# APPENDIX F

Mobile Source Input/Output Calculation Files

# F - 1 This page left intentionally blank.

# MOBILE SOURCE EMISSIONS INVENTORY FOR THE CINCINNATI OZONE NONATTAINMENT AREA Includes a portion of Dearborn County Indiana, the counties of Boone, Campbell, Kenton in Kentucky, and the counties of Butler, Clermont, Clinton, Hamilton, and Warren in Ohio. Emission Estimates for the Year 2005, 2008, 2015 and 2020 developed in support of the Ozone SIP



# OCTOBER 2009

Revised

Prepared for the Indiana Department of Environmenta l Management, the Kentucky Division for Air Quality and the Ohio Environmental Protection Agency by

OKI Regional Council of Governments

# Acknowledgments

Title Mobile Source Emissions Inventory for Cincinnati O zone Nonattainment Area

Abstract This report documents the methodology and results f rom the development of the mobile source emission inventory for ozone precursors in the Cincinnati ozone nonattainm ent area. The nonattainment area includes a portion of Dearbo rn County Indiana, Boone, Campbell and Kenton counties in Ken tucky, and Butler, Clermont, Clinton, Hamilton and Warren counties in Ohio. The ozone precursors include volatile org anic compounds (VOCs) and oxides of nitrogen (NO
x 

# ). The new 2005, 2008, 2015, and 2020 inventory, as provided i n this report, includes the benefits of low RVP fuel in Bu tler, Clermont, Hamilton and Warren counties. It is expe cted that the 2008 inventory, plus an additional safety margi n, will be
established as the revised 8-hour ozone motor vehic le emissions budgets for the Cincinnati nonattainment area.

Date October 2009

Agency Ohio-Kentucky-Indiana Regional Council of Governme nts Mark Policinski, Executive Director

Project Manager Robert Koehler, P.E., Deputy Director

Project Staff

Andrew J. Reser, AICP, Principal Author Harikishan Perugu

The preparation of this document was financed coope ratively by the Federal Highway Administration, the Federal Transit Administration, the Commonwealth of Kentucky Transportation Cabinet, the Ohio Department of Tran sportation, and the units of local and county government in the OKI region. The opinions, findings, and conclusions expressed in this document are those of the OKI Regional Coun cil of Governments and are not necessarily those of the U.S. Department of Transpo rtation. This report does not constitute a standard, specification, or regulation

.

# Table of Contents

Page

1. Introduction ..................................

................................................... ................................ 1 Figure 1-Cincinnati Ozone Nonattainment Area .....

................................................... ......2
2. Mobile Source Emission Forecast Process ........

................................................... ............3 3. Mobile Source Emission Inventory ...............

................................................... ................7 Table 1-Mobile Source Emissions Inventory by State/ County for the Cincinnati
Ozone Nonattainment Area...........................

................................................... .................7 Table 1-Mobile Source Emissions Inventory for the I ndiana and Ohio Portions of
the Cincinnati Ozone Nonattainment Area ...........

................................................... .........8 Table 2-Mobile Source Emissions Inventory for the K entucky Portion of the
Cincinnati Ozone Nonattainment Area ...............

................................................... ...........8

Appendix A – MOBILE6.2 Input/Output Files for the I ndiana Portion of the
Nonattainment Area Appendix B – MOBILE6.2 Input/Output Files for the K entucky Portion of the
Nonattainment Area Appendix C – MOBILE6.2 Input/Output Files for the O hio Portion of the
Nonattainment Area Appendix D – Air Quality Impact Summary for the OKI Portion of the Nonattainment Area and Emissions by State/County Appendix E – Clinton County Air Quality Analysis

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1. INTRODUCTION

At the request of the Indiana Department of Environ mental Management, the Kentucky Division for Air Quality, and the Ohio Environmenta l Protection Agency, the OhioKentucky-Indiana Regional Council of Governments (O KI) has prepared this mobile source emissions inventory of ozone precursor pollu tants. Pursuant to provisions of the CAAA of 1990, U.S. EPA designated a nine county are a in the Cincinnati area as a basic nonattainment area for ozone under the eight-hour o zone standard in April 2004. The
Cincinnati ozone nonattainment area includes Lawren ceburg Township in Dearborn County Indiana, the Kentucky counties of Boone, Cam pbell and Kenton, and the Ohio counties of Butler, Clermont, Clinton, Hamilton and Warren (Figure 1). Ozone is formed through chemical reactions induced when sunlight re acts with volatile organic compounds (VOCs; principally hydrocarbons) and nitr ogen oxides (NO X 

# ). VOCs and
NO X 

# occur from incomplete combustion of fossil fuels. Transportation-related sources are a major contributor of these pollutants. Since heat speeds the reactions, ozone levels are typically highest during hot summer days.

The OKI Regional Council of Governments, as the Met ropolitan Planning Organization (MPO), consists of Dearborn, Boone, Campbell, Kento n, Butler, Clermont, Hamilton and
Warren counties

. The cities of Franklin and Carlisle in Warren Count y are part of the Miami Valley Regional Planning Commission (MVRPC) p lanning area. Emissions for this portion of Warren County have been included in the inventory. Clinton County is outside of the OKI region, but is part of the ozone nonattainment area. The Ohio Department of Transportation (ODOT) is the lead pla nning agency for Clinton County. The Clinton County emissions analysis has been prep ared by ODOT and has been included in this emissions inventory.

OKI, as the MPO, is responsible for transportation planning and air quality/transportation conformity. Transportation conformity is a mechanis m to ensure that federal funding and approval are given to those transportation activiti es that are consistent with the air quality goals of the State Implementation Plans (SIPs) for Indiana, Kentucky and Ohio. The SIPs include an inventory of projected emissions fr om vehicles. The projected inventory is also known as the emissions budget. This budget establishes a maximum allowable limit on future emissions from vehicles (mobile sou rces). OKI’s transportation plans and programs must be shown to be in conformity with all SIP provisions. The conformity process is a quantitative analysis, using U.S.EPA’s vehicle emissions software (currently MOBILE), demonstrating that forecasted regional veh icle emissions do not exceed the established budget.

This report documents the process for developing th e mobile emissions inventory for the
Cincinnati ozone nonattainment area. Section 2 de tails the process and procedures used and Section 3 describes the transportation network. Section 4 provides the mobile emissions inventory.HighlandHighlandHighlandHighlandBrkenacBrkenBrackenBrackenPendletonPendletonPendletonPendletonCarrollCarrollCarrollCarrollGallatinGallatinGallatinGallatinSwitzerlandSwitzerlandSwitzerlandSwitzerlandOhioOhioOhioOhioBooneBooneBooneBooneKentonKentonKentonKentonCampbellCampbellCampbellCampbellHamiltonHamiltonHamiltonHamiltonFayetteFayetteFayetteFayetteGreeneGreeneGreeneGreeneFayetteFayetteFayetteFayetteCincinnatiCincinnatiCincinnatiCincinnatiCincinnatiCincinnatiCincinnatiCincinnatiCincinnatiGreenfieldManchesterBethelWashingtonCourtHouseConnersvilleDearbornDearbornDearbornDearbornFranklinFranklinFranklinFranklinRipleyRipleyRipleyRipleyUnoniUnonUnoniUnonGrantGrantGrantGrantAdamsAdasmAdamsAdasBrownBrownBrownBrownButlerButlerButlerButlerClermontClermontClermontClermontClintonClintonClintonClintonWarrenWarrenWarrenWarrenOxfordWilmingtonHamiltonBlanchesterHillsboroGeorgetownRipleyCincinnati-Hamilton,OH-KY-IN8-hourOzoneNonattainmentAreaDearbornCo(part)LawrenceburgTownshipBooneCoCampbellCoKentonCoButlerCoClermontCoClintonCoHamiltonCoWarrenCoBoundariesandlocationsareforillustrativepurposesonly.Thisisnotaregulatorydocument.

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2. MOBILE SOURCE EMISSION FORECAST PROCESS

OKI Travel Demand Model Transportation system performance was estimated usi ng the OKI Travel Demand Model Version 7.6. The OKI Travel Demand Model is compos ed of TRANPLAN programs, CUBE Voyager programs and a series of FORTRAN progr ams written by OKI. It is a state of the practice model that uses the standard 4 phase sequential modeling approach of trip generation, distribution, modal choice and ass ignment. The model uses demographic and land use data and capacity and free-flow speed characteristics for each roadway segment in the network to produce a “loaded” highwa y network with forecasted traffic volumes with revised speeds based on specified spee d/capacity relationships.

Travel analysis zones are the basic geographic unit for estimating travel in the OKI model. The OKI region is subdivided into 1608 traff ic analysis zones to permit detail as well as manageability. A variety of socioeconomic data items are used in the OKI transportation planning process. These data are use d primarily to forecast future travel patterns by serving as independent variables in OKI trip generation equations. The following categories of planning data are utilized:

• Population (household and group quarter)

• Households

• Household vehicles

• Employment (by employment category and zone of work )

• Labor force participation (by zone of residence)

• Area type

The principal data requirements of the OKI travel d emand forecasting model are population and employment. From these variables, ot her characteristics including households, labor force, and personal vehicles may be derived. OKI utilizes both base year (2005) and future year data (2010, 2020 and 20 30) in the planning process. Other years are interpolated as needed. Planning data ar e maintained at the Traffic Analysis Zone (TAZ) level, and originate in the 2000 Census of Population and Housing. Base year 2005 and future year data for each variable ar e developed through various methods. More detailed explanation of base year and future y ear data generation for each of the above-mentioned categories of planning data follows . All of the variables represent the latest OKI planning assumptions.

Population Base and Future Year Data: Population data for bas e year 2005 and future years 2010, 2020 and 2030 originate with the 2000 Census of Pop ulation and Housing. Utilizing ArcView GIS, population data at the zonal level for 2000 was derived from the area proportion allocation of block level population.

As a tri-state regional planning agency, OKI uses c ounty level projections as prepared by the respective state data centers (Ohio Department of Development Office of Strategic Research, Kentucky State Data Center and Indiana Bu siness Research Center) as control

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totals. The most current projections (years 2005 t o 2030) were released by the Ohio and Indiana state data centers in 2003 and the Kentucky State Data Center in 2004. Population projections at the zonal level are calcu lated by multiplying household size by the projected zonal households. Household size is f actored so that, in each county, the sum of the zonal populations equals the control tot al.

Households Base Year Data: Household data for base year 2005 originates with the 2000 Census of Population and Housing. Utilizing the geographic in formation system ArcMap,
household data at the zonal level for 2000 was deri ved from the area proportion
allocation of block level households. Year 2000 hou sehold data was updated to 2005 with residential building permits issued between January 2000 and December 2004. The residential building locations were geocoded in Arc Map, then aggregated to the TAZs. The housing unit totals for each TAZ were converted to households by applying a vacancy rate, an adjustment for permitted but unbui lt units, and subtracting demolitions (where data was available). These households were t hen added to the year Census 2000
zonal household total to arrive at 2005 households for each TAZ.

Future Year Data: The preparation of household proj ections was accomplished by calculating the number of households for a projecte d county population using ratios of householders to total population by age specific co horts derived from the 2000 Census for each analysis year. Disaggregation to TAZs was determined by historical trends, existing and future land use, topography, flood pla in information, availability of land, local knowledge and other factors.

Household Vehicles Base and Future Year Data: Base and future year ho usehold vehicle data were obtained from the 2000 Census of Population and Housing. The 2000 Census is the only source of household vehicle data available at the block group level. Average vehicles per household were calculated for block groups then app lied to the TAZs associated with each block group. The 2005, 2010, 2020 and 2030 veh icles per household level was held at the 2000 level based on the fact that, since 200 2, the number of vehicles per household has exceeded the number of drivers per household.

Labor Force Base and Future Year Data: The OKI labor force is a function of the population as determined by a labor force participation ratio (th e number of employed persons in the labor force per persons 16 and over). Household dat a for base year 2005 originates with the 2000 Census of Population and Housing. Utilizin g the geographic information system ArcMap, household data at the zonal level for 2000 was derived from the area proportion allocation of block group level employed labor forc e. The labor force projections for 2005, 2010, 2020 and 2030 were based on the most re cent projections of national labor force participation rates by age and sex cohorts fr om the U.S. Department of Labor, Bureau of Labor Statistics for each of those years. These rates were then applied to the projected county age/sex cohorts and adjusted to el iminate the unemployed to arrive at a county employed labor force control total. Employe d labor force at the zonal level is

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calculated by multiplying the labor force participa tion rate by the zonal population. The labor force participation rate is adjusted so that, in each county, the sum of the zonal labor force counts equals the control total.

Employment Base Year Data: Quarterly Census of Employment and Wages (QCEW or ES202) data for 2005 was utilized as the primary tool to calcul ate employment at the zonal level. Individual business records containing physical loc ation, number of employees and SIC code were geocoded through ArcMap and aggregated to the TAZ level. This data set was supplemented by other sources of data to complete t he commuting employment picture in the OKI region. Each zone’s employment was divided according to the SIC code into three classes (retail, office, industrial) based up on the potential for generating trips.

Future Year Data: For future year employment proje ction, calculation was first made of the employment at the regional level. At the region al level, employment is a calculation of the region’s employed labor force minus workers who live in the region but commute out to work, plus workers who live outside the regi on but commute in to work. The regional total was disaggregated first to the count y level based on historic trends and expected changes in the county’s share of the regio n’s employment and then to the TAZ level. Disaggregation to TAZs was determined by his torical trends, existing and future land use, topography, flood plain information, avai lability of land, local knowledge and
other factors.

Area Type Base and Future Year Data: For each analysis year, each TAZ is assigned an area type designation as CBD, Urban, Suburban or Rural based on population and employment
densities.

Model Calibration
OKI’s Travel Demand Model has been validated to obs erved traffic volumes for the model base year 2005. The modeling network encompa sses the entire ozone nonattainment area with the exception of Clinton Co unty, Ohio. The modeling network also includes Greene, Miami and Montgomery counties in Ohio and the remainder of Dearborn County Indiana. The difference between e stimated vehicle miles traveled (VMT) and 2005 observed VMT is less than 1%. A hig hway screenline analysis compares the screenline observed and simulated traf fic volume discrepancies with the
ODOT standard of maximum desirable deviation. The comparison shows that the model performs at a satisfactory level and all the errors were under the ODOT curve. Further information can be found in OKI’s 2007 report, “ OKI/MVRPC Travel Demand Model Methodology/ Validation Report ”. For the calibration, OKI used over 3000 traffic counts collected through 2006 by the Ohio Department of Tr ansportation (ODOT), the Kentucky Transportation Cabinet, many county and local gover nments, transportation engineering consultants, and OKI. These traffic counts cover n early 50% percent of the links in the OKI portion of the modeling network. The methodolo gy provides consistency with past emission inventory and conformity analysis work per formed by OKI.

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Local Inputs and Post-Model Processing OKI incorporates a variety of sources of local data to both improve and confirm the accuracy of VMT, as well as other travel-related pa rameters. Free flow speeds used on the highway and transit networks are based on trave l time studies performed locally. The OKI post-processing program, IMPACT, uses the loade d highway network to generate VMT by hour, VMT by speed distribution and VMT by f acility type. These tables are then included as input into MOBILE6.2. Two separat e sets of VMT tables are generated: one for the four Ohio counties plus Dearborn County Indiana, and a second for the three Kentucky counties. The VMT by hour tables utilize hourly traffic distribution and directional split factors for different roadway typ es as developed by OKI. The main source of the data was the permanent traffic counti ng stations located throughout the OKI region for the years of 1998-2002. This data was s upplemented with data collected at coverage count stations (locations with counts take n on only one-two days). The stations were classified by area type: urban and rural, and functional classification: freeway, arterial and collector. Speeds representing various “loaded” conditions (with traffic volumes) are estimated using techniques from the 19 97 Highway Capacity Manual. This permits the estimation of speeds as conditions vary from hour to hour on the different facility types throughout the region. The IMPACT p rogram performs the appropriate summation by area and roadway type as well as regio nal totals. OKI has also developed seasonal conversion factors to adjust traffic volum es to summer conditions. The factors were derived from local data collected at permanent traffic counting stations during 1994- 1997 utilizing the average daily traffic monthly co nversion factors for June, July and August. Further information on OKI’s IMPACT progra m is documented in the report, “Travel Demand Model Summary Reporting and Impact S ummary Reporting: OKI/MVRPC Travel Demand Model User’s Guide”, OKI 20 03.

Emission Factor Model OKI’s conformity assessment utilized U.S.EPA’s emis sions model MOBILE6.2 to develop emission factors for VOC’s, NO X 

# and PM2.5. The MOBILE6.2 input file contains local parameters, developed through consul tation with ODOT and OEPA, for temperature, fuel programs and fuel characteristics . The local parameters are combined
with the VMT tables from the OKI Travel Demand Mode l to produce one set of emission factors measured in grams per mile for the appropri ate calendar year (from 1952 to 2050). These emission factors are then multiplied by VMT. The methodologies incorporated into MOBILE6.2 for estimating emission s are based on methods and research conducted by U.S.EPA. OKI’s development o f MOBILE6.2 input values were guided by the U.S.EPA’s document “Technical Guidance on the Use of MOBILE6 for Emission Inventory Preparation”, January 2002 . MOBILE6.2 inputs and outputs are included in the appendices.

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3. MOBILE SOURCE EMISSIONS INVENTORY

Table 1. Mobile Source Emissions by State/County fo r the Cincinnati Ozone Nonattainment Area (tons per day)

State 2005 2008 2015 2020

Dearborn NonAttainment Portion
VOC 

# 1.00 0.75 0.50 0.42

NOx 

# 1.44 1.14 0.60 0.42 Kentucky

Boone
VOC 

# 4.33 4.00 3.17 2.96

CO 

# 47.20 44.46 37.41 38.21

NOx 

# 10.27 8.53 4.63 3.45 Campbell

VOC 

# 2.52 2.29 1.74 1.55

CO 

# 27.50 25.52 20.39 19.97

NOx 

# 5.98 4.88 2.54 1.81

Kenton
VOC 

# 4.32 3.85 2.8 5 2.5 6

CO 

# 47.19 42.76 33.68 32.97

NOx 

# 10.39 8.37 4.23 3.01

OKI KY Total
VOC 

# 11.17 10.14 7 .7 6 7.0 7

CO 

# 121.89 112.74 91.48 91.14

NOx 

# 26.64 21.78 11.40 8.27

Ohio

Butler
VOC 

# 9.94 7.87 4.87 4.50

NOx 

# 18.88 16.05 7.55 5.37

Clermont

VOC 

# 6.86 5.42 3.29 3.04

NOx 

# 13.04 11.05 5.10 3.63

Hamilton
VOC 

# 29.47 22.70 13.44 12.00

NOx 

# 56.51 46.80 21.11 14.44

Warren
VOC 

# 7.97 6.26 4.02 3.88

NOx 

# 15.15 12.76 6.23 4.63

OKI OH Total

VOC 

# 54.24 42.25 25.62 23.42

NOx 

# 103. 58 86.66 39.99 28.0 7

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Table 1 Cont. Clinton, OH

VOC 

# 3.02 2.33 1.47 1.22

NOx 

# 5.07 3.87 2.02 1.41

OH VOC Total 

# 57.26 44.58 27.09 24.64

OH NOx Total 

# 108.65 90.53 42.01 29.48

NonAttainment Area Total
VOC 

# 69.43 55.47 35.3 5 32.1 3

NOx 

# 136.73 113.45 54.01 38.17



# The mobile source VOC and NO
x 

# emissions inventory for all counties in the nonattainment area is provided in Table 1. Table 2 shows the mobile source inventory for the combined Indiana and Ohio portions of the C incinnati ozone nonattainment area. Table 3 is the mobile source emissions inventory fo r the Kentucky portion of the
nonattainment area. At the discretion of the India na Department of Environmental Management, the Kentucky Division for Air Quality a nd the Ohio EPA, an additional safety margin may be added to the 2008 inventory fo r the purpose of establishing a motor vehicle emission budget (MVEB). The addition of th is safety margin would not interfere with the SIPs purpose. In the absence of an additi onal safety margin, the 2008 inventory, as presented below, will serve as the (MVEB) for tr ansportation conformity.

Table 2 Mobile Source Emissions Inventory for the Indiana a nd Ohio Portions of the Cincinnati Ozone Nonattainment Area (tons per day)

2005 2008 MVEB 2015 2020

VOC 58.26 45.33 27.59 25.06

NOx 110.09 91.67 42.61 29.90

Table 3 Mobile Source Emissions Inventory for the Kentucky Portion of the Cincinnati Ozone Nonattainment Area (tons per day)

2005 2008 MVEB 2015 2020

VOC 11.17 10.14 7.7 6 7.0 7
NOx 26.64 21.78 11.40 8.27

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# APPENDIX A

MOBILE6.2 Input/Output Files for Indiana Portion of

Nonattainment Area

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VMT By Hour (INHVMT.D), all analysis years

VMT BY HOUR
0.0478 0.0719 0.0796 0.0666 0.0563 0.0532
0.0545 0.0543 0.0515 0.0523 0.0560 0.0565
0.0504 0.0377 0.0266 0.0209 0.0197 0.0171
0.0142 0.0156 0.0188 0.0224 0.0251 0.0310



# 2005 VMT by Speed Bin (INSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0115 0.0098 0.0000 0.0000 0.0000 0.0000 0.9787
1 2 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 47 0.0053 0.0085 0.0000 0.0000 0.0000 0.0000 0.9814
1 3 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 44 0.0049 0.0079 0.0000 0.0000 0.0000 0.0000 0.9828
1 4 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0093 0.0079 0.0000 0.0000 0.0000 0.0000 0.9829
1 5 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0090 0.0077 0.0000 0.0000 0.0000 0.0000 0.9833
1 6 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0096 0.0082 0.0000 0.0000 0.0000 0.0000 0.9822
1 7 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0093 0.0079 0.0000 0.0000 0.0000 0.0000 0.9827
1 8 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0090 0.0076 0.0000 0.0000 0.0000 0.0000 0.9834
1 9 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0086 0.0073 0.0000 0.0000 0.0000 0.0000 0.9841
1 10 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0083 0.0070 0.0000 0.0000 0.0000 0.0000 0.9847
1 11 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0080 0.0068 0.0000 0.0000 0.0000 0.0000 0.9852
1 12 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0067 0.0057 0.0000 0.0000 0.0000 0.0000 0.9876
1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0066 0.0056 0.0000 0.0000 0.0000 0.0000 0.9878
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0079 0.0067 0.0000 0.0000 0.0000 0.0000 0.9853
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0080 0.0068 0.0000 0.0000 0.0000 0.0000 0.9852
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0076 0.0065 0.0000 0.0000 0.0000 0.0000 0.9859
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0085 0.0073 0.0000 0.0000 0.0000 0.0000 0.9842
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0075 0.0063 0.0000 0.0000 0.0000 0.0000 0.9862
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0088 0.0075 0.0000 0.0000 0.0000 0.0000 0.9837
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0098 0.0083 0.0000 0.0000 0.0000 0.0000 0.9819
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0094 0.0080 0.0000 0.0000 0.0000 0.0000 0.9827
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0098 0.0083 0.0000 0.0000 0.0000 0.0000 0.9818
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0100 0.0085 0.0000 0.0000 0.0000 0.0000 0.9815
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0104 0.0089 0.0000 0.0000 0.0000 0.0000 0.9807
2 1 0.0000 0.0000 0.0000 0.1622 0.0097 0.1308 0.04 17 0.0908 0.5647 0.0000 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0000 0.0000 0.1713 0.0099 0.1305 0.04 52 0.0877 0.5553 0.0000 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0000 0.0000 0.1783 0.0101 0.1313 0.04 53 0.0886 0.5464 0.0000 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0000 0.0000 0.2060 0.0103 0.1221 0.03 79 0.0894 0.5343 0.0000 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0000 0.2128 0.0104 0.1212 0.03 75 0.0893 0.5288 0.0000 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0000 0.2008 0.0101 0.1206 0.03 75 0.0880 0.5430 0.0000 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0000 0.0000 0.2200 0.0104 0.1172 0.03 60 0.0876 0.5288 0.0000 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0000 0.0000 0.2243 0.0106 0.1184 0.03 63 0.0886 0.5217 0.0000 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0000 0.2208 0.0106 0.1200 0.03 69 0.0892 0.5226 0.0000 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0000 0.2360 0.0108 0.1176 0.03 58 0.0891 0.5108 0.0000 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0000 0.0000 0.2240 0.0107 0.1216 0.03 74 0.0904 0.5159 0.0000 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0000 0.2072 0.0105 0.1266 0.03 94 0.0918 0.5244 0.0000 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.2062 0.0108 0.1324 0.04 14 0.0950 0.5141 0.0000 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.1941 0.0107 0.1370 0.04 33 0.0967 0.5182 0.0000 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.2127 0.0109 0.1325 0.04 14 0.0956 0.5069 0.0000 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.2142 0.0109 0.1304 0.04 06 0.0945 0.5094 0.0000 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.2076 0.0106 0.1272 0.03 96 0.0922 0.5228 0.0000 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.2327 0.0110 0.1233 0.03 78 0.0920 0.5032 0.0000 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.2009 0.0097 0.1118 0.03 45 0.0832 0.5600 0.0000 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.1925 0.0096 0.1137 0.03 53 0.0836 0.5652 0.0000 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.2259 0.0108 0.1228 0.03 78 0.0913 0.5114 0.0000 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.1941 0.0104 0.1305 0.04 10 0.0931 0.5308 0.0000 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.1926 0.0105 0.1339 0.04 22 0.0949 0.5258 0.0000 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.1856 0.0103 0.1314 0.04 15 0.0929 0.5383 0.0000 0.0000 0.0000 0.0000 0.0000



# 2005 VMT by Facility (INFVMT.D)

VMT BY FACILITY
1 0.236 0.530 0.229 0.005
0.258 0.508 0.229 0.005
0.261 0.500 0.234 0.005
0.260 0.487 0.248 0.005
0.259 0.484 0.253 0.004
0.256 0.495 0.244 0.005
0.252 0.486 0.257 0.004
0.252 0.482 0.262 0.004
0.260 0.478 0.258 0.004
0.263 0.467 0.266 0.004

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 11

0.267 0.470 0.259 0.004
0.301 0.457 0.238 0.004
0.290 0.461 0.246 0.004
0.255 0.489 0.252 0.004
0.247 0.484 0.266 0.004
0.260 0.476 0.261 0.004
0.257 0.485 0.254 0.004
0.274 0.458 0.264 0.004
0.296 0.475 0.225 0.005
0.279 0.490 0.225 0.005
0.248 0.480 0.268 0.004
0.239 0.504 0.252 0.004
0.228 0.510 0.258 0.004
0.230 0.516 0.249 0.005

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004



# 2005 MOBILE6.2 Input File (INSCN.IN)

* Mobile6 file for Dearborn County, IN * created 6/7/06, ajr,pre 2006
******************* Header Section ************** **********
MOBILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE REPORT FILE : in.rpt

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : inemiss.tb1

RUN DATA

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 12 ******************* Run Section ***************** **********

VMT BY HOUR : INHVMT.D

SPEED VMT : INSVMT.D

VMT BY FACILITY : INFVMT.D
*REG DIST : INREG.D

EXPRESS HC AS VOC :

EXPAND BUS EFS : ******************* Summer Scenario Section ***** ***************** SCENARIO RECORD : Indiana Emissions - CY20xx
CALENDAR YEAR : 2005
EVALUATION MONTH : 7
SEASON : 1 MIN/MAX TEMP : 61.0 95.0
ABSOLUTE HUMIDITY : 75.0
FUEL PROGRAM : 1
FUEL RVP : 9.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 313.00 ******************* Annual Scenario Section ***** ***************** SCENARIO RECORD : Indiana Emissions - CY20xx
CALENDAR YEAR : 2005
EVALUATION MONTH : 7 MIN/MAX TEMP : 47.0 64.0
FUEL PROGRAM : 1
FUEL RVP : 9.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 318.00
******************* End of Run ****************** **********

END OF RUN



# 2005 MOBILE6.2 Output Report (IN.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: INSCN.IN (file 1, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external * data file: INHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: INSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: INFVMT.D

Reading User Supplied ROADWAY VMT Factors

* # # # # # # # # # # # # # # # # # # # # # # # # #
* Indiana Emissions - CY20xx * File 1, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b

* Reading Ammonia (NH3) Basic Emissiion Rates
* from the external data file PMNH3BER.D

* Reading Ammonia (NH3) Sulfur Deterioration Rates
* from the external data file PMNH3SDR.D

Calendar Year: 2005 Month: July Altitude: Low Minimum Temperature: 61.0 (F) Maximum Temperature: 95.0 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 8.5 psi Fuel Sulfur Content: 92. ppm

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 13 Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.4158 0.3387 0.1165 0.0360 0.0006 0.0019 0.0849 0.0057 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 1.421 1.461 2.332 1.684 2.335 0.626 0.870 0.620 3.37 1.516 Composite CO : 12.72 15.11 20.39 16.46 22.20 1.741 1.521 3.691 20.98 14.019 Composite NOX : 0.948 1.148 1.483 1.234 4.207 1.485 1.544 12.551 1.20 2.183

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0003 0.0009 0.0016

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 9.702 0.586 0.842 Composite CO : 137.29 4.535 3.219 Composite NOX : 8.274 15.786 13.826

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # # * Indiana Emissions - CY20xx * File 1, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b

Calendar Year: 2005 Month: July Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 9.0 psi Fuel Sulfur Content: 92. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.4158 0.3387 0.1165 0.0360 0.0006 0.0019 0.0849 0.0057 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 1.148 1.297 2.093 1.501 1.786 0.626 0.870 0.620 2.22 1.292 Composite CO : 15.35 18.58 24.01 19.97 20.81 1.741 1.521 3.691 17.79 16.641 Composite NOX : 0.924 1.190 1.544 1.281 4.334 1.485 1.544 12.551 1.41 2.200

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0003 0.0009 0.0016

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 7.662 0.586 0.842 Composite CO : 118.47 4.535 3.219 Composite NOX : 8.782 15.786 13.826

--------------------------------------------------- --------------------------------------------------- ----------------


# 2008 VMT by Speed bin (INSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0132 0.0090 0.0000 0.0000 0.0000 0.0000 0.9779
1 2 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 47 0.0068 0.0078 0.0000 0.0000 0.0000 0.0000 0.9807
1 3 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 44 0.0063 0.0072 0.0000 0.0000 0.0000 0.0000 0.9821
1 4 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0106 0.0072 0.0000 0.0000 0.0000 0.0000 0.9822
1 5 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0103 0.0070 0.0000 0.0000 0.0000 0.0000 0.9827
1 6 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0110 0.0075 0.0000 0.0000 0.0000 0.0000 0.9815
1 7 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0107 0.0073 0.0000 0.0000 0.0000 0.0000 0.9820
1 8 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0103 0.0070 0.0000 0.0000 0.0000 0.0000 0.9827
1 9 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0098 0.0067 0.0000 0.0000 0.0000 0.0000 0.9835
1 10 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0095 0.0064 0.0000 0.0000 0.0000 0.0000 0.9841
1 11 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0092 0.0062 0.0000 0.0000 0.0000 0.0000 0.9846
1 12 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0077 0.0052 0.0000 0.0000 0.0000 0.0000 0.9871
1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0076 0.0052 0.0000 0.0000 0.0000 0.0000 0.9873
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0091 0.0062 0.0000 0.0000 0.0000 0.0000 0.9848
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0092 0.0062 0.0000 0.0000 0.0000 0.0000 0.9846

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 14 1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0087 0.0059 0.0000 0.0000 0.0000 0.0000 0.9853
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0098 0.0067 0.0000 0.0000 0.0000 0.0000 0.9836
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0086 0.0058 0.0000 0.0000 0.0000 0.0000 0.9856
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0101 0.0069 0.0000 0.0000 0.0000 0.0000 0.9831
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0112 0.0076 0.0000 0.0000 0.0000 0.0000 0.9812
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0107 0.0073 0.0000 0.0000 0.0000 0.0000 0.9820
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0112 0.0076 0.0000 0.0000 0.0000 0.0000 0.9811
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0115 0.0078 0.0000 0.0000 0.0000 0.0000 0.9807
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0119 0.0081 0.0000 0.0000 0.0000 0.0000 0.9799
2 1 0.0000 0.0000 0.0000 0.1745 0.0083 0.1008 0.04 69 0.0340 0.6355 0.0000 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0000 0.0000 0.1844 0.0088 0.1002 0.05 07 0.0299 0.6260 0.0000 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0000 0.0000 0.1909 0.0091 0.0999 0.05 06 0.0299 0.6195 0.0000 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0000 0.0000 0.2202 0.0105 0.0909 0.04 27 0.0319 0.6037 0.0000 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0000 0.2268 0.0108 0.0896 0.04 21 0.0316 0.5991 0.0000 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0000 0.2140 0.0102 0.0896 0.04 21 0.0314 0.6126 0.0000 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0000 0.0000 0.2339 0.0111 0.0858 0.04 04 0.0306 0.5981 0.0000 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0000 0.0000 0.2380 0.0113 0.0864 0.04 07 0.0308 0.5928 0.0000 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0000 0.2343 0.0112 0.0878 0.04 14 0.0312 0.5941 0.0000 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0000 0.2505 0.0119 0.0852 0.04 03 0.0307 0.5813 0.0000 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0000 0.0000 0.2374 0.0113 0.0890 0.04 19 0.0315 0.5889 0.0000 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0000 0.2191 0.0104 0.0936 0.04 39 0.0324 0.6006 0.0000 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.2180 0.0104 0.0983 0.04 60 0.0336 0.5936 0.0000 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.2056 0.0098 0.1029 0.04 80 0.0347 0.5990 0.0000 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.2249 0.0107 0.0981 0.04 60 0.0337 0.5865 0.0000 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.2265 0.0108 0.0964 0.04 52 0.0332 0.5880 0.0000 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.2206 0.0105 0.0945 0.04 43 0.0327 0.5974 0.0000 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.2472 0.0118 0.0901 0.04 25 0.0320 0.5764 0.0000 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.2152 0.0103 0.0829 0.03 90 0.0297 0.6229 0.0000 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.2069 0.0099 0.0852 0.04 00 0.0303 0.6278 0.0000 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.2422 0.0115 0.0908 0.04 28 0.0322 0.5805 0.0000 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.2073 0.0099 0.0983 0.04 60 0.0337 0.6049 0.0000 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.2054 0.0098 0.1010 0.04 72 0.0343 0.6024 0.0000 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.1980 0.0094 0.0993 0.04 64 0.0338 0.6131 0.0000 0.0000 0.0000 0.0000 0.0000



# 2008 VMT by Facility Type (INFVMT.D)

VMT BY FACILITY
1 0.244 0.539 0.211 0.006
0.267 0.516 0.212 0.005
0.269 0.510 0.216 0.005
0.268 0.495 0.233 0.005
0.266 0.492 0.237 0.005
0.262 0.504 0.229 0.005
0.258 0.494 0.242 0.005
0.257 0.492 0.247 0.005
0.266 0.488 0.242 0.004
0.269 0.475 0.252 0.004
0.273 0.480 0.243 0.004
0.307 0.468 0.221 0.004
0.295 0.473 0.228 0.004
0.261 0.503 0.233 0.004
0.252 0.497 0.247 0.004
0.265 0.489 0.243 0.004
0.263 0.495 0.237 0.004
0.280 0.467 0.249 0.004
0.304 0.479 0.212 0.005
0.288 0.494 0.212 0.006
0.256 0.486 0.253 0.005
0.246 0.514 0.235 0.005
0.234 0.522 0.239 0.005
0.237 0.527 0.231 0.005

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 15

0.010 0.949 0.035 0.002
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004



# 2008 MOBILE6.2 Input File (INSCN.IN) * Mobile6 file for Dearborn County, IN * created 4/9/07, ajr post em62in.06c
******************* Header Section ************** **********
MOBILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE REPORT FILE : in.rpt

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : inemiss.tb1

RUN DATA ******************* Run Section ***************** **********

VMT BY HOUR : INHVMT.D

SPEED VMT : INSVMT.D

VMT BY FACILITY : INFVMT.D

EXPAND BUS EFS :
REBUILD EFFECTS : 0.10
******************* Summer Scenario Section ***** ***************** SCENARIO RECORD : Indiana Emissions - CY20xx
CALENDAR YEAR : 2008

EVALUATION MONTH : 7
SEASON : 1

M IN/MAX TEMP : 62.0 91.3
FUEL PROGRAM : 1
FUEL RVP : 9.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 16

DIESEL SULFUR : 43 ******************* Annual Scenario Section ***** ***************** SCENARIO RECORD : Indiana Emissions - CY20xx
CALENDAR YEAR : 2008

EVALUATION MONTH : 7 MIN/MAX TEMP : 47.0 64.0
FUEL PROGRAM : 1
FUEL RVP : 9.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43
******************* End of Run ****************** ***** *****

END OF RUN



# 2008 MOBILE6.2 Output Report (IN.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: INSCN.IN (file 1, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external
* data file: INHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: INSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: INFVMT.D

Reading User Supplied ROADWAY VMT Factors

* # # # # # # # # # # # # # # # # # # # # # # # # #
* Indiana Emissions - CY20xx * File 1, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b

HDDV DEFEAT DEVICE EFFECTS ARE PRESENT. THE REBUIL D FRACTION IS 0.10.

* Reading Ammonia (NH3) Basic Emissiion Rates
* from the external data file PMNH3BER.D

* Reading Ammonia (NH3) Sulfur Deterioration Rates
* from the external data file PMNH3SDR.D M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds
the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2008 Month: July
Altitude: Low Minimum Temperature: 62.0 (F) Maximum Temperature: 91.3 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 8.6 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 17 Reformulated Gas: No

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All
Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ -----

- VMT Distribution: 0.3728 0.3705 0.1273 0.0359 0.0004 0.0019 0.0857 0.0055
1.0000

------------------------------------------------- --------------------------------------------------- -----------------

- Composite Emission Factors (g/mi): Composite VOC : 1.026 1.055 1.747 1.232 1.634 0.311 0.595 0.504 2.98
1.115 Composite CO : 9.67 11.41 15.71 12.51 15.69 1.215 1.028 2.758 19.79
10.745 Composite NOX : 0.686 0.860 1.238 0.957 2.909 0.776 1.065 9.881 1.23
1.692

------------------------------------------------- --------------------------------------------------- -----------------

- Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0002 0.0009 0.0017

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 7.973 0.374 0.726 Composite CO : 104.18 3.451 2.765 Composite NOX : 7.683 13.272 11.989

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # #
* Indiana Emissions - CY20xx * File 1, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds
the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2008 Month: July
Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 9.0 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All
Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ -----

- VMT Distribution: 0.3728 0.3705 0.1273 0.0359 0.0004 0.0019 0.0857 0.0055
1.0000

------------------------------------------------- --------------------------------------------------- -----------------

- Composite Emission Factors (g/mi): Composite VOC : 0.876 0.968 1.598 1.129 1.299 0.311 0.595 0.504 2.18
0.992 Composite CO : 12.16 14.76 19.91 16.08 15.68 1.215 1.028 2.758 17.64
13.440 Composite NOX : 0.675 0.901 1.302 1.003 3.017 0.776 1.065 9.881 1.42
1.716

------------------------------------------------- --------------------------------------------------- -----------------

- Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 18 VMT Mix: 0.0002 0.0009 0.0017

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 6.524 0.374 0.726 Composite CO : 98.89 3.451 2.765 Composite NOX : 8.570 13.272 11.989

--------------------------------------------------- --------------------------------------------------- ---------------- 

# 2015 VMT by Speed Bin (INSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0135 0.0089 0.0000 0.0000 0.0000 0.0000 0.9777
1 2 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 96 0.0022 0.0077 0.0000 0.0000 0.0000 0.0000 0.9805
1 3 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 89 0.0020 0.0072 0.0000 0.0000 0.0000 0.0000 0.9820
1 4 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 43 0.0066 0.0071 0.0000 0.0000 0.0000 0.0000 0.9820
1 5 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0105 0.0069 0.0000 0.0000 0.0000 0.0000 0.9825
1 6 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0112 0.0074 0.0000 0.0000 0.0000 0.0000 0.9814
1 7 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0109 0.0072 0.0000 0.0000 0.0000 0.0000 0.9819
1 8 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0105 0.0069 0.0000 0.0000 0.0000 0.0000 0.9826
1 9 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0101 0.0066 0.0000 0.0000 0.0000 0.0000 0.9833
1 10 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0097 0.0064 0.0000 0.0000 0.0000 0.0000 0.9839
1 11 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0094 0.0062 0.0000 0.0000 0.0000 0.0000 0.9845
1 12 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0078 0.0052 0.0000 0.0000 0.0000 0.0000 0.9870
1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0077 0.0051 0.0000 0.0000 0.0000 0.0000 0.9872
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0093 0.0061 0.0000 0.0000 0.0000 0.0000 0.9846
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0094 0.0062 0.0000 0.0000 0.0000 0.0000 0.9844
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0089 0.0059 0.0000 0.0000 0.0000 0.0000 0.9852
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0100 0.0066 0.0000 0.0000 0.0000 0.0000 0.9834
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0087 0.0058 0.0000 0.0000 0.0000 0.0000 0.9855
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0103 0.0068 0.0000 0.0000 0.0000 0.0000 0.9829
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0114 0.0075 0.0000 0.0000 0.0000 0.0000 0.9810
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0110 0.0072 0.0000 0.0000 0.0000 0.0000 0.9818
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0115 0.0076 0.0000 0.0000 0.0000 0.0000 0.9809
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0117 0.0077 0.0000 0.0000 0.0000 0.0000 0.9805
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0122 0.0080 0.0000 0.0000 0.0000 0.0000 0.9797
2 1 0.0000 0.0000 0.0000 0.1735 0.0086 0.0897 0.06 35 0.0801 0.5846 0.0000 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0000 0.0000 0.1832 0.0087 0.0914 0.06 54 0.0766 0.5746 0.0000 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0000 0.0000 0.1907 0.0089 0.0937 0.06 75 0.0905 0.5487 0.0000 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0000 0.0000 0.2194 0.0090 0.0844 0.05 91 0.0774 0.5508 0.0000 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0000 0.2266 0.0091 0.0838 0.05 68 0.0790 0.5448 0.0000 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0000 0.2138 0.0088 0.0832 0.05 68 0.0778 0.5596 0.0000 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0000 0.0000 0.2339 0.0090 0.0811 0.05 44 0.0775 0.5440 0.0000 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0000 0.0000 0.2386 0.0091 0.0821 0.05 49 0.0784 0.5369 0.0000 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0000 0.2350 0.0092 0.0831 0.05 59 0.0789 0.5380 0.0000 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0000 0.2508 0.0093 0.0816 0.05 41 0.0789 0.5252 0.0000 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0000 0.0000 0.2385 0.0093 0.0843 0.05 67 0.0800 0.5313 0.0000 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0000 0.2211 0.0092 0.0875 0.05 99 0.0812 0.5411 0.0000 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.2206 0.0095 0.0915 0.06 31 0.0841 0.5313 0.0000 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.2080 0.0095 0.0946 0.06 60 0.0855 0.5364 0.0000 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.2275 0.0096 0.0917 0.06 30 0.0846 0.5237 0.0000 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.2289 0.0095 0.0903 0.06 18 0.0837 0.5259 0.0000 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.2216 0.0092 0.0879 0.06 02 0.0816 0.5395 0.0000 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.2479 0.0095 0.0856 0.05 73 0.0816 0.5181 0.0000 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.2131 0.0084 0.0771 0.05 20 0.0734 0.5759 0.0000 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.2044 0.0084 0.0783 0.05 34 0.0738 0.5818 0.0000 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.2406 0.0094 0.0851 0.05 72 0.0809 0.5268 0.0000 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.2075 0.0092 0.0900 0.06 24 0.0823 0.5486 0.0000 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.2062 0.0093 0.0924 0.06 43 0.0839 0.5439 0.0000 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.1984 0.0090 0.0905 0.06 32 0.0821 0.5568 0.0000 0.0000 0.0000 0.0000 0.0000



# 2015 VMT by Facility Type (INFVMT.D)

VMT BY FACILITY
1 0.248 0.545 0.201 0.006
0.270 0.522 0.202 0.005
0.274 0.514 0.208 0.005
0.272 0.499 0.225 0.005
0.271 0.495 0.230 0.005
0.267 0.507 0.221 0.005
0.263 0.496 0.236 0.005
0.262 0.493 0.240 0.005
0.271 0.489 0.236 0.005
0.274 0.477 0.245 0.004
0.278 0.480 0.237 0.004
0.314 0.467 0.215 0.004

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 19

0.303 0.472 0.221 0.004
0.268 0.503 0.226 0.004
0.258 0.497 0.241 0.004
0.272 0.488 0.236 0.004
0.269 0.497 0.230 0.005
0.285 0.468 0.242 0.004
0.307 0.483 0.204 0.005
0.290 0.500 0.204 0.006
0.259 0.491 0.245 0.005
0.251 0.518 0.227 0.005
0.239 0.525 0.231 0.005
0.242 0.530 0.223 0.005

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004



# 2015 MOBILE6.2 Input File (INSCN.IN) * Mobile6 file for Dearborn County, IN * created 4/9/07, ajr post em62in.06c
******************* Header Section ************** **********
MOBILE6 INPUT FILE :

POLLU TANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE REPORT FILE : in.rpt

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : inemiss.tb1

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 20

RUN DATA ******************* Run Section ***************** ******** **

VMT BY HOUR : INHVMT.D

SPEED VMT : INSVMT.D

VMT BY FACILITY : INF VMT.D

EXPAND BUS EFS :
REBUILD EFFECTS : 0.10 ******************* Summer Scenario Section ***** ***************** SCENARIO RECORD : Indiana Emissions - CY20xx
CALENDAR YEAR : 2015
EVALUATION MONTH : 7
SEASON : 1 MIN/MAX TEMP : 62.0 91.3
FUEL PROGRAM : 1
FUEL RVP : 9.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43 ******************* Annual Scenario Section ***** ***************** SCENARIO RECORD : Indiana Emissions - CY20xx
CALENDAR YEAR : 2015
EVALUATION MONTH : 7 MIN/MAX TEMP : 47.0 64.0
FUEL PROGRAM : 1
FUEL RVP : 9.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43
******************* End of Run ****************** **********

END OF RUN



# 2015 MOBILE6.2 Output File (IN.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: INSCN.IN (file 1, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external
* data file: INHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: INSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: INFVMT.D

Reading User Supplied ROADWAY VMT Factors

* # # # # # # # # # # # # # # # # # # # # # # # # #
* Indiana Emissions - CY20xx * File 1, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 21 * Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12

HDDV DEFEAT DEVICE EFFECTS ARE PRESENT. THE REBUIL D FRACTION IS 0.10.

* Reading Ammonia (NH3) Basic Emissiion Rates
* from the external data file PMNH3BER.D

* Reading Ammonia (NH3) Sulfur Deterioration Rates
* from the external data file PMNH3SDR.D M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds
the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2015 Month: July
Altitude: Low Minimum Temperature: 62.0 (F) Maximum Temperature: 91.3 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 8.6 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All
Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ -----

- VMT Distribution: 0.3031 0.4218 0.1449 0.0360 0.0003 0.0021 0.0866 0.0053
1.0000

------------------------------------------------- --------------------------------------------------- -----------------

- Composite Emission Factors (g/mi): Composite VOC : 0.544 0.634 1.127 0.760 0.858 0.106 0.324 0.337 2.97
0.672 Composite CO : 7.05 8.04 10.87 8.76 9.92 0.799 0.641 0.941 19.78
7.645 Composite NOX : 0.369 0.475 0.835 0.567 1.086 0.173 0.474 3.747 1.23
0.804

------------------------------------------------- --------------------------------------------------- -----------------

- Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 2.719 0.269 0.513 Composite CO : 18.47 1.573 1.485 Composite NOX : 3.970 6.114 7.085

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # #
* Indiana Emissions - CY20xx * File 1, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12 M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds
the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 22 Calendar Year: 2015 Month: July
Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 9.0 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All
Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ -----

- VMT Distribution: 0.3031 0.4218 0.1449 0.0360 0.0003 0.0021 0.0866 0.0053
1.0000

------------------------------------------------- --------------------------------------------------- -----------------

- Composite Emission Factors (g/mi): Composite VOC : 0.480 0.594 1.045 0.709 0.680 0.106 0.324 0.337 2.17
0.613 Composite CO : 9.61 10.58 13.92 11.44 10.16 0.799 0.641 0.941 17.63
9.935 Composite NOX : 0.358 0.494 0.873 0.591 1.114 0.173 0.474 3.747 1.43
0.817

------------------------------------------------- --------------------------------------------------- -----------------

- Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 2.104 0.269 0.513 Composite CO : 18.91 1.573 1.485 Composite NOX : 4.073 6.114 7.085

--------------------------------------------------- --------------------------------------------------- ----------------



# 2020 VMT by Speed Bin (INSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 53 0.0082 0.0086 0.0000 0.0000 0.0000 0.0000 0.9779
1 2 0.0000 0.0000 0.0000 0.0000 0.0000 0.0046 0.00 50 0.0021 0.0075 0.0000 0.0000 0.0000 0.0000 0.9807
1 3 0.0000 0.0000 0.0000 0.0000 0.0000 0.0043 0.00 46 0.0020 0.0070 0.0000 0.0000 0.0000 0.0000 0.9822
1 4 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 43 0.0066 0.0069 0.0000 0.0000 0.0000 0.0000 0.9822
1 5 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0105 0.0068 0.0000 0.0000 0.0000 0.0000 0.9827
1 6 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0112 0.0072 0.0000 0.0000 0.0000 0.0000 0.9816
1 7 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0109 0.0070 0.0000 0.0000 0.0000 0.0000 0.9821
1 8 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0105 0.0067 0.0000 0.0000 0.0000 0.0000 0.9827
1 9 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0101 0.0064 0.0000 0.0000 0.0000 0.0000 0.9835
1 10 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0097 0.0062 0.0000 0.0000 0.0000 0.0000 0.9841
1 11 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0094 0.0060 0.0000 0.0000 0.0000 0.0000 0.9846
1 12 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0078 0.0050 0.0000 0.0000 0.0000 0.0000 0.9872
1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0077 0.0050 0.0000 0.0000 0.0000 0.0000 0.9873
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0093 0.0059 0.0000 0.0000 0.0000 0.0000 0.9848
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0094 0.0060 0.0000 0.0000 0.0000 0.0000 0.9846
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0089 0.0057 0.0000 0.0000 0.0000 0.0000 0.9854
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0100 0.0064 0.0000 0.0000 0.0000 0.0000 0.9836
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0087 0.0056 0.0000 0.0000 0.0000 0.0000 0.9857
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0103 0.0066 0.0000 0.0000 0.0000 0.0000 0.9831
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0114 0.0073 0.0000 0.0000 0.0000 0.0000 0.9812
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0109 0.0070 0.0000 0.0000 0.0000 0.0000 0.9820
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0115 0.0074 0.0000 0.0000 0.0000 0.0000 0.9812
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0117 0.0075 0.0000 0.0000 0.0000 0.0000 0.9808
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0122 0.0078 0.0000 0.0000 0.0000 0.0000 0.9800
2 1 0.0000 0.0000 0.0000 0.1833 0.0076 0.0842 0.06 79 0.0777 0.5793 0.0000 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0000 0.0000 0.1934 0.0095 0.0864 0.06 88 0.0965 0.5455 0.0000 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0000 0.0000 0.2013 0.0096 0.0869 0.07 24 0.1084 0.5214 0.0000 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0000 0.0000 0.2313 0.0078 0.0790 0.06 89 0.0870 0.5259 0.0000 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0000 0.2388 0.0079 0.0785 0.06 05 0.0763 0.5380 0.0000 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0000 0.2255 0.0077 0.0780 0.06 06 0.0752 0.5531 0.0000 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0000 0.0000 0.2465 0.0078 0.0760 0.05 80 0.0748 0.5370 0.0000 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0000 0.0000 0.2514 0.0079 0.0768 0.05 85 0.0833 0.5220 0.0000 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0000 0.2476 0.0080 0.0778 0.05 95 0.0762 0.5310 0.0000 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0000 0.2641 0.0081 0.0764 0.05 76 0.0760 0.5179 0.0000 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0000 0.0000 0.2513 0.0081 0.0789 0.06 04 0.0772 0.5242 0.0000 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0000 0.2332 0.0081 0.0820 0.06 39 0.0824 0.5305 0.0000 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.2327 0.0083 0.0858 0.06 73 0.0813 0.5246 0.0000 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.2195 0.0083 0.0887 0.07 05 0.0828 0.5301 0.0000 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.2399 0.0084 0.0859 0.06 71 0.0818 0.5169 0.0000 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.2413 0.0083 0.0846 0.06 59 0.0809 0.5190 0.0000 0.0000 0.0000 0.0000 0.0000

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 23 2 17 0.0000 0.0000 0.0000 0.2336 0.0081 0.0823 0.06 42 0.0788 0.5329 0.0000 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.2610 0.0083 0.0801 0.06 11 0.0786 0.5110 0.0000 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.2247 0.0073 0.0722 0.05 55 0.0709 0.5693 0.0000 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.2155 0.0073 0.0734 0.05 69 0.0713 0.5755 0.0000 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.2533 0.0081 0.0796 0.06 09 0.0779 0.5200 0.0000 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.2189 0.0080 0.0844 0.06 66 0.0796 0.5425 0.0000 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.2175 0.0082 0.0866 0.06 86 0.0812 0.5378 0.0000 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.2094 0.0080 0.0849 0.06 74 0.0795 0.5508 0.0000 0.0000 0.0000 0.0000 0.0000



# 2020 VMT by Facility Type (INFVMT.D)

VMT BY FACILITY
1 0.251 0.541 0.202 0.006
0.273 0.518 0.204 0.005
0.277 0.509 0.209 0.005
0.274 0.493 0.227 0.005
0.273 0.489 0.233 0.005
0.270 0.502 0.224 0.005
0.266 0.490 0.239 0.005
0.265 0.487 0.244 0.005
0.274 0.483 0.239 0.005
0.276 0.471 0.249 0.004
0.281 0.475 0.240 0.004
0.317 0.461 0.218 0.004
0.306 0.467 0.224 0.004
0.270 0.498 0.227 0.004
0.261 0.491 0.243 0.004
0.274 0.482 0.239 0.004
0.271 0.492 0.233 0.005
0.288 0.462 0.245 0.004
0.310 0.478 0.207 0.005
0.293 0.495 0.206 0.006
0.261 0.485 0.248 0.005
0.253 0.513 0.229 0.005
0.242 0.521 0.233 0.005
0.244 0.526 0.225 0.005

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.010 0.949 0.035 0.002
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 24

0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004
0.003 0.963 0.030 0.004



# 2020 MOBILE6.2 Input File (INSCN.IN) * Mobile6 file for Dearborn County, IN * created 4/9/07, ajr post em62in.06c
******************* Header Section ************** **********
MOBILE6 INPUT FILE :

POLLU TANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE REPORT FILE : in.rpt

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : inemiss.tb1

RUN DATA ******************* Run Section ***************** ******** **

VMT BY HOUR : INHVMT.D

SPEED VMT : INSVMT.D

VMT BY FACILITY : INF VMT.D

EXPAND BUS EFS :
REBUILD EFFECTS : 0.10
******************* Summer Scenario Section ***** ***************** SCENARIO RECORD : Indiana Emissions - CY20xx
CALENDAR YEAR : 2020
EVALUATION MONTH : 7
SEASON : 1 MIN/MAX TEMP : 62.0 91.3
FUEL PROGRAM : 1
FUEL RVP : 9.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43 ******************* Annual Scenario Section ***** ***************** SCENARIO RECORD : Indiana Emissions - CY20xx
CALENDAR YEAR : 2020
EVALUATION MONTH : 7 MIN/MAX TEMP : 47.0 64.0
FUEL PROGRAM : 1
FUEL RVP : 9.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43
******************* End of Run ****************** **********

END OF RUN

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 25

2020 MOBILE6.2 Output File (IN.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: INSCN.IN (file 1, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external
* data file: INHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: INSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: INFVMT.D

Reading User Supplied ROADWAY VMT Factors

* # # # # # # # # # # # # # # # # # # # # # # # # # * Indiana Emissions - CY20xx * File 1, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12

HDDV DEFEAT DEVICE EFFECTS ARE PRESENT. THE REBUIL D FRACTION IS 0.10.

* Reading Ammonia (NH3) Basic Emissiion Rates
* from the external data file PMNH3BER.D

* Reading Ammonia (NH3) Sulfur Deterioration Rates
* from the external data file PMNH3SDR.D M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2020 Month: July Altitude: Low Minimum Temperature: 62.0 (F) Maximum Temperature: 91.3 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 8.6 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.2788 0.4388 0.1507 0.0365 0.0003 0.0022 0.0876 0.0051 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.420 0.513 0.824 0.593 0.611 0.069 0.224 0.300 2.97 0.531 Composite CO : 6.40 7.27 9.44 7.82 9.61 0.709 0.514 0.551 19.90 6.896 Composite NOX : 0.269 0.372 0.656 0.445 0.583 0.071 0.296 1.931 1.23 0.534

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 1.573 0.256 0.434 Composite CO : 17.72 0.734 1.006 Composite NOX : 2.132 2.704 4.692

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # #
* Indiana Emissions - CY20xx * File 1, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 26 * Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12 M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2020 Month: July Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 9.0 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.2788 0.4388 0.1507 0.0365 0.0003 0.0022 0.0876 0.0051 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.375 0.489 0.788 0.566 0.488 0.069 0.224 0.300 2.18 0.494 Composite CO : 8.95 9.49 11.97 10.13 9.83 0.709 0.514 0.551 17.73 8.966 Composite NOX : 0.257 0.383 0.681 0.459 0.599 0.071 0.296 1.931 1.43 0.541

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 1.258 0.256 0.434 Composite CO : 18.14 0.734 1.006 Composite NOX : 2.187 2.704 4.692

--------------------------------------------------- --------------------------------------------------- ----------------

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 27 

# APPENDIX B

MOBILE6.2 Input/Output Files for Kentucky Portion o f

Nonattainment Area

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 28

VMT By Hour (KYHVMT.D), all analysis years

VMT BY HOUR
0.0478 0.0719 0.0796 0.0666 0.0563 0.0532
0.0545 0.0543 0.0515 0.0523 0.0560 0.0565
0.0504 0.0377 0.0266 0.0209 0.0197 0.0171
0.0142 0.0156 0.0188 0.0224 0.0251 0.0310



# 2005 VMT by Speed Bin (KYSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0052 0.0000 0.00 11 0.0222 0.0279 0.0462 0.0454 0.0566 0.1746 0.6208
1 2 0.0006 0.0040 0.0017 0.0039 0.0000 0.0010 0.00 55 0.0151 0.0228 0.0433 0.0401 0.0807 0.1605 0.6206
1 3 0.0048 0.0000 0.0015 0.0039 0.0006 0.0027 0.00 78 0.0146 0.0224 0.0811 0.0687 0.1074 0.0805 0.6041
1 4 0.0054 0.0000 0.0000 0.0000 0.0007 0.0019 0.01 01 0.0176 0.0249 0.0493 0.0371 0.0832 0.1618 0.6081
1 5 0.0058 0.0000 0.0000 0.0000 0.0000 0.0007 0.01 07 0.0152 0.0282 0.0469 0.0484 0.0585 0.1751 0.6105
1 6 0.0060 0.0000 0.0000 0.0000 0.0000 0.0007 0.00 71 0.0196 0.0291 0.0461 0.0510 0.0589 0.1744 0.6070
1 7 0.0064 0.0000 0.0000 0.0000 0.0008 0.0000 0.01 22 0.0174 0.0295 0.0515 0.0479 0.0597 0.1736 0.6009
1 8 0.0064 0.0000 0.0000 0.0000 0.0008 0.0000 0.01 22 0.0173 0.0294 0.0535 0.0447 0.0600 0.1749 0.6010
1 9 0.0060 0.0000 0.0000 0.0000 0.0000 0.0007 0.00 95 0.0172 0.0290 0.0450 0.0500 0.0594 0.1764 0.6067
1 10 0.0059 0.0000 0.0000 0.0000 0.0000 0.0007 0.00 92 0.0167 0.0282 0.0443 0.0487 0.0593 0.1778 0.6092
1 11 0.0057 0.0000 0.0000 0.0000 0.0007 0.0000 0.01 08 0.0153 0.0261 0.0482 0.0424 0.0615 0.1858 0.6036
1 12 0.0054 0.0000 0.0000 0.0000 0.0007 0.0000 0.01 02 0.0145 0.0246 0.0496 0.0400 0.0602 0.1852 0.6095
1 13 0.0000 0.0052 0.0000 0.0000 0.0000 0.0000 0.00 47 0.0188 0.0249 0.0397 0.0478 0.0578 0.1796 0.6214
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0053 0.00 06 0.0229 0.0263 0.0379 0.0502 0.0584 0.1803 0.6180
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0247 0.0333 0.0364 0.0525 0.0594 0.1812 0.6127
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0237 0.0319 0.0361 0.0503 0.0591 0.1826 0.6163
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0214 0.0289 0.0346 0.0459 0.0587 0.1870 0.6234
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0190 0.0255 0.0331 0.0405 0.0584 0.1918 0.6318
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0195 0.0261 0.0357 0.0421 0.0575 0.1875 0.6315
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0205 0.0276 0.0375 0.0448 0.0573 0.1839 0.6285
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0214 0.0288 0.0379 0.0465 0.0575 0.1824 0.6256
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0242 0.0326 0.0393 0.0525 0.0580 0.1775 0.6159
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0254 0.0342 0.0391 0.0549 0.0585 0.1764 0.6114
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0323 0.0295 0.0398 0.0571 0.0586 0.1744 0.6083
2 1 0.0000 0.0000 0.0000 0.1120 0.1106 0.1128 0.24 11 0.1801 0.2150 0.0283 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0000 0.0000 0.1200 0.1265 0.1351 0.21 75 0.1662 0.2073 0.0275 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0023 0.0021 0.1299 0.1238 0.1504 0.20 73 0.1546 0.2008 0.0289 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0000 0.0026 0.1266 0.1284 0.1293 0.20 77 0.1753 0.2002 0.0300 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0024 0.1170 0.1230 0.1168 0.22 00 0.1815 0.2085 0.0307 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0000 0.1136 0.1149 0.1132 0.22 27 0.1869 0.2170 0.0316 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0000 0.0025 0.1155 0.1226 0.1149 0.21 60 0.1874 0.2090 0.0319 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0000 0.0028 0.1204 0.1198 0.1134 0.21 63 0.1907 0.2046 0.0320 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0000 0.1167 0.1183 0.1101 0.22 30 0.1888 0.2113 0.0318 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0000 0.1221 0.1252 0.1118 0.21 82 0.1850 0.2064 0.0313 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0000 0.0028 0.1163 0.1256 0.1145 0.21 68 0.1858 0.2067 0.0316 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0029 0.1098 0.1164 0.1141 0.22 11 0.1909 0.2125 0.0323 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.1129 0.1080 0.1087 0.23 37 0.1894 0.2161 0.0312 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.1106 0.1085 0.1006 0.24 26 0.1932 0.2143 0.0302 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.1139 0.1111 0.0913 0.24 55 0.1952 0.2124 0.0306 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.1129 0.1100 0.0892 0.24 49 0.1977 0.2141 0.0311 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.1144 0.1115 0.0906 0.24 47 0.1945 0.2136 0.0306 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.1228 0.1189 0.0878 0.24 44 0.1900 0.2061 0.0300 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.1120 0.1087 0.0836 0.24 18 0.2008 0.2211 0.0320 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.1140 0.1109 0.0881 0.24 25 0.1947 0.2188 0.0310 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.1328 0.1288 0.0955 0.24 55 0.1736 0.1963 0.0275 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.1174 0.1148 0.0985 0.24 62 0.1846 0.2096 0.0290 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.1165 0.1142 0.1001 0.24 68 0.1843 0.2093 0.0289 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.1123 0.1101 0.1004 0.24 37 0.1893 0.2145 0.0297 0.0000 0.0000 0.0000 0.0000



# 2005 VMT by Facility (KYFVMT.D)

VMT BY FACILITY
1 0.467 0.332 0.154 0.047
0.490 0.313 0.154 0.044
0.498 0.313 0.144 0.045
0.474 0.328 0.149 0.048
0.458 0.342 0.150 0.051
0.455 0.349 0.144 0.052
0.441 0.357 0.148 0.054
0.443 0.356 0.147 0.054
0.457 0.346 0.144 0.052
0.461 0.340 0.148 0.051

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 29

0.474 0.334 0.141 0.050
0.497 0.325 0.129 0.049
0.497 0.321 0.134 0.047
0.482 0.328 0.142 0.048
0.471 0.335 0.145 0.049
0.486 0.327 0.139 0.048
0.510 0.309 0.135 0.046
0.539 0.286 0.133 0.042
0.547 0.290 0.119 0.044
0.525 0.301 0.129 0.045
0.482 0.310 0.164 0.043
0.462 0.334 0.156 0.048
0.448 0.343 0.160 0.049
0.444 0.350 0.155 0.051

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.196 0.753 0.024 0.027
0.196 0.753 0.024 0.027
0.196 0.753 0.024 0.027
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.196 0.753 0.024 0.027
0.196 0.753 0.024 0.027
0.196 0.753 0.024 0.027
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014



# 2005 MOBILE6.2 Input File (KYSCN.IN) * Mobile6 file for Boone, Campbell and Kenton count ies * pre 2006 analys is years, includes annual scenario * created 10/12/05,AJR

************************ Header Section *********** ******
MOBILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE

REPORT FILE : KY.RPT

DATABASE OUTPUT :

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 30

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111

DAILY OUTPUT : EMISSIONS TABLE : kyemis s.tb1

RUN DATA ************************ Run Section ************** ***** > post 1999, KY counties of Boone, Campbell and Ken ton
*REG DIST : KYREG.D

VMT BY HOUR : KYHVMT.D

SPEED VMT : KYSVMT.D

VMT BY FACILITY : KYFVMT.D

EXPRESS HC AS VOC : I/M PROGRAM : 1 1999 2005 2 T/O IDLE I/M MODEL YEARS : 1 1968 2005 I/M VEHICLES : 1 22222 22211111 1 I/M STRINGENCY : 1 20.0 I/M COMPLIANCE : 1 99.0 I/M WAIVER RATES : 1 18.0 10.0 I/M PROGRAM : 2 1999 2005 2 T/O FP & GC I/M MODEL Y EARS : 2 1981 2005 I/M VEHICLES : 2 22222 11111111 1 I/M STRINGENCY : 2 20.0 I/M COMPLIANCE : 2 99.0 I/M WAIVER RATES : 2 18.0 10.0

ANTI-TAMP PROGR :
99 75 50 22222 22211111 1 12 099. 22222222

STAGE II REFUELING :
99 2 86. 86.

EXPAND BUS EFS : ********************* Summer Scenario Section ***** ***********

SCENARIO RECORD : KY EMISSIONS - CY20xx
CALENDAR YEAR : 2005
EVALUATION MONTH : 7

F UEL RVP : 7.8
FUEL PROGRAM : 2 N
PARTICLE SIZE : 2.5 MIN/MAX TEMP : 66.0 89.0
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 323 ********************* Annual Scenario Section ***** ************

SCENARIO RECORD : KY EMISSIONS - CY20xx
CALENDAR YEAR : 2005
EVALUATION MONTH : 7
FUEL RVP : 9.0
FUEL PROGRAM : 2 N
PARTICLE SIZE : 2.5 MIN/MAX TEMP : 47.0 64.0
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 324
*********************************** END OF RUN   ** *** ********

END OF RUN

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 31

2005 MOBILE6.2 Output Report (KY.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: KYSCN.IN (file 2, run 1). *

*************************************************** ************************ * post 1999, KY counties of Boone, Campbell and Ken ton

* Reading Hourly VMT distribution from the followin g external
* data file: KYHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: KYSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: KYFVMT.D

Reading User Supplied ROADWAY VMT Factors
M601 Comment:
User has enabled STAGE II REFUELING.

* # # # # # # # # # # # # # # # # # # # # # # # # #
* KY EMISSIONS - CY20xx * File 2, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV *** I/M credits for Tech1&2 vehicles were read from the following external
data file: TECH12.D M 48 Warning:
there are no sales for vehicle class HDGV8b

Calendar Year: 2005 Month: July
Altitude: Low Minimum Temperature: 66.0 (F) Maximum Temperature: 89.0 (F) Absolute Humidity: 75. grains/lb Fuel Sulfur Content: 90. ppm

Exhaust I/M Program: Yes Evap I/M Program: Yes
ATP Program: Yes
Reformulated Gas: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All
Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ -----

- VMT Distribution: 0.4158 0.3387 0.1165 0.0360 0.0006 0.0019 0.0849 0.0057
1.0000

------------------------------------------------- --------------------------------------------------- -----------------

- Composite Emission Factors (g/mi): Composite VOC : 0.871 0.901 1.428 1.035 1.244 0.575 0.796 0.536 2.19
0.938 Composite CO : 10.18 11.84 15.33 12.73 14.37 1.611 1.408 3.205 15.87
10.912 Composite NOX : 0.920 1.099 1.415 1.180 4.396 1.537 1.599 13.396 1.31
2.226

------------------------------------------------- --------------------------------------------------- -----------------

- Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0003 0.0009 0.0016

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 6.036 0.578 0.727 Composite CO : 98.01 4.483 2.790 Composite NOX : 8.754 16.461 14.355

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # #
* KY EMISSIONS - CY20xx * File 2, Run 1, Scenario 2.

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 32 * # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b

Calendar Year: 2005 Month: July
Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Fuel Sulfur Content: 90. ppm

Exhaust I/M Program: Yes Evap I/M Program: Yes
ATP Program: Yes
Reformulated Gas: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All
Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ -----

- VMT Distribution: 0.4158 0.3387 0.1165 0.0360 0.0006 0.0019 0.0849 0.0057
1.0000

------------------------------------------------- --------------------------------------------------- -----------------

- Composite Emission Factors (g/mi): Composite VOC : 0.864 0.941 1.520 1.089 1.154 0.575 0.796 0.536 2.08
0.956 Composite CO : 13.44 16.12 19.94 17.10 14.60 1.611 1.408 3.205 14.58
14.257 Composite NOX : 0.931 1.166 1.506 1.253 4.517 1.537 1.599 13.396 1.52
2.269

------------------------------------------------- --------------------------------------------------- -----------------

- Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0003 0.0009 0.0016

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 5.574 0.578 0.727 Composite CO : 90.66 4.483 2.790 Composite NOX : 9.196 16.461 14.355

--------------------------------------------------- --------------------------------------------------- ---------------- 

# 2008 VMT by Speed bin (KYSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0000 0.0014 0.00 34 0.0213 0.0225 0.0599 0.0156 0.0469 0.0285 0.8004
1 2 0.0000 0.0010 0.0033 0.0003 0.0004 0.0027 0.00 40 0.0175 0.0153 0.0639 0.0092 0.0770 0.0609 0.7445
1 3 0.0000 0.0036 0.0005 0.0011 0.0020 0.0033 0.00 57 0.0347 0.0215 0.0679 0.0706 0.0701 0.0428 0.6760
1 4 0.0000 0.0000 0.0000 0.0014 0.0018 0.0055 0.00 78 0.0148 0.0197 0.0670 0.0053 0.0765 0.0620 0.7384
1 5 0.0000 0.0000 0.0000 0.0000 0.0006 0.0037 0.00 64 0.0192 0.0222 0.0702 0.0066 0.0462 0.0288 0.7960
1 6 0.0000 0.0000 0.0000 0.0000 0.0006 0.0035 0.00 60 0.0208 0.0231 0.0677 0.0099 0.0460 0.0288 0.7936
1 7 0.0000 0.0000 0.0000 0.0007 0.0012 0.0038 0.00 85 0.0180 0.0244 0.0727 0.0063 0.0456 0.0288 0.7900
1 8 0.0000 0.0000 0.0000 0.0007 0.0011 0.0038 0.00 89 0.0175 0.0243 0.0720 0.0063 0.0455 0.0290 0.7910
1 9 0.0000 0.0000 0.0000 0.0000 0.0006 0.0038 0.00 57 0.0199 0.0202 0.0729 0.0068 0.0458 0.0291 0.7951
1 10 0.0000 0.0000 0.0000 0.0000 0.0006 0.0037 0.00 53 0.0197 0.0196 0.0719 0.0066 0.0458 0.0293 0.7974
1 11 0.0000 0.0000 0.0000 0.0006 0.0010 0.0035 0.00 71 0.0166 0.0213 0.0687 0.0055 0.0519 0.0526 0.7711
1 12 0.0000 0.0000 0.0000 0.0006 0.0010 0.0034 0.00 67 0.0158 0.0194 0.0695 0.0052 0.0766 0.0465 0.7553
1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0020 0.00 44 0.0190 0.0181 0.0648 0.0108 0.0465 0.0491 0.7853
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0015 0.00 06 0.0232 0.0190 0.0575 0.0188 0.0462 0.0295 0.8037
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0015 0.00 00 0.0249 0.0201 0.0570 0.0195 0.0457 0.0298 0.8016
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0015 0.00 00 0.0240 0.0192 0.0564 0.0186 0.0458 0.0299 0.8045
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0015 0.00 00 0.0221 0.0173 0.0546 0.0171 0.0459 0.0305 0.8110
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0015 0.00 00 0.0200 0.0152 0.0527 0.0149 0.0460 0.0311 0.8186
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0015 0.00 00 0.0204 0.0156 0.0545 0.0159 0.0464 0.0304 0.8153
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0015 0.00 00 0.0213 0.0165 0.0560 0.0172 0.0465 0.0298 0.8111
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0015 0.00 00 0.0220 0.0172 0.0567 0.0177 0.0465 0.0297 0.8087
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0014 0.00 00 0.0244 0.0197 0.0586 0.0201 0.0463 0.0291 0.8003

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 33 1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0014 0.00 00 0.0255 0.0207 0.0590 0.0210 0.0461 0.0290 0.7973
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0014 0.00 00 0.0263 0.0215 0.0598 0.0219 0.0461 0.0287 0.7942
2 1 0.0000 0.0000 0.0000 0.1888 0.0882 0.0726 0.20 34 0.1932 0.2201 0.0338 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0000 0.0000 0.1976 0.1003 0.0869 0.19 39 0.1737 0.2146 0.0330 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0001 0.0007 0.2011 0.1046 0.0965 0.19 06 0.1654 0.2085 0.0325 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0001 0.0002 0.2043 0.1007 0.0869 0.19 03 0.1806 0.2031 0.0338 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0001 0.1975 0.0969 0.0737 0.19 08 0.1986 0.2084 0.0341 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0001 0.1896 0.0890 0.0733 0.19 34 0.2034 0.2162 0.0350 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0001 0.0001 0.1949 0.0958 0.0755 0.19 19 0.1997 0.2074 0.0349 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0001 0.0002 0.1948 0.0963 0.0766 0.19 16 0.1989 0.2067 0.0347 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0001 0.1943 0.0916 0.0719 0.19 20 0.2034 0.2121 0.0346 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0001 0.2017 0.0989 0.0691 0.18 92 0.2000 0.2070 0.0340 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0001 0.0000 0.1963 0.0965 0.0760 0.19 40 0.1974 0.2055 0.0342 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0001 0.0003 0.1862 0.0881 0.0800 0.19 76 0.2013 0.2116 0.0348 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.1893 0.0886 0.0691 0.20 03 0.2015 0.2174 0.0338 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.1891 0.0883 0.0638 0.20 32 0.2055 0.2168 0.0333 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.1940 0.0906 0.0600 0.20 08 0.2076 0.2137 0.0333 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.1927 0.0900 0.0588 0.20 01 0.2097 0.2151 0.0337 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.1942 0.0907 0.0593 0.20 01 0.2068 0.2151 0.0338 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.2053 0.0958 0.0570 0.19 73 0.2042 0.2074 0.0330 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.1904 0.0889 0.0549 0.19 73 0.2110 0.2218 0.0358 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.1924 0.0898 0.0575 0.19 86 0.2058 0.2204 0.0354 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.2170 0.1013 0.0608 0.19 82 0.1914 0.1994 0.0318 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.1973 0.0921 0.0639 0.20 25 0.1985 0.2126 0.0331 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.1963 0.0917 0.0650 0.20 34 0.1983 0.2125 0.0328 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.1907 0.0890 0.0641 0.20 35 0.2017 0.2173 0.0337 0.0000 0.0000 0.0000 0.0000



# 2008 VMT by Facility Type (KYFVMT.D)

VMT BY FACILITY
1 0.462 0.337 0.170 0.030
0.482 0.321 0.170 0.028
0.494 0.317 0.161 0.029
0.469 0.330 0.170 0.031
0.454 0.341 0.173 0.032
0.455 0.345 0.166 0.034
0.440 0.353 0.172 0.035
0.443 0.351 0.172 0.034
0.457 0.342 0.168 0.033
0.458 0.337 0.173 0.032
0.473 0.331 0.164 0.032
0.499 0.320 0.149 0.032
0.498 0.318 0.154 0.030
0.481 0.327 0.161 0.030
0.469 0.333 0.167 0.031
0.485 0.324 0.160 0.031
0.508 0.308 0.155 0.029
0.533 0.287 0.153 0.027
0.546 0.288 0.138 0.028
0.521 0.301 0.148 0.029
0.469 0.318 0.186 0.027
0.457 0.337 0.176 0.030
0.443 0.346 0.180 0.031
0.442 0.351 0.175 0.032

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.215 0.733 0.032 0.019
0.215 0.733 0.032 0.019
0.215 0.733 0.032 0.019
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 34

0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.215 0.733 0.032 0.019
0.215 0.733 0.032 0.019
0.215 0.733 0.032 0.019
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007



# 2008 MOBILE6.2 Input File (KYSCN.IN) * Mobile6 file for Boone, Campbell and Kenton count ies * post 2005 analysis years, includes annual scenari o * created 4/9/07,AJR, post 2005 ************************ Header Section *********** ******
MOBILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE

REPORT FILE : KY.RPT

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : kyemiss.tb1

RUN DATA ************************ Run Section ************** *****

VMT BY HOUR : KYHVMT.D

SPEED VMT : KYSVMT.D

VMT BY FACILITY : KYFVMT .D

STAGE II REFUELING :
99 2 86. 86.

EXPAND BUS EFS :
REBUILD EFFECTS : 0.30 ********************* Summer Scenario Section ***** *** ********

SCENARIO RECORD : KY EMISSIONS - CY20xx
CALENDAR YEAR : 2008
EVALUATION MONTH : 7
FUEL RVP : 7.8
FUEL PROGRAM : 2 N
PARTICLE SIZE : 2.5 MIN/MAX TEMP : 61.0 95.0
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV

DIESEL SULFUR : 43

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 35

********************* Annual Scenario Section ***** ************
SCENARIO RECORD : KY EMISSIONS - CY20xx
CALENDAR YEAR : 2008
EVALUATION MONTH : 7
FUEL RVP : 9.0

FUEL PROGRAM : 2 N
PARTICLE SIZE : 2.5 MIN/MAX TEMP : 47.0 64.0
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43
*********************************** END OF RUN   ** ***********

END OF RUN



# 2008 MOBILE6.2 Output Report (KY.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: KYSCN.IN (file 2, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external * data file: KYHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: KYSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: KYFVMT.D

Reading User Supplied ROADWAY VMT Factors
M601 Comment:
User has enabled STAGE II REFUELING.

* # # # # # # # # # # # # # # # # # # # # # # # # #
* KY EMISSIONS - CY20xx * File 2, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b

HDDV DEFEAT DEVICE EFFECTS ARE PRESENT. THE REBUIL D FRACTION IS 0.30. M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2008 Month: July Altitude: Low Minimum Temperature: 61.0 (F) Maximum Temperature: 95.0 (F) Absolute Humidity: 75. grains/lb Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.3728 0.3705 0.1273 0.0359 0.0004 0.0019 0.0857 0.0055 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.765 0.795 1.288 0.921 1.044 0.291 0.556 0.456 2.32 0.834 Composite CO : 9.18 10.54 14.15 11.47 12.43 1.153 0.977 2.537 18.01 9.895 Composite NOX : 0.695 0.874 1.254 0.971 3.039 0.825 1.132 10.682 1.30 1.776

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0002 0.0009 0.0017

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 5.712 0.383 0.654 Composite CO : 87.14 3.588 2.539

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 36 Composite NOX : 7.927 14.073 12.793

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # #
* KY EMISSIONS - CY20xx * File 2, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2008 Month: July Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.3728 0.3705 0.1273 0.0359 0.0004 0.0019 0.0857 0.0055 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.734 0.799 1.302 0.928 0.923 0.291 0.556 0.456 2.11 0.821 Composite CO : 11.88 14.19 18.70 15.34 12.85 1.153 0.977 2.537 15.32 12.832 Composite NOX : 0.687 0.914 1.318 1.017 3.135 0.825 1.132 10.682 1.53 1.801

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0002 0.0009 0.0017

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 4.970 0.383 0.654 Composite CO : 80.26 3.588 2.539 Composite NOX : 8.913 14.073 12.793

--------------------------------------------------- --------------------------------------------------- ----------------


# 2015 VMT by Speed Bin (KYSVMT.D)

SPEED VMT
1 1 0.0000 0.0005 0.0000 0.0000 0.0000 0.0000 0.00 10 0.0181 0.0280 0.0690 0.0389 0.0448 0.1520 0.6475
1 2 0.0005 0.0000 0.0033 0.0000 0.0006 0.0005 0.00 68 0.0259 0.0336 0.0733 0.0566 0.0927 0.0599 0.6463
1 3 0.0005 0.0002 0.0083 0.0247 0.0007 0.0070 0.03 20 0.0356 0.0194 0.1146 0.0389 0.0565 0.0235 0.6380
1 4 0.0006 0.0000 0.0002 0.0007 0.0011 0.0014 0.01 59 0.0325 0.0247 0.0783 0.0606 0.0898 0.0605 0.6336
1 5 0.0006 0.0000 0.0000 0.0002 0.0008 0.0007 0.00 81 0.0155 0.0232 0.0821 0.0384 0.0687 0.1246 0.6369
1 6 0.0006 0.0000 0.0000 0.0000 0.0008 0.0004 0.00 89 0.0154 0.0247 0.0833 0.0347 0.0735 0.1242 0.6334
1 7 0.0007 0.0000 0.0000 0.0012 0.0000 0.0022 0.00 88 0.0166 0.0243 0.0877 0.0340 0.0735 0.1237 0.6272
1 8 0.0007 0.0000 0.0003 0.0009 0.0004 0.0024 0.00 82 0.0169 0.0239 0.0869 0.0335 0.0740 0.1246 0.6273
1 9 0.0006 0.0000 0.0000 0.0000 0.0011 0.0002 0.00 87 0.0155 0.0246 0.0815 0.0346 0.0743 0.1257 0.6332
1 10 0.0006 0.0000 0.0000 0.0000 0.0011 0.0007 0.00 79 0.0150 0.0239 0.0799 0.0385 0.0698 0.1267 0.6357
1 11 0.0006 0.0000 0.0000 0.0010 0.0000 0.0020 0.00 78 0.0147 0.0264 0.1042 0.0300 0.0906 0.0837 0.6390
1 12 0.0006 0.0000 0.0000 0.0010 0.0000 0.0018 0.00 74 0.0187 0.0438 0.0803 0.0565 0.0693 0.0857 0.6349
1 13 0.0005 0.0000 0.0000 0.0000 0.0000 0.0007 0.00 55 0.0138 0.0230 0.0681 0.0665 0.0507 0.1231 0.6480
1 14 0.0000 0.0000 0.0006 0.0000 0.0000 0.0000 0.00 05 0.0187 0.0246 0.0656 0.0416 0.0463 0.1572 0.6448
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 06 0.0202 0.0259 0.0654 0.0435 0.0468 0.1581 0.6395
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0194 0.0254 0.0640 0.0417 0.0470 0.1594 0.6432
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0176 0.0230 0.0599 0.0381 0.0475 0.1633 0.6507
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0155 0.0204 0.0556 0.0336 0.0481 0.1675 0.6594
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0159 0.0208 0.0587 0.0349 0.0471 0.1636 0.6589
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0168 0.0220 0.0616 0.0371 0.0465 0.1604 0.6557
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0175 0.0229 0.0631 0.0385 0.0463 0.1590 0.6527
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0198 0.0259 0.0677 0.0434 0.0458 0.1547 0.6426
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0208 0.0272 0.0689 0.0455 0.0458 0.1538 0.6380
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0006 0.00 00 0.0216 0.0276 0.0706 0.0472 0.0455 0.1520 0.6348
2 1 0.0000 0.0000 0.0000 0.3682 0.0762 0.0569 0.15 21 0.1330 0.1717 0.0418 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0000 0.0000 0.3865 0.0820 0.0769 0.13 11 0.1185 0.1651 0.0400 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0001 0.0053 0.3753 0.0895 0.0806 0.13 77 0.1062 0.1641 0.0410 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0000 0.0014 0.3846 0.0847 0.0696 0.13 81 0.1146 0.1659 0.0409 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0001 0.3783 0.0803 0.0611 0.14 00 0.1283 0.1703 0.0416 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0000 0.3632 0.0759 0.0597 0.14 33 0.1355 0.1788 0.0436 0.0000 0.0000 0.0000 0.0000

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 37 2 7 0.0000 0.0000 0.0000 0.3704 0.0796 0.0613 0.14 06 0.1300 0.1751 0.0430 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0000 0.0000 0.3721 0.0789 0.0610 0.14 28 0.1273 0.1752 0.0427 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0000 0.3700 0.0774 0.0586 0.14 22 0.1345 0.1748 0.0425 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0001 0.3838 0.0804 0.0577 0.13 80 0.1302 0.1687 0.0411 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0000 0.0000 0.3743 0.0793 0.0635 0.13 93 0.1283 0.1733 0.0419 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0000 0.3559 0.0752 0.0640 0.14 58 0.1339 0.1815 0.0437 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.3625 0.0738 0.0556 0.14 63 0.1418 0.1781 0.0419 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.3637 0.0745 0.0503 0.15 17 0.1426 0.1760 0.0411 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.3709 0.0754 0.0458 0.15 10 0.1427 0.1736 0.0407 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.3682 0.0747 0.0449 0.15 05 0.1448 0.1754 0.0413 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.3720 0.0755 0.0455 0.15 03 0.1421 0.1733 0.0414 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.3905 0.0786 0.0439 0.14 73 0.1360 0.1644 0.0392 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.3655 0.0738 0.0424 0.14 80 0.1473 0.1783 0.0446 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.3706 0.0751 0.0444 0.14 88 0.1424 0.1748 0.0439 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.4133 0.0833 0.0469 0.14 70 0.1218 0.1514 0.0364 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.3796 0.0775 0.0489 0.15 20 0.1343 0.1677 0.0400 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.3778 0.0774 0.0496 0.15 29 0.1344 0.1682 0.0397 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.3678 0.0754 0.0490 0.15 32 0.1393 0.1738 0.0415 0.0000 0.0000 0.0000 0.0000



# 2015 VMT by Facility Type (KYFVMT.D)

VMT BY FACILITY
1 0.376 0.309 0.285 0.030
0.395 0.292 0.286 0.028
0.404 0.295 0.272 0.029
0.379 0.304 0.286 0.030
0.364 0.316 0.288 0.032
0.365 0.325 0.277 0.033
0.350 0.329 0.287 0.034
0.352 0.329 0.286 0.034
0.365 0.321 0.281 0.033
0.365 0.313 0.290 0.032
0.380 0.312 0.276 0.032
0.406 0.309 0.253 0.032
0.405 0.304 0.260 0.031
0.390 0.309 0.271 0.031
0.377 0.312 0.279 0.031
0.393 0.307 0.270 0.031
0.415 0.293 0.263 0.029
0.438 0.271 0.264 0.027
0.453 0.279 0.239 0.029
0.430 0.287 0.254 0.029
0.378 0.283 0.313 0.027
0.368 0.309 0.293 0.030
0.355 0.316 0.299 0.031
0.354 0.324 0.290 0.032

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 38

0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009



# 2015 MOBILE6.2 Input File (KYSCN.IN) * Mobile6 file for Boone, Campbell and Kenton count ies * post 2005 analysis years, includes a nnual scenario * created 4/9/07,AJR, post 2005 ************************ Header Section *********** ******

MOB ILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE

REPORT FILE : KY.RPT

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : kyemiss.tb1

RUN DATA ************************ Run Section ************** *****

VMT BY HOUR : KYHVMT.D

SPEED VMT : K YSVMT.D

VMT BY FACILITY : KYFVMT.D

STAGE II REFUELING :
99 2 86. 86.

EXPAND BUS EFS :
REBUILD EFFECTS : 0.30 ********************* Summer Scenario Section ***** ***********

SCENARIO RECORD : KY EMISSIONS - CY20xx
CALENDAR YEAR : 2015
EVALUATION MONTH : 7
FUEL RVP : 7.8
FUEL PROGRAM : 2 N
PARTICLE SIZE : 2.5 MIN/MAX TEMP : 61.0 95.0
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43 ********************* Annual Scenario Section ***** ************

SCENARIO RECORD : KY EMISSIONS - CY20xx
CALENDAR YEAR : 2015
EVALUATION MONTH : 7

FUEL RVP : 9.0
FUEL PROGRAM : 2 N

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 39

PARTICLE SIZE : 2.5 MIN/MAX TEMP : 47.0 64.0
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43

*********************************** END OF RUN   ** ***********

END OF RUN



# 2015 MOBILE6.2 Output File (KY.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: KYSCN.IN (file 2, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external * data file: KYHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: KYSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: KYFVMT.D

Reading User Supplied ROADWAY VMT Factors
M601 Comment:
User has enabled STAGE II REFUELING.

* # # # # # # # # # # # # # # # # # # # # # # # # #
* KY EMISSIONS - CY20xx * File 2, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12

HDDV DEFEAT DEVICE EFFECTS ARE PRESENT. THE REBUIL D FRACTION IS 0.30. M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2015 Month: July
Altitude: Low Minimum Temperature: 61.0 (F) Maximum Temperature: 95.0 (F) Absolute Humidity: 75. grains/lb Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.3031 0.4218 0.1449 0.0360 0.0003 0.0021 0.0866 0.0053 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.446 0.530 0.927 0.632 0.616 0.110 0.337 0.357 2.42 0.560 Composite CO : 6.52 7.37 9.89 8.01 9.07 0.838 0.671 1.014 18.78 7.031 Composite NOX : 0.377 0.481 0.845 0.574 1.082 0.177 0.486 3.843 1.21 0.819

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 1.831 0.306 0.543 Composite CO : 16.29 1.871 1.597 Composite NOX : 3.958 6.649 7.289

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # #
* KY EMISSIONS - CY20xx * File 2, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 40 * Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12 M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2015 Month: July Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.3031 0.4218 0.1449 0.0360 0.0003 0.0021 0.0866 0.0053 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.437 0.532 0.929 0.634 0.558 0.110 0.337 0.357 2.20 0.555 Composite CO : 9.30 10.17 13.27 10.96 9.91 0.838 0.671 1.014 15.96 9.561 Composite NOX : 0.362 0.499 0.880 0.596 1.102 0.177 0.486 3.843 1.42 0.829

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 1.643 0.306 0.543 Composite CO : 17.81 1.871 1.597 Composite NOX : 4.030 6.649 7.289

--------------------------------------------------- --------------------------------------------------- ----------------


# 2020 VMT by Speed Bin (KYSVMT.D)

SPEED VMT
1 1 0.0002 0.0004 0.0000 0.0000 0.0000 0.0000 0.00 17 0.0173 0.0276 0.0712 0.0390 0.0446 0.1441 0.6540
1 2 0.0005 0.0000 0.0033 0.0000 0.0009 0.0013 0.02 04 0.0242 0.0204 0.0976 0.0425 0.0996 0.0358 0.6535
1 3 0.0005 0.0004 0.0307 0.0019 0.0067 0.0263 0.01 90 0.0234 0.0552 0.0868 0.0338 0.0475 0.0480 0.6197
1 4 0.0006 0.0002 0.0013 0.0002 0.0022 0.0062 0.02 05 0.0243 0.0216 0.1068 0.0491 0.0905 0.0361 0.6405
1 5 0.0007 0.0000 0.0003 0.0008 0.0008 0.0020 0.00 74 0.0147 0.0247 0.0845 0.0450 0.0623 0.1139 0.6431
1 6 0.0007 0.0000 0.0003 0.0002 0.0014 0.0011 0.00 83 0.0145 0.0239 0.0883 0.0323 0.0716 0.1178 0.6395
1 7 0.0007 0.0003 0.0003 0.0013 0.0011 0.0027 0.00 98 0.0134 0.0248 0.0901 0.0333 0.0717 0.1174 0.6332
1 8 0.0007 0.0003 0.0003 0.0014 0.0015 0.0029 0.01 00 0.0135 0.0236 0.0900 0.0459 0.0629 0.1139 0.6333
1 9 0.0007 0.0000 0.0003 0.0002 0.0014 0.0015 0.00 79 0.0148 0.0235 0.0865 0.0367 0.0679 0.1193 0.6393
1 10 0.0007 0.0000 0.0003 0.0002 0.0013 0.0020 0.00 72 0.0144 0.0228 0.0848 0.0453 0.0634 0.1158 0.6419
1 11 0.0006 0.0002 0.0002 0.0013 0.0008 0.0024 0.00 84 0.0121 0.0360 0.0956 0.0344 0.0905 0.0825 0.6348
1 12 0.0006 0.0002 0.0002 0.0012 0.0007 0.0022 0.01 26 0.0334 0.0226 0.0850 0.0500 0.1131 0.0362 0.6417
1 13 0.0006 0.0000 0.0000 0.0002 0.0000 0.0016 0.00 57 0.0141 0.0205 0.0898 0.0457 0.0723 0.0949 0.6545
1 14 0.0000 0.0006 0.0000 0.0000 0.0000 0.0000 0.00 09 0.0181 0.0244 0.0679 0.0416 0.0461 0.1492 0.6512
1 15 0.0000 0.0000 0.0000 0.0000 0.0006 0.0000 0.00 00 0.0198 0.0259 0.0679 0.0435 0.0466 0.1500 0.6457
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0196 0.0248 0.0664 0.0417 0.0467 0.1513 0.6495
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0172 0.0231 0.0621 0.0381 0.0473 0.1550 0.6573
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0152 0.0204 0.0576 0.0336 0.0479 0.1592 0.6662
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0157 0.0209 0.0607 0.0349 0.0469 0.1554 0.6657
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0165 0.0220 0.0636 0.0370 0.0462 0.1522 0.6624
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0172 0.0230 0.0652 0.0384 0.0461 0.1509 0.6593
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0197 0.0258 0.0700 0.0433 0.0455 0.1466 0.6490
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 02 0.0209 0.0266 0.0713 0.0454 0.0456 0.1458 0.6443
1 24 0.0000 0.0000 0.0000 0.0007 0.0000 0.0000 0.00 00 0.0212 0.0276 0.0731 0.0471 0.0453 0.1441 0.6410
2 1 0.0000 0.0000 0.0000 0.4825 0.0614 0.0493 0.12 35 0.1068 0.1415 0.0350 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0000 0.0032 0.4979 0.0675 0.0631 0.10 76 0.0929 0.1344 0.0333 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0021 0.0032 0.4922 0.0724 0.0735 0.10 81 0.0812 0.1329 0.0344 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0000 0.0027 0.4998 0.0712 0.0587 0.11 09 0.0913 0.1311 0.0342 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0000 0.4950 0.0651 0.0516 0.11 37 0.1001 0.1396 0.0349 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0001 0.4783 0.0628 0.0494 0.11 82 0.1080 0.1465 0.0369 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0000 0.0000 0.4878 0.0651 0.0522 0.11 72 0.1003 0.1412 0.0362 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0001 0.0000 0.4881 0.0651 0.0521 0.11 95 0.0978 0.1413 0.0360 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0001 0.4864 0.0639 0.0482 0.11 64 0.1056 0.1436 0.0359 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0000 0.5004 0.0657 0.0489 0.11 14 0.1014 0.1378 0.0344 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0000 0.0000 0.4920 0.0645 0.0530 0.11 64 0.0992 0.1396 0.0353 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0000 0.4717 0.0633 0.0524 0.12 33 0.1047 0.1475 0.0371 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.4774 0.0607 0.0493 0.11 91 0.1118 0.1463 0.0354 0.0000 0.0000 0.0000 0.0000

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 41 2 14 0.0000 0.0000 0.0000 0.4784 0.0601 0.0420 0.12 50 0.1147 0.1451 0.0347 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.4864 0.0606 0.0378 0.12 40 0.1143 0.1426 0.0343 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.4837 0.0601 0.0371 0.12 38 0.1161 0.1442 0.0349 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.4876 0.0606 0.0375 0.12 34 0.1138 0.1423 0.0348 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.5074 0.0625 0.0359 0.11 98 0.1079 0.1338 0.0327 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.4810 0.0594 0.0351 0.12 16 0.1183 0.1469 0.0376 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.4862 0.0603 0.0367 0.12 22 0.1141 0.1438 0.0369 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.5307 0.0654 0.0378 0.11 84 0.0956 0.1220 0.0300 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.4953 0.0620 0.0402 0.12 46 0.1071 0.1373 0.0334 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.4933 0.0619 0.0409 0.12 55 0.1073 0.1379 0.0332 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.4827 0.0607 0.0405 0.12 63 0.1117 0.1431 0.0349 0.0000 0.0000 0.0000 0.0000



# 2020 VMT by Facility Type (KYFVMT.D)

VMT BY FACILITY
1 0.331 0.277 0.366 0.026
0.347 0.261 0.368 0.024
0.357 0.265 0.353 0.025
0.332 0.271 0.370 0.026
0.319 0.281 0.373 0.027
0.322 0.290 0.360 0.029
0.307 0.293 0.371 0.029
0.308 0.292 0.370 0.029
0.321 0.286 0.364 0.028
0.320 0.278 0.375 0.027
0.335 0.279 0.359 0.028
0.361 0.279 0.332 0.028
0.359 0.274 0.340 0.027
0.344 0.278 0.352 0.027
0.332 0.279 0.362 0.027
0.347 0.275 0.351 0.027
0.367 0.264 0.343 0.026
0.387 0.244 0.346 0.023
0.405 0.253 0.316 0.026
0.382 0.259 0.334 0.026
0.327 0.249 0.401 0.023
0.322 0.275 0.377 0.026
0.310 0.281 0.383 0.026
0.310 0.288 0.374 0.028

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 2 0.331 0.277 0.366 0.026
0.347 0.261 0.368 0.024
0.357 0.265 0.353 0.025
0.332 0.271 0.370 0.026
0.319 0.281 0.373 0.027
0.322 0.290 0.360 0.029
0.307 0.293 0.371 0.029
0.308 0.292 0.370 0.029
0.321 0.286 0.364 0.028
0.320 0.278 0.375 0.027
0.335 0.279 0.359 0.028
0.361 0.279 0.332 0.028
0.359 0.274 0.340 0.027
0.344 0.278 0.352 0.027
0.332 0.279 0.362 0.027
0.347 0.275 0.351 0.027

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 42

0.367 0.264 0.343 0.026
0.387 0.244 0.346 0.023
0.405 0.253 0.316 0.026
0.382 0.259 0.334 0.026
0.327 0.249 0.401 0.023
0.322 0.275 0.377 0.026
0.310 0.281 0.383 0.026
0.310 0.288 0.374 0.028



# 2020 MOBILE6.2 Input File (KYSCN.IN)

* Mobile6 file for Boone, Campbell and Kenton counties * post 2005 analysis years, includes annual scenari o * created 4/9/07,AJR, post 2005 ************************ Header Section *********** ******
MOBILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE

REPORT FILE : KY.RPT

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : kyemiss.tb1

RUN DATA

******************* ***** Run Section *******************

VMT BY HOUR : KYHVMT.D

SPEED VMT : KYSVMT.D

VMT BY FACILITY : KYFVMT.D

STAGE II REFUELING :
99 2 86. 86.

EXPAND BUS EFS :
REBUILD EFFECTS : 0.30

*********** ********** Summer Scenario Section ****************

SCENARIO RECORD : KY EMISSIONS - CY20xx
CALENDAR YEAR : 2020

EVALUATION MONTH : 7
FUEL RVP : 7.8
FUEL PROGRAM : 2 N

PARTICLE SIZ E : 2.5 MIN/MAX TEMP : 61.0 95.0
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43 ********************* Annual Scenario Section ***** *********** *

SCENARIO RECORD : KY EMISSIONS - CY20xx
CALENDAR YEAR : 2020
EVALUATION MONTH : 7

F UEL RVP : 9.0
FUEL PROGRAM : 2 N
PARTICLE SIZE : 2.5 MIN/MAX TEMP : 47.0 64.0
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 43

DIESEL SULFUR : 43
*********************************** END OF RUN   ** ***********

END OF RUN



# 2020 MOBILE6.2 Output File (KY.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: KYSCN.IN (file 2, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external * data file: KYHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: KYSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: KYFVMT.D

Reading User Supplied ROADWAY VMT Factors
M601 Comment:
User has enabled STAGE II REFUELING.

* # # # # # # # # # # # # # # # # # # # # # # # # #
* KY EMISSIONS - CY20xx * File 2, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12

HDDV DEFEAT DEVICE EFFECTS ARE PRESENT. THE REBUIL D FRACTION IS 0.30. M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2020 Month: July
Altitude: Low Minimum Temperature: 61.0 (F) Maximum Temperature: 95.0 (F) Absolute Humidity: 75. grains/lb Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.2788 0.4388 0.1507 0.0365 0.0003 0.0022 0.0876 0.0051 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.357 0.448 0.715 0.516 0.461 0.076 0.245 0.344 2.51 0.464 Composite CO : 5.89 6.65 8.60 7.15 9.61 0.789 0.570 0.645 19.77 6.366 Composite NOX : 0.277 0.377 0.663 0.450 0.567 0.072 0.303 1.954 1.17 0.541

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 0.989 0.308 0.497 Composite CO : 17.32 0.930 1.177 Composite NOX : 2.073 2.990 4.807

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # #
* KY EMISSIONS - CY20xx * File 2, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #
M616 Comment: User has supplied post-1999 sulfur l evels.

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 44 * Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12 M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2020 Month: July
Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.2788 0.4388 0.1507 0.0365 0.0003 0.0022 0.0876 0.0051 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.353 0.452 0.728 0.523 0.425 0.076 0.245 0.344 2.29 0.465 Composite CO : 8.64 9.11 11.43 9.70 10.51 0.789 0.570 0.645 16.77 8.658 Composite NOX : 0.258 0.385 0.683 0.461 0.577 0.072 0.303 1.954 1.37 0.544

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 0.925 0.308 0.497 Composite CO : 18.93 0.930 1.177 Composite NOX : 2.110 2.990 4.807

--------------------------------------------------- --------------------------------------------------- ----------------

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 45 

# APPENDIX C

MOBILE6.2 Input/Output Files for the OKI’s Ohio Por tion of

Nonattainment Area

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 46

VMT By Hour (OHHVMT.D), all analysis years

VMT BY HOUR
0.0478 0.0719 0.0796 0.0666 0.0563 0.0532
0.0545 0.0543 0.0515 0.0523 0.0560 0.0565
0.0504 0.0377 0.0266 0.0209 0.0197 0.0171
0.0142 0.0156 0.0188 0.0224 0.0251 0.0310



# 2005 VMT by Speed Bin (OHSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 06 0.0245 0.0260 0.0457 0.0369 0.0977 0.0216 0.7471
1 2 0.0000 0.0000 0.0000 0.0000 0.0000 0.0006 0.00 78 0.0159 0.0228 0.0486 0.0272 0.0987 0.0226 0.7556
1 3 0.0000 0.0000 0.0004 0.0005 0.0032 0.0028 0.01 14 0.0156 0.0236 0.0401 0.0477 0.1113 0.0925 0.6510
1 4 0.0000 0.0000 0.0000 0.0004 0.0011 0.0036 0.01 04 0.0160 0.0278 0.0461 0.0267 0.0984 0.0262 0.7431
1 5 0.0000 0.0000 0.0000 0.0000 0.0002 0.0014 0.01 14 0.0169 0.0305 0.0519 0.0281 0.0984 0.0207 0.7404
1 6 0.0000 0.0000 0.0000 0.0000 0.0000 0.0011 0.01 06 0.0192 0.0294 0.0551 0.0293 0.0981 0.0206 0.7365
1 7 0.0000 0.0000 0.0000 0.0002 0.0005 0.0039 0.01 17 0.0176 0.0328 0.0552 0.0288 0.0979 0.0205 0.7308
1 8 0.0000 0.0000 0.0000 0.0002 0.0009 0.0039 0.01 24 0.0173 0.0320 0.0538 0.0285 0.0980 0.0205 0.7323
1 9 0.0000 0.0000 0.0000 0.0000 0.0002 0.0011 0.01 19 0.0175 0.0303 0.0524 0.0287 0.0983 0.0207 0.7389
1 10 0.0000 0.0000 0.0000 0.0000 0.0002 0.0011 0.01 16 0.0170 0.0299 0.0505 0.0281 0.0985 0.0208 0.7425
1 11 0.0000 0.0000 0.0000 0.0002 0.0004 0.0034 0.01 03 0.0154 0.0288 0.0487 0.0264 0.0991 0.0208 0.7465
1 12 0.0000 0.0000 0.0000 0.0002 0.0004 0.0034 0.00 98 0.0146 0.0277 0.0463 0.0255 0.0994 0.0225 0.7501
1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 59 0.0199 0.0247 0.0465 0.0272 0.0991 0.0215 0.7551
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 01 0.0251 0.0260 0.0408 0.0355 0.0982 0.0218 0.7525
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0257 0.0278 0.0411 0.0370 0.0980 0.0217 0.7487
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0246 0.0267 0.0395 0.0359 0.0982 0.0218 0.7533
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0221 0.0239 0.0371 0.0336 0.0984 0.0221 0.7628
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0194 0.0210 0.0331 0.0306 0.0988 0.0225 0.7745
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0201 0.0217 0.0356 0.0318 0.0986 0.0223 0.7700
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0213 0.0231 0.0383 0.0334 0.0983 0.0221 0.7636
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0223 0.0241 0.0391 0.0342 0.0983 0.0220 0.7600
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0254 0.0275 0.0433 0.0375 0.0978 0.0216 0.7469
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0266 0.0289 0.0448 0.0387 0.0977 0.0214 0.7419
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0277 0.0300 0.0465 0.0399 0.0975 0.0213 0.7371
2 1 0.0000 0.0000 0.0000 0.1578 0.0620 0.0730 0.27 65 0.1939 0.2275 0.0093 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0001 0.0003 0.1663 0.0714 0.1040 0.26 02 0.1730 0.2158 0.0090 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0003 0.0015 0.1669 0.0822 0.1318 0.24 18 0.1612 0.2066 0.0078 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0001 0.0007 0.1686 0.0757 0.1149 0.26 28 0.1640 0.2046 0.0087 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0000 0.1644 0.0669 0.0913 0.28 43 0.1791 0.2046 0.0092 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0000 0.1562 0.0624 0.0792 0.29 41 0.1881 0.2104 0.0096 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0000 0.0000 0.1608 0.0669 0.0953 0.28 68 0.1795 0.2012 0.0095 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0000 0.0000 0.1612 0.0679 0.0984 0.28 57 0.1780 0.1997 0.0089 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0001 0.1606 0.0644 0.0840 0.29 24 0.1866 0.2027 0.0094 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0000 0.1679 0.0681 0.0894 0.28 73 0.1807 0.1974 0.0091 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0000 0.0000 0.1627 0.0679 0.0981 0.28 50 0.1779 0.1989 0.0093 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0001 0.1531 0.0636 0.0912 0.29 32 0.1845 0.2046 0.0096 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.1567 0.0616 0.0752 0.29 45 0.1960 0.2068 0.0092 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.1572 0.0614 0.0694 0.28 77 0.2041 0.2111 0.0091 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.1613 0.0628 0.0682 0.28 97 0.2043 0.2046 0.0090 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.1598 0.0622 0.0672 0.29 05 0.2064 0.2047 0.0091 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.1614 0.0628 0.0678 0.28 80 0.2032 0.2075 0.0092 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.1722 0.0668 0.0686 0.28 81 0.1972 0.1983 0.0088 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.1568 0.0609 0.0645 0.28 71 0.2074 0.2135 0.0099 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.1593 0.0619 0.0662 0.28 40 0.2024 0.2165 0.0098 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.1847 0.0717 0.0727 0.28 13 0.1822 0.1991 0.0083 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.1653 0.0645 0.0708 0.28 33 0.1952 0.2120 0.0089 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.1645 0.0642 0.0713 0.28 37 0.1955 0.2119 0.0089 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.1587 0.0620 0.0697 0.28 43 0.2002 0.2159 0.0092 0.0000 0.0000 0.0000 0.0000



# 2005 VMT by Facility (OHFVMT.D)

VMT BY FACILITY
1 0.341 0.451 0.181 0.027
0.360 0.432 0.184 0.025
0.372 0.428 0.174 0.026
0.351 0.440 0.182 0.028
0.336 0.452 0.183 0.030
0.335 0.460 0.174 0.031
0.323 0.466 0.180 0.032
0.326 0.463 0.179 0.032
0.339 0.454 0.177 0.031
0.341 0.446 0.183 0.030

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 47

0.355 0.441 0.174 0.030
0.375 0.435 0.160 0.030
0.376 0.430 0.165 0.029
0.362 0.438 0.172 0.028
0.354 0.441 0.176 0.029
0.368 0.433 0.170 0.029
0.392 0.415 0.166 0.027
0.420 0.388 0.167 0.025
0.425 0.398 0.150 0.027
0.400 0.413 0.160 0.027
0.357 0.418 0.200 0.025
0.340 0.446 0.186 0.028
0.328 0.454 0.190 0.028
0.325 0.462 0.184 0.029

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.196 0.753 0.024 0.027
0.196 0.753 0.024 0.027
0.196 0.753 0.024 0.027
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.196 0.753 0.024 0.027
0.196 0.753 0.024 0.027
0.196 0.753 0.024 0.027
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014
0.038 0.920 0.028 0.014



# 2005 Vehicle Age Distribution File (OHREG.D), all a nalysis years

REG DIST
* OHREG.D * This file contains the Butler, Clermont, Hamilton and Warren * vehicle age distribution for LDV,LDT1,LDT2,LDT3, * and LDT4 vehicles from ODOT/OEPA 2004 VIN decodin g project.
* MOBILE6 default distributions are used for the re maining
* vehicle classes.

*
* LDV
1 0.0286 0.0381 0.0426 0.0379 0.0991 0.1052
0.0903 0.0968 0.0763 0.0745 0.0590 0.0502

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 48

0.0414 0.0335 0.0304 0.0232 0.0182 0.0128
0.0102 0.0066 0.0048 0.0023 0.0013 0.0009 0.0158
* LDT1
2 0.0278 0.0371 0.0412 0.0210 0.0450 0.0478
0.0564 0.0525 0.0865 0.0706 0.0922 0.0696
0.0503 0.0587 0.0469 0.0439 0.0418 0.0360
0.0280 0.0143 0.0074 0.0038 0.0044 0.0028 0.014
* LDT2
3 0.0345 0.0460 0.0511 0.0478 0.1204 0.1327
0.1232 0.1125 0.0802 0.0690 0.0550 0.0412
0.0269 0.0164 0.0120 0.0080 0.0095 0.0026
0.0029 0.0016 0.0016 0.0006 0.0005 0.0005 0.0033
* LDT3
4 0.0287 0.0383 0.0424 0.0398 0.1031 0.1525
0.0769 0.0740 0.0677 0.0768 0.0578 0.0461
0.0317 0.0221 0.0252 0.0249 0.0219 0.0136
0.0124 0.0083 0.0068 0.0030 0.0021 0.0008 0.0231
* LDT4
5 0.0386 0.0514 0.0569 0.0489 0.1129 0.2054
0.1223 0.1113 0.0698 0.0629 0.0500 0.0078
0.0133 0.0043 0.0046 0.0037 0.0039 0.0030
0.0030 0.0021 0.0018 0.0005 0.0002 0.0000 0.0214



# 2005 MOBILE6.2 Input File (OH.SCN)
* Mobile6 file for Butler, Clermont, Hamilton and W arren counties, * OBD program initiated on 1/5/04 * created 05/30/06 by ajr, new OEPA inputs for ozon e, pre 2006 ******************* Header Section ************** **********
MOBILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE

REPORT FILE : OH.RPT

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : ohemiss.tb1

RUN DATA ******************* Run Section ***************** **********

VMT BY HOUR : OHHVMT.D

SPEED VMT : OHSVMT.D

VMT BY FACILITY : OHFVMT.D

REG DIST : OHREG.D
FUEL RVP : 9.0

EXPRESS HC AS VOC :
* ANTI- TAMPERING PROGRAM

ANTI-TAMP PROG :
96 78 50 22222 21111111 1 12 098. 12111112

* I/M PROGRAM(S)

* OBD I/M PROGRAM : 1 2004 2005 2 T/O OBD I/M I/M MODEL YEARS : 1 1996 2050

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 49

I/M VEHICLES : 1 22222 21111111 1 I/M STRINGENCY : 1 30.0 I/M COMPLIANCE : 1 98.0 I/M WAIVER RATES : 1 1.0 1.0 I/M EXEMPTION AGE : 1 25 I/M GRACE PERIOD : 1 2

* EVAP OBD with no post '07 HDGV
I/M PROGRAM : 2 2004 2005 2 T/O EVAP OBD & G C I/M MODEL YEARS : 2 1996 2007 I/M VEHICLES : 2 22222 11111111 1 I/M COMPLIANCE : 2 98.0 I/M WAIVER RATES : 2 1.0 1.0 I/M EXEMPTION AGE : 2 25 I/M GRACE PERIOD : 2 2

* ASM 2525 I/M PROGRAM : 4 2001 2005 2 T/O ASM 2525 PHA SE- IN I/M MODEL YEARS : 4 1982 1995 I/M VEHICLES : 4 22222 21111111 1 I/M STRINGENCY : 4 30.0 I/M COMPLIANCE : 4 98.0 I/M WAIVER RATES : 4 1.0 1.0 I/M EXEMPTION AGE : 4 25 I/M GRACE PERIOD : 4 2

* IDLE I/M PROGRAM : 5 1998 2000 2 T/O IDLE I/M MODEL YEARS : 5 1973 1996 I/M VEHICLES : 5 22222 21111111 1 I/M STRINGENCY : 5 30.0 I/M COMPLIANCE : 5 98.0 I/M WAIVER RATES : 5 1.0 1.0 I/M EXEMPTION AGE : 5 25 I/M GRACE PERIOD : 5 2

* IM 240 I/M PROGRAM : 6 1996 1997 2 T/O IM240 I/M MODEL YEARS : 6 1971 1994 I/M VEHICLES : 6 22222 21111111 1 I/M STRINGENCY : 6 30.0 I/M COMPLIA NCE : 6 98.0 I/M WAIVER RATES : 6 1.0 1.0 I/M EXEMPTION AGE : 6 25 I/M CUTPOINTs : 6 CUTPOINT.D I/M GRACE PERIOD : 6 2

* GC I/M PROGRAM : 7 1996 2005 2 T/O GC I/M MODEL YEARS : 7 1982 1995 I/M VEHICLES : 7 22222 21111111 1 I/M COMPLIANCE : 7 98.0 I/M WAIVER RATES : 7 1.0 1.0 I/M EXEMPTION AGE : 7 25 I/M GRACE PERIOD : 7 2
FUEL PROGRAM : 1
OXYGENATED FUELS : .000 .420 .000 .036 2

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 50

STAGE II REFUELING :
93 3 86. 86.

EXPAND BUS EFS : ******************* Summer Scenario Section ***** ********** SCENARIO RECORD : Ohio Emissions - CY20xx
CALENDAR YEAR : 2005

EVALUATION MONTH : 7
SEASON : 1 MIN/MAX TEMP : 61.0 95.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV

DIESEL SULFUR : 317.00 ******************* Annual Scenario Section ***** ********** SCENARIO RECORD : Ohio Emissions - CY20xx
CALENDAR YEAR : 2005

EVALUATION MONTH : 7 MIN/MAX TEMP : 47.0 64.0

PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 317.00
******************* End of Run ****************** **********

END OF RUN



# 2005 MOBILE6.2 Output Report (OH.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: OHSCN.IN (file 3, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external * data file: OHHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: OHSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: OHFVMT.D

Reading User Supplied ROADWAY VMT Factors

* Reading Registration Distributions from the follo wing external
* data file: OHREG.D

* Reading ASM I/M Test Credits from ASMDATA.D

* Reading non-default I/M CUTPOINTS from the follow ing external
* data file: CUTPOINT.D
M616 Comment: User has supplied post-1999 sulfur l evels.
M601 Comment:
User has enabled STAGE II REFUELING.

* # # # # # # # # # # # # # # # # # # # # # # # # # * Ohio Emissions - CY20xx * File 3, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV *** I/M credits for Tech1&2 vehicles were read from the following external
data file: TECH12.D M 48 Warning:
there are no sales for vehicle class HDGV8b

Calendar Year: 2005 Month: July Altitude: Low Minimum Temperature: 61.0 (F) Maximum Temperature: 95.0 (F)

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 51 Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 8.9 psi Fuel Sulfur Content: 92. ppm

Exhaust I/M Program: Yes Evap I/M Program: Yes
ATP Program: Yes
Reformulated Gas: No

Ether Blend Market Share: 0.000 Alcohol Bl end Market Share: 0.420 Ether Blend Oxygen Content: 0.000 Alcohol Bl end Oxygen Content: 0.036
Alcohol B lend RVP Waiver: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.4050 0.3396 0.1270 0.0359 0.0006 0.0019 0.0845 0.0057 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 1.251 1.047 1.216 1.093 1.894 0.644 0.657 0.579 3.53 1.155 Composite CO : 12.48 13.44 15.01 13.87 18.13 1.751 1.132 3.410 17.88 12.568 Composite NOX : 0.915 1.164 1.494 1.254 4.265 1.606 1.480 12.715 1.23 2.194

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0003 0.0009 0.0016

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 8.840 0.583 0.787 Composite CO : 114.81 4.539 2.970 Composite NOX : 8.411 16.545 13.772

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # # * Ohio Emissions - CY20xx * File 3, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b

Calendar Year: 2005 Month: July Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 9.5 psi Fuel Sulfur Content: 92. ppm

Exhaust I/M Program: Yes Evap I/M Program: Yes
ATP Program: Yes
Reformulated Gas: No

Ether Blend Market Share: 0.000 Alcohol Bl end Market Share: 0.420 Ether Blend Oxygen Content: 0.000 Alcohol Bl end Oxygen Content: 0.036
Alcohol B lend RVP Waiver: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.4050 0.3396 0.1270 0.0359 0.0006 0.0019 0.0845 0.0057 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.994 0.913 1.096 0.963 1.414 0.644 0.657 0.579 2.15 0.965 Composite CO : 13.81 16.00 17.13 16.31 16.88 1.751 1.132 3.410 15.23 14.185 Composite NOX : 0.892 1.205 1.546 1.298 4.367 1.606 1.480 12.715 1.45 2.210

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0003 0.0009 0.0016

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 6.768 0.583 0.787 Composite CO : 99.19 4.539 2.970 Composite NOX : 8.902 16.545 13.772

--------------------------------------------------- --------------------------------------------------- ----------------



# 2008 VMT by Speed bin (OHSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 09 0.0170 0.0245 0.0392 0.0435 0.0977 0.0165 0.7606
1 2 0.0000 0.0000 0.0000 0.0002 0.0000 0.0012 0.00 63 0.0104 0.0223 0.0401 0.0340 0.0993 0.0282 0.7579
1 3 0.0000 0.0000 0.0008 0.0019 0.0021 0.0026 0.00 75 0.0099 0.0233 0.0378 0.0426 0.1159 0.0909 0.6648
1 4 0.0000 0.0000 0.0000 0.0010 0.0021 0.0028 0.00 79 0.0105 0.0250 0.0373 0.0337 0.0979 0.0282 0.7536
1 5 0.0000 0.0000 0.0000 0.0000 0.0006 0.0021 0.00 81 0.0127 0.0269 0.0418 0.0349 0.0981 0.0161 0.7588
1 6 0.0000 0.0000 0.0000 0.0000 0.0000 0.0022 0.00 82 0.0126 0.0285 0.0434 0.0362 0.0975 0.0165 0.7550
1 7 0.0000 0.0000 0.0000 0.0001 0.0021 0.0024 0.01 00 0.0121 0.0307 0.0413 0.0367 0.0979 0.0160 0.7508

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 52 1 8 0.0000 0.0000 0.0000 0.0005 0.0022 0.0024 0.01 02 0.0117 0.0310 0.0398 0.0356 0.0976 0.0160 0.7529
1 9 0.0000 0.0000 0.0000 0.0000 0.0003 0.0024 0.00 79 0.0129 0.0281 0.0415 0.0342 0.0976 0.0161 0.7589
1 10 0.0000 0.0000 0.0000 0.0000 0.0003 0.0024 0.00 79 0.0125 0.0271 0.0405 0.0330 0.0974 0.0162 0.7627
1 11 0.0000 0.0000 0.0000 0.0002 0.0017 0.0022 0.00 88 0.0105 0.0269 0.0373 0.0318 0.0979 0.0191 0.7637
1 12 0.0000 0.0000 0.0000 0.0002 0.0017 0.0021 0.00 84 0.0099 0.0259 0.0360 0.0300 0.0990 0.0260 0.7608
1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0002 0.00 62 0.0120 0.0252 0.0373 0.0299 0.0981 0.0165 0.7746
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 05 0.0170 0.0249 0.0343 0.0378 0.0969 0.0169 0.7717
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0183 0.0260 0.0332 0.0398 0.0963 0.0169 0.7695
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0176 0.0249 0.0322 0.0381 0.0962 0.0170 0.7740
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0158 0.0224 0.0308 0.0358 0.0952 0.0172 0.7827
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0139 0.0197 0.0281 0.0312 0.0946 0.0175 0.7949
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0144 0.0203 0.0302 0.0343 0.0955 0.0173 0.7879
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0153 0.0216 0.0322 0.0375 0.0961 0.0171 0.7802
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0160 0.0225 0.0327 0.0383 0.0964 0.0170 0.7771
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0182 0.0257 0.0353 0.0428 0.0971 0.0167 0.7642
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0191 0.0270 0.0361 0.0443 0.0971 0.0166 0.7598
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0198 0.0280 0.0372 0.0463 0.0974 0.0165 0.7547
2 1 0.0000 0.0000 0.0000 0.2542 0.0514 0.0702 0.23 35 0.1911 0.1904 0.0091 0.0000 0.0000 0.0000 0.0000
2 2 0.0001 0.0001 0.0004 0.2669 0.0666 0.1030 0.20 50 0.1671 0.1821 0.0088 0.0000 0.0000 0.0000 0.0000
2 3 0.0001 0.0004 0.0029 0.2676 0.0786 0.1230 0.19 61 0.1486 0.1736 0.0091 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0001 0.0007 0.2734 0.0676 0.1091 0.21 27 0.1617 0.1652 0.0094 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0001 0.2685 0.0580 0.0845 0.23 34 0.1818 0.1639 0.0099 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0000 0.2570 0.0536 0.0767 0.24 17 0.1915 0.1692 0.0103 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0000 0.0001 0.2648 0.0578 0.0871 0.23 99 0.1785 0.1616 0.0101 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0000 0.0001 0.2656 0.0588 0.0893 0.23 92 0.1771 0.1596 0.0102 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0000 0.2642 0.0561 0.0787 0.24 02 0.1894 0.1611 0.0103 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0001 0.2747 0.0590 0.0818 0.23 51 0.1837 0.1556 0.0100 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0000 0.0001 0.2673 0.0591 0.0898 0.23 73 0.1770 0.1593 0.0100 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0000 0.2537 0.0550 0.0864 0.24 55 0.1838 0.1652 0.0104 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.2577 0.0527 0.0716 0.24 18 0.2005 0.1656 0.0101 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.2570 0.0520 0.0636 0.24 13 0.2055 0.1706 0.0098 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.2642 0.0534 0.0618 0.24 15 0.2062 0.1630 0.0099 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.2625 0.0531 0.0609 0.24 17 0.2090 0.1626 0.0101 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.2640 0.0534 0.0613 0.24 04 0.2048 0.1662 0.0099 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.2796 0.0566 0.0610 0.23 94 0.1974 0.1565 0.0096 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.2581 0.0522 0.0580 0.23 89 0.2104 0.1720 0.0103 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.2603 0.0526 0.0596 0.23 77 0.2036 0.1762 0.0100 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.2941 0.0595 0.0641 0.23 59 0.1782 0.1596 0.0086 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.2672 0.0540 0.0641 0.23 87 0.1940 0.1726 0.0093 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.2660 0.0538 0.0648 0.23 92 0.1943 0.1726 0.0093 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.2582 0.0522 0.0637 0.23 96 0.2003 0.1764 0.0096 0.0000 0.0000 0.0000 0.0000



# 2008 VMT by Facility Type (OHFVMT.D)

VMT BY FACILITY
1 0.322 0.427 0.234 0.017
0.339 0.409 0.236 0.016
0.353 0.404 0.226 0.017
0.332 0.412 0.238 0.018
0.319 0.422 0.239 0.019
0.320 0.431 0.229 0.020
0.308 0.434 0.238 0.020
0.311 0.431 0.237 0.020
0.324 0.424 0.233 0.020
0.325 0.415 0.241 0.019
0.339 0.412 0.230 0.019
0.361 0.407 0.213 0.019
0.360 0.403 0.218 0.018
0.345 0.411 0.225 0.018
0.337 0.413 0.232 0.019
0.352 0.405 0.225 0.019
0.373 0.391 0.219 0.018
0.398 0.365 0.220 0.016
0.407 0.376 0.200 0.017
0.381 0.390 0.211 0.017
0.334 0.392 0.259 0.016
0.321 0.419 0.242 0.018
0.309 0.426 0.246 0.018

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 53

0.308 0.434 0.239 0.019

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.215 0.733 0.032 0.019
0.215 0.733 0.032 0.019
0.215 0.733 0.032 0.019
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.215 0.733 0.032 0.019
0.215 0.733 0.032 0.019
0.215 0.733 0.032 0.019
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007
0.029 0.927 0.037 0.007



# 2008 MOBILE6.2 Input File (OHSCN.IN)
* Mobile6 input file for Butler, Clermont, Hamilton and Warren counties, * low RVP beginning summer 2008 * created 4/9/07 by ajr, includes annual scenario,l ow RVP,post 2007 ******************* Header Section ************** **********
MOBILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE REPORT FILE : oh.rpt

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : ohemiss.tb1

RUN DATA ******************* Run Section ***************** **********

VMT BY HOUR : OHHVMT.D

SPEED VMT : OHSVMT.D

VMT BY FACILITY : OHFVMT.D

REG DIST : OHREG.D
FUEL PROGRAM : 1
OXYGENATED FUELS : .000 .420 .000 .036 2

STAGE II REFUELING :
93 3 86. 86.

EXPAND BUS EFS :
REBUILD EFFECTS : 0.10 ******************* Summer Scenario Section ***** **********

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 54 SCENARIO RECORD : Ohio Emissions - CY20xx
CALENDAR YEAR : 2008

EVALUATION MONTH : 7
FUEL RVP : 7.8
SEASON : 1 MIN/MAX TEMP : 62.0 91.3
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV PMDDR1.CSV
PMDDR2.CSV
DIESEL SULFUR : 43 ******************* Annual Scenario Section ***** ********** SCENARIO RECORD : Ohio Emissions - CY20xx
CALENDAR YEAR : 2008
EVALUATION MONTH : 7
FUEL RVP : 9.0 MIN/MAX TEMP : 47.0 64.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV PMDDR1.CSV
PMDDR2.CSV
DIESEL SULFUR : 43
******************* End of Run ****************** **********

END OF RUN



# 2008 MOBILE6.2 Output Report (OH.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: OHSCN.IN (file 3, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external * data file: OHHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: OHSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: OHFVMT.D

Reading User Supplied ROADWAY VMT Factors

* Reading Registration Distributions from the follo wing external
* data file: OHREG.D
M616 Comment: User has supplied post-1999 sulfur l evels.
M601 Comment:
User has enabled STAGE II REFUELING.

* # # # # # # # # # # # # # # # # # # # # # # # # #
* Ohio Emissions - CY20xx * File 3, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b

HDDV DEFEAT DEVICE EFFECTS ARE PRESENT. THE REBUIL D FRACTION IS 0.10. M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2008 Month: July
Altitude: Low Minimum Temperature: 62.0 (F) Maximum Temperature: 91.3 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 7.8 psi Weathered RVP: 8.0 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 55 Ether Blend Market Share: 0.000 Alcohol Bl end Market Share: 0.420 Ether Blend Oxygen Content: 0.000 Alcohol Bl end Oxygen Content: 0.036
Alcohol B lend RVP Waiver: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.3623 0.3705 0.1385 0.0357 0.0004 0.0020 0.0851 0.0055 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.923 0.802 1.007 0.858 1.312 0.344 0.566 0.516 2.74 0.878 Composite CO : 9.49 10.52 12.46 11.05 14.02 1.351 0.961 2.825 18.05 9.905 Composite NOX : 0.741 0.965 1.408 1.085 2.929 0.875 1.174 10.042 1.22 1.790

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0002 0.0009 0.0017

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 7.094 0.399 0.742 Composite CO : 94.69 3.770 2.830 Composite NOX : 7.696 14.196 12.082

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # # * Ohio Emissions - CY20xx * File 3, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2008 Month: July Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 9.5 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Ether Blend Market Share: 0.000 Alcohol Bl end Market Share: 0.420 Ether Blend Oxygen Content: 0.000 Alcohol Bl end Oxygen Content: 0.036
Alcohol B lend RVP Waiver: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.3623 0.3705 0.1385 0.0357 0.0004 0.0020 0.0851 0.0055 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.880 0.817 1.051 0.881 1.177 0.344 0.566 0.516 2.21 0.866 Composite CO : 12.77 14.60 16.75 15.18 14.75 1.351 0.961 2.825 16.12 13.214 Composite NOX : 0.736 1.018 1.487 1.146 2.981 0.875 1.174 10.042 1.42 1.822

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0002 0.0009 0.0017

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 6.413 0.399 0.742 Composite CO : 91.20 3.770 2.830 Composite NOX : 8.489 14.196 12.082

--------------------------------------------------- --------------------------------------------------- ----------------


# 2015 VMT by Speed Bin (OHSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 10 0.0166 0.0177 0.0522 0.0350 0.1026 0.0217 0.7531
1 2 0.0000 0.0000 0.0000 0.0000 0.0002 0.0014 0.00 60 0.0104 0.0153 0.0512 0.0329 0.0986 0.0326 0.7514
1 3 0.0000 0.0000 0.0005 0.0015 0.0021 0.0023 0.00 97 0.0118 0.0280 0.0446 0.0425 0.1089 0.0504 0.6978
1 4 0.0000 0.0000 0.0000 0.0012 0.0010 0.0031 0.00 84 0.0118 0.0171 0.0469 0.0333 0.0990 0.0334 0.7449
1 5 0.0000 0.0000 0.0000 0.0000 0.0009 0.0012 0.00 74 0.0141 0.0185 0.0523 0.0352 0.0982 0.0227 0.7494
1 6 0.0000 0.0000 0.0000 0.0000 0.0002 0.0016 0.00 76 0.0142 0.0199 0.0541 0.0359 0.0982 0.0216 0.7466
1 7 0.0000 0.0000 0.0000 0.0004 0.0013 0.0020 0.01 03 0.0146 0.0197 0.0533 0.0363 0.0983 0.0215 0.7422
1 8 0.0000 0.0000 0.0000 0.0004 0.0017 0.0022 0.01 04 0.0140 0.0196 0.0521 0.0357 0.0984 0.0216 0.7440
1 9 0.0000 0.0000 0.0000 0.0000 0.0004 0.0014 0.00 74 0.0149 0.0191 0.0515 0.0354 0.0983 0.0217 0.7498
1 10 0.0000 0.0000 0.0000 0.0000 0.0004 0.0014 0.00 74 0.0143 0.0186 0.0498 0.0347 0.0983 0.0228 0.7523
1 11 0.0000 0.0000 0.0000 0.0004 0.0011 0.0017 0.00 90 0.0128 0.0173 0.0465 0.0336 0.0983 0.0230 0.7562
1 12 0.0000 0.0000 0.0000 0.0003 0.0011 0.0021 0.00 84 0.0120 0.0165 0.0444 0.0325 0.0995 0.0326 0.7506

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 56 1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0007 0.00 55 0.0122 0.0174 0.0453 0.0329 0.0985 0.0232 0.7643
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 07 0.0170 0.0178 0.0429 0.0340 0.1035 0.0221 0.7620
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0185 0.0186 0.0430 0.0352 0.1035 0.0221 0.7591
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0177 0.0179 0.0412 0.0341 0.1035 0.0222 0.7633
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0159 0.0160 0.0394 0.0320 0.1032 0.0225 0.7710
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0140 0.0141 0.0346 0.0292 0.1032 0.0229 0.7820
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0144 0.0145 0.0385 0.0303 0.1030 0.0226 0.7766
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0153 0.0154 0.0422 0.0319 0.1029 0.0224 0.7699
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0160 0.0161 0.0428 0.0327 0.1031 0.0223 0.7671
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0183 0.0184 0.0473 0.0357 0.1031 0.0219 0.7553
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0192 0.0193 0.0487 0.0369 0.1032 0.0218 0.7510
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0199 0.0201 0.0508 0.0381 0.1031 0.0216 0.7464
2 1 0.0000 0.0000 0.0000 0.2312 0.0536 0.0672 0.23 61 0.1827 0.2125 0.0167 0.0000 0.0000 0.0000 0.0000
2 2 0.0000 0.0003 0.0007 0.2425 0.0638 0.0960 0.21 45 0.1665 0.1997 0.0159 0.0000 0.0000 0.0000 0.0000
2 3 0.0000 0.0010 0.0020 0.2432 0.0746 0.1140 0.20 82 0.1479 0.1937 0.0153 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0005 0.0006 0.2465 0.0686 0.1025 0.21 70 0.1588 0.1885 0.0170 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0000 0.0003 0.2407 0.0592 0.0853 0.23 34 0.1750 0.1887 0.0173 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0001 0.2299 0.0541 0.0771 0.24 16 0.1843 0.1951 0.0179 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0000 0.0004 0.2363 0.0594 0.0881 0.23 59 0.1754 0.1866 0.0179 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0000 0.0004 0.2369 0.0602 0.0901 0.23 68 0.1726 0.1850 0.0179 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0002 0.2359 0.0561 0.0798 0.24 08 0.1817 0.1876 0.0178 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0000 0.0003 0.2454 0.0596 0.0838 0.23 55 0.1760 0.1820 0.0174 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0001 0.0004 0.2388 0.0603 0.0908 0.23 36 0.1739 0.1845 0.0176 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0003 0.2263 0.0561 0.0867 0.24 08 0.1809 0.1909 0.0181 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.2302 0.0536 0.0726 0.24 35 0.1904 0.1922 0.0175 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.2307 0.0529 0.0627 0.24 60 0.1936 0.1970 0.0171 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.2364 0.0540 0.0612 0.24 68 0.1938 0.1905 0.0171 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.2345 0.0536 0.0605 0.24 75 0.1959 0.1907 0.0174 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.2365 0.0540 0.0609 0.24 53 0.1927 0.1933 0.0173 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.2508 0.0571 0.0611 0.24 38 0.1865 0.1840 0.0167 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.2305 0.0525 0.0580 0.24 45 0.1969 0.1994 0.0182 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.2337 0.0533 0.0595 0.24 20 0.1919 0.2018 0.0178 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.2672 0.0608 0.0643 0.23 73 0.1717 0.1831 0.0155 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.2415 0.0553 0.0634 0.24 16 0.1849 0.1968 0.0166 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.2404 0.0551 0.0639 0.24 21 0.1852 0.1968 0.0165 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.2327 0.0534 0.0627 0.24 31 0.1900 0.2010 0.0170 0.0000 0.0000 0.0000 0.0000



# 2015 VMT by Facility Type (OHFVMT.D)

VMT BY FACILITY
1 0.328 0.428 0.225 0.019
0.346 0.409 0.228 0.018
0.359 0.406 0.217 0.019
0.337 0.416 0.227 0.020
0.323 0.427 0.229 0.021
0.323 0.436 0.219 0.022
0.311 0.440 0.227 0.022
0.314 0.438 0.226 0.022
0.327 0.430 0.222 0.022
0.328 0.421 0.230 0.021
0.342 0.418 0.219 0.021
0.363 0.414 0.202 0.021
0.364 0.408 0.208 0.020
0.350 0.415 0.215 0.020
0.341 0.418 0.221 0.021
0.356 0.410 0.214 0.020
0.378 0.394 0.208 0.019
0.404 0.368 0.210 0.018
0.412 0.380 0.190 0.019
0.386 0.393 0.202 0.019
0.341 0.393 0.249 0.018
0.327 0.421 0.232 0.019
0.315 0.429 0.236 0.020
0.312 0.438 0.229 0.021

... Identical distribution for all veh. types with the exception of diesel
transit buses

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 57

26 0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009



# 2015 MOBILE6.2 Input File (OHSCN.IN) * Mobile6 input file for Butler, Clermont, Hamilton and Warren counties, * low RVP beginning summer 2008 * created 4/9/07 by ajr, includes annual scenario,l ow RVP,post 2007

************* ****** Header Section ************************
MOBILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE REPORT FILE : oh.rpt

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : ohemiss.tb1

RUN DATA ******************* Run Section ***************** **********

VMT BY HOUR : OHHVMT.D

SPEED VMT : OHSVMT.D

VMT BY FACILITY : OHFVMT.D

REG DIST : OHREG.D
FUEL PROGRAM : 1
OXYGENATED FUELS : .000 .420 .000 .036 2

STAGE II REFUELING :
93 3 86. 86.

EXPAND BUS EFS :

REBUILD EFF ECTS : 0.10

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 58

******************* Summer Scenario Section ***** ********** SCENARIO RECORD : Ohio Emissions - CY20xx

CALENDAR YEAR : 2015

EVALUATION MONTH : 7
FUEL RVP : 7.8

SEASON : 1 MIN/MAX TEMP : 62.0 91.3
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43 ******************* Annual Scenario Section ***** ********** SCENARIO RECORD : Ohio Emissions - CY20xx
CALENDAR YEAR : 2015

E VALUATION MONTH : 7
FUEL RVP : 9.0 MIN/MAX TEMP : 47.0 64.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV
PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43
******************* End of Run ****************** **********

END OF RUN



# 2015 MOBILE6.2 Output File (OH.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: OHSCN.IN (file 3, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external * data file: OHHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: OHSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: OHFVMT.D

Reading User Supplied ROADWAY VMT Factors

* Reading Registration Distributions from the follo wing external
* data file: OHREG.D
M616 Comment: User has supplied post-1999 sulfur l evels.
M601 Comment:
User has enabled STAGE II REFUELING.

* # # # # # # # # # # # # # # # # # # # # # # # # # * Ohio Emissions - CY20xx * File 3, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12

HDDV DEFEAT DEVICE EFFECTS ARE PRESENT. THE REBUIL D FRACTION IS 0.10. M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2015 Month: July Altitude: Low Minimum Temperature: 62.0 (F) Maximum Temperature: 91.3 (F) Absolute Humidity: 75. grains/lb

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 59 Nominal Fuel RVP: 7.8 psi Weathered RVP: 8.0 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Ether Blend Market Share: 0.000 Alcohol Bl end Market Share: 0.420 Ether Blend Oxygen Content: 0.000 Alcohol Bl end Oxygen Content: 0.036
Alcohol B lend RVP Waiver: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.2935 0.4202 0.1571 0.0357 0.0003 0.0023 0.0858 0.0052 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.491 0.462 0.588 0.496 0.674 0.112 0.213 0.340 2.71 0.498 Composite CO : 6.84 7.42 8.25 7.65 8.93 0.820 0.479 0.951 17.80 6.917 Composite NOX : 0.379 0.455 0.622 0.500 1.098 0.173 0.308 3.792 1.23 0.772

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0009 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 2.023 0.284 0.518 Composite CO : 16.22 1.696 1.499 Composite NOX : 4.015 6.477 7.115

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # # * Ohio Emissions - CY20xx * File 3, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12 M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2015 Month: July Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 9.5 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Ether Blend Market Share: 0.000 Alcohol Bl end Market Share: 0.420 Ether Blend Oxygen Content: 0.000 Alcohol Bl end Oxygen Content: 0.036
Alcohol B lend RVP Waiver: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.2935 0.4202 0.1571 0.0357 0.0003 0.0023 0.0858 0.0052 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.483 0.483 0.616 0.519 0.605 0.112 0.213 0.340 2.18 0.504 Composite CO : 10.09 10.46 11.35 10.70 9.79 0.820 0.479 0.951 15.90 9.654 Composite NOX : 0.373 0.476 0.651 0.523 1.104 0.173 0.308 3.792 1.43 0.784

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0009 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 1.794 0.284 0.518 Composite CO : 17.78 1.696 1.499 Composite NOX : 4.036 6.477 7.115

--------------------------------------------------- --------------------------------------------------- ----------------



# 2020 VMT by Speed Bin (OHSVMT.D)

SPEED VMT
1 1 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 10 0.0164 0.0170 0.0526 0.0353 0.1036 0.0214 0.7526
1 2 0.0000 0.0000 0.0002 0.0001 0.0005 0.0008 0.00 62 0.0106 0.0166 0.0490 0.0342 0.0987 0.0469 0.7362
1 3 0.0000 0.0000 0.0010 0.0019 0.0018 0.0038 0.01 03 0.0195 0.0277 0.0554 0.0287 0.1103 0.0632 0.6766
1 4 0.0000 0.0000 0.0000 0.0013 0.0016 0.0032 0.00 81 0.0121 0.0164 0.0478 0.0326 0.1078 0.0460 0.7230

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 60 1 5 0.0000 0.0000 0.0000 0.0000 0.0009 0.0016 0.00 86 0.0128 0.0188 0.0511 0.0352 0.0993 0.0223 0.7493
1 6 0.0000 0.0000 0.0000 0.0000 0.0006 0.0011 0.00 85 0.0132 0.0202 0.0530 0.0364 0.0992 0.0213 0.7465
1 7 0.0000 0.0000 0.0000 0.0008 0.0013 0.0031 0.00 91 0.0149 0.0190 0.0535 0.0355 0.0994 0.0221 0.7413
1 8 0.0000 0.0000 0.0000 0.0010 0.0014 0.0037 0.00 96 0.0140 0.0187 0.0518 0.0350 0.0994 0.0222 0.7431
1 9 0.0000 0.0000 0.0000 0.0000 0.0008 0.0018 0.00 85 0.0129 0.0198 0.0501 0.0356 0.0994 0.0224 0.7488
1 10 0.0000 0.0000 0.0000 0.0000 0.0007 0.0017 0.00 82 0.0125 0.0192 0.0487 0.0348 0.0994 0.0225 0.7522
1 11 0.0000 0.0000 0.0000 0.0007 0.0011 0.0028 0.00 80 0.0131 0.0167 0.0466 0.0330 0.1003 0.0293 0.7485
1 12 0.0000 0.0000 0.0000 0.0007 0.0012 0.0025 0.00 78 0.0123 0.0166 0.0437 0.0319 0.1006 0.0406 0.7422
1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0008 0.00 58 0.0117 0.0168 0.0451 0.0332 0.0996 0.0228 0.7642
1 14 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 09 0.0164 0.0173 0.0435 0.0339 0.1045 0.0218 0.7618
1 15 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0181 0.0181 0.0431 0.0355 0.1045 0.0217 0.7590
1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0173 0.0173 0.0413 0.0344 0.1045 0.0219 0.7632
1 17 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0156 0.0156 0.0395 0.0324 0.1041 0.0222 0.7707
1 18 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0137 0.0137 0.0348 0.0296 0.1042 0.0225 0.7816
1 19 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0141 0.0141 0.0387 0.0307 0.1040 0.0223 0.7761
1 20 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0150 0.0149 0.0425 0.0322 0.1039 0.0220 0.7694
1 21 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0157 0.0156 0.0430 0.0330 0.1040 0.0219 0.7667
1 22 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0179 0.0178 0.0476 0.0360 0.1041 0.0215 0.7550
1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0188 0.0187 0.0489 0.0372 0.1041 0.0214 0.7508
1 24 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.00 00 0.0195 0.0195 0.0511 0.0383 0.1041 0.0213 0.7462
2 1 0.0000 0.0000 0.0000 0.2688 0.0500 0.0658 0.22 43 0.1692 0.2056 0.0162 0.0000 0.0000 0.0000 0.0000
2 2 0.0001 0.0004 0.0006 0.2824 0.0622 0.0970 0.19 74 0.1545 0.1910 0.0145 0.0000 0.0000 0.0000 0.0000
2 3 0.0001 0.0010 0.0032 0.2832 0.0763 0.1114 0.19 12 0.1380 0.1821 0.0134 0.0000 0.0000 0.0000 0.0000
2 4 0.0000 0.0006 0.0011 0.2864 0.0669 0.1044 0.20 08 0.1441 0.1799 0.0158 0.0000 0.0000 0.0000 0.0000
2 5 0.0000 0.0001 0.0005 0.2800 0.0563 0.0875 0.21 59 0.1609 0.1819 0.0168 0.0000 0.0000 0.0000 0.0000
2 6 0.0000 0.0000 0.0002 0.2681 0.0522 0.0785 0.22 48 0.1703 0.1885 0.0174 0.0000 0.0000 0.0000 0.0000
2 7 0.0000 0.0001 0.0006 0.2754 0.0573 0.0907 0.21 86 0.1593 0.1806 0.0174 0.0000 0.0000 0.0000 0.0000
2 8 0.0000 0.0002 0.0005 0.2765 0.0580 0.0922 0.21 89 0.1584 0.1780 0.0174 0.0000 0.0000 0.0000 0.0000
2 9 0.0000 0.0000 0.0003 0.2747 0.0542 0.0818 0.22 28 0.1682 0.1808 0.0173 0.0000 0.0000 0.0000 0.0000
2 10 0.0000 0.0001 0.0005 0.2853 0.0572 0.0854 0.21 66 0.1631 0.1750 0.0168 0.0000 0.0000 0.0000 0.0000
2 11 0.0000 0.0001 0.0006 0.2783 0.0577 0.0923 0.21 79 0.1576 0.1785 0.0171 0.0000 0.0000 0.0000 0.0000
2 12 0.0000 0.0000 0.0004 0.2643 0.0540 0.0880 0.22 74 0.1638 0.1844 0.0176 0.0000 0.0000 0.0000 0.0000
2 13 0.0000 0.0000 0.0000 0.2684 0.0500 0.0730 0.23 02 0.1753 0.1861 0.0170 0.0000 0.0000 0.0000 0.0000
2 14 0.0000 0.0000 0.0000 0.2686 0.0493 0.0605 0.23 34 0.1809 0.1908 0.0166 0.0000 0.0000 0.0000 0.0000
2 15 0.0000 0.0000 0.0000 0.2752 0.0503 0.0588 0.23 39 0.1810 0.1843 0.0166 0.0000 0.0000 0.0000 0.0000
2 16 0.0000 0.0000 0.0000 0.2731 0.0499 0.0580 0.23 46 0.1830 0.1846 0.0169 0.0000 0.0000 0.0000 0.0000
2 17 0.0000 0.0000 0.0000 0.2753 0.0503 0.0584 0.23 24 0.1799 0.1870 0.0168 0.0000 0.0000 0.0000 0.0000
2 18 0.0000 0.0000 0.0000 0.2911 0.0530 0.0584 0.23 03 0.1736 0.1774 0.0161 0.0000 0.0000 0.0000 0.0000
2 19 0.0000 0.0000 0.0000 0.2688 0.0490 0.0557 0.23 18 0.1841 0.1930 0.0177 0.0000 0.0000 0.0000 0.0000
2 20 0.0000 0.0000 0.0000 0.2721 0.0497 0.0571 0.22 93 0.1793 0.1952 0.0173 0.0000 0.0000 0.0000 0.0000
2 21 0.0000 0.0000 0.0000 0.3086 0.0562 0.0612 0.22 37 0.1594 0.1759 0.0150 0.0000 0.0000 0.0000 0.0000
2 22 0.0000 0.0000 0.0000 0.2804 0.0514 0.0608 0.22 89 0.1724 0.1901 0.0161 0.0000 0.0000 0.0000 0.0000
2 23 0.0000 0.0000 0.0000 0.2792 0.0512 0.0613 0.22 94 0.1728 0.1902 0.0160 0.0000 0.0000 0.0000 0.0000
2 24 0.0000 0.0000 0.0000 0.2707 0.0497 0.0603 0.23 07 0.1775 0.1946 0.0166 0.0000 0.0000 0.0000 0.0000



# 2020 VMT by Facility Type (OHFVMT.D)

VMT BY FACILITY
1 0.319 0.414 0.249 0.018
0.336 0.395 0.252 0.017
0.349 0.393 0.241 0.018
0.328 0.401 0.253 0.019
0.314 0.412 0.254 0.020
0.315 0.421 0.244 0.021
0.303 0.424 0.252 0.021
0.306 0.422 0.251 0.021
0.318 0.414 0.247 0.021
0.319 0.405 0.256 0.020
0.333 0.403 0.244 0.020
0.355 0.400 0.225 0.020
0.354 0.395 0.232 0.019
0.340 0.402 0.239 0.019
0.331 0.403 0.246 0.019
0.346 0.396 0.238 0.019
0.368 0.381 0.232 0.018
0.393 0.355 0.235 0.017
0.402 0.368 0.212 0.018
0.376 0.380 0.225 0.018
0.330 0.377 0.276 0.017

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 61

0.317 0.406 0.258 0.018
0.305 0.414 0.262 0.019
0.304 0.423 0.254 0.020

... Identical distribution for all veh. types with the exception of diesel
transit buses


# 26 0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.179 0.747 0.054 0.020
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009
0.024 0.925 0.042 0.009



# 2020 MOBILE6.2 Input File (OHSCN.IN)

* Mobile6 input file for Butler, Clermont, Hamilton and Warren counties, * low RVP beginning summer 2008 * created 4/9/07 by ajr, includes annual scenario,l ow RVP,post 2007 ******************* Header Section ************** **********
MOBILE6 INPUT FILE :

POLLUTANTS : HC NOx CO

PARTICULATES :
* PARTICULATES REPORTED IN *.PM FILE REPORT FILE : oh.rpt

DATABASE OUTPUT :

WITH FIELDNAMES :
DATABASE EMISSIONS : 2211 1111 22

DAILY OUTPUT : EMISSIONS TABLE : ohemiss.tb1

RUN DATA ******************* Run Section ***************** **********

VMT BY HOUR : OHHVMT.D

SPEED VMT : OHSVMT.D

VMT BY FACILITY : OHFVMT.D

REG DIST : OHREG.D
FUEL PROGRAM : 1
OXYGENATED FUELS : .000 .420 .000 .036 2

STAGE II REFUELING :
93 3 86. 86.

EXPAND BUS EFS :
REBUILD EFFECTS : 0.10 ******************* Summer Scenario Section ***** ********** SCENARIO RECORD : Ohio Emissions - CY20xx

CALENDAR YEAR : 2020
EVALUATION MONTH : 7
FUEL RVP : 7.8
SEASON : 1 MIN/MAX TEMP : 62.0 91.3
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43 ******************* Annual Scenario Section ***** ********** SCENARIO RECORD : Ohio Emissions - CY20xx

CALENDAR YEAR : 2020
EVALUATION MONTH : 7
FUEL RVP : 9.0 MIN/MAX TEMP : 47.0 64.0
PARTICLE SIZE : 2.5
PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.C SV PMDZML.CSV PMDDR1.CSV PMDDR2.CSV
DIESEL SULFUR : 43
******************* End of Run ****************** **********

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 62 END OF RUN

2020 MOBILE6.2 Output File (OH.RPT)

*************************************************** ************************ * MOBILE6.2.03 (24-Sep-2003) * * Input file: OHSCN.IN (file 3, run 1). *

*************************************************** ************************

* Reading Hourly VMT distribution from the followin g external
* data file: OHHVMT.D

* Reading Hourly, Roadway, and Speed VMT dist. from the following external
* data file: OHSVMT.D

* Reading Hourly Roadway VMT distribution from the following external
* data file: OHFVMT.D

Reading User Supplied ROADWAY VMT Factors

* Reading Registration Distributions from the follo wing external
* data file: OHREG.D
M616 Comment: User has supplied post-1999 sulfur l evels.
M601 Comment:
User has enabled STAGE II REFUELING.

* # # # # # # # # # # # # # # # # # # # # # # # # # * Ohio Emissions - CY20xx * File 3, Run 1, Scenario 1.
* # # # # # # # # # # # # # # # # # # # # # # # # #

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

* Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12

HDDV DEFEAT DEVICE EFFECTS ARE PRESENT. THE REBUIL D FRACTION IS 0.10. M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2020 Month: July Altitude: Low Minimum Temperature: 62.0 (F) Maximum Temperature: 91.3 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 7.8 psi Weathered RVP: 8.0 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Ether Blend Market Share: 0.000 Alcohol Bl end Market Share: 0.420 Ether Blend Oxygen Content: 0.000 Alcohol Bl end Oxygen Content: 0.036
Alcohol B lend RVP Waiver: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.2697 0.4367 0.1632 0.0361 0.0002 0.0024 0.0866 0.0051 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.406 0.411 0.498 0.435 0.483 0.071 0.150 0.311 2.74 0.429 Composite CO : 6.26 6.92 7.62 7.11 8.96 0.738 0.426 0.572 18.16 6.420 Composite NOX : 0.282 0.365 0.489 0.399 0.586 0.066 0.188 1.946 1.22 0.512

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 1.010 0.275 0.449 Composite CO : 16.27 0.806 1.044 Composite NOX : 2.141 2.876 4.709

--------------------------------------------------- --------------------------------------------------- ----------------

* # # # # # # # # # # # # # # # # # # # # # # # # # * Ohio Emissions - CY20xx * File 3, Run 1, Scenario 2.
* # # # # # # # # # # # # # # # # # # # # # # # # #

* Reading PM Gas Carbon ZML Levels
* from the external data file PMGZML.CSV

* Reading PM Gas Carbon DR1 Levels
* from the external data file PMGDR1.CSV

* Reading PM Gas Carbon DR2 Levels
* from the external data file PMGDR2.CSV

* Reading PM Diesel Zero Mile Levels
* from the external data file PMDZML.CSV

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 63 * Reading the First PM Deterioration Rates
* from the external data file PMDDR1.CSV

* Reading the Second PM Deterioration Rates
* from the external data file PMDDR2.CSV M 48 Warning:
there are no sales for vehicle class HDGV8b M 48 Warning:
there are no sales for vehicle class LDDT12 M111 Warning: The input dIesel sulfur level of 43 .0 ppm exceeds the 2007 HDD Rule diesel sulfur limi t of 15 ppm.

Calendar Year: 2020 Month: July Altitude: Low Minimum Temperature: 47.0 (F) Maximum Temperature: 64.0 (F) Absolute Humidity: 75. grains/lb Nominal Fuel RVP: 9.0 psi Weathered RVP: 9.5 psi Fuel Sulfur Content: 30. ppm

Exhaust I/M Program: No Evap I/M Program: No
ATP Program: No
Reformulated Gas: No

Ether Blend Market Share: 0.000 Alcohol Bl end Market Share: 0.420 Ether Blend Oxygen Content: 0.000 Alcohol Bl end Oxygen Content: 0.036
Alcohol B lend RVP Waiver: Yes

Vehicle Type: LDGV LDGT12 LDGT34 LDGT HDGV LDDV LDDT HDDV MC All Veh
GVWR: <6000 >6000 (All)

------ ------ ------ ------ ------ ------ ------ ------ ------ ------ VMT Distribution: 0.2697 0.4367 0.1632 0.0361 0.0002 0.0024 0.0866 0.0051 1.0000

------------------------------------------------- --------------------------------------------------- ------------------ Composite Emission Factors (g/mi): Composite VOC : 0.401 0.431 0.523 0.456 0.439 0.071 0.150 0.311 2.22 0.436 Composite CO : 9.45 9.73 10.46 9.93 9.83 0.738 0.426 0.572 16.22 8.991 Composite NOX : 0.271 0.378 0.506 0.413 0.589 0.066 0.188 1.946 1.41 0.518

------------------------------------------------- --------------------------------------------------- ------------------ Veh. Type: GasBUS URBAN SCHOOL

------ ------ ------ VMT Mix: 0.0001 0.0010 0.0019

--------------------------------------------------- --------------------------------------------------- ---------------- Composite Emission Factors (g/mi): Composite VOC : 0.939 0.275 0.449 Composite CO : 17.83 0.806 1.044 Composite NOX : 2.152 2.876 4.709

--------------------------------------------------- --------------------------------------------------- ----------------

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 64

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 65 

# APPENDIX D

Air Quality Impact Summary for the OKI Portion of t he Nonattainment Area and Emissions by State/County

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 66

2005 Output Report (R7803)

DAILY AIR QUALITY IMPACT FOR OK I REGION SUMMARY 10-OCT-08

County or Network Network Vehicle VOC CO NOX PM Summer Township Road Miles Lane Miles Miles (Tons/Day) (Tons/Day) (Tons/Day) (Tons/Day) VMT

=================================================== =================================================== ============== Boone County 233.66 613.11 3900873. 4.304 46.921 10.214 0.176 4162762. Butler County 580.75 1441.60 7421978. 9.898 102.823 18.802 0.332 7774168. Campbell County 198.42 509.82 2276611. 2.511 27.384 5.958 0.103 2428092. Clermont County 427.95 983.82 5051723. 6.824 69.986 12.963 0.226 5359970. Dearborn County 147.07 348.94 1323712. 2.360 20.456 3.399 0.060 1412377. Hamilton County 1061.67 3076.64 21783578. 29.404 301.786 55.854 0.975 23094892. Kenton County 239.03 592.36 3908394. 4.304 47.012 10.214 0.176 4162693. Warren County 397.32 979.42 5853879. 7.935 81.099 15.074 0.262 6232673. Montgomery Cnty 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Greene County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Miami County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Clark County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Preble County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Clinton County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Lawrenceburg Twp 25.15 69.78 575202. 0.997 8.889 1.435 0.026 596322.

State

=================================================== =================================================== ============== IN Not AQ Region 147.07 348.94 1323712. 2.360 20.456 3.399 0.060 1412377. KY - OKI Only 671.11 1715.29 10085878. 11.119 121.317 26.386 0.455 10753546. OH - OKI Only 2467.69 6481.48 40111160. 54.061 555.693 102.692 1.795 42461700. OH - MVRPC Only 0.00 0.00 0. 0.000 0.000 0.000 0.000 0.
OH - Other 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. IN NonAttainment 25.15 69.78 575202. 0.997 8.889 1.435 0.026 596322.

=================================================== =================================================== ============== Region 3311.01 8615.49 52095952. 68.536 706.355 133.912 2.335 55223952. OKI OH+IN AQ Reg 2492.84 6551.26 40686360. 55.057 564.582 104.127 1.821 43058024.

Intra-Zonal VMT

=================================================== =================================================== ============== Boone County 23244. 0.024 0.280 0.057 0.001 Butler County 30308. 0.039 0.420 0.073 0.001 Campbell County 9606. 0.010 0.116 0.024 0.000 Clermont County 31608. 0.040 0.438 0.076 0.001 Dearborn County 16428. 0.027 0.254 0.040 0.001 Hamilton County 46049. 0.059 0.638 0.111 0.002 Kenton County 11183. 0.012 0.135 0.027 0.001 Warren County 30337. 0.039 0.420 0.073 0.001 Montgomery Cnty 0. 0.000 0.000 0.000 0.000 Greene County 0. 0.000 0.000 0.000 0.000 Miami County 0. 0.000 0.000 0.000 0.000 Clark County 0. 0.000 0.000 0.000 0.000 Preble County 0. 0.000 0.000 0.000 0.000 Clinton County 0. 0.000 0.000 0.000 0.000 Lawrenceburg Twp 3439. 0.004 0.048 0.008 0.000

=================================================== =================================================== ============== Total Intra-Zonal 202202. 0.253 2.747 0.490 0.009 OKI OH+IN AQ Region IZ 141741. 0.180 1.964 0.343 0.006

* Note: VMT reflects yearly average daily VMT. Emis sions for CO are based on yearly average daily VMT.
Emissions for VOC and NOX include a factor to represent summer travel.

Transit VMT

=================================================== =================================================== ============== IN Not AQ Region 0. 0.000 0.000 0.000 0.000 KY - OKI Only 8166. 0.005 0.040 0.148 0.005 OH - OKI Only 29825. 0.009 0.149 0.544 0.019 OH - MVRPC Only 0. 0.000 0.000 0.000 0.000
OH - Other 0. 0.000 0.000 0.000 0.000 IN NonAttainment 0. 0.000 0.000 0.000 0.000

=================================================== =================================================== ============== Total Transit 37992. 0.014 0.190 0.692 0.024 OKI OH+IN AQ Region 29825. 0.009 0.149 0.544 0.019

=================================================== =================================================== ==============

Grand Totals

=================================================== =================================================== ============== IN Not AQ Region 1340140. 2.388 20.710 3.438 0.060 KY - OKI Only 10138077. 11.170 121.887 26.643 0.462 OH - OKI Only 40279288. 54.246 557.758 103.571 1.820 OH - MVRPC Only 0. 0.000 0.000 0.000 0.000
OH - Other 0. 0.000 0.000 0.000 0.000
IN NonAttainment 578641. 1.001 8.936 1.443 0.026

=================================================== =================================================== ============== Grand Total 52133944. 68.550 706.544 134.604 2.360 OKI OH+IN AQ Region 40857928. 55.247 566.695 105.014 1.846

=================================================== =================================================== ==============

=================================================== =================================================== ============== * Note: VMT reflects yearly average daily VMT. Emis sions for CO are based on yearly average daily VMT.
Emissions for VOC and NOX include a factor to represent summer travel.

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 67

2008 Output Report (R7803)

DAILY AIR QUALITY IMPACT FOR OK I REGION SUMMARY 30-SEP-09

County or Network Network Vehicle VOC CO NOX PM Summer Township Road Miles Lane Miles Miles (Tons/Day) (Tons/Day) (Tons/Day) (Tons/Day) VMT

=================================================== =================================================== ============== Boone County 236.45 639.31 4051620. 3.981 44.192 8.478 0.138 4330563. Butler County 567.07 1473.35 7714861. 7.842 84.234 15.988 0.260 8102730. Campbell County 191.02 506.98 2329601. 2.285 25.410 4.865 0.079 2485233. Clermont County 416.74 972.04 5230069. 5.388 57.104 10.985 0.176 5567110. Dearborn County 144.53 342.91 1334278. 1.749 15.804 2.655 0.045 1423366. Hamilton County 1019.54 3042.53 22044516. 22.649 240.691 46.174 0.744 23401434. Kenton County 223.19 587.32 3904860. 3.838 42.592 8.173 0.133 4174555. Warren County 387.13 987.90 6025856. 6.226 65.793 12.693 0.203 6432735. Montgomery Cnty 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Greene County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Miami County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Clark County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Preble County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Clinton County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Lawrenceburg Twp 24.16 68.73 584186. 0.749 6.919 1.137 0.020 609631.

State

=================================================== =================================================== ============== IN Not AQ Region 144.53 342.91 1334278. 1.749 15.804 2.655 0.045 1423366. KY - OKI Only 650.65 1733.61 10286081. 10.104 112.194 21.516 0.349 10990352. OH - OKI Only 2390.48 6475.82 41015308. 42.104 447.821 85.839 1.383 43504008. OH - MVRPC Only 0.00 0.00 0. 0.000 0.000 0.000 0.000 0.
OH - Other 0.00 0.00 0. 0.000 0.000 0.000 0.000 0.
IN NonAttainment 24.16 68.73 584186. 0.749 6.919 1.137 0.020 609631.

=================================================== =================================================== ============== Region 3209.81 8621.07 53219848. 54.707 582.738 111.147 1.798 56527368. OKI OH+IN AQ Reg 2414.64 6544.55 41599492. 42.854 454.740 86.976 1.403 44113640.

Intra-Zonal VMT

=================================================== =================================================== ============== Boone County 24964. 0.023 0.272 0.049 0.001 Butler County 30824. 0.030 0.337 0.061 0.001 Campbell County 9941. 0.009 0.108 0.019 0.000 Clermont County 32420. 0.031 0.354 0.064 0.001 Dearborn County 16853. 0.021 0.200 0.031 0.001 Hamilton County 46026. 0.045 0.503 0.091 0.002 Kenton County 11097. 0.010 0.121 0.022 0.000 Warren County 31482. 0.030 0.344 0.062 0.001 Montgomery Cnty 0. 0.000 0.000 0.000 0.000 Greene County 0. 0.000 0.000 0.000 0.000 Miami County 0. 0.000 0.000 0.000 0.000 Clark County 0. 0.000 0.000 0.000 0.000 Preble County 0. 0.000 0.000 0.000 0.000 Clinton County 0. 0.000 0.000 0.000 0.000 Lawrenceburg Twp 3396. 0.003 0.037 0.007 0.000

=================================================== =================================================== ============== Total Intra-Zonal 207003. 0.203 2.275 0.406 0.007 OKI OH+IN AQ Region IZ 144148. 0.140 1.574 0.284 0.005

* Note: VMT reflects yearly average daily VMT. Emis sions for CO are based on yearly average daily VMT.
Emissions for VOC and NOX include a factor to represent summer travel.

Transit VMT

=================================================== =================================================== ============== IN Not AQ Region 0. 0.000 0.000 0.000 0.000 KY - OKI Only 11375. 0.005 0.045 0.176 0.004 OH - OKI Only 33961. 0.007 0.141 0.531 0.011 OH - MVRPC Only 0. 0.000 0.000 0.000 0.000
OH - Other 0. 0.000 0.000 0.000 0.000
IN NonAttainment 0. 0.000 0.000 0.000 0.000

=================================================== =================================================== ============== Total Transit 45336. 0.011 0.186 0.708 0.014 OKI OH+IN AQ Region 33961. 0.007 0.141 0.531 0.011

=================================================== =================================================== ==============

Grand Totals

=================================================== =================================================== ============== IN Not AQ Region 1351131. 1.770 16.003 2.686 0.046 KY - OKI Only 10343458. 10.151 112.741 21.782 0.354 OH - OKI Only 41190020. 42.247 449.499 86.648 1.399 OH - MVRPC Only 0. 0.000 0.000 0.000 0.000
OH - Other 0. 0.000 0.000 0.000 0.000
IN NonAttainment 587582. 0.753 6.956 1.144 0.020

=================================================== =================================================== ============== Grand Total 53265184. 54.718 582.924 111.855 1.812 OKI OH+IN AQ Region 41777604. 43.000 456.455 87.792 1.419

=================================================== =================================================== ==============

=================================================== =================================================== ============== * Note: VMT reflects yearly average daily VMT. Emis sions for CO are based on yearly average daily VMT.
Emissions for VOC and NOX include a factor to represent summer travel.

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 68

2015 Output Report (R7803)

DAILY AIR QUALITY IMPACT FOR OK I REGION SUMMARY 15-SEP-09

County or Network Network Vehicle VOC CO NOX PM Summer Township Road Miles Lane Miles Miles (Tons/Day) (Tons/Day) (Tons/Day) (Tons/Day) VMT

=================================================== =================================================== ============== Boone County 243.53 743.15 4798837. 3.152 37.193 4.609 0.092 5105800. Butler County 586.21 1539.89 8425674. 4.851 64.243 7.520 0.160 8836953. Campbell County 197.16 550.67 2620037. 1.728 20.306 2.527 0.050 2798785. Clermont County 424.04 989.87 5618901. 3.272 42.842 5.072 0.107 5960298. Dearborn County 152.37 367.83 1488387. 1.177 12.543 1.408 0.028 1588928. Hamilton County 1041.80 3193.63 23005940. 13.411 175.413 20.789 0.436 24429772. Kenton County 232.28 631.62 4330736. 2.841 33.565 4.154 0.083 4601830. Warren County 393.28 1024.31 6849283. 4.000 52.224 6.201 0.130 7286355. Montgomery Cnty 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Greene County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Miami County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Clark County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Preble County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Clinton County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Lawrenceburg Twp 24.82 70.88 644037. 0.496 5.427 0.594 0.012 670198.

State

=================================================== =================================================== ============== IN Not AQ Region 152.37 367.83 1488387. 1.177 12.543 1.408 0.028 1588928. KY - OKI Only 672.96 1925.44 11749610. 7.720 91.063 11.291 0.224 12506415. OH - OKI Only 2445.33 6747.70 43899792. 25.534 334.722 39.582 0.832 46513372. OH - MVRPC Only 0.00 0.00 0. 0.000 0.000 0.000 0.000 0.
OH - Other 0.00 0.00 0. 0.000 0.000 0.000 0.000 0.
IN NonAttainment 24.82 70.88 644037. 0.496 5.427 0.594 0.012 670198.

=================================================== =================================================== ============== Region 3295.48 9111.85 57781832. 34.927 443.756 52.875 1.097 61278912. OKI OH+IN AQ Reg 2470.15 6818.58 44543828. 26.030 340.149 40.176 0.845 47183568.

Intra-Zonal VMT

=================================================== =================================================== ============== Boone County 27656. 0.017 0.214 0.025 0.001 Butler County 32853. 0.018 0.250 0.028 0.001 Campbell County 11141. 0.007 0.086 0.010 0.000 Clermont County 35240. 0.019 0.269 0.030 0.001 Dearborn County 18309. 0.014 0.154 0.016 0.000 Hamilton County 46800. 0.026 0.357 0.040 0.001 Kenton County 12048. 0.007 0.093 0.011 0.000 Warren County 37749. 0.021 0.288 0.032 0.001 Montgomery Cnty 0. 0.000 0.000 0.000 0.000 Greene County 0. 0.000 0.000 0.000 0.000 Miami County 0. 0.000 0.000 0.000 0.000 Clark County 0. 0.000 0.000 0.000 0.000 Preble County 0. 0.000 0.000 0.000 0.000 Clinton County 0. 0.000 0.000 0.000 0.000 Lawrenceburg Twp 3434. 0.002 0.026 0.003 0.000

=================================================== =================================================== ============== Total Intra-Zonal 225230. 0.131 1.738 0.195 0.004 OKI OH+IN AQ Region IZ 156076. 0.086 1.190 0.133 0.003

* Note: VMT reflects yearly average daily VMT. Emis sions for CO are based on yearly average daily VMT.
Emissions for VOC and NOX include a factor to represent summer travel.

Transit VMT

=================================================== =================================================== ============== IN Not AQ Region 0. 0.000 0.000 0.000 0.000 KY - OKI Only 9160. 0.003 0.019 0.067 0.001 OH - OKI Only 39966. 0.006 0.075 0.285 0.004 OH - MVRPC Only 0. 0.000 0.000 0.000 0.000
OH - Other 0. 0.000 0.000 0.000 0.000
IN NonAttainment 0. 0.000 0.000 0.000 0.000

=================================================== =================================================== ============== Total Transit 49127. 0.009 0.094 0.352 0.005 OKI OH+IN AQ Region 39966. 0.006 0.075 0.285 0.004

=================================================== =================================================== ==============

Grand Totals

=================================================== =================================================== ============== IN Not AQ Region 1506696. 1.191 12.697 1.424 0.029 KY - OKI Only 11809615. 7.755 91.476 11.404 0.226 OH - OKI Only 44092400. 25.623 335.960 39.997 0.839 OH - MVRPC Only 0. 0.000 0.000 0.000 0.000
OH - Other 0. 0.000 0.000 0.000 0.000 IN NonAttainment 647471. 0.498 5.454 0.597 0.012

=================================================== =================================================== ============== Grand Total 57830960. 34.936 443.849 53.227 1.102 OKI OH+IN AQ Region 44739872. 26.122 341.414 40.594 0.852

=================================================== =================================================== ==============

=================================================== =================================================== ============== * Note: VMT reflects yearly average daily VMT. Emis sions for CO are based on yearly average daily VMT.
Emissions for VOC and NOX include a factor to represent summer travel.

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 69

2020 Output Report (R7803)

DAILY AIR QUALITY IMPACT FOR OK I REGION SUMMARY 16-SEP-09

County or Network Network Vehicle VOC CO NOX PM Summer Township Road Miles Lane Miles Miles (Tons/Day) (Tons/Day) (Tons/Day) (Tons/Day) VMT

=================================================== =================================================== ============== Boone County 243.53 743.15 5412408. 2.945 37.981 3.434 0.085 5757894. Butler County 586.21 1539.89 9042376. 4.486 63.991 5.354 0.143 9485722. Campbell County 197.16 550.67 2833751. 1.548 19.885 1.805 0.045 3027410. Clermont County 424.04 989.87 6030235. 3.025 42.675 3.611 0.095 6397591. Dearborn County 152.37 367.83 1640862. 1.026 12.473 1.031 0.026 1752277. Hamilton County 1041.80 3193.63 23837298. 11.974 168.692 14.290 0.376 25320182. Kenton County 232.28 631.62 4683779. 2.545 32.868 2.967 0.074 4976098. Warren County 393.28 1024.31 7672745. 3.862 54.299 4.609 0.121 8165845. Montgomery Cnty 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Greene County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Miami County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Clark County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Preble County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Clinton County 0.00 0.00 0. 0.000 0.000 0.000 0.000 0. Lawrenceburg Twp 24.82 70.88 683890. 0.417 5.199 0.419 0.011 712313.

State

=================================================== =================================================== ============== IN Not AQ Region 152.37 367.83 1640862. 1.026 12.473 1.031 0.026 1752277. KY - OKI Only 672.96 1925.44 12929937. 7.039 90.733 8.207 0.204 13761400. OH - OKI Only 2445.33 6747.70 46582656. 23.346 329.658 27.863 0.734 49369340. OH - MVRPC Only 0.00 0.00 0. 0.000 0.000 0.000 0.000 0.
OH - Other 0.00 0.00 0. 0.000 0.000 0.000 0.000 0.
IN NonAttainment 24.82 70.88 683890. 0.417 5.199 0.419 0.011 712313.

=================================================== =================================================== ============== Region 3295.48 9111.85 61837348. 31.827 438.063 37.521 0.975 65595328. OKI OH+IN AQ Reg 2470.15 6818.58 47266544. 23.763 334.856 28.283 0.745 50081652.

Intra-Zonal VMT

=================================================== =================================================== ============== Boone County 32337. 0.017 0.227 0.019 0.001 Butler County 35277. 0.017 0.250 0.020 0.001 Campbell County 11864. 0.006 0.083 0.007 0.000 Clermont County 36963. 0.017 0.262 0.021 0.001 Dearborn County 19281. 0.011 0.147 0.011 0.000 Hamilton County 47824. 0.023 0.338 0.027 0.001 Kenton County 12926. 0.007 0.091 0.008 0.000 Warren County 43391. 0.021 0.307 0.024 0.001 Montgomery Cnty 0. 0.000 0.000 0.000 0.000 Greene County 0. 0.000 0.000 0.000 0.000 Miami County 0. 0.000 0.000 0.000 0.000 Clark County 0. 0.000 0.000 0.000 0.000 Preble County 0. 0.000 0.000 0.000 0.000 Clinton County 0. 0.000 0.000 0.000 0.000 Lawrenceburg Twp 3610. 0.002 0.026 0.002 0.000

=================================================== =================================================== ============== Total Intra-Zonal 243473. 0.120 1.730 0.140 0.004 OKI OH+IN AQ Region IZ 167065. 0.079 1.182 0.094 0.003

* Note: VMT reflects yearly average daily VMT. Emis sions for CO are based on yearly average daily VMT.
Emissions for VOC and NOX include a factor to represent summer travel.

Transit VMT

=================================================== =================================================== ============== IN Not AQ Region 0. 0.000 0.000 0.000 0.000 KY - OKI Only 9160. 0.003 0.009 0.030 0.000 OH - OKI Only 39966. 0.006 0.036 0.127 0.002 OH - MVRPC Only 0. 0.000 0.000 0.000 0.000
OH - Other 0. 0.000 0.000 0.000 0.000
IN NonAttainment 0. 0.000 0.000 0.000 0.000

=================================================== =================================================== ============== Total Transit 49127. 0.009 0.045 0.157 0.003 OKI OH+IN AQ Region 39966. 0.006 0.036 0.127 0.002

=================================================== =================================================== ==============

Grand Totals

=================================================== =================================================== ============== IN Not AQ Region 1660143. 1.037 12.620 1.043 0.026 KY - OKI Only 12996224. 7.071 91.144 8.271 0.205 OH - OKI Only 46786076. 23.429 330.850 28.082 0.739 OH - MVRPC Only 0. 0.000 0.000 0.000 0.000
OH - Other 0. 0.000 0.000 0.000 0.000 IN NonAttainment 687500. 0.419 5.224 0.421 0.011

=================================================== =================================================== ============== Grand Total 61886476. 31.836 438.107 37.677 0.977 OKI OH+IN AQ Region 47473576. 23.848 336.074 28.504 0.750

=================================================== =================================================== ==============

=================================================== =================================================== ============== * Note: VMT reflects yearly average daily VMT. Emis sions for CO are based on yearly average daily VMT.
Emissions for VOC and NOX include a factor to represent summer travel.

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 70

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 71 Appendix E Clinton County Air Quality Analyis (provided by ODO T)

Clinton County OZONE YEAR 2005

VOC NOX

FUNCTIONAL HPMS ANNUAL 2005 POLLUTANT 2005 POLLUTANT

CLASSIFICATION 2005 GROWTH 2005 VOC EF BURDEN NOX E F BURDEN

VMT FACTOR VMT GM/MI TONS/DAY GM/MI TONS/DAY

RURAL
0 1 INTERSTATE 554,300 1.000 554,300 1.418 0.865 3.15 6 1.924 0
2 PRINCIPAL ARTERIAL 0 1.000 0 1.461 0.000 2.452 0.000
0 6 MINOR ARTERIAL 322,000 1.000 322,000 1.461 0.517 2.452 0.868 0 7 MAJOR ARTERIAL 339,140 1.000 339,140 1.552 0.579 2.223 0.829 0 8 MINOR COLLECTOR 5,400 1.000 5,400 1.552 0.009 2.223 0.013
0 9 LOCAL 393,470 1.000 393,470 1.552 0.672 2.223 0.9 62

URBAN
1 1 INTERSTATE 0 1.000 0 1.418 0.000 3.156 0.000
1
2 FREEWAY/EXPRE SSWAY 0 1.000 0 1.418 0.000 3.156 0.000
1
4 PRINCIPAL ARTERIAL 140,870 1.000 140,870 1.753 0.272 2.174 0. 337
1 6 MINOR ARTERIAL 21,980 1.000 21,980 1.753 0.042 2. 174 0.053
1 7 COLLECTOR 23,940 1.000 23,940 1.753 0.046 2.175 0 .057
1 9 LOCAL 8,500 1.000 8,500 1.753 0.016 2.269 0.021

2005 TOTAL 1,809,6 00 1,809,6 00 3.019 5.065

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 72 Clinton County OZONE YEAR 2008

VOC NOX

FUNCTIONAL HPMS ANNUAL 2008 POLLUTANT 2008 POLLUTANT

CLASSIFICATION 2008 GROWTH 2008 VOC EF BURDEN NOX E F BURDEN

VMT FACTOR VMT GM/MI TONS/DAY GM/MI TONS/DAY

RURAL 0 1 INTERSTATE 553,330 1.000 553,330 1.108 0.674 2.41 4 1.469 0
2 PRINCIPAL ARTERIAL 0 1.000 0 1.139 0.000 1.899 0.000 0 6 MINOR ARTERIAL 314,550 1.000 314,550 1.139 0.394 1.899 0.657 0 7 MAJOR ARTERIAL 360,620 1.000 360,620 1.204 0.478 1.721 0.683 0 8 MINOR COLLECTOR 5,200 1.000 5,200 1.204 0.007 1.721 0.010
0 9 LOCAL 369,170 1.000 369,170 1.204 0.489 1.721 0.6 99

URBAN
1 1 INTERSTATE 0 1.000 0 1.108 0.000 2.414 0.000
1
2 FREEWAY/EXPRE SSWAY 0 1.000 0 1.108 0.000 2.414 0.000
1
4 PRINCIPAL ARTERIAL 134,360 1.000 134,360 1.349 0.199 1.682 0. 249
1 6 MINOR ARTERIAL 22,620 1.000 22,620 1.349 0.034 1. 682 0.042
1 7 COLLECTOR 25,240 1.000 25,240 1.350 0.037 1.684 0 .047
1 9 LOCAL 8,490 1.000 8,490 1.450 0.014 1.757 0.016

2005 TOTAL 1,793,5 80 1,793,5 80 2.326 3.871

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 73 Clinton County OZONE YEAR 2015

VOC NOX

FUNCTIONAL HPMS ANNUAL 2015 POLLUTANT 2015 POLLUTANT

CLASSIFICATION 2008 GROWTH 2015 VOC EF BURDEN NOX E F BURDEN

VMT FACTOR VMT GM/MI TONS/DAY GM/MI TONS/DAY

RURAL
0 1 INTERSTATE 553,330 1.014 607,786 0.622 0.416 1.07 2 0.717 0
2 PRINCIPAL ARTERIAL* 0 1.013 104,288 0.632 0.073 0.873 0.100
0 6 MINOR ARTERIAL 314,550 1.008 331,901 0.632 0.231 0.873 0.319 0 7 MAJOR ARTERIAL 360,620 1.014 396,110 0.662 0.288 0.799 0.348 0 8 MINOR COLLECTOR 5,200 1.009 5,540 0.662 0.004 0.799 0.005
0 9 LOCAL 369,170 1.012 401,319 0.662 0.292 0.799 0.3 53

URBAN
1 1 INTERSTATE 0 0.000 0 0.622 0.000 1.072 0.000
1
2 FREEWAY/EXPRE SSWAY 0 0.000 0 0.622 0.000 1.072 0.000
1
4 PRINCIPAL ARTERIAL 134,360 1.008 142,462 0.735 0.115 0.784 0. 123
1 6 MINOR ARTERIAL 22,620 1.010 24,201 0.735 0.020 0. 784 0.021
1 7 COLLECTOR 25,240 1.009 26,874 0.735 0.022 0.785 0 .023
1 9 LOCAL 8,490 1.009 9,014 0.789 0.008 0.819 0.008

2005 TOTAL 1,793,5 80 2,049,4 96 1.468 2.016

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 74 Clinton County OZONE YEAR 2020

VOC NOX

FUNCTIONAL HPMS ANNUAL 2020 POLLUTANT 2020 POLLUTANT

CLASSIFICATION 2008 GROWTH 2020 VOC EF BURDEN NOX E F BURDEN

VMT FACTOR VMT GM/MI TONS/DAY GM/MI TONS/DAY

RURAL
0 1 INTERSTATE 553,330 1.014 649,934 0.486 0.347 0.68 7 0.491 0
2 PRINCIPAL ARTERIAL* 0 1.013 111,269 0.493 0.060 0.578 0.071
0 6 MINOR ARTERIAL 314,550 1.008 344,877 0.493 0.187 0.578 0.219 0 7 MAJOR ARTERIAL 360,620 1.014 423,579 0.517 0.241 0.535 0.249 0 8 MINOR COLLECTOR 5,200 1.009 5,797 0.517 0.003 0.535 0.003
0 9 LOCAL 369,170 1.012 425,983 0.517 0.242 0.535 0.2 51

URBAN
1 1 INTERSTATE 0 0.000 0 0.486 0.000 0.687 0.000
1
2 FREEWAY/EXPRE SSWAY 0 0.000 0 0.486 0.000 0.687 0.000
1
4 PRINCIPAL ARTERIAL 134,360 1.008 148,547 0.577 0.094 0.527 0. 086
1 6 MINOR ARTERIAL 22,620 1.010 25,398 0.577 0.016 0. 527 0.015
1 7 COLLECTOR 25,240 1.009 28,105 0.578 0.018 0.528 0 .016
1 9 LOCAL 8,490 1.009 9,409 0.622 0.006 0.551 0.006

2005 TOTAL 1,793,5 80 2,172,8 99 1.216 1.407



## *VMT due to new facilities estimated with the Ohio Statewide Travel Demand Model

### Mobile Source Emissions Inventory for the Cincinnat i 8-hour Ozone Nonattainment Area 

## , October 2009 

# 75

# APPENDIX G

Indiana Department of Environmental Management (IDEM) – Area Source Inventory Standard Operating Procedure

# This page left intentionally blank.

# Area Source Inventory
S-006-OAQ-R-MO-08-S-R1 

# Standard Operating Procedure

Office: Office of Air Quality Branch: Air Programs Branch Section: Technical Support and Modeling Section

Revised: 02/27/2008 Revision Cycle: 2 years Effective date: 02/15/07

Scope of operations This SOP is to identify source categories and develop emissions not calculated in point source inventories. This data is compiled ev ery three years as mandated by EPA.

Scope of applicability This SOP is for the Senior Environmental Manager and the Environmental Manager in the Emissions Group.



# Authorized Signatures I approve and authorize this Standard Operating Procedure:

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



# Table of Contents Scope of operations ....................................................................................................................................1 Scope of applicability .................................................................................................................................1 Authorized Signatures

............................................................................................................................... .1 1. Overview work flow chart .......................................................................................................................3 2. Definitions ................................................................................................................................................3 3. Roles .........................................................................................................................................................4 Responsibilities: .........................................................................................................................................4 4. Description of equipment, forms, and/or software to be used ...........................................................4 5. Procedure ................................................................................................................................................4 5.1 Procedural Flowchart ....................................................................................................................4 5.2 Procedure .......................................................................................................................................5 6. Standards and checklists .....................................................................................................................24 7. Records Management ...........................................................................................................................24 8. Quality Assurance / Quality Control ...................................................................................................25 9. Continuous Improvement Cycle ..........................................................................................................25 10. References

............................................................................................................................... ............25 11. History of Revisions ...........................................................................................................................25 12. Appendices

............................................................................................................................... ...........25

2

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



# 1. Overview work flow chart The process described is not part of a larger syst em and does not need an Overview work flow chart.



# 2. Definitions

AP-42 – Compilation of Air Pollutant Emission Factors AP- 42, Fifth Edition, Volume I: Stationary Point and Area Sources (January 1995) plus Supplements A – F (Updates 2001 – 2004). AP-42 can be obtained at www.epa.gov/ttn/chief/ap42/

.

Area Sources

- A collection of similar emission units within a geographic area that collectively represent individual sources that are small and numerous and ha ve not been inventoried as a specific point, mobile, or biogenic source.

Authorized - Established by official authority and usage; as with a policy, standard operating procedure (SOP), or quality assurance project pl an (QAPP) that is signed and dated.

EIIP (Emission Inventory Improvement Program) - The EIIP is an EPA program established in 1993 to promote the development and use of standard procedures for collecting, calculati ng, storing, reporting, and sharing air emissions date.

Emission Factors - An emission factor is the estimate of the quantity of pollutant released to the atmosphere (because of some operation or activity such as combustion or industrial production) divided by the level of that activity.

Process

- The term “process” used when describing area sources is used to name an operation or activity that produces emissions.

NEI - National Emission Inventory Air Pollutant Emission Trends, U.S. EPA.

Standard Industrial Classification (SIC) Code

- A Standard Industrial Classification code from the series of codes devised by the United States O ffice of Management and Budget (OMB) to classify establishments according to the type of economic activity in which they engage.

Source Classification Code (SCC)

- Source Classification Code is a process-level code that describes the equipment or operation emitting pollutants.

3

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



# 3. Roles

Title # of Staff Experience Qualifications Location

Senior Environmental Manager 1 N/A MS ACCESS, Emission Inventories and familiarity with the EIIP Air Programs Branch

Environmental Manager 1 N/A MS ACCESS, Emission Inventories and familiarity with the EIIP Air Programs Branch



## Responsibilities:

Senior Environmental Manager Oversees work of the Environmental Manager and ensures that all goals are met. The Senior Environmental Manager also does the final upload to the NEI.

Environmental Manager The Environmental Manager calculates the Area Source Emissions using the EIIP or other EPA guidance as provided. The Environmental Manager is also responsible for updating the SOP for the Emissions Group.



# 4. Description of equipment, forms, and/or software to be used

Equipment, Form, &/or Software Who uses it? Location

AP42 Senior Environmental Manager and Environmental Manager EPA’s website: http://www.epa.gov/ttn/chief/ap42/index. html

Emission Inventory Improvement Program (EIIP) Senior Environmental Manager and Environmental Manager EPA’s website: http://www.epa.gov/ttn/chief/eiip/techrep ort/

National Emission Inventory (NEI) Air Pollutant Emission Trends, U.S. EPA Senior Environmental Manager and Environmental Manager EPA’s website http://www.epa.gov/ttn/chief/trends/



# 5. Procedure

5.1 Procedural Flowchart The procedural flowchart below titled “Area Source Inventory” is us ed to calculate non-point source inventories. This data is compiled every three years as mandated by EPA. The guidance followed is located in the EIIP. Emissions from area source s are calculated at the county level and consist of individual sources that are small, numerous and that have not been inventoried as specific point, mobile, or biogenic sources according to the EIIP.

YES

NO Identify Categories Is the categor y an Area
Source?

Then calculate emissions using the SOP for Receiving Emission Statements or the SOP

for On-Road Mobile Source Inventory Calculate Area Source categories using the
EIIP or other EPA guidance as provided Enter data into
NEI



## 4

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## 5.2 Procedure 

# Category 1: Stationary Fuel Combustion

Sub-Category 1.1: Industrial Fuel Combustion

SCC: 2102002000, 210200400, 2102005000, 2102006000, 2102007000

Follow these steps when calculating emissions from industrial fuel combustion:

1. Obtain statewide fuel consumption for “Other Indu strial” for the following f uels: coal, distillate oil, natural gas, and liquefied petroleum gas (LPG). Us e the Energy Information Administration’s website
at http://www.eia.doe.gov/ to find fuel consumption.

Note: As of the date of this SOP, the followin g steps will lead to data for fuel consumption.

a. Go to http://www.eia.doe.gov/ b. Click on link for the various types of fuel consumption c. Click on consumption tab for state totals

2. To avoid double calculating the various fuel comb ustions, subtract reported source totals from the total statewide fuel consumption by querying the to tal process rates for the various SCC codes using the ACCESS data tables at K:\OAQ_INV\Steptool\Stp tl_02.mdb. The remaining number is the area source fuel consumpt ion for the state.

3. To distribute the remaining fuel to the county leve l, calculate the ratio of county to state employment for the manufacturing sector by dividing the numbe r of Manufacturing Employees for each county by the number of manufacturing employees statewide. Use the County Business Patterns website at http://www.census.gov/ to find the number of manufacturing employees for each county.

Note: As of the date of this SOP, the followin g steps will lead to data for Economic Census.

a. Go to http://www.census.gov/ b. Click on Economic Census c. Under 2002 Reports by State, use the down arrow key to select Indiana d. Now, select each of the counties to find the county manufacturing employees e. Use the total of employees for manuf acturing under the paid employees’ column

4. Multiply the ratio calculated above in step 3 by t he area source fuel consumpt ion to distribute the fuel to the county level. The remaining number is the pr ocess rate for each county. Multiply the process rate by the appropriate EPA emission factors for t he various fuels for industrial manufacturing found in AP-42, Fifth Edition, Volume 1, Chap ter 1, External Combustion Sources at http://www.epa.gov/ttn/chief/ap42/ch01/

.
Sub-Category 1.2: Commercial/ Institutional Fuel Combustion

SCC: 2103004000, 2103005000, 2103006000, 2103007000

Follow these steps when calculating emissions fr om commercial/institutional fuel combustion:

1. Obtain statewide fuel consumption for “Commercial” for the following fuels: distillate fuel oil, liquefied petroleum gas (LPG), natural gas, and residual fuel oil. Use the Energy Information Administration’s website at http://www.eia.doe.gov/ to find fuel consumption.

Note: Use the steps in sub-category 1.1-1 to navigate through the Energy Information Administration’s website.

5

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## 2. To avoid double calculating the various fuel comb ustions, subtract reported source totals from the total statewide fuel consumption by querying the to tal process rates for the various fuels using the SIC codes greater than 49 99 using the ACCESS data tables at K :\OAQ_INV\Steptool\Stptl_02.mdb. These are the SIC codes that identify all t he commercial/institutional area sources.

3. To distribute the remaining fuel to the county leve l, calculate the ratio of county to state employment for the commercial/institutional sector by dividi ng the number of commercial/ institutional employees for each county by the number of commercial/instit utional employees statewide. Use the County Business Patterns website at http://www.census.gov/ to find the number of commercial/institutional employees for each county.

Note: Use the steps in sub-category 1.1-3 to navi gate through the U.S. Census Bureau’s website.

4. Multiply the ratio calculated above in step 3 by t he area source fuel consumpt ion to distribute the fuel to the county level. The remaining number is the process rate for each county. Multiply the process rate by the appropriate EPA emission factors for t he various fuels for commercial/institutional found in AP-42, Fifth Edition, Volume 1, Chapter 1, External Combustion Sources at http://www.epa.gov/ttn/chief/ap42/ch01/

.

Sub-Category 1.3: Residential Fuel Combustion

SCC: 2104002000, 2104004000, 2104006000, 2104007000

Follow these steps when calculating emissions from residential fuel combustion:

1. Obtain statewide fuel consumpti on for “Residential” for the following fuels: coal, distillate oil, natural gas, and liquid petroleum gas. Use the Ener gy Information Administration’s website at http://www.eia.doe.gov/ to find fuel consumption.

Note: Use the steps in sub-category 1.1-1 to navigate through the Energy Information Administration’s website.

2. To distribute residential fuel to the county level, calculate the ratio of county fuel usage to statewide fuel usage using the breakdown of fuels by house hold per county divided by the breakdown of fuels by household per state using the U.S. Census Bureau’s website at http://www.census.gov/

.
Note: As of the date of this SOP, the following steps will lead to data for breakdown of fuels by household.

a. Go to http://www.census.gov/ b. On the left hand side click on “American Fact Finder” c. Using the drop down menu, click on Indiana d. Scroll to “Housing Characterist ics” and select “show more” e. On the left hand side, select “chan ge geography (state, county, place...)” f. Using the drop down menu, select county, state, and each county name to obtain housing

information

3. Multiply the ratio calculated abov e in step 3 by the area residential f uel use by state to distribute the fuel to the county level. The remaining number is the process rate for each county for the various fuels. Multiply the process rate by the approp riate EPA emission factors fo r the various fuels for residential found in AP-42, Fifth Edition, Volume 1, Chapter 1 External Combustion Sources at http://www.epa.gov/ttn/chief/ap42/ch01/

.

6

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## Sub-Category 1.4: Residential Heating Using Wood

SCC: 2104008001, 2104008002, 2104008003, 2104008004, 2104008010, 2104008030, 2104008050

Follow these steps when calculating emission s from residential heating using wood:

1. Obtain statewide wood consumption for “Residential” using the Energy Information Administration’s website at http://www.eia.doe.gov/ . To convert the statewide wood consumption from cords of wood consumed to tons, multiply the total cords consumed by 1.25.

Note: As of the date of this SOP, the followin g steps will lead to data for wood consumption.

a. Go to http://www.eia.doe.gov/ b. Click on Households, Buildings & Industry c. Under Consumption Summaries, click on “Annual” d. Now, over to the right click on “State Energy” e. Using the drop down menu at the bottom, select “Indiana” f. Under “Consumption” click on the “Residential” document

2. Using the ratio estimates provided by EPA found in the “Documentation For The Final 2002 NONPOINT SECTOR (FEB 06 version) NATION AL EMISSIONS INVENTORY FOR CRITERIA AND HAZARDOUS AIR POLLUTANTS” at http://www.epa.gov/ttn/chief/net/ 2002inventory.html#documentaiton the number calculated above in step 1 is broken out into three categories (fireplac e without inserts, fireplaces with inserts and woodstoves).

3. To distribute to the county level for the three ca tegories above, calculate a ratio of county to state using the statewide total of households and the count y total of households that burn wood found at the U.S. Census Bureau website http://www.census.gov/ . The remaining number is the process rate for each county. Multiply the pr ocess rate by the appropriate EPA em ission factors fo r each of the categories using the EIIP, Volume 3, Ch apter 2, Residential Wood Combustion at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/iii02_apr2001.pdf

.
Note: Use the steps in sub-category 1.3-2 to navigate through the Energy Information Administration’s website.



# Category 2: Industrial Processes

Sub-Category 2.1: Bakeries

SCC: 2302050000

Follow these steps when calculating emissions from bakeries:

1. Calculate a per capita consumption factor using the reported weight of yeast–raised product reported under the Bread, Cake, and Frozen Bakery Products from the Economic Census Bureau at http://www.census.gov/econ/census02/ and the U.S. population at the U.S. Census Bureau at http://census,gov/

.
Note: As of the date of this SOP, the following steps will lead to data for yeast-raised product.

a. Go to http://www.census.gov b. Under Business & Industry open “Economic Census” c. Now open “Subject Series” d. Under Manufacturing, open the table “Product Summary” e. Use the yeast – raised product under Commercial Bakeries (NAICS code 311812) and Frozen cakes, pies, and other pastries manufacturing (NAICS code 311813)

7

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## 2. Multiply the per capita consumption factor ca lculated above in step 1 by the Indiana population found at the U.S. Census Bureau at http://www.census.gov

. Note: As of the date of this SOP, the foll owing steps will lead to Indiana population data.

a. Go to http://www.census.gov b. Under Population Finder, use the drop down menu to select Indiana

3. To avoid double calculating the amount consumed for the state, subtract the reported process rate for both the straight-dough and sponge-dough by queryi ng the total process rates for the SCC 30203202 (straight-dough) and SCC 30203201 (sponge-do ugh) using the ACC ESS data tables at K:\OAQ_INV\Steptool\Stptl_02.mdb.

4. Multiply the remaining process rate by the strai ght-dough emission factor of .5 lbs VOC/1,000 pounds baked found in the EIIP, Volume 3, Area Source Me thod Abstracts: Baked Goods at Commercial/Retail Bakeries at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/index.html

.
5. Calculate a per capita factor by dividing the I ndiana population found in step 2 by the remaining process rate. Now multiply the per capita factor by each of the county populations to calculate the VOC emissions for each county.

Note: As of the date of this SOP, the fo llowing steps will lead to county population data.

a. Go to http://www.census.gov b. Under Population Finder, use the drop down menu to select Indiana c. Under “View more results”, select the county table



# Category 3: Solvent Utilization

Sub-Category 3.1: Architectural Coatings

SCC: 2401001000

Follow these steps when calculating emissions from architectural coatings:

1. Calculate an emission factor for architectural coating area sources first by adding all the solventbased paints together and all the water based paint s together using the U.S. Census Bureau’s website http://www.census.gov . Use Table 1 to select all solvent-based paints and Table 2 to select all water based paints.

Table 1 National Solvent Coating Sales Solvent Type 1,000 gallons Exterior Solvent Type XX Interior Solvent Type XX Architectural Lacquers XX

Architectural Coating N.S.K. XX Total Solvents XX

Table 2 National Water Based Coating Sales Water Type 1,000 gallons Exterior Water Type XX Interior Water Type XX Total Water Type XX

8

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## Note: As of the date of this SOP, the followin g steps will lead to architectural coating data.

a. Go to http://www.census.gov b. Under Business & Industry, select more c. Now select Current Industrial Reports (CIR) d. Select CIRs by Subject e. Tab down to find the report “Paints and Allied Products”

2. Now multiply the total national number for solvent -based paints by the average solvent-based coating content number (3.87 lbs VOC/gallon) and the total national number for water-based paints by the average water-based coating content number (0. 74 lbs VOC/gal) found in the EIIP, Volume 3, Chapter 3: Architectural Surface Coating at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/archsfc.pdf

.
3. Add the total solvent-based coatings and the water-based paints together for a total national VOC emission factor from architectural surface coatin g. Then divide this number by the total national population using the U.S. Census Bureau’s website http://www.census.gov

.
4. Multiply the number calculated abov e in step 3 by each of the county populations to calculate the total emissions per county.

Note: Use the steps in sub-category 2.1-5 to navigate through the Census Bureau’s website.

Sub-Category 3.2: Automobile Refinishing

SCC: 2401005000

Follow these steps when calculating emissions from automobile refinishing:

1. To avoid double calculating, first query the empl oyees from the reported sources using the SIC 7532- Body Repair and Paint Shops using the ACCESS data t ables at K:\OAQ_INV\Steptool\Stptl_02.mdb. Subtract this number from the coun ty employment for the same SIC using the U.S. Census Bureau’s website http://www.census.gov

.

Note: As of the date of this SOP, the foll owing steps will lead to county employment data.

a. Go to http://www.census.gov b. Under Business & Industry, select more c. Now select the County Business Patterns report for county d. Select Indiana e. Select each of the counties to find the number of employees for the corresponding SIC or NAICS code

2. Multiply the emission factor 3, 519 lbs VOC/employee found in the EIIP, Volume 3, Chapter 13 Auto Body Refinishing at http://www.epa.gov/ttn/chief/eiip /techreport/vol ume03/archsfc.pdf and the county employment found above in step 1 to calcul ate the VOC emissions for each county.

Sub-Category 3.3: Traffic Markings

SCC: 2401008000

Follow these steps when calculating for traffic markings:

1. First calculate the national emissions by finding t he amount of sales for traffic marking paints from the U.S. Census Bureau’s website http://www.census.gov and multiply 3.36 lb VOC/gallon the national average VOC content for water and solvent-based paint s from the EIIP, Volume 3, Chapter 14, Traffic Markings at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/iii14.pdf

.

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### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## Note: As of the date of this SOP, the foll owing steps will lead to traffic marking paints.

a. Go to http://www.census.gov b. Under Business & Industry, select more c. Now select Current Industrial Reports (CIR) d. Select CIRs by Subject e. Tab down to find the report “Paints and Allied Products” f. Use the quantity amount in 1000/gallons under “Tra ffic marking paints (all types: shelf goods and

highway department)

2. Allocate the national emissions calculated above in step 1 to the state level by dividing the amount of money spent in Indiana by the money spent nationally on highway maintenance using the category “Total Disbursements” at the Federal Highway Administration’s website http://www.fhwa.dot.gov/po licy/ohim/hs04/htm/sf2.htm

.
3. Calculate the emission factor for Indiana by divi ding the state level emissions by the total number of roadway miles in Indiana, given by contacting the Program Development Division, Highway Statistics, Indiana Department of Transportation or the Office of Air Quality, Technical Support and Modeling Section’s mobile inventory preparer.

4. Multiply the emission factor by the total number of roadway miles in each county using the information supplied from above in step 3.

Sub-Category 3.4: Industrial Surface Coating (employment based emission factor)

SCC: 2401015000, 2401020000, 2401030000, 2401040000, 2401045000, 2401055000, 2401060000, 2401065000, 2401070000, 2401075000, 2401080000

Follow these steps when calculating for industrial surface coating using the employment based emission factor:

1. Calculate an employee based emission factor for t he following SIC’s in the table below running a query to find the point source employment for each of the SIC’s and the reported VOC emissions for each using the ACCESS data tables at K:\OAQ_INV\Steptool\Stptl_02.mdb.

SCC Description SIC’s

2401015000 Factory Finished Wood 2426-2429,243-245, 2492, 2499

2401020000 Wood Furniture 25

2401030000 Paper Coating 26

2401040000 Metal Cans * 341

2401045000 Metal Coils * 3479

2401055000 Machinery and Equipment 35

2401060000 Appliances * 363

2401065000 Electronic and Other Electrical 3612, 3357

2401070000 New Motor Vehicles ** 3711

2401075000 Other Transportation 37 (not 3711, 373)

2401080000 Marine Coatings 373



## 10

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1

* Use the National default emission fact or because the reporting sources are low. ** Emissions reported in point source



## 2. Divide the reported VOC emission s for each of the SIC’s by the re ported employment for each SIC. Use this number for the emission factor.

3. Subtract the number of report ed employees found in step 1 from each of the SIC county totals using the U.S. Census Bureau’s website http://www.census.gov . Use the remaining number for the process rate for each of the counties.

Note: Use the steps in sub-category 3.2-1 to navigate through the County Business Patterns.

4. Multiply the process rates above f ound for each of the SIC’s in step 4 by the emission factors found in step 3 to allocate the emissions to each of the counties.

Sub-Category 3.5: Industrial Surface Coating (default emission factor)

SCC: 2401090000, 2401100000, 2401200000

Follow these steps when calculating emissions from i ndustrial surface coating using the default emission factor:

1. Calculate industrial surface coat ing emissions using the default emission fa ctor in the EIIP, Volume 3, Chapter 8, Industrial Surface Coating at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/iii08.pdf and multiply by the county populations found at the U.S. Census Bureau’s website http://www.census.gov

.
Note: Use the steps in 2.1-5 to navigate through U.S. Census Bureau’s website.

SCC’s Description Default Emission Factor

24-01-090-000 Miscellaneous Manuf acturing 0.600 lbs VOC/person

24-01-100-000 Industrial Maintena nce Coatings 0.800 lbs VOC/person

24-01-200-000 Other Special Pur pose Coatings 0.800 lbs VOC/person



## Sub-Category 3.6: Degreasing

SCC: 2415230000, 2415245000, 2415345000, 2415360000

Follow these steps when calculating emissions from degreasing activities:

1. Use the U.S. Census Bureau to find employment numbers for each of the counties for the categories in Table 1 below at http://www.census.gov

.
Note: Use the steps in 2.1-5 to navigate through U.S. Census Bureau’s website.

Source Classification Codes and Industries Associated with Degreasing
SCC SIC Description

2415230000 36 Electronic and other electronic equipment

25 Furniture and fixtures

33 Primary metal industries

34 Fabricated metal products

35 Industrial machinery and equipment

37 Transportation equipment

38 Instruments and related products



## 11

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1

39 Miscellaneous manufac turing industries

417 Bus Terminal and Service Facilities

423 Trucking terminal facilities

551 New and used car dealers

552 Used car dealers

554 Gasoline service stations

555 Boat dealers

556 Recreational vehicle dealers 2415245000

753 Automotive repair shops
25 Furniture and fixtures

33 Primary metal industries

34 Fabricated metal products

35 Industrial machinery and equipment

36 Electronic and other electronic equipment

37 Transportation equipment

38 Instruments and related products 2415345000

2415345000 cont. 39 Miscellaneous manufac turing industries
417 Bus Terminal and Service Facilities
423 Trucking terminal facilities
551 New and used car dealers
552 Used car dealers
554 Gasoline service stations
555 Boat dealers
556 Recreational vehicle dealers 2415360000

753 Automotive repair shops



## 2. Run a query to find reported employment numbers for each of the categories in the table above using the ACCESS data tables at K:\O AQ_INV\Steptool\Stptl_02.mdb.

3. Subtract the reported employment from the U.S Census Bureau’s numbers to find the process rates for each of the counties.

4 Calculate the VOC emissions by mult iplying the default emission factor in the EIIP, Volume 3, Chapter 6, Solvent Cleaning at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/iii06fin.pdf and the process rate for each of the counties found in step 3.

Sub-Category 3.7: Dry Cleaners

SCC: 2420010370

Follow these steps when calculating emissions from dry cleaners:

1. Calculate an emission factor by finding the numbe r of employees state wide and county wide for SIC 7216(Laundry and Garment Services) at the U.S. Census Bureau’s website http://www.census.gov

.
Note: Use the steps in 2.1-5 to navigate through U.S. Census Bureau’s website

2. Take the sum of the employment from the coun ties, multiply by 2000, and divide by the statewide total found in step 1. Use this number for the emission factor.

3. Calculate the process rate by running a query to find the number of reported employees for SIC 7216 using the ACCESS data tables at K:\OAQ_INV\St eptool\Stptl_02.mdb and subtract this number from the county total.

4. Multiply the process rate for each of the counties above by the em ission factor to calculate for VOC emissions.

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### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## Sub-Category 3.8: Graphic Arts

SCC: 2425000000

Follow these steps when calculating emissions from graphic arts activities:

1. Multiply the per capita factor found in the EIIP, Volume 3, Chapter 7, Graphic Arts at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/iii07.pdf by the state population from the Census Bureau http://www.census.gov to find the total emissions for the state.

Note: Use the steps in 2.1-2 to navigate th rough the U.S. Census Bureau’s website.

2. Develop an emission factor by subtracting point source emissions from the total emissions and dividing by the state pop ulation found in step 1.

3. Distribute to the counties by multiplying the emission factor by the population for each county.

Note: Use the steps in 2.1-5 to navigate th rough the U.S. Census Bureau’s website.

Sub-Category 3.9: Rubber and Plastics

SCC: 2430000000

Follow these steps when calculating emissions from rubber and plastics activities:

1. Run a query to find the total of reported emissi ons and number of reported employees for all SIC’s beginning with 30 using the ACCESS data tabl es at K:\OAQ_INV\Steptool\Stptl_02.mdb.

2. Calculate the emission factor by dividing the point source emissions by the reported employees.

3. Subtract the reported employment for SIC’s beginning with 30 from total employment for each of the counties.

Note: Use step 3.2-1 to navigate through the County Business Patterns.

4. Multiply the remaining number from above with the emission factor calculated in step 2.

Sub-Category 3.10: Miscellaneous Industrial Adhesives

SCC: 2440020000

Follow these steps when calculating emissions from industrial adhesives activities:

1. Using the guidance in the Ai r Pollutant Emission Trends at http://www.epa.gov/ttn/chief/trends

, calculate an emission factor by finding the total National Emissions from Industrial Adhesives and divide by the National Manufacturing Employm ent from the U.S. Census Bureau’s website http://www.census.gov

.
Note: As of the date of this SOP, the following st eps will lead to emission trends data for industrial adhesives.

a. Go to http://www.epa.gov/air /airtrends/aqtrnd03/ b. Select “Appendix A –Data Tables” c. Search for industrial adhesives

Note: As of the date of this SOP, the following steps will lead to National Manufacturing Employment.

a. Go to http://www.census.gov

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### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## b. Select Economic Census c. Now select “Businesses with paid employees” d. Use the manufacturing number under “paid employees”

2. To avoid double calculating, run a query collecting sources re porting adhesives using the ACCESS data tables at K:\OAQ_INV\Steptool\Stptl_02.mdb. Subtract the reported employment from the total amount of manufacturing employment. The remaining number is the process rate.

Sub-Category 3.11: Commercial/Consumer Solvents

SCC: 2460100000, 2460200000, 2460400000, 2460500000, 2460600000, 2460800000, 2460900000

Follow these steps when calculating emissions from commercial/consumer solvent usage:

1. Using the EIIP, Volume 3, Chapter 5, Consumer, and Commercial Solvent Use at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/iii05.pdf , multiply the per capita factors for each of SCC codes by the population for each county from the U.S. Census Bureau’s website http://www.census.gov

.
Note: Use the steps in 2.1-5 to navigate through the U.S. Census Bureau’s website.

Emission Factors for Commercial/Consumer Solvents

Source Classification Codes Product Category Per Capita Emission Factor (lb VOC/person)

2460100000 Personal Care Products 2.32

2460200000 Household Products 0.79

2460400000 Automotive Aftermarket Products 1.36

2460500000 Coatings and Related Products 0.95

2460600000 Adhesives and Sealants 0.57

2460800000 FIFRA-Regulated Products 1.78

2460900000 Miscellaneous Products 0.07



## Sub-Category 3.12: Asphalt Emulsions

SCC: 2461022000

Follow these steps when calculating emissions from asphalt emulsions:

1. To calculate the process rate, find the number of barrels of asphalt used for the state found at the State Energy Data website at http://www.eia.doe.gov/emeu/states/_seds_updates.html

.
2. Obtain the amount of roadway miles for the st ate and county from the Indiana Department of Transportation’s, Division of Roadway Management Section.

3. Divide the county roadway miles by the state roadw ay miles and multiply by the total asphalt usage for the state found above in step 1.

4. Multiply the process rate by the default emission factor in the E IIP, Volume 3, Chapter 17, Asphalt Paving http://www.epa.gov/ttn/chief/eiip/te chreport/volume03/ iii17_apr2001.pdf

.

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### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## Sub-Category 3.13: Pesticide Usage

SCC: 2461800000

Follow these steps when calculating emissions from pesticide usage:

1. Calculate pesticide usage by using a state spec ific emission factor. Develop the factor using a methodology that includes the retrieval of informat ion of pesticides used, an emission factor for each pesticide used, a calculation about the inert ingredien ts in each pesticide, and an estimate of the amount of crop oil concentrate (an adjuvant used for the application of herbicides) used in the state of Indiana.

2. Find the amount of active ingredients for herbicides and insecticides applied to Indiana fields at the Indiana Agricultural Statistics Service at http://www.usda.gov/nass/pubs/agr02/acro02.htm

.
3. Insert the numbers for both corn and soybeans to the Excel pesticide table found at K:OAQ_INV\Inv\pesticide.

4. Calculate the emission factor by adding the emis sions from crop oil concentrates obtained in the pesticide Excel table, pesticides, and solvent carrie rs and then divide by the total number of acres of corn and soybeans in Indiana found at the National Agricultural Statistics Services, United States Department of Agriculture http://www.nass.usda.gov/QuickStats/

.
5. Multiply the emission factor by the county-specific acreage for both corn and soybeans found at the National Agricultural Statistics Services, United States Department of Agriculture http://www.nass.usda.gov/QuickStats/

.


# Category 4: Petroleum Marketing

Follow these steps when calculating emissions for bulk terminals:

Sub-Category 4.1: Bulk Terminals

SCC: 2501050120

1. Find the amount of gasoline sold in Indiana at t he Federal Highway Administration, U.S. Department of Transportation http://www.fhwa.dot.gov/po licy/ohim/hs04/htm/mf21.htm

.
2. Find the amount of gasoline sold statewide and by county using, the NAICS code 447-Gasoline Service Station from the U.S. Cens us Bureau’s, Economic Census at http://www.census.gov/econ/census02/data/in/IN000_44.HTM#N447

.
3. Run a query to find the amount of point source reported gasoline using t he ACCESS data tables at K:\OAQ_INV\Steptool\Stptl_02.mdb and subtract from the amount sold statewide. Use this to allocate to each county.

4. Allocate the amount gasoline sold to each of the counties by dividing the amount of sales in each county by statewide sales and mult iplying by the number of gallons sold statewide found above in step 1.

5. EPA guidance suggests that only 25% of all gas oline consumed goes through bulk plants. To calculate process rate, multiply each county by 25% to estimate the amount of fuel transferred through bulk terminals.

6. Multiply process rate by the emission factors in the table below:

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### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## Emission Factors

Source Emission Factor (lb VOC/1000) gal
Storage Tanks Breathing Loss 5.0

Storage Tank Working Loss - Filling 9.6

Storage Tank Working Loss - Emptying 3.8
Gasoline Loading Racks (Vapor balance controlled) 11.9 (0.3)

Total 30.3

7. Bulk terminals also have controls set forth in the Indiana rule (326 IAC 8-4). This rule says that any source of this type that is new after January 1, 1980 is required to make sure that any transfer between a tank and transport uses a submer ged pipe vapor balance system. Using EPA’s default rule effectiveness, multiply the number in step 2 by the Control Efficiency (CE) 38%, a Rule Effectiveness (RE) of 80%, and a Rule Penetration (RP) of 13%, i.e. process rate X emission factor X (1-(CE x RE x RP)) X 1 ton/2000 lb = VOC tons.

Sub-Category 4.2: Portable Fuel Containers

SCC: 2501011011, 2501011012, 2501011016, 2501012011, 2501012012, 2501012016

Follow these steps when calculating emi ssions for portable fuel containers:

1. Calculate the emissions for Commercial and Residential gas cans by using the method developed by the California Environmental Protection Agency’s docu ment Public Meeting to Consider Approval of California’s Portable Gasoline-Cont ainer Emissions Inventory. Use the excel spreadsheet found at K:\OAQ_INV\Inv\Area Source\Gasoline.zip to calcul ate the emissions for permeation, diurnal, and transport

. Both the Spillage and Vapor losses are esti mated in the nonroad emissions inventory by EPA models.

2. Using the survey results below in Table 1, esti mate the number of fuel containers in the state for residential categories. The calculations are set up in an excel spreadsheet at K:\OAQ_INV\Inv\Area Source\ Gasoline.zip\250101\GasCan s.xls, insert the number of oc cupied housing, from the U.S. Census Bureau’s website at http://www.census.gov/ , in the space marked “households”.

Note: As of the data of this SOP, the following steps will lead to number of households in Indiana.

a. Go to http://www.census.gov/ b. On the left hand side select American Fact finder c. Now select housing d. Under “Occupancy Status”, select occupies housing units e. Now use the drop down menu and select Indiana

Table 1 Residential Survey Results

Percentage of households with at least one gas can 46%
Number of gas cans per household 1.8
Percentage of plastic cans/metal cans 76% / 24%
Weighted average gas can capacity (gal) 2.34
Percentage of gas cans stored with fuel 70%
Weighted average stored fuel volume (% of capacity) 49%



## 16

### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## Percentage of all gas cans that are plastic and stored open/closed 23% / 53%
Percentage of all gas cans that are metal and stored open/closed 11% / 13%
Percent of all cans stored open/closed 34% / 66%



## 3. Using the survey results below in Table 2, esti mate the number of fuel containers for commercial categories for the state. Do this by using the commercial population based on the number of identified businesses in Table 3 and insert into the excel spreadsheet at K:\OAQ_INV\Inv\Area Source\ Gasoline.zip\250101\GasCans.xls.

Table 2 Commercial Survey Results

Percentage of businesses with at least one gas can 80%
Number of gas cans per business 6.9
Percentage of plastic cans/metal cans 72% / 28%
Weighted average gas can capacity (gal) 3.43
Weighted average stored fuel volume (% of capacity) 49%
Percentage of all gas cans that are plastic and stored open/closed 39% / 33%
Percentage of all gas cans that are metal and stored open/closed 10% / 18%
Percent of all cans stored open/closed 49% / 51%



## Table 3 Category NAICS
Agricultural 115
Automotive Club and Towing Services 48841

Service Stations 8111

Lawn and Garden Maintenance Services 81141

General Contractors 23

Construction and Rental Yards 5324
Landscaping Services 561730



## 4. Calculate permeable emissions separately for bot h residential and commercial by using the emission rates given in the California document. Use 1.57g/gal /day for plastic contai ners and 0.6g/gal/day for metal containers. Insert the numbers for both resi dential and commercial into the excel spreadsheet at K:\OAQ_INV\Inv\Area Source\ Gaso line.zip\250101\GasCans.xls.

5. Calculate diurnal emissions by inserting the numbers for both residential and commercial into the excel spreadsheet at K:\OAQ_INV\Inv\Area Source\ Gasoline.zip\250101\GasCans.xls.

6. Calculate transport spillage emissions by inserting the numbers for both residential and commercial into the excel spreadsheet at K:\OAQ_INV\Inv\Area Source\ Gasoline.zip\250101\GasCans.xls

Sub-Category 4.3: Service Station Tank Loading or Tank Truck Unloading (Stage 1)

SCC: 2501060052 (uncontrolled), 2501060053 (controlled)

Follow these steps when calculating emissions from tank loading and unloading

1. Find the amount of gasoline sold in Indiana at the Federal Highway Administration, U.S. Department of Transportation http://www.fhwa.dot.gov/po licy/ohim/hs04/htm/mf21.htm

.
2. Find the amount of gasoline sold statewide and county wide by using the NAICS code 447-Gasoline Service Station from the U.S. Cens us Bureau’s, Economic Census at http://www.census.gov/econ/census02/data/in/IN000_44.HTM#N447

.

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## 3. Run a query to find the amount of point source reported gasoline using t he ACCESS data tables at K:\OAQ_INV\Steptool\Stptl_02.mdb and subtract from the amount sold statewide. Use this to allocate to each county.

4. Allocate the amount sold to each of the counties by dividing the amount of sales in each county by statewide sales and multiplying by the number of gallons sold statewide found above in step 1.

5. Find the amount of gasoline tank s from the Underground Storage Tank data files from the Office of Land Quality, Indiana Department of Environmental Management http://www.in.gov/idem/programs/land/ust/ust.html

.
6. Now copy the data into an Excel spreadsheet. Filt er finding the tanks that have only gasoline. Also filter out the tanks that are “permanently out of service”, “suspended per inspection”, and “unregulated”.

7. Using the Petroleum Sources Applicability Rule 326 IAC 8-4-1, filter out the t anks that are located in Clark, Boone, Dearborn, Elkhart, Floyd, Hamilton, Hancock, Harrison, Hendricks, Johnson, Lake, Marion, Morgan, Porter, Saint Joseph, and Shelby counties.

8. To find the amount of balanced tanks in Indiana, use the total of gasoline tanks found in step 7 and divide by the number of tanks that constructed after 1985 through current year. Use the spreadsheet created in step 7 and filter out the t anks that constructed prior to 1985.

9. Now apply the percentage found in step 8 to the amount of gasoline found in each county.

10. Apply the controlled emission factor to only those co unties identified in 326 IAC 8-4, i.e. Boone, Clark, Dearborn, Elkhart, Hamilton, Hancock, Harrison, Hendricks, Johnson, Lake, Marion, Morgan, Porter, Saint Joseph, and Shelby. Use the emission factor s for stage 1 controlled and uncontrolled in the EIIP, Volume 3, Chapter 11, Gasoline Marketing (Stage 1 and Stage 2) http://www.epa.gov/ttn/chief/eiip/techreport/volume03/iii11_apr2001.pdf

.

Sub-Category 4.4: Vehicle Fueling (Stage II) – Vapor Displacement

SCC: 2501060101 (uncontrolled), 2501060102 (controlled)

Follow these steps when calculating emissions from vehicle fueling – Vapor Displacement:

1. Find the amount of gasoline sold in Indiana at t he Federal Highway Administration, U.S. Department of Transportation http://www.fhwa.dot.gov/po licy/ohim/hs04/htm/mf21.htm

.
2. Find the amount of gasoline sold statewi de and by county using the NAICS code 447-Gasoline Service Station from the U.S. Cens us Bureau’s, Economic Census at http://www.census.gov/econ/census02/data/in/IN000_44.HTM#N447

.
3. Allocate the amount sold to each of the counties by dividing the amount of sales in each county by statewide sales and multiplying by the number of gallons sold statewide found above in step 1.

4. Calculate an emission factor using the input file s supplied from the mobile model. Table 1 and Table 2 show examples of how the emission factors fo r January and July for the Southern Counties were calculated. By using these two months, the other months are distributed. Use the average of all months for the emission factor for the Southern counties. Use the same methodology for the Northern counties, Central Countie s, Clark/Floyd, and Lake/Porter.

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## Table 1

January Run for Southern Counties

VTYPE GM_MILE MILES MPG VMT G/GAL Month Factor
1 0.0628 29.4642 23.89 0.463793 0.322719 1 1.01
2 0.1058 35.2923 18.77 0.070491 0.009868 2 1.14
3 0.1058 35.2923 18.77 0.234672 0.109364 3 1.28
4 0.1486 34.0851 14.31 0.071379 0.010834 4 1.41
5 0.1486 34.0851 14.31 0.032825 0.002291 5 1.55
6 0.2152 35.8919 9.88 0.028896 0.001775 6 1.69

7 0.2342 32.3617 9.08 0.001027 2.24E-06 7 1.82
8 0.2465 19.9098 8.63 0.000522 5.8E-07 8 1.69
9 0.2719 27.6093 7.82 0.001164 2.88E-06 9 1.55
10 0.2733 27.4686 7.78 0.002489 1.32E-05 10 1.41
11 0.2972 24.3758 7.15 0.001132 2.72E-06 11 1.28
12 0.3169 23.6257 6.71 0.000004 3.4E-11 12 1.14
25 0.3421 27.2301 6.22 0.000496 5.23E-07 Sum 16.97
0.456873 g/gal Average 1.41
1.007222 lb/E3gal

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### Area Source Inventory S-006-OAQ-R-MO-08-S-R1



## Table 2 July Run for Southern Counties
VTYPE GM_MILE MILES MPG VMT G/GAL

1 0.1144 29.1752 23.9 0.456768 0.570447
2 0.1955 34.8826 18.75 0.071404 0.018689
3 0.1955 34.8826 18.75 0.237712 0.207133
4 0.2882 33.944 14.3 0.072838 0.021865
5 0.2882 33.944 14.3 0.033496 0.004624
6 0.4164 35.8288 9.9 0.029201 0.003515

7 0.4529 32.4716 9.1 0.001038 4.44E-06
8 0.4763 19.6757 8.66 0.000509 1.07E-06
9 0.5264 27.4602 7.83 0.00116 5.55E-06
10 0.5283 27.3328 7.8 0.002482 2.54E-05

11 0.5749 24.2458 7.17 0.001122 5.19E-06
12 0.6128 23.3718 6.73 0.000004 6.6E-11
25 0.6629 27.2301 6.22 0.000485 9.7E-07
0.826316 g/gal
1.821697 lb/E3gal

5. Multiply the process rate in step 4 by the emission factor found in the mobile model.

Sub-Category 4.5: Vehicle Fue ling (Stage II) – Spillage

SCC: 2501060103

Follow these steps when calculating emi ssions from vehicle fueling – Spillage:

1. Find the amount of gasoline sold in Indiana at t he Federal Highway Administration, U.S. Department of Transportation http://www.fhwa.dot.gov/po licy/ohim/hs04/htm/mf21.htm

.
2. Find the amount of gasoline sold statewi de and by county using the NAICS code 447-Gasoline Service Station from the U.S. Cens us Bureau’s, Economic Census at http://www.census.gov/econ/census02/data/in/IN000_44.HTM#N447

.
3. Allocate the amount sold to each of the counties by dividing the amount of sales in each county by statewide sales and multiplying by the number of gallons sold statewide found above in step 1.

4. Apply the emission factor 0.7 lb VOC/1000 gallons in AP-42, Fifth Edition, Volume 1, Chapter 5, Petroleum Industry, Transportation, and Marketing of Petroleum Liquids http://www.epa.gov/ttn/chief/ap42/ch05/final/c05s02.pdf to the process rate found in step 4.

Sub-Category 4.6: Underground Tank Breathing

SCC: 2501060200

Follow these steps when calculating emi ssions from underground tank breathing:

1. Find the amount of gasoline sold in Indiana at t he Federal Highway Administration, U.S. Department of Transportation http://www.fhwa.dot.gov/po licy/ohim/hs04/htm/mf21.htm

.
2. Find the amount of gasoline sold statewi de and by county using the NAICS code 447-Gasoline Service Station from the U.S. Cens us Bureau’s, Economic Census at http://www.census.gov/econ/census02/data/in/IN000_44.HTM#N447

.

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## 3. Allocate the amount sold to each of the counties by dividing the amount of sales in each county by statewide sales and multiplying by the number of gallons sold statewide found above in step 1.

4. Apply the emission factor 1.0 lb VOC/1000 gallons in AP-42, Fifth Edition, Volume 1, Chapter 5, Petroleum Industry, Transportation, and Marketing of Petroleum Liquids http://www.epa.gov/ttn/chief/ap42/ch05/final/c05s02.pdf to the process rate found in step 4.

Sub-Category 4.7: Tank Trucks in Transit

SCC: 2505030120

Follow these steps when calculating emissions from tank trucks in transit:

1. Find the amount of gasoline sold in Indiana at t he Federal Highway Administration, U.S. Department of Transportation http://www.fhwa.dot.gov/po licy/ohim/hs04/htm/mf21.htm

.
2. Find the amount of gasoline sold statewi de and by county using the NAICS code 447-Gasoline Service Station from the U.S. Cens us Bureau’s, Economic Census at http://www.census.gov/econ/census02/data/in/IN000_44.HTM#N447

.
3. Allocate the amount sold to each of the counties by dividing the amount of sales in each county by statewide sales and multiplying by the number of gallons sold statewide found above in step 1.

4. Using the guidance in the EIIP, Volume 3, Chapt er 11, Gasoline Marketing (Stage I and State II) at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/iii11_apr2001.pdf ), multiply the activity rate 1.25 by the amount sold per county found in step 4.

5. Now multiply the process rate found in step 5 by the emission factor .06 lb VOC/gallon transported using the EIIP guidance above.



# Category 5: Waste Management Practices

Sub-Category 5.1: Solid Waste Incineration

5.1.1: Industrial Solid Waste Incineration

SCC: 2601010000

Follow these steps when calculating emissions from industrial solid waste incineration:

1. Find the number of manufacturing employees, NAICS code 31, for each county using the County Business Patterns at the U.S. Census Bureau’s website http://censtats.census.gov/c gi-bin/cbpnaic/cbpsel.pl

.
Note: Use the steps in 3.2-1 to navi gate through the county business patterns.

2. Multiply the county manufacturing employment by the default fuel-loading factor 420 tons / 1,000 manufacturing employees.

3. Multiply the process rate in step 2 by AP-42, Fi fth Edition, Volume 1, Chapter 2-1.12, Solid Waste Disposal at http://www.epa.gov/ttn/chief/ap42/ch02/index.html

.

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## 5.1.2: Commercial Solid Waste Incineration

SCC: 2601020000

Follow these steps when calculating emissions from commercial solid waste incineration:

1. Find the population for each county at the U.S. Census Bureau’s website http://www.census.gov/

.
Note: Use steps 2.1-5 to navigate thr ough the U.S. Census Bureau’s website.

2. Next find the default factor of .65lb/person/day from U.S. EPA Municipal Solid Waste Report http://www.epa.gov/epaoswer/non-hw/muncpl/msw99.htm

.
3. Find the percent of co mmercial solid waste from the U.S. EPA Municipal Solid Waste Report above.

4. Now, calculate the process rate for commercial solid waste incineration by multiplying population by the default factor of .65lb/person/day by the percent of commercial solid waste and number of days in
a year.

5. Multiply the process rate in step 4 by AP-42, Fi fth Edition, Volume 1, Chapter 2-1.12, Solid Waste Disposal at http://www.epa.gov/ttn/chief/ap42/ch02/index.html

.

5.1.3: Residential Solid Waste Incineration

SCC: 2601030000

Follow these steps when calculating emissions from residential solid waste incineration:

1. Find the population for each county at the U.S. Census Bureau’s website http://www.census.gov/

.
Note: Use step 2.1-5 to navigate through the U.S. Census Bureau’s website.

2. Next find the default factor of .65lb/person/day from U.S. EPA Municipal Solid Waste Report http://www.epa.gov/epaoswer/non-hw/muncpl/msw99.htm

.
3. Find the percent of residential solid waste from the U.S. EPA Municipal Solid Waste Report above.

4. Now, calculate the process rate for residentia l solid waste incineration by multiplying population by the default factor of .65lb/person/day by the percent of commercial solid waste and number of days in
a year.

5. Multiply the process rate in step 4 by AP-42, Fi fth Edition, Volume 1, Chapter 2-1.12, Solid Waste Disposal at http://www.epa.gov/ttn/chief/ap42/ch02/index.html

.
Sub-Category 5.2: Residential Open Burning

5.2.1: Leaf and Brush Burning

SCC: 2610000100 and 2610000400

Follow theses step when calculating emissions from leaf and brush burning:

1. Find a per capita factor for l eaf burning and a per capita for brus h burning by using the U.S. EPA’s Solid Waste Report at http://www.epa.gov/epaoswer/non-hw/muncpl/msw99.htm

.
2. Allocate the amount burned by adjusting the per c apita factor for leaves at 25% and for brush at 25%. Of the total waste generated only 28% burns.

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## 3. Once all the percentages from above are calculated, multiply the adjusted per capita factor by the rural population for each county from the U.S. Census Bureau at http://www.census.gov/

Note: As of the data of this SOP, the follow ing steps will lead to county rural population.

a. Go to http://www.census.gov/ b. On the left hand side, select American Fact Finder c. Select data sets d. Detailed tables e. County f. Indiana g. All counties

4 Use the table below to adjust the amount of wast e generated to account for the percentage of forest in each county. The percentages come from a doc ument from the United States Department of Agriculture at http://ncrs.fs.fed.us /pubs/rb/rb_nc253b.pdf

.

Percent Forested Acres per County Adjusted for Yard Waste Generated

< 10% 0% generated

>= 10%, and < 50% 50% generated

>= 50% 100% generated



## 5. Now, multiply the amount of leaves and brush by the emission factors found in AP-42, Fifth Edition, Volume 1, Chapter 2, Solid Waste Disposal, Table 2.5-5, and Table 2.5-6 at http://www.epa.gov/ttn/chief/ap42/ch02/final/c02s05.pdf

.

5.2.2: Residential Waste Incineration

SCC: 2610030000

Follow these steps when calculating emissions from for residential waste incineration:

1. Find a per capita factor for re sidential waste incinerati on by using the U.S. EPA’ s Solid Waste Report
at http://www.epa.gov/epaoswer/non-hw /muncpl/pubs/mswchar05.pdf

.
2. Using the Solid Waste Report above, subtract the percentage of recycled and composted material from the per capita factor above.

3. Now, subtract the percentages of combustibles i.e. glass, metal, yard trimmings, and other waste.

4. Using a document from EPA, it states that only 28% of waste ge nerated by rural popul ation burns and of that percent, 49% is actually combusted. Using this information multiply the per capita factor by 0.28 and then multiply that number by 0.49 actually burned in rural counties.

5. Once all the percentages are calculated, multiply the adjusted per capita factor by the rural population for each county from the U.S. Census Bureau at http://www.census.gov/

.
Note: Use steps 5.2.1-3 to find county rural population.

6. Calculate the amount of residentia l waste by the emission factors in the EIIP, Volume 3, Chapter 16, Open Burning at http://www.epa.gov/ttn/chief/eiip/techreport/volume03/index.html

.
Sub-Category 5.3: Public Owned Treatment Works (POTW’s)

SCC: 2630020000

Follow these steps when calculating emissions from POTW’s:

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## 1. To calculate the amount of annual flow for public owned treatment works, obtain the amount of monthly flow rate for each county. This is data is supplied by the Office of Water Quality. To calculate for annual flow multiply the monthly flow by the default of 0.16 that represents the amount of industrial flow.

2. Calculate the process rate above by the em ission factors in FIRE 6.25 using the SCC code
2630020000.

Sub-Category 5.4: Treatment, St orage, and Disposal Facilities

SCC: 2640000004

Follow these steps when calculating emissions fr om treatment, storage, and disposal facilities:

1. Obtain a list of treatment facilities and the amount of ignitable waste from each facility from IDEM’s Office of Land Quality.

2. Using the list of facilities from step 1, run a query using the ACCESS data tables at K:\OAQ_INV\Steptool\Stptl_02.mdb to obtain the amount of ignitable waste reported to IDEM’s Office of Air Quality.

3. Compare the two lists obtained in step 1 and step 2, for each facility subtract any quantity reported to OAQ from the quantity reported to OLQ. Do this in order to avoid double counting quantities reported to both offices. Combine the quantities reported from facilities within the same counties. Use these quantities as the process rate for each county.

4. Multiply the process rate above with th e combined emission factor in the table below:

Emission Source Emission Factor in AP-42 (lb VOC/Ton) Emission Factor Used (lb VOC/Ton) Storage Tank Vent 0.004-0.09 0.09

Spillage (filling) 0.20 0.20
Loading (filling) 0.00024-1.42 1.42
Spillage (emptying) 0.20 0.20
Loading (emptying) 0.00024-1.42 1.42


## Combined Emission Factor 3.33



# Category 6: Submit Data to EPA

Submit data in a format that is acceptable to EPA. At the present time the format is the National Emission Inventory (NEI).



# 6. Standards and checklists The Emission Reporting program does not have any chec klist for the Area Source Inventory at this time. The Emission Group does this electronically through an excel spreadsheet that is created when needed.



# 7. Records Management The Area Source Inventory files are kept el ectronically at K:\OAQ_INV\Inv\Area Source.

The Branch Contact for the Air Programs Branch a nd the Section contact for the Technical Support and Modeling Section will keep copies of the SOPs for the Technical Support and Modeling Section to be referenced as needed. An electronic copy will also be available on K:\OAQ_INV\SOPs.

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# 8. Quality Assuran ce / Quality Control Comparisons are made against the emissions estimates made by The U.S. EPA in the NEI.



# 9. Continuous Improvement Cycle A periodic review will be completed per updates and changes made to the EIIP.



# 10. References The Area Source Inventory is a requirement of 40 CF R Part 51 Subpart A - Emission Inventory Reporting Requirements.



# 11. History of Revisions

Date Month/day/year Revision Number Description

02/27/2008 1 Revised using new SOP template.



# 12. Appendices
None

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