IDEM INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT We Protect Hoosiers and Our Environment. 100 N. Senate Avenue • Indianapolis, IN 46204 (800) 451-6027 • (317) 232-8603 • www.idem.IN

. gov Michael R. Pence Governor



### Ms. Susan Hedman Regional Administrator U.S

. Environmental Protection Agency Region 5 77 West Jackson Boulevard Chicago, IL 60604-3950 Dear Ms. Hedman: July 2, 2013 Thomas W. Easterly C

ommi ssi011 er



### Re: MOBILE6.0 to MOVES MVEB Replacement Update to the Maintenance Plan for the 1997 8-Hour Ozone Standard for Vanderburgh and Warrick Counties, Indiana The Indiana Department of Environmental Management (IDEM) submits the enclosed MOBILE6.0 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 Vanderburgh and Warrick 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 Basic Nonattainment Area, for Vanderburgh and Warrick counties, Indiana, submitted by IDEM on June 2, 2005, with an effective date of January 30, 2006. 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 Vanderburgh and Warrick counties, Indiana, if a public hearing request was received by June 12, 2013. A hearing was scheduled for June 20, 2013. No request for a public hearing was received and the hearing was cancelled. IDEM received no comments during the public notice process
. Documents related to the public participation process are included in Appendix C of this submittal

An Equal Opportunity Employer 

# 0 @ R ecycled Paper A State**th at~** 

### Ms. Hedman Page 2 This MOBILE6.0 to MOVES MVEB replacement update incorporates onroad emission estimates and revised MVEBs using U.S. EPA's recently adopted MOVES model. The on road emission estimates were calculated using the MOVES-based emission factors and data extracted from the Vanderburgh and Warrick 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 original 1997 8-hour ozone maintenance plan. Onroad 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 Vanderburgh and Warrick 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 MOBILE6.0 to MOVES MVEB replacement update and revised transportation conformity budgets and approval into Indiana's State Implementation Plan for the Vanderburgh and Warrick 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,



# ~·· **3.1?'-y~** Keith Baugues Assistant Commissioner Office of Air Quality

On road Emissions MOBILE6.0 to MOVES MVEB Replacement Submittal for the Vanderburgh and Warrick Counties, Indiana, Maintenance Area under the 1997 8-Hour Ozone Standard and Appendices

### Ms. Hedman Page 3

cc: Doug Aburano, U.S. EPA Region 5 (no enclosures) Steve Rosenthal, U.S. EPA Region 5 (no enclosures) Ed Doty, U.S. EPA Region 5 (no enclosures) Pam Blakley, U.S. EPA Region 5 (no enclosures) Anthony Maietta, U.S. EPA Region 5 (no enclosures) Seyed Shokouhzadeh, EMPO (w/ enclosures) Keith Baugues, IDEM-OAQ (no enclosures) Scott Deloney, IDEM (no enclosures) Shawn Seals, IDEM (w/ enclosures)

# Onroad Emissions MOBILE6.0 to MOVES Replacement Submittal

For the Vanderburgh and Warrick Counties, Indiana, Maintenance Area under the 1997 8-Hour Ozone Standard

FINAL July 2013

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### Introduction On June 2, 2005, the Indiana Depmtment of Environmental Management (IDEM) submitted a 

### Requestfor Redesignation and Maintenance Planfor Ozone Attainment in the 8-Hour Ozone Nonatfainment Area, for Vanderburgh and Warrick Counties, Indiana. The United States Environmental Protection Agency (U.S. EPA) subsequently approved the Indiana redesignation of Vanderburgh and Warrick counties, Indiana, to attainment for the 1997 8-hour ozone standard on December 29, 2005 with an effective date ofJanuary 30, 2006 (70 FR 77026). Omoad emissions for the June 2, 2005, submittal were calculated using MOBILE6.0. 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 MOBILE6.0 to MOVES replacement update to the previously submitted 1997 8-hour ozone maintenance plan for the Vanderburgh and Warrick counties, Indiana, ozone maintenance area that incorporates MOVESbased onroad emissions. 

### Emission Inventory
Table 4.1 was included without title in Appendix B ofthe original Redesignation Petition and Maintenance Plan. Table 4.1 -A (to be considered a replacement ofthe table included in Appendix B) has been revised to incorporate updated omoad emission estimates for nitrogen oxides (NO,) and volatile organic compounds (VOCs) for the years 2002, 2010, and 2015; it results in a different overall safety margin for the area. 

### Table 4.1 Comparison of2002, 2010, and 2015 Emission Estimates in Tons Per Summer Day, Vauderburgh and Wat-rick Counties, 1997 8-Hour Ozone Nonattainment Area (MOBILE6.0-based Onroad Emissions) Sector 2002 NO, 2010 NO, 2015NO,

Area 2.95 3.20 3.27 Non-road 5.88 4.52 3.23

Mobile MAG l8{j**~**



### Point 70.19 30.18 31.43 

### Total 9M2 4+.49 

### 494 Sector 2002VOC 2010VOC 2015VOC

Area 18.60 21.36 23.46 Non-road 6.16 4.42 3.80

Mobile -1-hU**~** 

### 4-+.6

Point 5.16 6.77 8.09 

### Total 41-.H**~ ~** 



### 1

### Table 4.1-A Compar·ison of 2002, 2010, and 2015 Emission Estimates in Tons Per Summer Day, Vander·burgh and Wanicl<. Counties, 1997 8-Hour Ozone Maintenance Area (MOVES-based Onroad Emissions) Sector 2002 NOx 2010 NOx 2015 NOx Area 2.95 3.20 3.27 Nonroad 5.88 4.52 3.23

Onroad 36.23 18.99 10

.96

Point 70.19 30.18 31.43 Total 115.25 56.89 48.89 Sector 2002 

## voc 2010 

## voc 2015 

## voc

Area 18.60 21.36 23.46 Nonroad 6.16 4.42 3.80

Onroad 12.16 6.84 4.37

Point 5.16 6.77 8.09 Total 42.08 39.39 39.72
Onroad emission estimates in Table 4.1 -A were calculat ed 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 (MOBILE6.0). Preliminary use ofthe MOVES model indicates that emis s ion estimates can be considerably different than similar calculations using MOBJLE6.0, which was used to create the original MVEBs for the Vanderburgh and Warrick counties, Indiana, 1997 8- hour ozone nonattainment area. A general s ummary 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 stra tegy ass umptions for non-mobile sources (i.e. area, nomoad, and point) from the original submittal for the years 2002, 2010, and 2015 were developed before the economic challenges ofthe last several years . Because of this, the factors included in the original submittal may project more growth than will actually o ccur in the future. As a result, the growth and control strategy assumpt ions for the non-mobile sources for the yea rs 2002, 20 10 , and 2015 continue to be valid and do not affect the overall conclusions ofthe plan. Omoad safety margins have been included for omoad emission estimates to accommodate the wide mTay ofassumptions that are factored into the ca lculation process. Since assumptions change over time, it is necessary to have an onroad safety margin that w ill accmmnodate the impact of refined assumptions in the process. The plan continues to meet all applicable Clean Air Act (CAA) requirements as the revised emission inventor ies clearly illustrate that total NOx and VOC emissions in the Vanderburgh and Warrick counties, Indiana, 1997 8-hour ozone maintenance area will continue to decline leading to local reductions between 2002 (base year) and 2015 (maintenance plan hori zon budget year).

2

### Transportation Conformity Budgets Table 5.1 was included on Page 18 of the original Redesignation Petition and Maintenance Plan for the Vanderburgh and WatTick counties, Indiana, 1997 8-hour ozone maintenance area. Table 5.1- A (to be considered a replacement ofTable 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 Vanderburgh and Warrick Counties, 1997 8-Hour Ozone Nonattainment Area (MOBILE6.0-based Onroad Emissions)
2002 2010 2015 VMT (miles/day) 6,225,7 64 6,520,671 6,463,504 VOC (tons/day)**~ ~**  

### 4.-R 

### NOx (tons/day) 

### -l-6-AG**~ ~**  

### Table 5.1- A Emission Estimations for Onroad Mobile Sources for the Vanderburgh and Warrick Counties, 1997 8-Hour Ozone Nonattainment Area (MOVES-based Onroad Emissions)
2002 2010 2015 VOC (tons/day) 12. 16 6.84 4 .37 

### NOx (tons/day) 36

.23 18. 99 10. 96
Table 5.2 was also included on Page 18 ofthe original Redesignation Petition and Maintenance Plan for the Vanderburgh and Warrick 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 Mobile Vehicle Emission Budgets (MOBILE6.0-based Onroad Emissions)
2015 tons/day 

## voc 4.-2.-G NOx**~**


### 3

### Table 5.2- A Motor Vchicle E mission Budgets for the Vanderburgh and Warrick counties, Indiana, 1997 8-Hour· Ozone Maintenance Area (MOVES-based Onroad Emissions) 2015 VOC (tons/summer day) 5.02 NOx (tons/summer day) 12.61
Through the interagency consultation process, it was deter mined that a maintenance plan horizon year budget of2015, would be appropriate. The interagency consultation group approved onroad margins of safety of fifteen percent ( 15%) for both VOC and NOx onroad em ission e stimates for the year 2015. A summary ofthi s interagency consultation discussion can be found in Appendix B. These revised em ission inventories clearly illustrate that omoad VOC and NOxemissions in the Vanderburgh and Warrick counties, Indiana, 1997 8-hour ozone maintenance area w ill co ntinue to decline leading to loca l reductions between 2002 (base year) and 2015 (maintenance plan horizon budget year)

. Furthermore, when compared to the overall safety margin as defined in the Code ofFederal Regulations (CFR) at 40 CFR 93 .10 I , it is evident the onroad safety margin all ocation is reasonable and appropriate. More specifically, even with the allocation ofan 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 const rained to ensure that the total emissions (i

.e., all source categories) do not exceed the 2002 attainment year emissions ofeither VOC or NOx, thereby ensuring continued maintenance ofthe 1997 8-hom ozone standard. Conclusion This MOBILE6.0 to MOVES replacement update to the previously submitted Request for Redesignation and Maintenance Plan for Ozone A l!ainment in the 8-H our Ozone Basic Nonattainmen tArea, for Vanderburgh and Warrick counties, Indiana incorporates onroad emission estimates and a revised MVEB using U.S. EPA's recently adopted MOVES model. MVEBs have been revised in anticipation ofthe mandatory use ofthe MOVES model in future transportation conformity determinations. The omoad emission estimates were calculated using the MOVES

based emission factors and data extracted from the ar ea'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 t hat total VOC and NOx emissions (i.e. , all source categori es) do not exceed attainment year (2002) emissions to ensure continued maintenance ofthe 1997 8-hour ozone standard. With the addition ofMOVES-based onroad safety margi ns applied to mobile sources, the Vanderburgh and Warrick counties, Indiana, ozone maintenance area will conti n ue to remain well below the overall safety margins for all somces into the future. As such, the 1997 8-hour ozone maintena nce plan for Vanderburgh and Warrick counties, Indiana, continues to meet all applicable CAA requirements

. 4

# Appendix A



# Vanderburgh and Warrick Counties, Indiana, Maintenance Area MOVES Methodology

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# Vanderburgh and Warrick Counties MOVES2010a Input Data and Parameters
INDOT P lanning Contract 

# Final Report October 4, 2012



# CDMih Sm1Table 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- MOVES201 Oa Input Settings and Assumptions Appendix B- Vehicle Age Distributions for Vanderburgh and Warrick Counties Appendix C- Vehicle Populations for Vanderburgh and Warrick Counties Appendix D- Meteorological Data for Vanderburgh and Warrick 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 FractionsOverview: This report is being written to document the input parameters for a set of MOVES201 Oa runs for the Vanderburgh and Warrick Counties 8-hour Ozone Maintenance Area and the Vanderburgh and Warrick Counties PM 2.5 non-attainment area. This report contains a discussion on the intended input settings used in MOVES201 Oa 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 LAOCO 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 MOVES2010a 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 Vanderburgh and Warrick 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 LOT4). 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 lnventorv 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.

2Table 3: Distribution of MOBILES 2 Light Duty Trucks into 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 MOVES201 0 for Emission Inventory 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 calculated for each source type. The Evansville MPO, which is the metropolitan planning organization (MPO) for Vanderburgh and Warrick 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

3estimates derived for those 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 Vanderburgh and Warrick 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 Request for Redesiqnation and Maintenance Plan for Ozone Attainment in the 8-hour Ozone Basic Nonattainment Area, Appendix D, developed by Indiana Department of Environmental Management in June 2, 2005 and the draft Request for Redesiqnation and Maintenance Plan under the Annual National Ambient Air Quality Standard for Fine Particles, Appendix F, developed by the Indiana Department of Environmental Management in January, 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 Vanderburgh and Warrick 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.

4SiteiD 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 SR332 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 8/3/10-12/6/10 FORT WAYNE ALLEN 1-69 0.53 mi N of 4 Good SR 3 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 I 70 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.

5Furthermore, 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.

6Appendix A Number ofRuns:

Input Item Ozone PM 2.5 Years 2002 , 2010, 2008 , 2010 , 2015 , 2020 , 2015, 2020 , 2025, 2030, 2022 , 2030, 2035 , 2040 2035,2040 Pollutants/ Volatil e PM 2

.5 with all Processes Organic subsp ecies: Compound NOx (VOC ), NOx, and suppo rting Meteorology Summ e r Ave rage Annual #of MOVES 8 8 runsGeneral Parameters: MOVES Input Item Screen Ozone PM 2

.5 Description Description User Choice Scale Doma in/Sca le County Ca lculation Typ e Emi ss ion Rate Time Spans Time Hour Hour Aggregation Leve l Year 2002, 2010, 2008, 2010, 20 15 , 2020, 2016, 2020, 2025,2 030 , 2022,2030, 2035,2040 2035 , 2040 Months July April Days Weekday Weekday Hours Se lect A ll Select All Geographic Geographic Vanderburgh Vanderburgh Bounds Bounds County* Cou nty* Vehicles Vehicles All Gas and Diesel Comb i nati ons
Road Type Road Type Select All Pollutants/ Po llutants/ VOC, NOx, and PM 2.5 with all Processes Processes supporting subspecies ; NOx General Database Name Eva nsville Ozone Evansville PM Output Units Select "Grams" and "Miles" and "Million BTU" Activity Di stance, Po pul at ion Output On Road Select "Sou rce Use Type" and "Road Emissions Type" D e tail

* Re prese nts both Vanderb u r gh a nd W a rrick Cou nties
.

### 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 IN DOT using an analysis of permanent count station data from a statewide data set. HourVMTFraction Statewide default hourly fractions developed by INDOT
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 Populat ion by Age of Vehicle) Ramp Fraction RoadType Meteorology ZoneMonthHour Data

Fuel (% of FueiFormulation Market Share by Fuel Type) FueiSupply
1/M 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.
MOBILE6 Summer Met Data MOBILE6 12 month Met Converted to MOVES format Data Converted to MOVES format and averaged to annual meteorology MOVES Defaults Vanderburgh County MOVES Defaults for Summer (check if varies among counties) Vanderburgh County MOVES Defaults for annual (check if varies among counties) No ProgramAppendix B Vehicle Aae Distributions for Vanderbu_tgp and Warrick Counties: Source Types ageid 11 21 31 32 41 42 43 51 52 53 54 61 62 0 0.2109690540 0.0254913494 0.0108613399 0.0283536975 0.0643023355 0.0545743076 0.0622220643 0.0494240790 0.0588526168 0.0787544027 0.0615095870 0.0535634660 0.0670845256 1 0.1921154969 0.0471761977 0.0455523407 0.0691813189 0.0626728412 0.0531913309 0.0606452875 0.0481716155 0.0573612230 0.0767586735 0.0599508636 0.0535634660 0.0670845256 2 0.1573471585 0.0580075242 0.0532532087 0.0714378942 0.0624853859 0.0530322328 0.0604638952 0.0480275345 0.0571896519 0.0765290827 0.0597715492 0.0541045093 0.0677621447 3 0.1359771581 0.0527361307 0.0471399955 0.0603686832 0.0624229593 0.0529792497 0.0604034894 O.D479795509 0.0571325186 0.0764526251 0.0597118340 0.0575579884 0.0720873878 4 0.1058454735 0.0539901675 0.0713109281 0.0783771127 0.0617369906 0.0523970560 0.0597397140 0.0474523026 0.0565046834 0.0756124785 0.0590556596 0.0564182312 0.0706599203 5 0.0750909142 0.0553551809 0.0640255212 0.0718634254 0.0559170498 0.0474575929 0.0541080614 0.0429789769 0.0511779950 0.0684845018 0.0534884926 0.0489290859 0.0612802835 6 0.0476805323 0.0577522778 0.0726611766 0.0639022521 0.0468365056 0.0397508123 0.0453212873 0.0359994879 0.0428670388 0.0573630896 0.0448023279 0.0366034411 0.0458432683 7 0.0331026886 0.0625797645 0.0709548186 0.0653071651 0.0425786431 0.0361370941 0.0412011709 0.0327268079 0.0389700355 0.0521482660 0.0407293873 0.0340742206 0.0426755959 8 0.0197278356 0.0632456247 0.0616514578 0.0567925412 0.0468268516 0.0397426124 0.0453119367 0.0359920640 0.0428582007 0.0573512681 0.0447930981 0.03580931 DO 0.0448486759 9 0.0118473747 0.0721570542 0.0623636768 0.0628379241 0.0534377006 0.0453533365 0.0517089150 0.0410733035 0.0489087688 0.0654479137 0.0511168252 0.0526288382 0.0659139597 10 0.0053251777 0.0654096705 0.0604644261 0.0567073950 0.0532712252 0.0452120443 0.0515478328 0.0409453420 0.0487564067 0.0652440247 0.0509575859 0.0624520143 0.0782168041 11 0.0025378610 0.0559211621 0.0512946064 0.0461492614 0.0407951886 0.0536203440 0.0411075833 0.0313560350 0.0391491717 0.0523881239 0.0302729398 0.0478258601 0.0598985955 12 0.0013011470 0.0508939174 0.0480747830 0. 0399335859 0.0331924560 0.0489936472 ,0.0382933197 0.0255124310 0.0294483131 0.0394065607 0.0466101866 0.0389128550 0.0487354179 13 0.0006124019 0.0430811573 0.0375695526 0.0292051599 0.0277347637 0.0456089741 0.0333751020 0.0545980574 0.0316399801 0.0194774783 0.0291673253 0.0325145854 0.0462990441 14 0.0002476898 0.0433142083 0.0361154388 0.0285665631 0.0364294706 0.0377746681 0.0430863640 0.0632656498 0.0364439725 0.0194691525 0.0347804437 0.0427077419 0.0462072388 15 0.0001527705 0.0346136346 0.0357444914 0.0309932309 0.0283511969 0.0332950401 0.0210164622 0.0395649332 0.0357887614 0.0311848083 0.0335202065 0.0332372597 0.0300444032 16 0.0000668536 0.0300081013 0.0257882632 0.0210311210 0.0235884296

**0.027~132162** 0.0253671498 0.0341566540 0.0259987277 0.0230196849 0.0233151075 0.0276536739 0.0230524492 17 0.0000299603 0.0235936477 0.0221233029 0.0179658564 0.0175637044 0.0244970846 0.0206833627 0.0146346390 0.0197956396 0.0052258132 0.0206748599 0.0205906442 0.0138452217 18 0.0000127409 0.0196650723 0.0184731805 0.0145600068 0.0201192241 0.0250480695 0.0266888558 0.0401958334 0.0193740288 0.0037212159 0.0155464816 0.0235865809 0.0100066460 19 0.0000055369 0.0160361340 0.0154017360 0.0115798885 0.0225790392 0.0366610768 0.0301447753 0.0342277190 0.0227335396 0.0175775477 0.0203628520 0.0264703224 0.0098603738 20 0.0000022027

.. 0.0141717254 0.0150307886 0.0129848014 0.0226407923 0.0281971934 0.0173882093 0.0270081845 0.0289395633 0.0183874556 0.0265944575 0.0265427135 0.0095755112 21 0.0000010015 0.0106315684 0.0149120855 0.0124739240 0.0212965445 0.0224413685 0.0209032932 0.0367430589 0.0255089927 0.0121624816 0.0238465850 0.0249667984 0.0083402541 22 0.0000005320 0.0082566669 0.0097633356 0.0079611733 0.0221366577 0.0207614938 0.0211741003 0.0294241579 0.0211707159 0.0029207200 0.0232916866 0.0259516972 0.0021970287 23 0.0000002372 0.0061814025 0.0097781735 0.0078334540 0.0187753208 0.0176845935 0.0186862600 0.0367365508 0.0255742899 0.0006595597 0.0173635700 0.0220110680 0.0022815392 24 0.0000001072 0.0051493192 0.0086653313 0.0079611733 0.0165801584 0.0153441343 0.0162223474 0.0195371739 0.0181341022 0.0013228019 0.0186391363 0.0194375881 0.0028947085 25 0.0000000515 0.0038065010 0.0056235626 0.0052364937 0.0130464803 0,0119613578 0.0125269842 0.0202862884 0.0101534224 0.0013255722 0.0189070434 0.0152949162 0.0014963357 26 0.0000000201 0.0022417295 0.0038430151 0.0030226915 0.0052066606 0.0114707358 0.0046276161 0.0058785937 0.0158244798 0.0000000000 0.0123859355 0.0061039775 0.0003051544 27 0.0000000084 0.0014426972 0.0025817939 0.0022989484 0.0044375500 0.0062552616 0.0034269422 0.0066192300 0.0082431519 0.0005853113 0.0073123264 0.0052023202 0.0002365920 28 0.0000000046 0.0013983065 ,0.0019586023 0.0012771936 0.0038534093 0.0027153367 0.0040227141 0.0058648852 0.0078447522 0.0004224309 0.0040199156 0.0045175071 0.0007539156 29 0.0000000027 0.0016979436 0.0006825432 0.0005108774 0.0050202650 0.0073813428 0.0039557847 0.0014702211 0.0082910352 0.0000000000 0.0005297244 0.0058854602 0.0002483418 30 0.0000000060 0.0139941626 0.0163365235 0.0133253864 0.0041641999 0.0025473919 0.0046291194 0.0021486392 0.0093642209 0.0005969550 0.0069720059 0.0048818593 0.0002641374

Source: Quality assured vehicle registration ctata for the combined Vanderburgh County and Warrick County area for source types 21, 32, and 32, MOVES2010a default distributions for all other source types.Appendix C Vanderburah and Warrick Counties Vehicle p ooutations: Vehicle Populations Source Types 11 21 31 32 41 42 43 51 52 53 54 51 52 Annual Populations 2008 4,425 94,893 73,275 22,434 83 43 560 22 1,503 193 348 2,210 2,644 2009 4,446 95,335 73,616 22,539 83 43 564 22 1,513 194 350 2,225 2.662 2010 4,466 95,780 73,960 22,644 84 44 568 22 1,524 196 352 2,241 2,681 2011 4,487 96,227 74,305 22,750 84 44 572 22 1,535 197 355 2,257 2,700 2012 4,508 96,676 74,652 22,856 85 44 576 23 1,545 199 357 2,272 2,719 2013 4,529 97,127 75,000 22,962 85 45 580 23 1.556 200 360 2,288 2,738 2014 4,550 97,580 75,350 23,069 86 45 584 23 1,567 201 362 2,304 2,757 2015 4,572 98,035 75,701 23,177 87 45 588 23 1,578 203 365 2.321 2,776 2016 4,593 98,493 76,055 23,285 87 46 592 23 1,589 204 368 2,337 2,796 2017 4,614 98,952 76,409 23,394 88 46 597 23 1,600 206 370 2,353 2,815 2018 4,636 99,414 76,766 23,503 88 46 601 24 1,612 207 373 2,370 2,835. 2019 4,657 99,878 77,124 23,613 89 47 605 24 1,623 209 375 2,386 2,855 2020 4,679 .J00,344 77,484 23,723 90 47 609 24 1,634 210 378 2,403 2,875 2021 4,701 100,812 77,845 23,834 90 47 613 24 1,646 212 381 2,420 2,895 2022 4,723 101,282 78,209 23,945 91 48 618 24 1,657 213 383 2,437 2,915

.. 2023 4,745 101,755 78,573 24,056 92 48 622 24 1,669 215 386 2,454 2,936 2024 4,767 102,229

. 78,940 24,169 92 48 626 25 1,681 216 389 2,47,1 2,957 2025 4,789 102,706 79,308 24.281 93 49 631 25 1.692 218 391 2,489 2,977 2026 4,812 103,186 79,678 24,395 94 49 635 25 1,704 219 394 2,506 2,998 2027 4,834 103,667 80,050 24,509 94 49 640 25 1,716 221 397 2,524 3.019 2028 4,857 104,151 80,424 24,623 95 50 644 25 1,728 222 400 2,541 3,040 2029 4,879 104,637 80,799 24.738 96 50 649 25 1,741 224 402 2,559 3,062 2030 4,902 105,125 81,176 24,853 96 50 653 26 1,753 225 405 2,577 3,083 2031 4,925 105,615 81,554 24.969 97 51 658 26 1,765 227 408 2,595 3,105 2032 4,948 106,108 81,935 25,086 98 51 682 26 1,777 228 411 2,614 3,127 2033 4,971 106,603 82,317 25,203 98 51 667 26 1,790 230 414 2,632 3,149 2034 4,994 107,100 82,701 25,320 99 52 672 26 1,802 232 417 2,650 3,171 2035 5,018 107,600 83,087 25,438 100 52 677 27 1,815 233 420 2,669 3,193 2036 5,041 108,102 83,475 25,557 100 53 681 27 1,828 235 423 2,688 3,215 2037 5,065 108,606 83,864 25,676 101 53 686 27 1,841 237 426 2,707 3,238 2038 5,088 109,113 84,255 25,796 102 53 691 27 1,854 238 429 2,726 3,261 2039 5,112 109,622 84,649 25,916 102 54 696 27 1,867 240 432 2,745 3,284 2040 5,136 110,134 85.043 26,037 103 54 701 27 1,880 242 435 2,764 3,307 Source. Quality assured vehicle reg1strat1on data for the combmed Vanderburgh County and Wamck County area for source types 21, 32, and 32, MOVES2010a default m11eage accumu1at1on rates for all other source types. Population growth factors are taken from local socioeconomic data forecasts.Appendix D Vanderburgh and arrick Counties Meteorological Data: Ozone PM 2.5 monthiD zoneiD HouriD temperature reiHumidity monthiD zoneiD HouriD temperature reiHumidity 7 181730 1 72.6 63.9 4 181730 1 49.9 100.0 7 181730 2 71.3 66.6 4 181730 2 48.7 100.0 7 181730 3 70.4 68.8 4 181730 3 47.7 100.0 7 181730 4 69.7 70.5 4 181730 4 47.0 100.0 7 181730 5 69.1 71.8 4 181730 5 46.5 100.0 7 181730 6 68.5 73.3 4 181730 6 45.8 100.0 7 181730 7 68.0 74.6 4 181730 7 45.3 100.0 7 181730 8 68.4 73.5 4 181730 8 45.7 100.0 7 181730 9 71.1 67.2 4 181730 9 48.4 100.0 7 181730 10 75.3 58.3 4 181730 10 52.7 97.4 7 181730 11 79.6 50.6 4 181730 11 57.1 83.1 7 181730 12 83.2 44.9 4 181730 12 60.8 72.7 7 181730 13 86.5 40.5 4 181730 13 64.1 64.7 7 181730 14 88.2 38.3 4 181730 14 65.9 60.8 7 181730 15 88.8 37.6 4 181730 15 66.5 59.5 7 181730 16 89.0 37.4 4 181730 16 66.7 59.1 7 181730 17 88.6 37.9 4 181730 17 66.3 60.0 7 181730 18 87.3 39.4 4 181730 18 65.0 62.7 7 181730 19 85.2 42.1 4 181730 19 62.9 67.6 7 181730 20 82.5 45.9 4 181730 20 60.1 74.5 7 181730 21 79.8 50.2 4 181730 21 57.3 82.3 7 181730 22 77.5 54.2 4 181730 22 54.9 89.8 7 181730 23 75.8 57.3 4 181730 23 53.2 95.5 7 181730 24 74.1 60.6 4 181730 24 51.5 100.0 Source: Mobile 6.2 reported meteorological data from Request for Redesignation and MMntenance Plan for Ozone Attainment in the 8-hour Ozone Basic Nonattainment

**Area~** Appendix D, developed by Indiana Department of Environmental Management in June 2, 2005 and the draft Request for Redesignation and Maintenance Plan under the Annual National Ambient Air Quality Standard for Fine Particles, Appendix F, developed by the Indiana Department of Environmental Management in January, 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 Passenger 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 0.003973041 0.569953374 0.254198647 0.002831718 0.009082816 0.159960404 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.Appendix F fnd1ana D ' e auft Hourfv Distribution F actors for Road Tvoe 2- R IR ura estricted 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 O.D126607789 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 0.0084288563 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 0.0174195788 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 0.0390974746 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 0.055n12484 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 0.06286019J2 0.0577540296 0.0577540296 17 0.0754978425 0.0847160034 0.0792545794 0.0792545794 0.0557979766 0.0557979766 0.0557979766 0.0534712990 0.0534712990 0.0534712990 0.0534712990 0.0562910814 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 0.0620082513 0.0521045300 0.0521045300 0.0459665909 0.0459665909 0.0459665909 0.0363413126 0.0363413126 0.0363413126 0.0363413126 0.0502215100 0.0502215100 20 0.0432143461 0.0459015588 0.0390794599 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 0.0311015284 0.0311015284 0.0418602463 0.0418602463 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 0.0182964081 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 0.0157396039 0.0157396039 0.0307625891 0.0307625891
Source: Statewide averages developed from Indiana Department of Transportation traffic count data.n 1ana D (; ltH f o· b eau ounv. !Stn ut10n F fl R dT actors or oa IVIJe3- R IU nres ncte ura ccess: 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 0.00464B5153 0.0046485153 0.0073497934 0.0073497934 0.0073497934 0.0073497934 0.0165479051 0.0165479051 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 0.0143177758 0.0082534864 0.0082534864 0.0082534864 0.0153176438 0.0153176438 0.0153176438 0.0153176438 0.0258467673 0.0258467673 6 0.0292719118 0.0316782840 0.0354335195 0.0354335195 0.0293141068 0.0293141068 0.0293141068 0.0299744215 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 0.0557776279 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 0.0568454275 0.1186794422 0.1186794422 0.1186794422 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 0.0610818211 0.0610818211 0.0999905132 0.0999905132 0.0999905132 0.0858537212 0.0858537212 0.0858537212 0.0858537212 0.0644099711 0.0644099711

. 14 0.0708697265 0.0545001954 0.0632013074 0.0632013074 0.0864244379 0.0864244379 0.0864244379 0.0852196109 0.0852196109 0.0852196109 0.0852196109 0.0637040231 0.0637040231 15 0.0774626513 0.0656899700 0.0681384267 0.0681384267 0.0592922873 0.0592922873 0.0592922873 0.0774551039 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 0.0184043260 0.0184043260 0.0290727541 0.0290727541 0.0290727541 0.0290727541 0.0467760851 0.0467760851 19 0.0685259502 0.0656330958 0.0545272751 0.0545272751 0.0120481928 0.0120481928 0.0120481928 0.0187744815 0.0187744815 0.0187744815 0.0187744815 0.0413186686 0.0413186686 20 0.0503658989 0.0457301992 0.0390975413 0.0390975413 0.0118584575 O.D118584575 0.0118584575 0.0129711680 0.0129711680 0.0129711680 0.0129711680 0.0364127078 0.0364127078 21 0.0353421239 0.0400621944 0.0294058171 0.0294058171 0.0096765013 0.0096765013 0.0096765013 0.0106166656 0.0106166656 0.0106166656 0.0106166656 0.0318882915 0.0318882915 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 0.0119380838 0.0205028665 0.0136731866 0.0136731866 0.0048382506 0.0048382506 0.0048382506 0.0061564888 0.0061564888 0.0061564888 0.0061564888 0.0255574344 0.0255574344 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 lndiMa Department of Transportation traffic count data.Indiana Default Hourly Distribution Factors for Road Tvoe 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 0.0435263184 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 0.0581555587 0.0581555587 0.0581555587 0.0790728468 0.0790728486 0.0790728468 0.0790728486 0.0553194565 0.0553194585 11 0.0415130748 0.0428102608 0.0512594850 0.0512594850 0.0616027281 0.0816027281 0.0618027281 0.0824723032 0.0824723032 0.0824723032 0.0824723032 0.0583081277 0.0583081277 12 0.0465168969 0.0452333632 0.0529793024 0.0529793024 0.0844246353 0.0844246353 0.0644248353 0.0820640679 0.0820840879 0.0820640679 0.0820840879 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 0.0578880799 0.0625591325 0.0625591325 0.0625591325 0.0811795580 0.0811795580 0.0811795580 0.0811795580 0.0571667797 0.0571667797 15 0.0671882913 0.0580384620 0.0658779676 0.0656779678 0.0619482678 0.0619482678 0.0619482678 0.0795090490 0.0795090490 0.0795090490 0.0795090490 0.0573429674 0.0573429674 16 0.0810035452 0.0715596945 0.0786905659 0.0786905659 0.0609468141 0.0609466141 0.0609466141 0.0727723312 0.0727723312 0.0727723312 0.0727723312 0.0567213465 0.0567213465 17 0.0863864724 0.0838541123 0.0821371575 0.0821371575 0.0577258909 0.0577256909 0.0577256909 0.0563384761 0.0563364761 0.0563364761 0.0563364761 0.0551911545 0.0551911545 18 0.0843284717 0.0874512168 0.0756929494 0.0758929494 0.0510164625 0.0510164625 0.0510184825 0.0371719560 0.0371719560 0.0371719560 0.0371719560 0.0531125437 0.0531125437 19 0.0845951265 0.0804364374 0.0543873700 0.0543673700 0.0450990958 0.0450990958 0.0450990958 0.0249338618 0.0249336618 0.0249336618 0.0249336618 0.0487199307 0.0487199307 20 0.0469536991 0.0424749554 0.0373951308 0.0373951308 0.0384927086 0.0384927086 0.0384927066 0.0188134711 0.0188134711 0.0188134711 0.0188134711 0.0432101938 0.0432101938 21 0.0373781148 0.0353280630 0.0293181427 0.0293181427 0.0322318571 0.0322318571 0.0322318571 0.0162446774 0.0162446774 0.0162446774 0.0162446774 0.0390319248 0.0390319248

.. 22 0.0318564842 0.0313403787 0.0249971308 0.0249971308 0.0282046747 0.0282046747 0.0282048747 0.0142456600 0.0142456600 0.0142456600 0.0142456600 0.0355118448 0.0355118446 23 0.0245992722 0.0251562568 0.0203505544 0.0203505544 0.0242700475 0.0242700475 0.0242700475 0.0124474209 0.0124474209 0.0124474209 0.0124474209 0.0317711657 0.0317711657 24 0.0198157539 0.0189063955 0.0154823663 0.0154623683 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.fndiana 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 0.0069482800 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 0.0541952158 0.0541952158 0.0448331117 0.0448331117 0.0448331117 0.0418068371 0.0418068371 0.0418068371 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 0.0685413889 0.0685413889 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 0.0667909366 0.0667909366 0.0761037810 0.0761037810 0.0761037810 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 0.0775387708 0.0775387708 o.on5387708 0.0605241028 0.0605241028 17 0.0773519648 0.0803647101 0.0757034489 0.0757034489 0.0526405510 0.0526405510 0.0526405510 0.0464337395 0.0464337395 0.0464337395 0.0464337395 0.0557685235 0.0557685235 18 0.0770777578 0.0832250581 0.0684911688 0.0684911688 0.0347686748 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 0.0173341336 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 o.031066n12 21 0,0383158572 0.0386568197 0.0292289942 0.0292289942 0.0174082029 0.0174082029 0.0174082029 0.0076615624 0.0076615624 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 0.0193751364 24 0.0145073780 0.0159083752 0.0113147831 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 lndia11a Department of Transportation traffic count data.AppendixG /d'

**0~** ltDJD'I'bt' F 

### I 

### n tana e au 81/V 

### ts n u ton 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 0.2439742406 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 Vanderburgh and Warrick Counties Ramp Fractions:

Road Type 2 4 Ramp Fraction 2% 13% Source: Analysis of VHT from the Evansville MPO travel demand model.

# Appendix B

Combined Meeting Minutes for the 1997 8-Hour Ozone Standard for Vanderburgh and WarrickCounties,

Indiana, and the 1997 Annual Fine Particles Standard for the Southwestern Indiana Area Interagency Consultation Group Meeting Minutes/Summary

### This page left intentionally blank

### Interagency Consultation Group (ICG) Conference Call Minutes

For the MOBILE6.0 to MOVES MVEB Replacement Update Related to the 1997 8-Hour Ozone Standard for Vanderburgh and Warrick Counties, Indiana, and the 1997 Annual Fine Particles Standard for the Southwestern Indiana At·ea
ICG Confet·ence Call Date and Time
• February 13,2013 at lpm Eastern Standard Time


### ICG Attendees • Shawn Seals (IDEM), Anthony Maietta (EPA),Greg Karter (INDOT), Larry Heil (FHW A), Ron Hinsenkamp (WCIEDD), Dan White (WCIEDD), Seyed Shokouhzadeh (EMPO), and Vishu Lingala (EMPO)


### 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 ofthe 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 ofthe all sources margins of safety, it was reasonable and appropriate for inclusion in the MVEB replacement submittal.
2. For the PM 2.5 

### MVEB Replacement submittal, various mobile source margins of safety were discussed. A. After discussion, the consensus ofthe ICG was that as long as the a 15% mobile source margin of safety for NO, 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 the MVEB replacement submittal.

B- I

# Appendix C Vanderburgh and Warrick Counties, Indiana, Maintenance Area 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

### This page left intentionally blank

### LEGAL NOTICE OF PUBLIC HEARING Motor Vehicle Emission Budgets Replacement Update to the Maintenance Plan for the 1997 8-Hour Ozone Standard for Vanderburgh and Warrick Counties, Indiana Notice is hereby given under 40 CFR 51.102 that the Indiana Depmiment of Environmental Management (IDEM) is accepting written comment and providing an opportunity for public hearing regarding the Motor Vehicle Emission Budget (MVEB) replacement update to the maintenance plan for the 1997 8-hour ozone standard for Vanderburgh and Warrick 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 concerning the submittal of the proposed MVEB replacement update to the Vanderburgh and Warrick counties, Indiana, maintenance m·eas for the 1997 8-hour ozone standard. The purpose of this notice is to solicit public comment on Indiana's proposed MVEB replacement update. Vanderburgh and Warrick counties, Indiana, were designated as nonattainment for the 1997 8-hour ozone standard and are subject to the requirements of Section 172 ofthe Clean Air Act (CAA). One of the compliance requirements mandated by Section 175A(b) of the CAA, is the development ofa plan demonstrating that maintenance areas will continue to meet the 1997 8-hour ozone standard for the next ten years, which includes MVEBs for omoad sources, beyond the current maintenance period. This submittal of the proposed MVEB replacement update to the Request for Redesignation and Maintenance Planfor Ozone Attainment in the 8- Hour Ozone Basic Nonallainment Area for Vanderburgh and Warriclc counties, Indiana, that was originally submitted on June 2, 2005 is being drafted and submitted consistent with U.S. EPA guidance. Upon completion ofthis public notice process, the MOBILE6.2-based to MOVES-based MVEB replacement update will be submitted to U.S. EPA for approval into the State Implementation Plan. Copies ofthe draft documents will be available on or before May 22,2013, to any person upon request and at the following locations:

• Indiana Department ofEnvironmental Management, Office of Air Quality,

Indiana Government Center North, 100 Nmih Senate Avenue, Room Nl 003, Indianapolis, Indiana.

• Indiana Depm'lment ofEnvironmental Management, Southwest Regional Office, 1120 North Vincennes Avenue, Petersburg, Indiana.

• Evansville Vanderburgh Public Library, Central Branch, 200 SE Martin Luther

King Jr. Boulevard, Evansville, Indiana.



## c- 1

### • Boonville-Wa rrick County Public Library, 611 West Main Street, Boonville, Indiana. The draft documents will also be available on the following web page: http ://www. in

.gov/idem/airqualitv /2392.htm An electronic version of all MOVES mobile model input and output fi les will be avail ab le at the public hearing, ifheld, or upon request. Any person m ay submit written comments on the MVEB replacement update to the Vanderburgh and Warrick cmmties , Indiana, 1 997 8-hour ozone maintenance area on or before June 21, 2013. Written comments should be directed to Mr. Shawn Seals, Mail Code 61-50, Office of Air Quality, Indiana Department ofEnvironmental Management, I 00 North Senate Avenue, Indianapolis, Indiana 46204 ; or fax (3 17) 233 -5967; or email at SSeals@ idem .in .gov . Interested parties may also present oral or written comments at the public hearing, ifheld

. Oral statements w ill be heard, but for the accuracy of the record, statements should be submitted in writing . Written statements may be submitted to the attendant designa ted to receive written comments at the public hearing.
A public hearing on the MVEB replacement update to the maintenance plan f or the 1997 8

-hour ozone standard for Vanderburgh and Warrick counti es, Indiana will be held ifa public hearing request is received by June 12 , 20 13

. A hearing has been scheduled for June 20, 20 13. The meeting will convene at 6:00p .m. (local time) at the Evansville Vanderburgh Public Library, Central Branch, 200 SE Martin Lut her King Jr. Boulevard , Evansville, Indiana, 477 13. If a request fo r a public hearing is not received by June 12, 201 3, the hearing will be cancelled. Interested par ties can check the online IDEM calendar at http ://www

.in .gov/idem /5 474

.htm or contact Mr. Shawn Seals at (317) 233

- 0425 , after June 12,20 13, to see ifthe 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 avai lable to any p erson upon payment ofreproduction costs. Any person heard or represented at the hearin g or requesting notice shall be given written notice ofactions resulting from the hearing. For additional inf ormation contact Mr. Shawn Seals, at the Indiana Depar tment of Environmental Management, Office ofAir Quality, Room N100 1 , Indiana Government Center North, 100 Nm1h Senate Avenue, Indianapolis , 

### IN 46204 or call (317) 233 -0425 or (800) 451 -6027 ext. 3-0425 (in Indiana).



##   ** ******************************************************* *********** Indiv iduals requiring reasonable accommodations forpar ticipation in this hearing, ({ held, should contact the IDEMAmericans with DisabilitiesAct (ADA) coordinator at: Attn: ADA Coordinator

C-2

### Indiana Department of Environmental Management- Mail Code 50-10 100 Nmih Senate Avenue Indianapolis, IN 46204-2251 

### Or call (317) 233-1785 (voice) or (317) 232-6565 (TDD). Please provide a minimum of 72 hours notification.



## c- 3

### IDEM WEBMASTER CERTIFICATION OF LEGAL NOTICE PUBLICATION
May 23,2013



### CERTIFICATE OF PUBLICATION This is to certify that the Indiana Department ofEnvironmental Management (IDEM) Notice of the opportunity for a Public Hea ring regarding the following :

• Motor Vehicle Emission Budgets (MVEB) Replacement Update to the Maintenance Plan for the 1997 8-I-Iour Ozone Standard for Vanderburgh and Warrick Counties, Indi ana

was published on IDEM 's web site on May 16, 2013. It is expected that it will remain posted on the site unti 1at least June 21 , 2013. The noti ce in full was available online at the following web address, under "Southwestern". http://www .in .gov /idem /5474

.htm

Web publication ofthe notice was at the request of Scott Deloney, Branch Chief, Programs Branch, Office ofAir Quality, IDEM

.

Attachments: Copy ofweb page as published. By:

Mike Finklestein IDEM Webmaster

C-4

### SCREENSHOT VERIFICATION OF LEGAL NOTICE POSTING ON IDEM WEBSITE

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