidelines, 

showing that EGBE releases are not reasonably anticipated to pose adverse effects on the 

environment. 

The delisting provision of Section 112(b)(3)(C) of CAA [42 U.S.C. §7412(b)(3)(C)] is 

substantively at least as broad and stringent as that in EPCRA. The CAA provides that a 

chemical may be removed from the HAPs list if EPA finds that: 

c

At that time, the American Chemistry Council was known as the Chemical Manufacturers Association (CMA). 
12 

there is adequate data on the health and environmental effects of 

the substance to determine that emissions, ambient 

concentrations, bioaccumulation of deposition of the substance 

may not reasonably be anticipated to cause any adverse effects to 

the human health or adverse environmental effects. 

In reviewing and granting our HAPs delisting petition, EPA reevaluated the adequacy of 

the existing IRIS reference values by examining scientific data published after the 1999 IRIS 

assessment (EPA 1999a), including new toxicological studies addressing the relevance of 

limited rodent carcinogenicity data to humans, and conducted supplemental exposure modeling 

on some of the issues raised by the petition (discussed in greater detail below). The Agency’s 

review of the scientific record included a series of findings that should weigh heavily in the 

evaluation of this petition to remove EGBE from EPCRA’s TRI reporting list. 

First, with respect to the potential human health effects of EGBE exposure, EPA 

reaffirmed the adequacy of the previous IRIS RfC (13 milligrams per cubic meter [mg/m3]) and 

RfD (0.5 milligrams per kilogram body weight per day [mg/kg BW-day]) as protective against all 

known or potential human health effects of EGBE, including any potential sensitive 

subpopulations (68 FR 65654, 65656 [EPA 2003]). This review included a reevaluation of the 

1999 IRIS carcinogenicity assessment, which had concluded, under the then-current EPA 

(1986a) Guidelines for Carcinogen Risk Assessment, that EGBE is a “possible human 

carcinogen based on limited laboratory animal evidence and a lack of human studies” (EPA 

1999a). Based on post-IRIS toxicological studies testing the relevance of the limited animal 

findings to humans, EPA concluded that the previous IRIS “RfC and RfD values for EGBE have 

been set at levels that prevent ... the precursor events that would lead to tumors” in rodents. 

The Agency found, accordingly, that even if the rodent tumor findings are relevant to humans at 

all, “we would not expect to find these tumors in humans following environmental exposures” 

(69 FR 69322). 

Second, EPA found “the petition’s overall approach to exposure assessment to be 

acceptable” (68 FR 65653), and made the following specific determinations. 

The use of the 1993 TRI database to construct a complete list of emitting sources and 

emission levels “provides an adequate basis for dispersion modeling and the exposure 

assessment and is acceptable for that purpose” (68 FR 65652). 

The five-tier modeling approach used in our HAPs petition to evaluate maximum 

inhalation exposures “followed appropriate modeling guidance” and “would tend to overestimate 

rather than underestimate maximum annual ambient average concentrations” (68 FR 65652). 

EPA also observed that the modeling and assumptions used to assess ingestion and 

dermal exposures arising from surface water levels of EGBE, including supplemental analyses 

conducted by the Agency, were “conservative,” and the exposure estimates found to be below 

the IRIS RfD represented a “worst-case exposure scenario” (68 FR 65653-54). 

Third, EPA’s evaluation of potential environmental risks included the development of its 

own ERA, which was based in part on the same “worst-case exposure scenario” for predicted 

maximum surface water concentrations used in the evaluation of human ingestion and dermal 
13 

exposures. In addition, the Agency noted that the TRVs for small mammals and aquatic species 

used in the ERA “were derived from very minor effects which were unlikely to be ecologically 

significant at the population level of ecological organization” (68 FR 65657). 

Based on these and other findings, EPA concluded that maximum exposures to EGBE 

fall well below the IRIS RfC and RfD, as well as the TRVs developed to assess ecological risks. 

The Administrator (69 FR 69322) summarized the basis for the HAPs delisting of EGBE as 

follows: 

We can therefore conclude with confidence that emissions, 

ambient concentrations, bioaccumulation, or deposition of EGBE 

may not reasonably be anticipated to cause any adverse effects to 

the human health. 

Likewise, EPA found, based on the ERA, that “there are adequate data on 

environmental effects of EGBE to determine that ambient concentrations, bioaccumulation, or 

deposition of EGBE are not reasonably anticipated to cause adverse environmental effects” (68 

FR 65657). 

2.4 Regulatory Standards and Guidelines 

Federal and state regulatory standards and guidelines for EGBE are listed in Table 2-1. 

2.5 Production and Use 

As described by ATSDR (1998), ethylene glycol monoalkyl ethers are not manufactured 

as pure compounds but must be separated from the diethers and higher glycols (NTP 1993, as 

cited in ATSDR 1998; NIOSH 1990, as cited in ATSDR 1998). There are two common methods 

of producing EGBE: (1) reaction of ethylene oxide with anhydrous butyl alcohol in the presence 

of a catalyst, and (2) direct alkylation of ethylene chlorohydrin or ethylene glycol using sodium 

hydroxide and an alkylating agent such as dibutyl sulfate (HSDB 1997, as cited in ATSDR 1998; 

NIOSH 1990, as cited in ATSDR 1998; Rowe and Wolf 1982, as cited in ATSDR 1998). By far, 

the dominant method of EGBE production is treatment of butyl alcohol with ethylene oxide. 

Three facilities—Dow Chemical USA’s Seadrift, Texas plant, Eastman Chemical 

Company’s Longview, Texas plant and Equistar Chemicals, LP’s Bayport Texas plant—produce 

all domestic EGBE (SRI 2010). Between 1970 and 2009, production of EGBE in the United 

States increased by nearly five-fold from 53,500 tons per year (tpy) to approximately 250,000 

tpy (Figure 2-1, SRI 2010). Between 1999 and 2007, however, production of EGBE has 

fluctuated between 254,500 and 292,000 tpy, without showing a clear increase in production 

from year to year (SRI 2010). There was a 14% decrease in production of EGBE between 2007 

and 2009 (SRI 2010). The overall average annual growth rate in EGBE production is expected 

to be 2.8% between 2009 and 2014 (SRI 2010). 

Because of its favorable physical, chemical, and technical characteristics, EGBE has 

become the largest volume glycol ether consumed in the United States (SRI 2010). In 2009, 

United States consumption of EGBE was 135,000 tpy, which represents approximately 52% of 

all ethylene glycol ethers consumed (SRI 2010). This rate of consumption of EGBE represents a 
14 

1% increase since 1990, when consumption was 132,000 tpy (SRI 2010). During the economic 

recession in 2008-2009, the United States EGBE consumption dropped 19% from 166,500 tpy 

to 133,500 tpy between 2007 and 2009. The overall average annual growth rate of domestic 

EGBE consumption was expected to be 3.1% between 2009 and 2014 (SRI 2010). Because 

this growth in consumption is predicted to outpace growth in production, a concurrent decrease 

in exports was expected (SRI 2010). 

Despite growth in consumption since 1990, overall nationwide emissions of Certain 

Glycol Ethers to all media have decreased from 26,782 tpy in 1990 to 7,229 tpy in 2011, a 

reduction of 70% (www.epa.gov/triexplorer). The reduction in emissions is likely attributable 

principally to increased regulation under the CAA and state air pollution laws; corporate product 

stewardship programs (some no doubt in response to “right-to-know” initiatives like EPCRA 

itself); and the 1994 redefinition of the Certain Glycol Ethers category, which removed nonionic 

surfactant glycol ethers from the chemicals covered by the listing. 

Of the 135,000 tpy of EGBE consumed in the United States in 2009, 68,500 tons (51%) 

were used as solvents in paints, coatings, and inks (SRI 2010). In addition, 20,500 tons (15%) 

were used as solvents in metal cleaners and liquid household cleaners and 29,000 tons (21%) 

were used as solvents in other products (SRI 2010). Consumption of EGBE as a chemical 

intermediate in the production of 2-butoxyethyl acetate (EGBEA) accounted for 9,000 tons (7%) 

of EGBE consumption (SRI 2010). Consumption for production of other chemicals [including 

tris(2-butoxyethyl)phosphate, di(2-butoxyethyl)adipate and di(2-butoxyethyl)phthalate] 

accounted for another 7,500 tons (6%) of EGBE consumption (SRI 2010). 

Approximately 80% of EGBE consumed in surface coatings is used for industrial and 

specialty coatings; the remainder is used in architectural coatings (SRI 2010). Industrial 

coatings are defined as coatings that are factory-applied to manufactured goods as part of the 

production process (SRI 2004). They are also known as original equipment manufacturing 

(OEM) coatings. OEM coatings that contain EGBE include automotive paints, lacquers, quick 

drying varnishes, and enamels. Other industrial paints and coatings that employ EGBE include 

(1) coatings for metal cans and coils, ships, trucks, buses, and farm machinery and (2) paints 

and finishes for wood products, metal furniture, and fixtures (NPCA 1997, as cited in SRI 2004). 

Specialty coatings are those that are used primarily where durability is a key objective. Specialty 

coatings include high performance maintenance coatings, automotive refinishing paints, and 

aerosol paints (NPCA 1997, as cited in SRI 2004). Architectural coatings are paints and 

coatings that are applied onsite to new and existing residential, commercial, institutional, and 

industrial buildings. These products are generally distributed through retail and wholesale 

outlets and are bought by consumers, painters, contractors, builders, and government agencies 

(NPCA 1997, as cited in SRI 2004). 

The following are source categories that use EGBE and thus are potentially affected by 

this petition: 

 Auto and light duty truck (surface coating)

 Leather tanning and finishing operations
15 

 Manufacture of paints, coatings, and adhesives

 Metal can (surface coating)

 Metal coil (surface coating)

 Metal furniture (surface coating)

 Printing, coating, and dyeing of fabrics

 Printing/publishing (surface coating)

 Wood furniture (surface coating)

 Synthetic organic chemical manufacturing

 Ship building and repair (surface coating)

 Semiconductor manufacturing
16 

3.0 HAZARD ASSESSMENT 

Given EGBE’s (CAS 111-76-2) widespread use (as detailed in Section 2.5), it has 

undergone extensive toxicological testing in laboratory animals. Animal bioassay data are 

supplemented by information from case reports of intentional human ingestion episodes and 

controlled human exposure experiments, as well as ecotoxicological testing on microbes, plants, 

and aquatic organisms. EGBE has been tested for acute, subchronic, and chronic toxicity, 

reproductive and developmental toxicity, immunotoxicity, genotoxicity, and carcinogenicity. 

Although no toxicity data are available for terrestrial wildlife or birds, acute and chronic toxicity 

tests have been performed on a variety of aquatic organisms. 

The extensive database on the potential adverse human health effects of EGBE is 

reviewed in the EGBE IRIS assessment (EPA 2010) and the ATSDR toxicological profile of 

EGBE (ATSDR 1998). EGBE’s potential ecological hazards have been extensively reviewed in 

a series of assessments by WHO the Concise International Chemical Assessment Document or 

CICAD (WHO 1998, 2010), EU (INERIS 2006), and Environment Canada (2002). These 

assessments provide the starting point and primary basis for the qualitative hazard assessment 

presented in this section of the petition, supplemented as appropriate by descriptions of 

subsequently published studies. 

3.1 Chemical and Physical Properties 

EGBE’s chemical and physical properties, excerpted from the ATSDR toxicological 

profile for EGBE (ATSDR 1998), are summarized in Table 3-1. Additional information and 

implications of these properties are discussed in this subsection. 

EGBE is considered “readily” biodegradable (Price et al. 1974, as cited in ATSDR 1998) 

and has a relatively short residence time in the environment. Its half-life in both surface water 

and soil ranges from 7 days to 4 weeks, while its half-life in groundwater is 14 days to 8 weeks, 

and its half-life in the atmosphere is approximately 3.3 hours to 33 hours (Howard et al. 1991, 

as cited in ATSDR 1998). 

EGBE is highly mobile in soil and unlikely to partition from the water column to organic 

matter contained in sediments or suspended solids (Swann et al. 1983). The volatilization of 

EGBE from surface water and moist soil is slow (Lyman et al. 1982, as cited in ATSDR 1998). In 

the atmosphere, EGBE is expected to exist almost entirely in the vapor phase, although EGBE 

may be physically removed from air by precipitation (Eisenreich et al. 1981, as cited in ATSDR 

1998). The Hazardous Substance Data Bank (HSDB; http://toxnet.nlm.nih.gov) reports that an 

estimated bioconcentration factor (BCF) of 3 was calculated for EGBE, concluding that the 

potential for bioconcentration in aquatic organisms is low. 

The most important mechanism of removal of EGBE from aerobic soil and water is 

microbiotic degradation (ATSDR 1998). Concentrations of EGBE of less than 500 milligrams per 

liter (mg/L) were readily degraded by microorganisms in bench scale degradation tests using 

domestic activated sludge, with reported biodegradation rates of greater than 63% after three 

days and 100% after five days (Assessment Technologies, Inc. 1996). A 20-day biological 
17 

oxygen demand (BOD) test and an aerobic degradability 28-day closed bottle test resulted in 

EGBE degradation rates of 75% and 88% respectively (NICNAS 1996). 

Because EGBE does not undergo hydrolysis or direct photolysis in aquatic environments 

(Howard 1993, as cited in ATSDR 1998), abiotic degradation processes are assumed to play a 

negligible role in determining the ultimate fate of EGBE in surface water, groundwater, and soil. 

However, Atkinson (1987) calculated an atmospheric half-life of 17 hours for EGBE based on a 

second order photooxidation rate of 2.3 x 10-11 cubic centimeters (cm3)/molecules-second. 

Therefore, abiotic degradation can significantly affect the fate of EGBE in air. 

Limited data are available regarding degradation products of EGBE. The intermediate 

products of aerobic biodegradation were not identified in any of the screening tests considered 

by ATSDR (1998). However, as observed in human and animal studies (Johanson et al. 1989, 

as cited in ATSDR 1998), 2-butoxy-ethanol acetate (BAA) may enzymatically hydrolyze to 

EGBE and acetic acid as a result of biodegradation. By analogy to animal metabolism 

(Ghanayem et al. 1987, as cited in ATSDR 1998), it is possible that any EGBE formed through 

enzymatic hydrolysis may undergo further enzymatic oxidation (e.g., via dehydrogenase) to the 

butoxyacetaldehyde and finally to 2-butoxyacetic acid before being degraded to carbon dioxide 

and water. The reported products of photodegradation of EGBE in the atmosphere are 

propionaldehyde (CAS 123-38-6), butyraldehyde (CAS 123-72-8), butyl formate (CAS 592-84-

7), 2-hydroxyethyl formate (CAS 628-35-3), 3-hydroxybutyl formate, 2-hydroxybutyl formate, 

and an organic nitrate (Tuazon et al. 1998, as cited in INERIS 2005). No data are available on 

the anaerobic degradation products of EGBE. 

Given its relatively short residence time in the atmosphere, high water solubility, low 

octanol-water partition coefficient (Kow), and low vapor pressure (Table 3-1), EGBE released to 

the atmosphere partitions to surface water and soil. The Mackay fugacity model predicts that, 

although approximately 99% of EGBE released to the environment is released to the air, 

approximately 98% of the EGBE released partitions into soil and surface water at equilibrium 

(Section 8.2.2, below; Cadmus 2000a). 

3.2 Potential Human Health Hazards 

In this section, we briefly describe the pertinent information available on the potential 

health effects of human exposure to EGBE, both noncancer effects from brief (acute) and 

repeated (subchronic and chronic) exposures, and information on the potential carcinogenicity 

of EGBE. 

3.2.1 Noncancer Toxicity 

EGBE is well absorbed via the inhalation, dermal, and oral routes of exposure and is 

widely distributed throughout the body and metabolized primarily via alcohol dehydrogenase to 

BAA, which is rapidly excreted in urine. Studies in humans and rats indicate that the metabolic 

pathways are similar for both species. However, in humans, unlike rats, some BAA is 

conjugated with glycine or glutamine prior to excretion, while rats also have a minor oxidation 

pathway involving O-dealkylation by a cytochrome P450 dealkylase (CYP 2E1) that is not 
18 

involved in human metabolism of EGBE (EPA 2010). The following subsections describe the 

acute and chronic health effects of EGBE. More detailed information on these effects is 

available in the ATSDR (1998) and EPA (2010) toxicology profiles. 

3.2.1.1 Acute Toxicity 

EGBE’s acute toxicity has been evaluated in a number of studies in experimental 

animals, with the oral lethal dose to 50% of the test population (LD50) ranging from 320 to 3,000 

milligrams per kilogram (mg/kg) (ACGIH 2003). The oral LD50 values vary depending on the 

species, sex, and age of the test animals. The order of sensitivity from the most to the least 

sensitive is: rabbits (320 mg/kg) > adult rat (560 mg/kg) > mouse (1,230 mg/kg) > rat weanling 

(3,000 mg/kg). By inhalation, the lethal concentration for 50% of test organisms (LC50) has been 

reported as 700 parts per million (ppm) in mice exposed for seven hours, and 486 ppm in rats 

exposed for four hours (ACGIH 2003). Severe hemolysis and hemoglobinuria are primary signs 

in rodents near these lethal levels, but humans are much less sensitive to the hemolytic effects 

of EGBE than rodents. In a series of three studies reported by Carpenter et al. (1956), small 

groups of humans and rats were exposed concurrently for four hours to 113 ppm (547 mg/m3) 

EGBE; for two 4-hour periods separated by a 30-minute break to 195 ppm (944 mg/m3); or for 

eight hours to 100 ppm (484 mg/m3). While the rats showed increased red blood cell fragility, no 

increase in red blood cell fragility was seen in the humans, although they did experience nasal 

and ocular irritation. Increased red blood cell fragility has been reported in rats at airborne 

concentrations as low as 62 ppm (300 mg/m3) (Carpenter et al. 1956). Similarly, acute ingestion 

of EGBE at doses as low as 32 mg/kg produced red blood cell hemolysis in adult rats 

(Ghanayem et al. 1987, NTP 2000, Long et al. 2000, Nyska et al. 1999, while no hemolytic 

effects were seen in a case of attempted suicide by ingestion of EGBE solution providing a dose 

of EGBE of 1,100 to 1,500 mg/kg (Gualtieri et al. 1995). 

In vitro studies confirm that rat red blood cells are extremely sensitive to the hemolytic 

effects of EGBE’s primary metabolite, BAA, particularly compared to human red blood cells. In 

studies with blood from rats, dogs, rabbits, and humans, hemolysis occurred in rat red blood 

cells at BAA concentrations of 0.05% (500 mg/L) or more in normal saline, while red blood cells 

from dogs, rabbits, and humans did not undergo hemolysis at BAA concentrations up to 2% or 

20,000 mg/L (ICI 1985, as cited in CIR 1996). Similarly, Bartnik et al. (1987) reported complete 

hemolysis of rat red blood cells within one hour at 7.5 millimolar (mM) BAA or about 875 mg/L, 

and 20% hemolysis at 2.5 mM (about 300 mg/L). In contrast, human red blood cells showed no 

hemolysis at the highest concentration tested, 15 mM (1,750 mg/L), even after two hours of 

exposure, while rat red blood cells had 2% hemolysis at a concentration as low as 1.25 mM 

(about 150 mg/L). The same authors also found a more modest difference in sensitivity to the 

parent EGBE. Exposure of rat red blood cells to 200 mM (about 23,000 mg/L) EGBE produced 

100% hemolysis within 30 minutes, but the same concentration produced no hemolysis of 

human red blood cells in 30 minutes, although it did cause 100% hemolysis after 2 hours of 

exposure, as did 30 minutes exposure of human erythrocytes to a higher concentration (250 

mM or 30,000 mg/L) of EGBE (Bartnik et al. 1987). Similarly, Ghanayem and Sullivan (1993) 
19 

observed no effect on mean corpuscular volume (MCV) or hematocrit in vitro in human red 

blood cells exposed to concentrations of BAA causing 50% to 60% increases in these 

parameters in rat red blood cells. 

Udden (2002) reported similar patterns of changes in red cell rigidity and MCV in rat and 

human red blood cells exposed to 100-fold different concentrations of BAA; rat red blood cells 

were 100-fold more sensitive than human red blood cells to these effects. Physiologically based 

pharmacokinetic (PBPK) modeling (Corley et al. 1994) predicts that the acute exposures 

necessary for such concentrations of BAA are unlikely even in consumer product or 

occupational settings (Udden 2002, ACGIH 2003), much less in the ambient air near EGBEemitting facilities, where limited empirical data as well as estimates based on air quality 

modeling indicate that concentrations well below 1 mg/m3 are likely (WHO 2010, INERIS 2006; 

EPA 2003). 

Because of what the American Conference of Governmental Industrial Hygienists 

(ACGIH) has called the “minimal potential for 2-butoxyethanol exposures to produce red blood 

cell hemolysis in humans as compared to rats,” assessments of acute health hazards have 

defined mucous membrane irritation of the nose and eye as the critical effect of short-term 

exposures in humans, not hemolytic effects (CalEPA 1999, ACGIH 2003). As already 

mentioned, Carpenter et al. (1956) found that four adult male volunteers exposed to 113 ppm 

(550 mg/m3) EGBE for four hours, and two men and two women exposed to 100 ppm (485 

mg/m3) for eight hours reported eye, nose, and throat irritation. Erythrocyte osmotic fragility and 

urinalysis were normal in the subjects during and after exposure, and no other evidence of 

systemic toxicity was found. In another study (Johanson et al. 1986), seven healthy male adults 

were exposed to 20 ppm (97 mg/m3) EGBE in a chamber experiment designed to assess 

pulmonary uptake and metabolism of EGBE during light exercise. The authors reported that 

none of the subjects complained or showed any adverse effects from two hours of exposure. As 

described in detail in Section 6, the short-term Tier 3 modeling results indicate that ambient 

concentrations near EGBE-emitting facilities are at least a factor of 5 below the NOAEL in this 

study. Hence, no acute toxic effects due to EGBE are likely adjacent to EGBE-emitting facilities. 

3.2.1.2 Subchronic and Chronic Toxicity 

The 2010 IRIS assessment directly addresses the subject of the subchronic and chronic 

toxicity of EGBE, concluding that it is not immunotoxic, genotoxic, or teratogenic, and does not 

cause adverse reproductive effects of the sort that have been attributed to EGME and EGEE 

(EPA 2010). There was no reduction in the immune response to injected antigens in two studies 

in rats exposed to EGBE at up to 500 mg/kg BW-day, for up to 21 days (EPA 2010). EGBE had 

negative results in tests for genotoxicity in multiple studies: Salmonella typhimurium bacteria, 

Chinese hamster ovary cells (gene mutation, sister chromatid exchange, and chromosome 

aberration assays), and in vivo mouse micronucleus assay. Weakly positive, but not 

reproducible, responses were seen in a few in vitro studies, but EPA has determined in the IRIS 

assessment (EPA 2010) and the HAPs delisting decision (68 Fed. Reg. 65655 [EPA 2003]), that 

the overall weight of evidence indicates that EGBE is neither mutagenic nor clastogenic. 
20 

As summarized in the IRIS assessment (EPA 2010), EGBE has been extensively tested 

for reproductive and developmental effects by oral and inhalation exposure in rats, mice, and 

rabbits. While some generalized toxicity was seen at high exposure levels associated with 

EGBE’s hematologic effects, there was no indication of the specific reproductive effects 

attributed to EGME and EGEE, and no adverse effects on reproduction or development at 

doses below those associated with hematologic effects (EPA 2010). These studies support the 

conclusion that hemolysis is the most sensitive toxicity endpoint for rodents from a variety of 

exposure routes (EPA 2010). 

The extensive EGBE animal toxicology database lacks any indication of neurotoxicity. 

Human experience indicates that intentional ingestion of large amounts of EGBE (i.e., suicide 

attempts) can result in coma, possibly secondary to metabolic acidosis, but exposure from 

normal use has not resulted in any reports of potential neurotoxicity. Specific neurotoxicology 

studies have been performed in animals by standard testing guidelines for three other ethylene 

glycol ethers (diethylene glycol butyl ether [DGBE], triethylene glycol methyl ether [TGME], and 

ethylene glycol monopropyl ether [EGPE]) and none of these studies have indicated a concern 

for neurotoxicity. Any neurotoxicity testing of EGBE would be constrained by the well-known 

hemolytic effects in rodents that would limit the highest dose that could be tested. 

As described in the IRIS assessment, intravascular red blood cell hemolysis is the 

primary response in sensitive species following inhalation, oral, or dermal exposure to EGBE 

(EPA 2010). This primary hemolytic effect may also result in secondary toxic effects in spleen, 

liver, kidney, bone marrow, and thymus. However, hemolysis is the effect seen at the lowest 

exposure levels—i.e., it is the most sensitive endpoint (EPA 2010). The IRIS assessment 

concludes, therefore, that prevention of hemolysis will also be protective for all other toxic 

effects. Review of the recent research on the hemolytic effects of EGBE has led EPA (2010) to 

draw the following conclusions, apart from contact-site irritant effects. 

 Other effects resulting from EGBE are secondary to hemolysis.

 The primary metabolite of EGBE, BAA, is the proximate toxicant.

 Several species including humans are less sensitive than rats to the hemolytic effects of

BAA.

 Groups who might be thought to be more sensitive than average (including children, the

elderly, or those with congenital hemolytic diseases) do not show an increased hemolytic

response to BAA.

3.2.1.3 Relative Insensitivity of Humans to EGBE’s Hemolytic Effects 

It is important to note that EGBE is an exception to the general default assumption that 

humans are as sensitive as or more sensitive than the most sensitive animal species. In the 

case of EGBE, substantial rigorous data exist that demonstrate that humans are much less 

sensitive to the critical hemolytic effects of EGBE and its metabolite, BAA. The IRIS assessment 

describes six published PBPK models for EGBE. Employing the Corley et al. (1994, 1997) 

model, which allows both EGBE and BAA to be modeled in both humans and rats, EPA (2010) 

calculated tissue dose (BAA in blood) as a function of EGBE dose, route, and species. The 
21 

model demonstrated that prehemolytic changes in rat red blood cells occur at less than 1% of 

the level at which such changes are observed in human red blood cells. In the study used as the 

basis for the RfC and RfD, for example, the EGBE lowest observed adverse effect level 

(LOAEL) for prehemolytic changes in rat red blood cells, 31 ppm, 6 hours/day, 5 days/week was 

predicted to produce a peak blood concentration of BAA of 0.167 mM (EPA 2010). As noted 

earlier, Bartnik et al. (1987) reported no hemolysis of human red blood cells exposed to BAA 

levels almost 100 times higher (i.e., 15 mM) for three hours in vitro. 

Udden’s (2002) comprehensive study supports a susceptibility factor for rats as 

compared to humans of at least 100 (i.e., humans are at least 100times less sensitive than 

rats). Udden (2002) used a series of more specific and sensitive indicators of subhemolytic 

effects to quantify the difference in susceptibility to BAA of rat and human erythrocytes. Rat red 

blood cells were exposed to BAA at concentrations of 0, 0.025, 0.050, 0.075 and 0.1 mM, about 

an order of a magnitude lower than those used in previous work by Ghanayem (1989). 

Heparinized blood samples obtained from healthy adult volunteers were exposed to BAA at 

concentrations of 0, 2.5, 5.0, 7.5 and 10 mM, concentrations 100 times greater than those used 

for rat erythrocytes. The indices used to evaluate subhemolytic changes caused by BAA 

included microhematocrit, hemoglobin, red blood cell count, percent hemolysis determined by a 

colorimetric procedure, MCV calculated from microhematocrit and red blood cell count, 

distribution of red blood cell size, red cell deformability, erythrocyte osmotic fragility, erythrocyte 

density and red blood cell morphology. 

For each of these measures of prehemolytic effects, Udden (2002) found that human 

blood was at least 100 times less sensitive than rat blood. Specifically, a significant change in 

human erythrocyte deformability was observed at 7.5 and 10 mM while in rat a significant 

change was first seen at 0.05 mM. There was a comparable increase in human and rat red 

blood cell size at concentrations of 10 mM and 0.1 mM BAA, respectively. BAA did not 

significantly affect the osmotic fragility of human erythrocytes until reaching concentrations 

greater than 7.5 mM, while significant effects were noted in rat erythrocytes at BAA 

concentrations as low as 0.05 mM. Cell density was also markedly decreased in rat erythrocytes 

treated with 0.1 mM BAA while only slight effects were noted in human erythrocytes treated with 

10 mM BAA. Finally, no changes were noted in the morphology of the human erythrocytes 

treated with 10 mM BAA while rat erythrocytes treated with 0.1 mM showed increased numbers 

of spherocytes compared to controls. Udden (2000) previously demonstrated that 

“[S]tomatocytes, cup-shaped cells, and spherocytes are the principal morphological features of 

erythrocytes from rats exposed [in vivo] to [EGBE], or in vitro exposure to BAA.” 

Udden (2002) also conducted investigations on the blood from 11 more healthy subjects 

as well as hospitalized children and adults treated with 10 mM BAA. There was a slight increase 

in hemolysis in the samples from hospitalized adults, but the degree was not considered 

physiologically significant and was no greater than the hemolysis seen in the controls of the 

healthy adults. No difference was seen in the degree of hemolysis of the BAA treated 

erythrocytes of children. These findings are consistent with previous work by Udden (1994) 

showing that erythrocytes from potentially sensitive populations of humans, including young and 
22 

elderly subjects as well as those suffering from sickle cell disease and hereditary spherocytosis, 

were resistant to the hemolytic effect of BAA. 

The findings of Udden (2002) are supported by Gualtieri (1995), who reported actual 

data from suicide attempts by an individual whose blood concentration reached at least 4.9 mM 

BAA with no evidence of hemolysis. The Corley et al. (2005) PBPK model also predicts that the 

level of BAA in humans exposed continuously by inhalation to an EGBE-saturated atmosphere 

(greater than 1,000 ppm)d would result in maximum blood concentrations of BAA of just 2 mM, 

well below the level needed to produce hemolysis in human red blood cells (Udden 2002, EPA 

2010). 

These observation and modeling predictions imply that it would be physically impossible 

to achieve a blood concentration of BAA in humans high enough to cause the critical toxic effect 

of EGBE in rodents, hemolysis, via inhalation of EGBE vapor, further confirming its low toxicity 

potential in humans. 

The low hemolytic potential of EGBE in humans is further supported by the limited data 

on the effects of ingestion of EGBE by humans. EPA (2010) summarizes several cases of 

suicide attempts involving ingestion of large quantities of mixtures containing EGBE. These 

cases rarely resulted in hemolysis, despite ingestion of doses of EGBE as high as 1,500 mg/kg 

in some cases. Hematuria was noted in a couple of cases, but it is unclear whether this was due 

to hemolysis caused by EGBE and its metabolite BAA, or if it was secondary to the metabolic 

acidosis that developed at these high doses. 

3.2.2 Potential Carcinogenicity 

The National Toxicology Program (NTP) (2000) evaluated the carcinogenicity of EGBE 

in rats and mice exposed by inhalation. NTP (2000) reported that its study results indicate no 

evidence of carcinogenic activity in male F344/N rats and equivocal evidence of carcinogenic 

activity in female F344/N rats, based on increased combined incidence of benign and malignant 

pheochromocytomas (mostly benign). NTP (2000) also reported some evidence of carcinogenic 

activity in male B6C3F1 mice based on increased incidence of hemangiosarcomas of the liver, 

and some evidence of carcinogenic activity in female B6C3F1 mice based on increased 

incidence of forestomach squamous cell papillomas or carcinomas. 

EPA concluded in the HAPs delisting decision in 2003 (68 FR 65656) “that the available 

data establish a plausible nonlinear, nongenotoxic mode of action for the moderate increase 

observed by NTP (2000) in the incidence of forestomach tumors in female mice.” The Agency 

summarized the impact of this finding on its assessment of human health risk due to EGBE 

emissions as follows: 

... the exposure concentrations necessary to cause hyperplastic

effects in humans would be much higher than the existing RfD and 

dThe theoretical EGBE maximum airborne concentration is greater than 1,100 ppm, but in recent acute studies, the 

highest attainable concentrations were 600 to 700 ppm.
23 

RfC for EGBE. Given that humans, including potentially sensitive 

subpopulations such as children, have no known organ for the 

retention of a comparable target dose of EGBE or its metabolites, 

we feel it is reasonable to conclude that the RfC and RfD 

developed for EGBE are sufficient for the prevention of 

hyperplasia and associate tumors in humans. 

Similarly, EPA (68 FR 65656) found that the available data “establish a plausible 

nonlinear, nongenotoxic mode of action for the moderate increase observed by NTP (2000) in 

the incidence of liver tumors in male mice.” Thus, given “the relatively low sensitivity of humans, 

including subpopulations such as children, to the hemolytic effects of EGBE, we feel it is 

reasonable to conclude that the [1999] EGBE RfC and RfD (EPA 1999a) are sufficient for the 

prevention of hemolysis and associate tumors in humans.” Accordingly, the Administrator (69 

FR 69322) determined that the IRIS reference values will protect against both cancer and 

noncancer effects: 

... it is reasonable to expect that a lack of hemolytic effects in

humans would preclude the formation of liver tumors in humans 

and that a lack of hyperplastic effects in the region of the 

gastroesophogeal junction in humans would preclude the 

formation of gastrointestinal tumors in humans. That is, the data 

support the finding that we would not expect to find these tumors 

in humans following environmental exposures. The RfC and RfD 

values for EGBE have been set at levels that prevent both the 

precursor events that would lead to tumors and other noncancer 

effects ... 

The HAPs delisting findings are reaffirmed in the IRIS toxicological review of EGBE 

(EPA 2010), which concluded that the data establish a plausible nonlinear mode of action for 

both the forestomach and liver tumors in mice. Regarding the pheochromocytomas in female 

rats, EPA (2010) noted that, “given the marginal dose response, lack of tumor evidence in any 

other organ system of the rats, and reported difficulties in distinguishing pheochromocytomas 

from nonneoplastic adrenal medullary hyperplasia, this tumor type was not given significant 

weight in the qualitative or quantitative assessment of EGBE cancer potential.” 

The forestomach tumors were found to develop through sustained cytotoxicity and cell 

regeneration brought about by irritation and breakdown of the forestomach’s gastric mucosal 

barrier. This mechanism has been proposed for several other chemicals that cause rodent 

forestomach tumors, such as butylated hydroxyanisole (BHA), propionic acid, and ethyl acrylate 

(Kroes and Wester 1986, Harrison 1992, Clayson et al. 1990, 1991). A recent International 

Agency for Research on Cancer (IARC) assessment of the mechanism of rodent forestomach 

tumors and their potential relevance to humans specifically finds that the same irritation-based 

epigenetic mode of action accepted in EPA’s carcinogenicity assessment is supported for EGBE 

(IARC 2006). 

The EPA (2010) evaluation identifies a multistep mode of action for EGBE-induced 

mouse forestomach tumors: 
24 

1. Deposition of EGBE/BAA in the stomach and forestomach via consumption or

reingestion of EGBE laden mucus, salivary excretions, and fur material

2. Retention of EGBE/BAA in food particles of the forestomach long after being cleared

from other organs

3. Metabolism of EGBE to 2-butoxyacetaldehyde (BAL), which is rapidly metabolized to

BAA systemically and in the forestomach

4. Irritation of target cells by BAA leading to hyperplasia and ulceration

5. Continued injury by BAA and degeneration leading to high cell proliferation and turnover

6. High levels of cell proliferation and turnover leading to clonal growth of spontaneously

initiated forestomach cells

While such a process might theoretically occur in humans exposed to a sufficiently high

dose of EGBE, that dose would be substantially higher than the RfC or RfD, given that humans 

do not possess an anatomical equivalent to the mouse forestomach where EGBE and 

metabolites might be retained. Also, humans would not be expected to produce sufficiently high 

concentrations of BAA in other potentially sensitive tissues chronically to permit tumors to 

develop via this mode of action. 

Similarly, EPA (2010) concluded that the mouse liver tumors arose secondary to ironinduced oxidative stress resulting from the EGBE-induced hemolysis. It presented the following 

nine-step summary mode of action: 

1. EGBE is metabolized to BAL, which is subsequently oxidized to BAA

2. BAA causes red blood cell swelling, triggering sequestration in the spleen by resident

macrophages. When the capacity of these macrophages becomes overwhelmed, the

damaged red blood cells make their way into the liver

3. Excess hemoglobin (Hb) from damaged red blood cells is taken up by phagocytic

(Kupffer) cells of the liver and stored as hemosiderin

4. Oxidative damage and increased synthesis of endothelial and hepatocyte

deoxyribonucleic acid (DNA) are initiated by one or more of the following events:

 Generation of reactive oxygen species (ROS) from Hb-derived iron within

Kupffer cells and perhaps from within hepatocytes and sinusoidal endothelial

cells

 Activation of Kupffer cells to produce cytokines/growth factors that suppress

apoptosis and promote cell proliferation

5. ROS results in oxidative DNA damage to hepatocytes and endothelial cells

6. ROS modulates hepatocyte and endothelial cell gene expression

7. ROS stimulates hepatocyte and endothelial cell proliferation

8. ROS promotes initiation of hepatocyte and endothelial cells

9. ROS promotes neoplasm formation
25 

Support for the importance of several of these steps in the mode of action, particularly 

Steps 4, 5, 6, and 7, has accrued from studies performed since the initial publication of the NTP 

draft report in 1998. The validity of this pathway has been endorsed by independent scientific 

peer review of EPA’s analysis (EPA 2010). 

Corthals et al. (2006) addresses one previous area of uncertainty regarding EPA’s mode 

of action and the potential involvement of the short-lived intermediate metabolite of EGBE, BAL. 

Because BAL has exhibited some genotoxic activity in some assay systems, EPA scientists 

reviewing the HAPs delisting petition noted that the possibility of a genotoxic mode of action 

involving BAL had not been ruled out (68 Fed. Reg. 65660). Thus, although the Agency found 

PBPK modeling sufficient to find “that genotoxicity is not a factor in tumor development” when it 

deleted EGBE as a HAP; it nevertheless called for additional research (69 Fed. Reg. 69322). 

The study by Corthals et al. (2006), conducted in Dr. James Klaunig’s laboratory at the Indiana 

University School of Medicine, was specifically designed to further explore the possible BALgenotoxicity mode of action. 

Corthals et al. (2006) demonstrate that BAL does not express any genotoxic activity, as 

measured by the Comet assay, in mouse endothelial cells, the cell type from which 

hemangiosarcomas develop. EGBE and BAA also showed no genotoxic activity in this assay. 

DNA damage was produced in these cells, however, when treated with hemolyzed red blood 

cells, ferrous sulfate, or hydrogen peroxide, supporting the proposed role of reactive oxygen 

species generated from red blood cell hemolysis in the mode of action for mouse liver 

hemangiosarcomas. Hemolyzed red blood cells were also shown to activate macrophages, as 

evidenced by increased levels of tumor necrosis factor alpha (TNFα), and activated 

macrophages produced DNA damage in endothelial cells and stimulated endothelial cell 

proliferation (Corthals et al. 2006), providing further support for the mode of action accepted by 

EPA. 

Subsequently, EPA (2010) concluded: 

Under the Guidelines for Carcinogen Risk Assessment (U.S. EPA, 

2005, 086237), EGBE is deemed “not likely to be carcinogenic to 

humans” at environmental concentrations below or equivalent to 

the RfD and RfC, based on laboratory animal evidence, mode-ofaction information, and limited human study information. The 

available data indicate that carcinogenic effects from EGBE are 

not likely to occur in humans in the absence of the critical 

noncancer effects, including hepatic hemosiderin staining and 

irritant effects at the portal of entry, and are not likely to be 

carcinogenic to humans exposed to levels at or below the RfC and 

RfD values derived in this assessment. 

Similar considerations led IARC to conclude that EGBE is not classifiable as to its 

carcinogenicity to humans (Group 3) on the basis of limited evidence in experimental animals 

and inadequate evidence in humans (IARC 2006, Cogliano 2004). 

Based on these considerations, it is reasonable to conclude that EGBE presents no 

cancer risk to individual living near EGBE-emitting facilities. 
26 

3.3 Ecotoxicity 

The ecotoxicity of EGBE has been evaluated in five reviews, all of which conclude that 

EGBE poses a low potential for adverse ecological effects (WHO 1998, Staples 1998, Devillers 

et al. 2002, Environment Canada and Health Canada 2002, INERIS 2006). No information on 

the toxicity of EGBE to terrestrial organisms, including reptiles, birds, or wild mammalian 

species, was identified from the primary scientific literature or reviews. Acute aquatic ecotoxicity 

data are available for nine fish species and seven aquatic invertebrate species, while chronic 

ecotoxicity data are available for one amphibian species, two fish species, four aquatic 

invertebrate species, and eight species of algae, bacteria, and protozoans. Species tested 

include freshwater and marine vertebrates and invertebrates. All aquatic toxicity values listed in 

the five recent reviews cited above and identified in a supplemental search of the primary 

literature are compiled and sorted by organism, endpoint, and exposure duration in Table 3-2. 

Based on acute ecotoxicity testing, the most sensitive aquatic species to EGBE are 

mummichog (Fundulus heteroclitus) and grass shrimp (Palaeomonetes pugio), which have 96-

hour LC50 values of 6.7 mg/L and 5.4 mg/L, respectively (Biospherics 1981, as cited in 

Environment Canada and Health Canada 2002). However, both concentrations are more than 

an order of magnitude less than any other reported acute concentrations for EGBE. The 

ecotoxicity evaluation in the CICAD declined to rely on these findings because they represent 

“such an extreme outlier compared with the range of other data that it is difficult to justify [their] 

use as the basis for” selecting a toxicity criterion (WHO 2005). The primary study (Biospherics 

1981, as cited in Environment Canada and Health Canada 2002) was not available. However, 

the EU concluded that the study was not valid in the derivation of its predicted no effect 

concentration because of the methods employed in the original study (INERIS 2005). Therefore, 

the reliability of the grass shrimp and mummichog LC50 values is open to question. The next 

most sensitive species to acute exposures is an oyster (Crassostrea virginica), which has an 

LC50 of 89 mg/L (EPA 1984, as cited in WHO 1998; 2010). Several other fish and invertebrate 

species have LC50 values between 100 and 200 mg/L, but most fish species tested have LC50

values greater than 1,000 mg/L (Table 3-2). 

Relatively few aquatic chronic toxicity data are available for EGBE. The lowest reported 

chronic value for EGBE is from a reproduction study on a rotifer (Brachionus calyciflorus). Ten 

percent of the test population was affected at 7.2 mg/L and the median effect concentration 

(EC50) was 164 mg/L (Devillers et al. 2002). A blue-green algae species (Microcystis 

aeruginosa) and a protozoan (Entosiphon sulcatum) experienced growth effects with EGBE 

concentrations of 35 and 91 mg/L, respectively (Bringmann and Kuhn 1980, as cited in Staples 

et al. 1998). Two copepods (Daphnia magna and Ceriodaphnia dubia) experienced reproduction 

effects at EGBE concentrations near 130 mg/L (Devillers et al. 2002, 2003). Overall, most 

available aquatic chronic toxicity values for EGBE are below 1,000 mg/L (Table 3-2). 
27 

3.4 Evaluation of Potential Hazards of EGBE and Implications for TRI Listing 

EPA has interpreted the listing criteria of Section 313(d)(2) of EPCRA to call for a 

weight-of-evidence hazard assessment of the potential for a chemical to cause the three types 

of adverse effects specified in the statutory text: acute, chronic, and ecotoxic effects. Because 

“virtually any chemical substance can elicit a toxicological response at some dose level,” EPA’s 

interpretation recognizes that “the mere presence of the toxic response is not used in isolation in 

listing decisions under EPCRA Section 313” (59 FR 61445 [EPA 1994b]). Accordingly, EPA’s 

interpretation of the listing criteria calls for the consideration of exposure in certain 

circumstances, depending on the type of hazard in question. 

 In the case of adverse acute human health effects, Section 313(d)(2)(A) explicitly calls

for an exposure evaluation of whether such effects occur “at concentration levels that

are reasonably likely to exist beyond facility site boundaries as a result of continuous, or

frequently recurring, releases” (42 U.S.C. §11023(d)(2)(A)). Thus, EPA’s interpretation

provides for the consideration of exposure in determining whether to list or delist based

on acute health effects.

 For chronic human health hazards addressed in EPCRA Section 313(d)(2)(B), the

Agency has adopted the view that exposure considerations are not appropriate in

making listing determinations “for chemicals that exhibit moderately high to high human

toxicity ... based on a hazard assessment.” Consideration of exposure is called for,

however, in the case of “chemicals that exhibit low to moderately low toxicity based on a

hazard assessment” (59 FR 61441). Thus, “in instances where the hazard assessment

indicates that ... a chemical is of low toxicity and unrealistic exposures would be

necessary for it to pose a risk to communities ..., EPA may use exposure considerations

in its listing decisions” (59 FR 61442).

 For the adverse environmental effects subject to EPCRA Section 313(d)(2)(c), EPA

reads EPCRA to call for listing solely on the basis of a hazard assessment “for

chemicals that are highly ecotoxic or induce well-established adverse environmental

effects” that “do not affect solely one or two species but rather cause changes across a

whole ecosystem,” such as chemicals that threaten the “sustainability of a fragile

ecosystem such as an estuary.” Exposure is an appropriate factor, however, in listing

and delisting decisions on “chemicals that are low or moderately ecotoxic but do not

induce well-documented serious adverse effects” on entire ecosystems (59 FR 61433,

61441). 

The hazard assessment presented above indicates that EGBE poses low potential 

hazards to human health and the environment. Because exposure is always a relevant factor for 

acute human health effects, the following discussion focuses on chronic human health and 

ecological hazards with respect to the appropriateness of considering exposure. 

3.4.1 Low Potential for Adverse Chronic Human Health Effects 

The extensive data on the mode of action of EGBE as a toxicant, its limited spectrum of 

toxic effects, and the documentation in vitro and in vivo that humans are relatively insensitive to 
28 

its toxic effects, all show that EGBE is appropriately considered a low-toxicity chemical. The 

scientific evidence supports the conclusion that EGBE is not immunotoxic, genotoxic, or 

teratogenic, and it does not cause adverse reproductive effects. All of the toxic effects of EGBE 

seen in rodents are secondary to the irritant and hemolytic effects of EGBE and its primary 

metabolite, BAA, and EPA has determined that prevention of hemolytic effects in humans will 

also protect against other toxic effects (EPA 2010). The current IRIS assessment concludes that 

EGBE is “not likely to be carcinogenic to humans at environmental concentrations below or 

equivalent to the RfD and RfC” and that tumors observed in rodent studies are secondary to 

EGBE’s noncarcinogenic toxic effects (EPA 2010). 

The available data also demonstrate that the primary toxic effect of EGBE exposure— 

hemolysis produced by EGBE’s primary metabolite BAA—can reasonably be expected to occur 

in humans only at doses that are unrealistically high, thus making EGBE a low-toxicity chemical 

for which exposure is a relevant consideration in the delisting determination. Because human 

red blood cells are relatively resistant to the hemolytic effects of EGBE, particularly compared to 

laboratory rats, based on the PBPK model used by EPA (2010) in its assessment, the daily oral 

dose necessary to achieve a blood BAA concentration high enough to cause even minor 

prehemolytic effects (≥10 mM, based on Udden [2002]) would be at least 700 mg/kg BW-day. 

Evaluated under EPA’s TRI listing criteria (EPA 1994a, 1992c) and previous listing decisions, 

EGBE is clearly a low-toxicity chemical (like e.g., ethylene glycol, 62 FR 24919 [EPA 1997a]). 

Such ingestion exposures to EGBE, moreover, are unrealistically high in relation to expected 

community exposures in the vicinity of EGBE-emitting facilities. Assuming water consumption of 

2 liters per day (L/day) by a 70-kilogram (kg) human, the water concentration that theoretically 

would be needed to achieve a hemolytic concentration of BAA in blood would be more than 

4,000 times greater than the highest surface water concentration of EGBE that has been 

reported at a contaminated site (ATSDR 1998, Environment Canada 2002), and over 140 times 

previous estimates of surface water concentrations resulting from EGBE facility emissions 

(WHO 2010, INERIS 2006). 

For the primary anticipated route of exposure to EGBE for TRI-related exposures—

inhalation—the available data indicate that hemolysis is not expected to occur in humans, even 

if exposed continuously by inhalation to an EGBE-saturated atmosphere (greater than 1,000 

ppm) (see Section 3.2.1.2 above).e Such concentrations are, of course, physically impossible, 

and in any case they are 100 to 1,000 times higher than typical occupational exposure levels, 

and 50 times higher than the occupational threshold limit value (TLV) (ATSDR 1998, ACGIH 

2003), even farther above available (albeit limited) data on ambient air concentrations of EGBE 

(IPCS 1997, ECETOC 2005, WHO 2005), and much higher still—by a factor of approximately 

100,000—than previous estimates of ambient air concentrations based on air dispersion 

modeling of emissions from EGBE-using facilities (WHO 2010, INERIS 2006). 

eThe theoretical EGBE maximum airborne concentration is greater than 1,100 ppm, but in recent acute 

studies, the highest attainable concentrations were 600 to 700 ppm. 
29 

The limited laboratory animal carcinogenicity data do not justify an elevated hazard 

evaluation for EGBE under EPA’s TRI listing criteria and listing precedents. As noted in Section 

3.2.2, the current IRIS assessment classifies EGBE as “not likely to be carcinogenic to humans 

at environmental concentrations below or equivalent to the RfD and RfC” (EPA 2010). EPA has 

twice determined that even the higher carcinogenicity classification (based on the former cancer 

classification criteria) of “possible” human carcinogen does not support listing under EPCRA 

§313(d)(2)(B) (titanium dioxide, 53 FR 23108 [EPA 1988]; butyl benzyl phthalate, 60 FR 9299

[EPA 1995a]). Based on these precedents, it would be inappropriate to list a chemical that is 

classified as “not likely to be carcinogenic to humans.” 

3.4.2 Low Potential for Significant Adverse Ecological Effects 

EGBE’s potential to cause adverse ecological effects should likewise be characterized 

as low under EPA’s TRI listing criteria. The Agency found recently that EGBE causes only “very 

minor effects which were unlikely to be ecologically significant at the population level of 

ecological organization” (68 Fed. Reg. 65657 [EPA 2003]). EGBE therefore cannot be 

considered a high toxicity ecological hazard under the EPA’s TRI listing criteria on the basis of 

“well-established adverse environmental effects” “across a whole ecosystem” (59 FR 61441 

[EPA 1994b]). 

Furthermore, the “very minor” ecological effects of EGBE do not occur at concentrations 

that are considered to be low or moderate-to-low under EPA’s TRI listing guidelines. To the 

contrary, EGBE has low potential for persistence and bioaccumulation. LOAELs for acute 

toxicity to aquatic organisms are in most cases 1,000 mg/L or higher, and most chronic toxicity 

values are between 100 and 1,000 mg/L. The lowest LC50 for acute toxicity to an aquatic 

organism is 89 mg/L, and the lowest concentration reported to cause chronic aquatic toxicity is 7 

mg/L. Under EPA’s TRI listing criteria (EPA 1994a, 1992c) and previous listing decisions, EGBE 

meets the criteria for a low-toxicity chemical based on ecological effects. See, for example, 

Butyl Benzyl Phthalate (60 FR 9299 [EPA 1995a]); Diethyl Phthalate (61 FR 39356 [EPA 

1996b]); Di-(2-Ethylhexyl) Adipate (61 FR 39891 [EPA 1996c]); Ethylene Glycol (62 FR 24919 

[EPA 1997a]); Methyl Ethyl Ketone (63 FR 15195 [EPA 1998a]); Methyl Isobutyl Ketone (64 FR 

8769 [EPA 1999c]). 

It is also readily apparent that the concentrations found to cause aquatic toxicity are far 

above the surface water concentrations likely to be present in communities near EGBE-emitting 

facilities. The lowest reported aquatic toxicity level (7 mg/L for chronic effects) is greater than 

the highest surface water concentration of EGBE that has been reported at a contaminated site

(5.7 mg/L; ATSDR 1998, Environment Canada 2002), and about a thousand times higher than 

available empirical and modeled estimates of surface water concentrations resulting from EGBE 

facility emissions (Environment Canada 2002, WHO 2010, INERIS 2006). 

3.4.3 Conclusion 

EPA’s interpretation of the TRI listing criteria of EPCRA Section 313(d)(2) calls for the 

consideration of exposure levels for potential adverse chronic human health and significant 
30 

environmental effects if “a chemical is of low toxicity and unrealistic exposures would be 

necessary for it to pose a risk to communities” (59 FR 61442). 

As discussed above, even relatively minor prehemolytic effects are not expected in 

humans even at exposures: (1) that are considered high under EPA’s TRI listing criteria and 

precedents and (2) that are far above exposures likely to occur in communities near EGBEemitting facilities. EPA’s findings in the HAPs delisting decision and in its carcinogenicity 

evaluation (EPA 2010) confirm that prevention of hemolysis protects against any other potential 

adverse health effect of EGBE exposure. Similarly, the available ecotoxicity data continue to 

support EPA’s determination in the HAPs proceeding that EGBE emissions present the potential 

for only “very minor effects” that are “unlikely to be ecologically significant,” and indicate that 

such minor effects are expected to occur only at concentrations (1) that are clearly high under 

EPA’s TRI listing criteria and precedents and (2) that are far above exposures likely to occur in 

communities near EGBE-emitting facilities. 

Accordingly, EGBE presents a low potential for adverse effects on human health or the 

environment, and an exposure assessment is warranted. 
31 

4.0 CRITERIA FOR EVALUATING ACUTE AND 

CHRONIC HUMAN EXPOSURES 

As noted earlier, under Section 313 of EPCRA, a chemical may be added to TRI on the 

basis of acute toxicity in humans, chronic toxicity in humans, or significant adverse effects on 

the environment. The criteria for evaluating acute and chronic human exposures are addressed 

below as they relate to EGBE. 

4.1 Acute Toxicity 

As specified in Section 313(d)(2) of the statute, a chemical may be added to the list of 

chemicals requiring reporting under Section 313 if: 

the chemical is known to cause or can reasonably be anticipated 

to cause significant adverse acute human health effects at 

concentration levels that are reasonably likely to exist beyond 

facility site boundaries as a result of continuous or frequently 

recurring releases; 

As discussed by EPA (2010) and ATSDR (1998), and noted in Section 3.2.1.1 of this 

petition, EGBE is of low acute toxicity, with the most sensitive endpoint in humans being eye 

and upper respiratory tract irritation at airborne concentrations above the occupational TLV of 

20 ppm (97 mg/m3). Such a concentration is far higher than anything that has been monitored or 

modeled near an EGBE-emitting facility (IPCS 1997, ECETOC 2005, WHO 2010, INERIS 

2006), and would not, therefore be “reasonably likely to exist beyond facility site boundaries as 

a result of continuous, or frequently recurring, releases.” 

4.2 Chronic Toxicity 

The EPA HAPs delisting decision used the IRIS RfC and RfD to evaluate potential 

chronic human health effects from facility releases of EGBE. EPA’s policies and precedents 

under EPCRA’s TRI listing provisions strongly support the use of IRIS criteria where available 

(59 FR 61444-45 [EPA 1994b]). Accordingly, the evaluation of chronic human exposures and 

risks in this petition is based on the IRIS reference levels. EPA derived the RfC and RfDf

 after a 

careful review of the available dose-response database for EGBE, emphasizing mechanistic 

information. EPA used dose-response information for EGBE-induced hematological effects as 

the basis for the IRIS RfC and RfD values. EPA derived both the RfC and the RfD from data on 

hemosiderin staining in the liver in rats in the 2-year NTP (2000) inhalation study. Using 

benchmark concentration (BMC) and PBPK modeling, EPA estimated that the 95% lower 

f The RfD is defined by EPA as “an estimate (with uncertainty spanning perhaps an order of magnitude) of a daily 

oral exposure to the human population (including sensitive subgroups) that is likely to be without an appreciable 

risk of deleterious effects during a lifetime.” Similarly, the RfC is defined as “an estimate (with uncertainty spanning 

perhaps an order of magnitude) of a continuous inhalation exposure to the human population (including sensitive 

subgroups) that is likely to be without an appreciable risk of deleterious effects during a lifetime. 
32 

confidence limit on the concentration predicted to produce a 10% increase in hemosiderin 

staining was 16 mg/m3. To derive the RfC, EPA applied an intraspecies uncertainty factor of 10, 

to account for variation in sensitivity within the human population. Because the PBPK model 

was used, and because the adverse effect endpoint was a minimally adverse effect in a species 

more sensitive than humans, EPA used an uncertainty factor of 1 for LOAEL-to-NOAEL 

extrapolation, resulting in the final RfC of 1.6 mg/m3. 

EPA derived the oral RfD based on the same data as the RfC by using the Corley et al. 

1994, 1997) PBPK model to perform route-to-route extrapolation to derive the 95% lower 

confidence limit on the daily oral dose of EGBE predicted to produce a 10% increase in 

hemosiderin staining of 1.4 mg/kg BW-day. To derive the RfD, EPA applied an intraspecies 

uncertainty factor of 10, to account for variation in sensitivity within the human population. 

Because the PBPK model was used, and because the adverse effect endpoint was a minimally 

adverse effect in a species more sensitive than humans, EPA used an uncertainty factor of 1 for 

LOAEL-to-NOAEL extrapolation, resulting in the final RfD of 0.1 mg/kg BW-day (rounded). 

Both the RfD and RfC are based on the occurrence of hemolytic effects in rats. As noted 

previously, there is extensive evidence, both in vivo and in vitro that humans are much less 

sensitive than rats to the hemolytic effects of EGBE. Studies by Udden (2000, 2002) show that 

prehemolytic effects occur in rat red blood cells at concentrations of BAA, the proximate 

hemolytic agent, at least 100 times lower than concentrations that might affect human red blood 

cells. EPA accounts for this difference in susceptibility only partially in its derivation of the RfD 

and RfC by not using the standard 10-fold uncertainty factor for interspecies extrapolation, but 

rather assumes an interspecies correction factor of 1, implying that humans are equally 

sensitive rather than less sensitive than rats. However, the available relative toxicity data 

indicate that the actual interspecies factor from rats to humans is much less than 1. The 

hemolytic anemia comparative data from Udden et al. (2000, 2002) indicates that this 

interspecies factor should be no greater than 0.01, rather than 1, as used by EPA in deriving the 

RfD and RfC. This clearly demonstrates the very conservative nature of hemolytic effects in rats 

as a point of departure for establishing the EPA IRIS RfD and RfC. 

Clearly, the interspecies uncertainty factor and point of departure are very conservative. 

Indeed, there is also little reason to believe that the IRIS intraspecies uncertainty factor of 10 is 

scientifically justified. As discussed in the IRIS assessment, investigation of population groups 

that might be expected to show increased sensitivity to hemolytic effects of EGBE (e.g., the 

young, the old, and individuals with sickle cell anemia or hereditary spherocytosis), did not 

reveal increased susceptibility. Thus, the IRIS intraspecies uncertainty factor of 10 is also likely 

to contribute undue conservatism to the RfC and RfD. 

Another significant element of conservatism in the RfC and RfD relates to the fact that 

they were designed to be protective for continuous daily exposure for a full lifetime to EGBE. 

The emissions of interest in this petition are likely to fluctuate over time. As EPA recognized in 

the HAPs delisting decision (see Section 6.2.3, below), the lifetime average exposure level 

(which is the relevant metric for comparison to the RfD and RfC) will be substantially lower than 
33 

the peak concentration at the point of maximum impact (as assumed in the exposure 

assessment of this petition), thus providing an additional margin of safety.
34 

5.0 EMISSIONS INVENTORY 

As previously discussed, EPA determined in the HAPs delisting proceeding (68 FR 

65651-52 [EPA 2003]) that the EPCRA TRI database “provide[s] a reasonable representation of 

... EGBE emissions” and “an adequate basis for dispersion modeling and ... exposure

assessment.” Accordingly, this petition has conservatively developed an emission inventory of 

potential EGBE sources that includes all facilities that submitted TRI reports for Certain Glycol 

Ethers for the 2009, 2010, and 2011 calendar years, and which reported a non-zero release of 

Certain Glycol Ethers to air, either from onsite point or fugitive sources. In addition, because this 

petition also includes an assessment of potential human health and ecological risks based on 

exposures to other environmental media, facilities reporting non-zero releases of Certain Glycol 

Ethers to soil and surface water were added to the facilities included in emissions inventory 

(www.epa.gov/triexplorer). For the risk evaluation presented in Sections 6 through 8, it was 

conservatively assumed that all Certain Glycol Ethers released are EGBE for facilities without 

site-specific data on the proportion of Certain Glycol Ethers released that is EGBE.g Because 

EGBE represents 52% of ethylene glycol ethers consumed in the United States (SRI 2010), the 

application of this assumption in Sections 6 through 8 of this petition may overestimate 

exposures by two-fold. 

Table 5-1 presents summary information on the distributions and magnitude of releases 

to air, water, and land, as well as changes in releases since 1993 and the mid-2000s. The 1993 

data are used as a point of comparison because they formed the basis for the HAPs delisting 

decision and the 2003 through 2006 data were provided because they were compiled for ACC’s 

previous petition prior to EPA’s revision to the RfC and RfD. Because the Administrator 

determined in the HAPs delisting decision that releases of EGBE “may not reasonably be 

anticipated to cause any adverse effects” to human health or the environment (69 FR 69322), it 

is reasonable to expect that the same findings are justified in light of the substantial broadbased decrease in emissions since 1993, as shown in Table 5-1. In addition, Figure 5-1 shows 

the maximum reported emissions for Certain Glycol Ethers to the air by individual facilities for 

each year from 2000 through 2011. Note that the maximum facility air emissions have slowly 

declined over this time period.

Those facilities that reported non-zero TRI emissions of Certain Glycol Ethers during 

2009, 2010, and/or 2011 are the basis for the emission inventory used for evaluating potential 

inhalation exposures and risks (Section 6). This emission inventory includes 1,109 facilities that 

reported non-zero emissions of Certain Glycol Ethers during 2009, 1,149 facilities that reported 

non-zero emissions during 2010, and 1,099 facilities reporting non-zero emissions during 2011. 

g Facility-specific information on the percentage of Certain Glycol Ethers that is EGBE was requested for facilities 

evaluated in Steps B through Tier 3 
35 

6.0 INHALATION EXPOSURE ASSESSMENT AND RISK 

CHARACTERIZATION 

For the purposes of this petition, the exposure assessment and risk characterization 

related to EGBE has two specific objectives: (a) to determine whether emissions of EGBE to 

ambient air could result in air concentrations that may pose a risk for acute and/or chronic 

human health effects; and (b) to determine whether emissions of EGBE from clusters of facilities 

within a limited geographic area could result in air concentrations of EGBE that pose a risk for 

acute and/or chronic health effects, at or beyond facility boundaries. This introduction provides 

an overview of the approach and findings of these analyses, while subsequent subsections 

detail all aspects of the inhalation exposure assessment and risk characterization. 

The chronic (longer-term) and acute (short-term) exposure assessments were 

conducted for all facilities in the emissions inventory database developed as described in 

Section 5, in combination with a modified version of EPA’s tiered modeling approach for 

assessing risks from stationary emission sources, which is described in A Tiered Modeling 

Approach for Assessing the Risks Due to Sources of Hazardous Air Pollutants (EPA 1992a). 

The tiered screening approach used in this petition follows the same general methodology used 

for the 2004 EGBE HAPs delisting decision; a methodology EPA reviewed, approved, and 

deemed as appropriate and conservative (in the sense that it overstates exposures). In brief, the 

tiered modeling approach involves performing analytical simulations (modeling) of air pollutant 

dispersion of emissions from stationary emission sources, given that measurement of long-term 

and short-term ambient concentrations of a pollutant in the vicinity of each source would be a 

prohibitively expensive task. The first modeling tier in this approach is designed to address the 

question of whether or not an emission source has the potential to result in EGBE air 

concentrations above the air concentrations of concern, and is performed using a table of 

lookup values that provides an estimate of the worst-case impact of the emission source being 

modeled. For this petition, the first tier (i.e., Tier 1) is preceded by two additional precursor 

screening steps (Steps A and B) designed to reduce the number of facilities for which additional 

site-specific data collection is required, through the use of conservative assumptions for 

parameters such as the proportion of certain glycol ether reported emissions that are EGBE, 

emission release height, and distance to nearest receptor. Facilities retained following these 

conservative, precursor screening steps are then subjected to the additional three tiers of the 

tiered modeling approach. In the tiered modeling approach, if predicted screening impacts at a 

given tier are less than the appropriate level(s) of concern, then no further modeling is needed 

in order to rule out the potential for adverse effects. Thus, facilities “screen out” of this tiered 

analysis only if their estimated maximum airborne concentrations of EGBE are determined not 

to pose a potential risk to human health. In the application of the tiered modeling approach in 

this petition, the exposure assessments performed for all facilities consistently employed 

conservative assumptions for emission-related parameters. 

The screening approach for evaluating chronic EGBE exposures estimated the worstcase annual average airborne EGBE concentrations associated with EGBE emissions from 
36 

individual facilities or clusters of facilities at or beyond the facility property boundaries, for 

comparison to the EGBE RfC of 1.6 mg/m3, in order to determine whether EGBE-emitting 

facilities pose a significant risk of adverse chronic human health effects. The analysis evaluated 

chronic exposures for all facilities that reported non-zero emissions of Certain Glycol Ethers to 

TRI in 2009, 2010, and/or 2011. The results of the tiered screening for chronic EGBE exposures 

demonstrated that maximum annual average EGBE concentrations at or beyond facility property 

boundaries, both for individual facilities and clusters of facilities emitting EGBE, are below the 

EGBE RfC, thus supporting a conclusion that emissions of EGBE do not result in a significant 

risk of chronic health effects. 

The primary outcomes of the chronic exposure emissions modeling, as described in 

detail in this section, is a demonstration that (a) no ambient air concentrations of EGBE in the 

United States are predicted to exceed the EGBE RfC of 1.6 mg/m3 and (b) the vast majority of 

EGBE air concentrations throughout the United States are well below that value. The first 

outcome is demonstrated through modeling performed for facilities that reported non-zero 

emissions of Certain Glycol Ethers in their TRI reports during 2009 through 2011: 1,109 facilities 

reporting Certain Glycol Ethers emissions for 2009; 1,149 facilities reporting Certain Glycol 

Ethers emissions for 2010; and 1,099 facilities reporting Certain Glycol Ethers emissions for 

2011. The modeling demonstrated that long-term ambient air concentrations of EGBE at or 

beyond the fencelines of all these facilities are below 1.6 mg/m3. 

The conservatism of this conclusion is demonstrated in several ways. First, the modeled 

air concentration estimates in the initial modeling tiers (e.g. Tier 1) are based on a screening 

dispersion model. Screening dispersion models are intentionally designed to overestimate 

ambient air concentrations. Thus a facility that screens out in the earlier tiers does so based on 

a substantial overestimate of its EGBE ambient air concentrations. Second, when facilities that 

do not screen out at earlier tiers (e.g., Tier 1) are modeled in successive Tiers using 

increasingly realistic yet still conservative estimates, the results show substantial reductions in 

the predicted maximum EGBE concentrations compared to earlier modeling tiers, thus further 

demonstrating the conservatism of the conclusion that emissions of EGBE from even the 

highest emitting facilities and clusters of closely located facilities do not result in long-term 

ambient air concentrations of EGBE above the RfC. For example, up to an average 92% 

reduction in maximum predicted concentrations was realized in moving from Tier 1 modeling to 

Tier 2 modeling to Tier 3 modeling, and an average 99.3% reduction was realized in moving 

from Step A to Tier 3 modeling. Facilities predicted under Tier 1 modeling to have maximum 

annual average concentrations greater than 1.6 mg/m3 were predicted under Tiers 2 and 3 to 

have maximum annual average concentrations as low as 0.043 mg/m3. 

Because an EPA RfC for short-term exposures is not available, the tiered screening 

approach for evaluating potential acute EGBE exposures uses the estimated worst-case 1-hour 

average airborne EGBE concentrations combined with a MOE methodology frequently used by 

EPA in TRI delisting decisions, in cases where an EPA reference concentration for short-term 

exposures is not available. The results of the analysis indicated that maximum 1-hour average 

concentrations at or beyond facility property boundaries equate to a MOE in excess of 5 below 
37 

the NOAEL for all facilities evaluated, supporting a conclusion that acute effects from EGBE 

emissions are highly unlikely. For the acute exposure assessment for clusters of facilities 

(located within a small geographic area), the maximum 1-hour average concentrations at or 

beyond facility property boundaries for the clustered facilities equate to a MOE in excess of 4. 

As a further note on the conservatism in this analysis, the acute NOAEL on which the MOE is 

based is derived from 2-hour human exposure data that was not adjusted to the 1-hour 

concentration. If the MOE was adjusted to the 1-hour concentration, the MOE would increase by 

about 40%. 

6.1 Overview of the Tiered Modeling Method for Assessing Risks from Air Exposures 

As described in Section 5, an emissions inventory of potential EGBE-emitting facilities 

was developed based on all facilities that reported non-zero emissions of Certain Glycol Ethers 

in their TRI reports for the 2009, 2010, and/or 2011 reporting years. For each facility reporting 

non-zero Certain Glycol Ethers emissions to EPA during these years, the potential for each 

facility’s emissions to result in ambient air concentrations of EGBE above acute or chronic 

exposure concentrations of concern was evaluated using a conservative risk-based screening 

approach consistent with EPA’s (1992a) guidance document, A Tiered Modeling Approach for 

Assessing the Risks Due to Sources of Hazardous Air Pollutants (“EPA’s Tiered Modeling 

Guidance”). This guidance outlines EPA-approved procedures for assessing risks due to the 

atmospheric dispersion of emissions of pollutants from stationary sources. In brief, EPA’s Tiered 

Modeling Guidance describes an approach that involves performing analytical simulations of air 

pollutant dispersion from stationary sources, given that measurement of long-term and shortterm ambient concentrations of a pollutant in the vicinity of each source would be a prohibitively 

expensive task. 

EPA’s Tiered Modeling Guidance describes a three-tiered modeling approach, 

consisting of the following: 

 Tier 1 – Lookup table

 Tier 2 – Screening air dispersion modeling

 Tier 3 – Detailed air dispersion modeling

EPA’s Tiered Modeling Guidance states that if predicted screening impacts at a given

tier are less than the appropriate level(s) of concern, then no further (refined) modeling is 

indicated. However, if the predicted screening impacts are above any levels of concern, the 

guidance states that further (refined) analysis of these impacts at a higher tier would be 

performed (i.e. successive refined modeling tiers) to obtain more accurate (realistic) results. 

In EPA’s Tiered Modeling Guidance, Tier 1 is designed to address the question of 

whether or not an emission source has the potential to cause a significant impact. Tier 1 
38 

screening uses lookup tables based on EPA’s 1992h guidance, which are straightforward to use 

and require fairly limited input data. The values provided by the lookup table are the estimated 

worst-case air concentration associated with each emission source being modeled. Although 

EPA’s (1992a) Tier 1 modeling step involves use of a lookup table that is straightforward to use 

and requires fairly limited input data, it requires more information than is available solely from 

TRI reports. As such, a more conservative and simpler two-step precursor screening procedure 

was developed for use prior to the Tier 1 screening step. The precursor procedure is designed 

to reduce the number of facilities for which additional data collection was required to perform the 

more refined Tier 1 screening. Thus, Step A of the two-step precursor screening procedure 

relies solely on data available from TRI submissions (i.e. total annual emissions of Certain 

Glycol Ethers), while Step B requires the total annual emissions data from TRI plus a small 

number of additional facility-specific parameters (though less than are required for Tier 1 

screening). In instances where facility specific inputs were not available for Step B, conservative 

default assumptions for those parameters were used. 

Step A uses an “inverted” Tier 1 table (see Table 6-1) that was generated using the 

same methodology that was used to generate the inverted Tier 1 table used for the same 

purpose in the HAPs delisting petition (CMA 1997). The inverted Tier 1 table (Table 6-1) 

provides a threshold emission rate below which a facility is not predicted to exceed a specific 

ambient air concentration, based on an assumed release height and distance to fenceline. 

Highly conservative assumptions were used to generate the “inverted” Tier 1 table used in Step 

A, such as an assumption that all emissions (combined point and fugitive emissions) of Certain 

Glycol Ethers are assumed to be EGBEi

, and that all emissions are assumed to be released 

from a single point source with a release height of zero meters. In the HAPs delisting decision, 

EPA specifically approved this adaptation of EPA’s modeling guidelines as ”reasonable” 

because it is based on “sound analytic principles” “and would tend to overestimate rather than 

underestimate maximum annual ambient average concentrations” (68 FR 65652, 65660 [EPA 

2003]). 

The Step B precursor screening step uses a modified version of EPA’s Tier 1 lookup 

table (the same lookup table used for the Tier 1 screening step), along with a small number of 

facility-specific parameters required to model the maximum impact from each facility. However, 

as described in Section 6.2.3, Step B is more conservative than the Tier 1 screening. For Step B 

highly conservative assumptions were applied for facilities for which existing facility-specific 

h Note that EPA’s 2004 Community Air Screening How-To Manual (EPA 2004c) guidance also includes 

an analogous screening lookup table. However, an analysis of the 2004 lookup table using a subset of 

the highest emitting facilities evaluated as part of this petition, indicates that the 2004 screening lookup 

table is less conservative (predicts lower modeled concentrations) than the lookup table based on EPA’s 

1992 Tiered Modeling Guidance. As such, to maximize the conservatism of the tiered modeling 

approach used in this petition, a screening lookup table based on EPA’s 1992 guidance lookup table is 

used, which is the same screening lookup table used for the same purpose in the HAPs delisting petition 

(CMA 1997).

i This assumption is considered conservative because EGBE comprises 52 percent (%) of the United 

States annual consumption of glycol ethers (SRI 2010).
39 

information had been obtained for the 2007 EGBE TRI delisting petition, or was obtained from 

Step B survey responses received as part of this petition. For each of these facilities, very 

conservative assumptions were used with the lookup table, such as assuming that the 

combined point-source emissions for a facility were emitted from a single hypothetical stack, 

with a release height equal to the minimum stack height among all facility stacks, and the 

minimum distance to fenceline among all facility stacks. For all facilities without site-specific 

information for the required parameters, conservative default Step B input parameters were 

assumed, as described further below. 

The conservative nature of the Step A and Step B prescreening steps is designed to 

ensure that maximum EGBE concentrations in ambient air at/beyond the fenceline of facilities 

that screen out using this methodology will not exceed the applicable levels of concern for 

EGBE for both chronic and acute inhalation exposures. For those facilities that did not screen 

out from Step A and Step B, more refined screening for both acute and chronic exposures was 

performed using slightly modified versions of EPA’s Tier 1 lookup table (identical to the Tier 1 

table used for the EGBE HAPs delisting petition). The Tier 1 lookup tables (acute and chronic) 

require additional site-specific data not required for the Step B screening step. Thus, the 

maximum concentrations predicted by the Tier 1 lookup tables, more precisely estimate the 

short-term and long-term ambient concentrations of EGBE, compared to Step A and Step B. 

Those facilities for which the maximum Tier 1 predicted concentrations are below the 

applicable levels of concern for EGBE for acute or chronic inhalation exposures do not require 

further refined analysis. For the remaining facilities with predicted Tier 1 EGBE air 

concentrations above the acute or chronic concentrations of concern, more refined screening 

modeling was performed in the Tier 2 screening step using EPA’s AERSCREEN v.11126. 

AERSCREEN is a screening-level air dispersion model designed to produce estimates of worstcase 1-hour concentrations for a single source, without the need for hourly meteorological data, 

and also includes conversion factors to estimate "worst-case" annual concentrations. If any 

facility with maximum predicted Tier 2 modeled EGBE concentrations in ambient air had 

exceeded the applicable levels of concern for EGBE for acute or chronic inhalation exposures, 

then the most refined and realistic analysis (Tier 3) using EPA’s refined dispersion model 

AERMOD v.12060, would have been used. However, although all facilities screened out at Tier 

2, in order to further test the conservatism of the screening procedure and to estimate the 

margin of safetyj

 provided by the screening procedure, a subset of facilities screening out at Tier 

2 were nonetheless subjected to Tier 3 analysis as part of the sensitivity and uncertainty 

analysis discussed in Section 6.6. 

As discussed further in the remainder of this section, the exposure assessments 

performed for all facilities using EPA’s tiered modeling approach consistently employed 

j For purposes of this petition, margin of safety is defined as the factor by which concentrations could 

increase while remaining below the short-term reference concentration (e.g., predicted concentration 

divided by the no adverse effects level). It is recognized that in other applications, margin of safety does 

not incorporate the uncertainty factors that are built into the IRIS RFC.
40 

conservative estimates of emission-related parameters whenever data were incomplete. Details 

of the tiered methodology used to support this delisting petition and the resulting risks for 

estimated long-term and short-term exposures to potential EGBE-emitting facilities are 

described in further detail in Sections 6.2 through 6.5. 

6.2 Step A and B Prescreening 

6.2.1 Step A Prescreening Methodology 

Step A uses an “inverted” Tier 1 table, developed using the same methods used to 

develop the inverted Tier 1 table in the 1997 HAPs delisting petition (CMA 1997).k This inverted 

screening table provides annual EGBE emission thresholds (expressed as tpy) above which the 

annual average EGBE concentration would be predicted to exceed the RfC of 1.6 mg/m3. The 

Step A inverted Tier 1 table is shown in Table 6-1. 

The annual threshold emission levels listed in this table are computed by dividing the 

RfC by the normalized ambient concentrations in EPA’s (1992a) Tier 1 table: 

Qthreshold = RfC ÷ [χ/Q] Tier 1 Eqn. 3 

where: 

Qthreshold = threshold emissions (tpy) 

RfC = Reference Concentration (expressed in micrograms per cubic meter or 

μg/m3), and 

[χ/Q]Tier 1 = normalized ambient concentration in Tier 1 table (μg•m-3/tpy) 

The annual emission thresholds for the screening table are tabulated by source type, 

release height, and downwind distance.l

For Step A, each facility’s annual TRI combined stack and fugitive Certain Glycol Ethers 

emissions are conservatively used to represent each facility’s total annual EGBE emissions. 

Consistent with the HAPs petition’s (CMA 1997) inverted Tier 1 table screening, Step A 

assumed that all stack and fugitive emissions from a given facility exhaust from a single point 

source with an emission height of zero meters and a minimum distance to fenceline of 50 

meters. Based on the EGBE RfC of 1.6 mg/m3, the corresponding threshold EGBE annual 

threshold emission rate for Step A screening is 4.9 tpy (Table 6-1). Based on these conservative 

assumptions regarding point-source releases, distances to fenceline, and percent of Certain 

Glycol Ethers that are EGBE, any facility emitting less than 4.9 tpy of Certain Glycol Ethers is 

predicted to have fenceline concentrations below the RfC. 

k

 The difference between the inverted Tier 1 table developed for the 1997 HAP delisting petition and the 

inverted Tier 1 table developed for this petition is that the former was derived based on the prior EGBE 

reference concentration of 13 mg/m3, while the Step A screening table for this petition is derived from 

the current RfC of 1.6 mg/m3 based on the 2010 IRIS assessment. 

l

 The emission source types in the screening table are identical to those listed in the Tier 1 lookup table.
41 

6.2.2 Step A Results 

All facilities reporting non-zero Certain Glycol Ethers emissions during the 2009, 2010, 

and/or 2011 TRI reporting years were evaluated using Step A. Step A screens out facilities that 

emit Certain Glycol Ethers (combined point and fugitive emissions) less than the lowest 

emission threshold for a 50 meter fenceline distance (i.e., 4.9 tpy). The results of the Step A 

screening are summarized below and in Table 6-2: 

 Of the 1,109 facilities that reported non-zero emissions of Certain Glycol Ethers to air in

2009, 824 (76%) screened out from further analysis based on Step A, leaving 260

facilities warranting further evaluation in Step B.

 Of the 1,149 facilities that reported non-zero emissions of Certain Glycol Ethers to air in

2010, 850 (76%) were screened out from further analysis based on Step A, leaving 273

facilities warranting further evaluation in Step B.

 Of the 1,099 facilities that reported non-zero emissions of Certain Glycol Ethers to air in

2011, 823 (75%) were screened out from further analysis based on Step A, leaving 276

facilities warranting further evaluation in Step B.

A detailed listing of each facility included in the Step A analysis is provided in Tables C1, C-2, and C-3 of Appendix C. For those facilities that reported total Certain Glycol Ethers 

emissions of more than the 4.9 tpy during 2009, 2010, and/or 2011, a more refined Step B 

screening evaluation was performed, as described below. 

6.2.3 Step B Prescreening Methodology 

Step B uses the same lookup table used for the Tier 1 analysis, which is a modified 

version of EPA’s Tier 1 lookup table (similar to the Tier 1 table used for the EGBE HAPs 

delisting petition), along with a small number of facility-specific parameters required to model 

the maximum impact from each facilitym – i.e. projected EGBE ambient air concentrations at or 

beyond the property boundary. Step B screening conservatively models all point-source 

emissions from a facility as if released from a single stack, and models fugitive releases as a 

single volume source, consistent with the EPA’s Tier 1 screening process (EPA 1992a). 

The parameters required for Step B for each facility are 

1. point and fugitive release heights for EGBE emissions sources at each facility;

2. distance from each EGBE emission source to fenceline; and

3. proportion of Certain Glycol Ethers emissions reported to TRI that is EGBE.

The values assumed for each of these parameters were based on site-specific data or

conservative default assumptions, as described in detail below. In addition, Step B was 

performed as a two-part process in order to reduce the number of facilities for which a survey 

was performed to collect additional site-specific information for this petition. 

m Facilities that closed after emissions were reported to the TRI were excluded from subsequent modeling 

tiers, given the inability to obtain site-specific data and the lack of current emissions from the facility.
42 

In the first part of Step B, existing available facility-specific information was used to 

perform a Step B screening, when such information had been previously obtained for facilities 

as part of ACC’s work on a previous version of the EGBE delisting petition that was prepared in 

2007, prior to EPA’s revision to the RfC and RfDn. For each facility, the combined point-source 

emissions were conservatively assumed to be released from a single stack with a release height 

equivalent to lowest release height among all of that facility’s stacks, thereby maximizing 

calculated off-site concentrations of EGBE in ambient air. The combined maximum annual 

average concentration of EGBE in ambient air associated with each facility’s point and fugitive 

emissions was calculated as follows: 

 The greatest emission height in the table that is less than or equal to the minimum stack

height for the facility’s EGBE point sources (stacks) was selected from the modified Tier

1 Table (see Appendix D Table D-1).

 The greatest distance in the table that is less than or equal to the minimum distance

between any facility stack and the property line was selected (regardless of whether it

corresponded to the facility stack with the minimum height).

 If available, the site-specific percent of Certain Glycol Ethers emissions that are EGBE

was applied to the point and fugitive source emission rates obtained from TRI. If not

available, all TRI-reported Certain Glycol Ethers releases were assumed to be EGBE.

 The appropriate normalized maximum annual concentration for the stack (based on the

selected release height and distance to property line) was identified and multiplied by the

annual combined point-source EGBE emission rate (in tpy) to obtain the maximum

annual average ambient air concentration estimate (in μg/m3) associated with EGBE

point-source emission from the facility.

 The appropriate normalized maximum annual concentration for the fugitive emissions

(using the default volume source parameters described below in combination with the

minimum reported site-specific property line distance) was identified in the modified

lookup table (Table D-1) and multiplied by the annual combined point-source EGBE

emission rate (in tpy). This calculation provides the annual average ambient air

concentration estimate (in μg/m3) associated with EGBE fugitive emissions from the

facility.

 The cumulative annual average ambient air concentration estimate associated with each

facility (in μg/m3) is conservatively calculated by adding the maximum predicted ambient

air concentrations associated with the point-source emissions with the maximum

predicted concentration associated with the fugitive emissions.

For all facilities lacking site-specific data from the 2007 EGBE TRI delisting petition

(numbers of facilities provided in Table 6-3), the following conservative default assumptions 

were used in the first part of the Step B screening: 

n Site-specific data had previously been compiled for certain facilities as part of the American Chemistry 

Council’s petition submitted in 2007, prior to EPA’s revision to the RfC and RfD for EGBE.
43 

1. All TRI-reported Certain Glycol Ethers releases to air were assumed to be EGBE.

2. Point emissions were modeled as a 10 meter stack.

3. Fugitive emissions were modeled as a volume source with a lateral dimension of 10

meters and a release height of 3 meters.

4. The distance from each emission source (point or volume) to the nearest fenceline was

assumed to be 50 meters.

These Step B default parameter assumptions for stack and fugitive emissions are

identical to those used in EPA’s exposure assessment for ethylene glycol (EPA 1995b) and the 

EGBE HAP delisting petition (CMA 1997). 

The total maximum impact (maximum predicted ambient air concentration at or beyond 

the fenceline) for each facility lacking site-specific parameters was calculated based on these 

default assumptions, as the sum of stack and fugitive impacts derived from the modified EPA 

Tier 1 lookup table (see Appendix D Table D-1). 

At the conclusion of the first part of the Step B analysis, each facility’s total maximum 

impact (maximum predicted ambient air concentration at or beyond the fenceline) was 

compared to the RfC for EGBE of 1.6 mg/m3. A survey was conducted for all facilities modeled 

using only default parameter assumptions for which the maximum predicted annual average 

concentration was above the RfC. The survey was intended to collect the site-specific 

information for use in the Step B screening. To increase responsiveness to the survey, the Can 

Manufacturers Institute (CMI) was enlisted to provide assistance with survey implementation for 

the CMI member facilities subject to this Step B screening. CMI identified contact names and 

addresses, distributed the Step B surveys to its member facilities, and provided survey follow 

up. Two facilities that were contacted as part of the Step B survey effort did not respond to the 

survey (Ford Dearborn and RR Donnelley Harrisonburg). For these two, facility-specific 

information was obtained from publically available sources to the extent that such information 

was publically available. In particular, EPA’s National Emissions Inventoryo (NEI) database was 

used to obtain information on facility stack heights. EPA prepares the NEI every three years, 

largely relying on EPA emission estimates and emission model inputs provided by state, local, 

and tribal air agencies for sources in their jurisdictions. As the NEI is a comprehensive and 

detailed estimate of air emissions of criteria pollutants (including volatile organic compounds or 

VOCs) from all air emissions sources, NEI’s stack information is a reasonable estimate of facility 

stack parameters for purposes of subjecting these facilities to Step B modeling. Because the 

NEI database does not contain information on distances between each stack and a facility’s 

property boundary, this distance was estimated for each stack by measuring distances between 

facility structures in aerial imagery and property boundaries obtained from municipal tax 

assessors’ databases. 

o http://www.epa.gov/ttn/chief/eiinformation.html. Data from both the 2005 and 2008 NEI datasets were

queried for this petition.
44 

Table C-4 in Appendix C summarizes all site-specific minimum stack height and distance 

to property line data obtained and used in the Step B screening analysis. Using these values, 

the maximum annual average concentration of EGBE in ambient air associated with each 

facility’s point-source emissions was calculated described above. As described previously, for 

all other facilities lacking site-specific data for the required input parameters, the Step B default 

assumptions were used for stack and fugitive emissions. The total maximum impact for each 

facility was calculated as the sum of the facility’s stack and fugitive impacts from the lookup 

table based on these assumptions, and then compared to the RfC for EGBE of 1.6 mg/m3. 

6.2.4 Step B Results 

Based on the above assumptions, the modified Tier 1 lookup table was used to obtain 

maximum impacts associated with EGBE point and fugitive emissions. The total maximum 

impact for each facility was then calculated by summing stack and fugitive impacts, and the total 

impact was compared to EGBE’s RfC of 1.6 mg/m3. The final results of the Step B screening are 

summarized below and in Table 6-3 and Appendix C (Table C-4): 

 Of the 260 facilities that reported non-zero emissions Certain Glycol Ethers to air during

2009 and that did not screen out based on Step A, 245 (94%) screened out from further

analysis at Step B, leaving 15 facilities warranting further evaluation in Tier 1.

 Of the 273 facilities that reported non-zero emissions Certain Glycol Ethers to air during

2010 and that did not screen out based on Step A, 258 (95%) screened out from further

analysis based on Step B, leaving 15 facilities warranting further evaluation in Tier 1.

 Of the 276 facilities that reported non-zero emissions Certain Glycol Ethers to air in 2011

and did not screen out based on Step A, 262 (95%) screened out from further analysis

based on Step B, leaving 14 facilities warranting further evaluation in Tier 1.

For the 2009 TRI reporting year, one facility did not screen out at Step B, but was

excluded from further analysis because it has since closed. Thus, it was not possible to obtain 

the site-specific data needed for more refined modeling. In any event, a facility that is not 

operating also would not emit Certain Glycol Ethers. This facility was the Aurora Casket in 

Aurora, IL. However, as discussed further in the uncertainty analysis (Section 6.6), if this facility 

was operating, it would be expected to screen out at the higher tiers based on the reported 

emissions of Certain Glycol Ethers when it was operating, as well as the demonstrated margin 

of safety provided by the analysis. 

6.3 Chronic Inhalation Exposure Assessment for Individual Facilities 

6.3.1 Tier 1 Screening for Individual Facilities 

6.3.1.1 Tier 1 Methodology 

Tier 1 screening was performed based on the Tier 1 of EPA’s Tiered Modeling Guidance 

(1992a) guidance using a slightly modified version of EPA’s Tier 1 lookup table (Appendix D, 

Table D-1). This approach is also consistent with that used for the EGBE HAPs delisting petition 
45 

(and the same used for Step B in this petition). As with Step B, the Tier 1 analysis for chronic 

exposures accounts for both fugitive emissions and individual point-source (stack) EGBE 

emissions. However, Tier 1 screening methodology differs from the Step B screening analysis in 

that Tier 1 screening individually evaluates each EGBE-emitting stack at a facility and each 

stack’s respective minimum distance to the fenceline (assuming all point-source emissions are 

emitted by the given stack); whereas, Step B conservatively evaluates a single hypothetical 

stack (assuming all point-source emissions are emitted by the given stack) using the minimum 

emission height and minimum distance to fenceline among all stacks at a given facility. In other 

words, the principle difference between Step B and Tier 1 is that Step B uses the minimum 

fenceline distance and stack height among all stacks at a facility, regardless of whether those 

values relate to the same stack. The other difference is that Tier 1 uses more site-specific 

information for the estimation of impacts from fugitive emissions (e.g, it uses the actual fenceline 

distance from fugitive sources rather than the minimum stack distance to represent fenceline 

distances from fugitive sources). 

The following site-specific information was required for Tier 1 modeling of each facility’s 

EGBE emissions: 

 The proportion of Certain Glycol Ethers emissions reported to TRI that is EGBE

 Annual emissions of EGBE (point and fugitive emissions) from each facility in tpy

 Height of the release point above ground in meters, for each point source

 Nearest distance to the property line in meters for point sources and fugitive sources

Point-source emissions release heights and receptor distances were derived from

facility-specific data obtained from facility survey responses. Those responses were collected as 

part of Step B. As with Step B, for facilities that did not provide facility-specific data, information 

was obtained from publically available sources to the extent relevant information was available 

(i.e. EPA’s NEI, aerial imagery, and municipal tax assessors’ information). Because nearly all 

facilities requiring Tier 1 modeling responded to the Step B survey, information from publically 

available sources was only needed for one facility in the Tier 1 screening for all three years of 

TRI data (2009-2011)–the RR Donnelly facility in Harrisonburg, Virginia. 

The Tier 1 point-source contribution to each facility’s maximum annual ambient air 

concentration of EGBE was determined for each stack at each facility using the following 

procedure: 

 The facility’s combined point-source EGBE emissions were assumed to be emitted from

each stack evaluated at the facility.

 The greatest emission height in the table that is less than or equal to the stack height for

the EGBE-emitting stack was selected from the modified Tier 1 Table (see Appendix D

Table D-1).

 The greatest distance in the table that is less than or equal to the distance between this

stack and the property line was selected.
46 

 The appropriate normalized maximum annual concentration for this stack (based on its

release height and distance to fenceline) was selected and multiplied by the annual

combined point-source EGBE emission rate (in tpy) to obtain the maximum annual

average ambient air concentration estimate (in μg/m3) associated with EGBE pointsource emission from the facility.

For Tier 1 screening, this procedure described above was performed for each EGBEemitting stack at a facility. Then, the maximum annual Tier 1 concentration among these 

individual stack analyses was conservatively selected to represent the maximum impact for 

facility point-source emissions of EGBE. Each facility’s fugitive EGBE emissions were assumed 

to be represented by a single volume source with a lateral dimension of 10 meters and a 

release height of 3 meters, as was the case for Step B. These assumptions are identical to 

those used in EPA’s exposure assessment for ethylene glycol (EPA 1995b) and the EGBE HAP 

delisting petition (CMA 1997). The distances to the nearest receptors for fugitive emissions were 

based on site-specific data from the survey responses or from measurements of the minimum 

distance from the fugitive source (facility building) to the property boundary based on aerial 

imagery. For each facility, the maximum Tier 1 modeled annual average concentration of EGBE 

in ambient air was conservatively assumed to be the sum of fugitive impact and worst-case 

stack impact for the facility. 

6.3.1.2 Tier 1 Results for Individual Facilities 

For each facility, the maximum chronic EGBE exposure (impact) in ambient air at or 

beyond the property boundary was determined as described above, and the result was 

compared to the RfC of 1.6 mg/m3 by calculating the chronic Hazard Quotient (HQ)p. Those 

facilities, for which the Tier 1 modeling result was less than the RfC, screened out and did not 

undergo further analysis. As summarized below and further detailed in Table 6-4 and Appendix 

D, two of the facilities subjected to Tier 1 screened out at this step: 

 For the 14 facilities reporting non-zero emissions Certain Glycol Ethers in 2009 that did

not screen out in Step B, 2 screened out in the Tier 1 screening step, leaving 12 facilities

for additional refined evaluation in Tier 2.

 For the 15 facilities reporting non-zero emissions Certain Glycol Ethers in 2010 that did

not screen out in Step B, 2 screened out in the Tier 1 screening step, leaving 13 facilities

for additional refined evaluation in Tier 2.

 For the 14 facilities reporting non-zero emissions Certain Glycol Ethers in 2011 that did

not screen out in Step B, 3 screened out in the Tier 1 screening step, leaving 11 facilities

for additional refined evaluation in Tier 2.

For facilities subject to Tier 1 screening, the Tier 1 results were approximately 24%

lower, on average, than Step B modeled impacts, with individual facility reductions (Step B to 

p The HQ is calculated as the ratio of the maximum estimated exposure concentration to the RfC. 
47 

Tier 1) in the maximum estimated EGBE exposure concentrations that ranged from 0% to 

approximately 70% (see Table 6-10). Few additional facilities screened out in the Tier 1 

screening. This result is not unexpected given general similarities between the Step B and Tier 

1 approaches (i.e. use of the same lookup table). As discussed above, the principle difference 

between Step B and Tier 1 for point source emissions is that Step B uses the minimum 

fenceline distances and stack heights, regardless of whether those values relate to the same 

emission source. Thus, small reductions from Step B to Tier 1 indicate that the worst-case 

hypothetical stack assumed for Step B had only slightly worse dispersion characteristics than 

the worst case individual stack selected from among each facility’s actual EGBE emitting stacks. 

Large reductions in the modeled exposure concentration from Step B to Tier 1 indicated that the 

Step B hypothetical stack height and minimum distance to fenceline assumptions had worse 

dispersion characteristics than any actual stack at the facility, further demonstrating the 

conservativeness of the Step B approach, with respect to Tier 1. Those facilities that did not 

screen out with the Tier 1 analysis were subjected to more refined Tier 2 modeling using EPA’s 

AERSCREEN air dispersion model, as discussed in the next subsection. 

6.3.2 Tier 2 Screening for Individual Facilities 

Chronic exposure Tier 2 modeling was performed for each facility that did not screen out 

using the Tier 1 screening analysis. Tier 2 modeling was performed using EPA’s recommended 

screening air dispersion model, AERSCREEN (EPA 2011a)q. AERSCREEN is designed to 

provide conservative estimates of ambient air concentrations. AERSCREEN requires additional 

facility-specific information beyond that which was required for the Tier 1 modeling. Specifically, 

the following facility-specific data is required for the Tier 2 modeling with AERSCREEN: (1) 

inside stack diameters; (2) exhaust velocities; (3) exit gas temperatures for all stack (point) 

releases; (4) extent of the facility property boundary; (5) building dimensions (used to 

parameterize fugitive EGBE emissions and evaluate the building downwash impacts for point 

sources); and (6) classification of the surrounding area as urban or rural. AERSCREEN also 

requires additional information related to land surface characteristics around each facility, as 

well as information on general meteorological characteristics for each site, which are used to 

generate the screening meteorological data applied with AERSCREEN. 

AERSCREEN models the worst-case 1-hour average ambient air concentration based 

on a closely spaced receptor grid around each facility, which extends outward a distance of 

5,000 meters (16,404 feet) and assumes the AERSCREEN default receptor spacing (within this 

grid) of 25 meters (82 feet). To estimate the maximum (chronic) annual average EGBE ambient 

air concentrations, AERSCREEN applies a scaling factor of 0.1 to the model-generated 

maximum 1-hour average concentration output, in accordance with EPA’s AERSCREEN 

q AERSCREEN is a screening-level air quality model based on AERMOD. AERSCREEN was 

implemented as the screening option in AERMOD, using a nonsequential meteorological data file 

representing a matrix of conditions, specifically worst-case meteorological conditions generated by the 

MAKEMET program.
48 

guidance (EPA 2011). For each facility modeled using this approach, the Tier 2 AERSCREEN 

result represents the combined impact of point and fugitive EGBE emissions. Because 

AERSCREEN is limited to modeling a single emission source in each model run, point and 

fugitive sources for a facility were modeled separately in Tier 2. The maximum impact for the 

facility’s total EGBE emissions (point and fugitive) was conservatively calculated as the sum of 

the maximum predicted AERSCREEN result for the point-source EGBE emissions combined 

with the maximum predicted AERSCREEN result for the facility’s fugitive EGBE emissions. 

A detailed discussion of inputs required by AERSCREEN and the methodology used to 

perform the modeling is provided in the remainder of this section. The results of the Tier 2 

Screening are provided in Section 6.3.2.5. 

6.3.2.1 AERSCREEN Meteorological Inputs 

AERSCREEN modeling was carried out using simulated location-specific (worst-case) 

screening meteorological data generated by MAKEMET program version 09183 (EPA 2011a), 

using local temperature extremes and surface characteristics information. The screening 

meteorological data produced by MAKEMET is a location-specific matrix of meteorological 

conditions intended to be representative the meteorological possibilities for that geographic 

location. The screening meteorological data was generated for each facility subject to Tier 2 

modeling using minimum and maximum ambient temperatures derived from historical daily 

temperature records at meteorological station closets to the facility, in the United States 

Historical Climatology Network. Extremes were determined using all historical records, spanning 

from 50 and over 100 years, depending on the station location. Site-specific surface 

characteristic data for the area around the facility were processed using United States 

Geological Survey National Land Cover Data (USGS) and EPA model AERSUFRACE (EPA 

2008). Surface characteristics (albedo, Bowen ration and surface roughness) were provided in 

the form of seasonal 12 sector characteristics representative of a one kilometer (km) radius area 

centered at the facility. The remaining MAKEMET input parameters, such as minimum wind 

speed, anemometer height, and specified number of wind directions etc. used the default 

AERSCREEN values. 

6.3.2.2 AERSCREEN Buildings and Receptor Location Inputs 

EGBE 1-hour modeled concentrations are calculated by AERSCREEN at specific 

locations within the user-specified grid. For the Tier 2 screening, the specified receptor grid for 

each facility extended outward from each facility’s property line to a distance of 5,000 meters 

(16,404 feet). The AERSCREEN default receptor spacing (within this grid) of 25 meters (82 feet) 

was used for the entire grid. 

Property boundary information required for AERSCREEN modeling was obtained from 

Tier 2 survey responses, or was obtained from publically available sources, as described for 

Step B and Tier 1 screening. The property plans and images obtained from the local agencies 

were georeferenced by overlaying them onto an aerial image from Google Earth. For Tier 2 

screening, the building dimensions, orientation, and distance to the property line were 
49 

determined using the Google Earth program. For buildings with multiple roof heights, each roof 

level was estimated using Google Earth’s “Street View” feature and comparing the building 

height to a known height (e.g., a door). In the absence of a clear street view image, the height of 

the building’s shadow was compared to that of a known shadow height such as that of a truck 

trailer or power line post, in order to estimate the building height. 

6.3.2.3 AERSCREEN Elevation Data Inputs 

AERSCREEN requires a determination whether complex terrainr

 is present within 5 km 

of the facility being modeled. Aerial imagery with elevations was also used to make that 

determination. Only one facility subject to Tier 2 modeling was identified as having the potential 

for complex terrain—the Crown facility in Weirton, WV (“Crown-Weirton”). All remaining sites for 

which Tier 2 modeling was required are located in areas with relatively flat terrain. For the 

Crown-Weirton facility in WV, potential effects of complex terrain were evaluated in 

AERSCREEN by incorporating digital elevation data from the National Elevation Dataset (NED) 

(USGS; EPA 2009), at the resolution of 0.33 arc-second. For this facility, the results of the 

AERSCREEN modeling with terrain effects produced slightly lower annual average EGBE 

concentrations than if terrain effects were omitted. Consequently, complex terrain effects are not 

significant at the Crown-Weirton WV facility. Nonetheless, to be conservative, the slightly higher 

AERSCREEN results that excluded terrain effects were used to represent the Tier 2 modeling 

results for this facility. 

6.3.2.4 AERSCREEN EGBE Point and Fugitive Source Inputs 

Tier 2 surveys were distributed to all facilities requiring Tier 2 modeling in order to collect 

the following facility-specific information: stack inside diameters, exit gas temperatures, building 

dimensions/configuration, and detailed information on the extent of the property boundary. As 

with the Step B/Tier 1 surveys, in order to increase responsiveness among the CMI-member 

facilities, CMI was enlisted to assist with survey distribution and follow up. 

Following survey data collection, facilities were categorized as either (1) facilities for 

which Tier 2 survey responses were received or (2) facilities for which Tier 2 survey information 

was not provided. For facilities that did not respond, the missing information was obtained from 

publically available sources, in the same manner as described above with respect to Step B and 

Tier 1 screening. Where required parameters were not available from either survey responses 

or publically available sources, default assumptions were used, as described further below. 

EGBE Point and Fugitive Emission Rates 

Stack and fugitive emission rates used for chronic exposure modeling in the model (in 

units of grams per second [gps]) were derived from annual Certain Glycol Ether emissions 

reported to TRI and the proportion of Certain Glycol Ether emissions that EGBE comprises (as 

r

 Complex terrain term refers to the setting where terrain features surrounding the facility, within a 5 km 

radius, exceed the stack height. 
50 

reported by each facility in their Tier 2 survey response). Where facilities did not provide this 

information, EGBE emissions were conservatively assumed to be 100% of the Certain Glycol 

Ether emissions reported to TRI. For evaluating chronic exposures, the EGBE emission rates 

used to model each point (stack) and volume source were developed from annual EGBE 

emissions for each facility, based on an assumption that facilities operate continuously. Based 

on survey responses received for facilities modeled during Tier 2 (surveys were received from 

92% of facilities modeled during Tier 2), this assumption is reasonable. All respondents 

indicated that their facilities operated continuously throughout the year. 

EGBE Point-Source Parameters 

Separate AERSCREEN model runs were performed for each facility’s stack emissions. 

In each model run, the facility’s total EGBE point-source emissions were assumed to exhaust 

from a single stack. Sources of information for stack parameters used in Tier 2 modeling are 

discussed below. 

For the two facilities that did not provide Tier 2 survey responses (i.e., RR Donnelley in 

Harrisonburg, VA and Crown in La Crosse, WI), information from the 2005 and 2008 NEI 

databases was used to estimate individual stack parameters. Based on the NEI database 

information, these facilities each reported VOC releases from a single stack at each facility. The 

NEI data provided the following stack parameters for these two facilities: stack height; stack 

inner diameter; exhaust temperature; and exit velocity. However, because the NEI database 

does not provide specific information on the location of the stacks at a facility, a sensitivity 

analysis was performed using AERSCREEN to determine the most conservative hypothetical 

stack location for the stack at each of these two facilities (i.e., the location that produced the 

highest modeled air concentration based on the stack parameters in the NEI database). First, to 

determine the likely location of the stack at each facility, aerial images were analyzed to first 

identify the section of each facility’s building(s) that was most likely associated with process 

emissions (i.e., the portion of the building where stacks were visible). For point-sources (stacks), 

this analysis involved modeling a range of stack-to-property distances and stack-to-building 

configurations, including hypothetical stack locations that would be expected to result in higher 

modeled concentrations due to building downwash effects or proximity of the source to the 

property line. The worst-case stack location at each facility as determined in the sensitivity 

analyses was used for the final point-source AERSCREEN model run for these two facilities. 

For facilities that provided Tier 2 survey responses, AERSCREEN was used to model 

each facility’s total point-source EGBE emissions. For each stack determined to emit or 

potentially emit EGBE at the facility, individual AERSCREEN model runs were performed. For 

each model run, the facility’s combined EGBE stack emissions were assumed to exhaust from 

each stack independently. The AERSCREEN model run that resulted in the highest predicted 

annual average EGBE concentration for a facility was conservatively selected to represent the 

worst-case (maximum) predicted airborne EGBE concentration for all point-source EGBE 

emissions from that facility. 
51 

EGBE Fugitive Source Parameters 

For Tier 2, fugitive EGBE emissions were modeled as a single volume source, where the 

initial vertical dimension (y) was derived from the facility’s roof height and the initial horizontal 

dimension (z) was derived from the building area, consistent with EPA guidance for selecting 

volume source parameters (EPA 1995d). The information provided by the facilities in Tier 2 

survey indicates that fugitive EGBE emissions are released from rooftop vents on the portion of 

the building encompassing manufacturing operations. The release height of the volume source 

was therefore considered to be equivalent to each building’s height. For facilities that did not 

respond to the Tier 2 survey and that had multiple buildings on site, aerial images were 

examined to identify likely production areas, based on presence of stacks, roof vents, etc. 

Fugitive emissions were assumed to be associated with those likely production areas. For all 

facilities (both with and without Tier 2 survey responses), volume sources were checked for the 

presence of an “exclusion zone condition” in AERSCREEN. Specifically, an exclusion zone 

condition applies if the distance between the volume center and closest property line (referred to 

as “PD”) is less than or equal to 2.15 times the initial horizontal lateral dimension. In such cases, 

the volume source lateral dimension was reduced to ensure that the resulting z was equal to 

(PD-1)/2.15. 

6.3.2.5 Tier 2 Results 

For each facility in the three TRI emission data sets (2009, 2010, 2011 calendar years) 

subjected to Tier 2 screening, a facility’s Tier 2 worst-case (maximum) predicted airborne EGBE 

concentration was compared to the EGBE RfC of 1.6 mg/m3. Facilities for which the worst-case 

Tier 2 concentration of EGBE in ambient air was less than the RfC screened out and required 

no further analysis. As summarized in Table 6-5 and detailed in Appendix D, all facilities 

screened out at Tier 2 because all worst-case EGBE airborne concentrations at or beyond the 

property boundaries were predicted to be below the EGBE RfC of 1.6 mg/m3. The results of the 

Tier 2 chronic exposure assessment are summarized below: 

 For the 12 facilities retained for Tier 2 modeling based on 2009 emissions, the maximum

predicted annual average concentration was 1.20 mg/m3 (i.e., 75% of the RfC). The

minimum and average concentrations modeled for all facilities were 0.25 mg/m3 and

0.54 mg/m3 (corresponding to 15% and 33% of the RfC), respectively.

 For the 13 facilities retained for Tier 2 analysis based on 2010 emissions, the maximum

predicted annual average concentration was 1.04 mg/m3 (i.e., 65% of the RfC). The

minimum and average concentrations modeled for all facilities were 0.25 mg/m3 and

0.54 mg/m3 (corresponding to 15% and 33% of the RfC), respectively.

 For the 12 facilities retained for Tier 2 analysis based on 2011 emissions, the maximum

predicted annual concentration was less than or equal to 1.16 mg/m3 (i.e., 73% of the

RfC). The minimum and average concentrations modeled for all facilities were 0.24

mg/m3 and 0.51 mg/m3 (corresponding to 15% and 31% of the RfC), respectively.

Of the facilities for which Tier 2 modeling was performed, the Crown facility in Lawrence,

MA produced the highest modeled chronic EGBE impacts for all three years, with a maximum 
52 

annual average EGBE concentration of 1.20 mg/m3 (i.e., 75% of the RfC), based on 2009 

emissions data. Despite the use of very conservative assumptions and the inherent 

conservatism of the AERSCREEN model and screening meteorological data, the Tier 2 

screening results demonstrate that EGBE emissions from individual facilities do not pose a 

significant risk of chronic health effects at or beyond the property boundaries for individual 

facilities. AERSCREEN model output files are provided in Appendix F. 

Although all facilities screened out at Tier 2, in order to further test the conservatism of 

the screening procedure and to estimate the margin of safety provided by the screening 

procedure, six facilities that had screened out in Tier 2 modeling were subjected to additional 

analysis using EPA’s long-term Tier 3 analysis. This analysis is described in Section 6.6, which 

discusses an analysis of uncertainty and conservatism of assumptions used to model chronic 

exposures from individual facilities. 

6.4 Chronic Inhalation Exposure Assessment for Clusters of Facilities 

The preceding analysis focused on potential risks associated with exposures to 

emissions from individual facilities. In the event that several emitting facilities are located within 

a limited geographic area, local residents may be exposed to the combined emissions from 

clusters of facilities. Therefore, the potential for chronic EGBE ambient air impacts from clusters 

of facilities was also evaluated as part of this petition. 

Zip codes were selected as the geographic area used in this analysis, which evaluated 

potential chronic EGBE concentrations in ambient air from facilities located within all zip codes 

containing at least two facilities reporting non-zero emissions of Certain Glycol Ether emissions 

to TRI in 2009, 2010, and 2011. For the reasons described in greater detail below (Section 

6.5.3), the zip code approach used in this petition is more conservative than the zip 

code/census tract approach used by Dolinoy and Miranda (2004). In addition, the method used 

for this facility cluster evaluation is similar to, but more refined than use of the metropolitan 

areas for the cluster evaluation used in the HAP delisting petition, a methodology EPA reviewed 

and accepted as appropriate and conservative that metropolitan area cluster evaluation as part 

of the HAPs delisting decision (68 FR 65653). 

6.4.1 Facility Cluster Evaluation Tiered Screening Methodology 

A conservative tiered modeling approach was also used to evaluate potential chronic 

airborne EGBE concentrations in ambient air from clusters of proximate facilities. The 

methodology used is analogous to the tiered modeling approach applied to individual facilities 

(see Sections 6.2 and 6.3), as discussed further below. 

6.4.2 Step A Screening (Cluster Evaluation) 

For the facility cluster evaluation, Step A was used to prescreen the inventory of all 

facilities that reported non-zero emissions of Certain Glycol Ethers to TRI for the 2009, 2010 

and 2011 reporting years. Any zip code that contained at least two facilities reporting emissions 

of Certain Glycol Ethers during these three years was retained for evaluation in Step A. As with 
53 

the Step A screening performed on individual facilities, each facility’s annual TRI combined 

stack and fugitive Certain Glycol Ethers emissions were conservatively combined and used to 

represent the facility’s total annual EGBE emissions. 

This approach differs from that employed by Dolinoy and Miranda (2004) in their 

evaluation of TRI-reported and potential non-TRI-reported emissions, but is a more conservative 

and appropriate basis for screening the clusters of facilities throughout the United States. 

Dolinoy and Miranda (2004) evaluated different spatial scales for estimating exposures to glycol 

ethers by modeling potential air concentrations at specific locations. Their approach took into 

account the relative distances to each source and the dispersion that occurs over those 

distances. They concluded that, for the purposes of determining spatially explicit exposure 

patterns, finer-grained resolution (e.g., census blocks) modeling revealed potential localized 

exposure hot-spots that are not apparent when modeling at higher resolution (e.g., zip codes). 

The screening approach in this petition, however, is not spatially explicit and combines facilities 

over geographic areas and treats them as a single source. Therefore, this approach does not 

account for air dispersion that occurs between facility boundaries. In addition, pooling facilities 

from larger geographic areas (i.e., zip codes rather than census blocks) captures more facilities 

within a single unit, and thus is considered more conservative than use of the potentially smaller 

subset of facilities when using smaller geographic areas. 

In the facility cluster evaluation, Step A used the same “inverted” Tier 1 table described 

in Section 6.2.1. The inverted Tier 1 table provides annual EGBE emission thresholds 

(expressed as tpy) above which the annual average EGBE concentration would be predicted to 

exceed the RfC of 1.6 mg/m3. Stack and fugitive emissions of Certain Glycol Ethers from all 

facilities in the same zip code were summed, and treated as if exhausted from a single point 

source with an emission height of zero meters and a minimum distance to fenceline of 50 

meters. Based on the EGBE RfC of 1.6 mg/m3, the corresponding threshold EGBE annual 

threshold emission rate for Step A screening is 4.9 tpy. Consistent with the Step A screening for 

individual facilities, any zip code for which the combined EGBE (point and fugitive) exceeded 

4.9 tpy, was retained for further refined analysis. 

The number of zip codes containing more than one facility reporting Certain Glycol Ether 

emissions was 158 in 2009, 164 in 2010, and 159 in 2011 (Table 6-6). The greatest number of 

facilities within a single zip code was 6 (zip code 60007, Elk Grove Village, IL). These zip codes 

were subjected to the Step A screening, with the following results: 

 Of the 158 zip codes subjected to Step A screening for the 2009 TRI reporting year, 58

had cumulative emissions of Certain Glycol Ethers (assumed to be 100% EGBE) greater

than 4.9 tpy;

 Of the 164 zip codes subjected to Step A screening for the 2010 TRI reporting year, 62

had cumulative emissions of Certain Glycol Ethers (assumed to be 100% EGBE) greater

than 4.9 tpy; and

 Of the 159 zip codes subjected to Step A screening for the 2011 TRI reporting year, 65

had cumulative emissions of Certain Glycol Ethers (assumed to be 100% EGBE) greater

than 4.9 tpy.
54 

Those zip codes with combined emissions of Certain Glycol Ethers above 4.9 tpy 

underwent Step B screening, as discussed below. 

6.4.3 Step B Screening (Cluster Evaluation) 

The purpose of the Step B screening for facility clusters is to provide an initial 

assessment of chronic exposures for geographic areas (zip codes) that contain more than one 

facility emitting EGBE (or potentially emitting EGBE—i.e., reported TRI emissions of Certain 

Glycol Ethers). This screening consisted of two components. The first component included zip 

codes where emissions were dominated by a single facility. The second component included 

the remaining zip codes, where emissions were more evenly distributed across multiple 

facilities. 

In order to identify the clusters dominated by one facility, the Certain Glycol Ethers 

emissions from the top reporting facility were compared to the cumulative Certain Glycol Ethers 

emissions for the zip code. If the percentage of cumulative emissions from one facility was at 

least 90% of the total, the zip code was evaluated as part of the first component of the Step B 

screen (i.e., dominated by a single facility). Any zip code for which the percentage of emissions 

from a single facility was less than 90% of the total was evaluated as part of the second 

component of the Step B screening. 

For those zip codes evaluated under the first component of the facility cluster Step B 

screening, the maximum impacts from the individual facility Step B screening (Section 6.2.4 and 

Appendix C, Table C-4) for each facility in the zip code were compared to the RfC of 1.6 mg/m3. 

If the maximum annual average EGBE concentration among all facilities in the zip code was 

less than 90% of the RfC, the zip code screened out and no further analysis was required. The 

cumulative zip code emissions from those zip codes that did not screen out at this point were 

compared to a threshold emissions level derived from the inverted Tier 1 lookup table 

developed for the Step A screening (Table 6-1). The threshold emissions level was determined 

based on the following assumptions, consistent with the Step B screening for individual facilities 

(Section 6.2.3): 

1. All air emissions of Certain Glycol Ethers were assumed to be EGBE.

2. All air emissions in the zip code were assumed to be released from a single point source

that was 10 meters high and 50 meters from the fenceline.

3. Fugitive emissions were combined with point-source emissions.

Based on these conservative assumptions, the threshold emissions rate that would

correspond to the RfC is 75.8 tpy (Table 6-1). Zip codes with cumulative emissions greater than 

75.8 tpy were retained for more refined facility cluster evaluation. The screening results from 

this first analysis are summarized below: 

Based on the 2009 TRI inventory of facilities emitting Certain Glycol Ethers, 31 of the 58 

zip codes that did not screen out at Step A contained one facility that represented more than 

90% of the Certain Glycol Ethers emissions released in that zip code. The estimated maximum 

annual average EGBE concentrations for all 31 zip codes were less than 90% of the RfC. Thus, 
55 

none of the 31 zip codes were retained for the more refined Tier 1 analysis based on 2009 TRI 

data. 

Based on the 2010 TRI inventory of facilities emitting Certain Glycol Ethers, 30 of the 62 

zip codes that did not screen out at Step A contained one facility that represented more than 

90% of the Certain Glycol Ethers emissions released in that zip code. The estimated maximum 

annual average EGBE concentrations for 29 of these zip codes were less than 90% of the RfC. 

Thus, one of these zip codes (i.e., 27320 in Reidsville, NC), was retained for the more refined 

Tier 1 analysis based on 2010 TRI data. 

Based on the 2011 TRI inventory of facilities emitting Certain Glycol Ethers, 30 of the 64 

zip codes that did not screen out at Step A contained one facility that represented more than 

90% of the Certain Glycol Ethers emissions released in that zip code. The estimated maximum 

annual average EGBE concentrations for 29 of these zip codes were less than 90% of the RfC. 

Thus, one of these zip codes (i.e., 27320 in Reidsville, NC), was retained for the more refined 

Tier 1 analysis based on 2011 TRI data. 

The second component of the Step B facility cluster evaluation evaluated all remaining 

zip codes that contain at least two facilities emitting EGBE (or potentially emitting EGBE—i.e., 

reported TRI emissions of Certain Glycol Ethers) and were not included in the preceding 

analysis. This second component of Step B was conducted for the following zip codes: (1) 24 

zip codes for the 2009 TRI emission inventory; (2) 26 zip codes for the 2010 TRI emission 

inventory; and (3) 31 zip codes for the 2011 emission TRI inventory). The cumulative EGBE 

emissions (sum of the EGBE emissions for the TRI-reporting facilities in the zip code) for each 

zip code were compared to the threshold emissions level of 75.8 tpy, described above. 

Based on these conservative assumptions, the majority of zip codes evaluated in the 

second component of Step B screened out. Those retained are shown in Table 6-7 and 

summarized below: 

21 of the 24 zip codes analyzed based on the 2009 TRI emission inventory screened out 

at Step B. The three zip codes retained for more refined modeling were 60609 in Chicago, IL; 

45840 in Findlay, OH; and 26062 in Weirton, WV. 

22 of 26 zip codes analyzed based on the 2010 TRI emission inventory screened out at 

Step B. The four zip codes retained for more refined modeling were 60609 in Chicago, IL; 

45840 in Findlay, OH; 46350 in La Porte, IN; and 26062 in Weirton, WV. 

29 of 31 zip codes zip codes analyzed based on the 2011 TRI emission inventory 

screened out at Step B. The two zip codes retained for more refined modeling were 45840 in 

Findlay, OH and 26062 in Weirton, WV. 

Combining the results from the two component analyses of the Step B screening, a total 

of five unique zip codes required further refined modeling in the Tier 2 screening using 

AERSCREEN to determine if long-term EGBE exposures resulting from EGBE emissions from 

clusters of facilities in these zip codes exceed the RfC, when less conservative assumptions are 

used. This included three zip codes based on the 2009 TRI data, five zip codes for 2010, and 

three zip codes for 2011. 
56 

6.4.4 Tier 2 Screening (Cluster Evaluation) 

Because the initial Tier 1 lookup table for point sources does not lend itself for use in 

screening clusters of sources beyond the initial Step B screening step described in the previous 

section, Tier 1 analysis was not conducted as part of the cluster evaluation. As such, the five zip 

codes that did not screen out during Step B (cluster evaluation) were subjected to Tier 2 

modeling instead. The Tier 2 modeling for the facility clusters was carried out using the same 

general approach used for the Tier 2 AERSCREEN modeling of individual facilities described in 

Section 6.3, with some minor differences discussed below. 

AERSCREEN modeling of each facility within the five zip codes was performed using 

location-specific screening meteorological data generated by MAKEMET. However, while local 

meteorological inputs into the MAKEMET (e.g., temperature extremes) were identical for all 

facilities within the zip code, surface characteristic inputs were unique for each facility and were 

therefore based on the land cover characteristics of a 1-km radius area surrounding the 

individual facility. All individual facilities within the five zip codes were modeled assuming flat 

terrains and using the same receptor grid configuration described in Section 6.3. As with the Tier 

2 modeling of individual facilities, AERSCREEN 1-hour concentration results were converted to 

maximum annual average (chronic) impacts for comparison to the RfC, by multiplying the 1-hour 

average values by the scaling factor of 0.1t

. 

As with the Tier 2 analysis for individual facilities, the facility cluster evaluation included 

facilities that provided Tier 2 survey responses and those that did not. Of the 12 facilities 

included in the facility cluster evaluation, 7 provided Tier 2 survey responses and 5 did not. For 

facilities that provided Tier 2 survey responses, source parameterization and AERSCREEN 

modeling of each facility was carried out in the same manner as described in Section 6.3.2 for 

individual facilities. Modeling was based on facility-specific information provided in the survey 

response, including actual stack parameters (stack height, diameter, temperature, and exit 

velocity), building dimensions, property boundary information and urban or rural setting 

designation. 

 Five facilities (one in each of these five zip codes) did not provide Tier 2 survey 

responses. For these facilities, point and fugitive emission source parameter inputs required for 

Tier 2 modeling were derived from publically available sources. Where the NEI database 

provided information on stack parameters, a sensitivity analysis was performed to determine the 

worst-case stack-to-building configuration and stack-to-fenceline distance, in the same manner 

s As discussed in Section 6.2.3.2, with the exception of one facility in WV, all other facilities subject to Tier 

2 modeling were located in areas of relatively flat terrain. For the facility in WV, the potential effects for 

complex terrain were evaluated in AERSCREEN by incorporating digital elevation data. For this facility, 

the results of the AERSCREEN modeling with terrain effects produced slightly lower annual average 

EGBE concentrations than if terrain effects were omitted. Consequently, complex terrain effects are not 

significant at this facility. Nonetheless, to be conservative, the slightly higher AERSCREEN results that 

excluded terrain effects were used to represent the Tier 2 modeling results for this facility. 

t

 To estimate the maximum (chronic) annual average EGBE ambient air concentrations, AERSCREEN 

applies a scaling factor of 0.1 to the model-generated maximum 1-hour average concentration output, in 

accordance with EPA’s AERSCREEN guidance (EPA 2011)
57 

described in Section 6.3.2. A summary of the treatment of NEI stack data for these facilities is 

provided below: 

 For two facilities, Whirlpool in Findlay, OH and Dystar LP in Reidsville, NC, the NEI

database provided information on a single stack at each facility. For these, stack

parameters from the NEI database were used for the Tier 2 modeling, and the most

conservative location for the single stack was determined through a sensitivity analysis

performed in the same manner described for the Tier 2 screening for individual facilities

(see Section 6.3.2).

 For two other facilities, Edsal in Chicago, IL and Roll Coater in La Porte, IN, the NEI

database provided information on multiple stacks at each facility (e.g., NEI provides

information on 20 stacks for Edsal). For these facilities, the sensitivity analysis was

simplified by selecting the most conservative combination of stack parameters among all

stacks for which parameters were provided (i.e. conservative, from the perspective of

resulting in the highest modeled annual average EGBE concentration). In other words,

the hypothetical stack used in the Tier 2 modeling for that facility would have the height

of the shortest NEI reported stacks, the exhaust temperature of the coolest stack, and

the smallest diameter and the lowest velocity among all NEI stacks reported for the

facility. This practice yields a hypothetical stack with the most conservative combined

assumptions (more conservative than any of the individual stacks), and thus

approximates the worst possible dispersion scenario for point-source emissions. The

most conservative location for this hypothetical stack was determined through a

sensitivity analysis performed in the same manner described for the Tier 2 screening for

individual facilities.

 For the fifth facility (i.e., Roll Coater in Weirton, WV) lacking a survey response, the NEI

database included no information on stack parameters. For this facility, all point-source

releases were therefore very conservatively modeled as fugitive emissions for the Tier 2

modeling (i.e. both point and fugitive emission rates were combined and modeled as a

single volume source centered on the presumed production area of the facility building).

Fugitive emissions at each facility were modeled as a volume source, with modeling

input parameters developed in the same manner as described in Section 6.3.2. The maximum 

modeled chronic impact for each facility in the zip code was calculated as the sum of the 

modeled maximum concentration from the volume source and the worst-case stack. 

The maximum annual average air concentration for the entire zip code was calculated as 

the sum of the maximum impacts from each of the modeled facilities within the zip code 

(calculated using AERSCREEN in the same manner as described in Section 6.3.2). The 

individual facility maximum impacts were summed, regardless of where these maximum impacts 

occurred—i.e. for each facility modeled, the maximum impact for that facility may not occur at 

the same receptor location as the other facilities. The Tier 2 results of the maximum chronic 

(annual average) impacts for each cluster (zip code) are presented in Table 6-8 and modeling 

output files for the Tier 2 modeling are provided in Appendix F. 
58 

As shown in Table 6-8 for all three inventories (2009, 2010, and 2011), projected worstcase annual average EGBE concentrations at or beyond the property line for all five zip codes 

were appreciably below the RfC of 1.6 mg/m3, as summarized below: 

 Based on 2009 TRI emissions of facilities emitting Certain Glycol Ethers, the predicted

maximum annual average concentration across all five zip codes modeled using Tier 2

was 0.91 mg/m3 (i.e., 57% of the RfC). The minimum and average results for the five zip

codes were 0.26 mg/m3 and 0.52 mg/m3, respectively (corresponding to 16% and 32%

of the RfC, respectively).

 Based on 2010 TRI emissions of facilities emitting Certain Glycol Ethers, the maximum

annual average concentration across all five zip codes modeled using Tier 2 was 1.16

mg/m3 (i.e., 73% of the RfC). The minimum and average results for the five zip codes

were 0.27 mg/m3 and 0.58 mg/m3 respectively (corresponding to 17% and 36% of the

RfC, respectively).

 Based on 2011 TRI emissions of facilities emitting Certain Glycol Ethers, the maximum

annual average concentration across all five zip codes modeled using Tier 2 was 0.74

mg/m3 (i.e., 47% of the RfC). The minimum and average results for the five zip codes

were 0.26 mg/m3 and 0.49 mg/m3 respectively (corresponding to 16% and 31% of the

RfC, respectively).

Tier 2 modeling of the zip codes based on 2009, 2010, and 2011 TRI data indicated that the 

Chicago IL zip code (facility cluster) yielded the highest predicted chronic EGBE impact for all 

years evaluated, with a maximum calculated maximum annual average concentration of 1.16 

mg/m3 (i.e., 73% of the RfC) based on 2010 emissions. 

Section 6.5 provides an analysis of uncertainty and conservatism of assumptions used in 

modeling chronic exposures from clusters of EGBE-emitting facilities. 

6.5 Uncertainty Analysis 

Based on the results of the tiered modeling approach for individual facilities and clusters 

of facilities presented in Sections 6.2 through 6.4 of this petition, the maximum annual average 

emissions of EGBE are not predicted to exceed the RfC for EGBE. Thus, even under highly 

conservative assumptions, EGBE emissions from facilities in the U.S. do not pose a risk to 

populations living around the facilities. 

Nonetheless, to further demonstrate the margin of safety for this conclusion, all facilities 

and zip code clusters screened out at Tier 2 modeling were subjected to more refined modeling 

using AERMOD (Tier 3). In addition, the conservatism of assumptions made during each of the 

steps of the tiered analysis is discussed in further detail in this uncertainty analysis, and 

generally would apply to both the chronic and acute tiered modeling, although for the acute 

exposure assessment additional discussion of uncertainty is provided in the acute MOE 

assessment found in Section 6.6.3. 
59 

6.5.1 Conservatism of Step A through Tier 2 

In several ways, Step A and Step B provide a more conservative screening approach 

than EPA’s long-term Tier 1 analysis: 

 In Step A, all reported Certain Glycol Ethers emissions were assumed to be EGBE, even

though EGBE represents only about 52% of the market share (SRI 2010).

 In Steps A and B, all stack emissions were conservatively assumed to exhaust from one

stack.

 In Step A, all emissions data were initially evaluated as if they are emitted through a

single stack with a release height of 0 meters with a distance to fenceline of 50 meters.

This scenario is not likely to occur often, if at all. The conservatism of the default

assumption of a 0-meter emissions source height was evaluated based on the sitespecific data provided by the facilities. The minimum release height reported is just over

3 meters. Furthermore, if the Step A screening is based on a release height of 2 meters

and a distance to fence line of 10 meters, the screening threshold is 8.6 tpy (Table 6-1),

75% higher than the screening emission threshold used in our analysis.

The Tier 1 screening analysis also affords significant conservatism in the treatment of

point and fugitive emission sources of EGBE: 

 For Tier 1 screening, all point-source emissions are conservatively assumed to be

released from a single stack from the list of all stacks onsite that could possibly release

EGBE. The single stack selected was the one that yields the maximum potential

fenceline concentration, regardless of whether it is the stack from which the majority of

the EGBE is actually released.

 For Tier 1 screening, all fugitive emissions are assumed to be released from a single

fugitive source, wherein the distance to fenceline was determined by the minimum

distance from the edge of the fugitive source to the property boundary.

Conservatism of the Tier 2 analysis is also present on several levels. It is inherent in the

use of a screening-level model such as AERSCREEN, and in the use of screening meteorology 

used by the model. Conservatism is also provided by the selection of parameters used for the 

Tier 2 modeling of each facility’s point and fugitive EGBE emissions, and in the methodology 

used to calculate the combined point and fugitive impacts for each facility. These various levels 

of conservatism in the Tier 2 analysis are discussed in more detail in the remainder of this 

section. 

Screening air quality models such as AERSCREEN are conservative by design, and are 

intended to provide the means for performing a prescreening analysis prior to engaging in full 

scale modeling using models such as AERMOD/AERMET (EPA 2012, 2004d). AERSCREEN’s 

conservatism stems from the following key model characteristics and assumptions: 

 The use of screening meteorological data in AERSCREEN (generated by MAKEMET) is

designed to include the worst-case meteorological extremes for a given geographic

location, including the least favorable dispersion conditions, which would be expected to

produce the highest modeled ambient air concentrations (impacts). These most extreme
60 

combinations of meteorological parameters in the screening meteorological dataset 

would rarely if ever occur in actual meteorological data and thus represent a level of 

conservativeness in the AERSCREEN modeling. 

 The screening meteorological data is a theoretical sequence of meteorological hourly

conditions that AERSCREEN uses to predict the maximum 1-hour average

concentration at each prescribed location. As discussed above, for purposes of

evaluating maximum predicted long-term air concentrations in the Tier 2 modeling, this

maximum 1-hour result is scaled by 0.1 to approximate a maximum annual average air

concentration. The resulting maximum annual average result is therefore based on a

worst-case meteorological hour. This practice is far more conservative than the

approach used in AERMOD, which employs actual meteorological data to calculate an

annual average result from all meteorological hours.

 While AERSCREEN uses the same algorithms as the full-scale dispersion model

AERMOD, AERSCREEN employs certain conservative assumptions not used in

AERMOD modeling. For instance, information on the closest distance between the

source and the fenceline is treated conservatively in AERSCREEN, which uniformly

assumes this distance for all directions from the emission source. AERMOD instead

allows that the property boundary be defined realistically at varying distances to the

source in different directions.

In addition to the built in conservatism of the AERSCREEN model, the assumptions

used in modeling point-source emissions at each facility provides an additional level of 

conservatism in Tier 2 modeling, as summarized below: 

 As with the very conservative Step A screening, stack impacts were modeled as if each

facility’s total stack emissions were emitted from the single stack that produced the

worst-case results, even though point-source emissions would actually be distributed

across multiple stacks (providing greater dispersion).

 AERSCREEN is capable of modeling only one source at the time. As such, for multiple

emission sources such as those modeled for this petition, the combined contribution of

all sources at a facility are conservatively calculated as the sum of maximum results

from the individual emission source model runs. In almost all circumstances, this

practice would overestimate the result achieved by modeling all emission sources

simultaneously.

In addition to the conservatism of the assumptions and methods used in the Tier 2

modeling of individual facilities, the facility cluster evaluation also incorporated the following 

additional conservative elements: 

 Each of the five zip codes (clusters) modeled using the Tier 2 methodology included one

facility for which a Tier 2 survey response was not received. For these facilities, highly

conservative assumptions were used to model facility EGBE emissions. Specifically,

point-source emission for each of these facilities were conservatively modeled using the

least favorable stack location (based on a sensitivity analysis of predicted AERSCREEN

results) and the most conservative combination of stack parameters reported to the NEI.
61 

In addition, all Certain Glycol Ether reported air emissions from these facilities were 

conservatively assumed to be 100% EGBE. 

 As an additional source of “spatial” conservatism in the AERSCREEN modeled results

for each cluster, the cumulative impacts from multiple facilities in each zip code modeled

were calculated as the sum of the maximum predicted impact from each facility at or

beyond the property boundary, regardless of the specific (receptor) location that this

impact was determined by the model to occur. Given that the receptor location of

maximum impact for each facility is invariably closely located to the facility boundary,

and distances between individual facilities in certain clusters are as much as 1,500

meters, the estimated maximum cumulative impact for each cluster was almost certainly

overestimated.

 And finally, in addition to the spatial conservatism resulting from summing each facility

impacts irrespective of the receptor location at which they occurred, a “temporal”

conservatism is also present in the Tier 2 application of AERSCREEN for modeling

facility clusters. AERSCREEN calculates a worst-case result for each facility emission

source, which is based on the worst-case meteorological hour in the screening

meteorological data set. This worst-case meteorological hour is likely to differ from

emission source to emission source at a facility as well as from facility to facility. As

such, the summing of maximum impacts across facilities introduces a level of temporal

conservatism that almost certainly overestimates the maximum cumulative impact for

each cluster.

Even though all individual facilities and facility clusters (zip codes) with non-zero Certain

Glycol Ether emissions reported to TRI for 2009, 2010, and 2011 screened out at the 

conservative Tier 2 modeling step (i.e. the maximum annual average EGBE air concentrations 

at/beyond facility boundaries were below the RfC), in order to further demonstrate the margin of 

safety afforded in the tiered modeling approach, Tier 3 modeling using the EPA-approved 

refined air dispersion model AERMOD was performed, as discussed below. 

6.5.2 Tier 3 Modeling (Individual Facilities) 

 As a further demonstration of the conservatism of the tiered modeling approach for 

individual facilities, and to provide further evidence of the “margin of safety” afforded for all 

facilities that screened out at Step A, Step B, Tier 1, or Tier 2, six facilities were modeled using 

EPA’s regulatory AERMOD (EPA 2004d, EPA 2012) and AERMET (EPA 2004f, EPA 2011b) 

system (i.e., Tier 3 of the tiered modeling approach). These six facilities all previously screened 

out at Tier 2 based on their 2009, 2010, and 2011 TRI emissions and were also facilities that 

provided detailed information in Tier 2 survey responses. They included 

 the three individual facilities that had the highest Tier 2 modeled maximum annual

average EGBE concentrations (Crown Beverage in Lawrence, MA, Rexam in Kent, WA,

and Rexam in Bishopville, SC);

 two additional facilities that were also part of the Tier 2 facility cluster evaluations, and

which were top emitters within their respective zip codes (Crown Beverage in Weirton,

WV, Rexam in Chicago, IL); and
62 

 one additional facility that reported the maximum annual emissions of Certain Glycol

Ethers in the TRI from 2009 through 2011 (Rexam in Winston Salem, NC).

The six facilities subjected to Tier 3 modeling were also among the top 4% of emitters

among all facilities reporting Certain Glycol Ethers emissions in their TRI reports for 2009 

through 2011 (see Appendix B Tables B-1 through B-3). For each of these facilities, EGBE 

comprised between 85% and 100% of each facility’s Certain Glycol Ether reported emissions. 

Tier 3 modeling using AERMOD is the most refined analysis step, and is consistent with 

EPA’s Tiered Modeling Guidelines (EPA 1992a). The Tier 3 analysis was conducted with the 

AERMOD model (v.12345, EPA 2012) in accordance with EPA’s Guideline on Air Quality 

Models (40 CFR Part 51 Appendix W), EPA’s tiered modeling guidelines (EPA 1992a), the 

AERMOD User Guide (EPA 2004d), and the AERMOD Implementation Guide (EPA 2009). 

Compared to Tier 2 modeling, Tier 3 modeling with AERMOD provides more realistic (yet still 

conservative) estimates of projected impacts of EGBE emission at locations at or beyond each 

facility’s fenceline. The principle refinements afforded by AERMOD over AERSCREEN are 

summarized below, and discussed in more detail in the remainder of this section: 

 The Tier 3 AERMOD modeling uses actual meteorological data from the closest weather

station, rather than the artificially generated screening meteorological data sets used

with AERSCREEN.

 Tier 3 modeling takes into account the variability of the actual property boundary, rather

than using a single distance between each emission source and the property boundary,

as is assumed for AERSCREEN. This refinement allows a more realistic treatment of

dispersion effects between a stack and receptors.

 The Tier 3 modeling incorporates the distribution of EGBE emissions across stacks at a

facility, rather than assuming that all stack emissions of EGBE occur from a single stack

(with the worst stack location assumed).

 Tier 3 modeling with AERMOD permits simultaneous modeling of multiple emission

sources, which yields collective impacts from all sources for each receptor location.

 Tier 3 modeling with AERMOD modeling allows for the direct calculation of long-term

averages for predicted air concentrations through use of multi-year meteorological data

sets.

The use of representative meteorological data processed using AERMET provides more

realistic estimates of predicted impacts under actual atmospheric dispersion conditions 

characteristic of the geographic setting at each facility. The AERMOD modeling for each 

location was performed using five years of recent representative meteorological data (2006 

through 2010 calendar years), from the meteorological stations closest to each facility. 

Meteorological data were processed using EPA’s AERMET v. 11059 (EPA 2004f, EPA 2011b) 

meteorological preprocessor. The use of five years of hourly meteorological data ensures that 

AERMOD modeling results incorporate expected interyear meteorological variability at each 

location, while capturing the occasional short-term extreme meteorological conditions. The use 

of actual meteorological measurements in sequence also allows for the modeling of long-term 
63 

(chronic) concentrations directly, without needing to estimate them empirically by scaling 1-hour 

(short-term) impacts, as was required when using AERSCREEN. 

Finally, AERMOD’s capability to model multiple sources in a single run allows that the 

combined impacts from multiple sources within a facility, or those from multiple facilities in a 

given domain be estimated more realistically than by simply superimposing their maxima as it 

was done in the Tier 2 screening. 

The Tier 3 AERMOD modeling used Universal Transverse Mercator (UTM) geographic 

coordinates for all emission sources, buildings and receptor locations modeled. NED terrain 

elevation data from USGS with resolution at 0.33 arc-second were used to incorporate elevation 

information for emission sources and receptor locations. Offsite concentrations were calculated 

at specified receptor locations within a nested receptor grid and along each facility’s property 

boundary. Property boundary receptors were spaced at 25 meter intervals. Offsite receptors 

were spaced at 50 meters in the Cartesian receptor grid out to a distance of 350 meters from 

the facility. A second coarser receptor grid with spacing of 100 meters was used for distances 

between 350 meters up to 2 km from each facility; 500 meter receptor spacing was used for 

receptors at distances from 2 km to 5 km from the approximate center of each facility. 

While the Tier 3 modeling for all six facilities relied on the same individual stack and 

volume source parameters used for Tier 2 modeling, the Tier 3 modeling also considered the 

distribution of EGBE emissions among the different stacks at a given facility, which was a level 

of refinement not considered in the Tier 2 screening. For one of the six facilities evaluated using 

Tier 3 modeling (the Crown facility located in Lawrence, MA), the distribution of EGBE 

emissions between stacks was not provided. For this facility, stack emissions were assumed to 

be equally distributed among facility stacks for the Tier 3 modeling. 

As discussed above, the Tier 3 modeling used five years of actual meteorological data. 

The AERMOD modeling was performed independently for each year, resulting in predicted 

maximum annual average concentrations at each receptor for each year of meteorological data. 

The maximum predicted annual average concentration for each receptor location was then 

conservatively calculated as the highest of the five modeled annual average concentrations for 

a given receptor. Results of the chronic (annual average) Tier 3 AERMOD modeling results for 

individual facilities is provided in Table 6-9 and model output files are provided in Appendix F. 

As shown in Table 6-9: 

 Based on 2009 emissions, the maximum Tier 3 result among the six facilities was 0.269

mg/m3, for the Rexam facility in WA, which represents less than 17% of the RfC.

 Based on 2010 emissions, the maximum Tier 3 result among the six facilities was 0.253

mg/m3, again for the Rexam facility in WA, which represents less than 16% of the RfC.

 Based on 2011 emissions, the maximum Tier 3 result among the six facilities was 0.256

mg/m3, for the Crown facility in MA, which represents less than 16% of the RfC.

These results indicate that, with the more refined and realistic (yet still conservative)

assumptions used in the Tier 3 modeling, chronic exposures to EGBE for the highest emitting 

facilities are well below the RfC. 
64 

6.5.3 Tier 3 Modeling (Clusters of Facilities) 

As a further demonstration of the conservatism of the tiered modeling approach for 

clusters of facilities, Tier 3 modeling was performed for facility clusters in two zip codes: (1) 

60609 in Chicago, IL, which had the highest cumulative Tier 2 impact among the five zip codes 

evaluated in Tier 2; and (2) 26062 in Weirton, WV, the zip code evaluated in Tier 2 that 

contained the largest number of individual facilities (i.e., five) reporting emissions of Certain 

Glycol Ethers to TRI in a single zip code. 

Tier 3 modeling for the facility cluster evaluation was performed with AERMOD using the 

same general methodology used for the Tier 3 modeling of individual facilities described in 

Section 6.5.2. Specifically, the AERMOD modeling for each facility relied on five years of 

representative meteorological data, with location information (UTM coordinates) and elevation 

data for all emission sources and buildings. Worst-case impacts from EGBE emissions at each 

facility were modeled for all receptor locations at or beyond each facility’s property boundary 

using the same receptor grid spacing specified in Section 6.5.2. The principle difference 

between Tier 3 modeling of individual facilities (Section 6.5.2) and the Tier 3 modeling of facility 

clusters is that for facility cluster modeling, all modeled facilities were modeled simultaneously in 

AERMOD, and thus the cumulative impact from all facilities was calculated by AERMOD 

simultaneously. 

Results of the chronic (annual average) Tier 3 AERMOD modeling of the two zip codes 

is provided in Table 6-8 (model output files are provided in Appendix F), and briefly summarized 

below: 

 Zip Code 60609 in Chicago, IL – The maximum Tier 3 impact for this zip code was 0.11

mg/m3 (2009 emissions), 0.18 mg/m3 (2010 emissions), and 0.14 mg/m3 (2011

emissions) corresponding to 7%, 12%, and 9% of the RfC, respectively.

 Zip Code 26062 in Weirton, WV – The maximum Tier 3 impact for this zip code was 0.16

mg/m3 (2009 emissions), 0.16 mg/m3 (2010 emissions), and 0.15 mg/m3 (2011

emissions) corresponding to 10% of the RfC, in each year.

Predicted worst-case EGBE air concentrations for all modeled clusters based on 2009,

2010, and 2011 emissions averaged 0.15 mg/m3, or 10% of the RfC. As these cluster analysis 

results demonstrate, even when considering the collective impacts of clusters of facilities in a 

zip code, and conservatively assuming the worst-case meteorological data year, the maximum 

annual average concentration of EGBE for all clusters modeled is predicted to be well below the 

RfC. 

The predicted worst-case clusters impacts were less than the highest individual facility 

impacts presented in Section 6.5.2. This outcome reflects the fact that none of the individual 

facilities with the highest individual impacts are located in zip codes considered in the facility 

cluster evaluation (i.e. none were located in zip codes that contained more than one facility 

reporting emissions of Certain Glycol Ethers to the TRI during 2009, 2010, or 2011). 
65 

6.5.4 Conservatism of the Tiered Modeling Approach 

In total, the potential for facility emissions of EGBE to result in chronic exposures greater 

than the RfC was evaluated for all United States facilities reporting non-zero emissions of 

Certain Glycol Ether to TRI during 2009 (1,109 facilities), 2010 (1,149 facilities), and 2011 

(1,099 facilities). 

The magnitude of conservatism (and margin of safety) built into the tiered modeling 

approach can be clearly demonstrated by comparing the reduction in maximum long-term 

modeled impacts between the lowest (most conservative) tier to the highest (most refined) 

modeling tiers. This reduction was demonstrated for the subset of individual facilities evaluated 

in all five tiers of the tiered modeling approach (Step A through Tier 3), the results of which are 

summarized below: 

 In comparing initial (Step A and B) screening results to the results of the chronic

exposure Tier 1, 2, and 3 analyses of high-emitting facilities, the maximum annual

average concentrations decreased by an average of 84% when the same facility was

evaluated first under Step Au and then under Step B.

 For the individual facilities subject to Tier 1, Tier 2, and Tier 3 modeling, the reduction in

maximum predicted annual average concentrations in moving from Step B to Tier 1

averaged 24%. The reduction in the maximum predicted annual average concentrations

in moving from Tier 1 to Tier 2 averaged 80% (based on 2009, 2010, and 2011 TRI

emissions). The reduction observed in moving from Tier 2 to Tier 3 averaged 70%

(Table 6-10).

 Thus, the cumulative conservatism of evaluating facilities using Step A, relative to Tier 3,

averaged 99%.

These results demonstrated that for the highest emitting facilities, the modeled maximum

annual average ambient concentrations resulting from Tier 3 modeling were consistently at least 

two orders of magnitude lower than the most conservative (Step A) screen applied, providing a 

significant margin of safety for those facilities screening out at lower tiers of modeling (Table 6-

10). This tiered modeling approach also indicates a significant margin of safety even when 

considering possible year to year variability of EGBE emissions from facilities. As a 

demonstration of this margin of safety, consider that even the facility with the highest Tier 3 

result of 0.269 mg/m3 (Rexam Beverage facility in Kent, Washington based on its 2009 

emissions) was well below (i.e., 17% of) the RfC. A gross estimate of range for overall interyear 

variability of EGBE emissions might be expected to generally follow the overall United States 

EGBE consumption trend, which is shown in Figure 2-1(SRI 2010). As illustrated in this figure, 

United States total EGBE consumption peaked in approximately 2005, and has steadily 

declined since then. The calculated ratio of United States total EGBE consumption in 2005 

u Although impacts were not explicitly calculated for the Step A screening, they were calculated for the comparison in 

Table 6-10 by using the EPA tier 1 lookup table and the conservative Step A assumptions (EGBE is 100% of 

Certain Glycol Ether emissions, all air emissions are released from a single point source with a stack height of 0 

meters and a fenceline distance of 50 meters). 
66 

versus 2009 is 1.3 (i.e., consumption was 30% higher in 2005 than in 2009). By comparison, the 

margin of safety (ratio) for the RfC compared to the maximum Tier 3 result is 5.9. The results of 

this analysis support the conclusion that the tiered modeling approach provides a sufficient 

margin of safety that encompasses reasonable interyear variability in facility EGBE emissions. 

A second analysis was conducted to further demonstrate that the margin of safety 

indicated by the tiered modeling is sufficient to account for interyear variability in facility EGBE 

emissions over time. This analysis considered the historical changes in the reported total 

Certain Glycol Ether emissions for all 13 facilities that were subject to Tier 2 modeling. Tier 3 

modeling performed for 6 of these high emitting facilities indicated that the highest Tier 3 chronic 

impact was 0.269 mg/m3, which represented only 17% of the RfC. This equates to a ratio 

(margin of safety) between the RfC and the worst-case Tier 3 impact of 5.9. For purposes of 

comparison, a review of the historical Certain Glycol Ether emissions reported for these six 

facilities (see Table 6-11) between 2000 and 2011 was used to calculate the ratio between the 

peak (highest) emissions of Certain Glycol Ethers and the emissions reported during 2009, 

2010, and 2011 (i.e. the years for which emissions were evaluated using the tiered modeling 

approach). These ratios also provide a reasonable representation of the expected maximum 

interyear variability in chronic impacts for each facility. The calculated ratios ranged from 1.1 to 

2.3, indicating that the interyear variability that is less than the calculated margin of safety (i.e., 

5.9) between the RfC and the worst-case Tier 3 modeled result. Similarly, this analysis can be 

extended to the eight other high emitting facilities modeled using the Tier 2 methodology. For 

these facilities, the calculated maximum ratios between peak year and 2009-2011 Certain 

Glycol Ether emissions ranged from 1.0 and 4.1, again demonstrating that interyear variability 

remains within the margin of safety demonstrated with the conservative Tier 3 modeling. Thus, it 

is highly unlikely that any facilities would have exceeded the RfC for EGBE even during each 

facility’s peak emission years. This analysis further supports the conclusion that the tiered 

modeling approach provides a sufficient margin of safety that encompasses reasonable 

interyear variability in facility EGBE emissions. This analysis conservatively assumed that 

historical EGBE emissions represent the same fraction of Certain Glycol Ether emissions as in 

recent years (2009-2011). 

Finally, the same conclusion of a sufficient margin of safety is also reached by 

examining trends in maximum TRI-reported Certain Glycol Ether emissions from any facility for 

each reporting year from 2000 to 2011 (see Figure 5-1). As shown in this figure, there has been 

remarkably little variability in the Certain Glycol Ether emissions from the highest emitting 

facilities over the past decade. Further, this variability is well within the margin of safety 

indicated by the ratio (5.9) between the 2009 Tier 3 modeled worst-case result and the RfC. 

Consistent with EPA’s conclusion in the HAPs delisting decision, the use of maximum 

annual average concentrations in each of the models significantly overstates the likely exposure 

levels of the actual exposed population (68 FR 65653): 

The use of the maximum annual average ambient concentration for each emission 

source to characterize the exposed population provides a conservative approach to 
67 

chronic exposure modeling. Furthermore, based on our experience, we judge that a 

refined exposure assessment estimating exposures for actual people living near these 

facilities would result in maximum individual exposures significantly lower than the 

maximum annual average ambient approach. Given the likely proximity of inhabitable 

areas and the variability of human activity patterns over an annualized time period, it is 

our expectation that actual maximum individual exposure would be at least a factor of 2 

less than predicted by the models. 

In conclusion, the maximum long-term exposures of persons in the vicinity of EGBEemitting facilities are likely to be far below the estimates generated by the screening and 

modeling approach employed in this petition. Despite that considerable conservatism, these 

estimates were determined to pose a negligible risk for chronic health effects to the populations 

around the facilities that emit EGBE. 

6.6 Acute Exposure Margin of Exposure (MOE) Assessment 

As previously discussed, in the absence of an EPA Acute Exposure Guideline Level 

(AEGL) or other RfC for acute effects, the tiered screening approach for evaluating potential 

acute EGBE exposures uses a MOE methodology, which is frequently used by EPA in TRI 

delisting decisions in cases where an EPA RfC for short-term exposures is not available. The 

remainder of this section outlines the methodology and results of the acute exposure and MOE 

assessment of the potential short-term exposures to EGBE from individual facilities and clusters 

of facilities. 

As discussed in Section 3.2.1.1, due to the relatively low sensitivity of human red blood 

cells to the hemolytic effects of EGBE, acute health effects are not expected to result from 

short-term ambient concentrations near EGBE-emitting facilities, and acute effects evaluations 

for EGBE have identified nonsystemic eye and upper respiratory tract irritation as the critical 

effect. Based on controlled studies of human volunteers, the lowest short-term concentration at 

which such irritation effects have been reported is 550 mg/m3 (Carpenter 1956), and no irritation 

effects have been observed from exposure to 97 mg/m3 for two hours during light physical 

exercise (Johanson et al., 1986). These acute air concentrations of concern are much higher 

than the predicted maximum annual average (chronic) air concentrations of EGBE estimated in 

Sections 6.3 through 6.5. In fact, the worst-case Tier 2 modeled chronic air concentrations for 

individual facilities and clusters of facilities were below these acute air concentrations of concern 

by factors of > 3,000 and > 500, respectively. Acute concentrations (typically evaluated based 

on maximum 1-hour averages) estimated using EPA tiered modeling are generally expected to 

be higher than chronic estimates (maximum annual averages) using the same modeling 

approaches. However, acute modeled concentrations that are 500 to 3,000 times greater than 

chronic results are highly unlikely. 

In addition, a comparison of Tier 2 modeled chronic air concentrations to acute 

concentration of concern (i.e. the NOAEL) itself does not likely reflect the full margin of safety as 

the NOAEL is based on a 2-hour exposure duration, while acute tiered-modeling results are 
68 

based on a 1-hour average. A 1-hour-equivalent NOAEL would be 137 mg/m3 (CalEPA 1999), 

over 40% higher. There is, therefore, a convincing basis to conclude that adverse acute effects 

from EGBE releases in the vicinity of emitting sources are unlikely. 

To confirm this conclusion, a tiered screening analysis based on EPA’s tiered modeling 

approach for short-term exposures to HAPs (EPA 1992a) was conducted for the 15 TRI facilities 

that did not screen out from Steps A & B of the chronic exposures assessment in Section 6.2. 

An additional tiered screening evaluation of potential short-term EGBE exposures was also 

conducted on the five zip codes evaluated in Section 6.3.1. 

6.6.1 Acute Exposure Assessment for Individual Facilities 

The tiered analysis used for short-term exposures is similar to the methodology 

presented for long-term exposures in Section 6.2, except that rather than modeling the 

maximum annual average concentrations of EGBE, the short-term modeling estimates 

maximum 1-hour concentrations of EGBE. The sections below describe the acute Tier 1 through 

Tier 2 screening methodology and results. As all individual facilities screened out at the Tier 2 

step, no further refined modeling was required. However, Tier 3 modeling was performed as 

part of the margin of safety analysis used for the acute exposure assessment. 

6.6.1.1 Tiered Modeling Methodology for Acute Exposures (Individual Facilities) 

Tier 1 screening for acute exposures was performed for all 15 facilities that did not 

screen out at Step B chronic exposure screening. These facilities were among the top 6% of all 

facilities in terms of the mass of Certain Glycol Ether air emissions reported to TRI for the 2009, 

2010, and 2011 (see Appendix B). These facilities also reported that EGBE made up at least 

85% of all Certain Glycol Ethers used at each facility. Because these facilities represent the 

highest Certain Glycol Ether emitting facilities and because EGBE is the dominant or only glycol 

ether used at these facilities, these facilities offer a reasonable approximation of “worst-case” 

facilities. 

A Tier 1 lookup table (Table E-1 of Appendix E) again was used to determine maximum 

acute (1-hour average) emissions based on distance to fenceline and stack height, consistent 

with EPA’s Tiered Modeling Guidance (EPA 1992a). For the acute Tier 1 analysis, the shortterm EGBE emissions rates (in gps) were calculated from facility annual EGBE emissions, 

based on the conservative assumption that EGBE releases occurred during a typical 40 hour 

work week for 50 weeks per year. 

These short-term emission rates were used in combination with the short-term Tier 1 

lookup table to determine the maximum point and fugitive 1-hour average (acute) 

concentrations (EPA 1992a), consistent with the method described for chronic exposure Tier 1 

analysis (see Section 6.3.1). Facility total EGBE point-source releases (in gps) were 

conservatively assumed to be emitted from each individual stack, and the maximum short-term 

concentration from the Tier 1 short-term lookup table for the individual stacks was 

conservatively selected to represent the maximum point-source-related impact for the entire 

facility. Fugitive emissions were modeled as a volume source with a release height of 0 meters 
69 

and a lateral dimension of 10 meters. The release height of 0 meters is more conservative than 

the default release height used in the long-term Tier 1 analysis (3 meters), which was based on 

a modified version of EPA’s Tier 1 table. This more conservative practice was adopted for 

consistency with the EGBE HAP delisting petition (CMA 1997). As such, the short-term 

exposure analysis for this petition uses an unmodified version of EPA’s short-term Tier 1 lookup 

table (1992a). For the Tier 1 analysis, the maximum acute impact for each facility was derived 

from the sum of each facility’s worst-case acute point and fugitive EGBE impacts, consistent 

with the chronic Tier 1 modeling (see Section 6.3.1). 

Acute exposure Tier 2 modeling was performed for all 13 facilities that did not screen out 

using the Tier 1 acute screening analysis. As with the chronic exposure Tier 2 modeling for 

individual facilities, the Tier 2 acute exposure modeling used AERSCREEN (EPA 2011a), 

which is designed to provide conservative estimates of ambient air concentrations. The same 

facility-specific inputs for point and fugitive sources used for the chronic Tier 2 modeling were 

used for the acute Tier 2 modeling. However, the acute exposure analysis uses AERSCREEN’s 

worst-case 1-hour average ambient air concentration results. 

Tier 3 modeling of short-term exposures was carried out using the same general 

methodology employed in long-term Tier 3 modeling for longer-term exposures (Section 6.5.2). 

The same dispersion model (AERMOD) and site-specific meteorological data were used to 

model the same six individual facilities modeled with AERMOD in Section 6.5.2. These six 

facilities include the top three ranked facilities from Tier 2 acute analysis, two dominant emitters 

in the top three ranked clusters in Tier 2 acute facility cluster evaluation, and the facility 

reporting the largest emissions of Certain Glycol Ethers in the TRI from 2009 through 2011. Tier 

3 modeling of short-term impacts was performed using the same source parameterization 

(assuming realistic emission distribution among stacks). The conservatism associated with 

AERMOD modeling is discussed in Section 6.5.4. 

6.6.1.2 Acute Tiered Modeling Results (Individual Facilities) 

The results from the short-term Tier 1 through Tier 3 modeling are presented in 

Appendix E. At the most conservative screening level (Tier 1), all but 2 of the 15 facilities had 

predicted maximum 1-hour concentrations above the NOAEL for acute irritation effects, 97 

mg/m3. The Ball Metal Food Container facility in Williamsburg, Virginia had the highest predicted 

1-hour Tier 1 concentrations (1,760 mg/m3 in 2010) from all three years of TRI datav

 (2009, 

2010, and 2011). Predicted 1-hour Tier 1 point-source and fugitive air concentrations are 

presented in Table 6-12. With the incorporation of site-specific data and more realistic 

accounting of stack emissions in Tier 2 and Tier 3 modeling, the predicted maximum 1-hour 

concentrations at all 13 remaining modeled facilities were significantly lower, as expected. The 

facility with the highest short-term Tier 2 concentration based on 2009-2011 TRI data the 

Crown Beverage Packaging facility in Lawrence, Massachusetts, which had a maximum shortv Concentrations presented are the sum of the combined maximum predicted 1-hour concentrations, at or beyond the 

fenceline, for fugitive/volume source emissions and point-source emissions.
70 

term concentration of 52.41 mg/m3 (54% of the NOAEL) based on 2009 TRI data (see Appendix 

E Table E-4). The maximum predicted 1-hour concentration for the short-term Tier 3 modeling 

for this facility was 15.24 mg/m3 in 2009, 13.24 mg/m3 in 2010, and 14.82 mg/m3 in 2011 (see 

Appendix E Table E-6). These concentrations represent less than 15% of the acute NOAEL. 

The Tier 3 results, presented in Table E-6 (Appendix E), show that maximum 1-hour 

concentrations of EGBE at all six facilities are far below the acute NOAEL with an average 

predicted facility impact over the three years (i.e., less than 10% of the acute NOAEL. 

6.6.2 Acute Exposure Assessment for Clusters of Facilities 

6.6.2.1 Tiered Modeling Methodology for Acute Exposures (Clusters of Facilities) 

Modeling the combined short-term impacts from multiple facilities within the same zip 

code was carried out using the same approach used in long-term facility cluster modeling. The 

five zip code areas that did not screen out in Step B were subjected to Tier 2 modeling. Shortterm Tier 2 impacts from the five zip codes were estimated using the same screening 

meteorological data developed for long-term analysis and AERSCREEN model. As discussed 

further in Section 6.6.3, short-term emission rates were estimated using the conservative 

assumption that facilities operate for only 40 hours per week and only 50 weeks per year. This 

assumption is likely to overestimate the short-term emission rates because the high emitting 

facilities are CMI members and CMI reported that member facilities typically operate those 

manufacturing processes that use EGBE continuously and year-round. 

 All five zip codes screened out at Tier 2. Nonetheless, Tier 3 modeling was conducted 

as part of the margin of safety analysis of acute exposures associated with clusters of facilities. 

Of the three clusters with highest estimated Tier 2 impacts, two zip codes with sufficient sitespecific data were selected for Tier 3 modeling. Tier 3 modeling of short-term impacts for two of 

the five zip codes for which sufficient site-specific data was available was performed using 

AERMOD and the same type of site-specific meteorological data developed for long-term 

analysis. 

As with short-term modeling of individual facilities, Tier 2 and Tier 3 modeling was used 

the same average annual emission rates originally developed and used in long-term Tier 2 and 

Tier 3 cluster modeling. As discussed in Section 6.3.1.3, conservative Tier 2 treatment of stack 

emissions assumes that total EGBE stack emissions from a facility are released from a single 

stack. More realistic parameterization of stack emissions in Tier 3 accounts for actual 

breakdown and proportioning of EGBE emissions among the different stacks at a facility (see 

Section 6.4.1). 

Maximum acute Tier 2 and Tier 3 impacts from clustered facilities were estimated 

following the same methodology used for long-term analysis (Sections 6.4.4 and 6.5.3). 

Maximum acute Tier 2 impacts for individual facilities were obtained by conservatively summing 

the maximum impacts for the separate volume and the worst-case stack scenarios, and the 

maximum cumulative impact for the entire cluster estimated by summing the maximum impacts 

from all individual facilities within the same zip code (irrespective of the specific receptor 
71 

location that each facility’s maximum impacts occurred). In Tier 3, the maximum combined 

impact from multiple sources within a facility and the multiple facilities within a cluster were 

modeled using AERMOD. As discussed previously, AERMOD allows for the simultaneous 

modeling (in a single model execution) of all facilities in the cluster, as well as the modeled 

emission sources at each facility. 

6.6.2.2 Acute Exposure Tiered Modeling Results (Clusters of Facilities) 

Acute EGBE impacts from Tier 2 and Tier 3 cluster modeling are presented in Table 6-

13. The highest short-term Tier 2 concentration based on TRI emission data from 2009 to 2011

was 50.9 mg/m3 (for zip code 60609, Chicago IL in 2010). The maximum predicted 1-hour 

concentration for the short-term Tier 3 modeling for this same cluster was 14.0 mg/m3, 23.5 

mg/m3, and 18.5 mg/m3 for 2009, 2010, and 2011, respectively. The highest of these 

concentrations represents less than 24% of the acute NOAEL. 

6.6.3 Acute Margin of Exposure (MOE) Assessment 

The MOE approach used to evaluate the risk of potential acute irritation effects 

associated with short-term exposures to EGBE is consistent with previous TRI listing decisions 

(e.g., MEK, EPA 1998a; MIBK, EPA 1999c). The MOE was calculated as the ratio of the 

NOAEL for acute irritation effects, 97 mg/m3, to the estimated short-term exposure level in the 

vicinity of EGBE-emitting facilities. The MOEs for the predicted 1-hour maximum concentrations 

for the 13 high-emitting facilities subjected to Tier 2 modeling, and the 6 facilities subjected to 

Tier 3 modeling, are presented in Table 6-14. 

In each case that EPA applied the MOE approach in TRI listing decisions, EPA identified 

a numerical level below which the MOE “is associated with a concern for toxic effects.” This 

level is generally expressed as the product of the applicable uncertainty and modifying factors 

uncertainty factors that the Agency considers for noncancer toxic effects. A MOE greater than 

this level “would generally indicate a low level of concern,” whereas a MOE less than the level 

“is judged to be of concern” (MIBK, EPA 1999c). In the case of EGBE’s acute irritation effects, 

the MOE determination is based on a NOAEL derived from human data. There is accordingly no 

need to apply uncertainty factors for interspecies extrapolation, or for LOAEL-to-NOAEL 

extrapolation. An intraspecies uncertainty factor of 10 has often been used to account for 

potentially susceptible subpopulations in EPA TRI and other program precedents. 

Although the minimum MOE among facilities subjected to the most sophisticated and 

realistic modeling ranges from 5 to 46 (Table 6-14), the level of concern is even lower than the 

MOE analysis indicates for several reasons. The Standard Operating Procedures for EPA’s 

AEGL program (NRC 2001) allow for interspecies uncertainty factors below 10 in some 

circumstances, and suggest that an intraspecies uncertainty factor of 3 is appropriate for 

substances for which only one or a small number of nonsystemic effects have been 

documented. As discussed in Section 3 

 EGBE’s systemic toxic effects are secondary to hemolysis;
72 

 because of the relative insensitivity of humans to EGBE’s hemolytic effects, and

because investigation of potentially sensitive subgroups have consistently failed to

reveal increased susceptibility, hemolytic effects—and other systemic effects—are not

expected to occur from short-term exposures near emitting facilities; and

 nonsystemic eye and upper respiratory irritation is the sole acute health effect that has

been associated with short-term exposures, and this effect is unlikely to depend

substantially on metabolic, pharmacokinetic or other systemic factors that introduce

variability into responses across the exposed human population.

Second, as observed above, the NOAEL for EGBE’s acute irritation effects is based on a

2-hour exposure duration, and a 1-hour-equivalent NOAEL would be 137 mg/m3 (CalEPA 1999), 

over 40% higher. Taken together, these two considerations effectively reduce the MOE concern 

level from 10 to about 2, a more than a factor of two below the lowest MOE derived from the 

reasonable worst-case short-term exposure assessment summarized above (Table 6-14). 

Accordingly, there is a persuasive basis for concluding that there is a low level of concern for 

acute health effects from EGBE facility emissions. 

Finally, short-term emission rates were estimated using the conservative assumption 

that facilities operate for only 40 hours per week and only 50 weeks per year. This assumption 

is likely to overestimate the short-term emission rates because the high emitting facilities are 

CMI members and CMI reported that member facilities typically operate those manufacturing 

processes that use EGBE continuously, with little variability year-round. Therefore, actual hourly 

emission rates could be as much as four orders of magnitude lower than those used in the 

acute assessment.w 

6.7 Risk Characterization Conclusions for Potential EGBE Inhalation Exposures 

None of the facilities that reported non-zero emissions of Certain Glycol Ethers to the air 

to TRI during the 2009, 2010, and 2011 reporting years were is associated with maximum 

annual average concentrations of EGBE at or above the current IRIS RfC. By subjecting 

facilities to the more refined long-term Tier 1, 2, and/or 3 analyses in accordance with EPA’s 

(1992a) Tiered Modeling Guidance, this petition has demonstrated that there exists at least a 

six-fold margin of safety as a result of the conservative screening procedure employed, not 

including the additional margin of safety built into the RfC value itself (see Section 3.1.3). 

Additionally, it was demonstrated that EGBE exposures at or above the RfC are not expected to 

result from emissions from multiple facilities within a limited geographic area (for this analysis, 

within the same zip code). Finally, screening of a subset of facilities with some of the highest 

annual EGBE emissions reported to TRI during 2009, 2010, and 2011 demonstrated that shortterm EGBE exposures near facilities reporting Certain Glycol Ethers emissions are also highly 

unlikely to be associated sufficient to have resulted in any acute health effects. 

w Continuous operations assume more than 4.3 times more hours of operations (and emissions) over the 

course of the year than the 40 hours per week, 50 weeks per year assumption (8,736 hours vs. 2,000 

hours). 
73 

7.0 SURFACE WATER EXPOSURES AND RISKS 

Although the 2009, 2010, and 2011 TRI data and the emissions inventory (Appendix B) 

indicate that releases to air far exceed releases to all other environmental media combined, 

chronic health effects posed by direct releases to water and partitioning to water were also 

evaluated. As previously discussed, EGBE (CAS 111-76-2) possesses physical characteristics 

that indicate a propensity to remain dissolved in water or to be transported to the water column. 

As detailed in Section 3.1, EGBE is readily biodegradable (Price et al. 1974, as cited in ATSDR 

1998) and has a relatively short residence time in the environment. Its half-life in both surface 

water and soil ranges from 7 days to 4 weeks, while its half-life in groundwater is 14 days to 8 

weeks, and its half-life in the atmosphere is approximately 3.3 to 33 hours (Howard et al. 1991, 

as cited in ATSDR 1998). EGBE is highly mobile in soil and is unlikely to partition from the water 

column to organic matter contained in sediments or suspended solids (Swann et al. 1983). The 

volatilization of EGBE from surface water and moist soil is slow (Lyman et al. 1982, as cited in 

ATSDR 1998). HSDB (http://toxnet.nlm.nih.gov) reports that an estimated BCF of 3 was 

calculated for EGBE, concluding that the potential for bioconcentration in aquatic organisms is 

low. In summary, EGBE is miscible in water and has low overall volatility, a limited tendency to 

bind to soil and low lipophilicity and thus low bioaccumulation potential. These characteristics 

indicate that the majority of EGBE in soil is in the more mobile soil water phase rather than the 

solid phase (Section 8.2.2). Thus, EGBE released to soil would be expected to readily move via 

surface runoff to surface water. 

In light of the fate and transport behaviors of EGBE, this section evaluates potential risks 

associated with human exposures to EGBE in surface water. The same methodologies 

reviewed and conducted by EPA in the HAPs delisting matter are employed here, with updates 

to reflect surface water concentrations based on 2009, 2010, and 2011 TRI release data, the 

most recent version of the Mackay fugacity model (EQC v2.02; CEMC 2003), the IRIS RfD, and 

current EPA (2004b) guidance for dermal risk assessment. Conservative exposure assumptions 

were used to determine potential for adverse effects associated with reasonable maximum 

exposure (RME) scenarios. 

7.1 Exposure Profiles 

Because this evaluation is meant to apply broadly to any surface water body used for 

recreational and/or potable water (i.e., residential) purposes, all assumptions employed are 

purposefully generic and conservative. As such, this profile describes RME scenarios, likely 

representing at most a very small proportion of the overall United States population. The bases 

for all assumptions presented below are further detailed in Section 7.3. 

Under the recreational scenario, three age groups (young children 1 through 5 years of 

age, older children 6 through 12 years of age, and adolescents/adults over 12 years of age) 

were assumed to swim and play in and around a lake, pond, stream, or river containing an 

estimated upper bound EGBE concentration of 0.000376 mg/L (i.e., the exposure point 

concentration). While playing and swimming in the water body, recreators were assumed to 
74 

contact EGBE dermally and through incidental ingestion of surface water. Under the residential 

scenario, the same three age groups were assumed to live at a house supplied with tap water 

containing the same exposure point concentration of EGBE. Individuals were assumed to 

contact EGBE in tap water through drinking water consumption and through dermal contact 

while showering and bathing. 

The exposure point concentration of EGBE in surface water was developed using the 

Mackay III distributional model (EQC v2.02; CEMC 2003), based on 2010 TRI data on 

discharges to air, land, and water, as detailed in Section 8.2.2. In brief, it was assumed that all 

emissions of Certain Glycol Ethers to air, soil, and surface water throughout the United States 

(as reported in the 2010 TRI reports; www.epa.gov/triexplorer) are EGBE.x

 It was further 

assumed that all emissions are concentrated into a 100,000 square kilometer (km2) area 

(approximately the size of Ohio), which is the Mackay model’s default unit area (CEMC 2003). 

Because emissions of Certain Glycol Ethers to all media were greater in 2010 than in 2009 or 

2011, the predicted surface water EGBE concentration using 2010 TRI data (0.000198 mg/L) 

was greater than the predicted surface water concentration based on 2009 and 2011 data 

(0.000190 mg/L and 0.000193 mg/L). Therefore, the water concentration based on the 20010 

TRI data was used as the more conservative estimate of the upper bound concentration of 

EGBE in surface water. The implications of increases in EGBE releases in the future are 

qualitatively addressed in the Section 9. 

7.2 Exposure Equations 

Potential dermal and ingestion exposures were modeled based on the average daily 

intake (ADI), expressed in units of mg/kg BW-day, consistent with EPA (1989, 2004b) risk 

assessment guidance. The equations for estimating ADI for each exposure pathway are 

presented below. Definitions of variables that remain constant across pathways are provided for 

the first pathway only. Parameters that are unique to a pathway are defined for that specific 

pathway. While the equation listed below for the ingestion pathway is identical to that used in 

the HAPs petition (CMA 1997), the equation listed below for the dermal pathway is updated to 

reflect current EPA (2004b) guidance for dermal risk assessment and consequently differs from 

that used in the HAPs petition. 

Ingestion of Drinking Water/Incidental Ingestion of Surface Water: 

Eqn. 4 

ADI (mg/kg BW-day) = Cw x IRw x EF x ED x Ao x (1/BW) x (1/AT) 

where: 

Cw = Concentration of EGBE in water (mg/L) 

IRw = Ingestion rate (L/day) 

x Releases to air were defined as those reported via On-Site Fugitive Air Emissions and On-Site Point Source Air 

Emissions. Releases to surface water were defined as those reported as On-Site Surface Water Discharges and 

releases to soil were defined as those reported as On-Site and Off-Site Land Treatment and Other Land Disposal. 
75 

EF = Exposure frequency (days/year) 

ED = Exposure duration (years) 

Ao = Oral absorption factor (unitless) 

BW = Body weight (kg) 

AT = Averaging time (days) 

Dermal Contact with Tap Water/Surface Water While Bathing, Showering, or Swimming: 

 Eqn. 5 

ADI (mg/kg BW-day) = DAevent x EV x ED x EF x SA x (1/BW) x (1/AT) 

where: 

DAevent = Absorbed dose per event (mg/cm2-event) 

EV = Event frequency (events/day) 

SA = Skin surface area exposed (square centimeters or cm2) 

7.3 Exposure Assumptions 

Calculation of ADI for the two pathways identified above requires the selection of 

exposure parameter values that reflect assumptions regarding individual behavior that results in 

contact with EGBE in surface water. All exposure factor values are listed in Tables 7-1 through 

7-4 and are further described below. In all cases, exposure factor values were selected with the 

objective of describing RME scenarios (i.e., using assumptions that are consistently 

conservative in the sense that they significantly overstate the exposures likely to be experienced 

by the general population). 

 Chemical concentration in water (Cw) − The assumed concentration of EGBE in surface

water, 0.000198 mg/L, is estimated by applying Mackay’s fugacity model to 2010 TRI

data on releases of Certain Glycol Ethers to land, air, and water (assuming that EGBE

comprises 100% of this chemical group), as further described in Section 8.2.2. For the

HAPs petition, the assumed concentration of EGBE in surface water was 0.13 mg/L.

Given the stronger technical basis for the value applied in this petition, it is likely more

appropriate than that used for the HAPs petition. That said, Section 7.4 explores the

effect that the value used in the HAPs petition has on predicted risks.

 Ingestion rate (IR) − Water IR values for both drinking water and incidental events while

swimming from EPA (1989) risk assessment guidance were employed in this analysis.

EPA (1989) reports a drinking water IR (IRw) of 2 L/day for adults and older children.

Young children are reported to drink 1 L/day of drinking water. For incidental ingestion of

water while swimming, EPA (1989) reports IRs of 0.13 L/day for all three age groups.

The same values were employed in the HAPs petition.

 Exposure frequency (EF) − Consistent with EPA (1989) risk assessment guidance, a

350 day/year EF was used for residential exposures for all age groups, assuming that

individuals vacation away from home a total of 15 days/year. For recreational exposures,

it was conservatively estimated that a warm climate that would permit swimming nine

months/year. Therefore, adults and young children were assumed to swim once per
76 

week, while older children were assumed to swim three times per week, yielding 

exposure frequencies of 36 and 108 days/year, respectively. For a cooler climate, these 

exposure frequencies could also represent a 4.5 month swimming season, in which 

adults and young children swim twice per week and older children swim six times per 

week. The same values were employed in the HAPs petition. 

 Exposure duration (ED) − For both recreational and residential exposures, the ED was

assumed to be 30 years broken down into 5 years as a young child, 7 years as an older

child, and 18 years as an adolescent and adult. This assumption is similar to EPA (1989)

risk assessment guidance and is consistent with the HAPs petition.

 Oral absorption factor (Ao) – It was conservatively assumed that 100% of the EGBE

ingested is absorbed in the gastrointestinal tract. This assumption was employed in the

HAPs petition.

 Body weight (BW) − EPA (1989) risk assessment guidance provides age-specific BWs of

70 kg, 30 kg, and 15 kg for adults and adolescents, older children, and young children,

respectively. Although slightly higher (and therefore less conservative) BWs are offered

in more recent EPA (1997b) guidance, the values first proposed by EPA (1989) were

employed in this analysis for consistency with most other risk assessments and to

ensure the conservatism of the overall assessment. The same values were employed in

the HAPs petition.

 Averaging time (AT) − The AT for noncarcinogens represents the length of time between

the first and last exposure, in days. Hence, the ATs for adults and adolescents, older

children, and young children were set equal to 6,570 days, 2,555 days, and 1,825 days,

respectively. The same values were employed in the HAPs petition.

 Event frequency (EV) – Consistent with EPA (2004b) dermal risk assessment guidance,

it was assumed that residents take one shower or bath daily. Although residents may

occasionally take two showers per day, they may also occasionally go without showering

for a day or shower at places other than their residence. Thus, on average, this

assumption is reasonable and conservative. Recreators are assumed to swim or wade

three times each day that they visit recreational water bodies. When the HAPs petition

was prepared, EPA guidance for dermal risk assessment did not require characterization

of EV.

 Skin surface area exposed (SA) − Age-specific skin surface areas were derived from

EPA (1997b) exposure assessment guidance. Surface areas of 23,000 cm2, 12,914 cm2,

and 7,446 cm2 are reported as upper percentile values for adults and adolescents, older

children, and young children, respectively. These values are consistent with more recent

EPA (2004b) guidance. It was assumed that 100% of the body contacts water during

swimming, showering, and bathing. Skin surface areas applied in the HAPs petition were

based on older EPA (1989) guidance and were slightly lower (i.e., less conservative)

than those listed above. The HAPs petition employed surface areas of 20,900 cm2,

12,349 cm2, and 7,252 cm2 for adults, older children, and young children, respectively.

 Absorbed Dose (DAevent) – Exhibit B-3 of EPA’s (2004b) current dermal risk assessment

guidelines lists a calculated value of 1.8E-6 milligrams per square centimeter (mg/cm2)-

event for the absorbed dose of EGBE via dermal contact with water (listed in the exhibit

as butoxyethanol-2), assuming a chemical concentration of 1 mg/L in water. Thus, the
77 

value of DAevent employed in this risk assessment was 3.6 x10-10 mg/cm2-event, which is 

the product of the estimated concentration in water (0.000198 mg/L) and the default 

value listed in Exhibit B-3 (1.8 x 10-6 mg/cm2-event). When the HAPs petition was 

prepared, EPA guidance for dermal risk assessment did not require characterization of 

DAevent. 

7.4 Results and Conclusions 

The exposure factor values were entered into the exposure equations listed above to 

yield ADIs for each exposure scenario, as presented in Tables 7-1 through 7-4. The ADIs were 

then divided by the IRIS RfD of 0.1 mg/kg BW-day (EPA 2010), to yield pathway-specific hazard 

quotients (HQs). Pathway-specific HQs were then summed to yield cumulative hazard indices, 

presented in Table 7-5. All HQs are several orders of magnitude below 1, the benchmark of 

acceptable hazard specified in the National Contingency Plan (EPA 1990a). Because the ADIs 

estimated here represent RME levels, it is likely that the ADIs and HQs in Table 7-5 represent 

significant overstatements of exposures and potential health risks for the vast majority of the 

United States population. Thus, adverse health effects are not anticipated to result from either 

recreational or residential exposures to EGBE in surface water. 

As shown in Table 7-6, there are three main differences between the methods employed 

in the HAPs petition and in this petition to evaluate dermal and ingestion exposures from EGBE 

in surface water. First, both the underlying data (i.e., 1993 vs. 2010 TRI release data) and the 

model used to estimate the concentration of EGBE in surface water differ, such that the HAPs 

petition employed an exposure point concentration of 0.13 mg/L, while this petition uses a value 

of 0.00020 mg/L, a value that is 650-fold lower. Because the lower value is based on the latest 

release data and the current version of Mackay’s fugacity model, it is expected to be the more 

accurate value. Nonetheless, the impact of assuming that surface water contains 0.13 mg/L on 

overall hazard estimates is evident by simply multiplying the maximum HQ shown in Table 7-5 

(i.e., 0.0001) by 650, which yields a theoretical HQ of 0.08. Because this value is also well 

below 1, the assumed exposure point concentration does not affect the overall conclusions of 

this risk assessment. 

The second main difference between the surface water hazards calculated in the HAPs 

petition and in this petition relates to the RfD. In 1997, EPA had not yet completed work on the 

IRIS RfD, and accordingly the draft interim value of 3 mg/kg BW-day under review at that time 

was employed in the 1997 HAPs petition. Thus, the final IRIS RfD of 0.1 mg/kg BW-day 

employed in this petition has a stronger scientific basis and is 30-fold more conservative than 

that used in the HAPs petition. 

Third, in 1997, the equation typically used to estimate dermal dose differed from that 

now recommended by EPA (2004b) dermal exposure guidelines. However, given the much 

greater influence of the ingestion pathway over the dermal pathway in terms of the cumulative 

hazard, the change in approach to dermal risk assessment has minimal effect on overall 

conclusions regarding risk. Nonetheless, the method employed was updated to reflect the 

strongest technical basis and current regulatory practice. 
78 

In conclusion, the three main changes to the approach employed to calculate surface 

water hazards reflect the most recent emissions data, and advances in knowledge and practice 

related to fugacity modeling, EGBE toxicity, and dermal risk assessment. While these updates 

are certainly appropriate for generating more realistic estimates of potential hazards, they do not 

substantially change the overall conclusions of the assessment that predicted ingestion/dermal 

hazards (as measured by HQs) are well below 1 regardless of the combination of assumptions 

employed. Indeed, the maximum surface water HQ predicted in the HAPs petition was 0.007, 

while the maximum value predicted in this petition is 0.0001 (Table 7-6). 
79 

8.0 ECOLOGICAL RISKS 

A series of ERAs has been prepared for EGBE (CAS 111-76-2), including several ERAs 

prepared in the HAPs delisting proceeding. All have concluded that EGBE is not expected to 

cause significant adverse environmental effects. Nevertheless, an updated ERA was performed 

as part of this petition to account for changes in emissions rates since the mid-1990s, as well as 

to incorporate more recent ecotoxicological information. The ERAs conducted for the HAPs 

delisting petition are summarized below, followed by a detailed description of the updated ERA 

developed to support this petition. 

8.1 HAPs Delisting Ecological Risk Assessments 

Several ERAs were conducted for EGBE in connection with EPA’s review of the petition 

to remove EGBE from the CAA HAPs list. The first was prepared on behalf of the Panel as part 

of the HAPs delisting petition (CMA 1997). EPA’s Office of Air Quality Planning and Standards 

then retained the Cadmus Group to prepare Tier 1 and Tier 2 ERAs. The Tier 1 ERA (Cadmus 

2000b) employed extremely conservative point estimates of exposure and effects, while 

somewhat less conservative assumptions were used for the Tier 2 ERA (Cadmus 2000a). While 

the same general approach was employed in all three ERAs, specific assumptions varied. 

Nonetheless, the Panel and the EPA Tier 2 ERAs concluded that EGBE is not expected to 

cause significant adverse ecological effects, and the Agency ultimately made the same finding 

when it removed EGBE from the CAA HAPs list. The HAPs ERAs for EGBE are summarized 

below. 

8.1.1 The Panel’s ERA 

Based on a review of the ecotoxicological literature and an evaluation of the relative 

sensitivities to EGBE by many receptors, the Panel’s HAPs ERA (CMA 1997) evaluated two 

assessment endpoints: (1) sustainability of aquatic plant communities and (2) sustainability of 

small mammal populations. 

The Panel’s HAPs assessment used the Mackay Level III model to calculate the 

distribution of EGBE in air, water, and soil based on 1996 TRI national emissions. EGBE 

releases into the 100,000 km2 area contained within the Mackay model were estimated by 

assuming that EGBE represents 50% of all Certain Glycol Ethers releases reported nationally 

as (1) point and fugitive air emissions; (2) releases directly to surface water; (3) releases to 

publicly owned treatment works (POTWs); (4) onsite land releases; and (5) transfers off site for 

disposal. The 1996 releases to air, water, and soil used in the Panel’s HAPs analysis are listed 

in Table 8-1. 

The Mackay model predicted that the majority of EGBE released to air is deposited to 

soil and water, while EGBE released to water and soil tends to remain in those media. The 

overall persistence of EGBE in the environment was estimated to be 19 days and losses were 

largely attributed to advection and reactions (e.g., degradation). Application of the Mackay Level 
80 

III model predicted concentrations of EGBE in air, water, and soil (at equilibrium), as shown in 

Table 8-2. 

The predicted equilibrium water concentration (0.00135 mg/L) was used to evaluate 

exposure of aquatic plants to EGBE. Exposure of small mammals to EGBE was estimated 

based on EPA’s (1993a) exposure equations for deer mice (Peromyscus maniculatus), 

considering direct ingestion of soil, water, and food, resulting in an EGBE dose of 0.203 mg/kg 

BW-day for small mammals. 

An aquatic TRV was derived from the lowest relevant toxicity value available for aquatic 

plants—a 125 mg/L acute no observed effect concentration (NOEC) for growth rate inhibition in 

green algae (Dow 1988, Table 3-2). An uncertainty factor of 100 was applied to adjust the acute 

NOEC to be representative of chronic effects, because no data were available to clarify the 

potential difference in effects between acute and chronic exposures. Therefore, the Panel’s 

HAPs assessment (CMA 1997) employed a TRV of 1.25 mg/L for evaluating risk to aquatic 

plants. 

In the absence of any available studies of EGBE toxicity in wildlife, the small mammal 

TRV was derived from the 91-day drinking water study in female Fischer rats, which was also 

used in the IRIS assessment that was available at that time (EPA 1999a) to develop the human 

oral RfD for EGBE. The chronic LOAEL for this study was 59 mg/kg BW-day (Appendix A-2).y

The rat chronic LOAEL was divided by a uncertainty factor of three to adjust for the absence of 

a NOAEL, to derive a TRV of 20 mg/kg BW-day for small mammals (CMA 1997).

Dividing the surface water concentration predicted by Mackay Level III modeling 

(0.00135 mg/L) by the aquatic TRV (1.25 mg/L) yielded an HQ of 0.0012. For small mammals, 

the predicted dose of 0.203 mg/kg BW-day was divided by the TRV of 20 mg/kg BW-day, to 

yield an HQ of 0.01. HQs less than 1.0 indicate that ecological effects are unlikely to occur. 

Thus, the Panel’s HAPs assessment (CMA 1997) concluded that EGBE was unlikely to pose 

significant ecological risk under current or future uses. 

8.1.2 EPA ERAs 

The EPA HAPs ERAs (Cadmus 2000a, b) narrowed the assessment endpoints selected 

by CMA (1997) to some degree, selecting the following receptors for their analysis: (1) aquatic 

microorganisms in waters receiving atmospheric emissions of EGBE from nearby large sources 

and (2) small mammals with home ranges located immediately downwind of large sources of 

EGBE emissions. These endpoints are inherently more conservative than those employed by 

the earlier Panel assessment because they focus on those organisms that are in the immediate 

vicinity of EGBE emissions. EPA employed a tiered approach, wherein the first tier of analysis 

was intentionally very conservative. The Tier 1 ERA was not designed to generate a definitive 

y The chronic LOAEL used to calculate the RfD differs slightly form the published LOAEL in the original study (82 

mg/kg BW-day; NTP 1993) and presented in Appendix A-2 because IRIS (EPA 1999a) used water consumption 

rates and female body weights measured during the last week of exposure to calculate dose. 
81 

conclusion regarding potential ecological risks. Rather, it was intended to screen out those 

scenarios that clearly do not present concern.

8.1.3 Tier 1 ERA 

EPA’s application of the Mackay model differed somewhat from that used in the Panel’s 

HAPs analysis. In particular, for Tier 1, EPA used the Level I Mackay model to determine the 

equilibrium distribution of EGBE in a model environment with 1,000 kg of EGBE emitted to the 

air. The Level I model does not account for any advection or degradation reaction losses of 

EGBE, and it predicted that more than 99% of the EGBE released to the model environment 

partitioned to water. The predicted air concentration was 0.000000423 mg/m3, the predicted 

water concentration was 0.000497 mg/L, and the predicted soil concentration was 0.000024 

mg/kg (Cadmus 2000b). 

Because the assumed EGBE release rate used in the EPA Tier 1 assessment (1,000 kg) 

is arbitrary and unrelated to actual releases, the exposure concentrations were scaled as a 

function of both the distribution of EGBE determined from the Level I Mackay model and the 

predicted maximum annual average concentration of EGBE from the highest emitter in the 1993 

TRI. The predicted maximum annual average concentration (0.327 mg/m3) was 773,050 times 

greater than the air concentration (4.23 x 10-7 mg/m3) predicted by the Level I Mackay model 

using the arbitrary release of 1,000 kg. The predicted water and soil concentrations were 

converted to concentrations that would be in equilibrium with the maximum annual average 

concentration at or beyond the fenceline, by multiplying each Mackay Level I modeled 

concentration by 773,050. This assumption is unrealistically high by a very large margin 

because maximum annual average air concentrations were calculated by assuming no 

interchange between EGBE in air, soil, or water. The Mackay model indicates that EGBE 

preferentially partitions to soil and water from air, which would dramatically lower maximum 

annual average concentrations at or beyond the fenceline. This assumption is also unrealistic 

because it does not account for the effect of dilution of air concentrations over time or space. 

The concentrations used in the EPA Tier 1 assessment (Cadmus 2000b) are presented in Table 

8-2.

The equilibrium water concentration listed in Table 8-2 was used to evaluate exposure of 

aquatic microorganisms to EGBE. For small mammals, EPA’s Tier 1 ERA used the meadow 

vole (Microtus pennsylvanicus) rather than the deer mouse, because the vole’s diet has a higher 

proportion of plants and thus would likely have higher exposures to EGBE (Cadmus 2000b). In 

addition to dietary and drinking water pathways, the inhalation pathway for small mammals was 

evaluated. Exposure factor values and the dose equation were drawn from EPA (1993a) wildlife 

exposure assessment guidance, resulting in an estimated dose of 163.8 mg/kg BW-day for the 

meadow vole. 

The lowest relevant toxicity value identified in the EPA Tier 1 assessment (Cadmus 

2000b) for aquatic microorganisms was for the protozoan Endosiphon sulcatum, which 

experienced inhibition of cell multiplication following a 72-hour acute exposure to 91 mg/L. An 

acute-to-chronic uncertainty factor of 100 was applied to derive a TRV of 0.91 mg/L for aquatic 
82 

microorganisms. For small mammals, the EPA Tier 1 assessment adopted the same TRV 

developed by the Panel, 20 mg/kg BW-day. The resulting Tier 1 HQ for aquatic microorganisms 

was 422, while the Tier 1 HQ for small mammals was 8.2. Therefore, EPA concluded that 

additional ecological evaluation for both receptors was warranted and proceeded with a Tier 2 

ERA.

8.1.4 Tier 2 ERA 

The EPA Tier 2 ERA (Cadmus 2000a) evaluated the same assessment endpoints and 

pathways considered in the Tier 1 ERA; however, several of the unrealistic assumptions used in 

the Tier 1 assessment were replaced with more plausible estimates of exposure and effects. 

The Mackay Level III model was used to determine the equilibrium distribution of EGBE in a 

model environment with 1,000 kilograms per hour (kg/hr) of EGBE emitted to the air. Because 

advection and degradation reactions are accounted for in the Level III model, the predicted 

equilibrium concentrations were considerably lower than the Tier 1 model predictions. The 

predicted air concentration was 5.89 x 10-5 mg/m3, the predicted water concentration was 6.56 x 

10-4 mg/L, and the predicted soil concentration was 1.19 x 10-2 mg/kg (Cadmus 2000a). 

Because the assumed release rate (1,000 kg/hr) was arbitrary, it was again necessary to scale 

the predicted concentration based on the maximum annual average concentration predicted 

from the 1993 TRI (0.327 mg/m3). The resulting concentrations, listed in Table 8-2, were used in 

the Tier 2 exposure assessment. 

A water concentration of 3.64 mg/L (Table 8-2) was used to evaluate exposure of 

aquatic microorganisms to EGBE. The exposure model for the meadow vole (EPA 1993a) was 

used to estimate small mammal exposure to EGBE, yielding an estimated dose of 2.15 mg/kg 

BW-day. 

For the Tier 2 effects assessment, EPA applied an acute-to-chronic uncertainty factor of 

10 to the lowest relevant toxicity value of 91 mg/L, yielding a TRV of 9.1 mg/L for aquatic 

microorganisms. For small mammals, the same TRV (20 mg/kg BW-day) used in the Panel ERA 

and EPA’s Tier 1 ERA was also applied in the Tier 2 ERA. The Tier 2 HQ for aquatic 

microorganisms was 0.40 and the Tier 2 HQ for small mammals was 0.11. Because both HQs 

were less than 1, the ERA conducted on behalf of EPA concluded that ecological risks due to 

exposure to EGBE are unlikely (Cadmus 2000a). When EPA evaluated these results in the 

HAPs delisting determination, it found the water concentration of 3.64 mg/L predicted in the Tier 

2 ERA to be a “worst-case estimate” that would not be approached in communities near EGBEemitting facilities, “because numerous variables were not taken into consideration that, if 

considered, were likely to reduce estimates of EGBE in water” (68 FR 65653 [EPA 2003]). 

8.2 Updated ERA 

For this petition, the previous HAPs ERAs were updated to reflect more realistic 

assumptions related to EGBE fate and transport in environmental media, current data on EGBE 

releases, and recent publications on EGBE ecotoxicity. 
83 

8.2.1 Problem Formulation 

The assessment endpoints selected for this ERA were (1) sustainability of aquatic 

populations and communities and (2) sustainability of small terrestrial mammal populations. As 

detailed below in the effects assessment, because the aquatic organism TRV was selected 

based on the most sensitive aquatic species tested, the first assessment endpoint is considered 

protective of all types of aquatic organisms. Thus, it is not necessary to limit this endpoint to 

aquatic plants (as had been done in the Panel’s HAPs assessment [CMA 1997]) or aquatic 

microorganisms (as had been done in the EPA HAPs ERAs [Cadmus 2000a,b]). As in the 

previous ERAs, the selected assessment endpoints were evaluated based on HQs, which are 

equal to the ratio of the estimated exposure concentration (or dose) to the TRV. 

As in the EPA HAPs analyses, this ERA used meadow voles to represent small 

terrestrial mammals, given their expected higher exposures compared to other small mammal 

species. The same pathways used in the previous ERAs were also used in this analysis. 

Therefore, aquatic organism exposure was evaluated based on estimated surface water 

concentrations, and small terrestrial mammal exposure was evaluated based on the same 

exposure model used by the EPA HAPs analyses, considering the exposure pathways of 

inhalation and direct ingestion of soil, water, and food. 

8.2.2 Exposure Assessment 

The Mackay Level III fugacity model (EQC v2.02; CEMC 2003) was used to estimate the 

distribution of EGBE in air, water, and soils based on 2009, 2010, and 2011 TRI release data. 

Four types of releases of Certain Glycol Ethers were applied to the model: (1) point and fugitive 

air emissions; (2) releases directly to surface water; (3) onsite land treatment and other land 

releases; and (4) transfers off site for land treatment and other land disposal. These reported 

releases were used to estimate national release rates (in kg/hr) to air, water, and soil. Although 

EGBE comprises less than 50% of all ethylene glycol ethers consumed in the United States 

(SRI 2010), it was conservatively assumed to make up 100% of Certain Glycol Ethers reported 

by TRI as released in 2009, 2010, and 2011. National release rates from 2009, 2010, and 2011 

were used to model the distribution of EGBE in air, water, and soil within the modeled area 

(100,000 km2). That is, it was assumed that all Certain Glycol Ethers released nationwide in 

2009, 2010, and 2011 were actually EGBE and were actually released within an area the size of 

the state of Ohio. While these assumptions are clearly conservative, because they are not 

arbitrary (i.e., they are based on actual release data), they require substantially less 

extrapolation and therefore introduce considerably less uncertainty compared to those applied 

in the EPA ERAs. Table 8-1 lists the 2009, 2010, and 2011 release rates used in the model. 

With the exception of the updated release rates, input parameter values used in the Level III 

model (Table 8-3) were consistent with those used by EPA (Cadmus 2000a). The predicted air, 

water, and soil concentrations based on 2009, 2010, and 2011 release rates are presented in 

Table 8-2. 

Because the equilibrium air, surface water, and soil concentrations were highest in 2010, 

all ecological risk assessment calculations were conducted based on the 2010 TRI release data. 
84 

The predicted equilibrium water concentration (1.98 x 10-4 mg/L) of EGBE was used to evaluate 

exposure of aquatic organisms. Exposure of small terrestrial mammals to EGBE was estimated 

based on inhalation and direct ingestion of soil, water, and plants using the same total daily 

intake (TDI) equation and input values used by EPA (Cadmus 2000a) for meadow voles: 

Eqn. 6 

    N

i aa ww diet PC ii IRCTDI IRIRC 1 ( )()3 )(

where: 

Ca = concentration of EGBE in air (mg/m3) 

IRa = inhalation rate (cubic meters per kilogram body weight per day or 

m3/kg BW-day) 

Cw = concentration of EGBE in water (mg/L) 

IRw = water ingestion rate (kilograms per kilogram body weight per day or 

kg/kg BW-day) 

IRdiet = total food ingestion rate (kg/kg BW-day) 

Ci = concentration of EGBE in diet item i (mg/kg) 

Pi = proportion of diet made up by diet item i (unitless) 

In this equation, consistent with EPA (1993a) wildlife exposure assessment guidance 

and EPA’s HAPs ERA for EGBE (Cadmus 2000a), the inhalation rate was multiplied by three to 

account for the inhalation rates derived in the laboratory, rather than from field metabolic rates. 

EPA (1993a) guidance recommends adjusting inhalation rates upwards by a factor of two to 

three to estimate rates expected in the wild. The values used for each of these parameters are 

presented in Table 8-4. The resulting EGBE dose for small terrestrial mammals is predicted to 

be 0.029 mg/kg BW-day. 

8.2.3 Effects Assessment 

The toxicity data compiled for aquatic organisms in Table 3-2 were reviewed to 

determine whether the TRVs used in the HAPs ERAs warrant updating. Because aquatic 

toxicity data are available for a variety of aquatic species representing a range of taxa and 

trophic levels (Table 3-2), a species sensitivity distribution approach was used for the aquatic 

organism effects assessment. The species sensitivity distribution approach can be used when 

toxicity values for the same endpoint (i.e., mortality) are available for a range of species. The 

advantage of this approach is that it incorporates all available toxicity data rather than relying on 

a single critical study. It is not possible, however, to use a species sensitivity distribution 

approach for the terrestrial mammalian effects assessment, because the available laboratory 

mammal toxicity data cover many different endpoints, but only a few species. Therefore, this 

assessment relies on the same TRV approach to assess potential risks to terrestrial mammals 

as used in the Panel and EPA HAPs ERAs. The following two subsections further detail the 

effects assessments for aquatic organisms and terrestrial mammals. 
85 

8.2.3.1 Aquatic Species Effects Assessment 

Acute toxicity tests have been conducted on a variety of aquatic species (Table 3-2). 

Therefore, rather than relying on a single critical study, a species sensitivity distribution 

approach is used to assess potential effects to all aquatic organisms. Species sensitivity 

distributions have been used in previous ERAs (Solomon et al. 1996, Hall et al. 1998), they are 

included in the EPA guidance for ERAs (EPA 1998b), are implicit in EPA’s derivation of ambient 

water quality criteria (Stephan et al. 1985, Fisher and Burton 2003), and they are the focus of a 

book reviewing their use in ecotoxicology in North America and Europe (Posthuma et al. 2002). 

In short, the approach is well tested and well accepted by the scientific and regulatory 

communities alike. 

Species sensitivity distributions incorporate toxicity data from all species tested for 

similar endpoints (e.g., LC50 findings) into a distribution showing the percent of organisms that 

are affected at various chemical concentrations. The distribution of toxicity values can then be 

easily compared to environmental concentrations to determine the percent of species likely to 

be affected at the observed or predicted environmental concentrations. 

Acute species sensitivity distributions were compiled from the aquatic vertebrate and 

invertebrate values presented in Table 3-2. For consistency across species, the following rules 

were adapted from EPA guidance on calculating ambient water quality criteria (Stephan et al. 

1985) for selecting toxicity values to incorporate into the acute species sensitivity distribution: 

 Endpoint – Only LC50 determinations were included.

 Exposure duration – With one exception, values derived from 96-hour exposures were

preferred for most species. Per Stephan et al. (1985), 48-hour exposures were preferred

for Daphnia sp. If values derived from 96-hour exposures were not available for a given

species, 72-hour or 48-hour exposures were used.

 Species weighting – Rather than using the geometric mean of multiple acute values for a

given species to obtain a species mean acute value (in accordance with Stephan et al.

1985), each acceptable acute value for a species was retained as a discrete point in the

distribution. Acute values were then weighted by the number of tests per species to

account for intraspecies variability, using methods described by Duboudin et al. (2004b).

Chronic toxicity values were available for seven species of aquatic vertebrates and

invertebrates (Table 3-2) and the lowest chronic value (7.2 mg/L, rotifer) was greater than the 

lowest acute value (5.4 mg/L, grass shrimp). As discussed in Section 3.3 above, questions have 

been raised about the validity of the toxicity finding in the grass shrimp. Because the species 

sensitivity distribution generated from the chronic toxicity data incorporated fewer species and 

did not include values for the most sensitive species from the acute data, a more conservative 

approach was used to generate a chronic species sensitivity distribution, as follows. 

Duboudin et al. (2004a) present a method for extrapolating chronic species sensitivity 

distributions for chemicals with limited chronic toxicity data by using the acute species sensitivity 

distributions for vertebrates and invertebrates (Figure 8-1). The acute species sensitivity 

distributions are used to calculate means and standard deviations for chronic vertebrate and 
86 

invertebrate species sensitivity distributions, based on empirical relationships between the acute 

and chronic toxicity distributions for 25 representative chemicals (Duboudin et al. 2004a). The 

calculated chronic distribution means and standard deviations for vertebrate and invertebrate 

species are then used to calculate chronic values from each of the acute toxicity values, thus 

populating the chronic species sensitivity distributions for vertebrates and invertebrates (Table 

8-5). The calculated vertebrate and invertebrate chronic toxicity values are then combined with 

any algae or microbe toxicity data that might be available for the chemical, in order to generate 

a chronic species sensitivity distribution representative of all aquatic organisms (Duboudin et al. 

2004a). The vertebrate and invertebrate acute species sensitivity distributions and the chronic 

species sensitivity distribution for all aquatic organisms for EGBE are presented in Figure 8-2. 

 The chronic species sensitivity distribution was used to assess effects to aquatic 

organisms by using the distribution to determine the EGBE surface water concentration that is 

predicted to protect at least 80% of aquatic organisms. Because the acute to chronic distribution 

relationship was established using LC50 findings for acute values and NOECs for chronic values 

(Duboudin et al. 2004a), the calculated chronic values for aquatic organisms (Table 8-5) 

represent predicted NOECs following chronic exposures. Therefore, the 80th percentile of the 

calculated chronic species sensitivity distribution represents the concentration at which no 

chronic effects (e.g., growth or reproduction) occur in at least 80% of the species tested. The 

80th percentile of the no effect distribution was selected for this assessment based on a review 

of regulatory precedents to establish minimum acceptable ecological effect levels for remedial 

decisions at hazardous waste sites (Suter et al. 1995). Twenty percent was determined to be 

the minimum detectable effect level in the chronic and subchronic toxicity tests and field-based 

bioassessment protocols that are typically used to detect effects in ecological endpoints (Suter 

et al. 1995). One advantage of the species sensitivity distribution approach, however, is that any 

percentile can be readily identified and used, depending upon the degree of protection 

preferred. For example, ambient water quality criteria are derived based on the 95th percentile of 

the acute effect distribution (Stephan et al. 1985, Fisher and Burton 2003), while the 90th

percentile of chronic effect distributions has been used in several ERAs (Klaine et al. 1996, 

Solomon et al. 1996, Hall et al. 1998). The 80th percentile of the no effect chronic distribution is 

8.7 mg/L (Figure 8-2). While this value is used to evaluate risks to aquatic organisms in Section 

8.2.4, the effect of using the 90th and 95th percentiles is also discussed. 

8.2.3.2 Mammalian Effects Assessment 

Several EGBE toxicity studies in laboratory mammals have been released since the last 

compilation of toxicity values (ATSDR 1998), but few provide relevant endpoints for ERA 

(Appendix A-2). As discussed above, due to its low Kow and relatively short atmospheric half-life, 

EGBE released into the environment partitions into surface water (Section 8.1.2, Table 8-3). 

 Therefore, laboratory mammal toxicity studies focusing on inhalation, injection, or in vitro routes 

of exposure do not represent environmental exposure to EGBE for small mammals. The results 

from three drinking water studies have been published since the ATSDR (1998) compilation was 

issued (Appendix A-2). One is an acute toxicity study on F344 rats where a LOAEL for 
87 

histopathological effects of 250 mg/kg BW-day is reported after two to four doses (Nyska et al. 

2003); the second is from a single dose mortality study with guinea pigs where an LD50 of 1,414 

mg/kg BW is reported (Gingell et al. 1998); and the third is from a multigenerational chronic 

study with mice where the LOAEL for mortality, growth, and reproductive effects was 10,000 

mg/kg BW-day (Lamb et al. 1997). The first two acute studies do not provide an appropriate 

representation of environmental exposures to EGBE and all three studies present toxicity values 

much greater than the toxicity value that is the basis for EPA’s RfD. In addition, none of the 

other oral exposure studies (e.g., oral gavage) provide a more sensitive toxicity value than the 

basis for the RfD (Appendix A-2). Therefore, this assessment uses the same small mammal 

TRV (20 mg/kg BW-day) applied in the previous HAPs ERAs. However, in light of the Lamb et 

al. (1997) study, this TRV is certainly conservative. 

8.2.4 Risk Characterization 

HQs were calculated to evaluate ecological risks using the equation below: 

Eqn. 7 

TRV

Exposure HQ

Based on 80th percentile, the HQ for aquatic organisms is 0.00002, indicating that they 

are not likely to be at risk from the highly conservative EGBE exposure scenario presented 

above. Based on the 95th and 90th percentiles, the HQs for aquatic organisms are 0.00005 and 

0.00009, respectively. Similarly, the HQ for small mammals was 0.001, indicating that they also 

are not likely to be at risk, even under the conservative assumptions used in this exposure 

scenario. 

Both calculations reflect a high margin of safety because the HQs are much less 

than 1. For example, surface water concentrations would have to be more than 10,000 times 

higher than was predicted using the Mackay Level III model in order for exposures to approach 

the 80th percentile of the chronic species sensitivity distribution for aquatic organisms. Similarly, 

the dose to small mammals would have to be 300 times higher in order for exposures to 

approach the mammalian TRV. 

The many conservative assumptions used to determine EGBE distribution, toxicity, and 

exposure further contribute to the margin of safety provided by this ERA. For example, in the 

Level III Mackay model, the total 2010 national emission rates for Certain Glycol Ethers were 

applied to a default model area approximately the size of the state of Ohio. Although the 

equilibrium distributions based on the 2009 and 2011 national emissions were also modeled, 

the equilibrium concentrations from the 2010 were used in the ERA because they were the 

highest from the three most recent years. In addition, the modeled area is 100,000 km2 (Mackay 

et al. 1992) which is approximately 1.3% of the size of the continental United States. Because 

the modeled area is based on a default value, the modeled concentrations are expected to 

overestimate actual ambient concentrations, by up to three orders of magnitude. 
88 

In addition, although EGBE makes up only about half of the ethylene glycol ethers 

consumed in the United States, all releases of Certain Glycol Ethers in the TRI were 

conservatively assumed to be EGBE. Thus, the ERA was based on the conservative 

assumption that EGBE consumption is two-fold higher than most recent data suggest (SRI 

2010).. Uncertainty is also potentially contributed to this analysis through the selected TRVs. 

The 80th percentile from the calculated chronic species sensitivity distribution was used for the 

aquatic organism TRV in this assessment. Although the 80th percentile of the no effect 

distribution is believed to be the most appropriate effect level for evaluating population and 

community level effects, it is worth noting that using the 95th percentile (2.3 mg/L) or the 90th

percentile (4.2 mg/L) would only slightly increase the HQ for aquatic organisms. In addition, 

because the Duboudin et al. (2004a) method for extrapolating chronic species sensitivity 

distributions from acute distributions is still being evaluated for a variety of chemicals, it is worth 

noting that the TRV derived from the 80th percentile of the chronic species sensitivity distribution 

in this analysis is generally comparable to the TRVs used in the HAPs ERAs: 1.25 mg/L (CMA 

1997), 0.91 mg/L (Cadmus 2000b), and 9.1 mg/L (Cadmus 2000a). Aquatic HQs calculated 

using the TRVs employed by the Panel (CMA 1997) and in EPA’s Tier 1 and 2 assessments 

(Cadmus 2000a,b) would be 0.0002, 0.0002, and 0.00002, respectively. Therefore, using any of 

the TRVs from the previous ERAs would not significantly change the HQ for aquatic organisms 

calculated above. 

8.3 Conclusions 

Potential ecological risks posed by EGBE are the subject of three separate ERAs—the 

Panel’s HAPs ERA (CMA 1997), EPA’s HAPs ERA (Cadmus 2000a, b; EPA 2003, 2004a), and 

the analysis presented in this petition. Each assessment is consistent with EPA modeling and 

exposure assessment guidance and founded on highly conservative assumptions about EGBE 

distribution, toxicity, and exposure. The findings of all three assessments support the conclusion 

that EGBE does not meet the ecotoxicity listing criteria in Section 313(d)(2)(C). The Panel’s 

HAPs analysis found no evidence of risk to aquatic plants or small terrestrial mammals from 

EGBE using national emissions data from the 1996 TRI when glycol ether emissions were 

almost double their current levels. The EPA HAPs analyses used what the Agency has called 

“worst-case” assumptions about EGBE mixing in the environment downwind of the facility with 

the highest glycol ether emissions in the country, but nevertheless found no evidence of risk to 

aquatic microorganisms and small terrestrial mammals. The updated assessment presented in 

this petition blends the most scientifically sound methods and assumptions from the previous 

analyses with updated emissions and ecotoxicological data and the more conservative 

assumption that EGBE represents 100% of reported releases of Certain Glycol Ethers. Like its 

predecessors, this ERA finds no evidence of adverse effects in aquatic organisms or small 

mammals from facility releases of EGBE. The margins of safety associated with the HQs 

generated in this ERA are sufficiently large to ensure that adjustments to individual input values 

(such as those related to the concentration of EGBE in surface water and the TRV) will not 
89 

change the conclusion of this ERA that EGBE is not expected to cause significant adverse 

environmental effects. 
90 

9.0 SUMMARY AND RATIONALE FOR DELISTING EGBE 

The case for removing EGBE (CAS 111-76-2) from the EPCRA TRI reporting list is 

straightforward and compelling. The available scientific data indicate that EGBE poses a low 

potential for adverse human health and environmental effects, thus making an exposure 

assessment appropriate under EPA’s interpretation of the TRI listing criteria in Section 313(d)(2) 

of EPCRA. This petition uses essentially the same protective health and environmental criteria 

and is consistent with the conservative exposure assessment methods that formed the basis of 

the Agency’s HAPs delisting decision. Because emissions of EGBE are about half the levels 

evaluated in the HAPs delisting decision, EPA’s HAPs findings that EGBE releases may not 

reasonably be anticipated to cause any adverse effects to the human health or the environment 

have an even stronger basis in the context of this petition. 

In addition, the policies and goals of the TRI program would be well served by deleting 

EGBE from the EPCRA Section 313 reporting list. EPA’s policy of ensuring consistency with 

other Agency decisions should be highly influential here, particularly in light of the confusion— 

and the concomitant potential for misdirected community priorities—that currently exists 

because EGBE has been found not to be “hazardous” under the CAA but remains on the 

EPCRA list of chemicals deemed to be “toxic” based on essentially identical statutory criteria. In 

this instance, misdirected local priorities can have real environmental consequences. Because 

EGBE is an effective cosolvent for water-based coatings, inks, and similar products, removing it 

from the TRI list would eliminate the disincentive that currently exists under EPCRA to its use in 

formulations that have substantial VOC-reduction benefits as compared to many other solvents. 

9.1 Delisting EGBE Is Fully Consistent with EPCRA’s TRI Listing Criteria as Interpreted 

by EPA 

Section 313(d) of EPCRA calls for the delisting of a chemical where “there is not 

sufficient evidence to establish” that the chemical “is known to cause or can reasonably be 

anticipated to cause” any of three types of effects: 

(A) significant adverse acute human health effects; 

(B) (i) cancer or teratogenic effects, or (ii) serious or irreversible 

reproductive dysfunctions, neurological disorders, heritable 

genetic mutations, or other chronic health effects; or 

(C) a significant adverse effect on the environment of sufficient 

seriousness, in the judgment of the Administrator, to warrant 

reporting under EPCRA. 

As EPA has interpreted these criteria (59 FR 61432 [EPA 1994a]), exposure may be 

considered for chronic human health and environmental effects if a substance exhibits “low to 

moderately low toxicity based on a hazard assessment,” so that “unrealistic exposures would be 

necessary for it to pose a risk to communities.” As detailed in the qualitative hazard evaluation 

presented in Section 3 above and summarized in Table 9-1, EGBE’s potential to cause adverse 
91 

human health or environmental effects is appropriately assessed as low under EPA’s hazard 

assessment criteria for TRI listing determinations. 

With respect to potential adverse chronic human health effects, EPA has determined 

that hemolysis is the critical effect, and that prevention of hemolysis will protect against any 

other systemic effect potentially associated with EGBE exposure (Section 3.2). The scientific 

data show, moreover, that humans are resistant to the hemolytic effects of EGBE (Section 

3.2.1.3). The PBPK model used in the IRIS assessment (Corley et al. 1994) predicts that, even 

in humans exposed continuously by inhalation to an EGBE-saturated atmosphere, maximum 

blood concentrations of EGBE’s toxic metabolite (BAA) would be well below the level needed to 

produce hemolysis in humans (Udden 2002, EPA 2010). Likewise, even minor prehemolytic 

effects are not expected to occur in humans from ingestion exposures in excess of 500 mg/kg 

BW-day. Such inhalation and ingestion doses are not realistically expected to occur in the 

vicinity of EGBE-emitting facilities, where empirical and modeling-based estimates of air and 

surface water concentrations are many orders of magnitude below such exposures. (See 

Section 3.4.1 and Table 9-1). 

EGBE’s potential to cause significant adverse ecological effects is likewise appropriately 

evaluated as low under EPA’s TRI hazard assessment criteria and past listing decisions. EGBE 

exhibits low potential for persistence or bioaccumulation (Section 3.1). Consistent with the 

findings of a series of ecotoxicity reviews of EGBE (WHO 1998, 2010, Staples 1998, Devillers et 

al. 2002, Environment Canada 2002, INERIS 2006), EPA concluded in the HAPs delisting 

rulemaking that EGBE causes only “very minor” effects that “are unlikely to be ecologically 

significant” (68 Fed. Reg. 65657 [EPA 2003]). In addition to the absence of any impacts on 

ecosystems, the scientific data indicate that EGBE’s limited adverse effects on aquatic 

organisms occur only at what EPA’s TRI listing criteria consider to be high exposures, meaning 

that EGBE is properly evaluated as a low-toxicity chemical in terms of potential environmental 

effects (see Sections 3.3 and 3.4.2; Table 9-1).

Because EGBE “is of low toxicity and unrealistic exposures would be necessary for it to 

pose a risk to communities,” EPA’s interpretation of EPCRA’s TRI listing criteria calls for the 

consideration of exposures in determining whether to grant this petition and delist EGBE (59 FR 

61442 [EPA 2004a]). Potential human and environmental exposures to EGBE were studied 

intensively by EPA in the HAPs rulemaking. There, EPA stated it was “confident” that “the 

results are more likely to overestimate rather than underestimate true exposures and risks” and, 

accordingly, determined that “the potential for adverse human health and environmental effects 

to occur from projected exposures is sufficiently low to provide reasonable assurance that such 

adverse effects will not occur” (68 Fed. Reg. 65660 [EPA 2003]). As summarized in Table 9-2, 

there is an even stronger basis for making this finding here. 

Specifically, the general approach and specific assumptions employed in the exposure 

assessment presented here (Sections 4 through 8) are consistent with those that the 

Administrator’s HAPs delisting decision found to be appropriate and conservative. EPA 

determined in the HAPs delisting proceeding (68 FR 65651-52) that the EPCRA TRI database 

“provide[s] a reasonable representation of ... EGBE emissions” and “an adequate basis for 
92 

dispersion modeling and ... exposure assessment.” Accordingly, nationwide exposure potential 

is assessed in Section 5 by developing an inventory of Certain Glycol Ether releases using 

2009, 2010, and 2011 TRI data, applying the assumption, in the absence of facility-specific 

information to the contrary, that EGBE represents 100% of reported glycol ether releases. More 

importantly, because this petition is based on current TRI data showing that emissions have 

declined by more than half from the 1993 TRI data used in the HAPs delisting rulemaking, 

predicted exposures have fallen substantially from the levels EPA evaluated in the HAPs 

context. 

As described in Section 6, every EGBE-emitting facility listed in the TRI database has 

been subjected to a screening process very similar to that used in the HAPs proceeding to 

determine whether any facility has the potential to have maximum annual average 

concentrations of EGBE greater than the IRIS RfC of 1.6 mg/m3 at or beyond the fenceline. 

Despite the highly conservative assumptions used in the screening, no EGBE-emitting facility 

was found to have potential maximum exposures above the RfC. AERMOD modeling conducted 

to test the conservatism of the screening step predicts that the maximum annual average 

concentrations are likely to be approximately two orders of magnitude below the RfC (see 

Section 6.5). Similarly, potential cumulative impacts from clusters of smaller sources are 

separately evaluated in Sections 6.4 and 6.5 using a methodology more conservative than that 

used in the HAPs proceeding, and the results show predicted maximum annual average 

concentrations of EGBE resulting from clusters of smaller sources within the same zip code are 

well below the RfC. The key findings of the facility and cluster assessments appear in Table 9-2.

In addition to screening facilities for long-term exposures to EGBE, we also evaluated 

the potential for short-term exposures near EGBE-emitting facilities to cause acute human 

health effects, viz., eye and upper respiratory tract irritation, which has been identified as the 

critical effect for short-term exposures. As discussed in Section 3.2.1.1, above, because of the 

relatively high insensitivity of human red blood cells to the hemolytic effects of EGBE, the lowest 

short-term exposure level at which such irritation effects have been reported is 550 mg/m3, and 

no irritation effects have been observed at 97 mg/m3. These concentrations are higher than the 

maximum annual average concentrations estimated above based on EPA modeling guidelines 

by factors of >3,000 and >500, respectively. There is, accordingly, a convincing basis to 

conclude that adverse acute effects from EGBE facility releases is unlikely. Nevertheless, six 

high-emitting facilities offering a reasonable approximation of “worst-case” acute exposures 

were screened using EPA’s short-term modeling methods for HAPs (EPA 1992a). The results 

were evaluated against the NOAEL of 97 mg/m3 in a MOE analysis. Predicted maximum 1-hour 

concentrations at or beyond the fencelines of all six facilities screened were far below the 

NOAEL based on Tier 2 and 3 modeling, with Tier 3 MOEs ranging from 25 to 198. These 

results, presented in Section 6.6 and summarized in Table 9-2, are more than adequate to 

support a finding that EPCRA’s acute effects delisting criterion is met, because the NOAEL is 

derived from human data meaning, in accordance with EPA TRI listing decisions, that MOEs 

above 10 “indicate a low level of concern” for potential acute effects. As developed in Section 
93 

6.4, several additional considerations suggest strongly that the potential for acute effects is far 

lower than the MOE analysis indicates. 

This petition also evaluates the potential for chronic health effects posed by human 

contact with EGBE in surface water, based on essentially the same conservative assumptions 

and models that EPA used in the HAPs evaluation, with updates to reflect: the estimated 

surface water concentration based on 2009, 2010, and 2011 TRI data, the current RfD, and 

changes in EPA (2004b) guidance for dermal risk assessment. As developed in Section 7, the 

worst-case dose—for residents that consume and bathe in impacted water year-round for 30 

years—was estimated to be 0.00001 mg/kg BW-day. Dividing the dose by the RfD yields an HQ 

of 0.0001 (see Table 9-2). 

To assess potential adverse environmental effects, Section 8 builds on the three ERAs 

conducted in the HAPs proceeding by applying 2009, 2010, and 2011 TRI data to the Mackay 

Level III fugacity model to yield updated estimates of the maximum surface water concentration. 

Applying an updated TRV for aquatic organisms identified in a supplemental review of the 

ecotoxicity literature for EGBE, the ERA presented in this petition predicts HQs of 0.00002 for 

aquatic organisms and 0.001 for small mammals. (See Table 9-2.) 

The results of these assessments show that estimated EGBE exposures in the vicinity of 

emitting facilities anywhere in the United States are well below the IRIS RfC and RfD for 

inhalation and dermal/ingestion exposures as well as appropriate ecological TRVs. All HQs 

generated by the exposure assessments developed for this petition are well below 1.0 and even 

lower than the HQs that led EPA to find in the HAPs delisting proceeding that releases of EGBE 

may not reasonably be anticipated to cause adverse human health or environmental effects. 

Because this petition uses assessment methods consistent with those EPA found appropriate 

and conservative in the HAPs case, there is an even stronger basis for making the same 

determination here. 

9.2 Substantial Conservatism is Incorporated into Every Primary Element of the 

Toxicological, Exposure, and Ecological Assessments Presented in this Petition 

The HQs estimated in this petition are overstated by at least three to five orders of 

magnitude because of the substantial conservatism built into every principal part of HHRA and 

ERA presented here, as summarized in Table 9-3 and discussed below. 

9.2.1 IRIS Reference Values 

In general, IRIS reference values are conservative criteria establishing a “daily exposure 

to the human population, including sensitive subgroups, that is likely to be without an 

appreciable risk of deleterious effects during a lifetime” (EPA 2010). As discussed in Section 4.2 

above and summarized in Table 9-3, the specific IRIS RfC and RfD values that EPA derived for 

EGBE should provide ample protection against acute human health effects and reflect several 

significant elements of conservatism that likely render them significantly lower than necessary to 

protect against chronic health effects. 
94 

First, both the RfC and RfD were based on hemolytic effects in rats and, although the 

available data indicate that humans are 100 times less sensitive to the hemolytic effects of 

EGBE (see Section 3.2.1.3), the IRIS assessment uses interspecies uncertainty factors of 1 

(ingestion) and 3 (inhalation) in deriving the reference values. The IRIS values therefore may 

reflect an additional safety margin of 100 to 300, and the available scientific data suggest that 

they may be far below exposure levels that would be fully protective of human health (EPA 

2010). 

Second, both the RfC and RfD incorporate an intraspecies uncertainty factor of 10 (EPA 

2010). This factor is probably unnecessarily high by a factor of 3 to 10, because investigations 

of population groups that might be expected to show increased sensitivity to hemolytic effects of 

EGBE (including the young, the old, and individuals with sickle cell anemia or hereditary 

spherocytosis) do not show increased susceptibility. 

Third, although the RfC is developed to be protective of continuous exposures over a 

human lifetime, the air concentrations that are compared to the RfC in the analysis are 

maximum predicted annual average concentrations. Concentrations averaged over a 70-year 

lifetime would be expected to be considerably lower than maximum annual averages, although 

the degree of conservatism contributed by this assumption cannot be quantified. 

Finally, although the 2010 IRIS assessment finds “limited” evidence of potential 

carcinogenicity from rodent studies, subsequent mechanistic studies have led EPA to conclude 

that, even if the limited tumor findings in rodents are relevant to humans, the current RfC and 

RfD provide adequate protection against any such risk. Therefore, any uncertainties relating to 

the limited animal carcinogenicity data evaluated in the IRIS assessment have been eliminated 

and should not be significant considerations in an up-to-date assessment of human health risks. 

9.2.2 Exposure Assessments 

As developed in Sections 5, 6, and 7 of this petition and as summarized in Table 9-3, the 

models and assumptions used in the human inhalation and surface water exposure 

assessments presented in this petition reflect several significant elements of conservatism. 

First, the inventory developed here (Section 5) assumes that all releases of Certain 

Glycol Ethers reported in the TRI database are EGBE, unless facility-specific information to the 

contrary is available. Because EGBE comprises 52% of United States annual consumption of 

glycol ethers (SRI 2010), the inventory’s assumption that all releases of Certain Glycol Ether are 

EGBE (in the absence of facility-specific information to the contrary) generally overstates EGBE 

releases by a factor of two. 

Second, the chronic screening approach used in this petition (Section 6) predicts 

maximum annual average concentrations of EGBE for every emitting facility in the United States 

required to file Form R reports under TRI. Similarly, the acute screening approach predicts the 

maximum 1-hour average concentration of EGBE at facility fencelines. As EPA observed in the 

HAPs proceeding, the “use of the maximum annual average ambient concentration for each 

emission source to characterize the exposed population provides a conservative approach to 

chronic exposure modeling” and “[g]iven the likely proximity of inhabitable areas and the 
95 

variability of human activity patterns over an annualized time period, it is our expectation that 

actual maximum individual exposure would be at least a factor of 2 less than predicted by the 

models” (68 FR 65653 [EPA 2003]). 

Third, the conservatism built into the screening procedure is evident when a subset of 

those facilities that screened out at Step B was subjected to Tier 1, 2, and/or 3 analyses. On 

average, the maximum annual average concentrations decreased by 99.3% when the same 

facility that was first evaluated under Step A was subsequently evaluated under Tier 3. That is, 

the maximum predicted annual average concentration generated under the more robust Tier 3 

modeling was more than two orders of magnitude lower than that generated by the most 

conservative Step A screen. The Step B screen yielded maximum predicted annual average 

concentrations that were, on average, more than 26-fold higher than those generated using Tier 

3 modeling. 

 Fourth, our assessment of potential acute health effects, based on (1) the NOAEL of 97 

mg/m3 derived from human data and (2) the estimated reasonable worst-case estimated 

maximum hourly average concentration, resulted in acute MOEs of over 5. An MOE above 5 is 

protective because the NOAEL is based on human data, EPA AEGL guidance calls for an 

interspecies uncertainty factor from 3 to 10 for nonsystemic irritation effects, and an appropriate 

time-adjustment would support an estimated 1-hr NOAEL of 137 mg/m3, over 40% higher that 

the value used in the MOE derivation. 

Fifth, EPA found that the modeling and assumptions used to assess ingestion and 

dermal exposures arising from EGBE in surface water levels were conservative and the 

maximum exposure estimates developed using the Agency’s model, shown in Table 7-5, 

represents a worst-case exposure scenario (68 FR 65653-54). In addition, exposure point 

concentrations in surface water were calculated by assuming that 100% of releases of Certain 

Glycol Ethers to all media were EGBE and were concentrated into 100,000 km2. In reality, 

because EGBE represents 52% of the market share of ethylene glycol ethers, actual releases of 

EGBE are likely overestimated by two-fold. Because the 100,000 km2 unit area represents 1.3% 

of the total land area of the United States, actual concentrations may be overestimated by up to 

two orders of magnitude. 

9.2.3 Ecological Risk Assessment 

The ERAs previously conducted in the HAPs delisting proceeding and the updated ERA 

prepared for this petition conclude that EGBE concentrations are three or more orders of 

magnitude lower than highly protective levels of ecotoxicological concern (Section 8). In 

addition, EPA noted in the HAPs delisting decision that the TRVs used in the ERA “were derived 

from very minor effects which were unlikely to be ecologically significant” (68 FR 65657 [EPA 

2003]). 

As noted above, the exposure point concentrations in surface water are likely 

overestimated by up to 150-fold, due to the assumptions that 100% of releases of Certain Glycol 

Ethers to all media are EGBE and are concentrated into 100,000 km2 (an area that is 

approximately 1.3% of the area of the United States). Conservative exposure assumptions 
96 

applied to the TDI calculation for small mammals are consistent with those employed in EPA’s 

HAPs ERAs. Conservatism is also contributed by the TRVs for aquatic species (based on the 

most sensitive organism tested), and small mammals (based on the same underlying study 

used to generate the RfD, which may be too low by a factor of 50 to 100). Finally, as EPA found 

in the HAPs delisting decision, the evaluation of relatively nonsevere effects on individual 

organisms rather than effects that are likely to be ecologically significant at more complex levels 

of organization (population, community, ecosystem) contributes substantial conservatism to the 

ERA. 

As summarized in Table 9-3, the above considerations, taken together, indicate that the 

already low HQs derived in Sections 6 through 8 and summarized in Table 9-2 may overstate 

potential chronic health and environmental risks of EGBE releases by as much as two to five 

orders of magnitude. Accordingly, the toxicity, exposure, and ecotoxicity assessments 

presented in this petition support an even higher level of confidence than EPA expressed in the 

HAPs delisting decision for the conclusion that there is “reasonable assurance” that “adverse 

human health and environmental effects” from EGBE facility emissions “will not occur.” 

9.3 In Light of the HAPs Delisting Decision, EPA’s Policy of Ensuring Consistency with 

Other Agency Decisions Supports Removal of EGBE from the TRI Reporting List 

EPA has emphasized the need to ensure that TRI listing decisions are consistent with 

“other EPA decisions on the same chemical, to the extent that such decisions relate to the same 

basic criteria for human health and the environment” (52 FR 5481 [EPA 1987a]). A policy of 

maintaining consistency across different environmental programs has long been in place at 

EPA, because it is essential to maintain the Agency’s credibility as a scientific and regulatory 

body. But it has special significance here because, as developed below, the conclusion that 

EGBE should be removed from the TRI reporting list follows directly from the findings the 

Administrator made recently in the HAPs delisting. 

CAA Section 112 calls for the removal of substances from the HAPs list where EPA finds 

that “there is adequate data on the health and environmental effects of the substance to 

determine that ... the substance may not reasonably be anticipated to cause any adverse 

effects to the human health or adverse environmental effects.” By its plain language, Section 

112 places a higher burden on delisting decisions than does EPCRA Section 313. EPCRA calls 

for delisting where “there is not sufficient evidence to establish” that a chemical “can reasonably 

be anticipated to cause” the designated health and environmental effects. Section 112, in 

contrast, requires more than a finding that the data are “not sufficient” to establish the stated 

health and environmental findings. Section 112 requires “adequate data” “to determine that ... 

the substance may not reasonably be anticipated to cause” adverse health or environmental 

effects. 

Moreover, Section 112 requires a showing that a substance may not reasonably be 

anticipated to cause “any adverse effects to the human health.” The CAA finding clearly 

encompasses the EPCRA human health delisting criteria in Section 313(d)(2)(A) & (B), which 

are limited to the specific health effects mentioned in the statute. Likewise, Section 112 requires 
97 

a demonstration that the substance to be delisted may not reasonably be anticipated to cause 

“adverse environmental effects,” a test that is at least as broad, if not broader, than EPCRA 

Section 313(d)(2)(C), which refers to “a significant adverse effect on the environment of 

sufficient seriousness ... to warrant reporting under this section.” 

In short, the Administrator’s finding under Section 112 that EGBE “may not reasonably 

be anticipated to cause any adverse effects to the human health” or “adverse environmental 

effects” should be given at least heavy weight in applying the EPCRA delisting criteria to this 

petition unless, of course, significant changes in the relevant scientific and other data indicate 

that potential adverse human health and ecological risks are significantly greater than EPA 

found in 2004. This petition demonstrates that any such risks are far lower. 

As demonstrated above, this petition is based on essentially the same exposure 

assessment methodology and ecological criteria that formed the basis for EPA’s HAPs findings. 

The only significant differences between the scientific and factual record the Agency evaluated 

in the HAPs proceeding and the demonstrations made here are updates to human health 

criteria and use of the most recent TRI data available. Despite (i.e., 1%) growth in consumption 

since 1990 (SRI 2010), EGBE emissions have declined significantly as compared to the 1993 

TRI data considered in the HAPs case, principally as a result of VOC emission control 

regulations and other environmental programs. Although the toxicity criteria have changed due 

to refinement of the data and modeling procedures used by EPA in deriving its RfD and RfC, as 

shown in Table 9-3, these criteria incorporate substantial levels of conservatism. Furthermore, 

the greater stringency in the toxicity criteria is more than balanced by the reduction in emissions 

and resultant human exposure such that predicted risks have decreased since the HAPs 

evaluation. 

The human and environmental exposures conservatively estimated here are significantly 

lower than those EPA found appropriate to delist EGBE under Section 112. Consequently, 

EPA’s determinations in the HAPs delisting proceeding, that EGBE releases “may not 

reasonably be anticipated to cause any adverse effects to the human health” or “adverse 

environmental effects,” have an even stronger scientific and factual basis in the context of this 

petition under EPCRA. Further, the concurrent increase in consumption (+1%) and decrease in 

emissions (-70%) since 1993 suggests that the scientific basis for these findings would not be 

undermined even if current consumption and emission patterns of EGBE are taken into account. 

9.4 Removing EGBE from the TRI Would Promote the Local Risk Management and 

Pollution Prevention Objectives of EPCRA 

The purposes of EPCRA are to “to inform persons about releases of toxic chemicals to 

the environment; to assist governmental agencies, researchers, and other persons in the 

conduct of research and data gathering; [and] to aid in the development of appropriate 

regulations, guidelines, and standards” (42 U.S.C. § 11023(h)). Thus, the EPA TRI website 

(http://www.epa.gov/tri/whatis.htm) describes the objectives of the program as follows: 

One of Emergency Planning and Community Right-to-Know Act 

(EPCRA)’s primary purposes is to inform citizens of toxic chemical 
98 

releases in their areas. EPCRA Section 313 requires EPA and the 

States to collect data annually on releases and transfers of certain 

toxic chemicals from industrial facilities and make the data 

available to the public through the Toxics Release Inventory 

(TRI).....The goal of the Toxics Release Inventory Program is to 

provide communities with information about toxic chemical 

releases and waste management activities and to support 

informed decision making at all levels by industry, government, 

non-governmental organizations, and the public. 

EPA has indicated elsewhere (59 FR 61443) that “[b]y listing chemicals that present a 

hazard and providing TRI data on these chemicals to the public, EPA allows the public to make 

the determination as to whether there is a risk in their community.” As this passage indicates, 

the dissemination of accurate information on “chemicals that present a hazard” is critical to the 

success of the TRI program. An inventory that includes nonhazardous chemicals, particularly 

high-volume chemicals like EGBE, undermines the statutory goals by diverting the attention and 

resources of the public, regulatory officials, and researchers away from facilities and chemicals 

that should be the focus of local risk management and pollution prevention programs. 

These considerations are significant in the case of EGBE. Many EGBE-using facilities, 

particularly can manufacturing plants, do not release reportable quantities of other TRI 

chemicals, including other chemicals in the “Certain Glycol Ethers” category. Nevertheless, as 

long as EGBE remains on the TRI, many of these facilities will continue to routinely appear on 

local and regional lists of “top toxics emitters” even though EPA has found that EGBE releases 

may not reasonably be anticipated to cause adverse human health or environmental effects. 

The contradictory signals that EPA is sending to local communities are confusing, undermine 

the credibility of the TRI program as a reliable source of information on toxic releases, and 

unfairly brand some EGBE-using facilities as major sources of “toxics.” 

VOC control considerations also support the delisting of EGBE from the TRI. Although it 

is now settled that EGBE’s status as a VOC is not a sufficient basis for keeping it on the TRI 

reporting list,z facilities emitting EGBE remain subject to national and state/local emissions 

reporting and control programs under the ozone attainment provisions of Title I of the CAA. In 

fact, when EPA removed EGBE from the CAA HAPs list, it emphasized that it “will continue to 

be ... regulated under EPA’s criteria pollutant (ozone) program (69 FR 69321 [EPA 2004a]).aa

Accordingly, removal of EGBE from the TRI reporting list should not adversely affect ozone 

attainment programs under Title I of the CAA. 

Delisting EGBE may assist in achieving objectives of Title I. VOC emission control has 

long been a bedrock of EPA’s ozone attainment strategy, particularly in consumer and 

z American Chemistry Council v. Whitman, 406 F.3d 738, 742 (D.C. Cir. 2005). 

aaEPA also indicated in the same passage that EGBE would continue to be listed on the TRI, but at that time the 

Agency continued to adhere to the position, since reversed on judicial review, that EGBE’s status as a VOC is an 

adequate basis for listing on the TRI.
99 

commercial products (EPA 1995, 2007). Although EGBE is a VOC, its physical characteristics 

support its use as a cosolvent for water-based formulations in many consumer and commercial 

coating products. In some applications, the switch to waterborne solvent formulations may 

reduce solvent content from up to 80% of the formulation to as little as 2% to 10%. EPA has 

often recognized that waterborne formulation, where commercially feasible, can contribute 

significantly to the ozone attainment objectives of the CAA. As recently as July 2007, the 

Agency emphasized that “water-based coatings are an environmentally friendly technology that 

we do not want to be lost as an option to manufacturers” (72 FR 38966 [EPA 2007]). EPA also 

has acknowledged that “it is important that manufacturers retain as much flexibility as possible” 

in developing reformulations that reduce the ozone-forming potential of their products while 

continuing to “meet the performance specifications required” (ibid.). The Agency has 

recognized, accordingly, the need to avoid regulatory measures that needlessly discourage 

manufacturers from using “environmentally friendly technologies” or unintentionally encourage 

the public, local regulators and manufacturers to use other solvents that may be toxic or highly 

reactive compounds that actually generate more ozone (ibid.). 

As mentioned above, the primary goal of the TRI program, as EPA has put it, is to 

“empower” citizens and local regulators to “hold companies accountable” for releases of toxic 

chemicals, and to “make informed decisions about how toxic chemicals are to be managed.” 

Maintaining EGBE on the TRI, particularly after the Agency has concluded that facility releases 

are not hazardous to human health or the environment, invites confusion and the concomitant 

potential for local decisions that actually impede the ozone attainment goals of Title I of the 

CAA. Conversely, removing EGBE from the TRI would eliminate an existing impediment to the 

replacement of solvent-based products with EGBE/water-based solvents with the potential to 

significantly lower overall VOC emissions. In short, as long as EGBE remains on the TRI, the 

Inventory cannot achieve its fundamental objective of providing accurate information that will 

enable business, regulators and the public to make environmentally sound decisions. 

Significantly, the possibility of future increases in EGBE consumption—whether as a 

continuation of current favorable trends in favor of water-based solvents as a result of the 

removal of EGBE from the TRI reporting list or for other reasons—would not cast doubt, now or 

in the future, on the conclusion that facility releases of EGBE may not reasonably be anticipated 

to cause any adverse human health or adverse environmental effects. As discussed in Section 

2.5, VOC emission limits, together with other potential factors such as corporate product 

stewardship programs, are likely responsible for the substantial (about 70%) reduction in EGBE 

emissions since the mid-1990s even while annual consumption increased through the 1990s 

and early 2000s (Figure 2-1). More recently, the national consumption of EGBE has stabilized 

and even declined. These factors keep to a minimum the potential for increased community 

exposures to EGBE in the future even if production or consumption rise in response to its 

removal from the TRI reporting list or for other reasons. In any case, the substantial 

conservatism built into very significant element of the toxicological, exposure, and ecological 

assessments presented in this petition—as measured by the two-to-five orders of magnitude 

overstatements in the HQs presented in Tables 9-2 and 9-3 above, render theoretical any 
100 

concern that future increases in EGBE production or consumption might justify a reevaluation of 

the determination that facility releases of EGBE may not reasonably be anticipated to cause any 

adverse human health or adverse environmental effects. 

In conclusion, removing EGBE from the TRI reporting list is called for under the listing 

criteria of EPCRA Section 313(d)(2) as interpreted by EPA, is necessary to ensure consistency 

with other EPA programs (particularly the HAPs program), and would promote the objectives of 

the statute by encouraging increased use of a chemical with demonstrated environmental 

benefits without interfering with other federal or local environmental programs and policies. 

Accordingly, the Panel respectfully requests that the Administrator grant this petition and 

remove EGBE from the TRI reporting list. 
101 

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TABLES 
Toxicity Endpoint

Acute Toxicity

Chronic Toxicity

 Carcinogenicity

Mutagenicity

Developmental Toxicity

Reproductive Toxicity

Immunotoxicity

Other Chronic Toxicity

Environmental Toxicity

Persistence

Bioaccumulation

Terrestrial Mammals and Birds

• Most sensitive credible LC50 = 89 mg/L

• Most LC50 values > 1000 mg/L

• Most sensitive EC50 = 164 mg/L

• Most sensitive LOAEL = 7.2 mg/L

• Most LOAELs > 100 mg/L

EGBE: ethylene glycol monobutyl ether

EPA: U.S. Environmental Protection Agency

IRIS: Integrated risk information system

LOAEL: lowest observed adverse effect level

mg/kg-day: milligrams per kilogram body weight per day

mg/L: milligrams per liter

mg/m3

: milligrams per cubic meter

NOAEL: no observed adverse effect level

EGBE causes only “very minor” effects that “are unlikely to be ecologically significant” (EPA 

2003 [68 Fed. Reg. 65657])

• Because nonlinear, nongenotoxic modes of action are likely responsible for the tumors

observed in rodent studies, the IRIS RfD and RfC are adequately protective of any possible 

carcinogenic effects in humans (EPA Cancer Evaluation [EPA 2005a]).

Table ES-1. Key Findings of the Qualitative Hazard Evaluation

Summary Evaluation and Principal Reference

Primary acute effects in humans are eye and nasal irritation at levels >500 mg/m3

 (Carpenter 

1956); no irritation was found at current occupational exposure limits - 97 mg/m3

 (Johansen 

1986). Facility fenceline and environmental concentrations are far lower. 

Releases of EGBE “may not reasonably be anticipated to cause any adverse effects to human 

health” (EPA, 69 FR 69322).

• “Limited” evidence of carcinogenicity in animals; the human carcinogenic potential of

EGBE cannot be determined (IARC 2006).

Not expected to be mutagenic or clastogenic. (EPA 2010)

A “minimal” LOAEL for developmental effects = 700 mg/kg-day based on a very slight decrease 

in pup weight (EPA 2010).

700 and 1,300 mg/kg-day are considered to be NOAEL and LOAEL, respectively, for both 

maternal and reproductive effects (EPA 2010).

Not immunotoxic (EPA 2010)

Continuous inhalation exposure to an EGBE-saturated atmosphere expected to result in 

maximum blood concentrations of EGBE’s toxic metabolite (BAA) well below the level needed 

to produce hemolysis in humans (Udden 2002, EPA 2010).

• Readily biodegradable

• Half-life = 1-4 weeks in water and soil (ATSDR 1998)

• Bioconcentration factor = 3

• Octanol-water partition coefficient (Log Kow) = 0.8 (HSDB 1997)

No Data [Section 3.3, below]

Acute Aquatic Toxicity

(Section 3.3, below)

Chronic Aquatic Toxicity

(Section 3.3, below)
HAPs Petition This Petition

(1993 TRI Release Data) (2009-2011 TRI Release Data)

Human Inhalation Exposures

Chronic

Maximum Annual Average 

Concentration (MAAC)

 0.327 mg/m3

, based on Tier 3 

(ISCST3) air dispersion modeling for 

the maximum impact facility. 

All facilities screened out prior to chronic Tier 2 and 3 

analyses. For subset of facilities that screened out in Tier 

2, Tier 3 modeling was conducted to test the conservatism 

of this assessment found a predicted MAAC using Tier 3 

(AERMOD) of 0.27 mg/m3

 based on 2009, 2010, and 2011 

data. 

RfC 13 mg/m3 1.6 mg/m3

Hazard Quotient (chronic) 0.02 ≤ 0.2

 Acute

Maximum Hourly Average 

Concentration (MHAC)

n/a For a subset of the highest emitting facilities, tiered 

modeling of acute exposures found a predicted MHAC 

using Tier 3 (AERMOD) of 3.9 mg/m3 based on the 2009, 

2010, and 2011 data. 

NOAEL (Irritation Based on 

Human Data)

n/a 97 mg/m3

Margin of Exposure n/a > 25

Human Dermal and Ingestion Exposures

Maximum Exposure 0.02 mg/kg BW-day 0.00001 mg/kg BW-day

RfD 3 mg/kg BW-day 0.1 mg/kg BW-day

Hazard Quotient 0.007 0.0001

Ecological Risk

Small Mammals (from Cadmus 2000a)

Maximum Exposure 2.15 mg/kg BW-day 0.029 mg/kg BW-day

Toxicity Reference Value 20 mg/kg BW-day 20 mg/kg BW-day

Hazard Quotient 0.11 0.001

Aquatic Organisms (from Cadmus 2000a)

Maximum Exposure 3.64 mg/L 0.00019 mg/L

TRV 9.1 mg/L 8.7 mg/L

Hazard Quotient 0.4 0.00002

MAAC: maximum annual average concentration

mg/kg BW-day: milligrams per kilogram body weight per day

mg/L: milligrams per liter

mg/m3

: milligrams per cubic meter

RfC: IRIS reference concentration

RfD: IRIS reference dose

TRV: toxicity reference value

Table ES-2. Key Findings of the Exposure and Risk Assessments
Section Source of Uncertainty Likely Effect on Outcome

3.0 Hazard Assessment

Humans are at least 100 times less sensitive than rats to hemolytic 

effects of EGBE. While a stand default interspecies UFs of 10 was not 

used - RfD uses UF of 1 and RfC uses UF of 3 – the actual 

interspecies factor is approximately 0.01.

RfD may be 100-fold overly conservative. RfC may be 300-fold overly 

conservative. Thus, HQs may be overestimated by a factor of 100 to 300.

Intraspecies UF of 10 is probably overly conservative. A number of 

studies have found no evidence of increased susceptibility to hemolysis 

among sensitive subpopulations.

RfD and RfC may be overstated by an additional factor of 3 to 10. 

IARC (2006) concluded that the carcinogenicity of EGBE to humans 

cannot be determined and EPA (2010) concluded that carcinogenic 

effects from EGBE are not likely to occur in humans in the absence of 

critical noncancer effects.

 EPA (2005) concluded that the RfD and RfC are adequately protective of 

carcinogenic effects in humans, if any. Thus, question of carcinogenicity 

does not affect petition outcome.

5.0 Emissions Inventory

TRI only lists releases of Certain Glycol Ethers. In the absence of 

specific data for EGBE releases, assumed all Certain Glycol Ethers 

releases were EGBE.

Because EGBE represents 52% of market share of ethylene glycol ethers 

(SRI 2010), actual releases of EGBE may be overestimated 2-fold, on 

average.

TRI data are self-reported using a variety of methods. Individual facility 

data vary considerably in certainty.

Actual releases of Certain Glycol Ethers by facilities may be greater than or 

less than those reported on TRI. No evidence of systematic underreporting.

6.0 Screening of Airborne Concentrations

a. Chronic

Step A assumed 100% of reported releases to air were exhausted 

through a single point 0 m high and 50 m from fence line. Resultant 

threshold rate (4.9 tpy) more conservative than that associated with 2 

m high emission point located 10 m from fenceline (8.6 tpy), which 

encompasses virtually all facilities in inventory for which stack 

configuration data are available. 

Maximum annual average concentrations predicted under Step A were up 

to 250-fold higher than those predicted using Tier 3 dispersion modeling. 

Thus, HQs predicted using Step A overestimated by 85-250 times.

Tier 2 employed site-specific data on emission rates, stack and fugitive 

source physical parameters, and property boundaries. The maximum 

MAAC under Tier 2 was 1.2 mg/m3

, as compared to maximum MAAC 

under Tier 3 of 0.3 mg/m3

. Tier 2 results differed from Tier 3 results for 

the same facilities by factors of 1.2 to 6.7. 

HQs predicted using Tier 2 overestimated by 2 times or more.

Modeled maximum annual average concentration is highly 

conservative estimate of exposure over a lifetime. 

Per EPA, actual maximum annual average concentrations are 2-fold lower 

than modeled values. Comparison of an annual average concentration to 

an RfC designed to be protective over a lifetime substantially overstates risk 

by an unknown margin.

DEGREE OF CONSERVATISM ASSOCIATED WITH CHRONIC 

HUMAN INHALATION HAZARDS

(50 to 100) x (3 to 10) x 2 x (2 to 85) x ? = 600 to 170,000 or more

b. Acute

The acute MOE based on the NOAEL of 97 mg/m3 and the estimated 

reasonable worst-case estimated MHAC is approximately 18 mg/m3

. 

Because the NOAEL is derived from human data, per EPA TRI 

precedents MOEs >10 “indicate a low level of concern” for acute 

effects associated with EGBE facility releases.

An MOE above 5 is protective because EPA AEGL guidance calls for an 

interspecies uncertainty factor from 3-10 for non-systemic irritation effects, 

and an appropriate time-adjustment would support a 1-hr NOAEL of 137 

mg/m3

.

Table ES-3. Sources of Uncertainty and Conservatism

Page 1 of 2
Section Source of Uncertainty Likely Effect on Outcome

Table ES-3. Sources of Uncertainty and Conservatism

7.0 Surface Water Exposures and Risks

Exposure point concentrations in surface water calculated by assuming 

that 100% of U.S. releases of Certain Glycol Ethers to all media are 

EGBE and are concentrated into an area the size of the state of Ohio.

Because EGBE represents 52% of consumption of ethylene glycol ethers 

(SRI 2010), actual releases of EGBE may be overestimated 2-fold, on 

average. Because 100,000 km2

 represents 1.3% of total land area of U.S., 

actual concentrations of EGBE may be overestimated 77-fold.

Exposure assumptions (350 day/yr, 70 years, all water contacted 

contains EGBE)

Actual exposure intensity likely to be considerably lower, but degree of 

conservatism cannot be quantified.

DEGREE OF CONSERVATISM ASSOCIATED WITH HUMAN 

DERMAL AND INGESTION HAZARDS

(50 to 100) x (3 to 10) x 2 x 77 x ? = 23,100 to 154,000 or more

8.0 Ecological Risk Assessment

Exposure point concentrations in surface water calculated by assuming 

that 100% of U.S. releases of Certain Glycol Ethers to all media are 

EGBE and are concentrated into an area the size of the state of Ohio.

As previously noted, actual releases of EGBE may be overestimated 2-fold, 

on average, and actual concentrations of EGBE may be overestimated 77-

fold.

Conservative exposure assumptions for small mammals (inhalation 

rate, ingestion rate, bioaccumulation factor) consistent with Cadmus 

(2000a)

Actual exposure intensity likely to be considerably lower, but degree of 

conservatism cannot be quantified.

TRV for aquatic organisms based on most sensitive species tested, 

which may not be representative of aquatic community present in most 

U.S. water bodies.

Although actual sensitivity of other aquatic organisms to EGBE may be 

considerably lower, degree of conservatism cannot be quantified.

TRV for small mammals is based on same underlying data used to 

derive RfD. Thus, small mammal TRV shares same uncertainties as 

listed above with respect to Section 3.0.

TRV may be 50 to 1,000-fold overly conservative due to UFs. 

HQs focused on what EPA calls “very minor” effects on individual 

organisms, rather than effects that are likely to be ecologically 

significant. 

Although individual organisms are likely to be substantially more sensitive 

than populations, communities, or ecosystems, degree of conservatism 

cannot be quantified.

DEGREE OF CONSERVATISM ASSOCIATED WITH RISKS TO 

AQUATIC ORGANISMS

2 x 77 x ? = 154 or more

DEGREE OF CONSERVATISM ASSOCIATED WITH RISKS TO 

SMALL MAMMALS

2 x 77 x (50 to 1,000) x ? = 7,700 to 154,000 or more

EGBE: ethylene glycol monobutyl ether

EPA: U.S. Environmental Protection Agency

FR: Federal Register

HQ: hazard quotient

IARC: International Agency for Research on Cancer

IRIS: Integrated Risk Information Service

km2

: square kilometer

m: meter

MAAC: Maximum annual average concentration

mg/m3

: milligrams per cubic meter

RfC: reference concentration

RfD: reference dose

tpy: tons per year

TRI: Toxics Release Inventory

TRV: toxicity reference value

UF: uncertainty factor

Page 2 of 2
Media Agency Description Information References a

Air EPA 

OAQPS List of Chemicals Produced by Affected Facilities Yes 40 CFR 60.489, EPA 1977

EPA 

OAQPS

Chemicals Affected by Standards of Performance for 

Volatile Organic Emissions from Synthetic Organic 

Chemical Manufacturing Industry Distillation 

Operations

Yes 40 CFR 60.667, EPA 1990b

EPA 

OAQPS

Chemicals Affected by Standards of Performance for 

Volatile Organic Compound Emissions from 

Synthetic Organic Chemical Manufacturing Industry 

Reactor Processes

Yes 40 CFR 60.707, EPA 1993b

EPA 

OAQPS

Synthetic Organic Chemical Manufacturing Industry 

Chemicals Yes 40 CFR 63 Table 1 to Subpart F, EPA 1992b

OSHA Permissible Exposure Limit (TWA)b 50 ppm (240 

mg/m3

) skin c 29 CFR 1910.100, OSHA 1974

Water EPA OW

Effluent Guidelines and Standards - Organic 

Chemicals, Plastics, and Synthetic Fibers - Bulk 

Organic Chemicals

Yes 40 CFR 414, subpart G, EPA 

1987b

Other EPA 

OPPTS Tolerance Range for Agriculture Products

Conditionally 

Exempted from 

Tolerance

40 CFR 180.920, EPA 1971

EPA 

OPPTS

Substance Subject to All Provisions of Health and 

Safety Data Reporting Yes 40 CFR 716.120, EPA 1986b

20 ppm

(97 mg/m3)

50 ppm

(240 mg/m3

) skin b

NIOSH Immediately Dangerous to Life or Health (IDLH) 700 ppm (3,383 

mg/m3

) NIOSH 2001

NIOSH Recommended Exposure Limit for Occupational 

Exposure (TWA)e

5 ppm (24 mg/m3) 

skin b NIOSH 1990

Air AZ AZ Ambient Air Quality Guidelines (24 hours) 0.9 mg/m3

AZ AZ Ambient Air Quality Guidelines (1 hour) 3.6 mg/m3

CA Inhalation Reference Level (1 hour) 14 mg/m3 CalEPA 1999

CT Hazard Limit Value (8 hours) 2.4 mg/m3

Hazard Limit Value (30 minutes) 12 mg/m3

NATIONAL

STATE

Regulations and Guidelines:

http://www.azdeq.gov/environ/air/d

ownload/modeling.pdf

Reg. of CT State Agencies, 

Section 22a-174-29

OSHA Permissible Exposure Limit - TWA for Occupational 

Exposure d 29 CFR 1910.1000

Table 2-1. Regulatory Standards and Guidelines Applicable to EGBE

Regulations:

Guidelines:

Air ACGIH TLV-TWA for Occupational Exposure d ACGIH 2012

Page 1 of 2
Media Agency Description Information References a

NATIONAL

Table 2-1. Regulatory Standards and Guidelines Applicable to EGBE

Air ND Guideline Concentration (8 hours) 1.9 mg/m3

http://www.ndhealth.gov/AQ/Toxic

s/North%20Dakota%20Air%20Tox

ics%20Policy.pdf

TX Effects Screening Level (1 hour) 0.21 mg/m3

TX Effects Screening Level (Annual) 3.7 mg/m3

a. As cited in ATSDR 1998

d. ACGIH TLV-TWA is a time-weighted averaged concentration for an 8-hour workday and a 40-hour workweek.

ACGIH: American Conference of Governmental Industrial Hygienists

EGBE: ethylene glycol monobutyl ether

EPA: U.S. Environmental Protection Agency

mg/m3

: milligrams per cubic meter

NIOSH: Naitonal Institute for Occupational Safety and Health

OAQPS: Office of Air Quality Planning and Standards

OPPTS: Office of Pollution Prevention and Toxic Substances

OSHA: Occupational Safety and Health Administration

OW: Office of Water

ppm: parts per million

TLV: Threshold Limit Value

TWA: Time Weighted Average

c. Skin designation that there is a potential for dermal absorption and that skin exposure should be prevented through the use of

gloves, coveralls, goggles, and other appropriate equipment.

e. Recommended exposure limit is a time-weighted average concentration for up to a 10-hour workday during a 40-hour work week.

http://www.tceq.texas.gov/toxicolo

gy/esl/list_main.html#esl_1

b. Time-weighted average concentrations that must not be exceeded during any 8-hour work shift of a 40-hour week

Page 2 of 2
Table 3-1. Physical and Chemical Properties of EGBE 

Property Information Reference a

Molecular weight 118.17 Merck 1989

colorless Marsden and Mann 1963

Physical state liquid Merck 1989

-70 C HSDB 1997

-75 C ASTER 1995

171 C at 760 mm Hg Weast 1975

50 C at 4 mm Hg Weast 1989

0.9019 g/mL Merck 1989

Faint odor Marsden and Mann 1963

Mild ethereal odor ACGIH 1991

Odor threshold

Air 0.10 ppm (v/v) Amoore and Hautala 1983

0.4 ppm (v/v) OSHA 1990

Water No data

Solubility

Water at 25 C Soluble in all proportions Riddick and Bunger 1970, Weast 1975

Organic solvent(s) Miscible with alcohol, ether Weast 1975

Soluble in most organic solvents Merck 1989

Partition coefficients

Log Kow 0.83 HSDB 1997

0.84 ASTER 1995

Log Koc 1.83 (calculated) HSDB 1997, Lyman et al. 1982

1.79 (calculated) ASTER 1995

Bioconcentration factor

Log BCF 0.40 (calculated) HSDB 1997, Lyman et al. 1982

Vapor pressure

At 20 C 0.76 mm Hg HSDB 1997

At 25 C 0.88 mmHg Dow 1993

Henry's law constant 2.08 x 10-8 (calculated) Howard 1993, HSDB 1997

(atm-m3

/mol) 5.44 x 10-6 (calculated) ASTER 1995

1.96 x 10-11 cm3/molecule-second 

at 25 C (estimated)

Atkinson 1987

17 hours (calculated) HSDB 1997

Autoignition temperature 238 C HSDB 1997

244 C Marsden and Mann 1963, OSHA 1990

60°C (closed cup) Merck 1989

62°C (closed cup) HSDB 1997

69°C (open cup) OSHA 1990

74°C (open cup) Marsden and Mann 1963

Explosive limits 1.1% (lower); 10.1% (upper) OSHA 1990

a. All references are as cited in ATSDR 1998

ASTER: Assessment Tools for the Evaluation of Risk

ATSDR: Agency for Toxic Substances and Disease Registry

BCF: bioconcentration factor

C: degrees Celsius

EGBE: ethylene glycol monobutyl ether

HSDB: Hazardous Substance Data Bank

Koc: organic carbon partition coefficient

Kow: octanol-water partition coefficient

OSHA: Occupational Safety and Health Administration

Flashpoint

Flammability HSDB 1997

Atmospheric half-life at 25 C and 5 x 

105

 hydroxyl radicals/m3

Vapor-phase rate constant for reaction 

with photochemically produced hydroxy 

radicals

May be ignited by heat, sparks or 

open flame

Color

Melting point

Boiling point

Density at 20 C

Odor
Table 3-2. Aquatic Ecotoxicity Data for EGBE

Toxicity Review Source

Scientific Name Common Name Effect Endpoint Duration

EGBE 

Concentration 

(mg/L)

WHO 1998; 

2005

Staples et al. 

1998

Devillers et al. 

2002

EC and HC 

2002

INERIS 2005 C

FishFundulus heteroclitus mummichog mortality LC50 96 hr 6.7 x x B

Cyprinodon variegatus sheepshead minnow mortality LC50 96 hr 116 x x MCyprinodon variegatus sheepshead minnow mortality LC50 72 hr 121 x MCyprinodon variegatus sheepshead minnow mortality LC50 48 hr 126 x MCyprinodon variegatus sheepshead minnow mortality LC50 24 hr 149 x x OLepomis macrochirus bluegill mortality LC50 96 hr 127 x x CLepomis macrochirus bluegill mortality LC50 96 hr 1490 x x NLepomis macrochirus bluegill mortality LC50 24 hr 2950 x x x DLepomis macrochirus bluegill mortality LC50 96 hr 2950 x x NLeuciscus idus melanotus golden ide mortality LC00 48 hr 1170 x x JuLeuciscus idus melanotus golden ide mortality LC00 48 hr 1350 x x JuLeuciscus idus melanotus golden ide mortality LC50 48 hr 1395 x x JuLeuciscus idus melanotus golden ide mortality LC100 48 hr 1490 x x JuLeuciscus idus melanotus golden ide mortality LC50 48 hr 1575 x x x JuLeuciscus idus melanotus golden ide mortality LC100 48 hr 1620 x x JuLeuciscus idus melanotus golden ide mortality LC50 48 hr 1880 x x CMenidia beryllina inland silverside mortality LC50 96 hr 1250 x x x x DCarassius auratus goldfish mortality LC50 24 hr 1650 x x VCarassius auratus goldfish mortality LC50 24 hr 1700 x x x x BOncorhynchus mykiss rainbow trout mortality LC50 96 hr 1700 x EOncorhynchus mykiss rainbow trout mortality LC50 96 hr >1000 x x DPimephales promelas fathead minnow mortality LC50 96 hr 2137 x x x DNotropus atherinoides emerald shiner mortality LC50 72 hr >500 x x DPalaemonetes pugio grass shrimp mortality LC50 96 hr 5.4 x x x BCrassostrea virginica oyster mortality LC50 96 hr 89 x x x ECrassostrea virginica oyster mortality LC50 72 hr 114 x MCrassostrea virginica oyster mortality LC50 48 hr 160 x MCrassostrea virginica oyster mortality LC50 24 hr 181 x MPenaeus setiferus white shrimp mortality LC50 96 hr 117 x WPenaeus setiferus white shrimp mortality LC50 96 hr 130 x O

ACUTE EXPOSURES

Invertebrates

Page 1 of 3
Table 3-2. Aquatic Ecotoxicity Data for EGBE

Toxicity Review Source

Scientific Name Common Name Effect Endpoint Duration

EGBE 

Concentration 

(mg/L)

WHO 1998; 

2005

Staples et al. 

1998

Devillers et al. 

2002

EC and HC 

2002

INERIS 2005 C

Penaeus setiferus white shrimp mortality LC50 72 hr 147 x MPenaeus setiferus white shrimp mortality LC50 48 hr 173 x MCrangon crangon brown shrimp mortality LC50 96 hr 550 x x VCrangon crangon brown shrimp mortality LC50 48 hr 600 x x VCrangon crangon brown shrimp mortality LC50 96 hr 698 x BHydra vulgaris coelenterate mortality LC50 72 hr 690 x x BDaphnia magna water flea mortality LC50 48 hr 835 x x x DDaphnia magna water flea mortality LC00 24 hr 1140 x x BDaphnia magna water flea mortality EC00 24 hr 1283 x x BDaphnia magna water flea immobilization EC50 48 hr 1600 x x DDaphnia magna water flea mortality LC50 24 hr 1698 x x x x BDaphnia magna water flea mortality LC50 24 hr 1720 x x x x BDaphnia magna water flea mortality LC100 24 hr 2500 x x BDaphnia magna water flea mortality EC100 24 hr 2500 x x BDaphnia magna water flea mortality LC50 24 hr 5000 x x x CArtemia salina brine shrimp mortality LC50 24 hr 1000 x x PXenopus laevis African clawed frog mortality LOEC 12 d 2000 x DFishBrachydanio rerio zebrafish mortality LOEC 21 d >100 x EPoecilia reticulata guppy mortality LC50 7 day 982 x x x x KInvertebratesBrachionus calyciflorus rotifer reproduction EC10 48 hr 7.2 x x DBrachionus calyciflorus rotifer reproduction EC20 48 hr 14.3 x x DBrachionus calyciflorus rotifer reproduction EC50 48 hr 164 x x DDaphnia magna water flea reproduction NOEC 21 d 100 x x DDaphnia magna water flea reproduction EC10 21 d 134 x EDaphnia magna water flea reproduction EC20 21 d 175 x EDaphnia magna water flea reproduction EC50 21 d 297 x ECeriodaphnia dubia water flea reproduction EC10 7 d 134.9 x x DCrassostrea gigas Japanese oyster development NOEC 24 hr 100 x DCrassostrea gigas Japanese oyster development LOEC 24 hr 1000 x D

CHRONIC/INTERMEDIATE EXPOSURES

Amphibian

Page 2 of 3
Table 3-2. Aquatic Ecotoxicity Data for EGBE

Toxicity Review Source

Scientific Name Common Name Effect Endpoint Duration

EGBE 

Concentration 

(mg/L)

WHO 1998; 

2005

Staples et al. 

1998

Devillers et al. 

2002

EC and HC 

2002

INERIS 2005 C

Microcystis aeruginosa cyanobacterium growth LOEC 8 day 35 x x x x x BEntosiphon sulcatum protozoan growth LOEC 72 hr 91 x x x x BSelenastrum capricornutum green alga growth NOEC 7 day 125 x x x DSelenastrum capricornutum green alga growth LOEC 7 day 250 x x DSelenastrum capricornutum green alga growth EC50 7 day >1000 x x x DUronema parduczi protozoan growth EC05 48 hr 463 x x x x BPseudomonas putida bacterium growth LOEC 16 hr 700 x x x x BScenedesmus quadricaudata green alga growth LOEC 7 day 900 x x x x BChilomonas parmecium protozoan growth EC05 48 hr 911 x x x x BPseudokirchneriella subcapitata algae growth (biomass NOEC 72 hr 88.2 x D

Pseudokirchneriella subcapitata algae growth (rate) NOEC 72 hr 286 x x DPseudokirchneriella subcapitata algae growth EC50 72 hr 944 x D

Pseudokirchneriella subcapitata algae growth EC50 72 hr 1840 x D

Pseudokirchneriella subcapitata algae growth EC50 24 hr 4183 E

A. Ecotoxicity values did not meet data quality requirements for inclusion in other risk assessments (INERIS 2005)EC: Environment CanadaEC00: effect concentration for 0 percent of organisms testedEC05: effect concentration for 5 percent of organisms testedEC10: effect concentration for 10 percent of organisms testedEC100: effect concentration for 100 percent of organisms testedEC20: effect concentration for 20 percent of organisms testedEC50: median effect concentrationEGBE: ethylene glycol monobutyl etherHC: Health CanadaINERIS: National Institute for Industrial Environment and Risks (France)LC00: lethal concentration for 0 percent of organisms testedLC100: lethal concentration for 100 percent of organisms testedLC50: median lethal concentrationLOEC: lowest observed effect concentrationNOEC: no observed effect concentrationWHO: World Health OrganizationAlgae, Bacteria, Protozoans

Page 3 of 3
Table 5-1. Comparison of Glycol Ether TRI-Reported Releases from 1993 through 2011

Information 1993a 2003 2004 2005 2006 2008 2009 2010 

Number of Facilities Reporting GE Emissions to Any Media

2,251 1,913 1,850 1,793 1,740 1,579 1,478 1,510 

Number of Facilities Reporting Non-zero GE Emissions to Any Media

2,036 1,459 1,423 1,372 1,247 1,198 1,109 1,149 

Total GE Releases (All Facilities) (tpy) 24,106 12,463 11,774 10,924 10,148 8,353 7,015 7,434 Maximum GE Release per Facility (tpy) 375 196 347 495 396 393 293 365 95th Percentile Release per Facility (tpy) 57 44 39 35 36 29 31 29 50th Percentile Release per Facility (tpy) 1.9 1.4 1.2 1.0 1.3 0.9 0.7 0.6 Average Release per Facility (tpy) 12 8.5 8.3 8.0 8.1 7.0 6.3 6.5 % Releases to Air (All Facilities) 97% 94% 93% 89% 90% 87% 90% 88% Average % Released to Air (by Facility) 92% 89% 89% 89% 89% 87% 88% 88% 

Total GE Releases to Air (All Facilities) (tpy) 23,448 11,699 10,942 9,699 9,101 7,282 6,285 6,541 Maximum GE Release to Air per Facility (tpy) 375 196 176 187 179 167 172 189 95th Percentile Release to Air per Facility (tpy)

56 41 37 35 35 28 31 28 

50th Percentile Release to Air per Facility (tpy)

1.5 0.86 0.75 0.75 0.88 0.55 0.49 0.43 

Average Release to Air per Facility (tpy) 12 8.0 7.7 7.2 7.4 6.2 5.8 5.8 Source: www.epa.gov/tria. 1993 TRI data are included because they were the basis for the Hazardous Air Pollutants petition (CMA 1997)GE: Certain Glycol Etherstpy: tons per yearTRI: Toxic Release Inventory
Table 6-1. Screening Table Showing Threshold Emissions (tpy) 

for the Reference Concentration of 1.6 mg/m3

Release

Source Height Receptor DistanceType (m) 10 m 30 m 50 m 100 m 200 m 500 mArea (10 m) 0 1.7 5.3 9.8 24.7 69.0 289Area (20 m) 0 3.1 8.7 15.0 33.5 83.8 317Area (30 m) 0 4.6 12.2 20.2 42.8 99.4 349.3Point 0 0.3 2.0 4.9a 16.5 55.0 263

Point 2 8.6 11.3 11.9 22.0 60.6 268

Point 5 16.6 21.4 30.9 58.8 108.1 309

Point 10 57.8 65.6 75.8b 117.6 223 556

Point 20 232 354 354 421 656 1,509Point 35 708 708 1,416 1,441 1,782 3,628Point 50 1,441 1,455 1,441 3,412 3,783 6,324a. Preliminary emission rate used in the Step A screening (Table 6-2)b. Preliminary emission rate used in the Step A screening of the cluster analysism: meter(s)tpy: tons per year WHERE: 

[P/Q]Tier 1 = normalized ambient concentration in Tier 1 (USEPA 1992c) lookup table (μg×m-3/tpy)

 Qthreshold = RfC / [P/Q]Tier 1

Qthreshold = threshold emissions (tpy)

RfC = Reference Concentration (expressed in μg/m3), and
Table 6-2. Number of Facilities with Total TRI-Reported Air Emissions of Certain Glycol Ethers 

Relative to 4.9 tpy (Step A)

Classification No. Facilities (2009) No. Facilities (2010) No. Facilities (2011)

Less than 4.9 tpy 824 850 823

Equal to or Greater than 4.9 tpy 260 273 276

Total 1,084 1,123 1,099

Percent of Total Less than 4.9 tpy 76% 76% 75%

tpy: tons per year

Emissions Data Source: Toxics Release Inventory (TRI)
Table 6-3. Number of Facilities with Total Air Emissions of Certain Glycol Ethers Greater than Site-Specific Screening Valu

2009 2010 

Classification

Number of 

Facilities 

Screened

Number 

Screened Outa

Number 

Retained

Number of 

Facilities 

Screened

Number 

Screened Out

Number 

Retained

Number of 

Facilities 

Screened

Complete Site-Specific Data Received 35 21 14 34 20 14 31 

Partial Site-Specific Data Received 4 4 0 4 3 1 4 

Default Assumptions Used 221 220 1 235 235 0 241 

Total 260 245 15 273 258 15 276 

a. All facilities retained for additional screening following Step A in any of the 3 years were subjected to Step B screening.Note that one facility retained from the 2009 TRI (Aurora Casket) was not subjected to additional Tier 1 screening because it is no longer operational.Emissions Data Source: Toxics Release Inventory (TRI)Note: Site-specific data employed:

1) Minimum stack release height (meters)2) Minimum distance to property fenceline (meters)3) Percent of certain glycol ethers released as ethylene glycol monobutyl ether (EGBE)
Table 6-4. Long-Term (Chronic Exposure) Tier 1 Modeling Results

2009 TRI 2010 TRI 2011 TRI

Maximum 

Annual Tier I 

EGBE Conc. 

(μg/m3

)

Long-Term 

HQ 

(combined)

Maximum 

Annual Tier I 

EGBE Conc. 

(μg/m3)

Long-Term 

HQ 

(combined)

Maximum 

Annual Tier I 

EGBE Conc. 

(μg/m3)

Long-Term 

HQ 

(combined)

Crown Beverage Packaging - Lawrence Point 3654.7 3176.1 3553.4

Volume 589.5 512.3 573.2

RR Donnelley-Harrisonburg Point 104.4 87.5 74.7

Volume 498.5 535.1 623.5

Ball Metal Food Container Corp- Williamsburg Point 2852.4 3056.1 2954.3

Volume 651.8 688.0 675.9

Crown Cork & Seal Co (USA) - Weirton Point 1753.1 1665.4 1598.8

Volume 1526.5 1450.2 1392.2

Rexam Beverage Can Company- Winston-Salem Point 2885.0 3158.4 2214.1

Volume 971.0 1070.7 882.0

Rexam Beverage Can Company- Bishopville Point 2268.3 2275.3 2099.0

Volume 521.7 523.3 482.6

Ball Container LLC - Columbus Point 1049.7 1364.6 1469.6

Volume 718.4 413.1 431.0

Ball Metal Beverage Container Corp- Findlay Point 2743.0 2743.0 2848.5

Volume 884.5 902.5 920.6

Silgan Containers Manufacturing Corp- LaPorte Point 1329.8 1354.2 1298.8

Volume 451.3 463.9 440.1

Crown Beverage Packaging - Lacrosse Point 47.4 46.0 49.8

Volume 823.6 799.2 865.6

Crown Food Packaging - Owatonna Point 1833.0 1919.7 1998.5

Volume 725.5 761.0 789.3

Rexam Beverage Can Company- Chicago Point 1342.4 1395.9 691.5

Volume 515.3 536.8 246.4

Crown Beverage Packaging - Bradley Point 1253.3 1171.5 1185.5

Volume 608.1 568.4 575.2

Rexam Beverage Can Company- Kent Point 2068.4 1953.6 1950.4

Volume 475.7 449.3 448.6

Crown Beverage Packaging - Olympia Point 1177.4 1336.4 1100.4

Volume 579.7 659.1 542.7

Hazard quotient (HQ) equals the sum of the maximum annual average concentration for fugitive/volume source emissions and point source emissions, at or beyond the fe

EGBE: ethylene glycol monobutyl ether

HQ: hazard quotient

RfC: reference concentration

TRI: Toxics Release Inventory

μg/m3

: micrograms per cubic meter

Bold text indicates an HQ greater than 1

2 2 1

1 11

1 1 0.6

1 11

0.5 0.5 0.6

2 22

2 22

1 11

1 11

2 32

2 22

2 22

2 22

0.4 0.4 0.4

Site Name Source 

Type

3 23
Table 6-5. Long-Term (Chronic Exposure) Tier 2 Modeling Results (2009, 2010, and 2011 TRI Data)

Facility Name City State Zip Code

Maximum 

Predicted 

Annual 

Concentration 

(mg/m3)a

Chronic HQ 

(combined 

fugitive and 

point)

Maximum 

Predicted 

Annual 

Concentration 

(mg/m3)a

Chronic HQ 

(combined 

fugitive and 

point)

Crown Beverage Packaging Lawrence MA 01843 1.20 0.7 1.04 0.6 

Ball Metal Beverage Container Corp Williamsburg VA 23185 0.54 0.3 0.58 0.4 

Crown Cork & Seal Co (Usa) Inc Crown Closure Div Weirton WV 26062 0.28 0.2 0.26 0.2 

Rexam Beverage Can Co Re: Winston Salem Plant Winston-Salem NC 27107 0.36 0.2 0.40 0.2 Rexam Beverage Can Co Re: Bishopville Sc Facility Bishopville SC 29010 0.89 0.6 0.89 0.6 

Ball Container Llc - Columbus Can Plant Columbus OH 43213 0.46 0.3 0.56 0.3 

Ball Metal Beverage Container Corp Findlay OH 45840 0.28 0.2 0.28 0.2 

Silgan Containers Manufacturing Corp La Porte IN 46350 0.25 0.2 0.25 0.2 

Crown Food Packaging Owatonna MN 55060 0.30 0.2 0.32 0.2 

Rexam Beverage Can Co Re : Chicago Plant Chicago IL 60609 0.57 0.4 0.59 0.4 Crown Beverage Packaging Bradley IL 60915 0.28 0.2 0.26 0.2 Rexam Beverage Can Co Kent Wa Facility Kent WA 98032 1.08 0.7 1.02 0.6 

Crown Beverage Packaging Olympia WA 98501 0.47 0.3 0.54 0.3 

*: Rexam Chicago facility was screened out from further analysis for the 2011 data following Step B.

HQ: hazard quotient. Maximum Predicted Annual Concentrations/RfCmg/m3: milligrams per cubic meter

RfC: Reference concentration (1.6 mg/m3)

TRI: Toxics Release Inventorya. Concentrations include point and volume/fugitive source emissions. For point sources, the result for the individual stack at the facility with the maximum predicted c

2009 TRI 2010 TRI 
2009 2010 2011 2009 2010 2011

00985 Carolina Puerto Rico 2 2 2 30.2 27.7 24.3

01843 Lawrence Massachusetts 2 2 NA 72.2 62.7 NA

01950 Newburyport Massachusetts NA NA 2 NA NA 0.1

02021 Canton Massachusetts 2 2 2 0.4 0.4 0.4

07001 Avenel New Jersey 2 2 2 1.2 1.3 1.2

07036 Linden New Jersey 2 NA NA 0.0 NA NA

07105 Newark New Jersey NA NA 2 NA NA 0.3

12866 Saratoga Springs New York 2 NA 2 24.2 NA 23.1

16148 Hermitage Pennsylvania NA 2 2 NA 2.3 2.4

16323 Franklin Pennsylvania 2 2 2 11.4 11.9 8.7

17331 Hanover Pennsylvania 2 2 2 37.4 37.7 33.3

17402 York Pennsylvania NA 2 2 NA 1.2 1.1

17601 Lancaster Pennsylvania 2 2 2 12.8 11.5 17.0

17603 Lancaster Pennsylvania 2 NA NA 1.7 NA NA

19067 Morrisville Pennsylvania 2 NA 2 0.4 NA 1.3

19605 Reading Pennsylvania 2 2 2 0.3 0.3 0.3

19904 Dover Delaware 2 2 2 6.5 4.0 2.6

26062 Weirton West Virginia 5 5 5 149.5 132.2 110.1

27261 High Point North Carolina 3 2 NA 0.8 0.3 NA

27320 Reidsville North Carolina 2 2 2 77.1 94.6 102.1

27409 Greensboro North Carolina 2 2 2 0.1 0.2 0.1

27703 Durham North Carolina 2 2 2 5.6 6.6 0.2

28273 Charlotte North Carolina 4 3 5 2.3 2.7 3.0

29605 Greenville South Carolina NA NA 2 NA NA 0.4

29644 Fountain Inn South Carolina 2 2 2 0.2 0.1 0.1

29730 Rock Hill South Carolina 2 2 2 0.3 0.1 0.2

30043 Lawrenceville Georgia 2 2 2 0.9 2.3 2.7

30062 Marietta Georgia 2 2 2 0.4 0.4 0.5

30253 Mc Donough Georgia 2 3 4 8.8 20.5 20.5

30260 Morrow Georgia 2 2 2 0.4 0.4 0.4

32254 Jacksonville Florida NA 2 2 NA 35.0 25.6

32837 Orlando Florida NA 2 2 NA 2.0 1.6

33760 Clearwater Florida 2 2 NA 0.5 0.4 NA

35064 Fairfield Alabama 2 2 2 3.7 3.6 2.7

35234 Birmingham Alabama 2 2 NA 11.6 10.3 NA

35401 Tuscaloosa Alabama 3 3 NA 0.8 0.9 NA

37355 Manchester Tennessee NA 2 2 NA 20.6 34.6

38024 Dyersburg Tennessee 2 2 NA 6.4 1.5 NA

38109 Memphis Tennessee NA 3 2 NA 0.1 0.0

38113 Memphis Tennessee 3 3 2 7.1 3.4 1.8

38118 Memphis Tennessee 2 NA NA 0.0 NA NA

38606 Batesville Mississippi 2 2 2 29.5 25.7 26.0

38654 Olive Branch Mississippi 3 NA NA 92.2 NA NA

39272 Jackson Mississippi 2 2 2 18.7 15.0 15.4

40210 Louisville Kentucky 2 2 4 1.7 1.9 4.1

42101 Bowling Green Kentucky 2 2 2 1.0 1.1 1.2

43015 Delaware Ohio 2 2 2 0.1 0.1 0.1

43207 Columbus Ohio 2 2 2 0.1 0.1 0.1

43537 Maumee Ohio 2 2 2 0.8 1.0 1.0

43607 Toledo Ohio 2 2 2 11.3 17.2 16.8

43612 Toledo Ohio 3 3 3 12.5 15.4 29.3

Table 6-6. ZIP Codes with More than One Facility Reporting Air Emissions of Certain Glycol Ethers to the TRI in 2009 

through 2011

Number of Facilities Total Reported Emissions 

ZIP City State (tpy)

Page 1 of 4
2009 2010 2011 2009 2010 2011

Table 6-6. ZIP Codes with More than One Facility Reporting Air Emissions of Certain Glycol Ethers to the TRI in 2009 

through 2011

Number of Facilities Total Reported Emissions 

ZIP City State (tpy)

43615 Toledo Ohio 2 2 2 1.1 1.0 1.2

44062 Middlefield Ohio NA 2 NA NA 0.2 NA

44077 Painesville Ohio 2 2 2 0.3 0.8 1.1

44087 Twinsburg Ohio 2 2 2 0.3 0.3 0.3

44109 Cleveland Ohio 2 2 2 0.1 0.1 0.3

44483 Warren Ohio 2 2 2 21.7 19.4 22.3

45036 Lebanon Ohio NA 2 NA NA 3.8 NA

45365 Sidney Ohio 2 2 2 15.8 17.7 24.0

45840 Findlay Ohio 2 2 2 177.3 177.4 182.0

46135 Greencastle Indiana 2 NA 2 3.2 NA 6.9

46225 Indianapolis Indiana 2 2 NA 0.0 0.1 NA

46320 Hammond Indiana 2 2 2 6.0 6.3 5.9

46350 La Porte Indiana 2 2 2 72.0 76.1 72.4

46540 Middlebury Indiana NA 2 2 NA 4.0 6.1

46705 Ashley Indiana NA 2 NA NA 10.1 NA

46721 Butler Indiana 2 2 NA 31.0 29.8 NA

47331 Connersville Indiana 2 2 2 0.1 0.1 0.1

47905 Lafayette Indiana 3 3 3 23.3 37.7 32.3

47933 Crawfordsville Indiana 2 2 2 23.7 26.1 28.2

48091 Warren Michigan 3 3 3 7.0 6.2 9.4

48121 Dearborn Michigan 3 3 3 88.8 66.5 66.2

48174 Romulus Michigan NA 2 2 NA 0.2 0.2

48184 Wayne Michigan 2 3 2 8.6 11.6 6.2

48192 Wyandotte Michigan 2 2 2 2.4 3.1 3.1

48211 Detroit Michigan 2 2 2 4.1 3.6 2.8

48220 Ferndale Michigan 2 2 2 0.0 0.0 0.1

48312 Sterling Heights Michigan 2 2 2 2.2 1.7 5.0

48341 Pontiac Michigan 2 NA NA 3.5 NA NA

48359 Lake Orion Michigan NA NA 2 NA NA 4.0

53014 Chilton Wisconsin NA NA 2 NA NA 11.5

53027 Hartford Wisconsin 2 2 2 23.2 21.7 20.6

53051 Menomonee Falls Wisconsin 3 4 4 5.8 5.5 6.1

53066 Oconomowoc Wisconsin NA NA 2 NA NA 7.1

53095 West Bend Wisconsin 2 2 2 0.3 0.3 0.2

53154 Oak Creek Wisconsin 2 3 3 15.9 46.0 54.2

53177 Sturtevant Wisconsin 2 2 3 0.5 0.5 0.8

53223 Milwaukee Wisconsin 2 2 NA 0.4 0.3 NA

53224 Milwaukee Wisconsin 3 3 3 51.7 47.4 44.4

53913 Baraboo Wisconsin NA NA 2 NA NA 30.1

54143 Marinette Wisconsin 2 NA NA 3.2 NA NA

54220 Manitowoc Wisconsin NA NA 2 NA NA 2.6

60007 Elk Grove Village Illinois 6 6 6 8.4 12.3 9.9

60090 Wheeling Illinois 2 2 2 0.2 0.2 0.2

60174 Saint Charles Illinois 2 2 2 2.4 1.4 1.3

60178 Sycamore Illinois NA 2 2 NA 10.6 7.4

60410 Channahon Illinois 2 NA NA 0.0 NA NA

60411 Chicago Heights Illinois 2 2 2 31.5 37.6 36.2

60426 Harvey Illinois 2 2 2 16.2 25.9 7.2

60439 Lemont Illinois 2 2 2 0.1 0.1 0.1

60455 Bridgeview Illinois 2 2 2 8.4 9.5 8.5

60501 Bedford Park Illinois 2 NA NA 0.5 NA NA

Page 2 of 4
2009 2010 2011 2009 2010 2011

Table 6-6. ZIP Codes with More than One Facility Reporting Air Emissions of Certain Glycol Ethers to the TRI in 2009 

through 2011

Number of Facilities Total Reported Emissions 

ZIP City State (tpy)

60510 Batavia Illinois 3 3 3 0.8 1.1 2.2

60517 Woodridge Illinois 2 NA NA 0.0 NA NA

60608 Chicago Illinois 2 2 2 9.9 14.4 3.4

60609 Chicago Illinois 2 2 2 91.1 111.1 67.1

60623 Chicago Illinois 3 3 3 24.7 48.0 46.1

60632 Chicago Illinois NA 2 2 NA 6.6 8.9

60633 Chicago Illinois 2 2 2 1.1 1.6 1.2

60803 Alsip Illinois NA NA 2 NA NA 19.0

61104 Rockford Illinois 2 NA NA 1.2 NA NA

61265 Moline Illinois 2 2 2 1.7 1.6 1.6

62040 Granite City Illinois NA 2 2 NA 6.0 5.8

62201 Sauget Illinois NA 2 2 NA 0.0 0.0

63043 Maryland Heights Missouri 2 NA NA 2.1 NA NA

63077 Saint Clair Missouri 2 2 2 0.3 0.7 0.1

63111 Saint Louis Missouri 2 2 NA 0.2 0.2 NA

63147 Saint Louis Missouri 2 2 2 0.3 0.3 0.3

64116 North Kansas City Missouri 3 3 3 4.8 2.9 2.9

65708 Monett Missouri NA 2 NA NA 11.2 NA

65712 Mount Vernon Missouri 2 2 NA 12.8 11.7 NA

66106 Kansas City Kansas 2 2 2 0.2 0.2 0.2

67219 Wichita Kansas NA 2 2 NA 6.1 5.9

68701 Norfolk Nebraska 2 2 2 11.5 10.4 10.4

70560 New Iberia Louisiana NA 2 2 NA 1.6 1.9

70765 Plaquemine Louisiana 2 2 NA 0.6 1.9 NA

70776 Saint Gabriel Louisiana 2 NA NA 0.5 NA NA

70805 Baton Rouge Louisiana 2 2 2 0.4 0.8 0.1

72315 Blytheville Arizona NA NA 2 NA NA 12.0

72764 Springdale Arizona NA NA 2 NA NA 12.1

72764 Springdale Arkansas 2 2 NA 12.9 10.0 NA

73036 El Reno Oklahoma NA 2 2 NA 7.8 7.7

74063 Sand Springs Oklahoma NA 2 2 NA 0.2 0.1

74075 Stillwater Oklahoma 2 2 2 4.9 2.3 3.5

74601 Ponca City Oklahoma 2 2 NA 24.0 20.6 NA

75006 Carrollton Texas 2 3 3 3.2 2.3 2.3

75041 Garland Texas 3 3 4 0.2 0.2 0.2

75149 Mesquite Texas NA NA 2 NA NA 2.0

75165 Waxahachie Texas 4 2 NA 0.7 0.1 NA

75501 Texarkana Texas 2 NA NA 0.6 NA NA

75604 Longview Texas NA NA 2 NA NA 52.5

75662 Kilgore Texas NA 2 2 NA 0.1 0.1

75901 Lufkin Texas 2 2 2 2.2 2.3 1.8

76011 Arlington Texas 2 2 2 4.7 1.5 3.4

76063 Mansfield Texas NA NA 2 NA NA 0.6

77041 Houston Texas 2 2 2 1.8 1.3 1.4

77051 Houston Texas 2 2 2 1.1 1.0 0.8

77303 Conroe Texas 2 2 3 18.9 18.8 49.7

77478 Sugar Land Texas NA NA 2 NA NA 31.5

77507 Pasadena Texas 5 5 5 8.8 10.5 8.3

77571 La Porte Texas 2 2 NA 4.8 2.1 NA

77630 Orange Texas NA 2 2 NA 0.3 0.3

77651 Port Neches Texas NA 2 2 NA 0.3 0.2

Page 3 of 4
2009 2010 2011 2009 2010 2011

Table 6-6. ZIP Codes with More than One Facility Reporting Air Emissions of Certain Glycol Ethers to the TRI in 2009 

through 2011

Number of Facilities Total Reported Emissions 

ZIP City State (tpy)

80216 Denver Colorado 2 2 NA 0.0 0.0 NA

80550 Windsor Colorado 2 2 2 57.5 55.0 54.3

85043 Phoenix Arizona 2 NA NA 39.8 NA NA

90670 Santa Fe Springs California 5 5 5 0.8 0.8 0.7

90810 Carson California 2 2 2 0.3 0.4 0.4

91311 Chatsworth California 3 3 3 54.6 44.4 29.0

91730 Rancho Cucamonga California 2 3 3 0.4 1.4 1.3

92335 Fontana California 2 2 2 2.0 1.0 0.4

92704 Santa Ana California 2 NA NA 0.0 NA NA

93308 Bakersfield California NA 2 NA NA 0.0 NA

94533 Fairfield California 4 4 4 45.7 29.0 30.8

95824 Sacramento California NA NA 2 NA NA 5.2

97203 Portland Oregon 2 2 2 3.5 4.1 3.2

97210 Portland Oregon NA 2 NA NA 0.1 NA

98108 Seattle Washington 2 2 2 3.0 0.2 0.2

tpy: tons per year

NA: no releases reported

TRI: toxics release inventory

Page 4 of 4
Table 6-7. ZIP Codes and Facilities Identified for Dispersion Modeling Following Step B Screening 

Total Air (tpy)

Facility City State ZIP 2009 TRI 2010 TRI 2011 TRI

Edsal Manufacturing Co Inc Chicago IL 60609 26 43 34

Rexam Beverage Can Co Re : Chicago 

Plant Chicago IL 60609 65 68 33

Cumulative Zip Code Emissions 91 111 67

Whirlpool Corp Findlay Div Findlay OH 45840 23 22 22

Ball Metal Beverage Container Corp Findlay OH 45840 155 155 161

Cumulative Zip Code Emissions 177 177 182

Precoat Metals La Porte IN 46350 5 8 7

Silgan Containers Manufacturing Corp La Porte IN 46350 67 68 65

Cumulative Zip Code Emissions 72 76 72

Ardagh Metal Packaging USA Inc Weirton WV 26062 2 2 0.4

Ball Metal Food Container Corp Weirton WV 26062 37 23 13

Crown Cork & Seal Co (USA) Inc. Crown 

Closure Div. Weirton WV 26062 101 96 92

Precoat Metals Weirton WV 26062 6 7 3

Nestle Purina Petcarea Weirton WV 26062 4 4 2

Cumulative Zip Code Emissions 149 132 109

Ball Metal Beverage Container Corp Reidsville NC 27320 77 95 102

Dystar LP Reidsville NC 27320 0.05 0.05 0.05

Cumulative Zip Code Emissionsb 77 95 102

a. Nestle Purina Petcare facility in Weirton, WV closed in September 2011 and has not reopened.

RfC: reference concentration (1.6 mg/m3

)

tpy: tons per year

TRI: Toxic Release Inventory

b. Zip code included because although 1 facility accounted for more than 90% of emissions, the conservative

screening level was within 10% of the RfC.

Note: TRI Data are based on reported emissions of Certain Glycol Ethers, assuming that those are 100% 

ethylene glycol monobutyl ether.

Gray shading indicates zip codes that screened out from further analysis based on this screening. Cumulative 
Table 6-8. Results of Chronic Tier 2 & 3 Modeling for Facility Clusters

T2 AERMOD Modeling Result 

(Screening Met Data)

T3 AERMOD Modeling (SiteSpecific Met Data)

Zip Codes 

Chronic 

Exposure 

(mg/m3

) Chronic MOEa

Chronic 

Exposure 

(mg/m3

) Chronic MOEa

2009

Chicago, IL 60609 0.91 Out 0.11 15

Findlay, OH 45840 0.45 Out -- --

La Porte, IN 46350 0.26 Out -- --

Weirton, WV 26062 0.41 Out 0.16 10

Reidsville, NC 27320 0.57 Out -- --

2010

Chicago, IL 60609 1.16 Out 0.18 9

Findlay, OH 45840 0.45 Out -- --

La Porte, IN 46350 0.27 Out -- --

Weirton, WV 26062 0.32 Out 0.16 10

Reidsville, NC 27320 0.70 Out -- --

2011

Chicago, IL 60609 0.74 Out 0.14 11

Findlay, OH 45840 0.45 Out -- --

La Porte, IN 46350 0.26 Out -- --

Weirton, WV 26062 0.26 Out 0.15 10

Reidsville, NC 27320 0.74 Out -- --

Basis: 2009, 2010, and 2011 TRI data

--: Zip code not subjected to sensitivity analysis using Tier 3 modeling.

mg/m3

: milligrams per cubic meter

MOE: margin of exposure

a. Chronic exposure results are compared to the Reference Concentration (RfC) of 1.6 mg/m3

. "Out" indicates

the facility was screened out (concentration does not exceed the RfC) and "Retain" indicates the facility was 

not screened out.

b. The chronic MOE is determined by dividing the RfC by the estimated exposure concentration. It represents

the factor by which the estimated exposure would have to increase to equal the RfC.
Table 6-9. Uncertainty Analysis

Long-Term (Chronic Exposure) Tier 3 Modeling for Selected Facilities (2009, 2010, and 2011 TRI Data)

Facility Name City State Zip Code

AERMOD 

Maximum 

Predicted 

Annual 

Average 

Concentration 

(μg/m3)

Chronic HQ 

(combined 

fugitive and 

point)

AERMOD 

Maximum 

Predicted Annual 

Average 

Concentration 

(μg/m3)

Chronic HQ 

(combined 

fugitive and 

point)

A

M

Predi

A

Con

Crown Beverage Packaging Lawrence MA 01843 261.9 0.2 228.7 0.1 Rexam Beverage Can Company Kent WA 98032 269.4 0.2 253.4 0.2 Rexam Beverage Can Company Bishopville SC 29010 153.1 0.1 149.4 0.09 

Crown Cork & Seal Co (USA) Weirton WV 26062 158.1 0.1 158.1 0.10 

Rexam Beverage Can Company Winston Salem NC 27107 157.4 0.1 172.8 0.11 

Rexam Beverage Can Company Chicago IL 60609 85.3 0.05 87.7 0.05 HQ: hazard quotient. Maximum Predicted Annual Concentrations/RfCμg/m3: micrograms per cubic meter

RfC: Reference concentration (1,600 μg/m3)

TRI: Toxics Release InventoryModeling results based on 2009, 2010 and 2011 TRI data

2009 TRI 2010 TRI 
Table 6-10. Comparison of Concentrations Using the Tiered Modeling Approach

Facility Name

Step A 

Impacta

Step B 

Impactb

Tier 1 

Impact

Tier 2 

Impact 

Tier 3 

Impact 

Step A to 

Step B

Step B to 

Tier 1

Tier 1 to 

Tier 2

Tier 2 to 

Tier 3

Step A to Tier 

3

Crown Beverage Packaging - 

Lawrence

22.8 4.19 4.13 1.16 0.26 -82% -2% -72% -78.0% -98.9%

RR Donnelley-Harrisonburg 15.7 1.90 0.70 0.08 - -88% -63% -89% -- --

Ball Metal Food Container CorpWilliamsburg56.2 3.93 3.63 0.56 - -93% -8% -84% -- --

Crown Cork & Seal Co (USA) - 

Weirton

30.0 6.01 2.99 0.25 0.15 -80% -50% -92% -40.1% -99.5%

Rexam Beverage Can CompanyWinston-Salem44.3 3.10 3.10 0.29 0.13 -93% 0% -91% -55.7% -99.7%

Rexam Beverage Can CompanyBishopville29.0 3.81 2.58 0.83 0.14 -87% -32% -68% -83.3% -99.5%

Ball Container LLC - Columbus 26.7 2.18 1.90 0.60 - -92% -13% -68% -- --

Ball Metal Beverage Container CorpFindlay

52.2 3.77 3.77 0.29 - -93% 0% -92% -- --

Silgan Containers Manufacturing 

Corp- LaPorte

21.3 1.79 1.74 0.24 - -92% -3% -86% -- --

Crown Beverage Packaging - 

Lacrosse

8.4 3.11 0.92 0.14 - -63% -71% -85% -- --

Crown Food Packaging - Owatonna 41.5 3.14 2.79 0.33 - -92% -11% -88% -- --

Rexam Beverage Can CompanyChicago10.8 1.47 0.94 0.29 0.043 -86% -36.3% -69% -85.2% -99.6%

Crown Beverage Packaging - 

Bradley

21.1 3.01 1.76 0.27 - -86% -41% -85% -- --

Rexam Beverage Can CompanyKent27.0 3.54 2.40 1.02 0.25 -87% -32% -57% -75.2% -99.1%

Crown Beverage Packaging - 

Olympia

20.8 1.71 1.64 0.44 - -92% -4% -73% -- --

Note: The 2011 TRI data are shown here for illustrative purposes.

m: meter

mg/m3

: milligrams per cubic meter

TRI: Toxics Release Inventory

a. Step A impacts calculated based on Tier 1 lookup table assuming all air emissions are from point sourece, stack height is 0 m, receptor distance is 10 m, and all 

Certain Glycol Ether emissions are EGBE.

2011 Tiered Modeling Results (mg/m3

) Change in Maximum Impact

The percent changes in predicated concentrations are similar using 2009 and 2010 TRI data.
Table 6-11. Total TRI Air Emissions (Fugitive and Point-Source Air) by Year for Selec

Facility and City 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 

Ball Columbus 127.7 125.2 125.1 124.4 105.4 124.2 103.6 76.4 70.9 70.0 Ball Findlay 174.5 170.5 167.0 130.5 118.5 130.0 130.0 154.0 153.5 154.5 Ball Williamsburg 205.0 189.0 178.5 171.0 164.5 144.5 143.5 179.5 167.0 167.0 Crown Bradley 79.5 85.5 85.5 89.5 82.4 98.4 96.0 78.6 68.0 68.6 

Crown Lacrosse 98.0 86.0 89.4 80.0 55.3 18.7 25.5 24.9 23.5 24.5 

Crown Lawrence 89.5 105.5 103.2 91.5 91.5 96.0 91.8 56.4 74.4 72.2 Crown Olympia 65.0 75.5 73.5 61.5 40.0 57.8 39.3 33.9 34.2 68.4 

Crown Weirton 25.0 41.5 31.5 107.0 103.9 75.9 91.1 101.1 106.2 101.1 

Crown Owatonna 75.5 78.0 99.5 77.0 80.5 108.2 80.4 59.0 105.0 117.1 

Rexam Bishopville 95.8 108.8 108.3 104.9 97.6 89.8 102.0 90.0 103.0 96.5 

Rexam Chicago 76.5 73.8 72.0 70.4 76.2 70.3 71.1 68.5 68.4 65.4 

Rexam Kent 81.0 125.2 80.4 53.7 48.4 68.0 89.0 92.3 61.5 88.0 

Rexam Winston Salem 136.6 164.3 169.8 185.1 84.8 123.8 179.0 172.4 147.5 172.2 

Silgan LaPorte 81.2 72.5 56.0 65.0 62.0 58.0 63.5 65.8 61.5 67.0 

RR Donnelly Harrisonburg 11.1 10.0 4.8 7.7 7.7 2.5 NR NR 7.4 40.4 

Note:All emissions are for Certain Glycol Ethers as reported in the TRIBold indicates the year with the maximum reported Certain Glycol Ether emissions in the TRI from 2000-2011.a. Maximum long-term Tier 3 impact from 2009, 2010, and 2011 (Table 6-8)

Max: MaximumNR: not reportedTRI: Toxics Release Inventorytpy: tons per year--: Tier 3 modeling of facility emissions not conducted in this petition.

TRI Total Air Emissions (tpy)
Table 6-12. Short-Term (Acute Exposure) Tier 1 Modeling Results

2009 TRI 2010 TRI 2011 TRI

Site Name Source Type

Maximum 1-

Hour Average 

Tier I EGBE 

Conc. (μg/m3)

Short-Term 

HQ 

(combined)

Maximum 1-

Hour Average 

Tier I EGBE 

Conc. (μg/m3)

Short-Term 

HQ 

(combined)

Maximum 1-

Hour Average 

Tier I EGBE 

Conc. (μg/m3)

Sh

(co

Crown Beverage Packaging - Lawrence Point 1674648.6 1455360.1 1628244.9

Volume 25839.6 22455.8 25123.6

RR Donnelley-Harrisonburg Point 4575.2 3835.5 3274.4

Volume 21848.5 23455.4 27327.9

Ball Metal Food Container Corp- Williamsburg Point 1614548.3 1729873.2 1672210.7

Volume 28567.5 30154.6 29625.6

Crown Cork & Seal Co (USA) - Weirton Point 153263.2 145599.8 139775.7

Volume 66907.0 63561.5 61019.1

Rexam Beverage Can Company- Winston-Salem Point 126797.7 138811.6 97310.1

Volume 42558.5 46926.7 38656.2

Rexam Beverage Can Company- Bishopville Point 781664.4 784081.0 723321.2

Volume 22865.5 22936.6 21153.3

Ball Container LLC - Columbus Point 516703.7 671714.9 723385.2

Volume 31488.0 18105.6 18892.8

Ball Metal Beverage Container Corp- Findlay Point 602446.2 602446.2 625617.2

Volume 38766.6 39557.8 40348.9

Silgan Containers Manufacturing Corp- LaPorte Point 625779.2 637261.3 611214.0

Volume 19778.9 20332.7 19289.9

Crown Beverage Packaging - Lacrosse Point 2071.7 2010.6 2177.7

Volume 36099.6 35030.0 37941.4

Crown Food Packaging - Owatonna Point 373793.1 391475.5 407543.5

Volume 31796.9 33353.0 34594.6

Rexam Beverage Can Company- Chicago Point 487099.1 506509.5 250922.0

Volume 22587.1 23527.5 10798.1

Crown Beverage Packaging - Bradley Point 364345.2 340549.6 344624.2

Volume 26654.8 24914.5 25212.3

Rexam Beverage Can Company- Kent Point 884003.8 834954.6 833594.9

Volume 20850.7 19693.1 19661.5

Crown Beverage Packaging - Olympia Point 185857.0 210964.4 173700.7

Volume 25408.8 28888.5 23785.3

Hazard quotient (HQ) equals the sum of the maximum annual average concentration for fugitive/volume source emissions and point source emissions, at or be

EGBE: ethylene glycol monobutyl etherHQ: hazard quotientRfC: reference concentrationTRI: Toxics Release Inventoryμg/m3: micrograms per cubic meter

9 92 25 54 4

0.4 0.4 

4 47 77 76 72 2 8 8

17 18 

2 2

18 15 

0.3 0.3 
Table 6-13. Results of Acute Tier 2 & 3 Modeling for Facility Clusters

T2 AERMOD Modeling Result 

(Screening Met Data)

T3 AERMOD Modeling (SiteSpecific Met Data)

Zip Code and Facilities

Acute Exposure 

(mg/m3

) Acute MOEa

Acute Exposure 

(mg/m3

) Acute MOEa

2009

Chicago, IL 60609 39.7 Out 14.0 7

Findlay, OH 45840 19.7 Out -- --

La Porte, IN 46350 11.4 Out -- --

Weirton, WV 26062 18.4 Out 8.25 12

Reidsville, NC 27320 24.9 Out -- --

2010

Chicago, IL 60609 50.9 Out 23.5 4

Findlay, OH 45840 19.6 Out -- --

La Porte, IN 46350 12.0 Out -- --

Weirton, WV 26062 16.0 Out 7.84 12

Reidsville, NC 27320 30.6 Out -- --

2011

Chicago, IL 60609 32.4 Out 18.5 5

Findlay, OH 45840 19.7 Out -- --

La Porte, IN 46350 11.4 Out -- --

Weirton, WV 26062 13.5 Out 7.52 13

Reidsville, NC 27320 32.6 Out -- --

Basis: 2009, 2010, and 2011 TRI data

-- : Zip code not subjected to sensitivity analysis using Tier 3 modeling.

mg/m3

: milligrams per cubic meter

MOE: margin of exposure

a. Acute exposure results are compared to the no observed adverse effects level (NOAEL) of 97 mg/m3

. "Out"

indicates the facility was screened out (concentration does not exceed the NOAEL) and "Retain" indicates the 

facility was not screened out.

b. The acute MOE is determined by dividing the NOAEL by the estimated exposure concentration. It

represents the factor by which the estimated exposure would have to increase to equal the NOAEL.
Table 6-14. Results of Short-Term Tier 2 & 3 Modeling and Acute MOE Analysis for Selected High Emitt

Tier 2 Tier 3 Tier 2 

Facility City State Zip

Maximum 1-Hr 

Concentration 

(mg/m3

)

a

Acute 

MOE b

Maximum 1-Hr 

Concentration 

(mg/m3

)

a

Acute 

MOE b

Maximum 1-Hr 

Concentration 

(mg/m3

)

a

Acute 

MOE b

Ma

Co

Ball Container LLC Columbus OH 43213 19.99 4.9 -- -- 24.42 4.0 

Ball Metal Beverage Container Corp Findlay OH 45840 12.10 8.0 -- -- 12.19 8.0 

Ball Metal Food Container Corp

Williamsburg VA 23185 23.80 4.1 -- -- 25.47 3.8 

Crown Beverage Packaging Bradley IL 60915 12.39 7.8 -- -- 11.58 8.4 

Crown Beverage Packaging Olympia WA 98501 20.76 4.7 -- -- 23.56 4.1 

Crown Beverage Packaging Lawrence MA 01843 52.41 1.9 15.24 6.4 45.54 2.1 

Crown Cork & Seal Co (USA) Weirton WV 26062 12.16 8.0 8.24 12 11.55 8.4 

Crown Food Packaging Owatonna MN 55060 13.23 7.3 -- -- 13.86 7.0 

Rexam Beverage Can Company Bishopville SC 29010 39.05 2.5 9.06 11 39.17 2.5 

Rexam Beverage Can Company Chicago IL 60609 24.75 3.9 4.16 23 25.74 3.8 

Rexam Beverage Can Company Kent WA 98032 47.46 2.0 7.66 13 44.83 2.2 

Rexam Beverage Can Company Winston Salem NC 27107 15.36 6.3 16.71 5.8 16.85 5.8 

Silgan Containers Manufacturing Corp LaPorte IN 46350 10.76 9.0 -- -- 10.97 8.8 

Basis: 2009, 2010, and 2011 TRI data--: Facility not subjected to sensitivity analysis using Tier 3 modeling.mg/m3: milligrams per cubic meter 

MOE: margin of exposure

2009 2010 

a. Concentrations are the sum of the predicted maximum 1-hour concentration for (i) fugitive/volume source emissions and (ii) point source

emissions, at or beyond the fence line.b. To calculate the MOE, the no observed adverse effect level (NOAEL) for irritation in humans of 97 mg/m3 is divided by the concentration from

combined fugitive/volume and point source emissions.
Table 7-1. Hazards from Surface Water Exposure to EGBE

Residential Scenario: Ingestion of EGBE in Drinking Water

Hypothetical adolescent and adult (12+ years)

Cw IR EF ED Ao BW AT ADI RfD 

Conc. in Ingestion Exposure Exposure Oral Body Averaging Average Reference 

Chemical Water Rate Frequency Duration Abs. Factor Weight Time Daily Intake Dose 

(mg/L) (L/day) (days/year) (years) (unitless) (kg) (days) (mg/kg-day) (mg/kg-day) 

EGBE 0.00020 2 350 18 1.0 70 6,570 0.00001 0.1 

Hypothetical child (6-12 years)

Cw IR EF ED Ao BW AT ADI RfD 

Conc. in Ingestion Exposure Exposure Oral Body Averaging Average Reference 

Chemical Water Rate Frequency Duration Abs. Factor Weight Time Daily Intake Dose 

(mg/L) (L/day) (days/year) (years) (unitless) (kg) (days) (mg/kg-day) (mg/kg-day) 

EGBE 0.00020 2 350 7 1.0 30 2,555 0.00001 0.1 

Hypothetical young child (1-5 years)

Cw IR EF ED Ao BW AT ADI RfD 

Conc. in Ingestion Exposure Exposure Oral Body Averaging Average Reference 

Chemical Water Rate Frequency Duration Abs. Factor Weight Time Daily Intake Dose 

(mg/L) (L/day) (days/year) (years) (unitless) (kg) (days) (mg/kg-day) (mg/kg-day) 

EGBE 0.00020 1 350 5 1.0 15 1,825 0.00001 0.1 

ADI = Cw x IR x EF x ED x Ao x (1/BW) x (1/AT)HQ = ADI/RfDEGBE: ethylene glycol monobutyl ether
Table 7-2. Hazards from Surface Water Exposure to EGBE

Residential Scenario: Dermal Contact with EGBE While Bathing and Showering

Hypothetical adolescent and adult (12+ years)

DAevent SA EV EF ED BW AT ADI RfD 

Absorbed Skin Surface Event Exposure Exposure Body Averaging Average Reference 

Chemical Dose Area Exposed Frequency Frequency Duration Weight Time Daily Intake Dose 

(mg/cm2-event) (cm2) (events/day) (days/year) (years) (kg) (days) (mg/kg-day) (mg/kg-day) 

EGBE 3.6E-10 23,000 1 350 18 70 6,570 0.0000001 0.1 

Hypothetical child (6-12 years)

DAevent SA EV EF ED BW AT ADI RfD 

Chemical Absorbed Skin Surface Event Exposure Exposure Body Averaging Average Reference 

Dose Area Exposed Frequency Frequency Duration Weight Time Daily Intake Dose 

(mg/cm2-event) (cm2) (events/day) (days/year) (years) (kg) (days) (mg/kg-day) (mg/kg-day) 

EGBE 3.6E-10 12,914 1 350 7 30 2,555 0.0000001 0.1 

Hypothetical young child (1-5 years)

DAevent SA EV EF ED BW AT ADI RfD 

Chemical Absorbed Skin Surface Event Exposure Exposure Body Averaging Average Reference 

Dose Area Exposed Frequency Frequency Duration Weight Time Daily Intake Dose 

(mg/cm2-event) (cm2) (events/day) (days/year) (years) (kg) (days) (mg/kg-day) (mg/kg-day) 

EGBE 3.6E-10 7,446 1 350 5 15 1,825 0.0000002 0.1 

ADI = DAevent x SA x EV x EF x ED x (1/BW) x (1/AT)

HQ = ADI/RfDEGBE: ethylene glycol monobutyl ether
Table 7-3. Hazards from Surface Water Exposure to EGBE

Recreational Scenario: Incidental Ingestion of EGBE in Surface Water While Swimming

Hypothetical adolescent and adult (12+ years)

Cw IR EF ED Ao BW AT ADI RfD 

Conc. in Ingestion Exposure Exposure Oral Body Averaging Average Reference 

Chemical Water Rate Frequency Duration Abs. Factor Weight Time Daily Intake Dose 

(mg/L) (L/day) (days/year) (years) (unitless) (kg) (days) (mg/kg-day) (mg/kg-day) (

EGBE 0.00020 0.13 36 18 1.0 70 6,570 0.00000004 0.1 0

Hypothetical child (6-12 years)

Cw IR EF ED Ao BW AT ADI RfD 

Conc. in Ingestion Exposure Exposure Oral Body Averaging Average Reference 

Chemical Water Rate Frequency Duration Abs. Factor Weight Time Daily Intake Dose 

(mg/L) (L/day) (days/year) (years) (unitless) (kg) (days) (mg/kg-day) (mg/kg-day) (

EGBE 0.00020 0.13 108 7 1.0 30 2,555 0.0000003 0.1 0

Hypothetical young child (1-5 years)

Cw IR EF ED Ao BW AT ADI RfD

Chemical Conc. in Ingestion Exposure Exposure Oral Body Averaging Average Reference

Water Rate Frequency Duration Abs. Factor Weight Time Daily Intake Dose 

(mg/L) (L/day) (days/year) (years) (unitless) (kg) (days) (mg/kg-day) (mg/kg-day) (

EGBE 0.00020 0.13 36 5 1.0 15 1,825 0.0000002 0.1 0

ADI = Cw x IR x EF x ED x Ao x (1/BW) x (1/AT)HQ = ADI/RfDEGBE: ethylene glycol monobutyl ether
Table 7-4. Hazards from Surface Water Exposure to EGBE

Recreational Scenario: Dermal Contact with EGBE in Surface Water While Swimming

Hypothetical adolescent and adult (12+ years)

DAevent SA EV EF ED BW AT ADI RfD 

Absorbed Skin Surface Event Exposure Exposure Body Averaging Average Refere

Chemical Dose Area Exposed Frequency Frequency Duration Weight Time Daily Intake Dose 

(mg/cm2-event) (cm2) (events/day) (days/year) (years) (kg) (days) (mg/kg-day) (mg/kg-

EGBE 3.6E-10 23,000 3 36 18 70 6,570 3.5E-08 0.1 

Hypothetical child (6-12 years)

DAevent SA EV EF ED BW AT ADI RfD 

Absorbed Skin Surface Event Exposure Exposure Body Averaging Average Refere

Chemical Dose Area Exposed Frequency Frequency Duration Weight Time Daily Intake Dose 

(mg/cm2-event) (cm2) (events/day) (days/year) (years) (kg) (days) (mg/kg-day) (mg/kg-

EGBE 3.6E-10 12,914 3 108 7 30 2,555 1.4E-07 0.1 

Hypothetical young child (1-5 years)

DAevent SA EV EF ED BW AT ADI RfD

Chemical Absorbed Skin Surface Event Exposure Exposure Body Averaging Average Refere

Dose Area Exposed Frequency Frequency Duration Weight Time Daily Intake Dose 

(mg/cm2-event) (cm2) (events/day) (days/year) (years) (kg) (days) (mg/kg-day) (mg/kg-

EGBE 3.6E-10 7,446 3 36 5 15 1,825 5.3E-08 0.1 

ADI = DAevent x SA x EV x EF x ED x (1/BW) x (1/AT)

HQ = ADI/RfDEGBE: ethylene glycol monobutyl ether
Table 7-5. Summary of Hazards from Surface Water Exposures to EGBE

Pathway Hazard

Scenario Age Group Ingestion Dermal Contact QuotientResidential

Adolescent and adult (12+ years) 0.00005 0.000001 0.0001Child (6-12 years) 0.0001 0.000001 0.0001Young Child (1-5 years) 0.0001 0.000002 0.000130-year lifetime 0.0003 0.000004 0.0003

Recreational

Adolescent and adult (12+ years) 0.0000004 0.0000003 0.000001Child (6-12 years) 0.000003 0.000001 0.00000Young Child (1-5 years) 0.000002 0.0000005 0.00000230-year lifetime 0.00000 0.000002 0.00001

EGBE: ethylene glycol monobutyl etherNote: Hazard quotients less than 1 indicate that average daily intake is less than the reference dose and that negligible health effects are anticipated.
HAPs Petition This Petition

Maximum Exposed Individual Resident ResidentConcentration of EGBE in Water (mg/L) 0.13 0.00020

Predicted Ingestion Dose (mg/kg BW-day) 0.02 0.00001

Predicted Dermal Dose (mg/kg BW-day) 0.00004 0.0000002

Cumulative Predicted Dose (mg/kg BW-day) 0.02 0.00001

Reference Dose (mg/kg BW-day) 3 0.1Maximum Hazard Quotient 0.007 0.0001

EGBE: ethylene glycol monobutyl ethermg/L: milligrams per litermg/kg BW-day: milligrams per kilogram body weight per day

Table 7-6. Comparison of Hazards from Surface Water Exposures Predicted in 

HAPs Petition and This Petition
Table 8-1. EGBE Emissions Rates Used in Level III Mackay Distribution Model (kg/hr)

Receiving Media CMA 1997 a Updated Analysis with 2009 TRI datab Updated Analysis with 2010 TRI datab Updated Analysi

with 2011 TRI data

Air 1,047 651 679 653Soil 18 1.2 0.8 1.0

Water 292 335

a. CMA (1997) assumed 50 percent of Certain Glycol Ethers emitted was EGBE, based on 1996 TRI data.b. These analyses assume 100 percent of Certain Glycol Ethers emitted were EGBE.

c. The emissions rates for 2011 are based on the preliminary 2011 TRI data, as acquired on September 12, 2012.Air releases consisted of reported releases to "On-site Fugitive Air" and "On-site Point Source Air"EGBE: ethylene glycol monobutyl etherkg/hr: kilograms per hourTRI: Toxics Release InventorySoil releases consisted of reported releases to onsite and offsite "Land Treatment" and "Other Land Disposal"Water releases consisted of reported releases to "On-site Surface Water Discharges." 
Table 8-2. Modeled EGBE Exposure Concentrations Used in This and Previous Ecological Risk Assessments

Cadmus Cadmus Updated Updated Updated 

Environmental CMA 2000b 2000a Analysis Analysis Analysis 

Media 1997 a Tier 1 b Tier 2 c 2009 TRI d 2010 TRI d 2011 TRI de Unit

Air 6.20E-05 3.27E-01 3.27E-01 3.82E-05 3.98E-05 3.83E-05 mg/m

Surface water 1.40E-03 3.84E+02 3.64E+00 1.90E-04 1.98E-04 1.93E-04 mg/Soil 1.30E-02 1.86E+01 7.00E-02 6.26E-03 6.53E-03 6.28E-03 mg/ke. The emissions rates for 2011 are based on the preliminary 2011 TRI data, as acquired on September 12, 2012.f. Percent of the total EGBE in each pool at equilibrium. Based on the modeled environment in EQC.

EGBE: ethylene glycol monobutyl etherTRI: Toxics Release Inventorymg/m3: milligrams per cubic meter

mg/L: milligrams per litermg/kg: milligrams per kilogramc. EQC Level III was used to determine the equilibrium distribution of EGBE in the model environment (Cadmus 2000a). Concentrations were scaled to concentration as in Cadmus (2000b).d. EQC Level III was used to determine the equilibrium concentrations of EGBE in model environment receiving all national emissions of Certain Glycothat all Certain Glycol Ethers are EGBE.b. The Level I Mackay model was used to determine the equilibrium distribution of EGBE in the model environment (Cadmus 2000b). Concentrations wpredicted worst-case fenceline concentration, based on CMA (1997) (Confidential Facility 25).a. The Level III Mackay model was used to determine equilibrium concentrations of EGBE in model environment receiving all national EGBE emissions assuming that 50 percent of all Certain Glycol Ethers are EGBE. 
EGBE-Specific Input

Parameters Value Units Source

Molecular weight 118.17 g/mol Merck 1989

Melting point -75 °C ASTER 1995

Water solubility a 5.67E+06 g/m3 Calculated

Henry's law constant 2.11E-03 Pa-m3

/mol Howard 1993, HSDB 1997

Vapor pressurea 101.32 Pa HSDB 1997

Log Kow 0.83 unitless HSDB 1997

Reaction half lives

 Air 16 hr PBT Profiler Ver. 1.301

 Water 209 hr PBT Profiler Ver. 1.301

 Soil 408 hr PBT Profiler Ver. 1.301

 Sediment 1872 hr PBT Profiler Ver. 1.301

EQC Model Parameters Value Units

Total surface area 100,000 km2

Land surface area 90,000 km2

Water surface area 10,000 km2

Atmosphere depth 1,000 m

Water depth 20 m

Soil depth 0.2 m

Sediment depth 0.05 m

 Suspended solids 20% unitless

 Soil 2% unitless

 Sediment 4% unitless

a. values apply to the chemical at 20°C

EGBE: ethylene glycol monobutyl ether

EQC: Equilibrium Criteria Model

g/m3

: grams per cubic meter

g/mol: grams per mole

km2

: square kilometers

m: meter

Pa-m3

/mol: Pascal cubic meters per mole

Table 8-3. EQC Level III Input Parameter Values

Organic carbon content 
Variable Definition Value Units Source

Ca Concentration of EGBE in air 3.98E-05 mg/m3 Table 8-2a

IRa Inhalation rate 1.2 m3/kg BW-day EPA 1993a

Cw Concentration of EGBE in water 1.98E-04 mg/L Table 8-2a

IRw Water ingestion rate 0.21 kg/kg BW-day EPA 1993a

IRdiet Food ingestion rate 0.35 kg/kg BW-day EPA 1993a

Ci Concentration of EGBE

 Soil (Cs) 6.53E-03 mg/kg Table 8-2a Plants (Cp) 8.4E-02 mg/kg Cp = Bv x Cs

Pi Proportion of Diet

 Soil (Ps) 0.02 unitless Cadmus 2000a

 Plants (Pp) 0.98 unitless Cadmus 2000a

TDI Total Daily Intake 0.029 mg/kg BW-day Calculatedb

a. Based on 2010 Toxics Release Inventory datab. where:

EGBE: ethylene glycol monobutyl ethermg/m3: milligrams p

m3/kg BW-day: cubic meter per kilogram body weight per day

mg/L: milligrams per literkg/kg BW-day: kilograms per kilogram body weight per daymg/kg: milligrams per kilogrammg/kg BW-day: milligrams per kilogram body weight per day

Table 8-4. Exposure Assumptions for Small Mammals

    Ni aa w w diet PC ii TDI C IR C IRIR 1 ( )()3 )(
Table 8-5. Chronic Species Sensitivity Distribution Calculations for EGBE

Calculated Distribution

Group Species Endpoint a Duration LC50

(mg/L)

LC50 

(log)

Calc CV 

(log) b

Calc CV 

(mg/L) b

Rank 

among all 

CVs

Percent 

Protected

Fish mummichog LC50 96 hr 6.7 0.826 -0.159 0.7 1 99.3

Fish sheepshead minnow LC50 96 hr 116 2.064 0.761 5.8 3 90.6

Fish bluegill LC50 96 hr 127 2.104 0.790 6.2 4 86.3

Fish emerald shiner LC50 72 hr 500 2.699 1.232 17.1 8 76.3

Fish rainbow trout LC50 96 hr 1000 3.000 1.456 28.6 9 71.9

Fish inland silverside LC50 96 hr 1250 3.097 1.528 33.7 10 69.8

Fish golden ide LC50 48 hr 1395 3.145 1.563 36.6 12 61.2

Fish bluegill LC50 96 hr 1490 3.173 1.584 38.4 13 59.7

Fish golden ide LC50 48 hr 1575 3.197 1.602 40.0 14 58.3

Fish goldfish LC50 24 hr 1650 3.217 1.617 41.4 15 56.8

Fish rainbow trout LC50 96 hr 1700 3.230 1.627 42.4 16 54.7

Fish goldfish LC50 24 hr 1700 3.230 1.627 42.4 16 54.7

Fish golden ide LC50 48 hr 1880 3.274 1.659 45.6 18 50.4

Fish fathead minnow LC50 96 hr 2137 3.330 1.701 50.2 20 46.8

Fish bluegill LC50 96 hr 2950 3.470 1.805 63.8 23 36.0

Mean vertebrate (weighted) 524.3 2.720 1.247 17.7

Standard deviation (weighted) 6.2 0.794 0.59 3.9

Invertebrate grass shrimp LC50 96 hr 5.4 0.732 0.093 1.2 2 95.0

Invertebrate oyster LC50 96 hr 89 1.949 1.052 11.3 5 84.9

Invertebrate white shrimp LC50 96 hr 117 2.068 1.146 14.0 6 80.6

Invertebrate white shrimp LC50 96 hr 130 2.114 1.182 15.2 7 78.4

Invertebrate brown shrimp LC50 96 hr 550 2.740 1.676 47.4 19 48.9

Invertebrate coelenterate LC50 72 hr 690 2.839 1.753 56.6 21 42.4

Invertebrate brown shrimp LC50 96 hr 698 2.844 1.757 57.2 22 38.1

Invertebrate water flea LC50 48 hr 835 2.922 1.818 65.8 24 34.5

Invertebrate water flea EC50 48 hr 1600 3.204 2.041 109.9 26 28.1

Mean invertebrate acute (weighted) 175.6 2.244 1.285 19.3

Standard deviation (weighted) 6.7 0.825 0.65 4.5

Algae/microbes cyanobacterium LOEC 8 day na na 1.544 35 11 65.5

Algae/microbes protozoan LOEC 72 hr na na 1.959 91 25 32.4

Algae/microbes green alga LOEC 7 day na na 2.398 250 27 25.9

Algae/microbes algae NOEC 72 hr na na 2.456 286 28 21.6

Algae/microbes protozoan EC05 48 hr na na 2.666 463 29 17.3

Algae/microbes bacterium LOEC 16 hr na na 2.845 700 30 12.9

Algae/microbes green alga LOEC 7 day na na 2.954 900 31 8.6

Algae/microbes protozoan EC05 48 hr na na 2.960 911 32 4.3

a. All algae endpoints are growth

b. Algae/microbe chronic values are as reported in the literature; they are not calculated

CV: chronic value

EC05: concentration at which 5% of the population was affected

EC50: median effect concentration

EGBE: ethylene glycol monobutyl ether

LC50: median lethal concentration

LOEC: lowest observed effect concentration

mg/L: milligrams of EGBE per liter of water

na: not available/applicable

NOEC: no observed effect concentration
Table 9-1. Key Findings of the Qualitative Hazard Evaluation

Toxicity Endpoint

1. Acute Toxicity

2. Chronic Toxicity

b. Mutagenicity

c. Developmental Toxicity

d. Reproductive Toxicity

e. Immunotoxicity

f. Other Chronic Toxicity

3. Environmental Toxicity

c. Terrestrial Mammals and

Birds

Summary Evaluation and Principal Reference

Primary acute effects in humans are eye and nasal irritation at levels >500 mg/m3

 (Carpenter 

1956); no irritation was found at current occupational exposure limits - 97 mg/m3

 (Johansen 

1986). Facility fenceline and environmental concentrations are far lower. 

Not immunotoxic. (IRIS)

Continuous inhalation exposure to an EGBE-saturated atmosphere expected to result in 

maximum blood concentrations of EGBE’s toxic metabolite (BAA) well below the level needed to 

produce hemolysis in humans. (Udden 2002, EPA 2010)

EGBE causes only “very minor” effects that “are unlikely to be ecologically significant” (EPA 2003 

[68 Fed. Reg. 65657])

Releases of EGBE “may not reasonably be anticipated to cause any adverse effects to human 

health” (EPA, 69 FR 69322).

• “Limited” evidence of carcinogenicity in animals; the human carcinogenic potential of EGBE

cannot be determined (IARC 2006).

• Because nonlinear, nongenotoxic modes of action are likely responsible for the tumors

observed in rodent studies, the IRIS RfD and RfC are adequately protective of any possible 

carcinogenic effects in humans. (EPA Cancer Evaluation [EPA 2005a])

Not expected to be mutagenic or clastogenic. (EPA 2010)

A “minimal” LOAEL for developmental effects = 700 mg/kg-day based on a very slight decrease in 

pup weight. (EPA 2010)

a. Carcinogenicity

700 and 1,300 mg/kg-day are considered to be NOAEL and LOAEL, respectively, for both 

maternal and reproductive effects. (EPA 2010)

a. Persistence (ATSDR 1998)

b. Bioaccumulation

• Readily biodegradable

• Half-life = 1-4 weeks in water and soil

• Bioconcentration factor = 3 (HSDB 1997)

• Octanol-water partition coefficient (Log Kow) = 0.8

No Data. [Section 3.3, below]

Page 1 of 2
Table 9-1. Key Findings of the Qualitative Hazard Evaluation

Toxicity Endpoint Summary Evaluation and Principal Reference

• Most sensitive credible LC50 = 89 mg/L

• Most LC50 values > 1000 mg/L

• Most sensitive EC50 = 164 mg/L

• Most sensitive LOAEL = 7.2 mg/L

• Most LOAELs > 100 mg/L

EGBE: ethylene glycol monobutyl ether

EPA: U.S. Environmental Protection Agency

LOAEL: lowest observed adverse effect level

mg/kg: milligrams per kilogram

mg/kg-day: milligrams per kilogram body weight per day

mg/L: milligrams per liter

mg/m 3

: milligrams per cubic meter

NOAEL: no observed adverse effect level

RfC: reference concentration

RfD: reference dose

(Section 3.3, below)

e. Chronic Aquatic Toxicity (Section 3.3, below)

d. Acute Aquatic Toxicity

Page 2 of 2
HAPs Petition This Petition

(1993 TRI Release Data) (2009-2011 TRI Release Data)

1. Human Inhalation Exposures

a. Chronic

Maximum Annual Average 

Concentration (MAAC)

 0.327 mg/m3

, based on Tier 3 

(ISCST3) air dispersion modeling for 

the maximum impact facility. 

All facilities screened out prior to chronic Tier 2 and 3 

analyses. For subset of facilities that screened out in 

Tier 2, Tier 3 modeling was conducted to test the 

conservatism of this assessment found a predicted 

MAAC using Tier 3 (AERMOD) of 0.27 mg/m3

 based 

on 2009, 2010, and 2011 data. 

RfC 13 mg/m3 1.6 mg/m3

Hazard Quotient (chronic) 0.02 ≤ 0.2

b. Acute

Maximum Hourly Average 

Concentration (MHAC)

n/a For a subset of the highest emitting facilities, tiered 

modeling of acute exposures found a predicted 

MHAC using Tier 3 (AERMOD) of 3.9 mg/m3 based 

on the 2009, 2010, and 2011 data. 

NOAEL (Irritation Based on 

Human Data)

n/a 97 mg/m3

Margin of Exposure n/a > 25

2. Human Dermal and Ingestion Exposures

Maximum Exposure 0.02 mg/kg BW-day 0.00001 mg/kg BW-day

RfD 3 mg/kg BW-day 0.1 mg/kg BW-day

Hazard Quotient 0.007 0.0001

3. Ecological Risk

a. Small Mammals (from Cadmus 2000a)

Maximum Exposure 2.15 mg/kg BW-day 0.029 mg/kg BW-day

Toxicity Reference Value 20 mg/kg BW-day 20 mg/kg BW-day

Hazard Quotient 0.11 0.001

b. Aquatic Organisms (from Cadmus 2000a)

Maximum Exposure 3.64 mg/L 0.0002 mg/L

Toxicity Reference Value 9.1 mg/L 8.7 mg/L

Hazard Quotient 0.4 0.00002

mg/kg BW-day: milligrams per kilogram body weight per day

mg/L: milligrams per liter

mg/m3

: milligrams per cubic meter

RfC: IRIS reference concentration

RfD: IRIS reference dose

TRV: toxicity reference value

Table 9-2. Key Findings of the Exposure and Risk Assessments
Section Source of Uncertainty Likely Effect on Outcome

3.0 Hazard Assessment

Humans are at least 100 times less sensitive than rats to hemolytic 

effects of EGBE. While a stand default interspecies UFs of 10 was 

not used - RfD uses UF of 1 and RfC uses UF of 3 – the actual 

interspecies factor is approximately 0.01.

RfD may be 100-fold overly conservative. RfC may be 

300-fold overly conservative. Thus, HQs may be 

overestimated by a factor of 100 to 300.

Intraspecies UF of 10 is probably overly conservative. A number of 

studies have found no evidence of increased susceptibility to 

hemolysis among sensitive subpopulations.

RfD and RfC may be overstated by an additional factor 

of 3 to 10. 

IARC (2006) concluded that the carcinogenicity of EGBE to humans 

cannot be determined and EPA (2010) concluded that carcinogenic 

effects from EGBE are not likely to occur in humans in the absence 

of critical noncancer effects.

 EPA (2005) concluded that the RfD and RfC are 

adequately protective of carcinogenic effects in 

humans, if any. Thus, question of carcinogenicity 

does not affect petition outcome.

5.0 Emissions Inventory

TRI only lists releases of Certain Glycol Ethers. In the absence of 

specific data for EGBE releases, assumed all Certain Glycol Ethers 

releases were EGBE.

Because EGBE represents 52% of market share of 

ethylene glycol ethers (SRI 2010), actual releases of 

EGBE may be overestimated 2-fold, on average.

TRI data are self-reported using a variety of methods. Individual 

facility data vary considerably in certainty.

Actual releases of Certain Glycol Ethers by facilities 

may be greater than or less than those reported on 

TRI. No evidence of systematic under-reporting.

6.0 Screening of Airborne Concentrations

a. Chronic

Step A assumed 100% of reported releases to air were exhausted 

through a single point 0 m high and 50 m from fence line. Resultant 

threshold rate (4.9 tpy) more conservative than that associated with 

2 m high emission point located 10 m from fenceline (8.6 tpy), 

which encompasses virtually all facilities in inventory for which 

stack configuration data are available. 

Maximum annual average concentrations predicted 

under Step A were up to 250-fold higher than those 

predicted using Tier 3 dispersion modeling. Thus, 

HQs predicted using Step A overestimated by 85-250 

times.

Tier 2 employed site-specific data on emission rates, stack and 

fugitive source physical parameters, and property boundaries. The 

maximum MAAC under Tier 2 was 1.2 mg/m3

, as compared to 

maximum MAAC under Tier 3 of 0.3 mg/m3

. Tier 2 results differed 

from Tier 3 results for the same facilities by factors of 1.2 to 6.7. 

HQs predicted using Tier 2 overestimated by 2 times 

or more.

Modeled maximum annual average concentration is highly 

conservative estimate of exposure over a lifetime. 

Per EPA, actual maximum annual average 

concentrations are 2-fold lower than modeled values. 

Comparison of an annual average concentration to an 

RfC designed to be protective over a lifetime 

substantially overstates risk by an unknown margin.

DEGREE OF CONSERVATISM ASSOCIATED WITH CHRONIC 

HUMAN INHALATION HAZARDS

(50 to 100) x (3 to 10) x 2 x (2 to 85) x ? = 600 to 

170,000 or more

b. Acute

The acute MOE based on the NOAEL of 97 mg/m3 and the 

estimated reasonable worst-case estimated MHAC is approximately 

18 mg/m3

. Because the NOAEL is derived from human data, per 

EPA TRI precedents MOEs >10 “indicate a low level of concern” for 

acute effects associated with EGBE facility releases.

An MOE above 5 is protective because EPA AEGL 

guidance calls for an interspecies uncertainty factor 

from 3-10 for non-systemic irritation effects, and an 

appropriate time-adjustment would support a 1-hr 

NOAEL of 137 mg/m3

.

Table 9-3. Sources of Uncertainty and Conservatism

Page 1 of 2
Section Source of Uncertainty Likely Effect on Outcome

Table 9-3. Sources of Uncertainty and Conservatism

7.0 Surface Water Exposures and Risks

Exposure point concentrations in surface water calculated by 

assuming that 100% of U.S. releases of Certain Glycol Ethers to all 

media are EGBE and are concentrated into an area the size of the 

state of Ohio.

Because EGBE represents 52% of consumption of 

ethylene glycol ethers (SRI 2010), actual releases of 

EGBE may be overestimated 2-fold, on average. 

Because 100,000 km2

 represents 1.3% of total land 

area of U.S., actual concentrations of EGBE may be 

overestimated 77-fold.

Exposure assumptions (350 day/yr, 70 years, all water contacted 

contains EGBE)

Actual exposure intensity likely to be considerably 

lower, but degree of conservatism cannot be 

quantified.

DEGREE OF CONSERVATISM ASSOCIATED WITH HUMAN 

DERMAL AND INGESTION HAZARDS

(50 to 100) x (3 to 10) x 2 x 77 x ? = 23,100 to 

154,000 or more

8.0 Ecological Risk Assessment

Exposure point concentrations in surface water calculated by 

assuming that 100% of U.S. releases of Certain Glycol Ethers to all 

media are EGBE and are concentrated into an area the size of the 

state of Ohio.

Actual releases of EGBE may be overestimated 2-fold, 

on average, and actual concentrations of EGBE may 

be overestimated 77-fold.

Conservative exposure assumptions for small mammals (inhalation 

rate, ingestion rate, bioaccumulation factor) consistent with 

Cadmus (2000a)

Actual exposure intensity likely to be considerably 

lower, but degree of conservatism cannot be 

quantified.

TRV for aquatic organisms based on most sensitive species tested, 

which may not be representative of aquatic community present in 

most U.S. water bodies

Although actual sensitivity of other aquatic organisms 

to EGBE may be considerably lower, degree of 

conservatism cannot be quantified.

TRV for small mammals is based on same underlying data used to 

derive RfD. Thus, small mammal TRV shares same uncertainties 

as listed above with respect to Section 3.0.

TRV may be 50 to 1,000-fold overly conservative due 

to UFs. 

HQs focused on what EPA calls “very minor” effects on individual 

organisms, rather than effects that are likely to be ecologically 

significant. 

Although individual organisms are likely to be 

substantially more sensitive than populations, 

communities, or ecosystems, degree of conservatism 

cannot be quantified.

DEGREE OF CONSERVATISM ASSOCIATED WITH RISKS TO 

AQUATIC ORGANISMS

2 x 77 x ? = 154 or more

DEGREE OF CONSERVATISM ASSOCIATED WITH RISKS TO 

SMALL MAMMALS

2 x 77 x (50 to 1,000) x ? = 7,700 to 154,000 or more

EGBE: ethylene glycol monobutyl ether

FR: Federal Register

HQ: hazard quotient

IRIS: Integrated Risk Information Service

km2

: square kilometer

m: meter

mg/m3

: milligrams per cubic meter

RfC: reference concentration

RfD: reference dose

tpy: tons per year

TRI: Toxics Release Inventory

TRV: toxicity reference value

UF: uncertainty factor

EPA: U.S. Environmental Protection Agency

Page 2 of 2
FIGURES 
Annual Production and Consumption of 

 EGBE in the United States (1970-2009
0

255075

100125150175200225250

1998 2000 2002 2004 2006 2008 2010 

Total Certain Glycol Ethers (tpy)

Year

Maximum Individual Facility Annual Certain Glycol Ether Releases to Air (2000 – 20

Source: Toxics Release Inventorytpy: tons per year
Figure

8-1

Compile aquatic vertebrate and 

invertebrate acute values

Vertebrate

acute distribution:

• mean (μAv)

•standard dev (Av)

Vertebrate

chronic distribution:

• mean (μCv)

•standard dev (Cv)

Empirical acute to chronic distribution

relationships (Duboudin et al. 2004a):

μCv = 0.82*μAv – 0.62* Av – 0.49

μCi = 0.58*μAi – 1.96* Ai + 1.60

Vertebrate

chronic values

Invertebrate

chronic values

All aquatic organism chronic species sensitivity distribution

Compile algae/microbe 

chronic values

Aquatic Organism Species Sensitivity Distribution Approach

Invertebrate

acute distribution:

• mean (μAi)

•standard dev (Ai)

Invertebrate

chronic distribution:

• mean (μCi)

•standard dev (Ci)

Log-transform

Log-transform

Chronic value = C*((Acute value-μA)/A)+μC

μC, μ A = mean chronic or acute value, respectively

C, A = standard deviation of chronic and acute distribution, respectively
Aquatic Organism Species Sensitivity Distributions for EGBE 

* Includes observed chronic values for algae and microbes and calculated chronic values forvertebrates and invertebrates (Duboudin et al. 2004a)

8.7

80th percentile

4.2

90th percentile

2.3

95th percentile

0.0

10.020.030.040.050.060.070.080.090.0

100.0

0.1 1 10 100 1000 

Percent species protected

EGBE (mg/L)

Aquatic organisms: Calculated chronic dAquatic vertebratesAquatic invertebrate
APPENDIX A 

Toxicity Values in Laboratory Mammals 
 

APPENDIX A-1 

Toxicity Values in Laboratory Mammals from ATSDR 1998 
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
Appendix A. Mammalian Toxicity Values from ATSDR 1998
APPENDIX A-2 

Toxicity Values in Laboratory Mammals Published After 1998
Appendix A-2. Mammalian EGBE Toxicity Data Published Since 1998 

Test 

Organism 

Exposure 

Route 

Exposure 

Duration 

Effect 

Measurement Endpoint Effects Notes 

EGBE 

Concentra 

tion Units Reference 

ACUTE EXPOSURES

BALB/c mice Dermal 1 dose Other sublethal NOEC 

Immune system response 1 mg/ear Singh et al. 2002 

BALB/c mice Dermal 1 dose Other sublethal LOEC 

Immune system response 4 mg/ear Singh et al. 2002 

BALB/c mice Dermal 4 days Other sublethal LOAEL 

Immune system response 500 

mg/kg day Singh et al. 2001 

F344 rats In vitro Other sublethal other 

Hemolytic effects 11.8 mg/L Udden 2002 

Syrian hamster In vitro <3 hrs Other sublethal other 

Inhibition of pADPr synthesis 591 mg/L 

Hoflack et al. 1997 

Syrian hamster In vitro 7 hr Other sublethal NOAEL 

Cellular transformation induction 2364 mg/L Park et al. 2002b 

Opossum In vitro 24 hr Mortality EC50 Cell viability 1000 mg/L 

Dartsch et al. 1999 

B6C3F1 mice Inhalation 6 hr Other sublethal LOAEL 

Forestomach lesions 250 ppm Green et al. 2002 
Appendix A-2. Mammalian EGBE Toxicity Data Published Since 1998 

Test 

Organism 

Exposure 

Route 

Exposure 

Duration 

Effect 

Measurement Endpoint Effects Notes 

EGBE 

Concentra 

tion Units Reference 

guinea pig Inhalation 1 hr Mortality NOEC 633 ppm 

Gingell et al. 1998 

B6C3F1 mice Injection 1 dose Other sublethal LOAEL 

Forestomach lesions 10 

mg/kg bw Green et al. 2002 

guinea pig Injection 1 dose Mortality NOAEL 2000 

mg/kg bw 

Gingell et al. 1998 

F344 rats Oral - dw 2-4 days Other sublethal LOAEL 

Histopathology 250 

mg/kg bw-day Nyska et al. 2003 

guinea pig Oral - dw 1 dose Mortality LD50 1414 

mg/kg bw 

Gingell et al. 1998 

B6C3F1 mice 

Oral - gavage 4 days Other sublethal LOAEL 

Forestomach lesions 400 

mg/kg bw-day Poet et al. 2003 

B6C3F1 mice 

Oral - gavage 4 days Mortality LOAEL 400 

mg/kg bw-day Poet et al. 2003 

B6C3F1 mice 

Oral - gavage 7 days Other sublethal LOAEL Hepatic stress 450 

mg/kg bw-day Park et al. 2002a 

B6C3F1 mice 

Oral - gavage 1 dose Other sublethal other 

EGBE metabolism and distribution 600 

mg/kg bw 

Deisinger et al. 2004 

F344 rats 

Oral - gavage 1 dose Other sublethal LOAEL 

Hemolytic effects 125 

mg/kg bw Udden 2000 
Appendix A-2. Mammalian EGBE Toxicity Data Published Since 1998 

Test 

Organism 

Exposure 

Route 

Exposure 

Duration 

Effect 

Measurement Endpoint Effects Notes 

EGBE 

Concentra 

tion Units Reference 

F344 rats 

Oral - gavage 2-4 days Other sublethal LOEC 

Increased adherence of RBCs to extracellular matrix 250 

mg/kg bw-day 

Koshkaryev et al2003 

F344 rats 

Oral - gavage 1-3 days Other sublethal LOAEL 

Acute regenerative hemolytic anemia 250 

mg/kg bw-day 

Ghanayem et al. 2001 

F344 rats 

Oral - gavage 1 dose Other sublethal LOAEL 

Various hemotologic parameters 250 

mg/kg bw 

Ghanayem et al. 2000 

F344 rats 

Oral - gavage 3 days Other sublethal LOAEL 

Histopathology 250 

mg/kg bw-day 

Nyska et al. 1999a 

Sprague Dawley rats 

Oral - gavage 1-4 doses Mortality NOEC 500 

mg/kg bw-day 

Sawant et al. 1999 

Sprague Dawley rats 

Oral - gavage 1-4 doses Mortality LOEC 1500 

mg/kg bw-day 

Sawant et al. 1999 

CHRONIC EXPOSURES

B6C3F1 mice Inhalation 14 wk Other sublethal LOEC 

Hemolytic effects 31.2 ppm NTP 2000 

B6C3F1 mice Inhalation 2 years Other sublethal LOAEL 

Hepatic lesions and forestomach effects 62.5 ppm 

Boatman et al. 2004 
Appendix A-2. Mammalian EGBE Toxicity Data Published Since 1998 

Test 

Organism 

Exposure 

Route 

Exposure 

Duration 

Effect 

Measurement Endpoint Effects Notes 

EGBE 

Concentra 

tion Units Reference 

B6C3F1 mice Inhalation 2 years Mortality NOEC 62.5 ppm NTP 2000 B6C3F1 mice Inhalation 14 wk Growth NOEC 62.5 ppm NTP 2000 B6C3F1 mice Inhalation 2 years Mortality LOEC 125 ppm NTP 2000 B6C3F1 mice Inhalation 14 wk Growth LOEC 125 ppm NTP 2000 B6C3F1 mice Inhalation 18 mo Mortality NOEC 

Elimination kinetics study, no mortality observed 250 ppm Dill et al. 1998 

F344 rats Inhalation 2 years Other sublethal LOEC 

Hemolytic effects (e.g., anemia) 31.2 ppm NTP 2000 

F344 rats Inhalation 13 wks Other sublethal LOEC 

Histopathology 32 ppm 

Long et al. 2000Nyska et al. 1999b 

F344 rats Inhalation 2 years Growth NOEC 62.5 ppm NTP 2000 F344 rats Inhalation 18 mo Mortality NOEC 

Elimination kinetics study, no mortality observed 125 ppm Dill et al. 1998 
Appendix A-2. Mammalian EGBE Toxicity Data Published Since 1998 

Test 

Organism 

Exposure 

Route 

Exposure 

Duration 

Effect 

Measurement Endpoint Effects Notes 

EGBE 

Concentra 

tion Units Reference 

F344 rats Inhalation 13 wks Immobilization NOEC Moribund 125 ppm 

Long et al. 2000Nyska et al. 1999b 

F344 rats Inhalation 2 years Mortality NOEC 125 ppm NTP 2000 F344 rats Inhalation 2 years Growth LOEC 125 ppm NTP 2000 F344 rats Inhalation 13 wks Immobilization LOEC Moribund 250 ppm 

Long et al. 2000Nyska et al. 1999b 

F344 rats Inhalation 2 years Mortality LOEC 250 ppm NTP 2000 Swiss CD-1 mice Oral - dw 

2 generations M, R, G NOEC 

Slight reproductive effects in 2nd

generation 5000 mg/L Lamb et al 1997 

Swiss CD-1 mice Oral - dw 

2 generations M, R, G LOEC 

Statistically significant effects 10000 mg/L Lamb et al 1997 

B6C3F1 mice 

Oral - gavage ≤ 90 days Other sublethal LOAEL 

Hemolytic and hepatic effects 225 

mg/kg bw Siesky et al. 200

B6C3F1 mice 

Oral - gavage ≤ 90 days Mortality NOAEL 900 

mg/kg bw Siesky et al. 200

F344 rats 

Oral - gavage ≤ 90 days Other sublethal LOAEL 

Hemolytic and hepatic effects 225 

mg/kg bw Siesky et al. 200
Appendix A-2. Mammalian EGBE Toxicity Data Published Since 1998 

Test 

Organism 

Exposure 

Route 

Exposure 

Duration 

Effect 

Measurement Endpoint Effects Notes 

EGBE 

Concentra 

tion Units Reference 

F344 rats 

Oral - gavage ≤ 90 days Mortality NOAEL 450 

mg/kg bw Siesky et al. 200

2-BAA: 2-butoxyacetaldehyde M, R, G: mortality, growth, reprodDNA: deoxyribonucleic acid MCV: mean corpuscular volume Dw: drinking water NOAEL: no observed adverse effeEC50: median effect concentration NOEC: no observed effect concenLD50: median lethal dose NTP: National Toxicology Program LOAEL: lowest observed adverse effect level pADPr: poly adenosine diphosphaLOEC: lowest observed effect concentration RBC: red blood cells 
APPENDIX B 

Emissions Inventory 
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

EQ DETROIT INC 1923 FREDERICK DETROIT Michigan 48211 0 

REXAM BEVERAGE CAN CO RE: WINSTON SALEM PLANT 4000 OLD MILWAUKEE LN WINSTON-SALEM North Carolina 27107 28.312 

BALL METAL BEVERAGE CONTAINER CORP 8935 POCAHONTAS TRAIL JAMES RI WILLIAMSBURG Virginia 23185 27 BALL METAL BEVERAGE CONTAINER CORP 12340 TOWNSHIP RD 99 E FINDLAY Ohio 45840 24.5 

SANYO SOLAR (USA) LLC 970 E 236TH ST CARSON California 90745 0.0005 REXAM BEVERAGE CAN CO RE: FREMONT PLANT 2145 CEDAR FREMONT Ohio 43420 17.873 

CROWN FOOD PACKAGING 2929 W BRIDGE ST OWATONNA Minnesota 55060 29.3115 AURORA CASKET CO INC 10944 MARSH RD AURORA Indiana 47001 0.0025 

CROWN CORK & SEAL CO (USA) INC CROWN CLOSURE DIV 3011 BIRCH DR WEIRTON West Virginia 26062 37.8575 

REXAM BEVERAGE CAN CO RE: BISHOPVILLE SC FACILITY 609 COUSAR ST BISHOPVILLE South Carolina 29010 14.4695 REXAM BEVERAGE CAN CO RE: EVA STREET ST PAUL MN 139 EVA ST SAINT PAUL Minnesota 55107 14.029 

FORD MOTOR CO DEARBORN TRUCK PLANT 3001 MILLER RD DEARBORN Michigan 48121 3.8 

REXAM BEVERAGE CAN CO OLIVE BRANCH FACILITY 10800 MARINA DR OLIVE BRANCH Mississippi 38654 19.6495 REXAM BEVERAGE CAN CO KENT WA FACILITY 1220 N SECOND AVE KENT Washington 98032 13.1945 

BALL METAL BEVERAGE CONTAINER CORP 1900 BARNES ST REIDSVILLE North Carolina 27320 12 CROWN BEVERAGE PACKAGING GLEN & SHEPARD ST LAWRENCE Massachusetts 01843 18.0445 

BMW MANUFACTURING CO LLC 1400 HWY 101 S GREER South Carolina 29651 3.543 

BALL CONTAINER LLC COLUMBUS CAN PLANT 350 MCCORMICK BLVD COLUMBUS Ohio 43213 20 

CROWN BEVERAGE PACKAGING 1035 E NORTH ST BRADLEY Illinois 60915 17.1385 

CROWN BEVERAGE PACKAGING 1202 FONES RD OLYMPIA Washington 98501 17.083 SILGAN CONTAINERS MANUFACTURING CORP 300 N FAIL RD LA PORTE Indiana 46350 12.5 REXAM BEVERAGE CAN CO LONGVIEW FACILITY 1001 FISHER RD LONGVIEW Texas 75604 17.6895 

REXAM BEVERAGE CAN CO RE : CHICAGO PLANT 1101 W 43RD ST CHICAGO Illinois 60609 13.6425 

METAL CONTAINER CORP - JACKSONVILLE CAN PLANT 1100 N ELLIS RD JACKSONVILLE Florida 32254 6.8885 

METAL CONTAINER CORPORTION - WINDSOR CAN PLANT 1201 METAL CONTAINER CT WINDSOR Colorado 80550 15.125 

WHIRLPOOL CORP MARION D IVISION 1300 MARION-AGOSTA RD MARION Ohio 43302 0.05 

Page 1 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

REXAM BEVERAGE CAN CO CHATSWORTH FACILITY 20730 PRAIRIE ST CHATSWORTH California 91311 14.307 SILGAN CONTAINERS MANUFACTURING CORP 1400 PLOVER RD PO BOX 97 PLOVER Wisconsin 54467 10.75 

BALL CONTAINER LLC ROME CAN PLANT 110 MCC DR ROME Georgia 30161 34.5 REXAM BEVERAGE CAN CO RE: WHITEHOUSE PLANT 10444 WATERVILLE WHITEHOUSE Ohio 43571 16.48 

METAL CONTAINER CORP - NEWBURGH CAN PLANT 130 BREUNIG RD NEW WINDSOR New York 12553 12.0965 

HONDA OF AMERICA MANUFACTURING INC 24000 HONDA PKY MARYSVILLE Ohio 43040 10.078 CROWN BEVERAGE PACKAGING 620 N 4TH ST WORLAND Wyoming 82401 11.1305 

METAL CONTAINER CORP - ARNOLD CAN PLANT 42 TENBROOK INDUSTRIAL PARK ARNOLD Missouri 63010 17.1215 

BALL METAL BEVERAGE CONTAINER CORP 8500 W TOWER AVE MILWAUKEE Wisconsin 53224 35.5 

FORD MOTOR COMPANY--KANSAS CITY ASSEMBLY PLANT 8121 E US HWY 69 CLAYCOMO Missouri 64119 2.25 

RR DONNELLEY 2347 KRATZER RD HARRISONBURG Virginia 22802 36.14 

REXAM BEVERAGE CAN CO PHOENIX FACILITY 211 N 51ST AVE PHOENIX Arizona 85043 5.2365 

ROCKY MOUNTAIN METAL CONTAINER 17755 W 32ND AVE GOLDEN Colorado 80401 30.5 

CHRYSLER ST LOUIS NORTH ASSEMBLY PLANT 1050 DODGE DR FENTON Missouri 63026 5.5 NEW UNITED MOTOR MANUFACTURING INC 45500 FREMONT BLVD MAIL STOP 16FREMONT California 94538 29.686 

BALL METAL FOOD CONTAINER CORP 3010 BIRCH DR WEIRTON West Virginia 26062 25.5 WHIRLPOOL CORP - CLYDE DIV 119 BIRDSEYE ST CLYDE Ohio 43410 1.0635 

GM TRUCK GROUP FLINT ASSEMBLY PLANT VAN SLYKE COMPLEX

G-3100 VAN SLYKE RD FLINT Michigan 48551 0.29 

BALL METAL BEVERAGE CONTAINER CORP 501 N SIXTH ST MONTICELLO Indiana 47960 26 

CROWN BEVERAGE PACKAGING 2501 N FRAZIER ST CONROE Texas 77305 29.291 

CROWN FOOD PACKAGING 8801 CITATION RD BALTIMORE Maryland 21221 8.4905 

BALL METAL BEVERAGE CONTAINER CORP 500 CRENSHAW BLVD TORRANCE California 90503 31 

REXAM BEVERAGE CAN CO RE:OKLAHOMA CITY PLANT 3400 S COUNCIL RD OKLAHOMA CITY Oklahoma 73179 5.032 FORD MOTOR CO KENTUCKY TRUCK PLANT 3001 CHAMBERLAIN LN LOUISVILLE Kentucky 40241 0.9 

NISSAN NA INC SMYRNA MANUFACTURING PLANT 983 NISSAN DR SMYRNA Tennessee 37167 1.379 

Page 2 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

METAL CONTAINER CORP - MIRA LOMA CAN PLANT 10980 INLAND AVE MIRA LOMA California 91752 29.0325 GREIF PACKAGING LLC 7425 INDUSTRIAL RD FLORENCE Kentucky 41042 1.3765 CROWN BEVERAGE PACKAGING 12910 JESS PIRTLE BLVD SUGAR LAND Texas 77478 27.9735 BALL METAL BEVERAGE CONTAINER CORP 2400 HUNTINGTON DR FAIRFIELD California 94533 12.5 BALL METAL BEVERAGE CONTAINER CORP 4525 INDIANA ST GOLDEN Colorado 80403 21 CHICAGO HEIGHTS STEEL 211 E MAIN ST CHICAGO HEIGHTS Illinois 60411 6.2785 

THERMA-TRU CORP 601 RE JONES RD BUTLER Indiana 46721 0 SENECA FOODS CORP 801 SAUK AVE BARABOO Wisconsin 53913 0 CROWN BEVERAGE PACKAGING 380 CALLE FABRIL ST KM 126 PR-3, PCAROLINA Puerto Rico 00985 7.531 

HONDA OF AMERICA MANUFACTURING INC 11000 STATE RT 347 EAST LIBERTY Ohio 43319 1.95 

EFCO CORP 1000 COUNTY RD MONETT Missouri 65708 1.1695 

BALL METAL BEVERAGE CONTAINER CORP 4700 WHITEWAY DR TAMPA Florida 33617 11.5 

NISSAN NORTH AMERICA INC CANTON MS 300 NISSAN DR CANTON Mississippi 39046 2.0275 

CHRYSLER JEFFERSON NORTH ASSEMBLY PLANT 2101 CONNOR AVE DETROIT Michigan 48215 6.5 

FLINT HILLS RESOURCES LP - WEST PLANT 2825 SUNTIDE RD CORPUS CHRISTI Texas 78410 0.055 

NYW REALTY LLC/ HANOVER 500 E MIDDLE ST HANOVER Pennsylvania 17331 0 EDSAL MANUFACTURING CO INC 4400 S PACKER CHICAGO Illinois 60609 0 

AVX CORP MYRTLE BEACH 801 17TH AVE S MYRTLE BEACH South Carolina 29577 7.2445 

CROWN BEVERAGE PACKAGING 195 CROWN RD BATESVILLE Mississippi 38606 22.54 

CROWN BEVERAGE PACKAGING 1501 ST JAMES ST LA CROSSE Wisconsin 54603 22.8145 SAPA EXTRUSIONS INC 2500 ALUMAX RD YANKTON South Dakota 57078 0 

MAGNA STEYR NORTH AMERICA 3800 STICKNEY AVE TOLEDO Ohio 43608 2.95 

AIR SYSTEM COMPONENTS LP 900 DARR PARK DR PONCA CITY Oklahoma 74601 0.2435 

MOBIL CHEMICAL CO 41501 WOLVERINE RD SHAWNEE Oklahoma 74804 0.375 

WHIRLPOOL CORP FINDLAY DIV 4901 N MAIN ST FINDLAY Ohio 45840 2.2845 S B FOOT TANNING CO 805 BENCH ST RED WING Minnesota 55066 0 

CROWN BEVERAGE PACKAGING 100 EVANS ROW CHERAW South Carolina 29520 19.606 

SUBARU OF INDIANA AUTOMOTIVE INC 5500 STATE RD 38E LAFAYETTE Indiana 47905 0.22 BATESVILLE MANUFACTURING INC 175 MONOGARD DR MANCHESTER Tennessee 37355 1.088 

Page 3 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

MEMC PASADENA INC 3000 N S ST PASADENA Texas 77503 12.6555 

PPG INDUSTRIES OHIO INC - DELAWARE 760 PITTSBURGH DR DELAWARE Ohio 43015 0.057 BWAY CORP 1601 VALDOSTA HWY HOMERVILLE Georgia 31634 19.247 

BALL METAL BEVERAGE CONTAINER CORP 1001 N FM 3083 E CONROE Texas 77303 14 

SPECTRUM METAL FINISHING 535 BEV RD YOUNGSTOWN Ohio 44512 0.37 

DEXTER CHASSIS GROUP PLANT 55 501 S MILLER DR WHITE PIGEON Michigan 49099 0 

ROLL COATER INC 1950 E MAIN ST GREENFIELD Indiana 46140 0.033 BALL METAL BEVERAGE CONTAINER CORP 11 ADAMS RD SARATOGA SPRINGSNew York 12866 3.3 

GM SPRING HILL MANUFACTURING 100 SATURN PKWY MAIL DROP 371-9SPRING HILL Tennessee 37174 0.175 

OLDCASTLE BUILDING ENVELOPE TEXAS FACILITY 803 AIRPORT RD TERRELL Texas 75160 2.7755 

UNION CARBIDE CORP SEADRIFT PLANT 7501 N HWY 185 SEADRIFT Texas 77983 13.899 HONDA MANUFACTURING OF ALABAMA LLC 1800 HONDA DR LINCOLN Alabama 35096 0.198 NUCOR VULCRAFT GROUP GRAPELAND DIV 175 COUNTY RD 2345 GRAPELAND Texas 75844 0.15 

PPG INDUSTRIES INC-OAK CREEK 10800 S 13TH ST OAK CREEK Wisconsin 53154 15.48 

NORTH COAST CONTAINER CORP 8806 CRANE AVE CLEVELAND Ohio 44105 0 

TOYOTA MOTOR MANUFACTURING INDIANA INC 4000 TULIP TREE DR PRINCETON Indiana 47670 9.7535 

ALLIED TUBE & CONDUIT CORP 16100 S LATHROP AVE HARVEY Illinois 60426 10.022 

NOVELIS CORP 390 GRISWOLD ST NE WARREN Ohio 44483 4.657 

METAL INDUSTRIES INC - BUSHNELL 400 W WALKER AVE BUSHNELL Florida 33513 0.0765 

BOEING COMMERCIAL AIRPLANE GROUP - EVERETT 3003 W CASINO RD EVERETT Washington 98204 1.6 AIR SYSTEM COMPONENTS LP 3301 N MAIN ST TARBORO North Carolina 27886 0.155 

HAMMER PACKAGING CORP 200 LUCIUS GORDON DR WEST HENRIETTA New York 14586 0 

S D WARREN CO 89 CUMBERLAND ST WESTBROOK Maine 04098 0.0015 SEIDEL TANNING CORP 1306 E MEINECKE AVE MILWAUKEE Wisconsin 53212 0 

HART & COOLEY INC 4910 MOORES MILL RD HUNTSVILLE Alabama 35811 0.852 

PELLA CORP 102 MAIN ST PELLA Iowa 50219 0.125 

BALL CONTAINER LLC 105 E BLACKHAWK DR FORT ATKINSON Wisconsin 53538 3.55 

ALCOA INC - WARRICK OPERATIONS HWYS 66 & 61 NEWBURGH Indiana 47629 0 

L A DARLING CO - PIGGOTT AR FACILITY HWY 49 S PIGGOTT Arkansas 72454 0.167 

Page 4 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

MPM SILICONES LLC 3500 S STATE RT 2 FRIENDLY West Virginia 26146 2.2045 

PROFESSIONAL DISPOSABLES INTERNATIONAL INC TWO NICE-PAK PARK ORANGEBURG New York 10962 0.043 

JOHNSON WELDED PRODUCTS INC 625 S EDGEWOOD AVE URBANA Ohio 43078 0 

REXAM BEVERAGE CAN CO FAIRFIELD PLANT 2433 CROCKER CIR FAIRFIELD California 94533 5.4755 

EASTMAN CHEMICAL CO TEXAS OPERATIONS 300 KODAK BLVD LONGVIEW Texas 75602 12 

MUELLER CO 956 INDUSTRIAL BLVD ALBERTVILLE Alabama 35950 6.892 

CROWN BEVERAGE PACKAGING 400 N WALNUT ST CRAWFORDSVILLE Indiana 47933 10.035 

ALSTOM POWER INC PLATE FORMED PRODUCTS DIV 911 W MAIN ST CHATTANOOGA Tennessee 37402 13.7535 

PRECOAT METALS 1095 MENDELL DAVIS DR JACKSON Mississippi 39272 12.341 

GENERAL MOTORS CORP LORDSTOWN COMPLEX 2300 HALLOCK-YOUNG RD LORDSTOWN Ohio 44481 12 

KNAPHEIDE MANUFACTURING CO 1848 WESTPHALIA STRASSE QUINCY Illinois 62305 0.131 

BEMIS MANUFACTURING CO PLANT B 300 MILL ST SHEBOYGAN FALLS Wisconsin 53085 0 

BALL METAL BEVERAGE CONTAINER CORP 95 BALLARD RD MIDDLETOWN New York 10940 6 

BALL METAL BEVERAGE CONTAINER CORP 6600 WILL ROGERS BLVD FORT WORTH Texas 76140 5.5 

CAN CORP OF AMERICA INC 326 JUNE AVE BLANDON Pennsylvania 19510 3.168 SILGAN CONTAINERS MANUFACTURING CORP 305 W N ST MOUNT VERNON Missouri 65712 2.621 

BALL METAL BEVERAGE CONTAINER CORP 91-320 KOMOHANA ST KAPOLEI Hawaii 96707 2.2 

AUTOALLIANCE INTERNATIONAL INC 1 INTERNATIONAL DR FLAT ROCK Michigan 48134 0.0025 

BEDFORD MATERIALS CO INC 7676 ALLEGHENY RD MANNS CHOICE Pennsylvania 15550 1.2505 

HUNTSMAN PETROCHEMICAL LLC PORT NECHES PERFORMANCE PRODUCTS

6001 HWY 366 PORT NECHES Texas 77651 0.079 

QUAD/GRAPHICS INC 1900 W SUMNER ST HARTFORD Wisconsin 53027 12 

FORD LOUISVILLE ASSEMBLY 2000 FERN VALLEY RD LOUISVILLE Kentucky 40213 0.125 MERCEDES-BENZ US INTERNATIONAL INC 1 MERCEDES DR VANCE Alabama 35490 2.3115 

MODINE MANUFACTURING CO INC 551 TAPP RD HARRODSBURG Kentucky 40330 1.202 

M&B HANGERS 1313 PKWY DR SE LEEDS Alabama 35094 2.399 CROWN FOOD PACKAGING 1650 BROADWAY HANOVER Pennsylvania 17331 2.852 

TOKICO (USA) INC 301 MAYDE RD BEREA Kentucky 40403 0.245 

NUCOR CORP VULCRAFT/NUCOR COLD FINISH DIV 1601 W OMAHA AVE NORFOLK Nebraska 68701 0.8 

AKZO NOBEL COATINGS INC 1629 VANDERBILT RD BIRMINGHAM Alabama 35234 11.1405 

Page 5 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

MEADWESTVACO CONSUMER PACKAGING GROUP LLC 7411 OAKWOOD ST MEBANE North Carolina 27302 11.2585 CROWN FOOD PACKAGING 5201 ENTERPRISE BLVD TOLEDO Ohio 43612 2.806 AMERICAN TRIM LLC 1501 W MICHIGAN ST SIDNEY Ohio 45365 0 GEA BPO LLC 301 N CURRY PIKE BLOOMINGTON Indiana 47404 0 HEXION SPECIALTY CHEMICALS INC 2525 S COMBEE RD LAKELAND Florida 33801 9.3205 GERSTENSLAGER CO 1425 E BOWMAN ST WOOSTER Ohio 44691 0.325 BROAN-NUTONE LLC 926 W STATE ST HARTFORD Wisconsin 53027 0.1135 POWER PARTNERS INC 200 NEWTON BRIDGE RD ATHENS Georgia 30607 0 VESTAL MANUFACTURING ENTERPRISES INC 177 INDUSTRIAL PARK RD SWEETWATER Tennessee 37874 10.7105 FRANKLIN INVESTMENT CORP 600 ATLANTIC AVE FRANKLIN Pennsylvania 16323 10.7 TRI VULCRAFT OF NEW YORK INC 5362 RAILROAD ST CHEMUNG New York 14825 4.5235 CECO DOOR PRODUCTS 9159 TELECOM DR MILAN Tennessee 38358 5.289 INGERSOLL-RAND CO STEELCRAFT DIV 9017 BLUE ASH RD CINCINNATI Ohio 45242 2.5475 MEYER STEEL DRUM INC 2000 S KILBOURN AVE CHICAGO Illinois 60623 1.1265 BALL AEROSOL & SPECIALTY CONTAINER INC 1717 GIFFORD RD ELGIN Illinois 60120 1.65 CARDONE INDUSTRIES 5660 RISING SUN AVE PHILADELPHIA Pennsylvania 19120 1.987 KAWNEER CO INC 600 KAWNEER DR SPRINGDALE Arkansas 72764 4.781 MAYFLOWER VEHICLE SYSTEMS INC NORWALK FACILITY 55 N GARFIELD ST NORWALK Ohio 44857 0 YKK AP AMERICA INC 332 FIRETOWER RD DUBLIN Georgia 31021 9.541 RR DONNELLEY CRAWFORDSVILLE 1009 SLOAN ST CRAWFORDSVILLE Indiana 47933 5.107 BERENFIELD CONTAINERS SW LTD 3300 N HUTCHINSON ST WHITE HALL Arkansas 71602 0 COOK COMPOSITES & POLYMERS CO 340 RAILROAD ST SAUKVILLE Wisconsin 53080 0.7885 KEYMARK CORP OF FLORIDA 2540 KNIGHTS STATION RD LAKELAND Florida 33810 0.4925 LAKESIDE LITHOGRAPHY LLC 1600 S LAFLIN ST CHICAGO Illinois 60608 1 PENN COLOR INC 2755 BERGEY RD HATFIELD Pennsylvania 19440 0.2255 NUCOR VULCRAFT GROUP SAINT JOE DIV 6610 COUNTY RD 60 SAINT JOE Indiana 46785 4.2105 RINECO 1007 VULCAN RD- HASKELL BENTON Arkansas 72015 0.0495 ROYAL MOULDINGS LTD; MARION VIRGINIA 135 BEAR CREEK RD MARION Virginia 24354 0.3835 

Page 6 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

HEWLETT-PACKARD CARIBE BV SITE HWY 110 N KM 5.1 AGUADILLA Puerto Rico 00605 0.125 

3M CO - GUIN 6675 US HWY 43 GUIN Alabama 35563 0.001 

STANLEY WORKS HAND TOOLS DIV 600 MYRTLE ST NEW BRITAIN Connecticut 06052 0.946 

CIRCLE GRAPHICS INC 120 9TH AVE LONGMONT Colorado 80501 3.05 

NUCOR CORP VULCRAFT DIV 1501 W DARLINGTON ST FLORENCE South Carolina 29501 8.525 

EPCO EXTRUSION PAINTING CO 413 MCCLURG RD BOARDMAN Ohio 44512 0.8375 

QUAD/GRAPHICS INC N63 W23075 STATE HWY 74 ATTN: E SUSSEX Wisconsin 53089 8.275 

HALLSTAR CO ESTER SOLUTIONS FACILITY 5851 W 73RD ST BEDFORD PARK Illinois 60638 1.134 

SILGAN CONTAINERS MANUFACTURING CORP 2115 SW LOWER LAKE RD SAINT JOSEPH Missouri 64504 6.299 

KUBIN-NICHOLSON CORP 8448 N 87TH ST MILWAUKEE Wisconsin 53224 9.148 

SILGAN CAN CO 2120 NC HWY N UNIT A MAXTON North Carolina 28364 2.965 SILGAN CAN CO 12-773 ST RT 110 NAPOLEON Ohio 43545 2.438 

SQUARE D CO 1601 MERCER RD LEXINGTON Kentucky 40511 0 

HESS PRINT SOLUTIONS 3765 SUNNYBROOK RD BRIMFIELD Ohio 44240 9 CROWN AEROSOL PACKAGING 3737 E EXCHANGE AVE AURORA Illinois 60504 7.8805 

SILGAN CONTAINERS MANAUFACTURING CORP 520 W 2ND ST OCONOMOWOC Wisconsin 53066 1.75 

GENERAL MOTORS LANSING DELTA TOWNSHIP 8175 MILLETT HWY LANSING Michigan 48917 0.23 

TOPPAN INTERAMERICA INC 1131 HWY 155 S MC DONOUGH Georgia 30253 0 

SILGAN WHITE CAP CORP 2201 W MARYLAND ST EVANSVILLE Indiana 47710 1.9 

TOYOTA MOTOR MANUFACTURING TEX AS INC 1 LONE STAR PASS SAN ANTONIO Texas 78264 5.2135 

FORD MOTOR COMPANY-WAYNE ASSEMBLY 37625 MICHIGAN AVE WAYNE Michigan 48184 0.085 

MAYTAG CORP CLEVELAND COOKING PRODUCTS PLANT 1 740 KING EDWARD AVE SE CLEVELAND Tennessee 37311 0 

RR DONNELLEY & SONS CO 1145 CONWELL AVE WILLARD Ohio 44890 6.0815 SIGNODE 7701 W 71ST ST BRIDGEVIEW Illinois 60455 0.85 

BERENFIELD CONTAINERS INC 31 RAILROAD ST CLARENDON Pennsylvania 16313 0.0755 

GM ORION ASSEMBLY CENTER 4555 GIDDINGS RD ORION Michigan 48359 6.5 

MASTERBRAND CABINETS INC 217 S OAK ST ARTHUR Illinois 61911 0 

SILGAN CAN CO 500 NW LOOP 286 SUITE 101 PARIS Texas 75460 4.945 

BERENFIELD CONTAINERS INC MASON 1229 CASTLE DR MASON Ohio 45040 0.375 

Page 7 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

NOV DOWNHOLE TOOLS CASPER 778 CIR DR CASPER Wyoming 82601 0 

LA-Z-BOY TENNESSEE 500 WALNUT GROVE RD DAYTON Tennessee 37321 0 

DECORATIVE PANELS INTERNATIONA L 2900 HILL AVE TOLEDO Ohio 43607 7.5945 

GREIF PACKAGING LLC 2400 COOPER AVE MERCED California 95348 6.4965 

GM TRUCK GROUP FORT WAYNE ASSEMBLY 12200 LAFAYETTE CENTER RD ROANOKE Indiana 46783 0.475 

WHITING DOOR MANUFACTURING CORP 113 CEDAR ST AKRON New York 14001 0 

HOWARD FINISHING LLC 32565 DEQUINDRE MADISON HEIGHTS Michigan 48071 0.0025 

SILGAN CONTAINERS MANUFACTURING CORP 135 NATIONAL RD EDISON New Jersey 08817 6 

BWAY CORP 3200 S KILBOURN AVE CHICAGO Illinois 60623 4.3655 

SILGAN CONTAINERS MANUFACTURING CORP 1416 INDIANHEAD DR MENOMONIE Wisconsin 54751 1.45 

NASHVILLE WIRE PRODUCTS 1604 COUNTY HOSPITAL RD NASHVILLE Tennessee 37218 0.7 

CHICAGO STEEL CONTAINER CORP 1846 S KILBOURN AVE CHICAGO Illinois 60623 1.3 

DOW CHEMICAL CO FREEPORT FACILITY 2301 N BRAZOSPORT BLVD BUILDIN FREEPORT Texas 77541 0.1645 

BENJAMIN MOORE & CO JOHNSTOWN UNION AVE EXTENSION JOHNSTOWN New York 12095 0.014 

SHIELDCOAT TECHNOLOGIES INC (DBA CYBERSHIELD OF TEXAS)

2602 SPENCE ST LUFKIN Texas 75904 7.1205 

WIX FILTRATION CORP - ALLEN PLANT 2900 NW BLVD GASTONIA North Carolina 28052 0.0025 

RR DONNELLEY LANCASTER WEST 1375 HARRISBURG PIKE LANCASTER Pennsylvania 17601 6.6515 

NUCOR CORP VULCRAFT DIV 7205 GAULT AVE N FORT PAYNE Alabama 35967 5.101 

GREIF PACKAGING LLC 6000 JEFFERSON HWY NEW ORLEANS Louisiana 70123 2.673 

SONOCO PHOENIX - PRESIDENTS ISLAND 2755 HARBOR AVE MEMPHIS Tennessee 38113 0 

AFTON CHEMICAL CORP 725 CANNON BRIDGE RD ORANGEBURG South Carolina 29115 3.179 

ACME FINISHING CO INC 1595 E OAKTON ST ELK GROVE VILLAGEIllinois 60007 1.359 

EQUISTAR CHEMICALS BAYPORT CHEMICALS PLANT 5761 UNDERWOOD RD PASADENA Texas 77507 6.753 

COLOR COMMUNICATIONS INC 4242 W FILLMORE CHICAGO Illinois 60624 1.419 

CHRYSLER WARREN TRUCK ASSEMBLY PLANT (PART) 21500 MOUND RD WARREN Michigan 48091 6 

IMPRESS USA INC 936 BARRACUDA ST TERMINAL ISLAND California 90731 6.15 

BERENFIELD CONTAINERS SE LTD 12180 UNIVERSITY CITY BLVD HARRISBURG North Carolina 28075 0 

GMVM-LANSING GRAND RIVER ASSEMBLY 920 TOWNSEND ST MAIL CODE: 489-LANSING Michigan 48921 3.55 

Page 8 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

KITZINGER COOPERAGE CORP 2529 E NORWICH AVE SAINT FRANCIS Wisconsin 53235 0 

ARMSTRONG HARDWOOD FLOORING CO 565 HARTCO DR ONEIDA Tennessee 37841 0 

HIRSH INDUSTRIES INC 1525 MCKEE RD DOVER Delaware 19904 0.0025 WORLDCOLOR - DYERSBURG DIV 2030 SYLVAN RD DYERSBURG Tennessee 38024 6.2595 

ESCO CORP 9098 EASTSIDE DR EXT NEWTON Mississippi 39345 6.312 JOHN DEERE HARVESTER WORKS EAST MOLINE 1100 13TH AVE EAST MOLINE Illinois 61244 0.3145 AKZO NOBEL SURFACE CHEMISTRY LLC 15200 ALMEDA RD HOUSTON Texas 77053 0.626 

QUEBECOR WORLD DIRECT-PETTY 420 W INDUSTRIAL AVE EFFINGHAM Illinois 62401 6.155 

PACKAGING DYNAMICS INC BAGCRAFT/PAPERCON DIV 3400 BAGCRAFT BLVD BAXTER SPRINGS Kansas 66713 0 

GMTG - SHREVEPORT ASSEMBLY 7600 GENERAL MOTORS BLVD SHREVEPORT Louisiana 71129 0.105 SENECA FOODS CORP CAN PLANT 3709 MILL ST MARION New York 14505 0 

NOVOLYTE TECHNOLOGIES 111 W IRENE RD ZACHARY Louisiana 70791 4.7 

CARRY-ON TRAILER CORP 1965 HWY 30 MISSOURI VALLEY Iowa 51555 0 

SILGAN CONTAINERS MANUFACTURING CORP 2501 165TH ST HAMMOND Indiana 46320 0 

METOKOTE CORP PLANT 15 312 SAVANNAH CEDAR FALLS Iowa 50613 0 

ELECTROPRIME INC 63 DIXIE HWY ROSSFORD Ohio 43460 0 

QUAD/GRAPHICS INC 56 DUPLAINVILLE RD SARATOGA SPRINGSNew York 12866 5.575 

FIBERMARK NORTH AMERICA INC 5492 BOSTWICK ST LOWVILLE New York 13367 0.0595 

BRADFORD WHITE CORP 200 LAFAYETTE ST MIDDLEVILLE Michigan 49333 0 

TECNOCAP LLC 2100 GRISWOLD NE WARREN Ohio 44483 2.074 

VON HOFFMANN GRAPHICS INC 1005 COMMERCIAL DR OWENSVILLE Missouri 65066 4.147 

U.S. AIR FORCE TINKER AFB OK 7701 ARNOLD ST SUITE 204 TINKER A F B Oklahoma 73145 1.6 HUNTER DOUGLAS TUPELO CENTER RT 2 LEE INDUSTRIAL PARK E SHANNON Mississippi 38868 0.274 CROWN FOOD PACKAGING 851 E MAPLE ST WINTER GARDEN Florida 34787 1.3385 

RR DONNELLEY LANCASTER EAST 216 GREENFIELD RD LANCASTER Pennsylvania 17601 5.319 ROLL COATER INC 4502 FREEDOM WAY WEIRTON West Virginia 26062 0 

CNH AMERICA LLC 1930 DES MOINES AVE BURLINGTON Iowa 52601 0.175 

NAVISTAR INC 6125 URBANA RD SPRINGFIELD Ohio 45502 0.6 

HUSQVARNA CONSUMER OUTDOOR PRODUCTS 172 OLD ELLOREE RD ORANGEBURG South Carolina 29116 0.115 

Page 9 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

PRECOAT METALS 25 NORTHGATE INDUSTRIAL DR GRANITE CITY Illinois 62040 4.4645 

LOGAN ALUMINUM INC US HWY 431 N RUSSELLVILLE Kentucky 42276 0.0475 

PPG INDUSTRIES,INC-SPRINGDALE COMPLEX 125 COLFAX ST SPRINGDALE Pennsylvania 15144 5.4805 

GREIF PACKAGING LLC 4300 W 130TH ST ALSIP Illinois 60803 1.5795 

USS - CLAIRTON WORKS 400 STATE ST CLAIRTON Pennsylvania 15025 5.5 

CREE INC 4600 SILICON DR DURHAM North Carolina 27703 1.34 TOYOTA MOTOR MANUFACTURING KENTUCKY INC 1001 CHERRY BLOSSOM WAY GEORGETOWN Kentucky 40324 0.125 

PRIME TANNING CO - HARTLAND 9 MAIN ST HARTLAND Maine 04943 0.1085 

NAZDAR SHAWNEE 8501 HEDGE LN TERRACE SHAWNEE Kansas 66227 1.623 

BALL METAL FOOD CONTAINER CORP 300 W GREGER RD OAKDALE California 95361 0.75 

3M CO - CORDOVA 22614 RT 84 N CORDOVA Illinois 61242 0.27 

OWENS CORNING VETROTEX LLC 4837 HWY 81 S STARR South Carolina 29684 0.5355 

NEW MILLENNIUM BUILDING SYSTEMS 100 DIUGUIDS LN SALEM Virginia 24153 5.296 

MID CONTINENT CABINETRY 67 E 2ND ST N COTTONWOOD Minnesota 56229 0.5285 

AVERY DENNISON - IBMD LENOIR 950 GERMAN ST LENOIR North Carolina 28645 3.73 

GREIF PACKAGING LLC 10850 STRANG RD LA PORTE Texas 77571 4.1335 

SILGAN CAN CO 6200 FRANKLIN BLVD SUITE #100 SACRAMENTO California 95824 4.864 

ENKEI AMERICA INC 2900 W INWOOD DR COLUMBUS Indiana 47201 0 

WORTHINGTON CYLINDERS WISCONSI N LLC 300 E BREED ST CHILTON Wisconsin 53014 0.9375 

METAL COATERS MISSISSIPPI 951 PRISOCK RD JACKSON Mississippi 39272 0 

MEDALLION CABINETRY INC 180 INDUSTRIAL BLVD WACONIA Minnesota 55387 0 

PRECOAT METALS 16402 JACINTOPORT BLVD HOUSTON Texas 77015 4.8145 

TRAD NA INC 210 BILL BRYAN BLVD HOPKINSVILLE Kentucky 42240 0.004 

AGY AIKEN LLC 2556 WAGENER RD AIKEN South Carolina 29801 2.9835 

GREENWICH INDUSTRIES LP CLARIN DIV 927 N SHORE DR LAKE BLUFF Illinois 60044 0.0505 

ROLL COATER 858 E HUPP RD LA PORTE Indiana 46350 0.0025 

ALCOA HOME EXTERIORS INC 2615 CAMPBELL RD SIDNEY Ohio 45365 0.6675 

SCHAEFFER MANUFACTURING 102 BARTON ST SAINT LOUIS Missouri 63104 4.8465 

ASHLEY INDUSTRIAL MOLDING INC 310 S WABASH ASHLEY Indiana 46705 0.475 

Page 10 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

US ARMY LAKE CITY ARMY AMMUNITION PLANT INTERSECTION OF MO HWYS 7 & 78 INDEPENDENCE Missouri 64051 1.3775 

INX DIGITAL INK CO 405 INDUSTRIAL WAY DIXON California 95620 4.7155 NAHAN PRINTING INC 7000 SAUKVIEW DR SAINT CLOUD Minnesota 56303 4.577 

AAP ST MARYS CORP 1100 MCKINLEY RD SAINT MARYS Ohio 45885 0.031 

ZURN INDUSTRIES LLC 1301 RASPBERRY ST ERIE Pennsylvania 16502 4.674 

DUPONT PONTCHARTRAIN WORKS 586 HWY 44 LA PLACE Louisiana 70068 0.005 

ARVINMERITOR HEAVY VEHICLE SYSTEMS LLC 801 RAILROAD AVE YORK South Carolina 29745 0.001 

OMG AMERICAS TWO MILE RUN RD FRANKLIN Pennsylvania 16323 0.025 

SABIC INNOVATIVE PLASTICS MT VERNON LLC 1 LEXAN LN MOUNT VERNON Indiana 47620 2.7 

GENERAL MOTORS WENTZVILLE ASSEMBLY 1500 E RT A WENTZVILLE Missouri 63385 0.85 

RUSKIN CO HWY 27 N GENEVA Alabama 36340 0.027 

ALLIANCE INDUSTRIES WAUPACA N 2467 VAUGHAN RD WAUPACA Wisconsin 54981 0.447 

GENIE INDUSTRIES SOUTH CAMPUS 18700 NE 65TH ST REDMOND Washington 98052 0.125 ENDICOTT INTERCONNECT TECHNOLOGIES INC 1093 CLARK ST ENDICOTT New York 13760 0.25 BROWN PRINTING CO 2300 BROWN AVE WASECA Minnesota 56093 4.2665 

BALL METAL BEVERAGE CONTAINER CORP 1800 REYNOLDS AVE KANSAS CITY Missouri 64120 4.15 

BATESVILLE MANUFACTURING INC 310 CROWN RD BATESVILLE Mississippi 38606 0.6345 

SILGAN CONTAINERS MANUFACTURING CORP N90 W14600 COMMERCE DR MENOMONEE FALLSWisconsin 53051 0 

GREIF PACKAGING LLC 695 LOUIS DR WARMINSTER Pennsylvania 18974 0.4005 

SEQUA COATINGS CORP-PRECOAT M ETALS DIV US HWY 12 AT RT 249 PORTAGE Indiana 46368 0.2925 

R R DONNELLEY & SONS CO DANVILLE DIV JOHN HILL BAILEY INDL PARK HWY 3DANVILLE Kentucky 40422 3.8845 

BROWN PRINTING CO 11595 MCCONNELL RD WOODSTOCK Illinois 60098 4.035 

SILGAN CONTAINER MANUFACTURING CORP 3250 PATTERSON RD RIVERBANK California 95367 0.218 QUEBECOR WORLD 8649 HACKS CROSS RD OLIVE BRANCH Mississippi 38654 0.375 

CLARIANT CORP - MOUNT HOLLY WEST PLANT 625 E CATAWBA AVE MOUNT HOLLY North Carolina 28120 0 

VAN CAN CO 10837 ETIWANDA AVE FONTANA California 92337 3.5 

WORLDCOLOR STILLWATER (WAS QUEBECOR WORLD - STILLWATER DIV)

100 W AIRPORT RD STILLWATER Oklahoma 74075 3.517 

PRO LINE PRINTING ARLINGTON 401 N GREAT SW PKWY ARLINGTON Texas 76011 3.8005 

ALERIS ROLLED PRODUCTS INC 1372 KY HWY 1957 LEWISPORT Kentucky 42351 0.125 

Page 11 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

NESTLE PURINA PETCARE 1000 HAMILTON RD WEIRTON West Virginia 26062 0.993 

RR DONNELLEY LOS ANGELES MANUFACTURING 19681 PACIFIC GATEWAY DR TORRANCE California 90502 3.706 BROWN PRINTING CO 668 GRAVEL PIKE EAST GREENVILLE Pennsylvania 18041 3.6115 

INLAND LABEL & MARKETING 2009 W AVE S LA CROSSE Wisconsin 54601 3.7245 

PHOENIX CONTAINER INC 1202 AIRPORT RD NORTH BRUNSWICKNew Jersey 08902 1.4665 

BETCO CORP 1001 BROWN AVE TOLEDO Ohio 43607 3.674 

FUJIFILM NORTH AMERICA CORP 20 W 14TH AVE NORTH KANSAS CIT Missouri 64116 0 

FORD MOTOR CO TWIN CITIES ASSEMBLY PLANT 966 S MISSISSIPPI RIVER BLVD SAINT PAUL Minnesota 55116 0.41 

AVERY DENNISON INDUSTRIAL PRODUCTS DIV 17700 FOLTZ PKWY STRONGSVILLE Ohio 44149 0.4595 

BATESVILLE MANUFACTURING INC -DOLL PLANT 1000 E PEARL ST BATESVILLE Indiana 47006 0.175 

KODAK COLORADO DIV 9952 EASTMAN PARK DR WINDSOR Colorado 80551 0 

MERIX CORP 1521 POPLAR LN FOREST GROVE Oregon 97116 0.0895 

SCHWAN'S GLOBAL SUPPLY CHAIN - SALINA KS 3019 SCANLAN SALINA Kansas 67401 0 

BWAY CORP BWAY PACKAGING DIV 8200 BROADWELL RD CINCINNATI Ohio 45244 3.1135 

APOLLO COLORS INC 1550 MOUND RD ROCKDALE Illinois 60436 0 

TTM PRINTED CIRCUIT GROUP - S TAFFORD DIV 4 OLD MONSON RD STAFFORD Connecticut 06075 0 

BON L MANUFACTURING CO 508 W WILSON ST KENTLAND Indiana 47951 0.33 

PONTIAC ASSEMBLY CENTER 2100 S OPDYKE RD PONTIAC Michigan 48341 0.335 

WORLDCOLOR LEBANON DIV 760 FUJITEC DR LEBANON Ohio 45036 2.938 

QUEBECOR WORLD INC WINCHESTER VIRGINIA 160 CENTURY LN STONEWALL INDU WINCHESTER Virginia 22603 3.202 

AK STEEL CORP - ZANESVI LLE WORKS 1724 LINDEN AVE ZANESVILLE Ohio 43701 0 

SHERWIN-WILLIAMS CO 2150 W SAND LAKE RD ORLANDO Florida 32809 0 

KAWASAKI MOTORS MANUFACTURING CORP USA 6600 NW 27TH ST LINCOLN Nebraska 68524 0.3235 

SILGAN CONTAINERS MANUFACTURING CORP 8673 LYONS-MARENGO RD LYONS New York 14489 0.6 

TYCO FIRE SUPPRESSION & BUILDING PRODUCTS 1 STANTON ST MARINETTE Wisconsin 54143 0.0065 

CROWN FOOD PACKAGING 10200 N LOMBARD ST PORTLAND Oregon 97203 1.191 

ST CHARLES OPERATIONS (TAFT/STAR) UNION CARBIDE CORP

355 LA HWY 3142 (GATE 1) TAFT Louisiana 70057 0.62 

CROWN EQUIPMENT CORP 2600 E STATE RD 240 GREENCASTLE Indiana 46135 0 

SILGAN CONTAINERS MANUFACTURING CORP 400 N 15TH ST ROCHELLE Illinois 61068 1.8115 

Page 12 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

3M CO - MENOMONIE 1425 STOKKE PKWY MENOMONIE Wisconsin 54751 0 

MERCK SHARP & DOHME CORP 2778 SE SIDE HWY ELKTON Virginia 22827 0.705 

DISC GRAPHICS 10 GILPIN AVE HAUPPAUGE New York 11788 0.7425 

DOW CHEMICAL CO 1790 BUILDING MIDLAND Michigan 48667 2.65 

PPG INDUSTRIES ARCHITECTURAL FINISHES 1020 OLYMPIC DR BATAVIA Illinois 60510 0 

ACCESS BUSINESS GROUP LLC 7575 FULTON ST E ADA Michigan 49355 2.815 

ITW DYMON 805 E OLD 56 HWY OLATHE Kansas 66061 0.8825 

MAXIM INTEGRATED PRODUCTS INC 9651 WESTOVER HILLS BLVD SAN ANTONIO Texas 78251 0 

SAPA EXTRUDER INC 2905 OLD OAKWOOD RD GAINESVILLE Georgia 30504 0 

U.S. AIR FORCE ROBINS AFB GA 775 MACON ST BUILDING 1555 ROBINS AFB Georgia 31098 1.597 

PRECOAT METALS 3399 DAVEY ALLISON BLVD HUEYTOWN Alabama 35023 2.209 

VERTIS COMMUNICATIONS 4051 FONDORF DR COLUMBUS Ohio 43228 2.579 

MAUSER CORP 14 CONVERY BLVD WOODBRIDGE New Jersey 07095 0.023 

MOTOR CASTINGS CO 1323 S 65TH MILWAUKEE Wisconsin 53214 0 

CURTIS METAL FINISHING CO 6645 SIMS DR STERLING HEIGHTS Michigan 48313 2.039 

TITAN COATINGS INC 2025 EXCHANGE PL BESSEMER Alabama 35023 2.85 

BALL METAL FOOD CONTAINER CORP 1200 S CRUTCHER ST SPRINGDALE Arkansas 72764 0.015 

MAXIM INTEGRATED PRODUCTS INC 3725 N FIRST ST SAN JOSE California 95134 2.785 

3M CO - HUTCHINSON 905/915 ADAMS ST SE HUTCHINSON Minnesota 55350 0 

MICHELIN NORTH AMERICA INC 5101 21ST ST TUSCALOOSA Alabama 35401 0.004 

GOODYEAR TIRE & RUBBER CO. AKRON TECHNICAL CENTER

200 S. MARTHA AVE AKRON Ohio 44309 0 

WORLDCOLOR ATGLEN 4581 LOWER VALLEY RD ATGLEN Pennsylvania 19310 2.5835 

RR DONNELLEY STRASBURG DIV ONE SHENANDOAH VALLEY DR STRASBURG Virginia 22657 2.6 RHODIA INC 2ND ST & BLUEBALL AVE MARCUS HOOK Pennsylvania 19061 0.161 

CENTRIA 530 N SECOND ST CAMBRIDGE Ohio 43725 1.3625 

BON L MANUFACTURING CO HWY 53 BONNELL RD CARTHAGE Tennessee 37030 0.9755 

MISSION KLEENSWEEP PRODUCTS INC 2434 BIRKDALE ST LOS ANGELES California 90031 2.6 

SOLIANT LLC 1872 HWY 9 BYPASS W LANCASTER South Carolina 29721 0.566 

GREIF INDUSTRIAL PACKAGING & SERVICES 7604 RAILROAD AVE WINFIELD Kansas 67156 0.255 

Page 13 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

KNS COMPANYS INC 475 RANDY RD CAROL STREAM Illinois 60188 0.5035 

BRILLION IRON WORKS INC 200 PARK AVE BRILLION Wisconsin 54110 2.0315 

TEXAS FINISHING CO 1801 SURVEYOR BLVD CARROLLTON Texas 75006 0 

WORLDCOLOR 451 INTERNATIONAL BLVD CLARKSVILLE Tennessee 37040 2.35 

BRUNSWICK CORP MERCURY MARINE DIV W6250 PIONEER RD FOND DU LAC Wisconsin 54935 0.2425 

DENSO MANUFACTURING TENNESSEE INC 1720, 1725, 1755 ROBERT C JACKSO MARYVILLE Tennesee 37801 0 

MASTER GUARD CORP 1200 E 8TH ST VEEDERSBURG Indiana 47987 0.024 

SANFORD LP 1 PENCIL ST SHELBYVILLE Tennessee 37160 0.125 

ABC COMPOUNDING CO INC 6970 JONESBORO RD MORROW Georgia 30260 0.0025 

ROPPE CORP 1602 N UNION ST FOSTORIA Ohio 44830 0.125 

AMERICAN COLOR GRAPHICS INC 215 N ZARFOSS DR YORK Pennsylvania 17404 2.073 

SUN CHEMICAL CORP 2445 PRODUCTION DR SAINT CHARLES Illinois 60174 0.299 

3M CO - BROWNWOOD 4501 HWY 377 S BROWNWOOD Texas 76801 0.065 

KIK (HOUSTON) INC 2921 CORDER ST HOUSTON Texas 77054 2.265 

SAFETY-KLEEN SYSTEMS INC 130 A FRONTAGE RD LEXINGTON South Carolina 29073 0 

KAWNEER CO INC 2785 MCCRACKEN RD HERNANDO Mississippi 38632 0.2475 

AMERICAN COLOR GRAPHICS - LUFKIN 3001 ATKINSON DR LUFKIN Texas 75901 2.009 

CENTURY INDUSTRIAL COATINGS I NC HWY 69 S JACKSONVILLE Texas 75766 0.089 

LEHIGH PRESS CADILLAC (DBA LEHIGH DIRECT DIVISION) 1900 S 25TH AVE BROADVIEW Illinois 60153 1.9755 MACDERMID PRINTING SOLUTIONS 260 S PACIFIC ST SAN MARCOS California 92078 0 

UNION CARBIDE CORP SOUTH CHARLESTON FACILITY 437 MACCORKLE AVE SW SOUTH CHARLESTOWest Virginia 25303 2.058 

THREE RIVERS ALUMINUM CO 71 PROGRESS AVE CRANBERRY TOWNSPennsylvania 16066 0.2195 

NCP COATINGS INC 225 FORT ST NILES Michigan 49120 2.1075 

PRECOAT METALS 4301 S SPRING AVE SAINT LOUIS Missouri 63116 0.57 

VERTIS COMMUNICATIONS 10911 GRANITE ST CHARLOTTE North Carolina 28273 1.841 

DUPONT YERKES PLANT 3115 RIVER RD BUFFALO New York 14207 0.039 

TORO CO 200 SIME AVE TOMAH Wisconsin 54660 0 

CADON PLATING CO 3715 11TH ST WYANDOTTE Michigan 48192 1.121 

WORLD COLOR PRESS 50 JOHN HANCOCK RD TAUNTON Massachusetts 02780 1.605 

Page 14 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

AVX CORP CONWAY 2875 HWY 501 E CONWAY South Carolina 29526 0.888 

SILGAN CONTAINERS MANUFACTURING CORP 2200 WILBUR AVE ANTIOCH California 94509 0 

STEELSCAPE INC 7001 ALLISON-BONNET MEMORIAL DFAIRFIELD Alabama 35064 0.0045 

BASF CORP - CLEAR LAKE PLANT 11200 BAY AREA BLVD PASADENA Texas 77507 1.95 

BOEING COMMERCIAL AIRPLANE GROUP NORTH BOEING FIELD (PART)

7500 E MARGINAL WAY S SEATTLE Washington 98108 0.1155 

RR DONNELLEY PINEVILLE 10519 INDUSTRIAL DR PINEVILLE North Carolina 28134 1.85 

THIRD COAST PACKAGING INC PEARLAND 1871 MYKAWA PEARLAND Texas 77581 0 

NOV TUBOSCOPE NAVASOTA 9574 FM 1227 NAVASOTA Texas 77868 0.8325 TYSON FRESH MEATS INC HWY 66 E & FARM RD 1912 AMARILLO Texas 79187 0.07 

TREND OFFSET PRINTING SERVICES INC 3791 CATALINA ST LOS ALAMITOS California 90720 1.8 

WARREN UNILUBE INC 1200 S 8TH ST WEST MEMPHIS Arkansas 72301 1.9085 

HYUNDAI MOTOR MANUFACTURING ALABAMA LLC 700 HYUNDAI BLVD MONTGOMERY Alabama 36105 1.2395 

PRIOR COATED METALS 2233 26TH ST SW ALLENTOWN Pennsylvania 18103 1.305 

KEYMARK CORP 1188 CAYADUTTA ST RT 334 FONDA New York 12068 0.007 

BUCKEYE INTERNATIONAL INC 2700 WAGNER PL MARYLAND HEIGHTSMissouri 63043 0.125 

AMERICAN COLOR GRAPHICS 810 E S ST MARENGO Iowa 52301 1.669 

HANNA STEEL CORP 3812 COMMERCE AVE FAIRFIELD Alabama 35064 0.6905 

DUPONT CHAMBERS WORKS RT 130 DEEPWATER New Jersey 08023 0.139 ASTRO COATINGS INC 27 MAIN ST STRUTHERS Ohio 44471 0.65 

IMPRESS USA INC 3030 BIRCH DR HALF MOON INDUST WEIRTON West Virginia 26062 0.006 

EASTMAN KODAK CO EASTMAN BUSINESS PARK 1669 LAKE AVE ROCHESTER New York 14652 0.001 

CUMMINS POWER GENERATION 1400 73RD AVE NE FRIDLEY Minnesota 55432 0.09 NOV TUBOSCOPE WEST LITTLE YORK COATING 12100 W LITTLE YORK RD HOUSTON Texas 77041 0.0535 

TTM TECHNOLOGIES INC 710 N 600 W LOGAN Utah 84321 0.12 

FORD MOTOR CO - OHIO ASSEMBLY PLANT 650 MILLER RD AVON LAKE Ohio 44012 1.65 

LION COPOLYMER LLC 5955 SCENIC HWY BATON ROUGE Louisiana 70805 0 

REICHHOLD INC 425 S PACE BLVD PENSACOLA Florida 32502 0.1065 J&M MANUFACTURING CO INC 284 RAILROAD ST FORT RECOVERY Ohio 45846 0 RR DONNELLEY 100 QUALITY CT CHARLESTOWN Indiana 47111 1.6325 

Page 15 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

BOEING COMMERCIAL AIRPLANE GROUP - RENTON 8TH & LOGAN AVE N RENTON Washington 98055 0.697 

GMC TRUCK GROUP ARLINGTON ASSEMBLY PLANT 2525 E ABRAMS ST ARLINGTON Texas 76010 0.5 

PRO LINE PRINTING / RR DONNELLEY 365 PARR CIR RENO Nevada 89512 1.5035 

TRELLEBORG COATED SYSTEMS US INC / GRACE ADVANCED MATERIALS

715 RAILROAD AVE & HWY 74 RUTHERFORDTON North Carolina 28139 0 

EASTMAN CHEMICAL CO TENNESSEE OPERATIONS 100 EASTMAN RD KINGSPORT Tennessee 37662 0.5725 

RR DONNELLEY VON HOFFMANN CORP 321 WILSON DR JEFFERSON CITY Missouri 65109 1.6195 

COMPLEMENTARY COATINGS CORP 308 OLD COUNTY RD EDGEWATER Florida 32132 1.639 

CHRYSLER STERLING HEIGHTS ASSEMBLY PLANT 38111 VAN DYKE STERLING HEIGHTS Michigan 48312 0.9 COLOR CORP OF AMERICA 1630 W HILL ST LOUISVILLE Kentucky 40210 0 

U S CHEMICAL 316 HART ST WATERTOWN Wisconsin 53094 0 

U.S. AIR FORCE OGDEN AIR LOGISTICS CENTER 7274 WARDLEIGH DR HILL AFB Utah 84056 0.8625 

AKZONOBEL AEROSPACE COATINGS 1 E WATER ST WAUKEGAN Illinois 60085 0.775 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

901 N GREENWOOD AVE KANKAKEE Illinois 60901 0.9585 

BENCHMARK ENERGY PRODUCTS LLC 4113 W INDUSTRIAL AVE MIDLAND Texas 79703 0.125 

IVC INDUSTRIAL COATINGS INC 2245-50 VALLEY AVE INDIANAPOLIS Indiana 46218 0.2955 VANEX INC 1700 S SHAWNEE ST MOUNT VERNON Illinois 62864 0 

SAPA INC COATINGS DIVSION 5325 NE SKYPORT WAY PORTLAND Oregon 97218 1.0905 

VEYANCE TECHNOLOGIES INC 2701 W OMAHA AVE NORFOLK Nebraska 68701 0.0615 

ARANDELL CORP N82 W13118 LEON RD MENOMONEE FALLSWisconsin 53051 1.418 

WHEELING CORRUGATING CO - BEECH BOTTOM PLANT 2481 RIVER RD WELLSBURG West Virginia 26070 0 

ZEP INC 1310 SEABOARD INDUSTRIAL BLVD ATLANTA Georgia 30318 0.1435 

CARDINAL ALUMINUM CO PLAN T 3 4005 OAKLAWN DR LOUISVILLE Kentucky 40219 0.05 

GREIF INDUSTRIAL PACKAGING & SERVICES LLC 8250 ALMERIA AVE FONTANA California 92335 0.1915 

DECOSTAR INDUSTRIES INC 1 DECOMA DR CARROLLTON Georgia 30117 0.125 

ALERIS ROLLED PRODUCTS INC 1 REYNOLDS RD ASHVILLE Ohio 43103 0.668 

MITSUBISHI MOTORS NORTH AMERICA INC 100 N MITSUBISHI MOTORWAY NORMAL Illinois 61761 1.41 

GATES CORP - CHARLESTON 1300 S PLANT RD CHARLESTON Missouri 63834 0.0795 

BRENNTAG SOUTHWEST INC HOUS TON 14826 HOOPER RD HOUSTON Texas 77047 0.02 

Page 16 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

CAMACO COLUMBUS MANUFACTURING 1851 E 32ND AVE COLUMBUS Nebraska 68601 0 ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

372 CLEVELAND ST ROCHESTER Pennsylvania 15074 0.53 

TAIYO AMERICA INC 2675 ANTLER DR CARSON CITY Nevada 89701 0.005 

W W HENRY 150 MOONEY DR BOURBONNAIS Illinois 60914 1.3725 

UNIVAR USA INC MORRISVILLE BRANCH 200 DEAN SIEVERS PL MORRISVILLE Pennsylvania 19067 0.002 

JOHN DEERE SEEDING & CYLINDER 501 RIVER DR MOLINE Illinois 61265 0 

CROWN AEROSOL PACKAGING 4TH ST & PARK AVE FARIBAULT Minnesota 55021 0.877 

BRENNTAG SOUTHWEST INC LANC ASTER 704 E WINTERGREEN RD LANCASTER Texas 75134 0.0175 

GM MLCG FAIRFAX ASSEMBLY 3201 FAIRFAX TRAFFICWAY KANSAS CITY Kansas 66115 0.0175 

ARR-MAZ CUSTOM CHEMICALS 4800 STATE RD 60 E MULBERRY Florida 33860 0.0625 

SILGAN WHITE CAP CORP 350 JAYCEE DR VALMONT INDUSTRIHAZLETON Pennsylvania 18201 0.7 

AKZO NOBEL COATINGS INC 1313 WINDSOR AVE COLUMBUS Ohio 43211 0.7545 

ARMSTRONG WORLD INDUSTRIES LANCASTER PLANT 1067 DILLERVILLE RD LANCASTER Pennsylvania 17603 0.8895 GENERAL MOTORS MLCG DETROIT-HAMTRAMCK ASSEM BLY CENTER

2500 E GENERAL MOTORS BLVD DETROIT Michigan 48211 1.15 

CHEMCOAT INC 2790 CANFIELDS LN MONTOURSVILLE Pennsylvania 17754 0.125 

PPG ARCHITECTURAL FINISHES EAST POINT 1377 OAKLEIGH DR EAST POINT Georgia 30344 0.001 

PARKER HANNIFIN TECH SEAL DIV 2600 WILCO BLVD WILSON North Carolina 27893 0 

DAIMLERCHRYSLER CORP TOLEDO ASSEMBLY PLANT 4000 STICKNEY AVE TOLEDO Ohio 43612 0.355 

SHEBOYGAN PAINT CO 608 CANAL ST CEDARTOWN Georgia 30125 0.687 

RR DONNELLEY & SONS CO 60 SECURITY DR AVON Connecticut 06001 1.2045 CONSOLIDATED SYSTEMS INC 650 ROSEWOOD DR COLUMBIA South Carolina 29201 0 

CHRYSLER BELVIDERE ASSEMBLY PLANT 3000 W CHRYSLER DR BELVIDERE Illinois 61008 0.12 

DURA COAT PRODUCTS INC 26655 PEOPLES RD MADISON Alabama 35756 1.2145 CLEVELAND STEEL CONTAINER - NI LES 115 ERIE ST NILES Ohio 44446 0.0025 

CCL CONTAINER AEROSOL DIV ONE LLODIO DR HERMITAGE Pennsylvania 16148 0.0935 

CATERPILLAR INC 3701 STATE RD 26 E LAFAYETTE Indiana 47905 0.0475 

GFX INTERNATIONAL 333 BARRON BLVD GRAYSLAKE Illinois 60030 0 

BEHR PROCESS CORP 3400 W GARRY AVE SANTA ANA California 92704 0.0035 

Page 17 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

WINSLOW-BROWNING INC 215 BROWNSVILLE AVE LIBERTY Indiana 47353 1.148 

CHEMTURA CORP - TAFT PLANT 471 HWY 3142 KILLONA Louisiana 70066 0.105 

J L CLARK INC 923 23RD AVE ROCKFORD Illinois 61104 0.304 

PRECOAT METALS 6754 SANTA BARBARA CT ELKRIDGE Maryland 21075 0 HARCROS CHEMICALS INC 5200 SPEAKER RD KANSAS CITY Kansas 66106 0.0175 

NICHOLS ALUMINUM ALABAMA INC 2001 HWY 20 W DECATUR Alabama 35601 0.913 

SONY ELECTRONICS INC 4275 W MAIN ST DOTHAN Alabama 36305 0 

GENTEK BUILDING PRODUCTS 11 CRAGWOOD RD AVENEL New Jersey 07001 0.2 

OHIO ART CO ONE TOY ST BRYAN Ohio 43506 0.8965 

RED SPOT WESTLAND INC 550 S EDWIN ST WESTLAND Michigan 48186 0.628 

TRELLEBORG OFFSHORE US RANKIN ROAD FACILITY 1902 RANKIN RD HOUSTON Texas 77073 1.1105 

INCHEM CORP 800 CEL-RIVER RD ROCK HILL South Carolina 29730 0.125 

HUNTSMAN PETROCHEMICAL LLC 3892 US HWY 90 DAYTON Texas 77535 0.001 

TEXAS INSTRUMENTS INC 12201 SW FWY MS600 STAFFORD Texas 77477 0.0025 

TESORO REFINING & MARKETING CO - MANDAN REFINERY 900 OLD RED TRAIL NE MANDAN North Dakota 58554 1.1 CANFIELD METAL COATING CORP 460 W MAIN ST CANFIELD Ohio 44406 0 BEAULIEU OF AMERICA PLANT 560-MODEL 950 RIVERBEND RD DALTON Georgia 30721 0 COOK COMPOSITES & POLYMERS CO 1415 STEELE AVE SW GRAND RAPIDS Michigan 49507 0.7325 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

701 SHILOH RD GARLAND Texas 75042 0.644 

POLYMERIC IMAGING INC 117 E 14TH AVE NORTH KANSAS CIT Missouri 64116 0 

CELLU TISSUE/CITYFOREST LLC 1215 WORDEN AVE E LADYSMITH Wisconsin 54848 0 

COMBE PRODUCTS INC EL DUQUE INDUSTRIAL PARK RD 97 NAGUABO Puerto Rico 00718 0 

CANBERRA CORP 3610 HOLLAND-SYLVANIA RD TOLEDO Ohio 43615 0.675 

NEXTEER AUTOMOTIVE CORP 3900 HOLLAND RD SAGINAW Michigan 48601 0.1045 

SPRAYLAT CORP CA 3465 S LA CIENAGA BLVD LOS ANGELES California 90016 0.52 

AKZONOBEL COATINGS INC 120 FRANKLIN RD PONTIAC Michigan 48341 0.105 

ROLL COATER INC 2604 RIVER RD HAWESVILLE Kentucky 42348 0 RED SPOT PAINT & VARNISH CO INC 1016 E COLUMBIA ST EVANSVILLE Indiana 47711 0.6065 

Page 18 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

STAR BUILDING SYSTEMS 151 JUDGE DON LEWIS RD ELIZABETHTON Tennessee 37643 0 

BOEING COMMERCIAL AIRPLANE GROUP PLANT 2 (PART) 7755 E MARGINAL WAY S SEATTLE Washington 98108 0.9965 

HYDRITE CHEMICAL CO 114 N MAIN ST COTTAGE GROVE Wisconsin 53527 0 

ARMSTRONG WORLD INDUSTRIES INC 4115 N PERKINS RD STILLWATER Oklahoma 74075 0.3885 

VERSO PAPER HOLDINGS LLC ANDROSCOGGIN MILL RILEY RD JAY Maine 04239 0.0125 

TTM TECHNOLOGIES-SANTA CLARA 407 MATHEW ST SANTA CLARA California 95050 0 

COOK COMPOSITES & POLYMERS CO 2434 HOLMES RD HOUSTON Texas 77051 0.9225 

IVC SOUTH 875 PROGRESS CENTER AVE LAWRENCEVILLE Georgia 30043 0.185 

HADCO (SANMINA) CORP - OWEGO DIV 1200 TAYLOR RD OWEGO New York 13827 0.009 

WATSON STANDARD CO (NEVILLE ISLAND PLANT) 2895 GRAND AVE NEVILLE ISLAND Pennsylvania 15225 0.8975 MAXIM INTEGRATED PRODUCTS 4350 S BELTWOOD PKWY DALLAS Texas 75244 0 SYNDICATE SYSTEMS INC 402 N MAIN ST MIDDLEBURY Indiana 46540 0 

B-WAY PACKAGING INC 6 LITHO RD TRENTON New Jersey 08648 0.085 

BEHR PROCESS CORP ALLENTOWN 7529 MORRIS CT BLDG 500 W PARK ALLENTOWN Pennsylvania 18106 0.021 

EVONIK DEGUSSA CORP TIPPECANOE LABORATORIES 1650 LILLY RD LAFAYETTE Indiana 47909 0.7 

SPRAYLAT CORP IL 1701 E 122-ND ST CHICAGO Illinois 60633 0.041 

NJT ENTERPRISES LLC 42400 MERRILL RD STERLING HEIGHTS Michigan 48314 0 

STEEL DYNAMICS INC 5134 LOOP RD JEFFERSONVILLE Indiana 47130 0 

ICL-IP AMERICA INC 11636 HUNTINGTON GALLIPOLIS FERRY West Virginia 25515 0.0635 

FLINT HILLS RESOURCES LP 13775 CLARK RD ROSEMOUNT Minnesota 55068 0.8 

COMPLEMENTARY COATINGS CORP 4701 O'DONNELL ST BALTIMORE Maryland 21224 0.8 

BERRYMAN PRODUCTS INC 3800 E RANDOL MILL RD ARLINGTON Texas 76011 0.8 IC OF OKLAHOMA LLC 2322 N MINGO RD TULSA Oklahoma 74116 0 

GENERAL MOTORS LLC BOWLING GREEN ASSEMBLY PLANT

600 CORVETTE DR BOWLING GREEN Kentucky 42101 0.135 

METALS USA BUILDING PRODUCTS 227 S TOWN E BLVD MESQUITE Texas 75149 0.391 

SUN CHEMICAL CORP 1380 FORD RD MAUMEE Ohio 43537 0.114 VISTA PAINT CORP 2020 E ORANGETHORPE AVE FULLERTON California 92831 0.673 UNITED PAINT & CHEMICAL 24671 TELEGRAPH RD SOUTHFIELD Michigan 48034 0.7525 

Page 19 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

DELEET MERCHANDISING 26 BLANCHARD ST NEWARK New Jersey 07105 0.375 

TEXAS TILE MANUFACTURING LLC 1705 N OLIVER HOUSTON Texas 77007 0.001 

HB FULLER 12110 HARLAND DR NE COVINGTON Georgia 30014 0.386 

LONGABERGER CO 5565 RAIDERS RD FRAZEYSBURG Ohio 43822 0.2325 

KAWNEER CO INC 7200 DOE AVE VISALIA California 93291 0.5005 

HUNT REFINING CO A CORP 1855 FAIRLAWN RD TUSCALOOSA Alabama 35401 0.7205 

RYCOLINE PRODUCTS LLC 5540 NW HWY CHICAGO Illinois 60630 0.108 

VEYANCE TECHNOLOGIES INC 400 N GOODYEAR RD MOUNT PLEASANT Iowa 52641 0.0005 

MARCUS PAINT CO 235 E MARKET ST LOUISVILLE Kentucky 40202 0.7 

WESTERN EXTRUSIONS CORP 1735 SANDY LAKE RD CARROLLTON Texas 75006 0.125 

ELEMENTIS SPECIALTIES 400 CLAREMONT AVE JERSEY CITY New Jersey 07304 0.2 

SPARTAN CHEMICAL CO INC 1110 SPARTAN DR MAUMEE Ohio 43537 0.0675 

KAWNEER CO INC 500 E 12TH ST BLOOMSBURG Pennsylvania 17815 0.117 

CLEVELAND STEEL CONTAINER - PE OTONE FACILITY 117 E LINCOLN ST PEOTONE Illinois 60468 0.008 

WEST PENN OIL CO, INC130130 2305 MARKET ST EXT WARREN Pennsylvania 16365 0.6945 TERNIUM USA INC 2500 RON BEAN BLVD SHREVEPORT Louisiana 71115 0.0165 SONOCO PRODUCTS CO 1854 CENTRAL FLORIDA PKWY ORLANDO Florida 32837 0.385 

FERRO GLASS & COLOR CORP W WYLIE AVE WASHINGTON Pennsylvania 15301 0.1255 

BJ CHEMICAL SERVICES 707 N LEECH HOBBS New Mexico 88240 0.0065 

FINISHES UNLIMITED INC 482 WHEELER RD SUGAR GROVE Illinois 60554 0.3325 

VANGUARD PAINTS & FINISHES INC 1409 GREENE ST MARIETTA Ohio 45750 0.648 

SYNGENTA CROP PROTECTION INC SAINT GABRIEL FACILITY

3905 HWY 75 SAINT GABRIEL Louisiana 70776 0.249 

SILGAN CONTAINERS MANUFACTURING CORP 12130 LYNN AVE S SAVAGE Minnesota 55378 0 

CRYSTAL FINISHING SYSTEMS INC 2608 ROSS AVE SCHOFIELD Wisconsin 54476 0 

HERCULES INC KENEDY TEXAS ONE MILL ST KENEDY Texas 78119 0.602 

BASF CORP 1175 MARTIN ST GREENVILLE Ohio 45331 0.12 

CENTRIA 500 PERTH DR NEW ECONOMY BUS AMBRIDGE Pennsylvania 15003 0 

TRINKOTE INDUSTRIAL FINISHES INC 1800 PARK PL AVE FORT WORTH Texas 76110 0 

ALERIS ROLLED PRODUCTS INC 3321 DURHAM RD ROXBORO North Carolina 27573 0.0025 

Page 20 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

CHROMASOURCE INC 2433 S CR 600 E COLUMBIA CITY Indiana 46725 0 

MULTICIRCUITS 2301 UNIVERSAL ST OSHKOSH Wisconsin 54903 0.619 

TCI COATINGS INC 4501 BRADLEY ST LUBBOCK Texas 79415 0.616 

BRENNTAG SOUTHWEST INC ST GABRIEL 7200 HWY 74 SAINT GABRIEL Louisiana 70776 0.0075 GREIF INDUSTRIAL PACKAGING & SERVICES LLC 10700 STRANG RD LA PORTE Texas 77571 0.595 

ROCK TENN CO 2301 S 21ST ST CLINTON Iowa 52732 0 

ASHLAND DISTRIBUTION 8500 S WILLOW SPRINGS RD WILLOW SPRINGS Illinois 60480 0.538 

CLEVELAND STEEL CONTAINER CORP - STREETSBORO PLANT

10048 AURORA-HUDSON RD STREETSBORO Ohio 44241 0.006 

BECKER SPECIALTY CORP 15310 ARROW BLVD FONTANA California 92335 0.0285 

COMPLEX CHEMICALS CO INC MADISON PARISH INDUSTRIAL PARKTALLULAH Louisiana 71282 0.3 

NICHOLS ALUMINUM DAVENPORT 1725 ROCKINGHAM RD DAVENPORT Iowa 52802 0.159 

SUPERIOR OIL CO INC RECLAIMED ENERGY DIV 1500 WESTERN AVE CONNERSVILLE Indiana 47331 0.041 

SOUTHERN CLAY PRODUCTS INC 1335 S 13TH ST LOUISVILLE Kentucky 40210 0.0025 

ALUMAX MILL PRODUCTS INC 300 ALUMAX DR TEXARKANA Texas 75501 0 

CHRYSLER GROUP LLC STERLING STAMPING PLANT (PART)

35777 VAN DYKE STERLING HEIGHTS Michigan 48312 0.55 

HB FULLER CO 4440 MALSBARY RD BLUE ASH Ohio 45242 0.545 

BRADLEY COATINGS GROUP 608 W CRAWFORD AVE CONNELLSVILLE Pennsylvania 15425 0.389 

HOVENSA LLC 1 ESTATE HOPE CHRISTIANSTED Virgin Islands 00820 0.351 

FLINT GROUP NORTH AMERICA CORP 104 NATIONAL DR ANNISTON Alabama 36207 0.265 

GLASS COATINGS & CONCEPTS 300 LAWTON AVE MONROE Ohio 45050 0.5245 

NAPCO INC 125 MCFANN RD VALENCIA Pennsylvania 16059 0.48 

LEVLAD 9200 MASON AVE CHATSWORTH California 91311 0.0005 

ARROW GROUP INDUSTRIES INC 1 THIRD AVE HASKELL New Jersey 07420 0.0025 

RADIATOR SPECIALTY CO 600 RADIATOR RD INDIAN TRAIL North Carolina 28079 0.161 

NB COATINGS INC 2701 E 170TH ST LANSING Illinois 60438 0.315 DUBOIS CHEMICALS INC 3630 E KEMPER RD SHARONVILLE Ohio 45241 0 

FORREST PAINT CO 1011 MCKINLEY ST EUGENE Oregon 97402 0.206 

LOCKHEED MARTIN AERONAUTICS CO 1011 LOCKHEED WAY MZ 6607 PALMDALE California 93599 0.0715 

Page 21 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

INEOS OXIDE A DIV OF INEOS AMERICAS LLC 21255A HWY 1 S PLAQUEMINE Louisiana 70765 0.4805 

PPG INDUSTRIES ARCHITECTURAL FINISHES 1886 LYNNBURY WOODS RD DOVER Delaware 19904 0.0025 

BRIGHTSMITH LLC 120 ENTERPRISE AVE MORRISVILLE Pennsylvania 19067 0.1025 

CLARIANT CORP MARTIN PLANT 788 CHERT QUARRY RD MARTIN South Carolina 29836 0.125 

STEELSCAPE 222 W KALAMA RIVER RD KALAMA Washington 98625 0.003 

PPG INDUSTRIES INC 500 PITTSBURGH AVE MCCARRAN Nevada 89434 0 

ARCADIA INC 3225 E WASHINGTON BLVD VERNON California 90023 0.125 

SILBOND CORP 9901 SAND CREEK HWY WESTON Michigan 49289 0.125 

RUST-OLEUM CORP 8105 95TH ST PLEASANT PRAIRIE Wisconsin 53158 0.125 

SC JOHNSON & SON INC WAXDALE FACILITY 8311 16TH ST STURTEVANT Wisconsin 53177 0.125 

DERRICK CORP 3350 UNION RD CHEEKTOWAGA New York 14225 0 

HEXION SPECIALTY CHEMICALS INC 8600 W 71ST ST BEDFORD PARK Illinois 60501 0 EXXONMOBIL CHEMICAL BATON ROUGE CHEMICAL PLANT 4999 SCENIC HWY BATON ROUGE Louisiana 70805 0.245 

BECKER SPECIALTY CORP 2500 DELTA LN ELK GROVE VILLAGEIllinois 60007 0.005 

TTM TECHNOLOGIES INC 234 CASHMAN DR CHIPPEWA FALLS Wisconsin 54729 0 

PARKER HANNIFIN 400 S ST MC COOK Nebraska 69001 0 

ENGINEERED POLYMER SOLUTIONS I NC D/B/A VALSPAR COATINGS

90 CARSON RD BIRMINGHAM Alabama 35215 0.125 

UNIVAR USA INC SALEM BRANCH COLONIAL RD SALEM Massachusetts 01970 0.001 

SHERWIN-WILLIAMS CO 2802 W MILLER RD GARLAND Texas 75041 0.003 

SNAP-ON TOOLS MANUFACTURING CO 2600 US HWY 18 E ALGONA Iowa 50511 0.0055 

SKF SEALING SOLUTIONS 900 N STATE ST ELGIN Illinois 60123 0 

IVC INDUSTRIAL COATINGS INC 550-560 W CENTENNIAL BLVD CASA GRANDE Arizona 85222 0.091 UNIVERSAL CHEMICALS & COATINGS INC 1124 ELMHURST RD ELK GROVE VILLAGEIllinois 60007 0 

DUPONT MOUNT CLEMENS PLANT 400 GROESBECK HWY MOUNT CLEMENS Michigan 48043 0.0005 

NAZDAR CHICAGO 1087 N N BRANCH ST CHICAGO Illinois 60622 0.131 

APOLLO CHEMICAL 2001 WILLOW SPRINGS LN BURLINGTON North Carolina 27215 0.14 

ROHM & HAAS CHEMICALS LLC KNOXVILLE SITE 730 DALE AVE KNOXVILLE Tennessee 37921 0.002 

PFI INC 9215 SANTA FE SPRINGS RD SANTA FE SPRINGS California 90670 0.42 

Page 22 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

SILGAN WHITE CAP CORP 1701 WILLIAMSBURG PIKE RICHMOND Indiana 47375 0.055 

STANDARD PAINTS INC 940 S 6TH AVE MANSFIELD Texas 76063 0 

MUTI-PACK LLC 8372 N STEVEN RD MILWAUKEE Wisconsin 53223 0.415 

UNITED STATES ALUMINUM CORP 200 SINGLETON DR WAXAHACHIE Texas 75165 0.3775 

AMERIMAX HOME PRODUCTS INC 450 RICHARDSON DR LANCASTER Pennsylvania 17603 0.0115 

STP PRODUCTS MANUFACTURING CO 477 LEXINGTON AVE PAINESVILLE Ohio 44077 0.298 

DIAMOND VOGEL PAINTS 5111 E 36TH ST N TULSA Oklahoma 74115 0.008 

AMERICAN METALS CORP 1000 CROCKER RD WESTLAKE Ohio 44145 0 

FORBO ADHESIVES LLC 7440 W DUPONT RD MORRIS Illinois 60450 0.3905 ROLLEX CORP 800 CHASE AVE ELK GROVE VILLAGEIllinois 60007 0 

GSP MARKETING TECHNOLOGIES 5400 140TH AVE N CLEARWATER Florida 33760 0.384 

NALCO CO TULSA PLANT 102 6717 S 61ST W AVE TULSA Oklahoma 74131 0.0015 

EXXONMOBIL REFINING & SUPPLY BATON ROUGE REFINERY

4045 SCENIC HWY BATON ROUGE Louisiana 70805 0.175 

BASF CORP 1609 BIDDLE AVE WYANDOTTE Michigan 48192 0.375 

INTERNATIONAL PAINT LLC 6001 ANTOINE DR HOUSTON Texas 77091 0.0025 

TYSON FRESH MEATS INC JOSLIN IL HWY 92 & I-88 28424 38TH AVE N HILLSDALE Illinois 61257 0.0125 

FIBRO CHEM LLC 1804 KIMBERLY PARK DR DALTON Georgia 30720 0.125 

TOWER PRODUCTS INC 2703 FREEMANSBURG AVE EASTON Pennsylvania 18045 0.375 

RODDA PAINT CO 6123 N MARINE DR PORTLAND Oregon 97203 0.373 

QUEST CHEMICAL CORP 12255 FM 529 HOUSTON Texas 77041 0.375 

PARISER INDUSTRIES INC 91 MICHIGAN AVE PATERSON New Jersey 07503 0.375 

HILLYARD INDUSTRIES INC 402 N 3TH ST SAINT JOSEPH Missouri 64501 0.334 

SIKA CORP SIKA SARNAFIL DIV 100 DAN RD CANTON Massachusetts 02021 0 

NASCOTE INDUSTRIES 18310 ENTERPRISE AVE NASHVILLE Illinois 62263 0.1275 

MASCO RETAIL CABINET GROUP LLC 423 HOPEWELL RD WAVERLY Ohio 45690 0.0055 

FULLER BRUSH CO ONE FULLER WAY GREAT BEND Kansas 67530 0.1185 

WATSON LABORATORIES INC UTAH 575, 577, 579 CHIPETA WAY SALT LAKE CITY Utah 84108 0.353 

SHERWIN-WILLIAMS AUTOMOTIVE FINISHES CORP 395 BOGGS LN - S RICHMOND Kentucky 40475 0.32 

Page 23 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

1717 ENGLISH RD HIGH POINT North Carolina 27261 0.0635 

NELCO PRODUCTS INC 1107 E KIMBERLY ANAHEIM California 92801 0.027 ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

5400 23RD AVE MOLINE Illinois 61265 0.207 

ROHM & HAAS CHEMICALS LLC 200 RT 413 BRISTOL Pennsylvania 19007 0.0645 HERITAGE-WTI INC 1250 ST GEORGE ST EAST LIVERPOOL Ohio 43920 0.005 ROLL COATER INC 5888 E COUNTY RD 180 BLYTHEVILLE Arkansas 72315 0 ENERGIZER BATTERY MANUFACTURING INC 75 SWANTON RD SAINT ALBANS Vermont 05478 0.0025 ASHLAND DISTRIBUTION 3300 BALL ST BIRMINGHAM Alabama 35234 0.2985 ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

411 N DARLING FREMONT Michigan 49412 0.31 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

1647 ENGLISH RD HIGH POINT North Carolina 27261 0.0635 

HB FULLER 10500 INDUSTRIAL AVE ROSEVILLE California 95678 0.008 PACKAGING CORP OF AMERICA COUNCE MILL HWY 57 COUNCE Tennessee 38326 0.0205 KIK-SOCAL INC 9028 DICE RD SANTA FE SPRINGS California 90670 0.3255 ENTHONE INC 350 FRONTAGE RD WEST HAVEN Connecticut 06516 0.006 PILOT CHEMICAL CO 11623 N HOUSTON ROSSLYN RD HOUSTON Texas 77086 0.31 METAL COATERS OF CALIFORNIA INC 9133 CENTER AVE RANCHO CUCAMON California 91730 0.0285 PPG INDUSTRIES OHIO INC (CL) 3800 W 143 ST CLEVELAND Ohio 44111 0.001 ET PRODUCTS CO INC 747 DOUGLAS RD BREMEN Indiana 46506 0 DUCKBACK PRODUCTS 2644 HEGAN LN CHICO California 95928 0.298 SIERRA CORP 11400 W 47TH ST MINNETONKA Minnesota 55343 0.2975 SUMTER COATINGS INC 2410 HWY 15S SUMTER South Carolina 29150 0.0625 LINETEC 725 S 75TH AVE WAUSAU Wisconsin 54401 0.0205 CERTIFIED ENAMELING INC 3342 EMERY ST LOS ANGELES California 90023 0 CROWN CORK & SEAL CO (USA) INC CROWN CLOSURES DIV

940 MILL PARK DR LANCASTER Ohio 43130 0 

PPG ARCHITECTURAL FINISHES INC 400 S 13TH ST LOUISVILLE Kentucky 40203 0 CELLO PROFESSIONAL PRODUCTS 1354 OLD POST RD HAVRE DE GRACE Maryland 21078 0.2795 FORD MOTOR CO CHICAGO ASSEMBLY 12600 S TORRENCE AVE CHICAGO Illinois 60633 0.28 

Page 24 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

SERIGRAPH INC 3801 E DECORAH RD WEST BEND Wisconsin 53095 0.0455 

VIDEOJET TECHNOLOGIES INC 1855 ESTES AVE ELK GROVE VILLAGEIllinois 60007 0 

QUANTUM MARKETING INC 3606 CRAFTSMAN BLVD LAKELAND Florida 33803 0.272 

FUCHS LUBRICANTS CO-CORPORATE OFFICE 17050 S LATHROP AVE HARVEY Illinois 60426 0.2675 

HELEN,INC DBA ENVIRONMENTAL COATINGS,INC 6450 HANNA LAKE AVE SE CALEDONIA Michigan 49316 0.2 

SEQUA COATINGS CORP PRECOAT METALS DIV 3500 WALNUT ST MC KEESPORT Pennsylvania 15132 0.2105 

OLDCASTLE BUILDING ENVELOPE TENNESSEE FACILITY 920 POTTERTOWN RD MIDWAY Tennessee 37809 0 

HARLEY-DAVIDSON MOTOR CO OPERATIONS INC 1425 EDEN RD YORK Pennsylvania 17402 0.2365 

ASHLAND DISTRIBUTION CO 395 JAMES AVE SAINT PAUL Minnesota 55102 0.248 

GATES CORP 630 US HWY 150 E GALESBURG Illinois 61401 0 

HEXION SPECIALTY CHEMICALS INC 400 E COTTAGE PL CARPENTERSVILLE Illinois 60110 0.0645 

SHERWIN-WILLIAMS CO 180 CANAL ST TERRE HAUTE Indiana 47808 0.0165 

ASHLAND DISTRIBUTION 2315 CLIFTON AVE NASHVILLE Tennessee 37209 0.2435 CHASE PRODUCTS CO 2727 GARDNER RD BROADVIEW Illinois 60155 0.0015 

MOC PRODUCTS CO INC 12306 MONTAGUE ST PACOIMA California 91331 0.125 

BF GOODRICH TIRE MANUFACTURING 18906 US 24 E WOODBURN Indiana 46797 0.0025 

BACHMAN SERVICES INC 2220 S PROSPECT OKLAHOMA CITY Oklahoma 73129 0.125 

ASHLAND DISTRIBUTION CO 350 ROOSEVELT AVE CARTERET New Jersey 07008 0.229 

MISCO PRODUCTS CORP 1048 STINSON DR READING Pennsylvania 19605 0.125 

YENKIN-MAJESTIC PAINT CORPORAT ION 1920 LEONARD AVE COLUMBUS Ohio 43219 0.125 

QUANTUM COATINGS INC 1337 N WOOD BRANCH DR CHARLOTTE North Carolina 28273 0.125 

HONDA MANUFACTURING OF INDIANA LLC 2755 N MICHIGAN AVE GREENSBURG Indiana 47240 0.125 

MALCO PRODUCTS INC 361 FAIRVIEW AVE BARBERTON Ohio 44203 0.125 UNIVAR USA INC BERKELEY 8925 SEEGER INDUSTRIAL DR BERKELEY Missouri 63134 0.125 

CHEMICAL SPECIALISTS & DEVELOPMENT INC 9733 MEADOR RD CONROE Texas 77303 0.125 

EQUILON CARSON TERMINAL 20945 S WILMINGTON AVE CARSON California 90810 0.125 

PREMIER INK SYSTEMS INC 10420 N STATE ST HARRISON Ohio 45030 0.125 

PROCLEAN OF ARIZONA INC 4315 W VAN BUREN PHOENIX Arizona 85043 0 

UNIVAR USA INC METRO BLVD 2646 METRO BLVD MARYLAND HEIGHTSMissouri 63043 0.125 

Page 25 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

BERGQUIST CO 301 WASHINGTON ST CANNON FALLS Minnesota 55009 0.125 REICHHOLD INC 249 ST LOUIS AVE VALLEY PARK Missouri 63088 0.125 

CPJ TECHNOLOGIES 200 TANNER DR TAYLORS South Carolina 29687 0.125 ASHLAND DISTRIBUTION CO 1610 E HIGHLAND RD TWINSBURG Ohio 44087 0.229 

EFI / INKWARE 189 WAUKEWAN ST MEREDITH New Hampshire 03253 0 

FLINT GROUP NORTH AMERICA 4675 W PARK DR ATLANTA Georgia 30339 0.12 

ATMI MATERIALS LTD 706 HOUSTON CLINTON DR BURNET Texas 78611 0.051 

CAR PRODUCTS INC 630 BEAULIEU ST HOLYOKE Massachusetts 01040 0.236 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

347 CENTRAL AVE BOWLING GREEN Kentucky 42101 0.1285 

WARREN STAMPING PLANT (PART) 22800 MOUND RD WARREN Michigan 48091 0.23 

METAL COATERS OF GEORGIA 1150 MARIETTA INDUSTRIAL DR NE MARIETTA Georgia 30062 0.003 

CLEARWATER INTERNATIONAL LLC 4420 S FLORES ELMENDORF Texas 78112 0.0005 

COSMETIC LABORATORIES OF AMERICA 20245 SUNBURST ST CHATSWORTH California 91311 0 

FLUID ROUTING SOLUTIONS 1921 N BROAD ST LEXINGTON Tennessee 38351 0 

PERMA-PIPE OIL & GAS 5008-11 CURTIS LN NEW IBERIA Louisiana 70560 0.22 

MARY KAY INC 1330 REGAL ROW DALLAS Texas 75247 0.0005 

INTERNATIONAL EXTRUSION CORP TEXAS 202 SINGLETON DR WAXAHACHIE Texas 75165 0 

COLWELL INC 231 S PROGRESS DR E KENDALLVILLE Indiana 46755 0.19 ACTEGA KELSTAR INC 1050 TAYLORS LN CINNAMINSON New Jersey 08077 0.0015 GUARDIAN AUTOMOTIVE - MOREHEAD PLANT 200 GUARDIAN AVE MOREHEAD Kentucky 40351 0 

ASHLAND DISTRIBUTION CO 4550 NE EXPRESSWAY DORAVILLE Georgia 30340 0.1555 

CHAMPION TECHNOLOGIES INC 3303 HWY 135 N KILGORE Texas 75662 0.194 

RHODIA INC 577 BANKHEAD HWY WINDER Georgia 30680 0.16 

ROCKLINE INDUSTRIES 1113 MARYLAND AVE SHEBOYGAN Wisconsin 53081 0.193 

FIRST AMERICAN RESOURCES CO 2030 RIVERVIEW INDUSTRIAL DR MABLETON Georgia 30126 0 

SASOL NORTH AMERICA INC LAKE CHARLES CHEMICAL COMPLEX

2201 OLD SPANISH TRAIL WESTLAKE Louisiana 70669 0.124 

RUDD CO INC 1141 NW 50TH ST SEATTLE Washington 98107 0.175 

ASHLAND DISTRIBUTION 7710 POLK ST SAINT LOUIS Missouri 63111 0.1845 

CURTIS METAL FINISHING CO 9917 N ALPINE MACHESNEY PARK Illinois 61115 0.1325 

Page 26 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

TRITECH COATINGS CORP 1378 KINGSLAND AVE PAGEDALE Missouri 63133 0.1585 

ASHLAND DISTRIBUTION CO GARLAND TX 3101 WOOD DR GARLAND Texas 75041 0.151 

JAMESTOWN COATING TECHNOLOGIES 108 MAIN ST JAMESTOWN Pennsylvania 16134 0.1795 

NALCO CO PLANT 106 7701 US HWY 90A SUGAR LAND Texas 77478 0 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

1991 S WHEELING RD WHEELING Illinois 60090 0.0635 

ASHLAND INC - CHANDLER 6839 W CHICAGO ST CHANDLER Arizona 85226 0.149 

PLAZE INC 113 BOLTE LN SAINT CLAIR Missouri 63077 0.1745 

ASHLAND DISTRIBUTION CO 11109 S CHOCTAW DR BATON ROUGE Louisiana 70815 0.1625 

BYK USA INC 524 S CHERRY ST WALLINGFORD Connecticut 06492 0.17 

DUPONT FRONT ROYAL PLANT 7961 WINCHESTER RD FRONT ROYAL Virginia 22630 0.0005 

SHERWIN-WILLIAMS CO 1891 DUFFY RD FERNLEY Nevada 89408 0.0005 

ANCHOR PAINT MANUFACTURING CO INC 6707 E 14TH ST TULSA Oklahoma 74112 0.167 

JOHNSONDIVERSEY INC 8311 16TH ST STURTEVANT Wisconsin 53177 0.0255 

BEHR PROCESS CORP - CHICAGO 270 STATE ST CHICAGO HEIGHTS Illinois 60411 0.048 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

188 SIDE TRACK DR STATESVILLE North Carolina 28625 0.0635 

SONOCO FLEXIBLE PACKAGING 6502 S US HWY 31 N EDINBURGH Indiana 46124 0 

STOUSE INC 300 NEW CENTURY PKWY NEW CENTURY Kansas 66031 0.154 

DUPONT FORT MADISON PLANT 801 - 35TH ST FORT MADISON Iowa 52627 0 

WARREN OIL CO - NC 2340 US 301 N DUNN North Carolina 28335 0.1525 

HENTZEN COATINGS,INC BATAVIA FACILITY 1500 LATHEM ST BATAVIA Illinois 60510 0.151 

ROHM & HAAS ELECTRONIC MATERIA LS LLC 455 FOREST ST MARLBOROUGH Massachusetts 01752 0.0025 

BAKER PETROLITE CORP 9100 W 21ST ST SAND SPRINGS Oklahoma 74063 0.103 SUPERIOR SOLVENTS & CHEMICALS 320 NORTHPOINTE DR FAIRFIELD Ohio 45014 0.0365 

TNEMEC CO INC 123 W 23RD AVE NORTH KANSAS CIT Missouri 64116 0 

PPG INDUSTRIES OHIO INC CIRCLEVILLE OH 559 PITTSBURGH RD CIRCLEVILLE Ohio 43113 0.0345 MT ELLIOTT TOOL & DIE MANUFACTURING (PART) 3675 E OUTER DR DETROIT Michigan 48234 0.145 

DYCO PAINTS INC 5850 ULMERTON RD CLEARWATER Florida 33760 0 

MID-STATES PAINT & CHEMICAL CO 9315 WATSON INDUSTRIAL PARK CRESTWOOD Missouri 63126 0.1415 

Page 27 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

DOW CHEMICAL CO - LOUISIANA OPERATIONS 21255 LA HWY 1 S PLAQUEMINE Louisiana 70765 0.139 

ASHLAND DISTRIBUTION 2351 CHANNEL AVE MEMPHIS Tennessee 38113 0.1225 

AMREP INC 990 INDUSTRIAL PARK DR MARIETTA Georgia 30062 0.0435 ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

3050 HANFORD DR LEBANON Pennsylvania 17046 0.0635 

NALCO CO - ODESSA PLANT 114 12205 W COUNTY RD 125 ODESSA Texas 79765 0 

VARN INTERNATIONAL 1333 N KIRK RD BATAVIA Illinois 60510 0.125 

WATSON STANDARD CO HARWICK PLANT 616 HITE RD HARWICK Pennsylvania 15049 0.1165 

POWER SERVICE PRODUCTS INC 513 PEASTER HWY WEATHERFORD Texas 76086 0.0025 

BASF CORP 3455 SOUTHPORT RD SPARTANBURG South Carolina 29302 0.125 

PERMATEX SOLON 6875 PARKLAND BLVD SOLON Ohio 44139 0.0025 

CONOCOPHILLIPS PONCA CITY REFINERY 1000 S PINE ST PONCA CITY Oklahoma 74601 0.0025 CONOCOPHILLIPS OKLAHOMA CITY PRODUCTS TERMINAL 4600 NE 10TH ST OKLAHOMA CITY Oklahoma 73117 0.0025 GEORGE S COYNE CHEMICAL CO INC 3015 STATE RD CROYDON Pennsylvania 19021 0.125 

TAKASAGO INTERNATIONAL CORP (USA) 267 UNION ST NORTHVALE New Jersey 07647 0.125 

BRYCE CO LLC 4505 OLD LAMAR AVE MEMPHIS Tennessee 38118 0 

CHEMICALS INC 12321 HATCHERVILLE RD BAYTOWN Texas 77520 0.125 COASTAL CHEMICAL CO LLC 3520 VETERANS MEMORIAL BLVD ABBEVILLE Louisiana 70510 0.125 OAKLEY INC 1 ICON FOOTHILL RANCH California 92610 0.0025 

GE WATER & PROCESS TECHNOLOGIES ORANGE FACILITY 3901 WILLIAMS DR ORANGE Texas 77630 0.125 

BRENNTAG GREAT LAKES LLC 14765 W BOBOLINK AVE MENOMONEE FALLSWisconsin 53051 0.0025 

RESEARCH SOLVENTS & CHEMICALS INC 402 INDUSTRIAL PARK DR PELHAM Alabama 35124 0.125 

RESEARCH SOLVENTS & CHEMICALS INC 133 BAIN DR LA VERGNE Tennessee 37086 0.125 UNITED LABORATORIES INC 320 37TH AVE SAINT CHARLES Illinois 60174 0.125 

RR STREET & CO INC 2353 S BLUE ISLAND AVE CHICAGO Illinois 60608 0.0025 

NICCA USA INC 1044 S NELSON RD FOUNTAIN INN South Carolina 29644 0.0025 

ELANTAS PDG INC 5200 N SECOND ST SAINT LOUIS Missouri 63147 0.0025 

HARCROS CHEMICALS INC 4606 NEW W DR PASADENA Texas 77507 0.0345 

ACTON TECHNOLOGIES INC 100 THOMPSON ST PITTSTON Pennsylvania 18640 0.125 

Page 28 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

AKCROS CHEMICALS INC 500 JERSEY AVE NEW BRUNSWICK New Jersey 08901 0 

MAGNABLEND INC LIQUID PLANT 100 W STERRETT RD WAXAHACHIE Texas 75165 0.125 

KALCOR COATINGS CO 37721 STEVENS BLVD WILLOUGHBY Ohio 44094 0.125 

DANLIN INDUSTRIES CORP 23737 HWY 47 THOMAS Oklahoma 73669 0.125 

UNIVAR USA INC DALLAS DAN MORTON FACILITY 3636 DAN MORTON DR DALLAS Texas 75236 0.125 

TYSON FRESH MEATS INC HWY 50 W HOLCOMB Kansas 67851 0.125 

NOV TUBOSCOPE HOLMES ROAD 2811 HOLMES RD HOUSTON Texas 77051 0.125 

SICPA SECURINK CORP 8000 RESEARCH WAY SPRINGFIELD Virginia 22153 0.125 

TRANS CHEMICAL INC 419 E DE SOTO AVE SAINT LOUIS Missouri 63147 0.125 

JASPER RUBBER PRODUCTS INC 1010 FIRST AVE JASPER Indiana 47546 0 

CLEANING SYSTEMS INC 1997 AMERICAN BLVD DE PERE Wisconsin 54115 0.125 

CHEMETALL US INC 13177 HURON RIVER DR ROMULUS Michigan 48174 0 

CERAM-TRAZ CORP CERAMIC INDL COATINGS (DBA) 325 HWY 81 OSSEO Minnesota 55369 0.125 

COLUMBIA PAINT CORP 641 JACKSON AVE HUNTINGTON West Virginia 25704 0.125 

INX INTERNATIONAL INK CO 1000 MAPLE AVE HOMEWOOD Illinois 60430 0 

W M BARR & CO 2105 CHANNEL AVE MEMPHIS Tennessee 38113 0 

GOLD EAGLE CO 4400 S KILDARE AVE CHICAGO Illinois 60632 0.125 

AKZO NOBEL COATINGS INC 1431 PROGRESS AVE HIGH POINT North Carolina 27261 0.125 

ELECTRONICS FOR IMAGING INC 1260 JAMES L HART PKWY YPSILANTI Michigan 48197 0.124 

KEYSTONE ANILINE CORP 2165 HWY 292 INMAN South Carolina 29349 0.0615 

CAROLINA SOLVENTS INC 2274 1ST ST SE HICKORY North Carolina 28602 0.116 

ASHLAND DISTRIBUTION 4185 ALGONQUIN PKWY LOUISVILLE Kentucky 40211 0.1145 

ASHLAND DISTRIBUTION CO 3930 GLENWOOD DR CHARLOTTE North Carolina 28208 0.082 

AEP INDUSTRIES INC 1201 S PINE HILL RD GRIFFIN Georgia 30224 0.0025 

ALLEGHENY PETROLEUM PRODUCTS CO 999 AIRBRAKE AVE WILMERDING Pennsylvania 15148 0.0235 

ACCURATE DISPERSIONS 192 W 155TH ST SOUTH HOLLAND Illinois 60473 0.088 SUPERIOR SOLVENTS & CHEMICALS 4211 BRAMERS LN LOUISVILLE Kentucky 40216 0.004 

US MARINE CORPS AIR STATION YUMA AVE 3E YUMA Arizona 85369 0.096 TECHNICAL CHEMICAL CO 3327 PIPELINE RD CLEBURNE Texas 76033 0.1135 

Page 29 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

ARDEX LABORATORIES INC 2050 BYBERRY RD PHILADELPHIA Pennsylvania 19116 0.1125 ASHLAND INC - EVENDALE 2788 GLENDALE-MILFORD RD EVENDALE Ohio 45241 0.0805 

SHERWIN-WILLIAMS CO 2121 NEW WORLD DR COLUMBUS Ohio 43207 0.0085 

SHERWIN-WILLIAMS CO 1025 HOWARD ST GREENSBORO North Carolina 27403 0.053 3M CO - NEVADA 2120 E AUSTIN BLVD NEVADA Missouri 64772 0.01 DELTA LABORATORIES INC 3710 COUNTY RD 326 W OCALA Florida 34475 0.1085 

SHERWIN-WILLIAMS CO 636 E 40TH ST HOLLAND Michigan 49423 0.1045 

SUPERIOR OIL CO INC 400 W REGENT ST INDIANAPOLIS Indiana 46225 0.0045 FRAZEE INDUSTRIES 6625 MIRAMAR RD SAN DIEGO California 92121 0 

HENKEL CORP 23343 SHERWOOD AVE WARREN Michigan 48091 0.044 

CENTRAL MOTOR WHEEL OF AMERICA (DBA CMWA) 125 WHEAT DR PARIS Kentucky 40361 0 

ASHLAND DISTRIBUTION CO 2461 CROCKER CIR FAIRFIELD California 94533 0.1015 

STEELSCAPE INC RANCHO 11200 ARROW RT RANCHO CUCAMON California 91730 0.0035 

ASHLAND DISTRIBUTION CO 20915 S WILMINGTON AVE CARSON California 90810 0.0925 

MRCG-KRAFTMAID P3 150 GRAND VALLEY AVE ORWELL Ohio 44076 0.002 UNIVAR USA INC HAMILTON BRANCH 12 STANDEN DR HAMILTON Ohio 45015 0.007 

GROTTOES PLASTICS PLANT 149 GRAND CAVERNS DR GROTTOES Virginia 24441 0.022 CYTEC INDUSTRIES INC LANGLEY PLANT 403 CARLINE RD LANGLEY South Carolina 29834 0.0835 ASHLAND DISTRIBUTION CO 200 NE 181ST ST MIAMI Florida 33162 0.075 

CE BRADLEY LABORATORIES INC 55 BENNETT DR BRATTLEBORO Vermont 05301 0.093 

MULTI-COLOR CORP 2281 S US 31 SCOTTSBURG Indiana 47170 0 

ATHEA LABORATORIES INC 7855 N FAULKNER RD MILWAUKEE Wisconsin 53224 0.0905 

BRENNTAG PACIFIC INC 10747 PATTERSON PL SANTA FE SPRINGS California 90670 0.081 

DIC IMAGING PRODUCTS USA LLC 7335 S 10TH ST OAK CREEK Wisconsin 53154 0.0085 

NORTHERN COATINGS & CHEMICAL CO INC 705 6TH AVE MENOMINEE Michigan 49858 0.085 

CCI MANUFACTURING IL CORP 15550 CANAL BANK RD LEMONT Illinois 60439 0 

UNION TANK CAR ALEXANDRIA MANUFACTURING FACILITY 6325 HWY 1 N ALEXANDRIA Louisiana 71303 0.004 

CHAMPION TECHNOLOGIES INC 350 CENTAURUS RD CORPUS CHRISTI Texas 78405 0.0805 

ASHLAND DISTRIBUTION 400 MAIN ST TEWKSBURY Massachusetts 01876 0.076 

Page 30 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

THIRD COAST PACKAGING INC FRIENDSWOOD 18410 W CLOVER LN FRIENDSWOOD Texas 77549 0 

BERNER CHEESE CORP 2034 E FACTORY RD DAKOTA Illinois 61018 0 

CHAMPION TECHNOLOGIES INC 1100 HUGHIE LONG RD CRESSON Texas 76035 0.0795 

BUZZI UNICEM USA - GREENCASTLE PLANT 3301 S COUNTY RD 150 W GREENCASTLE Indiana 46135 0.0155 

KEY POLYMER 17 SHEPARD ST LAWRENCE INDUSTLAWRENCE Massachusetts 01843 0 

TEXAS INSTRUMENTS INC 13500 N CENTRAL EXPRESSWAY DALLAS Texas 75243 0 

AVERY DENNISON PFD 650 W 67TH AVE SCHERERVILLE Indiana 46375 0.0545 

ECOLAB 18383 E RAILROAD ST CITY OF INDUSTRY California 91748 0.018 

LUBRIZOL 9550 W 55TH ST MC COOK Illinois 60525 0 

ARCH CHEMICALS INC HWY 933 BRANDENBURG Kentucky 40108 0.02 

PLAZE INC 105 BOLTE LN SAINT CLAIR Missouri 63077 0.078 

ASHLAND DISTRIBUTION CO 5420 SPEAKER RD KANSAS CITY Kansas 66106 0.069 

AKZO NOBEL COATINGS INC 1000 INDUSTRIAL PARK DR CLINTON Mississippi 39056 0.0765 

MATTHEWS INTERNATIONAL CORP 101 FAIRVIEW AVE PITTSBURGH Pennsylvania 15238 0.064 CHEMICAL SOLVENTS JENNINGS ROAD FACILITY 3751 JENNINGS RD CLEVELAND Ohio 44109 0.069 CLOROX PRODUCTS MANUFACTURING CO 2600 HUNTINGTON DR FAIRFIELD California 94533 0.074 LAMBERTI USA INC WHARTON CHEMICAL COMPLEX HWY 59 AT COUNTY RD 212 HUNGERFORD Texas 77448 0.0115 

SPRAYLAT CORP 716 S COLUMBUS AVE MOUNT VERNON New York 10550 0.0035 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

2000 WESTHALL ST PITTSBURGH Pennsylvania 15233 0.063 

AKZO NOBEL COATINGS INC 1660 CROSS ST SE SALEM Oregon 97302 0.043 

BOEHRINGER INGELHEIM CHEMICALS INC 2820 N NORMANDY RD PETERSBURG Virginia 23805 0.009 VEYANCE TECHNOLOGIES INC 4021 N 56TH ST LINCOLN Nebraska 68504 0 

VEOLIA ES TECHNICAL SOLUTIONS LLC PORT ARTHUR FACILITY

HWY 73, 35 MILES W OF TAYLOR BA PORT ARTHUR Texas 77640 0.071 

ADCO CLEANING PRODUCTS LLC 900 W MAIN ST SEDALIA Missouri 65301 0.0235 

WARSAW CHEMICAL CO INC 390 ARGONNE RD WARSAW Indiana 46580 0.048 ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

901 W UNION ST MONTEBELLO California 90640 0.0635 

GENERAL DYNAMICS ORDNANCE & TACTICAL SYSTEMS GARLAND

1200 N GLENBROOK GARLAND Texas 75040 0.003 

Page 31 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

CARDINAL INDUSTRIAL FINISHES 1329 POTRERO AVE SOUTH EL MONTE California 91733 0.048 

MINUTEMAN INTERNATIONAL MULTI-CLEAN DIV 600 CARDIGAN RD SHOREVIEW Minnesota 55126 0.063 

UNIVAR USA INC INDIANAPOLIS WEST BRANCH 5850 W 82ND ST INDIANAPOLIS Indiana 46268 0.003 

KARCHER NORTH AMERICA- PROCHEM 325 S PRICE RD CHANDLER Arizona 85224 0.0625 

ICI PAINTS PUERTO RICO INC 65 INFANTERIA KM 134 CAROLINA Puerto Rico 00985 0.0615 

COOK COMPOSITES & POLYMERS C O 13511 MAIN ST LEMONT Illinois 60439 0.017 

MRCG-KRAFTMAID P1 16052 INDUSTRIAL PKWY MIDDLEFIELD Ohio 44062 0 

BRENNTAG SOUTHEAST INC 2000 E PETTIGREW ST DURHAM North Carolina 27703 0.043 

CONOCOPHILLIPS CO EAST ST LOUIS TERMINAL 3300 MISSISSIPPI AVE CAHOKIA Illinois 62206 0 CONTINENTAL CEMENT CO LLC 10107 HWY 79 HANNIBAL Missouri 63401 0.057 

ECOLAB INC 261 HWY 155 S MC DONOUGH Georgia 30253 0.0185 COGNIS CORP MAULDIN PLANT 1520 OLD STAGE RD MAULDIN South Carolina 29662 0.0465 

GRAPHIC CONTROLS LLC 400 EXCHANGE ST BUFFALO New York 14204 0.054 

UNIVAR USA INC 7050 W 71ST ST BEDFORD PARK Illinois 60499 0.0285 

ABC COMPOUNDING CO OF TEXAS INC 1102 AVE J E GRAND PRAIRIE Texas 75050 0.0025 

HANNA STEEL CORP 220 HANNA DR PEKIN Illinois 61554 0.0035 

DYSTAR LP 209 WATLINGTON INDUSTRIAL DR REIDSVILLE North Carolina 27320 0.035 NORTHERN LABS INC WEST DRIVE 5800 W DR MANITOWOC Wisconsin 54220 0.049 

BARTON SOLVENTS INC BETTENDORF 204 36TH ST BETTENDORF Iowa 52722 0.0115 

WHITFORD CORP 47 PARK AVE ELVERSON Pennsylvania 19520 0.046 AMERICAN COATINGS INC 10625 MAHAFFEY RD TOMBALL Texas 77375 0.013 

NORMAN FOX & CO 5511 S BOYLE AVE VERNON California 90058 0.0025 

KAY CHEMICAL CO 8300 CAPITAL DR GREENSBORO North Carolina 27409 0.0095 

ASHLAND DISTRIBUTION CO 5125 W HANNA AVE TAMPA Florida 33634 0.0015 

FRANKLIN INTERNATIONAL 2020 BRUCK ST COLUMBUS Ohio 43207 0.0045 

RECKITT BENCKISER 799 RT 206 & HILLSBOROUGH RD HILLSBOROUGH New Jersey 08844 0.045 

INOAC PACKAGING GROUP 901 NUTTER DR BARDSTOWN Kentucky 40004 0 

ECOLAB INC 3001 CHANNAHON RD JOLIET Illinois 60436 0.0305 

CORSICANA TECHNOLOGIES INC 2733 E HWY 31 CORSICANA Texas 75109 0.0065 

Page 32 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

KBP COIL COATERS INC 3600 E 44TH AVE DENVER Colorado 80216 0 

ENTHONE INC 9809 INDUSTRIAL DR BRIDGEVIEW Illinois 60455 0.004 FORD MOTOR CO MICHIGAN ASSEMBLY PLANT 38303 MICHIGAN AVE WAYNE Michigan 48184 0.0405 

RECTICEL INTERIORS NORTH AMERICA LLC 1420 INDUSTRIAL PARK DR TUSCALOOSA Alabama 35401 0.0005 BIOLAB INC 1735 DOGWOOD DR CONYERS Georgia 30012 0.039 BARTON SOLVENTS INC WICHITA 201 S CEDAR VALLEY CENTER Kansas 67147 0.008 

BARTON SOLVENTS INC KANSAS CITY 901 S 66TH TERRACE KANSAS CITY Kansas 66111 0.008 

SHERWIN-WILLIAMS CO 630 E 13TH ANDOVER Kansas 67002 0.0285 CLEAN HARBORS EL DORADO LLC 309 AMERICAN CIR UNION EL DORADO Arkansas 71730 0.037 

ECOLAB 383 N HIGH ST HEBRON Ohio 43025 0.0265 

EXCEL-POLYMERS LLC HWY 353 S PO BOX 377 JONESBOROUGH Tennessee 37659 0 

AIR PRODUCTS PERFORMANCE MANUFACTURING INC 337 VINCENT DR MILTON Wisconsin 53563 0.0025 

ECOLAB INC 942 BAKER RD MARTINSBURG West Virginia 25405 0.022 

HUNTSMAN ADVANCED MATERIALS AMERICAS INC 555 HUNTSMAN RD MC INTOSH Alabama 36553 0.0125 

ETHOX CHEMICALS LLC 1801 PERIMETER RD GREENVILLE South Carolina 29605 0.0025 

RICHARDSAPEX INC 4202-24 MAIN ST PHILADELPHIA Pennsylvania 19127 0.025 

GIANT CEMENT CO HWY 453 & I-26 (654 JUDGE ST) HARLEYVILLE South Carolina 29448 0.0015 

BRENNTAG NORTHEAST INC 81 W HULLER LN READING Pennsylvania 19605 0.0185 

LUBRIZOL CORP 29400 LAKELAND BLVD WICKLIFFE Ohio 44092 0.033 

RANBAR ELECTRICAL MATERIALS INC RTE 993 ONE MILE W OF RTE 130 MANOR Pennsylvania 15665 0 

DUPONT PARLIN PLANT CHEESEQUAKE RD PARLIN New Jersey 08859 0.004 

BARTON SOLVENTS INC WEST BEND 800 RAIL WAY WEST BEND Wisconsin 53095 0.005 

3M CO - KNOXVILLE 3406 E PLEASANT KNOXVILLE Iowa 50138 0 SI GROUP INC 1000 MAIN ST ROTTERDAM JUNCTNew York 12150 0.009 

UNIVAR USA INC - INDIANAPOLIS 7425 E 30TH ST INDIANAPOLIS Indiana 46219 0.008 

MACDERMID INC 1221 FARROW AVE FERNDALE Michigan 48220 0.0135 MEADWESTVACO SOUTH CAROLINA LLC 400 CROSBY RD DERIDDER Louisiana 70634 0.0025 

CARBOLINE CO 900 OPELOUSAS ST LAKE CHARLES Louisiana 70601 0 

ASHLAND DISTRIBUTION 2011 TURNER ST LANSING Michigan 48906 0.025 

Page 33 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

KEMIRA WATER SOLUTIONS INC 1 CYANAMID RD MOBILE Alabama 36614 0.013 UNIVAR USA INC - TOLEDO SOUTH BRANCH 4051 S AVE TOLEDO Ohio 43615 0.009 

ECOLAB INC 2305 SHERWIN ST GARLAND Texas 75041 0.0145 VEOLIA ES TECHNICAL SOLUTIONS LLC 125 FACTORY LN MIDDLESEX New Jersey 08846 0.0125 

AMPHENOL APC INC 91 NORTHEASTERN BLVD NASHUA New Hampshire 03062 0.0025 

CLEARWATER INTERNATIONAL LLC 100 INDUSTRIAL DR (BLDG 180, 150, LEETSDALE Pennsylvania 15056 0.0015 

BARTON SOLVENTS INC DES MOINES 1970 NE BROADWAY DES MOINES Iowa 50313 0.003 

HOLLY OAK CHEMICAL INC 101 CASE ST FOUNTAIN INN South Carolina 29644 0.025 

PROCTER & GAMBLE HAIR CARE LLC 2200 LOWER MUSCATINE RD IOWA CITY Iowa 52240 0.005 

EXCEL POLYMERS LLC 150 S CONNELL AVE DYERSBURG Tennessee 38024 0 

ASHLAND DISTRIBUTION CO 8901 OLD GALVESTON RD HOUSTON Texas 77034 0.0055 

SHERWIN-WILLIAMS CO 113 STAGE COACH TRAIL GREENSBORO North Carolina 27409 0.004 

SHERWIN-WILLIAMS CO 11700 S COTTAGE GROVE CHICAGO Illinois 60628 0 

FORD MOTOR CO DEARBORN TOOL & DIE PLANT 3001 MILLER RD DEARBORN Michigan 48121 0.001 

BASF CORP 1 JAMES ST BELVIDERE New Jersey 07823 0 

UNIVAR USA INC NORCROSS FACILI TY 2145 SKYLAND CT NORCROSS Georgia 30071 0.011 

ECOLAB INC 640 LENFEST RD SAN JOSE California 95133 0.0135 

VALERO THREE RIVERS REFINERY 301 LEROY ST THREE RIVERS Texas 78071 0.023 

BARTON SOLVENTS INC COUNCIL BLUFFS 2135 9TH AVE COUNCIL BLUFFS Iowa 51502 0.0015 

UNIVAR USA INC - TOLEDO BRANCH 30450 TRACY RD WALBRIDGE Ohio 43465 0.003 

PRIDE SOLVENTS & CHEMICAL CO OF NEW JERSEY 211 RANDOLPH AVE AVENEL New Jersey 07001 0.0055 

DAUBERT CHEMICAL CO 4700 S CENTRAL AVE CHICAGO Illinois 60638 0.0095 

KWAL-HOWELLS INC (DBA KWAL PAINT INC) 2430 ALBERT BROADFOOT ST BONHAM Texas 75418 0 

U.S. POLYMERS ACCUREZ LLC 300 E PRIMM ST SAINT LOUIS Missouri 63111 0.0085 

3M CO - SPRINGFIELD 3211 E CHESTNUT EXPY SPRINGFIELD Missouri 65802 0 

UNIVAR USA INC 68TH ST 8500 W 68 TH ST BEDFORD PARK Illinois 60501 0.01 

GAGE PRODUCTS CO 625 WANDA AVE FERNDALE Michigan 48220 0 

VALSPAR REFINISH 210 CROSBY ST PICAYUNE Mississippi 39466 0 

FISHER SCIENTIFIC INTERNATIONAL MTN DIAGNOSTICS PLANT

8365 VALLEY PIKE MIDDLETOWN Virginia 22645 0 

Page 34 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

ZEP COMMERCIAL 350 JOE FRANK HARRIS PKWY EMERSON Georgia 30137 0 

STEEL DYNAMICS INC 4500 COUNTY RD 59 BUTLER Indiana 46721 0 TRANSTAR AUTOBODY TECHNOLOGIES 2040 HEISERMAN DR BRIGHTON Michigan 48114 0.009 

ASHLAND DISTRIBUTION CO 1842 ENTERPRISE PKWY TWINSBURG Ohio 44087 0.0025 BLENTECH CORP 1305 RYE ST HOUSTON Texas 77029 0.0125 

ARLON INC ADHESIVES & FILMS DIV 2811 S HARBOR BLVD SANTA ANA California 92704 0 

HENKEL 14351 HWY 221 ENOREE South Carolina 29335 0.0005 

CHEMDESIGN PRODUCTS INC 2 STANTON ST MARINETTE Wisconsin 54143 0.006 

MONSANTO CO 2500 WIGGINS RD MUSCATINE Iowa 52761 0.0135 

SHERWIN-WILLIAMS CO 6795 S MAIN ST MORROW Georgia 30260 0.004 

PRIDE SOLVENT & CHEMICAL CO OF NY INC 6 LONG ISLAND AVE HOLTSVILLE New York 11742 0.0035 

SIMONIZ USA INC 201 BOSTON TURNPIKE BOLTON Connecticut 06043 0.0125 BRULIN CORP 2920 DR ANDREW J BROWN AVE INDIANAPOLIS Indiana 46205 0.003 EVONIK DEGUSSA CORP 4201 DEGUSSA RD THEODORE Alabama 36582 0.012 

UNIVAR USA INC 2600 S GARFIELD AVE COMMERCE California 90040 0.011 

HUBBARD-HALL INC 563 S LEONARD ST WATERBURY Connecticut 06708 0.0005 

GOODWIN CO 700 PROGRESS CENTER AVE LAWRENCEVILLE Georgia 30043 0.011 

HENKEL CORP 421 LONDON RD DELAWARE Ohio 43015 0.005 

SHERWIN-WILLIAMS CO 2325 HOLLINS FERRY RD BALTIMORE Maryland 21230 0.0065 

PRC-DESOTO INTERNATIONAL INC 11601 UNITED ST MOJAVE California 93501 0.004 

BERRIDGE MANUFACTURING CO 6515 FRATT RD SAN ANTONIO Texas 78218 0 

BUCKLEY OIL CO 1809 ROCK ISLAND ST DALLAS Texas 75207 0.0075 

CHEMOL CO INC 2300 RANDOLPH AVE GREENSBORO North Carolina 27406 0 

HYDRITE CHEMICAL CO 2545 BOND ST UNIVERSITY PARK Illinois 60466 0 

TRUE VALUE MANUFACTURING 201 JANDUS RD CARY Illinois 60013 0.0025 

DAVIES IMPERIAL COATINGS INC 1275 STATE ST HAMMOND Indiana 46320 0.0095 

UNIVAR USA INC SANTA FE SPRINGS 13900 CARMENITA RD SANTA FE SPRINGS California 90670 0.003 HENKEL ONTARIO 1496 E FRANCIS ST ONTARIO California 91761 0.0015 

BENJAMIN MOORE & CO PELL CITY 109 BAMBERG DR PELL CITY Alabama 35125 0.0085 

Page 35 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

GEORGIA-PACIFIC CHEMICALS LLC 1429 E LUFKIN AVE LUFKIN Texas 75901 0.008 SHERWIN-WILLIAMS CO 26300 FARGO AVE BEDFORD HEIGHTS Ohio 44146 0.0005 CRODA INC 315 CHERRY LN NEW CASTLE Delaware 19720 0.0075 

TARR ACQUISITION LLC 2429 N BORTHWICK AVE PORTLAND Oregon 97227 0.008 

INTERSTATE CHEMICAL CO INC 23247 W EAMES ST CHANNAHON Illinois 60410 0.0025 

DSM DESOTECH INC 1101 HWY 27 S STANLEY North Carolina 28164 0 

NEW DAWN MANUFACTURING CO 16001 TRADE ZONE AVE UPPER MARLBORO Maryland 20774 0.0075 

RUSTOLEUM CORP 7850 OHIO RIVER RD LESAGE West Virginia 25537 0.0025 3M COTTAGE GROVE CENTER 10746 INNOVATION RD COTTAGE GROVE Minnesota 55016 0 

SHERWIN-WILLIAMS CO 12401 INDUSTRIAL BLVD VICTORVILLE California 92392 0.0035 

DYNALOY LLC 6445 OLIVIA LN INDIANAPOLIS Indiana 46226 0.0015 

LUBRIZOL CORP PAINESVIL LE PLANT 155 FREEDOM RD PAINESVILLE Ohio 44077 0.0065 

SCOT LABORATORIES 16841 PARK CIR DR CHAGRIN FALLS Ohio 44023 0.0025 CLOROX PRODUCTS MANUFACTURING CO 17 LAKE MIRROR RD FOREST PARK Georgia 30297 0.0035 

CUSTOM CHEMICAL FORMULATORS 8707 MILLERGROVE DR SANTA FE SPRINGS California 90670 0.007 

HENKEL CORP 923 MAULDIN RD CALHOUN Georgia 30701 0 UNIVAR USA INC - SAN JOSE 2256 JUNCTION AVE SAN JOSE California 95131 0.003 DOW CHEMICAL JOLIET SITE 26332 S FRONTAGE RD W CHANNAHON Illinois 60410 0 

KEYSTONE CEMENT CO RT 329 BATH Pennsylvania 18014 0 

PROCTER & GAMBLE MANUFACTURING CO 1900 KANSAS AVE KANSAS CITY Kansas 66105 0.006 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

546 W ABBOTT ST INDIANAPOLIS Indiana 46225 0 

AROMATIC TECHNOLOGIES INC 130 INDUSTRIAL PKWY SOMERVILLE New Jersey 08876 0.0055 

CALLAHAN CHEMICAL CO 200 INDUSTRIAL AVE RIDGEFIELD PARK New Jersey 07660 0.003 

ACTEGA RADCURE INC 5 MANSARD CT WAYNE New Jersey 07470 0.0025 

INDEPENDENT INK INC 14705 S AVALON BLVD GARDENA California 90248 0.0025 

US ECOLOGY TEXAS INC 3277 COUNTY RD 69 ROBSTOWN Texas 78380 0.0025 

CUSTOM SYNTHESIS LLC 1704 DENVER RD ANDERSON South Carolina 29625 0.0025 

WORWAG COATINGS LLC NA 3420 KOSSUTH ST LAFAYETTE Indiana 47905 0.0025 

CR BRANDS INC 141 VENTURE BLVD SPARTANBURG South Carolina 29306 0.0025 

Page 36 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

CENTRAL SOLUTIONS INC 401 FUNSTON RD KANSAS CITY Kansas 66115 0 

UNIVAR USA INC LAKEVILLE 21675 HAMBURG AVE LAKEVILLE Minnesota 55044 0.0025 

CAR CARE PACKAGING LLC 1910 S STATE AVE INDIANAPOLIS Indiana 46203 0.0005 

SHIELD PACKAGING CO INC 50 OXFORD AVE DUDLEY Massachusetts 01571 0.0025 

GOODWIN CO 12361 MONARCH ST GARDEN GROVE California 92841 0.0045 

C P INC 196 S WATER CONNERSVILLE Indiana 47331 0.0025 

INTEL CORP - RONLER ACRES CAMPUS 2501 NW 229TH ST HILLSBORO Oregon 97124 0.0025 

BRAIN POWER INC 4470 SW 74TH AVE MIAMI Florida 33155 0.0025 

SARTOMER CO INC 601 TIGHTSQUEEZE INDUSTRIAL RDCHATHAM Virginia 24531 0.0025 

CHAMPION PACKAGING & DISTRIBUTING INC 1840 INTERNATIONALE PKWY WOODRIDGE Illinois 60517 0.0025 

INTEL CORP 4500 S DOBSON RD MAIL STOP: OC4CHANDLER Arizona 85248 0.0025 

SARTOMER CO INC 610 S BOLMAR ST WEST CHESTER Pennsylvania 19382 0.0025 

ASHLAND DISTRIBUTION CO FREEPORT CENTER BUILDING 12 POCLEARFIELD Utah 84016 0.0015 ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

1215 NELSON BLVD ROCKFORD Illinois 61104 0 

KING INDUSTRIES INC SCIENCE RD NORWALK Connecticut 06852 0.002 COGNIS CORP -- CHARLOTT E PLANT 3300 WESTINGHOUSE BLVD CHARLOTTE North Carolina 28273 0.004 

OMNIUM 1280 IMPERIAL RD HAMPTON Iowa 50441 0.0025 

CALLAHAN CHEMICAL CO 18 INDUSTRIAL RD WALPOLE Massachusetts 02081 0.002 

UNIVAR USA INC HOUSTON 777 BRISBANE ST HOUSTON Texas 77061 0.0035 

PENRAY COMPANIES INC 1801 ESTES AVE ELK GROVE VILLAGEIllinois 60007 0.0005 

ENGINEERED POLYMER SOLUTIONS INC 5501 E SLAUSON AVE CITY OF COMMERCECalifornia 90040 0.003 

CARESTREAM HEALTH COLORADO 2000 HOWARD SMITH AVE W C42 WINDSOR Colorado 80550 0.0035 

BAKER PETROLITE BAYPORT FACILI TY 13200 BAYPARK RD PASADENA Texas 77507 0.0035 

PENRAY COMPANIES INC 440 DENNISTON CT WHEELING Illinois 60090 0.0005 

BAKER PETROLITE 5135 BOYLAN ST BAKERSFIELD California 93308 0.0025 

DYNASOL INC 330 PINE ST CANTON Massachusetts 02021 0.003 

NORLITE CORP 628 S SARATOGA ST COHOES New York 12047 0.003 

FORD MOTOR CO DEARBORN DIVERSIFIED MANUFACTURING

3001 MILLER RD DEARBORN Michigan 48121 0.003 

Page 37 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

CALLAHAN CHEMICAL CO BROAD ST & FILMORE AVE PALMYRA New Jersey 08065 0.0015 

BAKER PETROLITE CORP 16950 WALLISVILLE RD HOUSTON Texas 77049 0.0005 

HEXION SPECIALTY CHEMICALS INC 2801 LYNWOOD RD LYNWOOD California 90262 0.0005 

MAINTEX INC 13300 E NELSON AVE CITY OF INDUSTRY California 91746 0.0025 

CLEAN HARBORS ENVIRONMENTAL SERVICES INC 2247 S HWY 71 KIMBALL Nebraska 69145 0.002 

ECP INC WOODRIDGE 11210 KATHERINE'S CROSSING SUITWOODRIDGE Illinois 60517 0.0025 

UNIVAR USA INC MEMPHIS 3909 OUTLAND RD MEMPHIS Tennessee 38118 0.0025 

CR BRANDS INC 230 OLD CONVERSE RD SPARTANBURG South Carolina 29307 0.0025 

MAHONING PAINT CORP 653 JONES ST YOUNGSTOWN Ohio 44502 0.0025 

UNION SPECIALTIES INC 3 MALCOLM HOYT DR NEWBURYPORT Massachusetts 01950 0.0005 

UNIVAR USA INC DENVER 4300 HOLLY ST DENVER Colorado 80216 0.0025 

SINCLAIR WYOMING REFINING CO 100 E LINCOLN AVE SINCLAIR Wyoming 82334 0 ATOTECH USA 1750 OVERVIEW DR ROCK HILL South Carolina 29730 0.0025 

FINGER LAKES CHEMICAL INC 418-424 ST PAUL ST ROCHESTER New York 14605 0.0025 

MALLINCKRODT BAKER INC 600 N BROAD ST PHILLIPSBURG New Jersey 08865 0.0025 

CHEMTEX LABORATORIES INC 2725 ARMENTROUT DR CONCORD North Carolina 28025 0.0025 

WYNNEWOOD REFINING CO 906 S POWELL WYNNEWOOD Oklahoma 73098 0 

BASF CORP 100 INDUSTRIAL BLVD SEAFORD Delaware 19973 0.0025 CONOCOPHILLIPS CO TREMLEY POINT TERMINAL FOOT OF S WOOD AVE LINDEN New Jersey 07036 0.0025 CONOCOPHILLIPS MT VERNON PRODUCTS TERMINAL 15138 HWY 96 MOUNT VERNON Missouri 65712 0 

NIACET CORP 400 47TH ST NIAGARA FALLS New York 14304 0.0025 

MAGNABLEND INC-CENTRAL PLANT 1601 W HWY 287 BYPASS WAXAHACHIE Texas 75165 0.0025 

INTEL CORP 4100 SARA RD MS RR5-491 RIO RANCHO New Mexico 87124 0.0025 

HERCULES INC 1111 HERCULES RD HOPEWELL Virginia 23860 0.0025 

MILPORT ENTERPRISES INC 2829 S 5TH CT MILWAUKEE Wisconsin 53207 0 

DELTA HOUSTON 334 TIDAL RD DEER PARK Texas 77536 0.0015 ASTRO CHEMICALS INC 126 MEMORIAL DR SPRINGFIELD Massachusetts 01104 0.0015 

DUPONT EKC TECHNOLOGY 2520 BARRINGTON CT HAYWARD California 94545 0.0005 

DOBER CHEMICAL CORP 14461 WAVERLY AVE MIDLOTHIAN Illinois 60445 0.002 

Page 38 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

GOODYEAR TIRE & RUBBER CO 3260 GOODYEAR BLVD UNION CITY Tennessee 38261 0 

UNIVAR USA INC- CINCINNATI OH BRANCH 4600 DUES DR CINCINNATI Ohio 45246 0.001 

KELLY-MOORE PAINT CO INC 1015 COMMERCIAL ST SAN CARLOS California 94070 0 

HYDRITE CHEMICAL CO 7300 W BRADLEY RD MILWAUKEE Wisconsin 53223 0.0005 FUJIFILM HUNT CHEMICALS USA INC 900 CARNEGIE ST ROLLING MEADOWSIllinois 60008 0.0015 

CLEAN HARBORS ARAGONITE LLC 11600 N APTUS RD GRANTSVILLE Utah 84029 0 

CHEMICAL SOLVENTS INC--DENISON FACILITY 1010 OLD DENNISON AVE CLEVELAND Ohio 44109 0.0015 

BAKER PETROLITE-RAYNE FACILITY 135 INDUSTRIAL DR RAYNE Louisiana 70578 0.0005 FIRST SOURCE WORLDWIDE LLC MILWAUKEE 11725 W FAIRVIEW AVE MILWAUKEE Wisconsin 53226 0.001 BUCKMAN LABORATORIES INC 1256 N MCLEAN BLVD MEMPHIS Tennessee 38108 0 

SHERWIN-WILLIAMS CO 404 E MALLORY AVE MEMPHIS Tennessee 38109 0.0005 

SHERWIN-WILLIAMS CO 10136 MAGNOLIA DR OLIVE BRANCH Mississippi 38654 0.0005 

VOLTAIX LLC 197 MEISTER AVE BRANCHBURG New Jersey 08876 0 

NALCO CO 3901 TERRY ST TEXARKANA Texas 75501 0 

HONEYWELL-PRESTONE PRODUCTS CORP 250 HALLS MILL RD FREEHOLD New Jersey 07728 0.001 

BRENNTAG SOUTHEAST INC 11750 FRUEHAUF DR CHARLOTTE North Carolina 28273 0.0005 

PPG ARCHITECTURAL COATINGS 6804 ENTERPRISE DR LOUISVILLE Kentucky 40214 0 

SAFETY-KLEEN SYSTEMS INC 1200 SYLVAN ST LINDEN New Jersey 07036 0.0005 

DSM NEORESINS INC 3110 W ST RD 28 FRANKFORT Indiana 46041 0.001 

SHERWIN-WILLIAMS CO 14 INDUSTRIAL PARK FLORA Illinois 62839 0 

MEADWESTVACO SC LLC CHARLESTON CHEMICAL PLANT 5598 VIRGINIA AVE NORTH CHARLESTOSouth Carolina 29406 0 

NATIONAL INDUSTRIAL COATINGS INC DBA NICOAT INC 1600 GLENLAKE AVE ITASCA Illinois 60143 0.0005 

LANCO MANUFACTURING CORP URBAPONTE #5 SAN LORENZO Puerto Rico 00754 0 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

5060 83RD ST SACRAMENTO California 95826 0 

IFF AUGUSTA LTD 3005 INTERNATIONAL BLVD AUGUSTA Georgia 30906 0 

SOLITE LLC RT 652 ARVONIA Virginia 23004 0 

HENTZEN COATINGS,INC 6937 W MILL RD MILWAUKEE Wisconsin 53218 0.0005 

RIKER PRODUCTS INC 4901 STICKNEY AVE TOLEDO Ohio 43612 0.0005 

Page 39 of 40
Table B-1. 2009 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions (tpy)

CLARIANT CORP CLEAR LAKE PLANT 9502 BAYPORT BLVD - ETOX UNIT PASADENA Texas 77507 0.0005 

LAMBERTI SYNTHESIS USA INC 4001 N HAWTHORNE ST CHATTANOOGA Tennessee 37406 0.0005 

a. Releases to Surface Water reported as "On-Site Releases to Surface Water."b. Releases to Soil is the sum of reported releases to onsite and offsite releases to land treatment and other land disposal.c. Releases to other media include reported releases to onsite and offsite groundwater and landfills.tpy: tons per year

Page 40 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

EQ DETROIT INC 1923 FREDERICK DETROIT Michigan 48211 0 REXAM BEVERAGE CAN CO RE: WINSTON SALEM PLANT 4000 OLD MILWAUKEE LN WINSTON-SALEM North Carolina 27107 31.218 1BALL METAL BEVERAGE CONTAINER CORP 8935 POCAHONTAS TRAIL J WILLIAMSBURG Virginia 23185 28.5 SANYO SOLAR (USA) LLC 970 E 236TH ST CARSON California 90745 0.0005 7BALL METAL BEVERAGE CONTAINER CORP 12340 TOWNSHIP RD 99 E FINDLAY Ohio 45840 25 CROWN FOOD PACKAGING 2929 W BRIDGE ST OWATONNA Minnesota 55060 30.746 REXAM BEVERAGE CAN CO RE: FREMONT PLANT 2145 CEDAR FREMONT Ohio 43420 15.931 REXAM BEVERAGE CAN CO RE: BISHOPVILLE SC FACILITY 609 COUSAR ST BISHOPVILLE South Carolina 29010 14.5145 

CROWN CORK & SEAL CO (USA) INC CROWN CLOSURE DIV

3011 BIRCH DR WEIRTON West Virginia 26062 35.9645 

BALL METAL BEVERAGE CONTAINER CORP 1900 BARNES ST REIDSVILLE North Carolina 27320 14.5 BMW MANUFACTURING CO LLC 1400 HWY 101 S GREER South Carolina 29651 1.8155 REXAM BEVERAGE CAN CO RE: EVA STREET ST PAUL MN 139 EVA ST SAINT PAUL Minnesota 55107 13.4245 REXAM BEVERAGE CAN CO KENT WA FACILITY 1220 N SECOND AVE KENT Washington 98032 12.462 CROWN BEVERAGE PACKAGING 1202 FONES RD OLYMPIA Washington 98501 19.4225 REXAM BEVERAGE CAN CO OLIVE BRANCH FACILITY 10800 MARINA DR OLIVE BRANCH Mississippi 38654 20.551 

BALL CONTAINER LLC COLUMBUS CAN PLANT 350 MCCORMICK BLVD COLUMBUS Ohio 43213 11.5 

SILGAN CONTAINERS MANUFACTURING CORP 300 N FAIL RD LA PORTE Indiana 46350 12.85 

AURORA CASKET CO INC 10944 MARSH RD AURORA Indiana 47001 0 6

REXAM BEVERAGE CAN CO RE : CHICAGO PLANT 1101 W 43RD ST CHICAGO Illinois 60609 14.2105 

REXAM BEVERAGE CAN CO RE: WHITEHOUSE PLANT 10444 WATERVILLE WHITEHOUSE Ohio 43571 23.1975 

FORD MOTOR CO DEARBORN TRUCK PLANT 3001 MILLER RD DEARBORN Michigan 48121 1.5 

CROWN BEVERAGE PACKAGING 1035 E NORTH ST BRADLEY Illinois 60915 16.0195 

CROWN BEVERAGE PACKAGING GLEN & SHEPARD ST LAWRENCE Massachusetts 01843 15.6815 

REXAM BEVERAGE CAN CO LONGVIEW FACILITY 1001 FISHER RD LONGVIEW Texas 75604 14.4385 WHIRLPOOL CORP MARION D IVISION 1300 MARION-AGOSTA RD MARION Ohio 43302 0.05 

BALL CONTAINER LLC ROME CAN PLANT 110 MCC DR ROME Georgia 30161 33.5 

METAL CONTAINER CORPORTION - WINDSOR CAN PLANT 1201 METAL CONTAINER CTWINDSOR Colorado 80550 14.9135 

Page 1 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

FORD MOTOR COMPANY--KANSAS CITY ASSEMBLY PLANT 8121 E US HWY 69 CLAYCOMO Missouri 64119 1.5 

CROWN BEVERAGE PACKAGING 620 N 4TH ST WORLAND Wyoming 82401 12.782 

HONDA OF AMERICA MANUFACTURING INC 11000 STATE RT 347 EAST LIBERTY Ohio 43319 2.2 

METAL CONTAINER CORP - ARNOLD CAN PLANT 42 TENBROOK INDUSTRIAL ARNOLD Missouri 63010 17.9475 

BWAY CORP 1601 VALDOSTA HWY HOMERVILLE Georgia 31634 37.053 MEMC PASADENA INC 3000 N S ST PASADENA Texas 77503 12.77 

REXAM BEVERAGE CAN CO CHATSWORTH FACILITY 20730 PRAIRIE ST CHATSWORTH California 91311 8.9005 EDSAL MANUFACTURING CO INC 4400 S PACKER CHICAGO Illinois 60609 0 HONDA OF AMERICA MANUFACTURING INC 24000 HONDA PKY MARYSVILLE Ohio 43040 3.8 RR DONNELLEY 2347 KRATZER RD HARRISONBURG Virginia 22802 38.798 

METAL CONTAINER CORP - NEWBURGH CAN PLANT 130 BREUNIG RD NEW WINDSOR New York 12553 11.4875 

REXAM BEVERAGE CAN CO PHOENIX FACILITY 211 N 51ST AVE PHOENIX Arizona 85043 5.2035 

BALL METAL BEVERAGE CONTAINER CORP 8500 W TOWER AVE MILWAUKEE Wisconsin 53224 29 

MAGNA STEYR NORTH AMERICA 3800 STICKNEY AVE TOLEDO Ohio 43608 4.65 

CHICAGO HEIGHTS STEEL 211 E MAIN ST CHICAGO HEIGHTS Illinois 60411 7.496 

ROCKY MOUNTAIN METAL CONTAINER 17755 W 32ND AVE GOLDEN Colorado 80401 29.5 

CROWN BEVERAGE PACKAGING 2501 N FRAZIER ST CONROE Texas 77305 30.8465 

SUBARU OF INDIANA AUTOMOTIVE INC 5500 STATE RD 38E LAFAYETTE Indiana 47905 0.355 CHRYSLER JEFFERSON NORTH ASSEMBLY PLANT 2101 CONNOR AVE DETROIT Michigan 48215 4.1 NISSAN NA INC SMYRNA MANUFACTURING PLANT 983 NISSAN DR SMYRNA Tennessee 37167 1.307 FORD MOTOR CO KENTUCKY TRUCK PLANT 3001 CHAMBERLAIN LN LOUISVILLE Kentucky 40241 2.4 

GREIF PACKAGING LLC 7425 INDUSTRIAL RD FLORENCE Kentucky 41042 1.7475 

SILGAN CONTAINERS MANUFACTURING CORP 1400 PLOVER RD PO BOX 97PLOVER Wisconsin 54467 7.6 

METAL CONTAINER CORP - JACKSONVILLE CAN PLANT 1100 N ELLIS RD JACKSONVILLE Florida 32254 6.952 

CROWN FOOD PACKAGING 8801 CITATION RD BALTIMORE Maryland 21221 8.5165 

CROWN BEVERAGE PACKAGING 12910 JESS PIRTLE BLVD SUGAR LAND Texas 77478 28.1175 METAL CONTAINER CORP - MIRA LOMA CAN PLANT 10980 INLAND AVE MIRA LOMA California 91752 28.5415 

BALL METAL BEVERAGE CONTAINER CORP 500 CRENSHAW BLVD TORRANCE California 90503 29 

BERENFIELD CONTAINERS SE LTD 12180 UNIVERSITY CITY BLVHARRISBURG North Carolina 28075 0 31

SENECA FOODS CORP 801 SAUK AVE BARABOO Wisconsin 53913 0 

Page 2 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

THERMA-TRU CORP 601 RE JONES RD BUTLER Indiana 46721 0 

BALL METAL BEVERAGE CONTAINER CORP 4525 INDIANA ST GOLDEN Colorado 80403 19.5 

BALL METAL BEVERAGE CONTAINER CORP 501 N SIXTH ST MONTICELLO Indiana 47960 12.5 

HUNTSMAN PETROCHEMICAL LLC PORT NECHES PERFORMANCE PRODUCTS

6001 HWY 366 PORT NECHES Texas 77651 0.141 

CROWN BEVERAGE PACKAGING 380 CALLE FABRIL ST KM 12CAROLINA Puerto Rico 00985 6.91 

S B FOOT TANNING CO 805 BENCH ST RED WING Minnesota 55066 0 

PPG INDUSTRIES INC-OAK CREEK 10800 S 13TH ST OAK CREEK Wisconsin 53154 25.224 

DEXTER CHASSIS GROUP PLANT 55 501 S MILLER DR WHITE PIGEON Michigan 49099 0 

MERCEDES-BENZ US INTERNATIONAL INC 1 MERCEDES DR VANCE Alabama 35490 0.366025 2

INGERSOLL-RAND CO STEELCRAFT DIV 9017 BLUE ASH RD CINCINNATI Ohio 45242 5.6855 

ALLIED TUBE & CONDUIT CORP 16100 S LATHROP AVE HARVEY Illinois 60426 16.0515 

BWAY CORP 3200 S KILBOURN AVE CHICAGO Illinois 60623 6.818275 18

GM TRUCK GROUP FLINT ASSEMBLY PLANT VAN SLYKE COMPLEX

G-3100 VAN SLYKE RD FLINT Michigan 48551 0.45 

WHIRLPOOL CORP - CLYDE DIV 119 BIRDSEYE ST CLYDE Ohio 43410 0.718 

ROLL COATER INC 1950 E MAIN ST GREENFIELD Indiana 46140 0 NYW REALTY LLC/ HANOVER 500 E MIDDLE ST HANOVER Pennsylvania 17331 0 

TOYOTA MOTOR MANUFACTURING INDIANA INC 4000 TULIP TREE DR PRINCETON Indiana 47670 10.3485 CROWN BEVERAGE PACKAGING 100 EVANS ROW CHERAW South Carolina 29520 21.398 

BALL METAL BEVERAGE CONTAINER CORP 4700 WHITEWAY DR TAMPA Florida 33617 9 

HONDA MANUFACTURING OF ALABAMA LLC 1800 HONDA DR LINCOLN Alabama 35096 0.4995 CROWN BEVERAGE PACKAGING 1501 ST JAMES ST LA CROSSE Wisconsin 54603 22.1385 

GENERAL MOTORS LANSING DELTA TOWNSHIP 8175 MILLETT HWY LANSING Michigan 48917 0.5 

S D WARREN CO 89 CUMBERLAND ST WESTBROOK Maine 04098 0.0025 

GREIF PACKAGING LLC 4300 W 130TH ST ALSIP Illinois 60803 1.99 

BALL METAL FOOD CONTAINER CORP 3010 BIRCH DR WEIRTON West Virginia 26062 14.5 CROWN BEVERAGE PACKAGING 195 CROWN RD BATESVILLE Mississippi 38606 19.5525 

WHIRLPOOL CORP FINDLAY DIV 4901 N MAIN ST FINDLAY Ohio 45840 2.2375 

AVX CORP MYRTLE BEACH 801 17TH AVE S MYRTLE BEACH South Carolina 29577 3.3725 

MOBIL CHEMICAL CO 41501 WOLVERINE RD SHAWNEE Oklahoma 74804 0.375 

Page 3 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

AMES TRUE TEMPER INC 1500 S CAMERON ST HARRISBURG PENNSYLVANIA17104 1.082 

NORTH COAST CONTAINER CORP 8806 CRANE AVE CLEVELAND Ohio 44105 0 

BALL CONTAINER LLC 105 E BLACKHAWK DR FORT ATKINSON Wisconsin 53538 3.85 

AIR SYSTEM COMPONENTS LP 900 DARR PARK DR PONCA CITY Oklahoma 74601 0.209 

PELLA CORP 102 MAIN ST PELLA Iowa 50219 0.125 

BALL METAL BEVERAGE CONTAINER CORP 11 ADAMS RD SARATOGA SPRINGSNew York 12866 3.35 

MID-AMERICA STEEL DRUM CO IN C 8570 S CHICAGO RD OAK CREEK WISCONSIN 53154 0 

BATESVILLE MANUFACTURING INC 175 MONOGARD DR MANCHESTER Tennessee 37355 1.0165 

CECO DOOR PRODUCTS 9159 TELECOM DR MILAN Tennessee 38358 10.0825 

BALL METAL BEVERAGE CONTAINER CORP 2400 HUNTINGTON DR FAIRFIELD California 94533 7.5 

WAYNE DISPOSAL INC 49350 N I-94 SERVICE DR BELLEVILLE MICHIGAN 48111 0 

CROWN BEVERAGE PACKAGING 400 N WALNUT ST CRAWFORDSVILLE Indiana 47933 13.8125 HALLSTAR CO ESTER SOLUTIONS FACILITY 5851 W 73RD ST BEDFORD PARK Illinois 60638 1.167 BALL METAL BEVERAGE CONTAINER CORP 1001 N FM 3083 E CONROE Texas 77303 14 

THOMAS BUILT BUSES INC 715 W FAIRFIELD RD HIGH POINT NORTH CAROL 27263 0 

UNION CARBIDE CORP SEADRIFT PLANT 7501 N HWY 185 SEADRIFT Texas 77983 13.946 

AIR SYSTEM COMPONENTS LP 3301 N MAIN ST TARBORO North Carolina 27886 0.1745 

NASHVILLE WIRE PRODUCTS 1604 COUNTY HOSPITAL RDNASHVILLE Tennessee 37218 1.7 

ALSTOM POWER INC PLATE FORMED PRODUCTS DIV 911 W MAIN ST CHATTANOOGA Tennessee 37402 16.67 

OLDCASTLE BUILDING ENVELOPE TEXAS FACILITY 803 AIRPORT RD TERRELL Texas 75160 3.2115 

SPECTRUM METAL FINISHING 535 BEV RD YOUNGSTOWN Ohio 44512 0.33 

TOKICO (USA) INC 301 MAYDE RD BEREA Kentucky 40403 0.341 AGY AIKEN LLC 2556 WAGENER RD AIKEN South Carolina 29801 10.0075 

SEIDEL TANNING CORP 1306 E MEINECKE AVE MILWAUKEE Wisconsin 53212 0 

METAL INDUSTRIES INC - BUSHNELL 400 W WALKER AVE BUSHNELL Florida 33513 0.075 

EASTMAN CHEMICAL CO TEXAS OPERATIONS 300 KODAK BLVD LONGVIEW Texas 75602 12.052 

NEW UNITED MOTOR MANUFACTURING INC 45500 FREMONT BLVD MAIL FREMONT California 94538 14.564 

MPM SILICONES LLC 3500 S STATE RT 2 FRIENDLY West Virginia 26146 2.193 

USS - CLAIRTON WORKS 400 STATE ST CLAIRTON Pennsylvania 15025 14.5 

LAKESIDE LITHOGRAPHY LLC 1600 S LAFLIN ST CHICAGO Illinois 60608 1.125 

Page 4 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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Emis

(tp

HART & COOLEY INC 4910 MOORES MILL RD HUNTSVILLE Alabama 35811 0.8045 JOHNSON WELDED PRODUCTS INC 625 S EDGEWOOD AVE URBANA Ohio 43078 0 BEDFORD MATERIALS CO INC 7676 ALLEGHENY RD MANNS CHOICE Pennsylvania 15550 1.403 

BALL METAL BEVERAGE CONTAINER CORP 95 BALLARD RD MIDDLETOWN New York 10940 6.5 QUAD/GRAPHICS INC 1900 W SUMNER ST HARTFORD Wisconsin 53027 13.5 

BEMIS MANUFACTURING CO PLANT B 300 MILL ST SHEBOYGAN FALLS Wisconsin 53085 0 

SILGAN WHITE CAP CORP 2201 W MARYLAND ST EVANSVILLE Indiana 47710 11.15 

CROWN FOOD PACKAGING 5201 ENTERPRISE BLVD TOLEDO Ohio 43612 3.457 

GERSTENSLAGER CO 1425 E BOWMAN ST WOOSTER Ohio 44691 0.4135 

ROYAL MOULDINGS LTD; MARION VIRGINIA 135 BEAR CREEK RD MARION Virginia 24354 0.6885 TOPPAN INTERAMERICA INC 1131 HWY 155 S MC DONOUGH Georgia 30253 0 

M&B HANGERS 1313 PKWY DR SE LEEDS Alabama 35094 2.732 KNAPHEIDE MANUFACTURING CO 1848 WESTPHALIA STRASSEQUINCY Illinois 62305 0.175 

CROWN FOOD PACKAGING 1650 BROADWAY HANOVER Pennsylvania 17331 3.382 

NUCOR VULCRAFT GROUP GRAPELAND DIV 175 COUNTY RD 2345 GRAPELAND Texas 75844 0.174 BALL METAL BEVERAGE CONTAINER CORP 6600 WILL ROGERS BLVD FORT WORTH Texas 76140 5.5 

PENN COLOR INC 2755 BERGEY RD HATFIELD Pennsylvania 19440 0.176 FLINT HILLS RESOURCES LP - WEST PLANT 2825 SUNTIDE RD CORPUS CHRISTI Texas 78410 0.0075 DECORATIVE PANELS INTERNATIONA L 2900 HILL AVE TOLEDO Ohio 43607 13.32944 

L A DARLING CO - PIGGOTT AR FACILITY HWY 49 S PIGGOTT Arkansas 72454 0.152 TRI VULCRAFT OF NEW YORK INC 5362 RAILROAD ST CHEMUNG New York 14825 5.101 

BALL METAL BEVERAGE CONTAINER CORP 91-320 KOMOHANA ST KAPOLEI Hawaii 96707 2.3 3M CO - GUIN 6675 US HWY 43 GUIN Alabama 35563 0.001 

TOYOTA MOTOR MANUFACTURING KENTUCKY INC 1001 CHERRY BLOSSOM WAGEORGETOWN Kentucky 40324 0.375 

AMERICAN TRIM LLC 1501 W MICHIGAN ST SIDNEY Ohio 45365 0 

KEYMARK CORP OF FLORIDA 2540 KNIGHTS STATION RD LAKELAND Florida 33810 0.619 VESTAL MANUFACTURING ENTERPRISES INC 177 INDUSTRIAL PARK RD SWEETWATER Tennessee 37874 12.168 

GM TRUCK GROUP FORT WAYNE ASSEMBLY 12200 LAFAYETTE CENTER ROANOKE Indiana 46783 0.65 

NOVELIS CORP 390 GRISWOLD ST NE WARREN Ohio 44483 3.543 BERENFIELD CONTAINERS INC MASON 1229 CASTLE DR MASON Ohio 45040 0.125 

Page 5 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

HOWARD FINISHING LLC 32565 DEQUINDRE MADISON HEIGHTS Michigan 48071 0.0025 

SILGAN CONTAINERS MANUFACTURING CORP 305 W N ST MOUNT VERNON Missouri 65712 2.35 

FRANKLIN INVESTMENT CORP 600 ATLANTIC AVE FRANKLIN Pennsylvania 16323 11.6 

CHICAGO STEEL CONTAINER CORP 1846 S KILBOURN AVE CHICAGO Illinois 60623 1.453 

MEYER STEEL DRUM INC 2000 S KILBOURN AVE CHICAGO Illinois 60623 1.247 

RINECO 1007 VULCAN RD- HASKELL BENTON Arkansas 72015 0.0495 

CARRY-ON TRAILER CORP 101 JOE HARVEY ST LAVONIA GEORGIA 30553 0 

SHAMROCK TECHNOLOGIES FOOT OF PACIFIC ST NEWARK NEW JERSEY 07114 0 

FORD MOTOR COMPANY-WAYNE ASSEMBLY 37625 MICHIGAN AVE WAYNE Michigan 48184 0.125 

PRECOAT METALS 1095 MENDELL DAVIS DR JACKSON Mississippi 39272 10.083 

BOEING COMMERCIAL AIRPLANE GROUP - EVERETT 3003 W CASINO RD EVERETT Washington 98204 2 PHOENIX COLOR CORP 18249 PHOENIX DR HAGERSTOWN MARYLAND 21742 11 

GEA BPO LLC 301 N CURRY PIKE BLOOMINGTON Indiana 47404 0 PROFESSIONAL DISPOSABLES INTERNATIONAL INC TWO NICE-PAK PARK ORANGEBURG New York 10962 0.10232 0TRILLA ST LOUIS CORP 2391 CASSENS DR FENTON MISSOURI 63026 1.59594 8

CARRY-ON TRAILER CORP 931 INDUSTRIAL BLVD MEXIA TEXAS 76667 0 MAVERICK TUBE LLC DBA TENARISCONROE 699 FM 3083 CONROE TEXAS 77301 0.423225 10.1

ACME FINISHING CO INC 1595 E OAKTON ST ELK GROVE VILLAGEIllinois 60007 2.089 

STATE INDUSTRIES INC 500 TENNESSEE WALTZ PK

WASHLAND CITY TENNESSEE 37015 0.104 

ANDERSON TULLY LUMBER CO WALTERSVILLE LUMBER MILL

1725 N WASHINGTON ST VICKSBURG MISSISSIPPI 39181 10.4095 

3M CO - CORDOVA 22614 RT 84 N CORDOVA Illinois 61242 0.7 

NUCOR CORP VULCRAFT/NUCOR COLD FINISH DIV 1601 W OMAHA AVE NORFOLK Nebraska 68701 0.26 

SILGAN CAN CO 2120 NC HWY N UNIT A MAXTON North Carolina 28364 3.2155 

SYCAMORE SYSTEMS LLC 449 N CALIFORNIA ST SYCAMORE ILLINOIS 60178 0 ASHLEY INDUSTRIAL MOLDING INC 310 S WABASH ASHLEY Indiana 46705 1.05 

BERENFIELD CONTAINERS SW LTD 3300 N HUTCHINSON ST WHITE HALL Arkansas 71602 0 

STANLEY WORKS HAND TOOLS DIV 600 MYRTLE ST NEW BRITAIN Connecticut 06052 0.997 SILGAN CONTAINERS MANAUFACTURING CORP 520 W 2ND ST OCONOMOWOC Wisconsin 53066 1.65 

RR DONNELLEY & SONS CO 1145 CONWELL AVE WILLARD Ohio 44890 7.5445 

Page 6 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

AKZO NOBEL COATINGS INC 1629 VANDERBILT RD BIRMINGHAM Alabama 35234 9.755 

CAN CORP OF AMERICA INC 326 JUNE AVE BLANDON Pennsylvania 19510 2.6565 

NUCOR CORP VULCRAFT DIV 1501 W DARLINGTON ST FLORENCE South Carolina 29501 8.9355 

SAFETY-KLEEN SYSTEMS INC 130 A FRONTAGE RD LEXINGTON South Carolina 29073 0 

NUCOR CORP VULCRAFT DIV 7205 GAULT AVE N FORT PAYNE Alabama 35967 6.1415 

YKK AP AMERICA INC 332 FIRETOWER RD DUBLIN Georgia 31021 9.3205 

QUAD/GRAPHICS INC N63 W23075 STATE HWY 74 SUSSEX Wisconsin 53089 8.62 

SIGNODE 7701 W 71ST ST BRIDGEVIEW Illinois 60455 0.95 SQUARE D CO 1601 MERCER RD LEXINGTON Kentucky 40511 0 

NUCOR VULCRAFT GROUP SAINT JOE DIV 6610 COUNTY RD 60 SAINT JOE Indiana 46785 3.5585 REXAM BEVERAGE CAN CO FAIRFIELD PLANT 2433 CROCKER CIR FAIRFIELD California 94533 5.4255 

KUBIN-NICHOLSON CORP 8448 N 87TH ST MILWAUKEE Wisconsin 53224 9.296 NATIONAL COATINGS INC 604 US HWY 150 E GALESBURG ILLINOIS 61401 9.247 

SILGAN CONTAINERS MANUFACTURING CORP 2115 SW LOWER LAKE RD SAINT JOSEPH Missouri 64504 5.4375 GREIF PACKAGING LLC 6000 JEFFERSON HWY NEW ORLEANS Louisiana 70123 3.396 

ALLIANCE INDUSTRIES WAUPACA N 2467 VAUGHAN RD WAUPACA Wisconsin 54981 0.8605 

COOK COMPOSITES & POLYMERS CO 340 RAILROAD ST SAUKVILLE Wisconsin 53080 0.866 

LA-Z-BOY TENNESSEE 500 WALNUT GROVE RD DAYTON Tennessee 37321 0 8.57

ESCO CORP 9098 EASTSIDE DR EXT NEWTON Mississippi 39345 8.5565 

HEXION SPECIALTY CHEMICALS INC 2525 S COMBEE RD LAKELAND Florida 33801 8.39 

CNH AMERICA LLC 600 E PEORIA ST GOODFIELD ILLINOIS 61742 0.125 

WHITING DOOR MANUFACTURING CORP 113 CEDAR ST AKRON New York 14001 0 

CIRCLE GRAPHICS INC 120 9TH AVE LONGMONT Colorado 80501 3 

BALL AEROSOL & SPECIALTY CONTAINER INC 1717 GIFFORD RD ELGIN Illinois 60120 0.85 

SILGAN CAN CO 12-773 ST RT 110 NAPOLEON Ohio 43545 2.3235 

DOW CHEMICAL CO FREEPORT FACILITY 2301 N BRAZOSPORT BLVD FREEPORT Texas 77541 0.4605 

SHIELDCOAT TECHNOLOGIES INC (DBA CYBERSHIELD OF TEXAS)

2602 SPENCE ST LUFKIN Texas 75904 8.303 

KAWNEER CO INC 600 KAWNEER DR SPRINGDALE Arkansas 72764 3.3635 

AM GENERAL LLC 13200 MCKINLEY HWY MISHAWAKA INDIANA 46545 0 

Page 7 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

CNH AMERICA LLC 1930 DES MOINES AVE BURLINGTON Iowa 52601 0.175 

SUPERIOR INDUSTRIES INTERNATIONAL ARKANSAS LLC 1901 E BORICK DR FAYETTEVILLE ARKANSAS 72701 0 SILGAN CONTAINERS MANUFACTURING CORP 1416 INDIANHEAD DR MENOMONIE Wisconsin 54751 1.6 

CROWN AEROSOL PACKAGING 3737 E EXCHANGE AVE AURORA Illinois 60504 7.0285 

CARRY-ON TRAILER CORP 1965 HWY 30 MISSOURI VALLEY Iowa 51555 0 

BROAN-NUTONE LLC 926 W STATE ST HARTFORD Wisconsin 53027 0.1135 

ROLL COATER 858 E HUPP RD LA PORTE Indiana 46350 0 

VON HOFFMANN GRAPHICS INC 1005 COMMERCIAL DR OWENSVILLE Missouri 65066 6.5635 

GMVM-LANSING GRAND RIVER ASSEMBLY 920 TOWNSEND ST MAIL COLANSING Michigan 48921 3.45 

GREIF INDUSTRIAL PACKAGING & SERVICES 7604 RAILROAD AVE WINFIELD Kansas 67156 0.7535 

HUTCHENS INDUSTRIES INC MANSFIELD FACILITY 898 E COMMERCIAL MANSFIELD MISSOURI 65704 0 

3M CO - MENOMONIE 1425 STOKKE PKWY MENOMONIE Wisconsin 54751 0 CARRY-ON TRAILER CORP 5300 WESTMORELAND RD WINNEMUCCA NEVADA 89445 0 AKZO NOBEL SURFACE CHEMISTRY LLC 15200 ALMEDA RD HOUSTON Texas 77053 0.445 

ELECTROPRIME INC 63 DIXIE HWY ROSSFORD Ohio 43460 0 

DEXTER AXLE 500 SE 27TH EL RENO OKLAHOMA 73036 0 EQUISTAR CHEMICALS BAYPORT CHEMICALS PLANT 5761 UNDERWOOD RD PASADENA Texas 77507 6.7145 

MICHELIN NORTH AMERICA INC 5101 21ST ST TUSCALOOSA Alabama 35401 0.003 U.S. AIR FORCE TINKER AFB OK 7701 ARNOLD ST SUITE 204 TINKER A F B Oklahoma 73145 1.3 

NAHAN PRINTING INC 7000 SAUKVIEW DR SAINT CLOUD Minnesota 56303 7.061195 0

CHRYSLER BELVIDERE ASSEMBLY PLANT 3000 W CHRYSLER DR BELVIDERE Illinois 61008 0.8 TECNOCAP LLC 2100 GRISWOLD NE WARREN Ohio 44483 1.5755 

AFTON CHEMICAL CORP 725 CANNON BRIDGE RD ORANGEBURG South Carolina 29115 2.813 

GENERAL MOTORS WENTZVILLE ASSEMBLY 1500 E RT A WENTZVILLE Missouri 63385 1.25 

GENERAL MOTORS CORP LORDSTOWN COMPLEX 2300 HALLOCK-YOUNG RD LORDSTOWN Ohio 44481 3.15 ROLL COATER INC 4502 FREEDOM WAY WEIRTON West Virginia 26062 0 

WIX FILTRATION CORP - ALLEN PLANT 2900 NW BLVD GASTONIA North Carolina 28052 0.0025 

ALCOA INC - WARRICK OPERATIONS HWYS 66 & 61 NEWBURGH Indiana 47629 0 

RR DONNELLEY CRAWFORDSVILLE 1009 SLOAN ST CRAWFORDSVILLE Indiana 47933 6.805 

Page 8 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

Fug

Emis

(tp

KITZINGER COOPERAGE CORP 2529 E NORWICH AVE SAINT FRANCIS Wisconsin 53235 0 

JOHN DEERE DES MOINES WORKS 825 SW IRVINEDALE DR ANKENY IOWA 50023 0 

AVERY DENNISON - IBMD LENOIR 950 GERMAN ST LENOIR North Carolina 28645 5.725 

BRIGHTSMITH LLC 120 ENTERPRISE AVE MORRISVILLE Pennsylvania 19067 0.06 

SILGAN CAN CO 500 NW LOOP 286 SUITE 101PARIS Texas 75460 4.034 

ENKEI AMERICA INC 2900 W INWOOD DR COLUMBUS Indiana 47201 0 

CARDONE INDUSTRIES 5660 RISING SUN AVE PHILADELPHIA Pennsylvania 19120 1.367 

MAUSER CORP 14 CONVERY BLVD WOODBRIDGE New Jersey 07095 0.0585 HAMMER PACKAGING CORP 200 LUCIUS GORDON DR WEST HENRIETTA New York 14586 0 

BRIGGS & STRATTON YARD POWER PRODUCTS MCDONOUGH OPERATIONS

535 MACON RD MC DONOUGH GEORGIA 30253 0 

SUPERIOR INDUSTRIES INTERNATIONAL ARKANSAS LLC 1301 N DIXIELAND RD ROGERS ARKANSAS 72756 0.0025 AAP ST MARYS CORP 1100 MCKINLEY RD SAINT MARYS Ohio 45885 0.0245 BERENFIELD CONTAINERS INC 31 RAILROAD ST CLARENDON Pennsylvania 16313 0.073365 SENECA FOODS CORP CAN PLANT 3709 MILL ST MARION New York 14505 0 

RR DONNELLEY LANCASTER EAST 216 GREENFIELD RD LANCASTER Pennsylvania 17601 6.2035 

CREE INC 4600 SILICON DR DURHAM North Carolina 27703 0 

HUSQVARNA CONSUMER OUTDOOR PRODUCTS 172 OLD ELLOREE RD ORANGEBURG South Carolina 29116 0.1325 

OWENS CORNING VETROTEX LLC 4837 HWY 81 S STARR South Carolina 29684 0.656 

WHEELING MACHINE PRODUCTS DIV PINE BLUFF 5411 INDUSTRIAL DR S PINE BLUFF ARKANSAS 71602 6.5 SILGAN CONTAINERS MANUFACTURIN G CORP 3591 MAPLE DR FORT DODGE IOWA 50501 0.00028 

SKOLNIK INDUSTRIES 4900 S KILBOURN AVE CHICAGO ILLINOIS 60632 0.65 

NISSAN NORTH AMERICA INC CANTON MS 300 NISSAN DR CANTON Mississippi 39046 2.534 

SILGAN CONTAINERS MANUFACTURING CORP 2501 165TH ST HAMMOND Indiana 46320 0 

SAPA EXTRUSIONS INC 2500 ALUMAX RD YANKTON South Dakota 57078 0 6.31

BRADFORD WHITE CORP 200 LAFAYETTE ST MIDDLEVILLE Michigan 49333 0 

MAYTAG CORP CLEVELAND COOKING PRODUCTS PLANT 1

740 KING EDWARD AVE SE CLEVELAND Tennessee 37311 0 

EFCO CORP 1000 COUNTY RD MONETT Missouri 65708 0.958 

HUNTER DOUGLAS TUPELO CENTER RT 2 LEE INDUSTRIAL PARKSHANNON Mississippi 38868 0.2935 5

Page 9 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

NAVISTAR INC 6125 URBANA RD SPRINGFIELD Ohio 45502 0.6 

SILGAN CAN CO 6200 FRANKLIN BLVD SUITESACRAMENTO California 95824 5.1925 

THE COLEMAN CO INC 3600 N HYDRAULIC WICHITA KANSAS 67219 0.001 

AK STEEL CORP - ZANESVI LLE WORKS 1724 LINDEN AVE ZANESVILLE Ohio 43701 0 BOBCAT CO (MELROE) 210 1ST AVE NE GWINNER NORTH DAKOT 58040 0 

PACKAGING DYNAMICS INC BAGCRAFT/PAPERCON DIV 3400 BAGCRAFT BLVD BAXTER SPRINGS Kansas 66713 5.9425 

CHRYSLER WARREN TRUCK ASSEMBLY PLANT (PART) 21500 MOUND RD WARREN Michigan 48091 5.5 

QUEBECOR WORLD INC WINCHESTER VIRGINIA 160 CENTURY LN STONEWAWINCHESTER Virginia 22603 5.48138 

GREIF PACKAGING LLC 2400 COOPER AVE MERCED California 95348 4.5705 SCHAEFFER MANUFACTURING 102 BARTON ST SAINT LOUIS Missouri 63104 5.84243 

WORTHINGTON CYLINDERS WISCONSI N LLC 300 E BREED ST CHILTON Wisconsin 53014 0.8835 

SILGAN CONTAINERS MANUFACTURING CORP 400 N 15TH ST ROCHELLE Illinois 61068 4.3695 TTM TECHNOLOGIES INC 710 N 600 W LOGAN Utah 84321 0.432 

NAZDAR SHAWNEE 8501 HEDGE LN TERRACE SHAWNEE Kansas 66227 1.7235 ALCOA HOME EXTERIORS INC 2615 CAMPBELL RD SIDNEY Ohio 45365 0.8075 

TACO INC - CRANSTON 1160 CRANSTON ST CRANSTON RHODE ISLAND02920 0.0575 

METOKOTE CORP PLANT 15 312 SAVANNAH CEDAR FALLS Iowa 50613 0 INX DIGITAL INK CO 405 INDUSTRIAL WAY DIXON California 95620 5.621 

NOVOLYTE TECHNOLOGIES 111 W IRENE RD ZACHARY Louisiana 70791 5.05 

PRECOAT METALS 25 NORTHGATE INDUSTRIA GRANITE CITY Illinois 62040 4.516 

DUPONT PONTCHARTRAIN WORKS 586 HWY 44 LA PLACE Louisiana 70068 0.006 

SILGAN CONTAINERS MANUFACTURING CORP 135 NATIONAL RD EDISON New Jersey 08817 4.45 KNS COMPANYS INC 475 RANDY RD CAROL STREAM Illinois 60188 1.099 

LOGAN ALUMINUM INC US HWY 431 N RUSSELLVILLE Kentucky 42276 0.0355 DU PONT ELECTRONICS MICROCIRCU ITS INDUSTRIES LTD

HWY 686 KM 23 MANATI PUERTO RICO 00674 0 

NOV TUBOSCOPE NAVASOTA 9574 FM 1227 NAVASOTA Texas 77868 4.911 

AJAX METAL PROCESSING INC 4651 BELLEVUE AVE DETROIT MICHIGAN 48207 0 

FIBERMARK NORTH AMERICA INC 5492 BOSTWICK ST LOWVILLE New York 13367 0.083 

PPG INDUSTRIES,INC-SPRINGDALE COMPLEX 125 COLFAX ST SPRINGDALE Pennsylvania 15144 5.2425 

Page 10 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

BATESVILLE MANUFACTURING INC -DOLL PLANT 1000 E PEARL ST BATESVILLE Indiana 47006 0.265 

AUTOALLIANCE INTERNATIONAL INC 1 INTERNATIONAL DR FLAT ROCK Michigan 48134 0.48 

ARMSTRONG HARDWOOD FLOORING CO 565 HARTCO DR ONEIDA Tennessee 37841 0 

US ARMY LAKE CITY ARMY AMMUNITION PLANT INTERSECTION OF MO HWYINDEPENDENCE Missouri 64051 1.302 

RUSKIN CO HWY 27 N GENEVA Alabama 36340 0.019 

PELLA CORP CARROLL OPERATIONS 1750 E US HWY 30 E CARROLL IOWA 51401 0 

GREIF PACKAGING LLC 695 LOUIS DR WARMINSTER Pennsylvania 18974 2.1455 

HYDRO ALUMINUM NORTH AMERICA INC 808 COUNTY RD MONETT MISSOURI 65708 0.252 

RR DONNELLEY LANCASTER WEST 1375 HARRISBURG PIKE LANCASTER Pennsylvania 17601 4.5877 PRECOAT METALS 16402 JACINTOPORT BLVD HOUSTON Texas 77015 4.5625 

PHOENIX CONTAINER INC 1202 AIRPORT RD NORTH BRUNSWICKNew Jersey 08902 1.871 

SILGAN CONTAINER MANUFACTURING CORP 3250 PATTERSON RD RIVERBANK California 95367 0.2825 

FORD MOTOR CO TWIN CITIES ASSEMBLY PLANT 966 S MISSISSIPPI RIVER BLSAINT PAUL Minnesota 55116 0.39 

CROWN AEROSOL PACKAGING 4TH ST & PARK AVE FARIBAULT Minnesota 55021 3.029 

HYUNDAI MOTOR MANUFACTURING ALABAMA LLC 700 HYUNDAI BLVD MONTGOMERY Alabama 36105 2.7715 

COLOR COMMUNICATIONS INC 4242 W FILLMORE CHICAGO Illinois 60624 0.81 

PRECOAT METALS 4301 S SPRING AVE SAINT LOUIS Missouri 63116 1.073 

PRIME TANNING CO - HARTLAND 9 MAIN ST HARTLAND Maine 04943 0.0915 

RR DONNELLEY-WETMORE PLANT 1645 W SAM HOUSTON PK

WHOUSTON TEXAS 77043 4.5675 

VOLVO TRUCKS NORTH AMERICA 4881 COUGAR TRAIL RD DUBLIN VIRGINIA 24084 2.15 R R DONNELLEY & SONS CO DANVILLE DIV JOHN HILL BAILEY INDL PARDANVILLE Kentucky 40422 4.208 

NESTLE PURINA PETCARE 1000 HAMILTON RD WEIRTON West Virginia 26062 1.2665 

IMPRESS USA INC 936 BARRACUDA ST TERMINAL ISLAND California 90731 4.1 

BROWN PRINTING CO 2300 BROWN AVE WASECA Minnesota 56093 4.4155 CURTIS METAL FINISHING CO 6645 SIMS DR STERLING HEIGHTS Michigan 48313 3.19 ARVINMERITOR HEAVY VEHICLE SYSTEMS LLC 801 RAILROAD AVE YORK South Carolina 29745 0.001 ENDICOTT INTERCONNECT TECHNOLOGIES INC 1093 CLARK ST ENDICOTT New York 13760 0.25 

WORLDCOLOR 451 INTERNATIONAL BLVD CLARKSVILLE Tennessee 37040 3.7745 

MERIX CORP 1521 POPLAR LN FOREST GROVE Oregon 97116 0.0835 INLAND LABEL & MARKETING 2009 W AVE S LA CROSSE Wisconsin 54601 2.0245 

Page 11 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

SAPA EXTRUDER INC 2905 OLD OAKWOOD RD GAINESVILLE Georgia 30504 0 

CARRY-ON TRAILER CORP 159 INDUSTRIAL PARK RD MONTROSS VIRGINIA 22520 0 GENIE INDUSTRIES SOUTH CAMPUS 18700 NE 65TH ST REDMOND Washington 98052 0.23425 

SEQUA COATINGS CORP-PRECOAT M ETALS DIV US HWY 12 AT RT 249 PORTAGE Indiana 46368 0.284 

BROWN PRINTING CO 11595 MCCONNELL RD WOODSTOCK Illinois 60098 3.915 METAL COATERS MISSISSIPPI 951 PRISOCK RD JACKSON Mississippi 39272 0 

BALL METAL FOOD CONTAINER CORP 300 W GREGER RD OAKDALE California 95361 0.134 

HIRSH INDUSTRIES INC 1525 MCKEE RD DOVER Delaware 19904 0.0025 

SILGAN CONTAINERS MANUFACTURING CORP N90 W14600 COMMERCE DRMENOMONEE FALLSWisconsin 53051 0 

BETCO CORP 1001 BROWN AVE TOLEDO Ohio 43607 3.885 QUEBECOR WORLD DIRECT-PETTY 420 W INDUSTRIAL AVE EFFINGHAM Illinois 62401 3.43 

MAGNA MIRRORS CORP - NEWAYGO 700 S PARK DR NEWAYGO MICHIGAN 49337 1.1175 

GMTG - SHREVEPORT ASSEMBLY 7600 GENERAL MOTORS BL SHREVEPORT Louisiana 71129 0.095 

VAN CAN CO 10837 ETIWANDA AVE FONTANA California 92337 3.2 

CROWN FOOD PACKAGING 10200 N LOMBARD ST PORTLAND Oregon 97203 1.583 

TAIYO AMERICA INC 2675 ANTLER DR CARSON CITY Nevada 89701 0.005 

BROWN PRINTING CO 668 GRAVEL PIKE EAST GREENVILLE Pennsylvania 18041 3.423 

RR DONNELLEY & SONS CO 6821 E COUNTY RD 1100 N MATTOON ILLINOIS 61938 3.2385 BRILLION IRON WORKS INC 200 PARK AVE BRILLION Wisconsin 54110 2.4496 

OMG AMERICAS TWO MILE RUN RD FRANKLIN Pennsylvania 16323 0.025 TITAN COATINGS INC 2025 EXCHANGE PL BESSEMER Alabama 35023 3.42 

TTM PRINTED CIRCUIT GROUP - S TAFFORD DIV 4 OLD MONSON RD STAFFORD Connecticut 06075 0 

TORO CO 200 SIME AVE TOMAH Wisconsin 54660 0 

ALERIS ROLLED PRODUCTS INC 1372 KY HWY 1957 LEWISPORT Kentucky 42351 0.125 

AVERY DENNISON INDUSTRIAL PRODUCTS DIV 17700 FOLTZ PKWY STRONGSVILLE Ohio 44149 0.431 

RADIATOR SPECIALTY CO 600 RADIATOR RD INDIAN TRAIL North Carolina 28079 2.1845 CENTURY INDUSTRIAL COATINGS I NC HWY 69 S JACKSONVILLE Texas 75766 0.074 

SILGAN CONTAINERS MANUFACTURING CORP 8673 LYONS-MARENGO RD LYONS New York 14489 0.5625 

GM SPRING HILL MANUFACTURING 100 SATURN PKWY MAIL DRSPRING HILL Tennessee 37174 0.0065 

QUAD/GRAPHICS INC 555 S 108TH ST WEST ALLIS WISCONSIN 53214 3.17 

Page 12 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

BATESVILLE MANUFACTURING INC 310 CROWN RD BATESVILLE Mississippi 38606 0.488 

PRECOAT METALS 3399 DAVEY ALLISON BLVD HUEYTOWN Alabama 35023 2.5065 

MIDDLEBURY HARDWOOD PRODUCTS 101 JOAN DR MIDDLEBURY INDIANA 46540 0 

WORLDCOLOR LEBANON DIV 760 FUJITEC DR LEBANON Ohio 45036 3.1125 

CADON PLATING CO 3715 11TH ST WYANDOTTE Michigan 48192 1.6414 1SONOCO PHOENIX - PRESIDENTS ISLAND 2755 HARBOR AVE MEMPHIS Tennessee 38113 0 

RR DONNELLEY STRASBURG DIV ONE SHENANDOAH VALLEYSTRASBURG Virginia 22657 2.95 

BASF CORP - CLEAR LAKE PLANT 11200 BAY AREA BLVD PASADENA Texas 77507 3.0356 0.043

KAWASAKI MOTORS MANUFACTURING CORP USA 6600 NW 27TH ST LINCOLN Nebraska 68524 0.2995 

SPRAYLAT CORP CA 3465 S LA CIENAGA BLVD LOS ANGELES California 90016 1.5375 

U.S. AIR FORCE ROBINS AFB GA 775 MACON ST BUILDING 15ROBINS AFB Georgia 31098 2.4135 

RR DONNELLEY LOS ANGELES MANUFACTURING 19681 PACIFIC GATEWAY D TORRANCE California 90502 2.9545 

JELD-WEN 600 JELD-WEN RD CRAIGSVILLE WEST VIRGINIA26205 0.1395 

BENJAMIN MOORE & CO JOHNSTOWN UNION AVE EXTENSION JOHNSTOWN New York 12095 0.0148 0

ST CHARLES OPERATIONS (TAFT/STAR) UNION CARBIDE CORP

355 LA HWY 3142 (GATE 1) TAFT Louisiana 70057 0.2455 

VERTIS COMMUNICATIONS 4051 FONDORF DR COLUMBUS Ohio 43228 2.5835 

DOW CHEMICAL CO 1790 BUILDING MIDLAND Michigan 48667 2.75 QUAD/GRAPHICS INC N11896 HWY 175 PO BOX 27LOMIRA WISCONSIN 53048 2.5685 

TOYOTA MOTOR MANUFACTURING TEX AS INC 1 LONE STAR PASS SAN ANTONIO Texas 78264 2.39455575 0.42GM MLCG FAIRFAX ASSEMBLY 3201 FAIRFAX TRAFFICWAYKANSAS CITY Kansas 66115 0.032 SOLIANT LLC 1872 HWY 9 BYPASS W LANCASTER South Carolina 29721 0.554 

KIA MOTORS MANUFACTURING OF GEORGIA 7777 KIA PKWY WEST POINT GEORGIA 31833 0.0525 

APOLLO COLORS INC 1550 MOUND RD ROCKDALE Illinois 60436 0 

VERTIS COMMUNICATIONS 10911 GRANITE ST CHARLOTTE North Carolina 28273 2.3815 

ABC COMPOUNDING CO INC 6970 JONESBORO RD MORROW Georgia 30260 0.0025 

ITW DYMON 805 E OLD 56 HWY OLATHE Kansas 66061 0.7835 

FORD MOTOR CO - OHIO ASSEMBLY PLANT 650 MILLER RD AVON LAKE Ohio 44012 2.4 

ARR-MAZ CUSTOM CHEMICALS 4800 STATE RD 60 E MULBERRY Florida 33860 0.101 

BON L MANUFACTURING CO HWY 53 BONNELL RD CARTHAGE Tennessee 37030 0.5795 

DERRICK CORP 3350 UNION RD CHEEKTOWAGA New York 14225 0 

Page 13 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

TYCO FIRE SUPPRESSION & BUILDING PRODUCTS 1 STANTON ST MARINETTE Wisconsin 54143 0.0035 IC OF OKLAHOMA LLC 2322 N MINGO RD TULSA Oklahoma 74116 0 BWAY CORP BWAY PACKAGING DIV 8200 BROADWELL RD CINCINNATI Ohio 45244 1.65079 BRUNSWICK CORP MERCURY MARINE DIV W6250 PIONEER RD FOND DU LAC Wisconsin 54935 0.2525 ACCESS BUSINESS GROUP LLC 7575 FULTON ST E ADA Michigan 49355 2.3755 MISSION KLEENSWEEP PRODUCTS INC 2434 BIRKDALE ST LOS ANGELES California 90031 2.5 ROHM & HAAS CHEMICALS LLC 200 RT 413 BRISTOL Pennsylvania 19007 0.05715 POWER PARTNERS INC 200 NEWTON BRIDGE RD ATHENS Georgia 30607 0 AMERICAN COLOR GRAPHICS 810 E S ST MARENGO Iowa 52301 2.2715 CENTRIA 530 N SECOND ST CAMBRIDGE Ohio 43725 1.209 CUMMINS POWER GENERATION 1400 73RD AVE NE FRIDLEY Minnesota 55432 0.12 HEWLETT-PACKARD CARIBE BV SITE HWY 110 N KM 5.1 AGUADILLA Puerto Rico 00605 0.125 MOTOR CASTINGS CO 1323 S 65TH MILWAUKEE Wisconsin 53214 0 VERTIS INC RNS SPRINGFIELD DIV 245 BENTON DR EAST LONGMEADO

WMASSACHUSET01028 2.311 

CADMUS SPECIALTY PUBLICATIONS 2901 BYRDHILL RD RICHMOND VIRGINIA 23228 2.242785 0ROPPE CORP 1602 N UNION ST FOSTORIA Ohio 44830 0.125 

CCL CONTAINER AEROSOL DIV ONE LLODIO DR HERMITAGE Pennsylvania 16148 0.1835 

AMERICAN COLOR GRAPHICS - LUFKIN 3001 ATKINSON DR LUFKIN Texas 75901 2.2015 

IVC SOUTH 875 PROGRESS CENTER AVLAWRENCEVILLE Georgia 30043 0.4575 

NCP COATINGS INC 225 FORT ST NILES Michigan 49120 2.275 DENSO MANUFACTURING TENNESSEE INC 1720, 1725, 1755 ROBERT C MARYVILLE Tennesee 37801 0 

3M CO - HUTCHINSON 905/915 ADAMS ST SE HUTCHINSON Minnesota 55350 0 

SABIC INNOVATIVE PLASTICS MT VERNON LLC 1 LEXAN LN MOUNT VERNON Indiana 47620 1.3 HONDA MANUFACTURING OF INDIANA LLC 2755 N MICHIGAN AVE GREENSBURG Indiana 47240 1.7 

GATES CORP 1450 MONTANA RD IOLA KANSAS 66749 0 

GREIF PACKAGING LLC 10850 STRANG RD LA PORTE Texas 77571 1.6775 

VANEX INC 1700 S SHAWNEE ST MOUNT VERNON Illinois 62864 0 

RED SPOT WESTLAND INC 550 S EDWIN ST WESTLAND Michigan 48186 1.192 BENCHMARK ENERGY PRODUCTS LLC 4113 W INDUSTRIAL AVE MIDLAND Texas 79703 0.191 

VERTIS 7619 DOANE DR MANASSAS VIRGINIA 20109 1.9855 

Page 14 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

BRENNTAG SOUTHWEST INC LANC ASTER 704 E WINTERGREEN RD LANCASTER Texas 75134 0.0225 

HANNA STEEL CORP 3812 COMMERCE AVE FAIRFIELD Alabama 35064 0.77 

SAPA INC COATINGS DIVSION 5325 NE SKYPORT WAY PORTLAND Oregon 97218 1.6348493 0.38

CLEVELAND STEEL CONTAINER - NI LES 115 ERIE ST NILES Ohio 44446 0.0025 WORLD COLOR PRESS 50 JOHN HANCOCK RD TAUNTON Massachusetts 02780 1.605 DUPONT YERKES PLANT 3115 RIVER RD BUFFALO New York 14207 0.753 

CLEVELAND STEEL CONTAINER CORP 350 MILL ST QUAKERTOWN PENNSYLVANIA18951 0.0145 

KEYMARK CORP 1188 CAYADUTTA ST RT 334FONDA New York 12068 0.007 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

901 N GREENWOOD AVE KANKAKEE Illinois 60901 0.8285 

PPG INDUSTRIES ARCHITECTURAL FINISHES 1020 OLYMPIC DR BATAVIA Illinois 60510 0 

ZEP INC 1310 SEABOARD INDUSTRIAATLANTA Georgia 30318 0.117 

ASTRO COATINGS INC 27 MAIN ST STRUTHERS Ohio 44471 0.5915 FORD LOUISVILLE ASSEMBLY 2000 FERN VALLEY RD LOUISVILLE Kentucky 40213 0.215 REICHHOLD INC 425 S PACE BLVD PENSACOLA Florida 32502 0.169 

VERTIS COMMUNICATIONS 4646 S GRADY AVE TAMPA FLORIDA 33611 1.7675 

CONSOLIDATED SYSTEMS INC 650 ROSEWOOD DR COLUMBIA South Carolina 29201 0 SC JOHNSON & SON INC WAXDALE FACILITY 8311 16TH ST STURTEVANT Wisconsin 53177 0.125 

GATES CORP - CHARLESTON 1300 S PLANT RD CHARLESTON Missouri 63834 0 

WARREN UNILUBE INC 1200 S 8TH ST WEST MEMPHIS Arkansas 72301 1.892 

IMPRESS USA INC 3030 BIRCH DR HALF MOONWEIRTON West Virginia 26062 0.0065 

DURA COAT PRODUCTS INC 26655 PEOPLES RD MADISON Alabama 35756 1.64203 AKZONOBEL AEROSPACE COATINGS 1 E WATER ST WAUKEGAN Illinois 60085 0.916 

GENERAL MOTORS MLCG DETROIT-HAMTRAMCK ASSEM BLY CENTER

2500 E GENERAL MOTORS BDETROIT Michigan 48211 1.6 

PRO LINE PRINTING / RR DONNELLEY 365 PARR CIR RENO Nevada 89512 1.759 

EASTMAN CHEMICAL CO TENNESSEE OPERATIONS 100 EASTMAN RD KINGSPORT Tennessee 37662 0.8855 

BALL METAL FOOD CONTAINER CORP 1200 S CRUTCHER ST SPRINGDALE Arkansas 72764 0.09 COLOR CORP OF AMERICA 1630 W HILL ST LOUISVILLE Kentucky 40210 0.009 RHODIA INC 2ND ST & BLUEBALL AVE MARCUS HOOK Pennsylvania 19061 0.201 

CAMACO COLUMBUS MANUFACTURING 1851 E 32ND AVE COLUMBUS Nebraska 68601 0 

Page 15 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

RR DONNELLEY PINEVILLE 10519 INDUSTRIAL DR PINEVILLE North Carolina 28134 1.6305 

STEELSCAPE INC 7001 ALLISON-BONNET MEMFAIRFIELD Alabama 35064 0.003895 1

SILGAN CONTAINERS MANUFACTURING CORP 2200 WILBUR AVE ANTIOCH California 94509 0 

FUJIFILM NORTH AMERICA CORP 20 W 14TH AVE NORTH KANSAS CIT Missouri 64116 0 

U S CHEMICAL 316 HART ST WATERTOWN Wisconsin 53094 0.00011 

EASTMAN KODAK CO EASTMAN BUSINESS PARK 1669 LAKE AVE ROCHESTER New York 14652 0.001 

DAIMLERCHRYSLER CORP TOLEDO ASSEMBLY PLANT 4000 STICKNEY AVE TOLEDO Ohio 43612 0.50765 

STP PRODUCTS MANUFACTURING CO 477 LEXINGTON AVE PAINESVILLE Ohio 44077 0.81 

HUNTSMAN PETROCHEMICAL LLC 5451 JEFFERSON CHEMICALCONROE Texas 77301 0 

RR DONNELLEY VON HOFFMANN CORP 321 WILSON DR JEFFERSON CITY Missouri 65109 1.534445 

J L CLARK INC 923 23RD AVE ROCKFORD Illinois 61104 0.26 

DOW CHEMICAL CO - LOUISIANA OPERATIONS 21255 LA HWY 1 S PLAQUEMINE Louisiana 70765 1.538 WORLDCOLOR - DYERSBURG DIV 2030 SYLVAN RD DYERSBURG Tennessee 38024 1.4305 

RANBAR ELECTRICAL MATERIALS INC RTE 993 ONE MILE W OF RTMANOR Pennsylvania 15665 0 

SILGAN WHITE CAP CORP 350 JAYCEE DR VALMONT INHAZLETON Pennsylvania 18201 0.75 

TEXAS FINISHING CO 1801 SURVEYOR BLVD CARROLLTON Texas 75006 0 

CARESTREAM HEALTH COLORADO 2000 HOWARD SMITH AVE 

WWINDSOR Colorado 80550 0.002 

CHRYSLER STERLING HEIGHTS ASSEMBLY PLANT 38111 VAN DYKE STERLING HEIGHTS Michigan 48312 0.55 WORLDCOLOR STILLWATER (WAS QUEBECOR WORLD - STILLWATER DIV)

100 W AIRPORT RD STILLWATER Oklahoma 74075 1.2965 

THIRD COAST PACKAGING INC PEARLAND 1871 MYKAWA PEARLAND Texas 77581 0 

RR DONNELLEY 100 QUALITY CT CHARLESTOWN Indiana 47111 1.362 

BAYOU COS INC 5200 CURTIS LN NEW IBERIA LOUISIANA 70560 1.4245 NICHOLS ALUMINUM ALABAMA INC 2001 HWY 20 W DECATUR Alabama 35601 1.135 

GMC TRUCK GROUP ARLINGTON ASSEMBLY PLANT 2525 E ABRAMS ST ARLINGTON Texas 76010 0.36 CARDINAL ALUMINUM CO PLAN T 3 4005 OAKLAWN DR LOUISVILLE Kentucky 40219 0.0485 

WHEELING CORRUGATING CO - BEECH BOTTOM PLANT 2481 RIVER RD WELLSBURG West Virginia 26070 0 

OHIO ART CO ONE TOY ST BRYAN Ohio 43506 0.944 PRO LINE PRINTING ARLINGTON 401 N GREAT SW PKWY ARLINGTON Texas 76011 1.25 

Page 16 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

372 CLEVELAND ST ROCHESTER Pennsylvania 15074 0.523 

GFX INTERNATIONAL 333 BARRON BLVD GRAYSLAKE Illinois 60030 0 HUNTSMAN PETROCHEMICAL LLC 3892 US HWY 90 DAYTON Texas 77535 0.001 CHROMASOURCE INC 2433 S CR 600 E COLUMBIA CITY Indiana 46725 0 VEYANCE TECHNOLOGIES INC 400 N GOODYEAR RD MOUNT PLEASANT Iowa 52641 0.0005 SHEBOYGAN PAINT CO 608 CANAL ST CEDARTOWN Georgia 30125 0.635 COOK COMPOSITES & POLYMERS CO 1415 STEELE AVE SW GRAND RAPIDS Michigan 49507 1.061 ICL-IP AMERICA INC 11636 HUNTINGTON GALLIPOLIS FERRY West Virginia 25515 0.005715 0RR DONNELLEY & SONS CO 60 SECURITY DR AVON Connecticut 06001 1.258 MASCO RETAIL CABINET GROUP LLC 423 HOPEWELL RD WAVERLY Ohio 45690 0.0055 CLEVELAND STEEL CONTAINER - PE OTONE FACILITY 117 E LINCOLN ST PEOTONE Illinois 60468 0.053 

CATERPILLAR INC 3701 STATE RD 26 E LAFAYETTE Indiana 47905 0.04 LION COPOLYMER LLC 5955 SCENIC HWY BATON ROUGE Louisiana 70805 0 GOODYEAR TIRE & RUBBER CO. AKRON TECHNICAL CENTER

200 S. MARTHA AVE AKRON Ohio 44309 0 

GENTEK BUILDING PRODUCTS 11 CRAGWOOD RD AVENEL New Jersey 07001 0.122 SUN CHEMICAL CORP 2445 PRODUCTION DR SAINT CHARLES Illinois 60174 0.185 PPG ARCHITECTURAL FINISHES EAST POINT 1377 OAKLEIGH DR EAST POINT Georgia 30344 0 AKZO NOBEL COATINGS INC 1313 WINDSOR AVE COLUMBUS Ohio 43211 0.7885 SPIRALKOTE FLEXIBLE PACKAGING 1200 CENTRAL FLORIDA PK ORLANDO FLORIDA 32837 0 

SPRAYLAT CORP IL 1701 E 122-ND ST CHICAGO Illinois 60633 0.06 

KIK (HOUSTON) INC 2921 CORDER ST HOUSTON Texas 77054 1.19 CP CONVERTERS INC 15 GRUMBACHER RD YORK PENNSYLVANIA17402 1.17007 

RED SPOT PAINT & VARNISH CO INC 1016 E COLUMBIA ST EVANSVILLE Indiana 47711 0.6865 

JOHN DEERE SEEDING & CYLINDER 501 RIVER DR MOLINE Illinois 61265 0 

VEYANCE TECHNOLOGIES INC 2701 W OMAHA AVE NORFOLK Nebraska 68701 0.03668 0

BJ CHEMICAL SERVICES 707 N LEECH HOBBS New Mexico 88240 0.014 

ARANDELL CORP N82 W13118 LEON RD MENOMONEE FALLSWisconsin 53051 1.094 

CHEMCOAT INC 2790 CANFIELDS LN MONTOURSVILLE Pennsylvania 17754 0.125 

W W HENRY 150 MOONEY DR BOURBONNAIS Illinois 60914 1.1105 

Page 17 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

DUBOIS CHEMICALS INC 3630 E KEMPER RD SHARONVILLE Ohio 45241 0 

BEAULIEU OF AMERICA PLANT 560-MODEL 950 RIVERBEND RD DALTON Georgia 30721 0 

TESORO REFINING & MARKETING CO - MANDAN REFINERY

900 OLD RED TRAIL NE MANDAN North Dakota 58554 1.1 

IVC INDUSTRIAL COATINGS INC 2245-50 VALLEY AVE INDIANAPOLIS Indiana 46218 0.21965 

VANGUARD PAINTS & FINISHES INC 1409 GREENE ST MARIETTA Ohio 45750 1.078 

WINSLOW-BROWNING INC 215 BROWNSVILLE AVE LIBERTY Indiana 47353 1.077 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

701 SHILOH RD GARLAND Texas 75042 0.5915 

GENERAL DYNAMICS ORDNANCE & TACTICAL SYSTEMS GARLAND

1200 N GLENBROOK GARLAND Texas 75040 0.002985 0

POLYMERIC IMAGING INC 117 E 14TH AVE NORTH KANSAS CIT Missouri 64116 0 

3M CO - BROWNWOOD 4501 HWY 377 S BROWNWOOD Texas 76801 0.0435 

HB FULLER 12110 HARLAND DR NE COVINGTON Georgia 30014 0.5815 COMPLEMENTARY COATINGS CORP 4701 O'DONNELL ST BALTIMORE Maryland 21224 1.029 UNITED PAINT & CHEMICAL 24671 TELEGRAPH RD SOUTHFIELD Michigan 48034 1.023 

COOK COMPOSITES & POLYMERS CO 2434 HOLMES RD HOUSTON Texas 77051 1.013 TTM TECHNOLOGIES INC 234 CASHMAN DR CHIPPEWA FALLS Wisconsin 54729 0 GENERAL MOTORS LLC BOWLING GREEN ASSEMBLY PLANT

600 CORVETTE DR BOWLING GREEN Kentucky 42101 0.1 

TTM TECHNOLOGIES-SANTA CLARA 407 MATHEW ST SANTA CLARA California 95050 0 NICHOLS ALUMINUM DAVENPORT 1725 ROCKINGHAM RD DAVENPORT Iowa 52802 0.2795 THREE RIVERS ALUMINUM CO 71 PROGRESS AVE CRANBERRY TOWNSPennsylvania 16066 0.3575 LEVLAD 9200 MASON AVE CHATSWORTH California 91311 0.000185 

SONY ELECTRONICS INC 4275 W MAIN ST DOTHAN Alabama 36305 0 

CANBERRA CORP 3610 HOLLAND-SYLVANIA R TOLEDO Ohio 43615 0.6 

PPG INDUSTRIES OHIO INC (CL) 3800 W 143 ST CLEVELAND Ohio 44111 0.4135 TEXAS INSTRUMENTS INC 12201 SW FWY MS600 STAFFORD Texas 77477 0.0025 

B-WAY PACKAGING INC 6 LITHO RD TRENTON New Jersey 08648 0.095 GATES CORP 1650 ROWE PKWY POPLAR BLUFF MISSOURI 63901 0 WESTERN METAL DECORATING CO 8875 INDUSTRIAL AVE RANCHO CUCAMON CALIFORNIA 91730 0.55 

HILLYARD INDUSTRIES INC 402 N 3TH ST SAINT JOSEPH Missouri 64501 0.3575 

Page 18 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

U.S. POLYMERS ACCUREZ LLC 300 E PRIMM ST SAINT LOUIS Missouri 63111 0.0045 

FORBO ADHESIVES LLC 7440 W DUPONT RD MORRIS Illinois 60450 0.896 NAPCO INC 125 MCFANN RD VALENCIA Pennsylvania 16059 0.817 

CRYSTAL FINISHING SYSTEMS INC 2608 ROSS AVE SCHOFIELD Wisconsin 54476 0 0.89HUNT REFINING CO A CORP 1855 FAIRLAWN RD TUSCALOOSA Alabama 35401 0.8905 

POLARTEC LLC 46 STAFFORD ST LAWRENCE MASSACHUSET1841 0.89 

SUN CHEMICAL CORP 1380 FORD RD MAUMEE Ohio 43537 0.133 

EXXONMOBIL CHEMICAL BATON ROUGE CHEMICAL PLANT

4999 SCENIC HWY BATON ROUGE Louisiana 70805 0.6 

HOVENSA LLC 1 ESTATE HOPE CHRISTIANSTED Virgin Islands 00820 0.702 

FINISHES UNLIMITED INC 482 WHEELER RD SUGAR GROVE Illinois 60554 0.438 

UNIVAR USA INC HOUSTON FM 529 11235 FM 529 HOUSTON TEXAS 77041 0.375 

UNIVERSAL CHEMICALS & COATINGS INC 1124 ELMHURST RD ELK GROVE VILLAGEIllinois 60007 0 

ARMSTRONG WORLD INDUSTRIES INC 4115 N PERKINS RD STILLWATER Oklahoma 74075 0.33403 

BRENNTAG SOUTHWEST INC HOUS TON 14826 HOOPER RD HOUSTON Texas 77047 0.0125 MITSUBISHI MOTORS NORTH AMERICA INC 100 N MITSUBISHI MOTOR

WNORMAL Illinois 61761 0.843 

CROWN CORK & SEAL CO (USA) INC CROWN CLOSURES DIV

940 MILL PARK DR LANCASTER Ohio 43130 0 

DPIX LLC 1635 AEROPLAZA DR COLORADO SPRING COLORADO 80916 0.3395 

SONOCO PRODUCTS CO 1854 CENTRAL FLORIDA PK ORLANDO Florida 32837 0.59 

NEXTEER AUTOMOTIVE CORP 3900 HOLLAND RD SAGINAW Michigan 48601 0.08 

FIVE STAR COATINGS GROUP 36616 89TH ST TWIN LAKES WISCONSIN 53181 0 

PEORIA DISPOSAL CO #1 4349 W SOUTHPORT RD PEORIA Illinois 61615 0.7925 

TRELLEBORG OFFSHORE US RANKIN ROAD FACILITY 1902 RANKIN RD HOUSTON Texas 77073 0.785 

SILGAN CONTAINERS MANUFACTURING CORP 12130 LYNN AVE S SAVAGE Minnesota 55378 0 

KAWNEER CO INC 500 E 12TH ST BLOOMSBURG Pennsylvania 17815 0.1305 

ASHLAND DISTRIBUTION CO GARLAND TX 3101 WOOD DR GARLAND Texas 75041 0.152 TCI COATINGS INC 4501 BRADLEY ST LUBBOCK Texas 79415 0.7665 STEEL DYNAMICS INC 5134 LOOP RD JEFFERSONVILLE Indiana 47130 0 

WORWAG COATINGS LLC NA 3420 KOSSUTH ST LAFAYETTE Indiana 47905 0.6285 

ROHM & HAAS ELECTRONIC MATERIA LS LLC 455 FOREST ST MARLBOROUGH Massachusetts 01752 0.0025 

Page 19 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

RUST-OLEUM CORP 8105 95TH ST PLEASANT PRAIRIE Wisconsin 53158 0.375 

BASF CORP 1175 MARTIN ST GREENVILLE Ohio 45331 0.095 PARKER HANNIFIN 400 S ST MC COOK Nebraska 69001 0 

SYNDICATE SYSTEMS INC 402 N MAIN ST MIDDLEBURY Indiana 46540 0 

MERCK SHARP & DOHME CORP 2778 SE SIDE HWY ELKTON Virginia 22827 0.21 

KODAK COLORADO DIV 9952 EASTMAN PARK DR WINDSOR Colorado 80551 0 

UNIVAR USA INC ROMULUS BRANCH 13395 HURON RIVER DR ROMULUS Michigan 48174 0.0105 

MARCUS PAINT CO 235 E MARKET ST LOUISVILLE Kentucky 40202 0.705 

SUPERIOR OIL CO INC RECLAIMED ENERGY DIV 1500 WESTERN AVE CONNERSVILLE Indiana 47331 0.05 GREIF INDUSTRIAL PACKAGING & SERVICES LLC 8250 ALMERIA AVE FONTANA California 92335 0.06325 WATSON STANDARD CO HARWICK PLANT 616 HITE RD HARWICK Pennsylvania 15049 0.5685 

WESTERN EXTRUSIONS CORP 1735 SANDY LAKE RD CARROLLTON Texas 75006 0.125 

WEST PENN OIL CO, INC130130 2305 MARKET ST EXT WARREN Pennsylvania 16365 0.678 

LOCKHEED MARTIN AERONAUTICS CO 1011 LOCKHEED WAY MZ 66PALMDALE California 93599 0.069 

TEXAS TILE MANUFACTURING LLC 1705 N OLIVER HOUSTON Texas 77007 0.001 NALCO CO PLANT 106 7701 US HWY 90A SUGAR LAND Texas 77478 0 SASOL NORTH AMERICA INC LAKE CHARLES CHEMICAL COMPLEX

2201 OLD SPANISH TRAIL WESTLAKE Louisiana 70669 0.547 

METALS USA BUILDING PRODUCTS 227 S TOWN E BLVD MESQUITE Texas 75149 0.332 

KAWNEER CO INC 7200 DOE AVE VISALIA California 93291 0.049 

BASF CORP 361 SHEEP PASTURE RD EAST SETAUKET NEW YORK 11733 0.008 

ROLL COATER INC 5888 E COUNTY RD 180 BLYTHEVILLE Arkansas 72315 0 

PRECOAT METALS 6754 SANTA BARBARA CT ELKRIDGE Maryland 21075 0 

STEELSCAPE 222 W KALAMA RIVER RD KALAMA Washington 98625 0.003865 TRINKOTE INDUSTRIAL FINISHES INC 1800 PARK PL AVE FORT WORTH Texas 76110 0 

TRELLEBORG COATED SYSTEMS US INC / GRACE ADVANCED MATERIALS

715 RAILROAD AVE & HWY 7RUTHERFORDTON North Carolina 28139 0 

SANFORD LP LIQUID MANUFACTURING & TECHNOLOGY CENTER

831 VOLUNTEER PKWY MANCHESTER TENNESSEE 37355 0.125 

FLINT GROUP NORTH AMERICA CORP 2675 HENKLE DR LEBANON Ohio 45036 0.604 

RYCOLINE PRODUCTS LLC 5540 NW HWY CHICAGO Illinois 60630 0.091 

Page 20 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

GLASS COATINGS & CONCEPTS 300 LAWTON AVE MONROE Ohio 45050 0.5905 

ALERIS ROLLED PRODUCTS INC 1 REYNOLDS RD ASHVILLE Ohio 43103 0.119 

ENGINEERED POLYMER SOLUTIONS I NC D/B/A VALSPAR COATINGS

90 CARSON RD BIRMINGHAM Alabama 35215 0.217 

CELLU TISSUE/CITYFOREST LLC 1215 WORDEN AVE E LADYSMITH Wisconsin 54848 0 

ASHLAND DISTRIBUTION 8500 S WILLOW SPRINGS R WILLOW SPRINGS Illinois 60480 0.536 

ROLL COATER INC 2604 RIVER RD HAWESVILLE Kentucky 42348 0 

DIAMOND VOGEL PAINTS 5111 E 36TH ST N TULSA Oklahoma 74115 0.0115 

HERCULES INC KENEDY TEXAS ONE MILL ST KENEDY Texas 78119 0.09493 

COMPLEX CHEMICALS CO INC MADISON PARISH INDUSTR TALLULAH Louisiana 71282 0.3 

PRIOR COATED METALS 2233 26TH ST SW ALLENTOWN Pennsylvania 18103 0 

DUCKBACK PRODUCTS 2644 HEGAN LN CHICO California 95928 0.5605 KLINGER PAINT CO INC 5555 WILLOW CREEK DR S

WCEDAR RAPIDS IOWA 52404 0.559 

CLARIANT CORP - MOUNT HOLLY WEST PLANT 625 E CATAWBA AVE MOUNT HOLLY North Carolina 28120 0 

SOUTHERN CLAY PRODUCTS INC 1335 S 13TH ST LOUISVILLE Kentucky 40210 0.0025 

FLINT HILLS RESOURCES LP 13775 CLARK RD ROSEMOUNT Minnesota 55068 0.55 

HYDRITE CHEMICAL CO 114 N MAIN ST COTTAGE GROVE Wisconsin 53527 0 

REICHHOLD INC 249 ST LOUIS AVE VALLEY PARK Missouri 63088 0.261075 DUPONT FORT MADISON PLANT 801 - 35TH ST FORT MADISON Iowa 52627 0 

SPARTAN CHEMICAL CO INC 1110 SPARTAN DR MAUMEE Ohio 43537 0.0675 CENTRIA 500 PERTH DR NEW ECONOAMBRIDGE Pennsylvania 15003 0 

PARISER INDUSTRIES INC 91 MICHIGAN AVE PATERSON New Jersey 07503 0.5275 

APOLLO CHEMICAL 2001 WILLOW SPRINGS LN BURLINGTON North Carolina 27215 0.230495 0

MARY KAY INC 1330 REGAL ROW DALLAS Texas 75247 0.00026 

DUPONT MOUNT CLEMENS PLANT 400 GROESBECK HWY MOUNT CLEMENS Michigan 48043 0.0025 

MAXIM INTEGRATED PRODUCTS INC 9651 WESTOVER HILLS BLVSAN ANTONIO Texas 78251 0 

ALERIS ROLLED PRODUCTS INC 3321 DURHAM RD ROXBORO North Carolina 27573 0.0025 

ARROW GROUP INDUSTRIES INC 1 THIRD AVE HASKELL New Jersey 07420 0.0025 

PLAZE INC 105 BOLTE LN SAINT CLAIR Missouri 63077 0.509 TERNIUM USA INC 2500 RON BEAN BLVD SHREVEPORT Louisiana 71115 0.0125 CLARIANT CORP MARTIN PLANT 788 CHERT QUARRY RD MARTIN South Carolina 29836 0.125 

Page 21 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

ARCADIA INC 3225 E WASHINGTON BLVD VERNON California 90023 0.125 

SILBOND CORP 9901 SAND CREEK HWY WESTON Michigan 49289 0.375 FERRO GLASS & COLOR CORP W WYLIE AVE WASHINGTON Pennsylvania 15301 0.125 EVONIK DEGUSSA CORP TIPPECANOE LABORATORIES 1650 LILLY RD LAFAYETTE Indiana 47909 0.375 

FORMULA CORP 4432 C ST NE AUBURN WASHINGTON 98002 0.125 

BEHR PROCESS CORP ALLENTOWN 7529 MORRIS CT BLDG 500 

WALLENTOWN Pennsylvania 18106 0.0066 

TRAD NA INC 210 BILL BRYAN BLVD HOPKINSVILLE Kentucky 42240 0 

CLEAN HARBORS EL DORADO LLC 309 AMERICAN CIR UNION EL DORADO Arkansas 71730 0 

FULLER BRUSH CO ONE FULLER WAY GREAT BEND Kansas 67530 0.161 

TYSON FRESH MEATS INC HWY 35/IBP AVE DAKOTA CITY NEBRASKA 68731 0.005 

NAZDAR CHICAGO 1087 N N BRANCH ST CHICAGO Illinois 60622 0.142 

SNAP-ON TOOLS MANUFACTURING CO 2600 US HWY 18 E ALGONA Iowa 50511 0.0055 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

5400 23RD AVE MOLINE Illinois 61265 0.207 

SHERWIN-WILLIAMS CO 2802 W MILLER RD GARLAND Texas 75041 0.0025 

CLEVELAND STEEL CONTAINER CORP - STREETSBORO PLANT

10048 AURORA-HUDSON RDSTREETSBORO Ohio 44241 0.0045 

ROCK TENN CO 2301 S 21ST ST CLINTON Iowa 52732 0 HEXION SPECIALTY CHEMICALS INC 8600 W 71ST ST BEDFORD PARK Illinois 60501 0 VISTA PAINT CORP 2020 E ORANGETHORPE AVFULLERTON California 92831 0.4065 

UNIVAR USA INC SALEM BRANCH COLONIAL RD SALEM Massachusetts 01970 0.001 

SOUTHWEST DISTRIBUTING CO 539 S DREW ST MESA Arizona 85210 0.0005 

FORREST PAINT CO 1011 MCKINLEY ST EUGENE Oregon 97402 0.1755 

SEYMOUR OF SYCAMORE INC 917 CROSBY AVE SYCAMORE ILLINOIS 60178 0.3785 

NB COATINGS INC 2701 E 170TH ST LANSING Illinois 60438 0.4065 PFI INC 9215 SANTA FE SPRINGS RDSANTA FE SPRINGS California 90670 0.43 

RODDA PAINT CO 6123 N MARINE DR PORTLAND Oregon 97203 0.427 NELCO PRODUCTS INC 1107 E KIMBERLY ANAHEIM California 92801 0.033 

ELEMENTIS SPECIALTIES 400 CLAREMONT AVE JERSEY CITY New Jersey 07304 0.1125 

NASCOTE INDUSTRIES 18310 ENTERPRISE AVE NASHVILLE Illinois 62263 0.149425 0

Page 22 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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Emis

(tp

ASHLAND DISTRIBUTION 3300 BALL ST BIRMINGHAM Alabama 35234 0.3735 

GEMINI COATINGS INC 2300 HOLLOWAY DR EL RENO OKLAHOMA 73036 0.4005 

BEHR PROCESS CORP - CHICAGO 270 STATE ST CHICAGO HEIGHTS Illinois 60411 0.0291 

MAGNABLEND INC-CENTRAL PLANT 1601 W HWY 287 BYPASS WAXAHACHIE Texas 75165 0.0025 

BRADLEY COATINGS GROUP 608 W CRAWFORD AVE CONNELLSVILLE Pennsylvania 15425 0.28171 

ROLLEX CORP 800 CHASE AVE ELK GROVE VILLAGEIllinois 60007 0 

NALCO CO TULSA PLANT 102 6717 S 61ST W AVE TULSA Oklahoma 74131 0 

INCHEM CORP 800 CEL-RIVER RD ROCK HILL South Carolina 29730 0.0025 

SIKA CORP SIKA SARNAFIL DIV 100 DAN RD CANTON Massachusetts 02021 0 

IMS ENGINEERED PRODUCTS LLC ONE INNOVATION DR DES PLAINES ILLINOIS 60016 0.0025 ZSCHIMMER & SCHWARZ 70 GA HWY 22 W MILLEDGEVILLE GEORGIA 31061 0.0025 

INTERNATIONAL PAINT LLC 6001 ANTOINE DR HOUSTON Texas 77091 0.0025 

QUEST CHEMICAL CORP 12255 FM 529 HOUSTON Texas 77041 0.375 TOWER PRODUCTS INC 2703 FREEMANSBURG AVE EASTON Pennsylvania 18045 0.375 

PATRIOT PAINT LLC 304 S BLAINE PIKE PORTLAND INDIANA 47371 0.375 BRYCE CO LLC 450 S BENTON ST SEARCY ARKANSAS 72143 0.125 JASPER RUBBER PRODUCTS INC 1010 FIRST AVE JASPER Indiana 47546 0 

MARCHEM TECHNOLOGIES LLC 20851 S SANTA FE AVE LONG BEACH California 90810 0 

FUCHS LUBRICANTS CO-CORPORATE OFFICE 17050 S LATHROP AVE HARVEY Illinois 60426 0.3715 FLINT GROUP NORTH AMERICA CORP 104 NATIONAL DR ANNISTON Alabama 36207 0.185 

METAL COATERS OF CALIFORNIA INC 9133 CENTER AVE RANCHO CUCAMON California 91730 0.033515 

TYSON FRESH MEATS INC JOSLIN IL HWY 92 & I-88 28424 38TH A HILLSDALE Illinois 61257 0.015 

MIDWEST METAL COATINGS 9 KONZEN CT GRANITE CITY ILLINOIS 62040 0.3 IVC INDUSTRIAL COATINGS INC 1825 E NATIONAL AVE BRAZIL INDIANA 47834 0.07321 

AKZONOBEL COATINGS INC 120 FRANKLIN RD PONTIAC Michigan 48341 0.0915 COMBE PRODUCTS INC EL DUQUE INDUSTRIAL PARNAGUABO Puerto Rico 00718 0 

CELLO PROFESSIONAL PRODUCTS 1354 OLD POST RD HAVRE DE GRACE Maryland 21078 0.3525 

EXXONMOBIL REFINING & SUPPLY BATON ROUGE REFINERY

4045 SCENIC HWY BATON ROUGE Louisiana 70805 0.16 

FORD MOTOR CO CHICAGO ASSEMBLY 12600 S TORRENCE AVE CHICAGO Illinois 60633 0.35 

Page 23 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

Fug

Emis

(tp

SHERWIN-WILLIAMS CO 180 CANAL ST TERRE HAUTE Indiana 47808 0.0235 

LONGABERGER CO 5565 RAIDERS RD FRAZEYSBURG Ohio 43822 0.2105 

INEOS OXIDE A DIV OF INEOS AMERICAS LLC 21255A HWY 1 S PLAQUEMINE Louisiana 70765 0.318275 

QUEST SPECIALTY COATINGS LLC MENOMONEE FALLS N92 W14701 ANTHONY AVE MENOMONEE FALLSWISCONSIN 53051 0.3475 

INX INTERNATIONAL INK CO 1000 MAPLE AVE HOMEWOOD Illinois 60430 0.00566 

PACKAGING CORP OF AMERICA COUNCE MILL HWY 57 COUNCE Tennessee 38326 0.0215 

DIVERSIFIED COATING SYSTEMS INC 309 ECHELON RD GREENVILLE SOUTHSOUTH CAROL 29605 0.0035 

SIERRA CORP 11400 W 47TH ST MINNETONKA Minnesota 55343 0.336 SHERWIN-WILLIAMS AUTOMOTIVE FINISHES CORP 395 BOGGS LN - S RICHMOND Kentucky 40475 0.3175 

BECKER SPECIALTY CORP 2500 DELTA LN ELK GROVE VILLAGEIllinois 60007 0.0275 

AMERIMAX HOME PRODUCTS INC 450 RICHARDSON DR LANCASTER Pennsylvania 17603 0.0095 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

411 N DARLING FREMONT Michigan 49412 0.31 

GATES CORP 630 US HWY 150 E GALESBURG Illinois 61401 0 

ENGLERT INC 1200 AMBOY AVE PERTH AMBOY NEW JERSEY 08861 0.1315 

ENERGIZER BATTERY MANUFACTURING INC 75 SWANTON RD SAINT ALBANS Vermont 05478 0.0025 

AMERIMAX COATED PRODUCTS 215 PHILLIPS 324 RD HELENA ARKANSAS 72342 0 

CURTIS METAL FINISHING CO 9917 N ALPINE MACHESNEY PARK Illinois 61115 0.22 LINETEC 725 S 75TH AVE WAUSAU Wisconsin 54401 0.0205 FORD MOTOR CO MICHIGAN ASSEMBLY PLANT 38303 MICHIGAN AVE WAYNE Michigan 48184 0.0015 

ET PRODUCTS CO INC 747 DOUGLAS RD BREMEN Indiana 46506 0 

AMERICAN METALS CORP 1000 CROCKER RD WESTLAKE Ohio 44145 0 MAXIM INTEGRATED PRODUCTS INC 3725 N FIRST ST SAN JOSE California 95134 0 

ATMI MATERIALS LTD 706 HOUSTON CLINTON DR BURNET Texas 78611 0.050745 0

MUTI-PACK LLC 8372 N STEVEN RD MILWAUKEE Wisconsin 53223 0.29 VIDEOJET TECHNOLOGIES INC 1855 ESTES AVE ELK GROVE VILLAGEIllinois 60007 0 

TRITECH COATINGS CORP 1378 KINGSLAND AVE PAGEDALE Missouri 63133 0.194 

ENTHONE INC 350 FRONTAGE RD WEST HAVEN Connecticut 06516 0.005595 0SHERWIN-WILLIAMS CO 2150 W SAND LAKE RD ORLANDO Florida 32809 0 

SUMTER COATINGS INC 2410 HWY 15S SUMTER South Carolina 29150 0.058 

Page 24 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

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Emis

(tp

SPRAYLAT CORP 716 S COLUMBUS AVE MOUNT VERNON New York 10550 0.0135 

INTEL CORP 4100 SARA RD MS RR5-491 RIO RANCHO New Mexico 87124 0.0025 

STANDARD PAINTS INC 940 S 6TH AVE MANSFIELD Texas 76063 0 

QUANTUM MARKETING INC 3606 CRAFTSMAN BLVD LAKELAND Florida 33803 0.268 

PPG ARCHITECTURAL FINISHES INC 400 S 13TH ST LOUISVILLE Kentucky 40203 0 SERIGRAPH INC 3801 E DECORAH RD WEST BEND Wisconsin 53095 0.0325 

HENKEL CORP 23343 SHERWOOD AVE WARREN Michigan 48091 0.125 

IVC INDUSTRIAL COATINGS INC 550-560 W CENTENNIAL BLVCASA GRANDE Arizona 85222 0.0520125 

MASCO RETAIL CABINET GROUP SAYRE PENNSYLVANIA PLANT

217 LAMOKA RD SAYRE PENNSYLVANIA18840 0 

ASHLAND DISTRIBUTION CO 395 JAMES AVE SAINT PAUL Minnesota 55102 0.2475 

ASHLAND DISTRIBUTION CO 350 ROOSEVELT AVE CARTERET New Jersey 07008 0.2305 

HENTZEN COATINGS,INC BATAVIA FACILITY 1500 LATHEM ST BATAVIA Illinois 60510 0.23381 0

PPG INDUSTRIES ARCHITECTURAL FINISHES 1886 LYNNBURY WOODS RDDOVER Delaware 19904 0.0025 

BACHMAN SERVICES INC 2220 S PROSPECT OKLAHOMA CITY Oklahoma 73129 0.125 

BF GOODRICH TIRE MANUFACTURING 18906 US 24 E WOODBURN Indiana 46797 0.0025 MOC PRODUCTS CO INC 12306 MONTAGUE ST PACOIMA California 91331 0.125 

ASHLAND DISTRIBUTION CO 1610 E HIGHLAND RD TWINSBURG Ohio 44087 0.2295 

RESEARCH SOLVENTS & CHEMICALS INC 402 INDUSTRIAL PARK DR PELHAM Alabama 35124 0.125 

MISCO PRODUCTS CORP 1048 STINSON DR READING Pennsylvania 19605 0.125 

METAL COATERS OF GEORGIA 1150 MARIETTA INDUSTRIALMARIETTA Georgia 30062 0.0035 

MAGNI INDUSTRIES INC 10250 TOEBBEN DR INDEPENDENCE KENTUCKY 41051 0.125 KEYSTONE ANILINE CORP 2165 HWY 292 INMAN South Carolina 29349 0.125 

EQUILON CARSON TERMINAL 20945 S WILMINGTON AVE CARSON California 90810 0.125 

CHEMICAL SPECIALISTS & DEVELOPMENT INC 9733 MEADOR RD CONROE Texas 77303 0.125 

BECKER SPECIALTY CORP 15310 ARROW BLVD FONTANA California 92335 0.125 

YENKIN-MAJESTIC PAINT CORPORAT ION 1920 LEONARD AVE COLUMBUS Ohio 43219 0.125 

MALCO PRODUCTS INC 361 FAIRVIEW AVE BARBERTON Ohio 44203 0.125 

HEXION SPECIALTY CHEMICALS INC 400 E COTTAGE PL CARPENTERSVILLE Illinois 60110 0.025 PREMIER INK SYSTEMS INC 10420 N STATE ST HARRISON Ohio 45030 0.125 

BRYCE CO LLC 4505 OLD LAMAR AVE MEMPHIS Tennessee 38118 0 

Page 25 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

Fug

Emis

(tp

AMERICAN COLORS INC DISPERSION PLANT SANDUSKY OHIO

1110 EDGEWATER AVE SANDUSKY OHIO 44870 0.125 

DUPONT FAYETTEVILLE PLANT 22828 NC HWY 87 W FAYETTEVILLE NORTH CAROL 28306 0.247 

CAR PRODUCTS INC 630 BEAULIEU ST HOLYOKE Massachusetts 01040 0.238 

WORLDCOLOR ATGLEN 4581 LOWER VALLEY RD ATGLEN Pennsylvania 19310 0.2285 

KIK-SOCAL INC 9028 DICE RD SANTA FE SPRINGS California 90670 0.2365 

BERGQUIST CO 301 WASHINGTON ST CANNON FALLS Minnesota 55009 0.069 

DYCO PAINTS INC 5850 ULMERTON RD CLEARWATER Florida 33760 0 

SUN CHEMICAL CORP 3301 HUNTING PARK AVE PHILADELPHIA Pennsylvania 19132 0.035 CHEMTURA CORP - TAFT PLANT 471 HWY 3142 KILLONA Louisiana 70066 0.069 

CHRYSLER GROUP LLC STERLING STAMPING PLANT (PART)

35777 VAN DYKE STERLING HEIGHTS Michigan 48312 0.228 

PPG INDUSTRIES OHIO INC CIRCLEVILLE OH 559 PITTSBURGH RD CIRCLEVILLE Ohio 43113 0.055 CERTIFIED ENAMELING INC 3342 EMERY ST LOS ANGELES California 90023 0.0025 

ACTEGA KELSTAR INC 1050 TAYLORS LN CINNAMINSON New Jersey 08077 0.003 

PERMA-PIPE OIL & GAS 5008-11 CURTIS LN NEW IBERIA Louisiana 70560 0.22 

RHODIA INC 577 BANKHEAD HWY WINDER Georgia 30680 0.16 

COLWELL INC 231 S PROGRESS DR E KENDALLVILLE Indiana 46755 0.195 

SYNGENTA CROP PROTECTION INC SAINT GABRIEL FACILITY

3905 HWY 75 SAINT GABRIEL Louisiana 70776 0.106 

ASHLAND DISTRIBUTION CO 4550 NE EXPRESSWAY DORAVILLE Georgia 30340 0.158 

FLINT GROUP NORTH AMERICA 4675 W PARK DR ATLANTA Georgia 30339 0.105 WARREN OIL CO - NC 2340 US 301 N DUNN North Carolina 28335 0.2075 BOEING COMMERCIAL AIRPLANE GROUP - RENTON 8TH & LOGAN AVE N RENTON Washington 98055 0.086 UNION CARBIDE CORP SOUTH CHARLESTON FACILITY 437 MACCORKLE AVE SW SOUTH CHARLESTOWest Virginia 25303 0.139 

FIRST AMERICAN RESOURCES CO 2030 RIVERVIEW INDUSTRIAMABLETON Georgia 30126 0 

BOEING COMMERCIAL AIRPLANE GROUP NORTH BOEING FIELD (PART)

7500 E MARGINAL WAY S SEATTLE Washington 98108 0.059 

RUDD CO INC 1141 NW 50TH ST SEATTLE Washington 98107 0.185 

UNIVERSAL CHEMICALS & COATINGS INC 1975 FOX LN ELGIN ILLINOIS 60123 0 

INTEL CORP - RONLER ACRES CAMPUS 2501 NW 229TH ST HILLSBORO Oregon 97124 0.0025 

Page 26 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

Fug

Emis

(tp

U.S. NAVY NAVAL AIR STATION JACKSONVILLE 6500 ROOSEVELT BLVD BUI JACKSONVILLE FLORIDA 32212 0.07 

HADCO (SANMINA) CORP - OWEGO DIV 1200 TAYLOR RD OWEGO New York 13827 0.0045 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

1991 S WHEELING RD WHEELING Illinois 60090 0.0635 

QUAD GRAPHICS NASHVILLE 2947 BRICK CHURCH PIKE NASHVILLE TENNESSEE 37207 0.1585 LAMBERTI USA INC WHARTON CHEMICAL COMPLEX HWY 59 AT COUNTY RD 212HUNGERFORD Texas 77448 0.0405 

SILGAN WHITE CAP CORP 1701 WILLIAMSBURG PIKE RICHMOND Indiana 47375 0.05 

BYK USA INC 524 S CHERRY ST WALLINGFORD Connecticut 06492 0.17 

ASHLAND DISTRIBUTION CO 11109 S CHOCTAW DR BATON ROUGE Louisiana 70815 0.1625 

CHAMPION TECHNOLOGIES INC 115 PROCTOR ODESSA Texas 79762 0.1615 

ASHLAND DISTRIBUTION 7710 POLK ST SAINT LOUIS Missouri 63111 0.1685 KAY CHEMICAL CO 8300 CAPITAL DR GREENSBORO North Carolina 27409 0.0075 

AMREP INC 990 INDUSTRIAL PARK DR MARIETTA Georgia 30062 0.054 

SUPERIOR SOLVENTS & CHEMICALS 320 NORTHPOINTE DR FAIRFIELD Ohio 45014 0.02254 

ANCHOR PAINT MANUFACTURING CO INC 6707 E 14TH ST TULSA Oklahoma 74112 0.16 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

1717 ENGLISH RD HIGH POINT North Carolina 27261 0.0635 

INTEL CORP 4500 S DOBSON RD MAIL STCHANDLER Arizona 85248 0.0025 

SHERWIN-WILLIAMS CO 1891 DUFFY RD FERNLEY Nevada 89408 0.0005 SUPERIOR SOLVENTS & CHEMICALS 4211 BRAMERS LN LOUISVILLE Kentucky 40216 0.0045 PLAZE INC 113 BOLTE LN SAINT CLAIR Missouri 63077 0.152 BAKER PETROLITE CORP 9100 W 21ST ST SAND SPRINGS Oklahoma 74063 0.123525 0

MID-STATES PAINT & CHEMICAL CO 9315 WATSON INDUSTRIAL CRESTWOOD Missouri 63126 0.151 

SONOCO FLEXIBLE PACKAGING 6502 S US HWY 31 N EDINBURGH Indiana 46124 0 

CENTRAL MOTOR WHEEL OF AMERICA (DBA CMWA) 125 WHEAT DR PARIS Kentucky 40361 0 GOJO INDUSTRIES INC 3783 STATE RD CUYAHOGA FALLS OHIO 44223 0.0015 0.0CHASE PRODUCTS CO 2727 GARDNER RD BROADVIEW Illinois 60155 0.0005 

DAVIS-FROST INC 3420 CANDLER'S MOUNTAINLYNCHBURG VIRGINIA 24506 0.1415 

BLENTECH CORP 1305 RYE ST HOUSTON Texas 77029 0.0125 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

3050 HANFORD DR LEBANON Pennsylvania 17046 0.0635 

Page 27 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

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Onsite Point 

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On

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Emis

(tp

ISP SYNTHETIC ELASTOMERS LP 1615 MAIN ST PORT NECHES TEXAS 77651 0 ASHLAND DISTRIBUTION 2351 CHANNEL AVE MEMPHIS Tennessee 38113 0.1215 

POWER SERVICE PRODUCTS INC 513 PEASTER HWY WEATHERFORD Texas 76086 0.125 

UNITED LABORATORIES INC 320 37TH AVE SAINT CHARLES Illinois 60174 0.125 

RESEARCH SOLVENTS & CHEMICALS INC 133 BAIN DR LA VERGNE Tennessee 37086 0.125 

PERMATEX SOLON 6875 PARKLAND BLVD SOLON Ohio 44139 0.0025 

ONESOURCE COIL COATERS 5110 140TH AVE CLEARWATER FLORIDA 33760 0.0025 

OAKLEY INC 1 ICON FOOTHILL RANCH California 92610 0.0025 

NICCA USA INC 1044 S NELSON RD FOUNTAIN INN South Carolina 29644 0.0025 

WESTERN TUBE & CONDUIT CORP 2001 E DOMINGUEZ ST LONG BEACH CALIFORNIA 90810 0.0025 

BRENNTAG GREAT LAKES LLC 14765 W BOBOLINK AVE MENOMONEE FALLSWisconsin 53051 0.0025 

RR STREET & CO INC 2353 S BLUE ISLAND AVE CHICAGO Illinois 60608 0.0025 

BASF CORP 3455 SOUTHPORT RD SPARTANBURG South Carolina 29302 0.125 

GE WATER & PROCESS TECHNOLOGIES ORANGE FACILITY

3901 WILLIAMS DR ORANGE Texas 77630 0.125 

CHEMICALS INC 12321 HATCHERVILLE RD BAYTOWN Texas 77520 0.125 COASTAL CHEMICAL CO LLC 3520 VETERANS MEMORIAL ABBEVILLE Louisiana 70510 0.125 

DELTA HOUSTON 334 TIDAL RD DEER PARK Texas 77536 0.125 

ELANTAS PDG INC 5200 N SECOND ST SAINT LOUIS Missouri 63147 0.0025 

ELECTRO PLATE CIRCUITRY INC 1430 CENTURY DR CARROLLTON TEXAS 75006 0.0025 

JOHNSON BRYCE INC 276 S PKWY W MEMPHIS TENNESSEE 38109 0 

ASHLAND DISTRIBUTION CO 3930 GLENWOOD DR CHARLOTTE North Carolina 28208 0.083 

WEBB CHEMICAL SERVICE CORP 2708 JARMAN MUSKEGON HEIGHT MICHIGAN 49444 0.08 

CERAM-TRAZ CORP CERAMIC INDL COATINGS (DBA) 325 HWY 81 OSSEO Minnesota 55369 0.125 

COLUMBIA PAINT CORP 641 JACKSON AVE HUNTINGTON West Virginia 25704 0.125 

CLEANING SYSTEMS INC 1997 AMERICAN BLVD DE PERE Wisconsin 54115 0.125 CHEMETALL US INC 13177 HURON RIVER DR ROMULUS Michigan 48174 0 

EXXONMOBIL OIL CORP - TORRANCE REFINERY 3700 W 190TH ST TORRANCE CALIFORNIA 90509 0.125 BERRYMAN PRODUCTS INC 3800 E RANDOL MILL RD ARLINGTON Texas 76011 0.125 

AMERICAN JETWAY CORP 34136 MYRTLE WAYNE MICHIGAN 48184 0.125 AKZO NOBEL COATINGS INC 1431 PROGRESS AVE HIGH POINT North Carolina 27261 0.125 

Page 28 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

Fug

Emis

(tp

GOLD KEY PROCESSING INC 14910 MADISON RD MIDDLEFIELD OHIO 44062 0.125 

ACTON TECHNOLOGIES INC 100 THOMPSON ST PITTSTON Pennsylvania 18640 0.125 GOLD EAGLE CO 4400 S KILDARE AVE CHICAGO Illinois 60632 0.125 

AKCROS CHEMICALS INC 500 JERSEY AVE NEW BRUNSWICK New Jersey 08901 0 

WM BARR & CO INC 2170 BUOY ST MEMPHIS TENNESSEE 38113 0 

INVISTA SARL - ORANGE SITE 3055A FM 1006 ORANGE TEXAS 77630 0.125 

KALCOR COATINGS CO 37721 STEVENS BLVD WILLOUGHBY Ohio 44094 0.125 

MAGNABLEND INC LIQUID PLANT 100 W STERRETT RD WAXAHACHIE Texas 75165 0.125 

MAINTEX INC 13300 E NELSON AVE CITY OF INDUSTRY California 91746 0.125 NORTHERN COATINGS & CHEMICAL CO INC 705 6TH AVE MENOMINEE Michigan 49858 0.125 PPG INDUSTRIES INC 500 PITTSBURGH AVE MCCARRAN Nevada 89434 0 

SICPA SECURINK CORP 8000 RESEARCH WAY SPRINGFIELD Virginia 22153 0.125 

TNEMEC CO INC 123 W 23RD AVE NORTH KANSAS CIT Missouri 64116 0 

TRANS CHEMICAL INC 419 E DE SOTO AVE SAINT LOUIS Missouri 63147 0.125 

TYSON FRESH MEATS INC HWY 50 W HOLCOMB Kansas 67851 0.125 

DANLIN INDUSTRIES CORP 23737 HWY 47 THOMAS Oklahoma 73669 0.125 

HERCULES INC 1111 HERCULES RD HOPEWELL Virginia 23860 0.125 FLUID ROUTING SOLUTIONS 1921 N BROAD ST LEXINGTON Tennessee 38351 0 WATSON LABORATORIES INC UTAH 575, 577, 579 CHIPETA WAY SALT LAKE CITY Utah 84108 0.124456 TECHNICAL CHEMICAL CO 3327 PIPELINE RD CLEBURNE Texas 76033 0.123 CYTEC INDUSTRIES INC LANGLEY PLANT 403 CARLINE RD LANGLEY South Carolina 29834 0.1075 

AEP INDUSTRIES INC 1201 S PINE HILL RD GRIFFIN Georgia 30224 0.00275 

ASHLAND INC - EVENDALE 2788 GLENDALE-MILFORD REVENDALE Ohio 45241 0.0815 

FRAZEE INDUSTRIES 6625 MIRAMAR RD SAN DIEGO California 92121 0 

ARDEX LABORATORIES INC 2050 BYBERRY RD PHILADELPHIA Pennsylvania 19116 0.119 

STOUSE INC 300 NEW CENTURY PKWY NEW CENTURY Kansas 66031 0.118 

SUPERIOR OIL CO INC 400 W REGENT ST INDIANAPOLIS Indiana 46225 0.007465 PILOT CHEMICAL CO 11623 N HOUSTON ROSSLY HOUSTON Texas 77086 0.11 

ELECTRONICS FOR IMAGING INC 1260 JAMES L HART PKWY YPSILANTI Michigan 48197 0.11 VEYANCE TECHNOLOGIES INC 4021 N 56TH ST LINCOLN Nebraska 68504 7.5E-09 

Page 29 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

TEXAS INSTRUMENTS INC 13500 N CENTRAL EXPRESSDALLAS Texas 75243 0 

DELTA LABORATORIES INC 3710 COUNTY RD 326 W OCALA Florida 34475 0.108 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

347 CENTRAL AVE BOWLING GREEN Kentucky 42101 0.065 

CAROLINA SOLVENTS INC 2274 1ST ST SE HICKORY North Carolina 28602 0.1015 

SKF SEALING SOLUTIONS 900 N STATE ST ELGIN Illinois 60123 0 

CHAMPION TECHNOLOGIES INC 350 CENTAURUS RD CORPUS CHRISTI Texas 78405 0.05455 

SHERWIN-WILLIAMS CO 636 E 40TH ST HOLLAND Michigan 49423 0.1045 

ACCURATE DISPERSIONS 192 W 155TH ST SOUTH HOLLAND Illinois 60473 0.0825 

CCI MANUFACTURING IL CORP 15550 CANAL BANK RD LEMONT Illinois 60439 0 

ASHLAND DISTRIBUTION CO 200 NE 181ST ST MIAMI Florida 33162 0.0755 

TWINCO ROMAX 3100 W MILL RD MILWAUKEE WISCONSIN 53209 0.0995 

ASHLAND DISTRIBUTION CO 20915 S WILMINGTON AVE CARSON California 90810 0.0905 ARCH CHEMICALS INC HWY 933 BRANDENBURG Kentucky 40108 0.042 BUZZI UNICEM USA - GREENCASTLE PLANT 3301 S COUNTY RD 150 W GREENCASTLE Indiana 46135 0.0225 

BRENNTAG PACIFIC INC 10747 PATTERSON PL SANTA FE SPRINGS California 90670 0.0955 

HARCROS CHEMICALS INC 5200 SPEAKER RD KANSAS CITY Kansas 66106 0.0245 

CE BRADLEY LABORATORIES INC 55 BENNETT DR BRATTLEBORO Vermont 05301 0.0985 

OLDCASTLE BUILDING ENVELOPE TENNESSEE FACILITY 920 POTTERTOWN RD MIDWAY Tennessee 37809 0 ALLEGHENY PETROLEUM PRODUCTS CO 999 AIRBRAKE AVE WILMERDING Pennsylvania 15148 0.019 

SHERWIN-WILLIAMS CO 1025 HOWARD ST GREENSBORO North Carolina 27403 0.0065 

CPJ TECHNOLOGIES 200 TANNER DR TAYLORS South Carolina 29687 0.034 TNEMEC CO INC 2300 EDGEWATER AVE BALTIMORE Maryland 21222 0 STEELSCAPE INC RANCHO 11200 ARROW RT RANCHO CUCAMON California 91730 0.0031 0ATHEA LABORATORIES INC 7855 N FAULKNER RD MILWAUKEE Wisconsin 53224 0.08874 COSMETIC LABORATORIES OF AMERICA 20245 SUNBURST ST CHATSWORTH California 91311 0 

MRCG-KRAFTMAID P3 150 GRAND VALLEY AVE ORWELL Ohio 44076 0 

ASHLAND DISTRIBUTION CO 2461 CROCKER CIR FAIRFIELD California 94533 0.0845 

ASHLAND DISTRIBUTION CO 5420 SPEAKER RD KANSAS CITY Kansas 66106 0.0755 AKZO NOBEL COATINGS INC 1000 INDUSTRIAL PARK DR CLINTON Mississippi 39056 0.082 

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Onsite Point 

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(tpy)

On

Fug

Emis

(tp

ASHLAND DISTRIBUTION 400 MAIN ST TEWKSBURY Massachusetts 01876 0.075 

MATTHEWS INTERNATIONAL CORP 101 FAIRVIEW AVE PITTSBURGH Pennsylvania 15238 0.0565 ICI PAINTS PUERTO RICO INC 65 INFANTERIA KM 134 CAROLINA Puerto Rico 00985 0.050405 

CORSICANA TECHNOLOGIES INC 2733 E HWY 31 CORSICANA Texas 75109 0.01949 

CHEMICAL SOLVENTS JENNINGS ROAD FACILITY 3751 JENNINGS RD CLEVELAND Ohio 44109 0.071 

IMPERIAL PAINT CO INC 2526 NW YEON AVE PORTLAND OREGON 97210 0 

AKZO NOBEL COATINGS INC 1660 CROSS ST SE SALEM Oregon 97302 0.045 WHITFORD CORP 47 PARK AVE ELVERSON Pennsylvania 19520 0.069255 0

CHAMPION TECHNOLOGIES INC 304 IDA RD BROUSSARD Louisiana 70518 0.071 PPG INDUSTRIES OHIO INC - DELAWARE 760 PITTSBURGH DR DELAWARE Ohio 43015 0.0695 

WARSAW CHEMICAL CO INC 390 ARGONNE RD WARSAW Indiana 46580 0.0465 LUBRIZOL 9550 W 55TH ST MC COOK Illinois 60525 0 

CARDINAL INDUSTRIAL FINISHES 1329 POTRERO AVE SOUTH EL MONTE California 91733 0.0475 

ADCO CLEANING PRODUCTS LLC 900 W MAIN ST SEDALIA Missouri 65301 0.022 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

901 W UNION ST MONTEBELLO California 90640 0.0635 

MRCG-KRAFTMAID P1 16052 INDUSTRIAL PKWY MIDDLEFIELD Ohio 44062 0 

KEY POLYMER 17 SHEPARD ST LAWRENCELAWRENCE Massachusetts 01843 0 

VEOLIA ES TECHNICAL SOLUTIONS LLC 125 FACTORY LN MIDDLESEX New Jersey 08846 0.045 

WARREN STAMPING PLANT (PART) 22800 MOUND RD WARREN Michigan 48091 0.06 

KARCHER NORTH AMERICA- PROCHEM 325 S PRICE RD CHANDLER Arizona 85224 0.0595 

ABC COMPOUNDING CO OF TEXAS INC 1102 AVE J E GRAND PRAIRIE Texas 75050 0.0025 AMPHENOL APC INC 91 NORTHEASTERN BLVD NASHUA New Hampshire 03062 0.0025 0.0

MINUTEMAN INTERNATIONAL MULTI-CLEAN DIV 600 CARDIGAN RD SHOREVIEW Minnesota 55126 0.0545 

ECOLAB INC 3001 CHANNAHON RD JOLIET Illinois 60436 0.044 

CHEVRON PRODUCTS CO PASCAGOULA REFINERY 250 INDUSTRIAL RD PASCAGOULA MISSISSIPPI 39581 0.055 

UNIVAR USA INC 2600 S GARFIELD AVE COMMERCE California 90040 0.0505 

CLEVELAND STEEL CONTAINER - KILGORE 5005 ELDER LAKE RD KILGORE TEXAS 75662 0.0025 

HARLEY-DAVIDSON MOTOR CO OPERATIONS INC 1425 EDEN RD YORK Pennsylvania 17402 0.02725 

3M CO - NEVADA 2120 E AUSTIN BLVD NEVADA Missouri 64772 0.004 

Page 31 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

UNIVAR USA INC - TOLEDO BRANCH 30450 TRACY RD WALBRIDGE Ohio 43465 0.017 

CLOROX PRODUCTS MANUFACTURING CO 2600 HUNTINGTON DR FAIRFIELD California 94533 0.053 

ROCKLINE INDUSTRIES 1113 MARYLAND AVE SHEBOYGAN Wisconsin 53081 0.0535 

FRANKLIN INTERNATIONAL 2020 BRUCK ST COLUMBUS Ohio 43207 0.0055 

ECOLAB INC 942 BAKER RD MARTINSBURG West Virginia 25405 0.0385 ECOLAB INC 261 HWY 155 S MC DONOUGH Georgia 30253 0.0155 

NEWMAN TECHNOLOGY INC 100 CAIRNS RD MANSFIELD OHIO 44903 0 

HANNA STEEL CORP 220 HANNA DR PEKIN Illinois 61554 0.0025 BENJAMIN MOORE & CO PELL CITY 109 BAMBERG DR PELL CITY Alabama 35125 0.04945 

DYSTAR LP 209 WATLINGTON INDUSTR REIDSVILLE North Carolina 27320 0.035 

CONOCOPHILLIPS OKLAHOMA CITY PRODUCTS TERMINAL

4600 NE 10TH ST OKLAHOMA CITY Oklahoma 73117 0.0025 

CHAMPION TECHNOLOGIES INC 3130 FM 521 FRESNO Texas 77545 0.0495 

VALERO REFINING CO - TENNESSEE LLC 2385 RIVERPORT RD MEMPHIS TENNESSEE 38109 0.0495 

AIR PRODUCTS & CHEMICALS INC 412 N MAIN ST CALVERT CITY Kentucky 42029 0 

BARTON SOLVENTS INC BETTENDORF 204 36TH ST BETTENDORF Iowa 52722 0.0115 UNIVAR USA INC HAMILTON BRANCH 12 STANDEN DR HAMILTON Ohio 45015 0.013 

EXCEL-POLYMERS LLC HWY 353 S PO BOX 377 JONESBOROUGH Tennessee 37659 0 

GRAPHIC CONTROLS LLC 400 EXCHANGE ST BUFFALO New York 14204 0.048 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

546 W ABBOTT ST INDIANAPOLIS Indiana 46225 0 

LUBRIZOL CORP 29400 LAKELAND BLVD WICKLIFFE Ohio 44092 0.0455 

RECKITT BENCKISER 799 RT 206 & HILLSBOROUGHILLSBOROUGH New Jersey 08844 0.0445 

BRENNTAG SOUTHEAST INC 2000 E PETTIGREW ST DURHAM North Carolina 27703 0.028 

WATSON STANDARD CO (NEVILLE ISLAND PLANT) 2895 GRAND AVE NEVILLE ISLAND Pennsylvania 15225 0.038 

UNIVAR USA INC DALLAS DAN MORTON FACILITY 3636 DAN MORTON DR DALLAS Texas 75236 0.0165 

HARCROS CHEMICALS INC 4606 NEW W DR PASADENA Texas 77507 0.015 

CUSTOM SYNTHESIS LLC 1704 DENVER RD ANDERSON South Carolina 29625 0.0025 

ASHLAND DISTRIBUTION CO 5125 W HANNA AVE TAMPA Florida 33634 0.0015 

BARTON SOLVENTS INC KANSAS CITY 901 S 66TH TERRACE KANSAS CITY Kansas 66111 0.009 

SHERWIN-WILLIAMS CO 630 E 13TH ANDOVER Kansas 67002 0.0315 

Page 32 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

BRENNTAG SOUTHWEST INC SAND SPRINGS 206 E MORROW RD SAND SPRINGS Oklahoma 74063 0.02 

RECTICEL INTERIORS NORTH AMERICA LLC 1420 INDUSTRIAL PARK DR TUSCALOOSA Alabama 35401 0.0005 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

2000 WESTHALL ST PITTSBURGH Pennsylvania 15233 0.032 

AIR PRODUCTS PERFORMANCE MANUFACTURING INC 337 VINCENT DR MILTON Wisconsin 53563 0.0025 

BIOLAB INC 1735 DOGWOOD DR CONYERS Georgia 30012 0.03915 

HUNTSMAN ADVANCED MATERIALS AMERICAS INC 555 HUNTSMAN RD MC INTOSH Alabama 36553 0.0125 

BASF CORP 100 INDUSTRIAL BLVD SEAFORD Delaware 19973 0.0025 

CLEARWATER INTERNATIONAL LLC 100 INDUSTRIAL DR (BLDG 1LEETSDALE Pennsylvania 15056 0 

RICHARDSAPEX INC 4202-24 MAIN ST PHILADELPHIA Pennsylvania 19127 0.02673425 

KEMIRA WATER SOLUTIONS INC 1 CYANAMID RD MOBILE Alabama 36614 0.013 

CONOCOPHILLIPS CO EAST ST LOUIS TERMINAL 3300 MISSISSIPPI AVE CAHOKIA Illinois 62206 0 

CONTINENTAL CEMENT CO LLC 10107 HWY 79 HANNIBAL Missouri 63401 0.0351 0

SI GROUP INC 1000 MAIN ST ROTTERDAM JUNCTNew York 12150 0 

BRENNTAG NORTHEAST INC 81 W HULLER LN READING Pennsylvania 19605 0.01975 UNIVAR USA INC BERKELEY 8925 SEEGER INDUSTRIAL DBERKELEY Missouri 63134 0.0295 

VEOLIA ES TECHNICAL SOLUTIONS LLC 7 MOBILE AVE SAUGET ILLINOIS 62201 0.0015 TRANSTAR AUTOBODY TECHNOLOGIES 2040 HEISERMAN DR BRIGHTON Michigan 48114 0.016435 

VALSPAR REFINISH 210 CROSBY ST PICAYUNE Mississippi 39466 0 

DUPONT PARLIN PLANT CHEESEQUAKE RD PARLIN New Jersey 08859 0.004 

ASHLAND DISTRIBUTION 2011 TURNER ST LANSING Michigan 48906 0.026 

AMERICAN COATINGS INC 10625 MAHAFFEY RD TOMBALL Texas 77375 0.0085 

COOK COMPOSITES & POLYMERS C O 13511 MAIN ST LEMONT Illinois 60439 0.0075 

BERNER CHEESE CORP 2034 E FACTORY RD DAKOTA Illinois 61018 0 

GEORGIA-PACIFIC CHEMICALS LLC 1429 E LUFKIN AVE LUFKIN Texas 75901 0.0285 ECOLAB 18383 E RAILROAD ST CITY OF INDUSTRY California 91748 0.015 

VERSO PAPER BUCKSPORT MILL RIVER RD BUCKSPORT MAINE 4416 0.0003 

BARTON SOLVENTS INC DES MOINES 1970 NE BROADWAY DES MOINES Iowa 50313 0.004 

KWAL-HOWELLS INC (DBA KWAL PAINT INC) 2430 ALBERT BROADFOOT SBONHAM Texas 75418 0 

SHERWIN-WILLIAMS CO 113 STAGE COACH TRAIL GREENSBORO North Carolina 27409 0.0045 

Page 33 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

BARTON SOLVENTS INC WEST BEND 800 RAIL WAY WEST BEND Wisconsin 53095 0.0015 

ASHLAND DISTRIBUTION CO 8901 OLD GALVESTON RD HOUSTON Texas 77034 0.0055 

VEOLIA ES TECHNICAL SOLUTIONS LLC PORT ARTHUR FACILITY

HWY 73, 35 MILES W OF TAYPORT ARTHUR Texas 77640 0.026735 

DIC IMAGING PRODUCTS USA LLC 7335 S 10TH ST OAK CREEK Wisconsin 53154 0.0025 

NORTHERN LABS INC WEST DRIVE 5800 W DR MANITOWOC Wisconsin 54220 0.025225 SUN CHEMICAL CORP 135 W LAKE ST NORTHLAKE ILLINOIS 60164 0.0035 

BARTON SOLVENTS INC COUNCIL BLUFFS 2135 9TH AVE COUNCIL BLUFFS Iowa 51502 0.0015 

VALERO THREE RIVERS REFINERY 301 LEROY ST THREE RIVERS Texas 78071 0.023 BARTON SOLVENTS INC WICHITA 201 S CEDAR VALLEY CENTER Kansas 67147 0.01 

DAUBERT CHEMICAL CO 4700 S CENTRAL AVE CHICAGO Illinois 60638 0.009615 0ARLON INC ADHESIVES & FILMS DIV 2811 S HARBOR BLVD SANTA ANA California 92704 0 

KBP COIL COATERS INC 3600 E 44TH AVE DENVER Colorado 80216 0 GAGE PRODUCTS CO 625 WANDA AVE FERNDALE Michigan 48220 0 PROCTER & GAMBLE HAIR CARE LLC 2200 LOWER MUSCATINE R IOWA CITY Iowa 52240 0.0065 

SHERWIN-WILLIAMS CO 11700 S COTTAGE GROVE CHICAGO Illinois 60628 0 

BASF CORP 1 JAMES ST BELVIDERE New Jersey 07823 0 

HERITAGE-WTI INC 1250 ST GEORGE ST EAST LIVERPOOL Ohio 43920 0.005 0

EXCEL POLYMERS LLC 14330 KINSMAN RD BURTON OHIO 44021 0 

3M CO - SPRINGFIELD 3211 E CHESTNUT EXPY SPRINGFIELD Missouri 65802 0 

AFTON CHEMICAL CORP 501 MONSANTO AVE SAUGET ILLINOIS 62201 0.005 

PRIDE SOLVENTS & CHEMICAL CO OF NEW JERSEY 211 RANDOLPH AVE AVENEL New Jersey 07001 0.005 

UNIVAR USA INC - TOLEDO SOUTH BRANCH 4051 S AVE TOLEDO Ohio 43615 0.009 

ECOLAB INC 2305 SHERWIN ST GARLAND Texas 75041 0.0085 

STEEL DYNAMICS INC 4500 COUNTY RD 59 BUTLER Indiana 46721 0 UNIVAR USA INC JACKSONVILLE FA CILITY 155 ELLIS RD S JACKSONVILLE Florida 32254 0.0145 ZEP COMMERCIAL 350 JOE FRANK HARRIS PK

WEMERSON Georgia 30137 0 

TAKASAGO INTERNATIONAL CORP (USA) 267 UNION ST NORTHVALE New Jersey 07647 0.017325 0SHERWIN-WILLIAMS CO 6795 S MAIN ST MORROW Georgia 30260 0.005 

DAVIES IMPERIAL COATINGS INC 1275 STATE ST HAMMOND Indiana 46320 0.0175 

SHERWIN-WILLIAMS CO 2121 NEW WORLD DR COLUMBUS Ohio 43207 0.009 

Page 34 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

UNIVAR USA INC 21600 DRAKE RD STRONGSVILLE Ohio 44136 0.0085 

HENKEL CORP 421 LONDON RD DELAWARE Ohio 43015 0 

RUST-OLEUM CORP IN MD 16410 INDUSTRIAL LN WILLIAMSPORT MARYLAND 21795 0.0085 

AVERY DENNISON PFD 650 W 67TH AVE SCHERERVILLE Indiana 46375 0.015 HOLLY OAK CHEMICAL INC 101 CASE ST FOUNTAIN INN South Carolina 29644 0.0153 ASHLAND DISTRIBUTION CO 1842 ENTERPRISE PKWY TWINSBURG Ohio 44087 0.002 

PRIDE SOLVENT & CHEMICAL CO OF NY INC 6 LONG ISLAND AVE HOLTSVILLE New York 11742 0.0035 

ETHOX CHEMICALS LLC 1801 PERIMETER RD GREENVILLE South Carolina 29605 0.0025 

UNIVAR USA INC - INDIANAPOLIS 7425 E 30TH ST INDIANAPOLIS Indiana 46219 0.0035 

SIMONIZ USA INC 201 BOSTON TURNPIKE BOLTON Connecticut 06043 0.0135 

MEADWESTVACO SOUTH CAROLINA LLC 400 CROSBY RD DERIDDER Louisiana 70634 0 

COGNIS CORP MAULDIN PLANT 1520 OLD STAGE RD MAULDIN South Carolina 29662 0.006 

INTERSTATE CHEMICAL CO INC 2797 FREEDLAND RD HERMITAGE PENNSYLVANIA16148 0.003 

EXCEL POLYMERS LLC 150 S CONNELL AVE DYERSBURG Tennessee 38024 0 

PRC-DESOTO INTERNATIONAL INC 11601 UNITED ST MOJAVE California 93501 0.006 

CARBOLINE CO 900 OPELOUSAS ST LAKE CHARLES Louisiana 70601 0 JOHNSONDIVERSEY INC 8311 16TH ST STURTEVANT Wisconsin 53177 0.001385 

UNIVAR USA INC TAMPA FACILITY 6049 OLD 41A HWY TAMPA Florida 33619 0.005 

PLASTI-KOTE INC 1000 LAKE RD MEDINA OHIO 44258 0 

GOODWIN CO 700 PROGRESS CENTER AVLAWRENCEVILLE Georgia 30043 0.012 

VARN INTERNATIONAL 1333 N KIRK RD BATAVIA Illinois 60510 0.0075 

TRUE VALUE MANUFACTURING 201 JANDUS RD CARY Illinois 60013 0.0025 

UNIVAR USA INC - SAN JOSE 2256 JUNCTION AVE SAN JOSE California 95131 0.002 

EVONIK DEGUSSA CORP 4201 DEGUSSA RD THEODORE Alabama 36582 0.011 

BERRIDGE MANUFACTURING CO 6515 FRATT RD SAN ANTONIO Texas 78218 0 

CLEAN HARBORS ENVIRONMENTAL SERVICES INC 2247 S HWY 71 KIMBALL Nebraska 69145 0.0065 

BUCKLEY OIL CO 1809 ROCK ISLAND ST DALLAS Texas 75207 0.0075 

CHEMOL CO INC 2300 RANDOLPH AVE GREENSBORO North Carolina 27406 0 0HYDRITE CHEMICAL CO 2545 BOND ST UNIVERSITY PARK Illinois 60466 0 

HENKEL CORP 923 MAULDIN RD CALHOUN Georgia 30701 0 

Page 35 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

SHERWIN-WILLIAMS CO 2325 HOLLINS FERRY RD BALTIMORE Maryland 21230 0.004 

SHERWIN-WILLIAMS CO 26300 FARGO AVE BEDFORD HEIGHTS Ohio 44146 0.0005 

DSM DESOTECH INC 1101 HWY 27 S STANLEY North Carolina 28164 0 

MULTI-COLOR CORP 2281 S US 31 SCOTTSBURG Indiana 47170 0 0

MARATHON PETROLEUM CO LLC 502 10TH ST S TEXAS CITY Texas 77590 0 

FERRO CORP WALTON HILLS OPERATIONS 7050 KRICK RD WALTON HILLS OHIO 44146 0.0035 

CLOROX PRODUCTS MANUFACTURING CO 17 LAKE MIRROR RD FOREST PARK Georgia 30297 0.003985 0MALLINCKRODT BAKER INC 600 N BROAD ST PHILLIPSBURG New Jersey 08865 0.0075 

US DOD USAF JOINT BASE ELMENDORF-RICHARDSON 6326 ARCTIC WARRIOR DR ELMENDORF AFB ALASKA 99506 0.005 

RUSTOLEUM CORP 7850 OHIO RIVER RD LESAGE West Virginia 25537 0.0025 

INTERSTATE CHEMICAL CO INC 23247 W EAMES ST CHANNAHON Illinois 60410 0.002 DYNALOY LLC 6445 OLIVIA LN INDIANAPOLIS Indiana 46226 0.0015 

BASF CORP 1609 BIDDLE AVE WYANDOTTE Michigan 48192 0.0025 

NATIONAL INDUSTRIAL COATINGS INC DBA NICOAT INC 1600 GLENLAKE AVE ITASCA Illinois 60143 0.0005 

BRULIN CORP 2920 DR ANDREW J BROWNINDIANAPOLIS Indiana 46205 0.0030875 

FORD MOTOR CO DEARBORN DIVERSIFIED MANUFACTURING

3001 MILLER RD DEARBORN Michigan 48121 0.007 

MARATHON PETROLEUM CO LLC - SPEEDWAY IN TERMINAL

1304 OLIN AVE INDIANAPOLIS Indiana 46222 0.007 

HONEYWELL-PRESTONE PRODUCTS CORP 250 HALLS MILL RD FREEHOLD New Jersey 07728 0.0035 

LANCO MANUFACTURING CORP URBAPONTE #5 SAN LORENZO Puerto Rico 00754 0.0068 NEW DAWN MANUFACTURING CO 16001 TRADE ZONE AVE UPPER MARLBORO Maryland 20774 0.006732805 

UNIVAR USA INC NORCROSS FACILI TY 2145 SKYLAND CT NORCROSS Georgia 30071 0.003 

SHERWIN-WILLIAMS CO 12401 INDUSTRIAL BLVD VICTORVILLE California 92392 0.003 VERSO PAPER HOLDINGS LLC ANDROSCOGGIN MILL RILEYJAY Maine 04239 0.0025 

PROCTER & GAMBLE MANUFACTURING CO 1900 KANSAS AVE KANSAS CITY Kansas 66105 0.005915 BP PRODUCTS NORTH AMERICA WHITING 2815 INDIANAPOLIS BLVD WHITING Indiana 46394 0.006 

CONOCOCPHILLIPS CO WICHITA TERMINAL 2400 E 37TH ST N WICHITA KANSAS 67219 0 

CALLAHAN CHEMICAL CO 200 INDUSTRIAL AVE RIDGEFIELD PARK New Jersey 07660 0.003 GOODWIN CO 12361 MONARCH ST GARDEN GROVE California 92841 0.005 

Page 36 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

HUBBARD-HALL INC 563 S LEONARD ST WATERBURY Connecticut 06708 0.0005 

LUBRIZOL CORP PAINESVIL LE PLANT 155 FREEDOM RD PAINESVILLE Ohio 44077 0.0045 

UNIVAR USA INC - BUNOLA BRANC H 328 BUNOLA RIVER RD BUNOLA Pennsylvania 15020 0.0025 

ENTHONE INC 9809 INDUSTRIAL DR BRIDGEVIEW Illinois 60455 0.00053 0

GE WATER & PROCESS TECHNOLOGIES 333 S LOMBARD RD ADDISON ILLINOIS 60101 0.0025 SHIELD PACKAGING CO INC 50 OXFORD AVE DUDLEY Massachusetts 01571 0.0025 SARTOMER CO INC 601 TIGHTSQUEEZE INDUSTCHATHAM Virginia 24531 0.0025 

UNIVAR USA INC LAKEVILLE 21675 HAMBURG AVE LAKEVILLE Minnesota 55044 0.0025 PVS NOLWOOD CHEMICALS INC 9000 HUBBELL AVE DETROIT MICHIGAN 48228 0.0025 INTERNATIONAL PAINT LLC 640 N ROCKY RIVER DR BEREA OHIO 44017 0.0025 

INDEPENDENT INK INC 14705 S AVALON BLVD GARDENA California 90248 0.0025 

GE WATER & PROCESS TECHNOLOGIES 2118 REISER AVE SE NEW PHILADELPHIA OHIO 44663 0.0025 

SARTOMER CO INC 610 S BOLMAR ST WEST CHESTER Pennsylvania 19382 0.0025 

FORD MOTOR CO DEARBORN TOOL & DIE PLANT 3001 MILLER RD DEARBORN Michigan 48121 0.005 

CR BRANDS INC 141 VENTURE BLVD SPARTANBURG South Carolina 29306 0.0025 

C P INC 196 S WATER CONNERSVILLE Indiana 47331 0.0025 BRAIN POWER INC 4470 SW 74TH AVE MIAMI Florida 33155 0.0025 ACTEGA RADCURE INC 5 MANSARD CT WAYNE New Jersey 07470 0.0025 

GE WATER & PROCESS TECHNOLOGIES - BAKERSFIELD 3050 PEGASUS RD BAKERSFIELD CALIFORNIA 93308 0.0025 

BOEING COMMERCIAL AIRPLANE GROUP PLANT 2 (PART) 7755 E MARGINAL WAY S SEATTLE Washington 98108 0.001 

CENTRAL SOLUTIONS INC 401 FUNSTON RD KANSAS CITY Kansas 66115 0 

BAKER PETROLITE BAYPORT FACILI TY 13200 BAYPARK RD PASADENA Texas 77507 0.0045 0EDCO PRODUCTS INC 8700 EXCELSIOR BLVD HOPKINS MINNESOTA 55343 0 

MEADWESTVACO SC LLC CHARLESTON CHEMICAL PLANT 5598 VIRGINIA AVE NORTH CHARLESTOSouth Carolina 29406 0.004475 0

LAFARGE MIDWEST INC (INCLD SYSTECH ENVIRONMENTAL)

1400 S CEMENT RD FREDONIA KANSAS 66736 0.0045 

COGNIS CORP -- CHARLOTT E PLANT 3300 WESTINGHOUSE BLVDCHARLOTTE North Carolina 28273 0.0045 

OMNIUM 1280 IMPERIAL RD HAMPTON Iowa 50441 0.0015 

CUSTOM CHEMICAL FORMULATORS 8707 MILLERGROVE DR SANTA FE SPRINGS California 90670 0.004 

Page 37 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

CHEMTEX LABORATORIES INC 2725 ARMENTROUT DR CONCORD North Carolina 28025 0.004 ASHLAND DISTRIBUTION 3701 RIVER RD TONAWANDA New York 14150 0.001 

NORLITE CORP 628 S SARATOGA ST COHOES New York 12047 0.003525 0PENRAY COMPANIES INC 1801 ESTES AVE ELK GROVE VILLAGEIllinois 60007 0.0005 

PENRAY COMPANIES INC 440 DENNISTON CT WHEELING Illinois 60090 0.0005 

BAKER PETROLITE 5135 BOYLAN ST BAKERSFIELD California 93308 0.003025 0

UNIVAR USA INC DENVER 4300 HOLLY ST DENVER Colorado 80216 0.0025 VOGEL PAINT & WAX CO INC 1020 ALBANY PL SE ORANGE CITY Iowa 51041 0.0025 UNIVAR USA INC- CINCINNATI OH BRANCH 4600 DUES DR CINCINNATI Ohio 45246 0.0015 

SHERWIN-WILLIAMS CO 404 E MALLORY AVE MEMPHIS Tennessee 38109 0.001 

3M COTTAGE GROVE CENTER 10746 INNOVATION RD COTTAGE GROVE Minnesota 55016 0 UNIVAR USA INC 3950 NW YEON AVE PORTLAND Oregon 97210 0.002 CONOCOPHILLIPS MT VERNON PRODUCTS TERMINAL 15138 HWY 96 MOUNT VERNON Missouri 65712 0 

MACDERMID INC 1221 FARROW AVE FERNDALE Michigan 48220 0.00131 

CONOCOPHILLIPS PONCA CITY REFINERY 1000 S PINE ST PONCA CITY Oklahoma 74601 0.0025 ASTRO CHEMICALS INC 126 MEMORIAL DR SPRINGFIELD Massachusetts 01104 0.002 

UNION SPECIALTIES INC 3 MALCOLM HOYT DR NEWBURYPORT Massachusetts 01950 0.0005 

PPG ARCHITECURAL COATINGS HOUSTON 3530 LANG RD HOUSTON Texas 77092 0.0025 

CONOCOPHILLIPS CO TREMLEY POINT TERMINAL FOOT OF S WOOD AVE LINDEN New Jersey 07036 0.0025 ECP INC WOODRIDGE 11210 KATHERINE'S CROSS WOODRIDGE Illinois 60517 0.0025 

MILPORT ENTERPRISES INC 2829 S 5TH CT MILWAUKEE Wisconsin 53207 0 

BRAINERD CHEMICAL CO INC 1200 N PEORIA TULSA OKLAHOMA 74147 0 

DOBER CHEMICAL CORP 14461 WAVERLY AVE MIDLOTHIAN Illinois 60445 0.0025 NOV TUBOSCOPE HOLMES ROAD 2811 HOLMES RD HOUSTON Texas 77051 0.0025 

FINGER LAKES CHEMICAL INC 418-424 ST PAUL ST ROCHESTER New York 14605 0.0025 

ATOTECH USA 1750 OVERVIEW DR ROCK HILL South Carolina 29730 0.0025 

KEYSTONE CEMENT CO RT 329 BATH Pennsylvania 18014 0 NIACET CORP 400 47TH ST NIAGARA FALLS New York 14304 0.0025 

BIOLAB INC 101 S PARKER DR ASHLEY INDIANA 46705 0.0025 

CR BRANDS INC 230 OLD CONVERSE RD SPARTANBURG South Carolina 29307 0.0025 

Page 38 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

WYNNEWOOD REFINING CO 906 S POWELL WYNNEWOOD Oklahoma 73098 0 

CHEMICAL SOLVENTS INC--DENISON FACILITY 1010 OLD DENNISON AVE CLEVELAND Ohio 44109 0.0025 

BAKER PETROLITE CORP 16950 WALLISVILLE RD HOUSTON Texas 77049 0.0003495 0

KING INDUSTRIES INC SCIENCE RD NORWALK Connecticut 06852 0.00125 CLARIANT CORP CLEAR LAKE PLANT 9502 BAYPORT BLVD - ETOXPASADENA Texas 77507 0.0023 

HENTZEN COATINGS,INC 6937 W MILL RD MILWAUKEE Wisconsin 53218 0.000875 

DYNASOL INC 330 PINE ST CANTON Massachusetts 02021 0.00215 UNIVAR USA INC SANTA FE SPRINGS 13900 CARMENITA RD SANTA FE SPRINGS California 90670 0.001 DUPONT EKC TECHNOLOGY 2520 BARRINGTON CT HAYWARD California 94545 0.0005 

CALLAHAN CHEMICAL CO 18 INDUSTRIAL RD WALPOLE Massachusetts 02081 0.0015 

ASHLAND DISTRIBUTION CO FREEPORT CENTER BUILDI CLEARFIELD Utah 84016 0.0005 

CRODA INC 315 CHERRY LN NEW CASTLE Delaware 19720 0.001405 

TARR ACQUISITION LLC 2429 N BORTHWICK AVE PORTLAND Oregon 97227 0.001825 BAKER PETROLITE-RAYNE FACILITY 135 INDUSTRIAL DR RAYNE Louisiana 70578 0.0005 

VOLTAIX LLC 197 MEISTER AVE BRANCHBURG New Jersey 08876 0.0005 

GIANT CEMENT CO HWY 453 & I-26 (654 JUDGE HARLEYVILLE South Carolina 29448 0.001 

BUCKMAN LABORATORIES INC 1256 N MCLEAN BLVD MEMPHIS Tennessee 38108 0 

KELLY-MOORE PAINT CO INC 1015 COMMERCIAL ST SAN CARLOS California 94070 0 

HYDRITE CHEMICAL CO 7300 W BRADLEY RD MILWAUKEE Wisconsin 53223 0.0005 

NALCO CO - ODESSA PLANT 114 12205 W COUNTY RD 125 ODESSA Texas 79765 0 

PPG ARCHITECTURAL COATINGS 6804 ENTERPRISE DR LOUISVILLE Kentucky 40214 0 

FUJIFILM HUNT CHEMICALS USA INC 900 CARNEGIE ST ROLLING MEADOWSIllinois 60008 0.00105 

FIRST SOURCE WORLDWIDE LLC MILWAUKEE 11725 W FAIRVIEW AVE MILWAUKEE Wisconsin 53226 0.0011 

MANN DISTRIBUTION 3134 POST RD WARWICK Rhode Island 02886 0.00112 

SHERWIN-WILLIAMS CO 14 INDUSTRIAL PARK FLORA Illinois 62839 0.0005 

MONSANTO CO 2500 WIGGINS RD MUSCATINE Iowa 52761 0 

CLEAN HARBORS DEER PARK LLC 2027 INDEPENDENCE PKWYLA PORTE TEXAS 77571 0.001 

BRENNTAG SOUTHEAST INC 11750 FRUEHAUF DR CHARLOTTE North Carolina 28273 0.0005 

BENJAMIN MOORE & CO - NEWARK 134 LISTER AVE NEWARK New Jersey 07105 0.001 

LAFARGE NA (INCLUDING SYSTECH ENV CORP) 11435 COUNTY RD 176 PAULDING OHIO 45879 0 

Page 39 of 40
Table B-2. 2010 Emissions Inventory: Non-Zero Certain Glycol Ether Reported R

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(tp

OMNOVA SOLUTIONS INC 1455 J A COCHRAN BY-PASSCHESTER South Carolina 29706 0.00075 

NALCO CO 3901 TERRY ST TEXARKANA Texas 75501 0 

HARWICK STANDARD DISTRIBUTION CORP 60 S SEIBERLING ST AKRON Ohio 44305 0.0005 

NALCO CO - EVANSVILLE PLANT 108 4900 E YELLOWSTONE HWYEVANSVILLE WYOMING 82636 0 

SURPASS CHEMICAL CO INC 1254 BROADWAY ALBANY New York 12204 0.000485 

NALCO CO 812 RENAUD DR SCOTT Louisiana 70583 0.000011 0.0

PARKER HANNIFIN TECH SEAL DIV 2600 WILCO BLVD WILSON North Carolina 27893 0 

LAMBERTI SYNTHESIS USA INC 4001 N HAWTHORNE ST CHATTANOOGA Tennessee 37406 0.0002205 

CHEMETALL US INC 1610 CLARA ST JACKSON Michigan 49203 0.0000441 0.0

IFF AUGUSTA LTD 3005 INTERNATIONAL BLVD AUGUSTA Georgia 30906 0 0

RIKER PRODUCTS INC 4901 STICKNEY AVE TOLEDO Ohio 43612 0.000082 BAKER PETROLITE KILGORE BLEND PLANT 806 PALUXY ST KILGORE Texas 75662 0.0000212 0.0EMERALD SERVICES INC 1825 E ALEXANDER AVE TACOMA Washington 98421 0 0NALCO CO 125 NALCO WAY/RT 65 ELLWOOD CITY Pennsylvania 16117 0.0000028 0

AIR PRODUCTS PERFORMANCE MANUFACTURING INC 474 W 19TH ST RESERVE Louisiana 70084 0 0a. Releases to Surface Water reported as "On-Site Releases to Surface Water."b. Releases to Soil is the sum of reported releases to onsite and offsite releases to land treatment and other land disposal.c. Releases to other media include reported releases to onsite and offsite groundwater and landfills.tpy: tons per year

Page 40 of 40
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

EQ DETROIT INC 1923 FREDERICK DETROIT MI 48211 0 BALL METAL BEVERAGE CONTAINER CORP 8935 POCAHONTAS TRAIL JWILLIAMSBURG VA 23185 28 

BALL METAL BEVERAGE CONTAINER CORP 12340 TOWNSHIP RD 99 E FINDLAY OH 45840 25.5 

BMW MANUFACTURING CO LLC 1400 HWY 101 S GREER SC 29651 2.4745 1

REXAM BEVERAGE CAN CO RE: WINSTON SALEM PLANT

4000 OLD MILWAUKEE LN WINSTON-SALEM NC 27107 25.716 

CROWN FOOD PACKAGING 2929 W BRIDGE ST OWATONNA MN 55060 31.8905 

REXAM BEVERAGE CAN CO RE: FREMONT PLANT 2145 CEDAR FREMONT OH 43420 19.034 

BALL METAL BEVERAGE CONTAINER CORP 1900 BARNES ST REIDSVILLE NC 27320 17 FLINT HILLS RESOURCES CORPUS CHRISTI LLC - WEST PLANT

2825 SUNTIDE RD CORPUS CHRISTI TX 78409 0.1435 

CROWN CORK & SEAL CO (USA) INC CROWN CLOSURE DIV

3011 BIRCH DR WEIRTON WV 26062 34.526 

REXAM BEVERAGE CAN CO RE: BISHOPVILLE SC FACILITY

609 COUSAR ST BISHOPVILLE SC 29010 13.386 

REXAM BEVERAGE CAN CO RE: KENT WA FACILITY 1220 N SECOND AVE KENT WA 98032 12.442 

REXAM BEVERAGE CAN CO RE: OLIVE BRANCH FACILITY

10800 MARINA DR OLIVE BRANCH MS 38654 18.811 

BALL CONTAINER LLC - COLUMBUS CAN PLANT 350 MCCORMICK BLVD COLUMBUS OH 43213 12 

REXAM BEVERAGE CAN CO RE: EVA STREET ST PAUL MN

139 EVA ST SAINT PAUL MN 55107 11.8215 

REXAM BEVERAGE CAN CO RE: WHITEHOUSE PLANT 10444 WATERVILLE WHITEHOUSE OH 43571 24.8555 

CROWN BEVERAGE PACKAGING GLEN & SHEPARD ST LAWRENCE MA 01843 17.5445 

FORD MOTOR CO DEARBORN TRUCK PLANT 3001 MILLER RD DEARBORN MI 48121 1.15 

PPG INDUSTRIES INC-OAK CREEK 10800 S 13TH ST OAK CREEK WI 53154 35.178 

SILGAN CONTAINERS MANUFACTURING CORP 300 N FAIL RD LA PORTE IN 46350 12.191 

CROWN BEVERAGE PACKAGING 1035 E N ST BRADLEY IL 60915 16.211 

CROWN BEVERAGE PACKAGING 1202 FONES RD OLYMPIA WA 98501 15.9915 

FORD MOTOR COMPANY--KANSAS CITY ASSEMBLY PLANT

8121 E U.S. HWY 69 CLAYCOMO MO 64119 1.55 

CHRYSLER JEFFERSON NORTH ASSEMBLY PLANT 2101 CONNOR AVE DETROIT MI 48215 6 METAL CONTAINER CORPORTION - WINDSOR CAN 

PLANT

1201 METAL CONTAINER CTWINDSOR CO 80550 14.5265 

CROWN BEVERAGE PACKAGING 620 N 4TH ST WORLAND WY 82401 13.335 

REXAM BEVERAGE CAN CO RE: LONGVIEW FACILITY 1001 FISHER RD LONGVIEW TX 75604 4.823 

Page 1 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

WHIRLPOOL CORP MARION DIV 1300 MARION-AGOSTA RD MARION OH 43302 0.05 

RR DONNELLEY 2347 KRATZER RD HARRISONBURG VA 22802 45.2035 

HUNTSMAN PETROCHEMICAL LLC PORT NECHES 

FACILITY

6001 HWY 366 PORT NECHES TX 77651 0.11 

BALL CONTAINER LLC ROME CAN PLANT 110 BALL DR ROME GA 30161 31 

FORD MOTOR CO KENTUCKY TRUCK PLANT 3001 CHAMBERLAIN LN LOUISVILLE KY 40241 3.25 

METAL CONTAINER CORP - ARNOLD CAN PLANT 42 TENBROOK INDUSTRIALARNOLD MO 63010 16.3535 

REXAM BEVERAGE CAN CO RE: PHOENIX FACILITY 211 N 51AVE PHOENIX AZ 85043 5.7315 

USS - CLAIRTON PLANT 400 STATE ST CLAIRTON PA 15025 41 METAL CONTAINER CORP - NEWBURGH CAN PLANT 130 BREUNIG RD NEW WINDSOR NY 12553 11.0015 

HONDA OF AMERICA MANUFACTURING INC 24000 HONDA PKWY MARYSVILLE OH 43040 2.7 HONDA OF AMERICA MANUFACTURING INC 11000 STATE RT 347 EAST LIBERTY OH 43319 2.3 

GREIF PACKAGING LLC 7425 INDUSTRIAL RD FLORENCE KY 41042 3.4725 

CHICAGO HEIGHTS STEEL 211 E MAIN ST CHICAGO HEIGHTS IL 60411 7.172 

S D WARREN CO 89 CUMBERLAND ST WESTBROOK ME 04098 0.00391 

BALL METAL BEVERAGE CONTAINER CORP 8500 W TOWER AVE MILWAUKEE WI 53224 27.5 

ROCKY MOUNTAIN METAL CONTAINER 17755 W 32ND AVE GOLDEN CO 80401 26.5 

CROWN FOOD PACKAGING 8801 CITATION RD BALTIMORE MD 21221 8.637 

BATESVILLE MANUFACTURING INC 175 MONOGARD DR MANCHESTER TN 37355 1.709 EDSAL MANUFACTURING CO INC 4400 S PACKER CHICAGO IL 60609 0 

REXAM BEVERAGE CAN CO RE : CHICAGO PLANT 1101 W 43RD ST CHICAGO IL 60609 6.522 

BALL METAL BEVERAGE CONTAINER CORP 501 N SIXTH ST MONTICELLO IN 47960 14.5 

INGERSOLL-RAND CO STEELCRAFT DIV 9017 BLUE ASH RD CINCINNATI OH 45242 7.5 

CROWN BEVERAGE PACKAGING 2501 N FRAZIER ST CONROE TX 77303 27.5695 

BALL METAL BEVERAGE CONTAINER CORP 4525 INDIANA ST GOLDEN CO 80403 20 

CROWN BEVERAGE PACKAGING 12910 JESS PIRTLE BLVD SUGAR LAND TX 77478 27.381 

METAL CONTAINER CORP - MIRA LOMA CAN PLANT 10980 INLAND AVE MIRA LOMA CA 91752 27.5195 

NISSAN NA INC SMYRNA MANUFACTURING PLANT 983 NISSAN DR SMYRNA TN 37167 0.02302895 30.7

SUBARU OF INDIANA AUTOMOTIVE INC 5500 STATE RD 38E LAFAYETTE IN 47905 0.295 

REXAM BEVERAGE CAN CO RE: CHATSWORTH FACILITY

20730 PRAIRIE ST CHATSWORTH CA 91311 6.4125 

MERCEDES-BENZ US INTERNATIONAL INC 1 MERCEDES DR VANCE AL 35490 0.501 

Page 2 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

NEW YORK WIRE 500 E MIDDLE ST HANOVER PA 17331 0 

ARKEMA COATING RESINS 340 RAILROAD ST SAUKVILLE WI 53080 0.6965 

AMES TRUE TEMPER INC 1500 S CAMERON ST HARRISBURG PA 17104 1.381 

SENECA FOODS CORP 801 SAUK AVE BARABOO WI 53913 0 

GM LLC POWERTRAIN FLINT ENGINE OPERATIONS 2100 BRISTOL RD FLINT MI 48552 0.6855 

CROWN BEVERAGE PACKAGING 1501 ST JAMES ST LA CROSSE WI 54603 23.9785 

METAL CONTAINER CORP - JACKSONVILLE CAN PLANT

1100 N ELLIS RD JACKSONVILLE FL 32254 6.4585 

HONDA MANUFACTURING OF ALABAMA LLC 1800 HONDA DR LINCOLN AL 35096 0.4995 

GENERAL MOTORS LANSING DELTA TOWNSHIP 8175 MILLETT HWY LANSING MI 48917 0.55 

THERMA-TRU CORP 601 RE JONES RD BUTLER IN 46721 0 

S B FOOT TANNING CO 805 BENCH ST RED WING MN 55066 0 

CROWN BEVERAGE PACKAGING 380 CALLE FABRIL ST KM 1 CAROLINA PR 00985 6.0485 

MEMC PASADENA INC 3000 N S ST PASADENA TX 77503 15.043 

ALSTOM POWER INC CHATTANOOGA BOILERS 1119 RIVERFRONT PKWY CHATTANOOGA TN 37402 23.9355 CROWN BEVERAGE PACKAGING 100 EVANS ROW CHERAW SC 29520 21.161 

BWAY CORP 3200 S KILBOURN AVE CHICAGO IL 60623 7.24545 

CROWN BEVERAGE PACKAGING 195 CROWN RD BATESVILLE MS 38606 19.269 

MAVERICK TUBE LLC DBA TENARISCONROE 699 F.M. 3083 CONROE TX 77301 0.95633545 5.98

CROWN BEVERAGE PACKAGING 400 N WALNUT ST CRAWFORDSVILLE IN 47933 15.725 

WHIRLPOOL CORP FINDLAY DIV 4901 N MAIN ST FINDLAY OH 45840 2.1509 

BALL METAL BEVERAGE CONTAINER CORP 2400 HUNTINGTON DR FAIRFIELD CA 94533 9 

SAF-HOLLAND USA INC 101 S ELM WARRENTON MO 63383 18.5495 

JOHN DEERE DES MOINES WORKS 825 SW IRVINEDALE DR ANKENY IA 50023 0 

ALCOA INC - WARRICK OPERATIONS HWYS 66 & 61 NEWBURGH IN 47629 0 

BOEING COMMERCIAL AIRPLANES - EVERETT 3003 W CASINO RD EVERETT WA 98204 3.45 AIR SYSTEM COMPONENTS LP 900 DARR PARK DR PONCA CITY OK 74601 0.2025 

AGY AIKEN LLC 2556 WAGENER RD AIKEN SC 29801 12.247 

PELLA CORP 102 MAIN ST PELLA IA 50219 0.125 

ITW SEXTON INC 3101 SEXTON RD DECATUR AL 35603 0.96278 1

BALL METAL BEVERAGE CONTAINER CORP 11 ADAMS RD SARATOGA SPRINGNY 12866 3.25 

Page 3 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

MOBIL CHEMICAL CO 41501 WOLVERINE RD SHAWNEE OK 74804 0.375 

GREIF PACKAGING LLC 4300 W 130TH ST ALSIP IL 60803 4.1295 

MID-AMERICA STEEL DRUM CO IN C 8570 S CHICAGO RD OAK CREEK WI 53154 0 NASHVILLE WIRE PRODUCTS 1604 COUNTY HOSPITAL RDNASHVILLE TN 37218 16.5 

TOYOTA MOTOR MANUFACTURING INDIANA INC 4000 TULIP TREE DR PRINCETON IN 47670 12.595 

UNION CARBIDE CORP SEADRIFT PLANT 7501 N HWY 185 SEADRIFT TX 77983 14.188 BALL METAL BEVERAGE CONTAINER CORP 95 BALLARD RD MIDDLETOWN NY 10940 8 

CARRY-ON TRAILER CORP 101 JOE HARVEY ST LAVONIA GA 30553 0 

NORTH COAST CONTAINER CORP 8806 CRANE AVE CLEVELAND OH 44105 0 

BALL METAL BEVERAGE CONTAINER CORP 1001 N FM 3083 E CONROE TX 77303 13 

BALL METAL BEVERAGE CONTAINER CORP 4700 WHITEWAY DR TAMPA FL 33617 8 

PENN COLOR INC 2755 BERGEY RD HATFIELD PA 19440 2.951 0

MAVERICK TUBE LLC 4950 N COUNTY RD 967 BLYTHEVILLE AR 72315 11.16161105 

AIR SYSTEM COMPONENTS LP 3301 N MAIN ST TARBORO NC 27886 0.172 CECO DOOR PRODUCTS 9159 TELECOM DR MILAN TN 38358 8.377 

CNH AMERICA LLC 600 E PEORIA ST GOODFIELD IL 61742 1.6725 

BALL METAL BEVERAGE CONTAINER CORP 500 CRENSHAW BLVD TORRANCE CA 90503 16 

KUKA TOLEDO PRODUCTION OPERATIONS 3770 STICKNEY AVE TOLEDO OH 43612 2.0510995 DEXTER CHASSIS GROUP PLANT 55 501 S MILLER DR WHITE PIGEON MI 49099 0 

THE KNAPHEIDE MANUFACTURING CO 1848 WESTPHALIA STRASSQUINCY IL 62305 0.141 

THOMAS BUILT BUSES INC 715 W FAIRFIELD RD HIGH POINT NC 27263 0 

MPM SILICONES LLC 3500 S STATE RT 2 FRIENDLY WV 26146 2.1935 NOVOLYTE PERFORMANCE MATERIALS 111 W IRENE RD ZACHARY LA 70791 4.75 

AVX CORP MYRTLE BEACH 801 17TH AVE S MYRTLE BEACH SC 29577 1.6645 SILGAN WHITE CAP CORP 2201 W MARYLAND ST EVANSVILLE IN 47710 11.6705 

EASTMAN CHEMICAL CO TEXAS OPERATIONS 300 KODAK BLVD LONGVIEW TX 75602 12.262 

OLDCASTLE BUILDING ENVELOPE - TEXAS FACILITY 803 AIRPORT RD TERRELL TX 75160 0 

GM TRUCK GROUP FORT WAYNE ASSEMBLY 12200 LAFAYETTE CENTERROANOKE IN 46783 0.7 

NOVELIS CORP 390 GRISWOLD ST NE WARREN OH 44483 4.568 

HITACHI AUTOMOTIVE SYSTEMS AMERICAS INCBEREA KY 301 MAYDE RD BEREA KY 40403 0.0675 

Page 4 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

BEDFORD MATERIALS CO INC 7676 ALLEGHENY RD MANNS CHOICE PA 15550 1.4135 

ANDERSON TULLY LUMBER CO WALTERSVILLE LUMBER MILL

1725 N WASHINGTON ST VICKSBURG MS 39181 14.1275 

SILGAN CONTAINERS MANUFACTURIN G CORP 3591 MAPLE DR FORT DODGE IA 50501 0.002535 

M&B HANGERS 1313 PKWY DR SE LEEDS AL 35094 2.6945 

ARTIFLEX MANUFACTURING LLC GERSTCO DIV WOOSTER

1425 E BOWMAN ST WOOSTER OH 44691 0.401 

BALL METAL FOOD CONTAINER CORP 3010 BIRCH DR WEIRTON WV 26062 9.95 

GRAPHIC PACKAGING INTERNATIONAL INC 10300 ROBERTS BLVD FORT SMITH AR 72916 0 

DECORATIVE PANELS INTERNATIONA L 2900 HILL AVE TOLEDO OH 43607 13.1175 

VESTAL MANUFACTURING ENTERPRISES INC 177 INDUSTRIAL PARK RD SWEETWATER TN 37874 13.094 

SIGNCRAFT SCREEN PRINT 100 A.J. HARLE DR GALENA IL 61036 12.185 

HALLSTAR CO ESTER SOLUTIONS FACILITY 5851 W 73RD ST BEDFORD PARK IL 60638 1.1705 

SUPERIOR INDUSTRIES INTERNATIONAL ARKANSAS 

LLC

1301 N DIXIELAND RD ROGERS AR 72756 0.0025 

QUAD/GRAPHICS INC N61 W23044 HARRY'S WAY SUSSEX WI 53089 11.55 

RUSKIN CO HWY 27 N GENEVA AL 36340 0.0565 

BEMIS MANUFACTURING CO PLANT B 300 MILL ST SHEBOYGAN FALLSWI 53085 0 

SILGAN CAN CO 12-773 ST RT 110 NAPOLEON OH 43545 5.3645 

CROWN FOOD PACKAGING 5201 ENTERPRISE BLVD TOLEDO OH 43612 3.1835 

BERENFIELD CONTAINERS INC MASON 1229 CASTLE DR MASON OH 45040 0.125 

CLEAN HARBORS LONE MOUNTAIN LLC LONE MOUNTAIN FACILITY

5 MILES E & 1 MILE N OF JUWAYNOKA OK 73860 0.00125 

3M CO - GUIN 6675 US HWY 43 GUIN AL 35563 0.001 

BALL METAL BEVERAGE CONTAINER CORP 6600 WILL ROGERS BLVD FORT WORTH TX 76140 5.5 

NUCOR VULCRAFT GROUP SAINT JOE DIV 6610 COUNTY RD 60 SAINT JOE IN 46785 2.877 

AKZO NOBEL COATINGS INC 1629 VANDERBILT RD BIRMINGHAM AL 35234 12.1875 

HOWARD FINISHING LLC 32565 DEQUINDRE MADISON HEIGHTS MI 48071 0.0025 

MEYER STEEL DRUM INC 2000 S KILBOURN AVE CHICAGO IL 60623 1.3505 

NUCOR CORP VULCRAFT DIV 1501 W DARLINGTON ST FLORENCE SC 29501 10.9885 

NUCOR VULCRAFT GROUP - GRAPELAND DIV 175 COUNTY RD 2345 GRAPELAND TX 75844 4.282 

PLY GEM 2615 CAMPBELL RD SIDNEY OH 45365 0.705 

BALL CONTAINER LLC 105 E BLACKHAWK DR FORT ATKINSON WI 53538 3.45 

Page 5 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

AMERICAN TRIM LLC 1501 W MICHIGAN ST SIDNEY OH 45365 0 

QUAD/GRAPHICS INC 1900 W SUMNER ST HARTFORD WI 53027 11.5 

SHAMROCK TECHNOLOGIES INC FOOT OF PACIFIC ST NEWARK NJ 07114 0 WHITING DOOR MANUFACTURING CORP 113 CEDAR ST AKRON NY 14001 0 

CNH AMERICA LLC 1930 DES MOINES AVE BURLINGTON IA 52601 0.18 

CHRYSLER BELVIDERE ASSEMBLY PLANT 3000 W CHRYSLER DR BELVIDERE IL 61008 1.15 

TOPPAN INTERAMERICA INC 1131 HWY 155 S MC DONOUGH GA 30253 0 

VULCRAFT OF NEW YORK INC 5362 RAILROAD ST CHEMUNG NY 14825 4.005 

SILGAN CONTAINERS MANUFACTURING CORP 400 N 15TH ST ROCHELLE IL 61068 7.265 

SUPERIOR INDUSTRIES INTERNATIONAL ARKANSAS LLC

1901 E BORICK DR FAYETTEVILLE AR 72701 0 

VOLKSWAGEN GROUP OF AMERICA CHATTANOOGA OPERATIONS LLC

8001 VOLKSWAGEN DR CHATTANOOGA TN 37416 0 11.0

BALL METAL BEVERAGE CONTAINER CORP 91-320 KOMOHANA ST KAPOLEI HI 96707 1.95 

TRADEBE TREATMENT & RECYCLING LLC 4343 KENNEDY AVE EAST CHICAGO IN 46312 0.4655 PRECOAT METALS 1095 MENDELL DAVIS DR JACKSON MS 39272 9.879 

CHICAGO STEEL CONTAINER CORP 1846 S KILBOURN AVE CHICAGO IL 60623 0.898 TRILLA ST LOUIS CORP 2391 CASSENS DR FENTON MO 63026 1.3775 

METAL INDUSTRIES INC - BUSHNELL 400 W WALKER AVE BUSHNELL FL 33513 0.0765 

STANLEY WORKS HAND TOOLS DIV 600 MYRTLE ST NEW BRITAIN CT 06052 1.055 

TYSON FRESH MEATS INC 5000 N FM 1912 AMARILLO TX 79108 0.02 

PROFESSIONAL DISPOSABLES INTERNATIONAL INC TWO NICE-PAK PARK ORANGEBURG NY 10962 0.097675 

ALLIANCE INDUSTRIES WAUPACA N 2467 VAUGHAN RD WAUPACA WI 54981 1.0415 

TRELLEBORG OFFSHORE US RANKIN ROAD FACILITY 1902 RANKIN RD HOUSTON TX 77073 0.5125 NUCOR CORP - VULCRAFT/NUCOR COLD FINISH DIV 1601 W OMAHA AVE NORFOLK NE 68701 0.25 

THE DIAL CORP A SUBSIDIARY OF HENKEL CONSUMER GOODS

6901 MCKISSOCK AVE SAINT LOUIS MO 63147 0.081 

KAWNEER CO INC 600 KAWNEER DR SPRINGDALE AR 72764 4.094 

TOYOTA MOTOR MANUFACTURING TEX AS INC 1 LONE STAR PASS SAN ANTONIO TX 78264 6.8057207 3.13

SILGAN CAN CO 2120 NC HWY N UNIT A MAXTON NC 28364 3.112 

KITZINGER COOPERAGE CORP 2529 E NORWICH AVE SAINT FRANCIS WI 53235 0 

NISSAN NORTH AMERICA INC CANTON MS 300 NISSAN DR CANTON MS 39046 7.6025 

Page 6 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

ESCO CORP 9098 EASTSIDE DR EXT. NEWTON MS 39345 9.578 

DOW CHEMICAL CO FREEPORT FACILITY 2301 N BRAZOSPORT BLVDFREEPORT TX 77541 0.0135 

GREIF PACKAGING LLC 6000 JEFFERSON HWY NEW ORLEANS LA 70123 1.433 

STATE INDUSTRIES INC 500 TENNESSEE WALTZ PKASHLAND CITY TN 37015 0.094 YKK AP AMERICA INC 1229 HWY 441 N BYPASS DUBLIN GA 31021 9.0285 

TOYOTA MOTOR MANUFACTURING KENTUCKY INC 1001 CHERRY BLOSSOM 

WGEORGETOWN KY 40324 0.1875 

KUBIN-NICHOLSON CORP 8448 N 87TH ST MILWAUKEE WI 53224 9.352 

ENVIRITE OF OHIO INC 2050 CENTRAL AVE SE CANTON OH 44707 0 

REXAM BEVERAGE CAN CO RE: FAIRFIELD PLANT 2433 CROCKER CIR FAIRFIELD CA 94533 5.29 

GREIF INDUSTRIAL PACKAGING & SERVICES 7604 RAILROAD AVE WINFIELD KS 67156 2.086 

SQUARE D CO 1601 MERCER RD LEXINGTON KY 40511 0.098 

RR DONNELLEY LANCASTER WEST 1375 HARRISBURG PIKE LANCASTER PA 17601 8.509 

GENERAL MOTORS WENTZVILLE ASSEMBLY 1500 E RT A WENTZVILLE MO 63385 1.05 BRIGGS & STRATTON POWER PRODUCTS MCDONOUGH OPERATIONS

535 MACON RD MC DONOUGH GA 30253 0 

KEYMARK CORP OF FLORIDA 2540 KNIGHTS STATION RDLAKELAND FL 33810 0.45 

SILGAN CONTAINERS MANUFACTURING CORP 2115 SW LOWER LAKE RD SAINT JOSEPH MO 64504 5.2455 

ROYAL MOULDINGS LTD; MARION VIRGINIA 135 BEAR CREEK RD MARION VA 24354 0.4475 

MAUSER CORP 14 CONVERY BLVD WOODBRIDGE NJ 07095 0.076 

KNS COS INC 475 RANDY RD CAROL STREAM IL 60188 1.76171 

SKOLNIK INDUSTRIES 4900 S KILBOURN AVE CHICAGO IL 60632 0.9 

ACME FINISHING CO INC 1595 E OAKTON ST ELK GROVE VILLAG IL 60007 1.758 BROAN-NUTONE LLC 926 W STATE ST HARTFORD WI 53027 0.1135 

RR DONNELLEY & SONS CO 1145 CONWELL AVE WILLARD OH 44890 6.8885 

CHRYSLER WARREN TRUCK ASSEMBLY PLANT (PART) 21500 MOUND RD WARREN MI 48091 8.5 

GRAPHIC PACKAGING INTERNATIONAL INC 1500 N PITCHER ST KALAMAZOO MI 49007 0.007 

HART & COOLEY INC 4910 MOORES MILL RD HUNTSVILLE AL 35811 0.5875 

BERENFIELD CONTAINERS SW LTD 3300 N HUTCHINSON ST WHITE HALL AR 71602 0 

CIRCLE GRAPHICS INC 120 9TH AVE LONGMONT CO 80501 3.3 3M CO - MENOMONIE 1425 STOKKE PKWY MENOMONIE WI 54751 0 

PHOENIX COLOR CORP 18249 PHOENIX DR HAGERSTOWN MD 21742 8.5 

Page 7 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

FRANKLIN INVESTMENT CORP 600 ATLANTIC AVE FRANKLIN PA 16323 8.5 MOMENTIVE SPECIALTY CHEMICALS INC 2525 S COMBEE RD LAKELAND FL 33801 8.357 

SIGNODE 7701 W 71ST ST BRIDGEVIEW IL 60455 0.85 

HAMMER PACKAGING CORP 200 LUCIUS GORDON DR WEST HENRIETTA NY 14586 0 RR DONNELLEY LANCASTER EAST 216 GREENFIELD RD LANCASTER PA 17601 7.417 

PRECOAT METALS 1950 E MAIN ST GREENFIELD IN 46140 0.026 

ELECTROPRIME INC 63 DIXIE HWY ROSSFORD OH 43460 0 

SILGAN CONTAINER MANUFACTURING CORP 3250 PATTERSON RD RIVERBANK CA 95367 0.5925 BWAY CORP 1601 VALDOSTA HWY HOMERVILLE GA 31634 5.993215 1

SILGAN CONTAINERS MANUFACTURING CORP 1416 INDIANHEAD DR MENOMONIE WI 54751 1.55 

GREIF PACKAGING LLC 695 LOUIS DR WARMINSTER PA 18974 3.072 SUPERPAC INC 1220 INDUSTRIAL BLVD SOUTHAMPTON PA 18966 0.038 

DEXTER AXLE 500 SE 27TH EL RENO OK 73036 0 

AAP ST MARYS CORP 1100 MCKINLEY RD SAINT MARYS OH 45885 0.011 AJAX METAL PROCESSING INC 4651 BELLEVUE AVE DETROIT MI 48207 0 

TTM TECHNOLOGIES INC 710 N 600 W LOGAN UT 84321 0.585 TECNOCAP LLC 2100 GRISWOLD NE WARREN OH 44483 1.5575 

NATIONAL COATINGS INC 604 US HWY 150 E GALESBURG IL 61401 7.3525 

DUPONT PONTCHARTRAIN WORKS 586 HWY 44 LA PLACE LA 70068 0.0075 FORD MOTOR CO TWIN CITIES ASSEMBLY PLANT 966 S MISSISSIPPI RIVER B SAINT PAUL MN 55116 0.08 

GM LORDSTOWN COMPLEX 2300 HALLOCK-YOUNG RD LORDSTOWN OH 44481 3.95 

BRADFORD WHITE CORP 200 LAFAYETTE ST MIDDLEVILLE MI 49333 0 

QUAD GRAPHICS NASHVILLE 2947 BRICK CHURCH PIKE NASHVILLE TN 37207 6.36 

PRECOAT METALS 858 E HUPP RD LA PORTE IN 46350 0.02 

AK STEEL CORP - ZANESVI LLE WORKS 1724 LINDEN AVE ZANESVILLE OH 43701 0 

ALLIED TUBE & CONDUIT CORP 16100 S LATHROP AVE HARVEY IL 60426 4.3175 

BROWN PRINTING CO 2300 BROWN AVE WASECA MN 56093 6.6725 

CROWN EQUIPMENT CORP 2600 E STATE RD 240 GREENCASTLE IN 46135 1.351405 5

SYCAMORE SYSTEMS LLC 449 N CALIFORNIA ST SYCAMORE IL 60178 0 

TEKNOR APEX TENNESSEE CO (AKA HAYWOOD CO) 751 DUPREE ST BROWNSVILLE TN 38012 0 

Page 8 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

SILGAN CAN CO 500 NW LOOP 286 SUITE 10PARIS TX 75460 3.412 

RR DONNELLEY CRAWFORDSVILLE 1009 SLOAN ST CRAWFORDSVILLE IN 47933 6.3135 

HUSQVARNA CONSUMER OUTDOOR PRODUCTS 172 OLD ELLOREE RD ORANGEBURG SC 29116 0.1325 

CAN CORP OF AMERICA INC 326 JUNE AVE BLANDON PA 19510 1.6585 

LA-Z-BOY TENNESSEE 500 WALNUT GROVE RD DAYTON TN 37321 0 6.58

SNAP-ON TOOLS MANUFACTURING CO 2600 US HWY 18 E ALGONA IA 50511 0.0015 

GEA BPO LLC 301 N CURRY PIKE BLOOMINGTON IN 47404 0 

SILGAN CONTAINERS MANUFACTURING CORP 520 W 2ND ST OCONOMOWOC WI 53066 1.3 

DUPONT CHAMBERS WORKS RT 130 DEEPWATER NJ 08023 0.092 

SCHAEFFER MANUFACTURING 102 BARTON ST SAINT LOUIS MO 63104 6.34465 

NUCOR CORP VULCRAFT DIV 7205 GAULT AVE N FORT PAYNE AL 35967 3.6825 

NORTHLAND ALUMINUM PRODUCTS I NC 5005 COUNTY RD 25 MINNEAPOLIS MN 55416 0 

AMERICAN FINISHING RESOURCES INC 476 CLAY ST CHILTON WI 53014 6.272 

BROWN PRINTING CO 11595 MCCONNELL RD WOODSTOCK IL 60098 6.125 

MAYTAG CORP CLEVELAND COOKING PRODUCTS PLANT 1

740 KING EDWARD AVE SE CLEVELAND TN 37311 0 

AKZO NOBEL SURFACE CHEMISTRY LLC 15200 ALMEDA RD HOUSTON TX 77053 0.045 

DU PONT ELECTRONICS MICROCIRCU ITS INDUSTRIES LTD (PART)

HWY 686 KM 2.3 MANATI PR 00674 0 

CURTIS METAL FINISHING CO 6645 SIMS DR STERLING HEIGHTSMI 48313 4.411 

HUNTER DOUGLAS TUPELO CENTER RT. 2 LEE INDUSTRIAL PARSHANNON MS 38868 0.2925 

3M CO - CORDOVA 22614 RT 84 N CORDOVA IL 61242 0.434 

FORD MOTOR CO MICHIGAN ASSEMBLY PLANT 38303 MICHIGAN AVE WAYNE MI 48184 0.065 

WHEELING MACHINE PRODUCTS DIV PINE BLUFF 5411 INDUSTRIAL DR S PINE BLUFF AR 71602 6 

ASHLEY INDUSTRIAL MOLDING INC 310 S WABASH ASHLEY IN 46705 0.6 

ENKEI AMERICA INC 2900 W INWOOD DR COLUMBUS IN 47201 0 

WIX FILTRATION CORP - ALLEN PLANT 2900 NW BLVD GASTONIA NC 28052 0.0025 

SILGAN CONTAINERS MANUFACTURING CORP 2501 165TH ST HAMMOND IN 46320 0 

THE COLEMAN CO INC 3600 N HYDRAULIC WICHITA KS 67219 0.001 

NAHAN PRINTING INC 7000 SAUKVIEW DR SAINT CLOUD MN 56303 5.67614 0

QG PRINTING II CORP 4708 KRUEGER DR JONESBORO AR 72401 3.55 

Page 9 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

PPG INDUSTRIES,INC-SPRINGDALE COMPLEX 125 COLFAX ST SPRINGDALE PA 15144 5.754 

GMVM-LANSING GRAND RIVER ASSEMBLY 920 TOWNSEND ST MAIL C

OLANSING MI 48921 2.6 

CROWN AEROSOL PACKAGING 3737 E EXCHANGE AVE AURORA IL 60504 5.0525 

AVERY DENNISON RBIS LENOIR 950 GERMAN ST LENOIR NC 28645 4.668 

TACO INC - CRANSTON 1160 CRANSTON ST CRANSTON RI 02920 0.058 

PELLA CORP CARROLL OPERATIONS 1750 E US HWY 30 E CARROLL IA 51401 0 

GREIF PACKAGING LLC 10850 STRANG RD LA PORTE TX 77571 4.47095 

JOHN DEERE HORICON WORKS-DT 300 N VINE ST HORICON WI 53032 0 

CARRY-ON TRAILER CORP 1965 HWY 30 MISSOURI VALLEY IA 51555 0 

L A DARLING CO - PIGGOTT AR FACILITY HWY 49 S PIGGOTT AR 72454 0.073 

TORO CO 200 SIME AVE TOMAH WI 54660 0 SENECA FOODS CORP CAN PLANT 3709 MILL ST MARION NY 14505 0 

COLOR COMMUNICATIONS INC 4242 W FILLMORE CHICAGO IL 60624 1.05 

MIDDLEBURY HARDWOOD PRODUCTS 101 JOAN DR MIDDLEBURY IN 46540 0 

SABIC INNOVATIVE PLASTICS MT VERNON LLC 1 LEXAN LN MOUNT VERNON IN 47620 3.2 

QUAD/GRAPHICS INC N11896 HWY 175 PO BOX 2 LOMIRA WI 53048 4.836 

BATESVILLE MANUFACTURING INC -DOLL PLANT 1000 E PEARL ST BATESVILLE IN 47006 0.2675 

BERENFIELD CONTAINERS SE LTD 12180 UNIVERSITY CITY BL HARRISBURG NC 28075 0 

GATES CORP 1450 MONTANA RD IOLA KS 66749 0 KOHLER CO 2000 N 5TH ST UNION CITY TN 38261 0.5345 

DUNBARTON CORP REDIFRAME DIV 1101 TECHNOLOGY DR DOTHAN AL 36303 0 

WORTHINGTON CYLINDERS WISCONSI N LLC 300 E BREED ST CHILTON WI 53014 0.2495 5

PRECOAT METALS 25 NORTHGATE INDUSTRIAGRANITE CITY IL 62040 4.232 

POWER PARTNERS INC 200 NEWTON BRIDGE RD ATHENS GA 30607 0 

EQUISTAR CHEMICALS BAYPORT CHEMICALS PLANT 5761 UNDERWOOD RD PASADENA TX 77507 5.0705 

CROWN FOOD PACKAGING 1650 BROADWAY HANOVER PA 17331 1.3065 

PRECOAT METALS 2604 RIVER RD HAWESVILLE KY 42348 0.007 

US DOD USAF TINKER AFB 72 CEG/CEA 7535 FIFTH ST TINKER AFB OK 73145 1.9 

COORSTEK 2449 RIVERSIDE PKWY GRAND JUNCTION CO 81505 0.0025 

VON HOFFMANN GRAPHICS INC 1005 COMMERCIAL DR OWENSVILLE MO 65066 3.703 

Page 10 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

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(t

SILGAN CAN CO 6200 FRANKLIN BLVD SUITESACRAMENTO CA 95824 4.432 

CARRY-ON TRAILER CORP 5300 WESTMORELAND RD WINNEMUCCA NV 89445 0 

HESS PRINT SOLUTIONS 3765 SUNNYBROOK RD BRIMFIELD OH 44240 5 

VALMONT INDUSTRIES INC 7002 N 288TH ST VALLEY NE 68064 5 

VAUGHAN-BASSETT FURNITURE CO GALAX 300 E GRAYSON ST GALAX VA 24333 0.74943095 4.2

SILGAN CONTAINERS MANUFACTURING CORP 135 NATIONAL RD EDISON NJ 08817 4.02 

KIA MOTORS MANUFACTURING OF GEORGIA 7777 KIA PKWY WEST POINT GA 31833 0.0525 LOGAN ALUMINUM INC US HWY 431 N RUSSELLVILLE KY 42276 0.035 

SEQUA COATINGS CORP-PRECOAT M ETALS DIV US HWY 12 AT RT 249 PORTAGE IN 46368 0.572 

ARVINMERITOR HEAVY VEHICLE SYSTEMS LLC 801 RAILROAD AVE YORK SC 29745 0.001 

AUTOALLIANCE INTERNATIONAL INC 1 INTERNATIONAL DR FLAT ROCK MI 48134 0.2 

OWENS CORNING VETROTEX LLC - ANDERSON SC 4837 HWY 81 S STARR SC 29684 0.479 

TEREX WASHINGTON SOUTH CAMPUS 18700 NE 65TH ST REDMOND WA 98052 0.1114 

ARMSTRONG HARDWOOD FLOORING CO 565 HARTCO DR ONEIDA TN 37841 0 

RR DONNELLEY-WETMORE PLANT 1645 W SAM HOUSTON PK

WHOUSTON TX 77043 4.6345 

PRECOAT METALS 16402 JACINTOPORT BLVD HOUSTON TX 77015 4.407 

CARDONE INDUSTRIES 5660 RISING SUN AVE PHILADELPHIA PA 19120 0.8115 

METAL COATERS 951 PRISOCK RD JACKSON MS 39272 0 

SILGAN CONTAINERS MANUFACTURING CORP 1400 PLOVER RD PLOVER WI 54467 1.31 

FIBERMARK NORTH AMERICA INC 5492 BOSTWICK ST LOWVILLE NY 13367 0.091 

BERENFIELD CONTAINERS INC 31 RAILROAD ST CLARENDON PA 16313 0.132025 

RR DONNELLEY BARABOO DIV 1300 SAUK AVE BARABOO WI 53913 4.1785 

ENDICOTT INTERCONNECT TECHNOLOGIES INC 1093 CLARK ST ENDICOTT NY 13760 0.25 

INX DIGITAL INK CO 405 INDUSTRIAL WAY DIXON CA 95620 4.3915 

TCI COATINGS INC 4501 BRADLEY ST LUBBOCK TX 79415 4.36875 

CHRYSLER STERLING HEIGHTS ASSEMBLY PLANT (PART)

38111 VAN DYKE STERLING HEIGHTSMI 48312 0.49 

SILGAN CONTAINERS MANUFACTURING CORP N90 W14600 COMMERCE D MENOMONEE FALLSWI 53051 0 

MASTERBRAND CABINETS INC 1002 EISENHOWER DR N GOSHEN IN 46526 0.0035 

QG LLC WINCHESTER VIRGINIA 160 CENTURY LN STONEWAWINCHESTER VA 22603 3.8727 0

ARDAGH METAL PACKAGING USA INC 936 BARRACUDA ST TERMINAL ISLAND CA 90731 3.8 

Page 11 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

Fug

Emis

(t

R R DONNELLEY & SONS CO DANVILLE DIV 3201 LEBANON RD DANVILLE KY 40422 3.8985 

ROHM & HAAS CHEMICALS LLC 200 RT 413 BRISTOL PA 19007 0.0519 

INLAND LABEL & MARKETING 2009 W AVE S LA CROSSE WI 54601 2.2045 

SC JOHNSON & SON INC WAXDALE FACILITY 8311 16TH ST STURTEVANT WI 53177 0.125 

HYUNDAI MOTOR MANUFACTURING ALABAMA LLC 700 HYUNDAI BLVD MONTGOMERY AL 36105 2.6025 

US ARMY LAKE CITY ARMY AMMUNITION PLANT INTERSECTION OF MO HWYINDEPENDENCE MO 64051 1.579 

CROWN AEROSOL PACKAGING 4TH ST & PARK AVE FARIBAULT MN 55021 2.6265 

CLEVELAND STEEL CONTAINER CORP 350 MILL ST QUAKERTOWN PA 18951 0.035 

RRD MAPLE GROVE 7401 KILMER LN MAPLE GROVE MN 55369 3.9335 

SILGAN CONTAINERS MANUFACTURING CORP 8673 LYONS-MARENGO RD LYONS NY 14489 0.7275 

THIRD COAST TERMINALS PEARLAND 1871 MYKAWA PEARLAND TX 77581 0 

PRO LINE PRINTING ARLINGTON 401 N GREAT SW PKWY ARLINGTON TX 76011 3.088685 

TTM PRINTED CIRCUIT GROUP - S TAFFORD DIV 4 OLD MONSON RD STAFFORD CT 06075 0 

CARRY-ON TRAILER CORP 159 INDUSTRIAL PARK RD MONTROSS VA 22520 0 

QUAD/GRAPHICS INC 56 DUPLAINVILLE RD SARATOGA SPRINGNY 12866 3.68 

NAVISTAR INC 6125 URBANA RD SPRINGFIELD OH 45502 0.415 

AFTON CHEMICAL CORP 725 CANNON BRIDGE RD ORANGEBURG SC 29115 2.813 BATESVILLE MANUFACTURING INC 310 CROWN RD BATESVILLE MS 38606 0.5695 

BENCHMARK ENERGY PRODUCTS LLC 4113 W INDUSTRIAL AVE MIDLAND TX 79703 0.344 

OMG AMERICAS TWO MILE RUN RD FRANKLIN PA 16323 0.025 

BETCO CORP 1001 BROWN AVE TOLEDO OH 43607 3.69 NAZDAR SHAWNEE 8501 HEDGE LN TERRACE SHAWNEE KS 66227 1.0955 

VIASYSTEMS CORP 1521 POPLAR LN FOREST GROVE OR 97116 0.0675 

TITAN COATINGS INC 2025 EXCHANGE PL BESSEMER AL 35023 3.59 

AUTOMOTIVE COMPONENTS HOLDINGS LLC SALINE PLANT

7700 MICHIGAN AVE SALINE MI 48176 0.06 

BALL METAL FOOD CONTAINER CORP 300 W GREGER RD OAKDALE CA 95361 0.152 

QUAD/GRAPHICS INC 555 S 108TH ST WEST ALLIS WI 53214 3.41 

MOTOR CASTINGS CO 1323 S 65TH MILWAUKEE WI 53214 0 GM MLCG FAIRFAX ASSEMBLY 3201 FAIRFAX TRAFFICWAYKANSAS CITY KS 66115 0.1 

FORD MOTOR CO - OHIO ASSEMBLY PLANT 650 MILLER RD AVON LAKE OH 44012 0.395 

Page 12 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

BROWN PRINTING CO 668 GRAVEL PIKE EAST GREENVILLE PA 18041 3.2665 

RHODIA INC 2ND ST & BLUEBALL AVE MARCUS HOOK PA 19061 0.1915 

SPRAYLAT CORP CA 3465 S LA CIENAGA BLVD LOS ANGELES CA 90016 1.679 PRECOAT METALS 4301 S SPRING AVE SAINT LOUIS MO 63116 0.926 LAKESIDE LITHOGRAPHY LLC 1600 S LAFLIN ST CHICAGO IL 60608 2.65 

AVERY DENNISON 17700 FOLTZ INDUSTRIAL PSTRONGSVILLE OH 44149 0.422 

HEWLETT-PACKARD CARIBE BV SITE HWY 110 N KM 5.1 AGUADILLA PR 00605 0 

QUAD GRAPHICS TAUNTON RETAIL 50 JOHN HANCOCK RD TAUNTON MA 02780 1.91685 

RR DONNELLEY STRASBURG DIV ONE SHENANDOAH VALLEYSTRASBURG VA 22657 3.1 

BRILLION IRON WORKS INC 200 PARK AVE BRILLION WI 54110 2.13095 CADON PLATING CO 3715 11TH ST WYANDOTTE MI 48192 1.708 

ABC COMPOUNDING CO INC 6970 JONESBORO RD MORROW GA 30260 0.0025 CLEAR LAKE CHEMICALS LLC 11200 BAY AREA BLVD PASADENA TX 77507 3.0356 CENTURY INDUSTRIAL COATINGS I NC HWY 69 S JACKSONVILLE TX 75766 0.085 

CLEVELAND STEEL CONTAINER - NI LES 115 ERIE ST NILES OH 44446 0.0025 

MEADWESTVACO CONSUMER PACKAGING GROUP 

LLC

7411 OAKWOOD ST MEBANE NC 27302 2.9255 

UNIVAR USA INC - BUNOLA BRANCH 328 BUNOLA RIVER RD BUNOLA PA 15020 0.125 

ARR-MAZ CUSTOM CHEMICALS 4800 STATE RD 60 E MULBERRY FL 33860 0.1415 

IVC INDUSTRIAL COATINGS INC 1825 E NATIONAL AVE BRAZIL IN 47834 0.577852 2

ROPPE CORP 1602 N UNION ST FOSTORIA OH 44830 0.125 

VAN CAN CO 10837 ETIWANDA AVE FONTANA CA 92337 2.45 

VANEX INC 1700 S SHAWNEE ST MOUNT VERNON IL 62864 0 

CROWN FOOD PACKAGING 10200 N LOMBARD ST PORTLAND OR 97203 1.2615 

CENTRIA 530 N SECOND ST CAMBRIDGE OH 43725 1.411 

RED SPOT WESTLAND INC 550 S EDWIN ST WESTLAND MI 48186 1.226 

CLEVELAND STEEL CONTAINER CORP - STREETSBORO PLANT

10048 AURORA-HUDSON R STREETSBORO OH 44241 0.0025 

ALERIS ROLLED PRODUCTS INC 1372 KY HWY 1957 LEWISPORT KY 42351 0.125 

IVC SOUTH 875 PROGRESS CENTER AVLAWRENCEVILLE GA 30043 0.538 

MAGNA MIRRORS CORP - NEWAYGO 700 S PARK DR NEWAYGO MI 49337 1.4755 

ASTRO COATINGS INC 27 MAIN ST STRUTHERS OH 44471 0.5225 

Page 13 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

IC OF OKLAHOMA LLC 2322 N MINGO RD TULSA OK 74116 0 

AKZONOBEL 1872 HWY 9 BYPASS W LANCASTER SC 29720 0.4955 

HIRSH INDUSTRIES INC 1525 MCKEE RD DOVER DE 19904 0.0025 

PRECOAT METALS 4502 FREEDOM WAY WEIRTON WV 26062 0 RADIATOR SPECIALTY CO 600 RADIATOR RD INDIAN TRAIL NC 28079 0.146 

PRECOAT METALS 3399 DAVEY ALLISON BLVDHUEYTOWN AL 35023 2.041 

ROBROY INDUSTRIES TEXAS LP 1100 US HWY 271 S GILMER TX 75644 0 NORTHERN LABS INC WEST DRIVE 5800 W DR MANITOWOC WI 54220 1.0045 

GMTG - SHREVEPORT ASSEMBLY 7600 GENERAL MOTORS BLSHREVEPORT LA 71129 0.125 

INTERNATIONAL PAPER PINE HILL MILL 7600 HWY 10 W PINE HILL AL 36769 0.058 

QG LLC 420 W INDUSTRIAL AVE EFFINGHAM IL 62401 2.19 

RR DONNELLEY LOS ANGELES MANUFACTURING 19681 PACIFIC GATEWAY DTORRANCE CA 90502 2.3775 

VERTIS COMMUNICATIONS 4051 FONDORF DR COLUMBUS OH 43228 2.1765 

CCL CONTAINER AEROSOL DIV ONE LLODIO DR HERMITAGE PA 16148 0.19 

SAPA EXTRUSIONS INC 2500 ALUMAX RD YANKTON SD 57078 0 2.4

CUMMINS POWER GENERATION 1400 73RD AVE NE FRIDLEY MN 55432 0.12 

QUAD/GRAPHICS INC 100 DUPLAINVILLE RD THE ROCK GA 30285 2.285 

SCHNEIDER ELECTRIC 1990 SANDIFER BLVD SENECA SC 29678 0 

APOLLO COLORS INC 1550 MOUND RD ROCKDALE IL 60436 0 

SAPA EXTRUDER INC 2905 OLD OAKWOOD RD GAINESVILLE GA 30504 0 

PPG INDUSTRIES ARCHITECTURAL FINISHES 1020 OLYMPIC DR BATAVIA IL 60510 0 

ST CHARLES OPERATIONS (TAFT/STAR) UNION CARBIDE CORP

355 LA HWY 3142 (GATE 1) TAFT LA 70057 0.6 

HANNA STEEL CORP 3812 COMMERCE AVE FAIRFIELD AL 35064 0.9095 

THE DOW CHEMICAL CO 1790 BUILDING MIDLAND MI 48667 2.2 

DUPONT TOWANDA PLANT 192 PATTERSON BLVD TOWANDA PA 18848 0.252 

HONDA MANUFACTURING OF INDIANA LLC 2755 N MICHIGAN AVE GREENSBURG IN 47240 1.785 COLOR CORP OF AMERICA 1630 W HILL ST LOUISVILLE KY 40210 0.009 

BRENNTAG SOUTHWEST INC LANC ASTER 704 E WINTERGREEN RD LANCASTER TX 75134 0.0225 

KAY AUTOMOTIVE GRAPHICS 57 KAY INDUSTRIAL DR LAKE ORION MI 48359 0 MAGNABLEND INC- LIQUID PLANT 100 W STERRETT RD WAXAHACHIE TX 75165 0.125 

Page 14 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

VERTIS 7619 DOANE DR MANASSAS VA 20109 2.1285 

NCP COATINGS INC 225 FORT ST NILES MI 49120 2.1685 

AMERICAN COLOR GRAPHICS 810 E S ST MARENGO IA 52301 2.02 

DERRICK CORP 3350 UNION RD CHEEKTOWAGA NY 14225 0 

BALL METAL FOOD CONTAINER CORP 1200 S CRUTCHER ST SPRINGDALE AR 72764 0.23 

RR DONNELLEY & SONS CO 6821 E COUNTY RD 1100 N MATTOON IL 61938 1.9725 

KEYMARK CORP 1188 CAYADUTTA ST RT 33 FONDA NY 12068 0 

RR DONNELLEY 100 QUALITY CT CHARLESTOWN IN 47111 1.955 

BON L MANUFACTURING CO HWY 53 BONNELL RD CARTHAGE TN 37030 0.644 

BWAY CORP 1202 AIRPORT RD NORTH BRUNSWICKNJ 08902 0.8015 

NEXTEER AUTOMOTIVE CORP 3900 HOLLAND RD SAGINAW MI 48601 0.2085 

VERTIS COMMUNICATIONS 10911 GRANITE ST CHARLOTTE NC 28273 1.8595 

GM ORION ASSEMBLY CENTER 4555 GIDDINGS RD LAKE ORION MI 48359 0.9 SILGAN CONTAINERS MANUFACTURING CORP 2200 WILBUR AVE ANTIOCH CA 94509 0 CONSOLIDATED SYSTEMS INC 650 ROSEWOOD DR COLUMBIA SC 29201 0 

QG LLC (WAS WORLDCOLOR STILLWATER) 100 W AIRPORT RD STILLWATER OK 74075 1.8275 DURA COAT PRODUCTS INC 26655 PEOPLES RD MADISON AL 35756 1.75171 

ITW DYMON 805 E OLD 56 HWY OLATHE KS 66061 0.6005 

CANFIELD METAL COATING CORP 460 W MAIN ST CANFIELD OH 44406 0 

VERTIS COMMUNICATIONS 4646 S GRADY AVE TAMPA FL 33611 1.818 

ACCESS BUSINESS GROUP LLC 7575 FULTON ST E ADA MI 49355 1.8935 

VEYANCE TECHNOLOGIES INC 2701 W OMAHA AVE NORFOLK NE 68701 0.037085 

CATERPILLAR INC 3701 STATE RD 26 E LAFAYETTE IN 47905 0.1205 

VANGUARD PAINTS & FINISHES INC 1409 GREENE ST MARIETTA OH 45750 1.965 

SENOX CORP 227 S TOWN E BLVD MESQUITE TX 75149 0.9865 

RR DONNELLEY / PINEVILLE 10519 INDUSTRIAL DR PINEVILLE NC 28134 1.8475 

CAMACO COLUMBUS MANUFACTURING 1851 E 32ND AVE COLUMBUS NE 68601 0 

OHIO ART CO ONE TOY ST BRYAN OH 43506 1.1855 

STEEL DYNAMICS INC 5134 LOOP RD JEFFERSONVILLE IN 47130 0 

DUPONT YERKES PLANT 3115 RIVER RD BUFFALO NY 14207 0.5085 

Page 15 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

BALL AEROSOL & SPECIALTY CONTAINER INC 1717 GIFFORD RD ELGIN IL 60120 0.438 

CARESTREAM HEALTH COLORADO 2000 HOWARD SMITH AVE 

WWINDSOR CO 80550 0.0015 

RR DONNELLEY / VON HOFFMANN CORP 321 WILSON DR JEFFERSON CITY MO 65109 1.78179 

SILGAN WHITE CAP CORP 350 JAYCEE DR VALMONT HAZLETON PA 18201 0.779 ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

901 N GREENWOOD AVE KANKAKEE IL 60901 0.7475 

STP PRODUCTS MANUFACTURING CO 477 LEXINGTON AVE PAINESVILLE OH 44077 1.0615 

REICHHOLD INC 425 S PACE BLVD PENSACOLA FL 32502 0.1375 

AMERICAN COLOR GRAPHICS - LUFKIN 3001 ATKINSON DR LUFKIN TX 75901 1.6675 

GFX INTERNATIONAL 333 BARRON BLVD GRAYSLAKE IL 60030 0 

BUCKEYE INTERNATIONAL INC 2700 WAGNER PL MARYLAND HEIGHT MO 63043 0.125 

WISMARQ CORP 11440 W ADDISON AVE FRANKLIN PARK IL 60131 0 

DIVERSEY INC 316 HART ST WATERTOWN WI 53094 0.00009 SAPA INC - COATINGS DIVSION 5325 NE SKYPORT WAY PORTLAND OR 97218 1.46070735 0SONOCO PRODUCTS CO - PRESIDENTS ISLAND 2755 HARBOR AVE MEMPHIS TN 38113 0 

EFCO CORP 1000 COUNTY RD MONETT MO 65708 1.11 

HUNTSMAN PETROCHEMICAL LLC 3892 US HWY 90 DAYTON TX 77535 0 FUJIFILM NORTH AMERICA CORP 20 W 14TH AVE NORTH KANSAS CITMO 64116 0 

TEXAS FINISHING CO 1801 SURVEYOR BLVD CARROLLTON TX 75006 0 

GATES CORP 1650 ROWE PKWY POPLAR BLUFF MO 63901 0 

BWAY CORP BWAY PACKAGING DIV 8200 BROADWELL RD CINCINNATI OH 45244 0.88529 

3M CO - HUTCHINSON 905/915 ADAMS ST SE HUTCHINSON MN 55350 0 

NESTLE PURINA PETCARE 1000 HAMILTON RD WEIRTON WV 26062 0.3935 

RR DONNELLEY & SONS CO 60 SECURITY DR AVON CT 06001 1.54 

GATES CORP - CHARLESTON 1300 S PLANT RD CHARLESTON MO 63834 0 

LION COPOLYMER LLC 5955 SCENIC HWY BATON ROUGE LA 70805 0 

FUJIFILM MANUFACTURING USA INC 211 PUCKETTS FERRY RD GREENWOOD SC 29649 0 

CRYSTAL FINISHING SYSTEMS INC 2608 ROSS AVE SCHOFIELD WI 54476 0 1.5

INDEPENDENT CAN CO 1300 BRASS MILL RD BELCAMP MD 21017 0 

MISSION KLEENSWEEP PRODUCTS INC 2434 BIRKDALE ST LOS ANGELES CA 90031 1.5 

BAYOU COS INC 5200 CURTIS LN NEW IBERIA LA 70560 1.5 

Page 16 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

Fug

Emis

(t

EASTMAN CHEMICAL CO TENNESSEE OPERATIONS 100 EASTMAN RD KINGSPORT TN 37662 0.8315 

DENSO MANUFACTURING TENNESSEE INC 1720, 1725, 1755 ROBERT CMARYVILLE TN 37801 0 

TAIYO AMERICA INC 2675 ANTLER DR CARSON CITY NV 89701 0.005 

BRIGHTSMITH LLC 120 ENTERPRISE AVE MORRISVILLE PA 19067 0.317 

CHROMASOURCE INC 2433 S CR 600 E COLUMBIA CITY IN 46725 0 

RANBAR ELECTRICAL MATERIALS INC 408 MANOR-HARRISON CITHARRISON CITY PA 15636 0 

DECOSTAR INDUSTRIES INC 1 DECOMA DR CARROLLTON GA 30117 0.125 

SONY CHEMICALS COPORATION OF AMERICA 215 SATELLITE BLVD NE SUSUWANEE GA 30024 0 

J L CLARK INC 923 23RD AVE ROCKFORD IL 61104 0.216 

AKZO NOBEL COATINGS INC 1313 WINDSOR AVE COLUMBUS OH 43211 0.9105 

INCHEM CORP 800 CEL-RIVER RD ROCK HILL SC 29730 0.025 ARMSTRONG WORLD INDUSTRIES INC 4115 N PERKINS RD STILLWATER OK 74075 0.566 

HENTZEN COATINGS,INC BATAVIA FACILITY 1500 LATHEM ST BATAVIA IL 60510 1.2675 

CARDINAL ALUMINUM CO PLAN T 3 4005 OAKLAWN DR LOUISVILLE KY 40219 0.0485 

FIVE STAR COATINGS GROUP 36616 89TH ST TWIN LAKES WI 53181 0 

RG STEEL WHEELING LLC BEECH BOTTOM PLANT 2481 RIVER RD WELLSBURG WV 26070 0 

TRINKOTE INDUSTRIAL FINISHES INC 1800 PARK PL AVE FORT WORTH TX 76110 0 ARANDELL CORP N82 W13118 LEON RD MENOMONEE FALLSWI 53051 1.324 

CATALYST OILFIELD SERVICES LLC 11999 E HWY 158 GARDENDALE TX 79758 1.35 

DUBOIS CHEMICALS INC 3630 E KEMPER RD SHARONVILLE OH 45241 0 

SHEBOYGAN PAINT CO 608 CANAL ST CEDARTOWN GA 30125 0.692 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

372 CLEVELAND ST ROCHESTER PA 15074 0.517 

KELLEY TECHNICAL COATINGS INC 1401 S 15TH ST LOUISVILLE KY 40210 1.3 

W W HENRY 150 MOONEY DR BOURBONNAIS IL 60914 1.299 

ICL-IP AMERICA INC 11636 HUNTINGTON GALLIPOLIS FERRY WV 25515 0.017145 GMC TRUCK GROUP ARLINGTON ASSEMBLY PLANT 2525 E ABRAMS ST ARLINGTON TX 76010 0.37 

BRUNSWICK CORP MERCURY MARINE DIV W6250 PIONEER RD FOND DU LAC WI 54935 0.127 

KMCO CROSBY PLANT 16503 RAMSEY RD CROSBY TX 77532 0.125 

WINSLOW-BROWNING INC 215 BROWNSVILLE AVE LIBERTY IN 47353 1.2345 

WARREN UNILUBE INC 1200 S 8TH ST WEST MEMPHIS AR 72301 1.2195 

Page 17 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

VEOLIA ES TECHNICAL SOLUTIONS LLC PORT ARTHUR FACILITY

HWY 73, 3.5 MILES W OF TAPORT ARTHUR TX 77640 0.01137 0

SUN CHEMICAL CORP 2445 PRODUCTION DR SAINT CHARLES IL 60174 0.1815 

NICHOLS ALUMINUM ALABAMA INC 2001 HWY 20 W DECATUR AL 35601 0.9685 

RYCOLINE PRODUCTS LLC 5540 NW HWY CHICAGO IL 60630 0.179 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

701 SHILOH RD GARLAND TX 75042 0.701 

MOMENTIVE SPECIALTY CHEMICALS INC 8600 W 71ST ST BEDFORD PARK IL 60501 0.202 

LOCKHEED MARTIN AERONAUTICS CO 1011 LOCKHEED WAY MZ 0 PALMDALE CA 93599 0.0475 

GENTEK BUILDING PRODUCTS 11 CRAGWOOD RD AVENEL NJ 07001 0.1105 

CANBERRA CORP 3610 N HOLLAND-SYLVANIATOLEDO OH 43615 0.75 

HILLYARD INDUSTRIES INC 402 N 3TH ST SAINT JOSEPH MO 64501 0.41 

WISMARQ VALENCIA LLC 125 MCFANN RD VALENCIA PA 16059 1.0195 

CROWN CORK & SEAL CO (USA) INC CROWN CLOSURES DIV

940 MILL PARK DR LANCASTER OH 43130 0 

CELLU TISSUE/CITYFOREST LLC 1215 WORDEN AVE E LADYSMITH WI 54848 0 

GENERAL MOTORS GM VA DETROIT-HAMTRAMCK ASSEMBLY CENTER

2500 E GENERAL MOTORS DETROIT MI 48211 0.85 

POLYMERIC IMAGING INC 117 E 14TH AVE NORTH KANSAS CITMO 64116 0 

JOHN DEERE SEEDING & CYLINDER 501 RIVER DR MOLINE IL 61265 0 TESORO REFINING & MARKETING CO - MANDAN REFINERY

900 OLD RED TRAIL NE MANDAN ND 58554 1.05 

RED SPOT PAINT & VARNISH CO INC 1016 E COLUMBIA ST EVANSVILLE IN 47711 0.621 

PPG INDUSTRIES OHIO INC (CL) 3800 W 143 ST CLEVELAND OH 44111 0.3955 

PPG ARCHITECTURAL FINISHES EAST POINT 1377 OAKLEIGH DR EAST POINT GA 30344 0.0025 MITSUBISHI MOTORS NORTH AMERICA INC 100 N MITSUBISHI MOTOR

WNORMAL IL 61761 1.0115 

CP CONVERTERS INC 15 GRUMBACHER RD YORK PA 17402 1.01857 

TTM TECHNOLOGIES-SANTA CLARA 407 MATHEW ST SANTA CLARA CA 95050 0 

POLARTEC LLC 46 STAFFORD ST LAWRENCE MA 01841 0.998 

AKZONOBEL AEROSPACE COATINGS 1 E WATER ST WAUKEGAN IL 60085 0.491 

SUN CHEMICAL CORP 1380 FORD RD MAUMEE OH 43537 0.145 

UNITED PAINT & CHEMICAL 24671 TELEGRAPH RD SOUTHFIELD MI 48034 0.9615 

INTEL CORP - RONLER ACRES CAMPUS 2501 NW 229TH ST HILLSBORO OR 97124 0.0025 

SPIRALKOTE FLEXIBLE PACKAGING 1200 CENTRAL FLORIDA PKORLANDO FL 32837 0 

Page 18 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

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Emis

(t

HUNT REFINING CO A CORP 1855 FAIRLAWN RD TUSCALOOSA AL 35401 0.932 PARKER HANNIFIN 400 S ST MC COOK NE 69001 0 COMPLEMENTARY COATINGS CORP 4701 O'DONNELL ST BALTIMORE MD 21224 0.9215 

3M CO - BROWNWOOD 4501 HWY 377 S BROWNWOOD TX 76801 0.06 

FINISHES UNLIMITED INC 482 WHEELER RD SUGAR GROVE IL 60554 0.4455 

WESTERN METAL DECORATING CO 8875 INDUSTRIAL AVE RANCHO CUCAMONCA 91730 0.5 

PRECOAT METALS 5888 E COUNTY RD 180 BLYTHEVILLE AR 72315 0 

LEVLAD 9200 MASON AVE CHATSWORTH CA 91311 0.00017 

PARISER INDUSTRIES INC 91 MICHIGAN AVE PATERSON NJ 07503 0.845 

CURTIS METAL FINISHING CO 9917 N ALPINE MACHESNEY PARK IL 61115 0.594 

GREIF PACKAGING LLC 2400 COOPER AVE MERCED CA 95348 0.174 

GENERAL MOTORS LLC BOWLING GREEN ASSEMBLY PLANT

600 CORVETTE DR BOWLING GREEN KY 42101 0.165 

CCP COMPOSITES US 2434 HOLMES RD HOUSTON TX 77051 0.8 

ALCOA COMMERCIAL WINDOWS LLC (DBA TRACO) 71 PROGRESS AVE CRANBERRY TOWN PA 16066 0.032 

TTM TECHNOLOGIES INC 234 CASHMAN DR CHIPPEWA FALLS WI 54729 0 

KAWNEER CO INC 7200 DOE AVE VISALIA CA 93291 0.054 

WATSON STANDARD CO (NEVILLE ISLAND PLANT) 2895 GRAND AVE PITTSBURGH PA 15225 0.6695 

CHAMPION TECHNOLOGIES INC 115 PROCTOR ODESSA TX 79762 0.2845 

NICHOLS ALUMINUM DAVENPORT 1725 ROCKINGHAM RD DAVENPORT IA 52802 0.217 

SPECTRUM METAL FINISHING 535 BEV RD YOUNGSTOWN OH 44512 0.4 

UNIVAR USA INC HOUSTON FM 529 11235 FM 529 HOUSTON TX 77041 0.375 

RUST-OLEUM CORP 8105 95TH ST PLEASANT PRAIRIE WI 53158 0.375 

STEELSCAPE 222 W KALAMA RIVER RD KALAMA WA 98625 0.00447 0

ZEP INC 1310 SEABOARD INDUSTRI ATLANTA GA 30318 0.104 

GLASS COATINGS & CONCEPTS 300 LAWTON AVE MONROE OH 45050 0.7245 

BASF CORP 1175 MARTIN ST GREENVILLE OH 45331 0.085 

SYNDICATE SYSTEMS INC 402 N MAIN ST MIDDLEBURY IN 46540 0 

CHRYSLER GROUP LLC STERLING STAMPING PLANT (PART)

35777 VAN DYKE STERLING HEIGHTSMI 48312 0.7 

SPARTAN CHEMICAL CO INC 1110 SPARTAN DR MAUMEE OH 43537 0.0675 WORWAG COATINGS LLC NORTH AMERICA 3420 KOSSUTH ST LAFAYETTE IN 47905 0.5495 

Page 19 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

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Onsite Point 

Source 

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DIAMOND VOGEL PAINTS 5111 E 36TH ST N TULSA OK 74115 0.658 

TERNIUM USA INC 2500 RON BEAN BLVD SHREVEPORT LA 71115 0.0205 

UNIVERSAL CHEMICALS & COATINGS INC 1124 ELMHURST RD ELK GROVE VILLAG IL 60007 0 

VISTA PAINT CORP 2020 E ORANGETHORPE AVFULLERTON CA 92831 0.6185 

SONOCO PRODUCTS CO 1854 CENTRAL FLORIDA PKORLANDO FL 32837 0.4935 

QUESTVAPCO CORP 12255 FM 529 HOUSTON TX 77041 0.65 

DPIX LLC 1635 AEROPLAZA DR COLORADO SPRINGCO 80916 0.4635 

SEYMOUR OF SYCAMORE INC 917 CROSBY AVE SYCAMORE IL 60178 0.585 

COMMERCIAL MERCHANDISING CORP 1337 J WOOD BRANCH DR CHARLOTTE NC 28273 0.32 

B-WAY PACKAGING INC 6 LITHO RD TRENTON NJ 08648 0.063 

PRECOAT METALS 6754 SANTA BARBARA CT ELKRIDGE MD 21075 0 0

SPRAYLAT CORP IL 1701 E 122-ND ST CHICAGO IL 60633 0.0315 

COMPLEX CHEMICALS CO INC MADISON PARISH INDUSTRTALLULAH LA 71282 0.375 

BOEING COMMERCIAL AIRPLANE GROUP - RENTON 737 LOGAN AVE N RENTON WA 98055 0.462 

FORD MOTOR CO CHICAGO ASSEMBLY 12600 S TORRENCE AVE CHICAGO IL 60633 0.49 

FLINT GROUP NORTH AMERICA CORP 2675 HENKLE DR LEBANON OH 45036 0.604 

ROCK TENN CO 2301 S 21ST ST CLINTON IA 52732 0.097 

WESTERN EXTRUSIONS CORP 1735 SANDY LAKE RD CARROLLTON TX 75006 0.125 

SUPERIOR OIL CO INC RECLAIMED ENERGY DIV 1500 WESTERN AVE CONNERSVILLE IN 47331 0.0725 

STEELSCAPE INC 7001 ALLISON-BONNET ME FAIRFIELD AL 35064 0.003895 

WISMARQ CORP 930 ARMOUR RD OCONOMOWOC WI 53066 0 

NEXEO SOLUTIONS LLC 8500 S WILLOW SPRINGS RWILLOW SPRINGS IL 60480 0.541 

CORSICANA TECHNOLOGIES INC 2733 E HWY 31 CORSICANA TX 75109 0.044 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

5400 23RD AVE MOLINE IL 61265 0.207 

DUPONT MOUNT CLEMENS PLANT 400 GROESBECK HWY MOUNT CLEMENS MI 48043 0.0025 

SILGAN CONTAINERS MANUFACTURING CORP 12130 LYNN AVE S SAVAGE MN 55378 0 

TRELLEBORG COATED SYSTEMS US INC / GRACE 

ADVANCED MATERIALS

715 RAILROAD AVE & HWY RUTHERFORDTON NC 28139 0 

CENTRIA 500 PERTH DR NEW ECON

OAMBRIDGE PA 15003 0 

PRIOR COATED METALS 2233 26TH ST SW ALLENTOWN PA 18103 0 

SIMONIZ USA INC 201 BOSTON TURNPIKE BOLTON CT 06043 0.0185 

Page 20 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

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On

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SOUTHERN CLAY PRODUCTS INC 1335 S 13TH ST LOUISVILLE KY 40210 0.0025 

ENGINEERED POLYMER SOLUTIONS I NC D/B/A 

VALSPAR COATINGS

90 CARSON RD BIRMINGHAM AL 35215 0.2075 

SOUTHWEST DISTRIBUTING CO 539 S DREW ST MESA AZ 85210 0.006 

HYDRITE CHEMICAL CO 114 N MAIN ST COTTAGE GROVE WI 53527 0.07 

MARY KAY INC 1330 REGAL ROW DALLAS TX 75247 0.00026 

VEYANCE TECHNOLOGIES INC 400 N GOODYEAR RD MOUNT PLEASANT IA 52641 0.0005 MARCUS PAINT CO 235 E MARKET ST LOUISVILLE KY 40202 0.52 

CLEVELAND STEEL CONTAINER - PE OTONE FACILITY 117 E LINCOLN ST PEOTONE IL 60468 0.0065 

NALCO CO TULSA PLANT 102 6717 S 61ST W AVE TULSA OK 74131 0.000435 REICHHOLD INC 249 ST LOUIS AVE VALLEY PARK MO 63088 0.256615 

BRADLEY COATINGS GROUP 608 W CRAWFORD AVE CONNELLSVILLE PA 15425 0.364595 

NALCO CO 812 RENAUD DR SCOTT LA 70583 0.000325 0.0

MIDWEST METAL COATINGS 9 KONZEN CT GRANITE CITY IL 62040 0.412 

BASF CORP 361 SHEEP PASTURE RD EAST SETAUKET NY 11733 0.008 

KAWNEER CO INC 500 E 12TH ST BLOOMSBURG PA 17815 0.3415 

CLARIANT CORP MARTIN PLANT 788 CHERT QUARRY RD MARTIN SC 29836 0.125 

FERRO CORP 251 W WYLIE AVE WASHINGTON PA 15301 0.125 

CHEMICAL SPECIALISTS & DEVELOPMENT INC 9733 MEADOR RD CONROE TX 77303 0.125 

ARKEMA INC 1415 STEELE AVE SW GRAND RAPIDS MI 49507 0.375 FORMULA CORP 4432 C ST NE AUBURN WA 98002 0.125 

SASOL NORTH AMERICA INC LAKE CHARLES CHEMICAL COMPLEX

2201 OLD SPANISH TRAIL WESTLAKE LA 70669 0.3395 

ALERIS ROLLED PRODUCTS INC 3321 DURHAM RD ROXBORO NC 27573 0.0025 

QG LLC 4581 LOWER VALLEY RD ATGLEN PA 19310 0.457 

WARREN STAMPING PLANT (PART) 22800 MOUND RD WARREN MI 48091 0.46 

SHERWIN-WILLIAMS CO 2802 W MILLER RD GARLAND TX 75041 0.003 

KELLEY TECHNICAL COATINGS INC 1445 S 15TH ST LOUISVILLE KY 40210 0.445 

FORREST PAINT CO 1011 MCKINLEY ST EUGENE OR 97402 0.1785 

ARDAGH METAL PACKAGING USA INC 3030 BIRCH DR HALF MOONWEIRTON WV 26062 0.0695 

RODDA PAINT CO 6123 N MARINE DR PORTLAND OR 97203 0.442 

ENGLERT INC 1200 AMBOY AVE PERTH AMBOY NJ 08861 0.1825 

Page 21 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

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Onsite Point 

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(tpy)

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ARROW SHED LLC 1 THIRD AVE HASKELL NJ 07420 0.0025 SPRAYLAT CORP 716 S COLUMBUS AVE MOUNT VERNON NY 10550 0.0215 SIKA CORP SIKA SARNAFIL DIV 100 DAN RD CANTON MA 02021 0 

WEST PENN OIL CO,INC130130 2305 MARKET ST EXT. WARREN PA 16365 0.4305 

PCCR USA INC 400 E COTTAGE AVE CARPENTERSVILLE IL 60110 0.008 

PACKAGING CORP OF AMERICA COUNCE MILL HWY 57 COUNCE TN 38326 0.025 

DUCKBACK PRODUCTS 2644 HEGAN LN CHICO CA 95928 0.4186 

NB COATINGS INC 2701 E 170TH ST LANSING IL 60438 0.4055 

WEBB CHEMICAL SERVICE CORP 2708 JARMAN MUSKEGON HEIGHTMI 49444 0.2605 

INTEL CORP 4100 SARA RD M/S RR5-491RIO RANCHO NM 87124 0.0025 

NAZDAR CHICAGO 1087 N N BRANCH ST CHICAGO IL 60622 0.1215 

BASF CORP 100 INDUSTRIAL BLVD SEAFORD DE 19973 0.0025 

SEWELL PRODUCTS OF FLORIDA LLC 909 MAGNOLIA AVE AUBURNDALE FL 33823 0.398 

THE DOW CHEMICAL CO - LOUISIANA OPERATIONS 21255 LA HWY 1 S PLAQUEMINE LA 70764 0.396 

PERMA-PIPE OIL & GAS 5008-11 CURTIS LN NEW IBERIA LA 70560 0.395 

AMERICAN METALS CORP 1000 CROCKER RD WESTLAKE OH 44145 0 

DIVERSIFIED COATING SYSTEMS INC 309 ECHELON RD GREENVILLE SC 29605 0.078 

VAN CAN CO 1226 S MANUFACTURERS RTRENTON TN 38382 0.003815 

SPECTRUM CUBIC INC 13 MCCONNELL ST SW GRAND RAPIDS MI 49503 0.0185 

3M CO - NEVADA 2120 E AUSTIN BLVD NEVADA MO 64772 0.195 

INEOS AMERICAS LLC INEOS OXIDE DIV 21255A HWY 1 S PLAQUEMINE LA 70765 0.348 

WISCONSIN ALUMINUM FOUNDRY CO INC 838 S 16TH ST MANITOWOC WI 54220 0 

METAL COATERS 9133 CENTER AVE RANCHO CUCAMONCA 91730 0.03486 

BASF CORP 1609 BIDDLE AVE WYANDOTTE MI 48192 0.0025 EURAMAX INTERNATIONAL INC 450 RICHARDSON DR LANCASTER PA 17603 0.01 

NASCOTE INDUSTRIES 18310 ENTERPRISE AVE NASHVILLE IL 62263 0.132475 

ALERIS ROLLED PRODUCTS INC 1 REYNOLDS RD ASHVILLE OH 43103 0.0355 

ZSCHIMMER & SCHWARZ 70 GA HWY 22 W MILLEDGEVILLE GA 31061 0.0025 

SANFORD LP LIQUID MANUFACTURING & TECHNOLOGY CENTER

831 VOLUNTEER PKWY MANCHESTER TN 37355 0.0025 

Page 22 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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Emis

(t

QUEST SPECIALTY COATINGS LLC - MENOMONEE FALLS

N92 W14701 ANTHONY AVEMENOMONEE FALLSWI 53051 0.375 

PATRIOT PAINT LLC 304 S BLAINE PIKE PORTLAND IN 47371 0.375 

CHEMICAL SOLVENTS JENNINGS ROAD FACILITY 3751 JENNINGS RD CLEVELAND OH 44109 0.125 JASPER RUBBER PRODUCTS INC 1010 FIRST AVE JASPER IN 47546 0 TOWER PRODUCTS INC 2703 FREEMANSBURG AVEEASTON PA 18045 0.375 

HB FULLER CO 7440 W DUPONT RD MORRIS IL 60450 0.3745 

FULLER BRUSH CO ONE FULLER WAY GREAT BEND KS 67530 0.1245 

LINETEC 725 S 75TH AVE WAUSAU WI 54401 0.0205 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

347 CENTRAL AVE BOWLING GREEN KY 42101 0.1285 

NALCO CO PLANT 106 7701 US HWY 90A SUGAR LAND TX 77478 0.0552903 0

PFI INC 9215 SANTA FE SPRINGS RSANTA FE SPRINGSCA 90670 0.369 

NELCO PRODUCTS INC 1107 E KIMBERLY ANAHEIM CA 92801 0.028 

COMBE PRODUCTS INC EL DUQUE INDUSTRIAL PARNAGUABO PR 00718 0 

BEHR PROCESS CORP - CHICAGO 270 STATE ST CHICAGO HEIGHTS IL 60411 0.32265 

DUPONT FORT MADISON PLANT 801 - 35TH ST FORT MADISON IA 52627 0 

UNIVAR USA INC SALEM BRANCH COLONIAL RD SALEM MA 01970 0.001 CELLO PROFESSIONAL PRODUCTS 1354 OLD POST RD HAVRE DE GRACE MD 21078 0.3425 

SHERWIN-WILLIAMS CO 395 BOGGS LN - S RICHMOND KY 40475 0.321 

CHEMGUARD INC 204 S 6TH AVE MANSFIELD TX 76063 0.2265 

EVONIK DEGUSSA CORP TIPPECANOE LABORATORIES 1650 LILLY RD LAFAYETTE IN 47909 0.235 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

411 N DARLING FREMONT MI 49412 0.31 

FUCHS LUBRICANTS CO-CORPORATE OFFICE 17050 S LATHROP AVE HARVEY IL 60426 0.329 

BEHR PROCESS CORP ATLANTA 130 DECLARATION DR MC DONOUGH GA 30253 0.299 

ENERGIZER BATTERY MANUFACTURING INC 75 SWANTON RD SAINT ALBANS VT 05478 0.0025 

CHEMCOAT INC 2790 CANFIELDS LN MONTOURSVILLE PA 17754 0.0025 CNH AMERICA LLC 2701 OAKES RD STURTEVANT WI 53177 0.317 

ACTEGA KELSTAR INC 1050 TAYLORS LN CINNAMINSON NJ 08077 0.0025 

EASTMAN KODAK CO EASTMAN BUSINESS PARK 1669 LAKE AVE ROCHESTER NY 14652 0 

AKZONOBEL COATINGS INC 120 FRANKLIN RD PONTIAC MI 48341 0.0485 

Page 23 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

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Onsite Point 

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On

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(t

SIERRA CORP 11400 W 47TH ST MINNETONKA MN 55343 0.3015 

PPG EUCLID PRETREATMENT & SPECIALTY 

PRODUCTS

23000 ST CLAIR AVE EUCLID OH 44117 0 

HADCO (SANMINA) CORP - OWEGO DIV 1200 TAYLOR RD OWEGO NY 13827 0.0105 

HARCROS CHEMICALS INC 5200 SPEAKER RD KANSAS CITY KS 66106 0.014 METAL COATERS 1150 MARIETTA INDUSTRIAMARIETTA GA 30062 0.004 

LONGABERGER CO 5565 RAIDERS RD FRAZEYSBURG OH 43822 0.164 

HENKEL CORP 23343 SHERWOOD AVE WARREN MI 48091 0.125 SHERWIN-WILLIAMS CO 180 CANAL ST TERRE HAUTE IN 47808 0.018 TMS MANUFACTURING 3555 W 123RD ST ALSIP IL 60803 0.213 

ATMI MATERIALS LTD 706 HOUSTON CLINTON DRBURNET TX 78611 0.050735 0

RUST-OLEUM CORP IN MD 16410 INDUSTRIAL LN WILLIAMSPORT MD 21795 0.108 

STANDARD PAINTS INC 940 S 6TH AVE MANSFIELD TX 76063 0 

VIDEOJET TECHNOLOGIES INC 1855 ESTES AVE ELK GROVE VILLAG IL 60007 0 

COLWELL INC 231 S PROGRESS DR E KENDALLVILLE IN 46755 0.23 

MACDERMID PRINTING SOLUTIONS 260 S PACIFIC ST SAN MARCOS CA 92078 0 

NEXEO SOLUTIONS LLC 395 JAMES AVE SAINT PAUL MN 55102 0.248 

IVC INDUSTRIAL COATINGS INC 550-560 W CENTENNIAL BLVCASA GRANDE AZ 85122 0.052032 0

SUMTER COATINGS INC 2410 HWY 15S SUMTER SC 29150 0.0545 

GATES CORP 630 US HWY 150 E GALESBURG IL 61401 0 

ELPACO COATINGS CORP 1378 KINGSLAND AVE PAGEDALE MO 63133 0.1845 

GOJO INDUSTRIES INC 3783 STATE RD CUYAHOGA FALLS OH 44223 0.0035 0

KIK-SOCAL INC 9028 DICE RD SANTA FE SPRINGSCA 90670 0.255 

NEXEO SOLUTIONS LLC CARTERET 350 ROOSEVELT AVE CARTERET NJ 07008 0.2295 

TEXAS INSTRUMENTS INC 12201 SW FWY MS600 STAFFORD TX 77477 0.0025 

MOC PRODUCTS CO INC 12306 MONTAGUE ST PACOIMA CA 91331 0.125 

WR MEADOWS INC 300 INDUSTRIAL DR HAMPSHIRE IL 60140 0.2525 

BACHMAN SERVICES INC 2220 S PROSPECT OKLAHOMA CITY OK 73129 0.125 

GE WATER & PROCESS TECHNOLOGIES ORANGE FACILITY

3901 WILLIAMS DR ORANGE TX 77630 0.125 

CONTINENTAL CEMENT CO LLC 10107 HWY 79 HANNIBAL MO 63401 0.125 

PPG INDUSTRIES ARCHITECTURAL FINISHES 1886 LYNNBURY WOODS R DOVER DE 19904 0.0025 

Page 24 of 38
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Onsite Point 

Source 

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(tpy)

On

Fug

Emis

(t

WATSON STANDARD CO HARWICK PLANT 616 HITE RD HARWICK PA 15049 0.229 

QUANTUM COATINGS INC 1337 N WOOD BRANCH DR CHARLOTTE NC 28273 0.125 

MISCO PRODUCTS CORP 1048 STINSON DR READING PA 19605 0.125 

MALCO PRODUCTS INC 361 FAIRVIEW AVE BARBERTON OH 44203 0.125 

KEYSTONE ANILINE CORP 2165 HWY 292 INMAN SC 29349 0.125 

EQUILON CARSON TERMINAL 20945 S WILMINGTON AVE CARSON CA 90810 0.125 

PREMIER INK SYSTEMS INC 10420 N STATE ST HARRISON OH 45030 0.125 

DELEET MERCHANDISING 26 BLANCHARD ST NEWARK NJ 07105 0.125 

CERAM TRAZ CORP CERAMIC INDL COATINGS 325 HWY 81 OSSEO MN 55369 0.125 

BECKER SPECIALTY CORP 15310 ARROW BLVD FONTANA CA 92335 0.125 

UNIVAR USA INC STRONGSVILLE BRANCH 21600 DRAKE RD STRONGSVILLE OH 44136 0.125 

ARCADIA INC 3225 E WASHINGTON BLVDVERNON CA 90058 0.125 

UNIVAR USA INC HOUSTON 777 BRISBANE ST HOUSTON TX 77061 0.125 

SILBOND CORP 9901 SAND CREEK HWY WESTON MI 49289 0.125 

YENKIN-MAJESTIC PAINT CORPORAT ION 1920 LEONARD AVE COLUMBUS OH 43219 0.125 

UNIVAR USA INC DALLAS DAN MORTON FACILITY 3636 DAN MORTON DR DALLAS TX 75236 0.125 

UNIVAR USA INC HAMILTON BRANCH 12 STANDEN DR HAMILTON OH 45015 0.125 

POWER SERVICE PRODUCTS INC 513 PEASTER HWY WEATHERFORD TX 76086 0.125 

BERGQUIST CO 301 WASHINGTON ST W CANNON FALLS MN 55009 0.078 

NEXEO SOLUTIONS LLC TWINSBURG HIGHLAND 1610 E HIGHLAND RD TWINSBURG OH 44087 0.2285 

AMREP INC 990 INDUSTRIAL PARK DR MARIETTA GA 30062 0.129 

ARLON INC ADHESIVES & FILMS DIV 2811 S HARBOR BLVD SANTA ANA CA 92704 0.132 

NEXEO SOLUTIONS LLC DORAVILLE 4550 NE EXPRESSWAY DORAVILLE GA 30340 0.159 

GEMINI COATINGS INC 2300 HOLLOWAY DR EL RENO OK 73036 0.219 

ROLLEX CORP 800 CHASE AVE ELK GROVE VILLAG IL 60007 0 

INTEL CORP 4500 S DOBSON RD MAIL S CHANDLER AZ 85248 0.0025 

DAVIS-FROST INC 3420 CANDLER'S MOUNTAI LYNCHBURG VA 24506 0.221 

LAMBERTI USA INC - WHARTON CHEMICAL COMPLEX HWY 59 AT COUNTY RD 212HUNGERFORD TX 77448 0.0495 

HENKEL CORP 923 MAULDIN RD CALHOUN GA 30701 0 

SERIGRAPH INC 3801 E DECORAH RD WEST BEND WI 53095 0.028 

Page 25 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

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Onsite Point 

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RUDD CO INC 1141 NW 50TH ST SEATTLE WA 98107 0.1925 

NOV TUBOSCOPE NAVASOTA 9574 FM 1227 NAVASOTA TX 77868 0.106895 

SONOCO FLEXIBLE PACKAGING 6502 S US HWY 31 EDINBURGH IN 46124 0 

SUN CHEMICAL CORP 3301 HUNTING PARK AVE PHILADELPHIA PA 19132 0.0305 

SILGAN WHITE CAP CORP 1701 WILLIAMSBURG PIKE RICHMOND IN 47375 0.118 JAMESTOWN COATING TECHNOLOGIES 108 MAIN ST JAMESTOWN PA 16134 0.201 

RHODIA INC 577 BANKHEAD HWY WINDER GA 30680 0.16 

CAR PRODUCTS INC 630 BEAULIEU ST HOLYOKE MA 01040 0.196 

WM BARR & CO INC 2170 BUOY ST MEMPHIS TN 38113 0.0025 FIRST AMERICAN RESOURCES CO 2030 RIVERVIEW INDUSTRI MABLETON GA 30126 0 

NEXEO SOLUTIONS LLC 7710 POLK ST SAINT LOUIS MO 63111 0.186 

GALATA CHEMICALS LLC - GALATA TAFT FACILITY 471 HWY 3142 HAHNVILLE LA 70057 0.0345 

NEXEO SOLUTIONS LLC 3101 WOOD DR GARLAND TX 75041 0.152 

ENGINEERED POLYMER SOLUTIONS INC (DBA VALSPAR COATINGS)

1717 W ENGLISH RD HIGH POINT NC 27261 0.0635 

MAXIM INTEGRATED PRODUCTS INC 9651 WESTOVER HILLS BLVSAN ANTONIO TX 78251 0 

ELEMENTIS SPECIALTIES 400 CLAREMONT AVE JERSEY CITY NJ 07304 0.0625 

GREIF INDUSTRIAL PACKAGING & SERVICES LLC 8250 ALMERIA AVE FONTANA CA 92335 0.01655 

NORTHERN COATINGS & CHEMICAL CO INC 705 6TH AVE MENOMINEE MI 49858 0.18 

CERTIFIED ENAMELING INC 3342 EMERY ST LOS ANGELES CA 90023 0.0025 

PPG ARCHITECTURAL FINISHES INC 400 S 13TH ST LOUISVILLE KY 40203 0 

PPG INDUSTRIES OHIO INC CIRCLEVILLE OH 559 PITTSBURGH RD CIRCLEVILLE OH 43113 0.0555 

3M CO - MEDINA 1030 LAKE RD MEDINA OH 44256 0.0365 

ITW PROFESSIONAL AUTOMOTIVE PRODUCTS 3606 CRAFTSMAN BLVD LAKELAND FL 33803 0.163 

BOEING COMMERCIAL AIRPLANE GROUP NORTH BOEING FIELD (PART)

7500 E MARGINAL WAY S SEATTLE WA 98108 0.0445 

ENTHONE INC 9809 INDUSTRIAL DR BRIDGEVIEW IL 60455 0.0438 

SHERWIN-WILLIAMS CO 2150 W SAND LAKE RD ORLANDO FL 32809 0 SUPERIOR SOLVENTS & CHEMICALS 320 NORTHPOINTE DR FAIRFIELD OH 45014 0.004085 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

1991 S WHEELING RD WHEELING IL 60090 0.0635 

AMERIMAX COATED PRODUCTS 215 PHILLIPS 324 RD HELENA AR 72342 0 

Page 26 of 38
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Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

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Emis

(t

BYK USA INC 524 S CHERRY ST WALLINGFORD CT 06492 0.15 

SUPERIOR OIL CO INC 400 W REGENT ST INDIANAPOLIS IN 46225 0.007065 FRAZEE INDUSTRIES 6625 MIRAMAR RD SAN DIEGO CA 92121 0 

WR MEADOWS OF ARIZONA INC 4220 S SARIVAL RD GOODYEAR AZ 85338 0.1515 BLENTECH CORP 1305 RYE ST HOUSTON TX 77029 0.0125 STOUSE INC 300 NEW CENTURY PKWY NEW CENTURY KS 66031 0.1475 

NEXEO SOLUTIONS LLC 2011 TURNER ST LANSING MI 48906 0.11 

ENTHONE INC 350 FRONTAGE RD WEST HAVEN CT 06516 0.00284 0

UNION CARBIDE CORP SOUTH CHARLESTON FACILITY 437 MACCORKLE AVE SW SOUTH CHARLEST

OWV 25303 0.0745 

NEXEO SOLUTIONS LLC 3930 GLENWOOD DR CHARLOTTE NC 28208 0.085 

MEADWESTVACO SOUTH CAROLINA LLC 400 CROSBY RD DERIDDER LA 70634 0.05 

BJ CHEMICAL SERVICES 707 N LEECH HOBBS NM 88240 0.01 0

SKF SEALING SOLUTIONS 900 N STATE ST ELGIN IL 60123 0 ACCURATE DISPERSIONS 192 W 155TH ST SOUTH HOLLAND IL 60473 0.103 

WARREN OIL CO - NC 2340 US 301 N DUNN NC 28335 0.137 

ARDEX LABORATORIES INC 2050 BYBERRY RD PHILADELPHIA PA 19116 0.1365 

SYNGENTA CROP PROTECTION LLC SAINT GABRIEL FACILITY

3905 HWY 75 SAINT GABRIEL LA 70776 0.0685 

MID-STATES PAINT & CHEMICAL CO 9315 WATSON INDUSTRIAL CRESTWOOD MO 63126 0.1325 

ISP SYNTHETIC ELASTOMERS LP 1615 MAIN ST PORT NECHES TX 77651 0 

BF GOODRICH TIRE MANUFACTURING 18906 US 24 E WOODBURN IN 46797 0.0025 

CYTEC INDUSTRIES INC LANGLEY PLANT 403 CARLINE RD LANGLEY SC 29834 0.12 

BASF CORP 3455 SOUTHPORT RD SPARTANBURG SC 29302 0.125 

BRENNTAG GREAT LAKES LLC 14765 W BOBOLINK AVE MENOMONEE FALLSWI 53051 0.0025 

CLEANING SYSTEMS INC 1997 AMERICAN BLVD DE PERE WI 54115 0.125 

COASTAL CHEMICAL CO LLC 3520 VETERANS MEMORIALABBEVILLE LA 70510 0.125 

US DOD DFSP SAN PEDRO 3171 N GAFFEY ST SAN PEDRO CA 90731 0.125 

NICCA USA INC 1044 S NELSON RD FOUNTAIN INN SC 29644 0.0025 

OAKLEY INC 1 ICON FOOTHILL RANCH CA 92610 0.0025 

PERMATEX SOLON 6875 PARKLAND BLVD SOLON OH 44139 0.0025 

RR STREET & CO INC 2353 S BLUE ISLAND AVE CHICAGO IL 60608 0.0025 

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Onsite Point 

Source 

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(tpy)

On

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Emis

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UNITED LABORATORIES INC 320 37TH AVE SAINT CHARLES IL 60174 0.125 

INTERNATIONAL PAINT LLC 6001 ANTOINE DR HOUSTON TX 77091 0.0025 

COSMETIC LABORATORIES OF AMERICA 20245 SUNBURST ST CHATSWORTH CA 91311 0 

SACRAMENTO- CAMPBELL SOUP SUPPLY CO 6200 FRANKLIN BLVD SACRAMENTO CA 95824 0.125 

MICHELMAN INC 9080 SHELL RD CINCINNATI OH 45236 0 FLUID ROUTING SOLUTIONS INC 1921 N BROAD ST LEXINGTON TN 38351 0 

MAINTEX INC 13300 E NELSON AVE CITY OF INDUSTRY CA 91746 0.125 PPG INDUSTRIES INC 500 PITTSBURGH AVE MCCARRAN NV 89434 0 

CHEMETALL US INC 13177 HURON RIVER DR ROMULUS MI 48174 0 

SICPA SECURINK CORP 8000 RESEARCH WAY SPRINGFIELD VA 22153 0.125 

TNEMEC CO INC 2300 EDGEWATER AVE BALTIMORE MD 21222 0 

TNEMEC CO INC 123 W 23RD AVE NORTH KANSAS CITMO 64116 0 

KALCOR COATINGS CO 37721 STEVENS BLVD WILLOUGHBY OH 44094 0.125 

TYSON FRESH MEATS INC HWY 50 W HOLCOMB KS 67851 0.125 

SAFETY-KLEEN SYSTEMS INC 130 A FRONTAGE RD LEXINGTON SC 29073 0 CREE INC 4600 SILICON DR DURHAM NC 27703 0 

DANLIN INDUSTRIES CORP 23737 HWY 47 THOMAS OK 73669 0.125 

GAGE PRODUCTS CO 625 WANDA AVE FERNDALE MI 48220 0 

GOLD EAGLE CO 4400 S KILDARE AVE CHICAGO IL 60632 0.125 

COLUMBIA PAINT CORP 641 JACKSON AVE HUNTINGTON WV 25704 0.125 

BERRYMAN PRODUCTS INC 3800 E RANDOL MILL RD ARLINGTON TX 76011 0.125 

TRANS CHEMICAL INC 419 E DE SOTO AVE SAINT LOUIS MO 63147 0.125 

AVON AUTOMOTIVE PLANT 1 603 W 7TH ST CADILLAC MI 49601 0.125 

AKCROS CHEMICALS INC 500 JERSEY AVE NEW BRUNSWICK NJ 08901 0 

AKZO NOBEL COATINGS INC 1431 PROGRESS AVE HIGH POINT NC 27260 0.125 

INVISTA SARL - ORANGE SITE 3055A FM 1006 ORANGE TX 77630 0 AMERICAN JETWAY CORP 34136 MYRTLE WAYNE MI 48184 0.125 

ARCH CHEMICALS INC HWY 933 BRANDENBURG KY 40108 0.065 

HOLCIM (US) INC HOLLY HILL PLANT 200 SAFETY ST / HWY 453 HOLLY HILL SC 29059 0.0045 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

3050 HANFORD DR LEBANON PA 17046 0.0635 

Page 28 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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(t

EXXONMOBIL REFINING & SUPPLY BATON ROUGE REFINERY

4045 SCENIC HWY BATON ROUGE LA 70805 0.055 

AEP INDUSTRIES INC 1201 S PINE HILL RD GRIFFIN GA 30224 0.00275 BUZZI UNICEM USA - GREENCASTLE PLANT 3301 S COUNTY RD 150 W GREENCASTLE IN 46135 0.027 AMPHENOL APC INC 91 NORTHEASTERN BLVD NASHUA NH 03062 0.0025 0.ANCHOR PAINT MANUFACTURING CO INC 6707 E 14TH ST TULSA OK 74112 0.1155 CCI MANUFACTURING IL CORP 15550 CANAL BANK RD LEMONT IL 60439 0 TEXAS INSTRUMENTS INC 13500 N CENTRAL EXPRES DALLAS TX 75243 0 3M COTTAGE GROVE CENTER 10746 INNOVATION RD COTTAGE GROVE MN 55016 0.0005 MEADWESTVACO SC LLC CHARLESTON CHEMICAL PLANT

5598 VIRGINIA AVE NORTH CHARLEST

OSC 29406 0.111 

CHASE PRODUCTS CO 2727 GARDNER RD BROADVIEW IL 60155 0.0005 

TECHNICAL CHEMICAL CO 3327 PIPELINE RD CLEBURNE TX 76033 0.1095 

NEXEO SOLUTIONS LLC - EVENDALE 2788 GLENDALE-MILFORD REVENDALE OH 45241 0.08 

CPJ TECHNOLOGIES 200 TANNER DR TAYLORS SC 29687 0.0395 

DELTA LABORATORIES INC 3710 W COUNTY RD 326 OCALA FL 34475 0.107 

KEMIRA WATER SOLUTIONS INC 1 CYANAMID RD MOBILE AL 36610 0.018 

PILOT CHEMICAL CO 11623 N HOUSTON ROSSLYHOUSTON TX 77086 0.105 

SHERWIN-WILLIAMS CO 636 E 40TH ST HOLLAND MI 49423 0.1045 

BENJAMIN MOORE & CO PELL CITY 109 BAMBERG DR PELL CITY AL 35125 0.1038 

NEXEO SOLUTIONS LLC MIAMI 200 NE 181ST ST MIAMI FL 33162 0.0755 

HERCULES INC KENEDY TEXAS ONE MILL ST KENEDY TX 78119 0.06448 0.0

NEXEO SOLUTIONS LLC CARSON 20915 S WILMINGTON AVE CARSON CA 90810 0.0905 

ROCKLINE INDUSTRIES 1113 MARYLAND AVE SHEBOYGAN WI 53081 0.0995 

CAROLINA SOLVENTS INC 2274 1ST ST SE HICKORY NC 28602 0.092 

AKZO NOBEL COATINGS INC 1000 INDUSTRIAL PARK DRCLINTON MS 39056 0.0945 

ROHM & HAAS ELECTRONIC MATERIA LS LLC 455 FOREST ST MARLBOROUGH MA 01752 0.0025 

TWINCO ROMAX 3100 W MILL RD MILWAUKEE WI 53209 0.0885 

WATSON LABORATORIES INC 575, 577, 579 CHIPETA WAYSALT LAKE CITY UT 84108 0.09024 

STEELSCAPE INC RANCHO 11200 ARROW RT RANCHO CUCAMONCA 91730 0.00313 0

MRCG-KRAFTMAID P3 150 GRAND VALLEY AVE ORWELL OH 44076 0.0055 PLASTI-KOTE INC 1000 LAKE RD MEDINA OH 44258 0.0635 

Page 29 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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(t

NEXEO SOLUTIONS LLC 5420 SPEAKER RD KANSAS CITY KS 66106 0.078 

CE BRADLEY LABORATORIES INC 55 BENNETT DR BRATTLEBORO VT 05301 0.0845 

OLDCASTLE BUILDING ENVELOPE - TENNESSEE FACILITY

920 POTTERTOWN RD MIDWAY TN 37809 0 

NEXEO SOLUTIONS LLC 400 MAIN ST TEWKSBURY MA 01876 0.0755 

EXXONMOBIL CHEMICAL BATON ROUGE CHEMICAL PLANT

4999 SCENIC HWY BATON ROUGE LA 70805 0.032 

AKZO NOBEL PAINTS PUERTO RICO LLC 65TH INFANTRY AVE KM. 13CAROLINA PR 00985 0.047 0

ATHEA LABORATORIES INC 7855 N FAULKNER RD MILWAUKEE WI 53224 0.0816 

UNIVAR USA INC ROMULUS BRANCH 13395 HURON RIVER DR ROMULUS MI 48174 0.034 

SOUTH FLORIDA MATERIALS CORP DBA VECENERGYPORT EVERGLADES 1200 SE 32ND ST FT LAUDERDALE FL 33316 0.078 

LUBRIZOL 9550 W 55TH ST MC COOK IL 60525 0 

SUPERIOR SOLVENTS & CHEMICALS 4211 BRAMERS LN LOUISVILLE KY 40216 0.0035 

PPG INDUSTRIES OHIO INC - DELAWARE 760 PITTSBURGH DR DELAWARE OH 43015 0.03892 

PROCTER & GAMBLE HAIR CARE LLC 2200 LOWER MUSCATINE RIOWA CITY IA 52240 0.0205 

MATTHEWS INTERNATIONAL CORP 101 FAIRVIEW AVE PITTSBURGH PA 15238 0.0515 

PLAZE INC 105 BOLTE LN SAINT CLAIR MO 63077 0.066 

WHITFORD CORP 47 PARK AVE ELVERSON PA 19520 0.062295 

KARCHER NORTH AMERICA PROCHEM 325 S PRICE RD CHANDLER AZ 85224 0.0655 

IMPERIAL PAINT CO INC 2526 NW YEON AVE PORTLAND OR 97210 0 

NEXEO SOLUTIONS LLC FAIRFIELD 2461 CROCKER CIR FAIRFIELD CA 94533 0.0615 

VALVOLINE 720 VAIDEN DR HERNANDO MS 38632 0.017 

MAXIM INTEGRATED PRODUCTS INC 3725 N FIRST ST SAN JOSE CA 95134 0 

VEOLIA ES TECHNICAL SOLUTIONS LLC 125 FACTORY LN MIDDLESEX NJ 08846 0.045 

ADCO CLEANING PRODUCTS LLC 900 W MAIN ST SEDALIA MO 65301 0.0195 

ABC COMPOUNDING CO OF TEXAS INC 1102 AVE J E GRAND PRAIRIE TX 75050 0.0025 KAY CHEMICAL CO 8300 CAPITAL DR GREENSBORO NC 27409 0.011 

CLOROX PRODUCTS MANUFACTURING CO 2600 HUNTINGTON DR FAIRFIELD CA 94533 0.0585 

NPA COATINGS INC 11120 BEREA RD CLEVELAND OH 44102 0 

MINUTEMAN INTERNATIONAL MULTI-CLEAN DIV 600 CARDIGAN RD SHOREVIEW MN 55126 0.056 

FRANKLIN INTERNATIONAL 2020 BRUCK ST COLUMBUS OH 43207 0.0055 

Page 30 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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(t

MRCG-KRAFTMAID P1 16052 INDUSTRIAL PKWY MIDDLEFIELD OH 44062 0 ECOLAB INC 942 BAKER RD MARTINSBURG WV 25405 0.0415 

ECOLAB INC 18383 E RAILROAD ST CITY OF INDUSTRY CA 91748 0.0195 

CLEVELAND STEEL CONTAINER - KILGORE 5005 ELDER LAKE RD KILGORE TX 75662 0.0025 

HARLEY-DAVIDSON MOTOR CO OPERATIONS INC 1425 EDEN RD YORK PA 17402 0.007 

RECKITT BENCKISER 799 RT 206 & HILLSBOROUGHILLSBOROUGH NJ 08844 0.0445 

VALSPAR SAMUEL CABOT DIV 100 HALE ST NEWBURYPORT MA 01950 0.0505 

CONOCOPHILLIPS PONCA CITY REFINERY 1000 S PINE ST PONCA CITY OK 74602 0.0025 

AKZO NOBEL COATINGS INC 1660 CROSS ST SE SALEM OR 97302 0.0275 

HUNTSMAN ADVANCED MATERIALS AMERICAS INC 555 HUNTSMAN RD MC INTOSH AL 36553 0.0146 

ECOLAB INC 3001 CHANNAHON RD JOLIET IL 60436 0.0375 

SHERWIN-WILLIAMS CO 630 E 13TH ANDOVER KS 67002 0.036 

UNIVAR USA INC - TOLEDO SOUTH BRANCH 4051 S AVE TOLEDO OH 43615 0.01 

CONOCOPHILLIPS OKLAHOMA CITY PRODUCTS TERMINAL

4700 NE 10TH ST OKLAHOMA CITY OK 73117 0.0025 

DYSTAR LP 209 WATLINGTON INDUSTRREIDSVILLE NC 27320 0.035 

HENKEL CORP 137 FOLLY MILL RD SEABROOK NH 03874 0.0025 

CUSTOM SYNTHESIS LLC 1704 DENVER RD ANDERSON SC 29625 0.0025 

BARTON SOLVENTS INC BETTENDORF 204 36TH ST BETTENDORF IA 52722 0.0115 

SHERWIN-WILLIAMS CO 113 STAGE COACH TRAIL GREENSBORO NC 27409 0.015 

ELECTRONICS FOR IMAGING INC 1260 JAMES L HART PKWY YPSILANTI MI 48197 0.0485 BRENNTAG SOUTHEAST INC 2000 E PETTIGREW ST DURHAM NC 27703 0.029 

DIC IMAGING PRODUCTS USA LLC 7335 S 10TH ST OAK CREEK WI 53154 0.0045 

GRAPHIC CONTROLS LLC 400 EXCHANGE ST BUFFALO NY 14204 0.046 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

901 W UNION ST MONTEBELLO CA 90640 0.037 

CHAMPION TECHNOLOGIES INC 3130 FM 521 FRESNO TX 77545 0.043 

BRENNTAG PACIFIC INC 10747 PATTERSON PL SANTA FE SPRINGSCA 90670 0.038 

CHAMPION TECHNOLOGIES INC 1816 S JACKSON ST MAGNOLIA AR 71753 0.042 

ECOLAB INC 261 HWY 155 S MC DONOUGH GA 30253 0.0075 

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR COATINGS

2000 WESTHALL ST PITTSBURGH PA 15233 0.0315 

Page 31 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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Emis

(t

VALERO THREE RIVERS REFINERY 301 LEROY ST THREE RIVERS TX 78071 0.0395 

BIOLAB INC 1735 DOGWOOD DR CONYERS GA 30012 0.03915 

HANNA STEEL CORP 220 HANNA DR PEKIN IL 61554 0.0025 

CONOCOPHILLIPS CO EAST ST LOUIS TERMINAL 3300 MISSISSIPPI AVE CAHOKIA IL 62206 0 

BRENNTAG SOUTHWEST INC SAND SPRINGS 206 E MORROW RD SAND SPRINGS OK 74063 0.0175 

LUBRIZOL CORP 29400 LAKELAND BLVD WICKLIFFE OH 44092 0.0365 

CHAMPION TECHNOLOGIES INC 710 MARVIN A SMITH BLVD LONGVIEW TX 75662 0.035 

HARCROS CHEMICALS INC 4606 NEW W DR PASADENA TX 77507 0.0125 

KWAL-HOWELLS INC (DBA KWAL PAINT INC) 2430 ALBERT BROADFOOT BONHAM TX 75418 0 

BARTON SOLVENTS INC DES MOINES 1970 NE BROADWAY DES MOINES IA 50313 0.0065 

BARTON SOLVENTS INC KANSAS CITY 901 S 66TH TERRACE KANSAS CITY KS 66111 0.01 

BRENNTAG NORTHEAST INC 81 W HULLER LN READING PA 19605 0.0177 

GEORGIA-PACIFIC CHEMICALS LLC 1429 E LUFKIN AVE LUFKIN TX 75901 0.032 

DAUBERT CHEMICAL CO 4700 S CENTRAL AVE CHICAGO IL 60638 0.01723 0

SI GROUP INC 1000 MAIN ST ROTTERDAM JUNCTNY 12150 0 

NEXEO SOLUTIONS LLC TAMPA 5125 W HANNA AVE TAMPA FL 33634 0.0015 

BOEING COMMERCIAL AIRPLANE GROUP PLANT 2 (PART)

7755 E MARGINAL WAY S SEATTLE WA 98108 0.0305 

NEXEO SOLUTIONS LLC HOUSTON 8901 OLD GALVESTON RD HOUSTON TX 77034 0.005 

HENKEL CORP 421 LONDON RD DELAWARE OH 43015 0 

BAKER PETROLITE CORP 9100 W 21ST ST SAND SPRINGS OK 74063 0.01406 

VALERO REFINING CO - TENNESSEE LLC 2385 RIVERPORT RD MEMPHIS TN 38109 0.03 

UNIVAR USA INC MORRISVILLE BRANCH 200 DEAN SIEVERS PL MORRISVILLE PA 19067 0.0135 

ARKEMA COATINGS & RESINS 13511 MAIN ST LEMONT IL 60439 0.0075 

RICHARDSAPEX INC 4202-24 MAIN ST PHILADELPHIA PA 19127 0.021111 

HEXPOL COMPOUNDING BURTON RUBBER PROCESSING

HWY 353 S JONESBOROUGH TN 37659 0 

BARTON SOLVENTS INC WEST BEND 800 RAIL WAY WEST BEND WI 53095 0.0025 SHERWIN-WILLIAMS CO 1025 HOWARD ST GREENSBORO NC 27403 0.0055 

TYCO FIRE SUPPRESSION & BUILDING PRODUCTS 1 STANTON ST MARINETTE WI 54143 0.002595 

BRENNTAG SOUTHWEST INC LONG VIEW 610 FISHER RD LONGVIEW TX 75604 0.014 

Page 32 of 38
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Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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(t

PLAZE INC 1000 INTEGRAM DR PACIFIC MO 63069 0.025 

BARTON SOLVENTS INC COUNCIL BLUFFS 2135 9TH AVE COUNCIL BLUFFS IA 51502 0.0015 

SHERWIN-WILLIAMS CO 2121 NEW WORLD DR COLUMBUS OH 43207 0.008 

SHERWIN-WILLIAMS CO 11700 S COTTAGE GROVE CHICAGO IL 60628 0 

ECOLAB INC 2305 SHERWIN ST GARLAND TX 75041 0.0105 

HERITAGE-WTI INC 1250 ST GEORGE ST EAST LIVERPOOL OH 43920 0.00495 

3M CO - SPRINGFIELD 3211 E CHESTNUT EXPY SPRINGFIELD MO 65802 0 

AFTON CHEMICAL CORP 501 MONSANTO AVE SAUGET IL 62201 0.005 

EXXONMOBIL OIL CORP - TORRANCE REFINERY 3700 W 190TH ST TORRANCE CA 90509 0.02 

PRIDE SOLVENTS & CHEMICAL CO OF NEW JERSEY 211 RANDOLPH AVE AVENEL NJ 07001 0.005 

HEXPOL COMPOUNDING BURTON RUBBER PROCESSING

14330 KINSMAN RD BURTON OH 44021 0 

BARTON SOLVENTS INC WICHITA 201 S CEDAR VALLEY CENTER KS 67147 0.01 

UNIVAR USA INC JACKSONVILLE FA CILITY 155 ELLIS RD S JACKSONVILLE FL 32254 0.015 

ZEP COMMERCIAL 350 JOE FRANK HARRIS PKEMERSON GA 30137 0 

VALSPAR REFINISH 210 CROSBY ST PICAYUNE MS 39466 0 

VEOLIA ES TECHNICAL SOLUTIONS LLC 7 MOBILE AVE SAUGET IL 62201 0.0015 

BENJAMIN MOORE & CO JOHNSTOWN UNION AVE EXTENSION JOHNSTOWN NY 12095 0.01885 0.0

VEYANCE TECHNOLOGIES INC 4021 N 56TH ST LINCOLN NE 68504 0.00000135 0.00

PRC-DESOTO INTERNATIONAL INC 11601 UNITED ST MOJAVE CA 93501 0.0075 

PLAZE INC 113 BOLTE LN SAINT CLAIR MO 63077 0.016 

DUPONT PARLIN PLANT CHEESEQUAKE RD PARLIN NJ 08859 0.002 

CLEARWATER INTERNATIONAL LLC 100 INDUSTRIAL DR (BLDG LEETSDALE PA 15056 0.006 0Z TECHNOLOGIES CORP 26500 CAPITOL AVE REDFORD MI 48239 0 

SHERWIN-WILLIAMS CO 6795 S MAIN ST MORROW GA 30260 0.004 

TOYO INK AMERICA LLC 2400 N HARVEY MITCHELL BRYAN TX 77807 0.005 

INTERSTATE CHEMICAL CO INC 2797 FREEDLAND RD HERMITAGE PA 16148 0.003 

RUSTOLEUM CORP 7850 OHIO RIVER RD LESAGE WV 25537 0.001 

AIR PRODUCTS PERFORMANCE MANUFACTURING INC 337 VINCENT DR MILTON WI 53563 0.0025 

DAVIES IMPERIAL COATINGS INC 1275 STATE ST HAMMOND IN 46320 0.013 

VARN INTERNATIONAL 1333 N KIRK RD BATAVIA IL 60510 0.008 

Page 33 of 38
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Onsite Point 

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(tpy)

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(t

GOODWIN CO 700 PROGRESS CENTER AVLAWRENCEVILLE GA 30043 0.01091 

PRIDE SOLVENT & CHEMICAL CO OF NY INC 6 LONG ISLAND AVE HOLTSVILLE NY 11742 0.003 

SHERWIN-WILLIAMS CO 2325 HOLLINS FERRY RD BALTIMORE MD 21230 0.0015 

NEXEO SOLUTIONS LLC TWINSBURG ENTERPRISE 1842 ENTERPRISE PKWY TWINSBURG OH 44087 0.002 

DSM DESOTECH INC 1101 HWY 27 S STANLEY NC 28164 0 

RESEARCH SOLUTIONS GROUP INC 133 BAIN DR LA VERGNE TN 37086 0.0003 

TRUE VALUE MANUFACTURING 201 JANDUS RD CARY IL 60013 0.0025 

DUPONT FRONT ROYAL PLANT 7961 WINCHESTER RD FRONT ROYAL VA 22630 0.001 

SHERWIN-WILLIAMS CO 26300 FARGO AVE BEDFORD HEIGHTS OH 44146 0.0005 

HYDRITE CHEMICAL CO 2545 BOND ST UNIVERSITY PARK IL 60466 0 

GIANT CEMENT CO HWY 453 & I-26 (654 JUDGEHARLEYVILLE SC 29448 0.001 

FERRO CORP WALTON HILLS OPERATIONS 7050 KRICK RD WALTON HILLS OH 44146 0.0035 

TAKASAGO INTERNATIONAL CORP (USA) 267 UNION ST NORTHVALE NJ 07647 0.01 

VOGEL PAINT & WAX CO INC 1020 ALBANY PL SE ORANGE CITY IA 51041 0.0025 HOLLY OAK CHEMICAL INC 101 CASE ST FOUNTAIN INN SC 29644 0.010345 

SHERWIN-WILLIAMS CO 12401 INDUSTRIAL BLVD VICTORVILLE CA 92392 0.0045 

UNIVAR USA INC NORCROSS FACILI TY 2145 SKYLAND CT NORCROSS GA 30071 0.0035 

HUBBARD-HALL INC 563 S LEONARD ST WATERBURY CT 06708 0.0005 

CARBOLINE CO 900 OPELOUSAS ST LAKE CHARLES LA 70601 0 

ETHOX CHEMICALS LLC 1801 PERIMETER RD GREENVILLE SC 29605 0.0025 

BUCKLEY OIL CO 1809 ROCK ISLAND ST DALLAS TX 75207 0.007 

UNIVAR USA INC 7050 W 71ST ST BEDFORD PARK IL 60499 0.00472 

BERRIDGE MANUFACTURING CO 6515 FRATT RD SAN ANTONIO TX 78218 0 

GACO WESTERN 1245 CHAPMAN DR WAUKESHA WI 53186 0.0085 

CHEMOL CO INC 2300 RANDOLPH AVE GREENSBORO NC 27406 0 

INTERSTATE CHEMICAL CO INC 23247 W EAMES ST CHANNAHON IL 60410 0.002 CLEAN HARBORS ENVIRONMENTAL SERVICES INC 2247 S HWY 71 KIMBALL NE 69145 0.005 

UNIVAR USA INC NEW BERLIN 2400 S 170TH ST NEW BERLIN WI 53151 0.00505 

FORD MOTOR CO DEARBORN TOOL & DIE PLANT 3001 MILLER RD DEARBORN MI 48121 0.007 

VERSO PAPER HOLDINGS LLC ANDROSCOGGIN MILL RILEJAY ME 04239 0.0025 

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Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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(t

PROCTER & GAMBLE CO GPDF 5348 VINE ST CINCINNATI OH 45217 0.0065 

UNIVAR USA INC TAMPA FACILITY 6049 OLD 41A HWY TAMPA FL 33619 0.002 

UNIVAR USA INC DORAVILLE FACILITY 1 ALCHEMY PL DORAVILLE GA 30362 0.003 

SHERWIN-WILLIAMS CO 404 E MALLORY AVE MEMPHIS TN 38109 0.002 

PPG ARCHITECURAL COATINGS HOUSTON 3530 LANG RD HOUSTON TX 77092 0.0025 

IGM RESINS CHARLOTTE 3300 WESTINGHOUSE BLVDCHARLOTTE NC 28273 0.0065 

CONOCOCPHILLIPS CO WICHITA TERMINAL 2400 E 37TH ST N WICHITA KS 67219 0 

BRULIN CORP 2920 DR ANDREW J BROWNINDIANAPOLIS IN 46205 0.002642 0

PROCTER & GAMBLE MANUFACTURING CO 1900 KANSAS AVE KANSAS CITY KS 66105 0.005905 0

NEW DAWN MANUFACTURING CO 16001 TRADE ZONE AVE UPPER MARLBORO MD 20774 0.0060048 

UNIVAR USA INC JAMESTOWN FACILITY 108 OAKDALE RD JAMESTOWN NC 27282 0.003 

UNIVAR USA INC 2600 S GARFIELD AVE COMMERCE CA 90040 0.006 

KING INDUSTRIES INC SCIENCE RD NORWALK CT 06852 0.0031 

LANCO MANUFACTURING CORP URB.APONTE #5 SAN LORENZO PR 00754 0.0056 

DIVERSEY INC - WAXDALE FACILITY 8311 16TH ST STURTEVANT WI 53177 0.00025 0

CHEMTEX LABORATORIES INC 2725 ARMENTROUT DR CONCORD NC 28025 0.0055 

OMNIUM 1280 IMPERIAL RD HAMPTON IA 50441 0.002 

CALLAHAN CHEMICAL CO 200 INDUSTRIAL AVE RIDGEFIELD PARK NJ 07660 0.0025 

INTERNATIONAL PAINT LLC 640 N ROCKY RIVER DR BEREA OH 44017 0.0025 

CENTRAL SOLUTIONS INC 401 FUNSTON RD KANSAS CITY KS 66115 0 

SARTOMER USA LLC 601 TIGHTSQUEEZE INDUS CHATHAM VA 24531 0.0025 

ANDERSON DEVELOPMENT CO 1415 E MICHIGAN ST ADRIAN MI 49221 0.0025 

CUSTOM CHEMICAL FORMULATORS INC 8707 MILLERGROVE DR SANTA FE SPRINGSCA 90670 0.005 

GE WATER & PROCESS TECHNOLOGIES 333 S LOMBARD RD ADDISON IL 60101 0.0025 

CR BRANDS INC 141 VENTURE BLVD SPARTANBURG SC 29306 0.0025 

ACTON TECHNOLOGIES INC 100 THOMPSON ST PITTSTON PA 18640 0.005 

CLOROX PRODUCTS MANUFACTURING CO 17 LAKE MIRROR RD FOREST PARK GA 30297 0.0025 

GE WATER & PROCESS TECHNOLOGIES 2118 REISER AVE SE NEW PHILADELPHIAOH 44663 0.0025 

C P INC 196 S WATER CONNERSVILLE IN 47331 0.0025 

INDEPENDENT INK INC 14705 S AVALON BLVD GARDENA CA 90248 0.0025 

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Facility Name Address City State Zip Code

Onsite Point 

Source 

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(tpy)

On

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OAKITE PRODUCTS INC (AKA CHEMETALL OAKITE) 16961 KNOTT AVE LA MIRADA CA 90638 0.0025 

PVS NOLWOOD CHEMICALS INC 9000 HUBBELL AVE DETROIT MI 48228 0.0025 

SARTOMER USA LLC 610 S BOLMAR ST WEST CHESTER PA 19382 0.0025 

GOODWIN CO 12361 MONARCH ST GARDEN GROVE CA 92841 0.004 

BRAIN POWER INC 4470 SW 74TH AVE MIAMI FL 33155 0.0025 

REICHHOLD INC - AZUSA PLANT 237 S MOTOR AVE AZUSA CA 91702 0.0025 

EDCO PRODUCTS INC 8700 EXCELSIOR BLVD HOPKINS MN 55343 0 

EVONIK DEGUSSA CORP 4201 DEGUSSA RD THEODORE AL 36582 0.004 

LUBRIZOL CORP PAINESVIL LE PLANT 155 FREEDOM RD PAINESVILLE OH 44077 0.004 RESEARCH SOLUTIONS GROUP INC 402 INDUSTRIAL PARK DR PELHAM AL 35124 0.00241 

TRANSTAR AUTOBODY TECHNOLOGIES 2040 HEISERMAN DR BRIGHTON MI 48114 0.00211 

PRESTONE PRODUCTS CORP 250 HALLS MILL RD FREEHOLD NJ 07728 0.002 

MACDERMID INC 1221 FARROW AVE FERNDALE MI 48220 0.00178 

UNIVAR USA INC SANTA FE SPRINGS 13900 CARMENITA RD SANTA FE SPRINGSCA 90670 0.0005 

PENRAY COS INC 1801 ESTES AVE ELK GROVE VILLAG IL 60007 0.0005 

SHERWIN-WILLIAMS CO 14 INDUSTRIAL PARK FLORA IL 62839 0.0015 

BOEHRINGER INGELHEIM CHEMICALS INC 2820 N NORMANDY DR PETERSBURG VA 23805 0.0015 

CLARIANT CORP CLEAR LAKE PLANT 9502 BAYPORT BLVD - ET

O PASADENA TX 77507 0.0031 

HENTZEN COATINGS,INC 6937 W MILL RD MILWAUKEE WI 53218 0.00125 

SUN CHEMICAL CORP 135 W LAKE ST NORTHLAKE IL 60164 0.0005 

AVANTOR PERFORMANCE MATERIALS 600 N BROAD ST PHILLIPSBURG NJ 08865 0.003 

CONOCOPHILLIPS MT VERNON PRODUCTS TERMINAL 15138 HWY 96 MOUNT VERNON MO 65712 0 

BRAINERD CHEMICAL CO INC 1200 N PEORIA TULSA OK 74147 0 

ECP INC WOODRIDGE 11210 KATHERINE'S CROSSWOODRIDGE IL 60517 0.0025 

WYNNEWOOD REFINING CO 906 S POWELL WYNNEWOOD OK 73098 0 US DOD DFSP VERONA 5449 W MAIN ST VERONA NY 13478 0.0025 

UNION SPECIALTIES INC 3 MALCOLM HOYT DR NEWBURYPORT MA 01950 0.0005 

RENESSENZ LLC JACKSONVILLE 601 CRESTWOOD ST JACKSONVILLE FL 32208 0.0025 

NOV TUBOSCOPE HOLMES ROAD 2811 HOLMES RD HOUSTON TX 77051 0.0025 

NIACET CORP 400 47TH ST NIAGARA FALLS NY 14304 0.0025 

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Onsite Point 

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On

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KEYSTONE CEMENT CO RT 329 BATH PA 18014 0 

HERCULES INC 1111 HERCULES RD HOPEWELL VA 23860 0.0025 

HARWICK STANDARD DISTRIBUTION CORP 60 S SEIBERLING ST AKRON OH 44305 0.0025 

A BRITE CO 3217 WOOD DR GARLAND TX 75041 0.0025 

FINGER LAKES CHEMICAL INC 418-424 ST PAUL ST ROCHESTER NY 14605 0.0025 

ATOTECH USA 1750 OVERVIEW DR ROCK HILL SC 29730 0.0025 DUPONT EKC TECHNOLOGY 2520 BARRINGTON CT HAYWARD CA 94545 0.0005 CR BRANDS INC 230 OLD CONVERSE RD SPARTANBURG SC 29307 0.0025 

CHEMICAL SOLVENTS INC--DENISON FACILITY 1010 OLD DENISON AVE CLEVELAND OH 44109 0.0025 

BRENNTAG SOUTHEAST INC 11750 FRUEHAUF DR CHARLOTTE NC 28273 0.001 

FISHER SCIENTIFIC INTERNATIONAL MTN DIAGNOSTICS PLANT

8365 VALLEY PIKE MIDDLETOWN VA 22645 0 

ASTRO CHEMICALS INC 126 MEMORIAL DR SPRINGFIELD MA 01104 0.0015 

CALLAHAN CHEMICAL CO 18 INDUSTRIAL RD WALPOLE MA 02081 0.001 

FORD MOTOR CO DEARBORN DIVERSIFIED MANUFACTURING

3001 MILLER RD DEARBORN MI 48121 0.002 

INTERCOASTAL PAINT CO INC 14029 W HARDY HOUSTON TX 77060 0.002 

MARATHON PETROLEUM CO - SPEEDWAY IN 

TERMINAL

1304 OLIN AVE INDIANAPOLIS IN 46222 0.002 

GENERAL DYNAMICS ORDNANCE & TACTICAL SYSTEMS GARLAND

1200 N GLENBROOK GARLAND TX 75040 0.00199 0

UNIVAR USA INC - TOLEDO BRANCH 30450 TRACY RD WALBRIDGE OH 43465 0.001005 0

VOLTAIX LLC 197 MEISTER AVE BRANCHBURG NJ 08876 0.0005 

ROHM & HAAS CHEMICALS LLC 2401 E PRATT BLVD ELK GROVE VILLAG IL 60007 0 

PENRAY COS INC 440 DENNISTON CT WHEELING IL 60090 0.0005 

HYDRITE CHEMICAL CO 7300 W BRADLEY RD MILWAUKEE WI 53223 0.0005 

ENGINEERED POLYMER SOLUTIONS INC 5501 E SLAUSON AVE CITY OF COMMERC CA 90040 0 

BUCKMAN LABORATORIES INC 1256 N MCLEAN BLVD MEMPHIS TN 38108 0 

DYNASOL INC 330 PINE ST CANTON MA 02021 0.00145 

BENJAMIN MOORE & CO - NEWARK 134 LISTER AVE NEWARK NJ 07105 0.00135 

BENJAMIN MOORE & CO - DALLAS 700 W KEARNEY MESQUITE TX 75149 0.001315 0

NORLITE CORP 628 S SARATOGA ST COHOES NY 12047 0.00108 0

CRODA INC 315 CHERRY LN NEW CASTLE DE 19720 0.000645 

Page 37 of 38
Table B-3. 2011 Emissions Inventory: Non-Zero Certain Glycol Ether Reported 

Facility Name Address City State Zip Code

Onsite Point 

Source 

Emissions 

(tpy)

On

Fug

Emis

(t

FUJIFILM HUNT CHEMICALS USA INC 900 CARNEGIE ST ROLLING MEADOWSIL 60008 0.00095 

MANN DISTRIBUTION 3134 POST RD WARWICK RI 02886 0.001055 

SINCLAIR WYOMING REFINING CO 100 E LINCOLN AVE SINCLAIR WY 82334 0.0005 

SDC TECHNOLOGIES INC 45 PARKER IRVINE CA 92618 0.0005 

OMNOVA SOLUTIONS INC 1455 J A COCHRAN BY-PASCHESTER SC 29706 0.000955 0

RIKER PRODUCTS INC 4901 STICKNEY AVE TOLEDO OH 43612 0.000945 

PPG ARCHITECTURAL COATINGS 6804 ENTERPRISE DR LOUISVILLE KY 40214 0 

LAMBERTI SYNTHESIS USA INC 4001 N HAWTHORNE ST CHATTANOOGA TN 37406 0.0005255 

BP PRODUCTS NORTH AMERICA WHITING 2815 INDIANAPOLIS BLVD WHITING IN 46394 0.0005 

NATIONAL INDUSTRIAL COATINGS INC DBA NICOAT 

INC

1600 GLENLAKE AVE ITASCA IL 60143 0.0005 

NALCO CO 3901 TERRY ST TEXARKANA TX 75501 0 

BAKER PETROLITE-RAYNE FACILITY 135 INDUSTRIAL DR RAYNE LA 70578 0 

IFF AUGUSTA LTD 3005 INTERNATIONAL BLVDAUGUSTA GA 30906 0 0.0

PARKER HANNIFIN TECH SEAL DIV 2600 WILCO BLVD WILSON NC 27893 0 0

GLIDDEN CO 1900 N JOSEY LN CARROLLTON TX 75006 0 0

BAKER PETROLITE KILGORE BLEND PLANT 806 PALUXY ST KILGORE TX 75662 0.0001935 0

BAKER PETROLITE CORP 16950 WALLISVILLE RD HOUSTON TX 77049 0.000048 0

CHEMETALL US INC 1610 CLARA ST JACKSON MI 49203 0.0000441 0.0

BAKER PETROLITE BAYPORT FACILI TY 13200 BAYPARK RD PASADENA TX 77507 0 0.0

MULTI-COLOR CORP 2281 S US 31 SCOTTSBURG IN 47170 0 0.000

NALCO CO 125 NALCO WAY/RT 65 ELLWOOD CITY PA 16117 0.00000224 

EMERALD SERVICES INC 1825 E ALEXANDER AVE TACOMA WA 98421 0 AIR PRODUCTS PERFORMANCE MANUFACTURING INC 474 W 19TH ST RESERVE LA 70084 0 0.0

a. Releases to Surface Water reported as "On-Site Releases to Surface Water"b. Releases to Soil is the sum of reported releases to onsite and offsite releases to land treatment and other land disposal.c. Releases to other media include reported releases to on-site and offsite groundwater and landfills.tpy: tons per year

Page 38 of 38
APPENDIX C 

Outcome of Screening Procedure for Long-Term Exposures 
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

REXAM BEVERAGE CAN CO RE: WINSTON SALEM PLANT WINSTON-SALEM North Carolina 27107 172.2405 Retain

BALL METAL BEVERAGE CONTAINER CORP WILLIAMSBURG Virginia 23185 167 Retain

BALL METAL BEVERAGE CONTAINER CORP FINDLAY Ohio 45840 154.5 Retain

REXAM BEVERAGE CAN CO RE: FREMONT PLANT FREMONT Ohio 43420 120.081 Retain

CROWN FOOD PACKAGING OWATONNA Minnesota 55060 117.0605 Retain

AURORA CASKET CO INC AURORA Indiana 47001 107.6265 Retain

CROWN CORK & SEAL CO (USA) INC CROWN CLOSURE DIV WEIRTON West Virginia 26062 101.1455 Retain

REXAM BEVERAGE CAN CO RE: BISHOPVILLE SC FACILITY BISHOPVILLE South Carolina 29010 96.4635 Retain

REXAM BEVERAGE CAN CO RE: EVA STREET ST PAUL MN SAINT PAUL Minnesota 55107 93.5265 Retain

FORD MOTOR CO DEARBORN TRUCK PLANT DEARBORN Michigan 48121 88.8 Retain

REXAM BEVERAGE CAN CO OLIVE BRANCH FACILITY OLIVE BRANCH Mississippi 38654 88.089 Retain

REXAM BEVERAGE CAN CO KENT WA FACILITY KENT Washington 98032 87.962 Retain

BALL METAL BEVERAGE CONTAINER CORP REIDSVILLE North Carolina 27320 77 Retain

CROWN BEVERAGE PACKAGING LAWRENCE Massachusetts 01843 72.1775 Retain

BMW MANUFACTURING CO LLC GREER South Carolina 29651 70.632 Retain

BALL CONTAINER LLC COLUMBUS CAN PLANT COLUMBUS Ohio 43213 70 Retain

CROWN BEVERAGE PACKAGING BRADLEY Illinois 60915 68.5545 Retain

CROWN BEVERAGE PACKAGING OLYMPIA Washington 98501 68.4155 Retain

SILGAN CONTAINERS MANUFACTURING CORP LA PORTE Indiana 46350 67 Retain

REXAM BEVERAGE CAN CO LONGVIEW FACILITY LONGVIEW Texas 75604 66.9795 Retain

REXAM BEVERAGE CAN CO RE : CHICAGO PLANT CHICAGO Illinois 60609 65.3755 Retain

METAL CONTAINER CORP - JACKSONVILLE CAN PLANT JACKSONVILLE Florida 32254 61.44 Retain

METAL CONTAINER CORPORTION - WINDSOR CAN PLANT WINDSOR Colorado 80550 57.504 Retain

WHIRLPOOL CORP MARION D IVISION MARION Ohio 43302 55.801 Retain

REXAM BEVERAGE CAN CO CHATSWORTH FACILITY CHATSWORTH California 91311 54.6345 Retain

SILGAN CONTAINERS MANUFACTURING CORP PLOVER Wisconsin 54467 50.75 Retain

BALL CONTAINER LLC ROME CAN PLANT ROME Georgia 30161 49.5 Retain

REXAM BEVERAGE CAN CO RE: WHITEHOUSE PLANT WHITEHOUSE Ohio 43571 48.081 Retain

METAL CONTAINER CORP - NEWBURGH CAN PLANT NEW WINDSOR New York 12553 46.4585 Retain

HONDA OF AMERICA MANUFACTURING INC MARYSVILLE Ohio 43040 44.873 Retain

CROWN BEVERAGE PACKAGING WORLAND Wyoming 82401 44.5215 Retain

METAL CONTAINER CORP - ARNOLD CAN PLANT ARNOLD Missouri 63010 44.1865 Retain

BALL METAL BEVERAGE CONTAINER CORP MILWAUKEE Wisconsin 53224 42.5 Retain

FORD MOTOR COMPANY--KANSAS CITY ASSEMBLY PLANT CLAYCOMO Missouri 64119 41.75 Retain

RR DONNELLEY HARRISONBURG Virginia 22802 40.417 Retain

REXAM BEVERAGE CAN CO PHOENIX FACILITY PHOENIX Arizona 85043 39.648 Retain

CHRYSLER ST LOUIS NORTH ASSEMBLY PLANT FENTON Missouri 63026 37.5 Retain

NEW UNITED MOTOR MANUFACTURING INC FREMONT California 94538 37.124 Retain

BALL METAL FOOD CONTAINER CORP WEIRTON West Virginia 26062 37 Retain

ROCKY MOUNTAIN METAL CONTAINER GOLDEN Colorado 80401 36.5 Retain

BALL METAL BEVERAGE CONTAINER CORP MONTICELLO Indiana 47960 36 Retain

GM TRUCK GROUP FLINT ASSEMBLY PLANT VAN SLYKE 

COMPLEX

FLINT Michigan 48551 35.79 Retain

WHIRLPOOL CORP - CLYDE DIV CLYDE Ohio 43410 35.3585 Retain

CROWN BEVERAGE PACKAGING CONROE Texas 77305 34.066 Retain

CROWN FOOD PACKAGING BALTIMORE Maryland 21221 33.9615 Retain

BALL METAL BEVERAGE CONTAINER CORP TORRANCE California 90503 33.65 Retain

REXAM BEVERAGE CAN CO RE:OKLAHOMA CITY PLANT OKLAHOMA CITY Oklahoma 73179 33.5495 Retain

FORD MOTOR CO KENTUCKY TRUCK PLANT LOUISVILLE Kentucky 40241 33.4 Retain

NISSAN NA INC SMYRNA MANUFACTURING PLANT SMYRNA Tennessee 37167 33.318 Retain

METAL CONTAINER CORP - MIRA LOMA CAN PLANT MIRA LOMA California 91752 32.785 Retain

CROWN BEVERAGE PACKAGING SUGAR LAND Texas 77478 32.1695 Retain

BALL METAL BEVERAGE CONTAINER CORP FAIRFIELD California 94533 31.5 Retain

BALL METAL BEVERAGE CONTAINER CORP GOLDEN Colorado 80403 31.5 Retain

CHICAGO HEIGHTS STEEL CHICAGO HEIGHTS Illinois 60411 31.3915 Retain

THERMA-TRU CORP BUTLER Indiana 46721 31.029 Retain

CROWN BEVERAGE PACKAGING CAROLINA Puerto Rico 00985 30.1245 Retain

SENECA FOODS CORP BARABOO Wisconsin 53913 29.8385 Retain

HONDA OF AMERICA MANUFACTURING INC EAST LIBERTY Ohio 43319 29.45 Retain

EFCO CORP MONETT Missouri 65708 29.234 Retain

GREIF PACKAGING LLC FLORENCE Kentucky 41042 27.5305 Retain

BALL METAL BEVERAGE CONTAINER CORP TAMPA Florida 33617 27 Retain

NISSAN NORTH AMERICA INC CANTON MS CANTON Mississippi 39046 26.619 Retain

CHRYSLER JEFFERSON NORTH ASSEMBLY PLANT DETROIT Michigan 48215 26.5 Retain

NYW REALTY LLC/ HANOVER HANOVER Pennsylvania 17331 25.986 Retain

EDSAL MANUFACTURING CO INC CHICAGO Illinois 60609 25.7385 Retain

CROWN BEVERAGE PACKAGING BATESVILLE Mississippi 38606 25.251 Retain

CROWN BEVERAGE PACKAGING LA CROSSE Wisconsin 54603 24.5255 Retain

SAPA EXTRUSIONS INC YANKTON South Dakota 57078 24.4475 Retain

MAGNA STEYR NORTH AMERICA TOLEDO Ohio 43608 23.95 Retain

AIR SYSTEM COMPONENTS LP PONCA CITY Oklahoma 74601 23.856 Retain

MOBIL CHEMICAL CO SHAWNEE Oklahoma 74804 23.375 Retain

Page 1 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

WHIRLPOOL CORP FINDLAY DIV FINDLAY Ohio 45840 22.8465 Retain

S B FOOT TANNING CO RED WING Minnesota 55066 22.8265 Retain

CROWN BEVERAGE PACKAGING CHERAW South Carolina 29520 22.1215 Retain

SUBARU OF INDIANA AUTOMOTIVE INC LAFAYETTE Indiana 47905 22.12 Retain

BATESVILLE MANUFACTURING INC MANCHESTER Tennessee 37355 21.7615 Retain

MEMC PASADENA INC PASADENA Texas 77503 20.685 Retain

BWAY CORP HOMERVILLE Georgia 31634 19.6085 Retain

BALL METAL BEVERAGE CONTAINER CORP CONROE Texas 77303 18.6 Retain

SPECTRUM METAL FINISHING YOUNGSTOWN Ohio 44512 18.42 Retain

ROLL COATER INC GREENFIELD Indiana 46140 18.351 Retain

BALL METAL BEVERAGE CONTAINER CORP SARATOGA SPRINGS New York 12866 18.3 Retain

DEXTER CHASSIS GROUP PLANT 55 WHITE PIGEON Michigan 49099 18.265 Retain

GM SPRING HILL MANUFACTURING SPRING HILL Tennessee 37174 18.175 Retain

OLDCASTLE BUILDING ENVELOPE TEXAS FACILITY TERRELL Texas 75160 17.65 Retain

UNION CARBIDE CORP SEADRIFT PLANT SEADRIFT Texas 77983 17.0355 Retain

HONDA MANUFACTURING OF ALABAMA LLC LINCOLN Alabama 35096 16.753 Retain

NUCOR VULCRAFT GROUP GRAPELAND DIV GRAPELAND Texas 75844 16.437 Retain

NORTH COAST CONTAINER CORP CLEVELAND Ohio 44105 16.0815 Retain

TOYOTA MOTOR MANUFACTURING INDIANA INC PRINCETON Indiana 47670 16.069 Retain

ALLIED TUBE & CONDUIT CORP HARVEY Illinois 60426 15.9335 Retain

NOVELIS CORP WARREN Ohio 44483 15.922 Retain

PPG INDUSTRIES INC-OAK CREEK OAK CREEK Wisconsin 53154 15.854 Retain

METAL INDUSTRIES INC - BUSHNELL BUSHNELL Florida 33513 15.8185 Retain

BOEING COMMERCIAL AIRPLANE GROUP - EVERETT EVERETT Washington 98204 15.6 Retain

HAMMER PACKAGING CORP WEST HENRIETTA New York 14586 15.118 Retain

S D WARREN CO WESTBROOK Maine 04098 15.0015 Retain

AIR SYSTEM COMPONENTS LP TARBORO North Carolina 27886 14.9185 Retain

SEIDEL TANNING CORP MILWAUKEE Wisconsin 53212 14.8525 Retain

PELLA CORP PELLA Iowa 50219 14.569 Retain

BALL CONTAINER LLC FORT ATKINSON Wisconsin 53538 14.55 Retain

ALCOA INC - WARRICK OPERATIONS NEWBURGH Indiana 47629 14.5275 Retain

L A DARLING CO - PIGGOTT AR FACILITY PIGGOTT Arkansas 72454 14.37 Retain

HART & COOLEY INC HUNTSVILLE Alabama 35811 14.2525 Retain

JOHNSON WELDED PRODUCTS INC URBANA Ohio 43078 14.069 Retain

REXAM BEVERAGE CAN CO FAIRFIELD PLANT FAIRFIELD California 94533 13.981 Retain

EASTMAN CHEMICAL CO TEXAS OPERATIONS LONGVIEW Texas 75602 13.8 Retain

MUELLER CO ALBERTVILLE Alabama 35950 13.784 Retain

CROWN BEVERAGE PACKAGING CRAWFORDSVILLE Indiana 47933 13.7785 Retain

ALSTOM POWER INC PLATE FORMED PRODUCTS DIV CHATTANOOGA Tennessee 37402 13.7535 Retain

PRECOAT METALS JACKSON Mississippi 39272 13.624 Retain

KNAPHEIDE MANUFACTURING CO QUINCY Illinois 62305 13.111 Retain

BEMIS MANUFACTURING CO PLANT B SHEBOYGAN FALLS Wisconsin 53085 13.105 Retain

BALL METAL BEVERAGE CONTAINER CORP MIDDLETOWN New York 10940 13 Retain

BALL METAL BEVERAGE CONTAINER CORP FORT WORTH Texas 76140 13 Retain

CAN CORP OF AMERICA INC BLANDON Pennsylvania 19510 12.769 Retain

SILGAN CONTAINERS MANUFACTURING CORP MOUNT VERNON Missouri 65712 12.7475 Retain

BALL METAL BEVERAGE CONTAINER CORP KAPOLEI Hawaii 96707 12.7 Retain

AUTOALLIANCE INTERNATIONAL INC FLAT ROCK Michigan 48134 12.6 Retain

BEDFORD MATERIALS CO INC MANNS CHOICE Pennsylvania 15550 12.572 Retain

QUAD/GRAPHICS INC HARTFORD Wisconsin 53027 12.4 Retain

GENERAL MOTORS CORP LORDSTOWN COMPLEX LORDSTOWN Ohio 44481 12.22 Retain

MERCEDES-BENZ US INTERNATIONAL INC VANCE Alabama 35490 12.209 Retain

FORD LOUISVILLE ASSEMBLY LOUISVILLE Kentucky 40213 12.125 Retain

MODINE MANUFACTURING CO INC HARRODSBURG Kentucky 40330 12.019 Retain

M&B HANGERS LEEDS Alabama 35094 11.995 Retain

CROWN FOOD PACKAGING HANOVER Pennsylvania 17331 11.4075 Retain

TOKICO (USA) INC BEREA Kentucky 40403 11.303 Retain

NUCOR CORP VULCRAFT/NUCOR COLD FINISH DIV NORFOLK Nebraska 68701 11.3 Retain

AKZO NOBEL COATINGS INC BIRMINGHAM Alabama 35234 11.2995 Retain

MEADWESTVACO CONSUMER PACKAGING GROUP LLC MEBANE North Carolina 27302 11.2585 Retain

CROWN FOOD PACKAGING TOLEDO Ohio 43612 11.215 Retain

AMERICAN TRIM LLC SIDNEY Ohio 45365 11.167 Retain

GEA BPO LLC BLOOMINGTON Indiana 47404 11.046 Retain

GERSTENSLAGER CO WOOSTER Ohio 44691 10.837 Retain

BROAN-NUTONE LLC HARTFORD Wisconsin 53027 10.75 Retain

POWER PARTNERS INC ATHENS Georgia 30607 10.75 Retain

VESTAL MANUFACTURING ENTERPRISES INC SWEETWATER Tennessee 37874 10.7105 Retain

FRANKLIN INVESTMENT CORP FRANKLIN Pennsylvania 16323 10.7 Retain

CECO DOOR PRODUCTS MILAN Tennessee 38358 10.578 Retain

INGERSOLL-RAND CO STEELCRAFT DIV CINCINNATI Ohio 45242 10.48 Retain

TRI VULCRAFT OF NEW YORK INC CHEMUNG New York 14825 10.322 Retain

MEYER STEEL DRUM INC CHICAGO Illinois 60623 10.2385 Retain

Page 2 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

BALL AEROSOL & SPECIALTY CONTAINER INC ELGIN Illinois 60120 10.15 Retain

CARDONE INDUSTRIES PHILADELPHIA Pennsylvania 19120 10.1045 Retain

KAWNEER CO INC SPRINGDALE Arkansas 72764 10.0795 Retain

MAYFLOWER VEHICLE SYSTEMS INC NORWALK FACILITY NORWALK Ohio 44857 10 Retain

YKK AP AMERICA INC DUBLIN Georgia 31021 9.892 Retain

RR DONNELLEY CRAWFORDSVILLE CRAWFORDSVILLE Indiana 47933 9.892 Retain

BERENFIELD CONTAINERS SW LTD WHITE HALL Arkansas 71602 9.8915 Retain

KEYMARK CORP OF FLORIDA LAKELAND Florida 33810 9.8475 Retain

LAKESIDE LITHOGRAPHY LLC CHICAGO Illinois 60608 9.75 Retain

ROYAL MOULDINGS LTD; MARION VIRGINIA MARION Virginia 24354 9.553 Retain

HEWLETT-PACKARD CARIBE BV SITE AGUADILLA Puerto Rico 00605 9.53 Retain

3M CO - GUIN GUIN Alabama 35563 9.501 Retain

STANLEY WORKS HAND TOOLS DIV NEW BRITAIN Connecticut 06052 9.46 Retain

NUCOR CORP VULCRAFT DIV FLORENCE South Carolina 29501 9.4365 Retain

AVX CORP MYRTLE BEACH MYRTLE BEACH South Carolina 29577 9.3805 Retain

HEXION SPECIALTY CHEMICALS INC LAKELAND Florida 33801 9.34 Retain

EPCO EXTRUSION PAINTING CO BOARDMAN Ohio 44512 9.2125 Retain

QUAD/GRAPHICS INC SUSSEX Wisconsin 53089 9.2 Retain

SILGAN CONTAINERS MANUFACTURING CORP SAINT JOSEPH Missouri 64504 9.19 Retain

KUBIN-NICHOLSON CORP MILWAUKEE Wisconsin 53224 9.148 Retain

SILGAN CAN CO MAXTON North Carolina 28364 9.125 Retain

SILGAN CAN CO NAPOLEON Ohio 43545 9.009 Retain

SQUARE D CO LEXINGTON Kentucky 40511 9.0085 Retain

HESS PRINT SOLUTIONS BRIMFIELD Ohio 44240 9 Retain

CROWN AEROSOL PACKAGING AURORA Illinois 60504 8.8715 Retain

SILGAN CONTAINERS MANAUFACTURING CORP OCONOMOWOC Wisconsin 53066 8.8 Retain

GENERAL MOTORS LANSING DELTA TOWNSHIP LANSING Michigan 48917 8.73 Retain

TOPPAN INTERAMERICA INC MC DONOUGH Georgia 30253 8.7 Retain

SILGAN WHITE CAP CORP EVANSVILLE Indiana 47710 8.65 Retain

TOYOTA MOTOR MANUFACTURING TEX AS INC SAN ANTONIO Texas 78264 8.625 Retain

FORD MOTOR COMPANY-WAYNE ASSEMBLY WAYNE Michigan 48184 8.585 Retain

MAYTAG CORP CLEVELAND COOKING PRODUCTS PLANT 1 CLEVELAND Tennessee 37311 8.5585 Retain

SANYO SOLAR (USA) LLC CARSON California 90745 8.482 Retain

RR DONNELLEY & SONS CO WILLARD Ohio 44890 8.4475 Retain

SIGNODE BRIDGEVIEW Illinois 60455 8.4 Retain

BERENFIELD CONTAINERS INC CLARENDON Pennsylvania 16313 8.368 Retain

MASTERBRAND CABINETS INC ARTHUR Illinois 61911 8.25 Retain

SILGAN CAN CO PARIS Texas 75460 8.162 Retain

BERENFIELD CONTAINERS INC MASON MASON Ohio 45040 7.883 Retain

LA-Z-BOY TENNESSEE DAYTON Tennessee 37321 7.823 Retain

DECORATIVE PANELS INTERNATIONA L TOLEDO Ohio 43607 7.608 Retain

GREIF PACKAGING LLC MERCED California 95348 7.557 Retain

GM TRUCK GROUP FORT WAYNE ASSEMBLY ROANOKE Indiana 46783 7.475 Retain

WHITING DOOR MANUFACTURING CORP AKRON New York 14001 7.4105 Retain

HOWARD FINISHING LLC MADISON HEIGHTS Michigan 48071 7.358 Retain

SILGAN CONTAINERS MANUFACTURING CORP EDISON New Jersey 08817 7.35 Retain

GM ORION ASSEMBLY CENTER ORION Michigan 48359 7.3 Retain

BWAY CORP CHICAGO Illinois 60623 7.2515 Retain

SILGAN CONTAINERS MANUFACTURING CORP MENOMONIE Wisconsin 54751 7.25 Retain

NASHVILLE WIRE PRODUCTS NASHVILLE Tennessee 37218 7.2 Retain

CHICAGO STEEL CONTAINER CORP CHICAGO Illinois 60623 7.19 Retain

SHIELDCOAT TECHNOLOGIES INC (DBA CYBERSHIELD OF 

TEXAS)

LUFKIN Texas 75904 7.1205 Retain

WIX FILTRATION CORP - ALLEN PLANT GASTONIA North Carolina 28052 7.1025 Retain

RR DONNELLEY LANCASTER WEST LANCASTER Pennsylvania 17601 7.0965 Retain

NUCOR CORP VULCRAFT DIV FORT PAYNE Alabama 35967 6.923 Retain

GREIF PACKAGING LLC NEW ORLEANS Louisiana 70123 6.8535 Retain

SONOCO PHOENIX - PRESIDENTS ISLAND MEMPHIS Tennessee 38113 6.841 Retain

ACME FINISHING CO INC ELK GROVE VILLAGE Illinois 60007 6.794 Retain

EQUISTAR CHEMICALS BAYPORT CHEMICALS PLANT PASADENA Texas 77507 6.7625 Retain

COLOR COMMUNICATIONS INC CHICAGO Illinois 60624 6.7335 Retain

CHRYSLER WARREN TRUCK ASSEMBLY PLANT (PART) WARREN Michigan 48091 6.7 Retain

IMPRESS USA INC TERMINAL ISLAND California 90731 6.7 Retain

BERENFIELD CONTAINERS SE LTD HARRISBURG North Carolina 28075 6.6745 Retain

GMVM-LANSING GRAND RIVER ASSEMBLY LANSING Michigan 48921 6.65 Retain

KITZINGER COOPERAGE CORP SAINT FRANCIS Wisconsin 53235 6.6085 Retain

ARMSTRONG HARDWOOD FLOORING CO ONEIDA Tennessee 37841 6.568 Retain

HIRSH INDUSTRIES INC DOVER Delaware 19904 6.516 Retain

WORLDCOLOR - DYERSBURG DIV DYERSBURG Tennessee 38024 6.3705 Retain

ESCO CORP NEWTON Mississippi 39345 6.312 Retain

JOHN DEERE HARVESTER WORKS EAST MOLINE EAST MOLINE Illinois 61244 6.29 Retain

QUEBECOR WORLD DIRECT-PETTY EFFINGHAM Illinois 62401 6.155 Retain

Page 3 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

PACKAGING DYNAMICS INC BAGCRAFT/PAPERCON DIV BAXTER SPRINGS Kansas 66713 6.15 Retain

GMTG - SHREVEPORT ASSEMBLY SHREVEPORT Louisiana 71129 6.105 Retain

SENECA FOODS CORP CAN PLANT MARION New York 14505 6.103 Retain

CARRY-ON TRAILER CORP MISSOURI VALLEY Iowa 51555 6.013 Retain

SILGAN CONTAINERS MANUFACTURING CORP HAMMOND Indiana 46320 6 Retain

METOKOTE CORP PLANT 15 CEDAR FALLS Iowa 50613 5.991 Retain

ELECTROPRIME INC ROSSFORD Ohio 43460 5.952 Retain

NUCOR VULCRAFT GROUP SAINT JOE DIV SAINT JOE Indiana 46785 5.906 Retain

QUAD/GRAPHICS INC SARATOGA SPRINGS New York 12866 5.9 Retain

FIBERMARK NORTH AMERICA INC LOWVILLE New York 13367 5.8595 Retain

BRADFORD WHITE CORP MIDDLEVILLE Michigan 49333 5.837 Retain

TECNOCAP LLC WARREN Ohio 44483 5.7945 Retain

VON HOFFMANN GRAPHICS INC OWENSVILLE Missouri 65066 5.7815 Retain

HUNTER DOUGLAS TUPELO CENTER SHANNON Mississippi 38868 5.7565 Retain

CROWN FOOD PACKAGING WINTER GARDEN Florida 34787 5.754 Retain

U.S. AIR FORCE TINKER AFB OK TINKER A F B Oklahoma 73145 5.75 Retain

RR DONNELLEY LANCASTER EAST LANCASTER Pennsylvania 17601 5.6915 Retain

ROLL COATER INC WEIRTON West Virginia 26062 5.684 Retain

CNH AMERICA LLC BURLINGTON Iowa 52601 5.675 Retain

HUSQVARNA CONSUMER OUTDOOR PRODUCTS ORANGEBURG South Carolina 29116 5.64 Retain

NAVISTAR INC SPRINGFIELD Ohio 45502 5.6 Retain

PRECOAT METALS GRANITE CITY Illinois 62040 5.559 Retain

LOGAN ALUMINUM INC RUSSELLVILLE Kentucky 42276 5.544 Retain

PPG INDUSTRIES,INC-SPRINGDALE COMPLEX SPRINGDALE Pennsylvania 15144 5.524 Retain

GREIF PACKAGING LLC ALSIP Illinois 60803 5.5095 Retain

USS - CLAIRTON WORKS CLAIRTON Pennsylvania 15025 5.5 Retain

CREE INC DURHAM North Carolina 27703 5.4965 Retain

TOYOTA MOTOR MANUFACTURING KENTUCKY INC GEORGETOWN Kentucky 40324 5.475 Retain

PRIME TANNING CO - HARTLAND HARTLAND Maine 04943 5.435 Retain

NAZDAR SHAWNEE SHAWNEE Kansas 66227 5.4105 Retain

BALL METAL FOOD CONTAINER CORP OAKDALE California 95361 5.4 Retain

OWENS CORNING VETROTEX LLC STARR South Carolina 29684 5.3545 Retain

NEW MILLENNIUM BUILDING SYSTEMS SALEM Virginia 24153 5.296 Retain

MID CONTINENT CABINETRY COTTONWOOD Minnesota 56229 5.2865 Retain

AVERY DENNISON - IBMD LENOIR LENOIR North Carolina 28645 5.286 Retain

SILGAN CAN CO SACRAMENTO California 95824 5.271 Retain

WORTHINGTON CYLINDERS WISCONSI N LLC CHILTON Wisconsin 53014 5.258 Retain

ENKEI AMERICA INC COLUMBUS Indiana 47201 5.25 Retain

NOVOLYTE TECHNOLOGIES ZACHARY Louisiana 70791 5.145 Retain

METAL COATERS MISSISSIPPI JACKSON Mississippi 39272 5.1255 Retain

MEDALLION CABINETRY INC WACONIA Minnesota 55387 5.0815 Retain

PRECOAT METALS HOUSTON Texas 77015 5.075 Retain

TRAD NA INC HOPKINSVILLE Kentucky 42240 5.07 Retain

GREENWICH INDUSTRIES LP CLARIN DIV LAKE BLUFF Illinois 60044 5.058 Retain

ROLL COATER LA PORTE Indiana 46350 5.028 Retain

CIRCLE GRAPHICS INC LONGMONT Colorado 80501 4.95 Retain

SCHAEFFER MANUFACTURING SAINT LOUIS Missouri 63104 4.8465 Screened Out

ASHLEY INDUSTRIAL MOLDING INC ASHLEY Indiana 46705 4.825 Screened Out

US ARMY LAKE CITY ARMY AMMUNITION PLANT INDEPENDENCE Missouri 64051 4.7265 Screened Out

INX DIGITAL INK CO DIXON California 95620 4.7155 Screened Out

NAHAN PRINTING INC SAINT CLOUD Minnesota 56303 4.709 Screened Out

AAP ST MARYS CORP SAINT MARYS Ohio 45885 4.6885 Screened Out

ZURN INDUSTRIES LLC ERIE Pennsylvania 16502 4.674 Screened Out

ALCOA HOME EXTERIORS INC SIDNEY Ohio 45365 4.6175 Screened Out

ARVINMERITOR HEAVY VEHICLE SYSTEMS LLC YORK South Carolina 29745 4.5795 Screened Out

GENERAL MOTORS WENTZVILLE ASSEMBLY WENTZVILLE Missouri 63385 4.5 Screened Out

RUSKIN CO GENEVA Alabama 36340 4.4905 Screened Out

ALLIANCE INDUSTRIES WAUPACA WAUPACA Wisconsin 54981 4.4685 Screened Out

GENIE INDUSTRIES SOUTH CAMPUS REDMOND Washington 98052 4.415 Screened Out

SABIC INNOVATIVE PLASTICS MT VERNON LLC MOUNT VERNON Indiana 47620 4.4 Screened Out

ENDICOTT INTERCONNECT TECHNOLOGIES INC ENDICOTT New York 13760 4.3655 Screened Out

BROWN PRINTING CO WASECA Minnesota 56093 4.3235 Screened Out

BALL METAL BEVERAGE CONTAINER CORP KANSAS CITY Missouri 64120 4.24 Screened Out

BATESVILLE MANUFACTURING INC BATESVILLE Mississippi 38606 4.23 Screened Out

GREIF PACKAGING LLC LA PORTE Texas 77571 4.2185 Screened Out

SILGAN CONTAINERS MANUFACTURING CORP MENOMONEE FALLS Wisconsin 53051 4.2 Screened Out

SEQUA COATINGS CORP-PRECOAT M ETALS DIV PORTAGE Indiana 46368 4.182 Screened Out

R R DONNELLEY & SONS CO DANVILLE DIV DANVILLE Kentucky 40422 4.1565 Screened Out

BROWN PRINTING CO WOODSTOCK Illinois 60098 4.125 Screened Out

SILGAN CONTAINER MANUFACTURING CORP RIVERBANK California 95367 4.1055 Screened Out

QUEBECOR WORLD OLIVE BRANCH Mississippi 38654 4.097 Screened Out

VAN CAN CO FONTANA California 92337 4.05 Screened Out

Page 4 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

WORLDCOLOR STILLWATER (WAS QUEBECOR WORLD - 

STILLWATER DIV)

STILLWATER Oklahoma 74075 3.9275 Screened Out

PRO LINE PRINTING ARLINGTON ARLINGTON Texas 76011 3.9255 Screened Out

AGY AIKEN LLC AIKEN South Carolina 29801 3.88 Screened Out

ALERIS ROLLED PRODUCTS INC LEWISPORT Kentucky 42351 3.8235 Screened Out

NESTLE PURINA PETCARE WEIRTON West Virginia 26062 3.802 Screened Out

RR DONNELLEY LOS ANGELES MANUFACTURING TORRANCE California 90502 3.7925 Screened Out

BROWN PRINTING CO EAST GREENVILLE Pennsylvania 18041 3.7365 Screened Out

INLAND LABEL & MARKETING LA CROSSE Wisconsin 54601 3.7245 Screened Out

AFTON CHEMICAL CORP ORANGEBURG South Carolina 29115 3.705 Screened Out

PHOENIX CONTAINER INC NORTH BRUNSWICK New Jersey 08902 3.6765 Screened Out

BETCO CORP TOLEDO Ohio 43607 3.674 Screened Out

FUJIFILM NORTH AMERICA CORP NORTH KANSAS CITY Missouri 64116 3.547 Screened Out

AVERY DENNISON INDUSTRIAL PRODUCTS DIV STRONGSVILLE Ohio 44149 3.535 Screened Out

BATESVILLE MANUFACTURING INC -DOLL PLANT BATESVILLE Indiana 47006 3.504 Screened Out

MERIX CORP FOREST GROVE Oregon 97116 3.485 Screened Out

SCHWAN'S GLOBAL SUPPLY CHAIN - SALINA KS SALINA Kansas 67401 3.4845 Screened Out

BWAY CORP BWAY PACKAGING DIV CINCINNATI Ohio 45244 3.48 Screened Out

FORD MOTOR CO TWIN CITIES ASSEMBLY PLANT SAINT PAUL Minnesota 55116 3.41 Screened Out

TTM PRINTED CIRCUIT GROUP - S TAFFORD DIV STAFFORD Connecticut 06075 3.403 Screened Out

PONTIAC ASSEMBLY CENTER PONTIAC Michigan 48341 3.385 Screened Out

BON L MANUFACTURING CO KENTLAND Indiana 47951 3.38 Screened Out

WORLDCOLOR LEBANON DIV LEBANON Ohio 45036 3.376 Screened Out

QUEBECOR WORLD INC WINCHESTER VIRGINIA WINCHESTER Virginia 22603 3.3515 Screened Out

SILGAN CONTAINERS MANUFACTURING CORP LYONS New York 14489 3.3 Screened Out

KAWASAKI MOTORS MANUFACTURING CORP USA LINCOLN Nebraska 68524 3.196 Screened Out

TYCO FIRE SUPPRESSION & BUILDING PRODUCTS MARINETTE Wisconsin 54143 3.1955 Screened Out

CROWN FOOD PACKAGING PORTLAND Oregon 97203 3.1635 Screened Out

CROWN EQUIPMENT CORP GREENCASTLE Indiana 46135 3.104 Screened Out

SILGAN CONTAINERS MANUFACTURING CORP ROCHELLE Illinois 61068 3.0715 Screened Out

DISC GRAPHICS HAUPPAUGE New York 11788 2.97 Screened Out

ACCESS BUSINESS GROUP LLC ADA Michigan 49355 2.947 Screened Out

ITW DYMON OLATHE Kansas 66061 2.9415 Screened Out

MAXIM INTEGRATED PRODUCTS INC SAN ANTONIO Texas 78251 2.9395 Screened Out

SAPA EXTRUDER INC GAINESVILLE Georgia 30504 2.926 Screened Out

PRECOAT METALS HUEYTOWN Alabama 35023 2.8985 Screened Out

VERTIS COMMUNICATIONS COLUMBUS Ohio 43228 2.88 Screened Out

MAUSER CORP WOODBRIDGE New Jersey 07095 2.877 Screened Out

CURTIS METAL FINISHING CO STERLING HEIGHTS Michigan 48313 2.852 Screened Out

TITAN COATINGS INC BESSEMER Alabama 35023 2.85 Screened Out

EQ DETROIT INC DETROIT Michigan 48211 2.8215 Screened Out

BALL METAL FOOD CONTAINER CORP SPRINGDALE Arkansas 72764 2.815 Screened Out

MAXIM INTEGRATED PRODUCTS INC SAN JOSE California 95134 2.785 Screened Out

3M CO - HUTCHINSON HUTCHINSON Minnesota 55350 2.767 Screened Out

WORLDCOLOR ATGLEN ATGLEN Pennsylvania 19310 2.704 Screened Out

RR DONNELLEY STRASBURG DIV STRASBURG Virginia 22657 2.7 Screened Out

DOW CHEMICAL CO MIDLAND Michigan 48667 2.695 Screened Out

CENTRIA CAMBRIDGE Ohio 43725 2.6515 Screened Out

MISSION KLEENSWEEP PRODUCTS INC LOS ANGELES California 90031 2.6 Screened Out

SOLIANT LLC LANCASTER South Carolina 29721 2.561 Screened Out

GREIF INDUSTRIAL PACKAGING & SERVICES WINFIELD Kansas 67156 2.5505 Screened Out

U.S. AIR FORCE ROBINS AFB GA ROBINS AFB Georgia 31098 2.527 Screened Out

KNS COMPANYS INC CAROL STREAM Illinois 60188 2.5185 Screened Out

TEXAS FINISHING CO CARROLLTON Texas 75006 2.4885 Screened Out

WORLDCOLOR CLARKSVILLE Tennessee 37040 2.47 Screened Out

AK STEEL CORP - ZANESVI LLE WORKS ZANESVILLE Ohio 43701 2.45 Screened Out

BRUNSWICK CORP MERCURY MARINE DIV FOND DU LAC Wisconsin 54935 2.424 Screened Out

DENSO MANUFACTURING TENNESSEE INC MARYVILLE Tennesee 37801 2.3935 Screened Out

BRILLION IRON WORKS INC BRILLION Wisconsin 54110 2.392 Screened Out

MASTER GUARD CORP VEEDERSBURG Indiana 47987 2.373 Screened Out

SANFORD LP SHELBYVILLE Tennessee 37160 2.351 Screened Out

ROPPE CORP FOSTORIA Ohio 44830 2.3295 Screened Out

AMERICAN COLOR GRAPHICS INC YORK Pennsylvania 17404 2.3125 Screened Out

SUN CHEMICAL CORP SAINT CHARLES Illinois 60174 2.2915 Screened Out

3M CO - BROWNWOOD BROWNWOOD Texas 76801 2.265 Screened Out

KIK (HOUSTON) INC HOUSTON Texas 77054 2.265 Screened Out

SAFETY-KLEEN SYSTEMS INC LEXINGTON South Carolina 29073 2.216 Screened Out

MPM SILICONES LLC FRIENDLY West Virginia 26146 2.2095 Screened Out

KAWNEER CO INC HERNANDO Mississippi 38632 2.207 Screened Out

BON L MANUFACTURING CO CARTHAGE Tennessee 37030 2.205 Screened Out

AMERICAN COLOR GRAPHICS - LUFKIN LUFKIN Texas 75901 2.181 Screened Out

LEHIGH PRESS CADILLAC (DBA LEHIGH DIRECT DIVISION) BROADVIEW Illinois 60153 2.125 Screened Out

Page 5 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

MACDERMID PRINTING SOLUTIONS SAN MARCOS California 92078 2.122 Screened Out

UNION CARBIDE CORP SOUTH CHARLESTON FACILITY SOUTH CHARLESTON West Virginia 25303 2.1175 Screened Out

THREE RIVERS ALUMINUM CO CRANBERRY TOWNSHIP Pennsylvania 16066 2.11 Screened Out

NCP COATINGS INC NILES Michigan 49120 2.1075 Screened Out

PRECOAT METALS SAINT LOUIS Missouri 63116 2.093 Screened Out

VERTIS COMMUNICATIONS CHARLOTTE North Carolina 28273 2.056 Screened Out

DUPONT YERKES PLANT BUFFALO New York 14207 2.053 Screened Out

TORO CO TOMAH Wisconsin 54660 2.0475 Screened Out

CADON PLATING CO WYANDOTTE Michigan 48192 2.036 Screened Out

AVX CORP CONWAY CONWAY South Carolina 29526 1.973 Screened Out

SILGAN CONTAINERS MANUFACTURING CORP ANTIOCH California 94509 1.9645 Screened Out

STEELSCAPE INC FAIRFIELD Alabama 35064 1.954 Screened Out

BASF CORP - CLEAR LAKE PLANT PASADENA Texas 77507 1.9505 Screened Out

BOEING COMMERCIAL AIRPLANE GROUP NORTH BOEING FIELD 

(PART)

SEATTLE Washington 98108 1.95 Screened Out

RR DONNELLEY PINEVILLE PINEVILLE North Carolina 28134 1.948 Screened Out

TREND OFFSET PRINTING SERVICES INC LOS ALAMITOS California 90720 1.925 Screened Out

WARREN UNILUBE INC WEST MEMPHIS Arkansas 72301 1.9155 Screened Out

HYUNDAI MOTOR MANUFACTURING ALABAMA LLC MONTGOMERY Alabama 36105 1.8995 Screened Out

PRIOR COATED METALS ALLENTOWN Pennsylvania 18103 1.886 Screened Out

KEYMARK CORP FONDA New York 12068 1.8835 Screened Out

BUCKEYE INTERNATIONAL INC MARYLAND HEIGHTS Missouri 63043 1.8765 Screened Out

AMERICAN COLOR GRAPHICS MARENGO Iowa 52301 1.8675 Screened Out

IMPRESS USA INC WEIRTON West Virginia 26062 1.8185 Screened Out

ASTRO COATINGS INC STRUTHERS Ohio 44471 1.8 Screened Out

CUMMINS POWER GENERATION FRIDLEY Minnesota 55432 1.79 Screened Out

CENTURY INDUSTRIAL COATINGS I NC JACKSONVILLE Texas 75766 1.779 Screened Out

FORD MOTOR CO - OHIO ASSEMBLY PLANT AVON LAKE Ohio 44012 1.77 Screened Out

REICHHOLD INC PENSACOLA Florida 32502 1.7345 Screened Out

J&M MANUFACTURING CO INC FORT RECOVERY Ohio 45846 1.7285 Screened Out

HANNA STEEL CORP FAIRFIELD Alabama 35064 1.7175 Screened Out

RR DONNELLEY CHARLESTOWN Indiana 47111 1.7085 Screened Out

BOEING COMMERCIAL AIRPLANE GROUP - RENTON RENTON Washington 98055 1.7035 Screened Out

GMC TRUCK GROUP ARLINGTON ASSEMBLY PLANT ARLINGTON Texas 76010 1.7 Screened Out

PRO LINE PRINTING / RR DONNELLEY RENO Nevada 89512 1.679 Screened Out

RR DONNELLEY VON HOFFMANN CORP JEFFERSON CITY Missouri 65109 1.6575 Screened Out

COMPLEMENTARY COATINGS CORP EDGEWATER Florida 32132 1.639 Screened Out

WORLD COLOR PRESS TAUNTON Massachusetts 02780 1.637 Screened Out

CHRYSLER STERLING HEIGHTS ASSEMBLY PLANT STERLING HEIGHTS Michigan 48312 1.6 Screened Out

COLOR CORP OF AMERICA LOUISVILLE Kentucky 40210 1.59 Screened Out

U.S. AIR FORCE OGDEN AIR LOGISTICS CENTER HILL AFB Utah 84056 1.5525 Screened Out

AKZONOBEL AEROSPACE COATINGS WAUKEGAN Illinois 60085 1.5515 Screened Out

ST CHARLES OPERATIONS (TAFT/STAR) UNION CARBIDE CORP TAFT Louisiana 70057 1.545 Screened Out

MERCK SHARP & DOHME CORP ELKTON Virginia 22827 1.51 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

KANKAKEE Illinois 60901 1.5035 Screened Out

BENCHMARK ENERGY PRODUCTS LLC MIDLAND Texas 79703 1.4975 Screened Out

IVC INDUSTRIAL COATINGS INC INDIANAPOLIS Indiana 46218 1.4785 Screened Out

VANEX INC MOUNT VERNON Illinois 62864 1.467 Screened Out

SAPA INC COATINGS DIVSION PORTLAND Oregon 97218 1.4665 Screened Out

MOTOR CASTINGS CO MILWAUKEE Wisconsin 53214 1.466 Screened Out

NOV TUBOSCOPE WEST LITTLE YORK COATING HOUSTON Texas 77041 1.4635 Screened Out

ARANDELL CORP MENOMONEE FALLS Wisconsin 53051 1.451 Screened Out

WHEELING CORRUGATING CO - BEECH BOTTOM PLANT WELLSBURG West Virginia 26070 1.45 Screened Out

CARDINAL ALUMINUM CO PLAN T 3 LOUISVILLE Kentucky 40219 1.4355 Screened Out

GREIF INDUSTRIAL PACKAGING & SERVICES LLC FONTANA California 92335 1.433 Screened Out

DECOSTAR INDUSTRIES INC CARROLLTON Georgia 30117 1.432 Screened Out

ALERIS ROLLED PRODUCTS INC ASHVILLE Ohio 43103 1.416 Screened Out

MITSUBISHI MOTORS NORTH AMERICA INC NORMAL Illinois 61761 1.4135 Screened Out

CAMACO COLUMBUS MANUFACTURING COLUMBUS Nebraska 68601 1.4005 Screened Out

EASTMAN CHEMICAL CO TENNESSEE OPERATIONS KINGSPORT Tennessee 37662 1.3975 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

ROCHESTER Pennsylvania 15074 1.3895 Screened Out

W W HENRY BOURBONNAIS Illinois 60914 1.3725 Screened Out

JOHN DEERE SEEDING & CYLINDER MOLINE Illinois 61265 1.353 Screened Out

CROWN AEROSOL PACKAGING FARIBAULT Minnesota 55021 1.3495 Screened Out

GM MLCG FAIRFAX ASSEMBLY KANSAS CITY Kansas 66115 1.3175 Screened Out

ARR-MAZ CUSTOM CHEMICALS MULBERRY Florida 33860 1.313 Screened Out

SILGAN WHITE CAP CORP HAZLETON Pennsylvania 18201 1.3 Screened Out

AKZO NOBEL COATINGS INC COLUMBUS Ohio 43211 1.3 Screened Out

ARMSTRONG WORLD INDUSTRIES LANCASTER PLANT LANCASTER Pennsylvania 17603 1.29 Screened Out

Page 6 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

GENERAL MOTORS MLCG DETROIT-HAMTRAMCK ASSEM BLY 

CENTER

DETROIT Michigan 48211 1.29 Screened Out

HALLSTAR CO ESTER SOLUTIONS FACILITY BEDFORD PARK Illinois 60638 1.2635 Screened Out

DAIMLERCHRYSLER CORP TOLEDO ASSEMBLY PLANT TOLEDO Ohio 43612 1.255 Screened Out

SHEBOYGAN PAINT CO CEDARTOWN Georgia 30125 1.241 Screened Out

RR DONNELLEY & SONS CO AVON Connecticut 06001 1.2325 Screened Out

CONSOLIDATED SYSTEMS INC COLUMBIA South Carolina 29201 1.23 Screened Out

CHRYSLER BELVIDERE ASSEMBLY PLANT BELVIDERE Illinois 61008 1.22 Screened Out

DURA COAT PRODUCTS INC MADISON Alabama 35756 1.217 Screened Out

CLEVELAND STEEL CONTAINER - NI LES NILES Ohio 44446 1.2045 Screened Out

TTM TECHNOLOGIES INC LOGAN Utah 84321 1.199 Screened Out

CCL CONTAINER AEROSOL DIV HERMITAGE Pennsylvania 16148 1.189 Screened Out

CATERPILLAR INC LAFAYETTE Indiana 47905 1.175 Screened Out

WINSLOW-BROWNING INC LIBERTY Indiana 47353 1.148 Screened Out

J L CLARK INC ROCKFORD Illinois 61104 1.1455 Screened Out

CHEMTURA CORP - TAFT PLANT KILLONA Louisiana 70066 1.1455 Screened Out

NOV TUBOSCOPE NAVASOTA NAVASOTA Texas 77868 1.1425 Screened Out

PRECOAT METALS ELKRIDGE Maryland 21075 1.1415 Screened Out

NICHOLS ALUMINUM ALABAMA INC DECATUR Alabama 35601 1.1375 Screened Out

GENTEK BUILDING PRODUCTS AVENEL New Jersey 07001 1.1335 Screened Out

OHIO ART CO BRYAN Ohio 43506 1.126 Screened Out

RED SPOT WESTLAND INC WESTLAND Michigan 48186 1.111 Screened Out

TRELLEBORG OFFSHORE US RANKIN ROAD FACILITY HOUSTON Texas 77073 1.1105 Screened Out

TESORO REFINING & MARKETING CO - MANDAN REFINERY MANDAN North Dakota 58554 1.1005 Screened Out

CANFIELD METAL COATING CORP CANFIELD Ohio 44406 1.1 Screened Out

BEAULIEU OF AMERICA PLANT 560-MODEL DALTON Georgia 30721 1.0865 Screened Out

COOK COMPOSITES & POLYMERS CO GRAND RAPIDS Michigan 49507 1.085 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

GARLAND Texas 75042 1.0845 Screened Out

POLYMERIC IMAGING INC NORTH KANSAS CITY Missouri 64116 1.0705 Screened Out

GREIF PACKAGING LLC WARMINSTER Pennsylvania 18974 1.0505 Screened Out

CANBERRA CORP TOLEDO Ohio 43615 1.05 Screened Out

NEXTEER AUTOMOTIVE CORP SAGINAW Michigan 48601 1.043 Screened Out

SPRAYLAT CORP CA LOS ANGELES California 90016 1.04 Screened Out

ROLL COATER INC HAWESVILLE Kentucky 42348 1.032 Screened Out

RED SPOT PAINT & VARNISH CO INC EVANSVILLE Indiana 47711 1.0225 Screened Out

STAR BUILDING SYSTEMS ELIZABETHTON Tennessee 37643 1.019 Screened Out

BOEING COMMERCIAL AIRPLANE GROUP PLANT 2 (PART) SEATTLE Washington 98108 1.009 Screened Out

HYDRITE CHEMICAL CO COTTAGE GROVE Wisconsin 53527 1 Screened Out

ARMSTRONG WORLD INDUSTRIES INC STILLWATER Oklahoma 74075 0.998 Screened Out

TTM TECHNOLOGIES-SANTA CLARA SANTA CLARA California 95050 0.9555 Screened Out

COOK COMPOSITES & POLYMERS CO HOUSTON Texas 77051 0.9265 Screened Out

IVC SOUTH LAWRENCEVILLE Georgia 30043 0.924 Screened Out

WATSON STANDARD CO (NEVILLE ISLAND PLANT) NEVILLE ISLAND Pennsylvania 15225 0.91 Screened Out

HADCO (SANMINA) CORP - OWEGO DIV OWEGO New York 13827 0.9025 Screened Out

MAXIM INTEGRATED PRODUCTS DALLAS Texas 75244 0.9005 Screened Out

SYNDICATE SYSTEMS INC MIDDLEBURY Indiana 46540 0.8555 Screened Out

COOK COMPOSITES & POLYMERS CO SAUKVILLE Wisconsin 53080 0.848 Screened Out

B-WAY PACKAGING INC TRENTON New Jersey 08648 0.848 Screened Out

EVONIK DEGUSSA CORP TIPPECANOE LABORATORIES LAFAYETTE Indiana 47909 0.825 Screened Out

SPRAYLAT CORP IL CHICAGO Illinois 60633 0.818 Screened Out

NJT ENTERPRISES LLC STERLING HEIGHTS Michigan 48314 0.8135 Screened Out

STEEL DYNAMICS INC JEFFERSONVILLE Indiana 47130 0.8125 Screened Out

FLINT HILLS RESOURCES LP ROSEMOUNT Minnesota 55068 0.8 Screened Out

COMPLEMENTARY COATINGS CORP BALTIMORE Maryland 21224 0.8 Screened Out

BERRYMAN PRODUCTS INC ARLINGTON Texas 76011 0.8 Screened Out

IC OF OKLAHOMA LLC TULSA Oklahoma 74116 0.8 Screened Out

TAIYO AMERICA INC CARSON CITY Nevada 89701 0.7935 Screened Out

PPG ARCHITECTURAL FINISHES EAST POINT EAST POINT Georgia 30344 0.792 Screened Out

GFX INTERNATIONAL GRAYSLAKE Illinois 60030 0.79 Screened Out

GENERAL MOTORS LLC BOWLING GREEN ASSEMBLY PLANT BOWLING GREEN Kentucky 42101 0.785 Screened Out

METALS USA BUILDING PRODUCTS MESQUITE Texas 75149 0.782 Screened Out

SUN CHEMICAL CORP MAUMEE Ohio 43537 0.7595 Screened Out

UNITED PAINT & CHEMICAL SOUTHFIELD Michigan 48034 0.7525 Screened Out

DELEET MERCHANDISING NEWARK New Jersey 07105 0.75 Screened Out

TEXAS TILE MANUFACTURING LLC HOUSTON Texas 77007 0.749 Screened Out

AKZO NOBEL SURFACE CHEMISTRY LLC HOUSTON Texas 77053 0.742 Screened Out

KAWNEER CO INC VISALIA California 93291 0.7255 Screened Out

HUNT REFINING CO A CORP TUSCALOOSA Alabama 35401 0.7205 Screened Out

RYCOLINE PRODUCTS LLC CHICAGO Illinois 60630 0.7195 Screened Out

PENN COLOR INC HATFIELD Pennsylvania 19440 0.7045 Screened Out

MARCUS PAINT CO LOUISVILLE Kentucky 40202 0.7025 Screened Out

Page 7 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

ELEMENTIS SPECIALTIES JERSEY CITY New Jersey 07304 0.7 Screened Out

WESTERN EXTRUSIONS CORP CARROLLTON Texas 75006 0.6985 Screened Out

KAWNEER CO INC BLOOMSBURG Pennsylvania 17815 0.696 Screened Out

CLEVELAND STEEL CONTAINER - PE OTONE FACILITY PEOTONE Illinois 60468 0.6945 Screened Out

WEST PENN OIL CO, INC130130 WARREN Pennsylvania 16365 0.6945 Screened Out

TERNIUM USA INC SHREVEPORT Louisiana 71115 0.6905 Screened Out

SONOCO PRODUCTS CO ORLANDO Florida 32837 0.677 Screened Out

FERRO GLASS & COLOR CORP WASHINGTON Pennsylvania 15301 0.6735 Screened Out

VISTA PAINT CORP FULLERTON California 92831 0.673 Screened Out

FINISHES UNLIMITED INC SUGAR GROVE Illinois 60554 0.665 Screened Out

HB FULLER COVINGTON Georgia 30014 0.661 Screened Out

OMG AMERICAS FRANKLIN Pennsylvania 16323 0.659 Screened Out

VANGUARD PAINTS & FINISHES INC MARIETTA Ohio 45750 0.648 Screened Out

SILGAN CONTAINERS MANUFACTURING CORP SAVAGE Minnesota 55378 0.642 Screened Out

CRYSTAL FINISHING SYSTEMS INC SCHOFIELD Wisconsin 54476 0.6405 Screened Out

HERCULES INC KENEDY TEXAS KENEDY Texas 78119 0.635 Screened Out

CENTRIA AMBRIDGE Pennsylvania 15003 0.635 Screened Out

TRINKOTE INDUSTRIAL FINISHES INC FORT WORTH Texas 76110 0.628 Screened Out

ALERIS ROLLED PRODUCTS INC ROXBORO North Carolina 27573 0.6265 Screened Out

CHROMASOURCE INC COLUMBIA CITY Indiana 46725 0.621 Screened Out

MULTICIRCUITS OSHKOSH Wisconsin 54903 0.619 Screened Out

TCI COATINGS INC LUBBOCK Texas 79415 0.616 Screened Out

GREIF INDUSTRIAL PACKAGING & SERVICES LLC LA PORTE Texas 77571 0.5975 Screened Out

ASHLAND DISTRIBUTION WILLOW SPRINGS Illinois 60480 0.586 Screened Out

ROCK TENN CO CLINTON Iowa 52732 0.585 Screened Out

CLEVELAND STEEL CONTAINER CORP - STREETSBORO PLANT STREETSBORO Ohio 44241 0.5795 Screened Out

BECKER SPECIALTY CORP FONTANA California 92335 0.5785 Screened Out

NICHOLS ALUMINUM DAVENPORT DAVENPORT Iowa 52802 0.567 Screened Out

ALUMAX MILL PRODUCTS INC TEXARKANA Texas 75501 0.5505 Screened Out

CHRYSLER GROUP LLC STERLING STAMPING PLANT (PART) STERLING HEIGHTS Michigan 48312 0.55 Screened Out

HB FULLER CO BLUE ASH Ohio 45242 0.5465 Screened Out

FLINT GROUP NORTH AMERICA CORP ANNISTON Alabama 36207 0.53 Screened Out

GLASS COATINGS & CONCEPTS MONROE Ohio 45050 0.5265 Screened Out

NAPCO INC VALENCIA Pennsylvania 16059 0.5245 Screened Out

PPG INDUSTRIES ARCHITECTURAL FINISHES BATAVIA Illinois 60510 0.52 Screened Out

FORREST PAINT CO EUGENE Oregon 97402 0.513 Screened Out

INEOS OXIDE A DIV OF INEOS AMERICAS LLC PLAQUEMINE Louisiana 70765 0.506 Screened Out

LOCKHEED MARTIN AERONAUTICS CO PALMDALE California 93599 0.5025 Screened Out

STEELSCAPE KALAMA Washington 98625 0.5025 Screened Out

COMPLEX CHEMICALS CO INC TALLULAH Louisiana 71282 0.5 Screened Out

SC JOHNSON & SON INC WAXDALE FACILITY STURTEVANT Wisconsin 53177 0.5 Screened Out

RUST-OLEUM CORP PLEASANT PRAIRIE Wisconsin 53158 0.5 Screened Out

SILBOND CORP WESTON Michigan 49289 0.5 Screened Out

ARCADIA INC VERNON California 90023 0.5 Screened Out

DERRICK CORP CHEEKTOWAGA New York 14225 0.4975 Screened Out

HEXION SPECIALTY CHEMICALS INC BEDFORD PARK Illinois 60501 0.4925 Screened Out

BECKER SPECIALTY CORP ELK GROVE VILLAGE Illinois 60007 0.49 Screened Out

TTM TECHNOLOGIES INC CHIPPEWA FALLS Wisconsin 54729 0.4895 Screened Out

ENGINEERED POLYMER SOLUTIONS I NC D/B/A VALSPAR 

COATINGS

BIRMINGHAM Alabama 35215 0.485 Screened Out

SNAP-ON TOOLS MANUFACTURING CO ALGONA Iowa 50511 0.4705 Screened Out

IVC INDUSTRIAL COATINGS INC CASA GRANDE Arizona 85222 0.4545 Screened Out

UNIVERSAL CHEMICALS & COATINGS INC ELK GROVE VILLAGE Illinois 60007 0.4505 Screened Out

SYNGENTA CROP PROTECTION INC SAINT GABRIEL FACILITY SAINT GABRIEL Louisiana 70776 0.45 Screened Out

DUPONT MOUNT CLEMENS PLANT MOUNT CLEMENS Michigan 48043 0.4495 Screened Out

LONGABERGER CO FRAZEYSBURG Ohio 43822 0.4465 Screened Out

NAZDAR CHICAGO CHICAGO Illinois 60622 0.4365 Screened Out

ZEP INC ATLANTA Georgia 30318 0.4305 Screened Out

PFI INC SANTA FE SPRINGS California 90670 0.42 Screened Out

SILGAN WHITE CAP CORP RICHMOND Indiana 47375 0.4175 Screened Out

MUTI-PACK LLC MILWAUKEE Wisconsin 53223 0.415 Screened Out

UNITED STATES ALUMINUM CORP WAXAHACHIE Texas 75165 0.4075 Screened Out

AMERIMAX HOME PRODUCTS INC LANCASTER Pennsylvania 17603 0.402 Screened Out

DIAMOND VOGEL PAINTS TULSA Oklahoma 74115 0.3975 Screened Out

AMERICAN METALS CORP WESTLAKE Ohio 44145 0.3955 Screened Out

NB COATINGS INC LANSING Illinois 60438 0.395 Screened Out

FORBO ADHESIVES LLC MORRIS Illinois 60450 0.3905 Screened Out

BRADLEY COATINGS GROUP CONNELLSVILLE Pennsylvania 15425 0.389 Screened Out

ROLLEX CORP ELK GROVE VILLAGE Illinois 60007 0.387 Screened Out

STANDARD PAINTS INC MANSFIELD Texas 76063 0.3865 Screened Out

GSP MARKETING TECHNOLOGIES CLEARWATER Florida 33760 0.384 Screened Out

Page 8 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

ABC COMPOUNDING CO INC MORROW Georgia 30260 0.3775 Screened Out

BASF CORP WYANDOTTE Michigan 48192 0.3775 Screened Out

INTERNATIONAL PAINT LLC HOUSTON Texas 77091 0.3775 Screened Out

TOWER PRODUCTS INC EASTON Pennsylvania 18045 0.375 Screened Out

RODDA PAINT CO PORTLAND Oregon 97203 0.375 Screened Out

QUEST CHEMICAL CORP HOUSTON Texas 77041 0.375 Screened Out

PARISER INDUSTRIES INC PATERSON New Jersey 07503 0.375 Screened Out

HILLYARD INDUSTRIES INC SAINT JOSEPH Missouri 64501 0.3675 Screened Out

SIKA CORP SIKA SARNAFIL DIV CANTON Massachusetts 02021 0.366 Screened Out

NASCOTE INDUSTRIES NASHVILLE Illinois 62263 0.365 Screened Out

MASCO RETAIL CABINET GROUP LLC WAVERLY Ohio 45690 0.358 Screened Out

FULLER BRUSH CO GREAT BEND Kansas 67530 0.3555 Screened Out

WATSON LABORATORIES INC UTAH SALT LAKE CITY Utah 84108 0.353 Screened Out

HOVENSA LLC CHRISTIANSTED Virgin Islands 00820 0.351 Screened Out

SHERWIN-WILLIAMS AUTOMOTIVE FINISHES CORP RICHMOND Kentucky 40475 0.35 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

HIGH POINT North Carolina 27261 0.349 Screened Out

NELCO PRODUCTS INC ANAHEIM California 92801 0.348 Screened Out

BRIGHTSMITH LLC MORRISVILLE Pennsylvania 19067 0.346 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

MOLINE Illinois 61265 0.341 Screened Out

ROLL COATER INC BLYTHEVILLE Arkansas 72315 0.334 Screened Out

ASHLAND DISTRIBUTION BIRMINGHAM Alabama 35234 0.3325 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

FREMONT Michigan 49412 0.3275 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

HIGH POINT North Carolina 27261 0.327 Screened Out

KIK-SOCAL INC SANTA FE SPRINGS California 90670 0.3255 Screened Out

ENTHONE INC WEST HAVEN Connecticut 06516 0.313 Screened Out

METAL COATERS OF CALIFORNIA INC RANCHO CUCAMONGA California 91730 0.311 Screened Out

PILOT CHEMICAL CO HOUSTON Texas 77086 0.3105 Screened Out

3M CO - CORDOVA CORDOVA Illinois 61242 0.3085 Screened Out

PPG INDUSTRIES OHIO INC (CL) CLEVELAND Ohio 44111 0.304 Screened Out

ET PRODUCTS CO INC BREMEN Indiana 46506 0.3 Screened Out

STP PRODUCTS MANUFACTURING CO PAINESVILLE Ohio 44077 0.298 Screened Out

DUCKBACK PRODUCTS CHICO California 95928 0.298 Screened Out

SIERRA CORP MINNETONKA Minnesota 55343 0.2975 Screened Out

LINETEC WAUSAU Wisconsin 54401 0.296 Screened Out

CERTIFIED ENAMELING INC LOS ANGELES California 90023 0.2905 Screened Out

CROWN CORK & SEAL CO (USA) INC CROWN CLOSURES DIV LANCASTER Ohio 43130 0.2905 Screened Out

PPG ARCHITECTURAL FINISHES INC LOUISVILLE Kentucky 40203 0.2895 Screened Out

CELLO PROFESSIONAL PRODUCTS HAVRE DE GRACE Maryland 21078 0.281 Screened Out

FORD MOTOR CO CHICAGO ASSEMBLY CHICAGO Illinois 60633 0.28 Screened Out

SERIGRAPH INC WEST BEND Wisconsin 53095 0.2795 Screened Out

VIDEOJET TECHNOLOGIES INC ELK GROVE VILLAGE Illinois 60007 0.275 Screened Out

QUANTUM MARKETING INC LAKELAND Florida 33803 0.272 Screened Out

FUCHS LUBRICANTS CO-CORPORATE OFFICE HARVEY Illinois 60426 0.2675 Screened Out

HB FULLER ROSEVILLE California 95678 0.2665 Screened Out

ROHM & HAAS CHEMICALS LLC BRISTOL Pennsylvania 19007 0.266 Screened Out

HELEN,INC DBA ENVIRONMENTAL COATINGS,INC CALEDONIA Michigan 49316 0.265 Screened Out

SEQUA COATINGS CORP PRECOAT METALS DIV MC KEESPORT Pennsylvania 15132 0.264 Screened Out

OLDCASTLE BUILDING ENVELOPE TENNESSEE FACILITY MIDWAY Tennessee 37809 0.2615 Screened Out

HARLEY-DAVIDSON MOTOR CO OPERATIONS INC YORK Pennsylvania 17402 0.2605 Screened Out

ASHLAND DISTRIBUTION CO SAINT PAUL Minnesota 55102 0.2595 Screened Out

HEXION SPECIALTY CHEMICALS INC CARPENTERSVILLE Illinois 60110 0.2585 Screened Out

ASHLAND DISTRIBUTION NASHVILLE Tennessee 37209 0.254 Screened Out

CHASE PRODUCTS CO BROADVIEW Illinois 60155 0.2535 Screened Out

SUMTER COATINGS INC SUMTER South Carolina 29150 0.252 Screened Out

ASHLAND DISTRIBUTION CO CARTERET New Jersey 07008 0.252 Screened Out

INCHEM CORP ROCK HILL South Carolina 29730 0.25 Screened Out

BASF CORP GREENVILLE Ohio 45331 0.25 Screened Out

BACHMAN SERVICES INC OKLAHOMA CITY Oklahoma 73129 0.25 Screened Out

REICHHOLD INC VALLEY PARK Missouri 63088 0.25 Screened Out

BERGQUIST CO CANNON FALLS Minnesota 55009 0.25 Screened Out

MISCO PRODUCTS CORP READING Pennsylvania 19605 0.25 Screened Out

CPJ TECHNOLOGIES TAYLORS South Carolina 29687 0.25 Screened Out

EQUILON CARSON TERMINAL CARSON California 90810 0.25 Screened Out

CHEMICAL SPECIALISTS & DEVELOPMENT INC CONROE Texas 77303 0.25 Screened Out

UNIVAR USA INC BERKELEY BERKELEY Missouri 63134 0.25 Screened Out

MALCO PRODUCTS INC BARBERTON Ohio 44203 0.25 Screened Out

HONDA MANUFACTURING OF INDIANA LLC GREENSBURG Indiana 47240 0.25 Screened Out

QUANTUM COATINGS INC CHARLOTTE North Carolina 28273 0.25 Screened Out

Page 9 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

YENKIN-MAJESTIC PAINT CORPORAT ION COLUMBUS Ohio 43219 0.25 Screened Out

UNIVAR USA INC METRO BLVD MARYLAND HEIGHTS Missouri 63043 0.25 Screened Out

ASHLAND DISTRIBUTION CO TWINSBURG Ohio 44087 0.248 Screened Out

EXXONMOBIL CHEMICAL BATON ROUGE CHEMICAL PLANT BATON ROUGE Louisiana 70805 0.2465 Screened Out

VEYANCE TECHNOLOGIES INC NORFOLK Nebraska 68701 0.2445 Screened Out

FLINT GROUP NORTH AMERICA ATLANTA Georgia 30339 0.24 Screened Out

CAR PRODUCTS INC HOLYOKE Massachusetts 01040 0.236 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

BOWLING GREEN Kentucky 42101 0.233 Screened Out

WARREN STAMPING PLANT (PART) WARREN Michigan 48091 0.23 Screened Out

METAL COATERS OF GEORGIA MARIETTA Georgia 30062 0.228 Screened Out

ICL-IP AMERICA INC GALLIPOLIS FERRY West Virginia 25515 0.222 Screened Out

ARROW GROUP INDUSTRIES INC HASKELL New Jersey 07420 0.2215 Screened Out

PERMA-PIPE OIL & GAS NEW IBERIA Louisiana 70560 0.22 Screened Out

INTERNATIONAL EXTRUSION CORP TEXAS WAXAHACHIE Texas 75165 0.2115 Screened Out

COLWELL INC KENDALLVILLE Indiana 46755 0.21 Screened Out

GUARDIAN AUTOMOTIVE - MOREHEAD PLANT MOREHEAD Kentucky 40351 0.203 Screened Out

ASHLAND DISTRIBUTION CO DORAVILLE Georgia 30340 0.2025 Screened Out

GATES CORP - CHARLESTON CHARLESTON Missouri 63834 0.1985 Screened Out

CHAMPION TECHNOLOGIES INC KILGORE Texas 75662 0.196 Screened Out

RHODIA INC WINDER Georgia 30680 0.1935 Screened Out

ROCKLINE INDUSTRIES SHEBOYGAN Wisconsin 53081 0.193 Screened Out

FIRST AMERICAN RESOURCES CO MABLETON Georgia 30126 0.191 Screened Out

SASOL NORTH AMERICA INC LAKE CHARLES CHEMICAL 

COMPLEX

WESTLAKE Louisiana 70669 0.1885 Screened Out

RUDD CO INC SEATTLE Washington 98107 0.1875 Screened Out

ASHLAND DISTRIBUTION SAINT LOUIS Missouri 63111 0.186 Screened Out

CURTIS METAL FINISHING CO MACHESNEY PARK Illinois 61115 0.1855 Screened Out

ASHLAND DISTRIBUTION CO GARLAND TX GARLAND Texas 75041 0.182 Screened Out

TRITECH COATINGS CORP PAGEDALE Missouri 63133 0.182 Screened Out

JAMESTOWN COATING TECHNOLOGIES JAMESTOWN Pennsylvania 16134 0.1795 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

WHEELING Illinois 60090 0.177 Screened Out

ASHLAND INC - CHANDLER CHANDLER Arizona 85226 0.177 Screened Out

PROFESSIONAL DISPOSABLES INTERNATIONAL INC ORANGEBURG New York 10962 0.176 Screened Out

EXXONMOBIL REFINING & SUPPLY BATON ROUGE REFINERY BATON ROUGE Louisiana 70805 0.176 Screened Out

PLAZE INC SAINT CLAIR Missouri 63077 0.1745 Screened Out

ENERGIZER BATTERY MANUFACTURING INC SAINT ALBANS Vermont 05478 0.174 Screened Out

BYK USA INC WALLINGFORD Connecticut 06492 0.173 Screened Out

ASHLAND DISTRIBUTION CO BATON ROUGE Louisiana 70815 0.173 Screened Out

DOW CHEMICAL CO FREEPORT FACILITY FREEPORT Texas 77541 0.168 Screened Out

DUPONT FRONT ROYAL PLANT FRONT ROYAL Virginia 22630 0.168 Screened Out

ANCHOR PAINT MANUFACTURING CO INC TULSA Oklahoma 74112 0.167 Screened Out

RHODIA INC MARCUS HOOK Pennsylvania 19061 0.1615 Screened Out

RADIATOR SPECIALTY CO INDIAN TRAIL North Carolina 28079 0.161 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

STATESVILLE North Carolina 28625 0.156 Screened Out

SONOCO FLEXIBLE PACKAGING EDINBURGH Indiana 46124 0.1545 Screened Out

STOUSE INC NEW CENTURY Kansas 66031 0.154 Screened Out

WARREN OIL CO - NC DUNN North Carolina 28335 0.153 Screened Out

HENTZEN COATINGS,INC BATAVIA FACILITY BATAVIA Illinois 60510 0.151 Screened Out

TNEMEC CO INC NORTH KANSAS CITY Missouri 64116 0.1465 Screened Out

PPG INDUSTRIES OHIO INC CIRCLEVILLE OH CIRCLEVILLE Ohio 43113 0.1455 Screened Out

MT ELLIOTT TOOL & DIE MANUFACTURING (PART) DETROIT Michigan 48234 0.145 Screened Out

DYCO PAINTS INC CLEARWATER Florida 33760 0.142 Screened Out

MID-STATES PAINT & CHEMICAL CO CRESTWOOD Missouri 63126 0.1415 Screened Out

DUPONT CHAMBERS WORKS DEEPWATER New Jersey 08023 0.14 Screened Out

APOLLO CHEMICAL BURLINGTON North Carolina 27215 0.14 Screened Out

DOW CHEMICAL CO - LOUISIANA OPERATIONS PLAQUEMINE Louisiana 70765 0.139 Screened Out

DUPONT FORT MADISON PLANT FORT MADISON Iowa 52627 0.135 Screened Out

ASHLAND DISTRIBUTION MEMPHIS Tennessee 38113 0.1345 Screened Out

BAKER PETROLITE CORP SAND SPRINGS Oklahoma 74063 0.1325 Screened Out

AMREP INC MARIETTA Georgia 30062 0.1315 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

LEBANON Pennsylvania 17046 0.1315 Screened Out

AKZONOBEL COATINGS INC PONTIAC Michigan 48341 0.131 Screened Out

BEHR PROCESS CORP - CHICAGO CHICAGO HEIGHTS Illinois 60411 0.1295 Screened Out

TEXAS INSTRUMENTS INC STAFFORD Texas 77477 0.1275 Screened Out

SOUTHERN CLAY PRODUCTS INC LOUISVILLE Kentucky 40210 0.1275 Screened Out

CLARIANT CORP MARTIN PLANT MARTIN South Carolina 29836 0.1275 Screened Out

MOC PRODUCTS CO INC PACOIMA California 91331 0.1275 Screened Out

BF GOODRICH TIRE MANUFACTURING WOODBURN Indiana 46797 0.1275 Screened Out

Page 10 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

VARN INTERNATIONAL BATAVIA Illinois 60510 0.1275 Screened Out

RR STREET & CO INC CHICAGO Illinois 60608 0.1275 Screened Out

UNITED LABORATORIES INC SAINT CHARLES Illinois 60174 0.1275 Screened Out

ELANTAS PDG INC SAINT LOUIS Missouri 63147 0.1275 Screened Out

RESEARCH SOLVENTS & CHEMICALS INC LA VERGNE Tennessee 37086 0.1275 Screened Out

RESEARCH SOLVENTS & CHEMICALS INC PELHAM Alabama 35124 0.1275 Screened Out

BRENNTAG GREAT LAKES LLC MENOMONEE FALLS Wisconsin 53051 0.1275 Screened Out

GE WATER & PROCESS TECHNOLOGIES ORANGE FACILITY ORANGE Texas 77630 0.1275 Screened Out

OAKLEY INC FOOTHILL RANCH California 92610 0.1275 Screened Out

NICCA USA INC FOUNTAIN INN South Carolina 29644 0.1275 Screened Out

CHEMICALS INC BAYTOWN Texas 77520 0.1275 Screened Out

POWER SERVICE PRODUCTS INC WEATHERFORD Texas 76086 0.1275 Screened Out

BASF CORP SPARTANBURG South Carolina 29302 0.1275 Screened Out

PERMATEX SOLON SOLON Ohio 44139 0.1275 Screened Out

CONOCOPHILLIPS PONCA CITY REFINERY PONCA CITY Oklahoma 74601 0.1275 Screened Out

CONOCOPHILLIPS OKLAHOMA CITY PRODUCTS TERMINAL OKLAHOMA CITY Oklahoma 73117 0.1275 Screened Out

COASTAL CHEMICAL CO LLC ABBEVILLE Louisiana 70510 0.1275 Screened Out

TAKASAGO INTERNATIONAL CORP (USA) NORTHVALE New Jersey 07647 0.1275 Screened Out

WATSON STANDARD CO HARWICK PLANT HARWICK Pennsylvania 15049 0.1275 Screened Out

GEORGE S COYNE CHEMICAL CO INC CROYDON Pennsylvania 19021 0.1275 Screened Out

TRELLEBORG COATED SYSTEMS US INC / GRACE ADVANCED 

MATERIALS

RUTHERFORDTON North Carolina 28139 0.125 Screened Out

CHEMCOAT INC MONTOURSVILLE Pennsylvania 17754 0.125 Screened Out

PPG INDUSTRIES INC MCCARRAN Nevada 89434 0.125 Screened Out

FIBRO CHEM LLC DALTON Georgia 30720 0.125 Screened Out

PROCLEAN OF ARIZONA INC PHOENIX Arizona 85043 0.125 Screened Out

PREMIER INK SYSTEMS INC HARRISON Ohio 45030 0.125 Screened Out

NALCO CO - ODESSA PLANT 114 ODESSA Texas 79765 0.125 Screened Out

AKZO NOBEL COATINGS INC HIGH POINT North Carolina 27261 0.125 Screened Out

GOLD EAGLE CO CHICAGO Illinois 60632 0.125 Screened Out

W M BARR & CO MEMPHIS Tennessee 38113 0.125 Screened Out

INX INTERNATIONAL INK CO HOMEWOOD Illinois 60430 0.125 Screened Out

COLUMBIA PAINT CORP HUNTINGTON West Virginia 25704 0.125 Screened Out

CERAM-TRAZ CORP CERAMIC INDL COATINGS (DBA) OSSEO Minnesota 55369 0.125 Screened Out

SICPA SECURINK CORP SPRINGFIELD Virginia 22153 0.125 Screened Out

CLEANING SYSTEMS INC DE PERE Wisconsin 54115 0.125 Screened Out

CHEMETALL US INC ROMULUS Michigan 48174 0.125 Screened Out

NOV TUBOSCOPE HOLMES ROAD HOUSTON Texas 77051 0.125 Screened Out

ACTON TECHNOLOGIES INC PITTSTON Pennsylvania 18640 0.125 Screened Out

AKCROS CHEMICALS INC NEW BRUNSWICK New Jersey 08901 0.125 Screened Out

MAGNABLEND INC LIQUID PLANT WAXAHACHIE Texas 75165 0.125 Screened Out

KALCOR COATINGS CO WILLOUGHBY Ohio 44094 0.125 Screened Out

DANLIN INDUSTRIES CORP THOMAS Oklahoma 73669 0.125 Screened Out

UNIVAR USA INC DALLAS DAN MORTON FACILITY DALLAS Texas 75236 0.125 Screened Out

TYSON FRESH MEATS INC HOLCOMB Kansas 67851 0.125 Screened Out

TRANS CHEMICAL INC SAINT LOUIS Missouri 63147 0.125 Screened Out

ELECTRONICS FOR IMAGING INC YPSILANTI Michigan 48197 0.124 Screened Out

KEYSTONE ANILINE CORP INMAN South Carolina 29349 0.123 Screened Out

ASHLAND DISTRIBUTION LOUISVILLE Kentucky 40211 0.121 Screened Out

CAROLINA SOLVENTS INC HICKORY North Carolina 28602 0.1185 Screened Out

ASHLAND DISTRIBUTION CO CHARLOTTE North Carolina 28208 0.118 Screened Out

AEP INDUSTRIES INC GRIFFIN Georgia 30224 0.1175 Screened Out

ALLEGHENY PETROLEUM PRODUCTS CO WILMERDING Pennsylvania 15148 0.1165 Screened Out

ACCURATE DISPERSIONS SOUTH HOLLAND Illinois 60473 0.116 Screened Out

US MARINE CORPS AIR STATION YUMA YUMA Arizona 85369 0.1145 Screened Out

TECHNICAL CHEMICAL CO CLEBURNE Texas 76033 0.1135 Screened Out

ARDEX LABORATORIES INC PHILADELPHIA Pennsylvania 19116 0.1125 Screened Out

ASHLAND INC - EVENDALE EVENDALE Ohio 45241 0.1125 Screened Out

SHERWIN-WILLIAMS CO GREENSBORO North Carolina 27403 0.11 Screened Out

3M CO - NEVADA NEVADA Missouri 64772 0.11 Screened Out

DELTA LABORATORIES INC OCALA Florida 34475 0.109 Screened Out

SHERWIN-WILLIAMS CO HOLLAND Michigan 49423 0.106 Screened Out

FRAZEE INDUSTRIES SAN DIEGO California 92121 0.103 Screened Out

CENTRAL MOTOR WHEEL OF AMERICA (DBA CMWA) PARIS Kentucky 40361 0.103 Screened Out

ASHLAND DISTRIBUTION CO FAIRFIELD California 94533 0.1025 Screened Out

STEELSCAPE INC RANCHO RANCHO CUCAMONGA California 91730 0.101 Screened Out

ASHLAND DISTRIBUTION CO CARSON California 90810 0.098 Screened Out

CYTEC INDUSTRIES INC LANGLEY PLANT LANGLEY South Carolina 29834 0.0935 Screened Out

ASHLAND DISTRIBUTION CO MIAMI Florida 33162 0.093 Screened Out

CE BRADLEY LABORATORIES INC BRATTLEBORO Vermont 05301 0.093 Screened Out

MULTI-COLOR CORP SCOTTSBURG Indiana 47170 0.091 Screened Out

ATHEA LABORATORIES INC MILWAUKEE Wisconsin 53224 0.0905 Screened Out

Page 11 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

HENKEL CORP WARREN Michigan 48091 0.088 Screened Out

HARCROS CHEMICALS INC KANSAS CITY Kansas 66106 0.0875 Screened Out

BRENNTAG PACIFIC INC SANTA FE SPRINGS California 90670 0.0875 Screened Out

DIC IMAGING PRODUCTS USA LLC OAK CREEK Wisconsin 53154 0.086 Screened Out

NORTHERN COATINGS & CHEMICAL CO INC MENOMINEE Michigan 49858 0.085 Screened Out

CCI MANUFACTURING IL CORP LEMONT Illinois 60439 0.0835 Screened Out

UNION TANK CAR ALEXANDRIA MANUFACTURING FACILITY ALEXANDRIA Louisiana 71303 0.0835 Screened Out

CHAMPION TECHNOLOGIES INC CORPUS CHRISTI Texas 78405 0.0825 Screened Out

ASHLAND DISTRIBUTION TEWKSBURY Massachusetts 01876 0.082 Screened Out

CHAMPION TECHNOLOGIES INC CRESSON Texas 76035 0.08 Screened Out

MRCG-KRAFTMAID P3 ORWELL Ohio 44076 0.0795 Screened Out

BUZZI UNICEM USA - GREENCASTLE PLANT GREENCASTLE Indiana 46135 0.0795 Screened Out

AVERY DENNISON PFD SCHERERVILLE Indiana 46375 0.0795 Screened Out

TEXAS INSTRUMENTS INC DALLAS Texas 75243 0.0795 Screened Out

HUNTSMAN PETROCHEMICAL LLC PORT NECHES 

PERFORMANCE PRODUCTS

PORT NECHES Texas 77651 0.079 Screened Out

ECOLAB CITY OF INDUSTRY California 91748 0.079 Screened Out

LUBRIZOL MC COOK Illinois 60525 0.078 Screened Out

ARCH CHEMICALS INC BRANDENBURG Kentucky 40108 0.078 Screened Out

PLAZE INC SAINT CLAIR Missouri 63077 0.078 Screened Out

ASHLAND DISTRIBUTION CO KANSAS CITY Kansas 66106 0.0775 Screened Out

AKZO NOBEL COATINGS INC CLINTON Mississippi 39056 0.0765 Screened Out

MATTHEWS INTERNATIONAL CORP PITTSBURGH Pennsylvania 15238 0.0765 Screened Out

CLOROX PRODUCTS MANUFACTURING CO FAIRFIELD California 94533 0.0745 Screened Out

SPRAYLAT CORP MOUNT VERNON New York 10550 0.074 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

PITTSBURGH Pennsylvania 15233 0.0735 Screened Out

AKZO NOBEL COATINGS INC SALEM Oregon 97302 0.073 Screened Out

BOEHRINGER INGELHEIM CHEMICALS INC PETERSBURG Virginia 23805 0.0725 Screened Out

CHEMICAL SOLVENTS JENNINGS ROAD FACILITY CLEVELAND Ohio 44109 0.072 Screened Out

VEOLIA ES TECHNICAL SOLUTIONS LLC PORT ARTHUR 

FACILITY

PORT ARTHUR Texas 77640 0.071 Screened Out

ADCO CLEANING PRODUCTS LLC SEDALIA Missouri 65301 0.071 Screened Out

TYSON FRESH MEATS INC AMARILLO Texas 79187 0.07 Screened Out

WARSAW CHEMICAL CO INC WARSAW Indiana 46580 0.07 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

MONTEBELLO California 90640 0.07 Screened Out

SPARTAN CHEMICAL CO INC MAUMEE Ohio 43537 0.0675 Screened Out

SUPERIOR OIL CO INC RECLAIMED ENERGY DIV CONNERSVILLE Indiana 47331 0.066 Screened Out

CARDINAL INDUSTRIAL FINISHES SOUTH EL MONTE California 91733 0.066 Screened Out

MINUTEMAN INTERNATIONAL MULTI-CLEAN DIV SHOREVIEW Minnesota 55126 0.0655 Screened Out

EFI / INKWARE MEREDITH New Hampshire 03253 0.0635 Screened Out

KARCHER NORTH AMERICA- PROCHEM CHANDLER Arizona 85224 0.0625 Screened Out

ICI PAINTS PUERTO RICO INC CAROLINA Puerto Rico 00985 0.0615 Screened Out

COOK COMPOSITES & POLYMERS C O LEMONT Illinois 60439 0.061 Screened Out

GROTTOES PLASTICS PLANT GROTTOES Virginia 24441 0.0595 Screened Out

SHERWIN-WILLIAMS CO TERRE HAUTE Indiana 47808 0.0585 Screened Out

BRENNTAG SOUTHEAST INC DURHAM North Carolina 27703 0.058 Screened Out

CONOCOPHILLIPS CO EAST ST LOUIS TERMINAL CAHOKIA Illinois 62206 0.0575 Screened Out

PPG INDUSTRIES OHIO INC - DELAWARE DELAWARE Ohio 43015 0.057 Screened Out

CONTINENTAL CEMENT CO LLC HANNIBAL Missouri 63401 0.057 Screened Out

ECOLAB INC MC DONOUGH Georgia 30253 0.057 Screened Out

COGNIS CORP MAULDIN PLANT MAULDIN South Carolina 29662 0.057 Screened Out

BEHR PROCESS CORP ALLENTOWN ALLENTOWN Pennsylvania 18106 0.0565 Screened Out

FLINT HILLS RESOURCES LP - WEST PLANT CORPUS CHRISTI Texas 78410 0.055 Screened Out

CLARIANT CORP - MOUNT HOLLY WEST PLANT MOUNT HOLLY North Carolina 28120 0.0545 Screened Out

GRAPHIC CONTROLS LLC BUFFALO New York 14204 0.054 Screened Out

UNIVAR USA INC BEDFORD PARK Illinois 60499 0.0535 Screened Out

ABC COMPOUNDING CO OF TEXAS INC GRAND PRAIRIE Texas 75050 0.0535 Screened Out

HANNA STEEL CORP PEKIN Illinois 61554 0.053 Screened Out

ATMI MATERIALS LTD BURNET Texas 78611 0.0515 Screened Out

DYSTAR LP REIDSVILLE North Carolina 27320 0.05 Screened Out

RINECO BENTON Arkansas 72015 0.0495 Screened Out

NORTHERN LABS INC WEST DRIVE MANITOWOC Wisconsin 54220 0.049 Screened Out

BARTON SOLVENTS INC BETTENDORF BETTENDORF Iowa 52722 0.049 Screened Out

MRCG-KRAFTMAID P1 MIDDLEFIELD Ohio 44062 0.0485 Screened Out

NORMAN FOX & CO VERNON California 90058 0.0485 Screened Out

WHITFORD CORP ELVERSON Pennsylvania 19520 0.0485 Screened Out

AMERICAN COATINGS INC TOMBALL Texas 77375 0.0485 Screened Out

KAY CHEMICAL CO GREENSBORO North Carolina 27409 0.048 Screened Out

ASHLAND DISTRIBUTION CO TAMPA Florida 33634 0.047 Screened Out

FRANKLIN INTERNATIONAL COLUMBUS Ohio 43207 0.047 Screened Out

Page 12 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

RECKITT BENCKISER HILLSBOROUGH New Jersey 08844 0.046 Screened Out

INOAC PACKAGING GROUP BARDSTOWN Kentucky 40004 0.044 Screened Out

ECOLAB INC JOLIET Illinois 60436 0.043 Screened Out

KBP COIL COATERS INC DENVER Colorado 80216 0.042 Screened Out

ENTHONE INC BRIDGEVIEW Illinois 60455 0.0415 Screened Out

FORD MOTOR CO MICHIGAN ASSEMBLY PLANT WAYNE Michigan 48184 0.0405 Screened Out

RECTICEL INTERIORS NORTH AMERICA LLC TUSCALOOSA Alabama 35401 0.0395 Screened Out

BIOLAB INC CONYERS Georgia 30012 0.039 Screened Out

BARTON SOLVENTS INC WICHITA VALLEY CENTER Kansas 67147 0.039 Screened Out

BARTON SOLVENTS INC KANSAS CITY KANSAS CITY Kansas 66111 0.039 Screened Out

SHERWIN-WILLIAMS CO ANDOVER Kansas 67002 0.0385 Screened Out

HARCROS CHEMICALS INC PASADENA Texas 77507 0.038 Screened Out

BRENNTAG SOUTHWEST INC HOUS TON HOUSTON Texas 77047 0.0375 Screened Out

CLEAN HARBORS EL DORADO LLC EL DORADO Arkansas 71730 0.037 Screened Out

ECOLAB HEBRON Ohio 43025 0.037 Screened Out

SUPERIOR SOLVENTS & CHEMICALS FAIRFIELD Ohio 45014 0.0365 Screened Out

EXCEL-POLYMERS LLC JONESBOROUGH Tennessee 37659 0.0365 Screened Out

AIR PRODUCTS PERFORMANCE MANUFACTURING INC MILTON Wisconsin 53563 0.036 Screened Out

JOHNSONDIVERSEY INC STURTEVANT Wisconsin 53177 0.0355 Screened Out

ECOLAB INC MARTINSBURG West Virginia 25405 0.0355 Screened Out

HUNTSMAN ADVANCED MATERIALS AMERICAS INC MC INTOSH Alabama 36553 0.0355 Screened Out

BRENNTAG SOUTHWEST INC LANC ASTER LANCASTER Texas 75134 0.035 Screened Out

ETHOX CHEMICALS LLC GREENVILLE South Carolina 29605 0.035 Screened Out

SHERWIN-WILLIAMS CO GARLAND Texas 75041 0.0345 Screened Out

BRENNTAG NORTHEAST INC READING Pennsylvania 19605 0.0335 Screened Out

LUBRIZOL CORP WICKLIFFE Ohio 44092 0.033 Screened Out

DUPONT PARLIN PLANT PARLIN New Jersey 08859 0.032 Screened Out

BARTON SOLVENTS INC WEST BEND WEST BEND Wisconsin 53095 0.0315 Screened Out

3M CO - KNOXVILLE KNOXVILLE Iowa 50138 0.0315 Screened Out

UNIVAR USA INC - INDIANAPOLIS INDIANAPOLIS Indiana 46219 0.0305 Screened Out

MACDERMID INC FERNDALE Michigan 48220 0.0285 Screened Out

MEADWESTVACO SOUTH CAROLINA LLC DERIDDER Louisiana 70634 0.028 Screened Out

CARBOLINE CO LAKE CHARLES Louisiana 70601 0.028 Screened Out

ASHLAND DISTRIBUTION LANSING Michigan 48906 0.0275 Screened Out

UNIVAR USA INC HAMILTON BRANCH HAMILTON Ohio 45015 0.027 Screened Out

ECOLAB INC GARLAND Texas 75041 0.0265 Screened Out

UNIVAR USA INC - TOLEDO SOUTH BRANCH TOLEDO Ohio 43615 0.0265 Screened Out

BARTON SOLVENTS INC DES MOINES DES MOINES Iowa 50313 0.026 Screened Out

VEOLIA ES TECHNICAL SOLUTIONS LLC MIDDLESEX New Jersey 08846 0.026 Screened Out

AMPHENOL APC INC NASHUA New Hampshire 03062 0.026 Screened Out

KEMIRA WATER SOLUTIONS INC MOBILE Alabama 36614 0.0255 Screened Out

RICHARDSAPEX INC PHILADELPHIA Pennsylvania 19127 0.025 Screened Out

HOLLY OAK CHEMICAL INC FOUNTAIN INN South Carolina 29644 0.025 Screened Out

CORSICANA TECHNOLOGIES INC CORSICANA Texas 75109 0.0245 Screened Out

EXCEL POLYMERS LLC DYERSBURG Tennessee 38024 0.0245 Screened Out

ASHLAND DISTRIBUTION CO HOUSTON Texas 77034 0.0245 Screened Out

SHERWIN-WILLIAMS CO GREENSBORO North Carolina 27409 0.0245 Screened Out

SI GROUP INC ROTTERDAM JUNCTION New York 12150 0.0235 Screened Out

UNIVAR USA INC NORCROSS FACILI TY NORCROSS Georgia 30071 0.0235 Screened Out

RANBAR ELECTRICAL MATERIALS INC MANOR Pennsylvania 15665 0.023 Screened Out

BARTON SOLVENTS INC COUNCIL BLUFFS COUNCIL BLUFFS Iowa 51502 0.023 Screened Out

ECOLAB INC SAN JOSE California 95133 0.023 Screened Out

VALERO THREE RIVERS REFINERY THREE RIVERS Texas 78071 0.023 Screened Out

PRIDE SOLVENTS & CHEMICAL CO OF NEW JERSEY AVENEL New Jersey 07001 0.0225 Screened Out

UNIVAR USA INC - TOLEDO BRANCH WALBRIDGE Ohio 43465 0.0225 Screened Out

DAUBERT CHEMICAL CO CHICAGO Illinois 60638 0.022 Screened Out

PACKAGING CORP OF AMERICA COUNCE MILL COUNCE Tennessee 38326 0.0205 Screened Out

BASF CORP BELVIDERE New Jersey 07823 0.02 Screened Out

3M CO - SPRINGFIELD SPRINGFIELD Missouri 65802 0.02 Screened Out

UNIVAR USA INC 68TH ST BEDFORD PARK Illinois 60501 0.0195 Screened Out

GAGE PRODUCTS CO FERNDALE Michigan 48220 0.0195 Screened Out

VALSPAR REFINISH PICAYUNE Mississippi 39466 0.019 Screened Out

FISHER SCIENTIFIC INTERNATIONAL MTN DIAGNOSTICS PLANT MIDDLETOWN Virginia 22645 0.019 Screened Out

ZEP COMMERCIAL EMERSON Georgia 30137 0.019 Screened Out

KWAL-HOWELLS INC (DBA KWAL PAINT INC) BONHAM Texas 75418 0.0185 Screened Out

STEEL DYNAMICS INC BUTLER Indiana 46721 0.0185 Screened Out

TRANSTAR AUTOBODY TECHNOLOGIES BRIGHTON Michigan 48114 0.018 Screened Out

EASTMAN KODAK CO EASTMAN BUSINESS PARK ROCHESTER New York 14652 0.0175 Screened Out

ASHLAND DISTRIBUTION CO TWINSBURG Ohio 44087 0.017 Screened Out

KEY POLYMER LAWRENCE Massachusetts 01843 0.0165 Screened Out

ARLON INC ADHESIVES & FILMS DIV SANTA ANA California 92704 0.0165 Screened Out

Page 13 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

BRENNTAG SOUTHWEST INC ST GABRIEL SAINT GABRIEL Louisiana 70776 0.0155 Screened Out

TYSON FRESH MEATS INC JOSLIN IL HILLSDALE Illinois 61257 0.015 Screened Out

SHERWIN-WILLIAMS CO COLUMBUS Ohio 43207 0.015 Screened Out

PROCTER & GAMBLE HAIR CARE LLC IOWA CITY Iowa 52240 0.015 Screened Out

HENKEL ENOREE South Carolina 29335 0.015 Screened Out

CHEMDESIGN PRODUCTS INC MARINETTE Wisconsin 54143 0.0145 Screened Out

MONSANTO CO MUSCATINE Iowa 52761 0.0145 Screened Out

SHERWIN-WILLIAMS CO MORROW Georgia 30260 0.0145 Screened Out

BENJAMIN MOORE & CO JOHNSTOWN JOHNSTOWN New York 12095 0.014 Screened Out

BLENTECH CORP HOUSTON Texas 77029 0.014 Screened Out

PRIDE SOLVENT & CHEMICAL CO OF NY INC HOLTSVILLE New York 11742 0.014 Screened Out

SIMONIZ USA INC BOLTON Connecticut 06043 0.0135 Screened Out

VERSO PAPER HOLDINGS LLC JAY Maine 04239 0.0125 Screened Out

BRULIN CORP INDIANAPOLIS Indiana 46205 0.0125 Screened Out

EVONIK DEGUSSA CORP THEODORE Alabama 36582 0.0125 Screened Out

UNIVAR USA INC COMMERCE California 90040 0.0125 Screened Out

HUBBARD-HALL INC WATERBURY Connecticut 06708 0.012 Screened Out

LAMBERTI USA INC WHARTON CHEMICAL COMPLEX HUNGERFORD Texas 77448 0.0115 Screened Out

UNIVAR USA INC INDIANAPOLIS WEST BRANCH INDIANAPOLIS Indiana 46268 0.0115 Screened Out

U.S. POLYMERS ACCUREZ LLC SAINT LOUIS Missouri 63111 0.0115 Screened Out

GOODWIN CO LAWRENCEVILLE Georgia 30043 0.0115 Screened Out

HENKEL CORP DELAWARE Ohio 43015 0.0115 Screened Out

SHERWIN-WILLIAMS CO BALTIMORE Maryland 21230 0.0105 Screened Out

MICHELIN NORTH AMERICA INC TUSCALOOSA Alabama 35401 0.01 Screened Out

PRC-DESOTO INTERNATIONAL INC MOJAVE California 93501 0.01 Screened Out

BERRIDGE MANUFACTURING CO SAN ANTONIO Texas 78218 0.01 Screened Out

BUCKLEY OIL CO DALLAS Texas 75207 0.01 Screened Out

CHEMOL CO INC GREENSBORO North Carolina 27406 0.0095 Screened Out

HYDRITE CHEMICAL CO UNIVERSITY PARK Illinois 60466 0.0095 Screened Out

TRUE VALUE MANUFACTURING CARY Illinois 60013 0.0095 Screened Out

DAVIES IMPERIAL COATINGS INC HAMMOND Indiana 46320 0.0095 Screened Out

UNIVAR USA INC SANTA FE SPRINGS SANTA FE SPRINGS California 90670 0.0095 Screened Out

BEHR PROCESS CORP SANTA ANA California 92704 0.009 Screened Out

HENKEL ONTARIO ONTARIO California 91761 0.009 Screened Out

BENJAMIN MOORE & CO PELL CITY PELL CITY Alabama 35125 0.0085 Screened Out

GEORGIA-PACIFIC CHEMICALS LLC LUFKIN Texas 75901 0.0085 Screened Out

BJ CHEMICAL SERVICES HOBBS New Mexico 88240 0.008 Screened Out

CRODA INC NEW CASTLE Delaware 19720 0.008 Screened Out

TARR ACQUISITION LLC PORTLAND Oregon 97227 0.008 Screened Out

INTERSTATE CHEMICAL CO INC CHANNAHON Illinois 60410 0.008 Screened Out

NALCO CO TULSA PLANT 102 TULSA Oklahoma 74131 0.0075 Screened Out

DSM DESOTECH INC STANLEY North Carolina 28164 0.0075 Screened Out

NEW DAWN MANUFACTURING CO UPPER MARLBORO Maryland 20774 0.0075 Screened Out

RUSTOLEUM CORP LESAGE West Virginia 25537 0.0075 Screened Out

SHERWIN-WILLIAMS CO VICTORVILLE California 92392 0.0075 Screened Out

DYNALOY LLC INDIANAPOLIS Indiana 46226 0.0075 Screened Out

LUBRIZOL CORP PAINESVIL LE PLANT PAINESVILLE Ohio 44077 0.0075 Screened Out

CLOROX PRODUCTS MANUFACTURING CO FOREST PARK Georgia 30297 0.007 Screened Out

CUSTOM CHEMICAL FORMULATORS SANTA FE SPRINGS California 90670 0.007 Screened Out

ACTEGA KELSTAR INC CINNAMINSON New Jersey 08077 0.0065 Screened Out

DOW CHEMICAL JOLIET SITE CHANNAHON Illinois 60410 0.0065 Screened Out

HENKEL CORP CALHOUN Georgia 30701 0.0065 Screened Out

UNIVAR USA INC - SAN JOSE SAN JOSE California 95131 0.0065 Screened Out

KEYSTONE CEMENT CO BATH Pennsylvania 18014 0.0065 Screened Out

PROCTER & GAMBLE MANUFACTURING CO KANSAS CITY Kansas 66105 0.006 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

INDIANAPOLIS Indiana 46225 0.006 Screened Out

AROMATIC TECHNOLOGIES INC SOMERVILLE New Jersey 08876 0.0055 Screened Out

CALLAHAN CHEMICAL CO RIDGEFIELD PARK New Jersey 07660 0.0055 Screened Out

DUPONT PONTCHARTRAIN WORKS LA PLACE Louisiana 70068 0.005 Screened Out

PPG INDUSTRIES ARCHITECTURAL FINISHES DOVER Delaware 19904 0.005 Screened Out

HERITAGE-WTI INC EAST LIVERPOOL Ohio 43920 0.005 Screened Out

ROHM & HAAS ELECTRONIC MATERIA LS LLC MARLBOROUGH Massachusetts 01752 0.005 Screened Out

CHAMPION PACKAGING & DISTRIBUTING INC WOODRIDGE Illinois 60517 0.005 Screened Out

SARTOMER CO INC CHATHAM Virginia 24531 0.005 Screened Out

UNIVAR USA INC LAKEVILLE LAKEVILLE Minnesota 55044 0.005 Screened Out

BRAIN POWER INC MIAMI Florida 33155 0.005 Screened Out

SARTOMER CO INC WEST CHESTER Pennsylvania 19382 0.005 Screened Out

INTEL CORP - RONLER ACRES CAMPUS HILLSBORO Oregon 97124 0.005 Screened Out

C P INC CONNERSVILLE Indiana 47331 0.005 Screened Out

GOODWIN CO GARDEN GROVE California 92841 0.005 Screened Out

INTEL CORP CHANDLER Arizona 85248 0.005 Screened Out

Page 14 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

CAR CARE PACKAGING LLC INDIANAPOLIS Indiana 46203 0.005 Screened Out

INDEPENDENT INK INC GARDENA California 90248 0.005 Screened Out

CUSTOM SYNTHESIS LLC ANDERSON South Carolina 29625 0.005 Screened Out

CR BRANDS INC SPARTANBURG South Carolina 29306 0.005 Screened Out

SHIELD PACKAGING CO INC DUDLEY Massachusetts 01571 0.005 Screened Out

ACTEGA RADCURE INC WAYNE New Jersey 07470 0.005 Screened Out

WORWAG COATINGS LLC NA LAFAYETTE Indiana 47905 0.005 Screened Out

UNIVAR USA INC MORRISVILLE BRANCH MORRISVILLE Pennsylvania 19067 0.0045 Screened Out

SUPERIOR OIL CO INC INDIANAPOLIS Indiana 46225 0.0045 Screened Out

ASHLAND DISTRIBUTION CO CLEARFIELD Utah 84016 0.0045 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

ROCKFORD Illinois 61104 0.0045 Screened Out

SUPERIOR SOLVENTS & CHEMICALS LOUISVILLE Kentucky 40216 0.004 Screened Out

OMNIUM HAMPTON Iowa 50441 0.004 Screened Out

COGNIS CORP -- CHARLOTT E PLANT CHARLOTTE North Carolina 28273 0.004 Screened Out

KING INDUSTRIES INC NORWALK Connecticut 06852 0.004 Screened Out

UNIVAR USA INC HOUSTON HOUSTON Texas 77061 0.0035 Screened Out

CALLAHAN CHEMICAL CO WALPOLE Massachusetts 02081 0.0035 Screened Out

ENGINEERED POLYMER SOLUTIONS INC CITY OF COMMERCE California 90040 0.0035 Screened Out

CARESTREAM HEALTH COLORADO WINDSOR Colorado 80550 0.0035 Screened Out

BAKER PETROLITE BAYPORT FACILI TY PASADENA Texas 77507 0.0035 Screened Out

GENERAL DYNAMICS ORDNANCE & TACTICAL SYSTEMS 

GARLAND

GARLAND Texas 75040 0.003 Screened Out

BAKER PETROLITE BAKERSFIELD California 93308 0.003 Screened Out

NORLITE CORP COHOES New York 12047 0.003 Screened Out

FORD MOTOR CO DEARBORN DIVERSIFIED MANUFACTURING DEARBORN Michigan 48121 0.003 Screened Out

CALLAHAN CHEMICAL CO PALMYRA New Jersey 08065 0.003 Screened Out

HEXION SPECIALTY CHEMICALS INC LYNWOOD California 90262 0.003 Screened Out

DYNASOL INC CANTON Massachusetts 02021 0.003 Screened Out

ROHM & HAAS CHEMICALS LLC KNOXVILLE SITE KNOXVILLE Tennessee 37921 0.0025 Screened Out

CLEARWATER INTERNATIONAL LLC ELMENDORF Texas 78112 0.0025 Screened Out

SHERWIN-WILLIAMS CO FERNLEY Nevada 89408 0.0025 Screened Out

BRYCE CO LLC MEMPHIS Tennessee 38118 0.0025 Screened Out

SCOT LABORATORIES CHAGRIN FALLS Ohio 44023 0.0025 Screened Out

US ECOLOGY TEXAS INC ROBSTOWN Texas 78380 0.0025 Screened Out

BAKER PETROLITE CORP HOUSTON Texas 77049 0.0025 Screened Out

FINGER LAKES CHEMICAL INC ROCHESTER New York 14605 0.0025 Screened Out

UNIVAR USA INC MEMPHIS MEMPHIS Tennessee 38118 0.0025 Screened Out

NIACET CORP NIAGARA FALLS New York 14304 0.0025 Screened Out

HERCULES INC HOPEWELL Virginia 23860 0.0025 Screened Out

CONOCOPHILLIPS CO TREMLEY POINT TERMINAL LINDEN New Jersey 07036 0.0025 Screened Out

BASF CORP SEAFORD Delaware 19973 0.0025 Screened Out

MAINTEX INC CITY OF INDUSTRY California 91746 0.0025 Screened Out

MALLINCKRODT BAKER INC PHILLIPSBURG New Jersey 08865 0.0025 Screened Out

INTEL CORP RIO RANCHO New Mexico 87124 0.0025 Screened Out

ATOTECH USA ROCK HILL South Carolina 29730 0.0025 Screened Out

SINCLAIR WYOMING REFINING CO SINCLAIR Wyoming 82334 0.0025 Screened Out

UNIVAR USA INC DENVER DENVER Colorado 80216 0.0025 Screened Out

UNION SPECIALTIES INC NEWBURYPORT Massachusetts 01950 0.0025 Screened Out

MAHONING PAINT CORP YOUNGSTOWN Ohio 44502 0.0025 Screened Out

CR BRANDS INC SPARTANBURG South Carolina 29307 0.0025 Screened Out

MAGNABLEND INC-CENTRAL PLANT WAXAHACHIE Texas 75165 0.0025 Screened Out

WYNNEWOOD REFINING CO WYNNEWOOD Oklahoma 73098 0.0025 Screened Out

CONOCOPHILLIPS MT VERNON PRODUCTS TERMINAL MOUNT VERNON Missouri 65712 0.0025 Screened Out

CHEMTEX LABORATORIES INC CONCORD North Carolina 28025 0.0025 Screened Out

ECP INC WOODRIDGE WOODRIDGE Illinois 60517 0.0025 Screened Out

CLEAN HARBORS ENVIRONMENTAL SERVICES INC KIMBALL Nebraska 69145 0.0025 Screened Out

UNIVAR USA INC SALEM BRANCH SALEM Massachusetts 01970 0.002 Screened Out

COSMETIC LABORATORIES OF AMERICA CHATSWORTH California 91311 0.002 Screened Out

GIANT CEMENT CO HARLEYVILLE South Carolina 29448 0.002 Screened Out

SHERWIN-WILLIAMS CO BEDFORD HEIGHTS Ohio 44146 0.002 Screened Out

3M COTTAGE GROVE CENTER COTTAGE GROVE Minnesota 55016 0.002 Screened Out

DOBER CHEMICAL CORP MIDLOTHIAN Illinois 60445 0.002 Screened Out

MILPORT ENTERPRISES INC MILWAUKEE Wisconsin 53207 0.002 Screened Out

DUPONT EKC TECHNOLOGY HAYWARD California 94545 0.002 Screened Out

UNIVAR USA INC- CINCINNATI OH BRANCH CINCINNATI Ohio 45246 0.002 Screened Out

ASTRO CHEMICALS INC SPRINGFIELD Massachusetts 01104 0.002 Screened Out

FUJIFILM HUNT CHEMICALS USA INC ROLLING MEADOWS Illinois 60008 0.002 Screened Out

SHERWIN-WILLIAMS CO ORLANDO Florida 32809 0.0015 Screened Out

CLEARWATER INTERNATIONAL LLC LEETSDALE Pennsylvania 15056 0.0015 Screened Out

DELTA HOUSTON DEER PARK Texas 77536 0.0015 Screened Out

BUCKMAN LABORATORIES INC MEMPHIS Tennessee 38108 0.0015 Screened Out

Page 15 of 16
Table C-1. Comparisons of 2009 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code

2009 Air 

Emissions 

(tpy)

Outcome

HYDRITE CHEMICAL CO MILWAUKEE Wisconsin 53223 0.0015 Screened Out

KELLY-MOORE PAINT CO INC SAN CARLOS California 94070 0.0015 Screened Out

CHEMICAL SOLVENTS INC--DENISON FACILITY CLEVELAND Ohio 44109 0.0015 Screened Out

BAKER PETROLITE-RAYNE FACILITY RAYNE Louisiana 70578 0.0015 Screened Out

HUNTSMAN PETROCHEMICAL LLC DAYTON Texas 77535 0.001 Screened Out

FORD MOTOR CO DEARBORN TOOL & DIE PLANT DEARBORN Michigan 48121 0.001 Screened Out

PENRAY COMPANIES INC WHEELING Illinois 60090 0.001 Screened Out

PENRAY COMPANIES INC ELK GROVE VILLAGE Illinois 60007 0.001 Screened Out

FIRST SOURCE WORLDWIDE LLC MILWAUKEE MILWAUKEE Wisconsin 53226 0.001 Screened Out

DSM NEORESINS INC FRANKFORT Indiana 46041 0.001 Screened Out

SHERWIN-WILLIAMS CO OLIVE BRANCH Mississippi 38654 0.001 Screened Out

SHERWIN-WILLIAMS CO MEMPHIS Tennessee 38109 0.001 Screened Out

VOLTAIX LLC BRANCHBURG New Jersey 08876 0.001 Screened Out

NALCO CO TEXARKANA Texas 75501 0.001 Screened Out

HONEYWELL-PRESTONE PRODUCTS CORP FREEHOLD New Jersey 07728 0.001 Screened Out

BRENNTAG SOUTHEAST INC CHARLOTTE North Carolina 28273 0.001 Screened Out

PPG ARCHITECTURAL COATINGS LOUISVILLE Kentucky 40214 0.001 Screened Out

HENTZEN COATINGS,INC MILWAUKEE Wisconsin 53218 0.001 Screened Out

RIKER PRODUCTS INC TOLEDO Ohio 43612 0.001 Screened Out

VEYANCE TECHNOLOGIES INC MOUNT PLEASANT Iowa 52641 0.0005 Screened Out

LEVLAD CHATSWORTH California 91311 0.0005 Screened Out

MARY KAY INC DALLAS Texas 75247 0.0005 Screened Out

GOODYEAR TIRE & RUBBER CO UNION CITY Tennessee 38261 0.0005 Screened Out

SAFETY-KLEEN SYSTEMS INC LINDEN New Jersey 07036 0.0005 Screened Out

CLARIANT CORP CLEAR LAKE PLANT PASADENA Texas 77507 0.0005 Screened Out

NATIONAL INDUSTRIAL COATINGS INC DBA NICOAT INC ITASCA Illinois 60143 0.0005 Screened Out

IFF AUGUSTA LTD AUGUSTA Georgia 30906 0.0005 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A VALSPAR 

COATINGS

SACRAMENTO California 95826 0.0005 Screened Out

SHERWIN-WILLIAMS CO FLORA Illinois 62839 0.0005 Screened Out

LANCO MANUFACTURING CORP SAN LORENZO Puerto Rico 00754 0.0005 Screened Out

MEADWESTVACO SC LLC CHARLESTON CHEMICAL PLANT NORTH CHARLESTON South Carolina 29406 0.0005 Screened Out

SOLITE LLC ARVONIA Virginia 23004 0.0005 Screened Out

LAMBERTI SYNTHESIS USA INC CHATTANOOGA Tennessee 37406 0.0005 Screened Out

tpy: tons per year

Page 16 of 16
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

REXAM BEVERAGE CAN CO RE: WINSTON SALEM 

PLANT

WINSTON-SALEM North Carolina 27107 188.7835 Retain

BALL METAL BEVERAGE CONTAINER CORP WILLIAMSBURG Virginia 23185 178.5 Retain

BALL METAL BEVERAGE CONTAINER CORP FINDLAY Ohio 45840 155 Retain

CROWN FOOD PACKAGING OWATONNA Minnesota 55060 122.646 Retain

REXAM BEVERAGE CAN CO RE: FREMONT PLANT FREMONT Ohio 43420 106.3225 Retain

REXAM BEVERAGE CAN CO RE: BISHOPVILLE SC 

FACILITY

BISHOPVILLE South Carolina 29010 96.762 Retain

CROWN CORK & SEAL CO (USA) INC CROWN 

CLOSURE DIV

WEIRTON West Virginia 26062 96.088 Retain

BALL METAL BEVERAGE CONTAINER CORP REIDSVILLE North Carolina 27320 94.5 Retain

BMW MANUFACTURING CO LLC GREER South Carolina 29651 91.2125 Retain

REXAM BEVERAGE CAN CO RE: EVA STREET ST PAUL 

MN

SAINT PAUL Minnesota 55107 89.498 Retain

REXAM BEVERAGE CAN CO KENT WA FACILITY KENT Washington 98032 83.081 Retain

CROWN BEVERAGE PACKAGING OLYMPIA Washington 98501 77.6895 Retain

REXAM BEVERAGE CAN CO OLIVE BRANCH FACILITY OLIVE BRANCH Mississippi 38654 76.824 Retain

BALL CONTAINER LLC COLUMBUS CAN PLANT COLUMBUS Ohio 43213 76.5 Retain

SILGAN CONTAINERS MANUFACTURING CORP LA PORTE Indiana 46350 68.35 Retain

AURORA CASKET CO INC AURORA Indiana 47001 68.17917 Retain

REXAM BEVERAGE CAN CO RE : CHICAGO PLANT CHICAGO Illinois 60609 68.005 Retain

REXAM BEVERAGE CAN CO RE: WHITEHOUSE PLANT WHITEHOUSE Ohio 43571 67.836 Retain

FORD MOTOR CO DEARBORN TRUCK PLANT DEARBORN Michigan 48121 66.5 Retain

CROWN BEVERAGE PACKAGING BRADLEY Illinois 60915 64.0775 Retain

CROWN BEVERAGE PACKAGING LAWRENCE Massachusetts 01843 62.726 Retain

REXAM BEVERAGE CAN CO LONGVIEW FACILITY LONGVIEW Texas 75604 57.4525 Retain

WHIRLPOOL CORP MARION D IVISION MARION Ohio 43302 57.2125 Retain

BALL CONTAINER LLC ROME CAN PLANT ROME Georgia 30161 55.5 Retain

METAL CONTAINER CORPORTION - WINDSOR CAN 

PLANT

WINDSOR Colorado 80550 54.9985 Retain

FORD MOTOR COMPANY--KANSAS CITY ASSEMBLY 

PLANT

CLAYCOMO Missouri 64119 51.5 Retain

CROWN BEVERAGE PACKAGING WORLAND Wyoming 82401 51.128 Retain

HONDA OF AMERICA MANUFACTURING INC EAST LIBERTY Ohio 43319 47.2 Retain

METAL CONTAINER CORP - ARNOLD CAN PLANT ARNOLD Missouri 63010 46.317 Retain

BWAY CORP HOMERVILLE Georgia 31634 45.9635 Retain

REXAM BEVERAGE CAN CO CHATSWORTH FACILITY CHATSWORTH California 91311 44.4135 Retain

EDSAL MANUFACTURING CO INC CHICAGO Illinois 60609 43.1447 Retain

RR DONNELLEY HARRISONBURG Virginia 22802 42.3835 Retain

HONDA OF AMERICA MANUFACTURING INC MARYSVILLE Ohio 43040 42.3 Retain

METAL CONTAINER CORP - NEWBURGH CAN PLANT NEW WINDSOR New York 12553 42.266 Retain

REXAM BEVERAGE CAN CO PHOENIX FACILITY PHOENIX Arizona 85043 38.161 Retain

BALL METAL BEVERAGE CONTAINER CORP MILWAUKEE Wisconsin 53224 38 Retain

MAGNA STEYR NORTH AMERICA TOLEDO Ohio 43608 37.65 Retain

CHICAGO HEIGHTS STEEL CHICAGO HEIGHTS Illinois 60411 37.48 Retain

CROWN BEVERAGE PACKAGING CONROE Texas 77305 35.875 Retain

SUBARU OF INDIANA AUTOMOTIVE INC LAFAYETTE Indiana 47905 35.69 Retain

CHRYSLER JEFFERSON NORTH ASSEMBLY PLANT DETROIT Michigan 48215 35.6 Retain

NISSAN NA INC SMYRNA MANUFACTURING PLANT SMYRNA Tennessee 37167 35.5795 Retain

ROCKY MOUNTAIN METAL CONTAINER GOLDEN Colorado 80401 35.5 Retain

FORD MOTOR CO KENTUCKY TRUCK PLANT LOUISVILLE Kentucky 40241 35.4 Retain

SILGAN CONTAINERS MANUFACTURING CORP PLOVER Wisconsin 54467 35.35 Retain

METAL CONTAINER CORP - JACKSONVILLE CAN 

PLANT

JACKSONVILLE Florida 32254 34.9825 Retain

GREIF PACKAGING LLC FLORENCE Kentucky 41042 34.946 Retain

CROWN FOOD PACKAGING BALTIMORE Maryland 21221 34.066 Retain

CROWN BEVERAGE PACKAGING SUGAR LAND Texas 77478 32.335 Retain

METAL CONTAINER CORP - MIRA LOMA CAN PLANT MIRA LOMA California 91752 32.253 Retain

BALL METAL BEVERAGE CONTAINER CORP TORRANCE California 90503 32 Retain

BERENFIELD CONTAINERS SE LTD HARRISBURG North Carolina 28075 31.510045 Retain

SENECA FOODS CORP BARABOO Wisconsin 53913 30.575 Retain

THERMA-TRU CORP BUTLER Indiana 46721 29.7775 Retain

BALL METAL BEVERAGE CONTAINER CORP GOLDEN Colorado 80403 29 Retain

BALL METAL BEVERAGE CONTAINER CORP MONTICELLO Indiana 47960 28.5 Retain

CROWN BEVERAGE PACKAGING CAROLINA Puerto Rico 00985 27.6395 Retain

S B FOOT TANNING CO RED WING Minnesota 55066 27.586 Retain

DEXTER CHASSIS GROUP PLANT 55 WHITE PIGEON Michigan 49099 26.3225 Retain

MERCEDES-BENZ US INTERNATIONAL INC VANCE Alabama 35490 25.946605 Retain

PPG INDUSTRIES INC-OAK CREEK OAK CREEK Wisconsin 53154 25.631 Retain

INGERSOLL-RAND CO STEELCRAFT DIV CINCINNATI Ohio 45242 25.585 Retain

Page 1 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

ALLIED TUBE & CONDUIT CORP HARVEY Illinois 60426 25.519 Retain

BWAY CORP CHICAGO Illinois 60623 25.49802 Retain

GM TRUCK GROUP FLINT ASSEMBLY PLANT VAN 

SLYKE COMPLEX

FLINT Michigan 48551 24.95 Retain

ROLL COATER INC GREENFIELD Indiana 46140 24.2775 Retain

NYW REALTY LLC/ HANOVER HANOVER Pennsylvania 17331 24.2 Retain

TOYOTA MOTOR MANUFACTURING INDIANA INC PRINCETON Indiana 47670 24.1785 Retain

CROWN BEVERAGE PACKAGING CHERAW South Carolina 29520 24.1435 Retain

BALL METAL BEVERAGE CONTAINER CORP TAMPA Florida 33617 24 Retain

HONDA MANUFACTURING OF ALABAMA LLC LINCOLN Alabama 35096 23.9835 Retain

CROWN BEVERAGE PACKAGING LA CROSSE Wisconsin 54603 23.799 Retain

S D WARREN CO WESTBROOK Maine 04098 23.5025 Retain

GENERAL MOTORS LANSING DELTA TOWNSHIP LANSING Michigan 48917 23.5 Retain

WHIRLPOOL CORP - CLYDE DIV CLYDE Ohio 43410 23.358 Retain

GREIF PACKAGING LLC ALSIP Illinois 60803 23.257 Retain

BALL METAL FOOD CONTAINER CORP WEIRTON West Virginia 26062 22.5 Retain

CROWN BEVERAGE PACKAGING BATESVILLE Mississippi 38606 22.4855 Retain

WHIRLPOOL CORP FINDLAY DIV FINDLAY Ohio 45840 22.375 Retain

MOBIL CHEMICAL CO SHAWNEE Oklahoma 74804 21.875 Retain

AMES TRUE TEMPER INC HARRISBURG PENNSYLVANIA 17104 21.639 Retain

MEMC PASADENA INC PASADENA Texas 77503 21.563 Retain

NORTH COAST CONTAINER CORP CLEVELAND Ohio 44105 21.231 Retain

BALL CONTAINER LLC FORT ATKINSON Wisconsin 53538 20.85 Retain

AIR SYSTEM COMPONENTS LP PONCA CITY Oklahoma 74601 20.6415 Retain

PELLA CORP PELLA Iowa 50219 20.3955 Retain

BALL METAL BEVERAGE CONTAINER CORP SARATOGA SPRINGS New York 12866 20.35 Retain

MID-AMERICA STEEL DRUM CO IN C OAK CREEK WISCONSIN 53154 20.3365 Retain

BATESVILLE MANUFACTURING INC MANCHESTER Tennessee 37355 20.3255 Retain

CECO DOOR PRODUCTS MILAN Tennessee 38358 20.165 Retain

BALL METAL BEVERAGE CONTAINER CORP FAIRFIELD California 94533 19.5 Retain

CROWN BEVERAGE PACKAGING CRAWFORDSVILLE Indiana 47933 18.97 Retain

BALL METAL BEVERAGE CONTAINER CORP CONROE Texas 77303 18.55 Retain

THOMAS BUILT BUSES INC HIGH POINT NORTH CAROLINA 27263 17.92 Retain

UNION CARBIDE CORP SEADRIFT PLANT SEADRIFT Texas 77983 17.4725 Retain

AIR SYSTEM COMPONENTS LP TARBORO North Carolina 27886 16.7595 Retain

NASHVILLE WIRE PRODUCTS NASHVILLE Tennessee 37218 16.7 Retain

ALSTOM POWER INC PLATE FORMED PRODUCTS DIV CHATTANOOGA Tennessee 37402 16.67 Retain

OLDCASTLE BUILDING ENVELOPE TEXAS FACILITY TERRELL Texas 75160 16.5975 Retain

SPECTRUM METAL FINISHING YOUNGSTOWN Ohio 44512 16.53 Retain

TOKICO (USA) INC BEREA Kentucky 40403 16.4665 Retain

SEIDEL TANNING CORP MILWAUKEE Wisconsin 53212 15.463 Retain

METAL INDUSTRIES INC - BUSHNELL BUSHNELL Florida 33513 14.8635 Retain

NEW UNITED MOTOR MANUFACTURING INC FREMONT California 94538 14.564 Retain

EASTMAN CHEMICAL CO TEXAS OPERATIONS LONGVIEW Texas 75602 14.5535 Retain

USS - CLAIRTON WORKS CLAIRTON Pennsylvania 15025 14.5 Retain

LAKESIDE LITHOGRAPHY LLC CHICAGO Illinois 60608 14.275 Retain

JOHNSON WELDED PRODUCTS INC URBANA Ohio 43078 14.1725 Retain

BEDFORD MATERIALS CO INC MANNS CHOICE Pennsylvania 15550 14.104 Retain

BALL METAL BEVERAGE CONTAINER CORP MIDDLETOWN New York 10940 14 Retain

QUAD/GRAPHICS INC HARTFORD Wisconsin 53027 13.935 Retain

BEMIS MANUFACTURING CO PLANT B SHEBOYGAN FALLS Wisconsin 53085 13.9125 Retain

SILGAN WHITE CAP CORP EVANSVILLE Indiana 47710 13.9 Retain

CROWN FOOD PACKAGING TOLEDO Ohio 43612 13.8175 Retain

GERSTENSLAGER CO WOOSTER Ohio 44691 13.79 Retain

ROYAL MOULDINGS LTD; MARION VIRGINIA MARION Virginia 24354 13.7645 Retain

TOPPAN INTERAMERICA INC MC DONOUGH Georgia 30253 13.7 Retain

M&B HANGERS LEEDS Alabama 35094 13.661 Retain

HART & COOLEY INC HUNTSVILLE Alabama 35811 13.637 Retain

KNAPHEIDE MANUFACTURING CO QUINCY Illinois 62305 13.6135 Retain

CROWN FOOD PACKAGING HANOVER Pennsylvania 17331 13.5285 Retain

NUCOR VULCRAFT GROUP GRAPELAND DIV GRAPELAND Texas 75844 13.507 Retain

BALL METAL BEVERAGE CONTAINER CORP FORT WORTH Texas 76140 13.5 Retain

DECORATIVE PANELS INTERNATIONA L TOLEDO Ohio 43607 13.32944 Retain

L A DARLING CO - PIGGOTT AR FACILITY PIGGOTT Arkansas 72454 13.31 Retain

AGY AIKEN LLC AIKEN South Carolina 29801 13.1095 Retain

BALL METAL BEVERAGE CONTAINER CORP KAPOLEI Hawaii 96707 12.8 Retain

3M CO - GUIN GUIN Alabama 35563 12.751 Retain

TOYOTA MOTOR MANUFACTURING KENTUCKY INC GEORGETOWN Kentucky 40324 12.677 Retain

AMERICAN TRIM LLC SIDNEY Ohio 45365 12.659 Retain

KEYMARK CORP OF FLORIDA LAKELAND Florida 33810 12.3785 Retain

TRI VULCRAFT OF NEW YORK INC CHEMUNG New York 14825 12.2325 Retain

Page 2 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

VESTAL MANUFACTURING ENTERPRISES INC SWEETWATER Tennessee 37874 12.168 Retain

GM TRUCK GROUP FORT WAYNE ASSEMBLY ROANOKE Indiana 46783 12.15 Retain

NOVELIS CORP WARREN Ohio 44483 12.122 Retain

BERENFIELD CONTAINERS INC MASON MASON Ohio 45040 11.7955 Retain

HOWARD FINISHING LLC MADISON HEIGHTS Michigan 48071 11.7535 Retain

SILGAN CONTAINERS MANUFACTURING CORP MOUNT VERNON Missouri 65712 11.677 Retain

FRANKLIN INVESTMENT CORP FRANKLIN Pennsylvania 16323 11.6 Retain

MEYER STEEL DRUM INC CHICAGO Illinois 60623 11.337 Retain

CARRY-ON TRAILER CORP LAVONIA GEORGIA 30553 11.244 Retain

CHICAGO STEEL CONTAINER CORP CHICAGO Illinois 60623 11.1945 Retain

FORD MOTOR COMPANY-WAYNE ASSEMBLY WAYNE Michigan 48184 11.125 Retain

PRECOAT METALS JACKSON Mississippi 39272 11.0325 Retain

BOEING COMMERCIAL AIRPLANE GROUP - EVERETT EVERETT Washington 98204 11 Retain

PHOENIX COLOR CORP HAGERSTOWN MARYLAND 21742 11 Retain

GEA BPO LLC BLOOMINGTON Indiana 47404 11 Retain

CARRY-ON TRAILER CORP MEXIA TEXAS 76667 10.7145 Retain

MAVERICK TUBE LLC DBA TENARISCONROE CONROE TEXAS 77301 10.5724638 Retain

ACME FINISHING CO INC ELK GROVE VILLAGE Illinois 60007 10.445 Retain

STATE INDUSTRIES INC ASHLAND CITY TENNESSEE 37015 10.4155 Retain

ANDERSON TULLY LUMBER CO WALTERSVILLE 

LUMBER MILL

VICKSBURG MISSISSIPPI 39181 10.4095 Retain

NUCOR CORP VULCRAFT/NUCOR COLD FINISH DIV NORFOLK Nebraska 68701 10.26 Retain

SILGAN CAN CO MAXTON North Carolina 28364 10.1855 Retain

SYCAMORE SYSTEMS LLC SYCAMORE ILLINOIS 60178 10.144 Retain

ASHLEY INDUSTRIAL MOLDING INC ASHLEY Indiana 46705 10.1 Retain

BERENFIELD CONTAINERS SW LTD WHITE HALL Arkansas 71602 10.0855 Retain

STANLEY WORKS HAND TOOLS DIV NEW BRITAIN Connecticut 06052 9.969 Retain

SILGAN CONTAINERS MANAUFACTURING CORP OCONOMOWOC Wisconsin 53066 9.95 Retain

RR DONNELLEY & SONS CO WILLARD Ohio 44890 9.915 Retain

AKZO NOBEL COATINGS INC BIRMINGHAM Alabama 35234 9.895 Retain

CAN CORP OF AMERICA INC BLANDON Pennsylvania 19510 9.889 Retain

TRILLA ST LOUIS CORP FENTON MISSOURI 63026 9.812685 Retain

NUCOR CORP VULCRAFT DIV FLORENCE South Carolina 29501 9.777 Retain

SAFETY-KLEEN SYSTEMS INC LEXINGTON South Carolina 29073 9.7255 Retain

NUCOR CORP VULCRAFT DIV FORT PAYNE Alabama 35967 9.6915 Retain

YKK AP AMERICA INC DUBLIN Georgia 31021 9.616 Retain

QUAD/GRAPHICS INC SUSSEX Wisconsin 53089 9.595 Retain

SIGNODE BRIDGEVIEW Illinois 60455 9.5 Retain

SQUARE D CO LEXINGTON Kentucky 40511 9.4845 Retain

REXAM BEVERAGE CAN CO FAIRFIELD PLANT FAIRFIELD California 94533 9.37 Retain

KUBIN-NICHOLSON CORP MILWAUKEE Wisconsin 53224 9.296 Retain

NATIONAL COATINGS INC GALESBURG ILLINOIS 61401 9.247 Retain

SILGAN CONTAINERS MANUFACTURING CORP SAINT JOSEPH Missouri 64504 9.015 Retain

GREIF PACKAGING LLC NEW ORLEANS Louisiana 70123 8.708 Retain

ALLIANCE INDUSTRIES WAUPACA WAUPACA Wisconsin 54981 8.605 Retain

LA-Z-BOY TENNESSEE DAYTON Tennessee 37321 8.57306025 Retain

ESCO CORP NEWTON Mississippi 39345 8.5565 Retain

CNH AMERICA LLC GOODFIELD ILLINOIS 61742 8.4305 Retain

WHITING DOOR MANUFACTURING CORP AKRON New York 14001 8.413 Retain

HEXION SPECIALTY CHEMICALS INC LAKELAND Florida 33801 8.3945 Retain

BALL AEROSOL & SPECIALTY CONTAINER INC ELGIN Illinois 60120 8.35 Retain

SILGAN CAN CO NAPOLEON Ohio 43545 8.3375 Retain

SHIELDCOAT TECHNOLOGIES INC (DBA CYBERSHIELD 

OF TEXAS)

LUFKIN Texas 75904 8.303 Retain

KAWNEER CO INC SPRINGDALE Arkansas 72764 8.213 Retain

AM GENERAL LLC MISHAWAKA INDIANA 46545 8.1875 Retain

CNH AMERICA LLC BURLINGTON Iowa 52601 8.175 Retain

SILGAN CONTAINERS MANUFACTURING CORP MENOMONIE Wisconsin 54751 7.85 Retain

CROWN AEROSOL PACKAGING AURORA Illinois 60504 7.8365 Retain

CARRY-ON TRAILER CORP MISSOURI VALLEY Iowa 51555 7.834 Retain

BROAN-NUTONE LLC HARTFORD Wisconsin 53027 7.737 Retain

ROLL COATER LA PORTE Indiana 46350 7.7325 Retain

VON HOFFMANN GRAPHICS INC OWENSVILLE Missouri 65066 7.665 Retain

GMVM-LANSING GRAND RIVER ASSEMBLY LANSING Michigan 48921 7.55 Retain

GREIF INDUSTRIAL PACKAGING & SERVICES WINFIELD Kansas 67156 7.533 Retain

HUTCHENS INDUSTRIES INC MANSFIELD FACILITY MANSFIELD MISSOURI 65704 7.505 Retain

CARRY-ON TRAILER CORP WINNEMUCCA NEVADA 89445 7.4985 Retain

ELECTROPRIME INC ROSSFORD Ohio 43460 7.4105 Retain

DEXTER AXLE EL RENO OKLAHOMA 73036 7.409 Retain

EQUISTAR CHEMICALS BAYPORT CHEMICALS PLANT PASADENA Texas 77507 7.4035 Retain

NAHAN PRINTING INC SAINT CLOUD Minnesota 56303 7.33722 Retain

Page 3 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

TECNOCAP LLC WARREN Ohio 44483 7.305 Retain

SUPERIOR INDUSTRIES INTERNATIONAL ARKANSAS 

LLC

FAYETTEVILLE ARKANSAS 72701 7.3 Retain

U.S. AIR FORCE TINKER AFB OK TINKER A F B Oklahoma 73145 7.3 Retain

CHRYSLER BELVIDERE ASSEMBLY PLANT BELVIDERE Illinois 61008 7.3 Retain

GENERAL MOTORS WENTZVILLE ASSEMBLY WENTZVILLE Missouri 63385 7.25 Retain

ROLL COATER INC WEIRTON West Virginia 26062 7.2295 Retain

WIX FILTRATION CORP - ALLEN PLANT GASTONIA North Carolina 28052 7.2025 Retain

SANYO SOLAR (USA) LLC CARSON California 90745 7.184775 Retain

RR DONNELLEY CRAWFORDSVILLE CRAWFORDSVILLE Indiana 47933 7.1225 Retain

KITZINGER COOPERAGE CORP SAINT FRANCIS Wisconsin 53235 7.09505 Retain

JOHN DEERE DES MOINES WORKS ANKENY IOWA 50023 7.0485 Retain

AVERY DENNISON - IBMD LENOIR LENOIR North Carolina 28645 7.0455 Retain

ALCOA INC - WARRICK OPERATIONS NEWBURGH Indiana 47629 7 Retain

SILGAN CAN CO PARIS Texas 75460 6.953 Retain

ENKEI AMERICA INC COLUMBUS Indiana 47201 6.95 Retain

CARDONE INDUSTRIES PHILADELPHIA Pennsylvania 19120 6.9415 Retain

MAUSER CORP WOODBRIDGE New Jersey 07095 6.8305 Retain

HAMMER PACKAGING CORP WEST HENRIETTA New York 14586 6.7935 Retain

BRIGGS & STRATTON YARD POWER PRODUCTS 

MCDONOUGH OPERATIONS

MC DONOUGH GEORGIA 30253 6.7395 Retain

SUPERIOR INDUSTRIES INTERNATIONAL ARKANSAS 

LLC

ROGERS ARKANSAS 72756 6.735 Retain

AAP ST MARYS CORP SAINT MARYS Ohio 45885 6.7315 Retain

BERENFIELD CONTAINERS INC CLARENDON Pennsylvania 16313 6.726985 Retain

SENECA FOODS CORP CAN PLANT MARION New York 14505 6.6935 Retain

RR DONNELLEY LANCASTER EAST LANCASTER Pennsylvania 17601 6.6375 Retain

CREE INC DURHAM North Carolina 27703 6.601 Retain

HUSQVARNA CONSUMER OUTDOOR PRODUCTS ORANGEBURG South Carolina 29116 6.56 Retain

OWENS CORNING VETROTEX LLC STARR South Carolina 29684 6.559 Retain

WHEELING MACHINE PRODUCTS DIV PINE BLUFF PINE BLUFF ARKANSAS 71602 6.5 Retain

SILGAN CONTAINERS MANUFACTURIN G CORP FORT DODGE IOWA 50501 6.49178 Retain

SKOLNIK INDUSTRIES CHICAGO ILLINOIS 60632 6.45 Retain

NUCOR VULCRAFT GROUP SAINT JOE DIV SAINT JOE Indiana 46785 6.3715 Retain

NISSAN NORTH AMERICA INC CANTON MS CANTON Mississippi 39046 6.3555 Retain

SILGAN CONTAINERS MANUFACTURING CORP HAMMOND Indiana 46320 6.331 Retain

SAPA EXTRUSIONS INC YANKTON South Dakota 57078 6.31004485 Retain

BRADFORD WHITE CORP MIDDLEVILLE Michigan 49333 6.2995 Retain

MAYTAG CORP CLEVELAND COOKING PRODUCTS 

PLANT 1

CLEVELAND Tennessee 37311 6.25 Retain

EFCO CORP MONETT Missouri 65708 6.1935 Retain

HUNTER DOUGLAS TUPELO CENTER SHANNON Mississippi 38868 6.164015 Retain

NAVISTAR INC SPRINGFIELD Ohio 45502 6.1 Retain

SILGAN CAN CO SACRAMENTO California 95824 6.085 Retain

THE COLEMAN CO INC WICHITA KANSAS 67219 6.051 Retain

BOBCAT CO (MELROE) GWINNER NORTH DAKOTA 58040 5.964 Retain

PACKAGING DYNAMICS INC BAGCRAFT/PAPERCON 

DIV

BAXTER SPRINGS Kansas 66713 5.9425 Retain

CHRYSLER WARREN TRUCK ASSEMBLY PLANT (PART) WARREN Michigan 48091 5.915 Retain

GREIF PACKAGING LLC MERCED California 95348 5.866 Retain

AVX CORP MYRTLE BEACH MYRTLE BEACH South Carolina 29577 5.8645 Retain

SCHAEFFER MANUFACTURING SAINT LOUIS Missouri 63104 5.84243 Retain

WORTHINGTON CYLINDERS WISCONSI N LLC CHILTON Wisconsin 53014 5.8315 Retain

SILGAN CONTAINERS MANUFACTURING CORP ROCHELLE Illinois 61068 5.806 Retain

NAZDAR SHAWNEE SHAWNEE Kansas 66227 5.745 Retain

QUEBECOR WORLD INC WINCHESTER VIRGINIA WINCHESTER Virginia 22603 5.73718 Retain

TACO INC - CRANSTON CRANSTON RHODE ISLAND 02920 5.7195 Retain

METOKOTE CORP PLANT 15 CEDAR FALLS Iowa 50613 5.66847 Retain

INX DIGITAL INK CO DIXON California 95620 5.621 Retain

PRECOAT METALS GRANITE CITY Illinois 62040 5.6115 Retain

SILGAN CONTAINERS MANUFACTURING CORP EDISON New Jersey 08817 5.55 Retain

NOVOLYTE TECHNOLOGIES ZACHARY Louisiana 70791 5.545 Retain

KNS COMPANYS INC CAROL STREAM Illinois 60188 5.496 Retain

LOGAN ALUMINUM INC RUSSELLVILLE Kentucky 42276 5.398 Retain

NOV TUBOSCOPE NAVASOTA NAVASOTA Texas 77868 5.391 Retain

AJAX METAL PROCESSING INC DETROIT MICHIGAN 48207 5.384 Retain

FIBERMARK NORTH AMERICA INC LOWVILLE New York 13367 5.3625 Retain

PPG INDUSTRIES,INC-SPRINGDALE COMPLEX SPRINGDALE Pennsylvania 15144 5.3045 Retain

BATESVILLE MANUFACTURING INC -DOLL PLANT BATESVILLE Indiana 47006 5.297 Retain

AUTOALLIANCE INTERNATIONAL INC FLAT ROCK Michigan 48134 5.28 Retain

ARMSTRONG HARDWOOD FLOORING CO ONEIDA Tennessee 37841 5.22175 Retain

Page 4 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

US ARMY LAKE CITY ARMY AMMUNITION PLANT INDEPENDENCE Missouri 64051 5.166 Retain

RUSKIN CO GENEVA Alabama 36340 5.1155 Retain

PELLA CORP CARROLL OPERATIONS CARROLL IOWA 51401 5.05 Retain

HYDRO ALUMINUM NORTH AMERICA INC MONETT MISSOURI 65708 5.0365 Retain

ALCOA HOME EXTERIORS INC SIDNEY Ohio 45365 5.0325 Retain

RR DONNELLEY LANCASTER WEST LANCASTER Pennsylvania 17601 4.8597 Screened Out

CIRCLE GRAPHICS INC LONGMONT Colorado 80501 4.85 Screened Out

PRECOAT METALS HOUSTON Texas 77015 4.815 Screened Out

PHOENIX CONTAINER INC NORTH BRUNSWICK New Jersey 08902 4.773 Screened Out

SILGAN CONTAINER MANUFACTURING CORP RIVERBANK California 95367 4.728 Screened Out

CROWN AEROSOL PACKAGING FARIBAULT Minnesota 55021 4.7155 Screened Out

HYUNDAI MOTOR MANUFACTURING ALABAMA LLC MONTGOMERY Alabama 36105 4.714 Screened Out

AK STEEL CORP - ZANESVI LLE WORKS ZANESVILLE Ohio 43701 4.7 Screened Out

COLOR COMMUNICATIONS INC CHICAGO Illinois 60624 4.65 Screened Out

PRECOAT METALS SAINT LOUIS Missouri 63116 4.6395 Screened Out

FORD MOTOR CO TWIN CITIES ASSEMBLY PLANT SAINT PAUL Minnesota 55116 4.59 Screened Out

PRIME TANNING CO - HARTLAND HARTLAND Maine 04943 4.587 Screened Out

RR DONNELLEY-WETMORE PLANT HOUSTON TEXAS 77043 4.5785 Screened Out

VOLVO TRUCKS NORTH AMERICA DUBLIN VIRGINIA 24084 4.55 Screened Out

R R DONNELLEY & SONS CO DANVILLE DIV DANVILLE Kentucky 40422 4.5025 Screened Out

NESTLE PURINA PETCARE WEIRTON West Virginia 26062 4.485 Screened Out

IMPRESS USA INC TERMINAL ISLAND California 90731 4.475 Screened Out

BROWN PRINTING CO WASECA Minnesota 56093 4.474 Screened Out

CURTIS METAL FINISHING CO STERLING HEIGHTS Michigan 48313 4.4615 Screened Out

ARVINMERITOR HEAVY VEHICLE SYSTEMS LLC YORK South Carolina 29745 4.4225 Screened Out

WORLDCOLOR CLARKSVILLE Tennessee 37040 4.3865 Screened Out

ENDICOTT INTERCONNECT TECHNOLOGIES INC ENDICOTT New York 13760 4.3655 Screened Out

TTM TECHNOLOGIES INC LOGAN Utah 84321 4.32 Screened Out

MERIX CORP FOREST GROVE Oregon 97116 4.273 Screened Out

INLAND LABEL & MARKETING LA CROSSE Wisconsin 54601 4.2335 Screened Out

SAPA EXTRUDER INC GAINESVILLE Georgia 30504 4.226 Screened Out

CARRY-ON TRAILER CORP MONTROSS VIRGINIA 22520 4.1765 Screened Out

GENIE INDUSTRIES SOUTH CAMPUS REDMOND Washington 98052 4.14645 Screened Out

SEQUA COATINGS CORP-PRECOAT M ETALS DIV PORTAGE Indiana 46368 4.1135 Screened Out

BROWN PRINTING CO WOODSTOCK Illinois 60098 4.005 Screened Out

METAL COATERS MISSISSIPPI JACKSON Mississippi 39272 3.9925 Screened Out

HIRSH INDUSTRIES INC DOVER Delaware 19904 3.984 Screened Out

BALL METAL FOOD CONTAINER CORP OAKDALE California 95361 3.984 Screened Out

SILGAN CONTAINERS MANUFACTURING CORP MENOMONEE FALLS Wisconsin 53051 3.95 Screened Out

GENERAL MOTORS CORP LORDSTOWN COMPLEX LORDSTOWN Ohio 44481 3.9 Screened Out

BETCO CORP TOLEDO Ohio 43607 3.885 Screened Out

QUEBECOR WORLD DIRECT-PETTY EFFINGHAM Illinois 62401 3.83 Screened Out

MAGNA MIRRORS CORP - NEWAYGO NEWAYGO MICHIGAN 49337 3.8065 Screened Out

GMTG - SHREVEPORT ASSEMBLY SHREVEPORT Louisiana 71129 3.745 Screened Out

VAN CAN CO FONTANA California 92337 3.7 Screened Out

CROWN FOOD PACKAGING PORTLAND Oregon 97203 3.6305 Screened Out

GREIF PACKAGING LLC WARMINSTER Pennsylvania 18974 3.5965 Screened Out

BROWN PRINTING CO EAST GREENVILLE Pennsylvania 18041 3.5415 Screened Out

AFTON CHEMICAL CORP ORANGEBURG South Carolina 29115 3.5095 Screened Out

RR DONNELLEY & SONS CO MATTOON ILLINOIS 61938 3.465 Screened Out

TITAN COATINGS INC BESSEMER Alabama 35023 3.42 Screened Out

TTM PRINTED CIRCUIT GROUP - S TAFFORD DIV STAFFORD Connecticut 06075 3.3675 Screened Out

TORO CO TOMAH Wisconsin 54660 3.331 Screened Out

ALERIS ROLLED PRODUCTS INC LEWISPORT Kentucky 42351 3.3235 Screened Out

AVERY DENNISON INDUSTRIAL PRODUCTS DIV STRONGSVILLE Ohio 44149 3.316 Screened Out

BRILLION IRON WORKS INC BRILLION Wisconsin 54110 3.30905 Screened Out

SILGAN CONTAINERS MANUFACTURING CORP LYONS New York 14489 3.2625 Screened Out

GM SPRING HILL MANUFACTURING SPRING HILL Tennessee 37174 3.2565 Screened Out

QUAD/GRAPHICS INC WEST ALLIS WISCONSIN 53214 3.255 Screened Out

BATESVILLE MANUFACTURING INC BATESVILLE Mississippi 38606 3.2525 Screened Out

PRECOAT METALS HUEYTOWN Alabama 35023 3.2315 Screened Out

MIDDLEBURY HARDWOOD PRODUCTS MIDDLEBURY INDIANA 46540 3.2215 Screened Out

WORLDCOLOR LEBANON DIV LEBANON Ohio 45036 3.186 Screened Out

CADON PLATING CO WYANDOTTE Michigan 48192 3.136775 Screened Out

SONOCO PHOENIX - PRESIDENTS ISLAND MEMPHIS Tennessee 38113 3.122 Screened Out

RR DONNELLEY STRASBURG DIV STRASBURG Virginia 22657 3.1 Screened Out

BASF CORP - CLEAR LAKE PLANT PASADENA Texas 77507 3.079167767 Screened Out

SPRAYLAT CORP CA LOS ANGELES California 90016 3.075 Screened Out

RR DONNELLEY LOS ANGELES MANUFACTURING TORRANCE California 90502 3.0235 Screened Out

JELD-WEN CRAIGSVILLE WEST VIRGINIA 26205 3.0215 Screened Out

KAWASAKI MOTORS MANUFACTURING CORP USA LINCOLN Nebraska 68524 2.951 Screened Out

VERTIS COMMUNICATIONS COLUMBUS Ohio 43228 2.8845 Screened Out

Page 5 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

DOW CHEMICAL CO MIDLAND Michigan 48667 2.85 Screened Out

QUAD/GRAPHICS INC LOMIRA WISCONSIN 53048 2.843 Screened Out

TOYOTA MOTOR MANUFACTURING TEX AS INC SAN ANTONIO Texas 78264 2.8200666 Screened Out

U.S. AIR FORCE ROBINS AFB GA ROBINS AFB Georgia 31098 2.7925 Screened Out

GM MLCG FAIRFAX ASSEMBLY KANSAS CITY Kansas 66115 2.782 Screened Out

SOLIANT LLC LANCASTER South Carolina 29721 2.758 Screened Out

KIA MOTORS MANUFACTURING OF GEORGIA WEST POINT GEORGIA 31833 2.7465 Screened Out

VERTIS COMMUNICATIONS CHARLOTTE North Carolina 28273 2.6575 Screened Out

ITW DYMON OLATHE Kansas 66061 2.612 Screened Out

FORD MOTOR CO - OHIO ASSEMBLY PLANT AVON LAKE Ohio 44012 2.595 Screened Out

ARR-MAZ CUSTOM CHEMICALS MULBERRY Florida 33860 2.5845 Screened Out

DERRICK CORP CHEEKTOWAGA New York 14225 2.58 Screened Out

TYCO FIRE SUPPRESSION & BUILDING PRODUCTS MARINETTE Wisconsin 54143 2.5585 Screened Out

IC OF OKLAHOMA LLC TULSA Oklahoma 74116 2.55 Screened Out

BWAY CORP BWAY PACKAGING DIV CINCINNATI Ohio 45244 2.54489 Screened Out

BRUNSWICK CORP MERCURY MARINE DIV FOND DU LAC Wisconsin 54935 2.5235 Screened Out

ACCESS BUSINESS GROUP LLC ADA Michigan 49355 2.5035 Screened Out

MISSION KLEENSWEEP PRODUCTS INC LOS ANGELES California 90031 2.5 Screened Out

POWER PARTNERS INC ATHENS Georgia 30607 2.4385 Screened Out

AMERICAN COLOR GRAPHICS MARENGO Iowa 52301 2.429 Screened Out

CENTRIA CAMBRIDGE Ohio 43725 2.4205 Screened Out

CUMMINS POWER GENERATION FRIDLEY Minnesota 55432 2.42 Screened Out

HEWLETT-PACKARD CARIBE BV SITE AGUADILLA Puerto Rico 00605 2.373 Screened Out

VERTIS INC RNS SPRINGFIELD DIV EAST LONGMEADOW MASSACHUSETTS 01028 2.3645 Screened Out

CADMUS SPECIALTY PUBLICATIONS RICHMOND VIRGINIA 23228 2.34746 Screened Out

ROPPE CORP FOSTORIA Ohio 44830 2.345 Screened Out

CCL CONTAINER AEROSOL DIV HERMITAGE Pennsylvania 16148 2.332 Screened Out

AMERICAN COLOR GRAPHICS - LUFKIN LUFKIN Texas 75901 2.304 Screened Out

IVC SOUTH LAWRENCEVILLE Georgia 30043 2.288 Screened Out

BON L MANUFACTURING CO CARTHAGE Tennessee 37030 2.279 Screened Out

NCP COATINGS INC NILES Michigan 49120 2.275 Screened Out

DENSO MANUFACTURING TENNESSEE INC MARYVILLE Tennesee 37801 2.2585 Screened Out

3M CO - HUTCHINSON HUTCHINSON Minnesota 55350 2.2255 Screened Out

HONDA MANUFACTURING OF INDIANA LLC GREENSBURG Indiana 47240 2.2 Screened Out

MPM SILICONES LLC FRIENDLY West Virginia 26146 2.1965 Screened Out

RADIATOR SPECIALTY CO INDIAN TRAIL North Carolina 28079 2.1845 Screened Out

GREIF PACKAGING LLC LA PORTE Texas 77571 2.1395 Screened Out

VANEX INC MOUNT VERNON Illinois 62864 2.1145 Screened Out

RED SPOT WESTLAND INC WESTLAND Michigan 48186 2.104 Screened Out

BENCHMARK ENERGY PRODUCTS LLC MIDLAND Texas 79703 2.103 Screened Out

SABIC INNOVATIVE PLASTICS MT VERNON LLC MOUNT VERNON Indiana 47620 2.1 Screened Out

VERTIS MANASSAS VIRGINIA 20109 2.0505 Screened Out

SAPA INC COATINGS DIVSION PORTLAND Oregon 97218 2.02415295 Screened Out

CLEVELAND STEEL CONTAINER - NI LES NILES Ohio 44446 2.021 Screened Out

DUPONT YERKES PLANT BUFFALO New York 14207 2.0045 Screened Out

CLEVELAND STEEL CONTAINER CORP QUAKERTOWN PENNSYLVANIA 18951 1.995 Screened Out

KEYMARK CORP FONDA New York 12068 1.9865 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

KANKAKEE Illinois 60901 1.9835 Screened Out

ASTRO COATINGS INC STRUTHERS Ohio 44471 1.952 Screened Out

REICHHOLD INC PENSACOLA Florida 32502 1.9355 Screened Out

VERTIS COMMUNICATIONS TAMPA FLORIDA 33611 1.9325 Screened Out

CONSOLIDATED SYSTEMS INC COLUMBIA South Carolina 29201 1.925 Screened Out

WARREN UNILUBE INC WEST MEMPHIS Arkansas 72301 1.899 Screened Out

HANNA STEEL CORP FAIRFIELD Alabama 35064 1.8805 Screened Out

IMPRESS USA INC WEIRTON West Virginia 26062 1.873 Screened Out

DURA COAT PRODUCTS INC MADISON Alabama 35756 1.859 Screened Out

AKZONOBEL AEROSPACE COATINGS WAUKEGAN Illinois 60085 1.834 Screened Out

EQ DETROIT INC DETROIT Michigan 48211 1.8155 Screened Out

FORD LOUISVILLE ASSEMBLY LOUISVILLE Kentucky 40213 1.815 Screened Out

PRO LINE PRINTING / RR DONNELLEY RENO Nevada 89512 1.8 Screened Out

GENERAL MOTORS MLCG DETROIT-HAMTRAMCK 

ASSEM BLY CENTER

DETROIT Michigan 48211 1.79 Screened Out

BALL METAL FOOD CONTAINER CORP SPRINGDALE Arkansas 72764 1.79 Screened Out

COLOR CORP OF AMERICA LOUISVILLE Kentucky 40210 1.765 Screened Out

CAMACO COLUMBUS MANUFACTURING COLUMBUS Nebraska 68601 1.753 Screened Out

EASTMAN CHEMICAL CO TENNESSEE OPERATIONS KINGSPORT Tennessee 37662 1.726 Screened Out

RR DONNELLEY PINEVILLE PINEVILLE North Carolina 28134 1.717 Screened Out

STEELSCAPE INC FAIRFIELD Alabama 35064 1.71311 Screened Out

SILGAN CONTAINERS MANUFACTURING CORP ANTIOCH California 94509 1.7065 Screened Out

FUJIFILM NORTH AMERICA CORP NORTH KANSAS CITY Missouri 64116 1.683 Screened Out

WORLD COLOR PRESS TAUNTON Massachusetts 02780 1.637 Screened Out

Page 6 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

DAIMLERCHRYSLER CORP TOLEDO ASSEMBLY PLANT TOLEDO Ohio 43612 1.60765 Screened Out

RR DONNELLEY VON HOFFMANN CORP JEFFERSON CITY Missouri 65109 1.572395 Screened Out

J L CLARK INC ROCKFORD Illinois 61104 1.5395 Screened Out

DOW CHEMICAL CO - LOUISIANA OPERATIONS PLAQUEMINE Louisiana 70765 1.538 Screened Out

WORLDCOLOR - DYERSBURG DIV DYERSBURG Tennessee 38024 1.529 Screened Out

SILGAN WHITE CAP CORP HAZLETON Pennsylvania 18201 1.5 Screened Out

CENTURY INDUSTRIAL COATINGS I NC JACKSONVILLE Texas 75766 1.4775 Screened Out

TEXAS FINISHING CO CARROLLTON Texas 75006 1.4565 Screened Out

ST CHARLES OPERATIONS (TAFT/STAR) UNION 

CARBIDE CORP

TAFT Louisiana 70057 1.4555 Screened Out

CHRYSLER STERLING HEIGHTS ASSEMBLY PLANT STERLING HEIGHTS Michigan 48312 1.45 Screened Out

WORLDCOLOR STILLWATER (WAS QUEBECOR 

WORLD - STILLWATER DIV)

STILLWATER Oklahoma 74075 1.448 Screened Out

RR DONNELLEY CHARLESTOWN Indiana 47111 1.4255 Screened Out

BAYOU COS INC NEW IBERIA LOUISIANA 70560 1.4245 Screened Out

NICHOLS ALUMINUM ALABAMA INC DECATUR Alabama 35601 1.414 Screened Out

GMC TRUCK GROUP ARLINGTON ASSEMBLY PLANT ARLINGTON Texas 76010 1.41 Screened Out

CARDINAL ALUMINUM CO PLAN T 3 LOUISVILLE Kentucky 40219 1.4025 Screened Out

WHEELING CORRUGATING CO - BEECH BOTTOM 

PLANT

WELLSBURG West Virginia 26070 1.4 Screened Out

OHIO ART CO BRYAN Ohio 43506 1.388 Screened Out

PRO LINE PRINTING ARLINGTON ARLINGTON Texas 76011 1.375 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

ROCHESTER Pennsylvania 15074 1.3745 Screened Out

CHROMASOURCE INC COLUMBIA CITY Indiana 46725 1.338 Screened Out

HALLSTAR CO ESTER SOLUTIONS FACILITY BEDFORD PARK Illinois 60638 1.3125 Screened Out

SHEBOYGAN PAINT CO CEDARTOWN Georgia 30125 1.312 Screened Out

COOK COMPOSITES & POLYMERS CO GRAND RAPIDS Michigan 49507 1.312 Screened Out

TAIYO AMERICA INC CARSON CITY Nevada 89701 1.295 Screened Out

RR DONNELLEY & SONS CO AVON Connecticut 06001 1.2875 Screened Out

CLEVELAND STEEL CONTAINER - PE OTONE FACILITY PEOTONE Illinois 60468 1.267 Screened Out

CATERPILLAR INC LAFAYETTE Indiana 47905 1.2555 Screened Out

GENTEK BUILDING PRODUCTS AVENEL New Jersey 07001 1.248 Screened Out

SUN CHEMICAL CORP SAINT CHARLES Illinois 60174 1.234 Screened Out

AKZO NOBEL COATINGS INC COLUMBUS Ohio 43211 1.225 Screened Out

SPIRALKOTE FLEXIBLE PACKAGING ORLANDO FLORIDA 32837 1.2105 Screened Out

COOK COMPOSITES & POLYMERS CO SAUKVILLE Wisconsin 53080 1.202 Screened Out

SPRAYLAT CORP IL CHICAGO Illinois 60633 1.201 Screened Out

KIK (HOUSTON) INC HOUSTON Texas 77054 1.19 Screened Out

MASCO RETAIL CABINET GROUP LLC WAVERLY Ohio 45690 1.173 Screened Out

CP CONVERTERS INC YORK PENNSYLVANIA 17402 1.17007 Screened Out

MOTOR CASTINGS CO MILWAUKEE Wisconsin 53214 1.159 Screened Out

RED SPOT PAINT & VARNISH CO INC EVANSVILLE Indiana 47711 1.156 Screened Out

JOHN DEERE SEEDING & CYLINDER MOLINE Illinois 61265 1.15 Screened Out

ARANDELL CORP MENOMONEE FALLS Wisconsin 53051 1.1195 Screened Out

W W HENRY BOURBONNAIS Illinois 60914 1.1105 Screened Out

BEAULIEU OF AMERICA PLANT 560-MODEL DALTON Georgia 30721 1.1095 Screened Out

TESORO REFINING & MARKETING CO - MANDAN 

REFINERY

MANDAN North Dakota 58554 1.1005 Screened Out

IVC INDUSTRIAL COATINGS INC INDIANAPOLIS Indiana 46218 1.0982 Screened Out

VANGUARD PAINTS & FINISHES INC MARIETTA Ohio 45750 1.078 Screened Out

WINSLOW-BROWNING INC LIBERTY Indiana 47353 1.077 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

GARLAND Texas 75042 1.068 Screened Out

POLYMERIC IMAGING INC NORTH KANSAS CITY Missouri 64116 1.0665 Screened Out

3M CO - BROWNWOOD BROWNWOOD Texas 76801 1.0435 Screened Out

COMPLEMENTARY COATINGS CORP BALTIMORE Maryland 21224 1.029 Screened Out

UNITED PAINT & CHEMICAL SOUTHFIELD Michigan 48034 1.023 Screened Out

COOK COMPOSITES & POLYMERS CO HOUSTON Texas 77051 1.019 Screened Out

TTM TECHNOLOGIES INC CHIPPEWA FALLS Wisconsin 54729 1.002 Screened Out

GENERAL MOTORS LLC BOWLING GREEN ASSEMBLY 

PLANT

BOWLING GREEN Kentucky 42101 1 Screened Out

TTM TECHNOLOGIES-SANTA CLARA SANTA CLARA California 95050 0.9985 Screened Out

NICHOLS ALUMINUM DAVENPORT DAVENPORT Iowa 52802 0.9965 Screened Out

THREE RIVERS ALUMINUM CO CRANBERRY TOWNSHIP Pennsylvania 16066 0.9945 Screened Out

CANBERRA CORP TOLEDO Ohio 43615 0.975 Screened Out

PPG INDUSTRIES OHIO INC (CL) CLEVELAND Ohio 44111 0.9675 Screened Out

B-WAY PACKAGING INC TRENTON New Jersey 08648 0.952 Screened Out

WESTERN METAL DECORATING CO RANCHO CUCAMONGA CALIFORNIA 91730 0.925 Screened Out

HILLYARD INDUSTRIES INC SAINT JOSEPH Missouri 64501 0.9205 Screened Out

FORBO ADHESIVES LLC MORRIS Illinois 60450 0.896 Screened Out

Page 7 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

NAPCO INC VALENCIA Pennsylvania 16059 0.893 Screened Out

CRYSTAL FINISHING SYSTEMS INC SCHOFIELD Wisconsin 54476 0.89296195 Screened Out

HUNT REFINING CO A CORP TUSCALOOSA Alabama 35401 0.8905 Screened Out

POLARTEC LLC LAWRENCE MASSACHUSETTS 1841 0.89 Screened Out

SUN CHEMICAL CORP MAUMEE Ohio 43537 0.8875 Screened Out

FINISHES UNLIMITED INC SUGAR GROVE Illinois 60554 0.876 Screened Out

UNIVAR USA INC HOUSTON FM 529 HOUSTON TEXAS 77041 0.875 Screened Out

UNIVERSAL CHEMICALS & COATINGS INC ELK GROVE VILLAGE Illinois 60007 0.8735 Screened Out

HB FULLER COVINGTON Georgia 30014 0.863 Screened Out

ARMSTRONG WORLD INDUSTRIES INC STILLWATER Oklahoma 74075 0.85822 Screened Out

MITSUBISHI MOTORS NORTH AMERICA INC NORMAL Illinois 61761 0.8485 Screened Out

GFX INTERNATIONAL GRAYSLAKE Illinois 60030 0.82 Screened Out

CROWN CORK & SEAL CO (USA) INC CROWN 

CLOSURES DIV

LANCASTER Ohio 43130 0.8195 Screened Out

STP PRODUCTS MANUFACTURING CO PAINESVILLE Ohio 44077 0.81 Screened Out

SONOCO PRODUCTS CO ORLANDO Florida 32837 0.81 Screened Out

NEXTEER AUTOMOTIVE CORP SAGINAW Michigan 48601 0.8 Screened Out

FIVE STAR COATINGS GROUP TWIN LAKES WISCONSIN 53181 0.798 Screened Out

PEORIA DISPOSAL CO #1 PEORIA Illinois 61615 0.7925 Screened Out

PPG INDUSTRIES ARCHITECTURAL FINISHES BATAVIA Illinois 60510 0.786 Screened Out

TRELLEBORG OFFSHORE US RANKIN ROAD FACILITY HOUSTON Texas 77073 0.785 Screened Out

SILGAN CONTAINERS MANUFACTURING CORP SAVAGE Minnesota 55378 0.785 Screened Out

KAWNEER CO INC BLOOMSBURG Pennsylvania 17815 0.7755 Screened Out

TCI COATINGS INC LUBBOCK Texas 79415 0.7665 Screened Out

3M CO - CORDOVA CORDOVA Illinois 61242 0.765 Screened Out

STEEL DYNAMICS INC JEFFERSONVILLE Indiana 47130 0.763 Screened Out

WORWAG COATINGS LLC NA LAFAYETTE Indiana 47905 0.7535 Screened Out

RUST-OLEUM CORP PLEASANT PRAIRIE Wisconsin 53158 0.75 Screened Out

SYNDICATE SYSTEMS INC MIDDLEBURY Indiana 46540 0.733 Screened Out

MARCUS PAINT CO LOUISVILLE Kentucky 40202 0.7075 Screened Out

GREIF INDUSTRIAL PACKAGING & SERVICES LLC FONTANA California 92335 0.70305 Screened Out

HOVENSA LLC CHRISTIANSTED Virgin Islands 00820 0.702 Screened Out

WATSON STANDARD CO HARWICK PLANT HARWICK Pennsylvania 15049 0.6935 Screened Out

PPG ARCHITECTURAL FINISHES EAST POINT EAST POINT Georgia 30344 0.691 Screened Out

WESTERN EXTRUSIONS CORP CARROLLTON Texas 75006 0.69 Screened Out

WEST PENN OIL CO, INC130130 WARREN Pennsylvania 16365 0.678 Screened Out

TEXAS TILE MANUFACTURING LLC HOUSTON Texas 77007 0.672 Screened Out

SASOL NORTH AMERICA INC LAKE CHARLES 

CHEMICAL COMPLEX

WESTLAKE Louisiana 70669 0.6685 Screened Out

METALS USA BUILDING PRODUCTS MESQUITE Texas 75149 0.663 Screened Out

KAWNEER CO INC VISALIA California 93291 0.658 Screened Out

ROLL COATER INC BLYTHEVILLE Arkansas 72315 0.6505 Screened Out

PRECOAT METALS ELKRIDGE Maryland 21075 0.634 Screened Out

STEELSCAPE KALAMA Washington 98625 0.632015 Screened Out

TRINKOTE INDUSTRIAL FINISHES INC FORT WORTH Texas 76110 0.628 Screened Out

FLINT GROUP NORTH AMERICA CORP LEBANON Ohio 45036 0.608 Screened Out

RYCOLINE PRODUCTS LLC CHICAGO Illinois 60630 0.6065 Screened Out

EXXONMOBIL CHEMICAL BATON ROUGE CHEMICAL 

PLANT

BATON ROUGE Louisiana 70805 0.6 Screened Out

GLASS COATINGS & CONCEPTS MONROE Ohio 45050 0.5925 Screened Out

AKZO NOBEL SURFACE CHEMISTRY LLC HOUSTON Texas 77053 0.59 Screened Out

ENGINEERED POLYMER SOLUTIONS I NC D/B/A 

VALSPAR COATINGS

BIRMINGHAM Alabama 35215 0.5885 Screened Out

ALERIS ROLLED PRODUCTS INC ASHVILLE Ohio 43103 0.5885 Screened Out

ASHLAND DISTRIBUTION WILLOW SPRINGS Illinois 60480 0.586 Screened Out

ROLL COATER INC HAWESVILLE Kentucky 42348 0.58 Screened Out

DIAMOND VOGEL PAINTS TULSA Oklahoma 74115 0.5795 Screened Out

PRIOR COATED METALS ALLENTOWN Pennsylvania 18103 0.568 Screened Out

DUCKBACK PRODUCTS CHICO California 95928 0.5605 Screened Out

KLINGER PAINT CO INC CEDAR RAPIDS IOWA 52404 0.55984 Screened Out

HYDRITE CHEMICAL CO COTTAGE GROVE Wisconsin 53527 0.55 Screened Out

FLINT HILLS RESOURCES LP ROSEMOUNT Minnesota 55068 0.55 Screened Out

REICHHOLD INC VALLEY PARK Missouri 63088 0.549875 Screened Out

DUPONT FORT MADISON PLANT FORT MADISON Iowa 52627 0.544 Screened Out

CENTRIA AMBRIDGE Pennsylvania 15003 0.5315 Screened Out

PARISER INDUSTRIES INC PATERSON New Jersey 07503 0.5275 Screened Out

DUPONT MOUNT CLEMENS PLANT MOUNT CLEMENS Michigan 48043 0.5265 Screened Out

COMPLEX CHEMICALS CO INC TALLULAH Louisiana 71282 0.525 Screened Out

MAXIM INTEGRATED PRODUCTS INC SAN ANTONIO Texas 78251 0.517 Screened Out

LOCKHEED MARTIN AERONAUTICS CO PALMDALE California 93599 0.514 Screened Out

ALERIS ROLLED PRODUCTS INC ROXBORO North Carolina 27573 0.513 Screened Out

Page 8 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

PLAZE INC SAINT CLAIR Missouri 63077 0.509 Screened Out

TERNIUM USA INC SHREVEPORT Louisiana 71115 0.5085 Screened Out

SC JOHNSON & SON INC WAXDALE FACILITY STURTEVANT Wisconsin 53177 0.5 Screened Out

SILBOND CORP WESTON Michigan 49289 0.5 Screened Out

FERRO GLASS & COLOR CORP WASHINGTON Pennsylvania 15301 0.5 Screened Out

EVONIK DEGUSSA CORP TIPPECANOE 

LABORATORIES

LAFAYETTE Indiana 47909 0.5 Screened Out

ARCADIA INC VERNON California 90023 0.5 Screened Out

TRAD NA INC HOPKINSVILLE Kentucky 42240 0.48455 Screened Out

FULLER BRUSH CO GREAT BEND Kansas 67530 0.4825 Screened Out

DPIX LLC COLORADO SPRINGS COLORADO 80916 0.475 Screened Out

NAZDAR CHICAGO CHICAGO Illinois 60622 0.4735 Screened Out

SNAP-ON TOOLS MANUFACTURING CO ALGONA Iowa 50511 0.4705 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

MOLINE Illinois 61265 0.47 Screened Out

CLEVELAND STEEL CONTAINER CORP - 

STREETSBORO PLANT

STREETSBORO Ohio 44241 0.468 Screened Out

ROCK TENN CO CLINTON Iowa 52732 0.466 Screened Out

DOW CHEMICAL CO FREEPORT FACILITY FREEPORT Texas 77541 0.4635 Screened Out

HEXION SPECIALTY CHEMICALS INC BEDFORD PARK Illinois 60501 0.458 Screened Out

FORREST PAINT CO EUGENE Oregon 97402 0.437 Screened Out

SEYMOUR OF SYCAMORE INC SYCAMORE ILLINOIS 60178 0.434 Screened Out

PFI INC SANTA FE SPRINGS California 90670 0.43 Screened Out

RODDA PAINT CO PORTLAND Oregon 97203 0.4295 Screened Out

NELCO PRODUCTS INC ANAHEIM California 92801 0.428 Screened Out

ELEMENTIS SPECIALTIES JERSEY CITY New Jersey 07304 0.428 Screened Out

NASCOTE INDUSTRIES NASHVILLE Illinois 62263 0.42766 Screened Out

ASHLAND DISTRIBUTION BIRMINGHAM Alabama 35234 0.4215 Screened Out

NB COATINGS INC LANSING Illinois 60438 0.40825 Screened Out

VISTA PAINT CORP FULLERTON California 92831 0.4065 Screened Out

GEMINI COATINGS INC EL RENO OKLAHOMA 73036 0.403 Screened Out

ROLLEX CORP ELK GROVE VILLAGE Illinois 60007 0.3955 Screened Out

SIKA CORP SIKA SARNAFIL DIV CANTON Massachusetts 02021 0.3895 Screened Out

MERCK SHARP & DOHME CORP ELKTON Virginia 22827 0.38 Screened Out

ABC COMPOUNDING CO INC MORROW Georgia 30260 0.3775 Screened Out

IMS ENGINEERED PRODUCTS LLC DES PLAINES ILLINOIS 60016 0.3775 Screened Out

ZSCHIMMER & SCHWARZ MILLEDGEVILLE GEORGIA 31061 0.3775 Screened Out

INTERNATIONAL PAINT LLC HOUSTON Texas 77091 0.3775 Screened Out

TOWER PRODUCTS INC EASTON Pennsylvania 18045 0.375 Screened Out

QUEST CHEMICAL CORP HOUSTON Texas 77041 0.375 Screened Out

PATRIOT PAINT LLC PORTLAND INDIANA 47371 0.375 Screened Out

FUCHS LUBRICANTS CO-CORPORATE OFFICE HARVEY Illinois 60426 0.3715 Screened Out

FLINT GROUP NORTH AMERICA CORP ANNISTON Alabama 36207 0.37 Screened Out

METAL COATERS OF CALIFORNIA INC RANCHO CUCAMONGA California 91730 0.368665 Screened Out

MIDWEST METAL COATINGS GRANITE CITY ILLINOIS 62040 0.367 Screened Out

IVC INDUSTRIAL COATINGS INC BRAZIL INDIANA 47834 0.36605 Screened Out

CELLO PROFESSIONAL PRODUCTS HAVRE DE GRACE Maryland 21078 0.354 Screened Out

ICL-IP AMERICA INC GALLIPOLIS FERRY West Virginia 25515 0.3506 Screened Out

FORD MOTOR CO CHICAGO ASSEMBLY CHICAGO Illinois 60633 0.35 Screened Out

INEOS OXIDE A DIV OF INEOS AMERICAS LLC PLAQUEMINE Louisiana 70765 0.347535 Screened Out

QUEST SPECIALTY COATINGS LLC MENOMONEE 

FALLS

MENOMONEE FALLS WISCONSIN 53051 0.3475 Screened Out

DIVERSIFIED COATING SYSTEMS INC GREENVILLE SOUTH SOUTH CAROLINA 29605 0.3375 Screened Out

SIERRA CORP MINNETONKA Minnesota 55343 0.336 Screened Out

SHERWIN-WILLIAMS AUTOMOTIVE FINISHES CORP RICHMOND Kentucky 40475 0.336 Screened Out

ZEP INC ATLANTA Georgia 30318 0.3355 Screened Out

BECKER SPECIALTY CORP ELK GROVE VILLAGE Illinois 60007 0.335 Screened Out

AMERIMAX HOME PRODUCTS INC LANCASTER Pennsylvania 17603 0.3325 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

FREMONT Michigan 49412 0.331 Screened Out

ENGLERT INC PERTH AMBOY NEW JERSEY 08861 0.3185 Screened Out

AMERIMAX COATED PRODUCTS HELENA ARKANSAS 72342 0.30835 Screened Out

CURTIS METAL FINISHING CO MACHESNEY PARK Illinois 61115 0.3075 Screened Out

LINETEC WAUSAU Wisconsin 54401 0.302 Screened Out

FORD MOTOR CO MICHIGAN ASSEMBLY PLANT WAYNE Michigan 48184 0.3015 Screened Out

ET PRODUCTS CO INC BREMEN Indiana 46506 0.3 Screened Out

AMERICAN METALS CORP WESTLAKE Ohio 44145 0.296 Screened Out

MAXIM INTEGRATED PRODUCTS INC SAN JOSE California 95134 0.295 Screened Out

MUTI-PACK LLC MILWAUKEE Wisconsin 53223 0.29 Screened Out

VIDEOJET TECHNOLOGIES INC ELK GROVE VILLAGE Illinois 60007 0.287 Screened Out

TRITECH COATINGS CORP PAGEDALE Missouri 63133 0.2865 Screened Out

ENTHONE INC WEST HAVEN Connecticut 06516 0.28527 Screened Out

Page 9 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

OMG AMERICAS FRANKLIN Pennsylvania 16323 0.284 Screened Out

BRADLEY COATINGS GROUP CONNELLSVILLE Pennsylvania 15425 0.28171 Screened Out

SPRAYLAT CORP MOUNT VERNON New York 10550 0.274 Screened Out

INTEL CORP RIO RANCHO New Mexico 87124 0.273 Screened Out

QUANTUM MARKETING INC LAKELAND Florida 33803 0.268 Screened Out

PPG ARCHITECTURAL FINISHES INC LOUISVILLE Kentucky 40203 0.2655 Screened Out

BRIGHTSMITH LLC MORRISVILLE Pennsylvania 19067 0.265 Screened Out

SERIGRAPH INC WEST BEND Wisconsin 53095 0.2645 Screened Out

IVC INDUSTRIAL COATINGS INC CASA GRANDE Arizona 85222 0.2600625 Screened Out

MASCO RETAIL CABINET GROUP SAYRE 

PENNSYLVANIA PLANT

SAYRE PENNSYLVANIA 18840 0.26 Screened Out

ASHLAND DISTRIBUTION CO SAINT PAUL Minnesota 55102 0.2595 Screened Out

ASHLAND DISTRIBUTION CO CARTERET New Jersey 07008 0.2595 Screened Out

HENTZEN COATINGS,INC BATAVIA FACILITY BATAVIA Illinois 60510 0.259455 Screened Out

ROHM & HAAS CHEMICALS LLC BRISTOL Pennsylvania 19007 0.255 Screened Out

ASHLAND DISTRIBUTION CO TWINSBURG Ohio 44087 0.2505 Screened Out

BASF CORP GREENVILLE Ohio 45331 0.25 Screened Out

SANFORD LP LIQUID MANUFACTURING & 

TECHNOLOGY CENTER

MANCHESTER TENNESSEE 37355 0.25 Screened Out

BRYCE CO LLC SEARCY ARKANSAS 72143 0.25 Screened Out

HENKEL CORP WARREN Michigan 48091 0.25 Screened Out

BACHMAN SERVICES INC OKLAHOMA CITY Oklahoma 73129 0.25 Screened Out

YENKIN-MAJESTIC PAINT CORPORAT ION COLUMBUS Ohio 43219 0.25 Screened Out

RESEARCH SOLVENTS & CHEMICALS INC PELHAM Alabama 35124 0.25 Screened Out

MISCO PRODUCTS CORP READING Pennsylvania 19605 0.25 Screened Out

METAL COATERS OF GEORGIA MARIETTA Georgia 30062 0.25 Screened Out

MALCO PRODUCTS INC BARBERTON Ohio 44203 0.25 Screened Out

MAGNI INDUSTRIES INC INDEPENDENCE KENTUCKY 41051 0.25 Screened Out

KEYSTONE ANILINE CORP INMAN South Carolina 29349 0.25 Screened Out

EQUILON CARSON TERMINAL CARSON California 90810 0.25 Screened Out

CHEMICAL SPECIALISTS & DEVELOPMENT INC CONROE Texas 77303 0.25 Screened Out

BECKER SPECIALTY CORP FONTANA California 92335 0.25 Screened Out

DUPONT FAYETTEVILLE PLANT FAYETTEVILLE NORTH CAROLINA 28306 0.247 Screened Out

HEXION SPECIALTY CHEMICALS INC CARPENTERSVILLE Illinois 60110 0.246 Screened Out

STANDARD PAINTS INC MANSFIELD Texas 76063 0.239 Screened Out

WORLDCOLOR ATGLEN ATGLEN Pennsylvania 19310 0.238 Screened Out

CAR PRODUCTS INC HOLYOKE Massachusetts 01040 0.238 Screened Out

KIK-SOCAL INC SANTA FE SPRINGS California 90670 0.2365 Screened Out

DYCO PAINTS INC CLEARWATER Florida 33760 0.236 Screened Out

BERGQUIST CO CANNON FALLS Minnesota 55009 0.236 Screened Out

PENN COLOR INC HATFIELD Pennsylvania 19440 0.234 Screened Out

SUN CHEMICAL CORP PHILADELPHIA Pennsylvania 19132 0.234 Screened Out

SUMTER COATINGS INC SUMTER South Carolina 29150 0.2335 Screened Out

CHEMTURA CORP - TAFT PLANT KILLONA Louisiana 70066 0.232 Screened Out

APOLLO CHEMICAL BURLINGTON North Carolina 27215 0.230497 Screened Out

CHRYSLER GROUP LLC STERLING STAMPING PLANT 

(PART)

STERLING HEIGHTS Michigan 48312 0.228 Screened Out

PPG INDUSTRIES OHIO INC CIRCLEVILLE OH CIRCLEVILLE Ohio 43113 0.226 Screened Out

LONGABERGER CO FRAZEYSBURG Ohio 43822 0.22475 Screened Out

CERTIFIED ENAMELING INC LOS ANGELES California 90023 0.2225 Screened Out

PERMA-PIPE OIL & GAS NEW IBERIA Louisiana 70560 0.22 Screened Out

RHODIA INC WINDER Georgia 30680 0.216 Screened Out

COLWELL INC KENDALLVILLE Indiana 46755 0.215 Screened Out

SYNGENTA CROP PROTECTION INC SAINT GABRIEL 

FACILITY

SAINT GABRIEL Louisiana 70776 0.2125 Screened Out

ASHLAND DISTRIBUTION CO DORAVILLE Georgia 30340 0.2115 Screened Out

FLINT GROUP NORTH AMERICA ATLANTA Georgia 30339 0.21 Screened Out

WARREN OIL CO - NC DUNN North Carolina 28335 0.208 Screened Out

UNION CARBIDE CORP SOUTH CHARLESTON FACILITY SOUTH CHARLESTON West Virginia 25303 0.2045 Screened Out

FIRST AMERICAN RESOURCES CO MABLETON Georgia 30126 0.203 Screened Out

RHODIA INC MARCUS HOOK Pennsylvania 19061 0.2015 Screened Out

BOEING COMMERCIAL AIRPLANE GROUP - RENTON RENTON Washington 98055 0.1975 Screened Out

RUDD CO INC SEATTLE Washington 98107 0.1975 Screened Out

UNIVERSAL CHEMICALS & COATINGS INC ELGIN ILLINOIS 60123 0.196 Screened Out

ARROW GROUP INDUSTRIES INC HASKELL New Jersey 07420 0.195 Screened Out

INTEL CORP - RONLER ACRES CAMPUS HILLSBORO Oregon 97124 0.1925 Screened Out

ASHLAND DISTRIBUTION CO GARLAND TX GARLAND Texas 75041 0.187 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

WHEELING Illinois 60090 0.18 Screened Out

HADCO (SANMINA) CORP - OWEGO DIV OWEGO New York 13827 0.177 Screened Out

QUAD GRAPHICS NASHVILLE NASHVILLE TENNESSEE 37207 0.177 Screened Out

Page 10 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

SILGAN WHITE CAP CORP RICHMOND Indiana 47375 0.175 Screened Out

BYK USA INC WALLINGFORD Connecticut 06492 0.174 Screened Out

ASHLAND DISTRIBUTION CO BATON ROUGE Louisiana 70815 0.1735 Screened Out

CHAMPION TECHNOLOGIES INC ODESSA Texas 79762 0.1695 Screened Out

ASHLAND DISTRIBUTION SAINT LOUIS Missouri 63111 0.1685 Screened Out

KAY CHEMICAL CO GREENSBORO North Carolina 27409 0.165 Screened Out

AMREP INC MARIETTA Georgia 30062 0.1625 Screened Out

EXXONMOBIL REFINING & SUPPLY BATON ROUGE 

REFINERY

BATON ROUGE Louisiana 70805 0.1615 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

HIGH POINT North Carolina 27261 0.16 Screened Out

ANCHOR PAINT MANUFACTURING CO INC TULSA Oklahoma 74112 0.16 Screened Out

ENERGIZER BATTERY MANUFACTURING INC SAINT ALBANS Vermont 05478 0.1595 Screened Out

BOEING COMMERCIAL AIRPLANE GROUP NORTH 

BOEING FIELD (PART)

SEATTLE Washington 98108 0.1595 Screened Out

INTEL CORP CHANDLER Arizona 85248 0.1565 Screened Out

PLAZE INC SAINT CLAIR Missouri 63077 0.152 Screened Out

MID-STATES PAINT & CHEMICAL CO CRESTWOOD Missouri 63126 0.151 Screened Out

SONOCO FLEXIBLE PACKAGING EDINBURGH Indiana 46124 0.14951 Screened Out

CENTRAL MOTOR WHEEL OF AMERICA (DBA CMWA) PARIS Kentucky 40361 0.1475 Screened Out

CHASE PRODUCTS CO BROADVIEW Illinois 60155 0.1455 Screened Out

VEYANCE TECHNOLOGIES INC NORFOLK Nebraska 68701 0.145215 Screened Out

DAVIS-FROST INC LYNCHBURG VIRGINIA 24506 0.1415 Screened Out

HUNTSMAN PETROCHEMICAL LLC PORT NECHES 

PERFORMANCE PRODUCTS

PORT NECHES Texas 77651 0.141 Screened Out

BAKER PETROLITE CORP SAND SPRINGS Oklahoma 74063 0.1368 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

LEBANON Pennsylvania 17046 0.136 Screened Out

PROFESSIONAL DISPOSABLES INTERNATIONAL INC ORANGEBURG New York 10962 0.135135 Screened Out

HERCULES INC KENEDY TEXAS KENEDY Texas 78119 0.13416 Screened Out

ISP SYNTHETIC ELASTOMERS LP PORT NECHES TEXAS 77651 0.132 Screened Out

ASHLAND DISTRIBUTION MEMPHIS Tennessee 38113 0.13 Screened Out

TEXAS INSTRUMENTS INC STAFFORD Texas 77477 0.1275 Screened Out

SOUTHERN CLAY PRODUCTS INC LOUISVILLE Kentucky 40210 0.1275 Screened Out

CLARIANT CORP MARTIN PLANT MARTIN South Carolina 29836 0.1275 Screened Out

INCHEM CORP ROCK HILL South Carolina 29730 0.1275 Screened Out

MOC PRODUCTS CO INC PACOIMA California 91331 0.1275 Screened Out

BF GOODRICH TIRE MANUFACTURING WOODBURN Indiana 46797 0.1275 Screened Out

WESTERN TUBE & CONDUIT CORP LONG BEACH CALIFORNIA 90810 0.1275 Screened Out

UNITED LABORATORIES INC SAINT CHARLES Illinois 60174 0.1275 Screened Out

RR STREET & CO INC CHICAGO Illinois 60608 0.1275 Screened Out

RESEARCH SOLVENTS & CHEMICALS INC LA VERGNE Tennessee 37086 0.1275 Screened Out

POWER SERVICE PRODUCTS INC WEATHERFORD Texas 76086 0.1275 Screened Out

PERMATEX SOLON SOLON Ohio 44139 0.1275 Screened Out

ONESOURCE COIL COATERS CLEARWATER FLORIDA 33760 0.1275 Screened Out

OAKLEY INC FOOTHILL RANCH California 92610 0.1275 Screened Out

NICCA USA INC FOUNTAIN INN South Carolina 29644 0.1275 Screened Out

GE WATER & PROCESS TECHNOLOGIES ORANGE 

FACILITY

ORANGE Texas 77630 0.1275 Screened Out

ELECTRO PLATE CIRCUITRY INC CARROLLTON TEXAS 75006 0.1275 Screened Out

ELANTAS PDG INC SAINT LOUIS Missouri 63147 0.1275 Screened Out

DELTA HOUSTON DEER PARK Texas 77536 0.1275 Screened Out

COASTAL CHEMICAL CO LLC ABBEVILLE Louisiana 70510 0.1275 Screened Out

CHEMICALS INC BAYTOWN Texas 77520 0.1275 Screened Out

BRENNTAG GREAT LAKES LLC MENOMONEE FALLS Wisconsin 53051 0.1275 Screened Out

BASF CORP SPARTANBURG South Carolina 29302 0.1275 Screened Out

ASHLAND DISTRIBUTION CO CHARLOTTE North Carolina 28208 0.1255 Screened Out

CHEMCOAT INC MONTOURSVILLE Pennsylvania 17754 0.125 Screened Out

FORMULA CORP AUBURN WASHINGTON 98002 0.125 Screened Out

PREMIER INK SYSTEMS INC HARRISON Ohio 45030 0.125 Screened Out

BRYCE CO LLC MEMPHIS Tennessee 38118 0.125 Screened Out

AMERICAN COLORS INC DISPERSION PLANT 

SANDUSKY OHIO

SANDUSKY OHIO 44870 0.125 Screened Out

WM BARR & CO INC MEMPHIS TENNESSEE 38113 0.125 Screened Out

TYSON FRESH MEATS INC HOLCOMB Kansas 67851 0.125 Screened Out

TRANS CHEMICAL INC SAINT LOUIS Missouri 63147 0.125 Screened Out

TNEMEC CO INC NORTH KANSAS CITY Missouri 64116 0.125 Screened Out

SICPA SECURINK CORP SPRINGFIELD Virginia 22153 0.125 Screened Out

PPG INDUSTRIES INC MCCARRAN Nevada 89434 0.125 Screened Out

NORTHERN COATINGS & CHEMICAL CO INC MENOMINEE Michigan 49858 0.125 Screened Out

MAINTEX INC CITY OF INDUSTRY California 91746 0.125 Screened Out

MAGNABLEND INC LIQUID PLANT WAXAHACHIE Texas 75165 0.125 Screened Out

Page 11 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

KALCOR COATINGS CO WILLOUGHBY Ohio 44094 0.125 Screened Out

INVISTA SARL - ORANGE SITE ORANGE TEXAS 77630 0.125 Screened Out

HERCULES INC HOPEWELL Virginia 23860 0.125 Screened Out

GOLD KEY PROCESSING INC MIDDLEFIELD OHIO 44062 0.125 Screened Out

GOLD EAGLE CO CHICAGO Illinois 60632 0.125 Screened Out

EXXONMOBIL OIL CORP - TORRANCE REFINERY TORRANCE CALIFORNIA 90509 0.125 Screened Out

DANLIN INDUSTRIES CORP THOMAS Oklahoma 73669 0.125 Screened Out

COLUMBIA PAINT CORP HUNTINGTON West Virginia 25704 0.125 Screened Out

CLEANING SYSTEMS INC DE PERE Wisconsin 54115 0.125 Screened Out

CHEMETALL US INC ROMULUS Michigan 48174 0.125 Screened Out

CERAM-TRAZ CORP CERAMIC INDL COATINGS (DBA) OSSEO Minnesota 55369 0.125 Screened Out

BERRYMAN PRODUCTS INC ARLINGTON Texas 76011 0.125 Screened Out

AMERICAN JETWAY CORP WAYNE MICHIGAN 48184 0.125 Screened Out

AKZO NOBEL COATINGS INC HIGH POINT North Carolina 27261 0.125 Screened Out

AKCROS CHEMICALS INC NEW BRUNSWICK New Jersey 08901 0.125 Screened Out

ACTON TECHNOLOGIES INC PITTSTON Pennsylvania 18640 0.125 Screened Out

WATSON LABORATORIES INC UTAH SALT LAKE CITY Utah 84108 0.124456 Screened Out

TECHNICAL CHEMICAL CO CLEBURNE Texas 76033 0.123 Screened Out

CYTEC INDUSTRIES INC LANGLEY PLANT LANGLEY South Carolina 29834 0.123 Screened Out

AEP INDUSTRIES INC GRIFFIN Georgia 30224 0.12275 Screened Out

ASHLAND INC - EVENDALE EVENDALE Ohio 45241 0.1215 Screened Out

FRAZEE INDUSTRIES SAN DIEGO California 92121 0.12 Screened Out

ARDEX LABORATORIES INC PHILADELPHIA Pennsylvania 19116 0.119 Screened Out

STOUSE INC NEW CENTURY Kansas 66031 0.118 Screened Out

U.S. NAVY NAVAL AIR STATION JACKSONVILLE JACKSONVILLE FLORIDA 32212 0.115 Screened Out

PILOT CHEMICAL CO HOUSTON Texas 77086 0.1105 Screened Out

ELECTRONICS FOR IMAGING INC YPSILANTI Michigan 48197 0.11 Screened Out

TEXAS INSTRUMENTS INC DALLAS Texas 75243 0.1095 Screened Out

DELTA LABORATORIES INC OCALA Florida 34475 0.1085 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

BOWLING GREEN Kentucky 42101 0.108 Screened Out

SHERWIN-WILLIAMS CO HOLLAND Michigan 49423 0.106 Screened Out

CAROLINA SOLVENTS INC HICKORY North Carolina 28602 0.104 Screened Out

CCI MANUFACTURING IL CORP LEMONT Illinois 60439 0.1035 Screened Out

ACCURATE DISPERSIONS SOUTH HOLLAND Illinois 60473 0.1035 Screened Out

ASHLAND DISTRIBUTION CO MIAMI Florida 33162 0.102 Screened Out

TWINCO ROMAX MILWAUKEE WISCONSIN 53209 0.10066 Screened Out

BUZZI UNICEM USA - GREENCASTLE PLANT GREENCASTLE Indiana 46135 0.1 Screened Out

BRENNTAG PACIFIC INC SANTA FE SPRINGS California 90670 0.1 Screened Out

ASHLAND DISTRIBUTION CO CARSON California 90810 0.1 Screened Out

ARCH CHEMICALS INC BRANDENBURG Kentucky 40108 0.1 Screened Out

AKZONOBEL COATINGS INC PONTIAC Michigan 48341 0.099 Screened Out

CE BRADLEY LABORATORIES INC BRATTLEBORO Vermont 05301 0.0985 Screened Out

HARCROS CHEMICALS INC KANSAS CITY Kansas 66106 0.097 Screened Out

OLDCASTLE BUILDING ENVELOPE TENNESSEE 

FACILITY

MIDWAY Tennessee 37809 0.0945 Screened Out

ALLEGHENY PETROLEUM PRODUCTS CO WILMERDING Pennsylvania 15148 0.0945 Screened Out

CPJ TECHNOLOGIES TAYLORS South Carolina 29687 0.092 Screened Out

TNEMEC CO INC BALTIMORE Maryland 21222 0.09 Screened Out

STEELSCAPE INC RANCHO RANCHO CUCAMONGA California 91730 0.089945 Screened Out

ATHEA LABORATORIES INC MILWAUKEE Wisconsin 53224 0.0888 Screened Out

ASHLAND DISTRIBUTION CO FAIRFIELD California 94533 0.0855 Screened Out

ASHLAND DISTRIBUTION CO KANSAS CITY Kansas 66106 0.084 Screened Out

SHERWIN-WILLIAMS CO TERRE HAUTE Indiana 47808 0.0835 Screened Out

AKZO NOBEL COATINGS INC CLINTON Mississippi 39056 0.082 Screened Out

WEBB CHEMICAL SERVICE CORP MUSKEGON HEIGHTS MICHIGAN 49444 0.08 Screened Out

ASHLAND DISTRIBUTION TEWKSBURY Massachusetts 01876 0.0795 Screened Out

BEHR PROCESS CORP - CHICAGO CHICAGO HEIGHTS Illinois 60411 0.0787 Screened Out

MATTHEWS INTERNATIONAL CORP PITTSBURGH Pennsylvania 15238 0.0775 Screened Out

ICI PAINTS PUERTO RICO INC CAROLINA Puerto Rico 00985 0.077225 Screened Out

CORSICANA TECHNOLOGIES INC CORSICANA Texas 75109 0.07708 Screened Out

IMPERIAL PAINT CO INC PORTLAND OREGON 97210 0.076 Screened Out

SUPERIOR OIL CO INC RECLAIMED ENERGY DIV CONNERSVILLE Indiana 47331 0.075 Screened Out

AKZO NOBEL COATINGS INC SALEM Oregon 97302 0.07415 Screened Out

CHEMICAL SOLVENTS JENNINGS ROAD FACILITY CLEVELAND Ohio 44109 0.07396 Screened Out

WHITFORD CORP ELVERSON Pennsylvania 19520 0.0729 Screened Out

DU PONT ELECTRONICS MICROCIRCU ITS 

INDUSTRIES LTD

MANATI PUERTO RICO 00674 0.0725 Screened Out

CHAMPION TECHNOLOGIES INC BROUSSARD Louisiana 70518 0.072 Screened Out

PPG INDUSTRIES OHIO INC - DELAWARE DELAWARE Ohio 43015 0.06956 Screened Out

MRCG-KRAFTMAID P3 ORWELL Ohio 44076 0.069 Screened Out

Page 12 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

WARSAW CHEMICAL CO INC WARSAW Indiana 46580 0.069 Screened Out

SPARTAN CHEMICAL CO INC MAUMEE Ohio 43537 0.0675 Screened Out

LUBRIZOL MC COOK Illinois 60525 0.067 Screened Out

CARDINAL INDUSTRIAL FINISHES SOUTH EL MONTE California 91733 0.067 Screened Out

ADCO CLEANING PRODUCTS LLC SEDALIA Missouri 65301 0.0665 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

MONTEBELLO California 90640 0.0655 Screened Out

WARREN STAMPING PLANT (PART) WARREN Michigan 48091 0.06 Screened Out

VEOLIA ES TECHNICAL SOLUTIONS LLC MIDDLESEX New Jersey 08846 0.0595 Screened Out

KARCHER NORTH AMERICA- PROCHEM CHANDLER Arizona 85224 0.0595 Screened Out

ABC COMPOUNDING CO OF TEXAS INC GRAND PRAIRIE Texas 75050 0.059 Screened Out

AMPHENOL APC INC NASHUA New Hampshire 03062 0.0574235 Screened Out

MINUTEMAN INTERNATIONAL MULTI-CLEAN DIV SHOREVIEW Minnesota 55126 0.057 Screened Out

ECOLAB INC JOLIET Illinois 60436 0.057 Screened Out

CHAMPION TECHNOLOGIES INC CORPUS CHRISTI Texas 78405 0.05615 Screened Out

CLARIANT CORP - MOUNT HOLLY WEST PLANT MOUNT HOLLY North Carolina 28120 0.0555 Screened Out

MRCG-KRAFTMAID P1 MIDDLEFIELD Ohio 44062 0.0555 Screened Out

CHEVRON PRODUCTS CO PASCAGOULA REFINERY PASCAGOULA MISSISSIPPI 39581 0.055 Screened Out

UNIVAR USA INC COMMERCE California 90040 0.0545 Screened Out

CLEVELAND STEEL CONTAINER - KILGORE KILGORE TEXAS 75662 0.0545 Screened Out

HARLEY-DAVIDSON MOTOR CO OPERATIONS INC YORK Pennsylvania 17402 0.05435 Screened Out

3M CO - NEVADA NEVADA Missouri 64772 0.054 Screened Out

UNIVAR USA INC - TOLEDO BRANCH WALBRIDGE Ohio 43465 0.0535 Screened Out

ROCKLINE INDUSTRIES SHEBOYGAN Wisconsin 53081 0.0535 Screened Out

FRANKLIN INTERNATIONAL COLUMBUS Ohio 43207 0.0535 Screened Out

CLOROX PRODUCTS MANUFACTURING CO FAIRFIELD California 94533 0.0535 Screened Out

ECOLAB INC MARTINSBURG West Virginia 25405 0.053 Screened Out

ECOLAB INC MC DONOUGH Georgia 30253 0.0525 Screened Out

ATMI MATERIALS LTD BURNET Texas 78611 0.05151 Screened Out

HANNA STEEL CORP PEKIN Illinois 61554 0.05061 Screened Out

DYSTAR LP REIDSVILLE North Carolina 27320 0.05 Screened Out

CONOCOPHILLIPS OKLAHOMA CITY PRODUCTS 

TERMINAL

OKLAHOMA CITY Oklahoma 73117 0.05 Screened Out

BENJAMIN MOORE & CO PELL CITY PELL CITY Alabama 35125 0.05 Screened Out

CHAMPION TECHNOLOGIES INC FRESNO Texas 77545 0.0496 Screened Out

RINECO BENTON Arkansas 72015 0.0495 Screened Out

VALERO REFINING CO - TENNESSEE LLC MEMPHIS TENNESSEE 38109 0.0495 Screened Out

UNIVAR USA INC HAMILTON BRANCH HAMILTON Ohio 45015 0.049 Screened Out

BARTON SOLVENTS INC BETTENDORF BETTENDORF Iowa 52722 0.049 Screened Out

AIR PRODUCTS & CHEMICALS INC CALVERT CITY Kentucky 42029 0.049 Screened Out

EXCEL-POLYMERS LLC JONESBOROUGH Tennessee 37659 0.0485 Screened Out

GRAPHIC CONTROLS LLC BUFFALO New York 14204 0.048 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

INDIANAPOLIS Indiana 46225 0.0465 Screened Out

RECKITT BENCKISER HILLSBOROUGH New Jersey 08844 0.0455 Screened Out

LUBRIZOL CORP WICKLIFFE Ohio 44092 0.0455 Screened Out

WATSON STANDARD CO (NEVILLE ISLAND PLANT) NEVILLE ISLAND Pennsylvania 15225 0.044 Screened Out

BRENNTAG SOUTHEAST INC DURHAM North Carolina 27703 0.044 Screened Out

UNIVAR USA INC DALLAS DAN MORTON FACILITY DALLAS Texas 75236 0.0435 Screened Out

BRENNTAG SOUTHWEST INC LANC ASTER LANCASTER Texas 75134 0.0425 Screened Out

CUSTOM SYNTHESIS LLC ANDERSON South Carolina 29625 0.0425 Screened Out

ASHLAND DISTRIBUTION CO TAMPA Florida 33634 0.042 Screened Out

BARTON SOLVENTS INC KANSAS CITY KANSAS CITY Kansas 66111 0.0415 Screened Out

SHERWIN-WILLIAMS CO ANDOVER Kansas 67002 0.041 Screened Out

LAMBERTI USA INC WHARTON CHEMICAL COMPLEX HUNGERFORD Texas 77448 0.0405 Screened Out

HARCROS CHEMICALS INC PASADENA Texas 77507 0.0405 Screened Out

RECTICEL INTERIORS NORTH AMERICA LLC TUSCALOOSA Alabama 35401 0.04 Screened Out

BRENNTAG SOUTHWEST INC SAND SPRINGS SAND SPRINGS Oklahoma 74063 0.04 Screened Out

ENGINEERED POLYMER SOLUTIONS INC D/B/A 

VALSPAR COATINGS

PITTSBURGH Pennsylvania 15233 0.0395 Screened Out

AIR PRODUCTS PERFORMANCE MANUFACTURING INC MILTON Wisconsin 53563 0.0395 Screened Out

BIOLAB INC CONYERS Georgia 30012 0.03915 Screened Out

HUNTSMAN ADVANCED MATERIALS AMERICAS INC MC INTOSH Alabama 36553 0.0388 Screened Out

UNIVAR USA INC ROMULUS BRANCH ROMULUS Michigan 48174 0.038 Screened Out

KEMIRA WATER SOLUTIONS INC MOBILE Alabama 36614 0.0365 Screened Out

CONOCOPHILLIPS CO EAST ST LOUIS TERMINAL CAHOKIA Illinois 62206 0.0355 Screened Out

CONTINENTAL CEMENT CO LLC HANNIBAL Missouri 63401 0.035125 Screened Out

BRENNTAG NORTHEAST INC READING Pennsylvania 19605 0.03375 Screened Out

UNIVAR USA INC BERKELEY BERKELEY Missouri 63134 0.033 Screened Out

TRANSTAR AUTOBODY TECHNOLOGIES BRIGHTON Michigan 48114 0.032545 Screened Out

VALSPAR REFINISH PICAYUNE Mississippi 39466 0.0315 Screened Out

Page 13 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

DUPONT PARLIN PLANT PARLIN New Jersey 08859 0.031 Screened Out

ASHLAND DISTRIBUTION LANSING Michigan 48906 0.031 Screened Out

AMERICAN COATINGS INC TOMBALL Texas 77375 0.0305 Screened Out

SHERWIN-WILLIAMS CO GARLAND Texas 75041 0.03 Screened Out

COOK COMPOSITES & POLYMERS C O LEMONT Illinois 60439 0.03 Screened Out

GEORGIA-PACIFIC CHEMICALS LLC LUFKIN Texas 75901 0.0295 Screened Out

ECOLAB CITY OF INDUSTRY California 91748 0.0295 Screened Out

KWAL-HOWELLS INC (DBA KWAL PAINT INC) BONHAM Texas 75418 0.029 Screened Out

BARTON SOLVENTS INC DES MOINES DES MOINES Iowa 50313 0.029 Screened Out

SHERWIN-WILLIAMS CO GREENSBORO North Carolina 27409 0.0285 Screened Out

BARTON SOLVENTS INC WEST BEND WEST BEND Wisconsin 53095 0.028 Screened Out

ASHLAND DISTRIBUTION CO HOUSTON Texas 77034 0.0275 Screened Out

VEOLIA ES TECHNICAL SOLUTIONS LLC PORT ARTHUR 

FACILITY

PORT ARTHUR Texas 77640 0.026795 Screened Out

RICHARDSAPEX INC PHILADELPHIA Pennsylvania 19127 0.02673425 Screened Out

DIC IMAGING PRODUCTS USA LLC OAK CREEK Wisconsin 53154 0.026 Screened Out

NORTHERN LABS INC WEST DRIVE MANITOWOC Wisconsin 54220 0.025225 Screened Out

BRENNTAG SOUTHWEST INC HOUS TON HOUSTON Texas 77047 0.025 Screened Out

SI GROUP INC ROTTERDAM JUNCTION New York 12150 0.0245 Screened Out

SUN CHEMICAL CORP NORTHLAKE ILLINOIS 60164 0.0245 Screened Out

VALERO THREE RIVERS REFINERY THREE RIVERS Texas 78071 0.023 Screened Out

BARTON SOLVENTS INC WICHITA VALLEY CENTER Kansas 67147 0.023 Screened Out

BARTON SOLVENTS INC COUNCIL BLUFFS COUNCIL BLUFFS Iowa 51502 0.023 Screened Out

DAUBERT CHEMICAL CO CHICAGO Illinois 60638 0.02295 Screened Out

SUPERIOR SOLVENTS & CHEMICALS FAIRFIELD Ohio 45014 0.02254 Screened Out

KBP COIL COATERS INC DENVER Colorado 80216 0.0225 Screened Out

ARLON INC ADHESIVES & FILMS DIV SANTA ANA California 92704 0.0225 Screened Out

PACKAGING CORP OF AMERICA COUNCE MILL COUNCE Tennessee 38326 0.0215 Screened Out

GAGE PRODUCTS CO FERNDALE Michigan 48220 0.0215 Screened Out

SHERWIN-WILLIAMS CO GREENSBORO North Carolina 27403 0.021 Screened Out

BASF CORP BELVIDERE New Jersey 07823 0.02 Screened Out

PRIDE SOLVENTS & CHEMICAL CO OF NEW JERSEY AVENEL New Jersey 07001 0.02 Screened Out

EXCEL POLYMERS LLC BURTON OHIO 44021 0.02 Screened Out

AFTON CHEMICAL CORP SAUGET ILLINOIS 62201 0.02 Screened Out

3M CO - SPRINGFIELD SPRINGFIELD Missouri 65802 0.02 Screened Out

UNIVAR USA INC - TOLEDO SOUTH BRANCH TOLEDO Ohio 43615 0.019 Screened Out

STEEL DYNAMICS INC BUTLER Indiana 46721 0.0185 Screened Out

ECOLAB INC GARLAND Texas 75041 0.0185 Screened Out

ZEP COMMERCIAL EMERSON Georgia 30137 0.018 Screened Out

UNIVAR USA INC JACKSONVILLE FA CILITY JACKSONVILLE Florida 32254 0.018 Screened Out

BEHR PROCESS CORP ALLENTOWN ALLENTOWN Pennsylvania 18106 0.0179 Screened Out

TAKASAGO INTERNATIONAL CORP (USA) NORTHVALE New Jersey 07647 0.01762 Screened Out

TYSON FRESH MEATS INC JOSLIN IL HILLSDALE Illinois 61257 0.0175 Screened Out

UNIVAR USA INC STRONGSVILLE Ohio 44136 0.0175 Screened Out

SHERWIN-WILLIAMS CO MORROW Georgia 30260 0.0175 Screened Out

SHERWIN-WILLIAMS CO COLUMBUS Ohio 43207 0.0175 Screened Out

DAVIES IMPERIAL COATINGS INC HAMMOND Indiana 46320 0.0175 Screened Out

BJ CHEMICAL SERVICES HOBBS New Mexico 88240 0.01735 Screened Out

PROCTER & GAMBLE HAIR CARE LLC IOWA CITY Iowa 52240 0.0165 Screened Out

RUST-OLEUM CORP IN MD WILLIAMSPORT MARYLAND 21795 0.0165 Screened Out

HENKEL CORP DELAWARE Ohio 43015 0.0165 Screened Out

AVERY DENNISON PFD SCHERERVILLE Indiana 46375 0.016 Screened Out

HOLLY OAK CHEMICAL INC FOUNTAIN INN South Carolina 29644 0.0153 Screened Out

BLENTECH CORP HOUSTON Texas 77029 0.015 Screened Out

ASHLAND DISTRIBUTION CO TWINSBURG Ohio 44087 0.015 Screened Out

BENJAMIN MOORE & CO JOHNSTOWN JOHNSTOWN New York 12095 0.014811 Screened Out

UNIVAR USA INC - INDIANAPOLIS INDIANAPOLIS Indiana 46219 0.0145 Screened Out

SIMONIZ USA INC BOLTON Connecticut 06043 0.0145 Screened Out

PRIDE SOLVENT & CHEMICAL CO OF NY INC HOLTSVILLE New York 11742 0.0145 Screened Out

MEADWESTVACO SOUTH CAROLINA LLC DERIDDER Louisiana 70634 0.0145 Screened Out

ETHOX CHEMICALS LLC GREENVILLE South Carolina 29605 0.0145 Screened Out

INTERSTATE CHEMICAL CO INC HERMITAGE PENNSYLVANIA 16148 0.014 Screened Out

COGNIS CORP MAULDIN PLANT MAULDIN South Carolina 29662 0.014 Screened Out

KEY POLYMER LAWRENCE Massachusetts 01843 0.01365 Screened Out

PRC-DESOTO INTERNATIONAL INC MOJAVE California 93501 0.0135 Screened Out

EXCEL POLYMERS LLC DYERSBURG Tennessee 38024 0.0135 Screened Out

CARBOLINE CO LAKE CHARLES Louisiana 70601 0.0135 Screened Out

UNIVAR USA INC TAMPA FACILITY TAMPA Florida 33619 0.013 Screened Out

PLASTI-KOTE INC MEDINA OHIO 44258 0.0125 Screened Out

GOODWIN CO LAWRENCEVILLE Georgia 30043 0.0125 Screened Out

TRUE VALUE MANUFACTURING CARY Illinois 60013 0.01213 Screened Out

ACTEGA KELSTAR INC CINNAMINSON New Jersey 08077 0.0115 Screened Out

Page 14 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

UNIVAR USA INC - SAN JOSE SAN JOSE California 95131 0.0115 Screened Out

EVONIK DEGUSSA CORP THEODORE Alabama 36582 0.0115 Screened Out

JOHNSONDIVERSEY INC STURTEVANT Wisconsin 53177 0.010815 Screened Out

TYSON FRESH MEATS INC DAKOTA CITY NEBRASKA 68731 0.01 Screened Out

VARN INTERNATIONAL BATAVIA Illinois 60510 0.01 Screened Out

CLEAN HARBORS ENVIRONMENTAL SERVICES INC KIMBALL Nebraska 69145 0.01 Screened Out

BUCKLEY OIL CO DALLAS Texas 75207 0.01 Screened Out

BERRIDGE MANUFACTURING CO SAN ANTONIO Texas 78218 0.01 Screened Out

CLEAN HARBORS EL DORADO LLC EL DORADO Arkansas 71730 0.0098 Screened Out

CHEMOL CO INC GREENSBORO North Carolina 27406 0.009535 Screened Out

SHERWIN-WILLIAMS CO BALTIMORE Maryland 21230 0.0095 Screened Out

HYDRITE CHEMICAL CO UNIVERSITY PARK Illinois 60466 0.0095 Screened Out

HENKEL CORP CALHOUN Georgia 30701 0.0095 Screened Out

DSM DESOTECH INC STANLEY North Carolina 28164 0.0093 Screened Out

MULTI-COLOR CORP SCOTTSBURG Indiana 47170 0.008625 Screened Out

MARATHON PETROLEUM CO LLC TEXAS CITY Texas 77590 0.0085 Screened Out

BASF CORP EAST SETAUKET NEW YORK 11733 0.008 Screened Out

CLOROX PRODUCTS MANUFACTURING CO FOREST PARK Georgia 30297 0.00797 Screened Out

FLINT HILLS RESOURCES LP - WEST PLANT CORPUS CHRISTI Texas 78410 0.0075 Screened Out

US DOD USAF JOINT BASE ELMENDORF-RICHARDSON ELMENDORF AFB ALASKA 99506 0.0075 Screened Out

RUSTOLEUM CORP LESAGE West Virginia 25537 0.0075 Screened Out

MALLINCKRODT BAKER INC PHILLIPSBURG New Jersey 08865 0.0075 Screened Out

INTERSTATE CHEMICAL CO INC CHANNAHON Illinois 60410 0.0075 Screened Out

DYNALOY LLC INDIANAPOLIS Indiana 46226 0.0075 Screened Out

SUPERIOR OIL CO INC INDIANAPOLIS Indiana 46225 0.007465 Screened Out

BRULIN CORP INDIANAPOLIS Indiana 46205 0.0072575 Screened Out

MICHELIN NORTH AMERICA INC TUSCALOOSA Alabama 35401 0.007 Screened Out

U.S. POLYMERS ACCUREZ LLC SAINT LOUIS Missouri 63111 0.007 Screened Out

MARATHON PETROLEUM CO LLC - SPEEDWAY IN 

TERMINAL

INDIANAPOLIS Indiana 46222 0.007 Screened Out

HONEYWELL-PRESTONE PRODUCTS CORP FREEHOLD New Jersey 07728 0.007 Screened Out

FORD MOTOR CO DEARBORN DIVERSIFIED 

MANUFACTURING

DEARBORN Michigan 48121 0.007 Screened Out

LANCO MANUFACTURING CORP SAN LORENZO Puerto Rico 00754 0.00684 Screened Out

NEW DAWN MANUFACTURING CO UPPER MARLBORO Maryland 20774 0.006732805 Screened Out

UNIVAR USA INC NORCROSS FACILI TY NORCROSS Georgia 30071 0.0065 Screened Out

SHERWIN-WILLIAMS CO VICTORVILLE California 92392 0.0065 Screened Out

TRELLEBORG COATED SYSTEMS US INC / GRACE 

ADVANCED MATERIALS

RUTHERFORDTON North Carolina 28139 0.00625 Screened Out

PROCTER & GAMBLE MANUFACTURING CO KANSAS CITY Kansas 66105 0.006095 Screened Out

DUPONT PONTCHARTRAIN WORKS LA PLACE Louisiana 70068 0.006 Screened Out

RANBAR ELECTRICAL MATERIALS INC MANOR Pennsylvania 15665 0.006 Screened Out

BP PRODUCTS NORTH AMERICA WHITING WHITING Indiana 46394 0.006 Screened Out

CONOCOCPHILLIPS CO WICHITA TERMINAL WICHITA KANSAS 67219 0.0059 Screened Out

INX INTERNATIONAL INK CO HOMEWOOD Illinois 60430 0.00566 Screened Out

GATES CORP - CHARLESTON CHARLESTON Missouri 63834 0.0056 Screened Out

UNIVAR USA INC - BUNOLA BRANC H BUNOLA Pennsylvania 15020 0.0055 Screened Out

LUBRIZOL CORP PAINESVIL LE PLANT PAINESVILLE Ohio 44077 0.0055 Screened Out

HUBBARD-HALL INC WATERBURY Connecticut 06708 0.0055 Screened Out

GOODWIN CO GARDEN GROVE California 92841 0.0055 Screened Out

CALLAHAN CHEMICAL CO RIDGEFIELD PARK New Jersey 07660 0.0055 Screened Out

ENTHONE INC BRIDGEVIEW Illinois 60455 0.005295 Screened Out

HERITAGE-WTI INC EAST LIVERPOOL Ohio 43920 0.005065 Screened Out

ROHM & HAAS ELECTRONIC MATERIA LS LLC MARLBOROUGH Massachusetts 01752 0.005 Screened Out

PPG INDUSTRIES ARCHITECTURAL FINISHES DOVER Delaware 19904 0.005 Screened Out

BASF CORP WYANDOTTE Michigan 48192 0.005 Screened Out

UNIVAR USA INC LAKEVILLE LAKEVILLE Minnesota 55044 0.005 Screened Out

SHIELD PACKAGING CO INC DUDLEY Massachusetts 01571 0.005 Screened Out

SARTOMER CO INC WEST CHESTER Pennsylvania 19382 0.005 Screened Out

SARTOMER CO INC CHATHAM Virginia 24531 0.005 Screened Out

PVS NOLWOOD CHEMICALS INC DETROIT MICHIGAN 48228 0.005 Screened Out

INTERNATIONAL PAINT LLC BEREA OHIO 44017 0.005 Screened Out

INDEPENDENT INK INC GARDENA California 90248 0.005 Screened Out

GE WATER & PROCESS TECHNOLOGIES - 

BAKERSFIELD

BAKERSFIELD CALIFORNIA 93308 0.005 Screened Out

GE WATER & PROCESS TECHNOLOGIES NEW PHILADELPHIA OHIO 44663 0.005 Screened Out

GE WATER & PROCESS TECHNOLOGIES ADDISON ILLINOIS 60101 0.005 Screened Out

FORD MOTOR CO DEARBORN TOOL & DIE PLANT DEARBORN Michigan 48121 0.005 Screened Out

CR BRANDS INC SPARTANBURG South Carolina 29306 0.005 Screened Out

C P INC CONNERSVILLE Indiana 47331 0.005 Screened Out

BRAIN POWER INC MIAMI Florida 33155 0.005 Screened Out

Page 15 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

ACTEGA RADCURE INC WAYNE New Jersey 07470 0.005 Screened Out

BAKER PETROLITE BAYPORT FACILI TY PASADENA Texas 77507 0.004635 Screened Out

EASTMAN KODAK CO EASTMAN BUSINESS PARK ROCHESTER New York 14652 0.0045 Screened Out

SUPERIOR SOLVENTS & CHEMICALS LOUISVILLE Kentucky 40216 0.0045 Screened Out

MEADWESTVACO SC LLC CHARLESTON CHEMICAL 

PLANT

NORTH CHARLESTON South Carolina 29406 0.0045 Screened Out

LAFARGE MIDWEST INC (INCLD SYSTECH 

ENVIRONMENTAL)

FREDONIA KANSAS 66736 0.0045 Screened Out

COGNIS CORP -- CHARLOTT E PLANT CHARLOTTE North Carolina 28273 0.0045 Screened Out

EDCO PRODUCTS INC HOPKINS MINNESOTA 55343 0.0045 Screened Out

WAYNE DISPOSAL INC BELLEVILLE MICHIGAN 48111 0.004 Screened Out

FERRO CORP WALTON HILLS OPERATIONS WALTON HILLS OHIO 44146 0.004 Screened Out

OMNIUM HAMPTON Iowa 50441 0.004 Screened Out

CUSTOM CHEMICAL FORMULATORS SANTA FE SPRINGS California 90670 0.004 Screened Out

CHEMTEX LABORATORIES INC CONCORD North Carolina 28025 0.004 Screened Out

ASHLAND DISTRIBUTION TONAWANDA New York 14150 0.004 Screened Out

NORLITE CORP COHOES New York 12047 0.00378 Screened Out

BAKER PETROLITE BAKERSFIELD California 93308 0.00346 Screened Out

VEOLIA ES TECHNICAL SOLUTIONS LLC SAUGET ILLINOIS 62201 0.003 Screened Out

VOGEL PAINT & WAX CO INC ORANGE CITY Iowa 51041 0.003 Screened Out

UNIVAR USA INC- CINCINNATI OH BRANCH CINCINNATI Ohio 45246 0.003 Screened Out

UNIVAR USA INC DENVER DENVER Colorado 80216 0.003 Screened Out

UNIVAR USA INC PORTLAND Oregon 97210 0.003 Screened Out

SHERWIN-WILLIAMS CO MEMPHIS Tennessee 38109 0.003 Screened Out

3M COTTAGE GROVE CENTER COTTAGE GROVE Minnesota 55016 0.003 Screened Out

GENERAL DYNAMICS ORDNANCE & TACTICAL 

SYSTEMS GARLAND

GARLAND Texas 75040 0.00299 Screened Out

CONOCOPHILLIPS MT VERNON PRODUCTS TERMINAL MOUNT VERNON Missouri 65712 0.00296 Screened Out

MACDERMID INC FERNDALE Michigan 48220 0.00275 Screened Out

CONOCOPHILLIPS PONCA CITY REFINERY PONCA CITY Oklahoma 74601 0.00266 Screened Out

MAGNABLEND INC-CENTRAL PLANT WAXAHACHIE Texas 75165 0.0025 Screened Out

SHERWIN-WILLIAMS CO FERNLEY Nevada 89408 0.0025 Screened Out

JOHNSON BRYCE INC MEMPHIS TENNESSEE 38109 0.0025 Screened Out

NEWMAN TECHNOLOGY INC MANSFIELD OHIO 44903 0.0025 Screened Out

BASF CORP SEAFORD Delaware 19973 0.0025 Screened Out

VERSO PAPER HOLDINGS LLC JAY Maine 04239 0.0025 Screened Out

WYNNEWOOD REFINING CO WYNNEWOOD Oklahoma 73098 0.0025 Screened Out

UNION SPECIALTIES INC NEWBURYPORT Massachusetts 01950 0.0025 Screened Out

PPG ARCHITECURAL COATINGS HOUSTON HOUSTON Texas 77092 0.0025 Screened Out

NOV TUBOSCOPE HOLMES ROAD HOUSTON Texas 77051 0.0025 Screened Out

NIACET CORP NIAGARA FALLS New York 14304 0.0025 Screened Out

MILPORT ENTERPRISES INC MILWAUKEE Wisconsin 53207 0.0025 Screened Out

KEYSTONE CEMENT CO BATH Pennsylvania 18014 0.0025 Screened Out

FINGER LAKES CHEMICAL INC ROCHESTER New York 14605 0.0025 Screened Out

ECP INC WOODRIDGE WOODRIDGE Illinois 60517 0.0025 Screened Out

DOBER CHEMICAL CORP MIDLOTHIAN Illinois 60445 0.0025 Screened Out

CR BRANDS INC SPARTANBURG South Carolina 29307 0.0025 Screened Out

CONOCOPHILLIPS CO TREMLEY POINT TERMINAL LINDEN New Jersey 07036 0.0025 Screened Out

CHEMICAL SOLVENTS INC--DENISON FACILITY CLEVELAND Ohio 44109 0.0025 Screened Out

BRAINERD CHEMICAL CO INC TULSA OKLAHOMA 74147 0.0025 Screened Out

BIOLAB INC ASHLEY INDIANA 46705 0.0025 Screened Out

ATOTECH USA ROCK HILL South Carolina 29730 0.0025 Screened Out

ASTRO CHEMICALS INC SPRINGFIELD Massachusetts 01104 0.0025 Screened Out

BAKER PETROLITE CORP HOUSTON Texas 77049 0.0024345 Screened Out

KING INDUSTRIES INC NORWALK Connecticut 06852 0.0024 Screened Out

GATES CORP IOLA KANSAS 66749 0.0023 Screened Out

CLARIANT CORP CLEAR LAKE PLANT PASADENA Texas 77507 0.0023 Screened Out

HENTZEN COATINGS,INC MILWAUKEE Wisconsin 53218 0.002185 Screened Out

DYNASOL INC CANTON Massachusetts 02021 0.00215 Screened Out

CARESTREAM HEALTH COLORADO WINDSOR Colorado 80550 0.002 Screened Out

HUNTSMAN PETROCHEMICAL LLC DAYTON Texas 77535 0.002 Screened Out

UNIVAR USA INC SALEM BRANCH SALEM Massachusetts 01970 0.002 Screened Out

SHERWIN-WILLIAMS CO ORLANDO Florida 32809 0.002 Screened Out

COSMETIC LABORATORIES OF AMERICA CHATSWORTH California 91311 0.002 Screened Out

SHERWIN-WILLIAMS CO BEDFORD HEIGHTS Ohio 44146 0.002 Screened Out

UNIVAR USA INC SANTA FE SPRINGS SANTA FE SPRINGS California 90670 0.002 Screened Out

DUPONT EKC TECHNOLOGY HAYWARD California 94545 0.002 Screened Out

CALLAHAN CHEMICAL CO WALPOLE Massachusetts 02081 0.002 Screened Out

ASHLAND DISTRIBUTION CO CLEARFIELD Utah 84016 0.002 Screened Out

CRODA INC NEW CASTLE Delaware 19720 0.001905 Screened Out

TARR ACQUISITION LLC PORTLAND Oregon 97227 0.001825 Screened Out

Page 16 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

GOJO INDUSTRIES INC CUYAHOGA FALLS OHIO 44223 0.0016295 Screened Out

VOLTAIX LLC BRANCHBURG New Jersey 08876 0.0015 Screened Out

KELLY-MOORE PAINT CO INC SAN CARLOS California 94070 0.0015 Screened Out

HYDRITE CHEMICAL CO MILWAUKEE Wisconsin 53223 0.0015 Screened Out

GIANT CEMENT CO HARLEYVILLE South Carolina 29448 0.0015 Screened Out

BUCKMAN LABORATORIES INC MEMPHIS Tennessee 38108 0.0015 Screened Out

BAKER PETROLITE-RAYNE FACILITY RAYNE Louisiana 70578 0.0015 Screened Out

FUJIFILM HUNT CHEMICALS USA INC ROLLING MEADOWS Illinois 60008 0.00125 Screened Out

FIRST SOURCE WORLDWIDE LLC MILWAUKEE MILWAUKEE Wisconsin 53226 0.00125 Screened Out

MANN DISTRIBUTION WARWICK Rhode Island 02886 0.00112 Screened Out

BOEING COMMERCIAL AIRPLANE GROUP PLANT 2 

(PART)

SEATTLE Washington 98108 0.001 Screened Out

PENRAY COMPANIES INC ELK GROVE VILLAGE Illinois 60007 0.001 Screened Out

PENRAY COMPANIES INC WHEELING Illinois 60090 0.001 Screened Out

SHERWIN-WILLIAMS CO FLORA Illinois 62839 0.001 Screened Out

MONSANTO CO MUSCATINE Iowa 52761 0.001 Screened Out

LAFARGE NA (INCLUDING SYSTECH ENV CORP) PAULDING OHIO 45879 0.001 Screened Out

CLEAN HARBORS DEER PARK LLC LA PORTE TEXAS 77571 0.001 Screened Out

BRENNTAG SOUTHEAST INC CHARLOTTE North Carolina 28273 0.001 Screened Out

BENJAMIN MOORE & CO - NEWARK NEWARK New Jersey 07105 0.001 Screened Out

PPG ARCHITECTURAL COATINGS LOUISVILLE Kentucky 40214 0.0008 Screened Out

OMNOVA SOLUTIONS INC CHESTER South Carolina 29706 0.00077 Screened Out

VEYANCE TECHNOLOGIES INC MOUNT PLEASANT Iowa 52641 0.0005 Screened Out

GATES CORP POPLAR BLUFF MISSOURI 63901 0.0005 Screened Out

SOUTHWEST DISTRIBUTING CO MESA Arizona 85210 0.0005 Screened Out

NATIONAL INDUSTRIAL COATINGS INC DBA NICOAT 

INC

ITASCA Illinois 60143 0.0005 Screened Out

NALCO CO TEXARKANA Texas 75501 0.0005 Screened Out

HARWICK STANDARD DISTRIBUTION CORP AKRON Ohio 44305 0.0005 Screened Out

SURPASS CHEMICAL CO INC ALBANY New York 12204 0.000485 Screened Out

NALCO CO SCOTT Louisiana 70583 0.0003385 Screened Out

VERSO PAPER BUCKSPORT MILL BUCKSPORT MAINE 4416 0.0003 Screened Out

PARKER HANNIFIN TECH SEAL DIV WILSON North Carolina 27893 0.00029 Screened Out

MARY KAY INC DALLAS Texas 75247 0.00026 Screened Out

LAMBERTI SYNTHESIS USA INC CHATTANOOGA Tennessee 37406 0.0002205 Screened Out

LEVLAD CHATSWORTH California 91311 0.000185 Screened Out

CHEMETALL US INC JACKSON Michigan 49203 0.0001654 Screened Out

U S CHEMICAL WATERTOWN Wisconsin 53094 0.00014 Screened Out

IFF AUGUSTA LTD AUGUSTA Georgia 30906 0.000085 Screened Out

RIKER PRODUCTS INC TOLEDO Ohio 43612 0.000082 Screened Out

BAKER PETROLITE KILGORE BLEND PLANT KILGORE Texas 75662 0.0000807 Screened Out

NALCO CO ELLWOOD CITY Pennsylvania 16117 0.0000118 Screened Out

EMERALD SERVICES INC TACOMA Washington 98421 0.000005 Screened Out

AIR PRODUCTS PERFORMANCE MANUFACTURING INC RESERVE Louisiana 70084 0.000002 Screened Out

VEYANCE TECHNOLOGIES INC LINCOLN Nebraska 68504 0.00000001 Screened Out

Page 17 of 18
Table C-2. Comparisons of 2010 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name City State Zip Code 2010 Air 

Emissions (tpy) Outcome

tpy: tons per year

Page 18 of 18
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

CROWN BEVERAGE PACKAGING 1202 FONES RD OLYMPIA WA 98501 63.9665 Retain

BOEING COMMERCIAL AIRPLANES - 

EVERETT

3003 W CASINO RD EVERETT WA 98204 20.45 Retain

REXAM BEVERAGE CAN CO RE: KENT WA 

FACILITY

1220 N SECOND AVE KENT WA 98032 82.946 Retain

BALL METAL BEVERAGE CONTAINER CORP 91-320 KOMOHANA ST KAPOLEI HI 96707 10.95 Retain

SILGAN CAN CO 6200 FRANKLIN BLVD SUITE #100 SACRAMENTO CA 95824 5.0385 Retain

SILGAN CONTAINER MANUFACTURING CORP 3250 PATTERSON RD RIVERBANK CA 95367 7.8095 Retain

REXAM BEVERAGE CAN CO RE: FAIRFIELD 

PLANT

2433 CROCKER CIR FAIRFIELD CA 94533 9.161 Retain

BALL METAL BEVERAGE CONTAINER CORP 2400 HUNTINGTON DR FAIRFIELD CA 94533 21.5 Retain

METAL CONTAINER CORP - MIRA LOMA CAN 

PLANT

10980 INLAND AVE MIRA LOMA CA 91752 31.1755 Retain

REXAM BEVERAGE CAN CO RE: 

CHATSWORTH FACILITY

20730 PRAIRIE ST CHATSWORTH CA 91311 29.0045 Retain

BALL METAL BEVERAGE CONTAINER CORP 500 CRENSHAW BLVD TORRANCE CA 90503 16.65 Retain

CARRY-ON TRAILER CORP 5300 WESTMORELAND RD WINNEMUCCA NV 89445 5.0015 Retain

REXAM BEVERAGE CAN CO RE: PHOENIX 

FACILITY

211 N 51AVE PHOENIX AZ 85043 41.904 Retain

TTM TECHNOLOGIES INC 710 N 600 W LOGAN UT 84321 5.851 Retain

CROWN BEVERAGE PACKAGING 620 N 4TH ST WORLAND WY 82401 53.3405 Retain

METAL CONTAINER CORPORTION - 

WINDSOR CAN PLANT

1201 METAL CONTAINER CT WINDSOR CO 80550 54.2575 Retain

CIRCLE GRAPHICS INC 120 9TH AVE LONGMONT CO 80501 5 Retain

BALL METAL BEVERAGE CONTAINER CORP 4525 INDIANA ST GOLDEN CO 80403 31.5 Retain

ROCKY MOUNTAIN METAL CONTAINER 17755 W 32ND AVE GOLDEN CO 80401 33.5 Retain

TOYOTA MOTOR MANUFACTURING TEX AS 

INC

1 LONE STAR PASS SAN ANTONIO TX 78264 9.93683575 Retain

UNION CARBIDE CORP SEADRIFT PLANT 7501 N HWY 185 SEADRIFT TX 77983 17.666 Retain

GREIF PACKAGING LLC 10850 STRANG RD LA PORTE TX 77571 5.00805 Retain

EQUISTAR CHEMICALS BAYPORT 

CHEMICALS PLANT

5761 UNDERWOOD RD PASADENA TX 77507 5.2385 Retain

MEMC PASADENA INC 3000 N S ST PASADENA TX 77503 23.8115 Retain

CROWN BEVERAGE PACKAGING 12910 JESS PIRTLE BLVD SUGAR LAND TX 77478 31.488 Retain

CROWN BEVERAGE PACKAGING 2501 N FRAZIER ST CONROE TX 77303 32.064 Retain

BALL METAL BEVERAGE CONTAINER CORP 1001 N FM 3083 E CONROE TX 77303 17.15 Retain

MAVERICK TUBE LLC DBA TENARISCONROE 699 F.M. 3083 CONROE TX 77301 6.9444811 Retain

BALL METAL BEVERAGE CONTAINER CORP 6600 WILL ROGERS BLVD FORT WORTH TX 76140 12.5 Retain

NUCOR VULCRAFT GROUP - GRAPELAND 

DIV

175 COUNTY RD 2345 GRAPELAND TX 75844 12.204 Retain

EASTMAN CHEMICAL CO TEXAS 

OPERATIONS

300 KODAK BLVD LONGVIEW TX 75602 15.3195 Retain

REXAM BEVERAGE CAN CO RE: LONGVIEW 

FACILITY

1001 FISHER RD LONGVIEW TX 75604 52.485 Retain

SILGAN CAN CO 500 NW LOOP 286 SUITE 101 PARIS TX 75460 6.6505 Retain

OLDCASTLE BUILDING ENVELOPE - TEXAS 

FACILITY

803 AIRPORT RD TERRELL TX 75160 15.309 Retain

MOBIL CHEMICAL CO 41501 WOLVERINE RD SHAWNEE OK 74804 19.075 Retain

AIR SYSTEM COMPONENTS LP 900 DARR PARK DR PONCA CITY OK 74601 19.8795 Retain

US DOD USAF TINKER AFB 72 CEG/CEA 7535 FIFTH ST TINKER AFB OK 73145 5.1 Retain

DEXTER AXLE 500 SE 27TH EL RENO OK 73036 7.514 Retain

GRAPHIC PACKAGING INTERNATIONAL INC 10300 ROBERTS BLVD FORT SMITH AR 72916 13.2445 Retain

KAWNEER CO INC 600 KAWNEER DR SPRINGDALE AR 72764 9.9965 Retain

SUPERIOR INDUSTRIES INTERNATIONAL 

ARKANSAS LLC

1301 N DIXIELAND RD ROGERS AR 72756 12.883 Retain

SUPERIOR INDUSTRIES INTERNATIONAL 

ARKANSAS LLC

1901 E BORICK DR FAYETTEVILLE AR 72701 10.9685 Retain

L A DARLING CO - PIGGOTT AR FACILITY HWY 49 S PIGGOTT AR 72454 5.4585 Retain

QG PRINTING II CORP 4708 KRUEGER DR JONESBORO AR 72401 5.85 Retain

MAVERICK TUBE LLC 4950 N COUNTY RD 967 BLYTHEVILLE AR 72315 11.16161105 Retain

WHEELING MACHINE PRODUCTS DIV PINE 

BLUFF

5411 INDUSTRIAL DR S PINE BLUFF AR 71602 6 Retain

BERENFIELD CONTAINERS SW LTD 3300 N HUTCHINSON ST WHITE HALL AR 71602 8.5085 Retain

NOVOLYTE PERFORMANCE MATERIALS 111 W IRENE RD ZACHARY LA 70791 5.355 Retain

GREIF PACKAGING LLC 6000 JEFFERSON HWY NEW ORLEANS LA 70123 9.5545 Retain

NUCOR CORP - VULCRAFT/NUCOR COLD 

FINISH DIV

1601 W OMAHA AVE NORFOLK NE 68701 10.25 Retain

VALMONT INDUSTRIES INC 7002 N 288TH ST VALLEY NE 68064 5 Retain

THE COLEMAN CO INC 3600 N HYDRAULIC WICHITA KS 67219 5.858 Retain

Page 1 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

GREIF INDUSTRIAL PACKAGING & SERVICES 7604 RAILROAD AVE WINFIELD KS 67156 9.1095 Retain

VON HOFFMANN GRAPHICS INC 1005 COMMERCIAL DR OWENSVILLE MO 65066 5.0775 Retain

SILGAN CONTAINERS MANUFACTURING 

CORP

2115 SW LOWER LAKE RD SAINT JOSEPH MO 64504 8.9735 Retain

FORD MOTOR COMPANY--KANSAS CITY 

ASSEMBLY PLANT

8121 E U.S. HWY 69 CLAYCOMO MO 64119 56.55 Retain

GENERAL MOTORS WENTZVILLE ASSEMBLY 1500 E RT A WENTZVILLE MO 63385 9.05 Retain

SAF-HOLLAND USA INC 101 S ELM WARRENTON MO 63383 21.4795 Retain

SCHAEFFER MANUFACTURING 102 BARTON ST SAINT LOUIS MO 63104 6.34465 Retain

TRILLA ST LOUIS CORP 2391 CASSENS DR FENTON MO 63026 9.628 Retain

METAL CONTAINER CORP - ARNOLD CAN 

PLANT

42 TENBROOK INDUSTRIAL PARK ARNOLD MO 63010 42.0245 Retain

THE KNAPHEIDE MANUFACTURING CO 1848 WESTPHALIA STRASSE QUINCY IL 62305 16.081 Retain

PRECOAT METALS 25 NORTHGATE INDUSTRIAL DR GRANITE CITY IL 62040 5.2675 Retain

CNH AMERICA LLC 600 E PEORIA ST GOODFIELD IL 61742 16.723 Retain

NATIONAL COATINGS INC 604 US HWY 150 E GALESBURG IL 61401 7.3525 Retain

SILGAN CONTAINERS MANUFACTURING 

CORP

400 N 15TH ST ROCHELLE IL 61068 11.045 Retain

SIGNCRAFT SCREEN PRINT 100 A.J. HARLE DR GALENA IL 61036 12.185 Retain

CHRYSLER BELVIDERE ASSEMBLY PLANT 3000 W CHRYSLER DR BELVIDERE IL 61008 11.15 Retain

CROWN BEVERAGE PACKAGING 1035 E N ST BRADLEY IL 60915 64.844 Retain

GREIF PACKAGING LLC 4300 W 130TH ST ALSIP IL 60803 18.7305 Retain

SKOLNIK INDUSTRIES 4900 S KILBOURN AVE CHICAGO IL 60632 8.8 Retain

COLOR COMMUNICATIONS INC 4242 W FILLMORE CHICAGO IL 60624 5.4 Retain

MEYER STEEL DRUM INC 2000 S KILBOURN AVE CHICAGO IL 60623 12.2775 Retain

BWAY CORP 3200 S KILBOURN AVE CHICAGO IL 60623 22.99445 Retain

CHICAGO STEEL CONTAINER CORP 1846 S KILBOURN AVE CHICAGO IL 60623 10.8335 Retain

REXAM BEVERAGE CAN CO RE : CHICAGO 

PLANT

1101 W 43RD ST CHICAGO IL 60609 33.1715 Retain

EDSAL MANUFACTURING CO INC 4400 S PACKER CHICAGO IL 60609 33.9425 Retain

CROWN AEROSOL PACKAGING 3737 E EXCHANGE AVE AURORA IL 60504 5.7695 Retain

SIGNODE 7701 W 71ST ST BRIDGEVIEW IL 60455 8.35 Retain

ALLIED TUBE & CONDUIT CORP 16100 S LATHROP AVE HARVEY IL 60426 6.864 Retain

CHICAGO HEIGHTS STEEL 211 E MAIN ST CHICAGO HEIGHTS IL 60411 35.8595 Retain

KNS COS INC 475 RANDY RD CAROL STREAM IL 60188 8.80855 Retain

SYCAMORE SYSTEMS LLC 449 N CALIFORNIA ST SYCAMORE IL 60178 6.722 Retain

BROWN PRINTING CO 11595 MCCONNELL RD WOODSTOCK IL 60098 6.265 Retain

ACME FINISHING CO INC 1595 E OAKTON ST ELK GROVE VILLAGE IL 60007 8.79 Retain

NAHAN PRINTING INC 7000 SAUKVIEW DR SAINT CLOUD MN 56303 5.856965 Retain

BROWN PRINTING CO 2300 BROWN AVE WASECA MN 56093 6.7615 Retain

NORTHLAND ALUMINUM PRODUCTS I NC 5005 COUNTY RD 25 MINNEAPOLIS MN 55416 6.3187 Retain

FORD MOTOR CO TWIN CITIES ASSEMBLY 

PLANT

966 S MISSISSIPPI RIVER BLVD SAINT PAUL MN 55116 7.08 Retain

REXAM BEVERAGE CAN CO RE: EVA STREET 

ST PAUL MN

139 EVA ST SAINT PAUL MN 55107 78.8155 Retain

S B FOOT TANNING CO 805 BENCH ST RED WING MN 55066 24.362 Retain

CROWN FOOD PACKAGING 2929 W BRIDGE ST OWATONNA MN 55060 127.5625 Retain

ALLIANCE INDUSTRIES WAUPACA N 2467 VAUGHAN RD WAUPACA WI 54981 10.415 Retain

SILGAN CONTAINERS MANUFACTURING 

CORP

1416 INDIANHEAD DR MENOMONIE WI 54751 7.75 Retain

TORO CO 200 SIME AVE TOMAH WI 54660 5.426 Retain

CROWN BEVERAGE PACKAGING 1501 ST JAMES ST LA CROSSE WI 54603 25.777 Retain

SENECA FOODS CORP 801 SAUK AVE BARABOO WI 53913 25.711 Retain

BALL CONTAINER LLC 105 E BLACKHAWK DR FORT ATKINSON WI 53538 11.95 Retain

BALL METAL BEVERAGE CONTAINER CORP 8500 W TOWER AVE MILWAUKEE WI 53224 35 Retain

KUBIN-NICHOLSON CORP 8448 N 87TH ST MILWAUKEE WI 53224 9.352 Retain

KITZINGER COOPERAGE CORP 2529 E NORWICH AVE SAINT FRANCIS WI 53235 9.7653 Retain

PPG INDUSTRIES INC-OAK CREEK 10800 S 13TH ST OAK CREEK WI 53154 35.58 Retain

MID-AMERICA STEEL DRUM CO IN C 8570 S CHICAGO RD OAK CREEK WI 53154 18.578 Retain

QUAD/GRAPHICS INC N61 W23044 HARRY'S WAY ATTN: 

ENVIRONMENTAL

SUSSEX WI 53089 12.85 Retain

BEMIS MANUFACTURING CO PLANT B 300 MILL ST SHEBOYGAN FALLS WI 53085 12.7415 Retain

SILGAN CONTAINERS MANUFACTURING 

CORP

520 W 2ND ST OCONOMOWOC WI 53066 6.475 Retain

QUAD/GRAPHICS INC N11896 HWY 175 PO BOX 2718 LOMIRA WI 53048 5.3675 Retain

JOHN DEERE HORICON WORKS-DT 300 N VINE ST HORICON WI 53032 5.5 Retain

QUAD/GRAPHICS INC 1900 W SUMNER ST HARTFORD WI 53027 11.85 Retain

BROAN-NUTONE LLC 926 W STATE ST HARTFORD WI 53027 8.7795 Retain

WORTHINGTON CYLINDERS WISCONSI N 

LLC

300 E BREED ST CHILTON WI 53014 5.270385 Retain

AMERICAN FINISHING RESOURCES INC 476 CLAY ST CHILTON WI 53014 6.272 Retain

CNH AMERICA LLC 1930 DES MOINES AVE BURLINGTON IA 52601 11.18 Retain

CARRY-ON TRAILER CORP 1965 HWY 30 MISSOURI VALLEY IA 51555 5.464 Retain

PELLA CORP CARROLL OPERATIONS 1750 E US HWY 30 E CARROLL IA 51401 5.5825 Retain

Page 2 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

SILGAN CONTAINERS MANUFACTURIN G 

CORP

3591 MAPLE DR FORT DODGE IA 50501 13.686535 Retain

PELLA CORP 102 MAIN ST PELLA IA 50219 19.5195 Retain

JOHN DEERE DES MOINES WORKS 825 SW IRVINEDALE DR ANKENY IA 50023 21.1695 Retain

BRADFORD WHITE CORP 200 LAFAYETTE ST MIDDLEVILLE MI 49333 7.1365 Retain

DEXTER CHASSIS GROUP PLANT 55 501 S MILLER DR WHITE PIGEON MI 49099 16.1035 Retain

GRAPHIC PACKAGING INTERNATIONAL INC 1500 N PITCHER ST KALAMAZOO MI 49007 8.6 Retain

GMVM-LANSING GRAND RIVER ASSEMBLY 920 TOWNSEND ST MAIL CODE: 

489-066-600

LANSING MI 48921 5.8 Retain

GENERAL MOTORS LANSING DELTA 

TOWNSHIP

8175 MILLETT HWY LANSING MI 48917 24.55 Retain

GM LLC POWERTRAIN FLINT ENGINE 

OPERATIONS

2100 BRISTOL RD FLINT MI 48552 26.1855 Retain

CHRYSLER JEFFERSON NORTH ASSEMBLY 

PLANT

2101 CONNOR AVE DETROIT MI 48215 56 Retain

AJAX METAL PROCESSING INC 4651 BELLEVUE AVE DETROIT MI 48207 7.4295 Retain

FORD MOTOR CO MICHIGAN ASSEMBLY 

PLANT

38303 MICHIGAN AVE WAYNE MI 48184 6.065 Retain

FORD MOTOR CO DEARBORN TRUCK PLANT 3001 MILLER RD DEARBORN MI 48121 66.15 Retain

CHRYSLER WARREN TRUCK ASSEMBLY 

PLANT (PART)

21500 MOUND RD WARREN MI 48091 8.655 Retain

CURTIS METAL FINISHING CO 6645 SIMS DR STERLING HEIGHTS MI 48313 6.169 Retain

HOWARD FINISHING LLC 32565 DEQUINDRE MADISON HEIGHTS MI 48071 12.3605 Retain

BALL METAL BEVERAGE CONTAINER CORP 501 N SIXTH ST MONTICELLO IN 47960 33 Retain

RR DONNELLEY CRAWFORDSVILLE 1009 SLOAN ST CRAWFORDSVILLE IN 47933 6.608 Retain

CROWN BEVERAGE PACKAGING 400 N WALNUT ST CRAWFORDSVILLE IN 47933 21.597 Retain

SUBARU OF INDIANA AUTOMOTIVE INC 5500 STATE RD 38E LAFAYETTE IN 47905 29.635 Retain

SILGAN WHITE CAP CORP 2201 W MARYLAND ST EVANSVILLE IN 47710 15.4125 Retain

TOYOTA MOTOR MANUFACTURING INDIANA 

INC

4000 TULIP TREE DR PRINCETON IN 47670 17.969 Retain

ALCOA INC - WARRICK OPERATIONS HWYS 66 & 61 NEWBURGH IN 47629 8.5 Retain

SABIC INNOVATIVE PLASTICS MT VERNON 

LLC

1 LEXAN LN MOUNT VERNON IN 47620 5.25 Retain

ASHLEY INDUSTRIAL MOLDING INC 310 S WABASH ASHLEY IN 46705 6 Retain

GEA BPO LLC 301 N CURRY PIKE BLOOMINGTON IN 47404 6.5 Retain

ENKEI AMERICA INC 2900 W INWOOD DR COLUMBUS IN 47201 6 Retain

BATESVILLE MANUFACTURING INC -DOLL 

PLANT

1000 E PEARL ST BATESVILLE IN 47006 5.3525 Retain

NUCOR VULCRAFT GROUP SAINT JOE DIV 6610 COUNTY RD 60 SAINT JOE IN 46785 8.231 Retain

GM TRUCK GROUP FORT WAYNE ASSEMBLY 12200 LAFAYETTE CENTER RD ROANOKE IN 46783 15.2 Retain

THERMA-TRU CORP 601 RE JONES RD BUTLER IN 46721 24.3635 Retain

MIDDLEBURY HARDWOOD PRODUCTS 101 JOAN DR MIDDLEBURY IN 46540 5.3965 Retain

SEQUA COATINGS CORP-PRECOAT M ETALS 

DIV

US HWY 12 AT RT 249 PORTAGE IN 46368 4.9 Screened Out

SILGAN CONTAINERS MANUFACTURING 

CORP

300 N FAIL RD LA PORTE IN 46350 65.4225 Retain

PRECOAT METALS 858 E HUPP RD LA PORTE IN 46350 6.935 Retain

SILGAN CONTAINERS MANUFACTURING 

CORP

2501 165TH ST HAMMOND IN 46320 5.873 Retain

PRECOAT METALS 1950 E MAIN ST GREENFIELD IN 46140 7.843 Retain

CROWN EQUIPMENT CORP 2600 E STATE RD 240 GREENCASTLE IN 46135 6.75701 Retain

AAP ST MARYS CORP 1100 MCKINLEY RD SAINT MARYS OH 45885 7.502 Retain

WHIRLPOOL CORP FINDLAY DIV 4901 N MAIN ST FINDLAY OH 45840 21.509 Retain

BALL METAL BEVERAGE CONTAINER CORP 12340 TOWNSHIP RD 99 E FINDLAY OH 45840 160.5 Retain

AMERICAN TRIM LLC 1501 W MICHIGAN ST SIDNEY OH 45365 11.892 Retain

PLY GEM 2615 CAMPBELL RD SIDNEY OH 45365 12.155 Retain

INGERSOLL-RAND CO STEELCRAFT DIV 9017 BLUE ASH RD CINCINNATI OH 45242 32.5 Retain

BERENFIELD CONTAINERS INC MASON 1229 CASTLE DR MASON OH 45040 12.689 Retain

RR DONNELLEY & SONS CO 1145 CONWELL AVE WILLARD OH 44890 8.7445 Retain

ARTIFLEX MANUFACTURING LLC GERSTCO 

DIV WOOSTER

1425 E BOWMAN ST WOOSTER OH 44691 13.3625 Retain

NOVELIS CORP 390 GRISWOLD ST NE WARREN OH 44483 14.966 Retain

TECNOCAP LLC 2100 GRISWOLD NE WARREN OH 44483 7.365 Retain

GM LORDSTOWN COMPLEX 2300 HALLOCK-YOUNG RD LORDSTOWN OH 44481 5 Retain

HESS PRINT SOLUTIONS 3765 SUNNYBROOK RD BRIMFIELD OH 44240 5 Retain

NORTH COAST CONTAINER CORP 8806 CRANE AVE CLEVELAND OH 44105 17.316 Retain

AK STEEL CORP - ZANESVI LLE WORKS 1724 LINDEN AVE ZANESVILLE OH 43701 6 Retain

CROWN FOOD PACKAGING 5201 ENTERPRISE BLVD TOLEDO OH 43612 12.7245 Retain

KUKA TOLEDO PRODUCTION OPERATIONS 3770 STICKNEY AVE TOLEDO OH 43612 16.5510995 Retain

DECORATIVE PANELS INTERNATIONA L 2900 HILL AVE TOLEDO OH 43607 13.1405 Retain

REXAM BEVERAGE CAN CO RE: 

WHITEHOUSE PLANT

10444 WATERVILLE WHITEHOUSE OH 43571 76.328 Retain

Page 3 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

SILGAN CAN CO 12-773 ST RT 110 NAPOLEON OH 43545 12.7305 Retain

ELECTROPRIME INC 63 DIXIE HWY ROSSFORD OH 43460 7.819 Retain

REXAM BEVERAGE CAN CO RE: FREMONT 

PLANT

2145 CEDAR FREMONT OH 43420 126.955 Retain

HONDA OF AMERICA MANUFACTURING INC 11000 STATE RT 347 EAST LIBERTY OH 43319 38.3 Retain

WHIRLPOOL CORP MARION DIV 1300 MARION-AGOSTA RD MARION OH 43302 51.461 Retain

BALL CONTAINER LLC - COLUMBUS CAN 

PLANT

350 MCCORMICK BLVD COLUMBUS OH 43213 82 Retain

HONDA OF AMERICA MANUFACTURING INC 24000 HONDA PKWY MARYSVILLE OH 43040 40.2 Retain

PRECOAT METALS 2604 RIVER RD HAWESVILLE KY 42348 5.218 Retain

LOGAN ALUMINUM INC US HWY 431 N RUSSELLVILLE KY 42276 4.9495 Retain

GREIF PACKAGING LLC 7425 INDUSTRIAL RD FLORENCE KY 41042 34.7245 Retain

SQUARE D CO 1601 MERCER RD LEXINGTON KY 40511 9.092 Retain

HITACHI AUTOMOTIVE SYSTEMS AMERICAS 

INC-BEREA KY

301 MAYDE RD BEREA KY 40403 14.7982 Retain

TOYOTA MOTOR MANUFACTURING 

KENTUCKY INC

1001 CHERRY BLOSSOM WAY GEORGETOWN KY 40324 9.387 Retain

FORD MOTOR CO KENTUCKY TRUCK PLANT 3001 CHAMBERLAIN LN LOUISVILLE KY 40241 44.25 Retain

ESCO CORP 9098 EASTSIDE DR EXT. NEWTON MS 39345 9.578 Retain

PRECOAT METALS 1095 MENDELL DAVIS DR JACKSON MS 39272 10.9045 Retain

ANDERSON TULLY LUMBER CO 

WALTERSVILLE LUMBER MILL

1725 N WASHINGTON ST VICKSBURG MS 39181 14.1275 Retain

NISSAN NORTH AMERICA INC CANTON MS 300 NISSAN DR CANTON MS 39046 9.612 Retain

HUNTER DOUGLAS TUPELO CENTER RT. 2 LEE INDUSTRIAL PARK E SHANNON MS 38868 6.1565 Retain

REXAM BEVERAGE CAN CO RE: OLIVE 

BRANCH FACILITY

10800 MARINA DR OLIVE BRANCH MS 38654 82.2945 Retain

CROWN BEVERAGE PACKAGING 195 CROWN RD BATESVILLE MS 38606 22.1595 Retain

CECO DOOR PRODUCTS 9159 TELECOM DR MILAN TN 38358 16.754 Retain

KOHLER CO 2000 N 5TH ST UNION CITY TN 38261 5.347 Retain

TEKNOR APEX TENNESSEE CO (AKA 

HAYWOOD CO)

751 DUPREE ST BROWNSVILLE TN 38012 6.669 Retain

VESTAL MANUFACTURING ENTERPRISES 

INC

177 INDUSTRIAL PARK RD SWEETWATER TN 37874 13.094 Retain

VOLKSWAGEN GROUP OF AMERICA 

CHATTANOOGA OPERATIONS LLC

8001 VOLKSWAGEN DR CHATTANOOGA TN 37416 11.0214265 Retain

ALSTOM POWER INC CHATTANOOGA 

BOILERS

1119 RIVERFRONT PKWY CHATTANOOGA TN 37402 23.9355 Retain

BATESVILLE MANUFACTURING INC 175 MONOGARD DR MANCHESTER TN 37355 34.1765 Retain

LA-Z-BOY TENNESSEE 500 WALNUT GROVE RD DAYTON TN 37321 6.58324085 Retain

MAYTAG CORP CLEVELAND COOKING 

PRODUCTS PLANT 1

740 KING EDWARD AVE SE CLEVELAND TN 37311 6.264 Retain

NASHVILLE WIRE PRODUCTS 1604 COUNTY HOSPITAL RD NASHVILLE TN 37218 18.35 Retain

QUAD GRAPHICS NASHVILLE 2947 BRICK CHURCH PIKE NASHVILLE TN 37207 7.102 Retain

NISSAN NA INC SMYRNA MANUFACTURING 

PLANT

983 NISSAN DR SMYRNA TN 37167 30.74138035 Retain

STATE INDUSTRIES INC 500 TENNESSEE WALTZ PKWY ASHLAND CITY TN 37015 9.4075 Retain

RUSKIN CO HWY 27 N GENEVA AL 36340 12.793 Retain

DUNBARTON CORP REDIFRAME DIV 1101 TECHNOLOGY DR DOTHAN AL 36303 5.3 Retain

NUCOR CORP VULCRAFT DIV 7205 GAULT AVE N FORT PAYNE AL 35967 6.3425 Retain

HART & COOLEY INC 4910 MOORES MILL RD HUNTSVILLE AL 35811 8.525 Retain

ITW SEXTON INC 3101 SEXTON RD DECATUR AL 35603 19.2556 Retain

3M CO - GUIN 6675 US HWY 43 GUIN AL 35563 12.501 Retain

MERCEDES-BENZ US INTERNATIONAL INC 1 MERCEDES DR VANCE AL 35490 28.302 Retain

AKZO NOBEL COATINGS INC 1629 VANDERBILT RD BIRMINGHAM AL 35234 12.3625 Retain

HONDA MANUFACTURING OF ALABAMA LLC 1800 HONDA DR LINCOLN AL 35096 25.27 Retain

M&B HANGERS 1313 PKWY DR SE LEEDS AL 35094 13.472 Retain

KEYMARK CORP OF FLORIDA 2540 KNIGHTS STATION RD LAKELAND FL 33810 8.999 Retain

MOMENTIVE SPECIALTY CHEMICALS INC 2525 S COMBEE RD LAKELAND FL 33801 8.3575 Retain

BALL METAL BEVERAGE CONTAINER CORP 4700 WHITEWAY DR TAMPA FL 33617 17 Retain

METAL INDUSTRIES INC - BUSHNELL 400 W WALKER AVE BUSHNELL FL 33513 10.6975 Retain

METAL CONTAINER CORP - JACKSONVILLE 

CAN PLANT

1100 N ELLIS RD JACKSONVILLE FL 32254 25.615 Retain

KIA MOTORS MANUFACTURING OF GEORGIA 7777 KIA PKWY WEST POINT GA 31833 4.9645 Retain

BWAY CORP 1601 VALDOSTA HWY HOMERVILLE GA 31634 7.80461 Retain

YKK AP AMERICA INC 1229 HWY 441 N BYPASS DUBLIN GA 31021 9.392 Retain

POWER PARTNERS INC 200 NEWTON BRIDGE RD ATHENS GA 30607 5.246 Retain

CARRY-ON TRAILER CORP 101 JOE HARVEY ST LAVONIA GA 30553 17.346 Retain

TOPPAN INTERAMERICA INC 1131 HWY 155 S MC DONOUGH GA 30253 11.15 Retain

BRIGGS & STRATTON POWER PRODUCTS 

MCDONOUGH OPERATIONS

535 MACON RD MC DONOUGH GA 30253 9.043 Retain

BALL CONTAINER LLC ROME CAN PLANT 110 BALL DR ROME GA 30161 44.5 Retain

AGY AIKEN LLC 2556 WAGENER RD AIKEN SC 29801 14.516 Retain

Page 4 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

BMW MANUFACTURING CO LLC 1400 HWY 101 S GREER SC 29651 152.52 Retain

CROWN BEVERAGE PACKAGING 100 EVANS ROW CHERAW SC 29520 23.876 Retain

NUCOR CORP VULCRAFT DIV 1501 W DARLINGTON ST FLORENCE SC 29501 12.2435 Retain

HUSQVARNA CONSUMER OUTDOOR 

PRODUCTS

172 OLD ELLOREE RD ORANGEBURG SC 29116 6.604 Retain

REXAM BEVERAGE CAN CO RE: 

BISHOPVILLE SC FACILITY

609 COUSAR ST BISHOPVILLE SC 29010 89.26 Retain

AVERY DENNISON RBIS LENOIR 950 GERMAN ST LENOIR NC 28645 5.734 Retain

SILGAN CAN CO 2120 NC HWY N UNIT A MAXTON NC 28364 9.7895 Retain

BERENFIELD CONTAINERS SE LTD 12180 UNIVERSITY CITY BLVD HARRISBURG NC 28075 5.351 Retain

WIX FILTRATION CORP - ALLEN PLANT 2900 NW BLVD GASTONIA NC 28052 5.9525 Retain

AIR SYSTEM COMPONENTS LP 3301 N MAIN ST TARBORO NC 27886 16.5235 Retain

BALL METAL BEVERAGE CONTAINER CORP 1900 BARNES ST REIDSVILLE NC 27320 102 Retain

THOMAS BUILT BUSES INC 715 W FAIRFIELD RD HIGH POINT NC 27263 15.9935 Retain

REXAM BEVERAGE CAN CO RE: WINSTON 

SALEM PLANT

4000 OLD MILWAUKEE LN WINSTON-SALEM NC 27107 136.173 Retain

CROWN CORK & SEAL CO (USA) INC CROWN 

CLOSURE DIV

3011 BIRCH DR WEIRTON WV 26062 92.2445 Retain

BALL METAL FOOD CONTAINER CORP 3010 BIRCH DR WEIRTON WV 26062 13.25 Retain

ROYAL MOULDINGS LTD; MARION VIRGINIA 135 BEAR CREEK RD MARION VA 24354 8.9435 Retain

VAUGHAN-BASSETT FURNITURE CO GALAX 300 E GRAYSON ST GALAX VA 24333 4.99620635 Retain

BALL METAL BEVERAGE CONTAINER CORP 8935 POCAHONTAS TRAIL JAMES 

RIVER COMMERCE CENTER

WILLIAMSBURG VA 23185 173 Retain

RR DONNELLEY 2347 KRATZER RD HARRISONBURG VA 22802 48.2645 Retain

PHOENIX COLOR CORP 18249 PHOENIX DR HAGERSTOWN MD 21742 8.5 Retain

CROWN FOOD PACKAGING 8801 CITATION RD BALTIMORE MD 21221 34.548 Retain

CAN CORP OF AMERICA INC 326 JUNE AVE BLANDON PA 19510 6.5965 Retain

GREIF PACKAGING LLC 695 LOUIS DR WARMINSTER PA 18974 6.028 Retain

SUPERPAC INC 1220 INDUSTRIAL BLVD SOUTHAMPTON PA 18966 7.5855 Retain

RR DONNELLEY LANCASTER EAST 216 GREENFIELD RD LANCASTER PA 17601 7.936 Retain

RR DONNELLEY LANCASTER WEST 1375 HARRISBURG PIKE LANCASTER PA 17601 9.08235 Retain

NEW YORK WIRE 500 E MIDDLE ST HANOVER PA 17331 28.0405 Retain

CROWN FOOD PACKAGING 1650 BROADWAY HANOVER PA 17331 5.2265 Retain

AMES TRUE TEMPER INC 1500 S CAMERON ST HARRISBURG PA 17104 27.6195 Retain

FRANKLIN INVESTMENT CORP 600 ATLANTIC AVE FRANKLIN PA 16323 8.5 Retain

BEDFORD MATERIALS CO INC 7676 ALLEGHENY RD MANNS CHOICE PA 15550 14.205 Retain

PPG INDUSTRIES,INC-SPRINGDALE 

COMPLEX

125 COLFAX ST SPRINGDALE PA 15144 5.8125 Retain

USS - CLAIRTON PLANT 400 STATE ST CLAIRTON PA 15025 41 Retain

VULCRAFT OF NEW YORK INC 5362 RAILROAD ST CHEMUNG NY 14825 10.4555 Retain

HAMMER PACKAGING CORP 200 LUCIUS GORDON DR WEST HENRIETTA NY 14586 8.2645 Retain

SENECA FOODS CORP CAN PLANT 3709 MILL ST MARION NY 14505 5.423 Retain

WHITING DOOR MANUFACTURING CORP 113 CEDAR ST AKRON NY 14001 11.6965 Retain

BALL METAL BEVERAGE CONTAINER CORP 11 ADAMS RD SARATOGA SPRINGS NY 12866 19.25 Retain

METAL CONTAINER CORP - NEWBURGH CAN 

PLANT

130 BREUNIG RD NEW WINDSOR NY 12553 40.4295 Retain

BALL METAL BEVERAGE CONTAINER CORP 95 BALLARD RD MIDDLETOWN NY 10940 17.5 Retain

SILGAN CONTAINERS MANUFACTURING 

CORP

135 NATIONAL RD EDISON NJ 08817 4.995 Retain

MAUSER CORP 14 CONVERY BLVD WOODBRIDGE NJ 07095 8.8765 Retain

STANLEY WORKS HAND TOOLS DIV 600 MYRTLE ST NEW BRITAIN CT 06052 10.5515 Retain

S D WARREN CO 89 CUMBERLAND ST WESTBROOK ME 04098 35.20941 Retain

TACO INC - CRANSTON 1160 CRANSTON ST CRANSTON RI 02920 5.7265 Retain

CROWN BEVERAGE PACKAGING GLEN & SHEPARD ST LAWRENCE MA 01843 70.1775 Retain

CROWN BEVERAGE PACKAGING 380 CALLE FABRIL ST KM 126 PR-3, 

PR INDUSTRIAL PARK

CAROLINA PR 00985 24.194 Retain

3M CO - SPRINGFIELD 3211 E CHESTNUT EXPY SPRINGFIELD MO 65802 0.02 Screened Out

ECOLAB INC 261 HWY 155 S MC DONOUGH GA 30253 0.041 Screened Out

ARLON GRAPHICS LLC 2811 S HARBOR BLVD SANTA ANA CA 92704 0.2365 Screened Out

CNH AMERICA LLC 2701 OAKES RD STURTEVANT WI 53177 0.317 Screened Out

3M CO - CORDOVA 22614 RT 84 N CORDOVA IL 61242 0.614 Screened Out

3M CO - BROWNWOOD 4501 HWY 377 S BROWNWOOD TX 76801 0.91 Screened Out

3M CO - HUTCHINSON 905/915 ADAMS ST SE HUTCHINSON MN 55350 1.585 Screened Out

3M CO - MEDINA 1030 LAKE RD MEDINA OH 44256 0.168 Screened Out

3M CO - NEVADA 2120 E AUSTIN BLVD NEVADA MO 64772 0.385 Screened Out

3M COTTAGE GROVE CENTER 10746 INNOVATION RD COTTAGE GROVE MN 55016 0.112 Screened Out

A BRITE CO 3217 WOOD DR GARLAND TX 75041 0.0025 Screened Out

ABC COMPOUNDING CO INC 6970 JONESBORO RD MORROW GA 30260 0.3775 Screened Out

ABC COMPOUNDING CO OF TEXAS INC 1102 AVE J E GRAND PRAIRIE TX 75050 0.06 Screened Out

ACCESS BUSINESS GROUP LLC 7575 FULTON ST E ADA MI 49355 1.9855 Screened Out

ACCURATE DISPERSIONS 192 W 155TH ST SOUTH HOLLAND IL 60473 0.1335 Screened Out

ACTEGA KELSTAR INC 1050 TAYLORS LN CINNAMINSON NJ 08077 0.01 Screened Out

ACTON TECHNOLOGIES INC 100 THOMPSON ST PITTSTON PA 18640 0.005 Screened Out

ADCO CLEANING PRODUCTS LLC 900 W MAIN ST SEDALIA MO 65301 0.0605 Screened Out

Page 5 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

AEP INDUSTRIES INC 1201 S PINE HILL RD GRIFFIN GA 30224 0.11925 Screened Out

AFTON CHEMICAL CORP 501 MONSANTO AVE SAUGET IL 62201 0.02 Screened Out

AFTON CHEMICAL CORP 725 CANNON BRIDGE RD ORANGEBURG SC 29115 3.301 Screened Out

AIR PRODUCTS PERFORMANCE 

MANUFACTURING INC

474 W 19TH ST RESERVE LA 70084 0.0000025 Screened Out

AIR PRODUCTS PERFORMANCE 

MANUFACTURING INC

337 VINCENT DR MILTON WI 53563 0.0135 Screened Out

AKCROS CHEMICALS INC 500 JERSEY AVE NEW BRUNSWICK NJ 08901 0.125 Screened Out

AKZO NOBEL COATINGS INC 1660 CROSS ST SE SALEM OR 97302 0.0519 Screened Out

AKZO NOBEL COATINGS INC 1000 INDUSTRIAL PARK DR CLINTON MS 39056 0.0945 Screened Out

AKZO NOBEL COATINGS INC 1431 PROGRESS AVE HIGH POINT NC 27260 0.125 Screened Out

AKZO NOBEL COATINGS INC 1313 WINDSOR AVE COLUMBUS OH 43211 1.416 Screened Out

AKZO NOBEL PAINTS PUERTO RICO LLC 65TH INFANTRY AVE KM. 13.4 CAROLINA PR 00985 0.081845 Screened Out

AKZO NOBEL SURFACE CHEMISTRY LLC 15200 ALMEDA RD HOUSTON TX 77053 0.174 Screened Out

AKZONOBEL 1872 HWY 9 BYPASS W LANCASTER SC 29720 2.6435 Screened Out

AKZONOBEL AEROSPACE COATINGS 1 E WATER ST WAUKEGAN IL 60085 0.984 Screened Out

AKZONOBEL COATINGS INC 120 FRANKLIN RD PONTIAC MI 48341 0.0605 Screened Out

ALCOA COMMERCIAL WINDOWS LLC (DBA 

TRACO)

71 PROGRESS AVE CRANBERRY TOWNSH PA 16066 0.7965 Screened Out

ALERIS ROLLED PRODUCTS INC 1 REYNOLDS RD ASHVILLE OH 43103 0.379 Screened Out

ALERIS ROLLED PRODUCTS INC 3321 DURHAM RD ROXBORO NC 27573 0.482 Screened Out

ALERIS ROLLED PRODUCTS INC 1372 KY HWY 1957 LEWISPORT KY 42351 2.696 Screened Out

AMERICAN COLOR GRAPHICS 810 E S ST MARENGO IA 52301 2.1595 Screened Out

AMERICAN COLOR GRAPHICS - LUFKIN 3001 ATKINSON DR LUFKIN TX 75901 1.7455 Screened Out

AMERICAN JETWAY CORP 34136 MYRTLE WAYNE MI 48184 0.125 Screened Out

AMERICAN METALS CORP 1000 CROCKER RD WESTLAKE OH 44145 0.391 Screened Out

AMERIMAX COATED PRODUCTS 215 PHILLIPS 324 RD HELENA AR 72342 0.154 Screened Out

AMPHENOL APC INC 91 NORTHEASTERN BLVD NASHUA NH 03062 0.1182165 Screened Out

AMREP INC 990 INDUSTRIAL PARK DR MARIETTA GA 30062 0.244 Screened Out

ANCHOR PAINT MANUFACTURING CO INC 6707 E 14TH ST TULSA OK 74112 0.1155 Screened Out

ANDERSON DEVELOPMENT CO 1415 E MICHIGAN ST ADRIAN MI 49221 0.005 Screened Out

ARANDELL CORP N82 W13118 LEON RD MENOMONEE FALLS WI 53051 1.355 Screened Out

ARCADIA INC 3225 E WASHINGTON BLVD VERNON CA 90058 0.25 Screened Out

ARCH CHEMICALS INC HWY 933 BRANDENBURG KY 40108 0.124 Screened Out

ARDAGH METAL PACKAGING USA INC 3030 BIRCH DR HALF MOON 

INDUSTRIAL PARK

WEIRTON WV 26062 0.4445 Screened Out

ARDAGH METAL PACKAGING USA INC 936 BARRACUDA ST TERMINAL ISLAND CA 90731 4.175 Screened Out

ARDEX LABORATORIES INC 2050 BYBERRY RD PHILADELPHIA PA 19116 0.1365 Screened Out

ARKEMA COATING RESINS 340 RAILROAD ST SAUKVILLE WI 53080 0.9005 Screened Out

ARKEMA COATINGS & RESINS 13511 MAIN ST LEMONT IL 60439 0.03 Screened Out

ARKEMA INC 1415 STEELE AVE SW GRAND RAPIDS MI 49507 0.5 Screened Out

ARMSTRONG HARDWOOD FLOORING CO 565 HARTCO DR ONEIDA TN 37841 4.7345 Screened Out

ARMSTRONG WORLD INDUSTRIES INC 4115 N PERKINS RD STILLWATER OK 74075 1.4105 Screened Out

ARR-MAZ CUSTOM CHEMICALS 4800 STATE RD 60 E MULBERRY FL 33860 2.9015 Screened Out

ARROW SHED LLC 1 THIRD AVE HASKELL NJ 07420 0.1685 Screened Out

ARVINMERITOR HEAVY VEHICLE SYSTEMS 

LLC

801 RAILROAD AVE YORK SC 29745 4.894 Screened Out

ASTRO CHEMICALS INC 126 MEMORIAL DR SPRINGFIELD MA 01104 0.002 Screened Out

ASTRO COATINGS INC 27 MAIN ST STRUTHERS OH 44471 2.651 Screened Out

ATHEA LABORATORIES INC 7855 N FAULKNER RD MILWAUKEE WI 53224 0.08166 Screened Out

ATMI MATERIALS LTD 706 HOUSTON CLINTON DR BURNET TX 78611 0.05139 Screened Out

ATOTECH USA 1750 OVERVIEW DR ROCK HILL SC 29730 0.0025 Screened Out

AUTOALLIANCE INTERNATIONAL INC 1 INTERNATIONAL DR FLAT ROCK MI 48134 4.85 Screened Out

AUTOMOTIVE COMPONENTS HOLDINGS LLC 

SALINE PLANT

7700 MICHIGAN AVE SALINE MI 48176 3.56 Screened Out

AVANTOR PERFORMANCE MATERIALS 600 N BROAD ST PHILLIPSBURG NJ 08865 0.003 Screened Out

AVERY DENNISON 17700 FOLTZ INDUSTRIAL PKWY STRONGSVILLE OH 44149 3.246 Screened Out

AVON AUTOMOTIVE PLANT 1 603 W 7TH ST CADILLAC MI 49601 0.125 Screened Out

AVX CORP MYRTLE BEACH 801 17TH AVE S MYRTLE BEACH SC 29577 2.6925 Screened Out

BACHMAN SERVICES INC 2220 S PROSPECT OKLAHOMA CITY OK 73129 0.25 Screened Out

BAKER PETROLITE BAYPORT FACILI TY 13200 BAYPARK RD PASADENA TX 77507 0.0001595 Screened Out

BAKER PETROLITE CORP 16950 WALLISVILLE RD HOUSTON TX 77049 0.000219 Screened Out

BAKER PETROLITE CORP 9100 W 21ST ST SAND SPRINGS OK 74063 0.01482 Screened Out

BAKER PETROLITE KILGORE BLEND PLANT 806 PALUXY ST KILGORE TX 75662 0.0002725 Screened Out

BAKER PETROLITE-RAYNE FACILITY 135 INDUSTRIAL DR RAYNE LA 70578 0.0005 Screened Out

BALL AEROSOL & SPECIALTY CONTAINER 

INC

1717 GIFFORD RD ELGIN IL 60120 1.838 Screened Out

BALL METAL FOOD CONTAINER CORP 1200 S CRUTCHER ST SPRINGDALE AR 72764 2.13 Screened Out

BALL METAL FOOD CONTAINER CORP 300 W GREGER RD OAKDALE CA 95361 3.552 Screened Out

BARTON SOLVENTS INC BETTENDORF 204 36TH ST BETTENDORF IA 52722 0.049 Screened Out

BARTON SOLVENTS INC COUNCIL BLUFFS 2135 9TH AVE COUNCIL BLUFFS IA 51502 0.023 Screened Out

BARTON SOLVENTS INC DES MOINES 1970 NE BROADWAY DES MOINES IA 50313 0.0355 Screened Out

BARTON SOLVENTS INC KANSAS CITY 901 S 66TH TERRACE KANSAS CITY KS 66111 0.035 Screened Out

BARTON SOLVENTS INC WEST BEND 800 RAIL WAY WEST BEND WI 53095 0.0265 Screened Out

BARTON SOLVENTS INC WICHITA 201 S CEDAR VALLEY CENTER KS 67147 0.0195 Screened Out

BASF CORP 100 INDUSTRIAL BLVD SEAFORD DE 19973 0.0025 Screened Out

BASF CORP 1609 BIDDLE AVE WYANDOTTE MI 48192 0.005 Screened Out

Page 6 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

BASF CORP 361 SHEEP PASTURE RD EAST SETAUKET NY 11733 0.008 Screened Out

BASF CORP 3455 SOUTHPORT RD SPARTANBURG SC 29302 0.1275 Screened Out

BASF CORP 1175 MARTIN ST GREENVILLE OH 45331 0.22 Screened Out

BATESVILLE MANUFACTURING INC 310 CROWN RD BATESVILLE MS 38606 3.796 Screened Out

BAYOU COS INC 5200 CURTIS LN NEW IBERIA LA 70560 1.5 Screened Out

BECKER SPECIALTY CORP 15310 ARROW BLVD FONTANA CA 92335 0.25 Screened Out

BEHR PROCESS CORP - CHICAGO 270 STATE ST CHICAGO HEIGHTS IL 60411 0.3259 Screened Out

BEHR PROCESS CORP ATLANTA 130 DECLARATION DR MC DONOUGH GA 30253 0.30055 Screened Out

BENCHMARK ENERGY PRODUCTS LLC 4113 W INDUSTRIAL AVE MIDLAND TX 79703 3.7855 Screened Out

BENJAMIN MOORE & CO - DALLAS 700 W KEARNEY MESQUITE TX 75149 0.001327 Screened Out

BENJAMIN MOORE & CO - NEWARK 134 LISTER AVE NEWARK NJ 07105 0.00135 Screened Out

BENJAMIN MOORE & CO JOHNSTOWN UNION AVE EXTENSION JOHNSTOWN NY 12095 0.0188675 Screened Out

BENJAMIN MOORE & CO PELL CITY 109 BAMBERG DR PELL CITY AL 35125 0.10425 Screened Out

BERENFIELD CONTAINERS INC 31 RAILROAD ST CLARENDON PA 16313 4.429515 Screened Out

BERGQUIST CO 301 WASHINGTON ST W CANNON FALLS MN 55009 0.249 Screened Out

BERRIDGE MANUFACTURING CO 6515 FRATT RD SAN ANTONIO TX 78218 0.0085 Screened Out

BERRYMAN PRODUCTS INC 3800 E RANDOL MILL RD ARLINGTON TX 76011 0.125 Screened Out

BETCO CORP 1001 BROWN AVE TOLEDO OH 43607 3.69 Screened Out

BF GOODRICH TIRE MANUFACTURING 18906 US 24 E WOODBURN IN 46797 0.005 Screened Out

BIOLAB INC 1735 DOGWOOD DR CONYERS GA 30012 0.03915 Screened Out

BJ CHEMICAL SERVICES 707 N LEECH HOBBS NM 88240 0.011905 Screened Out

BLENTECH CORP 1305 RYE ST HOUSTON TX 77029 0.0225 Screened Out

BOEHRINGER INGELHEIM CHEMICALS INC 2820 N NORMANDY DR PETERSBURG VA 23805 0.0035 Screened Out

BOEING COMMERCIAL AIRPLANE GROUP - 

RENTON

737 LOGAN AVE N RENTON WA 98055 0.577 Screened Out

BOEING COMMERCIAL AIRPLANE GROUP 

NORTH BOEING FIELD (PART)

7500 E MARGINAL WAY S SEATTLE WA 98108 0.1425 Screened Out

BOEING COMMERCIAL AIRPLANE GROUP 

PLANT 2 (PART)

7755 E MARGINAL WAY S SEATTLE WA 98108 0.0305 Screened Out

BON L MANUFACTURING CO HWY 53 BONNELL RD CARTHAGE TN 37030 1.873 Screened Out

BP PRODUCTS NORTH AMERICA WHITING 2815 INDIANAPOLIS BLVD WHITING IN 46394 0.0005 Screened Out

BRADLEY COATINGS GROUP 608 W CRAWFORD AVE CONNELLSVILLE PA 15425 0.364595 Screened Out

BRAIN POWER INC 4470 SW 74TH AVE MIAMI FL 33155 0.005 Screened Out

BRAINERD CHEMICAL CO INC 1200 N PEORIA TULSA OK 74147 0.0025 Screened Out

BRENNTAG GREAT LAKES LLC 14765 W BOBOLINK AVE MENOMONEE FALLS WI 53051 0.1275 Screened Out

BRENNTAG NORTHEAST INC 81 W HULLER LN READING PA 19605 0.0349 Screened Out

BRENNTAG PACIFIC INC 10747 PATTERSON PL SANTA FE SPRINGS CA 90670 0.0425 Screened Out

BRENNTAG SOUTHEAST INC 11750 FRUEHAUF DR CHARLOTTE NC 28273 0.0025 Screened Out

BRENNTAG SOUTHEAST INC 2000 E PETTIGREW ST DURHAM NC 27703 0.046 Screened Out

BRENNTAG SOUTHWEST INC LANC ASTER 704 E WINTERGREEN RD LANCASTER TX 75134 0.0475 Screened Out

BRENNTAG SOUTHWEST INC LONG VIEW 610 FISHER RD LONGVIEW TX 75604 0.026 Screened Out

BRENNTAG SOUTHWEST INC SAND 

SPRINGS

206 E MORROW RD SAND SPRINGS OK 74063 0.0375 Screened Out

BRIGHTSMITH LLC 120 ENTERPRISE AVE MORRISVILLE PA 19067 1.317 Screened Out

BRILLION IRON WORKS INC 200 PARK AVE BRILLION WI 54110 2.93465 Screened Out

BROWN PRINTING CO 668 GRAVEL PIKE EAST GREENVILLE PA 18041 3.38 Screened Out

BRULIN CORP 2920 DR ANDREW J BROWN AVE INDIANAPOLIS IN 46205 0.006137 Screened Out

BRUNSWICK CORP MERCURY MARINE DIV W6250 PIONEER RD FOND DU LAC WI 54935 1.27 Screened Out

BUCKEYE INTERNATIONAL INC 2700 WAGNER PL MARYLAND HEIGHTS MO 63043 1.7395 Screened Out

BUCKLEY OIL CO 1809 ROCK ISLAND ST DALLAS TX 75207 0.009 Screened Out

BUCKMAN LABORATORIES INC 1256 N MCLEAN BLVD MEMPHIS TN 38108 0.0015 Screened Out

BUZZI UNICEM USA - GREENCASTLE PLANT 3301 S COUNTY RD 150 W GREENCASTLE IN 46135 0.119 Screened Out

BWAY CORP 1202 AIRPORT RD NORTH BRUNSWICK NJ 08902 2.096 Screened Out

BWAY CORP BWAY PACKAGING DIV 8200 BROADWELL RD CINCINNATI OH 45244 1.61336 Screened Out

B-WAY PACKAGING INC 6 LITHO RD TRENTON NJ 08648 0.631 Screened Out

BYK USA INC 524 S CHERRY ST WALLINGFORD CT 06492 0.154 Screened Out

C P INC 196 S WATER CONNERSVILLE IN 47331 0.005 Screened Out

CADON PLATING CO 3715 11TH ST WYANDOTTE MI 48192 3.118 Screened Out

CALLAHAN CHEMICAL CO 18 INDUSTRIAL RD WALPOLE MA 02081 0.002 Screened Out

CALLAHAN CHEMICAL CO 200 INDUSTRIAL AVE RIDGEFIELD PARK NJ 07660 0.0055 Screened Out

CAMACO COLUMBUS MANUFACTURING 1851 E 32ND AVE COLUMBUS NE 68601 1.94 Screened Out

CANBERRA CORP 3610 N HOLLAND-SYLVANIA RD TOLEDO OH 43615 1.125 Screened Out

CANFIELD METAL COATING CORP 460 W MAIN ST CANFIELD OH 44406 2 Screened Out

CAR PRODUCTS INC 630 BEAULIEU ST HOLYOKE MA 01040 0.196 Screened Out

CARBOLINE CO 900 OPELOUSAS ST LAKE CHARLES LA 70601 0.0095 Screened Out

CARDINAL ALUMINUM CO PLAN T 3 4005 OAKLAWN DR LOUISVILLE KY 40219 1.4025 Screened Out

CARDONE INDUSTRIES 5660 RISING SUN AVE PHILADELPHIA PA 19120 4.65 Screened Out

CARESTREAM HEALTH COLORADO 2000 HOWARD SMITH AVE W C42 WINDSOR CO 80550 0.0015 Screened Out

CAROLINA SOLVENTS INC 2274 1ST ST SE HICKORY NC 28602 0.0945 Screened Out

CARRY-ON TRAILER CORP 159 INDUSTRIAL PARK RD MONTROSS VA 22520 3.925 Screened Out

CATALYST OILFIELD SERVICES LLC 11999 E HWY 158 GARDENDALE TX 79758 1.35 Screened Out

CATERPILLAR INC 3701 STATE RD 26 E LAFAYETTE IN 47905 1.975 Screened Out

CCI MANUFACTURING IL CORP 15550 CANAL BANK RD LEMONT IL 60439 0.115 Screened Out

CCL CONTAINER AEROSOL DIV ONE LLODIO DR HERMITAGE PA 16148 2.4165 Screened Out

CCP COMPOSITES US 2434 HOLMES RD HOUSTON TX 77051 0.8026 Screened Out

CE BRADLEY LABORATORIES INC 55 BENNETT DR BRATTLEBORO VT 05301 0.0845 Screened Out

Page 7 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

CELLO PROFESSIONAL PRODUCTS 1354 OLD POST RD HAVRE DE GRACE MD 21078 0.344 Screened Out

CENTRIA 500 PERTH DR NEW ECONOMY 

BUSINESS PARK

AMBRIDGE PA 15003 0.559 Screened Out

CENTRIA 530 N SECOND ST CAMBRIDGE OH 43725 2.746 Screened Out

CENTURY INDUSTRIAL COATINGS I NC HWY 69 S JACKSONVILLE TX 75766 1.696 Screened Out

CERAM TRAZ CORP CERAMIC INDL 

COATINGS

325 HWY 81 OSSEO MN 55369 0.25 Screened Out

CERTIFIED ENAMELING INC 3342 EMERY ST LOS ANGELES CA 90023 0.179 Screened Out

CHAMPION TECHNOLOGIES INC 710 MARVIN A SMITH BLVD LONGVIEW TX 75662 0.0365 Screened Out

CHAMPION TECHNOLOGIES INC 1816 S JACKSON ST MAGNOLIA AR 71753 0.04205 Screened Out

CHAMPION TECHNOLOGIES INC 3130 FM 521 FRESNO TX 77545 0.043 Screened Out

CHAMPION TECHNOLOGIES INC 115 PROCTOR ODESSA TX 79762 0.293 Screened Out

CHASE PRODUCTS CO 2727 GARDNER RD BROADVIEW IL 60155 0.111 Screened Out

CHEMCOAT INC 2790 CANFIELDS LN MONTOURSVILLE PA 17754 0.0025 Screened Out

CHEMETALL US INC 1610 CLARA ST JACKSON MI 49203 0.0001654 Screened Out

CHEMETALL US INC 13177 HURON RIVER DR ROMULUS MI 48174 0.125 Screened Out

CHEMGUARD INC 204 S 6TH AVE MANSFIELD TX 76063 0.337 Screened Out

CHEMICAL SOLVENTS INC--DENISON 

FACILITY

1010 OLD DENISON AVE CLEVELAND OH 44109 0.0025 Screened Out

CHEMICAL SOLVENTS JENNINGS ROAD 

FACILITY

3751 JENNINGS RD CLEVELAND OH 44109 0.25 Screened Out

CHEMICAL SPECIALISTS & DEVELOPMENT 

INC

9733 MEADOR RD CONROE TX 77303 0.5 Screened Out

CHEMOL CO INC 2300 RANDOLPH AVE GREENSBORO NC 27406 0.00812 Screened Out

CHEMTEX LABORATORIES INC 2725 ARMENTROUT DR CONCORD NC 28025 0.0055 Screened Out

CHROMASOURCE INC 2433 S CR 600 E COLUMBIA CITY IN 46725 1.453 Screened Out

CHRYSLER GROUP LLC STERLING 

STAMPING PLANT (PART)

35777 VAN DYKE STERLING HEIGHTS MI 48312 0.7 Screened Out

CHRYSLER STERLING HEIGHTS ASSEMBLY 

PLANT (PART)

38111 VAN DYKE STERLING HEIGHTS MI 48312 4.34 Screened Out

CLARIANT CORP CLEAR LAKE PLANT 9502 BAYPORT BLVD - ETOX UNIT PASADENA TX 77507 0.0031 Screened Out

CLARIANT CORP MARTIN PLANT 788 CHERT QUARRY RD MARTIN SC 29836 0.1275 Screened Out

CLEAN HARBORS ENVIRONMENTAL 

SERVICES INC

2247 S HWY 71 KIMBALL NE 69145 0.0075 Screened Out

CLEAN HARBORS LONE MOUNTAIN LLC 

LONE MOUNTAIN FACILITY

5 MILES E & 1 MILE N OF JUNCTION 

US HWYS 412 & 281

WAYNOKA OK 73860 0.00165 Screened Out

CLEANING SYSTEMS INC 1997 AMERICAN BLVD DE PERE WI 54115 0.1275 Screened Out

CLEAR LAKE CHEMICALS LLC 11200 BAY AREA BLVD PASADENA TX 77507 3.03655 Screened Out

CLEARWATER INTERNATIONAL LLC 100 INDUSTRIAL DR (BLDG 180, 

150, & 76)

LEETSDALE PA 15056 0.006085 Screened Out

CLEVELAND STEEL CONTAINER - KILGORE 5005 ELDER LAKE RD KILGORE TX 75662 0.0545 Screened Out

CLEVELAND STEEL CONTAINER - NI LES 115 ERIE ST NILES OH 44446 2.9905 Screened Out

CLEVELAND STEEL CONTAINER - PE OTONE 

FACILITY

117 E LINCOLN ST PEOTONE IL 60468 0.518 Screened Out

CLEVELAND STEEL CONTAINER CORP 350 MILL ST QUAKERTOWN PA 18951 4.075 Screened Out

CLEVELAND STEEL CONTAINER CORP - 

STREETSBORO PLANT

10048 AURORA-HUDSON RD STREETSBORO OH 44241 2.7175 Screened Out

CLOROX PRODUCTS MANUFACTURING CO 17 LAKE MIRROR RD FOREST PARK GA 30297 0.005 Screened Out

CLOROX PRODUCTS MANUFACTURING CO 2600 HUNTINGTON DR FAIRFIELD CA 94533 0.059 Screened Out

COASTAL CHEMICAL CO LLC 3520 VETERANS MEMORIAL BLVD ABBEVILLE LA 70510 0.1275 Screened Out

COLOR CORP OF AMERICA 1630 W HILL ST LOUISVILLE KY 40210 2.2275 Screened Out

COLUMBIA PAINT CORP 641 JACKSON AVE HUNTINGTON WV 25704 0.125 Screened Out

COLWELL INC 231 S PROGRESS DR E KENDALLVILLE IN 46755 0.268 Screened Out

COMMERCIAL MERCHANDISING CORP 1337 J WOOD BRANCH DR CHARLOTTE NC 28273 0.64 Screened Out

COMPLEMENTARY COATINGS CORP 4701 O'DONNELL ST BALTIMORE MD 21224 0.9215 Screened Out

COMPLEX CHEMICALS CO INC MADISON PARISH INDUSTRIAL 

PARK 177 COMPLEX CHEMICAL RD

TALLULAH LA 71282 0.5 Screened Out

CONOCOCPHILLIPS CO WICHITA TERMINAL 2400 E 37TH ST N WICHITA KS 67219 0.00648 Screened Out

CONOCOPHILLIPS CO EAST ST LOUIS 

TERMINAL

3300 MISSISSIPPI AVE CAHOKIA IL 62206 0.036 Screened Out

CONOCOPHILLIPS MT VERNON PRODUCTS 

TERMINAL

15138 HWY 96 MOUNT VERNON MO 65712 0.003 Screened Out

CONOCOPHILLIPS OKLAHOMA CITY 

PRODUCTS TERMINAL

4700 NE 10TH ST OKLAHOMA CITY OK 73117 0.05 Screened Out

CONOCOPHILLIPS PONCA CITY REFINERY 1000 S PINE ST PONCA CITY OK 74602 0.052 Screened Out

CONSOLIDATED SYSTEMS INC 650 ROSEWOOD DR COLUMBIA SC 29201 2.0475 Screened Out

CONTINENTAL CEMENT CO LLC 10107 HWY 79 HANNIBAL MO 63401 0.1275 Screened Out

COORSTEK 2449 RIVERSIDE PKWY GRAND JUNCTION CO 81505 4.8425 Screened Out

CORSICANA TECHNOLOGIES INC 2733 E HWY 31 CORSICANA TX 75109 0.0465 Screened Out

COSMETIC LABORATORIES OF AMERICA 20245 SUNBURST ST CHATSWORTH CA 91311 0.002 Screened Out

CP CONVERTERS INC 15 GRUMBACHER RD YORK PA 17402 1.01857 Screened Out

CPJ TECHNOLOGIES 200 TANNER DR TAYLORS SC 29687 0.108 Screened Out

CR BRANDS INC 230 OLD CONVERSE RD SPARTANBURG SC 29307 0.0025 Screened Out

Page 8 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

CR BRANDS INC 141 VENTURE BLVD SPARTANBURG SC 29306 0.005 Screened Out

CREE INC 4600 SILICON DR DURHAM NC 27703 0.125 Screened Out

CRODA INC 315 CHERRY LN NEW CASTLE DE 19720 0.001145 Screened Out

CROWN AEROSOL PACKAGING 4TH ST & PARK AVE FARIBAULT MN 55021 4.089 Screened Out

CROWN CORK & SEAL CO (USA) INC CROWN 

CLOSURES DIV

940 MILL PARK DR LANCASTER OH 43130 1.1105 Screened Out

CROWN FOOD PACKAGING 10200 N LOMBARD ST PORTLAND OR 97203 2.759 Screened Out

CRYSTAL FINISHING SYSTEMS INC 2608 ROSS AVE SCHOFIELD WI 54476 1.5361434 Screened Out

CUMMINS POWER GENERATION 1400 73RD AVE NE FRIDLEY MN 55432 2.4 Screened Out

CURTIS METAL FINISHING CO 9917 N ALPINE MACHESNEY PARK IL 61115 0.831 Screened Out

CUSTOM CHEMICAL FORMULATORS INC 8707 MILLERGROVE DR SANTA FE SPRINGS CA 90670 0.005 Screened Out

CUSTOM SYNTHESIS LLC 1704 DENVER RD ANDERSON SC 29625 0.0495 Screened Out

CYTEC INDUSTRIES INC LANGLEY PLANT 403 CARLINE RD LANGLEY SC 29834 0.129 Screened Out

DANLIN INDUSTRIES CORP 23737 HWY 47 THOMAS OK 73669 0.125 Screened Out

DAUBERT CHEMICAL CO 4700 S CENTRAL AVE CHICAGO IL 60638 0.033205 Screened Out

DAVIES IMPERIAL COATINGS INC 1275 STATE ST HAMMOND IN 46320 0.013 Screened Out

DAVIS-FROST INC 3420 CANDLER'S MOUNTAIN RD LYNCHBURG VA 24506 0.221 Screened Out

DECOSTAR INDUSTRIES INC 1 DECOMA DR CARROLLTON GA 30117 1.435 Screened Out

DELEET MERCHANDISING 26 BLANCHARD ST NEWARK NJ 07105 0.25 Screened Out

DELTA LABORATORIES INC 3710 W COUNTY RD 326 OCALA FL 34475 0.107 Screened Out

DENSO MANUFACTURING TENNESSEE INC 1720, 1725, 1755 ROBERT C 

JACKSON DR

MARYVILLE TN 37801 1.489 Screened Out

DERRICK CORP 3350 UNION RD CHEEKTOWAGA NY 14225 2.1335 Screened Out

DIAMOND VOGEL PAINTS 5111 E 36TH ST N TULSA OK 74115 0.6715 Screened Out

DIC IMAGING PRODUCTS USA LLC 7335 S 10TH ST OAK CREEK WI 53154 0.046 Screened Out

DIVERSEY INC 316 HART ST WATERTOWN WI 53094 0.00012 Screened Out

DIVERSEY INC - WAXDALE FACILITY 8311 16TH ST STURTEVANT WI 53177 0.005535 Screened Out

DIVERSIFIED COATING SYSTEMS INC 309 ECHELON RD GREENVILLE SC 29605 0.387 Screened Out

DOW CHEMICAL CO FREEPORT FACILITY 2301 N BRAZOSPORT BLVD FREEPORT TX 77541 0.015 Screened Out

DPIX LLC 1635 AEROPLAZA DR COLORADO SPRINGS CO 80916 0.649 Screened Out

DSM DESOTECH INC 1101 HWY 27 S STANLEY NC 28164 0.0112 Screened Out

DUCKBACK PRODUCTS 2644 HEGAN LN CHICO CA 95928 0.4186 Screened Out

DUPONT CHAMBERS WORKS RT 130 DEEPWATER NJ 08023 0.1615 Screened Out

DUPONT EKC TECHNOLOGY 2520 BARRINGTON CT HAYWARD CA 94545 0.0025 Screened Out

DUPONT FORT MADISON PLANT 801 - 35TH ST FORT MADISON IA 52627 0.357 Screened Out

DUPONT FRONT ROYAL PLANT 7961 WINCHESTER RD FRONT ROYAL VA 22630 0.011 Screened Out

DUPONT MOUNT CLEMENS PLANT 400 GROESBECK HWY MOUNT CLEMENS MI 48043 0.575 Screened Out

DUPONT PARLIN PLANT CHEESEQUAKE RD PARLIN NJ 08859 0.0155 Screened Out

DUPONT PONTCHARTRAIN WORKS 586 HWY 44 LA PLACE LA 70068 0.0075 Screened Out

DUPONT TOWANDA PLANT 192 PATTERSON BLVD TOWANDA PA 18848 2.2885 Screened Out

DUPONT YERKES PLANT 3115 RIVER RD BUFFALO NY 14207 1.8625 Screened Out

DURA COAT PRODUCTS INC 26655 PEOPLES RD MADISON AL 35756 2.03725 Screened Out

DYNASOL INC 330 PINE ST CANTON MA 02021 0.00145 Screened Out

DYSTAR LP 209 WATLINGTON INDUSTRIAL DR REIDSVILLE NC 27320 0.05 Screened Out

EASTMAN CHEMICAL CO TENNESSEE 

OPERATIONS

100 EASTMAN RD KINGSPORT TN 37662 1.408 Screened Out

EASTMAN KODAK CO EASTMAN BUSINESS 

PARK

1669 LAKE AVE ROCHESTER NY 14652 0.0035 Screened Out

ECOLAB INC 2305 SHERWIN ST GARLAND TX 75041 0.0205 Screened Out

ECOLAB INC 3001 CHANNAHON RD JOLIET IL 60436 0.0505 Screened Out

ECOLAB INC 18383 E RAILROAD ST CITY OF INDUSTRY CA 91748 0.055 Screened Out

ECOLAB INC 942 BAKER RD MARTINSBURG WV 25405 0.056 Screened Out

ECP INC WOODRIDGE 11210 KATHERINE'S CROSSING 

SUITE 100

WOODRIDGE IL 60517 0.0025 Screened Out

EDCO PRODUCTS INC 8700 EXCELSIOR BLVD HOPKINS MN 55343 0.0045 Screened Out

EFCO CORP 1000 COUNTY RD MONETT MO 65708 1.696 Screened Out

ELECTRONICS FOR IMAGING INC 1260 JAMES L HART PKWY YPSILANTI MI 48197 0.0485 Screened Out

ELEMENTIS SPECIALTIES 400 CLAREMONT AVE JERSEY CITY NJ 07304 0.184 Screened Out

ELPACO COATINGS CORP 1378 KINGSLAND AVE PAGEDALE MO 63133 0.2585 Screened Out

EMERALD SERVICES INC 1825 E ALEXANDER AVE TACOMA WA 98421 0.00001 Screened Out

ENDICOTT INTERCONNECT TECHNOLOGIES 

INC

1093 CLARK ST ENDICOTT NY 13760 4.3655 Screened Out

ENERGIZER BATTERY MANUFACTURING INC 75 SWANTON RD SAINT ALBANS VT 05478 0.162 Screened Out

ENGINEERED POLYMER SOLUTIONS I NC 

D/B/A VALSPAR COATINGS

90 CARSON RD BIRMINGHAM AL 35215 0.5385 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 5501 E SLAUSON AVE CITY OF COMMERCE CA 90040 0.0015 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

(DBA VALSPAR COATINGS)

1717 W ENGLISH RD HIGH POINT NC 27261 0.189 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

2000 WESTHALL ST PITTSBURGH PA 15233 0.0405 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

901 W UNION ST MONTEBELLO CA 90640 0.044 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

3050 HANFORD DR LEBANON PA 17046 0.1225 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

1991 S WHEELING RD WHEELING IL 60090 0.156 Screened Out

Page 9 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

411 N DARLING FREMONT MI 49412 0.3295 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

347 CENTRAL AVE BOWLING GREEN KY 42101 0.37 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

5400 23RD AVE MOLINE IL 61265 0.5755 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

701 SHILOH RD GARLAND TX 75042 1.178 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

372 CLEVELAND ST ROCHESTER PA 15074 1.3135 Screened Out

ENGINEERED POLYMER SOLUTIONS INC 

D/B/A VALSPAR COATINGS

901 N GREENWOOD AVE KANKAKEE IL 60901 1.8015 Screened Out

ENGLERT INC 1200 AMBOY AVE PERTH AMBOY NJ 08861 0.442 Screened Out

ENTHONE INC 350 FRONTAGE RD WEST HAVEN CT 06516 0.144915 Screened Out

ENTHONE INC 9809 INDUSTRIAL DR BRIDGEVIEW IL 60455 0.16206 Screened Out

EQ DETROIT INC 1923 FREDERICK DETROIT MI 48211 1.778 Screened Out

EQUILON CARSON TERMINAL 20945 S WILMINGTON AVE CARSON CA 90810 0.25 Screened Out

ETHOX CHEMICALS LLC 1801 PERIMETER RD GREENVILLE SC 29605 0.009 Screened Out

EURAMAX INTERNATIONAL INC 450 RICHARDSON DR LANCASTER PA 17603 0.381 Screened Out

EVONIK DEGUSSA CORP 4201 DEGUSSA RD THEODORE AL 36582 0.0045 Screened Out

EVONIK DEGUSSA CORP TIPPECANOE 

LABORATORIES

1650 LILLY RD LAFAYETTE IN 47909 0.331 Screened Out

EXXONMOBIL CHEMICAL BATON ROUGE 

CHEMICAL PLANT

4999 SCENIC HWY BATON ROUGE LA 70805 0.032 Screened Out

EXXONMOBIL OIL CORP - TORRANCE 

REFINERY

3700 W 190TH ST TORRANCE CA 90509 0.02 Screened Out

EXXONMOBIL REFINING & SUPPLY BATON 

ROUGE REFINERY

4045 SCENIC HWY BATON ROUGE LA 70805 0.0565 Screened Out

FERRO CORP 251 W WYLIE AVE WASHINGTON PA 15301 0.5 Screened Out

FERRO CORP WALTON HILLS OPERATIONS 7050 KRICK RD WALTON HILLS OH 44146 0.004 Screened Out

FIBERMARK NORTH AMERICA INC 5492 BOSTWICK ST LOWVILLE NY 13367 4.4445 Screened Out

FINGER LAKES CHEMICAL INC 418-424 ST PAUL ST ROCHESTER NY 14605 0.0025 Screened Out

FINISHES UNLIMITED INC 482 WHEELER RD SUGAR GROVE IL 60554 0.891 Screened Out

FIRST AMERICAN RESOURCES CO 2030 RIVERVIEW INDUSTRIAL DR MABLETON GA 30126 0.195 Screened Out

FISHER SCIENTIFIC INTERNATIONAL MTN 

DIAGNOSTICS PLANT

8365 VALLEY PIKE MIDDLETOWN VA 22645 0.0025 Screened Out

FIVE STAR COATINGS GROUP 36616 89TH ST TWIN LAKES WI 53181 1.4 Screened Out

FLINT GROUP NORTH AMERICA CORP 2675 HENKLE DR LEBANON OH 45036 0.608 Screened Out

FLINT HILLS RESOURCES CORPUS CHRISTI 

LLC - WEST PLANT

2825 SUNTIDE RD CORPUS CHRISTI TX 78409 0.1435 Screened Out

FORD MOTOR CO - OHIO ASSEMBLY PLANT 650 MILLER RD AVON LAKE OH 44012 3.395 Screened Out

FORD MOTOR CO CHICAGO ASSEMBLY 12600 S TORRENCE AVE CHICAGO IL 60633 0.615 Screened Out

FORD MOTOR CO DEARBORN DIVERSIFIED 

MANUFACTURING

3001 MILLER RD DEARBORN MI 48121 0.002 Screened Out

FORD MOTOR CO DEARBORN TOOL & DIE 

PLANT

3001 MILLER RD DEARBORN MI 48121 0.007 Screened Out

FORMULA CORP 4432 C ST NE AUBURN WA 98002 0.125 Screened Out

FORREST PAINT CO 1011 MCKINLEY ST EUGENE OR 97402 0.445 Screened Out

FRANKLIN INTERNATIONAL 2020 BRUCK ST COLUMBUS OH 43207 0.0575 Screened Out

FRAZEE INDUSTRIES 6625 MIRAMAR RD SAN DIEGO CA 92121 0.1517 Screened Out

FUCHS LUBRICANTS CO-CORPORATE 

OFFICE

17050 S LATHROP AVE HARVEY IL 60426 0.329 Screened Out

FUJIFILM HUNT CHEMICALS USA INC 900 CARNEGIE ST ROLLING MEADOWS IL 60008 0.00112 Screened Out

FUJIFILM MANUFACTURING USA INC 211 PUCKETTS FERRY RD GREENWOOD SC 29649 1.56 Screened Out

FUJIFILM NORTH AMERICA CORP 20 W 14TH AVE NORTH KANSAS CITY MO 64116 1.677 Screened Out

FULLER BRUSH CO ONE FULLER WAY GREAT BEND KS 67530 0.373 Screened Out

GACO WESTERN 1245 CHAPMAN DR WAUKESHA WI 53186 0.0085 Screened Out

GAGE PRODUCTS CO 625 WANDA AVE FERNDALE MI 48220 0.125 Screened Out

GALATA CHEMICALS LLC - GALATA TAFT 

FACILITY

471 HWY 3142 HAHNVILLE LA 70057 0.1935 Screened Out

GATES CORP 1650 ROWE PKWY POPLAR BLUFF MO 63901 0.001 Screened Out

GATES CORP 1450 MONTANA RD IOLA KS 66749 0.00295 Screened Out

GATES CORP - CHARLESTON 1300 S PLANT RD CHARLESTON MO 63834 0.00555 Screened Out

GE WATER & PROCESS TECHNOLOGIES 333 S LOMBARD RD ADDISON IL 60101 0.005 Screened Out

GE WATER & PROCESS TECHNOLOGIES 2118 REISER AVE SE NEW PHILADELPHIA OH 44663 0.005 Screened Out

GE WATER & PROCESS TECHNOLOGIES 

ORANGE FACILITY

3901 WILLIAMS DR ORANGE TX 77630 0.1275 Screened Out

GEMINI COATINGS INC 2300 HOLLOWAY DR EL RENO OK 73036 0.2215 Screened Out

GENERAL DYNAMICS ORDNANCE & 

TACTICAL SYSTEMS GARLAND

1200 N GLENBROOK GARLAND TX 75040 0.001995 Screened Out

GENERAL MOTORS GM VA DETROITHAMTRAMCK ASSEMBLY CENTER2500 E GENERAL MOTORS BLVD DETROIT MI 48211 1.06 Screened Out

GENERAL MOTORS LLC BOWLING GREEN 

ASSEMBLY PLANT

600 CORVETTE DR BOWLING GREEN KY 42101 0.815 Screened Out

GENTEK BUILDING PRODUCTS 11 CRAGWOOD RD AVENEL NJ 07001 1.131 Screened Out

GEORGIA-PACIFIC CHEMICALS LLC 1429 E LUFKIN AVE LUFKIN TX 75901 0.034 Screened Out

Page 10 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

GFX INTERNATIONAL 333 BARRON BLVD GRAYSLAKE IL 60030 1.075 Screened Out

GIANT CEMENT CO HWY 453 & I-26 (654 JUDGE ST) HARLEYVILLE SC 29448 0.002 Screened Out

GLASS COATINGS & CONCEPTS 300 LAWTON AVE MONROE OH 45050 0.727 Screened Out

GLIDDEN CO 1900 N JOSEY LN CARROLLTON TX 75006 0.000285 Screened Out

GM MLCG FAIRFAX ASSEMBLY 3201 FAIRFAX TRAFFICWAY KANSAS CITY KS 66115 3.45 Screened Out

GM ORION ASSEMBLY CENTER 4555 GIDDINGS RD LAKE ORION MI 48359 1.75 Screened Out

GMC TRUCK GROUP ARLINGTON ASSEMBLY 

PLANT

2525 E ABRAMS ST ARLINGTON TX 76010 1.27 Screened Out

GMTG - SHREVEPORT ASSEMBLY 7600 GENERAL MOTORS BLVD SHREVEPORT LA 71129 2.575 Screened Out

GOJO INDUSTRIES INC 3783 STATE RD CUYAHOGA FALLS OH 44223 0.003787 Screened Out

GOLD EAGLE CO 4400 S KILDARE AVE CHICAGO IL 60632 0.125 Screened Out

GOODWIN CO 12361 MONARCH ST GARDEN GROVE CA 92841 0.005 Screened Out

GOODWIN CO 700 PROGRESS CENTER AVE LAWRENCEVILLE GA 30043 0.01291 Screened Out

GRAPHIC CONTROLS LLC 400 EXCHANGE ST BUFFALO NY 14204 0.046 Screened Out

GREIF INDUSTRIAL PACKAGING & SERVICES 

LLC

8250 ALMERIA AVE FONTANA CA 92335 0.1818 Screened Out

GREIF PACKAGING LLC 2400 COOPER AVE MERCED CA 95348 0.826 Screened Out

HADCO (SANMINA) CORP - OWEGO DIV 1200 TAYLOR RD OWEGO NY 13827 0.155 Screened Out

HALLSTAR CO ESTER SOLUTIONS FACILITY 5851 W 73RD ST BEDFORD PARK IL 60638 1.327 Screened Out

HANNA STEEL CORP 220 HANNA DR PEKIN IL 61554 0.038 Screened Out

HANNA STEEL CORP 3812 COMMERCE AVE FAIRFIELD AL 35064 2.1105 Screened Out

HARCROS CHEMICALS INC 4606 NEW W DR PASADENA TX 77507 0.034 Screened Out

HARCROS CHEMICALS INC 5200 SPEAKER RD KANSAS CITY KS 66106 0.139 Screened Out

HARLEY-DAVIDSON MOTOR CO 

OPERATIONS INC

1425 EDEN RD YORK PA 17402 0.0545 Screened Out

HARWICK STANDARD DISTRIBUTION CORP 60 S SEIBERLING ST AKRON OH 44305 0.0025 Screened Out

HB FULLER CO 7440 W DUPONT RD MORRIS IL 60450 0.3745 Screened Out

HENKEL CORP 923 MAULDIN RD CALHOUN GA 30701 0.0065 Screened Out

HENKEL CORP 421 LONDON RD DELAWARE OH 43015 0.031 Screened Out

HENKEL CORP 137 FOLLY MILL RD SEABROOK NH 03874 0.04955 Screened Out

HENKEL CORP 23343 SHERWOOD AVE WARREN MI 48091 0.25 Screened Out

HENTZEN COATINGS,INC 6937 W MILL RD MILWAUKEE WI 53218 0.0031 Screened Out

HENTZEN COATINGS,INC BATAVIA FACILITY 1500 LATHEM ST BATAVIA IL 60510 1.4085 Screened Out

HERCULES INC 1111 HERCULES RD HOPEWELL VA 23860 0.0025 Screened Out

HERCULES INC KENEDY TEXAS ONE MILL ST KENEDY TX 78119 0.1009555 Screened Out

HERITAGE-WTI INC 1250 ST GEORGE ST EAST LIVERPOOL OH 43920 0.00501 Screened Out

HEWLETT-PACKARD CARIBE BV SITE HWY 110 N KM 5.1 AGUADILLA PR 00605 3.2155 Screened Out

HEXPOL COMPOUNDING BURTON RUBBER 

PROCESSING

14330 KINSMAN RD BURTON OH 44021 0.0195 Screened Out

HEXPOL COMPOUNDING BURTON RUBBER 

PROCESSING

HWY 353 S JONESBOROUGH TN 37659 0.0275 Screened Out

HILLYARD INDUSTRIES INC 402 N 3TH ST SAINT JOSEPH MO 64501 1.1175 Screened Out

HIRSH INDUSTRIES INC 1525 MCKEE RD DOVER DE 19904 2.6355 Screened Out

HOLCIM (US) INC HOLLY HILL PLANT 200 SAFETY ST / HWY 453 HOLLY HILL SC 29059 0.1225 Screened Out

HOLLY OAK CHEMICAL INC 101 CASE ST FOUNTAIN INN SC 29644 0.010345 Screened Out

HONDA MANUFACTURING OF INDIANA LLC 2755 N MICHIGAN AVE GREENSBURG IN 47240 2.282 Screened Out

HUBBARD-HALL INC 563 S LEONARD ST WATERBURY CT 06708 0.0095 Screened Out

HUNT REFINING CO A CORP 1855 FAIRLAWN RD TUSCALOOSA AL 35401 0.932 Screened Out

HUNTSMAN ADVANCED MATERIALS 

AMERICAS INC

555 HUNTSMAN RD MC INTOSH AL 36553 0.05115 Screened Out

HUNTSMAN PETROCHEMICAL LLC 3892 US HWY 90 DAYTON TX 77535 0.001 Screened Out

HUNTSMAN PETROCHEMICAL LLC PORT 

NECHES FACILITY

6001 HWY 366 PORT NECHES TX 77651 0.11 Screened Out

HYDRITE CHEMICAL CO 7300 W BRADLEY RD MILWAUKEE WI 53223 0.0015 Screened Out

HYDRITE CHEMICAL CO 2545 BOND ST UNIVERSITY PARK IL 60466 0.011 Screened Out

HYDRITE CHEMICAL CO 114 N MAIN ST COTTAGE GROVE WI 53527 0.53 Screened Out

HYUNDAI MOTOR MANUFACTURING 

ALABAMA LLC

700 HYUNDAI BLVD MONTGOMERY AL 36105 4.1085 Screened Out

IC OF OKLAHOMA LLC 2322 N MINGO RD TULSA OK 74116 2.65 Screened Out

ICL-IP AMERICA INC 11636 HUNTINGTON GALLIPOLIS FERRY WV 25515 0.373145 Screened Out

IFF AUGUSTA LTD 3005 INTERNATIONAL BLVD AUGUSTA GA 30906 0.0004385 Screened Out

IGM RESINS CHARLOTTE 3300 WESTINGHOUSE BLVD CHARLOTTE NC 28273 0.0065 Screened Out

IMPERIAL PAINT CO INC 2526 NW YEON AVE PORTLAND OR 97210 0.0635 Screened Out

INCHEM CORP 800 CEL-RIVER RD ROCK HILL SC 29730 0.2125 Screened Out

INDEPENDENT CAN CO 1300 BRASS MILL RD BELCAMP MD 21017 1.52745 Screened Out

INDEPENDENT INK INC 14705 S AVALON BLVD GARDENA CA 90248 0.005 Screened Out

INEOS AMERICAS LLC INEOS OXIDE DIV 21255A HWY 1 S PLAQUEMINE LA 70765 0.384 Screened Out

INLAND LABEL & MARKETING 2009 W AVE S LA CROSSE WI 54601 4.133 Screened Out

INTEL CORP 4500 S DOBSON RD MAIL STOP: 

OC4-005

CHANDLER AZ 85248 0.2225 Screened Out

INTEL CORP 4100 SARA RD M/S RR5-491 RIO RANCHO NM 87124 0.4075 Screened Out

INTEL CORP - RONLER ACRES CAMPUS 2501 NW 229TH ST HILLSBORO OR 97124 0.9525 Screened Out

INTERCOASTAL PAINT CO INC 14029 W HARDY HOUSTON TX 77060 0.002 Screened Out

INTERNATIONAL PAINT LLC 640 N ROCKY RIVER DR BEREA OH 44017 0.005 Screened Out

INTERNATIONAL PAINT LLC 6001 ANTOINE DR HOUSTON TX 77091 0.1275 Screened Out

Page 11 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

INTERNATIONAL PAPER PINE HILL MILL 7600 HWY 10 W PINE HILL AL 36769 0.058 Screened Out

INTERSTATE CHEMICAL CO INC 23247 W EAMES ST CHANNAHON IL 60410 0.0075 Screened Out

INTERSTATE CHEMICAL CO INC 2797 FREEDLAND RD HERMITAGE PA 16148 0.014 Screened Out

INVISTA SARL - ORANGE SITE 3055A FM 1006 ORANGE TX 77630 0.125 Screened Out

INX DIGITAL INK CO 405 INDUSTRIAL WAY DIXON CA 95620 4.3915 Screened Out

ISP SYNTHETIC ELASTOMERS LP 1615 MAIN ST PORT NECHES TX 77651 0.132 Screened Out

ITW DYMON 805 E OLD 56 HWY OLATHE KS 66061 2.002 Screened Out

ITW PROFESSIONAL AUTOMOTIVE 

PRODUCTS

3606 CRAFTSMAN BLVD LAKELAND FL 33803 0.163 Screened Out

IVC INDUSTRIAL COATINGS INC 550-560 W CENTENNIAL BLVD CASA GRANDE AZ 85122 0.26016 Screened Out

IVC INDUSTRIAL COATINGS INC 1825 E NATIONAL AVE BRAZIL IN 47834 2.88926 Screened Out

IVC SOUTH 875 PROGRESS CENTER AVE LAWRENCEVILLE GA 30043 2.6895 Screened Out

J L CLARK INC 923 23RD AVE ROCKFORD IL 61104 1.4165 Screened Out

JAMESTOWN COATING TECHNOLOGIES 108 MAIN ST JAMESTOWN PA 16134 0.201 Screened Out

JOHN DEERE SEEDING & CYLINDER 501 RIVER DR MOLINE IL 61265 1 Screened Out

KALCOR COATINGS CO 37721 STEVENS BLVD WILLOUGHBY OH 44094 0.125 Screened Out

KARCHER NORTH AMERICA PROCHEM 325 S PRICE RD CHANDLER AZ 85224 0.0655 Screened Out

KAWNEER CO INC 500 E 12TH ST BLOOMSBURG PA 17815 0.5055 Screened Out

KAWNEER CO INC 7200 DOE AVE VISALIA CA 93291 0.7835 Screened Out

KAY AUTOMOTIVE GRAPHICS 57 KAY INDUSTRIAL DR LAKE ORION MI 48359 2.2135 Screened Out

KAY CHEMICAL CO 8300 CAPITAL DR GREENSBORO NC 27409 0.0595 Screened Out

KELLEY TECHNICAL COATINGS INC 1445 S 15TH ST LOUISVILLE KY 40210 0.4475 Screened Out

KELLEY TECHNICAL COATINGS INC 1401 S 15TH ST LOUISVILLE KY 40210 1.3 Screened Out

KEMIRA WATER SOLUTIONS INC 1 CYANAMID RD MOBILE AL 36610 0.1065 Screened Out

KEYMARK CORP 1188 CAYADUTTA ST RT 334 FONDA NY 12068 2.105 Screened Out

KEYSTONE ANILINE CORP 2165 HWY 292 INMAN SC 29349 0.25 Screened Out

KEYSTONE CEMENT CO RT 329 BATH PA 18014 0.0025 Screened Out

KIK-SOCAL INC 9028 DICE RD SANTA FE SPRINGS CA 90670 0.255 Screened Out

KING INDUSTRIES INC SCIENCE RD NORWALK CT 06852 0.00585 Screened Out

KMCO CROSBY PLANT 16503 RAMSEY RD CROSBY TX 77532 0.25 Screened Out

KWAL-HOWELLS INC (DBA KWAL PAINT INC) 2430 ALBERT BROADFOOT ST BONHAM TX 75418 0.0355 Screened Out

LAKESIDE LITHOGRAPHY LLC 1600 S LAFLIN ST CHICAGO IL 60608 3.25 Screened Out

LAMBERTI SYNTHESIS USA INC 4001 N HAWTHORNE ST CHATTANOOGA TN 37406 0.0005255 Screened Out

LAMBERTI USA INC - WHARTON CHEMICAL 

COMPLEX

HWY 59 AT COUNTY RD 212 HUNGERFORD TX 77448 0.0495 Screened Out

LANCO MANUFACTURING CORP URB.APONTE #5 SAN LORENZO PR 00754 0.00563 Screened Out

LEVLAD 9200 MASON AVE CHATSWORTH CA 91311 0.00017 Screened Out

LINETEC 725 S 75TH AVE WAUSAU WI 54401 0.372 Screened Out

LOCKHEED MARTIN AERONAUTICS CO 1011 LOCKHEED WAY MZ 0824 PALMDALE CA 93599 0.478 Screened Out

LONGABERGER CO 5565 RAIDERS RD FRAZEYSBURG OH 43822 0.164 Screened Out

LUBRIZOL 9550 W 55TH ST MC COOK IL 60525 0.0745 Screened Out

LUBRIZOL CORP 29400 LAKELAND BLVD WICKLIFFE OH 44092 0.0365 Screened Out

LUBRIZOL CORP PAINESVIL LE PLANT 155 FREEDOM RD PAINESVILLE OH 44077 0.0045 Screened Out

MACDERMID INC 1221 FARROW AVE FERNDALE MI 48220 0.00374 Screened Out

MACDERMID PRINTING SOLUTIONS 260 S PACIFIC ST SAN MARCOS CA 92078 0.2615 Screened Out

MAGNA MIRRORS CORP - NEWAYGO 700 S PARK DR NEWAYGO MI 49337 2.673 Screened Out

MAGNABLEND INC- LIQUID PLANT 100 W STERRETT RD WAXAHACHIE TX 75165 0.125 Screened Out

MAINTEX INC 13300 E NELSON AVE CITY OF INDUSTRY CA 91746 0.125 Screened Out

MALCO PRODUCTS INC 361 FAIRVIEW AVE BARBERTON OH 44203 0.25 Screened Out

MANN DISTRIBUTION 3134 POST RD WARWICK RI 02886 0.001055 Screened Out

MARATHON PETROLEUM CO - SPEEDWAY IN 

TERMINAL

1304 OLIN AVE INDIANAPOLIS IN 46222 0.002 Screened Out

MARCUS PAINT CO 235 E MARKET ST LOUISVILLE KY 40202 0.5225 Screened Out

MARY KAY INC 1330 REGAL ROW DALLAS TX 75247 0.00026 Screened Out

MASTERBRAND CABINETS INC 1002 EISENHOWER DR N GOSHEN IN 46526 4.193 Screened Out

MATTHEWS INTERNATIONAL CORP 101 FAIRVIEW AVE PITTSBURGH PA 15238 0.067 Screened Out

MAXIM INTEGRATED PRODUCTS INC 3725 N FIRST ST SAN JOSE CA 95134 0.0615 Screened Out

MAXIM INTEGRATED PRODUCTS INC 9651 WESTOVER HILLS BLVD SAN ANTONIO TX 78251 0.188 Screened Out

MEADWESTVACO CONSUMER PACKAGING 

GROUP LLC

7411 OAKWOOD ST MEBANE NC 27302 2.9255 Screened Out

MEADWESTVACO SC LLC CHARLESTON 

CHEMICAL PLANT

5598 VIRGINIA AVE NORTH CHARLESTON SC 29406 0.11118 Screened Out

MEADWESTVACO SOUTH CAROLINA LLC 400 CROSBY RD DERIDDER LA 70634 0.14 Screened Out

METAL COATERS 1150 MARIETTA INDUSTRIAL DR 

NE

MARIETTA GA 30062 0.291 Screened Out

METAL COATERS 9133 CENTER AVE RANCHO CUCAMONG CA 91730 0.38345 Screened Out

METAL COATERS 951 PRISOCK RD JACKSON MS 39272 4.4805 Screened Out

MID-STATES PAINT & CHEMICAL CO 9315 WATSON INDUSTRIAL PARK CRESTWOOD MO 63126 0.1325 Screened Out

MIDWEST METAL COATINGS 9 KONZEN CT GRANITE CITY IL 62040 0.51 Screened Out

MINUTEMAN INTERNATIONAL MULTI-CLEAN 

DIV

600 CARDIGAN RD SHOREVIEW MN 55126 0.0585 Screened Out

MISCO PRODUCTS CORP 1048 STINSON DR READING PA 19605 0.25 Screened Out

MISSION KLEENSWEEP PRODUCTS INC 2434 BIRKDALE ST LOS ANGELES CA 90031 1.5 Screened Out

MITSUBISHI MOTORS NORTH AMERICA INC 100 N MITSUBISHI MOTORWAY NORMAL IL 61761 1.0215 Screened Out

MOC PRODUCTS CO INC 12306 MONTAGUE ST PACOIMA CA 91331 0.1275 Screened Out

MOMENTIVE SPECIALTY CHEMICALS INC 8600 W 71ST ST BEDFORD PARK IL 60501 1.168 Screened Out

MOTOR CASTINGS CO 1323 S 65TH MILWAUKEE WI 53214 1.5915 Screened Out

Page 12 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

MPM SILICONES LLC 3500 S STATE RT 2 FRIENDLY WV 26146 2.197 Screened Out

MRCG-KRAFTMAID P1 16052 INDUSTRIAL PKWY MIDDLEFIELD OH 44062 0.047 Screened Out

MRCG-KRAFTMAID P3 150 GRAND VALLEY AVE ORWELL OH 44076 0.07 Screened Out

MULTI-COLOR CORP 2281 S US 31 SCOTTSBURG IN 47170 0.000156929 Screened Out

NALCO CO 125 NALCO WAY/RT 65 ELLWOOD CITY PA 16117 0.00007224 Screened Out

NALCO CO 3901 TERRY ST TEXARKANA TX 75501 0.0005 Screened Out

NALCO CO 812 RENAUD DR SCOTT LA 70583 0.0008585 Screened Out

NALCO CO PLANT 106 7701 US HWY 90A SUGAR LAND TX 77478 0.0553553 Screened Out

NALCO CO TULSA PLANT 102 6717 S 61ST W AVE TULSA OK 74131 0.003785 Screened Out

NASCOTE INDUSTRIES 18310 ENTERPRISE AVE NASHVILLE IL 62263 0.379145 Screened Out

NATIONAL INDUSTRIAL COATINGS INC DBA 

NICOAT INC

1600 GLENLAKE AVE ITASCA IL 60143 0.0005 Screened Out

NAVISTAR INC 6125 URBANA RD SPRINGFIELD OH 45502 3.815 Screened Out

NAZDAR CHICAGO 1087 N N BRANCH ST CHICAGO IL 60622 0.405 Screened Out

NAZDAR SHAWNEE 8501 HEDGE LN TERRACE SHAWNEE KS 66227 3.6515 Screened Out

NB COATINGS INC 2701 E 170TH ST LANSING IL 60438 0.4055 Screened Out

NCP COATINGS INC 225 FORT ST NILES MI 49120 2.1685 Screened Out

NELCO PRODUCTS INC 1107 E KIMBERLY ANAHEIM CA 92801 0.3635 Screened Out

NESTLE PURINA PETCARE 1000 HAMILTON RD WEIRTON WV 26062 1.577 Screened Out

NEW DAWN MANUFACTURING CO 16001 TRADE ZONE AVE UPPER MARLBORO MD 20774 0.0060048 Screened Out

NEXEO SOLUTIONS LLC 400 MAIN ST TEWKSBURY MA 01876 0.083 Screened Out

NEXEO SOLUTIONS LLC 5420 SPEAKER RD KANSAS CITY KS 66106 0.086 Screened Out

NEXEO SOLUTIONS LLC 3930 GLENWOOD DR CHARLOTTE NC 28208 0.14 Screened Out

NEXEO SOLUTIONS LLC 2011 TURNER ST LANSING MI 48906 0.146 Screened Out

NEXEO SOLUTIONS LLC 3101 WOOD DR GARLAND TX 75041 0.191 Screened Out

NEXEO SOLUTIONS LLC 7710 POLK ST SAINT LOUIS MO 63111 0.1945 Screened Out

NEXEO SOLUTIONS LLC 395 JAMES AVE SAINT PAUL MN 55102 0.2615 Screened Out

NEXEO SOLUTIONS LLC 8500 S WILLOW SPRINGS RD WILLOW SPRINGS IL 60480 0.5895 Screened Out

NEXEO SOLUTIONS LLC - EVENDALE 2788 GLENDALE-MILFORD RD EVENDALE OH 45241 0.108 Screened Out

NEXEO SOLUTIONS LLC CARSON 20915 S WILMINGTON AVE CARSON CA 90810 0.1 Screened Out

NEXEO SOLUTIONS LLC CARTERET 350 ROOSEVELT AVE CARTERET NJ 07008 0.254 Screened Out

NEXEO SOLUTIONS LLC DORAVILLE 4550 NE EXPRESSWAY DORAVILLE GA 30340 0.2285 Screened Out

NEXEO SOLUTIONS LLC FAIRFIELD 2461 CROCKER CIR FAIRFIELD CA 94533 0.0625 Screened Out

NEXEO SOLUTIONS LLC HOUSTON 8901 OLD GALVESTON RD HOUSTON TX 77034 0.0315 Screened Out

NEXEO SOLUTIONS LLC MIAMI 200 NE 181ST ST MIAMI FL 33162 0.102 Screened Out

NEXEO SOLUTIONS LLC TAMPA 5125 W HANNA AVE TAMPA FL 33634 0.033 Screened Out

NEXEO SOLUTIONS LLC TWINSBURG 

ENTERPRISE

1842 ENTERPRISE PKWY TWINSBURG OH 44087 0.0115 Screened Out

NEXEO SOLUTIONS LLC TWINSBURG 

HIGHLAND

1610 E HIGHLAND RD TWINSBURG OH 44087 0.248 Screened Out

NEXTEER AUTOMOTIVE CORP 3900 HOLLAND RD SAGINAW MI 48601 2.0835 Screened Out

NIACET CORP 400 47TH ST NIAGARA FALLS NY 14304 0.0025 Screened Out

NICCA USA INC 1044 S NELSON RD FOUNTAIN INN SC 29644 0.1275 Screened Out

NICHOLS ALUMINUM ALABAMA INC 2001 HWY 20 W DECATUR AL 35601 1.207 Screened Out

NICHOLS ALUMINUM DAVENPORT 1725 ROCKINGHAM RD DAVENPORT IA 52802 0.773 Screened Out

NORLITE CORP 628 S SARATOGA ST COHOES NY 12047 0.001285 Screened Out

NORTHERN COATINGS & CHEMICAL CO INC 705 6TH AVE MENOMINEE MI 49858 0.18 Screened Out

NORTHERN LABS INC WEST DRIVE 5800 W DR MANITOWOC WI 54220 2.588 Screened Out

NOV TUBOSCOPE HOLMES ROAD 2811 HOLMES RD HOUSTON TX 77051 0.0025 Screened Out

NOV TUBOSCOPE NAVASOTA 9574 FM 1227 NAVASOTA TX 77868 0.204565 Screened Out

NPA COATINGS INC 11120 BEREA RD CLEVELAND OH 44102 0.0585 Screened Out

OAKITE PRODUCTS INC (AKA CHEMETALL 

OAKITE)

16961 KNOTT AVE LA MIRADA CA 90638 0.005 Screened Out

OAKLEY INC 1 ICON FOOTHILL RANCH CA 92610 0.1275 Screened Out

OHIO ART CO ONE TOY ST BRYAN OH 43506 1.884 Screened Out

OLDCASTLE BUILDING ENVELOPE - 

TENNESSEE FACILITY

920 POTTERTOWN RD MIDWAY TN 37809 0.0845 Screened Out

OMG AMERICAS TWO MILE RUN RD FRANKLIN PA 16323 0.248 Screened Out

OMNIUM 1280 IMPERIAL RD HAMPTON IA 50441 0.0055 Screened Out

OMNOVA SOLUTIONS INC 1455 J A COCHRAN BY-PASS CHESTER SC 29706 0.00098 Screened Out

OWENS CORNING VETROTEX LLC - 

ANDERSON SC

4837 HWY 81 S STARR SC 29684 4.7895 Screened Out

PACKAGING CORP OF AMERICA COUNCE 

MILL

HWY 57 COUNCE TN 38326 0.025 Screened Out

PARISER INDUSTRIES INC 91 MICHIGAN AVE PATERSON NJ 07503 0.845 Screened Out

PARKER HANNIFIN TECH SEAL DIV 2600 WILCO BLVD WILSON NC 27893 0.000405 Screened Out

PATRIOT PAINT LLC 304 S BLAINE PIKE PORTLAND IN 47371 0.375 Screened Out

PCCR USA INC 400 E COTTAGE AVE CARPENTERSVILLE IL 60110 0.4295 Screened Out

PENN COLOR INC 2755 BERGEY RD HATFIELD PA 19440 3.016805 Screened Out

PENRAY COS INC 1801 ESTES AVE ELK GROVE VILLAGE IL 60007 0.001 Screened Out

PENRAY COS INC 440 DENNISTON CT WHEELING IL 60090 0.001 Screened Out

PERMA-PIPE OIL & GAS 5008-11 CURTIS LN NEW IBERIA LA 70560 0.395 Screened Out

PERMATEX SOLON 6875 PARKLAND BLVD SOLON OH 44139 0.1275 Screened Out

PFI INC 9215 SANTA FE SPRINGS RD SANTA FE SPRINGS CA 90670 0.369 Screened Out

PILOT CHEMICAL CO 11623 N HOUSTON ROSSLYN RD HOUSTON TX 77086 0.106 Screened Out

PLASTI-KOTE INC 1000 LAKE RD MEDINA OH 44258 0.0865 Screened Out

PLAZE INC 113 BOLTE LN SAINT CLAIR MO 63077 0.016 Screened Out

Page 13 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

PLAZE INC 1000 INTEGRAM DR PACIFIC MO 63069 0.025 Screened Out

PLAZE INC 105 BOLTE LN SAINT CLAIR MO 63077 0.066 Screened Out

POLARTEC LLC 46 STAFFORD ST LAWRENCE MA 01841 0.998 Screened Out

POLYMERIC IMAGING INC 117 E 14TH AVE NORTH KANSAS CITY MO 64116 1.0535 Screened Out

POWER SERVICE PRODUCTS INC 513 PEASTER HWY WEATHERFORD TX 76086 0.25 Screened Out

PPG ARCHITECTURAL COATINGS 6804 ENTERPRISE DR LOUISVILLE KY 40214 0.0007 Screened Out

PPG ARCHITECTURAL FINISHES EAST POINT 1377 OAKLEIGH DR EAST POINT GA 30344 0.4615 Screened Out

PPG ARCHITECTURAL FINISHES INC 400 S 13TH ST LOUISVILLE KY 40203 0.1765 Screened Out

PPG ARCHITECURAL COATINGS HOUSTON 3530 LANG RD HOUSTON TX 77092 0.0065 Screened Out

PPG INDUSTRIES ARCHITECTURAL FINISHES 1886 LYNNBURY WOODS RD DOVER DE 19904 0.0025 Screened Out

PPG INDUSTRIES ARCHITECTURAL FINISHES 1020 OLYMPIC DR BATAVIA IL 60510 0.821 Screened Out

PPG INDUSTRIES INC 500 PITTSBURGH AVE MCCARRAN NV 89434 0.125 Screened Out

PPG INDUSTRIES OHIO INC - DELAWARE 760 PITTSBURGH DR DELAWARE OH 43015 0.06872 Screened Out

PPG INDUSTRIES OHIO INC (CL) 3800 W 143 ST CLEVELAND OH 44111 1.0425 Screened Out

PPG INDUSTRIES OHIO INC CIRCLEVILLE OH 559 PITTSBURGH RD CIRCLEVILLE OH 43113 0.1775 Screened Out

PRC-DESOTO INTERNATIONAL INC 11601 UNITED ST MOJAVE CA 93501 0.016 Screened Out

PRECOAT METALS 6754 SANTA BARBARA CT ELKRIDGE MD 21075 0.628695 Screened Out

PRECOAT METALS 5888 E COUNTY RD 180 BLYTHEVILLE AR 72315 0.874 Screened Out

PRECOAT METALS 3399 DAVEY ALLISON BLVD HUEYTOWN AL 35023 2.5915 Screened Out

PRECOAT METALS 4502 FREEDOM WAY WEIRTON WV 26062 2.6315 Screened Out

PRECOAT METALS 4301 S SPRING AVE SAINT LOUIS MO 63116 3.355 Screened Out

PRECOAT METALS 16402 JACINTOPORT BLVD HOUSTON TX 77015 4.652 Screened Out

PREMIER INK SYSTEMS INC 10420 N STATE ST HARRISON OH 45030 0.125 Screened Out

PRESTONE PRODUCTS CORP 250 HALLS MILL RD FREEHOLD NJ 07728 0.004 Screened Out

PRIDE SOLVENT & CHEMICAL CO OF NY INC 6 LONG ISLAND AVE HOLTSVILLE NY 11742 0.0125 Screened Out

PRIDE SOLVENTS & CHEMICAL CO OF NEW 

JERSEY

211 RANDOLPH AVE AVENEL NJ 07001 0.0195 Screened Out

PRIOR COATED METALS 2233 26TH ST SW ALLENTOWN PA 18103 0.5515 Screened Out

PRO LINE PRINTING ARLINGTON 401 N GREAT SW PKWY ARLINGTON TX 76011 3.266895 Screened Out

PROCTER & GAMBLE CO GPDF 5348 VINE ST CINCINNATI OH 45217 0.0065 Screened Out

PROCTER & GAMBLE HAIR CARE LLC 2200 LOWER MUSCATINE RD IOWA CITY IA 52240 0.0295 Screened Out

PROCTER & GAMBLE MANUFACTURING CO 1900 KANSAS AVE KANSAS CITY KS 66105 0.00611 Screened Out

PROFESSIONAL DISPOSABLES 

INTERNATIONAL INC

TWO NICE-PAK PARK ORANGEBURG NY 10962 0.129005 Screened Out

PVS NOLWOOD CHEMICALS INC 9000 HUBBELL AVE DETROIT MI 48228 0.005 Screened Out

QG LLC 4581 LOWER VALLEY RD ATGLEN PA 19310 0.47 Screened Out

QG LLC 420 W INDUSTRIAL AVE EFFINGHAM IL 62401 2.445 Screened Out

QG LLC (WAS WORLDCOLOR STILLWATER) 100 W AIRPORT RD STILLWATER OK 74075 2.0405 Screened Out

QG LLC WINCHESTER VIRGINIA 160 CENTURY LN STONEWALL 

INDUSTRIAL PARK

WINCHESTER VA 22603 4.053425 Screened Out

QUAD GRAPHICS TAUNTON RETAIL 50 JOHN HANCOCK RD TAUNTON MA 02780 1.9616 Screened Out

QUAD/GRAPHICS INC 100 DUPLAINVILLE RD THE ROCK GA 30285 2.395 Screened Out

QUAD/GRAPHICS INC 555 S 108TH ST WEST ALLIS WI 53214 3.505 Screened Out

QUAD/GRAPHICS INC 56 DUPLAINVILLE RD SARATOGA SPRINGS NY 12866 3.8675 Screened Out

QUANTUM COATINGS INC 1337 N WOOD BRANCH DR CHARLOTTE NC 28273 0.25 Screened Out

QUEST SPECIALTY COATINGS LLC - 

MENOMONEE FALLS

N92 W14701 ANTHONY AVE MENOMONEE FALLS WI 53051 0.375 Screened Out

QUESTVAPCO CORP 12255 FM 529 HOUSTON TX 77041 0.65 Screened Out

R R DONNELLEY & SONS CO DANVILLE DIV 3201 LEBANON RD DANVILLE KY 40422 4.1715 Screened Out

RADIATOR SPECIALTY CO 600 RADIATOR RD INDIAN TRAIL NC 28079 0.146 Screened Out

RANBAR ELECTRICAL MATERIALS INC 408 MANOR-HARRISON CITY RD HARRISON CITY PA 15636 0.0065 Screened Out

RECKITT BENCKISER 799 RT 206 & HILLSBOROUGH RD HILLSBOROUGH NJ 08844 0.0545 Screened Out

RED SPOT PAINT & VARNISH CO INC 1016 E COLUMBIA ST EVANSVILLE IN 47711 1.047 Screened Out

RED SPOT WESTLAND INC 550 S EDWIN ST WESTLAND MI 48186 2.7255 Screened Out

REICHHOLD INC 249 ST LOUIS AVE VALLEY PARK MO 63088 0.512645 Screened Out

REICHHOLD INC 425 S PACE BLVD PENSACOLA FL 32502 1.7695 Screened Out

REICHHOLD INC - AZUSA PLANT 237 S MOTOR AVE AZUSA CA 91702 0.005 Screened Out

RENESSENZ LLC JACKSONVILLE 601 CRESTWOOD ST JACKSONVILLE FL 32208 0.0025 Screened Out

RESEARCH SOLUTIONS GROUP INC 402 INDUSTRIAL PARK DR PELHAM AL 35124 0.00425 Screened Out

RESEARCH SOLUTIONS GROUP INC 133 BAIN DR LA VERGNE TN 37086 0.01117 Screened Out

RG STEEL WHEELING LLC BEECH BOTTOM 

PLANT

2481 RIVER RD WELLSBURG WV 26070 1.4 Screened Out

RHODIA INC 2ND ST & BLUEBALL AVE MARCUS HOOK PA 19061 0.192 Screened Out

RHODIA INC 577 BANKHEAD HWY WINDER GA 30680 0.1985 Screened Out

RICHARDSAPEX INC 4202-24 MAIN ST PHILADELPHIA PA 19127 0.021111 Screened Out

RIKER PRODUCTS INC 4901 STICKNEY AVE TOLEDO OH 43612 0.000945 Screened Out

ROBROY INDUSTRIES TEXAS LP 1100 US HWY 271 S GILMER TX 75644 0.041 Screened Out

ROCK TENN CO 2301 S 21ST ST CLINTON IA 52732 0.6065 Screened Out

Page 14 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

ROCKLINE INDUSTRIES 1113 MARYLAND AVE SHEBOYGAN WI 53081 0.0995 Screened Out

RODDA PAINT CO 6123 N MARINE DR PORTLAND OR 97203 0.442 Screened Out

ROHM & HAAS CHEMICALS LLC 2401 E PRATT BLVD ELK GROVE VILLAGE IL 60007 0.0015 Screened Out

ROHM & HAAS CHEMICALS LLC 200 RT 413 BRISTOL PA 19007 0.2424 Screened Out

ROHM & HAAS ELECTRONIC MATERIA LS LLC 455 FOREST ST MARLBOROUGH MA 01752 0.005 Screened Out

ROLLEX CORP 800 CHASE AVE ELK GROVE VILLAGE IL 60007 0.2235 Screened Out

ROPPE CORP 1602 N UNION ST FOSTORIA OH 44830 2.8505 Screened Out

RR DONNELLEY 100 QUALITY CT CHARLESTOWN IN 47111 2.103 Screened Out

RR DONNELLEY & SONS CO 60 SECURITY DR AVON CT 06001 1.5765 Screened Out

RR DONNELLEY & SONS CO 6821 E COUNTY RD 1100 N MATTOON IL 61938 2.1105 Screened Out

RR DONNELLEY / PINEVILLE 10519 INDUSTRIAL DR PINEVILLE NC 28134 1.9455 Screened Out

RR DONNELLEY / VON HOFFMANN CORP 321 WILSON DR JEFFERSON CITY MO 65109 1.82586 Screened Out

RR DONNELLEY BARABOO DIV 1300 SAUK AVE BARABOO WI 53913 4.422 Screened Out

RR DONNELLEY LOS ANGELES 

MANUFACTURING

19681 PACIFIC GATEWAY DR TORRANCE CA 90502 2.433 Screened Out

RR DONNELLEY STRASBURG DIV ONE SHENANDOAH VALLEY DR STRASBURG VA 22657 3.14 Screened Out

RR DONNELLEY-WETMORE PLANT 1645 W SAM HOUSTON PKWY N HOUSTON TX 77043 4.7265 Screened Out

RR STREET & CO INC 2353 S BLUE ISLAND AVE CHICAGO IL 60608 0.1275 Screened Out

RRD MAPLE GROVE 7401 KILMER LN MAPLE GROVE MN 55369 4.038 Screened Out

RUDD CO INC 1141 NW 50TH ST SEATTLE WA 98107 0.205 Screened Out

RUSTOLEUM CORP 7850 OHIO RIVER RD LESAGE WV 25537 0.0135 Screened Out

RUST-OLEUM CORP 8105 95TH ST PLEASANT PRAIRIE WI 53158 0.75 Screened Out

RUST-OLEUM CORP IN MD 16410 INDUSTRIAL LN WILLIAMSPORT MD 21795 0.271 Screened Out

RYCOLINE PRODUCTS LLC 5540 NW HWY CHICAGO IL 60630 1.194 Screened Out

SACRAMENTO- CAMPBELL SOUP SUPPLY CO 6200 FRANKLIN BLVD SACRAMENTO CA 95824 0.125 Screened Out

SAFETY-KLEEN SYSTEMS INC 130 A FRONTAGE RD LEXINGTON SC 29073 0.125 Screened Out

SANFORD LP LIQUID MANUFACTURING & 

TECHNOLOGY CENTER

831 VOLUNTEER PKWY MANCHESTER TN 37355 0.3775 Screened Out

SAPA EXTRUDER INC 2905 OLD OAKWOOD RD GAINESVILLE GA 30504 2.317 Screened Out

SAPA EXTRUSIONS INC 2500 ALUMAX RD YANKTON SD 57078 2.4011901 Screened Out

SAPA INC - COATINGS DIVSION 5325 NE SKYPORT WAY PORTLAND OR 97218 1.71267935 Screened Out

SARTOMER USA LLC 601 TIGHTSQUEEZE INDUSTRIAL 

RD

CHATHAM VA 24531 0.005 Screened Out

SARTOMER USA LLC 610 S BOLMAR ST WEST CHESTER PA 19382 0.005 Screened Out

SASOL NORTH AMERICA INC LAKE CHARLES 

CHEMICAL COMPLEX

2201 OLD SPANISH TRAIL WESTLAKE LA 70669 0.4905 Screened Out

SC JOHNSON & SON INC WAXDALE FACILITY 8311 16TH ST STURTEVANT WI 53177 0.5 Screened Out

SCHNEIDER ELECTRIC 1990 SANDIFER BLVD SENECA SC 29678 2.35 Screened Out

SDC TECHNOLOGIES INC 45 PARKER IRVINE CA 92618 0.001 Screened Out

SENOX CORP 227 S TOWN E BLVD MESQUITE TX 75149 1.963 Screened Out

SERIGRAPH INC 3801 E DECORAH RD WEST BEND WI 53095 0.206 Screened Out

SEWELL PRODUCTS OF FLORIDA LLC 909 MAGNOLIA AVE AUBURNDALE FL 33823 0.398 Screened Out

SEYMOUR OF SYCAMORE INC 917 CROSBY AVE SYCAMORE IL 60178 0.6485 Screened Out

SHEBOYGAN PAINT CO 608 CANAL ST CEDARTOWN GA 30125 1.3205 Screened Out

SHERWIN-WILLIAMS CO 2150 W SAND LAKE RD ORLANDO FL 32809 0.0015 Screened Out

SHERWIN-WILLIAMS CO 26300 FARGO AVE BEDFORD HEIGHTS OH 44146 0.002 Screened Out

SHERWIN-WILLIAMS CO 14 INDUSTRIAL PARK FLORA IL 62839 0.0035 Screened Out

SHERWIN-WILLIAMS CO 404 E MALLORY AVE MEMPHIS TN 38109 0.0065 Screened Out

SHERWIN-WILLIAMS CO 12401 INDUSTRIAL BLVD VICTORVILLE CA 92392 0.01 Screened Out

SHERWIN-WILLIAMS CO 2325 HOLLINS FERRY RD BALTIMORE MD 21230 0.012 Screened Out

SHERWIN-WILLIAMS CO 6795 S MAIN ST MORROW GA 30260 0.0145 Screened Out

SHERWIN-WILLIAMS CO 2121 NEW WORLD DR COLUMBUS OH 43207 0.0215 Screened Out

SHERWIN-WILLIAMS CO 1025 HOWARD ST GREENSBORO NC 27403 0.0265 Screened Out

SHERWIN-WILLIAMS CO 2802 W MILLER RD GARLAND TX 75041 0.028 Screened Out

SHERWIN-WILLIAMS CO 113 STAGE COACH TRAIL GREENSBORO NC 27409 0.049 Screened Out

SHERWIN-WILLIAMS CO 630 E 13TH ANDOVER KS 67002 0.0505 Screened Out

SHERWIN-WILLIAMS CO 180 CANAL ST TERRE HAUTE IN 47808 0.0635 Screened Out

SHERWIN-WILLIAMS CO 636 E 40TH ST HOLLAND MI 49423 0.106 Screened Out

SHERWIN-WILLIAMS CO 395 BOGGS LN - S RICHMOND KY 40475 0.342 Screened Out

SI GROUP INC 1000 MAIN ST ROTTERDAM JUNCTIO NY 12150 0.02354 Screened Out

SICPA SECURINK CORP 8000 RESEARCH WAY SPRINGFIELD VA 22153 0.125 Screened Out

SIERRA CORP 11400 W 47TH ST MINNETONKA MN 55343 0.3015 Screened Out

SIKA CORP SIKA SARNAFIL DIV 100 DAN RD CANTON MA 02021 0.433 Screened Out

SILBOND CORP 9901 SAND CREEK HWY WESTON MI 49289 0.25 Screened Out

SILGAN CONTAINERS MANUFACTURING 

CORP

12130 LYNN AVE S SAVAGE MN 55378 0.575 Screened Out

SILGAN CONTAINERS MANUFACTURING 

CORP

2200 WILBUR AVE ANTIOCH CA 94509 2.067 Screened Out

SILGAN CONTAINERS MANUFACTURING 

CORP

8673 LYONS-MARENGO RD LYONS NY 14489 4.034 Screened Out

SILGAN CONTAINERS MANUFACTURING 

CORP

N90 W14600 COMMERCE DR MENOMONEE FALLS WI 53051 4.2 Screened Out

SILGAN CONTAINERS MANUFACTURING 

CORP

1400 PLOVER RD PLOVER WI 54467 4.47 Screened Out

SILGAN WHITE CAP CORP 1701 WILLIAMSBURG PIKE RICHMOND IN 47375 0.202 Screened Out

Page 15 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

SILGAN WHITE CAP CORP 350 JAYCEE DR VALMONT 

INDUSTRIAL PARK

HAZLETON PA 18201 1.8125 Screened Out

SIMONIZ USA INC 201 BOSTON TURNPIKE BOLTON CT 06043 0.0195 Screened Out

SINCLAIR WYOMING REFINING CO 100 E LINCOLN AVE SINCLAIR WY 82334 0.001 Screened Out

SNAP-ON TOOLS MANUFACTURING CO 2600 US HWY 18 E ALGONA IA 50511 0.1205 Screened Out

SONOCO FLEXIBLE PACKAGING 6502 S US HWY 31 EDINBURGH IN 46124 0.2045 Screened Out

SONOCO PRODUCTS CO 1854 CENTRAL FLORIDA PKWY ORLANDO FL 32837 0.658 Screened Out

SONOCO PRODUCTS CO - PRESIDENTS 

ISLAND

2755 HARBOR AVE MEMPHIS TN 38113 1.7065 Screened Out

SOUTH FLORIDA MATERIALS CORP DBA 

VECENERGY-PORT EVERGLADES

1200 SE 32ND ST FT LAUDERDALE FL 33316 0.078 Screened Out

SOUTHERN CLAY PRODUCTS INC 1335 S 13TH ST LOUISVILLE KY 40210 0.1275 Screened Out

SOUTHWEST DISTRIBUTING CO 539 S DREW ST MESA AZ 85210 0.006 Screened Out

SPARTAN CHEMICAL CO INC 1110 SPARTAN DR MAUMEE OH 43537 0.0675 Screened Out

SPECTRUM CUBIC INC 13 MCCONNELL ST SW GRAND RAPIDS MI 49503 0.385 Screened Out

SPECTRUM METAL FINISHING 535 BEV RD YOUNGSTOWN OH 44512 0.75 Screened Out

SPIRALKOTE FLEXIBLE PACKAGING 1200 CENTRAL FLORIDA PKWY ORLANDO FL 32837 0.941 Screened Out

SPRAYLAT CORP 716 S COLUMBUS AVE MOUNT VERNON NY 10550 0.4335 Screened Out

SPRAYLAT CORP CA 3465 S LA CIENAGA BLVD LOS ANGELES CA 90016 3.358 Screened Out

SPRAYLAT CORP IL 1701 E 122-ND ST CHICAGO IL 60633 0.6265 Screened Out

ST CHARLES OPERATIONS (TAFT/STAR) 

UNION CARBIDE CORP

355 LA HWY 3142 (GATE 1) TAFT LA 70057 1.67 Screened Out

STANDARD PAINTS INC 940 S 6TH AVE MANSFIELD TX 76063 0.22855 Screened Out

STEEL DYNAMICS INC 5134 LOOP RD JEFFERSONVILLE IN 47130 1.87 Screened Out

STEELSCAPE 222 W KALAMA RIVER RD KALAMA WA 98625 0.735505 Screened Out

STEELSCAPE INC 7001 ALLISON-BONNET MEMORIAL 

D

FAIRFIELD AL 35064 0.603375 Screened Out

STEELSCAPE INC RANCHO 11200 ARROW RT RANCHO CUCAMONG CA 91730 0.087635 Screened Out

STOUSE INC 300 NEW CENTURY PKWY NEW CENTURY KS 66031 0.1475 Screened Out

STP PRODUCTS MANUFACTURING CO 477 LEXINGTON AVE PAINESVILLE OH 44077 1.0615 Screened Out

SUMTER COATINGS INC 2410 HWY 15S SUMTER SC 29150 0.22 Screened Out

SUN CHEMICAL CORP 135 W LAKE ST NORTHLAKE IL 60164 0.003 Screened Out

SUN CHEMICAL CORP 3301 HUNTING PARK AVE PHILADELPHIA PA 19132 0.2045 Screened Out

SUN CHEMICAL CORP 1380 FORD RD MAUMEE OH 43537 0.966 Screened Out

SUN CHEMICAL CORP 2445 PRODUCTION DR SAINT CHARLES IL 60174 1.2085 Screened Out

SUPERIOR OIL CO INC 400 W REGENT ST INDIANAPOLIS IN 46225 0.007065 Screened Out

SUPERIOR OIL CO INC RECLAIMED ENERGY 

DIV

1500 WESTERN AVE CONNERSVILLE IN 47331 0.074 Screened Out

SUPERIOR SOLVENTS & CHEMICALS 4211 BRAMERS LN LOUISVILLE KY 40216 0.0035 Screened Out

SUPERIOR SOLVENTS & CHEMICALS 320 NORTHPOINTE DR FAIRFIELD OH 45014 0.004085 Screened Out

SYNDICATE SYSTEMS INC 402 N MAIN ST MIDDLEBURY IN 46540 0.712 Screened Out

SYNGENTA CROP PROTECTION LLC SAINT 

GABRIEL FACILITY

3905 HWY 75 SAINT GABRIEL LA 70776 0.133 Screened Out

TAIYO AMERICA INC 2675 ANTLER DR CARSON CITY NV 89701 1.1335 Screened Out

TAKASAGO INTERNATIONAL CORP (USA) 267 UNION ST NORTHVALE NJ 07647 0.0105 Screened Out

TCI COATINGS INC 4501 BRADLEY ST LUBBOCK TX 79415 4.36875 Screened Out

TECHNICAL CHEMICAL CO 3327 PIPELINE RD CLEBURNE TX 76033 0.1095 Screened Out

TEREX WASHINGTON SOUTH CAMPUS 18700 NE 65TH ST REDMOND WA 98052 4.7679 Screened Out

TERNIUM USA INC 2500 RON BEAN BLVD SHREVEPORT LA 71115 0.6705 Screened Out

TESORO REFINING & MARKETING CO - 

MANDAN REFINERY

900 OLD RED TRAIL NE MANDAN ND 58554 1.0505 Screened Out

TEXAS FINISHING CO 1801 SURVEYOR BLVD CARROLLTON TX 75006 1.676 Screened Out

TEXAS INSTRUMENTS INC 13500 N CENTRAL EXPRESSWAY DALLAS TX 75243 0.114 Screened Out

TEXAS INSTRUMENTS INC 12201 SW FWY MS600 STAFFORD TX 77477 0.1275 Screened Out

THE DIAL CORP A SUBSIDIARY OF HENKEL 

CONSUMER GOODS

6901 MCKISSOCK AVE SAINT LOUIS MO 63147 0.162 Screened Out

THE DOW CHEMICAL CO 1790 BUILDING MIDLAND MI 48667 2.29 Screened Out

THE DOW CHEMICAL CO - LOUISIANA 

OPERATIONS

21255 LA HWY 1 S PLAQUEMINE LA 70764 0.396 Screened Out

TITAN COATINGS INC 2025 EXCHANGE PL BESSEMER AL 35023 3.59 Screened Out

TMS MANUFACTURING 3555 W 123RD ST ALSIP IL 60803 0.284 Screened Out

TNEMEC CO INC 2300 EDGEWATER AVE BALTIMORE MD 21222 0.125 Screened Out

TNEMEC CO INC 123 W 23RD AVE NORTH KANSAS CITY MO 64116 0.125 Screened Out

TOWER PRODUCTS INC 2703 FREEMANSBURG AVE EASTON PA 18045 0.375 Screened Out

TOYO INK AMERICA LLC 2400 N HARVEY MITCHELL PKWY BRYAN TX 77807 0.014 Screened Out

TRADEBE TREATMENT & RECYCLING LLC 4343 KENNEDY AVE EAST CHICAGO IN 46312 0.4655 Screened Out

TRANS CHEMICAL INC 419 E DE SOTO AVE SAINT LOUIS MO 63147 0.125 Screened Out

TRANSTAR AUTOBODY TECHNOLOGIES 2040 HEISERMAN DR BRIGHTON MI 48114 0.00418 Screened Out

TRELLEBORG COATED SYSTEMS US INC / 

GRACE ADVANCED MATERIALS

715 RAILROAD AVE & HWY 74 RUTHERFORDTON NC 28139 0.0055 Screened Out

TRELLEBORG OFFSHORE US RANKIN ROAD 

FACILITY

1902 RANKIN RD HOUSTON TX 77073 0.5125 Screened Out

TRINKOTE INDUSTRIAL FINISHES INC 1800 PARK PL AVE FORT WORTH TX 76110 1.37545 Screened Out

TRUE VALUE MANUFACTURING 201 JANDUS RD CARY IL 60013 0.011 Screened Out

TTM PRINTED CIRCUIT GROUP - S TAFFORD 

DIV

4 OLD MONSON RD STAFFORD CT 06075 3.9505 Screened Out

TTM TECHNOLOGIES INC 234 CASHMAN DR CHIPPEWA FALLS WI 54729 0.793 Screened Out

TTM TECHNOLOGIES-SANTA CLARA 407 MATHEW ST SANTA CLARA CA 95050 1.0005 Screened Out

Page 16 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

TWINCO ROMAX 3100 W MILL RD MILWAUKEE WI 53209 0.0905 Screened Out

TYCO FIRE SUPPRESSION & BUILDING 

PRODUCTS

1 STANTON ST MARINETTE WI 54143 0.026065 Screened Out

TYSON FRESH MEATS INC 5000 N FM 1912 AMARILLO TX 79108 0.02 Screened Out

TYSON FRESH MEATS INC HWY 50 W HOLCOMB KS 67851 0.125 Screened Out

UNION CARBIDE CORP SOUTH CHARLESTON 

FACILITY

437 MACCORKLE AVE SW SOUTH CHARLESTON WV 25303 0.144 Screened Out

UNION SPECIALTIES INC 3 MALCOLM HOYT DR NEWBURYPORT MA 01950 0.0025 Screened Out

UNITED LABORATORIES INC 320 37TH AVE SAINT CHARLES IL 60174 0.1275 Screened Out

UNITED PAINT & CHEMICAL 24671 TELEGRAPH RD SOUTHFIELD MI 48034 0.9615 Screened Out

UNIVAR USA INC 2600 S GARFIELD AVE COMMERCE CA 90040 0.006 Screened Out

UNIVAR USA INC 7050 W 71ST ST BEDFORD PARK IL 60499 0.00887 Screened Out

UNIVAR USA INC - TOLEDO SOUTH BRANCH 4051 S AVE TOLEDO OH 43615 0.0505 Screened Out

UNIVAR USA INC - BUNOLA BRANCH 328 BUNOLA RIVER RD BUNOLA PA 15020 0.1275 Screened Out

UNIVAR USA INC SALEM BRANCH COLONIAL RD SALEM MA 01970 0.002 Screened Out

UNIVAR USA INC - TOLEDO BRANCH 30450 TRACY RD WALBRIDGE OH 43465 0.00189 Screened Out

UNIVAR USA INC DALLAS DAN MORTON 

FACILITY

3636 DAN MORTON DR DALLAS TX 75236 0.25 Screened Out

UNIVAR USA INC DORAVILLE FACILITY 1 ALCHEMY PL DORAVILLE GA 30362 0.0065 Screened Out

UNIVAR USA INC HAMILTON BRANCH 12 STANDEN DR HAMILTON OH 45015 0.25 Screened Out

UNIVAR USA INC HOUSTON 777 BRISBANE ST HOUSTON TX 77061 0.25 Screened Out

UNIVAR USA INC HOUSTON FM 529 11235 FM 529 HOUSTON TX 77041 0.75 Screened Out

UNIVAR USA INC JACKSONVILLE FA CILITY 155 ELLIS RD S JACKSONVILLE FL 32254 0.0195 Screened Out

UNIVAR USA INC JAMESTOWN FACILITY 108 OAKDALE RD JAMESTOWN NC 27282 0.006 Screened Out

UNIVAR USA INC MORRISVILLE BRANCH 200 DEAN SIEVERS PL MORRISVILLE PA 19067 0.03 Screened Out

UNIVAR USA INC NEW BERLIN 2400 S 170TH ST NEW BERLIN WI 53151 0.00702 Screened Out

UNIVAR USA INC NORCROSS FACILI TY 2145 SKYLAND CT NORCROSS GA 30071 0.0095 Screened Out

UNIVAR USA INC ROMULUS BRANCH 13395 HURON RIVER DR ROMULUS MI 48174 0.0805 Screened Out

UNIVAR USA INC SANTA FE SPRINGS 13900 CARMENITA RD SANTA FE SPRINGS CA 90670 0.0035 Screened Out

UNIVAR USA INC STRONGSVILLE BRANCH 21600 DRAKE RD STRONGSVILLE OH 44136 0.25 Screened Out

UNIVAR USA INC TAMPA FACILITY 6049 OLD 41A HWY TAMPA FL 33619 0.0065 Screened Out

UNIVERSAL CHEMICALS & COATINGS INC 1124 ELMHURST RD ELK GROVE VILLAGE IL 60007 0.6585 Screened Out

US ARMY LAKE CITY ARMY AMMUNITION 

PLANT

INTERSECTION OF MO HWYS 7 & 

78

INDEPENDENCE MO 64051 4.095 Screened Out

US DOD DFSP SAN PEDRO 3171 N GAFFEY ST SAN PEDRO CA 90731 0.1275 Screened Out

US DOD DFSP VERONA 5449 W MAIN ST VERONA NY 13478 0.0025 Screened Out

VALERO REFINING CO - TENNESSEE LLC 2385 RIVERPORT RD MEMPHIS TN 38109 0.03 Screened Out

VALERO THREE RIVERS REFINERY 301 LEROY ST THREE RIVERS TX 78071 0.0395 Screened Out

VALSPAR REFINISH 210 CROSBY ST PICAYUNE MS 39466 0.019 Screened Out

VALSPAR SAMUEL CABOT DIV 100 HALE ST NEWBURYPORT MA 01950 0.0525 Screened Out

VALVOLINE 720 VAIDEN DR HERNANDO MS 38632 0.0615 Screened Out

VAN CAN CO 1226 S MANUFACTURERS ROW TRENTON TN 38382 0.385315 Screened Out

VAN CAN CO 10837 ETIWANDA AVE FONTANA CA 92337 2.825 Screened Out

VANEX INC 1700 S SHAWNEE ST MOUNT VERNON IL 62864 2.818 Screened Out

VANGUARD PAINTS & FINISHES INC 1409 GREENE ST MARIETTA OH 45750 1.965 Screened Out

VARN INTERNATIONAL 1333 N KIRK RD BATAVIA IL 60510 0.0105 Screened Out

VEOLIA ES TECHNICAL SOLUTIONS LLC 7 MOBILE AVE SAUGET IL 62201 0.0035 Screened Out

VEOLIA ES TECHNICAL SOLUTIONS LLC 125 FACTORY LN MIDDLESEX NJ 08846 0.0595 Screened Out

VEOLIA ES TECHNICAL SOLUTIONS LLC 

PORT ARTHUR FACILITY

HWY 73, 3.5 MILES W OF TAYLOR 

BAYOU

PORT ARTHUR TX 77640 0.011395 Screened Out

VERSO PAPER HOLDINGS LLC ANDROSCOGGIN MILL RILEY RD JAY ME 04239 0.0025 Screened Out

VERTIS 7619 DOANE DR MANASSAS VA 20109 2.198 Screened Out

VERTIS COMMUNICATIONS 4646 S GRADY AVE TAMPA FL 33611 1.9875 Screened Out

VERTIS COMMUNICATIONS 10911 GRANITE ST CHARLOTTE NC 28273 2.0745 Screened Out

VERTIS COMMUNICATIONS 4051 FONDORF DR COLUMBUS OH 43228 2.43 Screened Out

VEYANCE TECHNOLOGIES INC 4021 N 56TH ST LINCOLN NE 68504 0.0000014 Screened Out

VEYANCE TECHNOLOGIES INC 400 N GOODYEAR RD MOUNT PLEASANT IA 52641 0.0005 Screened Out

VEYANCE TECHNOLOGIES INC 2701 W OMAHA AVE NORFOLK NE 68701 0.146845 Screened Out

VIASYSTEMS CORP 1521 POPLAR LN FOREST GROVE OR 97116 3.6475 Screened Out

VIDEOJET TECHNOLOGIES INC 1855 ESTES AVE ELK GROVE VILLAGE IL 60007 0.269 Screened Out

VISTA PAINT CORP 2020 E ORANGETHORPE AVE FULLERTON CA 92831 0.6185 Screened Out

VOGEL PAINT & WAX CO INC 1020 ALBANY PL SE ORANGE CITY IA 51041 0.0105 Screened Out

VOLTAIX LLC 197 MEISTER AVE BRANCHBURG NJ 08876 0.0015 Screened Out

W W HENRY 150 MOONEY DR BOURBONNAIS IL 60914 1.299 Screened Out

WARREN OIL CO - NC 2340 US 301 N DUNN NC 28335 0.1375 Screened Out

WARREN STAMPING PLANT (PART) 22800 MOUND RD WARREN MI 48091 0.46 Screened Out

WARREN UNILUBE INC 1200 S 8TH ST WEST MEMPHIS AR 72301 1.224 Screened Out

WATSON LABORATORIES INC 575, 577, 579 CHIPETA WAY SALT LAKE CITY UT 84108 0.09024 Screened Out

WATSON STANDARD CO (NEVILLE ISLAND 

PLANT)

2895 GRAND AVE PITTSBURGH PA 15225 0.775 Screened Out

WATSON STANDARD CO HARWICK PLANT 616 HITE RD HARWICK PA 15049 0.2505 Screened Out

WEBB CHEMICAL SERVICE CORP 2708 JARMAN MUSKEGON HEIGHTS MI 49444 0.2605 Screened Out

WEST PENN OIL CO,INC130130 2305 MARKET ST EXT. WARREN PA 16365 0.4305 Screened Out

WESTERN EXTRUSIONS CORP 1735 SANDY LAKE RD CARROLLTON TX 75006 0.602 Screened Out

WESTERN METAL DECORATING CO 8875 INDUSTRIAL AVE RANCHO CUCAMONG CA 91730 0.875 Screened Out

WHITFORD CORP 47 PARK AVE ELVERSON PA 19520 0.065575 Screened Out

WINSLOW-BROWNING INC 215 BROWNSVILLE AVE LIBERTY IN 47353 1.2345 Screened Out

Page 17 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

WISCONSIN ALUMINUM FOUNDRY CO INC 838 S 16TH ST MANITOWOC WI 54220 0.03505 Screened Out

WISMARQ CORP 930 ARMOUR RD OCONOMOWOC WI 53066 0.599 Screened Out

WISMARQ CORP 11440 W ADDISON AVE FRANKLIN PARK IL 60131 1.7385 Screened Out

WISMARQ VALENCIA LLC 125 MCFANN RD VALENCIA PA 16059 1.1145 Screened Out

WM BARR & CO INC 2170 BUOY ST MEMPHIS TN 38113 0.1275 Screened Out

WORWAG COATINGS LLC NORTH AMERICA 3420 KOSSUTH ST LAFAYETTE IN 47905 0.6745 Screened Out

WR MEADOWS INC 300 INDUSTRIAL DR HAMPSHIRE IL 60140 0.2525 Screened Out

WR MEADOWS OF ARIZONA INC 4220 S SARIVAL RD GOODYEAR AZ 85338 0.1515 Screened Out

WYNNEWOOD REFINING CO 906 S POWELL WYNNEWOOD OK 73098 0.0025 Screened Out

YENKIN-MAJESTIC PAINT CORPORAT ION 1920 LEONARD AVE COLUMBUS OH 43219 0.25 Screened Out

Z TECHNOLOGIES CORP 26500 CAPITOL AVE REDFORD MI 48239 0.0125 Screened Out

ZEP COMMERCIAL 350 JOE FRANK HARRIS PKWY EMERSON GA 30137 0.019 Screened Out

ZEP INC 1310 SEABOARD INDUSTRIAL BLVD ATLANTA GA 30318 0.242 Screened Out

ZSCHIMMER & SCHWARZ 70 GA HWY 22 W MILLEDGEVILLE GA 31061 0.3775 Screened Out

Page 18 of 19
Table C-3. Comparisons of 2011 TRI Air Emissions Data for Certain Glycol Ethers to the Step A Screening Value of 4.9 tpy

Facility Name Address City State Zip Code

2011 Air 

Emissions 

(tpy)

Outcome

tpy: tons per year

Page 19 of 19
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

HEWLETT‐PACKARD CARIBE BV SITE AGUADILLA PR N 00605 0.1 9.4 9.5 

CROWN BEVERAGE PACKAGING CAROLINA PR N 00985 7.5 22.6 30.1 

DU PONT ELECTRONICS MICROCIRCUITS INDUSTRIES LTD

MANATI PR N 00674 NR NR NR 

HOVENSA LLC CHRISTIANSTED V Isl N 00820 0.4 0.0 0.4 

VERTIS INC RNS SPRINGFIELD DIV EAST

LONGMEADOW

MA N 01028 NR NR NR 

SHIELD PACKAGING CO INC DUDLEY MA N 01571 0.0 0.0 0.0 

POLARTEC LLC LAWRENCE MA N 01841 NR NR NR 

KEY POLYMER LAWRENCE MA N 01843 0.0 0.0 0.0 CROWN BEVERAGE PACKAGING LAWRENCE MA Y 01843 18.0 54.1 72.2 

VALSPAR SAMUEL CABOT DIV NEWBURYPORT MA N 01950 NR NR NR 

MANN DISTRIBUTION WARWICK RI N 02886 NR NR NR 

TACO INC ‐ CRANSTON CRANSTON RI N 02920 NR NR NR 

EFI / INKWARE MEREDITH NH N 03253 0.0 0.1 0.1 

HENKEL CORP SEABROOK NH N 03874 NR NR NR 

S D WARREN CO WESTBROOK ME N 04098 0.0 15.0 15.0 

VERSO PAPER BUCKSPORT MILL BUCKSPORT ME N 4416 NR NR NR 

PRIME TANNING CO ‐ HARTLAND HARTLAND ME N 04943 0.1 5.3 5.4 

STANLEY WORKS HAND TOOLS DIV NEW BRITAIN CT N 06052 0.9 8.5 9.5 

CONOCOPHILLIPS CO TREMLEY POINT

TERMINAL

LINDEN NJ N 07036 0.0 0.0 0.0 

SAFETY‐KLEEN SYSTEMS INC LINDEN NJ N 07036 0.0 0.0 0.0 MAUSER CORP WOODBRIDGE NJ N 07095 0.0 2.9 2.9 

BENJAMIN MOORE

& CO ‐ NEWARK NEWARK NJ N 07105 NR NR NR 

DELEET MERCHANDISING NEWARK NJ N 07105 0.4 0.4 0.8 

ACTEGA RADCURE INC WAYNE NJ N 07470 0.0 0.0 0.0 

BASF CORP BELVIDERE NJ N 07823 0.0 0.0 0.0 

DUPONT CHAMBERS WORKS DEEPWATER NJ N 08023 0.1 0.0 0.1 CALLAHAN CHEMICAL CO PALMYRA NJ N 08065 0.0 0.0 0.0 

SILGAN CONTAINERS

MANUFACTURING CORP

EDISON NJ N 08817 6.0 1.4 7.4 

ENGLERT INC PERTH AMBOY NJ N 08861 NR NR NR 

AROMATIC TECHNOLOGIES INC SOMERVILLE NJ N 08876 0.0 0.0 0.0 

BALL METAL BEVERAGE CONTAINER

CORP

MIDDLETOWN NY Y 10940 6.0 7.0 13.0 

BASF CORP EAST SETAUKET NY N 11733 NR NR NR 

DISC GRAPHICS HAUPPAUGE NY N 11788 0.7 2.2 3.0 

SURPASS CHEMICAL CO INC ALBANY NY N 12204 NR NR NR 

Page 1 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

METAL CONTAINER CORP ‐ NEWBURGH CAN PLANT

NEW WINDSOR NY Y 12553 12.1 34.4 46.5 

BALL METAL BEVERAGE CONTAINER

CORP

SARATOGASPRINGS

NY Y 12866 3.3 15.0 18.3 

QUAD/GRAPHICS INC SARATOGA

SPRINGS

NY N 12866 5.6 0.3 5.9 

FIBERMARK NORTH AMERICA INC LOWVILLE NY N 13367 0.1 5.8 5.9 

US DOD DFSP VERONA VERONA NY N 13478 NR NR NR 

WHITING DOOR MANUFACTURING

CORP

AKRON NY N 14001 0.0 7.4 7.4 

ASHLAND DISTRIBUTION TONAWANDA NY N 14150 NR NR NR 

SENECA FOODS CORP CAN PLANT MARION NY N 14505 0.0 6.1 6.1 HAMMER PACKAGING CORP WEST HENRIETTA NY N 14586 0.0 15.1 15.1 

TRI VULCRAFT OF NEW YORK INC CHEMUNG NY N 14825 4.5 5.8 10.3 

UNIVAR USA INC ‐ BUNOLA BRANC H BUNOLA PA N 15020 NR NR NR 

USS ‐ CLAIRTON PLANT CLAIRTON PA N 15025 5.5 0.0 5.5 CLEARWATER INTERNATIONAL LLC LEETSDALE PA N 15056 0.0 0.0 0.0 

SEQUA COATINGS CORP PRECOAT

METALS DIV

MC KEESPORT PA N 15132 0.2 0.1 0.3 

PPG INDUSTRIES,INC‐SPRINGDALE

COMPLEX

SPRINGDALE PA N 15144 5.5 0.0 5.5 

ALLEGHENY PETROLEUM PRODUCTS

CO

WILMERDING PA N 15148 0.0 0.1 0.1 

BEDFORD MATERIALS CO INC MANNS CHOICE PA N 15550 1.3 11.3 12.6 

NALCO CO ELLWOOD CITY PA N 16117 NR NR NR 

JAMESTOWN COATINGTECHNOLOGIES

JAMESTOWN PA N 16134 0.2 0.0 0.2 

INTERSTATE CHEMICAL CO INC HERMITAGE PA N 16148 NR NR NR 

BERENFIELD CONTAINERS INC CLARENDON PA N 16313 0.1 8.3 8.4 

FRANKLIN INVESTMENT CORP FRANKLIN PA N 16323 10.7 0.0 10.7 ZURN INDUSTRIES LLC ERIE PA N 16502 4.7 0.0 4.7 

AMES TRUE TEMPER INC HARRISBURG PA N 17104 NR NR NR 

CROWN FOOD PACKAGING HANOVER PA N 17331 2.9 8.6 11.4 

NEW YORK WIRE HANOVER PA N 17331 0.0 26.0 26.0 

AMERICAN COLOR GRAPHICS INC YORK PA N 17404 2.1 0.2 2.3 

CP CONVERTERS INC YORK PA N 17402 NR NR NR 

RR DONNELLEY LANCASTER WEST LANCASTER PA N 17601 6.7 0.4 7.1 RR DONNELLEY LANCASTER EAST LANCASTER PA N 17601 5.3 0.4 5.7 

Page 2 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

ARMSTRONG WORLD INDUSTRIESLANCASTER PLANT

LANCASTER PA N 17603 0.9 0.4 1.3 

BEHR PROCESS CORP ALLENTOWN ALLENTOWN PA N 18106 0.0 0.0 0.1 MASCO RETAIL CABINET GROUP

SAYRE PENNSYLVANIA PLANT

SAYRE PA N 18840 NR NR NR 

DUPONT TOWANDA PLANT TOWANDA PA N 18848 NR NR NR 

CLEVELAND STEEL CONTAINER CORP QUAKERTOWN PA N 18951 NR NR NR 

SUPERPAC INC SOUTHAMPTON PA N 18966 NR NR NR 

GREIF PACKAGING LLC WARMINSTER PA N 18974 0.4 0.7 1.1 

GEORGE S COYNE CHEMICAL CO INC CROYDON PA N 19021 0.1 0.0 0.1 UNIVAR USA INC MORRISVILLE

BRANCH

MORRISVILLE PA N 19067 0.0 0.0 0.0 

CARDONE INDUSTRIES PHILADELPHIA PA N 19120 2.0 8.1 10.1 

SUN CHEMICAL CORP PHILADELPHIA PA N 19132 NR NR NR CAN CORP OF AMERICA INC BLANDON PA N 19510 3.2 9.6 12.8 

HIRSH INDUSTRIES INC DOVER DE N 19904 0.0 6.5 6.5 

INDEPENDENT CAN CO BELCAMP MD N 21017 NR NR NR 

CROWN FOOD PACKAGING BALTIMORE MD N 21221 8.5 25.5 34.0 

TNEMEC CO INC BALTIMORE MD N 21222 NR NR NR 

RUST‐OLEUM CORP IN MD WILLIAMSPORT MD N 21795 NR NR NR 

PHOENIX COLOR CORP HAGERSTOWN MD N 21742 NR NR NR 

VERTIS MANASSAS VA N 20109 NR NR NR CARRY‐ON TRAILER CORP MONTROSS VA N 22520 NR NR NR QG LLC WINCHESTER VIRGINIA WINCHESTER VA N 22603 3.2 0.1 3.4 DUPONT FRONT ROYAL PLANT FRONT ROYAL VA N 22630 0.0 0.2 0.2 

FISHER SCIENTIFIC INTERNATIONAL

MTN DIAGNOSTICS PLANT

MIDDLETOWN VA N 22645 0.0 0.0 0.0 

RR DONNELLEY HARRISONBURG VA Y 22802 36.1 4.3 40.4 

MERCK SHARP

& DOHME CORP ELKTON VI N 22827 0.7 0.8 1.5 

SOLITE LLC ARVONIA VI N 23004 0.0 0.0 0.0 

BALL METAL BEVERAGE CONTAINER

CORP

WILLIAMSBURG VA Y 23185 27.0 140.0 167.0 

CADMUS SPECIALTY PUBLICATIONS RICHMOND VI N 23228 NR NR NR BOEHRINGER INGELHEIM CHEMICALS

INC

PETERSBURG VA N 23805 0.0 0.1 0.1 

VOLVO TRUCKS NORTH AMERICA DUBLIN VI N 24084 NR NR NR 

Page 3 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

NEW MILLENNIUM BUILDING

SYSTEMS

SALEM VI N 24153 5.3 0.0 5.3 

VAUGHAN‐BASSETT FURNITURE COGALAX

GALAX VA N 24333 NR NR NR 

ROYAL MOULDINGS LTD; MARION

VIRGINIA

MARION VA N 24354 0.4 9.2 9.6 

GROTTOES PLASTICS PLANT GROTTOES VI N 24441 0.0 0.0 0.1 

DAVIS‐FROST INC LYNCHBURG VA N 24506 NR NR NR BALL METAL FOOD CONTAINER CORP WEIRTON WV N 26062 25.5 11.5 37.0 

CROWN CORK

& SEAL CO (USA) INC

CROWN CLOSURE DIV

WEIRTON WV Y 26062 37.9 63.3 101.1 

PRECOAT METALS WEIRTON WV N 26062 0.0 5.7 5.7 JELD‐WEN CRAIGSVILLE WV N 26205 NR NR NR 

REXAM BEVERAGE CAN CO RE:

WINSTON SALEM PLANT

WINSTON‐SALEM NC Y 27107 28.3 143.9 172.2 

APOLLO CHEMICAL BURLINGTON NC N 27215 0.1 0.0 0.1 

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

HIGH POINT NC N 27261 0.1 0.3 0.3 

THOMAS BUILT BUSES INC HIGH POINT NC N 27263 NR NR NR 

UNIVAR USA INC JAMESTOWN

FACILITY

JAMESTOWN NC N 27282 NR NR NR 

MEADWESTVACO CONSUMERPACKAGING GROUP LLC

MEBANE NC N 27302 11.3 0.0 11.3 

BALL METAL BEVERAGE CONTAINER

CORP

REIDSVILLE NC Y 27320 12.0 65.0 77.0 

CREE INC DURHAM NC N 27703 1.3 4.2 5.5 

AIR SYSTEM COMPONENTS LP TARBORO NC N 27886 0.2 14.8 14.9 

PARKER HANNIFIN TECH SEAL DIV WILSON NC N 27893 NR NR NR WIX FILTRATION CORP ‐ ALLEN PLANT GASTONIA NC N 28052 0.0 7.1 7.1 

BERENFIELD CONTAINERS SE LTD HARRISBURG NC N 28075 0.0 6.7 6.7 

CLARIANT CORP ‐ MOUNT HOLLY

WEST PLANT

MOUNT HOLLY NC N 28120 0.0 0.1 0.1 

QUANTUM COATINGS INC CHARLOTTE NC N 28273 0.1 0.1 0.3 

COMMERCIAL MERCHANDISING CORP CHARLOTTE NC N 28273 NR NR NR 

DUPONT FAYETTEVILLE PLANT FAYETTEVILLE NC N 28306 NR NR NR SILGAN CAN CO MAXTON NC N 28364 3.0 6.2 9.1 

AVERY DENNISON ‐ IBMD LENOIR LENOIR NC N 28645 3.7 1.6 5.3 

Page 4 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

STATESVILLE NC N 28625 0.1 0.1 0.2 

REXAM BEVERAGE CAN CO RE:

BISHOPVILLE SC FACILITY

BISHOPVILLE SC Y 29010 14.5 82.0 96.5 

HOLCIM (US) INC HOLLY HILL PLANT HOLLY HILL SC N 29059 NR NR NR 

SAFETY‐KLEEN SYSTEMS INC LEXINGTON SC N 29073 0.0 2.2 2.2 HUSQVARNA CONSUMER OUTDOOR

PRODUCTS

ORANGEBURG SC N 29116 0.1 5.5 5.6 

HENKEL ENOREE SC N 29335 0.0 0.0 0.0 

NUCOR CORP VULCRAFT DIV FLORENCE SC N 29501 8.5 0.9 9.4 

CROWN BEVERAGE PACKAGING CHERAW SC N 29520 19.6 2.5 22.1 

AVX CORP CONWAY CONWAY SC N 29526 0.9 1.1 2.0 

AVX CORP MYRTLE BEACH MYRTLE BEACH SC Y 29577 7.2 2.1 9.4 

DIVERSIFIED COATING SYSTEMS INC GREENVILLE SC N 29605 NR NR NR 

OWENS CORNING VETROTEX LLC STARR SC N 29684 0.5 4.8 5.4 

FUJIFILM MANUFACTURING US

A INC GREENWOOD SC N 29649 NR NR NR 

BMW MANUFACTURING CO LLC GREER SC Y 29651 3.5 67.1 70.6 

COGNIS CORP MAULDIN PLANT MAULDIN SC N 29662 0.0 0.0 0.1 

SCHNEIDER ELECTRIC SENECA SC N 29678 NR NR NR 

OMNOVA SOLUTIONS INC CHESTER SC N 29706 NR NR NR 

AGY AIKEN LLC AIKEN SC N 29801 3.0 0.9 3.9 

DECOSTAR INDUSTRIES INC CARROLLTON GA N 30117 0.1 1.3 1.4 

BALL CONTAINER LLC ROME CAN

PLANT

ROME GA Y 30161 34.5 15.0 49.5 

HB FULLER COVINGTON GA N 30014 0.4 0.3 0.7 

BEHR PROCESS CORP ATLANTA MC DONOUGH GA N 30253 NR NR NR ECOLAB INC MC DONOUGH GA N 30253 0.0 0.0 0.1 

ECOLAB INC MC DONOUGH GA N 30253 NR NR NR 

BRIGGS

& STRATTON POWER

PRODUCTS MCDONOUGHOPERATIONS

MC DONOUGH GA N 30253 NR NR NR 

TOPPAN INTERAMERICA INC MC DONOUGH GA N 30253 0.0 8.7 8.7 

QUAD/GRAPHICS INC THE ROCK GA N 30285 NR NR NR 

FLINT GROUP NORTH AMERICA ATLANTA GA N 30339 0.1 0.1 0.2 

UNIVAR USA INC DORAVILLE FACILITY DORAVILLE GA N 30362 NR NR NR 

CARRY‐ON TRAILER CORP LAVONIA GA N 30553 NR NR NR POWER PARTNERS INC ATHENS GA N 30607 0.0 10.8 10.8 

Page 5 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

BEAULIEU OF AMERICA PLANT 560‐

MODEL

DALTON GA N 30721 0.0 1.1 1.1 

FIBRO CHEM LLC DALTON GA N 30720 0.1 0.0 0.1 

YKK AP AMERICA INC DUBLIN GA N 31021 9.5 0.4 9.9 

ZSCHIMMER

& SCHWARZ MILLEDGEVILLE GA N 31061 NR NR NR 

U.S. AIR FORCE ROBINS AFB GA ROBINS AFB GA N 31098 1.6 0.9 2.5 

BWAY CORP HOMERVILLE GA N 31634 19.2 0.4 19.6 

KIA MOTORS MANUFACTURING OF

GEORGIA

WEST POINT GA N 31833 NR NR NR 

COMPLEMENTARY COATINGS CORP EDGEWATER FL N 32132 1.6 0.0 1.6 

METAL CONTAINER CORP ‐  JACKSONVILLE CAN PLANT

JACKSONVILLE FL N 32254 6.9 54.6 61.4 

RENESSENZ LLC JACKSONVILLE JACKSONVILLE FL N 32208 NR NR NR 

U.S. NAVY NAVAL AIR STATION

JACKSONVILLE

JACKSONVILLE FL N 32212 NR NR NR 

UNIVAR USA INC JACKSONVILLE FA

CILITY

JACKSONVILLE FL N 32254 NR NR NR 

CROWN FOOD PACKAGING WINTER GARDEN FL N 34787 1.3 4.4 5.8 

SPIRALKOTE FLEXIBLE PACKAGING ORLANDO FL N 32837 NR NR NR 

SOUTH FLORIDA MATERIALS CORPDBA VECENERGY‐PORT EVERGLADES

FT LAUDERDALE FL N 33316 NR NR NR 

METAL INDUSTRIES INC ‐ BUSHNELL BUSHNELL FL N 33513 0.1 15.7 15.8 

BALL METAL BEVERAGE CONTAINER

CORP

TAMPA FL N 33617 11.5 15.5 27.0 

UNIVAR USA INC TAMPA FACILITY TAMPA FL N 33619 NR NR NR 

VERTIS COMMUNICATIONS TAMPA FL N 33611 NR NR NR 

GSP MARKETING TECHNOLOGIES CLEARWATER FL N 33760 0.4 0.0 0.4 

HEXION SPECIALTY CHEMICALS INC LAKELAND FL N 33801 9.3 0.0 9.3 

KEYMARK CORP OF FLORIDA LAKELAND FL N 33810 0.5 9.4 9.8 SEWELL PRODUCTS OF FLORIDA LLC AUBURNDALE FL N 33823 NR NR NR ONESOURCE COIL COATERS CLEARWATER FL N 33760 NR NR NR DYCO PAINTS INC CLEARWATER FL N 33760 0.0 0.1 0.1 

M&B HANGERS LEEDS AL N 35094 2.4 9.6 12.0 

HONDA MANUFACTURING OF

ALABAMA LLC

LINCOLN AL N 35096 0.2 16.6 16.8 

AKZO NOBEL COATINGS INC BIRMINGHAM AL N 35234 11.1 0.2 11.3 

ASHLAND DISTRIBUTION BIRMINGHAM AL N 35234 0.3 0.0 0.3 

Page 6 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

MICHELIN NORTH AMERICA INC TUSCALOOSA AL N 35401 0.0 0.0 0.0 

RECTICEL INTERIORS NORTH AMERICA

LLC

TUSCALOOSA AL N 35401 0.0 0.0 0.0 

MERCEDES‐BENZ US INTERNATIONAL

INC

VANCE AL N 35490 2.3 9.9 12.2 

3M CO ‐ GUIN GUIN AL N 35563 0.0 9.5 9.5 3M CO ‐ GUIN GUIN AL N 35563 NR NR NR ITW SEXTON INC DECATUR AL N 35603 NR NR NR 

HART

& COOLEY INC HUNTSVILLE AL N 35811 0.9 13.4 14.3 

MUELLER CO ALBERTVILLE AL N 35950 6.9 6.9 13.8 NUCOR CORP VULCRAFT DIV FORT PAYNE AL N 35967 5.1 1.8 6.9 

FLINT GROUP NORTH AMERICA CORP ANNISTON AL N 36207 0.3 0.3 0.5 

DUNBARTON CORP REDIFRAME DIV DOTHAN AL N 36303 NR NR NR 

RUSKIN CO GENEVA AL N 36340 0.0 4.5 4.5 

INTERNATIONAL PAPER PINE HILL MILL PINE HILL AL N 36769 NR NR NR 

STATE INDUSTRIES INC ASHLAND CITY TN N 37015 NR NR NR 

WORLDCOLOR CLARKSVILLE TN N 37040 2.4 0.1 2.5 SANFORD LP SHELBYVILLE TN N 37160 0.1 2.2 2.4 

NISSAN NA INC SMYRNA

MANUFACTURING PLANT

SMYRNA TN N 37167 1.4 31.9 33.3 

GM SPRING HILL MANUFACTURING SPRING HILL TN N 37174 0.2 18.0 18.2 

QUAD GRAPHICS NASHVILLE NASHVILLE TN N 37207 NR NR NR 

ASHLAND DISTRIBUTION NASHVILLE TN N 37209 0.2 0.0 0.3 

NASHVILLE WIRE PRODUCTS NASHVILLE TN N 37218 0.7 6.5 7.2 

MAYTAG CORP CLEVELAND COOKING

PRODUCTS PLANT 1

CLEVELAND TN N 37311 0.0 8.6 8.6 

LA‐Z‐BOY TENNESSEE DAYTON TN N 37321 0.0 7.8 7.8 BATESVILLE MANUFACTURING INC MANCHESTER TN N 37355 1.1 20.7 21.8 

SANFORD LP LIQUID

MANUFACTURING

& TECHNOLOGY

CENTER

MANCHESTER TN N 37355 NR NR NR 

ALSTOM POWER INC CHATTANOOGA

BOILERS

CHATTANOOGA TN N 37402 13.8 0.0 13.8 

VOLKSWAGEN GROUP OF AMERICA

CHATTANOOGA OPERATIONS LLC

CHATTANOOGA TN N 37416 NR NR NR 

STAR BUILDING SYSTEMS ELIZABETHTON TN N 37643 0.0 1.0 1.0 

Page 7 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

ARMSTRONG HARDWOOD FLOORING

CO

ONEIDA TN N 37841 0.0 6.6 6.6 

VESTAL MANUFACTURINGENTERPRISES INC

SWEETWATER TN N 37874 10.7 0.0 10.7 

ROHM

& HAAS CHEMICALS LLC

KNOXVILLE SITE

KNOXVILLE TN N 37921 0.0 0.0 0.0 

TEKNOR APEX TENNESSEE CO (AKA

HAYWOOD CO)

BROWNSVILLE TN N 38012 NR NR NR 

EXCEL POLYMERS LLC DYERSBURG TN N 38024 0.0 0.0 0.0 

WORLDCOLOR ‐ DYERSBURG DIV DYERSBURG TN N 38024 6.3 0.1 6.4 JOHNSON BRYCE INC MEMPHIS TN N 38109 NR NR NR 

VALERO REFINING CO ‐ TENNESSEE

LLC

MEMPHIS TN N 38109 NR NR NR 

ASHLAND DISTRIBUTION MEMPHIS TN N 38113 0.1 0.0 0.1 

SONOCO PHOENIX ‐ PRESIDENTS

ISLAND

MEMPHIS TN N 38113 0.0 6.8 6.8 

W

M BARR

& CO MEMPHIS TN N 38113 0.0 0.1 0.1 

BRYCE CO LLC MEMPHIS TN N 38118 0.0 0.0 0.0 UNIVAR USA INC MEMPHIS MEMPHIS TN N 38118 0.0 0.0 0.0 

WM BARR

& CO INC MEMPHIS TN N 38113 NR NR NR 

GOODYEAR TIRE

& RUBBER CO UNION CITY TN N 38261 0.0 0.0 0.0 

KOHLER CO UNION CITY TN N 38261 NR NR NR 

CECO DOOR PRODUCTS MILAN TN N 38358 5.3 5.3 10.6 

VAN CAN CO TRENTON TN N 38382 NR NR NR 

CROWN BEVERAGE PACKAGING BATESVILLE MS N 38606 22.5 2.7 25.3 

KAWNEER CO INC HERNANDO MS N 38632 0.2 2.0 2.2 

VALVOLINE HERNANDO MS N 38632 NR NR NR REXAM BEVERAGE CAN CO OLIVE

BRANCH FACILITY

OLIVE BRANCH MS Y 38654 19.6 68.4 88.1 

QUEBECOR WORLD OLIVE BRANCH MS N 38654 0.4 3.7 4.1 SHERWIN‐WILLIAMS CO OLIVE BRANCH MS N 38654 0.0 0.0 0.0 

HUNTER DOUGLAS TUPELO CENTER SHANNON MS N 38868 0.3 5.5 5.8 NISSAN NORTH AMERICA INC CANTON

MS

CANTON MS N 39046 2.0 24.6 26.6 

ANDERSON TULLY LUMBER CO

WALTERSVILLE LUMBER MILL

VICKSBURG MS N 39181 NR NR NR 

METAL COATERS JACKSON MS N 39272 0.0 5.1 5.1 

PRECOAT METALS JACKSON MS N 39272 12.3 1.3 13.6 ESCO CORP NEWTON MS N 39345 6.3 0.0 6.3 CHEVRON PRODUCTS COPASCAGOULA REFINERY

PASCAGOULA MS N 39581 NR NR NR 

Page 8 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

INOAC PACKAGING GROUP BARDSTOWN KY N 40004 0.0 0.0 0.0 KELLEY TECHNICAL COATINGS INC LOUISVILLE KY N 40210 NR NR NR 

ASHLAND DISTRIBUTION LOUISVILLE KY N 40211 0.1 0.0 0.1 FORD LOUISVILLE ASSEMBLY LOUISVILLE KY N 40213 0.1 12.0 12.1 

KELLEY TECHNICAL COATINGS INC LOUISVILLE KY N 40210 NR NR NR 

FORD MOTOR CO KENTUCKY TRUCK

PLANT

LOUISVILLE KY Y 40241 0.9 32.5 33.4 

TOYOTA MOTOR MANUFACTURING

KENTUCKY INC

GEORGETOWN KY N 40324 0.1 5.4 5.5 

MODINE MANUFACTURING CO INC HARRODSBURG KY N 40330 1.2 10.8 12.0 

GUARDIAN AUTOMOTIVE ‐ 

MOREHEAD PLANT

MOREHEAD KY N 40351 0.0 0.2 0.2 

CENTRAL MOTOR WHEEL OF AMERICA(DBA CMWA)

PARIS KY N 40361 0.0 0.1 0.1 

HITACHI AUTOMOTIVE SYSTEMSAMERICAS INC‐BEREA KY

BEREA KY N 40403 0.2 11.1 11.3 

SQUARE D CO LEXINGTON KY N 40511 0.0 9.0 9.0 

GREIF PACKAGING LLC FLORENCE KY N 41042 1.4 26.2 27.5 

MAGNI INDUSTRIES INC INDEPENDENCE KY N 41051 NR NR NR 

AIR PRODUCTS

& CHEMICALS INC CALVERT CITY KY N 42029 NR NR NR 

TRAD NA INC HOPKINSVILLE KY N 42240 0.0 5.1 5.1 

LOGAN ALUMINUM INC RUSSELLVILLE KY N 42276 0.0 5.5 5.5 

PRECOAT METALS HAWESVILLE KY N 42348 0.0 1.0 1.0 ECOLAB HEBRON OH N 43025 0.0 0.0 0.0 HONDA OF AMERICAMANUFACTURING INC

MARYSVILLE OH N 43040 10.1 34.8 44.9 

JOHNSON WELDED PRODUCTS INC URBANA OH N 43078 0.0 14.1 14.1 

BALL CONTAINER LLC ‐  COLUMBUS

CAN PLANT

COLUMBUS OH Y 43213 20.0 50.0 70.0 

WHIRLPOOL CORP MARION D IVISION MARION OH Y 43302 0.1 55.8 55.8 

HONDA OF AMERICAMANUFACTURING INC

EAST LIBERTY OH N 43319 2.0 27.5 29.5 

WHIRLPOOL CORP ‐ CLYDE DIV CLYDE OH N 43410 1.1 34.3 35.4 REXAM BEVERAGE CAN CO RE:

FREMONT PLANT

FREMONT OH Y 43420 17.9 102.2 120.1 

ELECTROPRIME INC ROSSFORD OH N 43460 0.0 6.0 6.0 

SILGAN CAN CO NAPOLEON OH N 43545 2.4 6.6 9.0 

REXAM BEVERAGE CAN CO RE:

WHITEHOUSE PLANT

WHITEHOUSE OH Y 43571 16.5 31.6 48.1 

Page 9 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

DECORATIVE PANELS INTERNATIONA L TOLEDO OH N 43607 7.6 0.0 7.6 MAGNA STEYR NORTH AMERICA TOLEDO OH N 43608 3.0 21.0 24.0 

DAIMLERCHRYSLER CORP TOLEDOASSEMBLY PLANT

TOLEDO OH N 43612 0.4 0.9 1.3 

CROWN FOOD PACKAGING TOLEDO OH N 43612 2.8 8.4 11.2 

AK STEEL CORP ‐ ZANESVI LLE WORKS ZANESVILLE OH N 43701 0.0 2.5 2.5 

INTERNATIONAL PAINT LLC BEREA OH N 44017 NR NR NR EXCEL POLYMERS LLC BURTON OH N 44021 NR NR NR 

SCOT LABORATORIES CHAGRIN FALLS OH N 44023 0.0 0.0 0.0 

GOLD KEY PROCESSING INC MIDDLEFIELD OH N 44062 NR NR NR 

NORTH COAST CONTAINER CORP CLEVELAND OH N 44105 0.0 16.1 16.1 NPA COATINGS INC CLEVELAND OH N 44102 NR NR NR 

UNIVAR USA INC STRONGSVILLE OH N 44136 NR NR NR 

FERRO CORP WALTON HILLSOPERATIONS

WALTON HILLS OH N 44146 NR NR NR 

GOJO INDUSTRIES INC CUYAHOGA FALLS OH N 44223 NR NR NR 

HESS PRINT SOLUTIONS BRIMFIELD OH N 44240 9.0 0.0 9.0 

PLASTI‐KOTE INC MEDINA OH N 44258 NR NR NR 

3M CO ‐ MEDINA MEDINA OH N 44256 NR NR NR HARWICK STANDARD DISTRIBUTION

CORP

AKRON OH N 44305 NR NR NR 

CANFIELD METAL COATING CORP CANFIELD OH N 44406 0.0 1.1 1.1 

GENERAL MOTORS CORP LORDSTOWNCOMPLEX

LORDSTOWN OH N 44481 12.0 0.2 12.2 

TECNOCAP LLC WARREN OH N 44483 2.1 3.7 5.8 NOVELIS CORP WARREN OH N 44483 4.7 11.3 15.9 MAHONING PAINT CORP YOUNGSTOWN OH N 44502 0.0 0.0 0.0 EPCO EXTRUSION PAINTING CO BOARDMAN OH N 44512 0.8 8.4 9.2 

SPECTRUM METAL FINISHING YOUNGSTOWN OH N 44512 0.4 18.1 18.4 

GE WATER

& PROCESS TECHNOLOGIES NEW

PHILADELPHIA

OH N 44663 NR NR NR 

ARTIFLEX MANUFACTURING LLC

GERSTCO DIV WOOSTER

WOOSTER OH N 44691 0.3 10.5 10.8 

MAYFLOWER VEHICLE SYSTEMS INC

NORWALK FACILITY

NORWALK OH N 44857 0.0 10.0 10.0 

AMERICAN COLORS INC DISPERSION

PLANT SANDUSKY OHIO

SANDUSKY OH N 44870 NR NR NR 

Page 10 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

RR DONNELLEY

& SONS CO WILLARD OH N 44890 6.1 2.4 8.4 

NEWMAN TECHNOLOGY INC MANSFIELD OH N 44903 NR NR NR 

FLINT GROUP NORTH AMERICA CORP LEBANON OH N 45036 NR NR NR 

WORLDCOLOR LEBANON DIV LEBANON OH N 45036 2.9 0.4 3.4 BERENFIELD CONTAINERS INC MASON MASON OH N 45040 0.4 7.5 7.9 

PROCTER

& GAMBLE CO GPDF CINCINNATI OH N 45217 NR NR NR 

HB FULLER CO BLUE ASH OH N 45242 0.5 0.0 0.5 

INGERSOLL‐RAND CO STEELCRAFT DIV CINCINNATI OH N 45242 2.5 7.9 10.5 UNIVAR USA INC‐ CINCINNATI OH

BRANCH

CINCINNATI OH N 45246 0.0 0.0 0.0 

ALCOA HOME EXTERIORS INC SIDNEY OH N 45365 0.7 4.0 4.6 

AMERICAN TRIM LLC SIDNEY OH N 45365 0.0 11.2 11.2 

NAVISTAR INC SPRINGFIELD OH N 45502 0.6 5.0 5.6 

MASCO RETAIL CABINET GROUP LLC WAVERLY OH N 45690 0.0 0.4 0.4 

BALL METAL BEVERAGE CONTAINER

CORP

FINDLAY OH Y 45840 24.5 130.0 154.5 

WHIRLPOOL CORP FINDLAY DIV FINDLAY OH N 45840 2.3 20.6 22.8 

J&M MANUFACTURING CO INC FORT RECOVERY OH N 45846 0.0 1.7 1.7 

LAFARGE NA (INCLUDING SYSTECH

ENV CORP)

PAULDING OH N 45879 NR NR NR 

AAP ST MARYS CORP SAINT MARYS OH N 45885 0.0 4.7 4.7 

DSM NEORESINS INC FRANKFORT IN N 46041 0.0 0.0 0.0 CROWN EQUIPMENT CORP GREENCASTLE IN N 46135 0.0 3.1 3.1 

PRECOAT METALS GREENFIELD IN N 46140 0.0 18.3 18.4 

CAR CARE PACKAGING LLC INDIANAPOLIS IN N 46203 0.0 0.0 0.0 

IVC INDUSTRIAL COATINGS INC INDIANAPOLIS IN N 46218 0.3 1.2 1.5 UNIVAR USA INC ‐ INDIANAPOLIS INDIANAPOLIS IN N 46219 0.0 0.0 0.0 

MARATHON PETROLEUM CO ‐ 

SPEEDWAY IN TERMINAL

INDIANAPOLIS IN N 46222 NR NR NR 

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

INDIANAPOLIS IN N 46225 0.0 0.0 0.0 

DYNALOY LLC INDIANAPOLIS IN N 46226 0.0 0.0 0.0 

UNIVAR USA INC INDIANAPOLIS WEST

BRANCH

INDIANAPOLIS IN N 46268 0.0 0.0 0.0 

TRADEBE TREATMENT

& RECYCLING

LLC

EAST CHICAGO IN N 46312 NR NR NR 

Page 11 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

SILGAN CONTAINERS

MANUFACTURING CORP

HAMMOND IN N 46320 0.0 6.0 6.0 

PRECOAT METALS LA PORTE IN N 46350 0.0 5.0 5.0 

SILGAN CONTAINERS

MANUFACTURING CORP

LA PORTE IN Y 46350 12.5 54.5 67.0 

AVERY DENNISON PFD SCHERERVILLE IN N 46375 0.1 0.0 0.1 BP PRODUCTS NORTH AMERICA

WHITING

WHITING IN N 46394 NR NR NR 

ET PRODUCTS CO INC BREMEN IN N 46506 0.0 0.3 0.3 

MASTERBRAND CABINETS INC GOSHEN IN N 46526 NR NR NR 

MIDDLEBURY HARDWOOD PRODUCTS MIDDLEBURY IN N 46540 NR NR NR AM GENERAL LLC MISHAWAKA IN N 46545 NR NR NR 

WARSAW CHEMICAL CO INC WARSAW IN N 46580 0.0 0.0 0.1 

BIOLAB INC ASHLEY IN N 46705 NR NR NR STEEL DYNAMICS INC BUTLER IN N 46721 0.0 0.0 0.0 

THERMA‐TRU CORP BUTLER IN N 46721 0.0 31.0 31.0 GM TRUCK GROUP FORT WAYNE

ASSEMBLY

ROANOKE IN N 46783 0.5 7.0 7.5 

NUCOR VULCRAFT GROUP SAINT JOE

DIV

SAINT JOE IN N 46785 4.2 1.7 5.9 

AURORA CASKET CO INC AURORA IN N 47001 0.0 107.6 107.6 

BATESVILLE MANUFACTURING INC ‐

DOLL PLANT

BATESVILLE IN N 47006 0.2 3.3 3.5 

ENKEI AMERICA INC COLUMBUS IN N 47201 0.0 5.3 5.3 PATRIOT PAINT LLC PORTLAND IN N 47371 NR NR NR GEA BPO LLC BLOOMINGTON IN N 47404 0.0 11.0 11.0 

ASHLEY INDUSTRIAL MOLDING INC ASHLEY IN N 46705 0.5 4.4 4.8 

SABIC INNOVATIVE PLASTICS MT

VERNON LLC

MOUNT VERNON IN N 47620 2.7 1.7 4.4 

ALCOA INC ‐ WARRICK OPERATIONS NEWBURGH IN N 47629 0.0 14.5 14.5 

TOYOTA MOTOR MANUFACTURING

INDIANA INC

PRINCETON IN N 47670 9.8 6.3 16.1 

SILGAN WHITE CAP CORP EVANSVILLE IN N 47710 1.9 6.8 8.7 

IVC INDUSTRIAL COATINGS INC BRAZIL IN N 47834 NR NR NR 

SUBARU OF INDIANA AUTOMOTIVE

INC

LAFAYETTE IN N 47905 0.2 21.9 22.1 

CROWN BEVERAGE PACKAGING CRAWFORDSVILLE IN N 47933 10.0 3.7 13.8 

Page 12 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

RR DONNELLEY CRAWFORDSVILLE CRAWFORDSVILLE IN N 47933 5.1 4.8 9.9 BON L MANUFACTURING CO KENTLAND IN N 47951 0.3 3.1 3.4 

BALL METAL BEVERAGE CONTAINER

CORP

MONTICELLO IN N 47960 26.0 10.0 36.0 

MASTER GUARD CORP VEEDERSBURG IN N 47987 0.0 2.3 2.4 

GM ORION ASSEMBLY CENTER LAKE ORION MI N 48359 6.5 0.8 7.3 

KAY AUTOMOTIVE GRAPHICS LAKE ORION MI N 48359 NR NR NR 

PONTIAC ASSEMBLY CENTER PONTIAC MI N 48341 0.3 3.1 3.4 

HOWARD FINISHING LLC MADISON

HEIGHTS

MI N 48071 0.0 7.4 7.4 

CURTIS METAL FINISHING CO STERLING HEIGHTS MI N 48313 2.0 0.8 2.9 

NJT ENTERPRISES LLC STERLING HEIGHTS MI N 48314 0.0 0.8 0.8 

CHRYSLER WARREN TRUCK ASSEMBLY

PLANT (PART)

WARREN MI N 48091 6.0 0.7 6.7 

WAYNE DISPOSAL INC BELLEVILLE MI N 48111 NR NR NR 

FORD MOTOR CO DEARBORN TRUCK

PLANT

DEARBORN MI Y 48121 3.8 85.0 88.8 

AUTOALLIANCE INTERNATIONAL INC FLAT ROCK MI N 48134 0.0 12.6 12.6 

UNIVAR USA INC ROMULUS BRANCH ROMULUS MI N 48174 NR NR NR 

AUTOMOTIVE COMPONENTSHOLDINGS LLC SALINE PLANT

SALINE MI N 48176 NR NR NR 

FORD MOTOR COMPANY‐WAYNE

ASSEMBLY

WAYNE MI N 48184 0.1 8.5 8.6 

FORD MOTOR CO MICHIGAN

ASSEMBLY PLANT

WAYNE MI N 48184 0.0 0.0 0.0 

AMERICAN JETWAY CORP WAYNE MI N 48184 NR NR NR 

AJAX METAL PROCESSING INC DETROIT MI N 48207 NR NR NR 

CHRYSLER JEFFERSON NORTHASSEMBLY PLANT

DETROIT MI N 48215 6.5 20.0 26.5 

PVS NOLWOOD CHEMICALS INC DETROIT MI N 48228 NR NR NR 

Z TECHNOLOGIES CORP REDFORD MI N 48239 NR NR NR 

MT ELLIOTT TOOL

& DIE

MANUFACTURING (PART)

DETROIT MI N 48234 0.1 0.0 0.1 

GM LLC POWERTRAIN FLINT ENGINE

OPERATIONS

FLINT MI N 48552 0.3 35.5 35.8 

Page 13 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

GENERAL MOTORS LANSING DELTA

TOWNSHIP

LANSING MI N 48917 0.2 8.5 8.7 

GMVM‐LANSING GRAND RIVER

ASSEMBLY

LANSING MI N 48921 3.6 3.1 6.7 

GRAPHIC PACKAGING INTERNATIONAL

INC

KALAMAZOO MI N 49007 NR NR NR 

DEXTER CHASSIS GROUP PLANT 55 WHITE PIGEON MI N 49099 0.0 18.3 18.3 

CHEMETALL US INC JACKSON MI N 49203 NR NR NR 

ANDERSON DEVELOPMENT CO ADRIAN MI N 49221 NR NR NR 

HELEN,INC DBA ENVIRONMENTAL

COATINGS,INC

CALEDONIA MI N 49316 0.2 0.1 0.3 

BRADFORD WHITE CORP MIDDLEVILLE MI N 49333 0.0 5.8 5.8 

MAGNA MIRRORS CORP ‐ NEWAYGO NEWAYGO MI N 49337 NR NR NR 

WEBB CHEMICAL SERVICE CORP MUSKEGON

HEIGHTS

MI N 49444 NR NR NR 

SPECTRUM CUBIC INC GRAND RAPIDS MI N 49503 NR NR NR 

AVON AUTOMOTIVE PLANT 1 CADILLAC MI N 49601 NR NR NR 

JOHN DEERE DES MOINES WORKS ANKENY IA N 50023 NR NR NR 

3M CO ‐ KNOXVILLE KNOXVILLE IA N 50138 0.0 0.0 0.0 

PELLA CORP PELLA IA N 50219 0.1 14.4 14.6 

SILGAN CONTAINERS MANUFACTURING CORP

FORT DODGE IA N 50501 NR NR NR 

METOKOTE CORP PLANT 15 CEDAR FALLS IA N 50613 0.0 6.0 6.0 VOGEL PAINT

& WAX CO INC ORANGE CITY IA N 51041 NR NR NR 

PELLA CORP CARROLL OPERATIONS CARROLL IA N 51401 NR NR NR 

CARRY‐ON TRAILER CORP MISSOURI VALLEY IA N 51555 0.0 6.0 6.0 

KLINGER PAINT CO INC CEDAR RAPIDS IA N 52404 NR NR NR 

CNH AMERICA LLC BURLINGTON IA N 52601 0.2 5.5 5.7 MONSANTO CO MUSCATINE IA N 52761 0.0 0.0 0.0 

AMERICAN FINISHING RESOURCES INC CHILTON WI N 53014 NR NR NR WORTHINGTON CYLINDERS WISCONSIN LLC

CHILTON WI N 53014 0.9 4.3 5.3 

BROAN‐NUTONE LLC HARTFORD WI N 53027 0.1 10.6 10.8 

QUAD/GRAPHICS INC HARTFORD WI N 53027 12.0 0.4 12.4 

JOHN DEERE HORICON WORKS‐DT HORICON WI N 53032 NR NR NR 

QUAD/GRAPHICS INC LOMIRA WI N 53048 NR NR NR 

Page 14 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

QUEST SPECIALTY COATINGS LLC ‐ 

MENOMONEE FALLS

MENOMONEEFALLS

WI N 53051 NR NR NR 

SILGAN CONTAINERS

MANAUFACTURING CORP

OCONOMOWOC WI N 53066 1.8 7.1 8.8 

WISMARQ CORP OCONOMOWOC WI N 53066 NR NR NR 

BEMIS MANUFACTURING CO PLANT B SHEBOYGAN FALLS WI N 53085 0.0 13.1 13.1 

QUAD/GRAPHICS INC SUSSEX WI N 53089 8.3 0.9 9.2 

DIVERSEY INC WATERTOWN WI N 53094 NR NR NR 

UNIVAR USA INC NEW BERLIN NEW BERLIN WI N 53151 NR NR NR 

MID‐AMERICA STEEL DRUM CO IN C OAK CREEK WI N 53154 NR NR NR 

PPG INDUSTRIES INC‐OAK CREEK OAK CREEK WI N 53154 15.5 0.4 15.9 

FIVE STAR COATINGS GROUP TWIN LAKES WI N 53181 NR NR NR 

GACO WESTERN WAUKESHA WI N 53186 NR NR NR 

KITZINGER COOPERAGE CORP SAINT FRANCIS WI N 53235 0.0 6.6 6.6 

MILPORT ENTERPRISES INC MILWAUKEE WI N 53207 0.0 0.0 0.0 

TWINCO ROMAX MILWAUKEE WI N 53209 NR NR NR 

SEIDEL TANNING CORP MILWAUKEE WI N 53212 0.0 14.9 14.9 QUAD/GRAPHICS INC WEST ALLIS WI N 53214 NR NR NR 

MUTI‐PACK LLC MILWAUKEE WI N 53223 0.4 0.0 0.4 

KUBIN‐NICHOLSON CORP MILWAUKEE WI N 53224 9.1 0.0 9.1 BALL METAL BEVERAGE CONTAINER

CORP

MILWAUKEE WI N 53224 35.5 7.0 42.5 

FIRST SOURCE WORLDWIDE LLC

MILWAUKEE

MILWAUKEE WI N 53226 0.0 0.0 0.0 

CNH AMERICA LLC STURTEVANT WI N 53177 NR NR NR BALL CONTAINER LLC FORT ATKINSON WI N 53538 3.6 11.0 14.6 

RR DONNELLEY BARABOO DIV BARABOO WI N 53913 NR NR NR SENECA FOODS CORP BARABOO WI N 53913 0.0 29.8 29.8 

CHEMDESIGN PRODUCTS INC MARINETTE WI N 54143 0.0 0.0 0.0 

WISCONSIN ALUMINUM FOUNDRY COINC

MANITOWOC WI N 54220 NR NR NR 

SILGAN CONTAINERS

MANUFACTURING CORP

PLOVER WI Y 54467 10.8 40.0 50.8 

CROWN BEVERAGE PACKAGING LA CROSSE WI Y 54603 22.8 1.7 24.5 

TORO CO TOMAH WI N 54660 0.0 2.0 2.0 

TORO CO TOMAH WI N 54660 NR NR NR SILGAN CONTAINERS

MANUFACTURING CORP

MENOMONIE WI N 54751 1.5 5.8 7.3 

MULTICIRCUITS OSHKOSH WI N 54903 0.6 0.0 0.6 

Page 15 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

ALLIANCE INDUSTRIES WAUPACA WAUPACA WI N 54981 0.4 4.0 4.5 

UNIVAR USA INC LAKEVILLE LAKEVILLE MN N 55044 0.0 0.0 0.0 

CROWN FOOD PACKAGING OWATONNA MN Y 55060 29.3 87.7 117.1 

S B FOOT TANNING CO RED WING MN N 55066 0.0 22.8 22.8 

REXAM BEVERAGE CAN CO RE: EVA

STREET ST PAUL MN

SAINT PAUL MN Y 55107 14.0 79.5 93.5 

FORD MOTOR CO TWIN CITIESASSEMBLY PLANT

SAINT PAUL MN N 55116 0.4 3.0 3.4 

FLINT HILLS RESOURCES LP ROSEMOUNT MN N 55068 0.8 0.0 0.8 EDCO PRODUCTS INC HOPKINS MN N 55343 NR NR NR 

RRD MAPLE GROVE MAPLE GROVE MN N 55369 NR NR NR 

MEDALLION CABINETRY INC WACONIA MN N 55387 0.0 5.1 5.1 NORTHLAND ALUMINUM PRODUCTS INC

MINNEAPOLIS MN N 55416 NR NR NR 

BROWN PRINTING CO

WASECA MN N 56093 4.3 0.1 4.3 

MID CONTINENT CABINETRY COTTONWOOD MN N 56229 0.5 4.8 5.3 NAHAN PRINTING INC SAINT CLOUD MN N 56303 4.6 0.1 4.7 

SAPA EXTRUSIONS INC YANKTON SD N 57078 0.0 24.4 24.4 

BOBCAT CO (MELROE) GWINNER ND N 58040 NR NR NR 

ACME FINISHING CO INC ELK GROVE

VILLAGE

IL N 60007 1.4 5.4 6.8 

ROHM

& HAAS CHEMICALS LLC ELK GROVE

VILLAGE

IL N 60007 NR NR NR 

BECKER SPECIALTY CORP ELK GROVE

VILLAGE

IL N 60007 0.0 0.5 0.5 

IMS ENGINEERED PRODUCTS LLC DES PLAINES IL N 60016 NR NR NR GREENWICH INDUSTRIES LP CLARIN

DIV

LAKE BLUFF IL N 60044 0.1 5.0 5.1 

BROWN PRINTING CO WOODSTOCK IL N 60098 4.0 0.1 4.1 GE WATER

& PROCESS TECHNOLOGIES ADDISON IL N 60101 NR NR NR 

BALL AEROSOL

& SPECIALTY

CONTAINER INC

ELGIN IL N 60120 1.7 8.5 10.2 

UNIVERSAL CHEMICALS

& COATINGS

INC

ELGIN IL N 60123 NR NR NR 

WISMARQ CORP FRANKLIN PARK IL N 60131 NR NR NR 

WR MEADOWS INC HAMPSHIRE IL N 60140 NR NR NR 

LEHIGH PRESS CADILLAC (DBA LEHIGH

DIRECT DIVISION)

BROADVIEW IL N 60153 2.0 0.1 2.1 

SUN CHEMICAL CORP NORTHLAKE IL N 60164 NR NR NR 

SYCAMORE SYSTEMS LLC SYCAMORE IL N 60178 NR NR NR 

Page 16 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

SEYMOUR OF SYCAMORE INC SYCAMORE IL N 60178 NR NR NR 

KNS COMPANYS INC CAROL STREAM IL N 60188 0.5 2.0 2.5 

TMS MANUFACTURING ALSIP IL N 60803 NR NR NR DOW CHEMICAL JOLIET SITE CHANNAHON IL N 60410 0.0 0.0 0.0 

CHICAGO HEIGHTS STEEL CHICAGO HEIGHTS IL N 60411 6.3 25.1 31.4 

ALLIED TUBE

& CONDUIT CORP HARVEY IL N 60426 10.0 5.9 15.9 

INX INTERNATIONAL INK CO HOMEWOOD IL N 60430 0.0 0.1 0.1 

DOBER CHEMICAL CORP MIDLOTHIAN IL N 60445 0.0 0.0 0.0 SIGNODE BRIDGEVIEW IL N 60455 0.9 7.6 8.4 UNIVAR USA INC BEDFORD PARK IL N 60499 0.0 0.0 0.1 

UNIVAR USA INC 68TH ST BEDFORD PARK IL N 60501 0.0 0.0 0.0 

CROWN AEROSOL PACKAGING AURORA IL N 60504 7.9 1.0 8.9 

CHAMPION PACKAGING

&

DISTRIBUTING INC

WOODRIDGE IL N 60517 0.0 0.0 0.0 

LAKESIDE LITHOGRAPHY LLC CHICAGO IL N 60608 1.0 8.8 9.8 

EDSAL MANUFACTURING CO INC CHICAGO IL N 60609 0.0 25.7 25.7 REXAM BEVERAGE CAN CO RE :

CHICAGO PLANT

CHICAGO IL Y 60609 13.6 51.7 65.4 

CHICAGO STEEL CONTAINER CORP CHICAGO IL N 60623 1.3 5.9 7.2 

BWAY CORP CHICAGO IL N 60623 4.4 2.9 7.3 MEYER STEEL DRUM INC CHICAGO IL N 60623 1.1 9.1 10.2 

COLOR COMMUNICATIONS INC CHICAGO IL N 60624 1.4 5.3 6.7 SKOLNIK INDUSTRIES CHICAGO IL N 60632 NR NR NR GREIF PACKAGING LLC ALSIP IL N 60803 1.6 3.9 5.5 CROWN BEVERAGE PACKAGING BRADLEY IL Y 60915 17.1 51.4 68.6 

CHRYSLER BELVIDERE ASSEMBLYPLANT

BELVIDERE IL N 61008 0.1 1.1 1.2 

SIGNCRAFT SCREEN PRINT GALENA IL N 61036 NR NR NR 

SILGAN CONTAINERS

MANUFACTURING CORP

ROCHELLE IL N 61068 1.8 1.3 3.1 

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

ROCKFORD IL N 61104 0.0 0.0 0.0 

3M CO ‐ CORDOVA CORDOVA IL N 61242 0.3 0.0 0.3 

3M CO ‐ CORDOVA CORDOVA IL N 61242 NR NR NR 

JOHN DEERE HARVESTER WORKS EAST

MOLINE

EAST MOLINE IL N 61244 0.3 6.0 6.3 

TYSON FRESH MEATS INC JOSLIN IL HILLSDALE IL N 61257 0.0 0.0 0.0 

NATIONAL COATINGS INC GALESBURG IL N 61401 NR NR NR 

PEORIA DISPOSAL CO #1 PEORIA IL N 61615 NR NR NR 

CNH AMERICA LLC GOODFIELD IL N 61742 NR NR NR 

Page 17 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

CNH AMERICA LLC GOODFIELD IL N 61742 NR NR NR MASTERBRAND CABINETS INC ARTHUR IL N 61911 0.0 8.3 8.3 

RR DONNELLEY

& SONS CO MATTOON IL N 61938 NR NR NR 

MIDWEST METAL COATINGS GRANITE CITY IL N 62040 NR NR NR PRECOAT METALS GRANITE CITY IL N 62040 4.5 1.1 5.6 AFTON CHEMICAL CORP SAUGET IL N 62201 NR NR NR VEOLIA ES TECHNICAL SOLUTIONS LLC SAUGET IL N 62201 NR NR NR 

KNAPHEIDE MANUFACTURING CO QUINCY IL N 62305 0.1 13.0 13.1 QG LLC EFFINGHAM IL N 62401 6.2 0.0 6.2 METAL CONTAINER CORP ‐ ARNOLD

CAN PLANT

ARNOLD MO Y 63010 17.1 27.1 44.2 

TRILLA ST LOUIS CORP FENTON MO N 63026 NR NR NR 

CHRYSLER ST LOUIS NORTH ASSEMBLY

PLANT

FENTON MO N 63026 5.5 32.0 37.5 

UNIVAR USA INC METRO BLVD MARYLAND

HEIGHTS

MO N 63043 0.1 0.1 0.3 

BUCKEYE INTERNATIONAL INC MARYLAND

HEIGHTS

MO N 63043 0.1 1.8 1.9 

PLAZE INC PACIFIC MO N 63069 NR NR NR 

SCHAEFFER MANUFACTURING SAINT LOUIS MO N 63104 4.8 0.0 4.8 

U.S. POLYMERS ACCUREZ LLC SAINT LOUIS MO N 63111 0.0 0.0 0.0 

UNIVAR USA INC BERKELEY BERKELEY MO N 63134 0.1 0.1 0.3 

ELANTAS PDG INC SAINT LOUIS MO N 63147 0.0 0.1 0.1 

THE DIAL CORP

A SUBSIDIARY OF

HENKEL CONSUMER GOODS

SAINT LOUIS MO N 63147 NR NR NR 

SAF‐HOLLAND USA INC WARRENTON MO N 63383 NR NR NR 

GENERAL MOTORS WENTZVILLE

ASSEMBLY

WENTZVILLE MO N 63385 0.9 3.7 4.5 

GATES CORP POPLAR BLUFF MO N 63901 NR NR NR US ARMY LAKE CITY ARMY

AMMUNITION PLANT

INDEPENDENCE MO N 64051 1.4 3.3 4.7 

FORD MOTOR COMPANY‐‐KANSAS

CITY ASSEMBLY PLANT

CLAYCOMO MO Y 64119 2.3 39.5 41.8 

BALL METAL BEVERAGE CONTAINER

CORP

KANSAS CITY MO N 64120 4.2 0.1 4.2 

SILGAN CONTAINERS

MANUFACTURING CORP

SAINT JOSEPH MO N 64504 6.3 2.9 9.2 

VON HOFFMANN GRAPHICS INC OWENSVILLE MO N 65066 4.1 1.6 5.8 

HUTCHENS INDUSTRIES INCMANSFIELD FACILITY

MANSFIELD MO N 65704 NR NR NR 

Page 18 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

EFCO CORP MONETT MO Y 65708 1.2 28.1 29.2 HYDRO ALUMINUM NORTH AMERICA

INC

MONETT MO N 65708 NR NR NR 

SILGAN CONTAINERS

MANUFACTURING CORP

MOUNT VERNON MO N 65712 2.6 10.1 12.7 

3M CO ‐ SPRINGFIELD SPRINGFIELD MO N 65802 0.0 0.0 0.0 

3M CO ‐ SPRINGFIELD SPRINGFIELD MO N 65802 NR NR NR 

NAZDAR SHAWNEE SHAWNEE KS N 66227 1.6 3.8 5.4 PACKAGING DYNAMICS INC

BAGCRAFT/PAPERCON DIV

BAXTER SPRINGS KS N 66713 0.0 6.2 6.2 

LAFARGE MIDWEST INC (INCLDSYSTECH ENVIRONMENTAL)

FREDONIA KS N 66736 NR NR NR 

GATES CORP IOLA KS N 66749 NR NR NR 

GREIF INDUSTRIAL PACKAGING

&

SERVICES

WINFIELD KS N 67156 0.3 2.3 2.6 

THE COLEMAN CO INC WICHITA KS N 67219 NR NR NR CONOCOCPHILLIPS CO WICHITA

TERMINAL

WICHITA KS N 67219 NR NR NR 

SCHWAN'S GLOBAL SUPPLY CHAIN ‐ SALINA KS

SALINA KS N 67401 0.0 3.5 3.5 

VALMONT INDUSTRIES INC VALLEY NE N 68064 NR NR NR 

VEYANCE TECHNOLOGIES INC LINCOLN NE N 68504 NR NR NR 

KAWASAKI MOTORSMANUFACTURING CORP USA

LINCOLN NE N 68524 0.3 2.9 3.2 

NUCOR CORP ‐ VULCRAFT/NUCORCOLD FINISH DIV

NORFOLK NE N 68701 0.8 10.5 11.3 

TYSON FRESH MEATS INC DAKOTA CITY NE N 68731 NR NR NR 

AIR PRODUCTS PERFORMANCEMANUFACTURING INC

RESERVE LA N 70084 NR NR NR 

GREIF PACKAGING LLC NEW ORLEANS LA N 70123 2.7 4.2 6.9 CHAMPION TECHNOLOGIES INC BROUSSARD LA N 70518 NR NR NR 

BAYOU COS INC NEW IBERIA LA N 70560 NR NR NR NALCO CO SCOTT LA N 70583 NR NR NR 

BRENNTAG SOUTHWEST INC ST

GABRIEL

SAINT GABRIEL LA N 70776 0.0 0.0 0.0 

NOVOLYTE PERFORMANCEMATERIALS

ZACHARY LA N 70791 4.7 0.4 5.1 

ASHLAND DISTRIBUTION CO BATON ROUGE LA N 70815 0.2 0.0 0.2 

GMTG ‐ SHREVEPORT ASSEMBLY SHREVEPORT LA N 71129 0.1 6.0 6.1 

UNION TANK CAR ALEXANDRIA

MANUFACTURING FACILITY

ALEXANDRIA LA N 71303 0.0 0.1 0.1 

Page 19 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

BERENFIELD CONTAINERS SW LTD WHITE HALL AR N 71602 0.0 9.9 9.9 

WHEELING MACHINE PRODUCTS DIV

PINE BLUFF

PINE BLUFF AR N 71602 NR NR NR 

CLEAN HARBORS EL DORADO LLC EL DORADO AR N 71730 0.0 0.0 0.0 

CHAMPION TECHNOLOGIES INC MAGNOLIA AR N 71753 NR NR NR 

RINECO BENTON AR N 72015 0.0 0.0 0.0 

BRYCE CO LLC SEARCY AR N 72143 NR NR NR 

MAVERICK TUBE LLC BLYTHEVILLE AR N 72315 NR NR NR 

AMERIMAX COATED PRODUCTS HELENA AR N 72342 NR NR NR QG PRINTING II CORP JONESBORO AR N 72401 NR NR NR 

L A DARLING CO ‐ PIGGOTT ARFACILITY

PIGGOTT AR N 72454 0.2 14.2 14.4 

SUPERIOR INDUSTRIES

INTERNATIONAL ARKANSAS LLC

FAYETTEVILLE AR N 72701 NR NR NR 

SUPERIOR INDUSTRIESINTERNATIONAL ARKANSAS LLC

ROGERS AR N 72756 NR NR NR 

KAWNEER CO INC SPRINGDALE AR N 72764 4.8 5.3 10.1 GRAPHIC PACKAGING INTERNATIONAL

INC

FORT SMITH AR N 72916 NR NR NR 

DEXTER AXLE EL RENO OK N 73036 NR NR NR 

GEMINI COATINGS INC EL RENO OK N 73036 NR NR NR U.S. AIR FORCE TINKER AFB OK TINKER

A F B OK N 73145 1.6 4.2 5.8 

REXAM BEVERAGE CAN CO

RE:OKLAHOMA CITY PLANT

OKLAHOMA CITY OK Y 73179 5.0 28.5 33.5 

CLEAN HARBORS LONE MOUNTAINLLC LONE MOUNTAIN FACILITY

WAYNOKA OK N 73860 NR NR NR 

BRENNTAG SOUTHWEST INC SAND

SPRINGS

SAND SPRINGS OK N 74063 NR NR NR 

NALCO CO TULSA PLANT 102 TULSA OK N 74131 0.0 0.0 0.0 

BRAINERD CHEMICAL CO INC TULSA OK N 74147 NR NR NR 

AIR SYSTEM COMPONENTS LP PONCA CITY OK N 74601 0.2 23.6 23.9 

MOBIL CHEMICAL CO SHAWNEE OK N 74804 0.4 23.0 23.4 ELECTRO PLATE CIRCUITRY INC CARROLLTON TX N 75006 NR NR NR 

GLIDDEN CO CARROLLTON TX N 75006 NR NR NR A BRITE CO GARLAND TX N 75041 NR NR NR 

BENJAMIN MOORE

& CO ‐ DALLAS MESQUITE TX N 75149 NR NR NR 

OLDCASTLE BUILDING ENVELOPE ‐ 

TEXAS FACILITY

TERRELL TX N 75160 2.8 14.9 17.7 

MAGNABLEND INC‐CENTRAL PLANT WAXAHACHIE TX N 75165 0.0 0.0 0.0 UNITED STATES ALUMINUM CORP WAXAHACHIE TX N 75165 0.4 0.0 0.4 

Page 20 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

INTERNATIONAL EXTRUSION CORP

TEXAS

WAXAHACHIE TX N 75165 0.0 0.2 0.2 

MAXIM INTEGRATED PRODUCTS DALLAS TX N 75244 0.0 0.9 0.9 

SILGAN CAN CO PARIS TX N 75460 4.9 3.2 8.2 

ALUMAX MILL PRODUCTS INC TEXARKANA TX N 75501 0.0 0.6 0.6 

BRENNTAG SOUTHWEST INC LONG

VIEW

LONGVIEW TX N 75604 NR NR NR 

REXAM BEVERAGE CAN CO LONGVIEW

FACILITY

LONGVIEW TX Y 75604 17.7 49.3 67.0 

EASTMAN CHEMICAL CO TEXASOPERATIONS

LONGVIEW TX N 75602 12.0 1.8 13.8 

ROBROY INDUSTRIES TEXAS LP GILMER TX N 75644 NR NR NR 

BAKER PETROLITE KILGORE BLEND

PLANT

KILGORE TX N 75662 NR NR NR 

CHAMPION TECHNOLOGIES INC KILGORE TX N 75662 0.2 0.0 0.2 

CHAMPION TECHNOLOGIES INC LONGVIEW TX N 75662 NR NR NR 

CLEVELAND STEEL CONTAINER ‐ 

KILGORE

KILGORE TX N 75662 NR NR NR 

NUCOR VULCRAFT GROUP ‐ 

GRAPELAND DIV

GRAPELAND TX N 75844 0.2 16.3 16.4 

SHIELDCOAT TECHNOLOGIES INC (DBA

CYBERSHIELD OF TEXAS)

LUFKIN TX N 75904 7.1 0.0 7.1 

CHAMPION TECHNOLOGIES INC CRESSON TX N 76035 0.1 0.0 0.1 

CHEMGUARD INC MANSFIELD TX N 76063 NR NR NR 

BALL METAL BEVERAGE CONTAINER

CORP

FORT WORTH TX N 76140 5.5 7.5 13.0 

CARRY‐ON TRAILER CORP MEXIA TX N 76667 NR NR NR 

TEXAS TILE MANUFACTURING LLC HOUSTON TX N 77007 0.0 0.7 0.7 

PRECOAT METALS HOUSTON TX N 77015 4.8 0.3 5.1 NOV TUBOSCOPE WEST LITTLE YORK

COATING

HOUSTON TX N 77041 0.1 1.4 1.5 

UNIVAR USA INC HOUSTON FM 529 HOUSTON TX N 77041 NR NR NR 

RR DONNELLEY‐WETMORE PLANT HOUSTON TX N 77043 NR NR NR BRENNTAG SOUTHWEST INC HOUS

TON

HOUSTON TX N 77047 0.0 0.0 0.0 

KIK (HOUSTON) INC HOUSTON TX N 77054 2.3 0.0 2.3 

INTERCOASTAL PAINT CO INC HOUSTON TX N 77060 NR NR NR 

PPG ARCHITECURAL COATINGS

HOUSTON

HOUSTON TX N 77092 NR NR NR 

Page 21 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

MAVERICK TUBE LLC DBA

TENARISCONROE

CONROE TX N 77301 NR NR NR 

BALL METAL BEVERAGE CONTAINER

CORP

CONROE TX N 77303 14.0 4.6 18.6 

CROWN BEVERAGE PACKAGING CONROE TX N 77303 29.3 4.8 34.1 

AMERICAN COATINGS INC TOMBALL TX N 77375 0.0 0.0 0.0 

CROWN BEVERAGE PACKAGING SUGAR LAND TX N 77478 28.0 4.2 32.2 

NALCO CO PLANT 106 SUGAR LAND TX N 77478 NR NR NR 

MEMC PASADENA INC PASADENA TX N 77503 12.7 8.0 20.7 EQUISTAR CHEMICALS BAYPORT

CHEMICALS PLANT

PASADENA TX N 77507 6.8 0.0 6.8 

CHEMICALS INC BAYTOWN TX N 77520 0.1 0.0 0.1 

KMCO CROSBY PLANT CROSBY TX N 77532 NR NR NR 

DELTA HOUSTON DEER PARK TX N 77536 0.0 0.0 0.0 

CLEAN HARBORS DEER PARK LLC LA PORTE TX N 77571 NR NR NR 

CHAMPION TECHNOLOGIES INC FRESNO TX N 77545 NR NR NR 

GREIF PACKAGING LLC LA PORTE TX N 77571 4.1 0.1 4.2 

GREIF INDUSTRIAL PACKAGING

&

SERVICES LLC

LA PORTE TX N 77571 0.6 0.0 0.6 

MARATHON PETROLEUM CO LLC TEXAS CITY TX N 77590 NR NR NR 

INVISTA SARL ‐ ORANGE SITE ORANGE TX N 77630 NR NR NR 

ISP SYNTHETIC ELASTOMERS LP PORT NECHES TX N 77651 NR NR NR 

TOYO INK AMERICA LLC BRYAN TX N 77807 NR NR NR 

NOV TUBOSCOPE NAVASOTA NAVASOTA TX N 77868 0.8 0.3 1.1 

UNION CARBIDE CORP SEADRIFTPLANT

SEADRIFT TX N 77983 13.9 3.1 17.0 

CLEARWATER INTERNATIONAL LLC ELMENDORF TX N 78112 0.0 0.0 0.0 

TOYOTA MOTOR MANUFACTURING

TEX AS INC

SAN ANTONIO TX N 78264 5.2 3.4 8.6 

US ECOLOGY TEXAS INC ROBSTOWN TX N 78380 0.0 0.0 0.0 

CHAMPION TECHNOLOGIES INC CORPUS CHRISTI TX N 78405 0.1 0.0 0.1 

TYSON FRESH MEATS INC AMARILLO TX N 79108 0.1 0.0 0.1 

CATALYST OILFIELD SERVICES LLC GARDENDALE TX N 79758 NR NR NR 

CHAMPION TECHNOLOGIES INC ODESSA TX N 79762 NR NR NR 

UNIVAR USA INC HOUSTON HOUSTON TX N 77061 0.0 0.0 0.0 

NALCO CO ‐ ODESSA PLANT 114 ODESSA TX N 79765 0.0 0.1 0.1 

KBP COIL COATERS INC DENVER CO N 80216 0.0 0.0 0.0 UNIVAR USA INC DENVER DENVER CO N 80216 0.0 0.0 0.0 

ROCKY MOUNTAIN METAL

CONTAINER

GOLDEN CO N 80401 30.5 6.0 36.5 

Page 22 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

BALL METAL BEVERAGE CONTAINER

CORP

GOLDEN CO N 80403 21.0 10.5 31.5 

CIRCLE GRAPHICS INC LONGMONT CO N 80501 3.1 1.9 5.0 

METAL CONTAINER CORPORTION ‐ 

WINDSOR CAN PLANT

WINDSOR CO Y 80550 15.1 42.4 57.5 

DPIX LLC COLORADO

SPRINGS

CO N 80916 NR NR NR 

COORSTEK GRAND JUNCTION CO N 81505 NR NR NR 

SINCLAIR WYOMING REFINING CO SINCLAIR WY N 82334 0.0 0.0 0.0 

CROWN BEVERAGE PACKAGING WORLAND WY N 82401 11.1 33.4 44.5 

ASHLAND DISTRIBUTION CO CLEARFIELD UT N 84016 0.0 0.0 0.0 

U.S. AIR FORCE OGDEN AIR LOGISTICS

CENTER

HILL AFB UT N 84056 0.9 0.7 1.6 

TTM TECHNOLOGIES INC LOGAN UT N 84321 0.1 1.1 1.2 

REXAM BEVERAGE CAN CO PHOENIX

FACILITY

PHOENIX AZ Y 85043 5.2 34.4 39.6 

PROCLEAN OF ARIZONA INC PHOENIX AZ N 85043 0.0 0.1 0.1 SOUTHWEST DISTRIBUTING CO MESA AZ N 85210 NR NR NR 

ASHLAND INC ‐ CHANDLER CHANDLER AZ N 85226 0.1 0.0 0.2 

WR MEADOWS OF ARIZONA INC GOODYEAR AZ N 85338 NR NR NR US MARINE CORPS AIR STATION YUMA YUMA AZ N 85369 0.1 0.0 0.1 

SHERWIN‐WILLIAMS CO FERNLEY NV N 89408 0.0 0.0 0.0 

CARRY‐ON TRAILER CORP WINNEMUCCA NV N 89445 NR NR NR 

PRO LINE PRINTING / RR DONNELLEY RENO NV N 89512 1.5 0.2 1.7 

ENGINEERED POLYMER SOLUTIONS

INC

CITY OF

COMMERCE

CA N 90040 0.0 0.0 0.0 

NORMAN FOX

& CO VERNON CA N 90058 0.0 0.0 0.0 

HEXION SPECIALTY CHEMICALS INC LYNWOOD CA N 90262 0.0 0.0 0.0 

BALL METAL BEVERAGE CONTAINER

CORP

TORRANCE CA N 90503 31.0 2.7 33.7 

EXXONMOBIL OIL CORP ‐ TORRANCEREFINERY

TORRANCE CA N 90509 NR NR NR 

OAKITE PRODUCTS INC (AKACHEMETALL OAKITE)

LA MIRADA CA N 90638 NR NR NR 

TREND OFFSET PRINTING SERVICES

INC

LOS ALAMITOS CA N 90720 1.8 0.1 1.9 

ARDAGH METAL PACKAGING USA INC TERMINAL ISLAND CA N 90731 6.2 0.6 6.7 

Page 23 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

US DOD DFSP SAN PEDRO SAN PEDRO CA N 90731 NR NR NR 

SANYO SOLAR (USA) LLC CARSON CA N 90745 0.0 8.5 8.5 WESTERN TUBE

& CONDUIT CORP LONG BEACH CA N 90810 NR NR NR 

REXAM BEVERAGE CAN CO

CHATSWORTH FACILITY

CHATSWORTH CA Y 91311 14.3 40.3 54.6 

REICHHOLD INC ‐ AZUSA PLANT AZUSA CA N 91702 NR NR NR 

WESTERN METAL DECORATING CO RANCHO

CUCAMONGA

CA N 91730 NR NR NR 

CARDINAL INDUSTRIAL FINISHES SOUTH EL MONTE CA N 91733 0.0 0.0 0.1 

METAL CONTAINER CORP ‐ MIRALOMA CAN PLANT

MIRA LOMA CA N 91752 29.0 3.8 32.8 

HENKEL ONTARIO ONTARIO CA N 91761 0.0 0.0 0.0 

MACDERMID PRINTING SOLUTIONS SAN MARCOS CA N 92078 0.0 2.1 2.1 

SDC TECHNOLOGIES INC IRVINE CA N 92618 NR NR NR 

BEHR PROCESS CORP SANTA ANA CA N 92704 0.0 0.0 0.0 

ARLON INC ADHESIVES

& FILMS DIV SANTA ANA CA N 92704 0.0 0.0 0.0 

ARLON GRAPHICS LLC SANTA ANA CA N 92704 NR NR NR 

BAKER PETROLITE BAKERSFIELD CA N 93308 0.0 0.0 0.0 GE WATER

& PROCESS TECHNOLOGIES

‐ BAKERSFIELD

BAKERSFIELD CA N 93308 NR NR NR 

KELLY‐MOORE PAINT CO INC SAN CARLOS CA N 94070 0.0 0.0 0.0 

BALL METAL BEVERAGE CONTAINER

CORP

FAIRFIELD CA N 94533 12.5 19.0 31.5 

REXAM BEVERAGE CAN CO RE:

FAIRFIELD PLANT

FAIRFIELD CA Y 94533 5.5 8.5 14.0 

NEW UNITED MOTOR

MANUFACTURING INC

FREMONT CA N 94538 29.7 7.4 37.1 

UNIVAR USA INC ‐ SAN JOSE SAN JOSE CA N 95131 0.0 0.0 0.0 

ECOLAB INC SAN JOSE CA N 95133 0.0 0.0 0.0 

GREIF PACKAGING LLC MERCED CA N 95348 6.5 1.1 7.6 

BALL METAL FOOD CONTAINER CORP OAKDALE CA N 95361 0.8 4.7 5.4 

SILGAN CONTAINER MANUFACTURING

CORP

RIVERBANK CA N 95367 0.2 3.9 4.1 

INX DIGITAL INK CO DIXON CA N 95620 4.7 0.0 4.7 

HB FULLER ROSEVILLE CA N 95678 0.0 0.3 0.3 SACRAMENTO‐ CAMPBELL SOUPSUPPLY CO

SACRAMENTO CA N 95824 NR NR NR 

Page 24 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

2009 

Facility City State Completed Survey Zip Code Fugitive Air Emissions (tpy) Point Source Air Emissions (tpy) Total Air Emissions (tpy) Fug

Em

SILGAN CAN CO SACRAMENTO CA N 95824 4.9 0.4 5.3 

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

SACRAMENTO CA N 95826 0.0 0.0 0.0 

BALL METAL BEVERAGE CONTAINER

CORP

KAPOLEI HI N 96707 2.2 10.5 12.7 

IMPERIAL PAINT CO INC PORTLAND OR N 97210 NR NR NR 

UNIVAR USA INC PORTLAND OR N 97210 NR NR NR 

TARR ACQUISITION LLC PORTLAND OR N 97227 0.0 0.0 0.0 

FORMULA CORP AUBURN WA N 98002 NR NR NR REXAM BEVERAGE CAN CO KENT WA

FACILITY

KENT WA Y 98032 13.2 74.8 88.0 

BOEING COMMERCIAL AIRPLANEGROUP ‐ EVERETT

EVERETT WA N 98204 1.6 14.0 15.6 

EMERALD SERVICES INC TACOMA WA N 98421 NR NR NR 

CROWN BEVERAGE PACKAGING OLYMPIA WA Y 98501 17.1 51.3 68.4 

US DOD USAF JOINT BASE

ELMENDORF‐RICHARDSON

ELMENDORF AFB AK N 99506 NR NR NR 

Page 25 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

HEWLETT‐PACKARD CARIBE BV SITE AGUADILLA PR N 00605

CROWN BEVERAGE PACKAGING CAROLINA PR N 00985

DU PONT ELECTRONICS MICROCIRCU

ITS INDUSTRIES LTD

MANATI PR N 00674

HOVENSA LLC CHRISTIANSTED V Isl N 00820

VERTIS INC RNS SPRINGFIELD DIV EAST

LONGMEADOW

MA N 01028

SHIELD PACKAGING CO INC DUDLEY MA N 01571

POLARTEC LLC LAWRENCE MA N 01841

KEY POLYMER LAWRENCE MA N 01843

CROWN BEVERAGE PACKAGING LAWRENCE MA Y 01843

VALSPAR SAMUEL CABOT DIV NEWBURYPORT MA N 01950

MANN DISTRIBUTION WARWICK RI N 02886

TACO INC ‐ CRANSTON CRANSTON RI N 02920

EFI / INKWARE MEREDITH NH N 03253

HENKEL CORP SEABROOK NH N 03874

S D WARREN CO WESTBROOK ME N 04098

VERSO PAPER BUCKSPORT MILL BUCKSPORT ME N 4416

PRIME TANNING CO ‐ HARTLAND HARTLAND ME N 04943

STANLEY WORKS HAND TOOLS DIV NEW BRITAIN CT N 06052

CONOCOPHILLIPS CO TREMLEY POINT

TERMINAL

LINDEN NJ N 07036

SAFETY‐KLEEN SYSTEMS INC LINDEN NJ N 07036

MAUSER CORP WOODBRIDGE NJ N 07095

BENJAMIN MOORE

& CO ‐ NEWARK NEWARK NJ N 07105

DELEET MERCHANDISING NEWARK NJ N 07105

ACTEGA RADCURE INC WAYNE NJ N 07470

BASF CORP BELVIDERE NJ N 07823

DUPONT CHAMBERS WORKS DEEPWATER NJ N 08023CALLAHAN CHEMICAL CO PALMYRA NJ N 08065

SILGAN CONTAINERS

MANUFACTURING CORP

EDISON NJ N 08817

ENGLERT INC PERTH AMBOY NJ N 08861

AROMATIC TECHNOLOGIES INC SOMERVILLE NJ N 08876

BALL METAL BEVERAGE CONTAINER

CORP

MIDDLETOWN NY Y 10940

BASF CORP EAST SETAUKET NY N 11733

DISC GRAPHICS HAUPPAUGE NY N 11788

SURPASS CHEMICAL CO INC ALBANY NY N 12204

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default 

8.7 34 0.905 

Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default 

15 122 0.98

Default Default Default Default Default Default Default Default Default 

Page 26 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

METAL CONTAINER CORP ‐ NEWBURGH CAN PLANT

NEW WINDSOR NY Y 12553

BALL METAL BEVERAGE CONTAINER

CORP

SARATOGASPRINGS

NY Y 12866

QUAD/GRAPHICS INC SARATOGA

SPRINGS

NY N 12866

FIBERMARK NORTH AMERICA INC LOWVILLE NY N 13367

US DOD DFSP VERONA VERONA NY N 13478

WHITING DOOR MANUFACTURING

CORP

AKRON NY N 14001

ASHLAND DISTRIBUTION TONAWANDA NY N 14150

SENECA FOODS CORP CAN PLANT MARION NY N 14505

HAMMER PACKAGING CORP WEST HENRIETTA NY N 14586

TRI VULCRAFT OF NEW YORK INC CHEMUNG NY N 14825

UNIVAR USA INC ‐ BUNOLA BRANC H BUNOLA PA N 15020

USS ‐ CLAIRTON PLANT CLAIRTON PA N 15025

CLEARWATER INTERNATIONAL LLC LEETSDALE PA N 15056

SEQUA COATINGS CORP PRECOAT

METALS DIV

MC KEESPORT PA N 15132

PPG INDUSTRIES,INC‐SPRINGDALE

COMPLEX

SPRINGDALE PA N 15144

ALLEGHENY PETROLEUM PRODUCTS

CO

WILMERDING PA N 15148

BEDFORD MATERIALS CO INC MANNS CHOICE PA N 15550

NALCO CO ELLWOOD CITY PA N 16117

JAMESTOWN COATINGTECHNOLOGIES

JAMESTOWN PA N 16134

INTERSTATE CHEMICAL CO INC HERMITAGE PA N 16148

BERENFIELD CONTAINERS INC CLARENDON PA N 16313

FRANKLIN INVESTMENT CORP FRANKLIN PA N 16323

ZURN INDUSTRIES LLC ERIE PA N 16502

AMES TRUE TEMPER INC HARRISBURG PA N 17104

CROWN FOOD PACKAGING HANOVER PA N 17331

NEW YORK WIRE HANOVER PA N 17331

AMERICAN COLOR GRAPHICS INC YORK PA N 17404

CP CONVERTERS INC YORK PA N 17402

RR DONNELLEY LANCASTER WEST LANCASTER PA N 17601

RR DONNELLEY LANCASTER EAST LANCASTER PA N 17601

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

12.192 73.152 0.87

20 66 1

Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default 

Page 27 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

ARMSTRONG WORLD INDUSTRIESLANCASTER PLANT

LANCASTER PA N 17603

BEHR PROCESS CORP ALLENTOWN ALLENTOWN PA N 18106

MASCO RETAIL CABINET GROUP

SAYRE PENNSYLVANIA PLANT

SAYRE PA N 18840

DUPONT TOWANDA PLANT TOWANDA PA N 18848CLEVELAND STEEL CONTAINER CORP QUAKERTOWN PA N 18951

SUPERPAC INC SOUTHAMPTON PA N 18966

GREIF PACKAGING LLC WARMINSTER PA N 18974

GEORGE S COYNE CHEMICAL CO INC CROYDON PA N 19021UNIVAR USA INC MORRISVILLE

BRANCH

MORRISVILLE PA N 19067

CARDONE INDUSTRIES PHILADELPHIA PA N 19120SUN CHEMICAL CORP PHILADELPHIA PA N 19132

CAN CORP OF AMERICA INC BLANDON PA N 19510

HIRSH INDUSTRIES INC DOVER DE N 19904

INDEPENDENT CAN CO BELCAMP MD N 21017

CROWN FOOD PACKAGING BALTIMORE MD N 21221

TNEMEC CO INC BALTIMORE MD N 21222

RUST‐OLEUM CORP IN MD WILLIAMSPORT MD N 21795

PHOENIX COLOR CORP HAGERSTOWN MD N 21742

VERTIS MANASSAS VA N 20109CARRY‐ON TRAILER CORP MONTROSS VA N 22520

QG LLC WINCHESTER VIRGINIA WINCHESTER VA N 22603DUPONT FRONT ROYAL PLANT FRONT ROYAL VA N 22630

FISHER SCIENTIFIC INTERNATIONAL

MTN DIAGNOSTICS PLANT

MIDDLETOWN VA N 22645

RR DONNELLEY HARRISONBURG VA Y 22802

MERCK SHARP

& DOHME CORP ELKTON VI N 22827

SOLITE LLC ARVONIA VI N 23004

BALL METAL BEVERAGE CONTAINER

CORP

WILLIAMSBURG VA Y 23185

CADMUS SPECIALTY PUBLICATIONS RICHMOND VI N 23228

BOEHRINGER INGELHEIM CHEMICALS

INC

PETERSBURG VA N 23805

VOLVO TRUCKS NORTH AMERICA DUBLIN VI N 24084

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default

11.2 45 Default 

Default Default Default Default Default Default 

13.1318 96 0.9656

Default Default DefaultDefault Default DefaultDefault Default Default 

Page 28 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

NEW MILLENNIUM BUILDING

SYSTEMS

SALEM VI N 24153

VAUGHAN‐BASSETT FURNITURE COGALAX

GALAX VA N 24333

ROYAL MOULDINGS LTD; MARION

VIRGINIA

MARION VA N 24354

GROTTOES PLASTICS PLANT GROTTOES VI N 24441

DAVIS‐FROST INC LYNCHBURG VA N 24506BALL METAL FOOD CONTAINER CORP WEIRTON WV N 26062

CROWN CORK

& SEAL CO (USA) INC

CROWN CLOSURE DIV

WEIRTON WV Y 26062

PRECOAT METALS WEIRTON WV N 26062JELD‐WEN CRAIGSVILLE WV N 26205

REXAM BEVERAGE CAN CO RE:

WINSTON SALEM PLANT

WINSTON‐SALEM NC Y 27107

APOLLO CHEMICAL BURLINGTON NC N 27215

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

HIGH POINT NC N 27261

THOMAS BUILT BUSES INC HIGH POINT NC N 27263

UNIVAR USA INC JAMESTOWN

FACILITY

JAMESTOWN NC N 27282

MEADWESTVACO CONSUMERPACKAGING GROUP LLC

MEBANE NC N 27302

BALL METAL BEVERAGE CONTAINER

CORP

REIDSVILLE NC Y 27320

CREE INC DURHAM NC N 27703

AIR SYSTEM COMPONENTS LP TARBORO NC N 27886

PARKER HANNIFIN TECH SEAL DIV WILSON NC N 27893

WIX FILTRATION CORP ‐ ALLEN PLANT GASTONIA NC N 28052

BERENFIELD CONTAINERS SE LTD HARRISBURG NC N 28075

CLARIANT CORP ‐ MOUNT HOLLY

WEST PLANT

MOUNT HOLLY NC N 28120

QUANTUM COATINGS INC CHARLOTTE NC N 28273

COMMERCIAL MERCHANDISING CORP CHARLOTTE NC N 28273

DUPONT FAYETTEVILLE PLANT FAYETTEVILLE NC N 28306

SILGAN CAN CO MAXTON NC N 28364

AVERY DENNISON ‐ IBMD LENOIR LENOIR NC N 28645

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default

11 12 1

Default Default Default Default Default Default 

14 75 0.95

Default Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default

16 137 1

Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default 

Page 29 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

STATESVILLE NC N 28625

REXAM BEVERAGE CAN CO RE:

BISHOPVILLE SC FACILITY

BISHOPVILLE SC Y 29010

HOLCIM (US) INC HOLLY HILL PLANT HOLLY HILL SC N 29059

SAFETY‐KLEEN SYSTEMS INC LEXINGTON SC N 29073HUSQVARNA CONSUMER OUTDOOR

PRODUCTS

ORANGEBURG SC N 29116

HENKEL ENOREE SC N 29335

NUCOR CORP VULCRAFT DIV FLORENCE SC N 29501

CROWN BEVERAGE PACKAGING CHERAW SC N 29520

AVX CORP CONWAY CONWAY SC N 29526

AVX CORP MYRTLE BEACH MYRTLE BEACH SC Y 29577

DIVERSIFIED COATING SYSTEMS INC GREENVILLE SC N 29605

OWENS CORNING VETROTEX LLC STARR SC N 29684

FUJIFILM MANUFACTURING US

A INC GREENWOOD SC N 29649

BMW MANUFACTURING CO LLC GREER SC Y 29651

COGNIS CORP MAULDIN PLANT MAULDIN SC N 29662

SCHNEIDER ELECTRIC SENECA SC N 29678OMNOVA SOLUTIONS INC CHESTER SC N 29706

AGY AIKEN LLC AIKEN SC N 29801

DECOSTAR INDUSTRIES INC CARROLLTON GA N 30117

BALL CONTAINER LLC ROME CAN

PLANT

ROME GA Y 30161

HB FULLER COVINGTON GA N 30014BEHR PROCESS CORP ATLANTA MC DONOUGH GA N 30253ECOLAB INC MC DONOUGH GA N 30253

ECOLAB INC MC DONOUGH GA N 30253

BRIGGS

& STRATTON POWER

PRODUCTS MCDONOUGHOPERATIONS

MC DONOUGH GA N 30253

TOPPAN INTERAMERICA INC MC DONOUGH GA N 30253

QUAD/GRAPHICS INC THE ROCK GA N 30285

FLINT GROUP NORTH AMERICA ATLANTA GA N 30339

UNIVAR USA INC DORAVILLE FACILITY DORAVILLE GA N 30362

CARRY‐ON TRAILER CORP LAVONIA GA N 30553POWER PARTNERS INC ATHENS GA N 30607

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default

11.5824 11 0.9987

Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default 

5.5 38.099998 0.75 

Default Default DefaultDefault Default Default Default Default Default

18.3 270 0.88 

Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default 

12.192 54.864 0.86

Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default 

Page 30 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

BEAULIEU OF AMERICA PLANT 560‐

MODEL

DALTON GA N 30721

FIBRO CHEM LLC DALTON GA N 30720

YKK AP AMERICA INC DUBLIN GA N 31021

ZSCHIMMER

& SCHWARZ MILLEDGEVILLE GA N 31061

U.S. AIR FORCE ROBINS AFB GA ROBINS AFB GA N 31098

BWAY CORP HOMERVILLE GA N 31634KIA MOTORS MANUFACTURING OF

GEORGIA

WEST POINT GA N 31833

COMPLEMENTARY COATINGS CORP EDGEWATER FL N 32132

METAL CONTAINER CORP ‐  JACKSONVILLE CAN PLANT

JACKSONVILLE FL N 32254

RENESSENZ LLC JACKSONVILLE JACKSONVILLE FL N 32208

U.S. NAVY NAVAL AIR STATION

JACKSONVILLE

JACKSONVILLE FL N 32212

UNIVAR USA INC JACKSONVILLE FA

CILITY

JACKSONVILLE FL N 32254

CROWN FOOD PACKAGING WINTER GARDEN FL N 34787

SPIRALKOTE FLEXIBLE PACKAGING ORLANDO FL N 32837SOUTH FLORIDA MATERIALS CORPDBA VECENERGY‐PORT EVERGLADES

FT LAUDERDALE FL N 33316

METAL INDUSTRIES INC ‐ BUSHNELL BUSHNELL FL N 33513

BALL METAL BEVERAGE CONTAINER

CORP

TAMPA FL N 33617

UNIVAR USA INC TAMPA FACILITY TAMPA FL N 33619

VERTIS COMMUNICATIONS TAMPA FL N 33611

GSP MARKETING TECHNOLOGIES CLEARWATER FL N 33760

HEXION SPECIALTY CHEMICALS INC LAKELAND FL N 33801

KEYMARK CORP OF FLORIDA LAKELAND FL N 33810

SEWELL PRODUCTS OF FLORIDA LLC AUBURNDALE FL N 33823ONESOURCE COIL COATERS CLEARWATER FL N 33760DYCO PAINTS INC CLEARWATER FL N 33760

M&B HANGERS LEEDS AL N 35094

HONDA MANUFACTURING OF

ALABAMA LLC

LINCOLN AL N 35096

AKZO NOBEL COATINGS INC BIRMINGHAM AL N 35234

ASHLAND DISTRIBUTION BIRMINGHAM AL N 35234

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default 

Page 31 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

MICHELIN NORTH AMERICA INC TUSCALOOSA AL N 35401

RECTICEL INTERIORS NORTH AMERICA

LLC

TUSCALOOSA AL N 35401

MERCEDES‐BENZ US INTERNATIONAL

INC

VANCE AL N 35490

3M CO ‐ GUIN GUIN AL N 35563

3M CO ‐ GUIN GUIN AL N 35563ITW SEXTON INC DECATUR AL N 35603

HART

& COOLEY INC HUNTSVILLE AL N 35811

MUELLER CO ALBERTVILLE AL N 35950NUCOR CORP VULCRAFT DIV FORT PAYNE AL N 35967

FLINT GROUP NORTH AMERICA CORP ANNISTON AL N 36207

DUNBARTON CORP REDIFRAME DIV DOTHAN AL N 36303

RUSKIN CO GENEVA AL N 36340

INTERNATIONAL PAPER PINE HILL MILL PINE HILL AL N 36769

STATE INDUSTRIES INC ASHLAND CITY TN N 37015

WORLDCOLOR CLARKSVILLE TN N 37040SANFORD LP SHELBYVILLE TN N 37160

NISSAN NA INC SMYRNA

MANUFACTURING PLANT

SMYRNA TN N 37167

GM SPRING HILL MANUFACTURING SPRING HILL TN N 37174

QUAD GRAPHICS NASHVILLE NASHVILLE TN N 37207

ASHLAND DISTRIBUTION NASHVILLE TN N 37209

NASHVILLE WIRE PRODUCTS NASHVILLE TN N 37218MAYTAG CORP CLEVELAND COOKING

PRODUCTS PLANT 1

CLEVELAND TN N 37311

LA‐Z‐BOY TENNESSEE DAYTON TN N 37321

BATESVILLE MANUFACTURING INC MANCHESTER TN N 37355

SANFORD LP LIQUID

MANUFACTURING

& TECHNOLOGY

CENTER

MANCHESTER TN N 37355

ALSTOM POWER INC CHATTANOOGA

BOILERS

CHATTANOOGA TN N 37402

VOLKSWAGEN GROUP OF AMERICA

CHATTANOOGA OPERATIONS LLC

CHATTANOOGA TN N 37416

STAR BUILDING SYSTEMS ELIZABETHTON TN N 37643

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default 

Page 32 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

ARMSTRONG HARDWOOD FLOORING

CO

ONEIDA TN N 37841

VESTAL MANUFACTURING

ENTERPRISES INC

SWEETWATER TN N 37874

ROHM

& HAAS CHEMICALS LLC

KNOXVILLE SITE

KNOXVILLE TN N 37921

TEKNOR APEX TENNESSEE CO (AKA

HAYWOOD CO)

BROWNSVILLE TN N 38012

EXCEL POLYMERS LLC DYERSBURG TN N 38024WORLDCOLOR ‐ DYERSBURG DIV DYERSBURG TN N 38024

JOHNSON BRYCE INC MEMPHIS TN N 38109

VALERO REFINING CO ‐ TENNESSEE

LLC

MEMPHIS TN N 38109

ASHLAND DISTRIBUTION MEMPHIS TN N 38113SONOCO PHOENIX ‐ PRESIDENTS

ISLAND

MEMPHIS TN N 38113

W

M BARR

& CO MEMPHIS TN N 38113

BRYCE CO LLC MEMPHIS TN N 38118

UNIVAR USA INC MEMPHIS MEMPHIS TN N 38118

WM BARR

& CO INC MEMPHIS TN N 38113

GOODYEAR TIRE

& RUBBER CO UNION CITY TN N 38261

KOHLER CO UNION CITY TN N 38261

CECO DOOR PRODUCTS MILAN TN N 38358

VAN CAN CO TRENTON TN N 38382

CROWN BEVERAGE PACKAGING BATESVILLE MS N 38606

KAWNEER CO INC HERNANDO MS N 38632

VALVOLINE HERNANDO MS N 38632REXAM BEVERAGE CAN CO OLIVE

BRANCH FACILITY

OLIVE BRANCH MS Y 38654

QUEBECOR WORLD OLIVE BRANCH MS N 38654SHERWIN‐WILLIAMS CO OLIVE BRANCH MS N 38654

HUNTER DOUGLAS TUPELO CENTER SHANNON MS N 38868

NISSAN NORTH AMERICA INC CANTON

MS

CANTON MS N 39046

ANDERSON TULLY LUMBER CO

WALTERSVILLE LUMBER MILL

VICKSBURG MS N 39181

METAL COATERS JACKSON MS N 39272

PRECOAT METALS JACKSON MS N 39272

ESCO CORP NEWTON MS N 39345

CHEVRON PRODUCTS COPASCAGOULA REFINERY

PASCAGOULA MS N 39581

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default 

12 100 0.95

Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default

Page 33 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

INOAC PACKAGING GROUP BARDSTOWN KY N 40004KELLEY TECHNICAL COATINGS INC LOUISVILLE KY N 40210

ASHLAND DISTRIBUTION LOUISVILLE KY N 40211

FORD LOUISVILLE ASSEMBLY LOUISVILLE KY N 40213

KELLEY TECHNICAL COATINGS INC LOUISVILLE KY N 40210

FORD MOTOR CO KENTUCKY TRUCK

PLANT

LOUISVILLE KY Y 40241

TOYOTA MOTOR MANUFACTURING

KENTUCKY INC

GEORGETOWN KY N 40324

MODINE MANUFACTURING CO INC HARRODSBURG KY N 40330

GUARDIAN AUTOMOTIVE ‐ 

MOREHEAD PLANT

MOREHEAD KY N 40351

CENTRAL MOTOR WHEEL OF AMERICA(DBA CMWA)

PARIS KY N 40361

HITACHI AUTOMOTIVE SYSTEMSAMERICAS INC‐BEREA KY

BEREA KY N 40403

SQUARE D CO LEXINGTON KY N 40511

GREIF PACKAGING LLC FLORENCE KY N 41042

MAGNI INDUSTRIES INC INDEPENDENCE KY N 41051

AIR PRODUCTS

& CHEMICALS INC CALVERT CITY KY N 42029

TRAD NA INC HOPKINSVILLE KY N 42240

LOGAN ALUMINUM INC RUSSELLVILLE KY N 42276

PRECOAT METALS HAWESVILLE KY N 42348ECOLAB HEBRON OH N 43025

HONDA OF AMERICAMANUFACTURING INC

MARYSVILLE OH N 43040

JOHNSON WELDED PRODUCTS INC URBANA OH N 43078

BALL CONTAINER LLC ‐  COLUMBUS

CAN PLANT

COLUMBUS OH Y 43213

WHIRLPOOL CORP MARION D IVISION MARION OH Y 43302

HONDA OF AMERICAMANUFACTURING INC

EAST LIBERTY OH N 43319

WHIRLPOOL CORP ‐ CLYDE DIV CLYDE OH N 43410

REXAM BEVERAGE CAN CO RE:

FREMONT PLANT

FREMONT OH Y 43420

ELECTROPRIME INC ROSSFORD OH N 43460

SILGAN CAN CO NAPOLEON OH N 43545

REXAM BEVERAGE CAN CO RE:

WHITEHOUSE PLANT

WHITEHOUSE OH Y 43571

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default 0.79Default Default DefaultDefault Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default 

13.52 37 0.995

12.2 95 1

Default Default DefaultDefault Default Default 

20 55 0.97

Default Default Default Default Default Default 

15 200 0.99

Page 34 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

DECORATIVE PANELS INTERNATIONA L TOLEDO OH N 43607MAGNA STEYR NORTH AMERICA TOLEDO OH N 43608

DAIMLERCHRYSLER CORP TOLEDOASSEMBLY PLANT

TOLEDO OH N 43612

CROWN FOOD PACKAGING TOLEDO OH N 43612

AK STEEL CORP ‐ ZANESVI LLE WORKS ZANESVILLE OH N 43701

INTERNATIONAL PAINT LLC BEREA OH N 44017

EXCEL POLYMERS LLC BURTON OH N 44021

SCOT LABORATORIES CHAGRIN FALLS OH N 44023

GOLD KEY PROCESSING INC MIDDLEFIELD OH N 44062

NORTH COAST CONTAINER CORP CLEVELAND OH N 44105

NPA COATINGS INC CLEVELAND OH N 44102

UNIVAR USA INC STRONGSVILLE OH N 44136

FERRO CORP WALTON HILLSOPERATIONS

WALTON HILLS OH N 44146

GOJO INDUSTRIES INC CUYAHOGA FALLS OH N 44223

HESS PRINT SOLUTIONS BRIMFIELD OH N 44240

PLASTI‐KOTE INC MEDINA OH N 44258

3M CO ‐ MEDINA MEDINA OH N 44256

HARWICK STANDARD DISTRIBUTION

CORP

AKRON OH N 44305

CANFIELD METAL COATING CORP CANFIELD OH N 44406

GENERAL MOTORS CORP LORDSTOWN

COMPLEX

LORDSTOWN OH N 44481

TECNOCAP LLC WARREN OH N 44483

NOVELIS CORP WARREN OH N 44483

MAHONING PAINT CORP YOUNGSTOWN OH N 44502EPCO EXTRUSION PAINTING CO BOARDMAN OH N 44512

SPECTRUM METAL FINISHING YOUNGSTOWN OH N 44512

GE WATER

& PROCESS TECHNOLOGIES NEW

PHILADELPHIA

OH N 44663

ARTIFLEX MANUFACTURING LLC

GERSTCO DIV WOOSTER

WOOSTER OH N 44691

MAYFLOWER VEHICLE SYSTEMS INC

NORWALK FACILITY

NORWALK OH N 44857

AMERICAN COLORS INC DISPERSION

PLANT SANDUSKY OHIO

SANDUSKY OH N 44870

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default

Page 35 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

RR DONNELLEY

& SONS CO WILLARD OH N 44890

NEWMAN TECHNOLOGY INC MANSFIELD OH N 44903

FLINT GROUP NORTH AMERICA CORP LEBANON OH N 45036

WORLDCOLOR LEBANON DIV LEBANON OH N 45036BERENFIELD CONTAINERS INC MASON MASON OH N 45040

PROCTER

& GAMBLE CO GPDF CINCINNATI OH N 45217

HB FULLER CO BLUE ASH OH N 45242

INGERSOLL‐RAND CO STEELCRAFT DIV CINCINNATI OH N 45242

UNIVAR USA INC‐ CINCINNATI OH

BRANCH

CINCINNATI OH N 45246

ALCOA HOME EXTERIORS INC SIDNEY OH N 45365

AMERICAN TRIM LLC SIDNEY OH N 45365

NAVISTAR INC SPRINGFIELD OH N 45502

MASCO RETAIL CABINET GROUP LLC WAVERLY OH N 45690

BALL METAL BEVERAGE CONTAINER

CORP

FINDLAY OH Y 45840

WHIRLPOOL CORP FINDLAY DIV FINDLAY OH N 45840

J&M MANUFACTURING CO INC FORT RECOVERY OH N 45846

LAFARGE NA (INCLUDING SYSTECH

ENV CORP)

PAULDING OH N 45879

AAP ST MARYS CORP SAINT MARYS OH N 45885

DSM NEORESINS INC FRANKFORT IN N 46041CROWN EQUIPMENT CORP GREENCASTLE IN N 46135

PRECOAT METALS GREENFIELD IN N 46140CAR CARE PACKAGING LLC INDIANAPOLIS IN N 46203

IVC INDUSTRIAL COATINGS INC INDIANAPOLIS IN N 46218UNIVAR USA INC ‐ INDIANAPOLIS INDIANAPOLIS IN N 46219

MARATHON PETROLEUM CO ‐ 

SPEEDWAY IN TERMINAL

INDIANAPOLIS IN N 46222

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

INDIANAPOLIS IN N 46225

DYNALOY LLC INDIANAPOLIS IN N 46226

UNIVAR USA INC INDIANAPOLIS WEST

BRANCH

INDIANAPOLIS IN N 46268

TRADEBE TREATMENT

& RECYCLING

LLC

EAST CHICAGO IN N 46312

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default

14.1732 89 1

Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default

Page 36 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

SILGAN CONTAINERS

MANUFACTURING CORP

HAMMOND IN N 46320

PRECOAT METALS LA PORTE IN N 46350

SILGAN CONTAINERS

MANUFACTURING CORP

LA PORTE IN Y 46350

AVERY DENNISON PFD SCHERERVILLE IN N 46375BP PRODUCTS NORTH AMERICA

WHITING

WHITING IN N 46394

ET PRODUCTS CO INC BREMEN IN N 46506

MASTERBRAND CABINETS INC GOSHEN IN N 46526MIDDLEBURY HARDWOOD PRODUCTS MIDDLEBURY IN N 46540

AM GENERAL LLC MISHAWAKA IN N 46545

WARSAW CHEMICAL CO INC WARSAW IN N 46580

BIOLAB INC ASHLEY IN N 46705

STEEL DYNAMICS INC BUTLER IN N 46721

THERMA‐TRU CORP BUTLER IN N 46721

GM TRUCK GROUP FORT WAYNE

ASSEMBLY

ROANOKE IN N 46783

NUCOR VULCRAFT GROUP SAINT JOE

DIV

SAINT JOE IN N 46785

AURORA CASKET CO INC AURORA IN N 47001

BATESVILLE MANUFACTURING INC ‐

DOLL PLANT

BATESVILLE IN N 47006

ENKEI AMERICA INC COLUMBUS IN N 47201PATRIOT PAINT LLC PORTLAND IN N 47371GEA BPO LLC BLOOMINGTON IN N 47404

ASHLEY INDUSTRIAL MOLDING INC ASHLEY IN N 46705

SABIC INNOVATIVE PLASTICS MT

VERNON LLC

MOUNT VERNON IN N 47620

ALCOA INC ‐ WARRICK OPERATIONS NEWBURGH IN N 47629

TOYOTA MOTOR MANUFACTURING

INDIANA INC

PRINCETON IN N 47670

SILGAN WHITE CAP CORP EVANSVILLE IN N 47710

IVC INDUSTRIAL COATINGS INC BRAZIL IN N 47834

SUBARU OF INDIANA AUTOMOTIVE

INC

LAFAYETTE IN N 47905

CROWN BEVERAGE PACKAGING CRAWFORDSVILLE IN N 47933

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default Default 

12.19 32.22 1

Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default

Page 37 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

RR DONNELLEY CRAWFORDSVILLE CRAWFORDSVILLE IN N 47933BON L MANUFACTURING CO KENTLAND IN N 47951

BALL METAL BEVERAGE CONTAINER

CORP

MONTICELLO IN N 47960

MASTER GUARD CORP VEEDERSBURG IN N 47987

GM ORION ASSEMBLY CENTER LAKE ORION MI N 48359

KAY AUTOMOTIVE GRAPHICS LAKE ORION MI N 48359

PONTIAC ASSEMBLY CENTER PONTIAC MI N 48341

HOWARD FINISHING LLC MADISON

HEIGHTS

MI N 48071

CURTIS METAL FINISHING CO STERLING HEIGHTS MI N 48313

NJT ENTERPRISES LLC STERLING HEIGHTS MI N 48314

CHRYSLER WARREN TRUCK ASSEMBLY

PLANT (PART)

WARREN MI N 48091

WAYNE DISPOSAL INC BELLEVILLE MI N 48111

FORD MOTOR CO DEARBORN TRUCK

PLANT

DEARBORN MI Y 48121

AUTOALLIANCE INTERNATIONAL INC FLAT ROCK MI N 48134

UNIVAR USA INC ROMULUS BRANCH ROMULUS MI N 48174

AUTOMOTIVE COMPONENTS

HOLDINGS LLC SALINE PLANT

SALINE MI N 48176

FORD MOTOR COMPANY‐WAYNE

ASSEMBLY

WAYNE MI N 48184

FORD MOTOR CO MICHIGAN

ASSEMBLY PLANT

WAYNE MI N 48184

AMERICAN JETWAY CORP WAYNE MI N 48184

AJAX METAL PROCESSING INC DETROIT MI N 48207

CHRYSLER JEFFERSON NORTHASSEMBLY PLANT

DETROIT MI N 48215

PVS NOLWOOD CHEMICALS INC DETROIT MI N 48228

Z TECHNOLOGIES CORP REDFORD MI N 48239

MT ELLIOTT TOOL

& DIE

MANUFACTURING (PART)

DETROIT MI N 48234

GM LLC POWERTRAIN FLINT ENGINE

OPERATIONS

FLINT MI N 48552

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default 

21.32926829 Default 0.97

Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default

Page 38 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

GENERAL MOTORS LANSING DELTA

TOWNSHIP

LANSING MI N 48917

GMVM‐LANSING GRAND RIVER

ASSEMBLY

LANSING MI N 48921

GRAPHIC PACKAGING INTERNATIONAL

INC

KALAMAZOO MI N 49007

DEXTER CHASSIS GROUP PLANT 55 WHITE PIGEON MI N 49099

CHEMETALL US INC JACKSON MI N 49203

ANDERSON DEVELOPMENT CO ADRIAN MI N 49221

HELEN,INC DBA ENVIRONMENTAL

COATINGS,INC

CALEDONIA MI N 49316

BRADFORD WHITE CORP MIDDLEVILLE MI N 49333

MAGNA MIRRORS CORP ‐ NEWAYGO NEWAYGO MI N 49337

WEBB CHEMICAL SERVICE CORP MUSKEGON

HEIGHTS

MI N 49444

SPECTRUM CUBIC INC GRAND RAPIDS MI N 49503

AVON AUTOMOTIVE PLANT 1 CADILLAC MI N 49601

JOHN DEERE DES MOINES WORKS ANKENY IA N 50023

3M CO ‐ KNOXVILLE KNOXVILLE IA N 50138

PELLA CORP PELLA IA N 50219

SILGAN CONTAINERS MANUFACTURING CORP

FORT DODGE IA N 50501

METOKOTE CORP PLANT 15 CEDAR FALLS IA N 50613VOGEL PAINT

& WAX CO INC ORANGE CITY IA N 51041

PELLA CORP CARROLL OPERATIONS CARROLL IA N 51401

CARRY‐ON TRAILER CORP MISSOURI VALLEY IA N 51555

KLINGER PAINT CO INC CEDAR RAPIDS IA N 52404

CNH AMERICA LLC BURLINGTON IA N 52601MONSANTO CO MUSCATINE IA N 52761AMERICAN FINISHING RESOURCES INC CHILTON WI N 53014WORTHINGTON CYLINDERS WISCONSIN LLC

CHILTON WI N 53014

BROAN‐NUTONE LLC HARTFORD WI N 53027QUAD/GRAPHICS INC HARTFORD WI N 53027

JOHN DEERE HORICON WORKS‐DT HORICON WI N 53032

QUAD/GRAPHICS INC LOMIRA WI N 53048

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default 

Page 39 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

QUEST SPECIALTY COATINGS LLC ‐ 

MENOMONEE FALLS

MENOMONEEFALLS

WI N 53051

SILGAN CONTAINERS

MANAUFACTURING CORP

OCONOMOWOC WI N 53066

WISMARQ CORP OCONOMOWOC WI N 53066

BEMIS MANUFACTURING CO PLANT B SHEBOYGAN FALLS WI N 53085

QUAD/GRAPHICS INC SUSSEX WI N 53089

DIVERSEY INC WATERTOWN WI N 53094

UNIVAR USA INC NEW BERLIN NEW BERLIN WI N 53151

MID‐AMERICA STEEL DRUM CO IN C OAK CREEK WI N 53154

PPG INDUSTRIES INC‐OAK CREEK OAK CREEK WI N 53154

FIVE STAR COATINGS GROUP TWIN LAKES WI N 53181

GACO WESTERN WAUKESHA WI N 53186

KITZINGER COOPERAGE CORP SAINT FRANCIS WI N 53235

MILPORT ENTERPRISES INC MILWAUKEE WI N 53207

TWINCO ROMAX MILWAUKEE WI N 53209SEIDEL TANNING CORP MILWAUKEE WI N 53212

QUAD/GRAPHICS INC WEST ALLIS WI N 53214

MUTI‐PACK LLC MILWAUKEE WI N 53223

KUBIN‐NICHOLSON CORP MILWAUKEE WI N 53224

BALL METAL BEVERAGE CONTAINER

CORP

MILWAUKEE WI N 53224

FIRST SOURCE WORLDWIDE LLC

MILWAUKEE

MILWAUKEE WI N 53226

CNH AMERICA LLC STURTEVANT WI N 53177

BALL CONTAINER LLC FORT ATKINSON WI N 53538

RR DONNELLEY BARABOO DIV BARABOO WI N 53913

SENECA FOODS CORP BARABOO WI N 53913

CHEMDESIGN PRODUCTS INC MARINETTE WI N 54143

WISCONSIN ALUMINUM FOUNDRY COINC

MANITOWOC WI N 54220

SILGAN CONTAINERS

MANUFACTURING CORP

PLOVER WI Y 54467

CROWN BEVERAGE PACKAGING LA CROSSE WI Y 54603

TORO CO TOMAH WI N 54660

TORO CO TOMAH WI N 54660

SILGAN CONTAINERS

MANUFACTURING CORP

MENOMONIE WI N 54751

MULTICIRCUITS OSHKOSH WI N 54903

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default

11.28 36.88 0.99

13.716 12 1 

Default Default Default Default Default Default Default Default DefaultDefault Default Default 

Page 40 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

ALLIANCE INDUSTRIES WAUPACA WAUPACA WI N 54981

UNIVAR USA INC LAKEVILLE LAKEVILLE MN N 55044

CROWN FOOD PACKAGING OWATONNA MN Y 55060

S B FOOT TANNING CO RED WING MN N 55066

REXAM BEVERAGE CAN CO RE: EVA

STREET ST PAUL MN

SAINT PAUL MN Y 55107

FORD MOTOR CO TWIN CITIES

ASSEMBLY PLANT

SAINT PAUL MN N 55116

FLINT HILLS RESOURCES LP ROSEMOUNT MN N 55068EDCO PRODUCTS INC HOPKINS MN N 55343

RRD MAPLE GROVE MAPLE GROVE MN N 55369

MEDALLION CABINETRY INC WACONIA MN N 55387

NORTHLAND ALUMINUM PRODUCTS I

NC

MINNEAPOLIS MN N 55416

BROWN PRINTING CO WASECA MN N 56093

MID CONTINENT CABINETRY COTTONWOOD MN N 56229NAHAN PRINTING INC SAINT CLOUD MN N 56303

SAPA EXTRUSIONS INC YANKTON SD N 57078BOBCAT CO (MELROE) GWINNER ND N 58040ACME FINISHING CO INC ELK GROVE

VILLAGE

IL N 60007

ROHM

& HAAS CHEMICALS LLC ELK GROVE

VILLAGE

IL N 60007

BECKER SPECIALTY CORP ELK GROVE

VILLAGE

IL N 60007

IMS ENGINEERED PRODUCTS LLC DES PLAINES IL N 60016GREENWICH INDUSTRIES LP CLARIN

DIV

LAKE BLUFF IL N 60044

BROWN PRINTING CO WOODSTOCK IL N 60098

GE WATER

& PROCESS TECHNOLOGIES ADDISON IL N 60101

BALL AEROSOL

& SPECIALTY

CONTAINER INC

ELGIN IL N 60120

UNIVERSAL CHEMICALS

& COATINGS

INC

ELGIN IL N 60123

WISMARQ CORP FRANKLIN PARK IL N 60131

WR MEADOWS INC HAMPSHIRE IL N 60140

LEHIGH PRESS CADILLAC (DBA LEHIGH

DIRECT DIVISION)

BROADVIEW IL N 60153

SUN CHEMICAL CORP NORTHLAKE IL N 60164

SYCAMORE SYSTEMS LLC SYCAMORE IL N 60178

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default Default Default Default 

17.98 70.7 0.99 

Default Default Default 

15 120 0.95

Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default 

Page 41 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

SEYMOUR OF SYCAMORE INC SYCAMORE IL N 60178

KNS COMPANYS INC CAROL STREAM IL N 60188

TMS MANUFACTURING ALSIP IL N 60803DOW CHEMICAL JOLIET SITE CHANNAHON IL N 60410

CHICAGO HEIGHTS STEEL CHICAGO HEIGHTS IL N 60411

ALLIED TUBE

& CONDUIT CORP HARVEY IL N 60426

INX INTERNATIONAL INK CO HOMEWOOD IL N 60430

DOBER CHEMICAL CORP MIDLOTHIAN IL N 60445

SIGNODE BRIDGEVIEW IL N 60455UNIVAR USA INC BEDFORD PARK IL N 60499

UNIVAR USA INC 68TH ST BEDFORD PARK IL N 60501

CROWN AEROSOL PACKAGING AURORA IL N 60504

CHAMPION PACKAGING

&

DISTRIBUTING INC

WOODRIDGE IL N 60517

LAKESIDE LITHOGRAPHY LLC CHICAGO IL N 60608EDSAL MANUFACTURING CO INC CHICAGO IL N 60609

REXAM BEVERAGE CAN CO RE :

CHICAGO PLANT

CHICAGO IL Y 60609

CHICAGO STEEL CONTAINER CORP CHICAGO IL N 60623BWAY CORP CHICAGO IL N 60623MEYER STEEL DRUM INC CHICAGO IL N 60623

COLOR COMMUNICATIONS INC CHICAGO IL N 60624

SKOLNIK INDUSTRIES CHICAGO IL N 60632

GREIF PACKAGING LLC ALSIP IL N 60803

CROWN BEVERAGE PACKAGING BRADLEY IL Y 60915

CHRYSLER BELVIDERE ASSEMBLY

PLANT

BELVIDERE IL N 61008

SIGNCRAFT SCREEN PRINT GALENA IL N 61036

SILGAN CONTAINERS

MANUFACTURING CORP

ROCHELLE IL N 61068

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

ROCKFORD IL N 61104

3M CO ‐ CORDOVA CORDOVA IL N 61242

3M CO ‐ CORDOVA CORDOVA IL N 61242

JOHN DEERE HARVESTER WORKS EAST

MOLINE

EAST MOLINE IL N 61244

TYSON FRESH MEATS INC JOSLIN IL HILLSDALE IL N 61257

NATIONAL COATINGS INC GALESBURG IL N 61401

PEORIA DISPOSAL CO #1 PEORIA IL N 61615

CNH AMERICA LLC GOODFIELD IL N 61742

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default 

12.192 19 0.9368

Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default 

15.24 18.71 0.88 

Default Default DefaultDefault Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default 

Page 42 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

CNH AMERICA LLC GOODFIELD IL N 61742

MASTERBRAND CABINETS INC ARTHUR IL N 61911

RR DONNELLEY

& SONS CO MATTOON IL N 61938

MIDWEST METAL COATINGS GRANITE CITY IL N 62040PRECOAT METALS GRANITE CITY IL N 62040

AFTON CHEMICAL CORP SAUGET IL N 62201VEOLIA ES TECHNICAL SOLUTIONS LLC SAUGET IL N 62201

KNAPHEIDE MANUFACTURING CO QUINCY IL N 62305QG LLC EFFINGHAM IL N 62401

METAL CONTAINER CORP ‐ ARNOLD

CAN PLANT

ARNOLD MO Y 63010

TRILLA ST LOUIS CORP FENTON MO N 63026

CHRYSLER ST LOUIS NORTH ASSEMBLY

PLANT

FENTON MO N 63026

UNIVAR USA INC METRO BLVD MARYLAND

HEIGHTS

MO N 63043

BUCKEYE INTERNATIONAL INC MARYLAND

HEIGHTS

MO N 63043

PLAZE INC PACIFIC MO N 63069

SCHAEFFER MANUFACTURING SAINT LOUIS MO N 63104

U.S. POLYMERS ACCUREZ LLC SAINT LOUIS MO N 63111

UNIVAR USA INC BERKELEY BERKELEY MO N 63134

ELANTAS PDG INC SAINT LOUIS MO N 63147

THE DIAL CORP

A SUBSIDIARY OF

HENKEL CONSUMER GOODS

SAINT LOUIS MO N 63147

SAF‐HOLLAND USA INC WARRENTON MO N 63383

GENERAL MOTORS WENTZVILLE

ASSEMBLY

WENTZVILLE MO N 63385

GATES CORP POPLAR BLUFF MO N 63901US ARMY LAKE CITY ARMY

AMMUNITION PLANT

INDEPENDENCE MO N 64051

FORD MOTOR COMPANY‐‐KANSAS

CITY ASSEMBLY PLANT

CLAYCOMO MO Y 64119

BALL METAL BEVERAGE CONTAINER

CORP

KANSAS CITY MO N 64120

SILGAN CONTAINERS

MANUFACTURING CORP

SAINT JOSEPH MO N 64504

VON HOFFMANN GRAPHICS INC OWENSVILLE MO N 65066

HUTCHENS INDUSTRIES INCMANSFIELD FACILITY

MANSFIELD MO N 65704

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default 

12.192 68.58 0.8

Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default 0.57Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default

Page 43 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

EFCO CORP MONETT MO Y 65708HYDRO ALUMINUM NORTH AMERICA

INC

MONETT MO N 65708

SILGAN CONTAINERS

MANUFACTURING CORP

MOUNT VERNON MO N 65712

3M CO ‐ SPRINGFIELD SPRINGFIELD MO N 658023M CO ‐ SPRINGFIELD SPRINGFIELD MO N 65802NAZDAR SHAWNEE SHAWNEE KS N 66227

PACKAGING DYNAMICS INC

BAGCRAFT/PAPERCON DIV

BAXTER SPRINGS KS N 66713

LAFARGE MIDWEST INC (INCLDSYSTECH ENVIRONMENTAL)

FREDONIA KS N 66736

GATES CORP IOLA KS N 66749

GREIF INDUSTRIAL PACKAGING

&

SERVICES

WINFIELD KS N 67156

THE COLEMAN CO INC WICHITA KS N 67219

CONOCOCPHILLIPS CO WICHITA

TERMINAL

WICHITA KS N 67219

SCHWAN'S GLOBAL SUPPLY CHAIN ‐ SALINA KS

SALINA KS N 67401

VALMONT INDUSTRIES INC VALLEY NE N 68064

VEYANCE TECHNOLOGIES INC LINCOLN NE N 68504

KAWASAKI MOTORS

MANUFACTURING CORP USA

LINCOLN NE N 68524

NUCOR CORP ‐ VULCRAFT/NUCORCOLD FINISH DIV

NORFOLK NE N 68701

TYSON FRESH MEATS INC DAKOTA CITY NE N 68731

AIR PRODUCTS PERFORMANCEMANUFACTURING INC

RESERVE LA N 70084

GREIF PACKAGING LLC NEW ORLEANS LA N 70123CHAMPION TECHNOLOGIES INC BROUSSARD LA N 70518

BAYOU COS INC NEW IBERIA LA N 70560NALCO CO SCOTT LA N 70583

BRENNTAG SOUTHWEST INC ST

GABRIEL

SAINT GABRIEL LA N 70776

NOVOLYTE PERFORMANCEMATERIALS

ZACHARY LA N 70791

ASHLAND DISTRIBUTION CO BATON ROUGE LA N 70815

GMTG ‐ SHREVEPORT ASSEMBLY SHREVEPORT LA N 71129

UNION TANK CAR ALEXANDRIA

MANUFACTURING FACILITY

ALEXANDRIA LA N 71303

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

6.096 3.048 0.11 

Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default

Page 44 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

BERENFIELD CONTAINERS SW LTD WHITE HALL AR N 71602

WHEELING MACHINE PRODUCTS DIV

PINE BLUFF

PINE BLUFF AR N 71602

CLEAN HARBORS EL DORADO LLC EL DORADO AR N 71730

CHAMPION TECHNOLOGIES INC MAGNOLIA AR N 71753

RINECO BENTON AR N 72015

BRYCE CO LLC SEARCY AR N 72143

MAVERICK TUBE LLC BLYTHEVILLE AR N 72315

AMERIMAX COATED PRODUCTS HELENA AR N 72342QG PRINTING II CORP JONESBORO AR N 72401

L A DARLING CO ‐ PIGGOTT ARFACILITY

PIGGOTT AR N 72454

SUPERIOR INDUSTRIES

INTERNATIONAL ARKANSAS LLC

FAYETTEVILLE AR N 72701

SUPERIOR INDUSTRIES

INTERNATIONAL ARKANSAS LLC

ROGERS AR N 72756

KAWNEER CO INC SPRINGDALE AR N 72764GRAPHIC PACKAGING INTERNATIONAL

INC

FORT SMITH AR N 72916

DEXTER AXLE EL RENO OK N 73036

GEMINI COATINGS INC EL RENO OK N 73036U.S. AIR FORCE TINKER AFB OK TINKER

A F B OK N 73145

REXAM BEVERAGE CAN CO

RE:OKLAHOMA CITY PLANT

OKLAHOMA CITY OK Y 73179

CLEAN HARBORS LONE MOUNTAINLLC LONE MOUNTAIN FACILITY

WAYNOKA OK N 73860

BRENNTAG SOUTHWEST INC SAND

SPRINGS

SAND SPRINGS OK N 74063

NALCO CO TULSA PLANT 102 TULSA OK N 74131

BRAINERD CHEMICAL CO INC TULSA OK N 74147

AIR SYSTEM COMPONENTS LP PONCA CITY OK N 74601

MOBIL CHEMICAL CO SHAWNEE OK N 74804

ELECTRO PLATE CIRCUITRY INC CARROLLTON TX N 75006

GLIDDEN CO CARROLLTON TX N 75006A BRITE CO GARLAND TX N 75041

BENJAMIN MOORE

& CO ‐ DALLAS MESQUITE TX N 75149

OLDCASTLE BUILDING ENVELOPE ‐ 

TEXAS FACILITY

TERRELL TX N 75160

MAGNABLEND INC‐CENTRAL PLANT WAXAHACHIE TX N 75165UNITED STATES ALUMINUM CORP WAXAHACHIE TX N 75165

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default 

13 100 0.85

Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default 

Page 45 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

INTERNATIONAL EXTRUSION CORP

TEXAS

WAXAHACHIE TX N 75165

MAXIM INTEGRATED PRODUCTS DALLAS TX N 75244

SILGAN CAN CO PARIS TX N 75460

ALUMAX MILL PRODUCTS INC TEXARKANA TX N 75501

BRENNTAG SOUTHWEST INC LONG

VIEW

LONGVIEW TX N 75604

REXAM BEVERAGE CAN CO LONGVIEW

FACILITY

LONGVIEW TX Y 75604

EASTMAN CHEMICAL CO TEXASOPERATIONS

LONGVIEW TX N 75602

ROBROY INDUSTRIES TEXAS LP GILMER TX N 75644

BAKER PETROLITE KILGORE BLEND

PLANT

KILGORE TX N 75662

CHAMPION TECHNOLOGIES INC KILGORE TX N 75662

CHAMPION TECHNOLOGIES INC LONGVIEW TX N 75662

CLEVELAND STEEL CONTAINER ‐ 

KILGORE

KILGORE TX N 75662

NUCOR VULCRAFT GROUP ‐ 

GRAPELAND DIV

GRAPELAND TX N 75844

SHIELDCOAT TECHNOLOGIES INC (DBA

CYBERSHIELD OF TEXAS)

LUFKIN TX N 75904

CHAMPION TECHNOLOGIES INC CRESSON TX N 76035

CHEMGUARD INC MANSFIELD TX N 76063

BALL METAL BEVERAGE CONTAINER

CORP

FORT WORTH TX N 76140

CARRY‐ON TRAILER CORP MEXIA TX N 76667

TEXAS TILE MANUFACTURING LLC HOUSTON TX N 77007

PRECOAT METALS HOUSTON TX N 77015NOV TUBOSCOPE WEST LITTLE YORK

COATING

HOUSTON TX N 77041

UNIVAR USA INC HOUSTON FM 529 HOUSTON TX N 77041

RR DONNELLEY‐WETMORE PLANT HOUSTON TX N 77043BRENNTAG SOUTHWEST INC HOUS

TON

HOUSTON TX N 77047

KIK (HOUSTON) INC HOUSTON TX N 77054

INTERCOASTAL PAINT CO INC HOUSTON TX N 77060

PPG ARCHITECURAL COATINGS

HOUSTON

HOUSTON TX N 77092

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default

18 80 0.91

Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default

Page 46 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

MAVERICK TUBE LLC DBA

TENARISCONROE

CONROE TX N 77301

BALL METAL BEVERAGE CONTAINER

CORP

CONROE TX N 77303

CROWN BEVERAGE PACKAGING CONROE TX N 77303

AMERICAN COATINGS INC TOMBALL TX N 77375

CROWN BEVERAGE PACKAGING SUGAR LAND TX N 77478

NALCO CO PLANT 106 SUGAR LAND TX N 77478

MEMC PASADENA INC PASADENA TX N 77503EQUISTAR CHEMICALS BAYPORT

CHEMICALS PLANT

PASADENA TX N 77507

CHEMICALS INC BAYTOWN TX N 77520

KMCO CROSBY PLANT CROSBY TX N 77532

DELTA HOUSTON DEER PARK TX N 77536

CLEAN HARBORS DEER PARK LLC LA PORTE TX N 77571

CHAMPION TECHNOLOGIES INC FRESNO TX N 77545

GREIF PACKAGING LLC LA PORTE TX N 77571GREIF INDUSTRIAL PACKAGING

&

SERVICES LLC

LA PORTE TX N 77571

MARATHON PETROLEUM CO LLC TEXAS CITY TX N 77590

INVISTA SARL ‐ ORANGE SITE ORANGE TX N 77630

ISP SYNTHETIC ELASTOMERS LP PORT NECHES TX N 77651

TOYO INK AMERICA LLC BRYAN TX N 77807

NOV TUBOSCOPE NAVASOTA NAVASOTA TX N 77868

UNION CARBIDE CORP SEADRIFTPLANT

SEADRIFT TX N 77983

CLEARWATER INTERNATIONAL LLC ELMENDORF TX N 78112

TOYOTA MOTOR MANUFACTURING

TEX AS INC

SAN ANTONIO TX N 78264

US ECOLOGY TEXAS INC ROBSTOWN TX N 78380

CHAMPION TECHNOLOGIES INC CORPUS CHRISTI TX N 78405

TYSON FRESH MEATS INC AMARILLO TX N 79108

CATALYST OILFIELD SERVICES LLC GARDENDALE TX N 79758

CHAMPION TECHNOLOGIES INC ODESSA TX N 79762

UNIVAR USA INC HOUSTON HOUSTON TX N 77061

NALCO CO ‐ ODESSA PLANT 114 ODESSA TX N 79765

KBP COIL COATERS INC DENVER CO N 80216UNIVAR USA INC DENVER DENVER CO N 80216

ROCKY MOUNTAIN METAL

CONTAINER

GOLDEN CO N 80401

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default Default

Page 47 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

BALL METAL BEVERAGE CONTAINER

CORP

GOLDEN CO N 80403

CIRCLE GRAPHICS INC LONGMONT CO N 80501

METAL CONTAINER CORPORTION ‐ 

WINDSOR CAN PLANT

WINDSOR CO Y 80550

DPIX LLC COLORADO

SPRINGS

CO N 80916

COORSTEK GRAND JUNCTION CO N 81505

SINCLAIR WYOMING REFINING CO SINCLAIR WY N 82334CROWN BEVERAGE PACKAGING WORLAND WY N 82401

ASHLAND DISTRIBUTION CO CLEARFIELD UT N 84016

U.S. AIR FORCE OGDEN AIR LOGISTICS

CENTER

HILL AFB UT N 84056

TTM TECHNOLOGIES INC LOGAN UT N 84321REXAM BEVERAGE CAN CO PHOENIX

FACILITY

PHOENIX AZ Y 85043

PROCLEAN OF ARIZONA INC PHOENIX AZ N 85043SOUTHWEST DISTRIBUTING CO MESA AZ N 85210

ASHLAND INC ‐ CHANDLER CHANDLER AZ N 85226

WR MEADOWS OF ARIZONA INC GOODYEAR AZ N 85338US MARINE CORPS AIR STATION YUMA YUMA AZ N 85369

SHERWIN‐WILLIAMS CO FERNLEY NV N 89408

CARRY‐ON TRAILER CORP WINNEMUCCA NV N 89445PRO LINE PRINTING / RR DONNELLEY RENO NV N 89512

ENGINEERED POLYMER SOLUTIONS

INC

CITY OF

COMMERCE

CA N 90040

NORMAN FOX

& CO VERNON CA N 90058

HEXION SPECIALTY CHEMICALS INC LYNWOOD CA N 90262

BALL METAL BEVERAGE CONTAINER

CORP

TORRANCE CA N 90503

EXXONMOBIL OIL CORP ‐ TORRANCEREFINERY

TORRANCE CA N 90509

OAKITE PRODUCTS INC (AKACHEMETALL OAKITE)

LA MIRADA CA N 90638

TREND OFFSET PRINTING SERVICES

INC

LOS ALAMITOS CA N 90720

ARDAGH METAL PACKAGING USA INC TERMINAL ISLAND CA N 90731

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default DefaultDefault Default Default 

14.224 61.8744 0.85

Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default 

14 30 1

Default Default Default Default Default Default Default Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default

Page 48 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

US DOD DFSP SAN PEDRO SAN PEDRO CA N 90731

SANYO SOLAR (USA) LLC CARSON CA N 90745

WESTERN TUBE

& CONDUIT CORP LONG BEACH CA N 90810

REXAM BEVERAGE CAN CO

CHATSWORTH FACILITY

CHATSWORTH CA Y 91311

REICHHOLD INC ‐ AZUSA PLANT AZUSA CA N 91702

WESTERN METAL DECORATING CO RANCHO

CUCAMONGA

CA N 91730

CARDINAL INDUSTRIAL FINISHES SOUTH EL MONTE CA N 91733

METAL CONTAINER CORP ‐ MIRALOMA CAN PLANT

MIRA LOMA CA N 91752

HENKEL ONTARIO ONTARIO CA N 91761

MACDERMID PRINTING SOLUTIONS SAN MARCOS CA N 92078

SDC TECHNOLOGIES INC IRVINE CA N 92618

BEHR PROCESS CORP SANTA ANA CA N 92704

ARLON INC ADHESIVES

& FILMS DIV SANTA ANA CA N 92704

ARLON GRAPHICS LLC SANTA ANA CA N 92704

BAKER PETROLITE BAKERSFIELD CA N 93308GE WATER

& PROCESS TECHNOLOGIES

‐ BAKERSFIELD

BAKERSFIELD CA N 93308

KELLY‐MOORE PAINT CO INC SAN CARLOS CA N 94070

BALL METAL BEVERAGE CONTAINER

CORP

FAIRFIELD CA N 94533

REXAM BEVERAGE CAN CO RE:

FAIRFIELD PLANT

FAIRFIELD CA Y 94533

NEW UNITED MOTOR

MANUFACTURING INC

FREMONT CA N 94538

UNIVAR USA INC ‐ SAN JOSE SAN JOSE CA N 95131

ECOLAB INC SAN JOSE CA N 95133

GREIF PACKAGING LLC MERCED CA N 95348

BALL METAL FOOD CONTAINER CORP OAKDALE CA N 95361

SILGAN CONTAINER MANUFACTURING

CORP

RIVERBANK CA N 95367

INX DIGITAL INK CO DIXON CA N 95620HB FULLER ROSEVILLE CA N 95678SACRAMENTO‐ CAMPBELL SOUP

SUPPLY CO

SACRAMENTO CA N 95824

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default Default Default Default Default Default Default 

15 30 0.98

Default Default Default Default Default DefaultDefault Default DefaultDefault Default DefaultDefault Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default Default Default DefaultDefault Default Default Default Default Default

15 50 0.98

Default Default DefaultDefault Default Default Default Default Default Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default

Page 49 of 50
Table C-4. Comparisons of 2009, 2010 and 2011 TRI Air Emissions Data for Certain Glycol Ethers to Site 

Facility City State Completed Survey Zip Code

SILGAN CAN CO SACRAMENTO CA N 95824

ENGINEERED POLYMER SOLUTIONS

INC D/B/A VALSPAR COATINGS

SACRAMENTO CA N 95826

BALL METAL BEVERAGE CONTAINER

CORP

KAPOLEI HI N 96707

IMPERIAL PAINT CO INC PORTLAND OR N 97210

UNIVAR USA INC PORTLAND OR N 97210

TARR ACQUISITION LLC PORTLAND OR N 97227

FORMULA CORP AUBURN WA N 98002REXAM BEVERAGE CAN CO KENT WA

FACILITY

KENT WA Y 98032

BOEING COMMERCIAL AIRPLANE

GROUP ‐ EVERETT

EVERETT WA N 98204

EMERALD SERVICES INC TACOMA WA N 98421

CROWN BEVERAGE PACKAGING OLYMPIA WA Y 98501

US DOD USAF JOINT BASE

ELMENDORF‐RICHARDSON

ELMENDORF AFB AK N 99506

Minimum 

Release Height 

(m)

Minimum 

Receptor 

Distance (m)

Proportion of 

Certain Glycol 

Ethers Used that 

are EGBE

Default Default Default Default Default DefaultDefault Default DefaultDefault Default Default Default Default Default Default Default Default Default Default Default 

13.19784 29 0.9987

Default Default DefaultDefault Default Default 

12.8 44.63 0.94 

Default Default Default

NR: no emissions reportedY: survey completedN: survey not completedtpy: tons per yearDefault: Because site-specific survey not completed, assmg/m3: concentration of EGBE in air (milligrams per cubic 

EGBE: ethylene glycol monobutyl etherm: meterTRI: Toxics Release Inventory

Page 50 of 50
APPENDIX D 

Outcome of Long-Term Tiered Modeling in 

Support of Uncertainty Analysis 
Table D-1. Tier 1 Table of Normalized Annual Concentrations (μg/m3

)/(tpy)

Receptor Distance

10 m 30 m 50 m 100 m 200 m 500 m

Area (10 m) 0.00 10.00 956 302.00 164.00 64.80 23.20 5.53

Area (10 m)a 3.00 10.00 103 32.47 29.94 28.09 17.73 5.18

Area (20 m) 0.00 20.00 515 183.00 107.00 47.80 19.10 5.04

Area (30 m) 0.00 30.00 351 131.00 79.20 37.40 16.10 4.58

Volume 3a 10.00 128 40.32 36.10 25.00 13.79 4.46

Point 0 - 5410 792.00 325.00 96.70 29.10 6.08

Point 2 - 187 142.00 135.00 72.80 26.40 5.96

Point 5 - 96.20 74.60 51.80 27.20 14.80 5.18

Point 10 - 27.70 24.40 21.10 13.60 7.17 2.88

Point 20 - 6.91 4.52 4.52 3.80 2.44 1.06

Point 35 - 2.26 2.26 1.13 1.11 0.90 0.44

Point 50 - 1.11 1.10 1.11 0.47 0.42 0.25

m: meter

tpy: ton per year

μg/m3

: micrograms per cubic meter

Source Type Release 

Height (m)

Side 

Length (m)

Normalized Maximum Annual Concentrations At or Beyond: 

a. Not included in EPA's Tier 1 table. Included in the EGBE HAPs Petition Table 4-2. These values are based on ratios

of predicted SCREEN3 impacts for each receptor distance. The 10 m2 area source with the 0 m release height was used 

as the basis for the SCREEN3 predicted ratios. Ratios at the 10 m receptor distance were set equal to the ratios at the 

30 m receptor distance.
Table D-2. Tier 1 Sensitivity Analysis Long-Term Modeling Parameters and Individual Source R

Facility Name Source ID Release Height (m)

Volume 

Source 

Length of 

Side (m)

Distance 

to Nearest 

Receptor 

(m)

Physical 

Fence 

(Y/N)

EPA Tier 1 Table: 

Normalized 

Maximum Annual 

Conc. 

(μg/m3)/(tpy)

Proportion 

EGBE of Certain 

Glycol Ethers

Ball Metal Beverage Container Corp- Findlay Stack 1 16.6 - 89 Y 21.10 1.00 

Ball Metal Beverage Container Corp- Findlay Stack 2 16.6 - 91 Y 21.10 1.00 Ball Metal Beverage Container Corp- Findlay Stack 3 19.8 - 89 Y 21.10 1.00 Ball Metal Beverage Container Corp- Findlay Stack 4 19.8 - 100 Y 13.60 1.00 Ball Metal Beverage Container Corp- Findlay Stack 5 14.2 - 127 Y 13.60 1.00 Ball Metal Beverage Container Corp- Findlay Stack 6 21.2 - 108 Y 3.80 1.00 Ball Metal Beverage Container Corp- Findlay Stack 7 21.6 - 135 Y 3.80 1.00 Ball Metal Beverage Container Corp- Findlay Stack 8 20.4 - 105 Y 3.80 1.00 Ball Metal Beverage Container Corp- Findlay Stack 9 20.7 - 100 Y 3.80 1.00 Ball Metal Beverage Container Corp- Findlay Fugitive 6.9 10 84 Y 36.10 1.00 Ball Container LLC - Columbus Stack 1 21.5 - 58 N 4.52 1.00 Ball Container LLC - Columbus Stack 2 21.8 - 61 N 4.52 1.00 Ball Container LLC - Columbus Stack 3 25.9 - 62 N 4.52 1.00 Ball Container LLC - Columbus Stack 4 15.9 - 68 N 21.10 1.00 Ball Container LLC - Columbus Stack 5 13.5 - 57 N 21.10 1.00 Ball Container LLC - Columbus Stack 6 13.5 - 68 N 21.10 1.00 Ball Container LLC - Columbus Stack 7 21.5 - 65 N 4.52 1.00 Ball Container LLC - Columbus Stack 8 21.8 - 70 N 4.52 1.00 Ball Container LLC - Columbus Stack 9 25.9 - 69 N 4.52 1.00 Ball Container LLC - Columbus Stack 10 25.9 - 60 N 4.52 1.00 Ball Container LLC - Columbus Stack 11 13.5 - 68 N 21.10 1.00 Ball Container LLC - Columbus Stack 12 13.5 - 68 N 21.10 1.00 Ball Container LLC - Columbus Stack 13 25.9 - 59 N 4.52 1.00 Ball Container LLC - Columbus Stack 14 21.8 - 55 N 4.52 1.00 Ball Container LLC - Columbus Stack 15 25.9 - 52 N 4.52 1.00 Ball Container LLC - Columbus Stack 16 25.9 - 48 N 4.52 1.00 Ball Container LLC - Columbus Stack 17 13.5 - 58 N 21.10 1.00 Ball Container LLC - Columbus Stack 18 13.5 - 57 N 21.10 1.00 Ball Container LLC - Columbus Stack 19 21.5 - 37 N 4.52 1.00 Ball Container LLC - Columbus Stack 20 25.9 - 49 N 4.52 1.00 Ball Container LLC - Columbus Stack 21 21.8 - 45 N 4.52 1.00 Ball Container LLC - Columbus Stack 22 25.9 - 43 N 4.52 1.00 Ball Container LLC - Columbus Stack 23 15.8 - 53 N 21.10 1.00 Ball Container LLC - Columbus Fugitive 5.8 10 50 N 36.10 1.00 Ball Metal Food Container Corp- Williamsburg Stack 1 18.5 - 147 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 2 18.9 - 127 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 3 15.5 - 102 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 4 15.2 - 102 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 5 13.1 - 98 Y 21.10 0.97 Ball Metal Food Container Corp- Williamsburg Stack 6 13.1 - 96 Y 21.10 0.97 Ball Metal Food Container Corp- Williamsburg Stack 7 18.5 - 140 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 8 18.4 - 145 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 9 18.3 - 122 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 10 18.6 - 118 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 11 18.3 - 103 Y 13.60 0.97 

Page 1 of 4
Table D-2. Tier 1 Sensitivity Analysis Long-Term Modeling Parameters and Individual Source R

Facility Name Source ID Release Height (m)

Volume 

Source 

Length of 

Side (m)

Distance 

to Nearest 

Receptor 

(m)

Physical 

Fence 

(Y/N)

EPA Tier 1 Table: 

Normalized 

Maximum Annual 

Conc. 

(μg/m3)/(tpy)

Proportion 

EGBE of Certain 

Glycol Ethers

Ball Metal Food Container Corp- Williamsburg Stack 12 18.3 - 111 Y 13.60 0.97 

Ball Metal Food Container Corp- Williamsburg Stack 13 18.3 - 121 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 14 18.5 - 142 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 15 15.5 - 106 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 16 15.5 - 110 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 17 17.9 - 136 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 18 17.9 - 116 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Stack 19 17.9 - 114 Y 13.60 0.97 Ball Metal Food Container Corp- Williamsburg Fugitive 6.8 10 135 Y 25.00 0.97 Crown Beverage Packaging - Bradley Stack 1 18.3 - 18.71 N 27.70 0.88 Crown Beverage Packaging - Bradley Stack 2 15.2 - 18.71 N 27.70 0.88 Crown Beverage Packaging - Bradley Stack 3 15.2 - 24 N 27.70 0.88 Crown Beverage Packaging - Bradley Stack 4 18.3 - 24 N 27.70 0.88 Crown Beverage Packaging - Bradley Stack 5 15.2 - 37.92 N 24.40 0.88 Crown Beverage Packaging - Bradley Stack 6 15.2 - 32.99 N 24.40 0.88 Crown Beverage Packaging - Bradley Stack 7 18.3 - 37.92 N 24.40 0.88 Crown Beverage Packaging - Bradley Fugitive 3.4 10 43.67 N 40.32 0.88 Crown Beverage Packaging - Lawrence Stack 1 8.7 - 38 N 74.60 0.91 Crown Beverage Packaging - Lawrence Stack 2 8.7 - 41 N 74.60 0.91 Crown Beverage Packaging - Lawrence Stack 3 8.7 - 39 N 74.60 0.91 Crown Beverage Packaging - Lawrence Stack 4 8.7 - 40 N 74.60 0.91 Crown Beverage Packaging - Lawrence Stack 5 8.7 - 34 N 74.60 0.91 Crown Beverage Packaging - Lawrence Stack 6 8.7 - 42 N 74.60 0.91 Crown Beverage Packaging - Lawrence Stack 7 8.7 - 60 N 51.80 0.91 Crown Beverage Packaging - Lawrence Stack 8 8.7 - 64 N 51.80 0.91 Crown Beverage Packaging - Lawrence Stack 9 8.7 - 46 N 74.60 0.91 Crown Beverage Packaging - Lawrence Stack 10 8.7 - 62 N 51.80 0.91 Crown Beverage Packaging - Lawrence Stack 11 8.7 - 63 N 51.80 0.91 Crown Beverage Packaging - Lawrence Stack 12 8.7 - 50 N 51.80 0.91 Crown Beverage Packaging - Lawrence Fugitive 2.8 10 75 N 36.10 0.91 Crown Beverage Packaging - Olympia Stack 1 14.3 - 44.63 N 24.40 0.94 Crown Beverage Packaging - Olympia Stack 2 16.8 - 55.57 N 21.10 0.94 Crown Beverage Packaging - Olympia Stack 3 12.8 - 63.77 N 21.10 0.94 Crown Beverage Packaging - Olympia Stack 4 12.8 - 72.24 N 21.10 0.94 Crown Beverage Packaging - Olympia Fugitive 5.0 10 69.36 N 36.10 0.94 Crown Food Packaging - Owatonna Stack 1 18.0 - 70.7 N 21.10 0.99 Crown Food Packaging - Owatonna Stack 2 18.0 - 81.66 N 21.10 0.99 Crown Food Packaging - Owatonna Stack 3 18.0 - 98.33 N 21.10 0.99 Crown Food Packaging - Owatonna Stack 4 18.0 - 104.03 N 13.60 0.99 Crown Food Packaging - Owatonna Stack 5 18.0 - 78.13 N 21.10 0.99 Crown Food Packaging - Owatonna Fugitive 5.0 10 102.8 N 25.00 0.99 Crown Cork & Seal Co (USA) - Weirton Stack 1 11.0 - 12 N 27.70 1.00 Crown Cork & Seal Co (USA) - Weirton Stack 2 17.0 - 15 N 27.70 1.00 Crown Cork & Seal Co (USA) - Weirton Fugitive 4.3 10 31.36 N 40.32 1.00 Rexam Beverage Can Company- Bishopville Stack 1 15.2 - 22 Y 27.70 1.00 

Page 2 of 4
Table D-2. Tier 1 Sensitivity Analysis Long-Term Modeling Parameters and Individual Source R

Facility Name Source ID Release Height (m)

Volume 

Source 

Length of 

Side (m)

Distance 

to Nearest 

Receptor 

(m)

Physical 

Fence 

(Y/N)

EPA Tier 1 Table: 

Normalized 

Maximum Annual 

Conc. 

(μg/m3)/(tpy)

Proportion 

EGBE of Certain 

Glycol Ethers

Rexam Beverage Can Company- Bishopville Stack 2 15.5 - 43 Y 24.40 1.00 

Rexam Beverage Can Company- Bishopville Stack 3 11.6 - 13 Y 27.70 1.00 Rexam Beverage Can Company- Bishopville Stack 4 14.0 - 16 Y 27.70 1.00 Rexam Beverage Can Company- Bishopville Stack 5 14.0 - 19 Y 27.70 1.00 Rexam Beverage Can Company- Bishopville Stack 6 15.2 - 11 Y 27.70 1.00 Rexam Beverage Can Company- Bishopville Stack 7 15.2 - 18 Y 27.70 1.00 Rexam Beverage Can Company- Bishopville Stack 8 15.2 - 23 Y 27.70 1.00 Rexam Beverage Can Company- Bishopville Fugitive 5.0 10 63 Y 36.10 1.00 Rexam Beverage Can Company- Kent Stack 1 14.6 - 36 Y 24.40 1.00 Rexam Beverage Can Company- Kent Stack 2 14.6 - 40 Y 24.40 1.00 Rexam Beverage Can Company- Kent Stack 3 16.6 - 42 Y 24.40 1.00 Rexam Beverage Can Company- Kent Stack 4 14.6 - 29 Y 27.70 1.00 Rexam Beverage Can Company- Kent Stack 5 13.5 - 56 Y 21.10 1.00 Rexam Beverage Can Company- Kent Stack 6 14.2 - 61 Y 21.10 1.00 Rexam Beverage Can Company- Kent Stack 7 13.2 - 62 Y 21.10 1.00 Rexam Beverage Can Company- Kent Stack 8 13.7 - 65 Y 21.10 1.00 Rexam Beverage Can Company- Kent Stack 9 15.2 - 56 Y 21.10 1.00 Rexam Beverage Can Company- Kent Stack 10 15.3 - 62 Y 21.10 1.00 Rexam Beverage Can Company- Kent Stack 11 15.3 - 65 Y 21.10 1.00 Rexam Beverage Can Company- Kent Stack 12 15.3 - 60 Y 21.10 1.00 Rexam Beverage Can Company- Kent Fugitive 3.7 10 64 Y 36.10 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 1 12.2 - 37.8 N 24.40 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 2 12.2 - 32.22 N 24.40 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 3 13.4 - 41.76 N 24.40 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 4 13.4 - 41.76 N 24.40 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 5 13.4 - 45.11 N 24.40 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 7 12.2 - 41.45 N 24.40 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 8 12.2 - 32.61 N 24.40 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 9 12.2 - 49.07 N 24.40 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 10 12.8 - 53.95 N 21.10 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 11 12.2 - 56.39 N 21.10 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 12 12.2 - 44.2 N 24.40 1.00 Silgan Containers Manufacturing Corp- LaPorte Fugitive 3.0 10 59 N 36.10 1.00 Rexam Beverage Can Company- Chicago Stack 1 13.1 - 30 Y 24.40 0.94 Rexam Beverage Can Company- Chicago Stack 2 12.6 - 38 Y 24.40 0.94 Rexam Beverage Can Company- Chicago Stack 3 13.2 - 44 Y 24.40 0.94 Rexam Beverage Can Company- Chicago Stack 4 12.2 - 19 Y 27.70 0.94 Rexam Beverage Can Company- Chicago Stack 5 12.8 - 23 Y 27.70 0.94 Rexam Beverage Can Company- Chicago Stack 6 13.7 - 31 Y 24.40 0.94 Rexam Beverage Can Company- Chicago Stack 7 14.0 - 26 Y 27.70 0.94 Rexam Beverage Can Company- Chicago Stack 8 14.0 - 34 Y 24.40 0.94 Rexam Beverage Can Company- Chicago Stack 9 15.2 - 41 Y 24.40 0.94 Rexam Beverage Can Company- Chicago Fugitive 4.3 10 46 Y 40.32 0.94 

Crown Beverage Packaging - Lacrosse Stack 1 13.7 - 12 N 27.70 1.00 Crown Beverage Packaging - Lacrosse Fugitive 3.0 10 70 N 36.10 1.00 

Page 3 of 4
Table D-2. Tier 1 Sensitivity Analysis Long-Term Modeling Parameters and Individual Source R

Facility Name Source ID Release Height (m)

Volume 

Source 

Length of 

Side (m)

Distance 

to Nearest 

Receptor 

(m)

Physical 

Fence 

(Y/N)

EPA Tier 1 Table: 

Normalized 

Maximum Annual 

Conc. 

(μg/m3)/(tpy)

Proportion 

EGBE of Certain 

Glycol Ethers

RR Donnelley-Harrisonburg Point 11.2 - 45 Unknown 24.40 1.00 

RR Donnelley-Harrisonburg Fugitive 3.1 10 210 Unknown 13.79 1.00 

Rexam Beverage Can Company- Winston-Sale Stacks 1-10 14.0 - 75 Unknown 21.10 0.95 Rexam Beverage Can Company- Winston-Sale Fugitive 3.0 10 91.7 Unknown 36.10 0.95 

Page 4 of 4
Table D-3. Tier 1 Sensitivity Analysis Long-Term Modeling Summary for Selected Facilities

2009 TRI 2010 TRI 2011 TRI

Maximum 

Annual Tier I 

EGBE Conc. 

(μg/m3

)

Long-Term 

HQ 

(combined)

Maximum 

Annual Tier I 

EGBE Conc. 

(μg/m3

)

Long-Term 

HQ 

(combined)

Maximum 

Annual Tier I 

EGBE Conc. 

(μg/m3

)

Lon

(co

Crown Beverage Packaging - Lawrence Point 3654.7 3176.1 3553.4

Volume 589.5 512.3 573.2

RR Donnelley-Harrisonburg Point 104.4 87.5 74.7

Volume 498.5 535.1 623.5

Ball Metal Food Container Corp- Williamsburg Point 2852.4 3056.1 2954.3

Volume 651.8 688.0 675.9

Crown Cork & Seal Co (USA) - Weirton Point 1753.1 1665.4 1598.8

Volume 1526.5 1450.2 1392.2

Rexam Beverage Can Company- Winston-Salem Point 2885.0 3158.4 2214.1

Volume 971.0 1070.7 882.0

Rexam Beverage Can Company- Bishopville Point 2268.3 2275.3 2099.0

Volume 521.7 523.3 482.6

Ball Container LLC - Columbus Point 1049.7 1364.6 1469.6

Volume 718.4 413.1 431.0

Ball Metal Beverage Container Corp- Findlay Point 2743.0 2743.0 2848.5

Volume 884.5 902.5 920.6

Silgan Containers Manufacturing Corp- LaPorte Point 1329.8 1354.2 1298.8

Volume 451.3 463.9 440.1

Crown Beverage Packaging - Lacrosse Point 47.4 46.0 49.8

Volume 823.6 799.2 865.6

Crown Food Packaging - Owatonna Point 1833.0 1919.7 1998.5

Volume 725.5 761.0 789.3

Rexam Beverage Can Company- Chicago Point 1342.4 1395.9 691.5

Volume 515.3 536.8 246.4

Crown Beverage Packaging - Bradley Point 1253.3 1171.5 1185.5

Volume 608.1 568.4 575.2

Rexam Beverage Can Company- Kent Point 2068.4 1953.6 1950.4

Volume 475.7 449.3 448.6

Crown Beverage Packaging - Olympia Point 1177.4 1336.4 1100.4

Volume 579.7 659.1 542.7

Bold text indicates an HQ greater than 1EGBE: ethylene glycol monobutyl etherHQ: hazard quotientRfC: reference concentrationTRI: Toxics Release Inventoryμg/m3: micrograms per cubic meter

Hazard quotient (HQ) equals the sum of the maximum annual average concentration for fugitive/volume source emissions and point source emissions, at or bethe fence line, is compared to an RfC for EGBE of 1,600 μg/m3

.

21

212112 121

0.5

1

0.5

211

2

0.4

223

Site Name Source Type

23

0.4

22221
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Te

Ball Container LLC - Columbus Stack 1 L1-IBO-Hot 21.49 0.686 9.64 

Ball Container LLC - Columbus Stack 2 L1-ISS 21.79 0.405 11.70 

Ball Container LLC - Columbus Stack 3 L1-PO1-Hot 25.91 0.381 19.16 

Ball Container LLC - Columbus Stack 4 L1-PO2-Hot 15.85 0.405 20.70 

Ball Container LLC - Columbus Stack 5 L1-PR-11 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 6 L1-PR-12 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 7 L2-IBO-Hot 21.49 0.686 2.71 

Ball Container LLC - Columbus Stack 8 L2-ISS 21.79 0.405 11.70 

Ball Container LLC - Columbus Stack 9 L2-PO1-Hot 25.91 0.393 19.19 

Ball Container LLC - Columbus Stack 10 L2-PO2-Hot 25.91 0.381 15.63 

Ball Container LLC - Columbus Stack 11 L2-PR-21 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 12 L2-PR-22 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 13 L3-IBO-Hot 25.91 0.686 7.59 

Ball Container LLC - Columbus Stack 14 L3-ISS 21.79 0.405 11.70 

Ball Container LLC - Columbus Stack 15 L3-PO1-Hot 25.91 0.381 17.20 

Ball Container LLC - Columbus Stack 16 L3-PO2-Hot 25.91 0.393 14.71 

Ball Container LLC - Columbus Stack 17 L3-PR-31 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 18 L3-PR-32 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 19 L4-BCO-Hot 21.49 0.393 17.23 

Ball Container LLC - Columbus Stack 20 L4-IBO-Hot 25.91 0.381 32.32 Ball Container LLC - Columbus Stack 21 L4-ISS 21.79 0.405 7.31 

Ball Container LLC - Columbus Stack 22 L4-PO-Hot 25.91 0.686 5.00 

Ball Container LLC - Columbus Stack 23 L4-PR-41 15.75 1.119 1.30 

Ball Metal Beverage Container Corp- Findlay Stack 1 B_PO11 PO11 16.61 0.457 7.00 

Ball Metal Beverage Container Corp- Findlay Stack 2 B_PO12 PO12 16.61 0.305 29.07 

Ball Metal Beverage Container Corp- Findlay Stack 3 B_PO21 PO21 19.81 0.457 9.79 

Ball Metal Beverage Container Corp- Findlay Stack 4 B_PO22 PO22 19.81 0.457 11.32 

Ball Metal Beverage Container Corp- Findlay Stack 5 B_IBO11 IBO11 14.17 0.610 11.62 

Ball Metal Beverage Container Corp- Findlay Stack 6 B_IBO21B IBO21-B 21.18 0.610 3.98 

Ball Metal Beverage Container Corp- Findlay Stack 7 B_IBO31 IBO31 21.64 0.864 5.12 

Ball Metal Beverage Container Corp- Findlay Stack 8 B_WCO31 WashCoat Ov 20.42 0.813 2.58 

Ball Metal Beverage Container Corp- Findlay Stack 9 B_BH Baghouse 20.73 0.330 37.48 

Ball Metal Food Container Corp- Williamsburg Stack 1 PO2 S019 18.47 0.406 13.53 

Ball Metal Food Container Corp- Williamsburg Stack 2 PO3 S006 18.87 0.406 12.25 

Ball Metal Food Container Corp- Williamsburg Stack 3 PO4Z1 S035 15.54 0.483 6.77 

Ball Metal Food Container Corp- Williamsburg Stack 4 PO4Z2 S036 15.16 0.483 9.49 

Table D-4. Tier 2 Modeling Stack Parameters and Individual Source Results at Individual 

Page 1 of 4
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Te

Table D-4. Tier 2 Modeling Stack Parameters and Individual Source Results at Individual 

Ball Metal Food Container Corp- Williamsburg Stack 5 PO5Z1 S037 13.13 0.483 9.63 Ball Metal Food Container Corp- Williamsburg Stack 6 PO5Z2 S038 13.13 0.483 8.84 Ball Metal Food Container Corp- Williamsburg Stack 7 IBO2Z1 S021 18.52 0.406 7.60 Ball Metal Food Container Corp- Williamsburg Stack 8 IBO2Z2 S020 18.42 0.508 6.60 Ball Metal Food Container Corp- Williamsburg Stack 9 IBO3Z1 S011 18.34 0.406 6.06 Ball Metal Food Container Corp- Williamsburg Stack 10 IBO3Z2 S010 18.59 0.508 7.29 Ball Metal Food Container Corp- Williamsburg Stack 11 IBO4/5Z1 S027 18.31 0.406 2.85 

Ball Metal Food Container Corp- Williamsburg Stack 12 IBO4/5Z2 S028 18.29 0.508 5.13 Ball Metal Food Container Corp- Williamsburg Stack 13 IBO4/5Z3 S039 18.34 0.406 13.05 

Ball Metal Food Container Corp- Williamsburg Stack 14 BCPOL2 S016 18.47 0.406 13.01 

Ball Metal Food Container Corp- Williamsburg Stack 15 BCPOL4Z1 S033 15.54 0.483 9.00 

Ball Metal Food Container Corp- Williamsburg Stack 16 BCPOL4Z2 S034 15.54 0.483 10.22 

Ball Metal Food Container Corp- Williamsburg Stack 17 ICEXH02 S024 17.86 0.305 11.26 

Ball Metal Food Container Corp- Williamsburg Stack 18 ICEXH03 S023 17.86 0.305 11.89 

Ball Metal Food Container Corp- Williamsburg Stack 19 ICEXH045 S022 17.86 0.406 8.61 

Crown Beverage Packaging - Bradley Stack 1 IBO IBO (Can Line 18.29 0.305 10.20 

Crown Beverage Packaging - Bradley Stack 2 Ross Ross (Can Lin 15.24 0.305 16.72 Crown Beverage Packaging - Bradley Stack 3 IBO IBO (Can Line 15.24 0.305 9.51 Crown Beverage Packaging - Bradley Stack 4 Ross Ross (Can Lin 18.29 0.305 16.72 Crown Beverage Packaging - Bradley Stack 5 IBO IBO (Can Line 15.24 0.305 10.20 

Crown Beverage Packaging - Bradley Stack 6 Ross Ross (Can Lin 15.24 0.305 16.72 

Crown Beverage Packaging - Bradley Stack 7 Ross Ross (Can Lin 18.29 0.305 16.72 Crown Beverage Packaging - Olympia Stack 1 IBO #1A 14.33 0.710 3.97 

Crown Beverage Packaging - Olympia Stack 2 IBO #2C 16.76 1.067 7.98 

Crown Beverage Packaging - Olympia Stack 3 LSM #1A 12.80 0.280 8.32 

Crown Beverage Packaging - Olympia Stack 4 LSM #2A 12.80 0.280 6.91 

Crown Beverage Packaging - Lawrence Stack 1 LSM2 8.53 0.457 1.42 

Crown Beverage Packaging - Lawrence Stack 2 L1PO 8.53 0.457 2.10 Crown Beverage Packaging - Lawrence Stack 3 IBO1 8.53 0.457 3.31 

Crown Beverage Packaging - Lawrence Stack 4 LSM1 8.53 0.457 1.18 

Crown Beverage Packaging - Lawrence Stack 5 L1V1 8.53 0.457 3.42 Crown Beverage Packaging - Lawrence Stack 6 IBO3 8.53 0.457 10.25 

Crown Beverage Packaging - Lawrence Stack 7 L3S 8.53 0.457 1.18 

Crown Beverage Packaging - Lawrence Stack 8 L3VI 8.53 0.457 3.42 

Crown Beverage Packaging - Lawrence Stack 9 IBO4 8.53 0.457 8.52 

Crown Beverage Packaging - Lawrence Stack 10 L4S 8.53 0.457 1.42 

Page 2 of 4
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Te

Table D-4. Tier 2 Modeling Stack Parameters and Individual Source Results at Individual 

Crown Beverage Packaging - Lawrence Stack 11 L3PO 8.53 0.457 3.42 

Crown Beverage Packaging - Lawrence Stack 12 IBO2 8.53 0.457 3.68 Crown Cork & Seal Co (USA) - Weirton Stack 1 TO-1 11.00 1.219 16.17 

Crown Cork & Seal Co (USA) - Weirton Stack 2 TO-2 17.00 0.597 13.49 Crown Food Packaging - Owatonna Stack 1 EU-001 17.98 0.311 31.08 Crown Food Packaging - Owatonna Stack 2 EU-003 17.98 0.311 18.65 Crown Food Packaging - Owatonna Stack 3 EU-005 17.98 0.311 18.65 Crown Food Packaging - Owatonna Stack 4 EU-007 17.98 0.311 31.08 Crown Food Packaging - Owatonna Stack 5 EU-008 17.98 0.311 31.08 Rexam Beverage Can Company- Bishopville Stack 1 SV4 Printer Oven S 15.24 0.457 6.10 

Rexam Beverage Can Company- Bishopville Stack 2 SV5 Printer Oven S 15.54 0.396 6.10 Rexam Beverage Can Company- Bishopville Stack 3 SV 6 Inside Spray M 11.58 0.610 3.96 

Rexam Beverage Can Company- Bishopville Stack 4 SV 7 Inside Spray M 14.02 0.610 3.96 

Rexam Beverage Can Company- Bishopville Stack 5 SV 8 Inside Spray M 14.02 0.610 3.96 Rexam Beverage Can Company- Bishopville Stack 6 SV9 Inside Bake O 15.24 0.762 4.88 Rexam Beverage Can Company- Bishopville Stack 7 SV10 Inside Bake O 15.24 0.762 4.88 Rexam Beverage Can Company- Bishopville Stack 8 SV11 Inside Bake O 15.24 0.762 4.88 Rexam Beverage Can Company- Chicago Stack 1 REX_SV21 Printer Oven S 13.11 0.396 9.58 Rexam Beverage Can Company- Chicago Stack 2 REX_SV22 Printer Oven S 12.65 0.396 9.57 Rexam Beverage Can Company- Chicago Stack 3 REX_SV23 Base Coater P 13.17 0.396 9.57 Rexam Beverage Can Company- Chicago Stack 4 RED_SV31 Inside Spray M 12.19 1.097 2.50 Rexam Beverage Can Company- Chicago Stack 5 REX_SV32 Inside Spray M 12.80 1.189 2.13 

Rexam Beverage Can Company- Chicago Stack 6 REX_SV33 Inside Spray M 13.72 0.914 3.59 

Rexam Beverage Can Company- Chicago Stack 7 REX_SV41 Inside Bake O 14.02 0.762 8.07 Rexam Beverage Can Company- Chicago Stack 8 REX_SV42 Inside Bake O 14.02 0.823 6.92 Rexam Beverage Can Company- Chicago Stack 9 REX_RTO Regenerative 15.24 1.158 7.61 

Rexam Beverage Can Company- Kent Stack 1 SV7A Printer Pin Ov 14.63 0.558 4.83 

Rexam Beverage Can Company- Kent Stack 2 SV7B Printer Pin Ov 14.63 0.558 4.83 Rexam Beverage Can Company- Kent Stack 3 SV7C Printer Pin Ov 16.61 0.914 1.80 Rexam Beverage Can Company- Kent Stack 4 SV7D Printer Pin Ov 14.63 0.610 4.04 Rexam Beverage Can Company- Kent Stack 5 SV8A Inside Spray M 13.50 0.838 2.14 Rexam Beverage Can Company- Kent Stack 6 SV8B Inside Spray M 14.17 0.838 2.14 Rexam Beverage Can Company- Kent Stack 7 SV8C Inside Spray M 13.20 0.850 2.08 

Rexam Beverage Can Company- Kent Stack 8 SV8D Inside Spray M 13.72 0.838 2.14 

Rexam Beverage Can Company- Kent Stack 9 SV9A Inside Bake O 15.24 0.762 3.62 Rexam Beverage Can Company- Kent Stack 10 SV9B Inside Bake O 15.33 0.762 3.62 

Page 3 of 4
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Te

Table D-4. Tier 2 Modeling Stack Parameters and Individual Source Results at Individual 

Rexam Beverage Can Company- Kent Stack 11 SV9C Inside Bake O 15.33 0.762 3.62 

Rexam Beverage Can Company- Kent Stack 12 SV9D Inside Bake O 15.33 0.762 3.62 Rexam Beverage Can Company- Salem Stack 1 Stack1 14.00 6.096 0.46 

Rexam Beverage Can Company- Salem Stack 2 Stack2 14.00 6.096 0.46 

Rexam Beverage Can Company- Salem Stack 3 Stack3 14.00 6.096 0.46 

Rexam Beverage Can Company- Salem Stack 4 Stack4 14.00 6.096 0.46 

Rexam Beverage Can Company- Salem Stack 5 Stack5 14.00 6.096 0.46 

Silgan Containers Manufacturing Corp- LaPorte Stack 1 C11 L1Roll1 15.80 0.719 17.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 2 C12 L1Roll2 15.80 0.719 7.37 

Silgan Containers Manufacturing Corp- LaPorte Stack 3 C13 L1IS1 17.11 0.905 5.13 

Silgan Containers Manufacturing Corp- LaPorte Stack 4 C14 L1IS2 17.11 0.905 5.13 

Silgan Containers Manufacturing Corp- LaPorte Stack 5 C15 L1IS3 17.11 0.905 12.32 

Silgan Containers Manufacturing Corp- LaPorte Stack 6 C16 L1IS4 17.11 0.914 10.78 

Silgan Containers Manufacturing Corp- LaPorte Stack 7 C21 L2Roll1 15.80 0.719 17.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 8 C22 L2Roll2 15.80 0.719 7.37 

Silgan Containers Manufacturing Corp- LaPorte Stack 9 C23 L2IS1 16.46 0.799 9.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 10 C24 L2IS2 16.78 0.799 18.85 

Silgan Containers Manufacturing Corp- LaPorte Stack 11 S1 IS_1_Over_Fu 16.00 0.695 12.44 

Silgan Containers Manufacturing Corp- LaPorte Stack 12 S2 IS_2_Over_Fu 16.13 0.362 45.87 

a. All point EGBE emissions were conservatively assumed to exhaust through each stack for AERSCREEN modeling.

The emission rate for each source is calculated from the TRI reported stack emissions of Certain Glycol Ethers as follows:

 EGBE Emission Rate (g/s) = Stack TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 8,760 (hrs/yr) The calculated emission rate assumes EGBE emissions occur continuously 8,760 hours per year.b. Worst case annual average unit emission rate concentration in (μg/m3) (1g/s) assumes stack emission rate of 1 g/s.

It is obtained by multiplying worst-case 1-hr average unit emission rate concentration by a factor of 0.1, in accordance with EPA's AERSCREE

 Tier 2 annual concentration for a stack is obtained by multiplying the unit emission rate concentration by Tier 2 stack emission rate (in g/s) for 

The maximum point source unit emission rate impact (considering all point sources for a facility) is shown in bolded text.

g/s: grams per secondK: degrees Kelvinm: meterm/s: meters per second

μg/m3: micrograms per cubic meter

tpy: ton per year

TRI: Toxic Release Inventory

Page 4 of 4
Site Name Source Type

Volume 

Release 

Height (m) b

Volume Intial 

Lateral 

Dimension (m) 

c

Volume Intial 

Vertical 

Dimension 

(m) d

2009 TRI 

Emission Rate 

(g/s)e

2010 TRI 

Emission Rate 

(g/s)e

2011 TRI 

Emission R

(g/s)e

Ball Container LLC - Columbus Volume 12.420 22.790 5.777 0.572 0.32916 0.34347 Ball Metal Beverage Container Corp- Findlay Volume 12.420 11.230 5.780 0.705 0.71917 0.73355 Ball Metal Food Container Corp- Williamsburg Volume 14.630 13.730 6.805 0.750 0.79165 0.77776 Crown Beverage Packaging - Bradley Volume 7.315 19.850 3.402 0.434 0.40553 0.41038 Crown Beverage Packaging - Olympia Volume 10.670 24.820 4.962 0.462 0.52520 0.43242 Crown Beverage Packaging - Lawrence Volume 6.096 27.300 2.835 0.470 0.40825 0.45675 Crown Cork & Seal Co (USA) - Weirton Volume 9.144 14.120 4.253 1.089 1.03458 0.99320 Crown Food Packaging - Owatonna Volume 10.670 30.710 4.962 0.835 0.87561 0.90821 Rexam Beverage Can Company- Bishopville Volume 10.670 28.840 4.962 0.416 0.41699 0.38457 Rexam Beverage Can Company- Chicago Volume 9.144 20.930 4.253 0.368 0.38295 0.17576 Rexam Beverage Can Company- Kent Volume 7.925 24.550 3.686 0.379 0.35802 0.35745 Rexam Beverage Can Company- Salem Volume 7.000 27.240 3.250 0.774 0.85314 0.70277 Silgan Containers Manufacturing Corp- LaPorte Volume 12.192 20.698 5.670 0.360 0.36965 0.35069 a. Fugitive releases of EGBE are reported to occur through the building's roof vents in the production

area of the facility building where stacks emitting EGBE are located. Fugitive emissions from the roof

vents are modeled as a single volume source.

b. The volume source release height is taken to be at the release height of fugitive emissions;

it is set to be equal to the roof height of the process building

c. Per EPA's AERMOD guidance, the volume source initial lateral dimension is taken to be the length of the side of

the volume divided by 4.3.

d. Per EPA's AERMOD guidance, the volume source initial vertical dimension is taken to be the

height of the volume source (roof height) divided by 2.15.

e. The emission rate for each source is calculated from the TRI reported fugitive emissions of Certain Glycol Ethers as follows:

EGBE Emission Rate (g/s) = Fugitive TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 8,760 (hrs/yr)

The calculated emission rate assumes EGBE emissions occur continuously 8,760 hours per year.

f. Worst case annual average unit emission rate concentration in (μg/m3) (1g/s) assumes fugitive emission rate of 1 g/s.

Tier 2 annual concentration for a fugitive volume is obtained by multiplying the unit emission rate concentration

by Tier 2 fugitive emission rate (in g/s) for a given TRI year

g/s: grams per secondhrs/yr: hours per yearm: metertpy: ton per year

TRI: Toxic Release Inventory

Table D-5. Tier 2 Modeling Fugitive Volume Parameters and Results at Individual Facilities
Table D-6. Tier 2 Modeling Stack Parameters and Individual Source Results in 

Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV21 Printer Oven Stack # 1 – SV 21 13.11 0.396 9.58 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV22 Printer Oven Stack # 2 – SV 22 12.65 0.396 9.57 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV23 Base Coater Pin Oven Stack # 3 – SV 23 13.17 0.396 9.57 

Rexam Beverage Can Company- Chicago Stack 4 RED_SV31 Inside Spray Machines Bank 1 – SV 31 12.19 1.097 2.50 

Rexam Beverage Can Company- Chicago Stack 5 REX_SV32 Inside Spray Machines Bank 2 – SV 32 12.80 1.189 2.13 Rexam Beverage Can Company- Chicago Stack 6 REX_SV33 Inside Spray Machines Bank 2 – SV 33 13.72 0.914 3.59 

Rexam Beverage Can Company- Chicago Stack 7 REX_SV41 Inside Bake Oven Stack # 1 – SV 41 14.02 0.762 8.07 

Rexam Beverage Can Company- Chicago Stack 8 REX_SV42 Inside Bake Oven Stack # 2 – SV 42 14.02 0.823 6.92 

Rexam Beverage Can Company- Chicago Stack 9 REX_RTO Regenerative Thermal Oxidizer Stack 15.24 1.158 7.61 

Edsal Manufacturing Co Inc- Chicago Stack1 N/A 3960*** 9.75 0.396 2.74 Ball Metal Beverage Container Corp- Findlay Stack 1 B_PO11 PO11 16.61 0.457 7.00 

Ball Metal Beverage Container Corp- Findlay Stack 2 B_PO12 PO12 16.61 0.305 29.07 

Ball Metal Beverage Container Corp- Findlay Stack 3 B_PO21 PO21 19.81 0.457 9.79 

Ball Metal Beverage Container Corp- Findlay Stack 4 B_PO22 PO22 19.81 0.457 11.32 

Ball Metal Beverage Container Corp- Findlay Stack 5 B_IBO11 IBO11 14.17 0.610 11.62 

Ball Metal Beverage Container Corp- Findlay Stack 6 B_IBO21B IBO21-B 21.18 0.610 3.98 

Ball Metal Beverage Container Corp- Findlay Stack 7 B_IBO31 IBO31 21.64 0.864 5.12 

Ball Metal Beverage Container Corp- Findlay Stack 8 B_WCO31 WashCoat Oven31 20.42 0.813 2.58 

Ball Metal Beverage Container Corp- Findlay Stack 9 B_BH Baghouse 20.73 0.330 37.48 

Whirlpool Corp Findlay Div- Findlay Stack 1 Stk_2 8194  12.19 0.305 0.39 Silgan Containers Manufacturing Corp- LaPorte Stack 1 C11 L1Roll1 15.80 0.719 17.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 2 C12 L1Roll2 15.80 0.719 7.37 

Silgan Containers Manufacturing Corp- LaPorte Stack 3 C13 L1IS1 17.11 0.905 5.13 

Silgan Containers Manufacturing Corp- LaPorte Stack 4 C14 L1IS2 17.11 0.905 5.13 

Silgan Containers Manufacturing Corp- LaPorte Stack 5 C15 L1IS3 17.11 0.905 12.32 

Silgan Containers Manufacturing Corp- LaPorte Stack 6 C16 L1IS4 17.11 0.914 10.78 

Silgan Containers Manufacturing Corp- LaPorte Stack 7 C21 L2Roll1 15.80 0.719 17.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 8 C22 L2Roll2 15.80 0.719 7.37 

Silgan Containers Manufacturing Corp- LaPorte Stack 9 C23 L2IS1 16.46 0.799 9.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 10 C24 L2IS2 16.78 0.799 18.85 

Silgan Containers Manufacturing Corp- LaPorte Stack 11 S1 IS_1_Over_Fug 16.00 0.695 12.44 Silgan Containers Manufacturing Corp- LaPorte Stack 12 S2 IS_2_Over_Fug 16.13 0.362 45.87 

Roll Coater- La Porte Stack 1 Stk_2 not used 9.14 0.914 3.23 Ball Metal Food Container Corp- Weirton Stack 1 0001 0001 (Bldg 5G) 12.80 2.070 8.41 Ball Metal Food Container Corp- Weirton Stack 2 TO-1 TO-1 (Bldg 5D) 11.58 1.220 7.80 Ball Metal Food Container Corp- Weirton Stack 3 TO-2 TO-2 (Bldg 5D) 10.67 0.670 6.86 Ball Metal Food Container Corp- Weirton Stack 4 0003 0003 (Bldg 5D) 10.05 0.640 1.66 Crown Cork & Seal Co (USA) - Weirton Stack 1 TO-1 11.00 1.219 16.17 

Crown Cork & Seal Co (USA) - Weirton Stack 2 TO-2 17.00 0.597 13.49 

Ardagh Metal Packaging USA Inc- Weirton Stack 1 Coater #1 12.50 0.610 31.01 

Ardagh Metal Packaging USA Inc- Weirton Stack 2 Coater #2 14.33 0.610 9.15 

Ardagh Metal Packaging USA Inc- Weirton Stack 3 Coater #3 12.50 0.457 22.27 

Ardagh Metal Packaging USA Inc- Weirton Stack 4 Coater #4 12.19 0.457 15.45 Roll Coater- Weirton Stack 1 No stack parameters available. All emissions (stack + fugitives) modeled as a volume

Page 1 of 2
Table D-6. Tier 2 Modeling Stack Parameters and Individual Source Results in 

Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Ball Metal Beverage Container Corp- Reidsville Stack 1 PO1 15.95 0.508 4.32 Ball Metal Beverage Container Corp- Reidsville Stack 2 PO2 16.31 0.508 4.28 Ball Metal Beverage Container Corp- Reidsville Stack 3 PO3 16.08 0.508 6.14 Ball Metal Beverage Container Corp- Reidsville Stack 4 IBO1 16.00 0.457 12.15 Ball Metal Beverage Container Corp- Reidsville Stack 5 IBO2 16.00 0.457 7.11 Ball Metal Beverage Container Corp- Reidsville Stack 6 IBO3 16.00 0.457 13.17 Ball Metal Beverage Container Corp- Reidsville Stack 7 Printer 1 15.95 0.508 0.50 

Ball Metal Beverage Container Corp- Reidsville Stack 8 Printer 2 15.90 0.508 0.50 Ball Metal Beverage Container Corp- Reidsville Stack 9 Printer 3 16.08 0.508 0.50 Ball Metal Beverage Container Corp- Reidsville Stack 10 Spray line 1 14.94 0.381 6.39 

Ball Metal Beverage Container Corp- Reidsville Stack 11 Spray line 2 14.99 0.381 7.28 Ball Metal Beverage Container Corp- Reidsville Stack 12 Spray line 3 14.99 0.381 8.74 Dystar LP- Reidsville Stack 1 Stk_2 11.64 0.432 5.44 

a. All point EGBE emissions were conservatively assumed to exhaust through each stack for AERSCREEN modeling. 

The emission rate for each source is calculated from the TRI reported stack emissions of Certain Glycol Ethers as follows:

 EGBE Emission Rate (g/s) = Stack TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 8,760 (hrs/yr) The calculated emission rate assumes EGBE emissions occur continuously 8,760 hours per year.b. Worst case annual average unit emission rate concentration in (μg/m3) (1g/s) assumes stack emission rate of 1 g/s.

It is obtained by multiplying worst-case 1-hr average unit emission rate concentration by a factor of 0.1, in accordance with EPA's AERSCREEN guidance

 Tier 2 annual concentration for a stack is obtained by multiplying the unit emission rate concentration by Tier 2 stack emission rate (in g/s) for a given TRI year

The maximum point source unit emission rate impact (considering all point sources for a facility) is shown in bolded text. 

g/s: grams per secondK: degrees Kelvinm: meterm/s: meters per second

μg/m3: micrograms per cubic meter

tpy: ton per year

TRI: Toxic Regulatory Index

Page 2 of 2
Table D-7. Tier 2 Modeling Fugitive Volume Parameters and Results in Clusters

Site Name Source Type

Volume 

Release 

Height (m) b

Volume Intial Lateral 

Dimension (m) c

Volume Intial 

Vertical 

Dimension (m) 

d

2009 TRI 

Emission 

Rate (g/s)e

2010 TRI 

Emission Rate 

(g/s)e

2011 

Emissio

(g/s

Rexam Beverage Can Company- Chicago Volume 9.144 20.930 4.253 0.368 0.38295 0.175Edsal Manufacturing Co Inc- Chicago Volume No fugitive emissions reported to TRI. All reported emissions modeled as a stack releaseBall Metal Beverage Container Corp- Findlay Volume 12.420 11.230 5.780 0.705 0.71917 0.733Whirlpool Corp Findlay Div- Findlay Volume 8.800 47.280 4.093 0.066 0.06437 0.06Silgan Containers Manufacturing Corp- LaPorte Volume 12.192 20.698 5.670 0.360 0.36965 0.350Roll Coater- La Porte Volume 9.144 39.535 4.251 0.000 0.00000 0.000Ball Metal Food Container Corp, Bldg_5D- Weirtong Volume 7.315 19.900 3.402 0.338 0.19243 0.132

Ball Metal Food Container Corp, Bldg_5G- Weirtong Volume 12.192 16.247 5.670 0.174 0.09913 0.068Crown Cork & Seal Co (USA) - Weirton Volume 9.144 14.120 4.253 1.089 1.03458 0.993Ardagh Metal Packaging USA Inc- Weirton Volume 9.750 11.881 4.540 0.000 0.00011 0.00

Roll Coater- Weirton Volume 9.144 16.000 4.250 0.164 0.20797 0.075Ball Metal Beverage Container Corp- Reidsville Volume 13.106 30.930 6.096 0.334 0.40419 0.473

Dystar LP- Reidsville Volume 10.000 9.698 4.651 0.001 0.00101 0.00

a. Fugitive releases of EGBE are reported to occur through the building's roof vents in the production

area of the facility building where stacks emitting EGBE are located. Fugitive emissions from the roof

vents are modeled as a single volume source.

b. The volume source release height is taken to be at the release height of fugitive emissions;

it is set to be equal to the roof height of the process building

c. Per EPA's AERMOD guidance, the volume source initial lateral dimension is taken to be the length of the side of

the volume divided by 4.3.

d. Per EPA's AERMOD guidance, the volume source initial vertical dimension is taken to be the

height of the volume source (roof height) divided by 2.15.

e. The emission rate for each source is calculated from the TRI reported fugitive emissions of Certain Glycol Ethers as follows:

EGBE Emission Rate (g/s) = Fugitive TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 8,760 (hrs/yr)

The calculated emission rate assumes EGBE emissions occur continuously 8,760 hours per year.

f. Worst case annual average unit emission rate concentration in (μg/m3) (1g/s) assumes fugitive emission rate of 1 g/s.

Tier 2 annual concentration for a fugitive volume is obtained by multiplying the unit emission rate concentration

by Tier 2 fugitive emission rate (in g/s) for a given TRI year

g. Ball Facility in Weirton has two distinct (physically separate) buildings associtaed with fugitive emissions which were modeled separately.

Their emissions were estimated based on the breakdown of the total fugitive emissions provided by the faciltiy in Tier 2 Survey a signle volume (building) with worse dispersion characteristics

g/s: grams per secondhrs/yr: hours per yearm: metertpy: ton per year

TRI: Toxic Release Inventory
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) 

Crown Beverage Packaging - Lawrence Stack 1 LSM2 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 2 L1PO 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 3 IBO1 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 4 LSM1 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 5 L1V1 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 6 IBO3 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 7 L3S 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 8 L3VI 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 9 IBO4 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 10 L4S 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 11 L3PO 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 12 IBO2 8.530 0.457 

Crown Beverage Packaging - Lacrosse Stack 1 S30 13.720 0.966 

Crown Cork & Seal Co (USA) - Weirton Stack 1 TO-1 11.000 1.219 Crown Cork & Seal Co (USA) - Weirton Stack 2 TO-2 17.000 0.597 Rexam Beverage Can Company- Bishopville Stack 1 SV4 Printer Oven Stack # 1 – SV4 15.200 0.460 

Rexam Beverage Can Company- Bishopville Stack 2 SV5 Printer Oven Stack # 2 – SV5 15.500 0.400 Rexam Beverage Can Company- Bishopville Stack 3 SV 6 Inside Spray Machines Bank 1 – SV 6 11.600 0.610 Rexam Beverage Can Company- Bishopville Stack 4 SV 7 Inside Spray Machines Bank 2 – SV 7 14.000 0.610 Rexam Beverage Can Company- Bishopville Stack 5 SV 8 Inside Spray Machines Bank 3 – SV 8 14.000 0.610 Rexam Beverage Can Company- Bishopville Stack 6 SV9 Inside Bake Oven Stack # 1 – SV9 15.200 0.760 

Rexam Beverage Can Company- Bishopville Stack 7 SV10 Inside Bake Oven Stack # 2 – SV10 15.200 0.760 

Rexam Beverage Can Company- Bishopville Stack 8 SV11 Inside Bake Oven Stack # 3 – SV11 15.200 0.760 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV21 Printer Oven Stack # 1 – SV 21 13.106 0.396 Rexam Beverage Can Company- Chicago Stack 1 REX_SV22 Printer Oven Stack # 2 – SV 22 12.649 0.396 Rexam Beverage Can Company- Chicago Stack 1 REX_SV23 Base Coater Pin Oven Stack # 3 – SV 23 13.167 0.396 Rexam Beverage Can Company- Chicago Stack 4 RED_SV31 Inside Spray Machines Bank 1 – SV 31 12.192 1.097 Rexam Beverage Can Company- Chicago Stack 5 REX_SV32 Inside Spray Machines Bank 2 – SV 32 12.802 1.189 Rexam Beverage Can Company- Chicago Stack 6 REX_SV33 Inside Spray Machines Bank 2 – SV 33 13.716 0.914 Rexam Beverage Can Company- Chicago Stack 7 REX_SV41 Inside Bake Oven Stack # 1 – SV 41 14.021 0.762 Rexam Beverage Can Company- Chicago Stack 8 REX_SV42 Inside Bake Oven Stack # 2 – SV 42 14.021 0.823 Rexam Beverage Can Company- Chicago Stack 9 REX_RTO Regenerative Thermal Oxidizer Stack 15.240 1.158 Rexam Beverage Can Company- Kent Stack 1 SV7A Printer Pin Oven Stack 1 – SV 7A 14.630 0.558 

Rexam Beverage Can Company- Kent Stack 2 SV7B Printer Pin Oven Stack 2 – SV 7B 14.630 0.558 

Rexam Beverage Can Company- Kent Stack 3 SV7C Printer Pin Oven Stack 3 – SV 7C 16.612 0.914 

Rexam Beverage Can Company- Kent Stack 4 SV7D Printer Pin Oven Stack 4 – SV 7D 14.630 0.610 

Rexam Beverage Can Company- Kent Stack 5 SV8A Inside Spray Machines Bank 1 – SV 8A 13.503 0.838 

Rexam Beverage Can Company- Kent Stack 6 SV8B Inside Spray Machines Bank 2 – SV 8B 14.173 0.838 

Rexam Beverage Can Company- Kent Stack 7 SV8C Inside Spray Machines Bank 3 – SV 8C 13.198 0.850 

Rexam Beverage Can Company- Kent Stack 8 SV8D Inside Spray Machines Bank 4 – SV 8D 13.716 0.838 

Rexam Beverage Can Company- Kent Stack 9 SV9A Inside Bake Oven Stack # 1 – SV 9A 15.240 0.762 

Table D-8. Tier 3 Modeling Stack Parameters at Individual Faciliti

Page 1 of 2
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) 

Table D-8. Tier 3 Modeling Stack Parameters at Individual Faciliti

Rexam Beverage Can Company- Kent Stack 10 SV9B Inside Bake Oven Stack # 2 – SV 9B 15.331 0.762 

Rexam Beverage Can Company- Kent Stack 11 SV9C Inside Bake Oven Stack # 3 – SV 9C 15.331 0.762 

Rexam Beverage Can Company- Kent Stack 12 SV9D Inside Bake Oven Stack # 4 – SV 9D 15.331 0.762 Rexam Beverage Can Company - Winston Salem Stack 1 WS1 14.000 0.457 Rexam Beverage Can Company - Winston Salem Stack 2 WS2 14.000 0.457 Rexam Beverage Can Company - Winston Salem Stack 3 WS3 14.000 0.457 Rexam Beverage Can Company - Winston Salem Stack 4 WS4 14.000 0.457 Rexam Beverage Can Company - Winston Salem Stack 5 WS5 14.000 0.457 

a. Individual stack emissions were based on total TRI Stack emissions and actual breakdown of EGBE emissions among individual stacks

The emission rate for each source is calculated from the TRI reported stack emissions of Certain Glycol Ethers as follows:

 EGBE Emission Rate (g/s) = Stack TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 8,760 (hrs/yr) x Stack_fraction

The calculated emission rate assumes EGBE emissions occur continuously 8,760 hours per year.Stack_fraction represents the percent of the total TRI stack emissions emitted through the individual stack

g/s: grams per secondK: degrees Kelvinm: meterm/s: meters per second

μg/m3: micrograms per cubic meter

tpy: ton per year

TRI: Toxic Release Inventory

Page 2 of 2
Table D-9. Tier 3 Modeling Fugitive Volume Parameters and Results at Individual Facilities

Site Name Source Type

Volume Release 

Height (m) b

Volume Intial 

Lateral 

Dimension (m) c

Volume Intial 

Vertical 

Dimension (m) d

2009 TRI 

Emission Rate 

(g/s)e

Crown Beverage Packaging - Lawrence Volume 6.096 27.310 2.840 0.470 

Crown Cork & Seal Co (USA) - Weirton Volume 9.144 14.120 4.253 1.089 

Rexam Beverage Can Company- Bishopville Volume 10.668 28.840 4.960 0.416 

Rexam Beverage Can Company- Chicago Volume 9.144 20.900 4.253 0.368 Rexam Beverage Can Company- Kent Volume 7.920 24.558 3.686 0.379 

Rexam Beverage Can Company - Winston Salem Volume 7.000 27.242 3.250 0.774 

a. Fugitive releases of EGBE are reported to occur through the building's roof vents in the production

area of the facility building where stacks emitting EGBE are located. Fugitive emissions from the roof

vents are modeled as a single volume source.

b. The volume source release height is taken to be at the release height of fugitive emissions;

it is set to be equal to the roof height of the process building

c. Per EPA's AERMOD guidance, the volume source initial lateral dimension is taken to be the length of the side of

the volume divided by 4.3.

d. Per EPA's AERMOD guidance, the volume source initial vertical dimension is taken to be the

height of the volume source (roof height) divided by 2.15.

e. The emission rate for each source is calculated from the TRI reported fugitive emissions of Certain Glycol Ethers as follows:

EGBE Emission Rate (g/s) = Fugitive TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 8,760 (hrs/yr)

The calculated emission rate assumes EGBE emissions occur continuously 8,760 hours per year.

g/s: grams per secondhrs/yr: hours per yearm: metertpy: ton per year

TRI: Toxic Release Inventory
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV21 Printer Oven Stack # 1 – SV 21 13.100 0.396 Rexam Beverage Can Company- Chicago Stack 1 REX_SV22 Printer Oven Stack # 2 – SV 22 12.649 0.396 Rexam Beverage Can Company- Chicago Stack 1 REX_SV23 Base Coater Pin Oven Stack # 3 – SV 23 13.167 0.396 Rexam Beverage Can Company- Chicago Stack 4 RED_SV31 Inside Spray Machines Bank 1 – SV 31 12.192 1.097 Rexam Beverage Can Company- Chicago Stack 5 REX_SV32 Inside Spray Machines Bank 2 – SV 32 12.802 1.189 Rexam Beverage Can Company- Chicago Stack 6 REX_SV33 Inside Spray Machines Bank 2 – SV 33 13.716 0.914 Rexam Beverage Can Company- Chicago Stack 7 REX_SV41 Inside Bake Oven Stack # 1 – SV 41 14.021 0.762 Rexam Beverage Can Company- Chicago Stack 8 REX_SV42 Inside Bake Oven Stack # 2 – SV 42 14.021 0.823 Rexam Beverage Can Company- Chicago Stack 9 REX_RTO Regenerative Thermal Oxidizer Stack 15.240 1.158 Edsal Manufacturing Co Inc- Chicago Stack1 N/A 3960** * 9.144 0.396 Ball Metal Food Container Corp- Weirton Stack 1 BA5G_P1 0001 (Bldg 5G) 12.802 2.070 Ball Metal Food Container Corp- Weirton Stack 1 BA5D_PT1 TO-1 (Bldg 5D) 11.580 1.220 Ball Metal Food Container Corp- Weirton Stack 1 BA5D_PT2 TO-2 (Bldg 5D) 10.670 0.670 Ball Metal Food Container Corp- Weirton Stack 4 BA5D_P3 0003 (Bldg 5D) 10.050 0.640 Crown Cork & Seal Co (USA) - Weirton Stack 1 CR_PTO1 TO-1 11.000 1.219 Crown Cork & Seal Co (USA) - Weirton Stack 2 CR_PTO2 TO-2 17.000 0.597 Ardagh Metal Packaging USA Inc- Weirton Stack 1 AR_PC1 Coater #1 12.497 0.610 Ardagh Metal Packaging USA Inc- Weirton Stack 2 AR_PC2 Coater #2 14.330 0.610 Ardagh Metal Packaging USA Inc- Weirton Stack 3 AR_PC3 Coater #3 12.497 0.457 Ardagh Metal Packaging USA Inc- Weirton Stack 4 AR_PC4 Coater #4 12.190 0.457 Roll Coater- Weirton Stack 1 No stack parameters available. All emissions (stack + fugitives) modeled as a v

a. Individual stack emissions were based on total TRI Stack emissions and actual breakdown of EGBE emissions among individual stacks

The emission rate for each source is calculated from the TRI reported stack emissions of Certain Glycol Ethers as follows:

 EGBE Emission Rate (g/s) = Stack TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 8,760 (hrs/yr) x Stack_fraction

The calculated emission rate assumes EGBE emissions occur continuously 8,760 hours per year.Stack_fraction represents the percent of the total TRI stack emissions emitted through the individual stack

g/s: grams per secondK: degrees Kelvinm: meterm/s: meters per second

μg/m3: micrograms per cubic meter

tpy: ton per year

TRI: Toxic Release Inventory

Table D-10. Tier 3 Modeling Stack Parameters and Individual Source Resu
Site Name Source Type Volume Release Height (m) b Volume Intial Lateral Dimension (m) c Volume Intial Vertical Dimension (m) d 2009 TRI Emission Rate (g/s)e 2

Rexam Beverage Can Company- Chicago Volume 9.144 20.900 4.253 0.368 Edsal Manufacturing Co Inc- Chicago Volume No fugitive emissions reported to TRI. All reported emissions modeled as a stack releaseBall Metal Food Container Corp, Bldg_5D- Weirtong Volume 7.315 19.900 3.402 0.338 

Ball Metal Food Container Corp, Bldg_5G- Weirtong Volume 12.192 16.247 5.670 0.174 

Crown Cork & Seal Co (USA) - Weirton Volume 9.144 14.120 4.253 1.089 

Ardagh Metal Packaging USA Inc- Weirton Volume 9.750 11.881 4.540 0.000 

Roll Coater- Weirton Volume 9.144 26.700 4.250 0.164 

a. Fugitive releases of EGBE are reported to occur through the building's roof vents in the production

area of the facility building where stacks emitting EGBE are located. Fugitive emissions from the roof

vents are modeled as a single volume source.

b. The volume source release height is taken to be at the release height of fugitive emissions;

it is set to be equal to the roof height of the process building

c. Per EPA's AERMOD guidance, the volume source initial lateral dimension is taken to be the length of the side of

the volume divided by 4.3.

d. Per EPA's AERMOD guidance, the volume source initial vertical dimension is taken to be the

height of the volume source (roof height) divided by 2.15.

e. The emission rate for each source is calculated from the TRI reported fugitive emissions of Certain Glycol Ethers as follows:

EGBE Emission Rate (g/s) = Fugitive TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 8,760 (hrs/yr)

The calculated emission rate assumes EGBE emissions occur continuously 8,760 hours per year.

g. Ball Facility in Weirton has two distinct (physically separate) buildings associtaed with fugitive emissions which were modeled separately.

Their emissions were estimated based on the breakdown of the total fugitive emissions provided by the faciltiy in Tier 2 Survey 

g/s: grams per secondhrs/yr: hours per yearm: metertpy: ton per year

TRI: Toxic Release Inventory

Table D-11. Tier 3 Modeling Fugitive Volume Parameters and Results in Clusters
APPENDIX E 

Outcome of Short-Term Tiered Modeling 
Table E-1. Tier 1 Table of Maximum Normalized 1-Hour Concentrations (μg/m 3

)/(gps)

Normalized Maximum 1-Hour Average Concentrations At or Beyond: 

Receptor Distance

10 m 30 m 50 m 100 m 200 m 500 m

Area (10 m) 0.00 10.00 332,000 105,000 57,000 22,500 8,070 1,920

Area (10 m)a 3.00 10.00 35,825 11,294 10,415 9,771 6,168 1,802

Area (20 m) 0.00 20.00 179,000 63,600 37,200 16,600 6,620 1,750

Area (30 m) 0.00 30.00 122,000 45,400 27,500 13,000 5,590 1,590

Volume 3a 10.00 44,427 14,027 12,558 8,697 4,798 1,553

Point 0 - 1,880,000 275,000 113,000 33,600 10,100 2,110

Point 2 - 65,100 49,200 46,900 25,300 9,180 2,070

Point 5 - 33,400 25,900 18,000 9,440 5,130 1,800

Point 10 - 9,610 8,490 7,360 4,710 2,490 1,000

Point 20 - 2,450 1,570 1,570 1,320 846 367

Point 35 - 784 784 394 385 312 153

Point 50 - 384 384 384 163 147 88

m: meter

gps: grams per second

μg/m3

: micrograms per cubic meter

Source Type Release 

Height (m)

Side 

Length (m)

a. Not included in EPA's Tier 1 table. Included in the EGBE HAPs Petition Table 4-2. These values are based on ratios of

predicted SCREEN3 impacts for each receptor distance. The 10 m2 area source with the 0 m release height was used as 

the basis for the SCREEN3 predicted ratios. Ratios at the 10 m receptor distance were set equal to the ratios at the 30 m 

receptor distance.
Table E-2. Tier 1 Short-Term Modeling Parameters and Individual Source Results at Selected Facil

Facility Name Source ID Release Height (m) Volume Source Length of Side (m) Distance to Nearest Receptor (m) Physical Fence (Y/N) Tier 1 Table: Normalized Maximum 1-Hour Average Conc. (μg/m3)/(gps) Proportion EGBE 

Certain Glycol Eth

Ball Metal Beverage Container Corp- Findlay Stack 1 16.6116 - 89 Y 7360.00 1.00 

Ball Metal Beverage Container Corp- Findlay Stack 2 16.6116 - 91 Y 7360.00 1.00 Ball Metal Beverage Container Corp- Findlay Stack 3 19.812 - 89 Y 7360.00 1.00 Ball Metal Beverage Container Corp- Findlay Stack 4 19.812 - 100 Y 4710.00 1.00 Ball Metal Beverage Container Corp- Findlay Stack 5 14.1732 - 127 Y 4710.00 1.00 Ball Metal Beverage Container Corp- Findlay Stack 6 21.1836 - 108 Y 1320.00 1.00 Ball Metal Beverage Container Corp- Findlay Stack 7 21.6408 - 135 Y 1320.00 1.00 Ball Metal Beverage Container Corp- Findlay Stack 8 20.4216 - 105 Y 1320.00 1.00 Ball Metal Beverage Container Corp- Findlay Stack 9 20.7264 - 100 Y 1320.00 1.00 Ball Metal Beverage Container Corp- Findlay Fugitive 6.911162791 10 84 Y 12558.23 1.00 

Ball Container LLC - Columbus Stack 1 21.49 - 58 N 1570.00 1.00 Ball Container LLC - Columbus Stack 2 21.79 - 61 N 1570.00 1.00 Ball Container LLC - Columbus Stack 3 25.91 - 62 N 1570.00 1.00 Ball Container LLC - Columbus Stack 4 15.85 - 68 N 7360.00 1.00 Ball Container LLC - Columbus Stack 5 13.52 - 57 N 7360.00 1.00 Ball Container LLC - Columbus Stack 6 13.52 - 68 N 7360.00 1.00 Ball Container LLC - Columbus Stack 7 21.49 - 65 N 1570.00 1.00 Ball Container LLC - Columbus Stack 8 21.79 - 70 N 1570.00 1.00 Ball Container LLC - Columbus Stack 9 25.91 - 69 N 1570.00 1.00 Ball Container LLC - Columbus Stack 10 25.91 - 60 N 1570.00 1.00 Ball Container LLC - Columbus Stack 11 13.52 - 68 N 7360.00 1.00 Ball Container LLC - Columbus Stack 12 13.52 - 68 N 7360.00 1.00 Ball Container LLC - Columbus Stack 13 25.91 - 59 N 1570.00 1.00 Ball Container LLC - Columbus Stack 14 21.79 - 55 N 1570.00 1.00 Ball Container LLC - Columbus Stack 15 25.91 - 52 N 1570.00 1.00 Ball Container LLC - Columbus Stack 16 25.91 - 48 N 1570.00 1.00 Ball Container LLC - Columbus Stack 17 13.52 - 58 N 7360.00 1.00 Ball Container LLC - Columbus Stack 18 13.52 - 57 N 7360.00 1.00 Ball Container LLC - Columbus Stack 19 21.49 - 37 N 1570.00 1.00 Ball Container LLC - Columbus Stack 20 25.91 - 49 N 1570.00 1.00 Ball Container LLC - Columbus Stack 21 21.79 - 45 N 1570.00 1.00 Ball Container LLC - Columbus Stack 22 25.91 - 43 N 1570.00 1.00 Ball Container LLC - Columbus Stack 23 15.75 - 53 N 7360.00 1.00 Ball Container LLC - Columbus Fugitive 5.777023256 10 50 N 12558.23 1.00 Ball Metal Food Container Corp- Williamsburg Stack 1 18.4658 - 147 Y 4710.00 0.97 

Ball Metal Food Container Corp- Williamsburg Stack 2 18.8722 - 127 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 3 15.5448 - 102 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 4 15.1638 - 102 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 5 13.1318 - 98 Y 7360.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 6 13.1318 - 96 Y 7360.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 7 18.5166 - 140 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 8 18.415 - 145 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 9 18.3388 - 122 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 10 18.5928 - 118 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 11 18.3134 - 103 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 12 18.288 - 111 Y 4710.00 0.97 

Page 1 of 4
Table E-2. Tier 1 Short-Term Modeling Parameters and Individual Source Results at Selected Facil

Facility Name Source ID Release Height (m) Volume Source Length of Side (m) Distance to Nearest Receptor (m) Physical Fence (Y/N) Tier 1 Table: Normalized Maximum 1-Hour Average Conc. (μg/m3)/(gps) Proportion EGBE 

Certain Glycol Eth

Ball Metal Food Container Corp- Williamsburg Stack 13 18.3388 - 121 Y 4710.00 0.97 

Ball Metal Food Container Corp- Williamsburg Stack 14 18.4658 - 142 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 15 15.5448 - 106 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 16 15.5448 - 110 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 17 17.8562 - 136 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 18 17.8562 - 116 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Stack 19 17.8562 - 114 Y 4710.00 0.97 Ball Metal Food Container Corp- Williamsburg Fugitive 6.804837209 10 135 Y 8696.57 0.97 

Crown Beverage Packaging - Bradley Stack 1 18.29 - 18.71 N 9610.00 0.88 Crown Beverage Packaging - Bradley Stack 2 15.24 - 18.71 N 9610.00 0.88 Crown Beverage Packaging - Bradley Stack 3 15.24 - 24 N 9610.00 0.88 Crown Beverage Packaging - Bradley Stack 4 18.29 - 24 N 9610.00 0.88 Crown Beverage Packaging - Bradley Stack 5 15.24 - 37.92 N 8490.00 0.88 Crown Beverage Packaging - Bradley Stack 6 15.24 - 32.99 N 8490.00 0.88 Crown Beverage Packaging - Bradley Stack 7 18.29 - 37.92 N 8490.00 0.88 Crown Beverage Packaging - Bradley Fugitive 3.402418605 10 43.67 N 14026.73 0.88 Crown Beverage Packaging - Lawrence Stack 1 8.7 - 38 N 25900.00 0.91 Crown Beverage Packaging - Lawrence Stack 2 8.7 - 41 N 25900.00 0.91 Crown Beverage Packaging - Lawrence Stack 3 8.7 - 39 N 25900.00 0.91 Crown Beverage Packaging - Lawrence Stack 4 8.7 - 40 N 25900.00 0.91 Crown Beverage Packaging - Lawrence Stack 5 8.7 - 34 N 25900.00 0.91 Crown Beverage Packaging - Lawrence Stack 6 8.7 - 42 N 25900.00 0.91 Crown Beverage Packaging - Lawrence Stack 7 8.7 - 60 N 18000.00 0.91 Crown Beverage Packaging - Lawrence Stack 8 8.7 - 64 N 18000.00 0.91 Crown Beverage Packaging - Lawrence Stack 9 8.7 - 46 N 25900.00 0.91 Crown Beverage Packaging - Lawrence Stack 10 8.7 - 62 N 18000.00 0.91 Crown Beverage Packaging - Lawrence Stack 11 8.7 - 63 N 18000.00 0.91 Crown Beverage Packaging - Lawrence Stack 12 8.7 - 50 N 18000.00 0.91 Crown Beverage Packaging - Lawrence Fugitive 2.835348837 10 75 N 12558.23 0.91 Crown Beverage Packaging - Olympia Stack 1 14.33 - 44.63 N 8490.00 0.94 Crown Beverage Packaging - Olympia Stack 2 16.76 - 55.57 N 7360.00 0.94 Crown Beverage Packaging - Olympia Stack 3 12.8 - 63.77 N 7360.00 0.94 Crown Beverage Packaging - Olympia Stack 4 12.8 - 72.24 N 7360.00 0.94 Crown Beverage Packaging - Olympia Fugitive 4.961860465 10 69.36 N 12558.23 0.94 Crown Food Packaging - Owatonna Stack 1 17.98 - 70.7 N 7360.00 0.99 

Crown Food Packaging - Owatonna Stack 2 17.98 - 81.66 N 7360.00 0.99 Crown Food Packaging - Owatonna Stack 3 17.98 - 98.33 N 7360.00 0.99 Crown Food Packaging - Owatonna Stack 4 17.98 - 104.03 N 4710.00 0.99 Crown Food Packaging - Owatonna Stack 5 17.98 - 78.13 N 7360.00 0.99 Crown Food Packaging - Owatonna Fugitive 4.961860465 10 102.8 N 8696.57 0.99 

Crown Cork & Seal Co (USA) - Weirton Stack 1 11 - 12 N 9610.00 1.00 Crown Cork & Seal Co (USA) - Weirton Stack 2 17 - 15 N 9610.00 1.00 Crown Cork & Seal Co (USA) - Weirton Fugitive 4.253023256 10 31.36 N 14026.73 1.00 Rexam Beverage Can Company- Bishopville Stack 1 15.24 - 22 Y 9610.00 1.00 

Rexam Beverage Can Company- Bishopville Stack 2 15.5448 - 43 Y 8490.00 1.00 Rexam Beverage Can Company- Bishopville Stack 3 11.5824 - 13 Y 9610.00 1.00 

Page 2 of 4
Table E-2. Tier 1 Short-Term Modeling Parameters and Individual Source Results at Selected Facil

Facility Name Source ID Release Height (m) Volume Source Length of Side (m) Distance to Nearest Receptor (m) Physical Fence (Y/N) Tier 1 Table: Normalized Maximum 1-Hour Average Conc. (μg/m3)/(gps) Proportion EGBE 

Certain Glycol Eth

Rexam Beverage Can Company- Bishopville Stack 4 14.0208 - 16 Y 9610.00 1.00 

Rexam Beverage Can Company- Bishopville Stack 5 14.0208 - 19 Y 9610.00 1.00 Rexam Beverage Can Company- Bishopville Stack 6 15.24 - 11 Y 9610.00 1.00 Rexam Beverage Can Company- Bishopville Stack 7 15.24 - 18 Y 9610.00 1.00 Rexam Beverage Can Company- Bishopville Stack 8 15.24 - 23 Y 9610.00 1.00 Rexam Beverage Can Company- Bishopville Fugitive 4.961860465 10 63 Y 12558.23 1.00 

Rexam Beverage Can Company- Kent Stack 1 14.6304 - 36 Y 8490.00 1.00 Rexam Beverage Can Company- Kent Stack 2 14.6304 - 40 Y 8490.00 1.00 Rexam Beverage Can Company- Kent Stack 3 16.6116 - 42 Y 8490.00 1.00 Rexam Beverage Can Company- Kent Stack 4 14.6304 - 29 Y 9610.00 1.00 Rexam Beverage Can Company- Kent Stack 5 13.50264 - 56 Y 7360.00 1.00 Rexam Beverage Can Company- Kent Stack 6 14.1732 - 61 Y 7360.00 1.00 Rexam Beverage Can Company- Kent Stack 7 13.19784 - 62 Y 7360.00 1.00 Rexam Beverage Can Company- Kent Stack 8 13.716 - 65 Y 7360.00 1.00 Rexam Beverage Can Company- Kent Stack 9 15.24 - 56 Y 7360.00 1.00 Rexam Beverage Can Company- Kent Stack 10 15.33144 - 62 Y 7360.00 1.00 Rexam Beverage Can Company- Kent Stack 11 15.33144 - 65 Y 7360.00 1.00 Rexam Beverage Can Company- Kent Stack 12 15.33144 - 60 Y 7360.00 1.00 Rexam Beverage Can Company- Kent Fugitive 3.685953488 10 64 Y 12558.23 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 1 12.19 - 37.8 N 8490.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 2 12.19 - 32.22 N 8490.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 3 13.41 - 41.76 N 8490.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 4 13.41 - 41.76 N 8490.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 5 13.41 - 45.11 N 8490.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 7 12.19 - 41.45 N 8490.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 8 12.19 - 32.61 N 8490.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 9 12.19 - 49.07 N 8490.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 10 12.8 - 53.95 N 7360.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 11 12.19 - 56.39 N 7360.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Stack 12 12.19 - 44.2 N 8490.00 1.00 Silgan Containers Manufacturing Corp- LaPorte Fugitive 3 10 59 N 12558.23 1.00 Rexam Beverage Can Company- Chicago Stack 1 13.1064 - 30 Y 8490.00 0.94 Rexam Beverage Can Company- Chicago Stack 2 12.6492 - 38 Y 8490.00 0.94 Rexam Beverage Can Company- Chicago Stack 3 13.16736 - 44 Y 8490.00 0.94 Rexam Beverage Can Company- Chicago Stack 4 12.192 - 19 Y 9610.00 0.94 Rexam Beverage Can Company- Chicago Stack 5 12.8016 - 23 Y 9610.00 0.94 Rexam Beverage Can Company- Chicago Stack 6 13.716 - 31 Y 8490.00 0.94 Rexam Beverage Can Company- Chicago Stack 7 14.0208 - 26 Y 9610.00 0.94 Rexam Beverage Can Company- Chicago Stack 8 14.0208 - 34 Y 8490.00 0.94 Rexam Beverage Can Company- Chicago Stack 9 15.24 - 41 Y 8490.00 0.94 Rexam Beverage Can Company- Chicago Fugitive 4.253023256 10 46 Y 14026.73 0.94 Crown Beverage Packaging - Lacrosse Stack 1 13.716 - 12 N 9610.00 1.00 Crown Beverage Packaging - Lacrosse Fugitive 3 10 70 N 12558.23 1.00 RR Donnelley-Harrisonburg Point 11.17 - 45 Unknown 8490.00 1.00 RR Donnelley-Harrisonburg Fugitive 3.05 10 210 Unknown 4798.11 1.00 

Rexam Beverage Can Company- Winston-Sale Stacks 1-10 14 - 75 Unknown 7360.00 0.95 

Page 3 of 4
Table E-2. Tier 1 Short-Term Modeling Parameters and Individual Source Results at Selected Facil

Facility Name Source ID Release Height (m) Volume Source Length of Side (m) Distance to Nearest Receptor (m) Physical Fence (Y/N) Tier 1 Table: Normalized Maximum 1-Hour Average Conc. (μg/m3)/(gps) Proportion EGBE 

Certain Glycol Eth

Rexam Beverage Can Company- Winston-Sale Fugitive 3 10 91.7 Unknown 12558.23 0.95 

Page 4 of 4
Table E-3. Tier 1 Short-Term Modeling Summary for Selected Facilities

2009 TRI 2010 TRI 2011 TRI

Site Name Source Type

Maximum 1-

Hour Average 

Tier I EGBE 

Conc. (μg/m3)

Short-Term 

HQ 

(combined)

Maximum 1-

Hour Average 

Tier I EGBE 

Conc. (μg/m3)

Short-Term 

HQ 

(combined)

Maximum 1-

Hour Average 

Tier I EGBE 

Conc. (μg/m3)

Sh

(co

Crown Beverage Packaging - Lawrence Point 1674648.6 1455360.1 1628244.9

Volume 25839.6 22455.8 25123.6

RR Donnelley-Harrisonburg Point 4575.2 3835.5 3274.4

Volume 21848.5 23455.4 27327.9

Ball Metal Food Container Corp- Williamsburg Point 1614548.3 1729873.2 1672210.7

Volume 28567.5 30154.6 29625.6

Crown Cork & Seal Co (USA) - Weirton Point 153263.2 145599.8 139775.7

Volume 66907.0 63561.5 61019.1

Rexam Beverage Can Company- Winston-Salem Point 126797.7 138811.6 97310.1

Volume 42558.5 46926.7 38656.2

Rexam Beverage Can Company- Bishopville Point 781664.4 784081.0 723321.2

Volume 22865.5 22936.6 21153.3

Ball Container LLC - Columbus Point 516703.7 671714.9 723385.2

Volume 31488.0 18105.6 18892.8

Ball Metal Beverage Container Corp- Findlay Point 602446.2 602446.2 625617.2

Volume 38766.6 39557.8 40348.9

Silgan Containers Manufacturing Corp- LaPorte Point 625779.2 637261.3 611214.0

Volume 19778.9 20332.7 19289.9

Crown Beverage Packaging - Lacrosse Point 2071.7 2010.6 2177.7

Volume 36099.6 35030.0 37941.4

Crown Food Packaging - Owatonna Point 373793.1 391475.5 407543.5

Volume 31796.9 33353.0 34594.6

Rexam Beverage Can Company- Chicago Point 487099.1 506509.5 250922.0

Volume 22587.1 23527.5 10798.1

Crown Beverage Packaging - Bradley Point 364345.2 340549.6 344624.2

Volume 26654.8 24914.5 25212.3

Rexam Beverage Can Company- Kent Point 884003.8 834954.6 833594.9

Volume 20850.7 19693.1 19661.5

Crown Beverage Packaging - Olympia Point 185857.0 210964.4 173700.7

Volume 25408.8 28888.5 23785.3

EGBE: ethylene glycol monobutyl etherHQ: hazard quotientRfC: reference concentrationTRI: Toxics Release Inventoryμg/m3: micrograms per cubic meter

Bold font indicates an HQ greather than 1.

92

92

15

0.3

8777

0.4

18

0.3

17

22

Hazard quotient (HQ) equals the sum of the maximum annual average concentration for fugitive/volume source emissions and point source emissions, at or befence line, is compared to a NOAEL for EGBE of 97,000 μg/m3.

18

22

7867

0.4

454

454
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Te

Ball Container LLC - Columbus Stack 1 L1-IBO-Hot 21.49 0.686 9.64 

Ball Container LLC - Columbus Stack 2 L1-ISS 21.79 0.405 11.70 

Ball Container LLC - Columbus Stack 3 L1-PO1-Hot 25.91 0.381 19.16 

Ball Container LLC - Columbus Stack 4 L1-PO2-Hot 15.85 0.405 20.70 

Ball Container LLC - Columbus Stack 5 L1-PR-11 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 6 L1-PR-12 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 7 L2-IBO-Hot 21.49 0.686 2.71 

Ball Container LLC - Columbus Stack 8 L2-ISS 21.79 0.405 11.70 

Ball Container LLC - Columbus Stack 9 L2-PO1-Hot 25.91 0.393 19.19 

Ball Container LLC - Columbus Stack 10 L2-PO2-Hot 25.91 0.381 15.63 

Ball Container LLC - Columbus Stack 11 L2-PR-21 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 12 L2-PR-22 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 13 L3-IBO-Hot 25.91 0.686 7.59 

Ball Container LLC - Columbus Stack 14 L3-ISS 21.79 0.405 11.70 

Ball Container LLC - Columbus Stack 15 L3-PO1-Hot 25.91 0.381 17.20 

Ball Container LLC - Columbus Stack 16 L3-PO2-Hot 25.91 0.393 14.71 

Ball Container LLC - Columbus Stack 17 L3-PR-31 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 18 L3-PR-32 13.52 0.399 10.18 

Ball Container LLC - Columbus Stack 19 L4-BCO-Hot 21.49 0.393 17.23 

Ball Container LLC - Columbus Stack 20 L4-IBO-Hot 25.91 0.381 32.32 Ball Container LLC - Columbus Stack 21 L4-ISS 21.79 0.405 7.31 

Ball Container LLC - Columbus Stack 22 L4-PO-Hot 25.91 0.686 5.00 

Ball Container LLC - Columbus Stack 23 L4-PR-41 15.75 1.119 1.30 

Ball Metal Beverage Container Corp- Findlay Stack 1 B_PO11 PO11 16.61 0.457 7.00 

Ball Metal Beverage Container Corp- Findlay Stack 2 B_PO12 PO12 16.61 0.305 29.07 

Ball Metal Beverage Container Corp- Findlay Stack 3 B_PO21 PO21 19.81 0.457 9.79 

Ball Metal Beverage Container Corp- Findlay Stack 4 B_PO22 PO22 19.81 0.457 11.32 

Ball Metal Beverage Container Corp- Findlay Stack 5 B_IBO11 IBO11 14.17 0.610 11.62 

Ball Metal Beverage Container Corp- Findlay Stack 6 B_IBO21B IBO21-B 21.18 0.610 3.98 

Ball Metal Beverage Container Corp- Findlay Stack 7 B_IBO31 IBO31 21.64 0.864 5.12 

Ball Metal Beverage Container Corp- Findlay Stack 8 B_WCO31 WashCoat Ov 20.42 0.813 2.58 

Ball Metal Beverage Container Corp- Findlay Stack 9 B_BH Baghouse 20.73 0.330 37.48 

Ball Metal Food Container Corp- Williamsburg Stack 1 PO2 S019 18.47 0.406 13.53 

Ball Metal Food Container Corp- Williamsburg Stack 2 PO3 S006 18.87 0.406 12.25 

Ball Metal Food Container Corp- Williamsburg Stack 3 PO4Z1 S035 15.54 0.483 6.77 

Ball Metal Food Container Corp- Williamsburg Stack 4 PO4Z2 S036 15.16 0.483 9.49 

Table E-4. Tier 2 Modeling Stack Parameters and Individual Source Results at Individual 

Page 1 of 4
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Te

Table E-4. Tier 2 Modeling Stack Parameters and Individual Source Results at Individual 

Ball Metal Food Container Corp- Williamsburg Stack 5 PO5Z1 S037 13.13 0.483 9.63 

Ball Metal Food Container Corp- Williamsburg Stack 6 PO5Z2 S038 13.13 0.483 8.84 

Ball Metal Food Container Corp- Williamsburg Stack 7 IBO2Z1 S021 18.52 0.406 7.60 

Ball Metal Food Container Corp- Williamsburg Stack 8 IBO2Z2 S020 18.42 0.508 6.60 

Ball Metal Food Container Corp- Williamsburg Stack 9 IBO3Z1 S011 18.34 0.406 6.06 

Ball Metal Food Container Corp- Williamsburg Stack 10 IBO3Z2 S010 18.59 0.508 7.29 

Ball Metal Food Container Corp- Williamsburg Stack 11 IBO4/5Z1 S027 18.31 0.406 2.85 

Ball Metal Food Container Corp- Williamsburg Stack 12 IBO4/5Z2 S028 18.29 0.508 5.13 

Ball Metal Food Container Corp- Williamsburg Stack 13 IBO4/5Z3 S039 18.34 0.406 13.05 

Ball Metal Food Container Corp- Williamsburg Stack 14 BCPOL2 S016 18.47 0.406 13.01 

Ball Metal Food Container Corp- Williamsburg Stack 15 BCPOL4Z1 S033 15.54 0.483 9.00 

Ball Metal Food Container Corp- Williamsburg Stack 16 BCPOL4Z2 S034 15.54 0.483 10.22 

Ball Metal Food Container Corp- Williamsburg Stack 17 ICEXH02 S024 17.86 0.305 11.26 

Ball Metal Food Container Corp- Williamsburg Stack 18 ICEXH03 S023 17.86 0.305 11.89 

Ball Metal Food Container Corp- Williamsburg Stack 19 ICEXH045 S022 17.86 0.406 8.61 

Crown Beverage Packaging - Bradley Stack 1 IBO IBO (Can Line 18.29 0.305 10.20 

Crown Beverage Packaging - Bradley Stack 2 Ross Ross (Can Lin 15.24 0.305 16.72 Crown Beverage Packaging - Bradley Stack 3 IBO IBO (Can Line 15.24 0.305 9.51 Crown Beverage Packaging - Bradley Stack 4 Ross Ross (Can Lin 18.29 0.305 16.72 Crown Beverage Packaging - Bradley Stack 5 IBO IBO (Can Line 15.24 0.305 10.20 

Crown Beverage Packaging - Bradley Stack 6 Ross Ross (Can Lin 15.24 0.305 16.72 

Crown Beverage Packaging - Bradley Stack 7 Ross Ross (Can Lin 18.29 0.305 16.72 Crown Beverage Packaging - Olympia Stack 1 IBO #1A 14.33 0.710 3.97 

Crown Beverage Packaging - Olympia Stack 2 IBO #2C 16.76 1.067 7.98 

Crown Beverage Packaging - Olympia Stack 3 LSM #1A 12.80 0.280 8.32 

Crown Beverage Packaging - Olympia Stack 4 LSM #2A 12.80 0.280 6.91 

Crown Beverage Packaging - Lawrence Stack 1 LSM2 8.53 0.457 1.42 

Crown Beverage Packaging - Lawrence Stack 2 L1PO 8.53 0.457 2.10 Crown Beverage Packaging - Lawrence Stack 3 IBO1 8.53 0.457 3.31 

Crown Beverage Packaging - Lawrence Stack 4 LSM1 8.53 0.457 1.18 

Crown Beverage Packaging - Lawrence Stack 5 L1V1 8.53 0.457 3.42 Crown Beverage Packaging - Lawrence Stack 6 IBO3 8.53 0.457 10.25 

Crown Beverage Packaging - Lawrence Stack 7 L3S 8.53 0.457 1.18 

Crown Beverage Packaging - Lawrence Stack 8 L3VI 8.53 0.457 3.42 

Crown Beverage Packaging - Lawrence Stack 9 IBO4 8.53 0.457 8.52 

Crown Beverage Packaging - Lawrence Stack 10 L4S 8.53 0.457 1.42 

Page 2 of 4
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Te

Table E-4. Tier 2 Modeling Stack Parameters and Individual Source Results at Individual 

Crown Beverage Packaging - Lawrence Stack 11 L3PO 8.53 0.457 3.42 Crown Beverage Packaging - Lawrence Stack 12 IBO2 8.53 0.457 3.68 

Crown Cork & Seal Co (USA) - Weirton Stack 1 TO-1 11.00 1.219 16.17 

Crown Cork & Seal Co (USA) - Weirton Stack 2 TO-2 17.00 0.597 13.49 

Crown Food Packaging - Owatonna Stack 1 EU-001 17.98 0.311 31.08 

Crown Food Packaging - Owatonna Stack 2 EU-003 17.98 0.311 18.65 

Crown Food Packaging - Owatonna Stack 3 EU-005 17.98 0.311 18.65 

Crown Food Packaging - Owatonna Stack 4 EU-007 17.98 0.311 31.08 

Crown Food Packaging - Owatonna Stack 5 EU-008 17.98 0.311 31.08 

Rexam Beverage Can Company- Bishopville Stack 1 SV4 Printer Oven S 15.24 0.457 6.10 

Rexam Beverage Can Company- Bishopville Stack 2 SV5 Printer Oven S 15.54 0.396 6.10 Rexam Beverage Can Company- Bishopville Stack 3 SV 6 Inside Spray M 11.58 0.610 3.96 

Rexam Beverage Can Company- Bishopville Stack 4 SV 7 Inside Spray M 14.02 0.610 3.96 

Rexam Beverage Can Company- Bishopville Stack 5 SV 8 Inside Spray M 14.02 0.610 3.96 Rexam Beverage Can Company- Bishopville Stack 6 SV9 Inside Bake O 15.24 0.762 4.88 Rexam Beverage Can Company- Bishopville Stack 7 SV10 Inside Bake O 15.24 0.762 4.88 Rexam Beverage Can Company- Bishopville Stack 8 SV11 Inside Bake O 15.24 0.762 4.88 Rexam Beverage Can Company- Chicago Stack 1 REX_SV21 Printer Oven S 13.11 0.396 9.58 Rexam Beverage Can Company- Chicago Stack 2 REX_SV22 Printer Oven S 12.65 0.396 9.57 Rexam Beverage Can Company- Chicago Stack 3 REX_SV23 Base Coater P 13.17 0.396 9.57 Rexam Beverage Can Company- Chicago Stack 4 RED_SV31 Inside Spray M 12.19 1.097 2.50 Rexam Beverage Can Company- Chicago Stack 5 REX_SV32 Inside Spray M 12.80 1.189 2.13 

Rexam Beverage Can Company- Chicago Stack 6 REX_SV33 Inside Spray M 13.72 0.914 3.59 

Rexam Beverage Can Company- Chicago Stack 7 REX_SV41 Inside Bake O 14.02 0.762 8.07 Rexam Beverage Can Company- Chicago Stack 8 REX_SV42 Inside Bake O 14.02 0.823 6.92 Rexam Beverage Can Company- Chicago Stack 9 REX_RTO Regenerative 15.24 1.158 7.61 

Rexam Beverage Can Company- Kent Stack 1 SV7A Printer Pin Ov 14.63 0.558 4.83 

Rexam Beverage Can Company- Kent Stack 2 SV7B Printer Pin Ov 14.63 0.558 4.83 Rexam Beverage Can Company- Kent Stack 3 SV7C Printer Pin Ov 16.61 0.914 1.80 Rexam Beverage Can Company- Kent Stack 4 SV7D Printer Pin Ov 14.63 0.610 4.04 Rexam Beverage Can Company- Kent Stack 5 SV8A Inside Spray M 13.50 0.838 2.14 Rexam Beverage Can Company- Kent Stack 6 SV8B Inside Spray M 14.17 0.838 2.14 Rexam Beverage Can Company- Kent Stack 7 SV8C Inside Spray M 13.20 0.850 2.08 

Rexam Beverage Can Company- Kent Stack 8 SV8D Inside Spray M 13.72 0.838 2.14 

Rexam Beverage Can Company- Kent Stack 9 SV9A Inside Bake O 15.24 0.762 3.62 Rexam Beverage Can Company- Kent Stack 10 SV9B Inside Bake O 15.33 0.762 3.62 

Page 3 of 4
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Te

Table E-4. Tier 2 Modeling Stack Parameters and Individual Source Results at Individual 

Rexam Beverage Can Company- Kent Stack 11 SV9C Inside Bake O 15.33 0.762 3.62 

Rexam Beverage Can Company- Kent Stack 12 SV9D Inside Bake O 15.33 0.762 3.62 Rexam Beverage Can Company- Salem Stack 1 Stack1 14.00 6.096 0.46 

Rexam Beverage Can Company- Salem Stack 2 Stack2 14.00 6.096 0.46 

Rexam Beverage Can Company- Salem Stack 3 Stack3 14.00 6.096 0.46 

Rexam Beverage Can Company- Salem Stack 4 Stack4 14.00 6.096 0.46 

Rexam Beverage Can Company- Salem Stack 5 Stack5 14.00 6.096 0.46 

Silgan Containers Manufacturing Corp- LaPorte Stack 1 C11 L1Roll1 15.80 0.719 17.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 2 C12 L1Roll2 15.80 0.719 7.37 

Silgan Containers Manufacturing Corp- LaPorte Stack 3 C13 L1IS1 17.11 0.905 5.13 

Silgan Containers Manufacturing Corp- LaPorte Stack 4 C14 L1IS2 17.11 0.905 5.13 

Silgan Containers Manufacturing Corp- LaPorte Stack 5 C15 L1IS3 17.11 0.905 12.32 

Silgan Containers Manufacturing Corp- LaPorte Stack 6 C16 L1IS4 17.11 0.914 10.78 

Silgan Containers Manufacturing Corp- LaPorte Stack 7 C21 L2Roll1 15.80 0.719 17.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 8 C22 L2Roll2 15.80 0.719 7.37 

Silgan Containers Manufacturing Corp- LaPorte Stack 9 C23 L2IS1 16.46 0.799 9.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 10 C24 L2IS2 16.78 0.799 18.85 

Silgan Containers Manufacturing Corp- LaPorte Stack 11 S1 IS_1_Over_Fu 16.00 0.695 12.44 

Silgan Containers Manufacturing Corp- LaPorte Stack 12 S2 IS_2_Over_Fu 16.13 0.362 45.87 

a. All point EGBE emissions were conservatively assumed to exhaust through each stack for AERSCREEN modeling.

The emission rate for each source is calculated from the TRI reported stack emissions of Certain Glycol Ethers as follows:

 EGBE Emission Rate (g/s) = Stack TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 2,000 (hrs/yr)

The calculated emission rate assumes the total annual EGBE emissions are relased over a period of 2,000 hours a year, which would correspto a facility steadily emitting EGBE 40 hours a week, 50 weeks per year.

b. Worst case 1-hr average unit emission rate concentration in (μg/m3) (1g/s) assumes stack emission rate of 1 g/s.

It is used to calculate Tier 2 1-hr concentration for a stack by multiplying the unit emission rate concentration by Tier 2 stack emission rate (in 

The maximum point source unit emission rate impact (considering all point sources for a facility) is shown in bolded text.

g/s: grams per secondK: degrees Kelvinm: meterm/s: meters per second

μg/m3: micrograms per cubic meter

tpy: ton per year

TRI: Toxic Release Inventory

Page 4 of 4
Site Name Source Type

Volume 

Release 

Height (m) b

Volume Intial 

Lateral 

Dimension (m) 

c

Volume Intial 

Vertical 

Dimension 

(m) d

2009 TRI 

Emission Rate 

(g/s)e

2010 TRI 

Emission Rate 

(g/s)e

2011 TRI 

Emission R

(g/s)e

Ball Container LLC - Columbus Volume 12.420 22.790 5.777 2.507 1.44173 1.50441 Ball Metal Beverage Container Corp- Findlay Volume 12.420 11.230 5.780 3.087 3.14995 3.21295 Ball Metal Food Container Corp- Williamsburg Volume 14.630 13.730 6.805 3.285 3.46741 3.40658 Crown Beverage Packaging - Bradley Volume 7.315 19.850 3.402 1.900 1.77621 1.79745 Crown Beverage Packaging - Olympia Volume 10.670 24.820 4.962 2.023 2.30036 1.89400 Crown Beverage Packaging - Lawrence Volume 6.096 27.300 2.835 2.058 1.78813 2.00057 Crown Cork & Seal Co (USA) - Weirton Volume 9.144 14.120 4.253 4.770 4.53145 4.35020 Crown Food Packaging - Owatonna Volume 10.670 30.710 4.962 3.656 3.83519 3.97795 Rexam Beverage Can Company- Bishopville Volume 10.670 28.840 4.962 1.821 1.82642 1.68442 Rexam Beverage Can Company- Chicago Volume 9.144 20.930 4.253 1.610 1.67733 0.76982 Rexam Beverage Can Company- Kent Volume 7.925 24.550 3.686 1.660 1.56814 1.56563 Rexam Beverage Can Company- Salem Volume 7.000 27.240 3.250 3.389 3.73673 3.07815 Silgan Containers Manufacturing Corp- LaPorte Volume 12.192 20.698 5.670 1.575 1.61907 1.53604 a. Fugitive releases of EGBE are reported to occur through the building's roof vents in the production

area of the facility building where stacks emitting EGBE are located. Fugitive emissions from the roof

vents are modeled as a single volume source.

b. The volume source release height is taken to be at the release height of fugitive emissions;

it is set to be equal to the roof height of the process building

c. Per EPA's AERMOD guidance, the volume source initial lateral dimension is taken to be the length of the side of

the volume divided by 4.3.

d. Per EPA's AERMOD guidance, the volume source initial vertical dimension is taken to be the

height of the volume source (roof height) divided by 2.15.

e. The emission rate for each source is calculated from the TRI reported fugitive emissions of Certain Glycol Ethers as follows:

EGBE Emission Rate (g/s) = Fugitive TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 2,000 (hrs/yr)

The calculated emission rate assumes the total annual EGBE emissions are relased over a period of 2,000 hours a year, which would correspondto a facility steadily emitting EGBE 40 hours a week, 50 weeks per year.

f. Worst case 1-hr average unit emission rate concentration in (μg/m3) (1g/s) assumes fugitive emission rate of 1 g/s.

It is used to calculate Tier 2 1-hr concentration for a fugitive volume by multiplying the unit emission rate concentration by

Tier 2 fugitive emission rate (in g/s) for a given TRI year

g/s: grams per secondhrs/yr: hours per yearm: meter

μg/m3: micrograms per cubic meter

tpy: ton per year

TRI: Toxic Release Inventory

Table E-5. Tier 2 Modeling Fugitive Volume Parameters and Results at Individual Facilities
Table E-6. Tier 2 Modeling Stack Parameters and Individual Source Results in 

Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV21 Printer Oven Stack # 1 – SV 21 13.11 0.396 9.58 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV22 Printer Oven Stack # 2 – SV 22 12.65 0.396 9.57 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV23 Base Coater Pin Oven Stack # 3 – SV 23 13.17 0.396 9.57 

Rexam Beverage Can Company- Chicago Stack 4 RED_SV31 Inside Spray Machines Bank 1 – SV 31 12.19 1.097 2.50 

Rexam Beverage Can Company- Chicago Stack 5 REX_SV32 Inside Spray Machines Bank 2 – SV 32 12.80 1.189 2.13 

Rexam Beverage Can Company- Chicago Stack 6 REX_SV33 Inside Spray Machines Bank 2 – SV 33 13.72 0.914 3.59 

Rexam Beverage Can Company- Chicago Stack 7 REX_SV41 Inside Bake Oven Stack # 1 – SV 41 14.02 0.762 8.07 

Rexam Beverage Can Company- Chicago Stack 8 REX_SV42 Inside Bake Oven Stack # 2 – SV 42 14.02 0.823 6.92 

Rexam Beverage Can Company- Chicago Stack 9 REX_RTO Regenerative Thermal Oxidizer Stack 15.24 1.158 7.61 

Edsal Manufacturing Co Inc- Chicago Stack1 N/A 3960*** 9.75 0.396 2.74 Ball Metal Beverage Container Corp- Findlay Stack 1 B_PO11 PO11 16.61 0.457 7.00 Ball Metal Beverage Container Corp- Findlay Stack 2 B_PO12 PO12 16.61 0.305 29.07 

Ball Metal Beverage Container Corp- Findlay Stack 3 B_PO21 PO21 19.81 0.457 9.79 

Ball Metal Beverage Container Corp- Findlay Stack 4 B_PO22 PO22 19.81 0.457 11.32 

Ball Metal Beverage Container Corp- Findlay Stack 5 B_IBO11 IBO11 14.17 0.610 11.62 

Ball Metal Beverage Container Corp- Findlay Stack 6 B_IBO21B IBO21-B 21.18 0.610 3.98 

Ball Metal Beverage Container Corp- Findlay Stack 7 B_IBO31 IBO31 21.64 0.864 5.12 

Ball Metal Beverage Container Corp- Findlay Stack 8 B_WCO31 WashCoat Oven31 20.42 0.813 2.58 

Ball Metal Beverage Container Corp- Findlay Stack 9 B_BH Baghouse 20.73 0.330 37.48 

Whirlpool Corp Findlay Div- Findlay Stack 1 Stk_2 8194  12.19 0.305 0.39 Silgan Containers Manufacturing Corp- LaPorte Stack 1 C11 L1Roll1 15.80 0.719 17.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 2 C12 L1Roll2 15.80 0.719 7.37 

Silgan Containers Manufacturing Corp- LaPorte Stack 3 C13 L1IS1 17.11 0.905 5.13 

Silgan Containers Manufacturing Corp- LaPorte Stack 4 C14 L1IS2 17.11 0.905 5.13 

Silgan Containers Manufacturing Corp- LaPorte Stack 5 C15 L1IS3 17.11 0.905 12.32 

Silgan Containers Manufacturing Corp- LaPorte Stack 6 C16 L1IS4 17.11 0.914 10.78 

Silgan Containers Manufacturing Corp- LaPorte Stack 7 C21 L2Roll1 15.80 0.719 17.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 8 C22 L2Roll2 15.80 0.719 7.37 

Silgan Containers Manufacturing Corp- LaPorte Stack 9 C23 L2IS1 16.46 0.799 9.42 

Silgan Containers Manufacturing Corp- LaPorte Stack 10 C24 L2IS2 16.78 0.799 18.85 

Silgan Containers Manufacturing Corp- LaPorte Stack 11 S1 IS_1_Over_Fug 16.00 0.695 12.44 

Silgan Containers Manufacturing Corp- LaPorte Stack 12 S2 IS_2_Over_Fug 16.13 0.362 45.87 

Roll Coater- La Porte Stack 1 Stk_2 not used 9.14 0.914 3.23 Ball Metal Food Container Corp- Weirton Stack 1 0001 0001 (Bldg 5G) 12.80 2.070 8.41 Ball Metal Food Container Corp- Weirton Stack 2 TO-1 TO-1 (Bldg 5D) 11.58 1.220 7.80 Ball Metal Food Container Corp- Weirton Stack 3 TO-2 TO-2 (Bldg 5D) 10.67 0.670 6.86 Ball Metal Food Container Corp- Weirton Stack 4 0003 0003 (Bldg 5D) 10.05 0.640 1.66 Crown Cork & Seal Co (USA) - Weirton Stack 1 TO-1 11.00 1.219 16.17 

Crown Cork & Seal Co (USA) - Weirton Stack 2 TO-2 17.00 0.597 13.49 

Ardagh Metal Packaging USA Inc- Weirton Stack 1 Coater #1 12.50 0.610 31.01 

Ardagh Metal Packaging USA Inc- Weirton Stack 2 Coater #2 14.33 0.610 9.15 Ardagh Metal Packaging USA Inc- Weirton Stack 3 Coater #3 12.50 0.457 22.27 

Ardagh Metal Packaging USA Inc- Weirton Stack 4 Coater #4 12.19 0.457 15.45 

Roll Coater- Weirton Stack 1 No stack parameters available. All emissions (stack + fugitives) modeled as a volume

Page 1 of 2
Table E-6. Tier 2 Modeling Stack Parameters and Individual Source Results in 

Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) Stack Exit Gas Velocity (m/s) 

Ball Metal Beverage Container Corp- Reidsville Stack 1 PO1 15.95 0.508 4.32 Ball Metal Beverage Container Corp- Reidsville Stack 2 PO2 16.31 0.508 4.28 Ball Metal Beverage Container Corp- Reidsville Stack 3 PO3 16.08 0.508 6.14 Ball Metal Beverage Container Corp- Reidsville Stack 4 IBO1 16.00 0.457 12.15 Ball Metal Beverage Container Corp- Reidsville Stack 5 IBO2 16.00 0.457 7.11 Ball Metal Beverage Container Corp- Reidsville Stack 6 IBO3 16.00 0.457 13.17 Ball Metal Beverage Container Corp- Reidsville Stack 7 Printer 1 15.95 0.508 0.50 Ball Metal Beverage Container Corp- Reidsville Stack 8 Printer 2 15.90 0.508 0.50 

Ball Metal Beverage Container Corp- Reidsville Stack 9 Printer 3 16.08 0.508 0.50 Ball Metal Beverage Container Corp- Reidsville Stack 10 Spray line 1 14.94 0.381 6.39 

Ball Metal Beverage Container Corp- Reidsville Stack 11 Spray line 2 14.99 0.381 7.28 Ball Metal Beverage Container Corp- Reidsville Stack 12 Spray line 3 14.99 0.381 8.74 Dystar LP- Reidsville Stack 1 Stk_2 11.64 0.432 5.44 

a. All point EGBE emissions were conservatively assumed to exhaust through each stack for AERSCREEN modeling. 

The emission rate for each source is calculated from the TRI reported stack emissions of Certain Glycol Ethers as follows:

 EGBE Emission Rate (g/s) = Stack TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 2,000 (hrs/yr)

The calculated emission rate assumes the total annual EGBE emissions are relased over a period of 2,000 hours a year, which would correspondto a facility steadily emitting EGBE 40 hours a week, 50 weeks per year. 

b. Worst case 1-hr average unit emission rate concentration in (μg/m3) (1g/s) assumes stack emission rate of 1 g/s.

It is used to calculate Tier 2 1-hr concentration for a stack by multiplying the unit emission rate concentration by Tier 2 stack emission rate (in g/s) for a given TRI year

The maximum point source unit emission rate impact (considering all point sources for a facility) is shown in bolded text. 

g/s: grams per secondK: degrees Kelvinm: meterm/s: meters per second

μg/m3: micrograms per cubic meter

tpy: ton per year

TRI: Toxic Release Inventory

Page 2 of 2
Table E-7. Tier 2 Modeling Fugitive Volume Parameters and Results in Clusters

Site Name Source Type

Volume 

Release 

Height (m) b

Volume Intial Lateral 

Dimension (m) c

Volume Intial 

Vertical 

Dimension (m) 

d

2009 TRI 

Emission 

Rate (g/s)e

2010 TRI 

Emission Rate 

(g/s)e

2011 

Emissio

(g/s

Rexam Beverage Can Company- Chicago Volume 9.144 20.930 4.253 1.610 1.67733 0.769Edsal Manufacturing Co Inc- Chicago Volume No fugitive emissions reported to TRI. All reported emissions modeled as a stack releaseBall Metal Beverage Container Corp- Findlay Volume 12.420 11.230 5.780 3.087 3.14995 3.212Whirlpool Corp Findlay Div- Findlay Volume 8.800 47.280 4.093 0.288 0.28192 0.27Silgan Containers Manufacturing Corp- LaPorte Volume 12.192 20.698 5.670 1.575 1.61907 1.536Roll Coater- La Porte Volume 9.144 39.535 4.251 0.000 0.00000 0.002Ball Metal Food Container Corp, Bldg_5D- Weirtong Volume 7.315 19.900 3.402 1.482 0.84285 0.578

Ball Metal Food Container Corp, Bldg_5G- Weirtong Volume 12.192 16.247 5.670 0.764 0.43420 0.297Crown Cork & Seal Co (USA) - Weirton Volume 9.144 14.120 4.253 4.770 4.53145 4.350

Ardagh Metal Packaging USA Inc- Weirton Volume 9.750 11.881 4.540 0.000 0.00048 0.005

Roll Coater- Weirton Volume 9.144 16.000 4.250 0.716 0.91090 0.33

Ball Metal Beverage Container Corp- Reidsville Volume 13.106 30.930 6.096 1.465 1.77033 2.075

Dystar LP- Reidsville Volume 10.000 9.698 4.651 0.004 0.00441 0.004

a. Fugitive releases of EGBE are reported to occur through the building's roof vents in the production

area of the facility building where stacks emitting EGBE are located. Fugitive emissions from the roof

vents are modeled as a single volume source.

b. The volume source release height is taken to be at the release height of fugitive emissions;

it is set to be equal to the roof height of the process building

c. Per EPA's AERMOD guidance, the volume source initial lateral dimension is taken to be the length of the side of

the volume divided by 4.3.

d. Per EPA's AERMOD guidance, the volume source initial vertical dimension is taken to be the

height of the volume source (roof height) divided by 2.15.

e. The emission rate for each source is calculated from the TRI reported fugitive emissions of Certain Glycol Ethers as follows:

EGBE Emission Rate (g/s) = Fugitive TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 2,000 (hrs/yr)

The calculated emission rate assumes the total annual EGBE emissions are relased over a period of 2,000 hours a year, which would correspondto a facility steadily emitting EGBE 40 hours a week, 50 weeks per year.

f. Worst case 1-hr average unit emission rate concentration in (μg/m3) (1g/s) assumes fugitive emission rate of 1 g/s.

It is used to calculate Tier 2 1-hr concentration for a fugitive volume by multiplying the unit emission rate concentration by

Tier 2 fugitive emission rate (in g/s) for a given TRI year

g. Ball Facility in Weirton has two distinct (physically separate) buildings associtaed with fugitive emissions which were modeled separately.

Their emissions were estimated based on the breakdown of the total fugitive emissions provided by the faciltiy in Tier 2 SurveyThe maximum impact from fugitive sources for that facility is obtained by summing maximum impacts of the two volume sources.

g/s: grams per secondhrs/yr: hours per yearm: metertpy: ton per yearTRI: Toxic Release Inventory
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) 

Crown Beverage Packaging - Lawrence Stack 1 LSM2 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 2 L1PO 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 3 IBO1 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 4 LSM1 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 5 L1V1 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 6 IBO3 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 7 L3S 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 8 L3VI 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 9 IBO4 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 10 L4S 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 11 L3PO 8.530 0.457 

Crown Beverage Packaging - Lawrence Stack 12 IBO2 8.530 0.457 

Crown Beverage Packaging - Lacrosse Stack 1 S30 13.720 0.966 

Crown Cork & Seal Co (USA) - Weirton Stack 1 TO-1 11.000 1.219 Crown Cork & Seal Co (USA) - Weirton Stack 2 TO-2 17.000 0.597 Rexam Beverage Can Company- Bishopville Stack 1 SV4 Printer Oven Stack # 1 – SV4 15.200 0.460 

Rexam Beverage Can Company- Bishopville Stack 2 SV5 Printer Oven Stack # 2 – SV5 15.500 0.400 Rexam Beverage Can Company- Bishopville Stack 3 SV 6 Inside Spray Machines Bank 1 – SV 6 11.600 0.610 Rexam Beverage Can Company- Bishopville Stack 4 SV 7 Inside Spray Machines Bank 2 – SV 7 14.000 0.610 Rexam Beverage Can Company- Bishopville Stack 5 SV 8 Inside Spray Machines Bank 3 – SV 8 14.000 0.610 Rexam Beverage Can Company- Bishopville Stack 6 SV9 Inside Bake Oven Stack # 1 – SV9 15.200 0.760 

Rexam Beverage Can Company- Bishopville Stack 7 SV10 Inside Bake Oven Stack # 2 – SV10 15.200 0.760 

Rexam Beverage Can Company- Bishopville Stack 8 SV11 Inside Bake Oven Stack # 3 – SV11 15.200 0.760 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV21 Printer Oven Stack # 1 – SV 21 13.106 0.396 Rexam Beverage Can Company- Chicago Stack 1 REX_SV22 Printer Oven Stack # 2 – SV 22 12.649 0.396 Rexam Beverage Can Company- Chicago Stack 1 REX_SV23 Base Coater Pin Oven Stack # 3 – SV 23 13.167 0.396 Rexam Beverage Can Company- Chicago Stack 4 RED_SV31 Inside Spray Machines Bank 1 – SV 31 12.192 1.097 Rexam Beverage Can Company- Chicago Stack 5 REX_SV32 Inside Spray Machines Bank 2 – SV 32 12.802 1.189 Rexam Beverage Can Company- Chicago Stack 6 REX_SV33 Inside Spray Machines Bank 2 – SV 33 13.716 0.914 Rexam Beverage Can Company- Chicago Stack 7 REX_SV41 Inside Bake Oven Stack # 1 – SV 41 14.021 0.762 Rexam Beverage Can Company- Chicago Stack 8 REX_SV42 Inside Bake Oven Stack # 2 – SV 42 14.021 0.823 Rexam Beverage Can Company- Chicago Stack 9 REX_RTO Regenerative Thermal Oxidizer Stack 15.240 1.158 Rexam Beverage Can Company- Kent Stack 1 SV7A Printer Pin Oven Stack 1 – SV 7A 14.630 0.558 

Rexam Beverage Can Company- Kent Stack 2 SV7B Printer Pin Oven Stack 2 – SV 7B 14.630 0.558 

Rexam Beverage Can Company- Kent Stack 3 SV7C Printer Pin Oven Stack 3 – SV 7C 16.612 0.914 

Rexam Beverage Can Company- Kent Stack 4 SV7D Printer Pin Oven Stack 4 – SV 7D 14.630 0.610 

Rexam Beverage Can Company- Kent Stack 5 SV8A Inside Spray Machines Bank 1 – SV 8A 13.503 0.838 

Rexam Beverage Can Company- Kent Stack 6 SV8B Inside Spray Machines Bank 2 – SV 8B 14.173 0.838 

Rexam Beverage Can Company- Kent Stack 7 SV8C Inside Spray Machines Bank 3 – SV 8C 13.198 0.850 

Rexam Beverage Can Company- Kent Stack 8 SV8D Inside Spray Machines Bank 4 – SV 8D 13.716 0.838 

Rexam Beverage Can Company- Kent Stack 9 SV9A Inside Bake Oven Stack # 1 – SV 9A 15.240 0.762 

Table E-8. Tier 3 Modeling Stack Parameters at Individual Facilitie

Page 1 of 2
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) 

Table E-8. Tier 3 Modeling Stack Parameters at Individual Faciliti

Rexam Beverage Can Company- Kent Stack 10 SV9B Inside Bake Oven Stack # 2 – SV 9B 15.331 0.762 

Rexam Beverage Can Company- Kent Stack 11 SV9C Inside Bake Oven Stack # 3 – SV 9C 15.331 0.762 

Rexam Beverage Can Company- Kent Stack 12 SV9D Inside Bake Oven Stack # 4 – SV 9D 15.331 0.762 Rexam Beverage Can Company - Winston Salem Stack 1 WS1 14.000 0.457 Rexam Beverage Can Company - Winston Salem Stack 2 WS2 14.000 0.457 Rexam Beverage Can Company - Winston Salem Stack 3 WS3 14.000 0.457 Rexam Beverage Can Company - Winston Salem Stack 4 WS4 14.000 0.457 Rexam Beverage Can Company - Winston Salem Stack 5 WS5 14.000 0.457 

a. Individual stack emissions were based on total TRI Stack emissions and actual breakdown of EGBE emissions among individual stacks

The emission rate for each source is calculated from the TRI reported stack emissions of Certain Glycol Ethers as follows:

 EGBE Emission Rate (g/s) = Stack TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 2,000 (hrs/yr) x Stack_fraction

The calculated emission rate assumes the total annual EGBE emissions are relased over a period of 2,000 hours a year, which would correspondto a facility steadily emitting EGBE 40 hours a week, 50 weeks per year.Stack_fraction represents the percent of the total TRI stack emissions emitted through the individual stack

g/s: grams per secondK: degrees Kelvinm: meterm/s: meters per second

μg/m3: micrograms per cubic meter

tpy: ton per year

TRI: Toxic Release Inventory

Page 2 of 2
Table E-9. Tier 3 Modeling Fugitive Volume Parameters and Results at Individual Facilities

Site Name Source Type

Volume Release 

Height (m) b

Volume Intial 

Lateral 

Dimension (m) c

Volume Intial 

Vertical 

Dimension (m) d

2009 TRI 

Emission Rate 

(g/s)e

Crown Beverage Packaging - Lawrence Volume 6.096 27.310 2.840 2.058 

Crown Cork & Seal Co (USA) - Weirton Volume 9.144 14.120 4.253 4.770 

Rexam Beverage Can Company- Bishopville Volume 10.668 28.840 4.960 1.821 

Rexam Beverage Can Company- Chicago Volume 9.144 20.900 4.253 1.610 Rexam Beverage Can Company- Kent Volume 7.920 24.558 3.686 1.660 

Rexam Beverage Can Company - Winston Salem Volume 7.000 27.242 3.250 3.389 

a. Fugitive releases of EGBE are reported to occur through the building's roof vents in the production

area of the facility building where stacks emitting EGBE are located. Fugitive emissions from the roof

vents are modeled as a single volume source.

b. The volume source release height is taken to be at the release height of fugitive emissions;

it is set to be equal to the roof height of the process building

c. Per EPA's AERMOD guidance, the volume source initial lateral dimension is taken to be the length of the side of

the volume divided by 4.3.

d. Per EPA's AERMOD guidance, the volume source initial vertical dimension is taken to be the

height of the volume source (roof height) divided by 2.15.

e. The emission rate for each source is calculated from the TRI reported fugitive emissions of Certain Glycol Ethers as follows:

EGBE Emission Rate (g/s) = Fugitive TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 2,000 (hrs/yr)

The calculated emission rate assumes the total annual EGBE emissions are relased over a period of 2,000 hours a year, which would correspondto a facility steadily emitting EGBE 40 hours a week, 50 weeks per year.

g/s: grams per secondhrs/yr: hours per yearm: metertpy: ton per year

TRI: Toxic Release Inventory
Facility Name Stack Stack ID Alternative Stack ID Release Height (m) Stack Inside Diameter (m) 

Rexam Beverage Can Company- Chicago Stack 1 REX_SV21 Printer Oven Stack # 1 – SV 21 13.100 0.396 Rexam Beverage Can Company- Chicago Stack 1 REX_SV22 Printer Oven Stack # 2 – SV 22 12.649 0.396 Rexam Beverage Can Company- Chicago Stack 1 REX_SV23 Base Coater Pin Oven Stack # 3 – SV 23 13.167 0.396 Rexam Beverage Can Company- Chicago Stack 4 RED_SV31 Inside Spray Machines Bank 1 – SV 31 12.192 1.097 Rexam Beverage Can Company- Chicago Stack 5 REX_SV32 Inside Spray Machines Bank 2 – SV 32 12.802 1.189 Rexam Beverage Can Company- Chicago Stack 6 REX_SV33 Inside Spray Machines Bank 2 – SV 33 13.716 0.914 Rexam Beverage Can Company- Chicago Stack 7 REX_SV41 Inside Bake Oven Stack # 1 – SV 41 14.021 0.762 Rexam Beverage Can Company- Chicago Stack 8 REX_SV42 Inside Bake Oven Stack # 2 – SV 42 14.021 0.823 Rexam Beverage Can Company- Chicago Stack 9 REX_RTO Regenerative Thermal Oxidizer Stack 15.240 1.158 Edsal Manufacturing Co Inc- Chicago Stack1 N/A 3960** * 9.144 0.396 Ball Metal Food Container Corp- Weirton Stack 1 BA5G_P1 0001 (Bldg 5G) 12.802 2.070 Ball Metal Food Container Corp- Weirton Stack 1 BA5D_PT1 TO-1 (Bldg 5D) 11.580 1.220 Ball Metal Food Container Corp- Weirton Stack 1 BA5D_PT2 TO-2 (Bldg 5D) 10.670 0.670 Ball Metal Food Container Corp- Weirton Stack 4 BA5D_P3 0003 (Bldg 5D) 10.050 0.640 Crown Cork & Seal Co (USA) - Weirton Stack 1 CR_PTO1 TO-1 11.000 1.219 Crown Cork & Seal Co (USA) - Weirton Stack 2 CR_PTO2 TO-2 17.000 0.597 Ardagh Metal Packaging USA Inc- Weirton Stack 1 AR_PC1 Coater #1 12.497 0.610 Ardagh Metal Packaging USA Inc- Weirton Stack 2 AR_PC2 Coater #2 14.330 0.610 Ardagh Metal Packaging USA Inc- Weirton Stack 3 AR_PC3 Coater #3 12.497 0.457 Ardagh Metal Packaging USA Inc- Weirton Stack 4 AR_PC4 Coater #4 12.190 0.457 Roll Coater- Weirton Stack 1 No stack parameters available. All emissions (stack + fugitives) modeled as a v

a. Individual stack emissions were based on total TRI Stack emissions and actual breakdown of EGBE emissions among individual stacks

The emission rate for each source is calculated from the TRI reported stack emissions of Certain Glycol Ethers as follows:

 EGBE Emission Rate (g/s) = Stack TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 2,000 (hrs/yr) x Stack_fraction

The calculated emission rate assumes the total annual EGBE emissions are relased over a period of 2,000 hours a year, which would correspondto a facility steadily emitting EGBE 40 hours a week, 50 weeks per year.Stack_fraction represents the percent of the total TRI stack emissions emitted through the individual stack

g/s: grams per secondK: degrees Kelvinm: meterm/s: meters per second

μg/m3: micrograms per cubic meter

TRI: Toxic Release Inventory

Table E-10. Tier 3 Modeling Stack Parameters and Individual Source Resu
Site Name Source Type Volume Release Height (m) b Volume Intial Lateral Dimension (m) c Volume Intial Vertical Dimension (m) d 2009 TRI Emission Rate (g/s)e 2

Rexam Beverage Can Company- Chicago Volume 9.144 20.900 4.253 1.610 Edsal Manufacturing Co Inc- Chicago Volume No fugitive emissions reported to TRI. All reported emissions modeled as a stack releaseBall Metal Food Container Corp, Bldg_5D- Weirtong Volume 7.315 19.900 3.402 1.482 

Ball Metal Food Container Corp, Bldg_5G- Weirtong Volume 12.192 16.247 5.670 0.764 

Crown Cork & Seal Co (USA) - Weirton Volume 9.144 14.120 4.253 4.770 

Ardagh Metal Packaging USA Inc- Weirton Volume 9.750 11.881 4.540 0.000 

Roll Coater- Weirton Volume 9.144 26.700 4.250 0.716 

a. Fugitive releases of EGBE are reported to occur through the building's roof vents in the production

area of the facility building where stacks emitting EGBE are located. Fugitive emissions from the roof

vents are modeled as a single volume source.

b. The volume source release height is taken to be at the release height of fugitive emissions;

it is set to be equal to the roof height of the process building

c. Per EPA's AERMOD guidance, the volume source initial lateral dimension is taken to be the length of the side of

the volume divided by 4.3.

d. Per EPA's AERMOD guidance, the volume source initial vertical dimension is taken to be the

height of the volume source (roof height) divided by 2.15.

e. The emission rate for each source is calculated from the TRI reported fugitive emissions of Certain Glycol Ethers as follows:

EGBE Emission Rate (g/s) = Fugitive TRI Emissions of Certain Glycol Ethers (tpy) x % EGBE x 254 (conversion factor) ÷ 2,000 (hrs/yr)

The calculated emission rate assumes the total annual EGBE emissions are relased over a period of 2,000 hours a year, which would correspondto a facility steadily emitting EGBE 40 hours a week, 50 weeks per year. 

g. Ball Facility in Weirton has two distinct (physically separate) buildings associtaed with fugitive emissions which were modeled separately.

Their emissions were estimated based on the breakdown of the total fugitive emissions provided by the faciltiy in Tier 2 Survey 

hrs/yr: hours per yearm: metertpy: ton per yearTRI: Toxic Release Inventory

Table E-11. Tier 3 Modeling Fugitive Volume Parameters and Results in Clusters
APPENDIX F 

Tier 2 and Tier 3 Modeling Output Files (CDROM)