Attachment I 

Final Attainment Demonstration and Technical 

Support Document for the Muncie, Delaware County, 

Indiana Lead Nonattainment Area 
This page intentionally left blank.
Lead Attainment Demonstration 

and 

Technical Support Document 

For the Muncie Nonattainment Area

Muncie, Delaware County

Indiana

Prepared By: 

Indiana Department of Environmental Management 

Office of Air Quality 

 March 2013

 
This page intentionally left blank.
i 

TABLE OF CONTENTS 

1.0 OVERVIEW ................................................................................................................. 1

1.1 Introduction .............................................................................................................. 1

1.2 National Ambient Air Quality Standards ................................................................. 1

1.3 Geographical Description ......................................................................................... 3

1.4 Control Strategy ....................................................................................................... 5

2.0 CLEAN AIR ACT REQUIREMENTS ...................................................................... 6

2.1 Reasonably Available Control Technology (RACT)/Reasonably Available Control 

Measures (RACM) (Section 172(c)(1)) ................................................................... 6

2.2 General Requirements for Demonstrating Reasonable Further Progress (Section 

172(c)(2)) .................................................................................................................. 7

2.3 Emission Inventory (Section 172(c)(3)) ................................................................... 7

2.4 Identification and Quantification of Emissions (Section 172(c)(4)) ........................ 7

2.5 Permit Program for New and Modified Major Stationary Sources (Section 

172(c)(5)) .................................................................................................................. 8

2.6 Other Control Measures, Means, or Techniques (Section 172(c)(6)) ...................... 8

2.7 Compliance with Section 110(a)(2) (Section 172(c)(7)) .......................................... 8

2.8 Equivalent Techniques (Section 172(c)(8)) ............................................................. 8

2.9 Contingency Measures (Section 172(c)(9)) ............................................................. 9

3.0 MODELING ................................................................................................................. 9

3.1 Air Quality Analysis ................................................................................................. 9

3.2 Analysis Results ..................................................................................................... 12

4.0 AIR QUALITY TRENDS .......................................................................................... 12

4.1 Wind Rose Analysis ............................................................................................... 18

4.2 Snow Cover and Precipitation Analysis ................................................................. 19

5.0 EMISSION TREND ANALYSIS .............................................................................. 22

6.0 TRANSPORTATION CONFORMITY ................................................................... 23

7.0 CONTROL STRATEGY ........................................................................................... 24

7.1 Prohibition on Gasoline Containing Lead or Lead Additives ................................ 24

7.2 New Source Review Provisions ............................................................................. 24

7.3 Controls to Remain in Effect .................................................................................. 24

7.4 Secondary Lead Smelting: National Emission Standards for Hazardous Air 

Pollutants ................................................................................................................ 24

7.5 Revisions to Indiana’s Lead Rule ........................................................................... 25
ii 

8.0 CONTINGENCY MEASURES ................................................................................ 25

9.0 PUBLIC PARTICIPATION ..................................................................................... 26

10.0CONCLUSION ........................................................................................................... 26 

TABLES

Table 1.1: National Ambient Air Quality Standards for Lead ............................................ 2

Table 1.2: Delaware County Air Quality Monitoring Data Used for Designation .............. 3

Table 3.1: 2009 Point Sources – Exide Technologies ....................................................... 11

Table 3.2: 2011 Point Sources – Exide Technologies ....................................................... 11

Table 4.1: Lead Quarterly Arithmetic Average Monitoring Data Summary, Muncie, 

Delaware County, Indiana ................................................................................ 13

Table 4.2: Lead Three-Month Rolling Average Values Data Summary, Muncie, 

 Delaware County, Indiana ................................................................................ 14

Table 4.3: Lead Historical Design Values for the Muncie, Delaware County, Indiana 

Monitors ........................................................................................................... 17

Table 4.4: Snow Cover Observed on Monitored Days (Delaware County – Johnson 

 ASOS Station) .................................................................................................. 19

Table 4.5: Precipitation Recorded on Monitored Days (Delaware County – Johnson 

 ASOS station) ................................................................................................... 20

Table 4.6: Wind Conditions/Precipitation on the Highest Concentration Days at the 

 Muncie – Exide East Site Monitor ................................................................... 21

Table 4.7: Wind Conditions/Precipitation on Highest Concentration Days at the 

 Muncie – Exide West Site Monitor .................................................................. 21

Table 5.1. Lead Emissions Inventory – Exide Technologies, Delaware County, 

 Indiana .............................................................................................................. 22

FIGURES

Figure 1.1: Muncie, Delaware County, Indiana Lead Nonattainment Area ......................... 4

Figure 1.2: Exide Technologies Site Plan ............................................................................. 5

Figure 3.1: Modeling Receptor Grid for Exide Technologies ............................................ 10

Figure 4.1: Annual Wind Roses for 2008-2011 .................................................................. 18

 
iii 

GRAPHS

Graph 4.1: Lead Highest Annual Quarterly Values, Muncie, Delaware County, 

 Indiana .............................................................................................................. 14

Graph 4.2: Lead Three-Month Rolling Average Values, Muncie, Delaware County, 

 Indiana .............................................................................................................. 16

Graph 4.3: Lead Historical Design Values for the Muncie, Delaware County, Indiana 

Monitors ........................................................................................................... 17

Graph 5.1: Lead Fugitive and Point Source Emission Trends – Exide Technologies, 

Muncie, Delaware County, Indiana .................................................................. 23

APPENDICES

A Air Quality System (AQS) and Indiana Department of Environmental Management 

 (IDEM) Lead Monitor Data Values for Delaware County, Indiana (2000 – October 2012) 

B Lead Area and Point Source Emissions (2000-2010), Delaware County, Indiana 

C Section 110(a)(1) and (2) Infrastructure SIP 

D Indiana’s Final Promulgated Lead Rule 

E Exide Technologies: Fugitive Dust Control Plan 

F Exide Technologies: Agreed Order Case No. 2008-18144-A 

G Modeling Summary 

H Public Participation Process Documentation 

ACRONYMS/ABBREVIATION LIST

ASOS Automated Surface Observing System 

CAA Clean Air Act 

CFR Code of Federal Regulations 

FR Federal Register 

IAC Indiana Administrative Code 

IDEM Indiana Department of Environmental Management 

mg/dscm milligrams per dry standard cubic meter 

NAAQS National Ambient Air Quality Standards 

NESHAP National Emissions Standards for Hazardous Air Pollutants 

NSR New Source Review 

PSD Prevention of Significant Deterioration 

RACM Reasonably Available Control Measures 

RACT Reasonably Available Control Technology 

RFP Reasonable Further Progress 

SIP State Implementation Plan 

tpy tons per year 

TRI Toxic Release Inventory 

U.S. EPA United States Environmental Protection Agency 

μg/m3

 micrograms per cubic meter
This page intentionally left blank. 
1 

LEAD ATTAINMENT DEMONSTRATION AND 

TECHNICAL SUPPORT DOCUMENT FOR THE MUNCIE, 

DELAWARE COUNTY, INDIANA NONATTAINMENT AREA

1.0 OVERVIEW 

1.1 Introduction

Lead is one of the six criteria air pollutants that scientists have identified as being particularly 

harmful to humans and the environment. National Ambient Air Quality Standards (NAAQS) have 

been developed for these six pollutants and are used as measurements of air quality. The Clean Air 

Act (CAA) requires the United States Environmental Protection Agency (U.S. EPA) to set primary 

standards at a level judged to be “requisite to protect the public health with an adequate margin of 

safety,” and establish secondary standards that are requisite to protect public welfare from “any 

known or anticipated effects associated with the pollutant in the ambient air,” including effects on 

crops, vegetation, wildlife, buildings and national monuments, and visibility. 

Lead is a naturally occurring toxic metal that is found in the air in the form of small particles. It is 

also emitted from some industrial processes and is present in some manufactured products. The 

major sources of lead emissions have historically been motor vehicles (such as cars and trucks) and 

industrial sources. Motor vehicle emissions have been dramatically reduced with the phase-out of 

leaded gasoline. Lead is currently only used as a fuel additive for aviation gasoline in some general 

aviation aircraft, but not in commercial jet aircraft. Larger industrial sources of lead emissions 

currently include metals processing, particularly primary and secondary lead smelters. U.S. EPA's 

lead air quality monitoring strategy generally focuses on areas surrounding these industrial sources. 

1.2 National Ambient Air Quality Standards

The CAA requires areas designated nonattainment for a NAAQS to develop State Implementation 

Plans (SIPs) to expeditiously attain and maintain the standard. The CAA requires U.S. EPA to 

review these standards once every five years to determine whether revisions to the NAAQS are 

appropriate. U.S. EPA issued revised primary and secondary NAAQS for lead in the November 12, 

2008, Federal Register (FR) published at 73 FR 66964, with an effective date of January 12, 2009. 

The revised NAAQS was strengthened by a factor of 10, from 1.5 micrograms per cubic meter 

(μg/m3

) using a quarterly average, to 0.15 μg/m3 using a rolling three-month average. The stronger 

standard provides increased protection against adverse health effects associated with exposure to 

lead in at-risk groups, including children. To provide increased protection against lead-related 

environmental and other welfare effects, U.S. EPA revised the secondary lead NAAQS to be 

identical to the revised primary standard. U.S. EPA determined that the pre-existing ambient lead 

monitoring network was inadequate for determining whether many areas were meeting the revised 

lead standards. 

U.S. EPA also established new criteria for siting ambient lead monitors and new data collection 

requirements on December 27, 2010, to better assess compliance with the 2008 lead NAAQS (75 

FR 81126). 
2 

Table 1.1 

National Ambient Air Quality Standards for Lead 

Primary Standards Secondary Standards 

 Level Averaging Time Level Averaging Time 

1978 Lead 

Standards 

1.5 μg/m3 Highest calendar 

quarter arithmetic 

average in a three-year 

period 

Same as primary 

2008 Lead 

Standards 

0.15 μg/m3 Highest rolling threemonth average in a 

three-year period 

Same as primary 

On November 22, 2010, U.S. EPA promulgated the initial lead nonattainment areas for the revised 

lead standard with an effective date of December 31, 2010 (75 FR 71033). Nonattainment areas are 

subject to Section 172 of the CAA, including the development of a plan within eighteen months of 

the effective date of designations (i.e., June 30, 2012) detailing how the lead standard will be 

attained by December 31, 2015. 

Based on the most recent three years of monitoring data, 2009 through 2011, the Muncie, Delaware 

County, Indiana lead nonattainment area (“Muncie Nonattainment Area”), has not measured air 

quality that meets the 2008 lead NAAQS. A comprehensive detail of the monitoring data is 

included in Appendix A. 

The Muncie Nonattainment Area, as defined in Section 1.3, has not previously been subject to 

nonattainment area rulemakings for lead. However, Delaware County had been subject to 

nonattainment area rulemakings under the 1997 8-hour ozone standard. The entire county was 

designated nonattainment under the 1997 8-hour ozone standard on June 15, 2004, and was 

subsequently redesignated to attainment and classified as maintenance on July 19, 2007. 

Previously, an upwind and a downwind lead monitor were located near the Exide Technologies, 

Muncie, Delaware County, Indiana secondary lead smelter (“Exide Technologies”). Exide 

Technologies is the only significant source of lead emissions in the Muncie Nonattainment Area. 

The upwind monitor, located west of Exide Technologies, (Muncie – Exide West Site, Site ID 18-

035-0008) was shut down at the end of December 2009. The downwind monitor, located east of 

Exide Technologies, (Muncie – Exide East Site, Site ID 18-035-0009) was moved further outside of 

the source’s property to Mount Pleasant Boulevard in March 2010. Designations were made based 

upon monitored air quality data measured from 2007 through 2009. Table 1.2 shows the monitored 

highest three-month rolling average lead values for 2006 through 2008 and 2007 through 2009. 

 
3 

Table 1.2 

Delaware County Air Quality Monitoring Data Used for Designation 

Site ID Site Name 

Highest Rolling 

Three-Month Lead 

Value, 2006-2008 

(μg/m3) 

Highest Rolling 

Three-Month Lead 

Value, 2007-2009 

(μg/m3) 

18-035-0008 Muncie – Exide West Site 0.52 0.34 

18-035-0009 Muncie – Exide East Site 2.17 2.17 

The CAA requires areas designated nonattainment for the lead NAAQS to develop SIPs to 

expeditiously attain and maintain the standard. Section 172 of the CAA stipulates the requirements 

nonattainment areas must meet, including the development of a plan to reduce lead emissions. The 

plan must include a demonstration that the area will meet the ambient air quality standard within 

five years of designation, or December 31, 2015. 

This document demonstrates that, with the combination of current clean air measures and the 

implementation of additional stationary point source and fugitive dust mitigation control measures 

at Exide Technologies, air quality in the Muncie Nonattainment Area will meet the 2008 lead 

NAAQS by the attainment date. This document contains the 2008 lead NAAQS attainment 

demonstration for the Muncie Nonattainment Area. The structure and content of this document 

addresses each of the elements required by the CAA and U.S. EPA guidance. 

1.3 Geographical Description

U.S. EPA designated a small portion of the City of Muncie in Delaware County as nonattainment 

for lead. As shown in Figure 1.1, the area includes the Exide Technologies facility and is bounded 

by the following city streets: West 26th Street/Hines Road to the north, Cowan Road to the east, 

West Fuson Road to the south, and South Hoyt Avenue extended to West 26th Street to the west. 
4 

Figure 1.1 

Muncie, Delaware County, Indiana Lead Nonattainment Area 

The nonattainment area was established in the immediate vicinity of Exide Technologies because 

lead is a heavy metal and airborne lead emissions do not travel far from the source of the emissions. 

Therefore, population exposure to airborne lead is minimal beyond the small area surrounding the 

source. The national emission standards for hazardous air pollutants (NESHAP) for secondary lead 

smelters at 40 Code of Federal Regulations (CFR) 635.44 requires facilities to operate process and 

other fugitive lead dust emission sources within total enclosures that are maintained under negative 

pressure and vented to a control device. Work practice standards at 40 CFR 63.545 require 

facilities to ensure fugitive dust is not generated outside of total enclosures and that fugitive dust 

generated inside total enclosures is not carried outside of the enclosures. Lead emissions from 

Exide Technologies are from a single, identifiable area, such as a stack or a vent and are minimized 

by pollution control devices as shown in Figure 1.2. 

 
5 

Figure 1.2 

Exide Technologies Site Plan 

1.4 Control Strategy

Control measures in place or those that will be implemented over the next few years will further 

reduce stationary lead point source and fugitive dust emissions from Exide Technologies. Exide 

Technologies is currently subject to the requirements of the Indiana Secondary Lead Smelter Rule 

found at 326 Indiana Administrative Code (IAC) 20-13. Indiana has recently amended its rules for 

secondary lead smelters, recodified at 326 IAC 20-13.1, to make necessary changes to address the 

federal revisions to the NESHAP for secondary lead smelters at 40 CFR 63, Subpart X (January 5, 

2012, 77 FR 580), and to include an expedited compliance schedule for certain NESHAP 

requirements for Exide Technologies. Additional control measures to be implemented or phased-in 

at Exide Technologies in order to meet these requirements shall be in place no later than October 1, 

2013. In addition to lead emission standards for individual emission units that are more stringent 

than those in the NESHAP, Indiana’s rule for secondary lead smelters includes opacity 

 
6 

limits and supplemental requirements for total enclosure monitoring. Indiana’s final promulgated 

lead rule (LSA Document#11-774(F)) was adopted by the Air Pollution Control Board on 

November 7, 2012. A copy of Indiana’s final rule which was filed with the Publisher of the Indiana 

Register on February 27, 2013 (DIN: 20130227-IR-326110774FRA) is included as Appendix D. 

2.0 CLEAN AIR ACT REQUIREMENTS 

Section 172(c) of the CAA specifies the various planning requirements that apply to lead 

nonattainment areas. The CAA specifies the following requirements: 

1 Reasonably Available Control Measures (RACM)/Reasonably Available Control 

 Technology (RACT). 

2. Reasonable Further Progress (RFP). 

3. Emissions inventory. 

4. Identification and quantification of emissions. 

5. Permit program for new and modified major stationary sources. 

6. Other control measures, means, or techniques. 

7. Compliance with Section 110(a)(2). 

8. Equivalent techniques. 

9. Contingency measures. 

These components were due to U.S. EPA by June 30, 2012. The following section provides an 

overview of Indiana’s progress in meeting the CAA requirements mentioned above. 

2.1 Reasonably Available Control Technology (RACT)/Reasonably Available Control Measures 

(RACM) (Section 172(c)(1))

Section 172(c)(1) of the CAA requires that the plan provisions provide for implementation of 

RACM as expeditiously as practicable (including such reductions in emissions from existing 

sources in the area as may be obtained through the adoption, at a minimum, of RACT) and provide 

for attainment of the national primary ambient air quality standards. In March 2012, U.S. EPA 

issued guidance entitled: “Implementation of the 2008 Lead National Ambient Air Quality 

Standards: Guide to Developing Reasonably Available Control Measures (RACM) for Controlling 

Lead Emissions” (RACM Guidance). The RACM Guidance provides basic steps that a state can 

use in determining what constitutes RACM. 

These requirements will be met with the implementation of additional control measures at Exide 

Technologies that are necessary to meet the expedited compliance schedule for certain NESHAP 

requirements contained in Indiana’s lead rule at 326 IAC 20-13.1. The annual lead values have 

been trending downward and, additional control measures to be implemented or phased-in at Exide 

Technologies by October 1, 2013, will further reduce lead values in the area and provide an ample 

margin of safety, well below U.S. EPA’s defined threshold for a detailed RACM/RACT analysis to 

be completed in conjunction with this submittal. 
7 

2.2 General Requirements for Demonstrating Reasonable Further Progress (Section 172(c)(2))

Section 172(c)(2) of the CAA requires areas that have been designated nonattainment for criteria 

pollutants to include a demonstration of RFP in attainment demonstrations. Section 172(c)(2) of 

the CAA defines RFP “as such annual incremental reductions in emissions of the relevant air 

pollution as required by Part D, or may reasonably be required by U.S. EPA for the purpose of 

ensuring attainment of the applicable NAAQS by the applicable attainment date”. 

As stated in U.S. EPA’s final lead rule for the 2008 lead NAAQS (73 FR 67039), effective January 

12, 2009, RFP is satisfied by the strict adherence to an ambitious compliance schedule which is 

expected to periodically yield significant emission reductions. 

Indiana does not intend to relax any control measures already implemented at Exide Technologies. 

Indiana has recently amended its lead rules to add emission standards for secondary lead smelters at 

326 IAC 20-13.1. Exide Technologies will be required to meet an expedited compliance schedule 

for certain NESHAP requirements. In addition to lead emission standards for individual emission 

units that are more stringent than those in the NESHAP, Indiana’s rule for secondary lead smelters 

includes opacity limits and supplemental requirements for total enclosure monitoring. These 

control measures and resulting emission reductions shall be achieved as soon as reasonably 

practicable, and by no later than October 1, 2013. Indiana’s rulemaking fulfills RFP as it will yield 

consistent and periodic significant lead emission reductions at Exide Technologies ensuring the 

Muncie Nonattainment Area will meet the lead NAAQS by the attainment date of December 31, 

2015. 

2.3 Emission Inventory (Section 172(c)(3))

Section 172(c)(3) of the CAA requires the development of a comprehensive, accurate, and current 

inventory of actual emissions from all sources of lead in the nonattainment area, including periodic 

revisions as the Administrator may determine necessary to assure that the requirements for this part 

are met. Federal requirements at 40 CFR 51.117 require lead emissions to be part of the state’s 

emissions inventory for the SIP. 

2.4 Identification and Quantification of Emissions (Section 172(c)(4))

Section 172(c)(4) of the CAA requires the SIP to identify and quantify the emissions of pollutants 

(in this case, lead) that sources will be allowed from the construction and operation of major new 

and modified sources in accordance with Section 173(a)(1)(B). These emissions must not interfere 

with attainment of the lead standard by the attainment date. Indiana’s permitting rules for 

nonattainment areas that meet this requirement are in 326 IAC 2-3. 

 
8 

2.5 Permit Program for New and Modified Major Stationary Sources (Section 172(c)(5))

Section 172(c)(5) of the CAA requires the state to implement a permit program consistent with the 

requirements of Section 173. Indiana has a long standing and fully-implemented New Source 

Review (NSR) permitting program in 326 IAC 2-2 and 326 IAC 2-3. Indiana’s NSR program was 

approved by U.S. EPA on October 7, 1994 (94 FR 24838), as part of the SIP. Any source or 

emission unit that is not listed in the emissions inventory, or for the closing of which credit was 

taken in demonstrating attainment, will not be allowed to construct, reopen, modify, or reconstruct 

without meeting all applicable permit rule requirements, including an air quality analysis to 

evaluate whether the new source will threaten the NAAQS. 

2.6 Other Control Measures, Means, or Techniques (Section 172(c)(6))

Section 172(c)(6) requires plan provisions to include enforceable emission limitations, and such 

other control measures, means or techniques, as well as schedules and timetables for compliance, as 

may be necessary or appropriate to provide for attainment by the applicable attainment date. 

Control measures to be phased-in or implemented at Exide Technologies in the next several years 

will bring the Muncie Nonattainment Area into attainment of the lead NAAQS and provide for an 

ample margin of safety. These control measures along with existing local, state, and national 

control measures will ensure that attainment of the lead standard in the area will be maintained with 

an increasing margin of safety over time. These measures are discussed in greater detail in Section 

7.0 of this document. 

2.7 Compliance with Section 110(a)(2) (Section 172(c)(7))

Section 172(c)(7) of the CAA requires nonattainment SIPs to meet the applicable provisions of 

Section 110(a)(2). The Indiana Department of Environmental Management (IDEM) has reviewed 

the requirements of Section 110(a)(2) of the CAA and has concluded that prior rule submittals, 

along with this attainment demonstration, address the relevant requirements associated with rule 

development, state implementation plan submissions, and implementation and enforcement of 

required control measures. Within a letter to U.S. EPA dated December 12, 2011, Indiana 

reaffirmed that it maintains the necessary infrastructure and resources to comply with Sections 

110(a)(1) and (2) of the CAA for all criteria pollutants (Appendix C). 

Due to the Muncie Nonattainment Area’s distance from the Indiana-Ohio state line, approximately 

30 miles, and the physical characteristics of lead emissions, it is not anticipated that lead emissions 

from this area will contribute significantly to nonattainment or interfere with maintenance of the 

lead NAAQS in the State of Ohio. 

2.8 Equivalent Techniques (Section 172(c)(8))

IDEM has followed U.S. EPA guidance on procedures for modeling, preparing emission 

inventories, and plan submittals. Therefore, IDEM is not requesting approval for equivalent 

techniques, as allowed under Section 172(c)(8) of the CAA. 

 
9 

2.9 Contingency Measures (Section 172(c)(9))

Section 172(c)(9) of the CAA requires states with nonattainment areas to include contingency 

measures as part of attainment demonstrations. Contingency measures are specific measures to be 

undertaken in the event that the area fails to attain the standard by the applicable attainment date. 

The selected contingency measures are discussed in greater detail in Section 8.0 of this document. 

3.0 MODELING 

This section presents details of the technical work done to analyze air quality data to demonstrate 

attainment of the lead standard. Lead SIP regulations found at 40 CFR 51.117 require states to 

conduct atmospheric dispersion modeling for the demonstration of attainment for areas in the 

vicinity of point sources listed in 40 CFR 51.117(a)(1). For attainment modeling, maximum 

allowable or federally enforceable permit limits should be the basis of the model input emissions, as 

described in Section 8.1 and Table 8-1 of Appendix W to 40 CFR Part 51 and U.S. EPA’s 

Guideline for Air Quality Models1

. 

3.1 Air Quality Analysis

IDEM conducted an air quality analysis using the NESHAP for secondary lead smelters in order to 

determine whether Exide Technologies would be able to meet the 2008 lead NAAQS. The most 

recent version of AERMOD (BEEST Version 9.90a) was used to conduct the analysis. 

Pre-processed meteorological data from Indianapolis International Airport and upper air data from 

Wright-Patterson Air Force base in Dayton, Ohio were used for the analysis. The data include 1-

minute readings from 2006 through 2010. 

All elevations for the buildings, sources, and receptors were calculated using U.S. EPA’s AERMAP 

terrain preprocessor for AERMOD. Building downwash from stationary point sources at Exide 

Technologies was considered in this analysis. Fugitive dust emissions were not considered. 

Receptors were placed 200 meters apart throughout the study area. Concentrations at 961 receptors 

were calculated. The receptor grid was taken from a previous modeling analysis. The entire 

nonattainment area (see Figure 1.1) and well beyond was covered by the receptors. The study area, 

as outlined in Figure 3.1, is bound by Jackson Street to the north, Interstate 67 to the south, 

Macedonia Avenue to the east, and Proctor Road to the west. 

 

 

1 http://www.epa.gov/scram001/guidance/guide/appw_05.pdf
10 

Figure 3.1 

Modeling Receptor Grid for Exide Technologies 

Exide’s sources are indicated by the red thumbtacks.

The 2009 input files contained four stationary point sources at Exide Technologies. Table 3.1 lists 

the unit permit source ID numbers and each unit’s permitted allowable maximum lead emissions 

rate in tons per year (tpy). The permitted lead emission rates were taken from Exide Technologies’ 

Title V Permit 035-22352-00028, issued by IDEM on September 7, 2007. Emission rates for 2011, 

as shown in Table 3.2, were calculated based on the grain/dry standard cubic foot proposed 

NESHAP limits. 
11 

Table 3.1 

2009 Point Sources – Exide Technologies 

Unit Description Permitted Lead 

Emission Limits (tpy) 

Unit 1 Lead Battery Crusher/Breaker 0.28 

Unit 4 Lead Reverberatory Furnace 1.49 

Unit 8 Material Handling 0.08 

Unit 9 Slag Crusher/Melting Pots 0.74 

Total Lead Emissions 2.59 

Table 3.2 lists the unit permit source ID numbers and each unit’s permitted allowable maximum 

lead emissions rate in tpy under the NESHAP for secondary lead smelters. 

Table 3.2 

2011 Point Sources – Exide Technologies 

Unit Description NESHAP Lead 

Emission Limits (tpy) 

Unit 1 Lead Battery Crusher/Breaker 0.27 

Unit 4 Lead Reverberatory Furnace 0.48 

Unit 8 Material Handling 0.004 

Unit 9 Slag Crusher/Melting Pots 0.008 

Total Lead Emissions 0.76 

After the air quality analysis was completed, LEADPOST was used to calculate the 3-month rolling 

average using the total tons per year emissions rate from Table 3.2. This tool calculates and outputs 

the rolling cumulative (all sources) 3-month average concentration at each modeled receptor with 

source group contributions and the maximum cumulative (all sources) rolling 3-month average 

concentration by receptor. LEADPOST calculated the maximum 3-month rolling average at 0.02 

μg/m3

 for the period ending February 2010. At the current permitted lead emission rates, 

LEADPOST calculated a 3-month rolling average of 0.19 μg/m3

. 

Implementation of the NESHAP for secondary lead smelters requires Exide Technologies to 

operate process and other fugitive lead dust sources within total enclosures that are maintained 

under negative pressure ensuring fugitive dust generated inside the facility is not released outside of 

the enclosures. This will aid in minimizing residual airborne lead emissions reintroduced into the 

atmosphere from the property. For attainment modeling purposes, maximum 3-month rolling 

average concentrations were modeled to provide a sufficient margin of error. Background 

concentrations were not added to modeled concentrations in this analysis. In order to determine any 

potential impacts background concentrations may have on lead concentrations at Exide 

Technologies, IDEM reviewed data from the lead monitoring network. Most sites are located in 

heavily industrialized areas, but two background/urban lead monitors could be representative of the 

impact at the facility (i.e., Evansville Civic Center/Post Office, Site ID # 18-163-0006/20, which 

was discontinued on March 22, 2011, and Indianapolis-Washington Park, Site ID# 18-097-0078). 

The most recent design value at both of these monitors was 0.01 μg/m3

. When considering a 

conservative concentration of 0.01 μg/m3 for background purposes and based on the fact that there 

are no significant local source contributions to lead levels modeled on the property, the modeled 
12 

design value provides an ample margin of safety from any increase in lead levels that could occur 

from the reintroduction of lead into the atmosphere from the property. 

According to U.S. EPA’s 2010 Toxic Release Inventory (TRI), fugitive lead emissions from Exide 

Technologies decreased from 433 total pounds per year in 2009 to zero total pounds per year in 

2010, therefore, it is reasonable to assume that significant quantities of uncontrolled fugitive 

emissions will not be released from Exide Technologies in the future. 

3.2 Analysis Results

According to the air quality analysis results, lead point source emissions from Exide Technologies 

should not contribute to an exceedance of the 2008 lead NAAQS under the NESHAP for secondary 

lead smelters. The current permitted lead emission rates could cause an exceedance of the NAAQS. 

However, most of the ambient lead concentrations from secondary lead smelters are from fugitive 

dust emissions. These fugitive dust emissions include reintroduction of lead into the atmosphere 

from the property. If all of the fugitive dust emissions are not captured and vented through a 

controlled stack, as required by the NESHAP for secondary lead smelters, exceedances of the 2008 

lead NAAQS are still possible. 

Monitoring data indicates that lead concentrations are currently well above the estimated 

concentrations of the modeled point sources. However, according to the modeling estimates, 

pending control measures to be implemented or phased-in as a result of the NESHAP for secondary 

lead smelters should improve air quality to levels below the 2008 lead NAAQS by December 31, 

2015. 

4.0 AIR QUALITY TRENDS 

Section 110(a)(2)(B) of the CAA requires a monitoring strategy for measuring, characterizing, and 

reporting lead. IDEM maintains a comprehensive network of air quality monitors throughout the 

state with the primary objective of being able to determine compliance with the lead NAAQS. 

The primary and secondary lead standards were first established in October 1978 at 1.5 μg/m3

. 

Attainment was determined by evaluating each calendar quarter arithmetic average, which could not 

exceed 1.5 μg/m3

 over a three-year period. U.S. EPA replaced the primary and secondary 1978 

lead standards with new primary and secondary lead standards of 0.15 μg/m3

 in October 2008. To 

attain the 2008 lead NAAQS, U.S. EPA uses a maximum (not-to-be-exceeded) rolling three-month 

average evaluated over a three-year period. Any three-month average exceeding 0.15 μg/m3 within 

a three-year period is considered a violation of the NAAQS. The three-month average is the 

average of three consecutive monthly averages (January to March, February to April, March to 

May, etc.). Each three-year period yields 36 three-month averages. Table 4.1 and Graph 4.1 reflect 

the highest annual quarterly arithmetic mean from 2000 through 2008, which was used to compare 

to the primary and secondary 1978 lead standards before they were revoked in 2008. Table 4.2 and 

Graph 4.2 show the rolling three-month averages for the time period of November 2007 through 

October 2012, which is used to compare to the 2008 primary and secondary lead standards. 
13 

Table 4.1 

Lead Quarterly Arithmetic Average Monitoring Data Summary, Muncie, 

Delaware County, Indiana 

Site # Site Name 

Quarterly Average (μg/m3

) 

1Q 

2000 

2Q 

2000 

3Q 

2000 

4Q 

2000 

1Q 

2001 

2Q 

2001 

3Q 

2001 

4Q 

2001 

1Q 

2002 

2Q 

2002 

3Q 

2002 

4Q 

2002 

18-035-0008 Muncie-Exide West Site 0.18 0.19 0.19 0.13 0.12 0.53 0.10 0.09 0.09 0.18 0.21 0.18 

18-035-0009 Muncie-Exide East Site 0.10 0.58 0.23 0.25 0.31 1.07 0.35 0.37 0.36 0.81 0.57 0.27 

 

Site # Site Name

1Q 

2003 

2Q 

2003 

3Q 

2003 

4Q 

2003 

1Q 

2004 

2Q 

2004 

3Q 

2004 

4Q 

2004 

1Q 

2005 

2Q 

2005 

3Q 

2005 

4Q 

2005 

18-035-0008 Muncie-Exide West Site 0.10 0.22 0.23 0.20 0.47 0.29 0.30 0.25 0.34 0.46 0.40 0.26 

18-035-0009 Muncie-Exide East Site 0.23 0.68 0.81 0.60 1.12 3.48 2.23 1.30 0.80 1.39 0.94 0.72 

Site # Site Name

1Q 

2006 

2Q 

2006 

3Q 

2006 

4Q 

2006 

1Q 

2007 

2Q 

2007 

3Q 

2007 

4Q 

2007 

1Q 

2008 

2Q 

2008 

3Q 

2008 

4Q 

2008 

18-035-0008 Muncie-Exide West Site 0.24 0.44 0.25 0.16 0.17 0.21 0.21 0.14 0.11 0.29 0.13 0.08 

18-035-0009 Muncie-Exide East Site 0.78 0.71 0.83 0.71 0.44 0.47 0.71 0.84 0.41 2.33 0.51 0.19 

Highlighted red numbers are over the 1978 lead standard of 1.5 μg/m3
14 

Graph 4.1 

Lead Highest Annual Quarterly Values, Muncie, Delaware County, Indiana 

Table 4.2 

Lead Three-Month Rolling Average Values Data Summary, Muncie, 

Delaware County, Indiana 

Site # Site Name 

Three-Month Average (μg/m3) 

11/07-

01/08 

12/07-

02/08 

01/08-

03/08 

02/08-

04/08 

03/08-

05/08 

04/08-

06/08 

05/08-

07/08 

06/08-

08/08 

07/08-

09/08 

08/08-

10/08 

09/08-

11/08 

10/08-

12/08 

18-035-0008 

MuncieExide West 

Site 

0.09 0.08 0.11 0.33 0.34 0.28 0.07 0.08 0.12 0.14 0.12 0.07 

18-035-0009 

MuncieExide East 

Site 

0.53 0.35 0.40 0.43 0.68 1.96 2.17 1.87 0.50 0.24 0.23 0.19 

18-035-0009 

Muncie-Mt. 

Pleasant 

Boulevard 

Monitor began operation in 2010. 

Site # Site Name 

11/08-

01/09 

12/08-

02/09 

01/09-

03/09 

02/09-

04/09 

03/09-

05/09 

04/09-

06/09 

05/09-

07/09 

06/09-

08/09 

07/09-

09/09 

08/09-

10/09 

09/09-

11/09 

10/09-

12/09 

18-035-0008 

MuncieExide West 

Site 

0.06 0.05 0.07 0.08 0.08 0.08 0.08 0.10 0.11 0.10 0.09 0.06 

18-035-0009 

MuncieExide East 

Site 

0.15 0.15 0.14 0.23 0.26 0.23 0.15 0.23 0.95 0.98 0.95 0.25 

18-035-0009 

Muncie-Mt. 

Pleasant 

Boulevard 

Monitor began operation in 2010. 

 

0.00

0.40

0.80

1.20

1.60

2.00

2.40

2.80

3.20

3.60

4.00

2000 2002 2004 2006 2008

Concentration (μg/m3)

Year

Lead Values 1978 Lead Standard (1.5 μg/m3) Trendline
15 

Site # Site Name 

11/09-

01/10 

12/09-

02/10 

01/10-

03/10 

02/10-

04/10 

03/10-

05/10 

04/10-

06/10 

05/10-

07/10 

06/10-

08/10 

07/10-

09/10 

08/10-

10/10 

09/10-

11/10 

10/10-

12/10 

18-035-0008 

MuncieExide West 

Site 

Monitor shut down 

18-035-0009 

MuncieExide East 

Site 

0.22 0.14 Downwind ambient monitor prior to 2010. Replaced by the Muncie-Mt. Pleasant Boulevard 

monitor in 2010. 

18-035-0009 

Muncie-Mt. 

Pleasant 

Boulevard 

Monitor began 

operation in 2010. 0.14 0.10 0.10 0.16 0.17 0.20 0.23 0.26 0.22 0.15 

Site # Site Name 

11/10-

01/11 

12/10-

02/11 

01/11-

03/11 

02/11-

04/11 

03/11-

05/11 

04/11-

06/11 

05/11-

07/11 

06/11-

08/11 

07/11-

09/11 

08/11-

10/11 

09/11-

11/11 

10/11-

12/11 

18-035-0008 

MuncieExide West 

Site 

Monitor shut down 

18-035-0009 

MuncieExide East 

Site 

Downwind ambient monitor prior to 2010. Replaced by the Muncie-Mt. Pleasant Boulevard monitor in 2010. 

18-035-0009 

Muncie-Mt. 

Pleasant 

Boulevard 

0.19 0.17 0.16 0.08 0.08 0.18 0.21 0.25 0.19 0.17 0.17 0.18 

Site # Site Name 

11/11-

01/12 

12/11-

02/12 

01/12-

03/12 

02/12-

04/12 

03/12-

05/12 

04/12-

06/12 

05/12-

07/12 

06/12-

08/12 

07/12-

09/12 

08/12-

10/12 

18-035-0008 

MuncieExide West 

Site 

Monitor shut down 

18-035-0009 

MuncieExide East 

Site 

Downwind ambient monitor prior to 2010. 

Replaced by the Muncie-Mt. Pleasant Boulevard 

monitor in 2010. 

18-035-0009 

Muncie-Mt. 

Pleasant 

Boulevard 

0.30 0.34 0.29 0.17 0.12 0.11 0.09 0.05 0.06 0.05 

Highlighted red numbers are rolling three-month averages above the 2008 lead standard of 0.15 μg/m3

The Muncie - Exide West Site monitor was discontinued on December 31, 2009. 

The Muncie - Exide East Site monitor was replaced by the Muncie - Mt. Pleasant Boulevard monitoring site on March 1, 2010. 
16 

Graph 4.2 

Lead Three-Month Rolling Average Values, Muncie, 

Delaware County, Indiana 

As Graph 4.1 illustrates, lead values in the Muncie Nonattainment Area were above the primary and 

secondary 1978 lead standards in 2004 and 2008. The high values in 2004 were due to a fire in the 

baghouse, and the high values in 2008 were due to an acute incident at the facility’s rotary dryer. In 

order to address these violations, Exide Technologies entered into an Agreed Order (2008-18144-

A) with IDEM on October 20, 2009, to implement additional fugitive dust emission control 

measures and mitigation control strategies (Appendix F). Exide Technologies has taken corrective 

action related to those incidents and has implemented steps to prevent recurrences. 

As shown in Graph 4.2, lead three-month rolling average values generally show a downward trend 

over time. However, as a result of the high values in 2008, lead values in the Muncie 

Nonattainment Area remain above the primary and secondary 2008 lead standards. Table 4.3 and 

Graph 4.3 show the highest rolling three-month average values for each of the lead monitors in the 

nonattainment area from the 2006 through 2011 three-year time periods. 

0.00

0.50

1.00

1.50

2.00

2.50

11/07 ‐ 01/08 12/07 ‐ 02/08 01/08 ‐ 03/08 02/08 ‐ 04/08 03/08 ‐ 05/08 04/08 ‐ 06/08 05/08 ‐ 07/08 06/08 ‐ 08/08 07/08 ‐ 09/08 08/08 ‐ 10/08 09/08 ‐ 11/08 10/08 ‐ 12/08 11/08 ‐ 01/09 12/08 ‐ 02/09 01/09 ‐ 03/09 02/09 ‐ 04/09 03/09 ‐ 05/09 04/09 ‐ 06/09 05/09 ‐ 07/09 06/09 ‐ 08/09 07/09 ‐ 09/09 08/09 ‐ 10/09 09/09 ‐ 11/09 10/09 ‐ 12/09 11/09 ‐ 01/10 12/09 ‐ 02/10 01/10 ‐ 03/10 02/10 ‐ 04/10 03/10 ‐ 05/10 04/10 ‐ 06/10 05/10 ‐ 07/10 06/10 ‐ 08/10 07/10 ‐ 09/10 08/10 ‐ 10/10 09/10 ‐ 11/10 10/10 ‐ 12/10 11/10 ‐ 01/11 12/10 ‐ 02/11 01/11 ‐ 03/11 02/11 ‐ 04/11 03/11 ‐ 05/11 04/11 ‐ 06/11 05/11 ‐ 07/11 06/11 ‐ 08/11 07/11 ‐ 09/11 08/11 ‐ 10/11 09/11 ‐ 11/11 10/11 ‐ 12/11 11/11 ‐ 01/12 12/11 ‐ 02/12 01/12 ‐ 03/12 02/12 ‐ 04/12 03/12 ‐ 05/12 04/12 ‐ 06/12 05/12‐07/12 06/12‐08/12 07/12‐09/12 08/12‐10/12

Concentration (μg/m3)

Year

Lead Three‐Month Rolling Average Values 2008 Lead Standard (0.15 μg/m3) Trendline
17 

Table 4.3 

Lead Historical Design Values for the Muncie, Delaware County, 

Indiana Monitors 

Site ID Site Name 

Highest Rolling 

Three-Month 

Lead Value, 

2006-2008 

(μg/m3) 

Highest 

Rolling ThreeMonth Lead 

Value, 2007-

2009 (μg/m3) 

Highest Rolling 

Three-Month 

Lead Value, 2008-

2010 (μg/m3) 

Highest Rolling 

Three-Month 

Lead Value, 2009-

2011 (μg/m3) 

18-035-0008 Muncie - Exide 

West Site 0.52 0.34 0.34* 

18-035-0009 Muncie - Exide 

East Site 2.17 2.17 2.17* 

18-035-0009 Muncie - Mt. 

Pleasant Boulevard 0.26* 

* Two years of data 

The Muncie - Exide West Site monitor was discontinued on December 31, 2009. 

The Muncie - Exide East Site monitor was replaced by the Muncie - Mt. Pleasant Boulevard monitoring site on March 1, 2010.

Graph 4.3 

Lead Historical Design Values for the Muncie, Delaware County, 

Indiana Monitors 

2008-2010 and 2009-2011 design values represent two years of data. 

The Muncie - Exide West Site monitor was discontinued on December 31, 2009. 

The Muncie - Exide East Site monitor was replaced by the Muncie - Mt. Pleasant Boulevard monitoring site on March 1, 2010.

 

0.0

0.5

1.0

1.5

2.0

2.5

Muncie - Exide West Site Muncie - Exide East Site Muncie - Mt. Pleasant Blvd

2006-2008 2007-2009 2008-2010 2009-2011 2008 Lead Standard (0.15 μg/m3)

μg/m3
18 

4.1 Wind Rose Analysis

In order to determine the meteorological effects on the elevated lead concentrations in the Muncie 

Nonattainment Area, meteorological data were gathered from the Delaware County – Johnson 

Automated Surface Observing System (ASOS), located approximately 5 miles to the north –

northeast of Exide Technologies, for 2008, 2009, 2010, and 2011. This data were formatted in 

order to create wind roses to identify prevailing wind directions. Figure 4.1 below shows the 

annual wind roses from the Delaware County ASOS station with prevailing winds found to be from 

the southwest, west, and northwest. 

Figure 4.1 

Annual Wind Roses for 2008-2011 

 2008 2009 

 
19 

 2010 2011

Based on the configuration of the Exide Technologies facility and the location of the Muncie, 

Mount Pleasant Boulevard lead monitor, Exide Technologies would impact the Muncie 

Nonattainment Area lead monitor when winds are from the southwest. 

4.2 Snow Cover and Precipitation Analysis

To help address fugitive lead road dust impacts on the Muncie – Exide East Site and the Muncie – 

West Site monitors, IDEM conducted a snow cover and precipitation analysis for all days that 

occurred from January 2008 through June 2011 when lead concentrations were observed at the 

monitors. There were high concentration days when snow cover or heavier precipitation events 

were observed. This fact, although not ruling out fugitive road dust impacts, would indicate that 

fugitive road dust impacts were less a factor to the higher monitored concentrations. Table 4.4 

shows the comparison of monitored days when snow cover was observed versus days when snow 

cover was not observed. 

Table 4.4 

Snow Cover Observed on Monitored Days (Delaware County 

– Johnson ASOS Station) 

Snow Cover on 33 days No Snow Cover on 227 days 

Exide East Site Exide West Site Exide East Site Exide West Site 

(μg/m3) (μg/m3) (μg/m3) (μg/m3) 

Average 0.324 0.058 0.710 0.171 

Maximum 1.650 0.289 39.080 5.800 
20 

Clearly, lead concentrations were higher when there was no snow cover observed. However, 

relatively high lead concentrations still occurred on days when snow cover was observed, thereby 

lessening fugitive road dust impacts. Even more telling is the comparison of precipitation days. 

Table 4.5 compares the days when precipitation was observed with the days when no precipitation 

occurred. This includes precipitation amounts ranging from a trace to amounts in excess of 1 inch 

for the monitored day. 

Table 4.5 

Precipitation Recorded on Monitored Days (Delaware County – 

Johnson ASOS station) 

 Exide East Site Exide West Site 

Concentrations when... (μg/m3

) (μg/m3) 

No precipitation was recorded 0.440 0.126 

Precipitation was recorded 0.913 0.193 

Precipitation was recorded on eleven of the top twenty maximum lead concentration days recorded 

at the Muncie – Exide East Site monitor and six out of the top ten maximum lead concentration 

days at the Muncie – Exide West Site monitor as shown in Tables 4.6 and 4.7. These tables also 

show the precipitation amount and general wind conditions during the days the highest 

concentrations were recorded. 
21 

Table 4.6 

Wind Conditions/Precipitation on the Highest Concentration Days at the 

Muncie – Exide East Site Monitor 

Date / Day 

Exide 

East Site 

Exide 

West Site Precipitation? Wind Conditions

(μg/m3) (μg/m3) (inches) (direction and speed) 

6/27/2008 - Friday 39.08 0.03 Yes - 0.21 rain SW winds (3 to 13 mph) all day 

6/5/2008 - Thursday 6.62 0.03 No SSW to SW winds (6 to 15 mph) all day 

5/26/2008 - Monday 4.26 0.04 Yes - trace rain SW to WSW winds (3 to 20 mph) all day 

7/3/2008 - Thursday 4.23 0.03 Yes - 1.03 rain Wind shift at noon from SW (3 to 17 mph) to NE 

6/9/2008 - Monday 3.99 0.03 Yes - 0.64 rain SW to SSW winds (6 to 15 mph) all day 

3/11/2008 - Tuesday 3.82 0.03 No NW to W to SW winds (3 to 20 mph) all day 

3/25/2008 - Tuesday 3.67 0.03 No SW to WSW to W winds (6 to 28 mph) all day 

5/14/2008 - Wednesday 3.47 0.03 Yes - 0.61 rain SW to S to SW to NW winds (5 to 15 mph) all day 

4/25/2009 - Saturday 2.98 0.03 No SW winds (7 to 24 mph) all day 

6/7/2008 - Saturday 2.79 0.03 Yes - 0.84 rain W to SW to S winds (4 to 16 mph) all day 

8/9/2009 - Sunday 2.64 0.03 No SW to W to SW winds (6 to 15 mph) all day 

6/29/2008 - Sunday 2.47 0.03 Yes - 0.08 rain SW to WSW to W to NW winds (5 to 20 mph) all day 

6/3/2008 - Tuesday 2.32 0.39 Yes - 0.52 rain SSW to SW to NW to E winds (5 to 13 mph) all day 

8/21/2009 - Friday 2.29 0.03 Yes - 0.03 rain SW to NW winds (5 to 16 mph) all day 

6/25/2008 - Wednesday 2.28 0.03 No S to SW winds (3 to 15 mph) all day 

7/11/2008 - Friday 2.14 0.05 Yes - trace rain WSW to W to SW winds (3 to 13 mph) all day 

7/7/2008 - Monday 1.94 0.14 No S to SW to W to SW winds (3 to 11 mph) all day 

6/8/2011 - Wednesday 1.80 N/A No S to SW to WSW to SW winds (6 to 15 mph) all day 

5/30/2008 - Friday 1.78 0.04 Yes - 0.08 rain S to SW winds (3 to 23 mph) all day 

1/23/2008 - Wednesday 1.65 0.03 No SW to W to SW winds (7 to 13 mph) all day 

Table 4.7 

Wind Conditions/Precipitation on Highest Concentration Days at the 

Muncie – Exide West Site Monitor

Date / Day 

Exide West

Site 

Exide East 

Site Precipitation? Wind Conditions

(μg/m3) (μg/m3) (inches) (direction and speed) 

4/10/2008 - Thursday 5.80 N/A Yes - 0.43 rain E to SE winds (9 to 18 mph) all day 

4/8/2008 - Tuesday 1.76 N/A Yes - trace rain NW to NE to SE to S winds (3 to 17 mph) all day 

4/24/2008 - Thursday 1.55 N/A Yes - 0.18 rain SE to S winds (5 to 23 mph) all day 

3/17/2008 - Monday 1.44 0.03 Yes - 0.1 rain SE winds (9 to 18 mph) all day 

3/21/2008 - Friday 1.01 0.44 Yes - 0.02 rain E to SE to NE winds (5 to 17 mph) all day 

9/23/2008 - Tuesday 0.59 0.04 No SE to S to SE winds (calm to 10 mph) all day 

10/7/2008 - Tuesday 0.57 0.17 Yes - 0.41 rain SE to SW to S winds (6 to 13 mph) all day 

9/19/2008 - Friday 0.56 0.06 No ESE to E to SE to SW winds (calm to 5 mph) all day 

7/14/2009 - Tuesday 0.50 0.031 No SE winds (calm to 15 mph) all day 

3/29/2008 - Saturday 0.49 0.03 No NE to E to SE to E winds (3 to 18 mph) all day 

 
22 

Based on the snow cover and precipitation analysis, IDEM is not negating the impacts from fugitive 

road dust on the lead monitors. However, on days when snow cover or precipitation was observed 

(events that would suppress fugitive dust impacts) relatively high lead concentrations were still 

monitored. This would indicate that emission sources, in addition to the fugitive road dust, may 

have larger impacts. 

5.0 EMISSION TREND ANALYSIS 

For emission inventory purposes, area and point source emissions data for Exide Technologies were 

retrieved from U.S. EPA’s TRI Explorer1 on May 5, 2012 (Appendix B). This dataset contains a 

more comprehensive amount of emissions data in comparison to the limited number of reports 

made through Indiana’s emission statement reporting program. As a relatively small source, Exide 

Technologies was not required to report lead emissions data to the state until recently (starting in 

2008 for inventory year 2007). Indiana’s Emissions Reporting Rule found in 326 IAC 2-6, only 

requires Exide Technologies to report lead emissions to the emission statement reporting program 

once every three years. TRI is an annual report that requires reporters to delineate a variety of 

disposal and release types, including air releases. The higher frequency of reporting and the longer 

span of time allows for a more comprehensive review of the trends at this facility. The emission 

inventories used in this attainment demonstration are also subject to public comment along with the 

full attainment demonstration. 

Table 5.1 and Graph 5.1 show historical lead emissions for Exide Technologies for the years 2001 

through 2010 reported under the TRI program. While occasional spikes can be seen, lead emissions 

have been trending downward since 2003. No explanation is provided in TRI as to why fugitive 

lead emissions decreased from 433 total pounds per year in 2009 to zero total pounds per year in 

2010. 

Table 5.1 

Lead Emissions Inventory – Exide Technologies, Delaware County, Indiana 

Lead Compounds (Total Pounds per Year) 

Year Fugitive Point Total 

2001 499 1,603 2,102 

2002 499 2,660 3,159 

2003 499 2,660 3,159 

2004 499 565 1,064 

2005 499 410 909 

2006 499 457 956 

2007 125 1,618 1,743 

2008 459 577 1,036 

2009 433 338 771 

2010 0 365 365 

 

 

1

 (http://iaspub.epa.gov/triexplorer/tri_release.chemical
23 

Graph 5.1 

Lead Fugitive and Point Source Emission Trends – 

Exide Technologies, Muncie, Delaware County, Indiana 

Point sources at Exide Technologies are already well controlled and have not historically exceeded 

permitted lead emission limits. Fugitive emissions are not released from a single point and are not 

minimized by pollution control technology. Exide Technologies continues to make improvements 

to their facility in order to minimize all potential fugitive lead emissions and, thereby, further 

reduce monitored lead levels in the future. 

6.0 TRANSPORTATION CONFORMITY 

Transportation conformity is required under Section 176(c) of the CAA to ensure that federally 

supported highway and transit project activities are consistent with (“conform to”) the purpose of 

the SIP. Transportation conformity applies to areas that are designated nonattainment, and those 

areas redesignated attainment after 1990 (“maintenance areas” with plans developed under Section 

175A of the CAA) for transportation-related criteria pollutants. In light of the elimination of lead 

additives from gasoline used as motor vehicle fuel, mobile sources are not a significant contributor 

of lead emissions. As such, transportation conformity is not of concern for the 2008 lead NAAQS 

(73 FR 67043). 

 

-

500 

1,000 

1,500 

2,000 

2,500 

3,000 

3,500 

2001 2002 2003 2004 2005 2006 2007 2008 2009 2010

Fugitive Point Total

Year

Total Pounds per Year
24 

7.0 CONTROL STRATEGY 

The following is a list of several state and federal control measures already in place or being 

implemented in the next several years that will reduce lead emissions in the Muncie Nonattainment 

Area. 

7.1 Prohibition on Gasoline Containing Lead or Lead Additives

On February 2, 1996, U.S. EPA issued a direct final rule to amend 40 CFR 80 to prohibit the 

introduction of gasoline which is produced with the use of any lead additive, or contains more than 

0.05 gram of lead per gallon, into commerce for use as motor vehicle fuel, effective January 1, 

1996, in accordance with Section 211(n) of the CAA. 

7.2 New Source Review Provisions

Indiana has a long standing and fully implemented New Source Review permitting program. New 

Source Review is addressed in 326 IAC 2. The rule includes provisions for the Prevention of 

Significant Deterioration (PSD) in 326 IAC 2-2 and Emission Offset requirements for 

nonattainment areas in 326 IAC 2-3. 

Any source that is not listed in the emission inventory, or for which credit is taken for closing in 

demonstrating attainment, will not be allowed to construct, reopen, modify, or reconstruct without 

meeting all applicable permit rule requirements. 

7.3 Controls to Remain in Effect

Indiana does not intend to relax any control measures already implemented. Indiana commits that 

any changes to its rules, or emission limits applicable to lead sources will be submitted to U.S. EPA 

for approval. Indiana intends to continue enforcing all rules that relate to emissions of lead in the 

Muncie Nonattainment Area. 

As part of existing requirements, Exide Technologies was required to develop Standard Operating 

Procedures for Fugitive Dust Control designed to prevent deterioration of control equipment 

performance and to minimize fugitive lead emissions. Provisions contained in Exide Technologies 

existing fugitive dust control plan shall continue to be implemented unless superseded by 

requirements contained in Indiana’s final lead rule. A copy of Exide Technologies Fugitive Dust 

Control Plan, dated October 2009, is included as Appendix E. 

7.4 Secondary Lead Smelting: National Emission Standards for Hazardous Air Pollutants

On January 5, 2012, U.S. EPA finalized the NESHAP for secondary lead smelting. The rule 

establishes a facility-wide, flow weighted average lead emissions limit from stacks of 0.20 

milligrams per dry standard cubic meter (mg/dscm) and an individual stack lead emissions limit of 

1.0 mg/dscm for each stack at existing sources. The standard also establishes modified and 

additional testing, monitoring, recordkeeping, reporting, notifications, and revisions to the 

regulatory provisions related to emissions during periods of startup, shutdown, and malfunction. 
25 

For existing sources, compliance with the requirements of the revised NESHAP must be 

demonstrated by no later than January 6, 2014. New sources must demonstrate compliance no later 

than January 5, 2012. These standards will result in significant lead point source emission 

reductions from secondary lead smelters. 

7.5 Revisions to Indiana’s Lead Rule

Indiana’s lead standard attainment rulemaking amends requirements for secondary lead smelters by 

adding 326 IAC 20-13.1. Indiana’s previous rule for secondary lead smelters incorporated portions 

of 40 CFR 63, Subpart X by reference, including certain operational standards and testing 

requirements. The current rulemaking directly incorporates text from the NESHAP to ensure 

Indiana’s rule is permanent and enforceable. 

Indiana’s rulemaking for secondary lead smelters makes necessary changes to address the federal 

revisions to the NESHAP for secondary lead smelters at 40 CFR 63, Subpart X and includes an 

expedited compliance schedule for Exide Technologies. Exide Technologies must demonstrate 

compliance with specified portions of the rule by October 1, 2013. In addition to lead emission 

standards for individual emission units at secondary lead smelters that are more stringent than those 

in the NESHAP, Indiana’s rule for secondary lead smelters includes opacity limits and 

supplemental requirements for total enclosure monitoring. These requirements will result in 

significant stationary point source and fugitive dust emission reductions at Exide Technologies, 

ensuring the Muncie Nonattainment Area will meet the lead NAAQS by the attainment date of 

December 31, 2015. Indiana’s final promulgated lead rule (LSA Document#11-774(F)) was 

adopted by the Air Pollution Control Board on November 7, 2012. A copy of Indiana’s final rule 

which was filed with the Publisher of the Indiana Register on February 27, 2013 (DIN: 20130227-

IR-326110774FRA) is included as Appendix D. 

8.0 CONTINGENCY MEASURES 

Indiana will consider necessary contingency measures to be phased-in or implemented at Exide 

Technologies from a comprehensive list of measures deemed appropriate and effective at the time 

the selection is made. Listed below are example measures that may be considered. The selection of 

measures will be based upon cost-effectiveness, emissions reduction potential, economic and social 

considerations, or other factors that IDEM deems appropriate. IDEM will solicit input from 

interested and affected persons in the nonattainment area prior to selecting appropriate contingency 

measures. All of the listed contingency measures are potentially effective or proven methods of 

obtaining significant reductions of lead emissions. Because it is not possible at this time to 

determine what control measure(s) will be appropriate at an unspecified time in the future, the list

of contingency measures outlined below is not comprehensive. Indiana anticipates that if 

contingency measures should ever be necessary, it is unlikely that a significant number (i.e., all 

those listed below) will be required. 

 
26 

1) Examples of contingency measures for controlling area source fugitive emissions may include 

stabilizing additional storage piles. 

2) Examples of contingency measures for process-related fugitive emissions include increasing the 

enclosure of buildings, increasing air flow in hoods, and/or modifying operation and 

maintenance procedures. 

3) Examples of contingency measures for stack sources include reducing hours of operation, 

changing the feed material to lower lead content, and reducing the occurrence of malfunctions by 

modifying operations and maintenance procedures. 

No contingency measure shall be implemented without providing the opportunity for full public 

participation during which the relative costs and benefits of individual measures, at the time they 

are under consideration, can be fully evaluated. 

9.0 PUBLIC PARTICIPATION 

In accordance with 40 CFR 51.102, public participation in this request was provided as follows: 

Notice of availability of the complete document and a request for the opportunity for a public 

hearing was made available on IDEM’s website on December 11, 2012 at 

http://www.in.gov/idem/6398.htm. It remained posted on the site until at least January 21, 2013. 

No comments were received during the public comment period. There was not a request for a 

public hearing during the public comment period and the hearing was not required to be held. 

A copy of the legal public notice and certification of publication can be found in Appendix H. 

10.0 CONCLUSION 

Monitored air quality in the Muncie, Delaware County, Indiana lead nonattainment area has 

generally shown a downward trend over time. Lead emissions in the Muncie Nonattainment Area 

are primarily from stationary point source and fugitive dust emissions from Exide Technologies. 

Lead point source emissions from Exide Technologies are already well controlled and have not 

historically exceeded permitted emission limits. Exide Technologies continues to make 

improvements to their facility in order to minimize all potential fugitive lead emissions and, 

thereby, reduce monitored lead levels in the future. 

This demonstration shows that lead emission reductions since designation have had a positive effect 

on monitored lead levels in the nonattainment area. This attainment demonstration shows that once 

the modeling results are considered along with additional stationary point source and fugitive dust 

mitigation control measures to be phased-in or implemented at Exide Technologies by October 

2013, air quality in the area will continue to improve and will achieve attainment of the lead 

standard by December 31, 2015, and provide for an ample margin of safety. 
27 

This plan satisfies Indiana’s obligation under Section 172(c) of the CAA to demonstrate how the 

area will attain the 2008 lead NAAQS by the attainment date, and, as a result, realize cleaner air. 

The development of this plan will bring this region into compliance with state and federal lead air 

quality standards, and provide real progress in the state’s journey toward cleaner air. 
This page intentionally left blank. 
Appendix A 

Air Quality System (AQS) and Indiana Department of 

Environmental Management (IDEM) Lead Monitor 

Data Values for Delaware County, Indiana 

(2000-October 2012) 
This page intentionally left blank. 
A-1

Delaware County Air Quality Monitoring Data used for Designation 

Site ID Site Name 

Highest Rolling Three-Month 

Lead Value, 2006-2008 

(μg/m3

) 

Highest Rolling Three-Month 

Lead Value, 2007-2009 

(μg/m3

) 

18-035-0008 Muncie – Exide West Site 0.52 0.34 

18-035-0009 Muncie – Exide East Site 2.17 2.17 

Lead Quarterly Arithmetic Average Monitoring Data Summary, Muncie, 

Delaware County, Indiana 

Site # Site Name 

Quarterly Average (μg/m3

) 

1Q 

2000 

2Q 

2000 

3Q 

2000 

4Q 

2000 

1Q 

2001 

2Q 

2001 

3Q 

2001 

4Q 

2001 

1Q 

2002 

2Q 

2002 

3Q 

2002 

4Q 

2002 

18-035-0008 Muncie – Exide West Site 0.18 0.19 0.19 0.13 0.12 0.53 0.10 0.09 0.09 0.18 0.21 0.18 

18-035-0009 Muncie – Exide East Site 0.10 0.58 0.23 0.25 0.31 1.07 0.35 0.37 0.36 0.81 0.57 0.27 

 

Site # Site Name

1Q 

2003 

2Q 

2003 

3Q 

2003 

4Q 

2003 

1Q 

2004 

2Q 

2004 

3Q 

2004 

4Q 

2004 

1Q 

2005 

2Q 

2005 

3Q 

2005 

4Q 

2005 

18-035-0008 Muncie – Exide West Site 0.10 0.22 0.23 0.20 0.47 0.29 0.30 0.25 0.34 0.46 0.40 0.26 

18-035-0009 Muncie – Exide East Site 0.23 0.68 0.81 0.60 1.12 3.48 2.23 1.30 0.80 1.39 0.94 0.72 

Site # Site Name

1Q 

2006 

2Q 

2006 

3Q 

2006 

4Q 

2006 

1Q 

2007 

2Q 

2007 

3Q 

2007 

4Q 

2007 

1Q 

2008 

2Q 

2008 

3Q 

2008 

4Q 

2008 

18-035-0008 Muncie – Exide West Site 0.24 0.44 0.25 0.16 0.17 0.21 0.21 0.14 0.11 0.29 0.13 0.08 

18-035-0009 Muncie – Exide East Site 0.78 0.71 0.83 0.71 0.44 0.47 0.71 0.84 0.41 2.33 0.51 0.19 

Highlighted red numbers are over the 1978 lead standard of 1.5 μg/m3
A-2

Lead Highest Annual Quarterly Values, Muncie, Delaware County, Indiana 

 Lead Three-Month Rolling Average Values Data Summary, Muncie, 

Delaware County, Indiana 

Site # Site Name 

Three-Month Average (μg/m3) 

11/07-

01/08 

12/07-

02/08 

01/08-

03/08 

02/08-

04/08 

03/08-

05/08 

04/08-

06/08 

05/08-

07/08 

06/08-

08/08 

07/08-

09/08 

08/08-

10/08 

09/08-

11/08 

10/08-

12/08 

18-035-0008 Muncie – Exide 

West Site 0.09 0.08 0.11 0.33 0.34 0.28 0.07 0.08 0.12 0.14 0.12 0.07 

18-035-0009 Muncie – Exide 

East Site 0.53 0.35 0.40 0.43 0.68 1.96 2.17 1.87 0.50 0.24 0.23 0.19 

18-035-0009 Muncie – Mt. 

Pleasant Boulevard Monitor began operation in 2010. 

Site # Site Name 

11/08-

01/09 

12/08-

02/09 

01/09-

03/09 

02/09-

04/09 

03/09-

05/09 

04/09-

06/09 

05/09-

07/09 

06/09-

08/09 

07/09-

09/09 

08/09-

10/09 

09/09-

11/09 

10/09-

12/09 

18-035-0008 Muncie – Exide 

West Site 0.06 0.05 0.07 0.08 0.08 0.08 0.08 0.10 0.11 0.10 0.09 0.06 

18-035-0009 Muncie – Exide 

East Site 0.15 0.15 0.14 0.23 0.26 0.23 0.15 0.23 0.95 0.98 0.95 0.25 

18-035-0009 Muncie – Mt. 

Pleasant Boulevard Monitor began operation in 2010. 

 

0.00

0.40

0.80

1.20

1.60

2.00

2.40

2.80

3.20

3.60

4.00

2000 2002 2004 2006 2008

Concentration (μg/m3)

Year

Lead Values 1978 Lead Standard (1.5 μg/m3) Trendline
A-3

Site # Site Name 

11/09-

01/10 

12/09-

02/10 

01/10-

03/10 

02/10-

04/10 

03/10-

05/10 

04/10-

06/10 

05/10-

07/10 

06/10-

08/10 

07/10-

09/10 

08/10-

10/10 

09/10-

11/10 

10/10-

12/10 

18-035-0008 Muncie – Exide 

West Site Monitor shut down 

18-035-0009 Muncie – Exide 

East Site 0.22 0.14 Downwind ambient monitor prior to 2010. Replaced by the Muncie-Mt. Pleasant Boulevard monitor in 2010. 

18-035-0009 Muncie – Mt. 

Pleasant Boulevard 

Monitor began 

operation in 2010. 0.14 0.10 0.10 0.16 0.17 0.20 0.23 0.26 0.22 0.15 

Site # Site Name 

11/10-

01/11 

12/10-

02/11 

01/11-

03/11 

02/11-

04/11 

03/11-

05/11 

04/11-

06/11 

05/11-

07/11 

06/11-

08/11 

07/11-

09/11 

08/11-

10/11 

09/11-

11/11 

10/11-

12/11 

18-035-0008 Muncie – Exide 

West Site Monitor shut down 

18-035-0009 Muncie – Exide 

East Site Downwind ambient monitor prior to 2010. Replaced by the Muncie-Mt. Pleasant Boulevard monitor in 2010. 

18-035-0009 Muncie – Mt. 

Pleasant Boulevard 0.19 0.17 0.16 0.08 0.08 0.18 0.21 0.25 0.19 0.17 0.17 0.18 

Site # Site Name 

11/11-

01/12 

12/11-

02/12 

01/12-

03/12 

02/12-

04/12 

03/12-

05/12 

04/12-

06/12 

05/12-

07/12 

06/12-

08/12 

07/12-

09/12 

08/12-

10/12 

18-035-0008 Muncie – Exide 

West Site Monitor shut down 

18-035-0009 Muncie – Exide 

East Site 

Downwind ambient monitor prior to 2010. 

Replaced by the Muncie-Mt. Pleasant 

Boulevard monitor in 2010. 

18-035-0009 Muncie – Mt. 

Pleasant Boulevard 0.30 0.34 0.29 0.17 0.12 0.11 0.09 0.05 0.06 0.05 

Highlighted red numbers are rolling three-month averages above the 2008 lead standard of 0.15 μg/m3

The Muncie - Exide West Site monitor was discontinued on December 31, 2009. 

The Muncie - Exide East Site monitor was replaced by the Muncie - Mt. Pleasant Boulevard monitoring site on March 1, 2010. 

 Lead Three-Month Rolling Average Values, Muncie, Delaware County, Indiana 

0.00

0.50

1.00

1.50

2.00

2.50

11/07 ‐ 01/08 12/07 ‐ 02/08 01/08 ‐ 03/08 02/08 ‐ 04/08 03/08 ‐ 05/08 04/08 ‐ 06/08 05/08 ‐ 07/08 06/08 ‐ 08/08 07/08 ‐ 09/08 08/08 ‐ 10/08 09/08 ‐ 11/08 10/08 ‐ 12/08 11/08 ‐ 01/09 12/08 ‐ 02/09 01/09 ‐ 03/09 02/09 ‐ 04/09 03/09 ‐ 05/09 04/09 ‐ 06/09 05/09 ‐ 07/09 06/09 ‐ 08/09 07/09 ‐ 09/09 08/09 ‐ 10/09 09/09 ‐ 11/09 10/09 ‐ 12/09 11/09 ‐ 01/10 12/09 ‐ 02/10 01/10 ‐ 03/10 02/10 ‐ 04/10 03/10 ‐ 05/10 04/10 ‐ 06/10 05/10 ‐ 07/10 06/10 ‐ 08/10 07/10 ‐ 09/10 08/10 ‐ 10/10 09/10 ‐ 11/10 10/10 ‐ 12/10 11/10 ‐ 01/11 12/10 ‐ 02/11 01/11 ‐ 03/11 02/11 ‐ 04/11 03/11 ‐ 05/11 04/11 ‐ 06/11 05/11 ‐ 07/11 06/11 ‐ 08/11 07/11 ‐ 09/11 08/11 ‐ 10/11 09/11 ‐ 11/11 10/11 ‐ 12/11 11/11 ‐ 01/12 12/11 ‐ 02/12 01/12 ‐ 03/12 02/12 ‐ 04/12 03/12 ‐ 05/12 04/12 ‐ 06/12 05/12‐07/12 06/12‐08/12 07/12‐09/12 08/12‐10/12

Concentration (μg/m3)

Year

Lead Three‐Month Rolling Average Values 2008 Lead Standard (0.15 μg/m3) Trendline
A-4

 Historical Design Values for the Muncie, Delaware County, Indiana Monitors 

Site ID Site Name 

Highest Rolling 

Three-Month Lead 

Value, 2006-2008 

(μg/m3) 

Highest 

Rolling ThreeMonth Lead 

Value, 2007-

2009 (μg/m3) 

Highest Rolling 

Three-Month 

Lead Value, 2008-

2010 (μg/m3) 

Highest Rolling 

Three-Month 

Lead Value, 2009-

2011 (μg/m3) 

18-035-0008 Muncie – Exide 

West Site 0.52 0.34 0.34* 

18-035-0009 Muncie – Exide 

East Site 2.17 2.17 2.17* 

18-035-0009 Muncie – Mt. 

Pleasant Boulevard 0.26* 

* Two years of data 

The Muncie - Exide West Site monitor was discontinued on December 31, 2009. 

The Muncie - Exide East Site monitor was replaced by the Muncie - Mt. Pleasant Boulevard monitoring site on March 1, 2010. 

Historical Design Values for the Muncie, Delaware County, Indiana Monitors 

2008-2010 and 2009-2011 design values represent two years of data. 

The Muncie - Exide West Site monitor was discontinued on December 31, 2009. 

The Muncie - Exide East Site monitor was replaced by the Muncie - Mt. Pleasant Boulevard monitoring site on March 1, 2010.

0.0

0.5

1.0

1.5

2.0

2.5

Muncie ‐ Exide West Site Muncie ‐ Exide East Site Muncie ‐ Mt. Pleasant Blvd

2006‐2008 2007‐2009

2008‐2010 2009‐2011

μg/m3
APPENDIX B

Lead Area and Point Source Emissions (2000 – 

2010), Delaware County, Indiana 
This page left intentionally blank.
B-1 

Lead Area and Point Emissions Inventory – Exide Technologies, 

Delaware County, Indiana 

Lead Compounds (Total Pounds per Year) 

Year Fugitive Point Total 

2001 499 1,603 2,102 

2002 499 2,660 3,159 

2003 499 2,660 3,159 

2004 499 565 1,064 

2005 499 410 909 

2006 499 457 956 

2007 125 1,618 1,743 

2008 459 577 1,036 

2009 433 338 771 

2010 0 365 365 

Lead Area and Point Emissions Inventory – Exide Technologies, 

Delaware County, Indiana

-

500 

1,000 

1,500 

2,000 

2,500 

3,000 

3,500 

2001 2002 2003 2004 2005 2006 2007 2008 2009 2010

Fugitive Point Total

Year

Total Punds per Year
This page intentionally left blank. 
Appendix C 

Section 110(a)(1) and (2) Infrastructure SIP
This page intentionally left blank. 
IDEM INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT 

Mitchell E. Daniels Jr. 

Governor 

Thomas W. Easterly 

Commissioner 

Susan Hedman 

Regional Administrator 

U.S. EPA, Region 5 

77 West Jackson Boulevard 

Chicago, Illinois 60604 

Dear Ms. Hedman: 

We Protect Hoosiers and Our Environment. 

December 12, 2011 

100 North Senate Avenue 

Indianapolis, Indiana 46204 

(317) 232-8603 

Toll Free (800) 451-6027 

www.idem.IN.gov 

Re: Indiana Infrastructure (Sections 110 (a)(1) 

and (a)(2)) State Implementation Plan Submittal 

I am writing to confirm that the State of Indiana continues to retain the resources 

necessary to evaluate ambient air quality, develop plans to attain new and existing 

ambient air quality standards, run a complete new source review program, and effectively 

enforce all applicable requirements of Section 110 of the Clean Air AcL(CAA). 

Specifically, the Indiana Department of Environmental Management (IDEM) can 

implement and satisfactorily complete the Section 110 requirements listed in the attached 

document. IDEM satisfies these requirements for the current and any future air quality 

standards, including the 2008 Lead National Ambient Air Quality Standard (NAAQS)and 

the 2008 Ozone NAAQS. · 

I believe that IDEM meets or exceeds all of the necessary infrastructure needs, 

enabling us to continue to satisfy these requirements of the Clean Air Act. If you have 

any questions feel free to contact Mr. Scott Deloney, Chief, Air Programs Branch at (317) 

233-5694. . 

KB/rk 

Recycled Paper (i) 

Sincerely, 

ps~r 

Keith Baugues 

Assistant Commissioner 

Office of Air Quality 

An Equal Opportunity Employer Please Recycle O 
Ms. Susan Hedman 

Page2 

cc: Steve Rosenthal 

Scott Deloney 

Christine Pedersen 

SIP file 

Attachments: Indiana Infrastructure SIP Submittal; Section 11 O(a)(1) and (a)(2) 

Elements 
Indiana Infrastructure (Sections 11 0(a)(1) and (a)(2)) State Implementation Plan 

Submittal; 2008 Lead NAAQS and 2008 Ozone NAAQS 

December 2011 
Indiana's Infrastructure State Implementation Plan (SIP) submittal was developed 

in consultation with U.S. EPA Region 5, and in accordance with 40 CFR 51, Appendix 

V, "Criteria for Determining the Completeness of Plan Submissions." The SIP elements 

listed below are required under Section 110(a)(2). Section 110(a)(1) provides the 

procedural and timing requirements for SIPs. Section 11 O(a)(2) lists the basic or 

"infrastructure" elements that all SIPs must contain. Following each Section 110(a)(2) 

element is IDEM's discussion of the department's ability to fulfill the requirement. 

Indiana Infrastructure SIP Submittal; Section 11 0(a)(2) Elements 

Section 110(a)(2)(A)-Emission Limits and Other Control Measures: Section 

11 O(a)(2)(A) requires SIPs to include enforceable emission limits and other control 

measures, means or techniques, as well as schedules and timetables for compliance. 

IDEM continues to update and implement needed revisions to Indiana's SIP, as 

necessary to meet the NAAQS. The authority to adopt emission standards and 

compliance schedules is found at Indiana Code (IC) 13-14-8, IC 13-17-3-4, IC 

13-17-3-11, and IC 13-17-3-14. 

In order to ensure the attainment and maintenance of the 2008 Lead NAAQS, 

IDEM establishes limitations on lead emissions from specific stationary sources 

in Indiana in accordance with the rules at326 lAC 15 and 326 lAC 20-13. 

U.S. EPA has designated a small portion of Delaware County in east central 

Indiana as nonattainment for the 2008 Lead NAAQS (75 FR 71033). Lead 

emissions in this area are generated primarily from a single source. As of 

October 20, 2009, this source had entered into an agreed order with IDEM to 

implement more stringent control measures for fugitive lead emissions. This 

source also agreed to upgrade other prevention and control measures. 

IDEM sets standards for the owners or operators of permitted facilities during 

startup, shutdown, and malfunction events in accordance with the rules at 326 

lAC 1-6, 326 lAC 2-5.1, and 326 lAC 2-6.1. 

Section 110(a)(2)(B)-Ambient Air Quality Monitoring/Data System: Section 

11 O(a)(2)(B) requires SIPs to include provisions to provide for the establishment and 

operation of appropriate devices, methods, systems, and procedures necessary to 

monitor, compile, and analyze data on ambient air quality, and upon request, make 

such data available to U.S. EPA. 

In October 2006, U.S. EPA issued final regulations concerning state and local 

agency ambient air monitoring networks. These regulations require states to 

submit an annual monitoring network review to U.S. EPA. This network plan is 

required to provide the framework for establishment and maintenance of an air 

quality surveillance system and to list any changes that are proposed to take 

place to the current network during the 2011 season. 

1 
In accordance with its SIP, IDEM operates an ambient air monitoring network. 

The data is used to determine compliance with U.S. EPA's NAAQS. Indiana's 

2011 Ambient Air Monitoring Annual Network Plan documents the framework for 

establishment and maintenance of Indiana's air quality surveillance system and 

lists any changes that are proposed to take place to the current network during 

2011. U.S. EPA approved Indiana's 2011 Ambient Air Monitoring Annual 

Network Plan on October 29, 2010. 

Section 11 O(a)(2)(C)-Programs for Enforcement, Prevention of Significant 

Deterioration (PSD), and New Source Review (NSR): Section 110(a)(2)(C) requires 

SIPs to include a program to provide for the enforcement of emission limits and other 

control measures, and regulation of the modification and construction of any stationary 

source within the areas covered by the plan as necessary to assure that the NAAQS are 

achieved, including a permit program. 

IDEM maintains an enforcement program to ensure compliance with SIP 

requirements. IC 13-14-1-12 provides the Commissioner with the authority to 

enforce rules "consistent with the purposes of the air pollution control laws." The 

Commissioner also has the authority, under IC 13-14-2-7 and IC 13-17-3-3, to 

assess civil penalties and obtain compliance with any applicable rule a board has 

adopted in order to enforce air pollution control laws. Additionally, IC 13-14-10-2 

allows for an emergency restraining order that will prevent "any person causing 

or contributing to the alleged pollution to stop the ... introduction of contaminants 

causing or contributing to the pollution." 

IDEM implements its PSD permit program and ensures that the construction and 

modification of major stationary sources do not cause or contribute to a violation 

of the lead NAAQS in accordance with the rules found at 326 lAC 2-2. 

IDEM intends to codify NOx as a precursor for ozone in accordance with U.S. 

EPA's Phase 2 Implementation Rule (73 FR 71612), found at LSA Document 

#11-251. 

IDEM ensures that new or modified sources will apply the Best Available Control 

Technology (BACT) to reduce lead emissions in accordance with the rules found 

at 326 lAC 2-2-3. 

IDEM has adopted U.S. EPA's Greenhouse Gas (GHG) Tailoring Rule at 326 

lAC 2-2. U.S. EPA approved Indiana's GHG PSD rules in the Indiana SIP on 

September 28, 2011 (76 FR 59899). 

Section 110(a)(2)(D)-Interstate Transport Provisions: Section 11 O(a)(2)(D) requires 

SIPs to include provisions prohibiting any source or other type of emissions activity 

within the state from emitting any air pollutant in amounts which will contribute 

significantly to nonattainment in, or interfere with maintenance by, any other state with 

2 
respect to any national primary or secondary ambient air quality standard, or interfere 

with measures required to be included in the applicable implementation plan for any 

other state to prevent significant deterioration of air quality or to protect visibility. 

To satisfy the requirements of Section 110(a)(2)(D)(i)(1), IDEM is in the process 

of promulgating rules that implement the Cross-State Air Pollution Rule. As of 

July 2011, U.S. EPA has promulgated Federal Implementation Plans (FIPs) for 

the state of Indiana that address the requirements of Section 11 O(a)(2)(D) with 

respect to the 1997 Ozone NAAQS, 1997 PM2.5 NAAQS, and 2006 PM2.5 

NAAQS. 

U.S. EPA has designated a small portion of Delaware County in east central 

Indiana as nonattainment for the 2008 Lead NAAQS (75 FR 71 033). This area is 

approximately 30 miles from the Indiana-Ohio state line. Due to its distance from 

the Indiana-Ohio state line and the physical characteristics of lead emissions, it is 

not anticipated that lead emissions from this area will contribute significantly to 

nonattainment or interfere with maintenance in Ohio. No other lead emission 

source in Indiana exceeds the emission threshold set in U.S. EPA's guidance for 

this submittal, and these sources are not anticipated to contribute to 

nonattainment or interfere with maintenance in the bordering states. 

In order to ensure the attainment and maintenance of the 2008 Lead NAAQS, 

IDEM has limitations on lead emissions from specific stationary sources in 

Indiana in its rules at 326 lAC 15 and 326 lAC 20-13. 

Indiana's SIP-approved PSD rules are found at 326 lAC 2-2, and it is IDEM's 

intention that these rules satisfy the requirements of Section 11 O(a)(2)(C), as well 

as the applicable requirements of Section 11 O(a)(2)(D)(i)(2). 

Indiana is subject to the regional haze program which addresses visibilityimpairing pollutants. 

Section 110(a)(2)(E)-Adequate Resources: Section 110(a)(2)(E) requires SIPs to 

provide necessary assurances that the state will have adequate personnel, funding, and 

legal authority under state law to carry out each implementation plan, and to provide 

necessary assurances that the state retains responsibility for ensuring adequate 

implementation of the SIP where the state relies on a local or regional government for 

implementation of any SIP provision. 

IDEM continues to update and implement needed revisions to Indiana's SIP, as 

necessary to meet the NAAQS. The authority to adopt emission standards and 

compliance schedules is found at IC 13-14-8, IC 13-17-3-4, IC 13-17-3-11, and 

IC 13-17-3-14. 

3 
In order to ensure the attainment and maintenance of the 2008 Lead NAAQS, 

IDEM has limitations on lead emissions from specific stationary sources in 

Indiana in its rules at 326 lAC 15 and 326 lAC 20-13. 

IDEM's biennial budget and the Performance Partnership Grant (PPG) 

agreement document funding and personnel plans for IDEM. As of 2009, IDEM 

no longer relies on local or regional governments for implementation of SIP 

provisions. 

IC 13-17-2-4 and IC 13-17-2-5 contain language similar to the requirements of 

Section 128(a)(1) and (2). Members of Indiana's Air Pollution Control Board 

represent varying public interests. These members do not derive a significant 

portion of their respective incomes from persons subject to permits or 

enforcement orders under the CAA. Lastly, members of Indiana's Air Pollution 

Control Board are required to fully disclose any potential conflicts of interest 

relating to permits or enforcement orders under the CAA. 

Section 11 O(a)(2)(F)-Stationary Source Monitoring System: Section 11 O(a)(2)(F) 

provides that SIPs are to require the installation, maintenance, and replacement of 

equipment, and the implementation of other necessary steps by owners or operators of 

stationary sources to monitor emissions from stationary sources. Section 110(a)(2)(F) 

also provides that SIPs are to require periodic reports on the nature and amounts of 

emissions and emissions-related data from the stationary source, and correlation of the 

reports by the state agency with any emission limitations or standards established; the 

reports shall be available at reasonable times for public inspection. 

Indiana's rules for monitoring requirements contained in 326 lAC 3 include rules 

that specify the continuous monitoring of emissions, minimum performance and 

operating specifications, quality assurance requirements, record keeping 

requirements, source sampling procedures, and fuel sampling and analysis 

procedures. Additional emission reporting requirements are found in 326 lAC 2-

6. Emission reports are available upon request by U.S. EPA or other interested 

parties. 

Section 110(a)(2)(G)-Emergency Episodes: Section 110(a)(2)(G) requires SIPs to 

provide authority to address activities causing imminent and substantial endangerment 

to public health, welfare, or the environment, and to provide for adequate contingency 

plans to implement the emergency episode provisions. 

Indiana's rule at 326 lAC 1-5 establishes air pollution episode levels based on 

concentrations of criteria pollutants. The rule requires that emergency reduction 

plans (ERPs) be submitted to the Commissioner by major air pollution sources. 

The ERPs shall state those actions that will be taken when each episode level is 

declared, to reduce or eliminate emissions of the appropriate air pollutants. 

4 
Under IC 13-17-4, Indiana also has the ability to declare an air pollution 

emergency and order all persons causing or contributing to the conditions 

warranting the air pollution emergency to immediately reduce or discontinue the 

emission of air contaminants. 

Section 11 O(a)(2)(H)-Future SIP Revisions: Section 11 O(a)(2)(H) requires SIPs to 

provide for the revision of the plan from time to time as may be necessary to take 

account of revisions of a national primary or secondary ambient air quality standard or 

the availability of improved or more expeditious methods of attaining the standard, and 

whenever U.S. EPA finds on the basis of information that the plan is substantially 

inadequate to attain the NAAQS which it implements. 

IDEM continues to update and implement needed revisions to Indiana's SIP as 

necessary to meet the NAAQS. Authority to adopt emissions standards and 

compliance schedules is found at IC 13-14-8, IC 13-17-3-4, IC 13-17-3-11, and 

IC 13-17-3-14. 

Section 11 O(a)(2)(J)-Consultation with Government Officials, Public Notification, 

PSD, and Visibility Protection: Section 11 O(a)(2)(J) requires SIPs to provide a 

process for consultation with local governments and Federal Land Managers carrying 

out NAAQS implementation requirements, States to notify the public if NAAQS are 

exceeded in an area and to enhance public awareness of measures that can be taken 

to prevent exceedances, and SIPs to meet applicable requirements of Part C of the 

CAA related to PSD and visibility protection. 

IDEM actively participates in the regional planning efforts that include state rule 

developers, representatives from the Federal Land Managers and other affected 

stakeholders. IDEM monitors air quality daily and, when necessary, reports the 

daily air quality index to the interested public and media. IDEM participates and 

submits information to U.S. EPA's AIRNOW program. Additionally, IDEM 

maintains SmogWatch which is an informational tool created by IDEM to share 

air quality forecasts each day. SmogWatch provides daily information about 

ground-level ozone, particulate matter concentration levels, health information, 

and monitoring data for seven regions in Indiana. Indiana's SIP-approved 

regional haze/Best Available Retrofit Technology (BART) rules are found in 326 

lAC 26. Lastly, Indiana's SIP-approved PSD rules are found in 326 lAC 2-2. 

Section 110(a)(2)(K)-Air Quality Modeling/Data: Section 110(a)(2)(K) requires SIPs to 

provide for the performance of air quality modeling that U.S. EPA may prescribe for the 

purpose of predicting the effect on ambient air quality of any emissions of any air 

pollutant for which U.S. EPA has established a NAAQS, and, upon request, the 

submission of data related to the air quality modeling to U.S. EPA. 

IDEM reviews the potential impact of major and some minor new sources. 

Indiana's rules regarding air quality monitoring modeling are contained in 326 

5 
lAC 2-2-4, 326 lAC 2-2-5, 326 lAC 2-2-6, and 3261AC 2-2-7. Modeling data are 

available upon request by U.S. EPA or other interested parties. 

Section 110(a)(2)(L)-Permitting Fees: Sections 110(a)(2)(L) requires SIPs to require 

the owner or operator of each major stationary source to pay to the permitting authority 

a fee sufficient to cover the reasonable costs of reviewing and acting upon any 

application for a permit, and if the owner or operator received a permit for a source, the 

reasonable costs of implementing and enforcing the terms and conditions of any permit, 

until the fee requirement is superseded with respect to the sources by U.S. EPA's 

approval of a fee program under Title V of the Clean Air Act. 

IDEM continues to implement the approved Title V program, including requiring 

major sources to pay permit fees. The authority to establish Title V permit fees 

are found at IC 13-17-8. The fees for Title V are at 326 lAC 2-7-19. All fees that 

may apply to Title V sources are found at 326 lAC 2-1.1-7, which was amended 

in LSA #07-286, adopted on August 3, 2011 and effective December 2011. 

Section 110(a)(2)(M)-Consultation/Participation by Affected Local Entities: Section 

11 O(a)(2)(M) requires SIPs to provide for consultation and participation by local political 

subdivisions affected by the SIP. 

IDEM rulemaking procedures at IC 13-14-9 allow for public participation in the 

SIP development process. IDEM also ensures that the requirements of 40 CFR 

51.102 are satisfied during the SIP development process. 

6 
This page intentionally left blank. 
Appendix D 

Indiana’s Final Promulgated Lead Rule
This page intentionally left blank. 
TITLE 326 AIR POLLUTION CONTROL DIVISION

Final Rule

LSA Document #11-774(F)

DIGEST

Amends 326 IAC 1-4-2 through 326 IAC 1-4-93 concerning the redesignation of all Indiana counties except

for a portion of Delaware County to attainment or unclassifiable for the 2008 lead national ambient air quality

standards (NAAQS). Amends 326 IAC 15-1-2 through 326 IAC 15-1-4 concerning administrative changes.

Amends 326 IAC 20-13 concerning administrative changes. Adds 326 IAC 20-13.1 concerning updates to the

national emission standards for hazardous air pollutants (NESHAP) for secondary lead smelters. Repeals 326

IAC 20-13. Partially effective 30 days after filing with the Publisher, partially effective October 1, 2013, and

partially effective January 6, 2014.

HISTORY

First Notice of Comment Period: December 28, 2011, Indiana Register (DIN: 20111228-IR-326110774FNA).

Second Notice of Comment Period: June 13, 2012, Indiana Register (DIN: 20120613-IR-326110774SNA).

Notice of First Hearing: June 13, 2012, Indiana Register (DIN: 20120613-IR-326110774PHA).

Date of First Hearing: August 1, 2012.

Proposed Rule: August 22, 2012, Indiana Register (DIN: 20120822-IR-326110774PRA).

Notice of Second Hearing: August 22, 2012, Indiana Register (DIN: 20120822-IR-326110774PHA).

Date of Second Hearing: November 7, 2012.

326 IAC 1-4-2; 326 IAC 1-4-3; 326 IAC 1-4-4; 326 IAC 1-4-5; 326 IAC 1-4-6; 326 IAC 1-4-7; 326 IAC 1-4-8; 326

IAC 1-4-9; 326 IAC 1-4-10; 326 IAC 1-4-11; 326 IAC 1-4-12; 326 IAC 1-4-13; 326 IAC 1-4-14; 326 IAC 1-4-15;

326 IAC 1-4-16; 326 IAC 1-4-17; 326 IAC 1-4-18; 326 IAC 1-4-19; 326 IAC 1-4-20; 326 IAC 1-4-21; 326 IAC 1-

4-22; 326 IAC 1-4-23; 326 IAC 1-4-24; 326 IAC 1-4-25; 326 IAC 1-4-26; 326 IAC 1-4-27; 326 IAC 1-4-28; 326

IAC 1-4-29; 326 IAC 1-4-30; 326 IAC 1-4-31; 326 IAC 1-4-32; 326 IAC 1-4-33; 326 IAC 1-4-34; 326 IAC 1-4-35;

326 IAC 1-4-36; 326 IAC 1-4-37; 326 IAC 1-4-38; 326 IAC 1-4-39; 326 IAC 1-4-40; 326 IAC 1-4-41; 326 IAC 1-

4-42; 326 IAC 1-4-43; 326 IAC 1-4-44; 326 IAC 1-4-45; 326 IAC 1-4-46; 326 IAC 1-4-47; 326 IAC 1-4-48; 326

IAC 1-4-49; 326 IAC 1-4-50; 326 IAC 1-4-51; 326 IAC 1-4-52; 326 IAC 1-4-53; 326 IAC 1-4-54; 326 IAC 1-4-55;

326 IAC 1-4-56; 326 IAC 1-4-57; 326 IAC 1-4-58; 326 IAC 1-4-59; 326 IAC 1-4-60; 326 IAC 1-4-61; 326 IAC 1-

4-62; 326 IAC 1-4-63; 326 IAC 1-4-64; 326 IAC 1-4-65; 326 IAC 1-4-66; 326 IAC 1-4-67; 326 IAC 1-4-68; 326

IAC 1-4-69; 326 IAC 1-4-70; 326 IAC 1-4-71; 326 IAC 1-4-72; 326 IAC 1-4-73; 326 IAC 1-4-74; 326 IAC 1-4-75;

326 IAC 1-4-76; 326 IAC 1-4-77; 326 IAC 1-4-78; 326 IAC 1-4-79; 326 IAC 1-4-80; 326 IAC 1-4-81; 326 IAC 1-

4-82; 326 IAC 1-4-83; 326 IAC 1-4-84; 326 IAC 1-4-85; 326 IAC 1-4-86; 326 IAC 1-4-87; 326 IAC 1-4-88; 326

IAC 1-4-89; 326 IAC 1-4-90; 326 IAC 1-4-91; 326 IAC 1-4-92; 326 IAC 1-4-93; 326 IAC 15-1-2; 326 IAC 15-1-3;

326 IAC 15-1-4; 326 IAC 20-13-1; 326 IAC 20-13-2; 326 IAC 20-13-3; 326 IAC 20-13-4; 326 IAC 20-13-5; 326

IAC 20-13-6; 326 IAC 20-13-7; 326 IAC 20-13-8; 326 IAC 20-13-9; 326 IAC 20-13.1

SECTION 1. 326 IAC 1-4-2 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-2 Adams County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 2. The following attainment status designations are applicable to Adams County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 1
1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-2; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 2. 326 IAC 1-4-3 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-3 Allen County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 3. The following attainment status designations are applicable to Allen County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective February 12, 2007, for the Fort Wayne area, including Allen County, for

the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-3; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 3. 326 IAC 1-4-4 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-4 Bartholomew County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 4. The following attainment status designations are applicable to Bartholomew County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-4; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 2
Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 4. 326 IAC 1-4-5 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-5 Benton County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 5. The following attainment status designations are applicable to Benton County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-5; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 5. 326 IAC 1-4-6 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-6 Blackford County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 6. The following attainment status designations are applicable to Blackford County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-6; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 6. 326 IAC 1-4-7 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-7 Boone County

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 3
Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 7. The following attainment status designations are applicable to Boone County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective October 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard, which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-7; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

May 14, 2008, 2:36 p.m.: 20080611-IR-326070840FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 7. 326 IAC 1-4-8 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-8 Brown County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 8. The following attainment status designations are applicable to Brown County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-8; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 8. 326 IAC 1-4-9 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-9 Carroll County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 9. The following attainment status designations are applicable to Carroll County:

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 4
Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-9; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 9. 326 IAC 1-4-10 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-10 Cass County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 10. The following attainment status designations are applicable to Cass County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-10; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 10. 326 IAC 1-4-11 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-11 Clark County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 11. The following attainment status designations are applicable to Clark County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective July 19, 2007, for the 8-hour ozone standard.1

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 5
PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Attainment effective October 23, 2001, for the 1-hour ozone standard for the Louisville area, including Clark

County, and is a maintenance area for the 1-hour ozone National Ambient Air Quality Standard (NAAQS) for

purposes of 40 CFR Part 51, Subpart X*. The 1-hour standard was revoked effective June 15, 2005.

*These documents are incorporated by reference. Copies referenced in this section may be obtained from the

Government Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review

and copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana Government

Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 1-4-11; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 11. 326 IAC 1-4-12 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-12 Clay County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 12. The following attainment status designations are applicable to Clay County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-12; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 12. 326 IAC 1-4-13 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-13 Clinton County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 13. The following attainment status designations are applicable to Clinton County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 6
PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-13; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 13. 326 IAC 1-4-14 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-14 Crawford County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 14. The following attainment status designations are applicable to Crawford County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-14; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 14. 326 IAC 1-4-15 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-15 Daviess County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 15. The following attainment status designations are applicable to Daviess County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 7
(Air Pollution Control Division; 326 IAC 1-4-15; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 15. 326 IAC 1-4-16 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-16 Dearborn County

Authority: IC 13-14-8; IC 13-17

Affected: IC 13-15

Sec. 16. The following attainment status designations are applicable to Dearborn County:

Pollutant Designation

SO2Cannot be classified.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective May 11, 2010, for the 8-hour ozone standard.1

PM2.5 Attainment effective December 23, 2011, for the annual PM2.5 standard for Lawrenceburg

Township.

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-16; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Oct 15, 2010, 1:51 p.m.: 20101110-IR-326100342FRA; filed Jun 12, 2012, 3:22 p.m.:

20120711-IR-326120044FRA; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 16. 326 IAC 1-4-17 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-17 Decatur County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 17. The following attainment status designations are applicable to Decatur County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-17; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 8
SECTION 17. 326 IAC 1-4-18 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-18 Dekalb County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 18. The following attainment status designations are applicable to Dekalb County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-18; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 18. 326 IAC 1-4-19 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-19 Delaware County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 19. The following attainment status designations are applicable to Delaware County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective January 3, 2006, for the Muncie area, including Delaware County, for the

8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Nonattainment effective December 31, 2010, for a portion of the city of

Muncie, Indiana bounded to the north by West Street/Hines Road, to the east by

Cowan Road, to the south by West Fuson Road, and to the west by a line running

south from the eastern edge of Victory Temple's driveway to South Hoyt Avenue and

then along South Hoyt Avenue. Unclassifiable or attainment effective December 31,

2011, for the remainder of the county.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-19; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 9
SECTION 19. 326 IAC 1-4-20 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-20 Dubois County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 20. The following attainment status designations are applicable to Dubois County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM2.5 Attainment effective October 27, 2011, for the annual PM2.5 standard.

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-20; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jun 7, 2012, 11:21 a.m.: 20120704-IR-326110742FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 20. 326 IAC 1-4-21 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-21 Elkhart County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 21. The following attainment status designations are applicable to Elkhart County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective July 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Attainment effective October 18, 2000, for the 1-hour ozone standard for the South Bend-Elkhart area, including

Elkhart County, and is a maintenance area for the 1-hour National Ambient Air Quality Standards (NAAQS) for

purposes of 40 CFR 51, Subpart X*. The 1-hour standard was revoked effective June 15, 2005.

*These documents are incorporated by reference. Copies referenced in this section may be obtained from the

Government Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review

and copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana Government

Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 1-4-21; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 10
Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 21. 326 IAC 1-4-22 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-22 Fayette County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 22. The following attainment status designations are applicable to Fayette County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-22; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 22. 326 IAC 1-4-23 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-23 Floyd County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 23. The following attainment status designations are applicable to Floyd County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective July 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Attainment effective October 23, 2001, for the 1-hour ozone standard for the Louisville area, including Floyd

County, and is a maintenance area for the 1-hour ozone National Ambient Air Quality Standard (NAAQS) for

purposes of 40 CFR Part 51, Subpart X*. The 1-hour standard was revoked effective June 15, 2005.

*These documents are incorporated by reference. Copies referenced in this section may be obtained from the

Government Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review

and copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana Government

Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 1-4-23; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 11
Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 23. 326 IAC 1-4-24 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-24 Fountain County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 24. The following attainment status designations are applicable to Fountain County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-24; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 24. 326 IAC 1-4-25 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-25 Franklin County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 25. The following attainment status designations are applicable to Franklin County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-25; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 25. 326 IAC 1-4-26 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-26 Fulton County

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 12
Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 26. The following attainment status designations are applicable to Fulton County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-26; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 26. 326 IAC 1-4-27 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-27 Gibson County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 27. The following attainment status designations are applicable to Gibson County:

Pollutant Designation

SO2Cannot be classified.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM2.5 Attainment effective October 27, 2011, for the annual PM2.5 standard for Montgomery

Township.

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-27; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jun 7, 2012, 11:21 a.m.: 20120704-IR-326110742FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 27. 326 IAC 1-4-28 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-28 Grant County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 13
Sec. 28. The following attainment status designations are applicable to Grant County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-28; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 28. 326 IAC 1-4-29 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-29 Greene County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 29. The following attainment status designations are applicable to Greene County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective December 29, 2005, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-29; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 29. 326 IAC 1-4-30 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-30 Hamilton County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 30. The following attainment status designations are applicable to Hamilton County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 14
O3

Attainment effective October 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard, which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-30; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

May 14, 2008, 2:36 p.m.: 20080611-IR-326070840FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 30. 326 IAC 1-4-31 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-31 Hancock County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 31. The following attainment status designations are applicable to Hancock County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective October 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard, which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-31; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

May 14, 2008, 2:36 p.m.: 20080611-IR-326070840FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 31. 326 IAC 1-4-32 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-32 Harrison County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 32. The following attainment status designations are applicable to Harrison County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 15
Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-32; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 32. 326 IAC 1-4-33 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-33 Hendricks County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 33. The following attainment status designations are applicable to Hendricks County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective October 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard, which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-33; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

May 14, 2008, 2:36 p.m.: 20080611-IR-326070840FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 33. 326 IAC 1-4-34 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-34 Henry County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 34. The following attainment status designations are applicable to Henry County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-34; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 16
Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 34. 326 IAC 1-4-35 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-35 Howard County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 35. The following attainment status designations are applicable to Howard County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-35; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 35. 326 IAC 1-4-36 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-36 Huntington County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 36. The following attainment status designations are applicable to Huntington County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-36; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 36. 326 IAC 1-4-37 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-37 Jackson County

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 17
Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 37. The following attainment status designations are applicable to Jackson County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective December 29, 2005, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-37; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 37. 326 IAC 1-4-38 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-38 Jasper County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 38. The following attainment status designations are applicable to Jasper County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-38; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 38. 326 IAC 1-4-39 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-39 Jay County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 39. The following attainment status designations are applicable to Jay County:

Pollutant Designation

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 18
SO2

Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-39; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 39. 326 IAC 1-4-40 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-40 Jefferson County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 40. The following attainment status designations are applicable to Jefferson County:

Pollutant Designation

SO2Cannot be classified.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-40; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 40. 326 IAC 1-4-41 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-41 Jennings County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 41. The following attainment status designations are applicable to Jennings County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 19
NO2

Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-41; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 41. 326 IAC 1-4-42 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-42 Johnson County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 42. The following attainment status designations are applicable to Johnson County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective October 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard, which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-42; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

May 14, 2008, 2:36 p.m.: 20080611-IR-326070840FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 42. 326 IAC 1-4-43 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-43 Knox County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 43. The following attainment status designations are applicable to Knox County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment as of June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 20
(Air Pollution Control Division; 326 IAC 1-4-43; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 43. 326 IAC 1-4-44 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-44 Kosciusko County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 44. The following attainment status designations are applicable to Kosciusko County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-44; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 44. 326 IAC 1-4-45 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-45 LaGrange County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 45. The following attainment status designations are applicable to LaGrange County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-45; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 45. 326 IAC 1-4-46 IS AMENDED TO READ AS FOLLOWS:

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 21
326 IAC 1-4-46 Lake County

Authority: IC 13-14-8; IC 13-17

Affected: IC 13-15

Sec. 46. The following attainment status designations are applicable to Lake County:

Pollutant Designation

SO2Better than national standards.

CO Attainment effective February 18, 2000, for the part of the city of East Chicago bounded by

Columbus Drive on the north; the Indiana Harbor Canal on the west; 148th Street, if

extended, on the south; and Euclid Avenue on the east. Unclassifiable or attainment effective

November 15, 1990, for the remainder of East Chicago and Lake County.

O3Attainment effective May 11, 2010, for the 8-hour ozone standard.1

PM2.5 Attainment effective February 6, 2012, for the annual PM2.5 standard.

PM10 Attainment effective March 11, 2003, for the cities of East Chicago, Hammond, Whiting, and

Gary. Unclassifiable effective November 15, 1990, for the remainder of Lake County.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Nonattainment Severe 17 effective November 15, 1990, for the Chicago-Gary-Lake County area for the 1-hour

ozone standard which was revoked effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-46; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Oct 15, 2010, 1:51 p.m.: 20101110-IR-326100342FRA; filed Jun 7, 2012, 11:21 a.m.:

20120704-IR-326110742FRA; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 46. 326 IAC 1-4-47 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-47 LaPorte County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 47. The following attainment status designations are applicable to LaPorte County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective July 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective November 15, 1990, for the 1-hour standard which was revoked effective

June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-47; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 47. 326 IAC 1-4-48 IS AMENDED TO READ AS FOLLOWS:

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 22
326 IAC 1-4-48 Lawrence County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 48. The following attainment status designations are applicable to Lawrence County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-48; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 48. 326 IAC 1-4-49 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-49 Madison County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 49. The following attainment status designations are applicable to Madison County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective October 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard, which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-49; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

May 14, 2008, 2:36 p.m.: 20080611-IR-326070840FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 49. 326 IAC 1-4-50 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-50 Marion County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 23
Sec. 50. The following attainment status designations are applicable to Marion County:

Pollutant Designation

SO2Better than national standards.

CO Attainment effective February 18, 2000, for the part of the city of Indianapolis bounded by

11th Street on the north; Capitol Avenue on the west; Georgia Street on the south; and

Delaware Street on the east. Unclassifiable or attainment effective November 15, 1990, for

the remainder of Indianapolis and Marion County.

O3Attainment effective October 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Attainment effective July 10, 2000, for the part of Franklin Township bounded by Thompson

Road on the south; Emerson Avenue on the west; Five Points Road on the east; and Troy

Avenue on the north. Attainment effective July 10, 2000, for the part of Wayne Township

bounded by Rockville Road on the north; Girls School Road on the east; Washington Street

on the south; and Bridgeport Road on the west. The remainder of the county is not

designated. Unclassifiable or attainment effective December 31, 2011.

1Attainment effective October 18, 2000, for the 1-hour ozone standard for the Indianapolis area, including Marion

County, and is a maintenance area for the 1-hour ozone National Ambient Air Quality Standards (NAAQS) for

purposes of 40 CFR 51, Subpart X*. The 1-hour designation was revoked effective June 15, 2005.

*These documents are incorporated by reference. Copies referenced in this section may be obtained from the

Government Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review

and copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana Government

Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 1-4-50; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

May 14, 2008, 2:36 p.m.: 20080611-IR-326070840FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 50. 326 IAC 1-4-51 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-51 Marshall County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 51. The following attainment status designations are applicable to Marshall County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-51; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 24
Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 51. 326 IAC 1-4-52 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-52 Martin County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 52. The following attainment status designations are applicable to Martin County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-52; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 52. 326 IAC 1-4-53 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-53 Miami County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 53. The following attainment status designations are applicable to Miami County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-53; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 53. 326 IAC 1-4-54 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-54 Monroe County

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 25
Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 54. The following attainment status designations are applicable to Monroe County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-54; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 54. 326 IAC 1-4-55 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-55 Montgomery County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 55. The following attainment status designations are applicable to Montgomery County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-55; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 55. 326 IAC 1-4-56 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-56 Morgan County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 56. The following attainment status designations are applicable to Morgan County:

Pollutant Designation

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 26
SO2

Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective October 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard, which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-56; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

May 14, 2008, 2:36 p.m.: 20080611-IR-326070840FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 56. 326 IAC 1-4-57 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-57 Newton County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 57. The following attainment status designations are applicable to Newton County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-57; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 57. 326 IAC 1-4-58 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-58 Noble County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 58. The following attainment status designations are applicable to Noble County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 27
NO2

Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-58; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 58. 326 IAC 1-4-59 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-59 Ohio County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 59. The following attainment status designations are applicable to Ohio County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-59; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 59. 326 IAC 1-4-60 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-60 Orange County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 60. The following attainment status designations are applicable to Orange County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 28
(Air Pollution Control Division; 326 IAC 1-4-60; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 60. 326 IAC 1-4-61 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-61 Owen County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 61. The following attainment status designations are applicable to Owen County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment is effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-61; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 61. 326 IAC 1-4-62 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-62 Parke County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 62. The following attainment status designations are applicable to Parke County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-62; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 62. 326 IAC 1-4-63 IS AMENDED TO READ AS FOLLOWS:

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 29
326 IAC 1-4-63 Perry County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 63. The following attainment status designations are applicable to Perry County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-63; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 63. 326 IAC 1-4-64 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-64 Pike County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 64. The following attainment status designations are applicable to Pike County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM2.5 Attainment effective October 27, 2011, for the annual PM2.5 standard for Washington

Township.

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-64; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jun 7, 2012, 11:21 a.m.: 20120704-IR-326110742FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 64. 326 IAC 1-4-65 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-65 Porter County

Authority: IC 13-14-8; IC 13-17

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 30
Affected: IC 13-15

Sec. 65. The following attainment status designations are applicable to Porter County:

Pollutant Designation

SO2Cannot be classified for the area bounded on the north by Lake Michigan; on the west by the

Lake County and Porter County line; on the south by I-80 and I-90; and on the east by the

LaPorte County and Porter County line. The remainder of Porter County is better than

national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective May 11, 2010, for the 8-hour ozone standard.1

PM2.5 Attainment effective February 6, 2012, for the annual PM2.5 standard.

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Nonattainment Severe 17 effective November 15, 1990, for the Chicago-Gary-Lake County area, including Porter

County, for the 1-hour ozone standard which was revoked effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-65; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Oct 15, 2010, 1:51 p.m.: 20101110-IR-326100342FRA; filed Jun 7, 2012, 11:21 a.m.:

20120704-IR-326110742FRA; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 65. 326 IAC 1-4-66 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-66 Posey County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 66. The following attainment status designations are applicable to Posey County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-66; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 66. 326 IAC 1-4-67 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-67 Pulaski County

Authority: IC 13-14-8; IC 13-17-3

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 31
Affected: IC 13-15; IC 13-17

Sec. 67. The following attainment status designations are applicable to Pulaski County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-67; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 67. 326 IAC 1-4-68 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-68 Putnam County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 68. The following attainment status designations are applicable to Putnam County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-68; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 68. 326 IAC 1-4-69 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-69 Randolph County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 69. The following attainment status designations are applicable to Randolph County:

Pollutant Designation

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 32
SO2

Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-69; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 69. 326 IAC 1-4-70 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-70 Ripley County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 70. The following attainment status designations are applicable to Ripley County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-70; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 70. 326 IAC 1-4-71 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-71 Rush County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 71. The following attainment status designations are applicable to Rush County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 33
NO2

Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-71; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 71. 326 IAC 1-4-72 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-72 Scott County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 72. The following attainment status designations are applicable to Scott County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-72; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 72. 326 IAC 1-4-73 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-73 Shelby County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 73. The following attainment status designations are applicable to Shelby County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective October 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard, which was revoked

effective June 15, 2005.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 34
(Air Pollution Control Division; 326 IAC 1-4-73; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

May 14, 2008, 2:36 p.m.: 20080611-IR-326070840FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 73. 326 IAC 1-4-74 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-74 Spencer County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 74. The following attainment status designations are applicable to Spencer County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM2.5 Attainment effective October 27, 2011, for the annual PM2.5 standard for Ohio Township.

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-74; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jun 7, 2012, 11:21 a.m.: 20120704-IR-326110742FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 74. 326 IAC 1-4-75 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-75 Starke County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 75. The following attainment status designations are applicable to Starke County:

Pollutant Designations

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-75; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 35
SECTION 75. 326 IAC 1-4-76 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-76 Steuben County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 76. The following attainment status designations are applicable to Steuben County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-76; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 76. 326 IAC 1-4-77 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-77 St. Joseph County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 77. The following attainment status designations are applicable to St. Joseph County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective July 19, 2007, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Attainment effective October 18, 2000, for the 1-hour ozone standard for the South Bend-Elkhart area, including

St. Joseph County, and is a maintenance area for the 1-hour ozone National Ambient Air Quality Standards

(NAAQS) for purposes of 40 CFR 51, Subpart X*. The 1-hour standard was revoked effective June 15, 2005.

*These documents are incorporated by reference. Copies referenced in this section may be obtained from the

Government Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review

and copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana Government

Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 1-4-77; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 36
SECTION 77. 326 IAC 1-4-78 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-78 Sullivan County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 78. The following attainment status designations are applicable to Sullivan County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-78; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 78. 326 IAC 1-4-79 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-79 Switzerland County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 79. The following attainment status designations are applicable to Switzerland County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-79; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 79. 326 IAC 1-4-80 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-80 Tippecanoe County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 37
Sec. 80. The following attainment status designations are applicable to Tippecanoe County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-80; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 80. 326 IAC 1-4-81 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-81 Tipton County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 81. The following attainment status designations are applicable to Tipton County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-81; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 81. 326 IAC 1-4-82 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-82 Union County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 82. The following attainment status designations are applicable to Union County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 38
O3

Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-82; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 82. 326 IAC 1-4-83 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-83 Vanderburgh County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 83. The following attainment status designations are applicable to Vanderburgh County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective January 30, 2006, for the Evansville area, including Vanderburgh

County, for the 8-hour ozone standard.1

PM2.5 Attainment effective October 27, 2011, for the annual PM2.5 standard.

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Attainment effective October 18, 2000, for the 1-hour ozone standard for the Evansville area, including

Vanderburgh County, and is a maintenance area for the 1-hour ozone National Ambient Air Quality Standards

(NAAQS) for purposes of 40 CFR 51, Subpart X*. The 1-hour designation was revoked effective June 15, 2005.

*These documents are incorporated by reference. Copies referenced in this section may be obtained from the

Government Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review

and copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana Government

Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 1-4-83; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jun 7, 2012, 11:21 a.m.: 20120704-IR-326110742FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 83. 326 IAC 1-4-84 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-84 Vermillion County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 84. The following attainment designated as status designations are applicable to Vermillion County:

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 39
Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Attainment effective October 27, 1997, for the part of Clinton Township that includes sections

15, 16, 21, 22, 27, 28, 33, and 34. Unclassifiable effective November 15, 1990, for the

remainder of Vermillion County.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-84; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 84. 326 IAC 1-4-85 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-85 Vigo County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 85. The following attainment status designations are applicable to Vigo County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective February 6, 2006, for the Terre Haute area, including Vigo County, for

the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-85; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 85. 326 IAC 1-4-86 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-86 Wabash County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 86. The following attainment status designations are applicable to Wabash County:

Pollutant Designation

SO2Better than national standards.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 40
CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-86; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 86. 326 IAC 1-4-87 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-87 Warren County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 87. The following attainment status designations are applicable to Warren County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-87; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 87. 326 IAC 1-4-88 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-88 Warrick County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 88. The following attainment status designations are applicable to Warrick County:

Pollutant Designation

SO2Cannot be classified.

CO Unclassifiable or attainment effective November 15, 1990.

O3Attainment effective January 30, 2006, for the Evansville area, including Warrick County, for

the 8-hour ozone standard.1

PM2.5 Attainment effective October 27, 2011, for the annual PM2.5 standard.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 41
PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-88; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jun 7, 2012, 11:21 a.m.: 20120704-IR-326110742FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 88. 326 IAC 1-4-89 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-89 Washington County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 89. The following attainment status designations are applicable to Washington County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-89; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 89. 326 IAC 1-4-90 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-90 Wayne County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 90. The following attainment status designations are applicable to Wayne County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 42
effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-90; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 90. 326 IAC 1-4-91 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-91 Wells County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 91. The following attainment status designations are applicable to Wells County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-91; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 91. 326 IAC 1-4-92 IS AMENDED TO READ AS FOLLOWS:

326 IAC 1-4-92 White County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 92. The following attainment status designations are applicable to White County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-92; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 92. 326 IAC 1-4-93 IS AMENDED TO READ AS FOLLOWS:

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 43
326 IAC 1-4-93 Whitley County

Authority: IC 13-14-8; IC 13-17-3

Affected: IC 13-15; IC 13-17

Sec. 93. The following attainment status designations are applicable to Whitley County:

Pollutant Designation

SO2Better than national standards.

CO Unclassifiable or attainment effective November 15, 1990.

O3Unclassifiable or attainment effective June 15, 2004, for the 8-hour ozone standard.1

PM10 Unclassifiable effective November 15, 1990.

NO2Cannot be classified or better than national standards.

Pb Not designated. Unclassifiable or attainment effective December 31, 2011.

1Unclassifiable or attainment effective October 18, 2000, for the 1-hour ozone standard which was revoked

effective June 15, 2005.

(Air Pollution Control Division; 326 IAC 1-4-93; filed Dec 26, 2007, 1:43 p.m.: 20080123-IR-326070308FRA; filed

Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 93. 326 IAC 15-1-2 IS AMENDED TO READ AS FOLLOWS:

326 IAC 15-1-2 Source-specific provisions

Authority: IC 13-14-8; IC 13-17-3-4

Affected: IC 13-17

Sec. 2. (a) The sources listed below in this subsection shall comply with the following emission and

operating provisions:

Emission Limitation

Source Facility Description lbs./hr.

(1) Refined Metals of Indianapolis M-1 baghouse stack10.91

M-2 baghouse stack10.15

M-3 baghouse stack10.15

M-4 baghouse stack10.30

1Compliance shall be achieved on or before April 30, 1992.

(A) On or before June 1, 1987, Refined Metals of Indianapolis shall install and operate hooding systems for

the blast furnace skip hoist and charging area, the blast furnace slag and lead tapping area, the casting

area, the refining kettles, and the lead dust furnace charging area.

(B) The hooding systems required for the operations listed in clause (A) shall vent the emissions through a

control device to one (1) of the four (4) stacks, M-1 through M-4.

(C) On or before June 1, 1987, Refined Metals of Indianapolis shall also install and operate enclosed screw

conveyors to transport lead flue dusts to the lead dust furnace. There shall be no visible emissions from the

screw conveyors. Compliance shall be determined by 40 CFR 60, Appendix A, Method 22**.

(D) The buildings housing the blast furnace, dust furnace, and materials storage shall be kept under

continuous negative pressure by constant flow rate fans ducted to control devices.

(E) The company shall install and operate a continuous monitoring system to measure and record pressure

differential to ensure that the materials storage building and the blast/dust furnace area are maintained

under negative pressure while the plant is in operation. The monitoring system shall be located on the north

wall of the materials storage building. It shall consist of a differential pressure sensor/transmitter, a

processor, and a recording device. This system shall produce valid data ninety-five percent (95%) of the

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 44
time when the plant is operating. Data generated by this monitoring system shall be kept available for

inspection at the site for a period of two (2) years.

(F) The blast furnace and the dust furnace fugitive emissions shall be drawn from the enclosure by a

constant flow rate fan to a control device. The control device shall vent to the atmosphere through the M-4

baghouse stack which shall be at least eighty (80) feet in height from ground level.

(G) Visible emissions from the M-1, M-2, M-3, and M-4 baghouse stacks shall not exceed a six (6) minute

average of five percent (5%) opacity for each stack as determined in accordance with 40 CFR 60, Appendix

A, Method 9**.

(H) Visible emissions from building openings such as doors and windows shall not exceed a three (3)

minute average of three percent (3%) opacity. Compliance with this limitation shall be determined by 40

CFR 60, Appendix A, Method 9**, except that the opacity standard shall be determined as an average of

twelve (12) consecutive observations recorded at fifteen (15) second intervals.

(I) Refined Metals of Indianapolis shall install and operate continuous opacity monitoring systems in the M-1

and the M-4 baghouse stacks or in the ductwork leading to those stacks. COMS data shall be used to

determine compliance with the five percent (5%) opacity limit required by clause (G). The COMS shall meet

the performance and installation requirements of 40 CFR 60, Appendix B, Performance Specification 1**.

The company shall also comply with the following:

(i) A complete written standard operating procedure (SOP) for COMS shall be submitted to the department

for approval. The department shall complete the review of the COMS SOP within sixty (60) days of

submittal. The COMS SOP shall contain, at minimum, complete step-by-step procedures for the following:

(AA) Calibration procedures.

(BB) Operation procedures.

(CC) Preventive maintenance procedures.

(DD) Quality control and quality assurance (QA) procedures.

(EE) Record keeping and reporting procedures.

(ii) The company shall perform quarterly COMS performance audits and notify the department fourteen

(14) days in advance of each audit. The company shall submit quarterly COMS QA reports to the

department within thirty (30) days following the end of the quarter. Each report shall summarize

performance audit results and provide an explanation for periods of time during the quarter when valid data

was not collected.

(iii) COMS excess emission reports shall be submitted to the department within thirty (30) days following

the end of each calendar quarter. These reports shall contain, at minimum, the following:

(AA) The operating time of the monitored facilities.

(BB) The date and time each COMS recorded opacity measurements above the five percent (5%) opacity

limit.

(CC) The date and time each COMS was inoperative or malfunctioning.

(DD) A description of the nature and cause of any excess emissions.

(J) Refined Metals of Indianapolis shall achieve compliance with clauses (D) through (I) by March 1, 1994.

In the event that the plant is idle on March 1, 1994, compliance with clauses (D) through (I) shall be

achieved by the date the plant resumes production. Refined Metals shall notify the department thirty (30)

days before production resumes to enable the department to make a compliance determination.

(K) Refined Metals of Indianapolis shall perform a stack test on the M-1, M-2, M-3, and M-4 baghouse

stacks and demonstrate compliance with this subdivision by June 30, 1992. All subsequent stack tests shall

be conducted utilizing the methodologies of 40 CFR 60, Appendix A, Methods 1, 2, 3, 4, 5, and 12**.

(L) Any violation of the National Ambient Air Quality Standards (NAAQS) shall result in an investigation by

Refined Metals to determine the cause of the violation. Such an investigation shall be completed within

ninety (90) days after the date the violation is confirmed. Refined Metals shall provide a corrective action

plan to the department for approval within ninety (90) days of the confirmation of the violation. The plan shall

specify the actions required to continuously meet the NAAQS. Refined Metals shall implement the plan upon

approval by the department. The department may require a cessation in production, if needed, to assure

continuous attainment of the NAAQS.

(2) Chrysler Corporation Foundry, Cupola stack 0.550

Indianapolis Cupola fugitive 1.894

(3) Delco Remy Division of General Lead oxide mfg. stack (each of 5) 0.068

Motors Corporation, Muncie Oxide grinder stack (each of 2) 0.123

*Central tunnel system stack (each of 4) 0.254

Reverberatory furnace stack 0.225

O.S.I. drying oven stack (each of 4) 0.0015

Electric melting pot stack 0.159

*On or before June 1, 1987, Delco Remy shall install ductwork to vent emissions from the vacuum cleaning lines

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 45
through the control devices and stacks serving the Central Tunnel System.

Source Emission Unit

Emission Limitation

lbs/hr

(4) (1) Indiana Oxide Corporation, Brazil Barton #1 reactor 0.215

Barton #2 reactor 0.215

Barton #3 reactor 0.215

Barton #4 reactor 0.215

Rake furnace 0.006

Kiln #2 0.002

*Franklin reactor 0.603

*Shall not operate more than 670 hours per quarter.

(5) U.S.S. Lead Refinery, East Chicago *Blast furnace stack 0.002

*Blast furnace fugitive

Charging 2.922

Lead tapping 0.002

Slag tapping 0.005

*Refining kettles fugitive 0.0001

*Casting fugitive 0.393

*Reverberatory furnace fugitive 0.345

*Shall not operate more than 334 hours per quarter.

(6) (2) Hammond Lead Products, Inc., Stack 4A-S-8 0.053

HLP-Lead Plant Stack 14-S-16 0.053

Stack 1-S-2 0.053

Stack 1-S-26 0.053

Stack 16-S-56 0.200

Stack 1-S-52 0.070

Stack 1-S-27 0.020

Stack 4-S-35 0.090

Stack 6-S-33 0.070

Stack 4B-S-34 0.080

Stack 6-S-47 0.021

Stack V-1 0.090

Stack V-11 0.006

(A) The ventilator control system (Stack V-1) shall consist of a fan with a constant flow rate that draws air

from the building through a HEPA filter which vents to the atmosphere through a stack. The HEPA filters

shall be maintained and operated in order to achieve maximum control efficiency. In addition to the

requirements contained in subsection (c), Hammond Lead Products, Inc. shall submit an operation and

maintenance plan by July 31, 1990, which incorporates good housekeeping practices for the ventilator

control systems. This operation and maintenance plan shall be incorporated into the operating permits for

Hammond Lead Products, Inc. and submitted to U.S. EPA as a revision to Indiana's lead state

implementation plan by December 31, 1990. The ventilator control systems shall be designed such so that

process fugitive emissions will not routinely escape the buildings except as vented through the ventilator

control systems. The compliance test method specified in section 4(a) of this rule shall be used to determine

compliance with the emission limitations for the ventilator control system stacks.

(B) By December 31, 1989, the stack heights for all processes except Stack 16-S-56, Stack 1-S-52, and the

ventilator control systems shall be no less than sixty (60) feet above grade; the stack heights for Stack

16-S-56 and Stack 1-S-52 shall be no less than eighty-two (82) feet above grade. and the stack height for

Vent 11 shall be no less than thirty-five (35) feet above grade. By July 31, 1990, the stack heights for the

other ventilator control systems shall be no less than sixty (60) feet above grade.

(C) Hammond Lead Products, Inc. shall install HEPA filters according to the following schedule:

Stack 4A-S-8 March 31, 1992

Stack 14-S-16 June 30, 1992

Stack 1-S-2 December 31, 1991

Stack 1-S-26 September 30, 1992

*Stack 16-S-56:

130 bag filter November 20, 1989

100 bag filter December 6, 1989

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 46
80 bag filter June 1, 1989

72 bag filter December 31, 1991

Stack 1-S-52 December 31, 1989

Stack 1-S-27 August 15, 1987

Stack 4-S-35 October 16, 1989

Stack 6-S-33 July 22, 1988

Stack 4B-S-34 October 5, 1989

Stack 6-S-47 May 26, 1988

*Four (4) bag filters are vented through common Stack 16-S-56.

(D) Hammond Lead Products, Inc. shall provide written notification to the commissioner within three (3) days

after the installation of HEPA filters is completed at each of the sites listed in clause (A).

(E) All emissions emission limitations in this subdivision shall be met by December 31, 1992.

(F) This subdivision shall be submitted to the U.S. EPA as a revision to the Indiana state implementation

plan.

Source Emission Unit

Emission Limitation

lbs/hr

(7) (3) Hammond Group-Halstab Division Stack S-1 0.04

Stack S-2 0.03

Stacks S-4, S-5 (each) 0.07

Stacks S-6, S-7, S-8 (each) 0.05

Stacks S-9, S-10, S-11 (each) 0.04

S-12, S-13 (each) 0.04

S-14, S-15, S-16 (each) 0.04

Stacks S-17, S-21 (each) 0.07

(A) Hammond Group-Halstab Division shall install and maintain one (1) baghouse with laminated filters

followed by one (1) HEPA filter in series with the baghouse on each of stacks S-1, S-2, S-4 through S-17,

and S-21.

(B) Hammond Group-Halstab Division shall submit a proposed ambient monitoring and quality assurance

plan within thirty (30) days of the effective date of this rule. March 10, 1988.

(C) Hammond Group-Halstab Division shall commence ambient monitoring within thirty (30) days of the

department's approval of the proposed ambient monitoring and quality assurance plan.

(D) Hammond Group-Halstab Division shall conduct a minimum of twenty-four (24) months of monitoring for

lead. The monitoring shall be:

(i) performed using U.S. EPA-approved methods, procedures, and quality assurance programs; and

(ii) in accordance with the ambient monitoring and quality assurance plan as approved by the department.

(E) The requirement to monitor shall expire twenty-four (24) months from the commencement date of the

monitoring provided the monitored values, averaged over a calendar quarter, do not exceed eighty percent

(80%) of the National Ambient Air Quality Standards (NAAQS) level for lead in any quarter during

twenty-four (24) months.

(F) If the monitored values averaged over a calendar quarter exceed eighty percent (80%) of the NAAQS

level for lead during the twenty-four (24) month period, monitoring shall be continued until eight (8)

continuous quarters of monitored values do not exceed eighty percent (80%) of the NAAQS level for lead.

(G) If the monitored values, averaged over a calendar quarter, exceed eighty percent (80%) of the NAAQS

level for lead for two (2) or more continuous quarters, the department and Hammond Group-Halstab

Division shall analyze and assess causes of the emissions and determine whether changes to control

requirements or operating practices are appropriate.

(b) In addition to the sources listed in subsection (a), the following sources C & D Batteries, Attica, shall

comply with subsection (c) and section 3 of this rule.

(1) Exide Corporation, Logansport.

(2) C & D Batteries, Attica.

(3) Exide Corporation, Frankfort.

(c) Operation and maintenance programs shall be designed to prevent deterioration of control equipment

performance. For sources listed in subsection (a)(1) through (a)(7), (a)(3), these programs shall be submitted to

the department of environmental management, office of air management, on or before June 1, 1987. For sources

the source listed in subsection (b), these programs shall be submitted to the office of air management

department on or before February 1, 1988. These programs will be incorporated into the individual source

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 47
operation permits.

**These documents are incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center-North,

Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 15-1-2; filed Mar 10, 1988, 1:20 p.m.: 11 IR 2564; errata filed Jul 6, 1988,

1:00 p.m.: 11 IR 3921; filed Jun 14, 1989, 5:00 p.m.: 12 IR 1850; filed Aug 8, 1991, 10:00 a.m.: 14 IR 2203; filed

Dec 17, 1992, 5:00 p.m.: 16 IR 1379; errata filed Mar 10, 1993, 5:00 p.m.: 16 IR 1832; filed Mar 28, 1994, 5:00

p.m.: 17 IR 1878; errata, 17 IR 2080; filed May 31, 1994, 5:00 p.m.: 17 IR 2233; errata filed Jun 10, 1994, 5:00

p.m.: 17 IR 2356; filed Jan 6, 1999, 4:23 p.m.: 22 IR 1427; filed Dec 1, 2000, 2:22 p.m.: 24 IR 954; readopted filed

Jan 10, 2001, 3:20 p.m.: 24 IR 1477; errata filed Dec 12, 2002, 3:30 p.m.: 26 IR 1565; filed Aug 26, 2004, 11:30

a.m.: 28 IR 95; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 94. 326 IAC 15-1-3 IS AMENDED TO READ AS FOLLOWS:

326 IAC 15-1-3 Control of fugitive lead dust

Authority: IC 13-14-8; IC 13-17-3-4

Affected: IC 13-11; IC 13-17

Sec. 3. All sources listed in section 2 of this rule shall comply with the following requirements:

(1) No source shall create or maintain outdoor storage of bulk materials containing more than one percent

(1.0%) lead by weight of less than two hundred (200) mesh size particles.

(2) All materials containing more than one percent (1.0%) lead by weight of less than two hundred (200) mesh

size particles shall be transported in closed containers or shall be transported by enclosed conveying systems

that are vented to the atmosphere through particulate matter control equipment or shall be transported wet.

(3) Control programs shall be designed to minimize emissions of lead from all nonprocess fugitive emission

points. The programs shall include good housekeeping practices for the cleanup of spills and for minimizing

emissions from loading and unloading areas as applicable. For sources listed in section 2(a) of this rule, these

programs shall be submitted to the department of environmental management, office of air management, on or

before June 1, 1987. For sources the source listed in section 2(b) of this rule, these programs shall be

submitted to the department of environmental management, office of air management, on or before February

1, 1988. These programs will be incorporated into the individual source operation permits.

(Air Pollution Control Division; 326 IAC 15-1-3; filed Mar 10, 1988, 1:20 p.m.: 11 IR 2566; errata filed Jul 6, 1988,

1:00 p.m.: 11 IR 3921; filed Jun 14, 1989, 5:00 p.m.: 12 IR 1853; filed Dec 1, 2000, 2:22 p.m.: 24 IR 958;

readopted filed Jan 10, 2001, 3:20 p.m.: 24 IR 1477; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 95. 326 IAC 15-1-4 IS AMENDED TO READ AS FOLLOWS:

326 IAC 15-1-4 Compliance

Authority: IC 13-14-8; IC 13-17-3-4

Affected: IC 13-17

Sec. 4. (a) Determination of compliance with the lead emission limitations established pursuant to section 2 of

this rule shall be made in accordance with the procedures outlined in 40 CFR 60, Appendix A, Method 12,* and

326 IAC 3-2, 326 IAC 3-6, Source Sampling Procedures.

(b) Those sources having restricted operating hours specified in section 2 of this rule shall be as follows:

(1) Maintain logs indicating hours of operation each day.

(2) Submit quarterly summaries of operating logs to the department of environmental management, office of

air management, before the end of the month following the completed quarter.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 48
*This document is incorporated by reference. Copies may be obtained from the Government Printing Office,

732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the Indiana

Department of Environmental Management, Office of Air Quality, Indiana Government Center North, Tenth Floor,

100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 15-1-4; filed Mar 10, 1988, 1:20 p.m.: 11 IR 2567; filed Jun 14, 1989, 5:00

p.m.: 12 IR 1854; readopted filed Jan 10, 2001, 3:20 p.m.: 24 IR 1477; errata filed Dec 12, 2002, 3:35 p.m.: 26 IR

1571; filed Aug 26, 2004, 11:30 a.m.: 28 IR 98; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 96. 326 IAC 20-13-1 IS AMENDED TO READ AS FOLLOWS:

326 IAC 20-13-1 Applicability; incorporation by reference of federal standards

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 1. (a) This rule applies to the following affected sources emission units constructed or reconstructed

before or on May 19, 2011, as defined in 40 CFR 63.542* 326 IAC 20-13.1-2, at all secondary lead smelters:

(1) Blast, reverberatory, rotary, and electric smelting furnaces.

(2) Refining kettles.

(3) Agglomerating furnaces.

(4) Dryers.

(5) Process fugitive emissions sources.

(6) Fugitive dust sources.

(7) Buildings containing lead bearing materials.

(b) This rule does not apply to:

(1) primary lead smelters;

(2) lead refiners; or

(3) lead remelters; or

(4) new emission units as defined in 326 IAC 20-13.1-2.

(c) The owner or operator of a secondary lead smelter shall comply with this rule upon the effective

date of this rule as amended in 2012. Compliance with this rule shall be maintained until the applicable

compliance dates in 326 IAC 20-13.1-1 and accordingly, through the dates in the following schedule:

(1) Except for Exide Technologies, Inc., Muncie, affected emission units

constructed or reconstructed on or before May 19, 2011:

January 5, 2014

(2) For Exide Technologies, Inc., Muncie, affected emission units constructed

or reconstructed on or before May 19, 2011:

September 30, 2013

(c) (d) The air pollution control board incorporates by reference the July 1, 2011, edition of 40 CFR 63,

Subpart X*, National Emission Standards for Hazardous Air Pollutants from Secondary Lead Smelting, with the

exception of the following sections:

(1) 40 CFR 63.543(a) and 40 CFR 63.543(j) concerning lead standards for process sources.

(2) 40 CFR 63.544(c), 40 CFR 63.544(d), and 40 CFR 63.544(h) concerning lead standards for process

fugitive emissions sources.

(3) 40 CFR 63.545(e) concerning lead standards for fugitive dust emissions.

(4) 40 CFR 63.543(h) and 40 CFR 63.543(i) concerning compliance demonstrations for process sources.

(5) 40 CFR 63.544(e) and 40 CFR 63.544(f) concerning compliance demonstrations for process fugitive

emissions sources.

(6) 40 CFR 63.548(e) concerning bag leak detection system requirements.

(7) 40 CFR 63.541(b) concerning the applicability of 40 CFR 63, Subpart A.

(e) The following general provisions as provided in the July 1, 2012, of 40 CFR 63, Subpart A* apply to

the owner or operator of a secondary lead smelter subject to this rule:

(1) 40 CFR 63.1 through 40 CFR 63.5*.

(2) 40 CFR 63.6(a) through 40 CFR 63.6(c)*.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 49
(3) 40 CFR 63.6(e)(1)(iii)*.

(4) 40 CFR 63.6(g)*.

(5) 40 CFR 63.6(i)* and 40 CFR 63.6(j)*.

(6) 40 CFR 63.7(a) through 40 CFR 63.7(d)*.

(7) 40 CFR 63.7(e)(2) through 40 CFR 63.7(e)(4)*.

(8) 40 CFR 63.7(f) through 40 CFR 63.7(h)*.

(9) 40 CFR 63.8(a)* and 40 CFR 63.8(b)*.

(10) 40 CFR 63.8(c)(1)(ii)*.

(11) 40 CFR 63.8(c)(2) through 40 CFR 63.8(c)(8)*.

(12) 40 CFR 63.8(d)(1) and 40 CFR 63.8(d)(2)*.

(13) 40 CFR 63.8(d)(3)*, except for a provision concerning the incorporation of the written procedures

of a quality control program into startup, shutdown, or malfunction plans.

(14) 40 CFR 63.8(e) through 40 CFR 63.8(g)*.

(15) 40 CFR 63.9(a) through 40 CFR 63.9(c)*.

(16) 40 CFR 63.9(e)*.

(17) 40 CFR 63.9(g)*.

(18) 40 CFR 63.9(h)(1) through 40 CFR 63.9(h)(3)*.

(19) 40 CFR 63.9(h)(5)* and 40 CFR 63.9(h)(6)*.

(20) 40 CFR 63.9(i)* and 40 CFR 63.9(j)*.

(21) 40 CFR 63.10(a)*.

(22) 40 CFR 63.10(b)(1)*.

(23) 40 CFR 63.10(b)(2)(iii)*.

(24) 40 CFR 63.10(b)(2)(vi) through 40 CFR 63.10(b)(2)(xiv)*.

(25) 40 CFR 63.10(b)(3)*.

(26) 40 CFR 63.10(c)(1) through 40 CFR 63.10(c)(9)*.

(27) 40 CFR 63.10(c)(12) through 40 CFR 63.10(c)(14)*.

(28) 40 CFR 63.10(d)(1) through 40 CFR 63.10(d)(4)*.

(29) 40 CFR 63.10(e)* and 40 CFR 63.10(f)*.

(30) 40 CFR 63.12 through 40 CFR 63.15*.

*These documents are incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center North,

Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13-1; filed Dec 1, 2000, 2:22 p.m.: 24 IR 958; filed May 21, 2002, 10:20

a.m.: 25 IR 3093; errata filed Feb 9, 2006, 10:20 a.m.: 29 IR 1936; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 97. 326 IAC 20-13-2 IS AMENDED TO READ AS FOLLOWS:

326 IAC 20-13-2 Emission limitations; lead standards for Quemetco, Incorporated

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 2. (a) In addition to the applicable requirements under section 1 of this rule, Quemetco, Inc., Indianapolis

shall comply with the following lead emission limitations and operating provisions:

Facility Description Emission Unit Emission Limitation mg/dscm

Stack 100 1.0

Stack 101 0.5

Stack 102 0.5

Stack 103 0.5

Stack 104 0.5

Stack 105 0.5

Stack 106 0.5

Stack 107 0.5

Stack 108 0.5

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 50
Stack 109 0.5

Stack 111 1.0

Process fugitive and fugitive dust emissions from stacks 101 through 109 shall be vented to the atmosphere

through high efficiency particulate air (HEPA) filters as defined in the July 1, 2011, edition of 40 CFR 63.542*.

(b) New or reconstructed affected sources, as defined in 40 CFR 63.542*, not described in subsection (a),

shall comply with the emission limitations under section 4 of this rule.

*This document is incorporated by reference. Copies may be obtained from the Government Printing Office,

732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the Indiana

Department of Environmental Management, Office of Air Quality, Indiana Government Center North, Tenth Floor,

100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13-2; filed Dec 1, 2000, 2:22 p.m.: 24 IR 958; filed May 21, 2002, 10:20

a.m.: 25 IR 3094; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 98. 326 IAC 20-13-3 IS AMENDED TO READ AS FOLLOWS:

326 IAC 20-13-3 Emission limitations; lead standards for Exide Technologies, Inc.

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 3. (a) In addition to the applicable requirements under section 1 of this rule, Exide Corporation

Technologies, Inc., Muncie shall comply with the following lead emission limitations and operating provisions:

Facility Description Emission Unit Emission Limitation mg/dscm

Ventilation baghouse 0.5

Refinery baghouse 0.5

Bin room baghouse 0.5

North scrubber 1.0

South scrubber 1.0

Battery breaker scrubber 0.5

(b) New or reconstructed affected sources, as defined in 40 CFR 63.542*, not described in subsection (a),

shall comply with the emission limitations under section 4 of this rule, except the requirement for HEPA filters

shall not apply if the new or reconstructed sources are vented to control devices operating prior to the effective

date of this rule.

(Air Pollution Control Division; 326 IAC 20-13-3; filed Dec 1, 2000, 2:22 p.m.: 24 IR 959; filed Jan 30, 2013, 12:34

p.m.: 20130227-IR-326110774FRA)

SECTION 99. 326 IAC 20-13-4 IS AMENDED TO READ AS FOLLOWS:

326 IAC 20-13-4 Emission limitations; other secondary lead smelters

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 4. In addition to the applicable requirements under section 1 of this rule, the owner or operator of any

secondary lead smelter not described under section 2 or 3 of this rule shall comply with the following lead

emission limitations and operating provisions:

Facility Description Emission Unit Emission Limitation mg/dscm

Process stacks 1.0

Process fugitive emission stacks 0.5

Stacks venting fugitive dust sources 0.5

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 51
Process fugitive emissions emission stacks and stacks venting fugitive dust sources shall be vented to the

atmosphere through high efficiency particulate air (HEPA) filters as defined in the July 1, 2011, edition of 40

CFR 63.542*.

*This document is incorporated by reference. Copies may be obtained from the Government Printing Office,

732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the Indiana

Department of Environmental Management, Office of Air Quality, Indiana Government Center North, Tenth Floor,

100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13-4; filed Dec 1, 2000, 2:22 p.m.: 24 IR 959; filed May 21, 2002, 10:20

a.m.: 25 IR 3094; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 100. 326 IAC 20-13-5 IS AMENDED TO READ AS FOLLOWS:

326 IAC 20-13-5 Operational and work practice standards

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 5. The owner or operator of a secondary lead smelter must install and continuously operate a bag leak

detection system for all baghouses controlling process and process fugitive emissions sources. In accordance

with the July 1, 2011, edition of 40 CFR 63.548(g)* and 40 CFR 63.548(h)*, baghouses equipped with HEPA

filters or used exclusively for the control of fugitive dust emissions are exempt from this requirement. The owner

or operator must maintain and operate each baghouse controlling process and process fugitive emissions

sources such that the following conditions are met:

(1) The alarm on the system does not activate for more than five percent (5%) of the total operating time in a

six (6) month reporting period.

(2) Procedures to determine the cause of the alarm are initiated according to the standard operating

procedures manual for corrective action required under the July 1, 2011, edition of 40 CFR 63.548*.

*These documents are incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center North,

Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13-5; filed Dec 1, 2000, 2:22 p.m.: 24 IR 959; filed May 21, 2002, 10:20

a.m.: 25 IR 3095; filed Feb 25, 2008, 2:12 p.m.: 20080326-IR-326070307FRA; filed Jan 30, 2013, 12:34 p.m.:

20130227-IR-326110774FRA)

SECTION 101. 326 IAC 20-13-6 IS AMENDED TO READ AS FOLLOWS:

326 IAC 20-13-6 Compliance testing

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 6. (a) Except as provided in subsection (b), the owner or operator of a secondary lead smelter shall

conduct a compliance test for lead compounds from process stacks on an annual basis, no later than twelve (12)

calendar months following the previous compliance test.

(b) If a compliance test demonstrates a source emitted lead compounds from process stacks less than or

equal to fifty percent (50%) of the applicable limit under this rule during the compliance test, the owner or operator

of a secondary lead smelter shall be allowed up to twenty-four (24) calendar months from the previous

compliance test to conduct the next compliance test for lead compounds.

(c) The owner or operator of a secondary lead smelter shall conduct a compliance test for lead compounds

from process fugitive stacks and fugitive dust stacks on the following schedule:

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 52
(1) Process fugitive emissions stacks shall be tested on a biennial basis, no later than twenty-four (24)

months following the previous compliance test.

(2) Fugitive dust stacks shall conduct an initial compliance test only and shall not be required to conduct

testing on an annual or biennial basis.

Nothing in this subsection shall prohibit the department from requesting a compliance test in accordance with 326

IAC 2-1.1-11.

(d) The following shall apply to tests conducted to demonstrate compliance with the emission limitations under

section 2, 3, or 4 of this rule:

(1) The owner or operator shall use the appropriate test methods under the July 1, 2011, edition of 40 CFR

63.547*.

(2) Test notification and reporting shall comply with 326 IAC 3-6.

(e) Performance testing of process sources conducted prior to the effective date of this rule December 31,

2000, shall be subject to the testing schedule of 40 CFR 63.543(i)*. subsection (b) of this section [subsection

(b)]. Performance testing of sources emission units conducted within twenty-four (24) months prior to the

effective date of this rule December 31, 2000, that demonstrates compliance with the emission limitations in

sections 2 through 4 of this rule shall be considered valid compliance tests for purposes of this rule.

*These documents are *This document is incorporated by reference. Copies may be obtained from the

Government Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review

and copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana Government

Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13-6; filed Dec 1, 2000, 2:22 p.m.: 24 IR 960; filed May 21, 2002, 10:20

a.m.: 25 IR 3095; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 102. 326 IAC 20-13-7 IS AMENDED TO READ AS FOLLOWS:

326 IAC 20-13-7 Compliance requirements

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 7. (a) Owners and operators of secondary lead smelters shall maintain purchasing records and

manufacturer's specifications of all high efficiency particulate air (HEPA) filters installed on process fugitive

emission and fugitive dust stacks demonstrating the filters have been certified by the manufacturer to meet the

definition of HEPA filters in the July 1, 2011, edition of 40 CFR 63.542*. The records and manufacturer's

specifications shall be maintained on site for three (3) years and shall be available for an additional two (2) years.

(b) The owner or operator of any secondary lead smelter shall comply with the following opacity limitations:

(1) Stacks exhausting process, process fugitive emissions, or fugitive dust emissions shall not exceed five

percent (5%) opacity from particulate matter emissions for any one (1) six (6) minute averaging period as

measured by 40 CFR 60, Appendix A, Reference Method 9*.

(2) Exterior dust handling systems of dry collectors of lead emitting processes (augers, hoppers, transfer

points) shall not discharge to the atmosphere visible emissions in excess of five percent (5%) of an

observation period consisting of three (3) twenty (20) minute periods, as determined by 40 CFR 60, Appendix

A, Reference Method 22*. The provisions under this subdivision for dust handling systems shall not apply

during maintenance and repair of the dust handling systems. During maintenance and repair of the dust

handling system, the owner or operator shall take reasonable measures to prevent or minimize fugitive dust

emissions.

(3) The opacity limitations in this subsection shall only apply to particulate matter emissions.

(c) In addition to the requirements of 40 CFR 63.8*, 40 CFR 63.10*, in section 1(e) of this rule, and the July

1, 2011, edition of 40 CFR 63.547(e)*, an owner or operator of any secondary lead smelter using a total

enclosure shall do the following:

(1) Submit a plan describing the installation and operation of a continuous monitoring system that meets the

requirements of the July 1, 2011, edition of 40 CFR 63.547(e)(2)*. The plan shall be postmarked or hand

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 53
delivered to the department one hundred twenty (120) days prior to installation of the continuous monitoring

system.

(2) Within one hundred eighty (180) days after written approval of the monitoring system plan by the

department, install and operate a continuous monitoring system to measure and record pressure differential.

The continuous monitoring system shall consist of the following:

(A) A differential pressure sensor capable of measuring pressure within a range of two-hundredths (0.02) to

two-tenths (0.2) millimeter of mercury (one-hundredth (0.01) to one-tenth (0.1) inch water).

(B) A processor.

(C) An alarm.

(D) A continuous recording device.

Any changes to the location or operation of the system shall require prior written approval by the department.

(3) Initiate corrective actions within thirty (30) minutes of a monitoring system alarm.

(4) Request, if desired, to cease monitoring pressure differential under this subsection twelve (12) months

from the commencement date of approved monitoring or the effective date of this rule, December 31, 2000,

whichever is later.

(5) Notify the department of any physical changes including, but not limited to, ventilation capacity and building

size. If the department determines the net effect of any such changes may potentially affect air pressure

readings of the building, then the owner or operator shall resume monitoring for an additional twelve (12)

months. Monitoring may be discontinued in accordance with the procedures under subdivision (4).

(6) Maintain the following on site for a period of three (3) years and have available for an additional two (2)

years:

(A) Records of the pressure differential.

(B) Logs of monitoring system alarms, including date and time.

(C) Logs of corrective actions, including date and time.

(d) The owner or operator of a secondary lead smelter shall demonstrate compliance with the bag leak

detection system requirements under section 5 of this rule, if applicable, by submitting reports showing that the

alarm on the system does not activate for more than five percent (5%) of the total operating time in a six (6)

month period or two hundred nineteen (219) hours, if operated for four thousand three hundred eighty (4,380)

hours in the six (6) month period, whichever is less. The percentage of total operating time the alarm on the bag

leak detection system activates shall be calculated as follows:

(1) Do not include alarms that occur due solely to a malfunction of the bag leak detection system in the

calculation.

(2) Do not include alarms that occur during startup, shutdown, and malfunction in the calculation if:

(A) the condition is described in the startup, shutdown, and malfunction plan; and

(B) the owner or operator follows all the procedures in the plan defined for this condition.

(3) Count the actual time it takes the owner or operator to identify and correct the cause of the alarm,

excluding any time that the process is shut down for repair.

(4) Calculate the percentage of time the alarm on the bag leak detection system activates as the ratio of the

sum of alarm times to the total operating time multiplied by one hundred (100).

(e) The owner or operator of a secondary lead smelter shall calculate the percentage of total operating

time the alarm on the bag leak detection system activates as the ratio of the sum of alarm times to the

total operating time multiplied by one hundred (100).

(e) (f) The owner or operator of any secondary lead smelter shall install and maintain an ambient air quality

monitoring network for lead as follows:

(1) Unless the owner or operator has received approval prior to the effective date of this rule December 31,

2000, to operate an ambient air quality monitoring network, the owner or operator shall submit a proposed

ambient monitoring and quality assurance plan to the department within ninety (90) days after the effective

date of this rule. December 31, 2000. The plan does not need to be submitted by the owner or operator if an

authorized air pollution control agency operates the monitoring network. The owner or operator may submit a

plan for an existing monitoring network that predates the effective date of this rule. December 31, 2000.

(2) An owner or operator that has not received approval prior to the effective date of this rule December 31,

2000, shall commence ambient monitoring within thirty (30) days after the department's approval of the

proposed ambient monitoring and quality assurance plan. An owner or operator that has received approval

prior to the effective date of this rule December 31, 2000, shall commence monitoring under this rule within

thirty (30) days after such date. on January 31, 2001.

(3) The ambient monitoring shall be:

(A) performed using U.S. EPA-approved methods, procedures, and quality assurance programs, and in

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 54
accordance with the ambient monitoring and quality assurance plan as approved by the department; or

(B) performed by an authorized air pollution control agency having jurisdiction to operate the network.

(4) The owner or operator shall submit a quarterly report to the department within forty-five (45) days after the

end of the quarter in which the data was collected. The report shall include the following:

(A) Ambient air quality monitoring network data.

(B) If a violation of the quarterly NAAQS for lead occurred, identification of the cause of the violation and

corrective actions taken to address the violation.

(5) After twenty-four (24) months from the commencement date of monitoring pursuant to the approved

monitoring plan, an owner or operator may submit a request to discontinue ambient monitoring. The

commissioner may deny the request if a determination is made that continued monitoring is in the interest of

public health and the environment.

(f) (g) Ventilation air from the following shall be conveyed or ventilated to a control device:

(1) All enclosure hoods and total enclosures.

(2) All dryer emission vents.

(3) Agglomerating furnace emission vents.

*These documents are incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center North,

Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13-7; filed Dec 1, 2000, 2:22 p.m.: 24 IR 960; filed May 21, 2002, 10:20

a.m.: 25 IR 3096; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 103. 326 IAC 20-13-8 IS AMENDED TO READ AS FOLLOWS:

326 IAC 20-13-8 Bag leak detection system requirements

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 8. (a) The bag leak detection system required by the July 1, 2011, edition of 40 CFR 63.548(c)(9)* and

section 5 of this rule shall meet the following requirements:

(1) The bag leak detection system must be certified by the manufacturer to be capable of detecting particulate

matter emissions at concentrations of ten (10) milligrams per actual cubic meter (forty-four ten thousandths

(0.0044) grains per actual cubic foot) or less.

(2) The bag leak detection system sensor must provide output of relative particulate matter loadings, and the

owner or operator must continuously record the output from the bag leak detection system.

(3) The bag leak detection system must be equipped with an alarm system that will alert appropriate plant

personnel when an increase in relative particulate loadings is detected over a preset level. The alarm must be

located where it can be heard by the appropriate plant personnel.

(4) Each bag leak detection system that works based on the triboelectric effect must be installed, calibrated,

operated, and maintained consistent with the U.S. Environmental Protection Agency guidance document

"Fabric Filter Bag Leak Detection Guidance" (EPA-454/R-98-015, September 1997)*. Other bag leak detection

systems must be installed, calibrated, and maintained consistent with the manufacturer's written specifications

and recommendations.

(5) The initial adjustment of the system must, at a minimum, consist of establishing:

(A) the baseline output by adjusting the sensitivity (range);

(B) the averaging period of the device;

(C) the alarm set points; and

(D) the alarm delay time.

(6) Following initial adjustment, the owner or operator must not adjust the:

(A) sensitivity or range;

(B) averaging period;

(C) alarm set points; or

(D) alarm delay time;

except as detailed in the maintenance plan required under the July 1, 2011, edition of 40 CFR 63.548(a)*. In

no event must the sensitivity be increased by more than one hundred percent (100%) or decreased more than

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 55
fifty percent (50%) over a three hundred sixty-five (365) day period unless a responsible official certifies the

baghouse has been inspected and found to be in good operating condition.

(7) Where multiple detectors are required, the system's instrumentation and alarm may be shared among

detectors.

(8) For negative pressure, induced air baghouses, and positive pressure baghouses that are discharged to the

atmosphere through a stack, the bag leak detector must be installed downstream of the baghouse and

upstream of any wet acid gas scrubber.

(b) In addition to the record keeping and reporting requirements under the July 1, 2011, edition of 40 CFR

63.550*, the owner or operator shall comply with the following:

(1) Submit a report within thirty (30) days after the end of each preceding six (6) month period ending June 30

and December 31 of each year that includes the following:

(A) A description of the actions taken following each bag leak detection system alarm pursuant to the July

1, 2011, edition of 40 CFR 63.548(f)(1)* and 40 CFR 63.548(f)(2)*.

(B) Calculations of the percentage of time the alarm on the bag leak detection system was activated during

the reporting period.

(2) Records for bag leak detection systems shall be maintained on site for a period of three (3) years and be

available for an additional two (2) years and shall include the following information:

(A) Records of bag leak detection system output.

(B) Identification of the date and time of all bag leak detection system alarms.

(C) The time that procedures to determine the cause of the alarm were initiated.

(D) The cause of the alarm.

(E) An explanation of the actions taken.

(F) The date and time the alarm was corrected.

(G) Records of total operating time of an affected source during smelting operations for each six (6) month

period.

*These documents are incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center North,

Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13-8; filed Dec 1, 2000, 2:22 p.m.: 24 IR 962; filed May 21, 2002, 10:20

a.m.: 25 IR 3097; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 104. 326 IAC 20-13-9 IS ADDED TO READ AS FOLLOWS:

326 IAC 20-13-9 Affirmative defense to civil penalties for exceedance of emissions limit during

malfunction

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 9. (a) In response to an action to enforce the standards set forth in this rule, the owner or

operator of a secondary lead smelter may assert an affirmative defense as defined in 326 IAC 20-13.1-2 to

a claim for civil penalties for exceedances of the standards that are caused by malfunction, as defined in

the July 1, 2012, edition of 40 CFR 63.2*. Appropriate penalties may be assessed if the owner or operator

of a secondary lead smelter fails to meet its burden of proving all of the requirements in the affirmative

defense. The affirmative defense shall not be available for claims for injunctive relief.

(b) To establish the affirmative defense in any action to enforce the standards set forth in this rule, the

owner or operator of a secondary lead smelter must timely meet the notification requirements of

subsection (c), and shall prove by a preponderance of evidence the following:

(1) The excess emissions:

(A) were caused by a sudden, infrequent, and unavoidable failure of air pollution control and

monitoring equipment, process equipment, or a process to operate in a normal or usual manner;

(B) could not have been prevented through careful planning, proper design or better operation and

maintenance practices;

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 56
(C) did not stem from any activity or event that could have been foreseen and avoided, or planned

for; and

(D) were not part of a recurring pattern indicative of inadequate design, operation, or maintenance.

(2) Repairs were made as expeditiously as possible when the applicable emission limitations were

being exceeded. Off-shift and overtime labor were used, to the extent practicable to make these

repairs.

(3) The frequency, amount, and duration of the excess emissions, including any bypass, were

minimized to the maximum extent practicable during periods of the emissions.

(4) If the excess emissions resulted from a bypass of control equipment or a process, then the bypass

was unavoidable to prevent loss of life, personal injury, or severe property damage.

(5) All possible steps were taken to minimize the impact of the excess emissions on ambient air

quality, the environment, and human health.

(6) All emissions monitoring and control systems were kept in operation if at all possible, consistent

with safety and good air pollution control practices.

(7) All of the actions in response to the excess emissions were documented by properly signed,

contemporaneous operating logs.

(8) At all times, the affected emission unit was operated in a manner consistent with good practices for

minimizing emissions.

(9) A written root cause analysis has been prepared, the purpose of which is to determine, correct, and

eliminate the primary causes of the malfunction and the excess emissions resulting from the

malfunction event at issue. The analysis shall also specify, using best monitoring methods and

engineering judgment, the amount of excess emissions that were the result of the malfunction.

(c) The owner or operator of the affected emission unit experiencing an exceedance of its emissions

limit during a malfunction shall notify the department by telephone or facsimile transmission as soon as

possible, but no later than two (2) business days after the initial occurrence of the malfunction, that it

wishes to avail itself of an affirmative defense to civil penalties for that malfunction. The owner or

operator of a secondary lead smelter seeking to assert an affirmative defense shall also submit a written

report to the department within forty-five (45) days of the initial occurrence of the exceedance of the

standard in this rule to demonstrate, with all necessary supporting documentation, that it has met the

requirements set forth in subsection (b). The owner or operator of a secondary lead smelter may seek an

extension of this deadline for up to thirty (30) additional days by submitting a written request to the

department before the expiration of the forty-five (45) day period. Until a request for an extension has

been approved by the department, the owner or operator of a secondary lead smelter is subject to the

requirement to submit the report within forty-five (45) days of the initial occurrence of the exceedance.

*This document is incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center

North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13-9; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 105. 326 IAC 20-13.1 IS ADDED TO READ AS FOLLOWS:

Rule 13.1. Secondary Lead Smelters

326 IAC 20-13.1-1 Applicability

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 1. (a) In accordance with the compliance schedule in subsection (c), this rule applies to the

following affected emission units at all secondary lead smelters:

(1) Blast, reverberatory, rotary, and electric furnaces.

(2) Refining kettles.

(3) Agglomerating furnaces.

(4) Dryers.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 57
(5) Process fugitive emissions sources.

(6) Buildings containing lead bearing materials.

(7) Fugitive dust sources.

(b) This rule does not apply to primary lead smelters, lead refiners, or lead remelters.

(c) The owner or operator of a secondary lead smelter shall comply with this rule beginning on the

applicable dates specified in the following schedule:

(1) Except for Exide Technologies, Inc., Muncie, affected emission units

constructed or reconstructed on or before May 19, 2011:

January 6, 2014

(2) Compliance with section 3(c) of this rule for affected emission units

constructed or reconstructed on or before May 19, 2011, at Exide

Technologies, Inc., Muncie:

October 1, 2013

(3) Except for the requirements of section 3(c) of this rule, compliance

with this rule for affected emission units constructed or reconstructed on

or before May 19, 2011, at Exide Technologies, Inc., Muncie:

January 6, 2014

(4) All new emission units as defined in section 2 of this rule: Effective date of this rule

(d) The following general provisions of 40 CFR 63, Subpart A* as published in the 2012 edition* of the

CFR apply to the owner or operator of a secondary lead smelter subject to this rule:

(1) 40 CFR 63.1 through 40 CFR 63.5*.

(2) 40 CFR 63.6(a) through 40 CFR 63.6(c)*.

(3) 40 CFR 63.6(e)(1)(iii)*.

(4) 40 CFR 63.6(g)*.

(5) 40 CFR 63.6(i)* and 40 CFR 63.6(j)*.

(6) 40 CFR 63.7(a) through 40 CFR 63.7(d)*.

(7) 40 CFR 63.7(e)(2) through 40 CFR 63.7(e)(4)*.

(8) 40 CFR 63.7(f) through 40 CFR 63.7(h)*.

(9) 40 CFR 63.8(a)* and 40 CFR 63.8(b)*.

(10) 40 CFR 63.8(c)(1)(ii)*.

(11) 40 CFR 63.8(c)(2) through 40 CFR 63.8(c)(8)*.

(12) 40 CFR 63.8(d)(1) and 40 CFR 63.8(d)(2)*.

(13) 40 CFR 63.8(d)(3)*, except for a provision concerning the incorporation of the written procedures

of a quality control program into startup, shutdown, or malfunction plans.

(14) 40 CFR 63.8(e) through 40 CFR 63.8(g)*.

(15) 40 CFR 63.9(a) through 40 CFR 63.9(c)*.

(16) 40 CFR 63.9(e)*.

(17) 40 CFR 63.9(g)*.

(18) 40 CFR 63.9(h)(1) through 40 CFR 63.9(h)(3)*.

(19) 40 CFR 63.9(h)(5)* and 40 CFR 63.9(h)(6)*.

(20) 40 CFR 63.9(i)* and 40 CFR 63.9(j)*.

(21) 40 CFR 63.10(a)*.

(22) 40 CFR 63.10(b)(1)*.

(23) 40 CFR 63.10(b)(2)(iii)*.

(24) 40 CFR 63.10(b)(2)(vi) through 40 CFR 63.10(b)(2)(xiv)*.

(25) 40 CFR 63.10(b)(3)*.

(26) 40 CFR 63.10(c)(1) through 40 CFR 63.10(c)(9)*.

(27) 40 CFR 63.10(c)(12) through 40 CFR 63.10(c)(14)*.

(28) 40 CFR 63.10(d)(1) through 40 CFR 63.10(d)(4)*.

(29) 40 CFR 63.10(e)* and 40 CFR 63.10(f)*.

(30) 40 CFR 63.12 through 40 CFR 63.15*.

(e) The owner or operator of a secondary lead smelter subject to this rule is also subject to Title V

permitting requirements under 326 IAC 2-7.

(f) Emission standards in this rule apply at all times.

*These documents are incorporated by reference. Copies may be obtained from the Government

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 58
Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and

copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana

Government Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-1; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-2 Definitions

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-11; IC 13-15; IC 13-17

Sec. 2. In addition to the definitions in IC 13-11, 326 IAC 1-2, and 326 IAC 20-1-3, the following

definitions apply throughout this rule:

(1) "Affected emission unit" means any of the following emission units at a secondary lead smelter:

(A) Blast, reverberatory, rotary, and electric furnaces.

(B) Refining kettles.

(C) Agglomerating furnaces.

(D) Dryers.

(E) Process fugitive emissions sources.

(F) Buildings containing lead-bearing materials.

(G) Fugitive dust sources.

(2) "Affirmative defense" means, in the context of an enforcement proceeding, a response or defense

put forward by a defendant, regarding which the defendant has the burden of proof, and the merits of

which are independently and objectively evaluated in a judicial or administrative proceeding.

(3) "Agglomerating furnace" means a furnace used to melt flue dust that is collected from a baghouse

into a solid mass.

(4) "Bag leak detection system" means an instrument that is capable of monitoring particulate matter

loadings in the exhaust of a baghouse in order to detect bag failures. A bag leak detection system

includes, but is not limited to, an instrument to monitor relative particulate matter loadings that

operates on:

(A) triboelectric;

(B) light scattering; or

(C) transmittance.

(5) "Battery breaking area" means the plant location at which lead-acid batteries are broken, crushed,

or disassembled and separated into components.

(6) "Blast furnace" means a smelting furnace consisting of a vertical cylinder atop a crucible, into

which lead-bearing charge materials are introduced at the top of the furnace and combustion air is

introduced through openings in the refractory lining and shell of the furnace at the bottom of the

cylinder and that:

(A) uses coke as a fuel source; and

(B) is operated at a temperature in the combustion zone of greater than nine hundred eighty (980)

degrees Celsius so that that lead compounds are chemically reduced to elemental lead metal.

(7) "Blast furnace charging location" means the physical opening through which raw materials are

introduced into a blast furnace.

(8) "Collocated blast furnace and reverberatory furnace" means operation at the same location of a

blast furnace and a reverberatory furnace where the vent streams of the furnaces are mixed before

cooling, with the volumetric flow rate discharged from the blast furnace being equal to or less than

that discharged from the reverberatory furnace.

(9) "Dryer" means a chamber that is heated and that is used to remove moisture from lead bearing

materials before they are charged to a smelting furnace.

(10) "Dryer transition equipment" means the junction between a dryer and the charge hopper or

conveyor, or the junction between the dryer and the smelting furnace feed chute or hopper located at

the ends of the dryer.

(11) "Electric furnace" means a smelting furnace consisting of a vessel into which reverberatory

furnace slag is introduced and that uses electrical energy to heat the reverberatory furnace slag to a

temperature of greater than nine hundred eighty (980) degrees Celsius so that lead compounds are

reduced to elemental lead metal.

(12) "Fugitive dust source" means a stationary source of hazardous air pollutant emissions at a

secondary lead smelter that is not associated with a specific process or process fugitive vent or stack.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 59
Fugitive dust sources include, but are not limited to, the following:

(A) Roadways.

(B) Storage piles.

(C) Lead-bearing material handling transfer points.

(D) Lead-bearing material transport areas.

(E) Lead-bearing material storage areas.

(F) Other lead-bearing material process areas.

(G) Other lead-bearing material process buildings.

(13) "Furnace and refining/casting area" means any area of a secondary lead smelter where:

(A) smelting furnaces are located;

(B) refining operations occur; or

(C) casting operations occur.

(14) "Lead alloy" means an alloy in which the predominant component is lead.

(15) "Lead-bearing material" means material with a lead content equal to or greater than five (5)

milligrams per liter (mg/l) as measured by United States Environmental Protection Agency (U.S. EPA)

Method 1311 "Test Methods for Evaluating Solid Waste, Physical/Chemical Method", U.S. EPA

Publication SW-846*. Under Method 1311, only materials with at least one hundred (100) parts per

million (ppm) lead will be considered to be lead-bearing.

(16) "Leeward wall" means the furthest exterior wall of a total enclosure that is opposite the windward

wall.

(17) "Maintenance activity" means any of the following routine maintenance and repair activities that

could generate fugitive lead dust:

(A) Replacement or repair of refractory, or any internal or external part of equipment used to

process, handle, or control lead-containing materials.

(B) Replacement of any duct section used to convey lead-containing exhaust.

(C) Metal cutting or welding that penetrates the metal structure of any equipment, and its associated

components, used to process lead-containing material so that lead dust within the internal structure

or its components can become fugitive lead dust.

(D) Resurfacing, repair, or removal of ground, pavement, concrete, or asphalt.

(18) "Materials storage and handling area" means any area of a secondary lead smelter where

lead-bearing materials are stored or handled between process steps including, but not limited to areas

in which materials are stored in open piles, bins, or tubs, and areas in which material is prepared for

charging to a smelting furnace. Lead-bearing materials in these areas include, but are not limited to,

the following:

(A) Broken battery components.

(B) Reverberatory furnace slag.

(C) Flue dust.

(D) Dross.

(19) "Natural draft opening" means any permanent opening in an enclosure that:

(A) remains open during operation of a secondary lead smelter; and

(B) is not connected to a duct in which a fan is installed.

(20) "New emissions unit" means any affected emissions unit at a secondary lead smelter that was

constructed or reconstructed after May 19, 2011. The term does not include a building that is

constructed for the purpose of controlling fugitive emissions from an existing emissions unit.

(21) "Partial enclosure" means a structure comprised of walls or partitions on at least three (3) sides

or three-quarters (3/4) of the perimeter surrounding stored materials or process equipment to prevent

the entrainment of particulate matter into the air.

(22) "Pavement cleaning" means the use of vacuum equipment, water sprays, or a combination thereof

to remove dust or other accumulated material from the paved areas of a secondary lead smelter.

(23) "Plant roadway" means any area of a secondary lead smelter outside of a total enclosure that is

subject to vehicle traffic, including traffic by forklifts, front-end loaders, or vehicles carrying whole

batteries or cast lead ingots. The term does not include employee and visitor parking areas, provided

they are not subject to traffic by vehicles carrying lead-bearing materials.

(24) "Pressurized dryer breaching seal" means a seal system connecting the dryer transition pieces

that is maintained at a higher pressure than the inside of the dryer.

(25) "Process fugitive emissions source" means a source of hazardous air pollutant emissions at a

secondary lead smelter that is associated with lead smelting or refining, but is not the primary exhaust

stream from a smelting furnace, and is not a fugitive dust source. Process fugitive emissions sources

include, but are not limited to, the following:

(A) Smelting furnace charging points.

(B) Smelting furnace lead and slag taps.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 60
(C) Refining kettles.

(D) Agglomerating furnaces.

(E) Drying kiln transition pieces.

(26) "Process vent" means the following:

(A) Furnace vents.

(B) Dryer vents.

(C) Agglomeration furnace vents.

(D) Vents from battery breakers.

(E) Vents from buildings containing lead-bearing material.

(F) Any ventilation system controlling lead emissions.

(27) "Refining kettle" means an open-top vessel that is constructed of cast iron or steel and is

indirectly heated from below and contains molten lead for the purpose of refining and alloying the

lead, including the following:

(A) Pot furnaces.

(B) Receiving kettles.

(C) Holding kettles.

(28) "Reverberatory furnace" means a refractory-lined furnace that uses one (1) or more flames to heat

the walls and roof of the furnace and lead-bearing scrap to a temperature of greater than nine hundred

eighty (980) degrees Celsius so that lead compounds are chemically reduced to elemental lead metal.

(29) "Rotary furnace," or "rotary reverberatory furnace" means a furnace consisting of a

refractory-lined chamber that rotates about a horizontal axis and that uses one (1) or more flames to

heat the walls of the furnace and lead-bearing scrap to a temperature of greater than nine hundred

eighty (980) degrees Celsius so that lead compounds are chemically reduced to elemental lead metal.

(30) "Secondary lead smelter" means any source where lead-bearing scrap material is recycled into

elemental lead or lead alloys by smelting, including, but not limited to, lead-acid batteries.

(31) "Shutdown" means the period when no lead-bearing materials are being fed to the furnace and

smelting operations have ceased during which the furnace is cooled from steady-state operating

temperature to ambient temperature.

(32) "Smelting" means the chemical reduction of lead compounds to elemental lead or lead alloys

through processing in high-temperature furnaces at a temperature of greater than nine hundred eighty

(980) degrees Celsius, including, but not limited to, the following:

(A) Blast furnaces.

(B) Reverberatory furnaces.

(C) Rotary furnaces.

(D) Electric furnaces.

(33) "Startup" means the period when no lead-bearing materials have been fed to the furnace and

smelting operations have not yet commenced during which the furnace is heated from ambient

temperature to steady-state operating temperature.

(34) "Total enclosure" means a containment building that is completely enclosed with a floor, walls,

and a roof to prevent exposure to the elements and to assure containment of lead-bearing material

with limited openings to allow access and egress for people and vehicles. The total enclosure must

provide an effective barrier against fugitive dust emissions so that the:

(A) direction of air flow through any openings is inward; and

(B) enclosure is maintained under constant negative pressure.

(35) "Vehicle wash" means a device for removing dust and other accumulated material from the

wheels, body, and underside of a vehicle to prevent the inadvertent transfer of lead-contaminated

material to another area of a secondary lead smelter or to public roadways.

(36) "Wet suppression" means the use of water, water combined with a chemical surfactant, or a

chemical binding agent to prevent the entrainment of dust into the air from fugitive dust sources.

(37) "Windward wall" means the exterior wall of a total enclosure that is most impacted by the wind in

its most prevailing direction determined by a wind rose using available data from the closest

representative meteorological station.

*This document is incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center

North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-2; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 61
326 IAC 20-13.1-3 Emission limitations; lead standards for Exide Technologies, Incorporated

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 3. (a) In addition to the applicable requirements of this rule, Exide Technologies, Inc., Muncie,

shall comply with the following lead emission limitations and operating provisions:

Emission Unit Emission Limitation mg/dscm

Ventilation baghouse 0.5

Refinery baghouse 0.5

Bin room baghouse 0.5

North scrubber 1.0

South scrubber 1.0

Battery breaker scrubber 0.5

(b) For new emission units, Exide Technologies, Inc. shall comply with the emission limitations under

section 5(c) of this rule.

(c) Exide Technologies, Inc., shall comply with the following requirements by October 1, 2013:

(1) Section 1 of this rule.

(2) Section 2 of this rule.

(3) Subsection (a) of this section [subsection (a)].

(4) Section 5(b) and 5(h) of this rule.

(5) Sections 6 through 9 of this rule.

(6) Section 10(a) through 10(d) of this rule.

(7) Section 11(a) through 11(c) and 11(f) of this rule.

(8) Section 12(a) of this rule.

(9) Section 14(a), 14(b), 14(c)(1) through 14(c)(8), 14(c)(10) through 14(c)(13), 14(c)(15) through

14(c)(17), 14(d), 14(e)(1), 14(e)(4) through 14(e)(7), and 14(e)(9) through 14(e)(12) of this rule.

(Air Pollution Control Division; 326 IAC 20-13.1-3; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-4 Emission limitations; lead standards for Quemetco, Incorporated

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 4. (a) In addition to the applicable requirements of this rule, Quemetco, Inc., Indianapolis, shall

comply with the following lead emission limitations and operating provisions:

Emission Unit Emission Limitation mg/dscm

Stack 100 1.0

Stack 101 0.5

Stack 102 0.5

Stack 103 0.5

Stack 104 0.5

Stack 105 0.5

Stack 106 0.5

Stack 107 0.5

Stack 108 0.5

Stack 109 0.5

Stack 111 1.0

Process fugitive and fugitive dust emissions from stacks 101 through 109 shall be vented to the

atmosphere through HEPA filters that have been certified by the manufacturer to remove ninety-nine and

ninety-seven hundredths percent (99.97%) of all particles three-tenths (0.3) micrometers and larger.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 62
(b) For new emission units, Quemetco, Inc. shall comply with the emission limitations under section

5(c) of this rule.

(Air Pollution Control Division; 326 IAC 20-13.1-4; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-5 Emission limitations and operating provisions

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 5. (a) The owner or operator of a secondary lead smelter not described in section 3 or 4 of this

rule shall maintain the following concentrations of lead compounds for affected emission units

constructed or reconstructed on or before May 19, 2011:

(1) From any process vent, at or below one (1.0) milligram of lead per dry standard cubic meter

(forty-three hundred-thousandths (0.00043) grains of lead per dry standard cubic foot).

(2) From any process fugitive emissions source, at or below five-tenths (0.5) milligram of lead per dry

standard cubic meter (twenty-two hundred-thousandths (0.00022) grains of lead per dry standard

cubic foot).

(3) From vents venting fugitive dust sources, at or below five-tenths (0.5) milligram of lead per dry

standard cubic meter (twenty-two hundred-thousandths (0.00022) grains of lead per dry standard

cubic foot).

(b) The owner or operator of a secondary lead smelter shall comply with the following lead emission

limitations and operating provisions for affected emission units constructed or reconstructed on or

before May 19, 2011:

(1) The owner or operator of a secondary lead smelter shall maintain the flow-weighted average

concentration of lead compounds in vent gases from a secondary lead smelter at or below two-tenths

(0.2) milligrams per dry standard cubic meter (eighty-seven millionths (0.000087) grains of lead per dry

standard cubic foot).

(2) The owner or operator of a secondary lead smelter shall demonstrate compliance with the

flow-weighted average emissions limit on a twelve (12) month rolling average basis, calculated

monthly using the most recent test data available.

(3) Until twelve (12) monthly weighted average emission rates have been accumulated, the owner or

operator of a secondary lead smelter shall calculate only the monthly average weighted emissions

rate.

(4) The owner or operator of a secondary lead smelter shall use the following equation to calculate the

flow-weighted average concentration of lead compounds from process vents:

Where: CFWA = Flow-weighted average concentration of all process vents.

n = Number of process vents.

F

i

= Flow rate from process vent i in dry standard cubic feet per minute, as

measured during the most recent compliance test.

Ci= Concentration of lead in process vent i, as measured during the most

recent compliance test.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 63
(5) Each month, the owner or operator of a secondary lead smelter shall use the concentration of lead

and flow rate obtained during the most recent compliance test performed prior to or during that month

to perform the calculation using the equation in subdivision (4).

(6) If a continuous emissions monitoring system (CEMS) is used to measure the concentration of lead

in a vent, the monthly average lead concentration and monthly average flow rate must be used rather

than the most recent compliance test data.

(c) For new emission units, the owner or operator of a secondary lead smelter shall maintain the

concentration of lead compounds in any process vent gas at or below twenty-hundredths (0.20)

milligrams of lead per dry standard cubic meter (eighty-seven millionths (0.000087) grains of lead per dry

standard cubic foot).

(d) The owner or operator of a secondary lead smelter shall meet the applicable emission limits for

total hydrocarbons and dioxins and furans from furnaces specified in the following table. There are no

standards for dioxins and furans during periods of startup and shutdown.

Emission Unit

Total Hydrocarbon

(Parts per million

by volume

expressed as

propane corrected

to four percent

(4%) carbon

dioxide)

Dioxin and furan

(nanograms per dry

standard cubic meter

expressed as toxic

equivalency quotient

(TEQ) corrected to

seven percent (7%)

oxygen)

Collocated blast furnace and reverberatory furnace (new and

existing)

20 0.50

Collocated blast furnace and reverberatory furnace when the

reverberatory furnace is not operating for units that

commence construction or reconstruction on or before June

9, 1994

360 170

Collocated blast furnace and reverberatory furnace when the

reverberatory furnace is not operating for units that

commence construction or reconstruction after June 9, 1994

70 170

Blast furnaces that commence construction or

reconstruction on or before June 9, 1994

360 170

Blast furnaces that commence construction or

reconstruction after June 9, 1994

70 170

Blast furnaces that commence construction or

reconstruction after May 19, 2011

70 10

Reverberatory and electric furnaces that commence

construction or reconstruction on or before May 19, 2011

12 0.20

Reverberatory and electric furnaces that commence

construction or reconstruction after May 19, 2011

12 0.10

(e) If the owner or operator of a secondary lead smelter combines furnace emissions from multiple

types of furnaces and these furnaces do not meet the definition of collocated blast furnace and

reverberatory furnace, the owner or operator of a secondary lead smelter shall calculate the emissions

limit for the combined furnace stream using the following equation:

Where: CEL = Flow-weighted average emissions limit (concentration) of combined

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 64
furnace vents.

n = Number of furnace vents.

F

i

= Flow rate from furnace vent i in dry standard cubic feet per minute.

CELi = Emissions limit (concentration) of pollutant in furnace vent i, as specified

in subsection (d).

(f) If the owner or operator of a secondary lead smelter combines furnace emissions with the furnace

charging process fugitive emissions and discharges them to the atmosphere through a common

emissions point, the owner or operator of a secondary lead smelter shall demonstrate compliance with

the applicable total hydrocarbons concentration limit specified in subsection (d) at a location

downstream from the point at which the two (2) emission streams are combined.

(g) If the owner or operator of a secondary lead smelter does not combine the furnace charging

process fugitive emissions with the furnace process emissions, and discharges the emissions to the

atmosphere through separate emission points, the owner or operator of a secondary lead smelter shall

maintain the total hydrocarbons concentration in the exhaust gas at or below twenty (20) parts per million

by volume, expressed as propane and corrected to four percent (4%) carbon dioxide.

(h) At all times, the owner or operator of a secondary lead smelter shall operate and maintain any

affected emission unit, including associated air pollution control equipment and monitoring equipment, in

a manner consistent with safety and good air pollution control practices for minimizing emissions.

Determination of whether appropriate operation and maintenance procedures are being used will be

based on information available to the department that may include, but is not limited to, the following:

(1) Monitoring results.

(2) Review of operation and maintenance procedures.

(3) Review of operation and maintenance records.

(4) Inspection of the source.

(i) If the owner or operator of a secondary lead smelter owns or operates a unit subject to emission

limits in subsection (d), the owner or operator of a secondary lead smelter shall minimize the unit's

startup and shutdown periods following the manufacturer's recommended procedures, if available. The

owner or operator of a secondary lead smelter shall develop and follow standard operating procedures

designed to minimize emissions of total hydrocarbons for each startup or shutdown scenario anticipated.

The owner or operator of a secondary lead smelter shall submit a signed statement in the Notification of

Compliance Status report that indicates that the owner or operator of a secondary lead smelter

conducted startups and shutdowns according to the manufacturer's recommended procedures, if

available, and the standard operating procedures designed to minimize emissions of total hydrocarbons.

(j) In addition to complying with the applicable emission limits for dioxins and furans listed in

subsection (d), the owner or operator of a secondary lead smelter shall operate a process to separate

plastic battery casing materials from all automotive batteries prior to introducing feed into a furnace.

(Air Pollution Control Division; 326 IAC 20-13.1-5; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-6 Total enclosure requirements

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 6. (a) The owner or operator of a secondary lead smelter shall operate the following process

fugitive emissions sources and fugitive dust sources in a total enclosure that meets the requirements in

subsection (c) of this section [subsection (c)] that is maintained at negative pressure at all times and

vented to a control device designed to capture lead particulate:

(1) Smelting furnaces.

(2) Smelting furnace charging areas.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 65
(3) Lead taps, slag taps, and molds during tapping.

(4) Battery breakers.

(5) Refining kettles, casting areas.

(6) Dryers.

(7) Agglomerating furnaces and agglomerating furnace product taps.

(8) Material handling areas for any lead-bearing materials except those listed in subsection (b).

(9) Areas where dust from fabric filters, sweepings, or used fabric filters are processed.

(b) The owner or operator of a secondary lead smelter is not required to maintain a total enclosure in

the following areas unless the area is in a total enclosure described in subsection (a):

(1) Lead ingot product handling areas.

(2) Stormwater and wastewater treatment areas.

(3) Intact battery storage areas.

(4) Areas where lead-bearing material is stored in closed containers or enclosed mechanical

conveyors.

(5) Areas where clean battery casing material is handled.

(c) The owner or operator of a secondary lead smelter shall do the following:

(1) Construct and operate a total enclosure for the process fugitive emissions sources and fugitive

dust sources listed in subsection (a) that is free of cracks, gaps, corrosion, or other deterioration that

could allow lead-bearing material to be released from the primary barrier.

(2) Put measures in place to prevent the tracking of lead-bearing material out of the plant by personnel

or by equipment used in handling the material.

(3) Designate an area to decontaminate equipment and collect and properly manage any rinsate.

(4) Ventilate the total enclosure for the process fugitive emissions sources and fugitive dust sources

listed in subsection (a) continuously to ensure negative pressure values of at least

thirteen-thousandths (0.013) millimeters of mercury (seven-thousandths (0.007) inches of water).

(5) Maintain an inward flow of air through all natural draft openings of the total enclosure.

(6) Inspect total enclosures and structures that contain any lead-bearing material at least once per

month.

(7) Repair any gaps, breaks, separations, leak points, or other possible routes for emissions of lead to

the atmosphere within one (1) week of identification unless the owner or operator of a secondary lead

smelter receives approval for an extension from the department and U.S. EPA before the repair period

is exceeded.

(Air Pollution Control Division; 326 IAC 20-13.1-6; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-7 Total enclosure monitoring requirements

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 7. (a) In addition to the requirements in section 1(d) of this rule, and the requirements in section 6

of this rule, the owner or operator of a secondary lead smelter using a total enclosure shall do the

following:

(1) Submit a monitoring system plan describing the installation and operation of a continuous

monitoring system that meets the requirements of subdivisions (2) and (3). The plan shall be

postmarked or hand delivered to the department one hundred twenty (120) days prior to installation of

the continuous monitoring system.

(2) The owner or operator of a secondary lead smelter shall install, operate, and maintain a minimum

of one (1) building digital differential pressure monitoring system to continuously monitor each total

enclosure at each of the following three (3) walls in each total enclosure that has a total ground

surface area of ten thousand (10,000) square feet or more:

(A) The leeward wall.

(B) The windward wall.

(C) An exterior wall that connects the leeward and windward wall at a location defined by the

intersection of a perpendicular line between a point on the connecting wall and a point on its

furthest opposite exterior wall, and intersecting within plus or minus ten (10) meters of the midpoint

of a straight line between the two (2) other monitors specified. The midpoint monitor must not be

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 66
located on the same wall as either of the other two (2) monitors.

(3) The owner or operator of a secondary lead smelter shall install and maintain a minimum of one (1)

building digital differential pressure monitoring system at the leeward wall of each total enclosure that

has a total ground surface area of less than ten thousand (10,000) square feet.

(b) Within one hundred eighty (180) days after written approval of the continuous monitoring system

plan by the department, the owner or operator of a secondary lead smelter shall install and operate a

continuous monitoring system that consists of the following:

(1) A digital differential pressure sensor capable of measuring pressure within a range of

one-hundredth (0.01) to two-tenths (0.2) millimeters mercury (five-thousandths (0.005) to

eleven-hundredths (0.11) inches of water) with a minimum accuracy of plus or minus one-thousandth

(0.001) millimeters of mercury (five ten-thousandths (0.0005) inches of water).

(2) A processor.

(3) An alarm.

(4) A continuous recording device.

(c) The owner or operator of a secondary lead smelter shall calibrate each digital differential pressure

monitoring system in accordance with the manufacturer's specifications at least once every twelve (12)

calendar months or more frequently if recommended by the manufacturer.

(d) The owner or operator of a secondary lead smelter shall obtain prior written approval from the

department for any changes to the location or operation of the continuous monitoring system.

(e) The owner or operator of a secondary lead smelter shall initiate corrective actions within thirty (30)

minutes of a monitoring system alarm.

(f) The owner or operator of a secondary lead smelter shall notify the department within seven (7) days

of any physical changes to the total enclosure including, but not limited to, ventilation capacity and

building size.

(g) The owner or operator of a secondary lead smelter shall maintain the following on site for a period

of three (3) years and have available the following records for an additional two (2) years:

(1) Records of the pressure differential.

(2) Logs of monitoring system alarms, including date and time.

(3) Logs of corrective actions, including date and time.

(Air Pollution Control Division; 326 IAC 20-13.1-7; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-8 Fugitive dust source requirements

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 8. (a) The owner or operator of a secondary lead smelter shall prepare and at all times operate in

accordance with a standard operating procedures manual that describes in detail the measures that will

be put in place and implemented to control the fugitive dust emissions from the following:

(1) Plant roadways.

(2) Plant buildings.

(3) Accidental releases.

(4) Battery storage areas.

(5) Equipment maintenance activities.

(6) Material storage areas.

(7) Material handling areas.

(b) The owner or operator of a secondary lead smelter shall submit the standard operating procedures

manual to the department for review and approval in accordance with section 13(b) of this rule and at any

time changes are made.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 67
(c) The controls specified in the standard operating procedures manual must, at a minimum, include

the following requirements:

(1) Where a cleaning practice is specified, the owner or operator of a secondary lead smelter shall

clean by wet wash or a vacuum equipped with a filter rated by the manufacturer to achieve ninety-nine

and ninety-seven hundredths percent (99.97%) capture efficiency for three-tenths (0.3) micron

particles in a manner that does not generate fugitive lead dust.

(2) The owner or operator of a secondary lead smelter shall pave all areas subject to vehicle traffic and

shall clean the pavement twice per day, except on days when natural precipitation makes cleaning

unnecessary or when sand or a similar material has been spread on plant roadways to provide traction

on ice or snow. Limited access and limited use roadways such as unpaved roads to remote locations

on the property may be exempt from this requirement if they are used no more than one (1) round trip

per day.

(3) The owner or operator of a secondary lead smelter shall initiate cleaning of all affected areas within

one (1) hour after detection of any accidental release of lead dust that exceeds ten (10) pounds in

accordance with the reportable quantity requirements for lead at 40 CFR 302.4*.

(4) The owner or operator of a secondary lead smelter shall inspect any batteries that are not stored in

a total enclosure once each week and move any broken batteries to an enclosure within seventy-two

(72) hours of identification. The owner or operator of a secondary lead smelter shall clean residue

from broken batteries within seventy-two (72) hours of identification.

(5) The owner or operator of a secondary lead smelter shall wash each vehicle at each exit of the

material storage and handling areas. The vehicle wash shall include washing of tires, undercarriage,

and exterior surface of the vehicle followed by vehicle inspection.

(6) The owner or operator of a secondary lead smelter shall perform all maintenance activities that

could generate lead dust in a manner that minimizes emissions of fugitive dust. This shall include one

(1) or more of the following:

(A) Performing maintenance inside a total enclosure maintained at negative pressure.

(B) Performing maintenance inside a temporary enclosure and use of a vacuum system either

equipped with a filter rated by the manufacturer to achieve a capture efficiency of ninety-nine and

ninety-seven hundredths percent (99.97%) for three-tenths (0.3) micron particles or routed to an

existing control device permitted for this activity.

(C) Performing maintenance inside a partial enclosure and use of wet suppression sufficient to

prevent dust formation.

(D) Decontamination of equipment prior to removal from an enclosure.

(E) Immediate repair of ductwork or structure leaks without an enclosure if the time to construct a

temporary enclosure would exceed the time to make a temporary or permanent repair, or if

construction of an enclosure would cause a higher level of emissions than if an enclosure were not

constructed.

(F) Activities required for inspection of fabric filters and maintenance of filters that are in need of

removal and replacement are not required to be conducted inside of total enclosures. Used fabric

filters shall be placed in sealed plastic bags or containers prior to removal from a baghouse.

(7) The owner or operator of a secondary lead smelter shall collect and transport all lead-bearing dust

within closed conveyor systems or in sealed, leak-proof containers unless the collection and transport

activities are contained within a total enclosure. All other lead-bearing material must be contained and

covered for transport outside of a total enclosure in a manner that prevents spillage or dust formation.

Intact batteries and lead ingot product are exempt from the requirement to be covered for transport.

(d) The standard operating procedures manual must specify that records be maintained of all

pavement cleaning, vehicle washing, and battery storage inspection activities performed to control

fugitive dust emissions.

(e) The owner or operator of a secondary lead smelter shall pave all grounds or plant ground cover

sufficient to prevent wind-blown dust. The owner or operator of a secondary lead smelter may use dust

suppressants on unpaved areas that will not support a ground cover, such as roadway shoulders, steep

slopes, and limited access and limited use roadways.

(f) As provided in the July 1, 2012, edition of 40 CFR 63.6(g)*, as an alternative to the requirements

specified in this section, the owner or operator of a secondary lead smelter can demonstrate to the

department that an alternative measure is equivalent or more protective of the environment than a

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 68
practice described in this section.

*These documents are incorporated by reference. Copies may be obtained from the Government

Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and

copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana

Government Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-8; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-9 Bag leak detection system requirements

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 9. (a) The owner or operator of a secondary lead smelter shall install and continuously operate a

bag leak detection system for all baghouses controlling process vents and process fugitive emissions

sources unless a system meeting the requirements of section 10(g) of this rule for a CEMS is installed for

monitoring the concentration of lead. Baghouses equipped with HEPA filters or baghouses followed by

wet electrostatic precipitators used as secondary control devices are exempt from this requirement. The

owner or operator of a secondary lead smelter shall maintain and operate each baghouse controlling

process vents and process fugitive emissions sources to meet the following conditions:

(1) The alarm on the system does not activate for more than five percent (5%) of the total operating

time in a six (6) month reporting period.

(2) The owner or operator of a secondary lead smelter shall include a corrective action plan in its

standard operating procedures manual required in subsection (c) that specifies the procedures that

will be used to determine and record the time and cause of the alarm in addition to necessary

corrective actions taken to minimize emissions as follows:

(A) The procedures used to determine the cause of the alarm shall be initiated within thirty (30)

minutes of the alarm.

(B) Procedures to determine and correct the cause of the alarm may include, but are not limited to,

the following standard operating procedures:

(i) Inspecting the baghouse for air leaks, torn or broken filter elements, or any other malfunction

that may cause an increase in emissions.

(ii) Sealing off defective bags or filter media.

(iii) Replacing defective bags or filter media, or otherwise repairing the control device.

(iv) Sealing off a defective baghouse compartment.

(v) Cleaning the bag leak detection system probe, or otherwise repairing the bag leak detection

system.

(vi) Shutting down the process producing the particulate emissions.

(b) The owner or operator of a secondary lead smelter shall demonstrate compliance with the bag leak

detection system requirements by submitting reports showing that the alarm on the system does not

activate for more than five percent (5%) of the total operating time in a six (6) month period or two

hundred nineteen (219) hours, if operated for four thousand three hundred eighty (4,380) hours in the six

(6) month period, whichever is less.

(c) The owner or operator of a secondary lead smelter shall calculate the percentage of total operating

time the alarm on the bag leak detection system activates as the ratio of the sum of alarm times to the

total operating time multiplied by one hundred (100).

(d) The owner or operator of a secondary lead smelter shall prepare and at all times operate in

accordance with a standard operating procedures manual that describes in detail procedures for

inspection, maintenance, and bag leak detection, and corrective action plans for all baghouses (fabric

filters or cartridge filters) that are used to control process vents, process fugitive, or fugitive dust

emissions from any source subject to the lead emission standards in sections 3, 4, 5, 6, and 8 of this rule,

including those used to control emissions from building ventilation.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 69
(e) The owner or operator of a secondary lead smelter shall submit the standard operating procedures

manual for baghouses required by subsection (d) to the department for review and approval in

accordance with section 13(b) of this rule.

(f) The procedures that the owner or operator of a secondary lead smelter specifies in the standard

operating procedures manual for inspections and routine maintenance must, at a minimum, include the

following requirements:

(1) Daily monitoring of pressure drop across each baghouse cell.

(2) Weekly confirmation that dust is being removed from hoppers through visual inspection, or

equivalent means of ensuring the proper functioning of removal mechanisms.

(3) Daily check of compressed air supply for pulse-jet baghouses.

(4) An appropriate methodology for monitoring cleaning cycles to ensure proper operation.

(5) Monthly check of bag cleaning mechanisms for proper functioning through visual inspection or

equivalent means.

(6) Monthly check of bag tension on reverse air and shaker-type baghouses. The checks are not

required for shaker-type baghouses using self-tensioning or spring loaded devices.

(7) Quarterly confirmation of the physical integrity of the baghouse through visual inspection of the

baghouse interior for air leaks.

(8) Quarterly inspection of fans for wear, material buildup, and corrosion through visual inspection,

vibration detectors, or equivalent means.

(9) Except as provided in subsection (a), continuous operation of a bag leak detection system, unless

a system meeting the requirements of section 10(g) of this rule for a CEMS is installed for monitoring

the concentration of lead.

(g) The procedures specified in the standard operating procedures manual for baghouse maintenance

shall include, at a minimum, a preventative maintenance schedule that is consistent with the baghouse

manufacturer's instructions for routine and long-term maintenance.

(h) The owner or operator of a secondary lead smelter shall operate a bag leak detection system that

meets the following requirements:

(1) The bag leak detection system must be certified by the manufacturer to be capable of detecting

particulate matter emissions at concentrations of one (1) milligram per actual cubic meter (forty-four

hundred-thousandths (0.00044) grains per actual cubic foot) or less.

(2) The bag leak detection system sensor must provide output of relative particulate matter loadings,

and the owner or operator of a secondary lead smelter shall continuously record the output from the

bag leak detection system.

(3) The bag leak detection system must be equipped with an alarm system that will alert appropriate

plant personnel when an increase in relative particulate loadings is detected over a preset level. The

alarm must be located where it can be heard by the appropriate plant personnel.

(4) Each bag leak detection system must be installed, calibrated, operated, and maintained consistent

with the U.S. EPA guidance document "Fabric Filter Bag Leak Detection Guidance" (EPA-454/R-98-015,

September 1997)* and with the manufacturer's written specifications and recommendations.

(5) The initial adjustment of the system must, at a minimum, consist of establishing the following:

(A) The baseline output by adjusting the sensitivity (range).

(B) The averaging period of the device.

(C) The alarm set points.

(D) The alarm delay time.

(6) Following initial adjustment and except as detailed in the standard operating procedures and

maintenance plan required under subsection (f), the owner or operator of a secondary lead smelter

shall not adjust the system's:

(A) sensitivity or range;

(B) averaging period;

(C) alarm set points; or

(D) alarm delay time.

The owner or operator of a secondary lead smelter shall not increase the sensitivity of the system by

more than one hundred percent (100%) or decrease the sensitivity by more than fifty percent (50%)

over a three hundred sixty-five (365) day period unless the adjustment follows a complete baghouse

inspection that demonstrates that the baghouse is in good operating condition.

(7) For negative pressure, induced air baghouses, and positive pressure baghouses that are

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 70
discharged to the atmosphere through a stack, the owner or operator of a secondary lead smelter

shall install the bag leak detector downstream of the baghouse and upstream of any wet acid gas

scrubber.

(8) Where multiple detectors are required, the system's instrumentation and alarm may be shared

among detectors.

(i) In addition to the record keeping and reporting requirements under section 14 of this rule, the

owner or operator of a secondary lead smelter shall comply with the following:

(1) Submit a report within thirty (30) days after the end of each preceding six (6) month period ending

June 30 and December 31 of each year that includes the following:

(A) A description of the actions taken following each bag leak detection system alarm pursuant to

subsection (a).

(B) Calculations of the percentage of total operating time, or the total operating time in hours and

minutes the alarm on the bag leak detection system was activated during the reporting period.

(2) Records for bag leak detection systems shall be maintained on site for a period of three (3) years

and be available for an additional two (2) years and shall include the following information:

(A) Records of bag leak detection system output.

(B) Identification of the date and time of all bag leak detection system alarms.

(C) The time that procedures to determine the cause of the alarm were initiated.

(D) The cause of the alarm.

(E) An explanation of the corrective actions taken.

(F) The date and time the cause of the alarm was corrected.

(G) Records of total operating time of an affected source during smelting operations for each six (6)

month period.

*This document is incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center

North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-9; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-10 Other requirements

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 10. (a) The owner or operator of a secondary lead smelter shall comply with the following opacity

limitations:

(1) Stacks exhausting process vents, process fugitive emissions, or fugitive dust emissions shall not

exceed five percent (5%) opacity from particulate matter emissions for any one (1) six (6) minute

averaging period as measured by 40 CFR 60, Appendix A, Method 9*.

(2) Exterior dust handling systems of dry collectors of lead emitting processes, such as augers,

hoppers, and transfer points, shall not discharge visible emissions to the atmosphere in excess of five

percent (5%) of an observation period consisting of three (3) twenty (20) minute periods, as

determined by 40 CFR 60, Appendix A, Method 22*. The provisions under this subdivision for dust

handling systems shall not apply during maintenance and repair of the dust handling systems. During

maintenance and repair of the dust handling system, the owner or operator shall take reasonable

measures to prevent or minimize fugitive dust emissions.

(3) The opacity limitations in this subsection shall only apply to particulate matter emissions.

(b) Ventilation air from the following shall be conveyed or ventilated to a control device:

(1) All enclosure hoods and total enclosures.

(2) All dryer emission vents.

(3) Agglomerating furnace emission vents.

(c) If the owner or operator of a secondary lead smelter uses baghouses equipped with HEPA filters as

a secondary filter used to control emissions from any source subject to the lead emission standards in

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 71
sections 3 through 5 of this rule, the owner or operator of secondary lead smelter must monitor and

record the pressure drop across each HEPA filter system daily as follows:

(1) If the pressure drop is outside the limit specified by the filter manufacturer, the owner or operator

of a secondary lead smelter shall take the appropriate corrective measures, including, but not limited

to, the following:

(A) Inspecting the filter and filter housing for air leaks and torn or broken filters.

(B) Replacing defective filter media, or otherwise repairing the control device.

(C) Sealing off a defective control device by routing air to other control devices.

(D) Shutting down the process producing the particulate emissions.

(2) The owner or operator of a secondary lead smelter shall maintain purchasing records and

manufacturer's specifications of any HEPA filters installed on process fugitive emissions and fugitive

dust stacks demonstrating the filters have been certified by the manufacturer to remove ninety-nine

and ninety-seven hundredths percent (99.97%) of all particles three-tenths (0.3) micrometers and

larger. The records and manufacturer's specifications shall be:

(A) maintained on site for three (3) years; and

(B) available for an additional two (2) years.

(d) If the owner or operator of a secondary lead smelter uses a wet scrubber to control particulate

matter and metal hazardous air pollutant emissions from a process vent to demonstrate continuous

compliance with the emission standards, the owner or operator of a secondary lead smelter must monitor

and record the pressure drop and water flow rate of the wet scrubber during the initial performance or

compliance test conducted to demonstrate compliance with the applicable lead emission limits under

sections 3 through 5 of this rule. Thereafter, the owner or operator of a secondary lead smelter shall:

(1) monitor and record the pressure drop and water flow rate values at least once every hour; and

(2) maintain the pressure drop and water flow rate at levels no lower than thirty percent (30%) below

the pressure drop and water flow rate measured during the initial performance or compliance test.

(e) The owner or operator of a secondary lead smelter shall demonstrate continuous compliance with

the total hydrocarbon and dioxin and furan emission standards. During periods of startup and shutdown,

the requirements of subdivision (4) do not apply. Instead, the owner or operator of a secondary lead

smelter shall demonstrate compliance with the standard for total hydrocarbon by meeting the

requirements of section 5(i) of this rule. The requirements to demonstrate continuous compliance are as

follows:

(1) The owner or operator of a secondary lead smelter shall install, calibrate, maintain, and

continuously operate a device to monitor and record the temperature of the afterburner or furnace

exhaust streams consistent with the requirements for continuous monitoring systems in the July 1,

2012, edition of 40 CFR 63.8*.

(2) Prior to or in conjunction with the initial performance or compliance test to determine compliance

with section 5(d) of this rule, the owner or operator of a secondary lead smelter shall conduct a

performance evaluation for the temperature monitoring device according to the July 1, 2012, edition of

40 CFR 63.8(e)*. The definitions, installation specifications, test procedures, and data reduction

procedures for determining calibration drift, relative accuracy, and reporting described in Performance

Specification 2, 40 CFR 60, Appendix B, sections 2*, 3*, 5*, 7*, 8*, 9*, and 10* must be used to conduct

the evaluation. The temperature monitoring device must meet the following performance and

equipment specifications:

(A) The recorder response range must include zero (0) and one and one-half (1.5) times the average

temperature identified in subdivision (3).

(B) The monitoring system calibration drift must not exceed two percent (2%) of one and one-half

(1.5) times the average temperature identified in subdivision (3).

(C) The monitoring system relative accuracy must not exceed twenty percent (20%).

(D) The reference method must be a National Institute of Standards and Technology calibrated

reference thermocouple-potentiometer system or an alternate reference method, subject to the

approval of U.S. EPA.

(3) The owner or operator of a secondary lead smelter shall monitor and record the temperature of the

afterburner or the furnace exhaust streams every fifteen (15) minutes during the initial performance or

compliance test for total hydrocarbons and dioxins and furans and determine an arithmetic average

for the recorded temperature measurements.

(4) To demonstrate continuous compliance with the standards for total hydrocarbons and dioxins and

furans, the owner or operator of a secondary lead smelter shall maintain an afterburner or exhaust

temperature so that the average temperature in any three (3) hour period does not fall more than

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 72
twenty-eight (28) degrees Celsius below the average established in subdivision (3).

(f) The owner or operator of a new emission unit subject to the requirements under sections 3 through

5 of this rule shall install, calibrate, maintain, and operate a CEMS for measuring lead emissions. In

addition to the requirements for CEMS in the July 1, 2012, edition of 40 CFR 63.8(c) that are referenced in

section 1(d) of this rule, the owner or operator of a secondary lead smelter shall comply with the

requirements for CEMS specified in subsection (h) and the following requirements:

(1) The owner or operator of a new emission unit subject to the emission limits for lead compounds

under sections 3 through 5 of this rule shall install a CEMS for measuring lead emissions within one

hundred eighty (180) days of promulgation by U.S. EPA of performance specifications for lead CEMS.

(2) Prior to one hundred eighty (180) days after U.S. EPA promulgates performance specifications for

CEMS used to measure lead concentrations, the owner or operator of a secondary lead smelter shall

use the procedure described in section 11(a)(1) of this rule to determine compliance.

(3) Vents from control devices that serve only to control emissions from buildings containing

lead-bearing materials are exempt from the requirement to install a CEMS for measuring lead

emissions.

(g) If a CEMS is used to measure lead emissions, the owner or operator of a secondary lead smelter

shall install a CEMS with a sensor in a location that provides representative measurement of the exhaust

gas flow rate at the sampling location of the CEMS used to measure lead emissions, taking into account

the manufacturer's recommendations. The flow rate sensor is that portion of the system that senses the

volumetric flow rate and generates an output proportional to that flow rate. The owner or operator of a

secondary lead smelter shall comply with the following requirements:

(1) The CEMS shall be designed to measure the exhaust gas flow rate over a range that extends from a

value of at least twenty percent (20%) less than the lowest expected exhaust flow rate to a value of at

least twenty percent (20%) greater than the highest expected exhaust gas flow rate.

(2) The CEMS shall be equipped with a data acquisition and recording system that is capable of

recording values over the entire range specified in subdivision (1).

(3) The owner or operator of a secondary lead smelter shall perform an initial relative accuracy test of

the CEMS in accordance with the applicable performance specification in 40 CFR 60, Appendix B*.

(4) The owner or operator of a secondary lead smelter shall operate the CEMS and record data during

all periods of operation of the affected emission unit including periods of startup, shutdown, and

malfunction, except for periods of monitoring system malfunctions, repairs associated with

monitoring system malfunctions, and required monitoring system quality assurance or quality control

activities including, as applicable, calibration checks and required zero and span adjustments.

(5) If the owner or operator of a secondary lead smelter uses a CEMS to measure lead emissions, the

owner or operator of a secondary lead smelter shall calculate the average lead concentration and flow

rate monthly to determine compliance with sections 3 through 5 of this rule.

(6) When the CEMS is unable to provide quality assured data, the following requirements apply:

(A) When data are not available for periods of up to forty-eight (48) hours, the highest recorded

hourly emissions rate from the previous twenty-four (24) hours shall be used.

(B) When data are not available for forty-eight (48) or more hours, the maximum daily emissions rate

based on the previous thirty (30) days shall be used.

*These documents are incorporated by reference. Copies may be obtained from the Government

Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and

copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana

Government Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-10; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-11 Compliance testing

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 11. (a) Following the initial performance or compliance test to demonstrate compliance with the

lead emission limits specified in sections 3 through 5 of this rule, the owner or operator of a secondary

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 73
lead smelter shall conduct performance tests for lead compounds in accordance with the following

schedule:

(1) Conduct an annual performance test for lead compounds from each process vent, no later than

twelve (12) calendar months following the previous compliance test, unless the owner or operator of a

secondary lead smelter installs and operates a CEMS meeting the requirements of the July 1, 2012,

edition of 40 CFR 63.8*.

(2) If an annual compliance test demonstrates that a process vent emitted lead compounds at

one-tenth (0.1) milligram of lead per dry standard cubic meter or less during the time of the annual

compliance test, the owner or operator of a secondary lead smelter may submit a written request to

the U.S. EPA applying for an extension of up to twenty-four (24) calendar months from the previous

compliance test to conduct the next compliance test for lead compounds.

(b) The owner or operator of a secondary lead smelter that vents fugitive dust shall:

(1) conduct an initial compliance test only; and

(2) not be required to conduct testing on an annual or biennial basis.

Nothing in this subsection shall prohibit the department from requesting a compliance test in accordance

with 326 IAC 2-1.1-11.

(c) Test notification and reporting shall be conducted in compliance with 326 IAC 3-6.

(d) Following the initial performance or compliance test to demonstrate compliance with the total

hydrocarbon emission limits in section 5(d) of this rule, the owner or operator of a secondary lead

smelter shall conduct performance tests for total hydrocarbons emissions in accordance with the

following schedule:

(1) Conduct an annual performance test for total hydrocarbon emissions from each process vent that

has established limits for total hydrocarbons, no later than twelve (12) calendar months following the

previous compliance test, unless the owner or operator of a secondary lead smelter installs and

operates a CEMS meeting the requirements of the July 1, 2012, edition of 40 CFR 63.8*.

(2) If an annual compliance test demonstrates that a process vent emitted total hydrocarbons at less

than fifty percent (50%) of the allowable limit during the time of the annual compliance test, the owner

or operator of a secondary lead smelter may submit a written request to U.S. EPA applying for an

extension of up to twenty-four (24) calendar months from the previous compliance test to conduct the

next compliance test for total hydrocarbons.

(e) Following the initial performance or compliance test to demonstrate compliance with the dioxin and

furan emission limits specified in section 5(d) of this rule, the owner or operator of a secondary lead

smelter shall conduct a performance test for dioxin and furan emissions from each process vent that has

established limits for dioxins and furans at least once every six (6) years following the previous

compliance test.

(f) The owner or operator of a secondary lead smelter shall conduct the performance tests specified in

subsections (a), (d), and (e) under maximum representative operating conditions for the process. During

the performance test, the owner or operator of a secondary lead smelter may operate the control device

at maximum or minimum representative operating conditions for monitored control device parameters,

whichever results in a lower emission reduction. Upon request, the owner or operator of a secondary lead

smelter shall make available to the department any records necessary to determine the conditions of

performance tests.

*This document is incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center

North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-11; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-12 Compliance testing methods

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 74
Affected: IC 13-15; IC 13-17

Sec. 12. (a) The owner or operator of a secondary lead smelter shall use the following test methods to

determine compliance with the emission standards for lead compounds:

(1) 40 CFR 60, Appendix A-1, Method 1* to select the sampling port location and the number of

traverse points.

(2) 40 CFR 60, Appendix A-1, Method 2* or 40 CFR 60, Appendix A-3, Method 5D, Section 8.3* for

positive pressure fabric filters, to measure volumetric flow rate.

(3) 40 CFR 60, Appendix A-2, Method 3*, 40 CFR 60, Appendix A-2, Method 3A*, or 40 CFR 60, Appendix

A-2, Method 3B* to determine the dry molecular weight of the stack gas.

(4) 40 CFR 60, Appendix A-3, Method 4* to determine moisture content of the stack gas.

(5) 40 CFR 60, Appendix A-8, Method 12* or 40 CFR 60, Appendix A-8, Method 29* to determine

compliance with the lead compound emission standards. The minimum sample volume must be two

(2.0) dry standard cubic meters (seventy (70) dry standard cubic feet) for each run. The owner or

operator of a secondary lead smelter shall perform three (3) test runs and determine compliance using

the average of the three (3) runs.

(b) The owner or operator of a secondary lead smelter shall use the following test methods to

determine compliance with the emission standards for total hydrocarbons:

(1) 40 CFR 60, Appendix A-1, Method 1* to select the sampling port location and number of traverse

points.

(2) The Single Point Integrated Sampling and Analytical Procedure in 40 CFR 60, Appendix A, Method

3B* to measure the carbon dioxide content of the stack gases when using either 40 CFR 60, Appendix

A-2, Method 3A* or 40 CFR 60, Appendix A-2, Method 3B*.

(3) 40 CFR 60, Appendix A-3, Method 4* to measure moisture content of the stack gases.

(4) 40 CFR 60, Appendix A-7, Method 25A* to measure total hydrocarbon emissions. The minimum

sampling time must be one (1) hour for each run. The owner or operator of a secondary lead smelter

shall perform a minimum of three (3) test runs. The owner or operator of a secondary lead smelter

shall calculate a one (1) hour average total hydrocarbons concentration for each run and use the

average of the three (3) one (1) hour averages to determine compliance.

(c) The owner or operator of a secondary lead smelter shall correct the measured total hydrocarbon

concentrations to four percent (4%) carbon dioxide, specified as follows:

(1) If the measured percent carbon dioxide is greater than four-tenths of one percent (0.4%) in each

compliance test, the owner or operator of a secondary lead smelter shall determine the correction

factor using the following equation:

Where: F = Correction factor (no units).

CO2= Percent carbon dioxide measured using 40 CFR 60, Appendix A-2, Method

3A* or 40 CFR 60, Appendix A-2, Method 3B*, where the measured carbon

dioxide is greater than four-tenths of one percent (0.4%).

(2) If the measured percent carbon dioxide is equal to or less than four-tenths of one percent (0.4%),

the owner or operator of a secondary lead smelter shall use a correction factor (F) of ten (10).

(3) The owner or operator of a secondary lead smelter shall determine the corrected total

hydrocarbons concentration by multiplying the measured total hydrocarbons concentration by the

correction factor (F) determined for each compliance test.

(d) The owner or operator of a secondary lead smelter shall use the following test methods to

determine compliance with the emission standards for dioxins and furans:

(1) 40 CFR 60, Appendix A-1, Method 1* to select the sampling port location and the number of

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 75
traverse points.

(2) 40 CFR 60, Appendix A-1, Method 2* or 40 CFR 60, Appendix A-3, Method 5D, Section 8.3* for

positive pressure fabric filters to measure volumetric flow rate.

(3) 40 CFR 60, Appendix A-2, Method 3A* or 40 CFR 60, Appendix A-2, Method 3B* to determine the

oxygen and carbon dioxide concentrations of the stack gas.

(4) 40 CFR 60, Appendix A-3, Method 4* to determine moisture content of the stack gas.

(5) 40 CFR 60, Appendix A-7, Method 23* to determine the dioxins and furans concentration.

(e) The owner or operator of a secondary lead smelter shall determine the dioxins and furans toxic

equivalency through the following procedures:

(1) Measure the concentration of each dioxins and furans congener shown in the following table using

40 CFR 60, Appendix A-7, Method 23*:

Dioxin/furan congener Toxic equivalency factor (TEQ)

2,3,7,8-tetrachlorinated dibenzo-p-dioxin 1

1,2,3,7,8-pentachlorinated dibenzo-p-dioxin 0.5

1,2,3,4,7,8-hexachlorinated dibenzo-p-dioxin 0.1

1,2,3,7,8,9- hexachlorinated dibenzo-p-dioxin 0.1

1,2,3,6,7,8- hexachlorinated dibenzo-p-dioxin 0.1

1,2,3,4,6,7,8-heptachlorinated dibenzo-p-dioxin 0.01

Octachlorinated dibenzo-p-dioxin 0.001

2,3,7,8-tetrachlorinated dibenzofuran 0.1

2,3,4,7,8-pentachlorinated dibenzofuran 0.05

1,2,3,7,8-pentachlorinated dibenzofuran 0.5

1,2,3,4,7,8-hexachlorinated dibenzofuran 0.1

1,2,3,6,7,8-hexachlorinated dibenzofuran 0.1

1,2,3,7,8,9-hexachlorinated dibenzofuran 0.1

(2) Correct the concentration of dioxins and furans in terms of toxic equivalency to seven percent (7%)

oxygen using the following equation:

Where: Cadj = Dioxins and furans concentration adjusted to seven percent (7%)

oxygen.

Cmeas= Dioxins and furans concentration measured in nanograms per dry

standard cubic meter.

(20.9-7) = Twenty and nine-tenths percent (20.9%) oxygen minus seven percent

(7%) oxygen (defined oxygen correction basis).

20.9 = Percent of oxygen concentration in air.

%O2= Percent of oxygen concentration measured on a dry basis.

(3) For each dioxins and furans congener measured as specified in subdivisions (1) and (2), multiply

the congener concentration by its corresponding toxic equivalency factor.

(4) Sum the values calculated as specified in subdivision (3) to obtain the total concentration of

dioxins and furans emitted in terms of toxic equivalency.

*These documents are incorporated by reference. Copies may be obtained from the Government

Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and

copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana

Government Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-12; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 76
326 IAC 20-13.1-13 Notification requirements

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 13. (a) The owner or operator of a secondary lead smelter shall comply with all of the notification

requirements of the July 1, 2012, edition of 40 CFR 63.9*.

(b) The owner or operator of a secondary lead smelter shall submit the fugitive dust control standard

operating procedures manual required under section 8 of this rule and the standard operating procedures

manual for baghouses required under section 9 of this rule to the department along with a notification

that the owner or operator of a secondary lead smelter is seeking review and approval of these plans and

procedures. The owner or operator of a secondary lead smelter shall submit this notification no later than

the effective date of this rule.

(c) For the owner or operator of a secondary lead smelter that commences construction or

reconstruction after January 5, 2012, and starts up on or after the effective date of this rule the owner or

operator of a secondary lead smelter shall submit this notification on or before one hundred eighty (180)

days before startup of the constructed or reconstructed secondary lead smelter.

(d) For an affected source that has received a construction permit from the department on or before

January 5, 2012, the owner or operator of a secondary lead smelter shall submit this notification no later

than January 7, 2014.

*This document is incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center

North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-13; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-14 Record keeping and reporting requirements

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 14. (a) The owner or operator of a secondary lead smelter shall comply with all of the record

keeping and reporting requirements specified in the July 1, 2012, edition of 40 CFR 63.10* that are

referenced in section 1(d) of this rule. Records shall be:

(1) maintained in a form suitable and readily available for expeditious review, in accordance with the

July 1, 2012, edition of 40 CFR 63.10(b)(1)*; and

(2) kept on site for at least two (2) years after the date of occurrence, measurement, maintenance,

corrective action, report, or record, in accordance with the July 1, 2012, edition of 40 CFR 63.10(b)(1)*.

(b) The standard operating procedure manuals required in sections 8 and 9 of this rule must be

submitted to the department in electronic format for review and approval of the initial submittal and

whenever an update is made to the procedures.

(c) The owner or operator of a secondary lead smelter shall maintain for a period of five (5) years the

following records:

(1) Electronic records of the bag leak detection system output.

(2) An identification of the date and time of any bag leak detection system alarms.

(3) The time that procedures were initiated to determine the cause of any bag leak detection system

alarm.

(4) The cause of any bag leak detection system alarm.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 77
(5) An explanation of the corrective actions taken in response to any bag leak detection system

alarms.

(6) The date and time the cause of any bag leak detection system alarms was corrected.

(7) All records of inspections and maintenance activities required in section 9(f) of this rule as part of

the practices described in the standard operating procedures manual for baghouses required under

section 9(d) of this rule.

(8) Electronic records of the pressure drop and water flow rate values for wet scrubbers used to

control metal hazardous air pollutant emissions from process vents as required in section 10(d) of this

rule.

(9) Electronic records of the output from the continuous temperature monitor required in section 10(e)

of this rule, an identification of periods when the three (3) hour average temperature fell below the

minimum temperature established under section 10(e)(4) of this rule, and an explanation of the

corrective action taken.

(10) Electronic records of the continuous pressure monitors for total enclosures required in section 7

of this rule, and an identification of periods when the pressure was not maintained as required in

section 6(c)(4) of this rule.

(11) Records of any time periods power was lost to the continuous pressure monitors for total

enclosures required in section 7 of this rule and records of loss of power to the air handling system

maintaining negative pressure on total enclosures.

(12) Records of the inspections of total enclosures required in section 6(c)(6) of this rule.

(13) Records of all cleaning and inspections required as part of the practices described in the standard

operating procedures manual required under section 8 of this rule.

(14) Electronic records of the output of any CEMS installed to monitor lead emissions meeting the

requirements in section 10(g) of this rule.

(15) Records of the occurrence and duration of each malfunction of operation or process equipment or

the air pollution control equipment and monitoring equipment.

(16) Records of actions taken during periods of malfunction to minimize emissions in accordance with

section 5(h) of this rule, including corrective actions to restore malfunctioning process and air

pollution control and monitoring equipment to its normal or usual manner of operation.

(17) Records of any periods of startup or shutdown of a furnace and actions taken to minimize

emissions during that period in accordance with section 5(i) of this rule.

(d) The owner or operator of a secondary lead smelter shall comply with all of the reporting

requirements specified in the July 1, 2012, edition of 40 CFR 63.10* in section 1(d) of this rule. The owner

or operator of a secondary lead smelter shall also comply with the following requirements:

(1) The owner or operator of a secondary lead smelter shall submit reports no less frequently than

specified under the July 1, 2012, edition of 40 CFR 63.10(e)(3)*.

(2) Once a violation of the standard or excess emissions is reported, the owner or operator of a

secondary lead smelter must follow the reporting format required under the July 1, 2012, edition of 40

CFR 63.10(e)(3)* until a request to reduce reporting frequency is approved by the department.

(e) In addition to the information required under the applicable sections of the July 1, 2012, edition of

40 CFR 63.10* in section 1(d) of this rule, the owner or operator of a secondary lead smelter shall include

the following information in the reports required under subsection (d):

(1) Records of the concentration of lead in each process vent, and records of the rolling twelve (12)

month flow-weighted average concentration of lead compounds in vent gases calculated monthly as

required in section 5(b) of this rule, except during the first year when the concentration is calculated

using the method described in section 5(b)(3) of this rule.

(2) Records of the concentration of total hydrocarbon and dioxins and furans in each process vent that

has established limits for total hydrocarbon and dioxins and furans as required in section 5(d) of this

rule.

(3) Records of all periods when monitoring using a CEMS for lead or total hydrocarbon was not in

compliance with applicable limits.

(4) Records of all alarms from the bag leak detection system specified in section 9 of this rule.

(5) A description of the procedures taken following each bag leak detection system alarm in

accordance with section 9(a)(2) and 9(a)(3) [sic] of this rule.

(6) A summary of the records maintained as part of the practices described in the standard operating

procedures manual for baghouses required under section 9 of this rule, including an explanation of

the periods when the procedures were not followed and the corrective actions taken.

(7) An identification of the periods when the pressure drop and water flow rate of wet scrubbers used

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 78
to control process vents dropped below the levels established in section 8 of this rule, and an

explanation of the corrective actions taken.

(8) Records of the temperature monitor output, in three (3) hour block averages, for those periods

when the temperature monitored in accordance with section 10(e) of this rule fell below the level

established in section 10(e)(4) of this rule.

(9) Certification that the plastic separation process for battery breakers required in section 5(j) of this

rule was operated at all times the battery breaker was in service.

(10) Records of periods when the pressure was not maintained as required in section 6(c)(4) of this

rule or power was lost to the continuous pressure monitoring system as required in section 7 of this

rule.

(11) If a malfunction occurred during the reporting period, the report must include the number,

duration, and a brief description for each type of malfunction that occurred during the reporting period

and caused or may have caused any applicable emissions limitation to be exceeded. The report must

also include a description of actions taken during a malfunction of an affected emission unit to

minimize emissions in accordance with section 5(h) of this rule, including actions taken to correct a

malfunction.

(12) A summary of the fugitive dust control measures performed during the required reporting period,

including an explanation of the periods when the procedures outlined in the standard operating

procedures manual in accordance with section 8 of this rule were not followed and the corrective

actions taken. The reports must not contain copies of the daily records required to demonstrate

compliance with the requirements of the standard operating procedures manuals required under

section 8 of this rule.

(13) Records of any periods of startup or shutdown of a furnace including an explanation of the

periods when the procedures required in section 5(i) of this rule were not followed and the corrective

actions taken.

(14) The owner or operator of a secondary lead smelter shall submit records as follows:

(A) As of the effective date of this rule, and within sixty (60) days after the date of completing each

performance test, as defined in the July 1, 2012, edition of 40 CFR 63.2*, the owner or operator of a

secondary lead smelter shall submit performance test data, except opacity data, electronically to

U.S. EPA's Central Data Exchange by using the U.S. EPA's Electronic Reporting Tool. Only data

collected using test methods compatible with the U.S. EPA's Electronic Reporting Tool are subject

to this requirement to be submitted electronically into U.S. EPA's WebFIRE database.

(B) Within sixty (60) days after the date of completing each CEMS performance evaluation test, as

defined in 40 CFR 63.2* and required by this rule, the owner or operator a secondary lead smelter

shall submit the relative accuracy test audit data electronically in to U.S. EPA's Central Data

Exchange by using the U.S. EPA's Electronic Reporting Tool as mentioned in clause (A). Only data

collected using test methods compatible with the U.S. EPA's Electronic Reporting Tool are subject

to the requirement to be submitted electronically into U.S. EPA's WebFIRE database.

(C) All reports required by this rule not subject to the requirements in clauses (A) and (B) must be

sent to U.S. EPA at the appropriate address listed in the July 1, 2012, edition of 40 CFR 63.13*. U.S.

EPA or the department may request a report in any form suitable for the specific case. U.S. EPA

retains the right to require submittal of reports subject to clauses (A) and (B) in paper format.

*These documents are incorporated by reference. Copies may be obtained from the Government

Printing Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and

copying at the Indiana Department of Environmental Management, Office of Air Quality, Indiana

Government Center North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-14; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

326 IAC 20-13.1-15 Affirmative defense to civil penalties for exceedance of emissions limit during

malfunction

Authority: IC 13-14-8; IC 13-17-3-4; IC 13-17-3-11

Affected: IC 13-15; IC 13-17

Sec. 15. (a) In response to an action to enforce the standards set forth in this rule, the owner or

operator of a secondary lead smelter may assert an affirmative defense to a claim for civil penalties for

exceedances of the standards that are caused by malfunction, as defined in the July 1, 2012, edition of 40

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 79
CFR 63.2*. Appropriate penalties may be assessed if the owner or operator of a secondary lead smelter

fails to meet its burden of proving all of the requirements in the affirmative defense. The affirmative

defense shall not be available for claims for injunctive relief.

(b) To establish the affirmative defense in any action to enforce the standards set forth in this rule, the

owner or operator of a secondary lead smelter must timely meet the notification requirements of

subsection (c), and shall prove by a preponderance of evidence the following:

(1) The excess emissions:

(A) were caused by a sudden, infrequent, and unavoidable failure of air pollution control and

monitoring equipment, process equipment, or a process to operate in a normal or usual manner;

(B) could not have been prevented through careful planning, proper design or better operation and

maintenance practices;

(C) did not stem from any activity or event that could have been foreseen and avoided, or planned

for; and

(D) were not part of a recurring pattern indicative of inadequate design, operation, or maintenance.

(2) Repairs were made as expeditiously as possible when the applicable emission limitations were

being exceeded. Off-shift and overtime labor were used, to the extent practicable to make these

repairs.

(3) The frequency, amount, and duration of the excess emissions, including any bypass, were

minimized to the maximum extent practicable during periods of the emissions.

(4) If the excess emissions resulted from a bypass of control equipment or a process, then the bypass

was unavoidable to prevent loss of life, personal injury, or severe property damage.

(5) All possible steps were taken to minimize the impact of the excess emissions on ambient air

quality, the environment, and human health.

(6) All emissions monitoring and control systems were kept in operation if at all possible, consistent

with safety and good air pollution control practices.

(7) All of the actions in response to the excess emissions were documented by properly signed,

contemporaneous operating logs.

(8) At all times, the affected emission unit was operated in a manner consistent with good practices for

minimizing emissions.

(9) A written root cause analysis has been prepared, the purpose of which is to determine, correct, and

eliminate the primary causes of the malfunction and the excess emissions resulting from the

malfunction event at issue. The analysis shall also specify, using best monitoring methods and

engineering judgment, the amount of excess emissions that were the result of the malfunction.

(c) The owner or operator of the affected emission unit experiencing an exceedance of its emissions

limit during a malfunction shall notify the department by telephone or facsimile transmission as soon as

possible, but no later than two (2) business days after the initial occurrence of the malfunction, that it

wishes to avail itself of an affirmative defense to civil penalties for that malfunction. The owner or

operator of a secondary lead smelter seeking to assert an affirmative defense shall also submit a written

report to the department within forty-five (45) days of the initial occurrence of the exceedance of the

standard in this rule to demonstrate, with all necessary supporting documentation, that it has met the

requirements set forth in subsection (b). The owner or operator of a secondary lead smelter may seek an

extension of this deadline for up to thirty (30) additional days by submitting a written request to the

department before the expiration of the forty-five (45) day period. Until a request for an extension has

been approved by the department, the owner or operator of a secondary lead smelter is subject to the

requirement to submit the report within forty-five (45) days of the initial occurrence of the exceedance.

*This document is incorporated by reference. Copies may be obtained from the Government Printing

Office, 732 North Capitol Street NW, Washington, D.C. 20401 or are available for review and copying at the

Indiana Department of Environmental Management, Office of Air Quality, Indiana Government Center

North, Tenth Floor, 100 North Senate Avenue, Indianapolis, Indiana 46204.

(Air Pollution Control Division; 326 IAC 20-13.1-15; filed Jan 30, 2013, 12:34 p.m.: 20130227-IR-326110774FRA)

SECTION 106. 326 IAC 20-13-3 IS REPEALED.

SECTION 107. THE FOLLOWING ARE REPEALED: 326 IAC 20-13-1; 326 IAC 20-13-2; 326 IAC 20-13-4;

326 IAC 20-13-5; 326 IAC 20-13-6; 326 IAC 20-13-7; 326 IAC 20-13-8; 326 IAC 20-13-9.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 80
SECTION 108. SECTION 106 of this document takes effect October 1, 2013.

SECTION 109. SECTION 107 of this document takes effect January 6, 2014.

LSA Document #11-774(F)

Proposed Rule: 20120822-IR-326110774PRA

Hearing Held: November 7, 2012

Approved by Attorney General: January 10, 2013

Approved by Governor: Deemed approved by the Governor without signature under IC 4-22-2-34 on January 26,

2013

Filed with Publisher: January 30, 2013, 12:34 p.m.

Documents Incorporated by Reference: 40 CFR 63, Subpart A, July 1, 2012; U.S. EPA Method 1311, Test

Methods for Evaluating Solid Waste, Physical/Chemical Method, U.S. EPA Publication SW-846; Fabric Filter Bag

Leak Detection Guidance, EPA-454/R-98-015

Small Business Regulatory Coordinator: Jessica Faust-Hamblin, IDEM Small Business Regulatory Coordinator,

MC 60-04 IGCS W041, 100 North Senate Avenue, Indianapolis, IN 46204-2251, (317) 232-8172 or (800)

988-7901, ctap@idem.in.gov

Small Business Assistance Program Ombudsman: Brad Baughn, IDEM Small Business Assistance Program

Ombudsman, MC 50-01 IGCN 1301, 100 North Senate Avenue, Indianapolis, IN 46204-2251, (317) 234-3386 or

(800) 451-6027, bbaughn@idem.in.gov

Posted: 02/27/2013 by Legislative Services Agency

An html version of this document.

Indiana Register

Date: Feb 27,2013 3:16:53PM EST DIN: 20130227-IR-326110774FRA Page 81
This page intentionally left blank. 
Appendix E 

Exide Technologies: 

Fugitive Dust Control Plan
This page intentionally left blank. 
TECHNOLOGIES 

Muncie, Indiana Facility 

FUGITIVE DUST CONTROL PLANStandard Operating Procedures for 

Control of Fugitive Dust Emission Sources 

Per 40 CFR § 63.545 Standards for Fugitive Dust Sources 

Revised- October 2009 

www.erm.com 
TABLE OF CONTENTS ___________ _ 

1.0 INTRODUCTION .....•......................•..................................... 1 

2.0 FUGITIVE DUST CONTROL PROGRAM ............................ 2 

3.0 OPERATION AND MAINTENANCE PROGRAM .•.•.•••••..•. 11 

RGURES ______________________________________ __ 

Figure 1 Facility Drawing 

ATTACHMENTS __________________________________ _ 

Attachment 1 Sweeper Maintenance and Operation Log 

Attachment 2 Quarterly Ventilation Test Points Drawing 

Attachment 3 Operational Controls 

Attachment 4 Venturi Shift Checklist 

Attachment 5 Daily Shift Log 

Attachment 6 Daily Visible Emissions and Operating Parameters Form 

Attachment 7 Baghouse Cell Checklists 

Attachment 8 Scrubber Shift Checklist 

Attachment 9 Hood Shift Checklist 

2 
INTRODUCTION __________________________________ _ 

The Fugitive Dust Control Plan is designed to prevent deterioration of control equipment 

performance and to minimize emissions of lead from fugitive emission points. Potential 

sources of fugitive emissions at secondary lead smelters have been identified by the U.S. 

Environmental Protection Agency (40 CFR Part 63.545) as the following: 

I. Plant Roadways 

II. Battery Breaking Area 

Ill. Furnace Area 

IV. Refinery and Casting Area 

V. Raw Material Storage and Handling Areas 

The program also provides a complete assessment of all operations that have a potential for 

emitting lead into the ambient air. This assessment includes a summary of potentially 

significant lead emission points, operation practices, and controls designed to reduce lead 

emissions. The program also establishes a fabric filter and scrubber maintenance guide and 

inspection schedule. Examples of the equipment operation logs and bag house checklists are 

provided as attachments. 

It is anticipated that this program will be subject to periodic review and, when necessary, 

revision. Modifications to the program and record keeping forms will be made by Exide 

Technologies. Exide Technologies recognizes that effective operation and maintenance and 

fugitive dust programs are necessary to ensure that operations do not produce emissions that 

may adversely impact the public health or environment. 

ERM EXIDE TECHNOLOGIES/63527/0CT 2009 
FUGITIVEDUSTCONTROLPROGRAM. __________________ ___ 

The purpose of the Fugitive Dust Plan (Plan) is to identify the potential sources of fugitive 

lead dust emissions from material handling, storage, and transportation activities during 

operations at the Exide Technologies facility located in Muncie, Indiana and to describe the 

control programs utilized to minimize fugitive emissions. This program is responsive to the 

applicable regulatory requirements in 326 lAC 6-5, 40 CFR Part 63 Subpart X: National 

Emission Standards for Hazardous Air Pollutants from Secondary Lead Smelting, and 

condition E.1.2 of the Title V Operating Permit (for Exide. 

Facility Information 

Name of Facility: Exide Technologies 

Facility Contact Name: Kimberly Davis, Environmental Manager 

Facility Responsible Official: Daniel Henke, Plant Manager 

Facility Location: 2601 West Mount Pleasant Boulevard 

Muncie, Indiana 47302 

Latitude and Longitude: Latitude: 040° 09' 27" 

Longitude: 5° 25' 03" 

Facility Operations Description: Secondary Lead Smelting 

Source Identification 

The following is a list of all processes, operations, and areas which have the potential to emit 

fugitive emissions as specified in 326 lAC 6-5-4 and 40 CFR 63.545: 

ERM 

Plant Roadways 

The plant is comprised of concrete material roadways and parking areas. 

Battery Breaking Area 

The Battery Breaking Area is located inside the Production Building. The following unit 

is located in the Battery Breaking Area: 

• Unit 1- One (1) lead-battery breaker/crusher 

Process and fugitive emission sources related to the Battery Breaking Area include: 

• Trailer unloading activities 

• Battery breaking 

• Material movement/conveyance 

Furnace Area. 

The Furnace Area is located inside the Production Building. The following units are 

located in the Furnace Area: 

• Unit 3- Natural Gas Rotary Dryer 

• Unit 4- Reverberatory Furnace 

2 EXIDE TECHNOLDGIES/63527/0CT 2009 
ERM 

• Unit 5- Blast Furnace (Cupola) 

Processes and fugitive emission sources related to the furnace operations include: 

• Lead taps 

• Slag taps 

• Furnace feed systems 

Refining and Casting Area 

The Refining and Casting Areas and related operations are located inside the 

Production Building. The following units are located in the Refining and Casting 

Areas: 

• Units 6K1-6K3 and Units 6K5-6K12- Eleven (11) natural gas-fired pot furnaces 

• Unit 7- Two (2) lead pig casting machines 

Processes and fugitive emission sources related the refining and casting area areas 

include: 

• Kettle- skimming/filling/mixing 

• Material transfer 

• Casting- blocks and pigs 

Materials Storage and Handling Areas 

The three primary materials storage and handling areas in the Production Building 

include: 

• Battery Breaking Area- Battery Breaking Area 

• Raw Material Storage- Bin Room 

• Processed/Finished Product (blocks and pigs)- Shipping and Receiving 

The lead bearing materials stored in the Bin Room prior to reclamation in the 

Reverberatory and Blast furnaces include: 

• Breaker/Furnace feed 

• Reverberatory Furnace slag 

• Blast Furnace slag 

The material handling operations in the Production Building include: 

• Slag Crusher 

• Strip Casting Machines- two units 

If materials need to be transported or stored outside of the plant building, all such 

materials will be transported or stored by the following methods: 

• Closed containers 

• Temporarily loaded and stored on completely enclosed trailers 

• Securely covered with plastic sheeting or tarpaulin 

• Dump trailers containing slag will have covers/tarps in place 

• Rolloffs will have covers/tarps in place 

Augers are used to convey lead bearing material from the Battery Breaking Area into 

the Bin Room. 

3 EX IDE TECHNOLOGIES/63527/0CT 2009 
Site Map 

The map in Figure 1 details the layout of the facility including: 

• Concrete surfaced parking areas 

• Concrete surfaced driveway areas 

• Material conveyance paths 

• Transfer points 

Vehicular Traffic 

Vehicular traffic on the Exide site consists of the following: 

• Semi-trucks: 20-50 deliveries per day 

· o Delivering lead-acid batteries and lead-bearing materials 

o Delivering bulk materials/liquid oxygen/chemicals/petroleum products 

o Delivering containerized/packaged materials and chemicals 

o Delivering/picking up rolloffs for scrap/trash/waste 

• Delivery trucks: 10-20 deliveries per day 

o Delivering parts/materials/metal stock 

o Delivering compressed gas cylinders 

• Cars and passenger trucks: 50-150 per day 

o Employee parking 

o Contractor parking 

o Visitor parking 

Materials Reclaimed 

ERM 

Spent Lead-Acid Batteries 

The types of batteries handled are spent lead-acid batteries with various uses 

including starting, lighting, and ignition of electrical systems. The sources of the 

batteries include automotive, commercial, industrial, and recreational uses. The spent 

batteries are comprised of three basic components: a liquid electrolyte battery acid 

that contains a solution of approximately 20% sulfuric acid, lead plates with rubber and 

paper separators, and a polypropylene casing. Exide typically recycles approximately 

3.5 million batteries per year. 

Lead-Containing Recyclable Materials 

Two types of lead-bearing materials generated off-site will be received and stored 

temporarily prior to recycling: lead-bearing spent materials being reclaimed and leadbearing scrap metal being reclaimed. The lead-containing recyclable materials will be 

accepted only if the materials contain no free liquids. 

Lead-Bearing Spent Materials Being Reclaimed 

Sources of these lead-bearing spent materials include: 

o Floor sweepings which contain particles of lead 

o Lead-bearing sediment from sump cleanouts in battery manufacturing 

process areas 

o Lead-contaminated clean-up rags, clothing, baghouse bags, scrubber 

sludge, wastewater treatment sludge, and other material. 

4 EXIDE TECHNOLOGIES/63527/0CT 2009 
Exide typically handles 2.5 million pounds of lead-bearing materials per year. 

Lead-Bearing Scrap Metal Being Reclaimed 

The majority of lead-bearing scrap metal is from the battery manufacturing 

process where lead plates are formed and pressed into grids which are then 

pasted onto separators to allow for the creation of individual battery cells. The 

battery manufacturing process produces lead scrap. Lead-bearing scrap is also 

be generated from sources other than the lead-acid battery industry. Exide 

typically handles 16.5 million pounds of lead-bearing scrap metal per year. 

Control Measures 

40 CFR 63.545(c) specifies the control measures for the process operations and areas 

located at a secondary lead smelting facility. The control measures that Exide will follow to 

meet the control requirements as specified under the NESHAP are as follows: 

ERM 

Plant Roadways 

Fugitive lead dust emissions from plant roadways and parking areas will be controlled 

by several different methods. The primary plant roadways and parking areas are 

paved with concrete, an impervious hard material that can be effectively cleaned and 

allow for removal of any fugitive lead dust that potentially could be present. Water 

flushing, wet scrubbing and mechanical sweeping are all utilized to clean the concrete 

surfaced plant roadways and parking areas. All paved areas are swept at least twice 

per day. Records of water flushing and mechanical sweeping will be recorded in the 

Sweeper Maintenance and Operation Log (Attachment 1). These methods will be 

applied daily, except under the following weather-related conditions: 

• Days with rain in excess of 0.01 inch 

• When sand or a simih;u material has been spread on plant roadways to provide 

traction on ice or snow 

• When the temperature is expected to be below 35° F 

During periods of temperature below 35° F and no precipitation, the paved areas will 

be mechanically swept at least twice per day, but water flushing will not be used to 

avoid hazards associated with ice accumulation on roadways. The climatology of the 

area suggests that these cold-weather conditions will occur primarily from December 

to March. 

During periods of temperature below 35° F and snow/ice accumulation, the 

accumulated snow/ice will be moved in to piles. The piles will be positioned on 

impervious surfaces so that the melted snow/ice will be collected and treated through 

the onsite industrial wastewater treatment plant. The treated water is then discharged 

to the sanitary sewer. Mechanical sweeping will not occur on days when snow/ice is 

present on the roadways and parking areas. Water flushing will not be performed 

during these conditions to avoid safety hazards associated with ice accumulation on 

roadways and parking areas. 

5 EXIDE TECHNOLOGIES/63527/0CT 2009 
ERM 

Vehicle speed will be limited to five miles per hour and by virtue of the fact that the 

longest stretch of plant roadway is less than 700 feet long (see Figure 1). This 

represents a defacto control that will further reduce emissions. 

The material storage area (Bin Room in Production Building) is designed so that all 

vehicles and mobile equipment exiting the Bin Room pass across a vehicle wash to 

remove any lead bearing debris from the vehicle wheels and body. A pressure washer 

can utilized to supplement cleaning of vehicles and mobile equipment as well as 

cleaning any equipment, scrap or other items leaving the Bin Room. 

Control of fugitive lead dust emissions from unpaved areas is not necessary and not 

feasible. There is potential for lead bearing material to be carried outside of the plant 

buildings on areas not completely flushed the vehicle wash. This material could be 

· tracked onto roadways and parking · areas by vehicle and mobile equipment traffic 

traveling out of the buildings. The control of these areas is discussed above. The 

perimeter of the paved area will be separated from unpaved areas by curbing to 

minimize the transfer of lead-bearing dust between paved and unpaved areas. 

Battery Breaking Area 

Fugitive dust emissions from the battery breaking operation are conducted entirely 

inside the Production Building. This building is maintained under constant negative 

pressure and is a structure that meets the requirements of 40 CFR 265.1101 (a) and 

(c). The inflow of air at each overhead doorway in the Production Building is measured 

and recorded on a quarterly basis on the Quarterly Ventilation Test Points Drawing. A 

third party contractor performs the monitoring and records the data. The quarterly 

data records are maintained in the CEMS room (Attachment 2). 

A Venturi Scrubber is utilized to capture the emissions from the Battery Breaking Area. 

The Venturi Scrubber is a 40,000 CFM emission control unit as permitted by the 

Indiana Department of Environmental Management (IDEM) Office of Air Quality 

(Operating Permit No. T035-22352-00028). This scrubber is operated and maintained 

in accordance with the facility's Operation and Maintenance Program. 

Furnace Area 

The Reverberatory Furnace and the Blast Furnace (Cupola) are located inside of the 

Production Building. This building is maintained under constant negative pressure and 

is a structure that meets the requirements of 40 CFR 265.1101(a) and (c). The inflow 

of air at each overhead doorway in the Production Building is measured and recorded 

on a quarterly basis on a quarterly basis on the Quarterly Ventilation Test Points 

Drawing. A third party contractor performs the monitoring and records the data. The 

quarterly data records are maintained in the CEMS room (Attachment 2). 

All processes and fugitive emission sources related to furnace operations, including 

the emissions from all lead taps, slag taps and furnace feed systems, are ventilated to 

fabric filter baghouses as permitted by the Office of Air Quality (Operating Permit No. 

T035-22352-00028). These baghouses are operated and maintained in accordance 

with the facility's Operation and Maintenance Program. 

Refining and Casting Area 

6 EXIDE TECHNOLOGIES/63527/0CT 2009 
ERM 

All refining and casting activities are conducted inside of the Production Building. This 

building is maintained under constant negative pressure and is a structure that meets 

the requirements of 40 CFR 265.1101(a) and (c). The inflow of air at each overhead 

doorway in the Production Building is measured and recorded on a quarterly basis on 

a quarterly basis on the Quarterly Ventilation Test Points Drawing. A third party 

contractor performs the monitoring and records the data. The quarterly data records 

are maintained in the CEMS room (Attachment 2). 

All process and fugitive emission sources related to refining and casting, including all 

kettle hoods (Units 6K1-6K3 and 6K5-6K12) and both casting machines, are ventilated 

to a fabric filter baghouse as permitted by the Office of Air Quality (Operating Permit 

No. T035c22352-00028). This baghouse is operated and. maintained in accordance . . 

with the facility's Operation and Maintenance Program. 

Materials Storage and Handling Area- Bag house 

Lead bearing materials are stored in the Bin Room prior to reclamation in the 

Reverberatory and Blast smelting furnaces. The material storage area (Bin Room) is 

located inside the Production Building. This building is maintained under constant 

negative pressure and is a structure that meets the requirements of 40 CFR 

265.1101 (a) and (c). The inflow of air at each overhead doorway in the Production 

Building is measured and recorded on a quarterly basis on a quarterly basis on the 

Quarterly Ventilation Test Points Drawing. A third party contractor performs the 

monitoring and records the data. The quarterly data records are maintained in the 

CEMS room (Attachment 2). · 

Potential fugitive emissions from this area are controlled by a fabric filter baghouse as 

permitted by the Office of Air Quality (Operating Permit No. T035-22352-00028). This 

baghouse is operated and maintained in accordance with the facility's Operation and 

Maintenance Program. 

Materials Storage and Handling Area- Outside Storage 

To minimize fugitive emissions, there will be no outside storage of bulk materials 

containing more than one percent (1%) lead by weight of less than 200-mesh-size 

particles. (Spent batteries may be temporarily stored outside the building if the batterybreaker equipment were to fail.) This would be for accumulation purposes only during 

equipment repair. Also, finished product may be stored outside in the event of an 

emergency. The product will be covered to prevent run-off. Likewise, all such materials 

will be transported or stored in closed containers, completely enclosed trailers, rolloffs 

or securely covered when outside of plant buildings. All loading/unloading of 

hazardous waste, lead bearing raw materials, and processed lead will be done in 

enclosed areas of the plant building which are to be maintained under constant 

negative pressure. This should prevent or minimize the potential release of any fugitive 

emissions to the environment. 

Materials Storage and Handling Area- Material Conveyance 

To minimize fugitive emissions associated with material conveyance, augers 

conveying emission control dust will be inspected daily for visible emissions. If visible 

emissions are observed, the conveyor will be repaired or resealed as required. All 

augers conveying emission control dust will be covered or otherwise completely 

7 EXIDE TECHNOLOGIES/63527/0CT 2009 
enclosed to minimize the potential release of any fugitive emissions. The conveyance 

distances will be minimized for all conveyances of emission control dust. 

Materials Storage and Handling Area- Vehicle Exiting 

The material storage area is also designed so that vehicles exiting the building must 

pass across a manual truck wash to remove any lead bearing debris from the tires and 

vehicle body. To supplement this process, all paved areas of the plant yard are swept 

at least twice per day (pending appropriate weather related conditions). A daily record 

is maintained of all sweeping operations in the Sweeper Maintenance and Operation 

Log (Attachment 1). In addition, all paved areas of the plant yard are washed down at 

least once per day. 

Additional information regarding the co~trol syst~ms y . ~t the Exide ·-

f~~ilitY ' . is included ~s . 

Attachment 3. 

To ensure that the control measures put in place by Exide are operating properly, a 

Preventative Maintenance Plan has been developed. The Preventative Maintenance 

Practices, including inspection and recordkeeping requirements, are included as Attachment 

4. 

Spill Cleanup 

Any spills of lead-bearing material that occur during loading/unloading would be enclosed 

areas of the Production Building. Fugitive lead dust emissions will be controlled inside the 

building as it is maintained under constant negative pressure. If the spilled material is 

batteries then they will be restacked if in good condition and not leaking. If the batteries are 

leaking or otherwise in poor condition they will be palletized or placed in container for 

transport and processing in the Battery Breaker. If the spilled material is debris, paste, 

. emission control dust or other lead-bearing pieces it will be collected and placed into 

containers or piles depending on the volume of spilled material. Spilled material placed in 

containers will be processed through Bin 6 or placed into and mixed into and aggregrate 

furnace feed pile. Excess material remaining on the building floor will be cleaned up to 

minimize the amount of material tracked out of the building onto the paved roadways. The 

lead-bearing material (particles, less than 200 mesh size and 1% by weight) will be 

transported in enclosed containers or wetted down. In this case, there will be no need to 

notify the IDEM of the spill because it occurred in a controlled environment. 

In the event of a spill outside of the plant buildings and on the facility site from outdoor 

material handling, baghouse failure, or spill from auger conveyors, the material will be 

reloaded for transport or removed to the appropriate enclosed storage area as soon as 

possible. If the clean-up activity will take more than one (1) day, IDEM will be notified of the 

incident. The material will be wetted down, if appropriate, to minimize the release of fugitive 

dust emissions. The spill area will be water-flushed and mechanically swept (permitting 

mechanical sweeping units can reach the area) to remove any residual material following the 

clean-up. 

Dust Suppressant Materials 

ERM 8 EXIDE TECHNOLOGIES/63527/0CT 2009 
Exide will utilize water as a dust suppressant on all paved roadways applied daily except 

under specific weather related conditions, as described above. No other dust suppressant 

materials are utilized on-site. Lead bearing materials are stored in the bin room prior to 

reclamation in the smelting furnaces and there is no outside storage of bulk materials 

containing more than one percent (1%) lead by weight of less than 200-mesh-size particles. 

Therefore, there are no aggregate piles stored outdoors that would require dust suppression 

to reduce fugitive dust emissions. 

Particulate Matter Collection and Control Equipment 

ERM 

Plant Roadways 

Fugitive leaddust emissiqnsfrom plant roadways/paved areas are controlled by water 

flushing and mechanical sweeping. All paved areas will be swept at least twice per day. · · ·· · · · · · · · · · · ·· · · · · · 

Battery Breaking Area 

All activities are conducted inside the main smelter building which is maintained under 

constant negative pressure. An emission control hood is located directly above the 

Battery Breaking Area. A Venturi Scrubber is utilized to capture the emissions from 

the Battery Breaking Area. The Venturi Scrubber is a 40,000 CFM emission control 

unit as permitted by the Indiana Department of Environmental Management (IDEM) 

Office of Air Quality (Operating Permit No. T035-22352-00028). This scrubber is 

operated and maintained in accordance with the facility's Operation and Maintenance 

Program. 

Furnace Area 

The Reverberatory Furnace and the Blast Furnace (Cupola) are located inside of the 

main smelter building which is maintained under constant negative pressure. All 

processes and fugitive. emission sources related to furnace operations, including the 

emissions from all lead taps, slag taps and furnace feed systems, are ventilated to 

fabric filter bag houses (Process and Ventilation Bag houses) as permitted by the Office 

of Air Quality (Permit No. T035-22352-00028). These baghouses are operated and 

maintained in accordance with the facility's Operation and Maintenance Program. 

Refining and Casting Area 

All refining and casting activities are conducted inside of the Production Building which 

is maintained under constant negative pressure. All process and fugitive emission 

sources related to refining and casting, including all kettle hoods (Units 6K1-6K3 and 

6K5-6K12) and both casting machines, are ventilated to a fabric filter baghouse 

(Refinery Baghouse) as permitted by the Office of Air Quality (Operating Permit No. 

T035-22352-00028). This baghouse is operated and maintained in accordance with 

the facility's Operation and Maintenance Program. 

Materials Storage and Handling Area 

Lead bearing materials are stored in the Bin Room prior to reclamation in the 

Reverberatory and Blast smelting furnaces. The material storage area (Bin Room) is 

located inside of the Production Building which is maintained under constant negative 

pressure. Potential fugitive emissions from this area are controlled by a fabric filter 

baghouse ( Bin Room Baghouse) as permitted by the Office of Air Quality (Operating 

9 EXIDE TECHNDLOGIES/63527/0CT 2009 
Permit No. T035-22352-00028). This baghouse is operated and maintained in 

accordance with the facility's Operation and Maintenance Program. 

The auger material conveyors are not covered. The augers are operated and 

maintained in accordance with the facility's Operation and Maintenance Program. 

When operating properly, fugitive emissions from the augers entering the Bin Room 

from the Battery Breaking Area are not expected to create fugitive emissions due to 

the material having a variable moisture content level. 

Compliance Schedule 

The initial compliance datefor the requirements of 40 CFR 63.545 was December 23, 1997, 

Exide is in compljance with the requirements for fugitive particulate matter emission control 

measures. 

Record Keeping 

Records to document all control measures and activities required under this Plan shall be 

maintained for a duration of five (5) years. The records must be stored on-site for three (3) 

years and can be moved to off-site storage for the last two (2) years. The following records 

must be maintained by Exide: 

ERM 

• Purchasing records and manufacturer's specifications of all HEPA filters on all 

process fugitive and fugitive dust stacks demonstrating that the HEPA filters meet 

the definition of a HEPA filter as stated in 40 CFR 63.542. 

• Daily records of all mechanical sweeping performed with mechanical sweeper unit 

to control fugitive dust emissions are documented on Attachment 1. 

• Quarterly records of the inflow of air at each doorway in the Production Building are 

· · ·· recorded on Attachment 2. 

10 EXIDE TECHNOLOGIES/63527/0CT 2009 
OPERATION AND MAINTENANCE PROGRAM _______ _ 

The purpose of the Operation and Maintenance Program (O&M Plan) is to detail the 

procedures for inspection, maintenance, bag leak detection and corrective action plans for all 

baghouses (fabric filters) that are used to control process, process fugitive, or fugitive dust 

emissions from the source. The O&M Plan is responsive to the applicable regulatory 

requirements in 40 CFR 63.548. A description of all manufacturing activities and associated 

controls are included as Attachment 3. 

Operation and Maintenance Guide- Fabric Filter Bag houses 

Table 1 presents the operation and maintenance guide for fabric filter baghouses. The table 

details potential operational issues with the fabric filter baghouses, possible causes for the 

operational issues, and potential corrective actions to return the baghouse to proper 

operation. 

T a e bl 1 0 f . 1pera 1on an d M am . t enance G Ul "d e- F b . a nc F"lt I er 8 ag1 h ouses 

Issue . Causes Corrective Action 

Isolate leaking compartment, if allowable without 

Bag leaking upsettinQ system. 

Replace bags. 

Blinded filter Isolate leaking compartment, if allowable without 

Fabric bleed through upsetting system. 

Isolate leaking compartment, if allowable without 

Bag clamps not sealing upsetting system. 

Smooth out cloth under clamp and re-clamp. 

Dirty discharge at stack or 

Check and tighten clamps. 

Broken bag leak detector Failure of seals in joints at Isolate leaking compartment, if allowable without 

upsettinQ system. alarm clean/dirty air connection. Caulk and repair joints. 

Isolate leaking compartment, if allowable without 

upsetting system. 

Insufficient filter cake CheckbaQs 

Allow more dust to build up on bags by cleaning less 

frequently 

Use a pre-coating of dust on bags. 

Bags too porous 

Send bag in for permeability test and review with 

manufacturer. 

Isolate leaking compartment if allowable without 

upsettinQ system. 

Bag cleaning mechanism not Check bag cleaning mechanical mechanisms for 

proper operation operating properly Increase duration of cleaninQ cycle. 

Check bag for blinding. 

Replace baQ. 

Cell isolation damper valve not Check mechanically. 

Check pneumatic system. open/closing Check electric sensor system. High baghouse pressure drop Isolate cell. 

Improper bag tension. Tighten bag. 

Shakedown cell. 

Cleaning time failure Check to see if timer is indexing to all contacts. 

Check output on all terminals. 

Not capable of removing dust Replace bags. from bags 

Incorrect static pressure 

Clean magnehelic lines. 

readings Calibrate magnehelic. 

Replace magnehelic. 

ERM 11 El<IDE TECHNOLOGIES/63527/0CT 2009 
. 

·.··. 

•• 

Change shaking cycle/duration. 

Excessive shaking Review furnace/lead pot operations and change if 

Excessive bag failure necessary to prolong bag life. 

Too much dust Check process operation. 

Cleaning cycle too frequent Slow down cleaning. 

Bag failure/burning Improper system operations Review operations and change to eliminate symptoms. 

Bag material improper for Analyze gas and dust and check with manufacturer. High bag failure chemical composition of gas or Treat with neutralizer before baghouse. decomposition dust 

Operating below acid dew point Increase inlet temperature. 

System not purged after Keep fan running for 5 to 10 minutes to purge exhaust 

shutdown gases from baghouse after process is shut down. 

Wall temperature below dew Raise gas temperature. 

Moisture inbaghouse • point • .. Insulate, if applicable. .. .. . .. 

lower dew point by keeping moisture out of system. 

·.·· .;·· .... Cold spots at structural .> Fully insulate or roast structural mernbers . members 

Screw conveyor undersized Measure houny collection of dust and consult 

High screw conveyor wear manufacturer. 

Conveyor speed too high Slow down speed 

Moisture in baghouse . Add hopper heaters • 

Material bridging in hopper Dust being stored Remove dust continuously 

Hopper slope insufficient Remove or replace hoppers. 

Conveyor opening too small Modify opening. 

Equipment undersized Consult manufacturer. 

Frequent screw conveyor/air Screw conveyor Align conveyor. 

lock failure Check sizing to see that each component is capable of 

Overloading components handling a 100% delivery from the previous 

component. 

High pneumatic conveyor Pneumatic blower too fast Slow down blower. 

Piping undersized Review design and slow blower or increase pipe size. 

wear (soda ash) Elbow radius too short Replace with long radius elbows. 

Pneumatic conveyor pipes Overloading pneumatic Review design 

conveyor plugging (soda ash) Moisture in dust See above. 

Sudden changes in monitored parameters may indicate a problem. For example, the failure 

or partial failure of the cleaning (shaker or pulse-jet) system or moisture generally will cause a 

relatively rapid increase in pressure drop in most systems. While the increase in pressure 

drop cannot by directly correlated to any increase in emissions, the timely identification, 

location, and correction of this problem can minimize operational problems and long-term 

effects on bag life. Although identification and subsequent correction of relatively minor 

problems have little short term impact on fabric life. If minor problems are ignored, they may 

ultimately have a deleterious effect. Thus the operation of a fabric filter baghouse must be 

tracked on a daily basis and any required corrective action taken in an expedient manner. 

Maintenance- Fabric Filter Baqhouses 

Pursuant to 40 CFR 63.548(c), the following inspection and routine maintenance for all dust 

collectors at Exide shall at a minimum include the following: 

• An appropriate method for monitoring cleaning cycles to ensure proper operation. 

• Daily monitoring of pressure drop across each bag house ceiL 

• Daily checks of compressed air supply for pulse-jet baghouses. 

ERM 12 EXIDE TECHNOLOGIES/63527/0CT 2009 
' 

• Weekly confirmation that dust is being removed from hoppers through visual 

inspection, or equivalent means of ensuring the proper function of removal 

mechanisms. 

• Monthly checks of bag cleaning mechanisms for proper functioning through visual 

inspection or equivalent means. 

• Monthly check of bag tension on reverse air and shaker-type baghouses. Such 

checks are not required for shaker-type baghouses using self-tensioning (spring 

loaded) devices. 

• Quarterly confirmation of the physical integrity of the baghouse through visual 

inspection of the bag house interior for air leaks. 

T a bl e 2 M . t f . 

. am enance nspec 1ons 5 h d c e u I e• F b a riC . F'lte I r B h agrouses ·· ..... ·.... .· .. ·.·. 

Inspection Freauencv Comoonent Procedure 

Shift Stack Check exhaust for visible emissions or plume 

discoloration. 

Shift Compressed air system Check system pressure and record- Refinery, Bin Room 

and Rotary Dryer/Kiln Baghouses. · 

Shift Collectors Check and record readings and status on all indicators. 

Shift Auger/screw conveyors Check for operation and proper rotation. Rotary valves 

Shift Dust conveyor systems Check discharge point of systems to ensure that 

collector hoppers are continuously purged. 

Daily Magnehelic Check and record 

Differential pressure at least one (1) time per day. 

Check differential pressure and visually inspect 

Daily Cleaning system compressed and mechanical systems for proper 

operation. 

Daily Fans Monitor and record vibration detector readings (or amp draw) . for all baghouse fans. · · · 

Daily ··Inlet/Outlet Dampers 

Confirmation dampers are operating properly can be 

confirmed by the pressure differential and visual 

inspections 

Weekly Filter Bags Visually confirm that bag tension is correct and adjust if 

required. 

Weekly Baghouse(s) Confirm physical integrity of unit by visually inspecting 

each cell for air leaks and integrity breeches. 

Quarterly Filter Bags Review replacement bag usage and re-bag compartments as 

required. 

Quarterly Baghouse cells Inspect the interior of each baghouse cell for air leaks or 

moisture. 

Quarterly Fans Inspect for wear, material buildup, and corrosion through 

visual inspection or equivalent means. 

Annually Ducts Visually inspect the interior of all ducts for air leaks or 

blockages-repair as required 

Annually Filter bags Visually inspect all filter bags for wear and proper tensionreplace and/or adjust as needed. 

Annually Cell doors Visually inspect and replace worn door gaskets to ensure a 

proper seal. 

Annually Shakers Inspect all shaker type cleaning mechanisms to ensure proper 

operation-repair as needed. 

Annually Pulse-jet cleaning system Inspect pulse-jet cleaning system for refinery and kiln 

baghouse to ensure proper operation-repair as needed. 

Annually Fans, housings, and motors Visually inspect all fans, fan housings and motors for 

deterioration-repair and/or replace as required. 

Annually Screw conveyor and hopper Inspect all screw conveyors and baghouse hoppers for leaks. 

Seal if leaks are present. 

ERM 13 EXIDE TECHNOLOGIES/63527/0CT 2009 
Annual Inspection/Preventive Maintenance- Fabric Filter Bag houses 

During the semi-annual scheduled maintenance rebuilds, bag house personnel will inspect the 

baghouse units for the following: 

At a minimum, a visual inspection will be conducted to include: 

1. The interior of all ducts for air leaks or blockages, 

2. The interior of each baghouse cell for air leaks or moisture, 

3. All filter bags for wear and proper tension, 

4. All gasket material on cell doors to ensure a proper seal, 

5. All shaker type cleaning mechanisms to ensure proper operation, 

6. The pulse-jet cleaning system for the refinery bag house and the rotary dryer bag house 

to ensure proper operation, 

7. All fans, fan housings and motors for apparent deterioration, and 

8. All screw conveyors and baghouse hoppers for leaks .. 

9. Structural integrity of enclosures and partial enclosures including structural steel, sheet 

metal, roofing panels, trim, etc. 

Any deficiencies noted during this inspection will be documented in the baghouse 

maintenance logbook and corrected in a timely manner. 

Beyond routine and preventive maintenance, regimented schedules cannot be established for 

such items as bag (filter) replacement and certain maintenance items. Bag failures tend to 

occur shortly after installation, near the end of a bag's useful life, or when operations or bag 

cleaning varies from normal. A rec;ord of bag failures and replacement is invaluable for 

identifying recurrent problems and identifying when the end of bag -life has beeri reached. 

Initial bag failures usually occur because of installation errors or bag manufacturing defects. 

When new bags are installed, a period with few or no bag failures is normally expected 

unless serious design or operational problems exist. As bags near the end of their useful life, 

the number of failures will increase. 

To help identify the need for wholesale bag replacement, baghouse employees will document 

the specific location of any individual bags replaced during daily (or weekly) inspections on 

the appropriate baghouse cell checklist (Attachment 7). The Environmental Supervisor will 

review these checklists on a quarterly basis to identify any apparent trends. Alarm logs for the 

broken bag detector system will also be utilized. 

To maintain an adequate supply of replacement filter bags, an inventory will be completed 

quarterly. Under normal conditions, a sufficient quantity of filter bags will be maintained onsite to replace one complete cell in each of the following units: 

1. Process baghouse, 

2. Ventilation baghouse, 

3. Rotary Dryer bag house, 

4. Refinery bag house, and 

ERM 14 El<IDE TECHNOLOGJES/63527/0CT 2009 
5. Bin room baghouse. 

leak Detection System- Fabric Filter Baqhouses 

In response to the requirements of the National Emission Standards for Hazardous Air 

Pollutants From Secondary Lead Smelting at 40 CFR Part 63, Subpart X, a broken bag leak 

detection system (BHA, Inc., Model CPM 5000) has been installed in the outlet ducts on the 

baghouses listed below: 

1. Process baghouse 

2. Ventilation baghouse 

3. Rotary Dryer/Kiln baghouse 

4. Refinery bag house 

5. Bin Room baghouse 

In accordance with 40 CFR 63.548 (e), the system is designed to meet the following 

specifications: 

• The bag leak detection system must be certified by the manufacturer to be capable of 

detecting particulate matter emissions at concentrations of 10 milligram per actual 

cubic meter (0.9944 grains per actual cubic foot) or less. 

• The bag leak detection system sensor must provide output of relative particulate 

matter loadings (mg/dscf). 

• The bag leak detection system must be equipped with an alarm system that will alarm 

whenan increase in relative particulate loading is detected over a preset level. 

• The bag leak detection system sh~ll b~. installed andoperatedil) ~ lll!llln~rcol)sist~llt .. 

with available written guidance from the U.S. Environmental Protection Agency, or in 

the absences of such written guidance, the manufacturer's written specifications and 

recommendations for installation, operation, and adjustment of the system. 

• The initial adjustment of the system shall, at a minimum, consist of establishing the 

baseline output by adjusting the sensitivity (range) and the averaging period of the 

device and establishing the alarm set points and the alarm delay time. 

• Following initial adjustment, the owner or operator shall not adjust the sensitivity or 

range, averaging period, alarm set points, or alarm delay time, except as detailed in 

the approved SOP required under paragraph (a) of this section. In no event shall the 

sensitivity be increased by more than 1 00 percent or decreased by more than 50 

percent over a 365 day period unless adjustment follows a complete baghouse 

inspection which demonstrates the bag house is in good operating condition. 

ERM 

• For negative pressure, induced air bag houses, and positive pressure baghouses that 

are discharged to the atmosphere through a stack, the bag leak detector must be 

installed downstream of the bag house and upstream of any wet acid gas scrubber. 

• Where multiple detectors are required, the system's instrumentation and alarm may be 

shared among detectors. 

15 EXIDE TECHNOLOGIES/63527/0CT 2009 
The broken bag leak detector installed in these locations has been certified by the 

manufacturer (BHA Group, Incorporated) to be capable of detecting particulate matter 

emissions at concentrations of 10 milligrams per actual cubic meter (0.0044 grains per actual 

cubic foot) or less. The CPM 5000 is a microprocessor based optical emissions monitoring 

device that measures particulate flow with a beam of light. The movement of particulate 

through the beam causes a variation or attenuation in the intensity of the light received. The 

BHA monitor does not utilize triboelectric or electrodynamic monitoring principles. Each of 

these units will be in continuous operation. The daily operation, calibration and maintenance 

of these units will be in accordance with the manufacturer's recommendations. 

The broken bag leak detector installed in the outlet duct of the Bin Room baghouse is not 

required by the NESHAP Standard. It was installed to provide the same monitoring and 

continuity. on that emission control unit as on the other units. The purpose of the Bin Room 

baghouse is to control dust generated by material storage and material transfer within the 

Production Building. 

Corrective Action Plan 

Pursuant to 63.548(f), a corrective action plan was developed to specify the 

· procedures to be followed in the event of a bag leak detection system alarm. These 

procedures will document the time and cause of the alarm, as well as the corrective 

actions taken to correct the control device malfunction or minimize emissions. 

Baghouse employees will monitor the broken bag detector emission alarm strobes 

during each shift. If an alarm occurs, baghouse employees will take the appropriate 

corrective action within 30 minutes of the alarm. At a minimum, the corrective action 

taken will include one or more of the following: 

1. Check to ensure alarm is not false: Check emissions from the emission points 

for particulates using a glass rod test following an opacity monitor alarm: In the · 

· •· ·· • event the glass rod test does not indicate particulate in the exhaust, then the 

alarm is likely to be a false alarm. If the alarm is false, no further action 

required. If alarm is not false continue with the remaining steps of the 

corrective action plan: 

2. Inspecting the baghouse for air leaks, torn or broken filter elements, or any 

other malfunction that may cause an increase in emissions; 

3. Sealing off defective bags or filter media; 

4. Replacing defective bags or filter media, or otherwise repairing the control 

device; 

5. Sealing off a defective bag house compartment; 

6. Cleaning the bag leak detection system optics or otherwise repairing the leak 

detection system if a false alarm is suspected; and/or 

7. Shutting down the process producing the particulate emissions. 

Baghouse employees will document all corrective action taken including the date and 

time completed in the shift log book (Attachment 5). The time of the initial alarm and 

the identification of the affected unit will be maintained in the computer database for 

the leak detection system. 

Operation and Maintenance Guide- Wet Scrubbers 

ERM 16 EXIDE TECHNOLOGIES/63527/0CT 2009 
Table 3 presents the operation and maintenance guide for a wet scrubber. The table 

provides operational issues with the wet scrubber, possible causes for the operational 

problems, and potential solutions to allow for the wet scrubber to return to proper operation. 

T a bl e 3: 0 >peration and M" amtenance G Ul "d e- W et Scrubbers 

Issue ..... · ·.··· Causes ... ........ ·.. . Corrective Action .. . .... ..... · ... ··· .. 

Particulate in plume (visible) Inadequate liquid to air contact Check liquid feed to scrubber. 

Check process for proper operation. 

Check soda ash feed. • 

Low Pressure drop Loss of liquid or packing Check liquid feed to scrubber. 

Check process for proper operation. 

Check soda ash feed.* 

Holes in scrubber Repair. 

HiQh pressure drop Excessive liquid feed Adiust feed. 

Damper improperly adjusted Adjust damper. 

• •'•·· ····'••<'·.· .... ··.·, ... ·.co. · ... ·. Blockin~ in packing · .·.· · · ·· · Isolate area and clean. ·· · . · .. ; . . . 

Elevated S02 emissions Inadequate air to liquid contact Check liquid feed. 

and reaction Check S02 monitor. 

Check pH control. 

Check soda ash addition. 

Check process operation. 

Correct as required . 

• Process scrubber only 

ERM 17 EXJDE TECHNOLOGIES/63527/0CT 2009 
Maintenance- Wet Scrubbers 

The following table presents the inspection and routine maintenance for all wet scrubbers at 

Ex ide: 

Ta bl e 4: M" amtenance nspections ShdiWS c e u e- et cru bb ers 

Freauencv c Comoonent Procedure 

Shift Stack Check for visible dust or discoloration of plume. 

Shift Liquid flow pumps Check each shift for rotation and motor current 

Shift pH controls Check each shift. 

Daily Pressure differential Check at least (1) time per day. 

Each shut down Internals Check for blockages, broken components. and corrosion. 

*Process system only 

Maintenance- Venturi Scrubber 

The following table presents the inspection and routine maintenance for the Venturi Scrubber 

at Exide: 

T a e bl 5 M . t f ShdiVt"S bb . 

. am enance nspec1ons c e u e- en un cru er 

Freauency Comoonent Procedure 

Shift Stack Check for visible dust or discoloration of plume. 

Shift Liquid flow pumps Check each shift for rotation and motor current 

Daily Pressure differential Check at least (1) lime per day. 

Each shut down Internals Check for blockages, broken components, and corrosion. 

*Process system only 

Attachment 4 provides a detailed daily shift checklist for the operation of the bag houses and 

wet scrubbers. 

ERM 18 EXIDE TECHNOLOGIES/63527/0CT 2009 
£X IDE® 

TECHNOLOGIES 

FIGURE 1 

FACILITY DRAWING 
L 

~~ ,_) ( ) i 

= 1 

·. I I 

! 

' 

/ u ~ I 

:E[J 

L 1n 

I 

~~- ~ I CICl .,._ .- --- -- -- I I ~ . =-21 iii I--~---

"-·-h·-· -· - .,_,_ ----- -- ,_,,. __ ",_~-- __________ ,._,., ----------------, .. ,,_,_,_"_ , __ ... ,,,,,,_ ··- "• ""·'-'""-~····· ---. RLI!I'l&tDBJRIP.I.Ilm '.- : ' "'' -- ····-····"---,-- _, _,., _____ ,_,..- .. ,, ... ____ , ___ " 

------

\ 

r 

I I 

r- h 

oo= 

~ 

LEGEND 

II REFINERY Fl EXIDE • RLS DEUVERIES EX/DE CORPORATIOI . 11!1 BREAKER DELlVERIES IIBINROOMF MUNCIE, INDIA 

• SHIPPING DOCK • BINROOMll METALS DI 

• TOOL ROOM DB.lVERIES • EQUIPMENT . TRAFFIC PATTERNS LAYO • BIN ROOM DELlVERIES ill! SODA ASH D 

D MAINTENANCE DELlVERIES • RAILCARS DRA\.JN TIM DATE l/9/2009 SCALE 1" = 

CHECKED DRA\.JING NO. 

APPROVED 348-320-0013 

L . 
SWEEPER MAINTENANCE AND OPERATION LOG 

SHIFT OPERATOR: DATE: 

MAINTEANCE LOG: 

1. TRUCK ENGINE OIL LEVEL _OK LOW 

2. TRUCK ENGINE COOLANT LEVEL OK LOW -

3. AUXILLARY ENGINE OIL LEVEL OK LOW - 4. AUXILLARY ENGINE AIR CLEANER INDICATOR OK UP - 5. AUXILLARY ENGINE COOLANT LEVEL _OK LOW 

6. HYDRAULIC OIL LEVEL _OK LOW 

7. HOPPER CONDITION OK IF NOT- REPORT - 8. ALL HOPPER DOORS SEALED _YES NO 

9. DUST COLLECTOR PRESSURE RELIEF VALVE _OK IF NOT- REPORT 

10. ALL LIGHTS WORKING __ OK NOT WORKING 

11. PICK-UP HEAD _OK NEEDS REPAIR 

12. VISIBLE LEAKS NO YES -

13. TIRE CONDITION OK IF NOT- REPORT 

14. TRUCK CLEANED AT END OF SHIFT _YES NO 

15. CAB CLEANED AT END OF SHIFT _YES NO 

16. AIR COMPRESSOR OIL LEVEL OK LOW -

OPERATION LOG: 

1. HOURSOFOPERATION TO 

2. PLANT ROADWAYS/PAVED AREAS SWEPT TWICE _YES NO 

IF NO- REASON (E.G. RAIN, SNOW) 

3. PLANT ROADWAYS/PAVED AREAS WASHED _YES NO 

IF NO- REASON (E.G. RAIN, SNOW) 

4. TRUCK WASH OPERATIONAL __ YES NO 

IF NO- CORRECTIVE ACTION TAKEN 

ADDITIONAL SPACE (IF NECESSARY) 
TECHNOLOGIES 

ATTACHMENT 2 

QUARTERLY VENTILATION TEST POINTS 

DRAWING 
OPERATIONAL CONTROLS 

Manufacturing Activities 

All manufacturing activities are conducted inside of the Production Building. The Production 

Building is completely enclosed, under negative pressure, has a concrete floor and solid doors 

at pedestrian and vehicle accesses. This building meets the requirements of 40 CFR 265.1101 

(a) and (c). The indraft at all doorways will be measured and recorded quarterly (see Attachment · 

2). 

Emission FreguencJl 0Qerational OQerational Documentation 

Control Unit Parameter Control 

Process daily bag house maintain Attachment 5- Daily Shift Log 

Bag house inspection temperature proper 

temperature 

range to 

prevent fabric 

deterioration 

Process daily differential pressure maintain Attachment 5- Daily Shift Log 

Bag house inspection proper 

differential 

pressure (2-

10inches 

water) to 

prevent fabric 

deterioration 

Process continuous monitor particulate in maintain Attachment 6- Daily Visible 

Bag house stack emissions broken bag Emissions and Operating 

leak detectors Parameters Form 

Process hourly reading specific gravity Maintain Attachment 8- Scrubber Shift 

Scrubbers proper level Checklist 

specific 

gravity in recirculation 

tanks for 

effectiveness 

in scrubbers 

Process daily differential pressure maintain Attachment 5- Daily Shift Log 

Scrubbers inspection proper 

differential 

pressure (5-

25 inches 

water) 

Process daily liquid flow maintain Attachment 5- Daily Shift Log 

Scrubbers inspection proper amp 

draw on pump 

Process continuous sulfur dioxide levels Maintain Attachment 5- Daily Shift Log 

Scrubber proper liquid 

flow 

Ventilation daily engineering control to Maintain Attachment 9- Hood Shift 

Hoods inspection collect fugitive integrity and Reference to Attachment 5- Daily 

emissions flow at Shift Log 

ventilation 

hoods 

Ventilation daily bag house maintain Attachment 5- Daily Shift Log 

Bag house inspection temperature proper 
temperature 

range to 

prevent fabric 

deterioration 

Ventilation daily differential pressure maintain Attachment 5- Daily Shift Log 

Bag house inspection proper 

differential 

pressure to 

prevent fabric 

deterioration 

Ventilation continuous monitor particulate in maintain Attachment 6- Daily Visible 

Bag house stack emissions broken bag Emissions and Operating 

leak detectors Parameters Form 

Rotary Dryer daily bag house maintain . Attachment 5- Daily Shift Log 

Bag house inspection temperature proper 

temperature 

range to 

prevent fabric 

deterioration 

Rotary Dryer daily differential pressure maintain Attachment 5- Daily Shift Log 

Bag house inspection proper 

differential 

pressure to 

prevent fabric 

deterioration 

Rotary Dryer continuous monitor particulate in maintain Attachment 6- Daily Visible 

Bag house stack emissions broken bag Emissions and Operating 

leak detectors Parameters Form 

Rotary Dryer daily monitor for particulate minimize Attachment 7- Bag house Cell 

Bag house inspection release inside release of Checklist for Kiln/Rotary Dryer 

Enclosure enclosure fugitive dust Bag house 

Rotary Dryer daily inspect integrity of minimize Attachment 7- Bag house Cell 

Bag house inspection structure including release of Checklist for Kiln/Rotary Dryer 

Enclosure doors fuQitive dust Bag house 

Bin Room daily differential pressure maintain Attachment 5- Daily Shift Log 

Bag house inspection proper 

differential 

pressure (2-

10inches 

water) to 

prevent fabric 

deterioration 

Battery Breaker 

Emission Freguencl£ O[!erational Ogerational Documentation 

Control Unit Parameter Control 

Venturi daily differential pressure maintain Attachment 4- Venturi Shift 

Scrubber inspection proper Checklist 

differential 

pressure ( 5-

25inches 

water) 

Venturi daily liquid flow maintain Attachment 4- Venturi Shift 

Scrubber inspection proper amp Checklist 

draw on pump 
Material Storage and Handling 

Emission FreguencJl 011erational 011erational Documentation 

Control Unit Parameter Control 

Bin Room daily differential pressure maintain Attachment 6- Daily Visible 

Bag house inspection proper Emissions and Operating 

differential Parameters Form 

pressure to Attachment 7- Bag house Shift 

prevent fabric Checklist 

deterioration 

Refinery and Casting Area 

Emission FreguencJl 011erational 011erational Documentation 

Control Unit Parameter Control 

Refinery daily bag house maintain Attachment 6- Daily Visible 

Bag house inspection temperature proper Emissions and Operating 

temperature Parameters Form 

range to Attachment 7- Bag house Shift 

prevent fabric Checklist 

deterioration 

Refinery daily differential pressure maintain Attachment 6- Daily Visible 

Bag house inspection proper Emissions and Operating 

differential Parameters Form 

pressure to Attachment 7- Bag house Shift 

prevent fabric Checklist 

deterioration 

Refinery continuous monitor particulate in maintain Attachment 6- Daily Visible 

Bag house stack emissions broken bag Emissions and Operating 

leak detectors Parameters Form 

Ventilation daily engineering control to Maintain Attachment 9- Hood Shift 

Hoods inspection collect fugitive integrity and Reference to Attachment 5- Daily 

emissions flow at Shift Log 

ventilation 

hoods 

Emissions Control Dust Handling and Transfer 

Emission control dust is conveyed through covered/completely enclosed auger conveying 

system to the inside of Production Building. Emission control dust is processed through the 

Reverberatory furnace for reclamation. 

Vehicular Traffic 

All storage and production areas constructed of concrete and enclosed under negative 

pressure. The material storage area (Bin Room in Production Building) is designed so that all 

vehicles and mobile equipment exiting the Bin Room pass across a vehicle wash to remove any 

lead bearing debris from the vehicle wheels and body. A pressure washer can utilized to 

supplement cleaning of vehicles and mobile equipment as well as cleaning any equipment, 

scrap or other items leaving the Bin Room. To supplement this process, all paved areas of the 

plant yard are swept at least twice per day (pending appropriate weather related conditions). A 

daily record is maintained of all sweeping operations in the Sweeper Maintenance and 
Operation Log (Attachment 1). In addition, all paved areas of the plant yard are washed down 

at least once per day. 
TECHNOLOGIES 

ATTACHMENT 4 

VENTURI SHIFT CHECKLIST 
VENTURI SHIFT CHECKLIST 

VENTURI VENTURI 

Flow Reading (gpm) Pump Amp Draw (amps) 

1 < . . · .... ,. · . 1 .· . ··. 

2 2 

3 3 

4 I 

I 

4 I 

5 

I 

5 I 

6 

--··· ._1 -·· ---- ------- ---- ------

6 I --- ------- ------ ' 

7 

I 

7 

I 

8 

I 

8 

I 

NOTES: 
€XI DE® 

TECHNOLOGIES· 

ATTACHMENT 5 

DAILY SHIFT LOG 
Date: _____ _ 

Shift Operator Signature 

Visible Emissions 

Process Temperature (inlet) 

Dust Discharge Functioning? 

Kiln Inlet Temperature 

Screw Conveyor FWlctioning? 

Compressed Air Pressure 

Process - North 

Process - South 

Re:fmery-"-North 

Refmery- South 

Ventilation- North 

Ventilation- South 

Bin Room 

Kiln 

Refmery Ventilation Hood 

Refinery draft/dross lines 

in place & functioning?. 

Refinery draft hoods in 

place & functioning? 

DAILY SHIFT LOG 

Complete atthe beginning of each shift 

Yes No Yes No 

Yes No Yes No 

Yes No Yes No 

If no, describe condition-

__ yes --no 

If no, describe conditionyes no 

Note any items needing attentiOn below or on reverse s1de of form: 

Yes 

Yes No 

Yes No 
Daily Visible Emissions And Operating Parameters Form 

EXIDE TECHNOLOGIES 

MUNCIE, IN 

TITLE V OPERATION PERMIT NO.: T035-22352-00028 

Visible Emissions Air Pollution Pressure Drop Time Observer's 

Control Device Normal Abnormal (in. water) initials 

Bin Room BH 

Ventilation BH N 

s 

North Scrubber • 

. • South Scrubber i 

. 

' • 

N 

,j 

Process BH N/A N/A 

s • 

Refinery BH 

.· I 

Kiln BH ; 

Venturi Scrubber I 

Soda Ash Silos iN/A 

.· 

DATE: ______________ _ 

. Comments- Explain any "Abnormal" 

readings. If none, then write "None" 

... 

2 

. 

---+. 

:} 

: 

.. · 

··· .• 

·.· 

General Comment . .,.·~-------------------------,---,------------

Page 1 of 1 
£X/DE® 

·TECHNOLOGIES.·.·.· 

ATTACHMENT 7 

BAGHOUSE CELL CHECKLISTS 
****DAILY KILN BAGHOUSE CELL CHECKLIST  

DATE: OPERATOR CELL# 

PRESSURE DROP WHILE CELL ISOLATED: 

INLET CLEAN: YES NO -EXPLAIN 

OUTLET DAMPER WORKING: YES NO EXPLAIN 

HOPPER BRIDGING: YES -HOW FAR NO 

ROTARY VALVE RUNNING: YES, --·.-- ·--·.·-NO·- · <-EXPLAIN··· ___ ' ' . . '-'':.-:· . . . ' . < •••..• ;. ·-·.,·,:< ,,,_., 

BAG SEAT TIGHT IN TUBESHEET: YES NO 

BAD BAGS: NO YES -LOCATION 

BLOWPIPE ASSEMBLY: OK YES NO -EXPLAIN 

HOLES IN DUCTWORK: NO YES -EXPLAIN 

PULSE JET AIR PRESSURE: PSI 

BAGS REPLACED: NO YES -LOCATION 

DOES CELL NEED CLEANED: NO YES -ACTION TAKEN 

'' 

000000000 ** *NOTES***- ------ 10 I , . . . , ... , . - .. - - . . - .. . . . ........ ,, ""''""''',--," __ , ____ ... - ·-·· '<"o'·--' -··- • •• ---··· ,., .. ,-o:~·,-.··:-y·•--•'"'"-"'-''·--.-c"'•-••'•• ""··~---·-

9 0 0 0 0 0 0 0 0 0 

8 0 0 0 0 0 0 0 0 0 

7 0 0 0 0 0 0 0 0 0 

6 0 0 0 0 0 0 0 0 0 

5 0 0 0 0 0 0 0 0 0 

4 0 0 0 0 0 0 0 0 0 

3 0 0 0 0 0 0 0 0 0 

2 0 0 0 0 0 0 0 0 0 

1 0 0 0 0 0 0 0 0 0 

A B c D E F G H I 

' .. 

DOOR 

-··-··· ,-,. _ _.,, 
DAILY PROCESS BAG HOUSE CELL CHECKLIST 

DATE: OPERATOR: CELL#: 

PRESSURE DROP WHILE CELL ISOLATED 

INLET DAMPER WORKING YES NO EXPLAIN -

OUTLET DAMPER WORKING YES NO EXPLAIN . ' 

HOPPER BRIDGING YES HOW FAR NO 

.\ 

AUGER RUNNING YES NO EXPLAIN 

8~~ f~'Ns'1of\l8ooo ~Es ... ,,No '~;_,.· .;_-_-,_ . : ..... ·· .. •.' 

LOCATION OF LOOSE BAG 

BAGS DOWN NO YES LOCATION 

BAD BAGS NO · YES LOCATION 

SHAKER ASSEMBLY OK YES NO EXPLAIN -

HOLES IN DUCTWORK NO YES EXPLAIN 

WATER TRAP MT YES NO OILER LEVEL 

BAGS REPLACED NO YES LOCATION 

DOES HOPPER VIBRATOR WORK YES NO EXPLAIN 

DOES CELL NEEDCLEANED YES NO 

·: ' 

NOTES A. B c D E F G H 

'7W" ···-·,--,·-·''~'7'''\f""'''~:·-c···-~-•--•- ' ,o"·"-- • '••-•-;"- ., ,, ' ,,.,_ o-o 0 0 ..... ····o 0 0 0 1 

0 0 0 0 0 0 0 0 2 

0 0 0 0 0 0 0 0 3 

0 0 0 0 0 0 0 0 4 

0 0 0 0 0 0 0 0 5 

0 0 0 0 0 0 0 0 6 

0 0 0 0 0 0 0 0 7 

0 0 0 0 0 0 0 0 8 

0 0 0 0 0 0 0 0 9 

0 0 0 0 0 0 0 0 10 

' 0 0 0 0 0 0 0 0 11 

0 0 0 0 0 0 0 0 12 ',•, 

.. 

0 0 0 0 0 0 0 0 13 

0 0 0 0 0 0 0 0 14 

0 0 0 0 0 0 0 0 15 

DOOR 
DAJL Y REFINERY BAGHOUSE CELL CHECKLIST 

DATE: OPERATOR: CELl#: 

PRESSURE DROP WHILE CELL ISOLATED 

INLEJ DAMPER WORKING YES NO EXPtA!N 

OUTLET DAMPER WORKING YES . NO EXPLAIN 

HOPPER BRIDGING YES HOW FAR NO 

ROTARYVALVERUNNING YES NO· EXPLAIN .. .. . . . ., " .. < ... · .. · . . .... '---- :-:.':'>-' ·.·· ! :. 

. BAG SEATTIGI-iT ATWBESHEET YES NO . 

-····· 

· ..... ··· ... 

BAD BAGS NO YES LOCATION 

BLOWPIPE ASS~BLY Ol< YES NO EXPLAIN 

HOLES IN DUCTWORK NO YES EXPLAIN . 

PULSE JET AIR PRESSURE PSI 

BAGS REPLACED NO YES LOCATION .• 

DOES CELL NEED CLEANED YES NO' 

' 

Nnl'Es A B CD E F G H I J K L M N 0-P ... Q R·· 

- ·····--•······· .. , .. ,-____ ~---- ---·-· ,. ·- --~ . .. .. ···~-- .. ... o· o·o ·a 0 0 o·:o :o o·o--o·-o·•o· 0:•-0: 0:::0 1 .,.,., 

0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 

0 0. 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 

0 0 0 0 0 0 0 0 0 0 0 0 0 0 d 0 0 0 4 .. -· 

0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 5 . 

0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 6 

0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0. 0 7 

0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 3 

0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9 

0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 10 

0 0 o- .o 0 0 0 0 0 0 0 0 ci, 0 0 0 0 0 11 

0 0 0 0 0 C) 0 o. 0 

;,_. -• 

() 0 0 () 0 0 0 e>-fO 12 

...... -- ---~- . . .. .. . -. 

; 

00 13 0 0 0 6 () 0 0 o· 0 o· o· o- o 0 0 0 

.. 0 0 0 0 0 0 0 0 0 0 0 0 0 d 0 0 0 0 14 

0 0 O· 0 0 6 0 0 0 0 0 0 0 0 0 0 0 0 15 -

0 0 0 0 0 0 0 0 0 0 0 0 0. 0 ·o. 0 0 (Y 16 

. DOOR 

t 
DAILY VENT BAGHOUSE CELL CHECKLIST 

DATE: OPERATOR: CELL#: 

PRESSUR~ DROP WHILE CELL ISOLATED 

. INLET DAMPER WORKING Y!=;;;!Sc:...·· __ nNO~ _ __~;EXP~LA~IN:!-----------......o~-------J 

OUTLET DAMPER WORKING YES NO EXPLAIN 

HOPPER BRIDGING YES HOWFAR ., NO 

AUGER RUNNING YES NO EXPLAIN 

. BAG TENSION GOOD YES ·NO LOCATION OF LOOSE BAG 

' .•. . . . • ' •' ,,_ • • .. • " . • .·. •. • • . . • .. . . > .... ····.·-· ... 

LOCATION 

BAD BAGS NO YES LOCATION 

SHAKER ASSEMBLY OK YES . NO EXPLAIN 

HOLES IN DUCiWORK NO YES EXPLAIN ~~~~~=£~~--~~L----S~~-----------------------~---------~ 

WATER TRAP MT YES NO OILER LEVEL 

BAGS REPLACED NO . YES LOCATION 

IDOES CELL NEED CLEANED YES NO 

NOTES ABCDEF GHIJ K L 

t------------'------------1 0 0 0 0 0 0 0 0 0 0 

000000 0000 r---~------------------------~~ 

r----'-'=~~"-='-"';.;;_;....:;;.;....;:;,;c;;;;...:.:=-....;;.c:=..::...:·:...:=. ·:...:·.:....·= ··:...:· -=-··;;_J .. o . o o o o o. o o _ o o 

.·,-. r-~,..--~-~--:--c----'-,..----~-'-'-~---'"~'-'---l 0 0 0 .. 9 ... 0 .Q.,...... Q 0 0 0 

· ·· ·· · · ·· · o o o o o .. o o ·o o o ~-~----:-'-----=------------! 0 0 0 0 0 0 0 0 0 0 0 0 6 

0 0 1 

0 0 2 

0 0 -3 

0 0 4 

0 0 5 

1------..,...-------,---------l 0 0 0 0 0 0 0 0 0 0 0 0 7 

r------·-----'------------l 0 0 0 0 0 0 0 0 0 0 0. 0 8 

r-----'-------·-----------1 0 0 0 0 0 0 0 0 0 0 0 0 9 

t-----.,..-----------'-------1 0 0 0 0 0 ·0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0· t------·----,-----------'----1 0 0 0 0 0 0 0 0 0 0 0 

0 10· 

0 11 . 

0 12 

t------·--------------1 0 0 0 0 0 0 0 0 0 0 0· 

t----...,------------------1 0 0 0 0 0. 0 0 0 0 0 0 

t------·--------------1 o o o o o o o o· o o o r------·------~--------l 0 0 0 0 0 0 0 0 0 0 0 

t----------.,.-------'------l 0 0 0 0 0 0 0 0 0 0 0 

'------'-- ·. __ ._;_ •. --·------------.···-._ .. ·--! 0 0 . 0 0 0 0 0 0 0 0. 0 

I 000000 00000 ~-~~.~ •• C::: •. ,::-;:T:::;.;::. ::::;;''"'?""·C" ..7;' •. ,:::;_,.,..-. ,.-,...,---,----,-~.--.,..--.,..-lo t:l 6 6 (j" () Q Q '"()'(f 0 

f------·--

r------.,.--~--------------1 0 0 0 0 0 0 0 0 0 0 0 

r----------------------1 0 0 0 0 0 0 0 0 0 0 0 

r-----=----------------1 0 0 0 0 0 0 0 0 0 0 0 

000000 00000 

0 13 

0 14 

0 15 

0 16 

0 17 

0 18 

0 19 

0 20 

0 .21 

0 22 

0 :13 

0 24 

DOOR 
 WEEKLY BIN ROOM BAGHOUSE CELL CHECKLIST** ** 

DATE: _____ OPERATOR: ____________ CELL#-______ _ 

PRESSURE DROP WHILE CELL ISOLATED _____ _ 

INLET DAMPER WORKING: YES __ NO __ - EXPLAIN, ___________ _ 

OUTLET DAMPER WORKING: YES NO -EXPLAIN, __________ _ 

HOPPER BRIDGING: YES, _ ____;-HOW FAR. ____ NO __ 

GATHER SCREW RUNNING: YES. __ NO. _ ____;-EXPLAIN, ___________ _ 

BAG'sEATTIGHT IN TUBESHEET: YEs._·_· _ 

BAD BAGS: NO. ___ YES, __ ____.:-LOCATION __________________ _ 

BLOWPIPE ASSEMBLY OK: YES. __ NO. _ ____;-EXPLAIN, ___________ _ 

HOLES IN DUCTWORK: NO. __ YES, __ -EXPLAIN, ________________ _ 

PULSE JET AIR PRESSURE: PSI 

BAGS REPLACED: NO· __ YES, _ ____;-LOCATION. ______________ _ 

DOES CELL NEED CLEANED: NO 

1 

.1 

1 

1 

1 

1 

1 

6 

5 

4 

3 

2 

1 

0 

9 

8 

7 

6 

5 

4 

3 

2 

1 

0 0 0 

0 0 0 - ~ - ·--- ---

0 0 0 ••••-•--;.'-o07•,•-,'-••'·• 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 . -- ... -.. -·-··' ... 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 0 0 0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

0 

YES -ACTION TAKEN 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 • •c'r•'-.·- "~M·•,ro-._ -------~--,, ..... ............. __ • .< ... , •• ~----

"''' ______________ _,,_, ____ ~-- ----- __________ , ___ -

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 0 0 

0 0 0 0 0 0 0 0 0 0 0 .0 0 -·-· -
TECHNOLOGIES 

ATTACHMENT 9 

HOOD SHIFT CHECKLIST 

THE HOOD SHIFT CHECKLIST IS INCLUDED ON THE DAILY SHIFT LOG. 
Appendix F 

Exide Technologies:

Agreed Order Case No. 2008-18144-A
This page intentionally left blank. 
.,. 

IDEM lNDJANA DEPARTjvfENT OF ENVIRONMENTAL J\!lANAGEMENT 

W'e Protect Hoo.iier.i and Our Erwiromnent. 

c!-il 

1986 

,\!itrlwll F nznil'!i, _!r. 

Governor 

j huiiliiS \\". f:,utN{J' 

Commissioner 

October 20, 2009 

100 North Senate Avenue 

Indianapolis. Indiana 46204 

(3"17) 232-8603 

Toll Free (800) 451-6027 

www.idem.IN.gov 

VIA CERTIFIED MAIL 7002 0510 0002 5825 1765 

Mr. Gordon Ulsh, President 

Exide Technologies, Inc. 

13000 Deerfield Parkway. Bldg. 200 

Milton, GA 30004 

Dear Mr. Ulsh: 

Re: Adoption of Agreed Order 

Commissioner, Indiana Department of 

Environmental Management 

v. 

Exicl.e Technologies, Inc. 

Case No. 2008-1 8144-A 

Muncie, Delaware Co. 

This is to inform you that the Agreed Order in the above-referenced case has been 

approved and adopted by the Indiana Department of Environmental Management. A copy of the 

Agreed Order is enclosed. 

Please note the terms of compliance contained in the Agreed Order. The time frames for 

compliance are effective upon your receipt of this COITespondence. Please note that the civil 

penalty is clue within forty-five ( 45) days after the effective elate of the Agreed Order. Payment 

should be made payable to the Environmental Management Special Fund and sent to CashierMail Code 50-IOC, IDEM, I 00 N. Senate Avenue, Indianapolis, Indiana 46204-2251. Please 

include the Case Number on the front of the check. If you have any questions. please contact 

Lynne Sullivan at (317) 233-5521 or via e-mail at lsulliva@idem.in.gov. 

Enclosure 

Sincerely. 

~Cf!py Phil Pen-y, Chief 

Compliance and Enforcement Branch 

Office of Air Quality 

cc: Joseph Acker, Exicle Technologies, Milton. GA 

Frederick Ganster, Exicle Technologies, Reading, PA 

Kimberly Davis, Exicle Technologies, !Vluncie, IN 

Rochelle Marceillars, US EPA, Region 5 

Delaware County Health Depa1iment 

!tynne Sullivan, Compliance and Enforcement Branch, OAQ 

"'Enforcement File 

http://www .IN .gov!iclem 

Reqde,/ Paper @ 
IDEM INDIANA DEPARTMENT OF ENVIRONMENTAL 1\llANAGEMENT 

Jfitche/1 E Dtmiels, Jr. 

Governor 

ThomtU \V Ea_;tcrl)' 

Commissioner 

STATE OF INDIANA 

COUNTY OF MARION 

\XIe Protect Hoo_,iers and Our Enuiromm"'nt. 

) 

) 

) 

100 North Senate Avenue 

Indianapolis, Indiana 46204 

(317) 232-8603 

Toll Free (800) 451-6027 

www.idem.IN gov 

SS: BEFORE THE INDIANA DEPARTMENT OF 

ENVIRONMENTAL MANAGEMENT 

) 

COMMISSIONER OF THE DEPARTMENT ) 

OF ENVIRONMENTAL MANAGEMENT ) 

) 

) 

Complainant, ) 

) 

v. ) 

) 

EXIDE TECHNOLOGIES, INC., ) 

) 

Respondent. ) 

AGREED ORDER 

Case No. 2008-18144-A 

Complainant and Respondent desire to settle and compromise this action without hearing or 

adjudication of any issue of fact or law, and consent to the entry of the toll owing Findings of Fact 

and Order. Pursuant to IC 13-30-3-3, entry into the terms of this Agreed Order does not constitute 

an admission of any violation contained herein. Respondent's entry into this Agreed Order shall 

not constitute a waiver of any defense, legal or equitable, which Respondent may have in any 

future administrative or judicial proceeding, except a proceeding to enforce this order. 

I. FINDINGS OF FACT 

1. Complainant is the Commissioner ("'Complainant") of the hi.diana D<.:partment oC 

Environmental Management ("IDEM"), a department of the State ofindiana created by 

Indiana Code ("IC") 13-13-1-1. 

2. Respondent is Exide Technologies, Inc. ("Respondent"), which owns and operates a 

secondary lead smelting company with Plant J.D. No. 035-00028 located at 2601 West 

Mount Pleasant Boulevard, in Muncie, Delaware County, Indiana ("Site .. ). 

3. IDEM has jurisdiction over the parties and the subject matter of this action. 

4. Pursuant to IC 13-30-3-3, IDEM issued a Notice of Violation ("NOV") on February 20, 

2009 via Certified Mail to: 
E\ick Technologie~. Inc. 

Ca:-:c' :!OOS-181-l-l-A 

Mr. Gordon Ulsh. President 

Exide Technologies. Inc. 

13000 Deerfield Parkway, Bldg . .200 

Alpharetta, GA 30004 

CT Corporation System 

.251 E. Ohio Street. Suite 1100 

Indianapolis. IN 46.204 

5. During an investigation conducted by representati\"CS of IDEM. the follmving violations 

were found: 

a. Pursuant to IC 13-30-2-1. a person may not discharge, emit, cause, allow, or 

threaten to discharge, emit, cause or allow any contaminant or waste into the 

environment in any form that causes or would cause pollution that violates or 

would violate rules, standards, or discharge or emission requirements adopted by 

the approptiate board under the environmental management laws. 

b. 326 lAC 1-3-4 establishes the maximum permissible ambient air quality level for 

lead to be 1.5 micrograms lead per cubic meter of air, averaged over a calendar 

qumier and measured as elemental lead. 

c. Respondent experienced a shoJi duration event (fire in the process dryer) that 

caused ambient lead concentrations from the Site to exceed 1.5 micrograms per 

cubic meter of air averaged over a calendar qumier during the 2nd Qumier of2008, 

in violation of IC 13-30-2-1 and 326 lAC 1-3-4. The average lead emissions for 

that quarter were reported to be 2.33 micrograms per cubic meter. 

6. In recognition of the settlement reached, Respondent waives any right to administrative 

ctndjudicial rc\icw ofthis r\grccd Order. 

II. ORDER 

1. This Agreed Order shall be effective ("'Effective Date'') when it is approved by 

Complainant or Complainant's delegate, and has been received by Respondent. This 

Agreed Order shall have no force or effect until the Effective Date. 

' Respondent shall comply with all applicable federal and state environmental statutes. rules 

and pennits. 

3. By October 15, 2009, Respondent shall construct a total enclosure sheet metal structure 

around the Rotary Dryer Kiln baghouse to minimize the potential release of fugitive lead 

emissions from the Rotary Dryer Kiln baghouse structure. 

4. Respondent shall update its Standard Operating Procedure Manual for Fugitive Dust 

Control by October 31, 2009 to include cleaning and maintenance ofbaghouse enclosures 

as specified by paragraph 3 of this Order, to minimize the potential release of fugitive lead 

emiSSIOI1S. 
Exidc Technologic~. Inc. 

Ca~e == 2008-1 R 1-t-t-.\ 

Page:.: 3 

5. By October 31. 2009. Respondent shall replace the existing I 35 n enclosecl/co\ creel auger 

at the Ventilation baghouse with a 25ft enclosed'cO\·erecl auger to convey baghousc dust 

directly into the Bin Room. 

6. Respondent shall install upgraded bags in the Refinery baghousc according to the 

following schedule. 

a. By October 31, 2009, Respondent shall install upgraded bags in one cell of the 

Refinery baghouse as specified in Attachment I. 

b. Respondent shall evaluate perfom1ance ofthe upgraded bags bet'vveen six (6) to eight 

(8) months of installation to determine if bag performance has been impro\·ed. 

c. Provided that performance ofupgraded bags has been improved, Respondent shall 

replace the remaining bags in the Refinery baghouse with the upgraded bags within 

ninety (90) days of the successful perfonnance evaluation. Respondent may utilize an 

equivalent baghousc bag as specified in Attachment I during the initial replacement 

phase and during any subsequent changes. 

d. In the event that the evaluation ofthe upgraded bags demonstrates unacceptable 

performance, Respondent shall submit a proposal for approval by IDEM to evaluate an 

altemative bag for evaluation within thirty (30) days of the performance evaluation 

specified in 6b. 

e. Within thirty (30) days of IDEM approval, Respondent shall initiate the steps in 

paragraph 6 of this Order. Should the events in paragraphs 6.d and 6.e. not produce a 

successful trial and perfonnance evaluation, Respondent has the option to continue 

utilizing the baghouse bags that were in place during the most recent perfonnance test 

that demonstrated compliance with the applicabLe emission standards. 

7. Respondent shall provide a written notification to IDEM within fifteen (15) clays of 

completion of each project required in paragraphs 3, 4, and 5. Respondent shall provide 

details and documentation of each completed project in the next subsequent status report 

after the completion of each project. This infonnation shall be submitted to IDEM as 

specified in paragraph 8 of this Order. 

8. Respondent shall provide a status rep01i to IDEM on the 15111 of each month to include an 

update of the project required in paragraph 6 including and until the elate the project is 

complete. 

9. All submittals required by this Agreed Order, unless Respondent is notified otherwise in 

writing by IDEM, shall be sent to: 

Lynne Sullivan, Compliance and Enforcement Manager 

Compliance and Enforcement Branch- Mail Code 61-53 

Indiana Depmiment of Environmental Management 

I 00 North Senate A venue 

Indianapolis, IN 46204-2251 

10. Respondent is assessed a civil penalty of Ninety-Seven Thousand Five Hundred Dollars 

($97,500). Within forty-five (45) clays of the Eflective Date of the Agreed Order, 

Respondent shall pay a poriion ofthis penalty in the amount ofNineteen Thousand Five 
Exick lcchnolc>gi~·~- Inc. 

Ca~L':: ~00:\-ISI-1-1-_.\ 

Page :: -1 

Hundred Dollars (S 10 . .500) to the Environmental Management Special Fund, noting the 

case number on the check_ In lieu of payment of the remaining ci\·il penalty. Respondent 

shall make a payment in the amount of Seventy-Eight Thousand Dollars ($78,000) to the 

El1\-ironmental Management Special Fund, noting "Diese!Wise Indiana Initiative .. on the 

check. to be used for diesel emission reduction projects in Indiana. Payment for the 

Diesel\Vise Indiana Initiative satisfies Respondent's obligation to uncler1ake a SEP to 

offset a portion of the civil penalty assessed in this matter. Implementation of this SEP 

will benefit Indiana's air quality by providing funds to IDEM's Diese!Wise Indiana 

Initiati\·e which works to reduce the exposure of pollution from diesel exhaust. 

I I. In the event that the civil penalty as stated in paragraph I 0 above is not paid within t()rtytlvc (45) days of the Effective Date, Respondent 'shall pay interest on the unpaid balance at 

the rate established by IC 24-4.6-I-1 0 I. The interest shall continue to accrue until the civil 

p~.?nalty is paid in full. 

I2. In the event that Respondent does not make its SEP payment within tor1y-tlve (45) clays of 

the Effective Date of this Agreed Order, the full amount of the civil penalty as stated in 

paragraph 10 above, plus interest established by IC 24-4.6-1-101 on the remaining amount, 

less the por1ion of the civil penalty Respondent has already paid, will be clue within tltteen 

( 15) days from Respondent's receipt of IDEM· s notice to pay. Interest, at the rate 

established by IC 24-4.6-1-101, shall be calculated on the amount clue from the date which 

is torty-tlve (45) days after the Effective Date of this Agreed Order until the full civil 

penalty is paid. 

13. In the event the tenns and conditions of the following paragraphs are violated, 

Compbinant may ~1sscss and Rcspumknt skdl pay~~ stipuL!tcd pcrnlty in the foliO\\ ing 

amount: 

Paragraph 

4 

5 

6a 

6b 

6c 

6d 

6e 

7 and g 

Violation 

Install enclosure on Rotary Dryer Kiln 

baghouse by October 15, 2009. 

Update SOP Manual by October 31, 

2009. 

Replace V cntilation baghousc auger 

bv October 3 I. 2000. 

Upgrade bags in one cell of Refinery 

baghouse by October 31, 2009. 

Evaluate pertonmmce of upgraded 

bags bet\veen 6 - 8 months of 

installation. 

Upgrade remaining hags in Refinery 

baghouse \\'ithin 90 days of successful 

perfonnance evaluation. 

Submit proposal for alternative bag, if 

necessary. 

Install altemative upgraded bags. if 

necessary. 

Provide reports un project status 

Stipulated Penalty 

$1,000 per week 

$500 per week 

S 1.000 per week 

$I ,000 per week 

S500 per week 

S 1.000 per week 

$500 per week 

$1,000 per week 

S 1 00 per week per report 
[.\ick Technologic~. Inc. 

Ca~c :; 200S-I S 1-l-l-.-\ 

Page =r 5 

1-1-. Stipulated penalties shall he clue and payable \\ithin thirty (30) days after Respondent 

receives \\Titten notice that Complainant has determined a stipulated penalty is due. 

Assessment and payment of stipulated penalties shall not preclude Complainant from 

seeking any additional relief against Respondent for' iolation of this Agreed Order. In lieu 

of any of the stipulated penalties set out above, Complainant may seek any other remedies 

or sanctions available by virtue of Respondent" s ,-iolation of this Agreed Order or Indiana 

law, including, but not limited to, civil penalties pursuant to IC 13-30-4. 

15. Civil and stipulated penalties are payable by check to the "'Environmental Management 

Special Fund_·· Checks shall include the Case Number of this action and shall be mailed 

to: 

Indiana Depmiment of Environmental Management 

Cashier- !viail Code 50- i OC 

100 North Senate A venue 

Indianapolis, IN 46204-:2251 

16. This Agreed Order shall apply to and be binding upon Respondent and its successors and 

assigns. Respondent's signatories to this Agreed Order certify that they are fully 

authorized to execute this Agreed Order and legally bind the party they represent. No 

change in ownership, corporate, or paiinership status of Respondent shall in any way alter 

its status or responsibilities under this Agreed Order. 

17. In the event that any tenns of this Agreed Order are found to be invalid, the remaining 

terms shall remain in full force and effect and shall he construed and enforced as if this 

Agreed Order did not contain the invalid terms. 

I 8. Respondent shall provide a copy of this Agreed Order, if in force, to any subsequent 

owners or successors before ownership rights are transferred. Respondent shall ensure 

that all contractors, firms and other persons performing work under this Agreed Order 

comply with the tenm of this Agreed Order. 

19. This Agreed Order is not and shall not be interpreted to be a pem1it or a modification of an 

existing permit. This Agreed Order. and IDEf'vl· s review or appn)\'al of any submittal 

made by Respondent pursuant to this Agreed Order, shall not in any way relieve 

Respondent of its obligation to comply with the requirements of its applicable pennits or 

any applicable Federal or State law or regulation. 

20. Complainant does not. by its approval of this Agreed Order, \varrant or a\'er in any manner 

that Respondent's compliance with any aspect of this Agreed Order will result in 

compliance with the provisions of any pennit. order, or any applicable Federal or State law 

or regulation. Additionally, IDEM or anyone acting on its behalf shall not be held liable 

for any costs or penalties Respondent may incur as a result of Respondent's eff01is to 

comply with this Agreed Order. 

21. Nothing in this Agreed Order shall prevent or limit IDEM"s rights to obtain penalties or 

injunctive relief under any applicable Federal or State law or regulation, except that IDEM 
Lxicle TL'Cimoklgics. Inc. 

Case ;.: 200S-l S J..f.f-!\ 

Pagt ": 6 

22. 

may not. and hereby wai\·cs its right to. seck adclitional ci\il penalties for the same 

\·iolations specified in the Notice of Violation. 

Nothing in this Agreed Order shall prevent IDEM or anyone acting on its behalf from 

communicating with the EPA or any other agency or entity about any matters relating to 

this enforcement action. IDEM or anyone acting on its behalf shall not be held liable for 

any costs or penalties Respondent may incur as a result of such communications with the 

EPA or any other agency or entity. 

Respondent shall perform the requirements of this On;ler in the manner and within the time 

limits set forth herein, unless the performance is prevented or delayed by events which 

constitute a fence majeure. Force mc!feurc, for purposes of this Agreed Order, is dctlncd as 

any event arising from causes totally beyond the control and without fault of Respondent 

that delays or prevents the performance of any obligation under this Agreed Order despite 

Respondent's best efforts to fulfill the obligation. The requirement that Respondent 

exercise "best efforts to fulfill the obligation .. includes using best efforts to anticipate any 

potential force mqjcure event and best efforts to address the effects of any potentiai/orcc 

majeure event (I) as it is occurring and (2) following the potentiai/orce mcy·eure event, 

such that the delay is minimized to the greatest extent possible. Force majeure does not 

include (I) changed business or economic conditions; (2) financial inability to complete 

the work required by this Agreed Order; or (3) increases in costs to pertom1 the work. 

Respondent shall notify IDEM by calling the case manager within three (3) calendar days 

and by writing no later than seven (7) calendar clays after it has knowledge of any event 

which Respondent contends is a force majeure. Such notification shall describe (1) the 

nnticipatecl length of the delay; (:2) the cause or causes of the delay;(]) the measures taken 

or to be taken by Respondent to minimize the delay; and ( 4) the timetable by which these 

measures will be implemented. Respondent shall include with any notice all available 

documentation supporting its claim that the delay was attributable to a force majeure. 

Failure to comply with the above requirements shall preclude Respondent from asserting 

any claim of force majeure for that event. Respondent shall have the burden of 

demonstrating that the event is a force majeure. The decision of whether an event is a 

force majeure shall be made by IDEM. 

!fa del<~y is attributable to a force majeure. IDEM shall extend. in writing, the time pe-riod 

for perfonnance under this Agreed Order, by the amount of time that is directly attributable 

to the event constituting the force majeure. 

24. This Agreed Order shall remain in effect until Respondent has complied with all terms and 

conditions of this Agreed Order and IDEM issues a Resolution of Case letter to 

Respondent. 
Lxidc: T(·chJwk•gic~. Inc. 

ca~c:.; 2001-1-1 s 1-1-'1-. \ 

Page c: 7 

TECHN!C'A.L REC0\1\!E~D.-\T!ON: 

Dcpartmci~. uf En=on ..n~c;ral :\·lanagcmcnt 

By:--- Craig ~~-·~-1 Henry·. Cl · f 

Compliance and nforcemen 

Section 4 

Office of Air Quality 

Date: cr/( ]/ 0 c:z 

COUNSEL FOR COMPLAINANT: 

For the Department of Environmental 

Mana~1 ment 

' ~ .IJ fl. . . fL. , By:/ 

Dep y Attorney 

~ 

General 

Date 9~ 5/;JD6{ 

RESPONDENT: 

Bv: 

Printed: ~~~_Ade.r 

Title:_~{+ ~ Nf ~l ,IY1c (j(f 

Date: I cfa;A>:1 

COUNSEL FOR RESPONDENT: 

By: __ _ 

Date:~---------

APPROVED AND ADOPT~~BJ THE INDIANA~P~RJ'!VIENT OF ENVIRONMENTAL 

MANAGEMENT THIS ~ Dr\ Y Or ----~ ___ _ __ . ~00 f!_ __ _ 
E.\icle Technologies. Inc. 

Case;; 2008-18144-A 

Page= 8 

stule: 

Fiber: 

Construction: 

Finish: 

Weight: 

Air Permeability: 

Minimum Mullen 

Burst Strength: 

t-1aximum Operating 

Temperature: 

Thermo! Stobility: 

Attachment I 

Filtrotion r-obric Ootasheet 

PE806 

100% Spun Bondecll'oliJeSter 

Non-woven. splln bonci 

Colenderccl. Hcot Set 

U- 25 ft3/min/fti lcfml 1ji1 S' HzO 

62lJ ·· 120 1/cJrn?/rnin (<'•) 200 Po 

6.5- 1?..5 cm3/cm2/s@ 1?5 Po 

?.87 psi 120 kg/cmz) 

275° F (135° C) 

-.451['1 D 73/IUS) 

01 f\J 5~:if38 i' (GerriJCilllJ) 

-.JIS L. 1096-/\ (Jopcrn) 

2% max.@ 275° F 2% rnox.@ 135° C 

GE Energl) Soles: 1800.821.2222/816.:5Sfi.8LJOO 8300 Eost 6:1'" St. J<cnsos Cit~1 HO ol1l.iJ lJ:; /'. 

The obcve dato rs r:omio:JI and pro,,ided for information only. il~is dato i":. nol to b-2 const~ued os 

rnonrlfocturino :.pec!kotions one!·~::-. suilject to chor:.gc. Ail me\ric cc~nvc::~\on~ o;t: U}Jpw:-:mwte. 

K61'!K857 Rev. 08/09/05 
This page intentionally left blank. 
APPENDIX G

Modeling Summary

 Air Quality Analysis

 Wind Rose Analysis

 Precipitation and Snow Cover Analysis
This page left intentionally blank.
G-1 

Modeling Receptor Grid for Exide Technologies

Exide’s sources are indicated by the red thumbtacks.

2009 Point Sources – Exide Technologies 

Unit Description Permitted Lead 

Emission Limits (tpy) 

Unit 1 Lead Battery Crusher/Breaker 0.28 

Unit 4 Lead Reverberatory Furnace 1.49 

Unit 8 Material Handling 0.08 

Unit 9 Slag Crusher/Melting Pots 0.74 

Total Lead Emissions 2.59 

 
G-2 

2011 Point Sources – Exide Technologies 

Unit Description NESHAP Lead 

Emission Limits (tpy) 

Unit 1 Lead Battery Crusher/Breaker 0.27 

Unit 4 Lead Reverberatory Furnace 0.48 

Unit 8 Material Handling 0.004 

Unit 9 Slag Crusher/Melting Pots 0.008 

Total Lead Emissions 0.76 

Annual Wind Roses for 2008-2011 

 2008 2009 

 

 2010 2011
G-3 

Snow Cover Observed on Monitored Days (Delaware County 

– Johnson ASOS Station) 

Snow Cover on 33 days No Snow Cover on 227 days 

Exide East Site Exide West Site Exide East Site Exide West Site 

(μg/m3) (μg/m3) (μg/m3) (μg/m3) 

Average 0.324 0.058 0.710 0.171 

Maximum 1.650 0.289 39.080 5.800 

Precipitation Recorded on Monitored Days (Delaware County – 

Johnson ASOS station) 

 Exide East Site Exide West Site 

Concentrations when... (μg/m3

) (μg/m3) 

No precipitation was recorded 0.440 0.126 

Precipitation was recorded 0.913 0.193 

Wind Conditions/Precipitation on the Highest Concentration Days at the 

Muncie – Exide East Site Monitor 

Date / Day 

Exide 

East Site 

Exide 

West Site Precipitation? Wind Conditions

(μg/m3) (μg/m3) (inches) (direction and speed) 

6/27/2008 - Friday 39.08 0.03 Yes - 0.21 rain SW winds (3 to 13 mph) all day 

6/5/2008 - Thursday 6.62 0.03 No SSW to SW winds (6 to 15 mph) all day 

5/26/2008 - Monday 4.26 0.04 Yes - trace rain SW to WSW winds (3 to 20 mph) all day 

7/3/2008 - Thursday 4.23 0.03 Yes - 1.03 rain Wind shift at noon from SW (3 to 17 mph) to NE 

6/9/2008 - Monday 3.99 0.03 Yes - 0.64 rain SW to SSW winds (6 to 15 mph) all day 

3/11/2008 - Tuesday 3.82 0.03 No NW to W to SW winds (3 to 20 mph) all day 

3/25/2008 - Tuesday 3.67 0.03 No SW to WSW to W winds (6 to 28 mph) all day 

5/14/2008 - Wednesday 3.47 0.03 Yes - 0.61 rain SW to S to SW to NW winds (5 to 15 mph) all day 

4/25/2009 - Saturday 2.98 0.03 No SW winds (7 to 24 mph) all day 

6/7/2008 - Saturday 2.79 0.03 Yes - 0.84 rain W to SW to S winds (4 to 16 mph) all day 

8/9/2009 - Sunday 2.64 0.03 No SW to W to SW winds (6 to 15 mph) all day 

6/29/2008 - Sunday 2.47 0.03 Yes - 0.08 rain SW to WSW to W to NW winds (5 to 20 mph) all day 

6/3/2008 - Tuesday 2.32 0.39 Yes - 0.52 rain SSW to SW to NW to E winds (5 to 13 mph) all day 

8/21/2009 - Friday 2.29 0.03 Yes - 0.03 rain SW to NW winds (5 to 16 mph) all day 

6/25/2008 - Wednesday 2.28 0.03 No S to SW winds (3 to 15 mph) all day 

7/11/2008 - Friday 2.14 0.05 Yes - trace rain WSW to W to SW winds (3 to 13 mph) all day 

7/7/2008 - Monday 1.94 0.14 No S to SW to W to SW winds (3 to 11 mph) all day 

6/8/2011 - Wednesday 1.80 N/A No S to SW to WSW to SW winds (6 to 15 mph) all day 

5/30/2008 - Friday 1.78 0.04 Yes - 0.08 rain S to SW winds (3 to 23 mph) all day 

1/23/2008 - Wednesday 1.65 0.03 No SW to W to SW winds (7 to 13 mph) all day 
G-4 

Wind Conditions/Precipitation on Highest Concentration Days at the 

Muncie – Exide West Site Monitor

Date / Day 

Exide West 

Site 

Exide 

East Site Precipitation? Wind Conditions

(μg/m3) (μg/m3) (inches) (direction and speed) 

4/10/2008 - Thursday 5.80 N/A Yes - 0.43 rain E to SE winds (9 to 18 mph) all day 

4/8/2008 - Tuesday 1.76 N/A Yes - trace rain NW to NE to SE to S winds (3 to 17 mph) all day 

4/24/2008 - Thursday 1.55 N/A Yes - 0.18 rain SE to S winds (5 to 23 mph) all day 

3/17/2008 - Monday 1.44 0.03 Yes - 0.1 rain SE winds (9 to 18 mph) all day 

3/21/2008 - Friday 1.01 0.44 Yes - 0.02 rain E to SE to NE winds (5 to 17 mph) all day 

9/23/2008 - Tuesday 0.59 0.04 No SE to S to SE winds (calm to 10 mph) all day 

10/7/2008 - Tuesday 0.57 0.17 Yes - 0.41 rain SE to SW to S winds (6 to 13 mph) all day 

9/19/2008 - Friday 0.56 0.06 No ESE to E to SE to SW winds (calm to 5 mph) all day 

7/14/2009 - Tuesday 0.50 0.031 No SE winds (calm to 15 mph) all day 

3/29/2008 - Saturday 0.49 0.03 No NE to E to SE to E winds (3 to 18 mph) all day 
AppendixH 

Public Participation Process Documentation 
This page intentionally left blank. 
LEGAL NOTICE OF PUBLIC HEARING 

Attainment Demonstration and Technical Support Document in association with the 

2008 Lead Standard for the Muncie, Delaware County, Indiana Area 

Notice is hereby given under 40 CFR 51.102 that the Indiana Department of 

Environmental Management (IDEM) is accepting written comment and providing an 

opportunity for public hearing regarding the Draft Attainment Demonstration and 

Technical Support Document in association with the 2008 lead standard, for the Muncie, 

Delaware County, Indiana area. The area includes the Exide Technologies, Muncie, 

Indiana facility and is bounded by the following city streets: West 26th Street/Hines Road 

to the nmth, Cowan Road to the east, West Fuson Road to the south, and South Hoyt 

A venue extended to West 26th Street to the west. All interested persons are invited and 

will be given reasonable oppmtunity to express their views conceming the submittal of 

the proposed Attainment Demonstration and Technical Suppmt Document in association 

with the 2008lead standard for the Muncie, Delaware County, Indiana area. 

The Muncie, Delaware County, Indiana area was designated as "nonattainment" 

for the 2008 lead standard and subject to the requirements of Section 172 of the Clean Air 

Act (CAA). One of the compliance requirements mandated by Section 172(c) of the 

CAA is the development of a plan demonstrating that the area will meet the federal 2008 

air quality standard by the required attainment date. This Attainment Demonstration and 

Technical Support Document is being drafted and submitted consistent with United 

States Environmental Protection Agency (U.S. EPA) guidance. 

Copies of the draft documents will be available on or before December 14, 2012, 

to any person upon request at the following locations: 

• Indiana Depmtment of Environmental Management, Office of Air Quality, 

Indiana Government Center Nmth, 100 Nmth Senate Avenue, Room N1003, 

Indianapolis, Indiana 

• Muncie-Center Township Public Library, 2005 South High Street, Muncie, 

Indiana 

• Yorktown-Mount Pleasant Township Public Librm·y, 8920 West Adaline Street, 

Yorktown, Indiana 

The draft documents will also be available on the following web page: 

http:/ /www.in.gov/idem/4654.htm 
Any person may submit written comments on the Attainment Demonstration and 

Technical Support Document in association with the 2008 lead standard, for the Muncie, 

Delaware County, Indiana area on or before January 21, 2013. Written comments should 

be directed to Mr. Gale Fenis, Mail Code 61-50, Office of Air Quality, Indiana 

Department of Environmental' Management, 100 North Senate Avenue, Indianapolis, 

Indiana 46204; or fax (317) 233-5967; or e-mail at gfenis@idem.in.gov. Interested 

parties may also present oral or written comments at the public hearing, if held. Oral 

statements will be heard, but for the accuracy of the record, statements should be 

submitted in writing. Written statements may be submitted to the attendant designated to 

receive written comments at the public hearing. 

A public hearing on the Attainment Demonstration and Teclmical Suppmi 

Document in association with the 2008 lead standard for the Muncie, Delaware County, 

Indiana area will be held if a public hearing request is received by January 7, 2013. A 

hearing has been scheduled for January 16, 2013. The hearing will convene at 6:00p.m. 

local time at the Kennedy Library located at 1700 West McGalliard Road, Muncie, 

Indiana 47304. If a request for a public hearing is not received by January 7, 2013, the 

hearing will be cancelled. Interested parties can check the online IDEM calendar at 

http://www.in.gov/idern/5390.htm or contact Mr. Gale Ferris at (317) 234-3653, after 

January 7, 2013, to see if the hearing has been cancelled or will convene. 

A transcript of the hearing and all written submissions provided at the public 

hearing shall be open to public inspection at IDEM and copies may be made available to 

any person upon payment of reproduction costs. Any person heard or represented at the 

hearing or requesting notice shall be given written notice of actions resulting from the 

hearing. 

For additional information contact Mr. Gale Ferris, at the Indiana Department of 

Environmental Management, Office of Air Quality, Room N1001, Indiana Government 

Center North, 100 Nmih Senate Avenue, Indianapolis, IN 46204 or call (317) 234-3653 

or (800) 451-6027 ext. 4-3653 (in Indiana) . 

••••••••••••••••••••••••••••••••••••••••••••••••••••••••••••••••••••••••• 

Individuals requiring reasonable accommodations for participation in this hearing, if 

held, should contact the IDEM Americans with Disabilities Act (ADA) coordinator at: 

Attn: ADA Coordinator 

Indiana Depa1iment of Environmental Management - Mail Code 5 0-10 

100 Nmih Senate Avenue 

Indianapolis, IN 46204-2251 

Or call (317) 233-1785 (voice) or (31 7) 232-6565 (I'DD). Please provide a minimum of 

72 hours notification. 
IDEM INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT 

We Protect Hoosiers and Our Environment. 

Mitchell E. Daniels Jr. 

Governor 

Thomas W. Easterly 

Commissioner 

December 11, 2012 

CERTIFICATE OF PUBLICATION 

100 North Senate Avenue 

Indianapolis, Indiana 46204 

(317) 232-8603 

Toll Free (800) 451-6027 

www.idem.IN.gov 

This is to certify that the Indiana Depmtment of Environmental Management (IDEM) Notice of 

the opp01tunity for a Public Hearing regarding the following: 

• Draft Attainment Demonstration and Technical Suppmi Document in association with the 

2008 Lead Standard for the Muncie, Delaware County, Indiana Area 

was published on IDEM's web site on December 11, 2012. It remained posted on the site until at 

least Janumy 21, 2013. · 

The notice in full was available online at the following web address, und~r "Delaware" county. 

http://www.in.gov/idem/6398.htm 

Web publication of the notice was at the request of Scott Deloney, Branch Chief, Programs 

Branch, Office of Air Quality, IDEM. 

Attachments: 

Copy of web page as published. 

Recycled Paper @ 

By: 

Mike Finklestein 

IDEM Webmaster 

An Equal Opportunity Employer Please Recycle O 
Environmental Information 

_ !~ur Comm~~ity·· . 

Your Environment 

AirToxics Program 

Blue-Green Algae o o o ~- o o o o O- L ·oo oL o -~~¥-- ••·------··----·· V 0 

CTAP: Compliance and Technical 

Assistance Program .... ............... . 

Recycle lru!iana .. --······· .. ·········--·----· -· ·-· ··-· --~-

Watersheds and Nonpoint Source 

Water Pollution 

. ~=-~~fi~~i~~~ r..~~~ g ____ - --

... C:ornl>'"'"·c: ...... ....................... ... . 

T~c::hnics. l Support Doc:Jment in 

asi::>d.stion wifh ±he 2.D<l3 Lead 

Sbn.::S.srd' f:-r th-e- Muncie. Oe s:.~sre 

Ct:-unty, ln<!is.n.s Ares 

r,.te:id.i.s.n Fo::x!s Celswsre, 

G:ant.J.sy, 

Madison, and 

Randol pi> 

8Jo:::Y.ville (town) ltf'llifT? Frs:nklin 

M::-::r.:l:s.nd t~OJn) WWTP 1-CanrJ 

Knightstown jtown) \WfTP Ke uy 

Time 

ITWTFS 

1 

2 3 4 5 6 i 8 

9 10 m 12 13 14 15 Y. 16 17 18 19 20 21 22 .. ~ ~ . 23 24 25 26 27 28 29 

30 31 jl 0:39:09AI~ ~ 

Current time zone: Eastern standard Tirne 

01/211~1:1. N::)ti c::e: 

H~s ri n:;;z TPC!"' 

S.~liQ w~gc. yng: 121141'2012- rio 1Pl'ojed. Arldr~on 

Acoiicaticn PeTmit {F'CFi . 12/;!gl2ll12 r...rs.ns.ger. Notice 

Brenda 

SF-;>hsnolf 

1\rFCES Fingl Rt:new31 11l1412ll12- Yes Pr<>j .. c:£ 

!E..Q.E 12/02121)12 Man.ager: Ms.tt 

~ 

' N"FCES Cr ft' F.~n.:;;\vs- 1 11/29.12012 - Yes Project 

~ 12i:1.112012 Ms.nsga: 

AJisss Fe.ilen 

AC'd:e»on 

IO:ctice: 

, 1\'PDES 01'9ft ~n-ew'31 1.2105/2!)12- y,. Pre>jad 

!E.Q£l 011071201:1. Msn.3ger. Bill 

.st::nng