·INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT 

We Protect Hoosiers and Our Environment. 

Michael R. Pence 1 00 North Senate Avenue 

Governor Indianapolis, Indiana 46204 

(317) 232-8603 

Thomas W. Easterly Toll Free (800) 451-6027 

Commissioner www.idem.IN.gov 

Ms. Susan Hedman 

Regional Administrator 

U.S. Environmental Protection Agency 

Region 5 

77 West Jackson Boulevard 

Chicago, IL 60604-3950 

Dear Ms. Hedman: 

February 1, 2013 

Re: MOBILE6.2 to MOVES MVEB 

Replacement Update to the Maintenance 

Plan for the 1997 8-Hour Ozone Standard 

for Lake and Porter Counties, Indiana 

The Indiana Department of Environmental Management (IDEM) submits the 

enclosed MOBILE6.2 to Motor Vehicle Emissions Simulator (MOVES) Motor Vehicle 

Emissions Budget (MVEB) replacement update to the maintenance plan for the 1997 8-

hour ozone standard for Lake and Porter counties, Indiana. The United States 

Environmental Protection Agency (U.S. EPA) approved the Request for Redesignation 

and Maintenance Plan for Ozone Attainment in the 8-Hour Ozone Nonattainment Area, 

Lake and Porter Counties, Indiana submitted by IDEM on June, 5, 2009, with an effective 

date of May 11, 2010. IDEM requests that U.S. EPA process this final submittal for 

approval into Indiana's State Implementation Plan. 

IDEM provided an opportunity for a public hearing on the MVEB replacement 

update to the maintenance plan for the 1997 8-hour ozone standard for Lake and Porter 

counties, Indiana, if a public hearing request was received by January 14, 2012. A 

hearing was scheduled for January 23, 2013. No request for a public hearing was 

received and the hearing was cancelled. In addition, IDEM received no comments during 

the public notice process. Documents related to the public participation process are 

included in Appendix C of this submittal. 

Recycled Paper G) An Equal Opportunity Employer Please Recycle O 
Ms. Hedman 

Page 2 

This MOBILE6.2 to MOVES MVEB replacement update incorporates onroad 

emission estimates and revised MVEBs using U.S. EPA's recently adopted MOVES 

model. The onroad emission estimates were calculated using the MOVES-based 

emission factors and data extracted from the Lake and Porter counties, Indiana, area's 

travel-demand model. 

MVEBs are being revised in anticipation of the mandatory use of the MOVES 

model in future transportation conformity determinations. Preliminary use of the new 

model indicates that emission estimates can be considerably different than similar 

calculations using MOBILE6.2, which was used to create the MVEBs in the original1997 

8-hour ozone maintenance plan. 

On road safety margins, established through the interagency consultation process, 

are included for nitrogen oxides (NOx) and volatile organic compounds (VOCs). These 

onroad safety margins are allocated to onroad emission estimates in order to account for 

the wide array of assumptions that are factored into the calculation process. With the 

addition of on road safety margins applied to mobile sources, the Lake and Porter 

counties, Indiana, ozone maintenance area will continue to remain well below the overall 

safety margins for all sources. MVEBs are also constrained to ensure that total NOx and 

VOC emissions (i.e., all source categories) do not exceed attainment year emissions to 

ensure continued maintenance of the 1997 8-hour ozone standard. 

This submittal consists of one (1) hard copy of the required documentation. An 

electronic version of the submittal in PDF format that is identical to the hard copy has 

been sent to Pamela Blakley, Chief of U.S. EPA Region 5's Control Strategies Section. 

IDEM respectfully requests that U.S. EPA proceed with review of the MOBILE6.2 

to MOVES MVEB replacement update and revised transportation conformity budgets and 

approval into Indiana's State Implementation Plan for the Lake and Porter counties, 

Indiana, maintenance area under the 1997 8-hour ozone standard. If you have any 

questions or need additional information, please contact Scott Deloney, Chief, Air 

Programs Branch, at (317) 233-5694. 

KB/sad/sms 

Enclosures: 

Sincerely, 

I . . ? 

:)v:kl (.),"'-M. 6~ 

Keith Baugues 

Assistant Commissioner 

Office of Air Quality 

MOBILE6.2 to MOVES MVEB Replacement Update to the Request for 

Redesignation and Maintenance Plan for Ozone Attainment in the 8-Hour Ozone 

Nonattainment Area for Lake and Porter Counties, Indiana and Appendices. 

Electronic MOVES-based modeling input and output data files. 
Ms. Hedman 

Page 3 

cc: George Czerniak, U.S. EPA Region 5 (no enclosures) 

John Mooney, U.S. EPA Region 5 (no enclosures) 

Doug Aburano, U.S. EPA Region 5 (w/ enclosures) 

Steve Rosenthal, U.S. EPA Region 5 (no enclosures) 

Ed Doty, U.S. EPA Region 5 (w/ enclosures) 

Anthony Maietta, U.S. EPA Region 5 (no enclosures) 

John Swanson, NIRPC (w/ enclosures) 

Bill Brown, NIRPC (w/ enclosures) 

Keith Baugues, IDEM-OAQ (no enclosures) 

Scott Deloney, IDEM (no enclosures) 

Shawn Seals, IDEM (w/ enclosures) 
This page intentionally left blank. 
Onroad Emissions MOBILE6.2 to 

MOVES Replacement Submittal 

For the Lake and Porter Counties, 

Indiana, Maintenance Area under 

the 1997 8-Hour Ozone Standard 

December 2012 

Final 
This page intentionally left blank 
Introduction 

On June 5, 2009, the Indiana Department of Environmental Management (IDEM) submitted a 

Request for Redesignation and Maintenance Plan for Ozone Attainment in the 8-Hour Ozone 

Nonattainment Area, Lake and Porter Counties, Indiana. The United States Environmental 

Protection Agency (U.S. EPA) subsequently approved the Indiana redesignation of Lake and Porter 

counties, Indiana, to attainment for the 1997 8-hour ozone standard on May 11, 201 0 (7 5 FR 

26113). Onroad emissions for the June 5, 2009, submittal were calculated using MOBILE6.2. U.S. 

EPA has encouraged mobile source stakeholders to transition to the new Motor Vehicle Emissions 

Simulator (MOVES) model as expeditiously as possible. Therefore, IDEM is providing this 

MOBILE6.2 to MOVES replacement update to the previously submitted 1997 8-hour ozone 

maintenance plan for the Lake and Porter counties, Indiana, ozone maintenance area that 

incorporates MOVES-based omoad emissions. 

Emission Inventory 

Table 4.1 was included without title in Appendix C of the original Redesignation Petition and 

Maintenance Plan. Table 4.1 -A (to be considered a replacement of the table included in 

Appendix C) has been revised to incorporate updated onroad emission estimates for nitrogen oxides 

(NOx) and volatile organic compounds (VOCs) for the years 2006,2010, and 2020; it results in a 

different overall safety margin for the area. 

Table 4.1 

Comparison of 2006 Estimated and 2010 and 2020 Projected Emission Estimates in Tons 

Per Summer Day, Lake and Porter 1997 8-Hour Ozone Nonattainment Area (MOBILE6.2-

based Onroad Emissions) 

Sector 2006NO, 2010NOx 2020 NOx 

Area 6.45 6.59 6.77 

Nomoad 31.17 28.50 21.37 

Omoad 6\W9 ~ -l--l-,9;1 

Point 126.15 110.49 114.75 

Total ;!;!i\.86 l84.;!i! 154.86 

Sector 2006VOC 2010VOC 2020 voc 

Area 32.47 28.80 29.24 

Nomoad 17.14 14.11 12.22 

Omoad ~ ~ ~ 

Point 19.04 18.18 22.25 

Total 83$7 um ~ 

1 
Table 4.1-A 

Comparison of2006 and 2010 Estimated and 2020 Projected Emission Estimates in Tons 

Per Summer Day, Lake and Porter 1997 8-Hour Ozone Maintenance Area (MOVES-based 

Onroad Emissions) 

Sector 2006 NOx 2010 NOx 2020 NOx 

Area 6.45 6.59 6.77 

Nomoad 31.17 28.50 21.37 

Omoad 49.64 47.26 16.69 

Point 126.15 110.49 114.75 

Total 213.41 192.84 159.58 

Sector 2006 voc 2010 voc 2020VOC 

Area 32.47 28.80 29.24 

Nomoad 17.14 14.11 12.22 

Omoad 17.25 13.99 5.99 

Point 19.04 18.18 22.25 

Total 85.90 75.08 69.70 

Onroad emission estimates in Table 4.1 - A were calculated using U.S. EPA's MOVES modelproduced emission factors and data extracted from the area's travel-demand model. The 

MOVES model implements a significantly different approach to emissions estimation than the 

previous model (MOBILE6.2). Preliminary use of the MOVES model indicates that emission 

estimates can be considerably different than similar calculations using MOBILE6.2, which was 

used to create the original MVEBs for the Lake and Porter counties, Indiana, 1997 8-hour ozone 

nonattainment area. A general summary of the MOVES methodology used in this area can be 

found in Appendix A. In addition, MOVES input and output files are being provided 

electronically with this submittal. Growth and control strategy assumptions for non-mobile 

sources (i.e. area, nomoad, and point) from the original submittal for the years 2006, 2010, and 

2020 were developed before the economic challenges of the last several years. Because of this, 

the factors included in the original submittal may project more growth than will actually occur in 

the future. As a result, the growth and control strategy assumptions for the non-mobile sources 

for the years 2006, 2010, and 2020 continue to be valid and do not affect the overall conclusions 

of the plan. 

Onroad safety margins have been included for omoad emission estimates to accommodate the 

wide array of assumptions that are factored into the calculation process. Since assumptions 

change over time, it is necessary to have an onroad safety margin that will accommodate the 

impact of refined assumptions in the process. The plan continues to meet all applicable Clean 

Air Act (CAA) requirements as the revised emission inventories clearly illustrate that total NOx 

and VOC emissions in the Lake and Porter counties, Indiana, 1997 8-hour ozone maintenance 

area will continue to decline leading to local reductions between 2006 (base year) and 2010 

(maintenance plan interim budget year), as well as 2006 (base year) and 2020 (maintenance plan 

horizon budget year). 

2 
Transportation Conformity Budgets 

Table 5.1 was included on Page 24 of the original Redesignation Petition and Maintenance Plan 

for the Lake and Porter counties, Indiana, 1997 8-hour ozone maintenance area. Table 5.1 -A (to 

be considered a replacement of Table 5.1) has been revised to incorporate U.S. EPA's MOVES 

model-produced emission factors and data extracted from the region's travel-demand model. 

Table 5.1 

Emission Estimations for On-Road Mobile Sources for the 

Lali:e and Pot·ter 1997 8-Hour Ozone Nonattainment At·ca (MOBILE6.2-based Onroad 

Emissions) 

Lake & Porter 2006 2010 2020 

VMT (miles/day) 19,141,485 21,194,922 24,958,812 

VOC (tons/day) +4--m, ~ ~ 

NOx (tons/day) ~ ~ -l--h9f 

Table 5.1- A 

Emission Estimations for On-Road Mobile Sources for the 

Lake and Porter 1997 8-Hom· Ozone Maintenance At·ca (MOVES-based Onroad 

Emissions) 

Lake & Porter 2006 2010 2020 

VOC (tons/day) 17.25 12.16 5.21 

NOx (tons/day) 49.64 41.09 14.52 

Table 5.2 was also included on Page 24 of the original Redesignation Petition and Maintenance 

Plan for the Lake and Porter counties, Indiana, 1997 8-hour ozone maintenance area. Table 5.2 -

A (to be considered a replacement of Table 5.2) has been revised to incorporate MVEBs calculated 

using U.S. EPA's MOVES model-produced emission factors and data extracted from the region's 

travel-demand model as detailed in Table 5.1 -A. 

Table 5.2 

Motor Vehicle Emission Budgets for the 

Lake and Porter 1997 8-Hour Ozone Nonattainment Area (MOBILE6.2-based Onroad 

Emissions) 

Lake & Porter 2010 2020 

VOC (tons/day) ~ eA 

NOx (tons/day) 4(}.6 -1-U} 

3 
Table 5.2- A 

Motor Vehicle Emission Budgets for the 

Lake and Porter 1997 8-Hour Ozone Maintenance Area (MOVES-based Onroad 

Emissions) 

Lal{e & Porter 2010 2020 

VOC (tons/day) 13.99 5.99 

NOx (tons/day) 47.26 16.69 

Through the interagency consultation process, it was determined that a maintenance plan interim 

year budget of 2010 and a horizon year budget of 2020, would be appropriate. The interagency 

consultation group approved omoad margins of safety of fifteen percent (15%) for both VOC and 

NOx omoad emission estimates for the years 2010 and 2020. A summary of this interagency 

consultation discussion can be found in Appendix B. These revised emission inventories clearly 

illustrate that onroad VOC and NOx emissions in the Lake and Porter counties, Indiana, 1997 8-

hour ozone maintenance area will continue to decline leading to local reductions between 2006 

(base year) and 2010 (maintenance plan interim budget year), as well as 2006 (base year) and 2020 

(maintenance plan horizon budget year). 

Furthermore, when compared to the overall safety margin as defined in the Code of Federal 

Regulations (CFR) at 40 CFR 93 .I 01, it is evident the omoad safety margin allocation is 

reasonable and appropriate. More specifically, even with the allocation of an omoad safety margin 

to mobile sources, emissions will continue to remain well below the overall safety margin for all 

sources as detailed in Table 4.1 - A. MVEBs are constrained to ensure that the total emissions 

(i.e., all source categories) do not exceed the 2006 attaimnent year emissions of either VOC or 

NOx, thereby ensuring continued maintenance ofthe 1997 8-hour ozone standard. 

Conclusion 

This MOBILE6.2 to MOVES replacement update to the previously submitted Request for 

Redesignation and Maintenance Plan.for Ozone Attainment in the 8-Hour Ozone Nonattainment 

Area, Lake and Porter Counties, Indiana incorporates omoad emission estimates and a revised 

MVEB using U.S. EPA's recently adopted MOVES model. MVEBs have been revised in 

anticipation ofthe mandatory use of the MOVES model in future transportation conformity 

determinations. The omoad emission estimates were calculated using the MOVES-based emission 

factors and data extracted from the area's travel-demand model. Onroad safety margins for VOCs 

and NOx, established through the interagency consultation process, are included in order to account 

for the wide array of assumptions that are factored into the calculation process. MVEBs are also 

constrained to ensure that total VOC and NOx emissions (i.e., all source categories) do not exceed 

attainment year (2006) emissions to ensure continued maintenance of the 1997 8-hour ozone 

standard. With the addition of MOVES-based onroad safety margins applied to mobile sources, 

the Lake and Porter counties, Indiana, ozone maintenance area will continue to remain well below 

the overall safety margins for all sources into the future. As such, the 1997 8-hour ozone 

maintenance plan for Lake and Porter counties, Indiana, continues to meet all applicable CAA 

requirements. 

4 
Appendix A 

Lake and Porter Counties, Indiana, 

Maintenance Area MOVES 

Methodology 
This page left intentionally blank 
Lake and Porter Counties 

MOVES2010a Input Data and 

Parameters 

INDOT Planning Contract 

Final Report 

October 2, 2012 

CDMih Sm1 
Table of Contents 

Overview .............................................................................................................................. 1 

Vehicle Age Distribution ....................................................................................................... 1 

Vehicle Population ................................................................................................................ 2 

Meteorological Data .............................................................................................................. 4 

Default VMT Distributions ..................................................................................................... 4 

Default Hourly Distributions .................................................................................................. 5 

Default Daily and Monthly Distributions ................................................................................ 6 

Ramp Fractions .................................................................................................................... 6 

LIST OF TABLES 

Table 1: MOVES2010a Source Type Codes ............................................................................. 1 

Table 2: MOVES2010a Road Type Codes ................................................................................ 1 

Table 3: Distribution of MOBILE 6.2 Light Duty Trucks into MOVES Source Types ................... 3 

Table 4: Inventory of Permanent Count Stations ....................................................................... 5 

LIST OF APPENDICES 

Appendix A- MOVES2010a Input Settings and Assumptions 

Appendix B- Vehicle Age Distributions for Lake and Porter Counties 

Appendix C- Vehicle Populations for Lake and Porter Counties 

Appendix D- Meteorological Data for Lake and Porter Counties 

Appendix E- Default Statewide Factors 

Appendix F- Statewide Default Hourly Distribution Factors 

Appendix G- Statewide Default Daily Distribution Factors 

Appendix H- Statewide Default Monthly Distribution Factors 

Appendix I - Ramp Fractions 
Overview: 

This report is being written to document the input parameters for a set of MOVES201 Oa 

runs for the Lake and Porter Counties 8-hour Ozone Maintenance Area and the Lake 

and Porter Counties PM 2.5 non-attainment area. This report contains a discussion on 

the intended input settings used in MOVES2010a and the development of the input 

datasets. These MOVES201 Oa runs are intended to develop a default set of emission 

rates that can be used for conformity determination and is part of a statewide effort being 

conducted by the Indiana Department of Transportation (IN DOT). 

Throughout this report references are made to MOVES 201 Oa codes for two types of 

data. The values for the source type codes are shown in Table 1. The values for the 

road type codes are shown in Table 2. MOVES201 Oa input settings and assumptions for 

this effort are shown in Appendix A. 

Table 1: MOVES2010a Source Type Codes 

sourcetypeid Description 

11 Motorcycles 

21 Passenger Car 

31 Passenger Truck 

32 Light Commercial Truck 

41 Intercity Bus 

42 Transit Bus 

43 School Bus 

51 Refuse Truck 

52 Single Unit Short-haul Truck 

53 Single Unit Long-haul Truck 

54 Motor Home 

61 Combination Short-haul Truck 

62 Combination Long-haul Truck 

Table 2: MOVES2010a Road Type Codes 

roadtypeid 

Vehicle Age Distribution: 

1 

2 

3 

4 

5 

Description 

Off Network 

Rural Restricted Access 

Rural Unrestricted Access 

Urban Restricted Access 

Urban Unrestricted Access 

The vehicle age distributions for MOVES source types 21, 31, and 32 (cars, passenger 

trucks, and light commercial vehicles respectively) were developed through an analysis 

of Indiana's 2009 vehicle registration data. The analysis was performed by Eastern 

Research Group (ERG) under contract to the Lake Michigan Air Directors Consortium 

(LADCO). ERG was provided with vehicle identification numbers (VIN) for vehicles in 

Indiana. 
There were approximately 6.37 million VINs in the statewide data set. Out of these, 

approximately 1.3 million returned errors. Of these, approximately 200,000 errors were 

deemed non-critical. This means that the model year and vehicle type assigned to the 

records were most likely correct despite there being an error in the VIN decoding. These 

records were included in ERG's analysis. The remaining errors were considered critical 

enough to call into question the accuracy of the model year and vehicle types. These 

critical errors were excluded from ERG's analysis. 

In all, approximately 5.2 million VINs from around the state were used in the analysis. 

Each VIN was associated to a specific county. ERG then developed age distributions for 

each county in the state along with seven combination areas comprised of two or more 

counties each. Additional information on the methodology used to develop the vehicle 

age distributions can be found in a May 28, 2010 report written by ERG for LADCO titled 

MOBILE6 and MOVES Registration Distribution Calculations for Indiana Registration 

Data. Each set of age distributions was provided in both MOBILE6 and MOVES formats. 

The MOVES formatted data will be used for these MOVES201 Oa runs. 

Due to limitations in ERG's VIN decoder, it was not possible to develop vehicle age 

distributions for any source types other than 21, 31, and 32 from the vehicle registration 

data. For all other source types, MOVES201 Oa default vehicle age distributions specific 

to each source types were used. This includes motorcycles and all heavy vehicles. 

Vehicle age distributions for all source types were kept constant for all future years. The 

vehicle age distributions for Lake and Porter Counties as a combined area are shown in 

Appendix B of this report. 

Vehicle Population: 

The vehicle populations for source types 21, 31, and 32 were developed directly from 

the vehicle registration data. All valid records that were identified from the vehicle 

registration data set were used to determine the number of vehicles for each of these 

three source types. The VIN decoded data provided to INDOT contained vehicle types 

according to MOBILE6.2 vehicle categories. There is a direct correlation between 

MOVES source type 21 (cars) and the MOBILE6.2 vehicle type LDV. All valid LDV 

records (those records not excluded from the vehicle age distribution analysis due to 

errors as was described in the section on Vehicle Age Distribution in this report) were 

counted in the vehicle population. 

There is not a direct correlation between MOVES source types 31 (passenger trucks) 

and 32 (light commercial vehicles) and the MOBILE6.2 light truck vehicle types (LDT1, 

LDT2, LDT3, and LDT4). All valid records from the vehicle registration data set for 

MOBILE6.2 light duty trucks were counted in the vehicle populations. The light duty 

trucks were distributed between MOVES source types 31 and 32 as per the 

Environmental Protection Agency's (EPA) guidance documented in Table A.1 of the 

appendix of the Technical Guidance on the Use of MOVES2010 for Emission Inventory 

Preparation in State Implementation Plans and Transportation Conformity. The guidance 

provides two sets of factors for distributing MOBILE6.2 light trucks between MOVES 

source types 31 and 32. These are based on fuel type and are shown in Table 3. 

2 
Table 3: Distribution of MOBILES 2 L' 19 h D t uty Trucks in to MOVES Source Types 

Source Types 

Fuel 31 32 

Gas 78% 22% 

Diesel 42% 58% 

As per ERG's assumption documented in MOBILE6 and MOVES Registration 

Distribution Calculations for Indiana Registration Data, all light duty trucks that did not 

have a fuel type identified were counted as diesel trucks. This was to prevent an 

underestimation of diesel trucks and their related emissions. 

Since only valid records from the vehicle registration data were used to calculate vehicle 

populations for source types 21, 31, and 32, it is reasonable to assume that some of the 

erroneous records that were discarded from the analysis actually belonged to these 

source types. The nature of these errors is not that the vehicle does not exist. Rather, it 

is that the vehicle could not be properly identified with any sense of certainty. It was 

therefore necessary to adjust the vehicle populations calculated from vehicle registration 

data to compensate for these discarded records. Based on an analysis of the error rate 

reported by ERG, vehicle populations for source types 21, 31, and 32 were increased by 

5.8 percent. 

Vehicle populations were not able to be developed directly from the vehicle registration 

data for some source types. This was due to the limitations in the VIN decoder used by 

ERG to process the vehicle registration data. Vehicle populations for all other source 

types (motorcycles and heavy vehicles) were derived by applying the Mileage 

Accumulation Rate (MAR) method documented in EPA's Technical Guidance on the Use 

of MOVES2010 for Emission lnventorv Preparation in State Implementation Plans and 

Transportation Conformity, Section 3.3 Source Type Population. 

The default MARs were extracted from MOVES by running MOVES for a single pollutant 

and a single year for all vehicles, fuels, months, days, and hours. The activity output was 

set to report both distance and population. A ratio of population to vehicle-miles-traveled 

(VMT) was calculated from these outputs. The ratios were calc;ulated for each source 

type. 

The Northwestern Indiana Regional Planning Commission (NIRPC), which is the 

metropolitan planning organization (MPO) for Lake and Porter Counties, provided VMT 

by MOVES road types extracted from their travel demand model's base year. Since the 

default MARs in MOVES vary by year (but not by location), the MOVES run that was 

executed to extract the MARs was run for a year consistent with the travel demand 

model's base year. This resulted in MARs that could be applied directly to the validated 

VMTs reported by the travel demand model. The travel demand model VMTs were 

converted into annual VMT and distributed by vehicle types using statewide default VMT 

distribution factors documented in this report in the section on Default VMT Distributions. 

The MARs were then applied to the annual vehicle type VMTs. The result was an 

estimated vehicle population for each source type for the travel demand model's base 

year. Since the vehicle populations for source types 21, 31, and 32 were developed 

directly from the vehicle registration data, the population estimates derived for those 

3 
source types using the MAR method were discarded and the observed data were used 

instead. 

Future year vehicle populations were developed base on socioeconomic growth rates for 

the maintenance area. The MPO provided base year and horizon year population and 

employment data for the area. Annual growth rates were calculated for population 

growth and employment growth individually. Population growth rates were then used to 

grow the light vehicle populations (source types 11, 21, 31, and 32). Employment growth 

rates were used to grow the heavy vehicle populations (source types 41, 42, 43, 51, 52, 

53, 54, 61, and 62). Vehicle populations were calculated for every year from 2008 to 

2040. These vehicle populations for Lake and Porter Counties as a combined area are 

shown in Appendix C. 

Meteorological Data: 

The default set of hourly temperatures and hourly relative humidity was developed using 

EPA's data converters for changing MOBILE6.2 minimum I maximum temperatures and 

absolute humidity to the MOVES equivalent formats. The values for the MOBILE6.2 

inputs were taken from the Air Quality Conformity Determination Between the 2040 

Regional Transportation Plan, the Fiscal Year 2012 to 2015 Transportation Improvement 

Program, and the Indiana State Implementation Plan for Air Quality, Appendix E, 

developed by NIRPC in June, 2011. 

Meteorological data reflect average annual conditions for the PM 2.5 runs. The 

MOBILE6.2 meteorological input data for each of the twelve months of the years were 

averaged together to create average annual temperatures and humidity. These were 

then passed through the data converters. The data reflect summer conditions for ozone 

using MOBILE6.2 inputs for July. The MOVES formatted meteorological data for Lake 

and Porter Counties as a combined area are presented in Appendix D of this report. 

Default VMT Distributions: 

As part of this effort, INDOT developed a default set of VMT distribution factors by 

Highway Performance Monitoring System (HPMS) vehicle type and by MOVES road 

type. These distribution factors were developed by analyzing four consecutive years of 

continuous traffic count data ending in 2010 for twenty permanent traffic count stations 

throughout Indiana. The stations were selected to provide a spread of locations 

corresponding to each of the four MOVES road types. Furthermore, these stations were 

selected from among sites that were concentrated in nonattainment and maintenance 

areas. In some cases, data from the requested site were either partially or completely 

unavailable. An inventory of the sites used to develop the distributions is shown in Table 

4. 

The vehicle counts reported at each station were provided by vehicle class. These were 

aggregated into the six basic HPMS vehicle types: motorcycle, passenger car, light 

truck, bus, single-unit heavy truck, and combination heavy truck. The distribution of VMT 

by vehicle type was calculated for each road type by taking each vehicle type's 

percentage of total traffic. These default statewide factors are shown in Appendix E. 

4 
SiteiD 

3000 

3200 

3300 

4000 

4500 

5600 

6100 

0105 

0201 

0210 

0303 

0327 

0403 

0501 

0502 

0507 

0602 

0603 

0608 

1315 

Table 4· Inventory of Permanent Count Stations 

City County Location Road Data Quality Type 

MUNCIE DELAWARE SR 332 RM 0.5 3 Closed since 9/26/2006. No 

data. 

CARMEL HAMILTON US 31 RM 125.7 5 Good 

INDY WEST MARION 1465 MM 10.0 4 Closed since 9/1/10 

GARY LAKE I 80 /I 94 MM 6.0 4 Only 2010 data passed QC 

LAPORTE LAPORTE SR 2 RM 65.2 3 Good 

SELLERSBURG CLARK 165 MM 8.0 4 Bad sensors. Not usable. 

EVANSVILLE GIBSON 164 MM 27.9 2 Good 

TERRE HAUTE VI GO US 41 RM 104.2 3 Good-closed 11/13/08-

5/13/09 

MIDDLEBURY ELKHART SR 120 RM 13.9 3 Good- closed 8/3/1 0-12/6/1 0 

FORT WAYNE ALLEN 1-69 0.53 mi N of 4 Good SR3 

MUNCIE DELAWARE US 35 RM 44.5 5 Good 

DALEVILLE DELAWARE 169 MM 31.4 2 Good-built in 12/10/2007 

SOUTH BEND ST. JOSEPH US 20 RM 77.1 4 Good 

INDY SOUTH MARION SR 37 RM 143.5 5 Good-closed 5/22/09-6/1/09 

MARTINSVILLE MORGAN SR 67 RM 80.6 3 Good 

SEYMOUR JACKSON 165 MM 47.0 2 Good 

HAZLETON GIBSON SR 56 RM 0.6 3 Good 

DUBOIS DUBOIS SR 56 RM 53.3 3 Good- closed 10/16/08-

3/20/09 

EVANSVILLE VANDERBURGH SR 66 RM 23.5 5 Good 

170 MARION 170 MM 83.5 4 Closed 5/17/06-3/24/08 

Default Hourly Distributions: 

The same set of twenty permanent traffic count locations discussed in the section on 

Default VMT Distributions was analyzed to develop a set of hourly distribution factors. 

These factors were calculated by road type, by HPMS vehicle type. Hourly factors were 

only calculated for the average weekday. The hourly distribution pattern for each traffic 

count location was reviewed. Any data that appeared to reflect either an error in the data 

or an outlier of behavior were removed to prevent bias in the data. The following data 

were excluded from the analysis: 

• Bus data from count stations 0105 and 0603 were excluded due to abnormal 

midnight peaks in the data; 

• An abnormal relationship between passenger cars and light duty trucks at count 

station 4500 prompted the exclusion of all data from this location due to 

questions of reliability; 

• Peak spreading behavior observed at count station 4000 from traffic related to 

Chicago was considered to be too unique to be included in a default statewide 

data set; and, 

• Combination truck traffic from station 3200 was excluded due to too much 

overnight traffic when compared to other vehicles and other stations. 

5 
Furthermore, traffic patterns reported by those count stations corresponding to road type 

3 (3000, 4500, 0105, 0201, 0502, 0602, and 0603) had a tendency to over represent 

long distance travel. This was most likely the result of statewide permanent count 

stations focusing primarily on higher order facilities. Rural collectors and local streets are 

less likely to reflect long distance travel. The hourly distributions for road type 3 (rural 

unrestricted access) were adjusted to better account for traffic behavior on lower order 

facilities in rural areas. A sample of traffic count data from Morgan County, IN was used 

to introduce more local traffic behavior in the road type 3 hourly distributions. An analysis 

of the Morgan County data showed a pattern more consistent with AM and PM peaking 

characteristics reflecting local commuting traffic on collectors and local streets for 

passenger cars and light duty trucks. The Morgan County data for passenger cars and 

light duty trucks on collectors and local streets were weighted and added to the road 

type 3 data set. This analysis assumed that rural collectors and local streets accounted 

for 20 percent of all VMT for road type 3. 

The statewide default hourly distribution factors are presented in Appendix F. 

Default Daily and Monthly Distributions: 

Default daily and monthly distribution factors were calculated from IN DOT's official count 

adjustment factors which are more commonly used to develop AADT from raw traffic 

counts. These factors are based on the set of daily traffic counts collected from all 

permanent count stations throughout the state. The daily distribution factors determine 

what percentage of VMT is occurring on weekdays and what percentage is occurring on 

weekends. The monthly distribution factors determine what percentage of annual VMT is 

occurring in each month of the year. The statewide default daily distribution factors are 

shown in Appendix G. The statewide default monthly distribution factors are shown in 

Appendix H. 

Ramp Fractions: 

The ramp fractions represent the percentage of vehicle-hours-traveled (VHT) for road 

types 2 (rural restricted access) and 4 (urban restricted access) occurring on the ramps 

associated with those road types. These fractions were calculated based on the 

percentage of VHT occurring on ramps reported by the base year travel demand model. 

These ramp fractions are reported in Appendix I. 

6 
Appendix A 

Number of Runs: 

Input Item Ozone PM 2.5 

Years 2006,2010, 2008, 2010, 

2015,2020, 2015, 2020, 

2025,2030, 2025,2030, 

2035,2040 2035,2040 

Pollutants/ Volatile PM 2.5 with all 

Processes Organic subspecies; 

Compound NOx 

(VOC), NOx, 

and supporting 

Meteorology Summer Average 

Annual 

#of MOVES 8 8 

runs 
General Parameters: 

MOVES Input Item 

Screen Ozone PM 2.5 

Description Description User Choice 

Scale Domain/Scale County 

Calculation Type Emission Rate 

Time Spans Time Hour Hour 

Aggregation 

Level 

Year 2004, 2010, 2008, 2010, 

2015, 2020, 2015, 2020, 

2025, 2030, 2025,2030, 

2035, 2040 2035,2040 

Months July April 

Days Weekday Weekday 

Hours Select All Select All 

Geographic Geographic Lake County* Lake County* 

Bounds Bounds 

Vehicles Vehicles All Gas and Diesel Combinations 

Road Type Road Type Select All 

Pollutants/ Pollutants/ VOC, NOx, and PM 2.5 with all 

Processes Processes supporting subspecies; NOx 

General Database Name LakePorter LakePorter PM 

Output Ozone 

Units Select "Grams" and "Miles" and 

"Million BTU" 

Activity Distance, Population 

Output On Road Select "Source Use Type" and "Road 

Emissions Type" 

Detail 

*Represents both Lake and Porter Counties. 
C t D t M • 

County Data Excel Sheet Tab 

Manager Input Name 

Source (Vehicle) sourceTypeYear 

Type Population 

Vehicle Type HPMSVTypeYear 

VMT {by 13 

MOVES Vehicle 

Types) 

Ozone PM 2.5 

Local Registration for Source Types 21, 31, and 32; 

Estimated population using default MOVES mileage 

accumulation rates and local VMT for all other source types. 

Future year vehicle populations based on population growth 

rates for source types 11, 21, 31 , and 32. Employment 

growth used for all other source types. 

Statewide default vehicle distributions across road types 

developed by INDOT using an analysis of permanent count 

station data from a statewide data set. 

MonthVMTFraction Statewide default monthly fractions developed by INDOT 

using an analysis of permanent count station data from a 

statewide data set. 

DayVMTFraction Statewide default daily fractions developed by INDOT using 

an analysis of permanent count station data from a 

statewide data set. 

HourVMTFraction Statewide default hourly fractions developed by IN DOT 

Average Speed avgSpeed 

Distribution (% Distribution 

of VHT in each 5 

mph speed bin) 

Road Type roadType 

Distribution Distribution 

(VMT by 5 

MOVES Road 

Types) 

Age Distribution sourceTypeAge 

(Vehicle Distribution 

Population by 

Age of Vehicle) 

Ramp Fraction RoadType 

Meteorology ZoneMonthHour 

Data 

Fuel (% of FueiFormulation 

Market Share by 

Fuel Type) FueiSupply 

JIM Program IMCoverage 

using an analysis of permanent count station data from a 

statewide data set. 

National defaults. 

Calculated from local VMT data. Use travel demand model 

base year distributions for all years. 

Local age distributions developed from vehicle registration 

data for source types 21 , 31, and 32. Default MOVES age 

distributions for all other source types. 

Based on local travel demand model. 

MOBILES Summer Met Data MOBILES 12 month Met 

Converted to MOVES format Data Converted to MOVES 

format and averaged to 

annual meteorology 

MOVES Defaults 

Lake County MOVES Lake County MOVES 

Defaults for Summer (check Defaults for annual (check if 

if varies among counties) varies among counties) 

Consistent with current locaii/M Program 
Appendix B 

Vehicle Age Distributions for Lake and Porter Counties: 

Source Types 

ageid 11 21 31 32 41 42 43 51 52 53 54 61 62 

0 0.2109690540 0.0267370941 ~0.0145061143 0.0355_122377 0.0643023355 0.0545743076 0.0622220643 0.0494240790 0.0588526168 0.0787544027 0.0615095870 0.0535634660 0.0670845256 

1 0.1921154969 0.0530181832 0.0500664299 0.0734065149 0.0626728412 0.0531913309 0.0606452875 0.0481716155 0.0573612230 0.0767586735 0.0599508636 0.0535634660 0.0670845256 

2 .. 0.1573471585 0.0665539321 0.'0582074781 0.07_86470016 0.0624853859 0.0530322"328 0,0604638952 0.0480275345 0.0571896519 0.0765290827 0.0597715492 0.0541045093 0.0677621447 

3 0.1359771581 0.0610324714 0.0519847618 0.0656648868 0.0624229593 0.0529792497 0.0604034894 0.0479795509 0.0571325186 0.0764526251 0.0597118340 0.0575579884 0,0720873878 

4 0.1058454735 0.0659801258 0.0780550961 0.07,936161;34 0.0617369906 0.0523970560 0.0597397140 0.0474523026 '0.0565046834 0.0756124785 0.0590556596 0.05641,82312 0.0706599203 

5 0.0750909142 0.0645627102 0.0733914482 0.0732874129 0.0559170498 0.0474575929 0.0541080614 0.0429789769 0.0511779950 0.0684845018 0.0534884926 0.0489290859 0.0612802835 

6 0.04?6805323 ·. 0.0608386692 0.0747132670 o:oS4771S220 0.0468365056 0.0397508123 0.0453212873 0.0359994879 0.0428670388 0.0573630896 0.0448023279 0,0366034411 0.0458432683 

7 0.0331026886 0.0649389143 0.0806648410 0.0721559442 0.0425786431 0.0361370941 0.0412011709 0.0327268079 0.0389700355 0.0521482660 0.0407293873 0.0340742206 0.04267_55959 

8 0.0197278356 0.0649997150 0.0643827445 0.0597693392 0.0468268516 0.0397426124 0.0453119367 0.0359920640 0.0428582007 0.0573512681 0.0447930981 0.0358093100 0.0448486759 

9 0.0118473747 0.0677129448 0.0689108213 0.0689004903 0.0534377006 0.0453533365 0.0517089150 0.0410733035 0.0489087688 0.0654479137 0.0511168252 0.0526288382 0.0659139597 

10 0.0053251777 0.0607512683 0.0648030151 0.0588165234 0.0532712252 0.0452120443 0.0515478328 0.0409453420 0.0487564067 0.0652440247 0.0509575859 0.0624520143 0.0782168041 

11 0.0025378610 0.0524367768 0.0558146471 0.0510748953 0.0407951886 0.0536203440 0.0411075833 0.0313560350 0.0391491717 0.0523881239 0.0302729398 0.0478258601 0.0598985955 

12 0.0013011470 0.0529801828 .. 0.0501.138798 0.0424003017 0.0331924560 0.0489936472 0.0382933197 .0.0255124310 0.0294483131 0.0394065607 0.0466101866 0.0389128550 0.0487354179 

13 0.0006124019 0.0425262678 0.0386377810 0.0326140898 0.0277347637 0.0456089741 0.0333751020 0.0545980574 0.0316399801 0.0194774783 0.0291673253 0.0325145854 0.0462990441 

14 0.0002476898 0.0448138930 0.0390038231 0.0330507970 0.0364294706 0,037_7.7:46681 _0._()4:3_08_63_6~0 0.06~2656498 0.0364439725 0.01.94691525 0.0347804437 o.04270n419 0.0462072388 

15 0.0001527705 0.0327297600 0.0357704509 0.0282867181 0.0283511969 0.0332950401 0.0210164622 0.0395649332 0.0357887614 0.0311848083 0.0335202065 0.0332372597 0.0300444032 

16 0.0000668536 0.0270600977 0.0244095876 0.019S716756 0.0235884296 0.0279132162 .. 0.025367.1498 0.0341566540 0.025998,7:277 .. 0.0230196849 0.0233151075 0.0276536739 0.0230524492 

17 0.0000299603 0.0197450172 0.0162482037 0.0135180737 0.0175637044 0.0244970846 0.0206833627 0.0146346390 0.0197956396 0.0052258132 0.0206748599 0.0205906442 0.0138452217 

.18 ..... 0.0000127409 0.0157207729 0.0129944958 0.0106794767 0.0201192241 0.0250480695. 0.0266888558 0.0401958334 . 0.0193(40288 0.0037212159 0.0155464816 0.0235865809 0.0100066460 

19 0.0000055369 0.0109327203 0.0097340094 0.0083371380 0.0225790392 0.0366610768 0.0301447753 0.0342277190 0.0227335396 0.0175775477 0.0203628520 0.0264703224 0.0098603738 

20 0.0000022027 0.0097167069 0.0096594452 0.0078607301 0.0226407923 0.0281971934 0.0173882093 0.0270081845 0.0289395633 0.0183874556 0.0265944575 0.0265427135 0.0095755112 

21 ... 0.0000010015 0.0060838669 0.0075445351 0.0053595887 0.0212965445 0.0224413685 0.0209032932 0.0367430589 0.0255089927 0.0121624816 .. 0.0238465850 0.0249667984 0.0083402541 

22 0.0000005320 0.0047196519 0.0043586128 0.0031760526 0.0221366577 0.0207614938 0.0211741003 0.0294241579 0.0211707159 0.0029207200 0.0232916866 0.0259516972 0.0021970287 

23 0.0000002372 0.0034656381 0.0032604864 0.0028187467 0.0187753208 0.0176845935 0.0186862600 0.0367365508 0.0255742899 0.0006595597 0.0173635700 0.0220110680 0.0022815392 

24 0.0000001072 0.0034048375 0.0028063230 0.0021239852 0.0165801584 0.0153441343 0.0162223474 0.0195371_739 0.0181341022 0.0013228019 0.0186391363 0.0194375881 0.0028947085 

25 0.0000000515 0.0020672227 0.0018979963 0.0014292237 0.0130464803 0.0119613578 0.0125269842 0.0202862884 0.0101534224 0.0013255722 0.0189070434 0.0152949162 0.0014963357 

26 0.0000000201 0.0015238168 0.0010100052 0.0009131151 0.0052066606 0.0114707358 0.0046276161 __ 0.0058785937 0.0158244798 0.0000000000 0.0123859355 0.0061039775 0.0003051544 

27 0.0000000084 0.0007410082 0.0008269841 0.0008535641 0.0044375500 0.0062552616 0.0034269422 0.0066192300 0.0082431519 0.0005853113 0.0073123264 0.0052023202 0.0002365920 

28 . 0.0000000046 0.0008208090 0.0006507416 0.0006550608 0.0038534093 0.0027153367 0.0040227141 0.0058648852 0.0078447522 0.0004224309 0.0040199156 0.0045175071 0.0007539156 

29 0.0000000027 0.0007486082 0.0002846994 0.0002382039 0.0050202650 0.0073813428 0.0039557847 0.0014702211 0.0082910352 0.0000000000 0.0005297244 0.0058854602 0.0002483418 

30 0.0000000060 0.0106363170 0.0052872753 0.0046449769 0.0041641999 0.0025473919 0.0046291194 0.0021486392 0.0093642209 0.0005969550 0.0069720059 0.0048818593 0.0002641374 

Source: Quality assured vehicle registration data for the combined Lake County and Porter County area for source types 21, 32, and 32, MOVES201 Oa default distributions for all other source types. 
Appendix C 

Lake and Porter Counties Vehicle Po u/ations: 

Vehicle 

Populations 

Annual Populations. 

2008' 

2009 

2010 

2011 

2012 

2013 

2014 

2015 

2016 __ _ 

2017 

2018 

2019 

2020 ___ 

2021 

2022 

2023 

2024 

2025 

2026 

2027 

2028 

2029 

2030 

2031 

2032 

2033 

2034 

2035 

2036 

2037 

2038 

2039 

2040 

12,164-

12,247 

12,330_ 

12,414 

12,499 

12,584 

12,670 

12,757 

}2,844 

12,931 

13,020 

1_3,108_ 

_13,198 __ _ 

13,288 

13,37:9 

13,470 

13,562 

13,654 

13,748 

13,841 

13,936 

14,031 

14,127_ 

14,223 

14,320 

14,418 

1:4,516 

14,615 

14,715 

14,815 

1:4,916 

15,018 

15,121 

276,531, 

278,418 

280,31_8 

282,231 

284,156 

286,095 

288,048 

290,013 

___ 291,992 

293,984 

295,990 

---298,0~ 0 __ _ 

__ ,_300,044:_ .. 

302,091 

304,152 

306,228 

308,317 

310,421 

312,539 

314,672 

316,819 

318,981 

321,1.58 

323,349 

325,556 

327,777 

330,01_4 

332,265 

334,533 

336,815 

339,114 

341,428 

_159,214 

160,301 

161,395 

162,496 

163,605 

164,721 

165,845 

166,977 

1_~8.~_:1_6'"" 

169,263 

48,746 

49,078 

49,413 

49,751 

50,090 

50,432 

50,776 

51,122 

5J,4:7.1 

51,822 

_170,41.8. ___ , ____ 52,176 

171,581 52,532 

__ J]2,7.:52~ --------- 52,89_1 __ 

173,931 

17'5,_1F .. _ 

176,312 

177,516 

178,727 

179,946 

181,174 

182,410 

183,655 

184,908 

186,170 

187,440 

188,7_19, 

1_90,007_ 

191,304 

192,609_ 

193,923 

195,247 

196,579 

197,920 

53,251 

53,615 

53,981 

54,349 

54,720 

55,093 

55,469 

55,848 

56,229 

56,612 

56,999 

57:,388 

57,779 

58,17:4 

58,571 

58,970 

59,373 

59,778 

60,186 

60,596 

293 

296 

298 

301 

303 

306 

308 

311 

314 

316 

319,-

322 

----~24_ 

327 

330 

332 

335 

338 

341 

344 

346 

349 

352 

355 

358 

361 

364 

367 

370 

373 

376 

380 

383 

42 

157 

- 159 

160 

161 

163 

164 

166 

167 

_1_68_ 

170 

__ 17_1 __ _ 

173 

____ 1_7~-

175 

m 

178 

180 

181 

183. 

184 

186 

187 

189 

191 

192 

194 

195 

197 

199 

200 

202 

204 

205 

2,005 58 

2,021 58 

2,038 59 

2,055 59 

2,072 ,60 

2,089 60 

2,107 61 

2,124 61 

2,1:42__ __62 

2,160 62 

2,17_8 

_2,196 

2,2J4 __ ,_ 

2,233 

2,251 

2,2(0." 

2,289 

2,308 

2,327 

2,347 

2,366 

2,386 

2,406 

2,426 

2,446 

2,467 

2,487_. 

2,508 

2,529 

2,550 

2,571 

2,593 

2,614 

63 

63 

64 

64 

" __ 65 

66 

66 

67 

67 

68 

68 

69 

69 

70 

:?:1_ 

71 

72 

72 

73 

74 

74 

75 

75 

3,634 

3,664 

3,694 

3,725 

3,756 

3,788 

3,819 

3,851 

3,883_ 

3,915 

3,948 

3,981 

4,014 

4,048 

4,081 

4.115 

4,150 

4,184 

4,219 

4,254 

4,290 

4,325 

4,361 

4,398 

4,434 

4,471 

4,509 

4,546 

4,584 

4,622 

4,661 

4,700 

4,739 

434 

437 

441 

445 

448 

452 

456 

460 

46?-

467 

471 

475 

479 

483 

487 

491 

495 

499 

504 

508 

512 

516 

521 

525 

529 

534 

538 

543 

547 

552 

556 

561 

566 

831 

838 

845 

852 

859 

867 

874 

881 

" .88?_ __ 

896 

___ 903 __ 

911 

- 918 

926 

__ 934 __ 

942 

949 

957 

965 

973 

982 

990 

998 

1,006 

1,015 

1,023 

1_,032 

1,040 

1,049 

1,058 

1,066 

1,075 

1,084 

61 

6,485 

6,539 

6,593 

6,648 

6,703 

6,759 

6,816 

6,872 

-~·~_;30_ 

6.987 

7,~6 

7,104 

- 7,163 

7,223 

7,283, 

_7,344 

7,405 

7,467 

7,529 

7,592 

_7,655 

7,719 

7_,"[83 

7,848 

__ 7,913 

7,979 

8,046 

8,1_13 

8,181 

8,249 

8,317 

_8_.387 

8,457 

62 

7,399 

7,481 

7,523 

7,586 

7,649 

7,713 

7,777 

7,842 

7,~07 .. _ 

7,973 

8,039 

8,106 

8,1_74 

8,242 

_8,31,1_ 

---8,380 

8,450 

8,520 

8,591 

8,663 

8,735 

8,808 

8,881 

8,955 

'9,030 

9,105 

9,181 

9,257 

9,334 

9,412 

9,490 

-9,570 

9,649 

Source: Quality assured vehicle registration data for the combined Lake County and Porter County area for source types 21, 32, and 32, MOVES2010a default mileage accumulation rates for all other source types. Population growth factors are taken from local 

socioeconomic data forecasts. 
Appendix D 

L k a e an dPrt o er C oun t" 1es Mt e eoro og1ca . I 0 a t a: 

Ozone PM2.5 

monthiD zoneiD HouriD temperature reiHumidity monthiD zoneiD HouriD temperature reiHumiditv 

7 180890 1 67.0 88.0 4 180890 1 43.7 100.0 

7 180890 2 65.8 91.8 4 180890 2 42.5 100.0 

7 180890 3 64.9 94.9 4 180890 3 41.6 100.0 

7 180890 4 64.2 97.2 4 180890 4 41.0 100.0 

7 180890 5 63.6 99.0 4 180890 5 40.5 100.0 

7 180890 6 63.0 100.0 4 180890 6 39.9 100.0 

7 180890 7 62.5 100.0 4 180890 7 39.4 100.0 

7 180890 8 62.9 100.0 4 180890 8 39.8 100.0 

7 180890 9 65.5 92.6 4 180890 9 42.3 100.0 

7 180890 10 69.7 80.2 4 180890 10 46.2 97.2 

7 180890 11 74.0 69.4 4 180890 11 50.3 83.5 

7 180890 12 77.7 61.4 4 180890 12 53.8 73.5 

7 180890 13 80.9 55.3 4 180890 13 56.8 65.8 

7 180890 14 82.6 52.2 4 180890 14 58.5 62.0 

7 180890 15 83.2 51.2 4 180890 15 59.0 60.7 

7 180890 16 83.4 50.9 4 180890 16 59.2 60.3 

7 180890 17 83.0 51.6 4 180890 17 58.8 61.2 

7 180890 18 81.7 53.7 4 180890 18 57.6 63.8 

7 180890 19 79.7 57.5 4 180890 19 55.7 68.6 

7 180890 20 77.0 62.9 4 180890 20 53.1 75.3 

7 180890 21 74.3 68.8 4 180890 21 50.5 82.7 

7 180890 22 71.9 74.5 4 180890 22 48.3 89.9 

7 180890 23 70.3 78.8 4 180890 23 46.7 95.4 

7 180890 24 68.6 83.4 4 180890 24 45.2 100.0 

Source: Mobile 6.2 reported meteorological data from Air Quality Conformity Determination Between the 2040 Regional Transportation Plan, the Fiscal Year 2012 

to 2015 Transportation Improvement Program, and the Indiana State Implementation Plan for Air Quality, Appendix E, developed by NIRPC in June, 2011 

converted using EPA data converter. 
Appendix E 

Indiana Default VMT Distributions by Vehicle Type and Road Type: 

Road Light Duty Single Unit Combination 

Type Motorcycle Passen(!er Car Truck Bus Truck Truck 

2 0.007033832 0.506408086 0.163786651 0.004174166 0.007773053 0.310824213 

3 0.001733929 0.659751199 0.225767175 0.000793168 0.010963315 0.100991214 

4 0.004429643 0.424581084 0.299243052 0.005271096 0.008735204 0.257739921 

5 0.002785022 0.702754695 0.245240087 0.001402085 0.009764356 0.038053756 

Source: Statewide averages developed from Indiana Department of Transportation traffic count data for all road types except for Road Type 4. Distributions for 

Road Type 4 taken specifically from HlO in Gary (count station 4000) as per ICG consensus to represent higher than average truck traffic in Gary. 
Appendix F 

Indiana Default Hourly Distribution Factors for Road Type 2- Rural Restricted Access: 

Source Types 

Hour 11 21 31 32 41 42 43 51 52 53 54 61 62 

1 0.0125903247 0.0101219844 0.0084967341 0.0084967341 0.0254913340 0.0254913340 0.0254913340 0.0126607789 0.0126607789 0.0126607789 0.0126607789 0.0197906895 0.0197906895 

2 0.0104070951 0.0069241973 0.0066421955 0.0066421955 0.0269500431 0.0269500431 0.0269500431 0.0114617645 0.0114617645 0.0114617645 0.0114617645 0.0212124099 0.0212124099 

3 0.0098043179 0.0056567534 0.0061275627 0.0061275627 0.0231103443 0.0231103443 0.0231103443 0.0107741941 0.0107741941 0.0107741941 0.0107741941 0.0201622890 0.0201622890 

4 0.0140329469 0.0069658232 0.0084286563 0.0084286563 0.0234460042 0.0234460042 0.0234460042 0.0128724692 0.0128724692 0.0128724692 0.0128724692 0.0213065902 0.0213065902 

5 0.0165212405 0.0100941552 0.0134026652 0.0134026652 0.0244090660 0.0244090660 .. 0.0244090660 0.0174195788 0.0174195788 0.017;41$)5788 0.0174195788 0.0250478552 0.0250478552 

6 ....... 0.0312047458 0.0241732202 0.0316551315 0.0316551315 0.0322923692 0.0322923692 0.0322923692 0.0261005783 0.0261005783 0.0261005783 0.0261005783 0.0304976568 0.0304976568 

7 0.0399082603 0.0390974748 0.0481531313 0.0481531313 0~0302344914 0.0302344914 0.0302344914 0.0420450985 0.0420450985 0.0420450985 0.0420450985 0.0339947725 0.0339947725 

8 0.0482864956 0.0528758381 0.0535145983 0.0535145983 0.0386071681 0.0386071681 0.0386071681 0.0556119122 0.0556119122 0.0556119122 0.0556119122 0.0383435322 0.0383435322 

9 0.0472316355 0.0493101459 0.0541442978 0.0541442978 0.0454144773 0.0454144773 0.0454144773 0.0647383083 0.0647383083 0.0647383083 0.0647383083 0.0447350945 0.0447350945 

10 0.0521292001 0.0488627065 0.0570682751 0.0570682751 0.0533197396 0.0533197396 0.0533197396 0.0711110358 0.0711110358 0.0711110358 0.0711110358 0.0517738130 0.0517738130 

11 0.0559204481 0.0513700269 0.0575854739 0.0575854739 0.0576707709 0.0576707709 0.0576707709 0.0730230234 0.0730230234 0.0730230234 0.0730230234 0.0557712484 0.0557712484 

12 0.0572822100 0.0533048469 0.0582753930 0.0582753930 0.0549541212 0.0549541212 0.0549541212 0.0731872952 0.0731872952 0.0731872952 0.0731872952 0.0571435296 0.0571435296 

13 0.0592008057 0.0551586141 0.0599414146 0.0599414146 0.0541541840 0.0541541840 0.0541541840 0.0739324454 0.0739324454 0.0739324454 0.0739324454 0.0567014536 0.0567014536 

14 0.0615145144 0.0595500442 0.0635019874 0.0635019874 0.0570747392 0.0570747392 0.0570747392 0.0746488056 0.0746488056 0.0746488056 0.0746488056 0.0567500887 0.0567500887 

15 0.0647783324 0.0662712693 0.0683897966 0.0683897966 0.0551925339 0.0551925339 0.0551925339 0.0704234655 0.0704234655 0.0704234655 0.0704234655 0.0578234055 0.0578234055 

16 0.0713500739 0.0764876319 0.0772110428 0.0772110428 0.0551956709 0.0551956709 0.0551956709 0.0628601912 0.0628601912 0.0628601912 0.0628601912 0.0577540296 0.0577540296 

17 0.0754978425 0.084'~160034 0.0792545794 0.0792545794 0.0557979766 0.0557979766 0.0557979766 0.0534712990 .. 0.0534712990 0.0534712990 0.0534712990 0.056291081~ 0.0562910814 

18 0.0693763461 0.0821220539 0.0693254052 0.0693254052 0.0501011685 0.0501011685 0.0501011685 0.0436895095 0.0436895095 0.0436895095 0.0436895095 0.0527021980 0.0527021980 

19 0.0542187052 0.062008251,3 ..•. _0.052_1045300 0.0521045300 0.0459665909 0.0459665909 0.0459665909 0.0363413126 0.0363413_126. 0.03634~3126 0.0363413126 0.05022_151.00' ',0.050221_5100 

20 0.0432143461 0.0459015588 0.039_0794599 0.0390794599 0.0462959768 0.0462959768 0.0462959768 0.0312048570 0.0312048570 0.0312048570 0.0312048570 0.0467116534_ 0.0467116534 

21 0.0358137860 0.0372595462 _0,031101_5284 0.0311015284 0.0418602463, 0.0418'602463 0.0418602463 0.0261242877 _0,0261242877 0.0261242877 0.0261242877 0.0421311043 0.0421311043 

22 0.0294294934 0.0312744978 0.0249803003 0.0249803003 0.0366496745 0.0366496745 0.0366496745 0.0215822587 0.0215822587 0.0215822587 0.0215822587 0.0381387483 0.0381387483 

23 0.0223450238 0.0235734666 0.0182964081 0.018296408'1 0.0347517842 0.0347517842 0.0347517842 0.0189759266 0.0189759266 0.0189759266 0.0189759266 0.0342326572 0.0342326572 

24 0.0179418099 0.0169198902 0.0133194323 0.0133194323 0.0310595247 0.0310595247 0.0310595247 0.0157396039 0.0157396039 O.D157396039 O.D157396039 0.0307625891 0.0307625891 

Source: Statewide averages developed from Indiana Department of Transportation traffic count data. 
n 1ana efaut ounv J 1stn ut10n F actors for R oa dT IVDe3- R ura /U nrestncted Access: 

Source Types 

Hour 11 21 31 32 41 42 43 51 52 53 54 61 62 

.1 0.0040299464 0.0073183989 0,0054636028 0.0054636028 0,0036998387 0,0036998387 0,0036998387 0.0043986387 0.0043986387 0.0043986387 0.0043986387 0.0164160879 0.0164160879 

2 0.0040299464 0.0041131835 0.0034619242 0.0034619242 0.0045536477 0.0045536477 0.0045536477 0.0041872686 0.0041872686 0.0041872686 0.0041872686 0.0167510731 0.0167510731 

3 0.0041817017 0.0032797517 0.0030691885 0.0030691885- 0.0046485153 0.0046485153 0.0046485~ 53 0.0073497934 0.0073497934 0.007_3497_934 0.007349(934 --. 0,0}6540Z905_1 0_,()_:1_65:47905_1 

4 0.0053114356 0.0057247729 0.0048082254 0.0048082254 0.0039844417 0.0039844417 0.0039844417 0.0084039684 0.0084039684 0.0084039684 0.0084039684 0.0195836328 0.0195836328 

5 . 0.0140963815 0.0151258840 ~ 0.0143177758 O.OH3F7?58 0.0082534864 ,0.0082534864 0.0082534864 0.0153176438 .. 0.0153176438 0.0153176438 o:o153176438 0.0258467673 0.0258467673 

6 0.0292719118 0.0316782840 0.0354335195 0.0354335195 0.0293141068 0.0293141068 0.0293141068 0.02997 44215 0.0299744215 0.0299744215 0.0299744215 0.0344245647 0.0344245647 

7 0.0397598894 0.0468485516 0.0516314034 0.0516314034 0.0496157860 0.0496157860 0.0496157860 0.0557776279 0.0557776279 o.ossm6279 0.0557776279 0.0440469233 0.0440469233 

8 0.0448183995 0.0633910409 0.0636260878 0.0636260878 0.0768428043 0.0768428043 0.0768428043 0.0778885464 0.0778885464 0.0778885464 0.0778885464 0.0512793380 0.0512793380 

9 0.0370114322 0.0460357746 0.0558633273 0.0558633273 0.1049236315 0.1049236315 "0.1049236315 0.0853025536 0.0853025536 0.0853025536 0.0853025536 _0.0568238265 0.0568238265 

10 0.0416989849 0.0427840868 0.0547852386 0.0547852386 0.1065363817 0.1065363817 0.1065363817 0.0879727734 0.0879727734 0.0879727734 0.0879727734 0.0599756501 0.0599756501 ..... 

11 0.0509391967 0.0444183487 "0.0568454275 0.05684542i:5 - 0.1186794422 0.1186794422 0.1~86794422 0.0886336394 0.0886336394 0.0886336394 0.0886336394. 0.0633505956 . 0.0633505956 

12 0.0563855259 0.0512966366 0.0618918527 0.0618918527 0.1154539418 0.1154539418 0.1154539418 0.0859045570 0.0859045570 0.0859045570 0.0859045570 0.0635864154 0.0635864154 

13 0.0638721209 0.0537246907 0.0810818211 0.0610818211 0.0999905132 0.0999905132 0.0999905132 0.0858537212 0.0858537212 0.0858537212 0.0858537212 0.0644099711 0.0644099711 

14 . 0.0708697265 ~ ~_D-0545001954 0.0632013074 0.0632013074 0.0864244379 0.0864244379 0.0864244379 0.0852196109 0.0852196109 0.0852196109 0.0852196109 0.0637040231 0.063_7040231 

iS .. 0.0774626513 0.0656899700 -~ p.os-8.1.$8;4267 - 0.0681_384267 0.05929228?3 0,.059292287_3 __ ~ 0.059292287~ .. 0.07_7455:1039 0.0774551039 0.0774551039 0.0774551039 0.0609657913 0.0609657913 

16 0.0849155229 0.0775959037 0.0765115831 0.0765115831 0.0295038421 0.0295038421 0.0295038421 0.0663381066 0.0663381066 0.0663381066 0.0663381066 0.0570058311 0.0570058311 

17 0.0916096179 0.0871890696 0.0796014405 0.0796014405 0.0317806660 0.0317806660 0.0317806660 0.0433522764 0.0433522764 0.0433522764 0.0433522764 0.0517440242 0.0517440242 

18 0.0855899909 0.0856725476 0.0737419189 0.0737419189 0.0184043260 O.D184043260 0.0184043260 0.0290727541 0.0290727541 0.0290727541 0.0290727541 0.0467760851 0.0467760851 ........ "' ' ,,,_ "" 

i9 0.0685259502 0.0656330958 0.0545272751 0.0545272751 . 0.0120481928 ___ 0.0120481928 0.0120481928 o.o1877A4815 0.0187744815 '0.0187744815 o.01S'V44815 0.0413186686 ~0.04:1,3:186686 . 

20 0.0503658989 0.0457301992 0.0390975413 0.0390975413 0.0118584575 0.0118584575 0.0118584575 0.0129711680 0.0129711680 0.0129711680 0.0129711680 0.0364127078 0.0364127078 .... 

21 .... 0.035342J239. 0,0400621944 0.0294058171 0.0294058171. 0.0096765013 0.00967650:13 0.0096765013 0.0106166656 ,0.0106166656 0.0106166656 0.0106166656 0.0318882915 0,03188829J5 

22 0.0217853168 0.0289018238 0.0218457686 0.0218457686 0.0061663979 0.0061663979 0.0061663979 0.0079972816 0.0079972816 0.0079972816 0.0079972816 0.0290264055 0.0290264055 

23 O.Q11938083S 0.0205028665 0.013'6731866 0.0136731866 . 0.0048382506 0.0048382$06 0.0048382506 0.0061564888 0.0061564888. "0_.0061564888 0.0061564888 .. 0.0255574344 0.025557 4344". 

24 0.0061882440 0.0127827290 0.0079763402 0.0079763402 0.0035101034 0.0035101034 0.0035101034 0.0050809093 0.0050809093 0.0050809093 0.0050809093 0.0225579868 0.0225579868 

Source: Statewide averages developed from Indiana Department of Transportation traffic count data. 
Indiana Default Hourly Distribution Factors for Road Tvpe 4 Urban Restricted Access: 

Source Types 

Hour 11 21 31 32 41 42 43 51 52 53 54 61 62 

1 0.0114838630 0.0104500369 0.0090397680 0.0090397680 0.0186488577 0.0186488577 0.0186488577 0.0090968023 0.0090968023 0.0090968023 0.0090968023 0.0194173119 0.0194173119 

2 0.0071800855 0.0062500477 0.0056304309 0.0056304309 0.0163411464 0.0163411464 0.0163411464 0.0080102618 0.0080102618 0.0080102618 0.0080102618 0.0198708197 0.0198708197 

3 0.0063691205 0.0049689741 0.0046493622 0.0046493622 0.0157775876 0.0157775876 0.0157775876 0.0078361983 0.0078361983 .. 0.0078361983 0.0078361983 0.0186489893 0.0186489893 

4 0.0073777516 0.0058427101 0.0058801326 0.0058801326 0.0161766037 0.0161766037 0.0161766037 0.0086827231 0.0086827231 0.0086827231 0.0086827231 0.0198231326 0.0198231326 

5 0.0108139353 0.0098545059 . 0.0108999000 0.0108999000 0,0221330492 0.0221330492 0.0221330492 0.0117453229 0.0117453229 0.0117453229 0,0117453229 0.0232515449 0.0232515449 

6 0.0235457656 0.0231603609 0.0263517526 0.0263517526 0.0299755654 0.0299755654 0.0299755654 0.0204013312 0.0204013312 0.0204013312 0.0204013312 0.0294638153 0.0294638153 

7 .. 0.0461747881 0.0495085217 0.0542414568 0.0542414568 0.0393812372 .. 0.0393812372. 0.0393812372 0.0435263184 0.0435263184 0.0435283184 0.0435263184 0.0375553768 0.0375553768 

8 0.0567226756 0.0788353145 0.0674512195 0.0674512195 0.0503870867 0.0503870867 0.0503870867 0.0659533819 0.0659533819 0.0659533819 0.0659533819 0.0446175773 0.0446175773 

9 0.0493171440 0.0638279223 0.0614111771 0.0614111771 0.0589556475 0.0589556475 0.0589556475 0.0756333178 0.0756333178 0.0756333178 0.0756333178 0.0515843704 0.0515843704 

10 0.0406144957 0.0466481655 0.0536303211 0.0536303211 0.0581_555587_ 0.0581555587 0.0581555587 0.0790728466 0.0790728466 0.0790728466 0.0790728466 0.0553194565 0.0553194565 

11 0.0415130748 0.0428102606 0.0512594850 0.0512594850 0.0616027281 0.0616027281 0.0616027281 0.0824723032 0.0824723032 0.0824723032 0:0824723032 0.0583081277 0.0583081277 

12 0.0465166969 0.0452333632 0.0529793024 0.0529793024 0.0644246353 0.0644246353 0.0644246353 0.0820640679 0.0820640679 0.0820640679 0.0820640679 0.0589378233 0.0589378233 

13 0.0517959830 0.0478487216 0.0547982766 0.0547982766 0.0637644078 0.0637644078 0.0637644078 0.0808088903 0.0808088903 0.0808088903 0.0808088903 0.0575925555 0.0575925555 

14 0.0566713893 0.0502151226 0.0576880799 0.0576880799 0.0625591325 0.0625591325 0.0625591325 0.0811795580 0.0811795580 0.0811795580 0.0811795580 0.0571667797 0.0571667797 

15 .. 0.0671882913 0.0580384620 0.0656779676 0.0656779676 0.0619482678 0.0619482678 0.0619482678 0.0795090490 0.0795090:4.90 0.0795090490 0.0795090490 0.0573_4296!4 0.057_3429674 

16 0.0810035452 0.0715596945 0.0786905659 0.0786905659 0.0609466141 0.0609466141 0.0609466141 0.0727723312 0.0727723312 0.0727723312 0.0727723312 0.0567213465 0.0567213465 

17 .. · "0.0863864724 0.0838541123 .. 9.082.1.371575. 0.0821371575 0.0577256909 0,0577256909 0.0577256909 0.0583364761 0.0563364761 0.0563364761 0.0563364761 .0.055_t9t1S45., 0.0551911545 

18 0.0843264717 0.0874512168 0.0756929494 0.0756929494 0.0510164625 0.0510164625 0.0510164625 0.0371719560 0.0371719560 0.0371719560 0.0371719560 0.0531125437 0.0531125437 

19 0.0645951265 0.0604364374 0.0543673700 0.0543673700 -.o:o45099osss ~ ·" 0.0450990958 0.0450990958 0.02493366~ 8 0.0249336618 0.0249336618 0.0249336618 0.0487199307 .. 0.0487~ 99307 

20 0.0469536991 0.0424749554 0.0373951308 0.0373951308 0.0384927066 0.0384927066 0.0384927066 0.0188134711 0.0188134711 0.0188134711 0.0188134711 0.0432101938 0.0432101938 . 

21 0.0373781148 0.0353280630 .. 0.0293181.427 0.0293181427 0.0322318571 0.03223~8571 0.0322318571 0.0~62446774 0.0162446774 0.0162446774 ;0.0162446774 .0.0390319248 0.0390319248 

22 0.0316564842 0.0313403787 0.0249971308 .. 0.0249_971308 0.0282046747 0.0282046747 0.0282046747 0.0142456600 0.0142456600 . ... 0.0142456600 ... 0.01:42456600 0.0355118446 0.0355118446 

23 0.0245992722 0.0251562568 0.0203505544 0.0203505544 0.0242700475 0.0242700475 0.0242700475 0.0124474209_ 0.0124474209 0.0,124474209 0.0124474209 0.0317,71'1657 0.03~7711657 

24 0.0198157539 0.0189063955 0.0154623663 0.0154623663 0.0217813392 0.0217813392 0.0217813392 0.0110419727 0.0110419727 0.0110419727 0.0110419727 0.0278292477 0.0278292477 

Source: Statewide averages developed from Indiana Department of Transportation traffic count data. 
Indiana Default Hourly Distribution Factors for Road Type 5 -Urban Unrestricted Access: 

Source Types 

Hour 11 21 31 32 41 42 43 51 52 53 54 61 62 

1 0.0092279794 0.0085268711 0.0060669694 0.0060669694 0.0126828270 0.0126828270 0.0126828270 0.0037158531 0.0037158531 0.0037158531 0.0037158531 0.0106396358 0.0106396358 

2 0.0055316691 0.0048527626 0.0037675180 0.0037675180 0.0099485186 0.0099485186 0.0099485186 0.0038117041 0.0038117041 0.0038117041 0.0038117041 0.0124309233 0.0124309233 

3 ..... 0.0047273286 0.0037895145 0.0033129405 0.0033129405 0.0069482800 0.0069~82800 0.0069482800 0.0044165887 0.0044165887 0.0044165887 0.0044165887 0.0121505035 0.0121505035 

4 0.0047017359 0.0044201159 0.0042394230 0.0042394230 0.0113599945 0.0113599945 0.0113599945 0.0056282193 0.0056282193 0.0056282193 0.0056282193 0.0144699998 0.0144699998 

5 0.0081859928 0.0079416389 0.0087215410 0.0087215410 0.0153898606 0.0153898606 0.0153898606 0.0086545038 0.0086545038 0.0086545038 0.0086545038 0.0210508569 0.0210508569 .. 

6 0.0225361588 0.0203863353 0.0238668712 0.0238668712 0.0256929528 0.0256929528 0.0256929528 0.0191822890 0.0191822890 0.0191822890 0.0191822890 0.0299165403 0.0299165403 

7 0.0435184779 0.0478282898 0.054:1952158 0.0541952158 0.0448331117 _0.0448331_117 __ 0.0448331117 0.0418068371 0.0418068371 0.041,8068371 __ . 0.0418068371 0.0436775030 0.0436775030 

8 0.0602121997 0.0721456866 0.0675347974 0.0675347974 0.0691895946 0.0691895946 0.0691895946 0.0731482386 0.0731482386 0.0731482386 0.0731482386 0.0588646976 0.0588646976 

9 0.0556311148 0.0567013667 0.0643660182 0.0643660182 0.0747059425 0.0747059425 0.0747059425 0.0880926125 0.0880926125 0.0880926125 0.0880926125 0.0640862836 0.0640862836 

10 0.0485821670 0.0466493163 0.0603283916 0.0603283916 0.0803995772 0.0803995772 0.0803995772 0.0921313810 0.0921313810 0.0921313810 0.0921313810 0.0680944168 0.0680944168 

11 0.0495985610 0.0468148434 0.0590657789 0.0590657789 0.0774061573 0.0774061573 0.0774061573 0.0943973720 0.0943973720 0.0943973720 0.0943973720 0.0703404942 0.0703404942 

12 0.0573056055 0.0516032787 0.0615645883 0.0615645883 0.0753332651 0.0753332651 0.0753332651 0.0911430924 0.0911430924 0.0911430924 0.0911430924 0.0698309800 0.0698309800 

13 .. 0.0607752380 0.0555323143 0.0626732860 0.0626732860 0.0739763390 0.0739763390 0.0739763390 0.0895629476 0.0895629476 0.0895629476 0.0895629476 0.0685413869 0.0665413669 

14 0.0609214817 0.0562211160 0.0629887267 0.0629887267 0.0779993863 0.0779993863 0.0779993863 0.0912650000 0.0912650000 0.0912650000 0.0912650000 0.0671175363 0.0671175363 

.15 0.0649907135 0.0607579027 " .Q.0667909366 0.066'?:909366 0.0761037810. ~ .o_,0?:6.1037.S1_o 0.0761_037~10 0.0905726397 0.0905726397 0.0905726397 0.0905726397 0.0651260461 0.0651260461 

16 0.0724418316 0.0715477952 0.0751790074 0.0751790074 0.0728035185 0.0728035185 0.0728035185 0.0775387708 0.0775367708 0.0775367708 0.0775387708 0.0605241028 0.060524102~' 

17 0.0773519646 0.0603647101 0.0757034489 . _0.0757034469 0.0526405510 0.0526405510 o;o526405510 0.0464337395 0.0464337395 0.0464337395 0.0464337395 0.0557685235 0.0557685235 

18 0.0770777578 0.0832250581 0.0684911688 0.0664911688 0.0347686746 0.0347686748 0.0347686748 0.0260342365 0.0260342365 0.0260342365 0.0260342365 0.0506461891 0.0506461891 ... 

19 0.0635977420 0.0637849687 0.0526386278 0.0526386278 0.0285090860 0.0285090860 0.0285090860 0.0.1?:3341336 0.0173341336 0.0173341336 0.0173341336 0.0402747366 0.0402747366 

20 0.0483079600 0.0462284324 0.0372839274 0.0372839274 0.0220585728 0.0220585728 0.0220585728 0.0112536468 0.0112536468 0.0112536468 0.0112536468 0.0310667712 0.0310667712 

21 ... 0.0383158572 0.0386568197 0.0292289942 0.0292289942 .. 0.0174082029 0.0174082029 0.0174062029 0.0076615624 0.007661_5624 0.0076615624 0.0076615624 0.0268533367 .0.0268533367 

22 0.0305027859 0.0325107827 0.0236169348 0.0236169348 0.0137124544 0.0137124544 0.0137124544 0.0062358957 0.0062358957 0.0062358957 0.0062358957 0.0231915644 0.0231915644 . 

23 .. 0.0214502991 0.0236017051 0.0170601049 0.0170601049 0.0139442910 0.0139442910 0.0139442910 0.0053276381 0.0053276381 0.0053276381 0.0053276381 0.0193751364 0.019375~364 

24 0.0145073780 0.0159063752 0.0113147631 0.0113147831 0.0121850602 0.0121850602 0.0121850602 0.0046510979 0.0046510979 0.0046510979 0.0046510979 0.0159618330 0.0159618330 

Source: Statewide averages developed from Indiana Department ofTransportation traffic count data. 
AppendixG 

/d" n 1ana 0(; e au ltD"ID"t"bt" auy 1sn uton F t ac ors: 

dayiD 

monthiD 2 5 

1 0.2325411725 0.7674588275 

2 0.2380547378 0.7619452622 

3 0.2393402049 0.7606597951 

4 0.2396052454 0.7603947546 

5 0.2484757701 0.7515242299 

6 0.2489743665 0.7510256335 

7 0.2481153021 0.7518846979 

8 0.2527028648 0.7472971352 

9 0.2496078420 0. 7503921580 

10 0.2462808693 0. 7537191307 

11 0.24397 42406 0. 7560257594 

12 0.2258784720 0.7741215280 

Source: Statewide averages developed from Indiana Department of Transportation traffic count data. 
Appendix H 

Indiana Default Monthly Distribution Factors: 

monthiD monthVMTFraction 

1 0.0733424010 

2 0.0693661929 

3 0.0827036024 

4 0.0831789580 

5 0.0891346903 

6 0.0888150873 

7 0.0907968617 

8 0.0918542094 

9 0.0854175366 

10 0.0875162272 

11 0.0812354405 

12 0.0766387926 

Source: Statewide averages developed from Indiana Department of Transportation traffic count data. 
Appendix I 

Lake and Porter Counties Ramp Fractions: 

Ramp 

Road Type Fraction 

2 

4 

0.79% 

6.66% 

Source: Analysis of VHT from the CMAP travel demand model. 
AppendixB 

Lake and Porter Counties, Indiana, 

Maintenance Area Interagency 

Consultation Group Meeting 

Minutes/Summary 
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Interagency Consultation Group (ICG) Conference Call Minutes 

For the MOBILE6.2 to MOVES MVEB Replacement Update 

Related to the Lake and Porter Counties, Indiana, Maintenance Area under 

the 1997 8-Hour Ozone Standard 

ICG Conference Call Date and Time 

• September 25,2012 at lOam Eastern 

ICG Attendees 

• Shawn Seals (IDEM), Linda McClure (IDEM), Patricia Morris (EPA), Steve 

Smith (INDOT), Greg Katter (INDOT), Larry Heil (FHW A), and Bill Brown 

(NIRPC) 

ICG Discussion Topics and Conclusions 

I. For the Ozone MVEB Replacement submittal, various mobile source margins of 

safety were discussed. 

A. After discussion, the consensus of the ICG was that as long as the a 15% 

mobile source margin of safety for VOC and NOx emissions does not result in 

an exceedance of the all sources margins of safety, it was reasonable and 

appropriate for inclusion in MVEB replacement submittal. 

2. For the PM2.s MVEB Replacement submittal, various mobile source margins of 

safety were discussed. 

A. After discussion, the consensus of the ICG was that as long as the a 15% 

mobile source margin of safety for NOx and PM2_5 emissions does not result in 

an exceedance of the all sources margins of safety, it was reasonable and 

appropriate for inclusion in MVEB replacement submittal. 

B-1 
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Appendix C 

Lake and Porter Counties, Indiana, 

Maintenance Area under the 1997 

8-Hour Ozone Standard 

Public Participation Documentation 

• Legal Notice of Public Hearing 

o IDEM Webmaster Certification of Legal Notice Publication 

o Screenshot Verification of Legal Notice Posting on IDEM Website 

• Summary of Comments and Responses Thereto 

o No Comments Received 
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LEGAL NOTICE OF PUBLIC HEARING 

Motor Vehicle Emission Budgets Replacement Updates to the Maintenance Plans 

for the 1997 8-Hour Ozone and Annual Fine Particles Standards for Lake and 

Porter Counties, Indiana 

Notice is hereby given under 40 CFR 51.1 02 that the Indiana Department of 

Environmental Management (IDEM) is accepting written comment and providing an 

opportunity for public hearing regarding the Motor Vehicle Emission Budget (MVEB) 

replacement updates to the maintenance plans for the 1997 8-hour ozone and annual fine 

particles standards for Lake and Porter counties, Indiana. Onroad emissions for the 

original submittals were calculated using the MOBILE6.2 mobile model and are now 

being replaced with the United States Environmental Protection Agency's (U.S. EPA's) 

recently adopted Motor Vehicle Emissions Simulator (MOVES) mobile model. All 

interested persons are invited and will be given reasonable oppmiunity to express their 

views conceming the submittal of the proposed MVEB replacement updates to the Lake 

and Pmier counties, Indiana, maintenance areas for the 1997 8-hour ozone and annual 

fine patiicles standard. 

The purpose of this notice is to solicit public comment on Indiana's proposed 

MVEB replacement updates. Lake and Porter counties, Indiana, were designated as 

nonattainment for the 1997 8-hour ozone and annual fine particles standards and are 

subject to the requirements of Section 172 of the Clean Air Act (CAA). One of the 

compliance requirements mandated by Section 175A(b) of the CAA, is the development 

of a plan demonstrating that maintenance areas will continue to meet the 1997 8-hour 

ozone and annual fine patiicles standard for the next ten years, which includes MVEBs 

for onroad sources, beyond the current maintenance period. This submittal of the 

proposed MVEB replacement updates to the Request for Redesignation and Maintenance 

Plan for Ozone Attainment in the 8-How· Ozone Nonattainment Area and Request for 

Redesignation and Maintenance Plan Under the Annual National Ambient Air Quality 

Standard for Fine Particles for the Lake and Porter counties, Indiana, maintenance areas 

that were originally submitted on June 5, 2009, and May 26, 2011 respectively, are being 

drafted and submitted consistent with U.S. EPA guidance. Upon completion of this 

public notice process, the MOBILE6.2-based to MOVES-based MVEB replacement 

updates will be submitted to U.S. EPA for approval into the State Implementation Plans. 

Copies of the draft documents will be available on or before December 21,2012, 

to any person upon request and at the following locations: 

• Indiana Department of Environmental Management, Office of Air Quality, 

Indiana Government Center Nmih, 100 North Senate Avenue, Room N1003, 

Indianapolis, Indiana. 

• Indiana Department of Environmental Management, Nmihwest Regional Office, 

8380 Louisiana Street, Menillville, Indiana. 

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• Crown Point Community Library, 214 South Court Street, Crown Point, Indiana. 

• Lake County Public Library-Highland Branch, located at 2841 Jewett Street, 

Highland Indiana. 

• Valparaiso Public Library, 103 Jefferson Street, Valparaiso, Indiana. 

• Gary Public Library, 220 West 5th Avenue, Gary, Indiana. 

• Hammond Public Library, 564 State Street, Hammond, Indiana. 

• Whiting Public Library, 1735 Oliver Street, Whiting, Indiana. 

The draft documents will also be available on the following web page: 

http://www.in.gov/idem/4658.htm 

An electronic version of all MOVES mobile model input and output files will be 

available at the public hearing, if held, or upon request. 

Any person may submit written comments on the MVEB replacement update to 

the Lake and Porter counties, Indiana, 1997 8-hour ozone maintenance area on or before 

January 25, 2013. Written comments should be directed to Mr. Shawn Seals, Mail Code 

61-50, Office of Air Quality, Indiana Department of Environmental Management, 100 

North Senate Avenue, Indianapolis, Indiana 46204; or fax (317) 233-5967; or email at 

SSeals@idem.in.gov. Interested parties may also present oral or written comments at the 

public hearing, if held. Oral statements will be heard, but for the accuracy ofthe record, 

statements should be submitted in writing. Written statements may be submitted to the 

attendant designated to receive written comments at the public hearing. 

A public hearing on the MVEB replacement updates to the maintenance plans for 

the 1997 8-hour ozone and annual fine particles standards for Lake and Porter counties, 

Indiana will be held if a public hearing request is received by January 14, 2013. A 

hearing has been scheduled for January 23, 2013. The meeting will convene at 6:00p.m. 

(local time) at the Lake Station-New Chicago Branch Public Library located at 2007 

Central Avenue, Lake Station, IN 46405. If a request for a public hearing is not received 

by January 14, 2013, the hearing will be cancelled. Interested pmiies can check the 

online IDEM calendar at http://www.in.gov/idem/5390.htm or contact Mr. Shawn Seals 

at (317) 233-0425, after January 14,2013, to see if the hearing has been cancelled or will 

convene. 

A transcript of the hearing and all written submissions provided at the public 

hearing shall be open to public inspection at IDEM and copies may be made available to 

any person upon payment of reproduction costs. Any person heard or represented at the 

hearing or requesting notice shall be given written notice of actions resulting from the 

hearing. 

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For additional information contact Mr. Shawn Seals, at the Indiana Department of 

Environmental Management, Office of Air Quality, Room N1001, Indiana Government 

Center North, 100 North Senate Avenue, Indianapolis, IN 46204 or call (317) 233-0425 

or (800) 451-6027 ext. 3-0425 (in Indiana). 

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

Individuals requiring reasonable accommodations for participation in this hearing, if 

held, should contact the IDEM Americans with Disabilities Act (ADA) coordinator at: 

Attn: ADA Coordinator 

Indiana Department of Environmental Management- Mail Code 50-10 

100 North Senate Avenue 

Indianapolis, IN 46204-2251 

Or call (317) 233-1785 (voice) or (317) 232-6565 (FDD). Please provide a minimum of 

72 hours notification. 

c- 3 
IDEM WEBMASTER CERTIFICATION OF LEGAL NOTICE PUBLICATION 

December 19,2012 

CERTIFICATE OF PUBLICATION 

This is to certify that the Indiana Department of Environmental Management (IDEM) 

Notice of the opportunity for a Public Hearing regarding the following: 

• Motor Vehicle Emission Budgets Replacement Updates to the Maintenance Plans 

for the 1997 8-Hour Ozone and Annual Fine Particles Standards for Lake and 

Porter Counties, Indiana 

was published on IDEM's web site on December 14, 2012. It is expected that it will 

remain posted on the site until at least January 25, 2013. 

The notice in full was available online at the following web address, under "Northwest 

Indiana", "Lake and Pmier". 

http://www.in.gov/idem/6408.htm 

Web publication of the notice was at the request of Scott Deloney, Branch Chief, 

Programs Branch, Office of Air Quality, IDEM. 

Attachments: 

Copy of web page as published. 

By: 

Mike Finklestein 

IDEM Webmaster 

C - 4 
SCREENSHOT VERIFICATION OF LEGAL NOTICE POSTING ON IDEM WEBSITE 

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