APPENDIX F 

Mobile Source Input/Output Calculation Files 
F - 1 

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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 Environmental 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 Ozone 

Nonattainment Area 

Abstract This report documents the methodology and results from the 

development of the mobile source emission inventory for 

ozone precursors in the Cincinnati ozone nonattainment area. 

The nonattainment area includes a portion of Dearborn County 

Indiana, Boone, Campbell and Kenton counties in Kentucky, 

and Butler, Clermont, Clinton, Hamilton and Warren counties 

in Ohio. The ozone precursors include volatile organic 

compounds (VOCs) and oxides of nitrogen (NOx). The new 

2005, 2008, 2015, and 2020 inventory, as provided in this 

report, includes the benefits of low RVP fuel in Butler, 

Clermont, Hamilton and Warren counties. It is expected that 

the 2008 inventory, plus an additional safety margin, will be 

established as the revised 8-hour ozone motor vehicle 

emissions budgets for the Cincinnati nonattainment area. 

Date October 2009 

Agency Ohio-Kentucky-Indiana Regional Council of Governments 

 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 cooperatively by the Federal Highway 

Administration, the Federal Transit Administration, the Commonwealth of Kentucky 

Transportation Cabinet, the Ohio Department of Transportation, 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 Council of Governments and are not 

necessarily those of the U.S. Department of Transportation. 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 Indiana and Ohio Portions of 

the Cincinnati Ozone Nonattainment Area .......................................................................8 

Table 2-Mobile Source Emissions Inventory for the Kentucky Portion of the 

Cincinnati Ozone Nonattainment Area .............................................................................8 

Appendix A – MOBILE6.2 Input/Output Files for the Indiana Portion of the 

Nonattainment Area 

Appendix B – MOBILE6.2 Input/Output Files for the Kentucky Portion of the 

Nonattainment Area 

Appendix C – MOBILE6.2 Input/Output Files for the Ohio 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 
 

 

 

 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

1 

1. INTRODUCTION 

At the request of the Indiana Department of Environmental Management, the Kentucky 

Division for Air Quality, and the Ohio Environmental Protection Agency, the OhioKentucky-Indiana Regional Council of Governments (OKI) has prepared this mobile 

source emissions inventory of ozone precursor pollutants. Pursuant to provisions of the 

CAAA of 1990, U.S. EPA designated a nine county area in the Cincinnati area as a basic 

nonattainment area for ozone under the eight-hour ozone standard in April 2004. The 

Cincinnati ozone nonattainment area includes Lawrenceburg Township in Dearborn 

County Indiana, the Kentucky counties of Boone, Campbell and Kenton, and the Ohio 

counties of Butler, Clermont, Clinton, Hamilton and Warren (Figure 1). Ozone is formed 

through chemical reactions induced when sunlight reacts with volatile organic 

compounds (VOCs; principally hydrocarbons) and nitrogen oxides (NOX). VOCs and 

NOX 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 Metropolitan Planning Organization 

(MPO), consists of Dearborn, Boone, Campbell, Kenton, Butler, Clermont, Hamilton and 

Warren counties. The cities of Franklin and Carlisle in Warren County are part of the 

Miami Valley Regional Planning Commission (MVRPC) planning 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 planning agency for Clinton County. 

The Clinton County emissions analysis has been prepared 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 mechanism to ensure that federal funding and 

approval are given to those transportation activities 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 from vehicles. The projected inventory 

is also known as the emissions budget. This budget establishes a maximum allowable 

limit on future emissions from vehicles (mobile sources). 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 vehicle emissions do not exceed the 

established budget. 

This report documents the process for developing the mobile emissions inventory for the 

Cincinnati ozone nonattainment area. Section 2 details the process and procedures used 

and Section 3 describes the transportation network. Section 4 provides the mobile 

emissions inventory. 






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daries and locations are for illustrative purposes only. This is not a regulatory document.
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

3 

2. MOBILE SOURCE EMISSION FORECAST PROCESS 

OKI Travel Demand Model 

Transportation system performance was estimated using the OKI Travel Demand Model 

Version 7.6. The OKI Travel Demand Model is composed of TRANPLAN programs, 

CUBE Voyager programs and a series of FORTRAN programs 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 assignment. 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” highway network with forecasted traffic 

volumes with revised speeds based on specified speed/capacity relationships. 

Travel analysis zones are the basic geographic unit for estimating travel in the OKI 

model. The OKI region is subdivided into 1608 traffic 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 used 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 demand forecasting model are 

population and employment. From these variables, other characteristics including 

households, labor force, and personal vehicles may be derived. OKI utilizes both base 

year (2005) and future year data (2010, 2020 and 2030) in the planning process. Other 

years are interpolated as needed. Planning data are 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 are developed through various methods. 

More detailed explanation of base year and future year 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 base year 2005 and future years 2010, 

2020 and 2030 originate with the 2000 Census of Population 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 county level projections as prepared by 

the respective state data centers (Ohio Department of Development Office of Strategic 

Research, Kentucky State Data Center and Indiana Business Research Center) as control 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

4 

totals. The most current projections (years 2005 to 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 calculated by multiplying household size by 

the projected zonal households. Household size is factored so that, in each county, the 

sum of the zonal populations equals the control total. 

Households 

Base Year Data: Household data for base year 2005 originates with the 2000 Census of 

Population and Housing. Utilizing the geographic information system ArcMap, 

household data at the zonal level for 2000 was derived from the area proportion 

allocation of block level households. Year 2000 household data was updated to 2005 with 

residential building permits issued between January 2000 and December 2004. The 

residential building locations were geocoded in ArcMap, 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 unbuilt units, and subtracting demolitions 

(where data was available). These households were then added to the year Census 2000 

zonal household total to arrive at 2005 households for each TAZ. 

Future Year Data: The preparation of household projections was accomplished by 

calculating the number of households for a projected county population using ratios of 

householders to total population by age specific cohorts derived from the 2000 Census 

for each analysis year. Disaggregation to TAZs was determined by historical trends, 

existing and future land use, topography, flood plain information, availability of land, 

local knowledge and other factors. 

Household Vehicles 

Base and Future Year Data: Base and future year household 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 applied to the TAZs associated with 

each block group. The 2005, 2010, 2020 and 2030 vehicles per household level was held 

at the 2000 level based on the fact that, since 2002, 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 (the number of employed persons in the 

labor force per persons 16 and over). Household data for base year 2005 originates with 

the 2000 Census of Population and Housing. Utilizing 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 force. The labor force projections for 

2005, 2010, 2020 and 2030 were based on the most recent projections of national labor 

force participation rates by age and sex cohorts from 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 eliminate the unemployed to arrive at a 

county employed labor force control total. Employed labor force at the zonal level is 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

5 

calculated by multiplying the labor force participation 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 calculate employment at the zonal level. 

Individual business records containing physical location, 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 the 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 upon the potential for generating trips. 

Future Year Data: For future year employment projection, calculation was first made of 

the employment at the regional level. At the regional 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 region but commute in to work. The 

regional total was disaggregated first to the county level based on historic trends and 

expected changes in the county’s share of the region’s employment and then to the TAZ 

level. Disaggregation to TAZs was determined by historical trends, existing and future 

land use, topography, flood plain information, availability 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 observed traffic volumes for the 

model base year 2005. The modeling network encompasses the entire ozone 

nonattainment area with the exception of Clinton County, Ohio. The modeling network 

also includes Greene, Miami and Montgomery counties in Ohio and the remainder of 

Dearborn County Indiana. The difference between estimated vehicle miles traveled 

(VMT) and 2005 observed VMT is less than 1%. A highway screenline analysis 

compares the screenline observed and simulated traffic 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 Transportation (ODOT), the Kentucky 

Transportation Cabinet, many county and local governments, transportation engineering 

consultants, and OKI. These traffic counts cover nearly 50% percent of the links in the 

OKI portion of the modeling network. The methodology provides consistency with past 

emission inventory and conformity analysis work performed by OKI. 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

6 

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 parameters. Free flow speeds used on 

the highway and transit networks are based on travel time studies performed locally. The 

OKI post-processing program, IMPACT, uses the loaded highway network to generate 

VMT by hour, VMT by speed distribution and VMT by facility type. These tables are 

then included as input into MOBILE6.2. Two separate 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 types as developed by OKI. The main 

source of the data was the permanent traffic counting stations located throughout the OKI 

region for the years of 1998-2002. This data was supplemented with data collected at 

coverage count stations (locations with counts taken 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 1997 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 program performs the appropriate 

summation by area and roadway type as well as regional totals. OKI has also developed 

seasonal conversion factors to adjust traffic volumes 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 conversion factors for June, July and 

August. Further information on OKI’s IMPACT program is documented in the report, 

“Travel Demand Model Summary Reporting and Impact Summary Reporting: 

OKI/MVRPC Travel Demand Model User’s Guide”, OKI 2003. 

Emission Factor Model

OKI’s conformity assessment utilized U.S.EPA’s emissions model MOBILE6.2 to 

develop emission factors for VOC’s, NOX and PM2.5. The MOBILE6.2 input file 

contains local parameters, developed through consultation 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 Model to produce one set of emission 

factors measured in grams per mile for the appropriate calendar year (from 1952 to 

2050). These emission factors are then multiplied by VMT. The methodologies 

incorporated into MOBILE6.2 for estimating emissions are based on methods and 

research conducted by U.S.EPA. OKI’s development of 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. 

 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

7 

3. MOBILE SOURCE EMISSIONS INVENTORY 

Table 1. Mobile Source Emissions by State/County for 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 2.85 2.56

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 7.76 7.07

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 28.07

 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

8 

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 35.35 32.13

NOx 136.73 113.45 54.01 38.17

The mobile source VOC and NOx 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 Cincinnati ozone nonattainment area. 

Table 3 is the mobile source emissions inventory for the Kentucky portion of the 

nonattainment area. At the discretion of the Indiana Department of Environmental 

Management, the Kentucky Division for Air Quality and the Ohio EPA, an additional 

safety margin may be added to the 2008 inventory for the purpose of establishing a motor 

vehicle emission budget (MVEB). The addition of this safety margin would not interfere 

with the SIPs purpose. In the absence of an additional safety margin, the 2008 inventory, 

as presented below, will serve as the (MVEB) for transportation conformity. 

Table 2 

Mobile Source Emissions Inventory for the Indiana and 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 7.76 7.07

NOx 26.64 21.78 11.40 8.27

 

 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

9 

APPENDIX A

MOBILE6.2 Input/Output Files for Indiana Portion of

Nonattainment Area 

 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

10 

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 0.0000 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 0.0047 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 0.0044 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0417 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 0.0452 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 0.0453 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 0.0379 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 0.0375 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 0.0375 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 0.0360 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 0.0363 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 0.0369 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 0.0358 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 0.0374 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 0.0394 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 0.0414 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 0.0433 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 0.0414 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 0.0406 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 0.0396 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 0.0378 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 0.0345 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 0.0353 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 0.0378 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 0.0410 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 0.0422 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 0.0415 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 Cincinnati 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 Cincinnati 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.CSV 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.CSV 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 following 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 levels. 

* 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 Cincinnati 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 levels. 

* 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 0.0000 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 0.0047 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 0.0044 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 0.0092 0.0062 0.0000 0.0000 0.0000 0.0000 0.9846
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

14 

1 16 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0469 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 0.0507 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 0.0506 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 0.0427 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 0.0421 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 0.0421 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 0.0404 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 0.0407 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 0.0414 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 0.0403 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 0.0419 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 0.0439 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 0.0460 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 0.0480 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 0.0460 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 0.0452 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 0.0443 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 0.0425 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 0.0390 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 0.0400 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 0.0428 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 0.0460 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 0.0472 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 0.0464 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 Cincinnati 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 

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.CSV PMDZML.CSV 

PMDDR1.CSV PMDDR2.CSV 
Mobile Source Emissions Inventory for the Cincinnati 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.CSV 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 following 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 levels. 

* 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 REBUILD 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 limit 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 Cincinnati 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 levels. 

* 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 limit 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 Cincinnati 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 0.0000 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 0.0096 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 0.0089 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 0.0043 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0635 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 0.0654 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 0.0675 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 0.0591 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 0.0568 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 0.0568 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 0.0544 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 0.0549 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 0.0559 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 0.0541 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 0.0567 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 0.0599 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 0.0631 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 0.0660 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 0.0630 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 0.0618 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 0.0602 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 0.0573 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 0.0520 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 0.0534 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 0.0572 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 0.0624 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 0.0643 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 0.0632 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 Cincinnati 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 : 

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 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

20 

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 : 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.CSV 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.CSV 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 following 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 levels. 

* 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 Cincinnati 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 REBUILD 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 limit 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 levels. 

* 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 limit of 15 ppm. 
Mobile Source Emissions Inventory for the Cincinnati 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 0.0053 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 0.0050 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 0.0046 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 0.0043 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0679 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 0.0688 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 0.0724 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 0.0689 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 0.0605 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 0.0606 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 0.0580 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 0.0585 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 0.0595 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 0.0576 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 0.0604 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 0.0639 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 0.0673 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 0.0705 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 0.0671 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 0.0659 0.0809 0.5190 0.0000 0.0000 0.0000 0.0000 0.0000
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

23 

2 17 0.0000 0.0000 0.0000 0.2336 0.0081 0.0823 0.0642 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 0.0611 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 0.0555 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 0.0569 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 0.0609 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 0.0666 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 0.0686 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 0.0674 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 Cincinnati 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 : 

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 : 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.CSV 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.CSV PMDZML.CSV 

PMDDR1.CSV PMDDR2.CSV 

DIESEL SULFUR : 43 

******************* End of Run **************************** 

END OF RUN 
Mobile Source Emissions Inventory for the Cincinnati 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 following 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 levels. 

* 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 REBUILD 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 limit 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 levels. 

* 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 Cincinnati 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 limit 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

27 

APPENDIX B

MOBILE6.2 Input/Output Files for Kentucky Portion of 

Nonattainment Area 

 
Mobile Source Emissions Inventory for the Cincinnati 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 0.0011 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 0.0055 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 0.0078 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 0.0101 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 0.0107 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 0.0071 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 0.0122 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 0.0122 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 0.0095 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 0.0092 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 0.0108 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 0.0102 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 0.0047 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 0.0006 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.2411 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 0.2175 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 0.2073 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 0.2077 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 0.2200 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 0.2227 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 0.2160 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 0.2163 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 0.2230 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 0.2182 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 0.2168 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 0.2211 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 0.2337 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 0.2426 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 0.2455 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 0.2449 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 0.2447 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 0.2444 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 0.2418 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 0.2425 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 0.2455 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 0.2462 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 0.2468 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 0.2437 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 Cincinnati 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 counties 

* pre 2006 analysis 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

30 

WITH FIELDNAMES : 

DATABASE EMISSIONS : 2211 1111 

DAILY OUTPUT : 

EMISSIONS TABLE : kyemiss.tb1 

RUN DATA 

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

> post 1999, KY counties of Boone, Campbell and Kenton 

*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 YEARS : 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 

FUEL 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.CSV 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.CSV PMDZML.CSV 

PMDDR1.CSV PMDDR2.CSV 

DIESEL SULFUR : 324 

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

END OF RUN 
Mobile Source Emissions Inventory for the Cincinnati 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 Kenton 

* Reading Hourly VMT distribution from the following 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 levels. 

* 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

32 

* # # # # # # # # # # # # # # # # # # # # # # # # #

 M616 Comment: 

 User has supplied post-1999 sulfur levels. 

* 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 0.0034 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 0.0040 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 0.0057 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 0.0078 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 0.0064 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 0.0060 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 0.0085 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 0.0089 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 0.0057 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 0.0053 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 0.0071 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 0.0067 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 0.0044 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 0.0006 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 0.0244 0.0197 0.0586 0.0201 0.0463 0.0291 0.8003
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

33 

1 23 0.0000 0.0000 0.0000 0.0000 0.0000 0.0014 0.0000 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 0.0000 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 0.2034 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 0.1939 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 0.1906 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 0.1903 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 0.1908 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 0.1934 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 0.1919 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 0.1916 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 0.1920 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 0.1892 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 0.1940 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 0.1976 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 0.2003 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 0.2032 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 0.2008 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 0.2001 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 0.2001 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 0.1973 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 0.1973 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 0.1986 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 0.1982 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 0.2025 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 0.2034 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 0.2035 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 Cincinnati 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 counties 

* post 2005 analysis years, includes annual scenario 

* 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.CSV PMDZML.CSV 

PMDDR1.CSV PMDDR2.CSV 

DIESEL SULFUR : 43 
Mobile Source Emissions Inventory for the Cincinnati 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.CSV 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 following 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 levels. 

* 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 REBUILD FRACTION IS 0.30. 

 M111 Warning: 

 The input dIesel sulfur level of 43.0 ppm exceeds 

 the 2007 HDD Rule diesel sulfur limit 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 Cincinnati 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 levels. 

* 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 limit 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 0.0010 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 0.0068 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 0.0320 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 0.0159 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 0.0081 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 0.0089 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 0.0088 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 0.0082 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 0.0087 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 0.0079 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 0.0078 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 0.0074 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 0.0055 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 0.0005 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 0.0006 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.1521 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 0.1311 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 0.1377 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 0.1381 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 0.1400 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 0.1433 0.1355 0.1788 0.0436 0.0000 0.0000 0.0000 0.0000
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

37 

2 7 0.0000 0.0000 0.0000 0.3704 0.0796 0.0613 0.1406 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 0.1428 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 0.1422 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 0.1380 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 0.1393 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 0.1458 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 0.1463 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 0.1517 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 0.1510 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 0.1505 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 0.1503 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 0.1473 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 0.1480 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 0.1488 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 0.1470 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 0.1520 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 0.1529 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 0.1532 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 Cincinnati 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 counties 

* post 2005 analysis years, includes annual scenario 

* 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 : 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.CSV 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 Cincinnati 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.CSV 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 following 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 levels. 

* 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 REBUILD FRACTION IS 0.30. 

 M111 Warning: 

 The input dIesel sulfur level of 43.0 ppm exceeds 

 the 2007 HDD Rule diesel sulfur limit 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 levels. 

* Reading PM Gas Carbon ZML Levels 

* from the external data file PMGZML.CSV 
Mobile Source Emissions Inventory for the Cincinnati 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 limit 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 0.0017 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 0.0204 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 0.0190 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 0.0205 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 0.0074 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 0.0083 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 0.0098 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 0.0100 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 0.0079 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 0.0072 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 0.0084 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 0.0126 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 0.0057 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 0.0009 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0002 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 0.0000 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 0.1235 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 0.1076 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 0.1081 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 0.1109 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 0.1137 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 0.1182 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 0.1172 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 0.1195 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 0.1164 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 0.1114 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 0.1164 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 0.1233 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 0.1191 0.1118 0.1463 0.0354 0.0000 0.0000 0.0000 0.0000
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

41 

2 14 0.0000 0.0000 0.0000 0.4784 0.0601 0.0420 0.1250 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 0.1240 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 0.1238 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 0.1234 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 0.1198 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 0.1216 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 0.1222 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 0.1184 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 0.1246 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 0.1255 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 0.1263 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 Cincinnati 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 scenario 

* 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 SIZE : 2.5 

MIN/MAX TEMP : 61.0 95.0 

PARTICULATE EF : PMGZML.CSV PMGDR1.CSV PMGDR2.CSV PMDZML.CSV 

PMDDR1.CSV PMDDR2.CSV 

DIESEL SULFUR : 43 

********************* Annual Scenario Section ***************** 

SCENARIO RECORD : KY EMISSIONS - CY20xx 

CALENDAR YEAR : 2020 

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.CSV PMDZML.CSV 

PMDDR1.CSV PMDDR2.CSV 
Mobile Source Emissions Inventory for the Cincinnati 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 following 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 levels. 

* 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 REBUILD FRACTION IS 0.30. 

 M111 Warning: 

 The input dIesel sulfur level of 43.0 ppm exceeds 

 the 2007 HDD Rule diesel sulfur limit 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 levels. 

* 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 Cincinnati 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 limit 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

45 

APPENDIX C

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

Nonattainment Area 

 
Mobile Source Emissions Inventory for the Cincinnati 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 0.0006 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 0.0078 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 0.0114 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 0.0104 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 0.0114 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 0.0106 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 0.0117 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 0.0124 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 0.0119 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 0.0116 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 0.0103 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 0.0098 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 0.0059 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 0.0001 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.2765 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 0.2602 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 0.2418 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 0.2628 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 0.2843 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 0.2941 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 0.2868 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 0.2857 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 0.2924 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 0.2873 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 0.2850 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 0.2932 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 0.2945 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 0.2877 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 0.2897 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 0.2905 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 0.2880 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 0.2881 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 0.2871 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 0.2840 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 0.2813 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 0.2833 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 0.2837 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 0.2843 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 Cincinnati 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 analysis 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 decoding project. 

* MOBILE6 default distributions are used for the remaining 

* 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 Cincinnati 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 Warren counties, 

* OBD program initiated on 1/5/04 

* created 05/30/06 by ajr, new OEPA inputs for ozone, 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 Cincinnati 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 & GC 

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 PHASE-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 COMPLIANCE : 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 Cincinnati 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.CSV 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.CSV 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 following 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 following external 

* data file: OHREG.D 

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

* Reading non-default I/M CUTPOINTS from the following external 

* data file: CUTPOINT.D 

 M616 Comment: 

 User has supplied post-1999 sulfur levels. 

 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 Cincinnati 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 Blend Market Share: 0.420 

 Ether Blend Oxygen Content: 0.000 Alcohol Blend Oxygen Content: 0.036 

 Alcohol Blend 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 Blend Market Share: 0.420 

 Ether Blend Oxygen Content: 0.000 Alcohol Blend Oxygen Content: 0.036 

 Alcohol Blend 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 0.0009 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 0.0063 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 0.0075 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 0.0079 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 0.0081 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 0.0082 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 0.0100 0.0121 0.0307 0.0413 0.0367 0.0979 0.0160 0.7508
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

52 

1 8 0.0000 0.0000 0.0000 0.0005 0.0022 0.0024 0.0102 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 0.0079 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 0.0079 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 0.0088 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 0.0084 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 0.0062 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 0.0005 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.2335 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 0.2050 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 0.1961 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 0.2127 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 0.2334 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 0.2417 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 0.2399 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 0.2392 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 0.2402 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 0.2351 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 0.2373 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 0.2455 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 0.2418 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 0.2413 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 0.2415 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 0.2417 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 0.2404 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 0.2394 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 0.2389 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 0.2377 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 0.2359 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 0.2387 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 0.2392 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 0.2396 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 Cincinnati 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,low 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 Cincinnati 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.CSV 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.CSV 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 following 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 following external 

* data file: OHREG.D 

 M616 Comment: 

 User has supplied post-1999 sulfur levels. 

 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 REBUILD FRACTION IS 0.10. 

 M111 Warning: 

 The input dIesel sulfur level of 43.0 ppm exceeds 

 the 2007 HDD Rule diesel sulfur limit 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

55 

 Ether Blend Market Share: 0.000 Alcohol Blend Market Share: 0.420 

 Ether Blend Oxygen Content: 0.000 Alcohol Blend Oxygen Content: 0.036 

 Alcohol Blend 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 limit 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 Blend Market Share: 0.420 

 Ether Blend Oxygen Content: 0.000 Alcohol Blend Oxygen Content: 0.036 

 Alcohol Blend 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 0.0010 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 0.0060 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 0.0097 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 0.0084 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 0.0074 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 0.0076 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 0.0103 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 0.0104 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 0.0074 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 0.0074 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 0.0090 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 0.0084 0.0120 0.0165 0.0444 0.0325 0.0995 0.0326 0.7506
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

56 

1 13 0.0000 0.0000 0.0000 0.0000 0.0000 0.0007 0.0055 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 0.0007 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.2361 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 0.2145 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 0.2082 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 0.2170 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 0.2334 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 0.2416 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 0.2359 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 0.2368 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 0.2408 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 0.2355 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 0.2336 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 0.2408 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 0.2435 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 0.2460 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 0.2468 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 0.2475 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 0.2453 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 0.2438 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 0.2445 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 0.2420 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 0.2373 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 0.2416 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 0.2421 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 0.2431 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 Cincinnati 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,low 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 
Mobile Source Emissions Inventory for the Cincinnati 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.CSV PMDZML.CSV 

PMDDR1.CSV PMDDR2.CSV 

DIESEL SULFUR : 43 

******************* Annual Scenario Section *************** 

SCENARIO RECORD : Ohio Emissions - CY20xx 

CALENDAR YEAR : 2015 

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.CSV 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 following 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 following external 

* data file: OHREG.D 

 M616 Comment: 

 User has supplied post-1999 sulfur levels. 

 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 REBUILD FRACTION IS 0.10. 

 M111 Warning: 

 The input dIesel sulfur level of 43.0 ppm exceeds 

 the 2007 HDD Rule diesel sulfur limit 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 Cincinnati 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 Blend Market Share: 0.420 

 Ether Blend Oxygen Content: 0.000 Alcohol Blend Oxygen Content: 0.036 

 Alcohol Blend 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 limit 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 Blend Market Share: 0.420 

 Ether Blend Oxygen Content: 0.000 Alcohol Blend Oxygen Content: 0.036 

 Alcohol Blend 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 0.0010 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 0.0062 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 0.0103 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 0.0081 0.0121 0.0164 0.0478 0.0326 0.1078 0.0460 0.7230
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

60 

1 5 0.0000 0.0000 0.0000 0.0000 0.0009 0.0016 0.0086 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 0.0085 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 0.0091 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 0.0096 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 0.0085 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 0.0082 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 0.0080 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 0.0078 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 0.0058 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 0.0009 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.0000 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 0.2243 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 0.1974 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 0.1912 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 0.2008 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 0.2159 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 0.2248 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 0.2186 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 0.2189 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 0.2228 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 0.2166 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 0.2179 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 0.2274 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 0.2302 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 0.2334 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 0.2339 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 0.2346 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 0.2324 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 0.2303 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 0.2318 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 0.2293 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 0.2237 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 0.2289 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 0.2294 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 0.2307 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 Cincinnati 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,low 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.CSV 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.CSV PMDZML.CSV PMDDR1.CSV PMDDR2.CSV 

DIESEL SULFUR : 43 

******************* End of Run **************************** 
Mobile Source Emissions Inventory for the Cincinnati 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 following 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 following external 

* data file: OHREG.D 

 M616 Comment: 

 User has supplied post-1999 sulfur levels. 

 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 REBUILD FRACTION IS 0.10. 

 M111 Warning: 

 The input dIesel sulfur level of 43.0 ppm exceeds 

 the 2007 HDD Rule diesel sulfur limit 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 Blend Market Share: 0.420 

 Ether Blend Oxygen Content: 0.000 Alcohol Blend Oxygen Content: 0.036 

 Alcohol Blend 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 Cincinnati 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 limit 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 Blend Market Share: 0.420 

 Ether Blend Oxygen Content: 0.000 Alcohol Blend Oxygen Content: 0.036 

 Alcohol Blend 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

64 

 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

65 

APPENDIX D

Air Quality Impact Summary for the OKI Portion of the 

Nonattainment Area and Emissions by State/County 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

66 

 

2005 Output Report (R7803)

 DAILY AIR QUALITY IMPACT FOR OKI 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. Emissions 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. Emissions 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

67 

2008 Output Report (R7803)

 DAILY AIR QUALITY IMPACT FOR OKI 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. Emissions 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. Emissions 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

68 

2015 Output Report (R7803)

 DAILY AIR QUALITY IMPACT FOR OKI 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. Emissions 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. Emissions 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

69 

2020 Output Report (R7803)

 DAILY AIR QUALITY IMPACT FOR OKI 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. Emissions 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. Emissions 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 Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

70 

 
Mobile Source Emissions Inventory for the Cincinnati 8-hour Ozone Nonattainment Area, October 2009 

71 

Appendix E 

Clinton County Air Quality Analyis (provided by ODOT) 

 

Clinton County 

OZONE YEAR 2005 

 

 VOC NOX 

 FUNCTIONAL HPMS ANNUAL 2005 POLLUTANT 2005 POLLUTANT 

 CLASSIFICATION 2005 GROWTH 2005 VOC EF BURDEN NOX EF 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 3.156 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 0.962 

 

 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 Cincinnati 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 EF 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 2.414 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 0.699 

 

 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 Cincinnati 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 EF 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 1.072 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 0.353 

 

 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 Cincinnati 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 EF 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 0.687 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 0.251 

 

 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 Cincinnati 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 every 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 system 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 have 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 plan (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, calculating, 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 Office 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 used 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 sources 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 category

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 Industrial” for the following fuels: coal, distillate oil, 

natural gas, and liquefied petroleum gas (LPG). Use 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 following 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 combustions, subtract reported source totals from the 

total statewide fuel consumption by querying the total process rates for the various SCC codes using 

the ACCESS data tables at K:\OAQ_INV\Steptool\Stptl_02.mdb. The remaining number is the area 

source fuel consumption for the state. 

3. To distribute the remaining fuel to the county level, calculate the ratio of county to state employment 

for the manufacturing sector by dividing the number 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 following 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 manufacturing under the paid employees’ column 

4. Multiply the ratio calculated above in step 3 by the area source fuel consumption 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 the various fuels for industrial manufacturing found 

in AP-42, Fifth Edition, Volume 1, Chapter 1, External Combustion Sources at 

http://www.epa.gov/ttn/chief/ap42/ch01/. 

Sub-Category 1.2: Commercial/Institutional Fuel Combustion 

SCC: 2103004000, 2103005000, 2103006000, 2103007000 

Follow these steps when calculating emissions from 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 combustions, subtract reported source totals from the 

total statewide fuel consumption by querying the total process rates for the various fuels using the 

SIC codes greater than 4999 using the ACCESS data tables at K:\OAQ_INV\Steptool\Stptl_02.mdb. 

These are the SIC codes that identify all the commercial/institutional area sources. 

3. To distribute the remaining fuel to the county level, calculate the ratio of county to state employment 

for the commercial/institutional sector by dividing the number of commercial/institutional employees 

for each county by the number of commercial/institutional 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 navigate through the U.S. Census Bureau’s website. 

4. Multiply the ratio calculated above in step 3 by the area source fuel consumption 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 the 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 consumption for “Residential” for the following fuels: coal, distillate oil, natural 

gas, and liquid petroleum gas. 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. 

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 household 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 Characteristics” and select “show more” 

e. On the left hand side, select “change 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 above in step 3 by the area residential fuel 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 appropriate EPA emission factors for 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 emissions 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 following 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) NATIONAL 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 (fireplace without inserts, fireplaces with inserts and 

woodstoves). 

3. To distribute to the county level for the three categories above, calculate a ratio of county to state 

using the statewide total of households and the county 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 process rate by the appropriate EPA emission factors for each of the 

categories using the EIIP, Volume 3, Chapter 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) 

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S-006-OAQ-R-MO-08-S-R1 

2. Multiply the per capita consumption factor calculated 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 following 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 querying the total process rates for the SCC 30203202 

(straight-dough) and SCC 30203201 (sponge-dough) using the ACCESS data tables at 

K:\OAQ_INV\Steptool\Stptl_02.mdb. 

4. Multiply the remaining process rate by the straight-dough emission factor of .5 lbs VOC/1,000 pounds 

baked found in the EIIP, Volume 3, Area Source Method 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 Indiana 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 following 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 paints 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 

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Note: As of the date of this SOP, the following 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 coating. 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 above 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 employees from the reported sources using the SIC 7532- 

Body Repair and Paint Shops using the ACCESS data tables at K:\OAQ_INV\Steptool\Stptl_02.mdb. 

Subtract this number from the county 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 following 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/volume03/archsfc.pdf and the county 

employment found above in step 1 to calculate 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 the 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 paints 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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 Note: As of the date of this SOP, the following 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 “Traffic 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/policy/ohim/hs04/htm/sf2.htm. 

3. Calculate the emission factor for Indiana by dividing 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 the 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 

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* Use the National default emission factor because the reporting sources are low. 

** Emissions reported in point source 

2. Divide the reported VOC emissions for each of the SIC’s by the reported employment for each SIC. 

Use this number for the emission factor. 

3. Subtract the number of reported 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 found 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 industrial surface coating using the default emission 

factor: 

1. Calculate industrial surface coating emissions using the default emission factor 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 Manufacturing 0.600 lbs VOC/person 

24-01-100-000 Industrial Maintenance Coatings 0.800 lbs VOC/person 

24-01-200-000 Other Special Purpose 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 

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S-006-OAQ-R-MO-08-S-R1 

39 Miscellaneous manufacturing 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 manufacturing 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:\OAQ_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 multiplying 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 number 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 counties, 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\Steptool\Stptl_02.mdb and subtract this number from 

the county total. 

4. Multiply the process rate for each of the counties above by the emission factor to calculate for VOC 

emissions. 

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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 through 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 population 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 through 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 emissions and number of reported employees for all SIC’s 

beginning with 30 using the ACCESS data tables 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 Air 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 Employment from the U.S. Census Bureau’s website 

http://www.census.gov. 

Note: As of the date of this SOP, the following steps 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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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 reporting 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 state and county from the Indiana Department of 

Transportation’s, Division of Roadway Management Section. 

3. Divide the county roadway miles by the state roadway 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 EIIP, Volume 3, Chapter 17, Asphalt 

Paving http://www.epa.gov/ttn/chief/eiip/techreport/volume03/iii17_apr2001.pdf. 

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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 specific emission factor. Develop the factor using a 

methodology that includes the retrieval of information of pesticides used, an emission factor for each 

pesticide used, a calculation about the inert ingredients 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 emissions from crop oil concentrates obtained in the 

pesticide Excel table, pesticides, and solvent carriers 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 the Federal Highway Administration, U.S. Department 

of Transportation http://www.fhwa.dot.gov/policy/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. Census 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 the 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 multiplying by the number of gallons sold statewide found above in 

step 1. 

5. EPA guidance suggests that only 25% of all gasoline 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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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 submerged 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 emissions 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 document Public Meeting to Consider Approval of 

California’s Portable Gasoline-Container Emissions Inventory. Use the excel spreadsheet found at 

K:\OAQ_INV\Inv\Area Source\Gasoline.zip to calculate the emissions for permeation, diurnal, and 

transport. Both the Spillage and Vapor losses are estimated in the nonroad emissions inventory by 

EPA models. 

2. Using the survey results below in Table 1, estimate 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\GasCans.xls, insert the number of occupied 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% 

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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, estimate 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 both residential and commercial by using the emission 

rates given in the California document. Use 1.57g/gal/day for plastic containers and 0.6g/gal/day for 

metal containers. Insert the numbers for both residential and commercial into the excel spreadsheet at 

K:\OAQ_INV\Inv\Area Source\ Gasoline.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/policy/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. Census 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 the 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 tanks 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. Filter 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 tanks 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 tanks 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 counties 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 factors 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 the Federal Highway Administration, U.S. Department 

of Transportation http://www.fhwa.dot.gov/policy/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. Census 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 files supplied from the mobile model. Table 1 and Table 

2 show examples of how the emission factors for 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 Counties, 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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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 Fueling (Stage II) – Spillage 

SCC: 2501060103 

Follow these steps when calculating emissions from vehicle fueling – Spillage: 

1. Find the amount of gasoline sold in Indiana at the Federal Highway Administration, U.S. Department 

of Transportation http://www.fhwa.dot.gov/policy/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. Census 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 emissions from underground tank breathing: 

1. Find the amount of gasoline sold in Indiana at the Federal Highway Administration, U.S. Department 

of Transportation http://www.fhwa.dot.gov/policy/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. Census 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 the Federal Highway Administration, U.S. Department 

of Transportation http://www.fhwa.dot.gov/policy/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. Census 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, Chapter 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/cgi-bin/cbpnaic/cbpsel.pl. 

 Note: Use the steps in 3.2-1 to navigate 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, Fifth 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 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 commercial 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, Fifth 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 residential 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, Fifth 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 leaf burning and a per capita for brush 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 capita 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 following 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 waste generated to account for the percentage of forest 

in each county. The percentages come from a document 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 residential waste incineration 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 generated by rural population 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 residential 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 emission factors in FIRE 6.25 using the SCC code 

2630020000. 

Sub-Category 5.4: Treatment, Storage, and Disposal Facilities 

SCC: 2640000004 

Follow these steps when calculating emissions from 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 the 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 checklist 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 electronically at K:\OAQ_INV\Inv\Area Source. 

The Branch Contact for the Air Programs Branch and 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 Assurance / 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 CFR 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 

25