Revision to the South Carolina Air Quality Implementation Plan Appendix A

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# Appendix A Point Source Inventory DocumentationRevision to the South Carolina Air Quality Implementation Plan Appendix A

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### This page intentionally left blankRevision to the South Carolina Air Quality Implementation Plan Appendix A

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### TABLE OF CONTENTS

1.0 INTRODUCTION AND SCOP E ... .......................................................................................4 2.0 OVERALL M ETHODOLOG Y ...............................................................................................4 3.0 QUALITY AS SURANC E........................................................................................................5 4.0 TOTAL POINT SO URCES EMI SSIONS ..............................................................................6 5.0 DISCUSSION OF POINT SOURCE CATE GORIES ...........................................................7

LIST OF TABLES

Table 4.1-1 Total NO
x Emissions in Tons per Day.................................................................................. 6 Table 4.1-2 Total VOC Emi ssions in Tons per Day................................................................................ . 6 Table 4.2-1 Summary of 2010 Point Source Emissions........................................................................... 6 Table 4.2-2 Summary of 2013 Point Source Emissions........................................................................... 6 Table 4.2-3 Summary of 2016 Point Source Emissions........................................................................... 7 Table 4.2-4 Summary of 2019 Point Source Emissions........................................................................... 7 Table 4.2-5 Summary of 2022 Point Source Emissions........................................................................... 7 Table 5.1-1 Summary of SCC 1-02-xxx-xx NO2 Emissions (ton per ozone day) for AbitibiBowater, Inc............................................................................................................ ................ 8 Table 5.1-2 Summary of SCC 1-02-xxx-xx VOC Emissions (ton per ozone day) for AbitibiBowater, Inc............................................................................................................ ................ 8 Table 5.1-3 Summary of SCC 1-05-xxx-xx NO2 Emissions (ton per ozone day) for Cytec ................... 9 Table 5.1-4 Summary of SCC 1-05-xxx-xx VOC Em issions (ton per ozone day) for Cytec .................. 9 Table 5.3-1 Summary of SCC 3-07-xxx-xx NO2 Emissions (ton per ozone day) for AbitibiBowater, Inc............................................................................................................ ................ 10 Table 5.3-2 Summary of SCC 3-07-xxx-xx VOC Emissions (ton per ozone day) for AbitibiBowater, Inc............................................................................................................ ................ 10 Table 5.3-3 Summary of SCC 3-01-xxx-xx NO2 Emissions (ton per ozone day) for Cytec ................... 10 Table 5.3-4 Summary of SCC 3-01-xxx-xx VOC Em issions (ton per ozone day) for Cytec .................. 11 Table 5.3-5 Summary of SCC 3-90-xxx-xx NO2 Emissions (ton per ozone day) for Cytec ................... 11 Table 5.3-6 Summary of SCC 3-90-xxx-xx VOC Em issions (ton per ozone day) for Cytec .................. 11 Table 5.5-1 Summary of SCC 5-03-xxx-xx NO2 Emissions (ton per ozone day) for AbitibiBowater, Inc............................................................................................................ ................ 12 Table 5.5-2 Summary of SCC 5-03-xxx-xx VOC Emissions (ton per ozone day) for AbitibiBowater, Inc............................................................................................................ ................ 12Revision to the South Carolina Air Quality Implementation Plan Appendix A

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## 1.0 INTRODUCTION AND SCOPE

The point source inventory consists of emissi ons from individual facilities. Primarily, these are larger industrial or commercial faci lities that must have Title V permits issued by the South Carolina Department of Hea lth and Environmenta l Control (SCDHEC) Bureau of Air Quality (BAQ).

Although the SCDHEC BAQ invent ories all the criteria pollutants and a large number of toxic pollutants, only the nitrogen oxides (NO x 

### ) and volatile organic compounds (VOC) are reported here since they are important for ozone forma tion. The emissions in this report represent 2010 (the base year) and ar e projected to the future years 2013, 2016, 2019, and 2022.

The point source inventories detailed in this section have been developed for York County as well as the Rock Hill Fort Mill Area Transportation Study (RFATS) Metropolitan Planning Organization (MPO) portion of York County (also referred to as the York NA area), South Carolina within the Charlotte -Gastonia-Rock Hill, NC-SC nonattainment area for the 1997 8-hour ozone NAAQS Redesi gnation Demonstratio n and Maintenance Plan. All emissions ar e calculated on a ton per summer day basis.



## 2.0 OVERALL METHODOLOGY

All large permitted sources defined as Invent ory Type A sources under the United States Environmental Protection Agency (EPA) Ai r Emissions Reporting Rule (AERR) are required to report emissions annually and other Title V sources are required to report every three years to SCDHEC BAQ. Add itionally, the EPA requires the SCDHEC BAQ to submit this data to the EPA Emissions I nventory System (EIS) on the same schedule. The latest year available for the Inventory T ype A point source inventory submitted to the EPA is 2010. For the smaller sources that re port emissions every three years, the most recent emissions inventory available (2008 ) was used as representative of 2010 emissions. These data were then projec ted to future years of 2013, 2016, 2019, 2022. The emissions data upon which this document is based were from file s maintained by the SCDHEC BAQ.

2.1 SOURCE IDENTIFICATION

All facilities required to have Title V perm its to operate sources of air pollution are known and are required to subm it emission inventories.

2.2 EMISSION ESTIMATION APPROACH

The emissions inventory information repor ted to SCDHEC BAQ was transferred to a state emissions inventory program that help s ensure required data elements are not omitted. The system also performs some calculations, thereby minimizing the occurrence of errors. Depending on the particular proce ss and facility, emissions may be calculatedRevision to the South Carolina Air Quality Implementation Plan Appendix A

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### by various means. In many cases, emissi ons are estimated using emission factors published in the EPA’s AP-42, Compilation of Air Pollutant Emission Factors. In a relatively few cases, locally produced emission factors may be used. Sometimes, a mass balance calculation can be employed. In some cases, there are stacks tests or direct continuous monitoring of emissi ons that are reported.

Emissions reported to and maintained by SC DHEC BAQ are annual em issions. There is also data for operating hours per day and per year, days per week, and the percent of emissions occurring in the summer quarter.

2.3 EMISSION PROJECTION

The most recently submitted emissions data was used as the baseline for the projected emissions in this report. The emissions i nventory was projected to future years by utilizing EPA’s Economic Growth Analysis Sy stem (E-GAS) version 5 software. There are two major data sources that are used as growth indicators in EGAS 5.0: the Department of Energy’s (DOE) Annual Ener gy Outlook and version 6.0 of state-level economic models from Regional Economic Models , Inc. (REMI). In general, DOE data are expected to be used as growth indicat ors for fuel combustion/ production categories, while REMI data will be used fo r all other source categories.

2.4 FUTURE EMISSION REDUCTIONS

The Maximum Achievable Control Technolog y (MACT) regulations are intended to reduce emissions of hazardous air pollutants (HAPs), some of which are VOCs. In some cases, reduction of HAPs that are VOCs is accomplished by switching to VOCs that are not HAPs, resulting in no reductions of VOC emissions. In other cases, compliance with a MACT regulation can be expected to reduce VOC emissions. It is likely there will be some additional VOC emission reductions du e to new MACT rules in the Metrolina nonattainment area, although the MACT regul ations do not always make a clear statement of how much VOC emission reduc tions will result from the HAPs emission reductions. Sometimes it is not possible to say until a particular affected source considers possible control options. Therefore, no emission reductions, as a result of MACT regulations, will be taken in this plan.

No additional emission reductions are expected for the facilities locat ed within the York NA area.



## 3.0 QUALITY ASSURANCE

The emission inventory has undergone a number of quality assurance checks so that it meets the standards for submitting the annual in ventory to the EPA. The state emissions inventory database program help s insure that important data elements are present. Where the program performs calculations, it helps av oid math errors. In addition, the StateRevision to the South Carolina Air Quality Implementation Plan Appendix A

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### works closely with all Title V sources to ensu re that all tons-per-year emissions reported

are accurate.



## 4.0 TOTAL POINT SOURCES EMISSIONS

In the following sections the emissions for the York NA area are totaled, as well as, the estimated facility emissions w ithin the county in th e nonattainment area are identified for the base year (2010) and the future maintenance years (2013, 2016, 2019 and 2022). Only the emissions for the sources actually located within the nona ttainment area are presented.

4.1 YORK NA AREA SUMMARY

Table 4.1-1 Total NO x 

### Emissions in Tons per Day 2010 2013 2016 2019 2022
York * 4.54 4.64 4.91 5.19 5.48

Table 4.1-2 Total VOC Emissions in Tons per Day 2010 2013 2016 2019 2022
York * 2.07 2.06 2.2 2.34 2.49

* Only the sources inside the York NA area are included.

4.2 SUMMARY OF EMISSIONS

Table 4.2-1 Summary of 2010 Point Source Emissions

PLANT SIC # VOC (tons / day) NO x 

### (tons / day) ABITIBIBOWATER, INC. 2621 1.94 4.34

CYTEC 3624 0.13 0.20 Total County Emissions 2.07 4.54

Table 4.2-2 Summary of 2013 Point Source Emissions

PLANT SIC # VOC (tons / day) NO x 

### (tons / day) ABITIBIBOWATER, INC. 2621 1.92 4.42

CYTEC 3624 0.14 0.22 Total County Emissions 2.06 4.64Revision to the South Carolina Air Quality Implementation Plan Appendix A

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### Table 4.2-3 Summary of 2016 Point Source Emissions

PLANT SIC # VOC (tons / day) NO x 

### (tons / day) ABITIBIBOWATER, INC. 2621 2.05 4.68

CYTEC 3624 0.15 0.23 Total County Emissions 2.20 4.91

Table 4.2-4 Summary of 2019 Point Source Emissions

PLANT SIC # VOC (tons / day) NO x 

### (tons / day) ABITIBIBOWATER, INC. 2621 2.18 4.94

CYTEC 3624 0.17 0.25 Total County Emissions 2.34 5.19

Table 4.2-5 Summary of 2022 Point Source Emissions

PLANT SIC # VOC (tons / day) NO x 

### (tons / day) ABITIBIBOWATER, INC. 2621 2.31 5.21

CYTEC 3624 0.18 0.27 Total County Emissions 2.49 5.48



## 5.0 DISCUSSION OF POIN T SOURCE CATEGORIES

Industrial processes in the i nventory are identified with 8-digit numbers known as the Source Classification Codes (SCC). These are grouped numerically into a number of categories for convenience. The following is the 2010 inventory reported by SCC. In general, the first three digits of the SCC code describe the process and the last five digits give more detail as to the fu el used, size of s ource, etc. The sections that follow are grouped by the first three digits of the SCC code.

It should be remembered that the SCC in any particular instance was selected by an individual entering inventory data into a computer maintained record. It may be that in some cases, other individuals w ould have selected other codes. In some cases, there are two or three parallel codes that describe the same sort of equipment, the difference being size. In other cases, one is able to select a general code for an overall process or useRevision to the South Carolina Air Quality Implementation Plan Appendix A

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### several more specific codes that together w ould be covered by the more general one. If, upon consideration, it app ears that a more appropriate code could have been selected, that does not mean that the reported emissions are inaccurate.

A listing of SCC with descriptions may be found in WebFIRE Source Classification Codes And Emission Factor Listing For Criteria Air Pollutants. Occasionally, new SCCs are defined so it may be useful to search the EPA’s website for new entries.

5.1 EXTERNAL COMBUSTION BOILERS

Tables 5.1-1 through 5.1-4 tabulate the emissions from the external combustion sources. These are primarily of interest due to NO x 

### emissions.

Table 5.1-1 Summary of SCC 1-02-xxx-xx NO2 Emissions (ton per ozone day) for AbitibiBowater, Inc.

SCC Unit ID Process ID 2010 2013 2016 2019 2022 10200401 8 3 0.0219 0.0232 0.0240 0.0244 0.0250 10200401 8 8 0.0312 0.0331 0.0342 0.0347 0.0357 10200402 7 3 0.0190 0.0202 0.0208 0.0212 0.0217 10200402 7 5 0.0198 0.0211 0.0217 0.0221 0.0227 10200405 8 1 0.0558 0.0593 0.0611 0.0621 0.0638 10200601 7 7 0.0008 0.0008 0.0008 0.0009 0.0009 10200601 8 4 0.0204 0.0208 0.0214 0.0225 0.0233 10200601 8 9 0.0332 0.0339 0.0348 0.0366 0.0379 10200603 6 5 0.0043 0.0044 0.0045 0.0047 0.0049 10200603 6 7 0.0986 0.1006 0.1035 0.1088 0.1128 10200604 8 2 0.0023 0.0024 0.0024 0.0025 0.0026 10200901 8 5 0.6625 0.7078 0.7444 0.7795 0.8120 10200901 8 10 0.9438 1.0083 1.0605 1.1105 1.1569
10201001 6 6 0.0000 0.0000 0.0000 0.0000 0.0000 10201001 6 8 0.0000 0.0000 0.0000 0.0000 0.0000 10201301 6 9 0.0004 0.0005 0.0005 0.0005 0.0005



### Table 5.1-2 Summary of SCC 1-02-xxx-xx VO C Emissions (ton per ozone day) for AbitibiBowater, Inc.

SCC Unit ID Process ID 2010 2013 2016 2019 2022
10200401 8 3 0.0004 0.0004 0.0004 0.0004 0.0004 10200401 8 8 0.0005 0.0005 0.0006 0.0006 0.0006
10200402 7 3 0.0001 0.0001 0.0001 0.0001 0.0001 10200402 7 5 0.0001 0.0001 0.0001 0.0001 0.0001 10200405 8 1 0.0011 0.0012 0.0012 0.0012 0.0013
10200601 7 7 0.0000 0.0000 0.0000 0.0000 0.0000 10200601 8 4 0.0004 0.0004 0.0004 0.0004 0.0005 10200601 8 9 0.0007 0.0007 0.0007 0.0007 0.0007Revision to the South Carolina Air Quality Implementation Plan Appendix A

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10200604 8 2 0.0001 0.0001 0.0001 0.0001 0.0001 10200901 8 5 0.0512 0.0547 0.0575 0.0602 0.0627 10200901 8 10 0.0729 0.0779 0.0819 0.0858 0.0894
10201001 6 6 0.0000 0.0000 0.0000 0.0000 0.0000 10201001 6 8 0.0000 0.0000 0.0000 0.0000 0.0000 10201301 6 9 0.0000 0.0000 0.0000 0.0000 0.0000



### Table 5.1-3 Summary of SCC 1-05-xxx-xx NO2 Em issions (ton per ozone day) for Cytec

SCC Unit ID Process ID 2010 2013 2016 2019 2022
10500106 IAS 2 0.0000 0.0000 0.0000 0.0000 0.0000
10500106 IAS 5 0.0000 0.0000 0.0000 0.0000 0.0000



### Table 5.1-4 Summary of SCC 1-05-xxx-xx VO C Emissions (ton per ozone day) for Cytec

SCC Unit ID Process ID 2010 2013 2016 2019 2022
10500106 IAS 2 0.0000 0.0000 0.0000 0.0000 0.0000 10500106 IAS 5 0.0000 0.0000 0.0000 0.0000 0.0000



### 5.2 INTERNAL COMBUSTION ENGINES

Stationary internal combustion (IC) engines can be used on a daily basis or used only for backup power. Fuels can be gasoline, oil or various combustible gases depending on the engine design. Engines may be either turb ines or reciprocating. No point source emissions of this type are located within the nonattainment area.

5.3 INDUSTRIAL PROCESES

There are large numbers of SCC under the he ading of industrial processes. Many of these are of most significance for VOC but some do emit NO x 

### . Codes 3-01-xxx-xx are chemical manufacturing. Codes 3-02-xxx-xx ar e for processes particular to food and agriculture. Codes 3-04-xxx-xx pertain to secondary metal production. Mineral products processes are in SCC 3-05xxx-xx and pulp and paper and wood products are in 3-07-xxxxx. Codes 3-08-xxx-xx pertain to rubber and mis cellaneous plastics pr oducts. Fabricated metal products are 3-09-xxx-xx. 3-12xxx-xx is miscellaneous machinery. Electrical equipment manufacturing falls under code 3-13xxx-xx. Transportation equipment is under 3-14-xxx-xx. Processes for textile products are found under 3-30-xxx-xx. Inprocess fuel use can result in significant NO x 

### emissions and is in category 3-90-xxx-xx. Miscellaneous manufacturing indus tries are in group 3-99-xxx-xx.Revision to the South Carolina Air Quality Implementation Plan Appendix A

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RFATS Redesignation Demonstration and Maintenance Plan May 31, 2011 Table 5.3-1 Summary of SCC 3-07-xxx-xx NO2 Emissions (ton per ozone day) for AbitibiBowater, Inc.

SCC Unit ID Process ID 2010 2013 2016 2019 2022
30700103 7 1 0.0000 0.0000 0.0000 0.0000 0.0000 30700105 7 8 0.0115 0.0113 0.0120 0.0128 0.0137 30700105 7 9 0.0206 0.0203 0.0216 0.0230 0.0245 30700106 7 10 0.4837 0.4763 0.5081 0.5410 0.5760 30700110 7 4 0.8462 0.8332 0.8889 0.9464 1.0077 30700110 7 6 1.0604 1.0442 1.1139 1.1860 1.2627 30700121 9 1 0.0000 0.0000 0.0000 0.0000 0.0000 30700122 7 11 0.0000 0.0000 0.0000 0.0000 0.0000 30700199 7 2 0.0000 0.0000 0.0000 0.0000 0.0000 30700199 9 2 0.0000 0.0000 0.0000 0.0000 0.0000

Table 5.3-2 Summary of SCC 3-07-xxx-xx VOC Emissions (ton per ozone day) for AbitibiBowater, Inc.

SCC Unit ID Process ID 2010 2013 2016 2019 2022 30700103 7 1 0.0091 0.0090 0.0096 0.0102 0.0109 30700105 7 8 0.0143 0.0141 0.0151 0.0160 0.0171 30700105 7 9 0.0257 0.0253 0.0270 0.0288 0.0306 30700106 7 10 0.0114 0.0112 0.0119 0.0127 0.0135 30700110 7 4 0.0803 0.0790 0.0843 0.0898 0.0956 30700110 7 6 0.1426 0.1404 0.1498 0.1595 0.1698 30700121 9 1 1.4473 1.4251 1.5204 1.6187 1.7234 30700122 7 11 0.0688 0.0677 0.0723 0.0770 0.0819 30700199 7 2 0.0064 0.0063 0.0067 0.0071 0.0076 30700199 9 2 0.0006 0.0006 0.0006 0.0006 0.0007

Table 5.3-3 Summary of SCC 3-01-xxx-xx NO2 Emissions (ton per ozone day) for Cytec

SCC Unit ID Process ID 2010 2013 2016 2019 2022
30102432 IAS 3 0.0000 0.0000 0.0000 0.0000 0.0000 30102499 1 3 0.0465 0.0494 0.0535 0.0576 0.0622 30102499 1 5 0.0465 0.0494 0.0535 0.0576 0.0622 30102499 1 7 0.0465 0.0494 0.0535 0.0576 0.0622 30102499 1 9 0.0152 0.0161 0.0174 0.0188 0.0203 30102499 1 10 0.0152 0.0161 0.0174 0.0188 0.0203 30102499 1 11 0.0152 0.0161 0.0174 0.0188 0.0203 30102499 1 13 0.0000 0.0000 0.0000 0.0000 0.0000 30102499 IAS 1 0.0000 0.0000 0.0000 0.0000 0.0000Revision to the South Carolina Air Quality Implementation Plan Appendix A

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RFATS Redesignation Demonstration and Maintenance Plan May 31, 2011 Table 5.3-4 Summary of SCC 3-01-xxx-xx VOC Emissions (ton per ozone day) for Cytec

SCC Unit ID Process ID 2010 2013 2016 2019 2022
30102432 IAS 3 0.0003 0.0003 0.0003 0.0003 0.0003 30102499 1 3 0.0441 0.0469 0.0507 0.0546 0.0590 30102499 1 5 0.0441 0.0469 0.0507 0.0546 0.0590 30102499 1 7 0.0441 0.0469 0.0507 0.0546 0.0590 30102499 1 9 0.0001 0.0001 0.0001 0.0001 0.0001 30102499 1 10 0.0001 0.0001 0.0001 0.0001 0.0001 30102499 1 11 0.0001 0.0001 0.0001 0.0001 0.0001 30102499 1 13 0.0007 0.0007 0.0008 0.0008 0.0009 30102499 IAS 1 0.0000 0.0000 0.0000 0.0000 0.0000

Table 5.3-5 Summary of SCC 3-90-xxx-xx NO2 Emissions (ton per ozone day) for Cytec

SCC Unit ID Process ID 2010 2013 2016 2019 2022 39000689* 1 1 0.0000 0.0000 0.0000 0.0000 0.0000 39000689* 1 2 0.0050 0.0054 0.0058 0.0062 0.0067 39000689* 1 4 0.0034 0.0034 0.0035 0.0042 0.0038 39000689* 1 6 0.0034 0.0034 0.0035 0.0037 0.0038 39000689* 1 8 0.0041 0.0042 0.0043 0.0045 0.0047 39000689* 1 12 0.0011 0.0011 0.0012 0.0012 0.0013 39000689* N01 1 0.0028 0.0029 0.0029 0.0031 0.0032 * 39000689 is now 39000699 for compatibility with EPA’s list of valid SCC codes.

Table 5.3-6 Summary of SCC 3-90-xxx-xx VOC Emissions (ton per ozone day) for Cytec

SCC Unit ID Process ID 2010 2013 2016 2019 2022 39000689* 1 1 0.0000 0.0000 0.0000 0.0000 0.0000 39000689* 1 2 0.0003 0.0003 0.0003 0.0003 0.0003 39000689* 1 4 0.0002 0.0002 0.0002 0.0002 0.0002 39000689* 1 6 0.0002 0.0002 0.0002 0.0002 0.0002 39000689* 1 8 0.0002 0.0002 0.0002 0.0002 0.0003 39000689* 1 12 0.0001 0.0001 0.0001 0.0001 0.0001 39000689* N01 1 0.0000 0.0000 0.0000 0.0000 0.0000 * 39000689 is now 39000699 for compatibility with EPA’s list of valid SCC codes.



### 5.4 PETROLEUM AND SOLVERT EVAPORATION

This group of sources emits VOC. SCC in the 4-01-xxx-xx group are for organic solvent evaporation. Surface coating operations are grouped under SCC 4-02-xxx-xx. Petroleum product storage is grouped under 4-03-xxx-xx. Non-refinery petroleum liquids storage falls under group 4-04-xxx-xx. Printing and pub lishing are in the 4-05-xxx-xx group of SCC. SCC group 4-07-xxx-xx covers orga nic chemical storage. SCC 4-08-xxx-xx pertains to organic chemical transportati on. Organic solvent evaporation falls under 4-Revision to the South Carolina Air Quality Implementation Plan Appendix A

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### 90-xxx-xx. No sources from thee categories are located at the point sources within the York NA area.

5.5 WASTE DISPOSAL

Waste disposal includes government solid waste disposal, in group 5-01-xxx-xx. Commercial and institutional solid waste di sposal processes are in the 5-02-xxx-xx SCC group. Industrial solid waste dis posal falls into group 5-03-xxx-xx.

Table 5.5-1 Summary of SCC 5-03-xxx-xx NO2 Emissions (ton per ozone day) for AbitibiBowater, Inc.

SCC Unit ID Process ID 2010 2013 2016 2019 2022
50300107 8 6 0.0000 0.0000 0.0000 0.0000 0.0000 50300107 8 11 0.0000 0.0000 0.0000 0.0000 0.0000

Table 5.5-2 Summary of SCC 5-03-xxx-xx VOC Emissions (ton per ozone day) for AbitibiBowater, Inc.

SCC Unit ID Process ID 2010 2013 2016 2019 2022
50300107 8 6 0.0000 0.0000 0.0000 0.0000 0.0000 50300107 8 11 0.0000 0.0000 0.0000 0.0000 0.0000