### INDIANA DEPARTM E NT OF ENVIRONMENTAL MANAG E MENT We Protect Hoos i er s and Our Env iro nm ent. 100 N . S enate Avenue • Indianapoli s , IN 46204 (800) 451-6027 • ( 3 17) 232 -8603 • www
. idem

. IN

.gov Michael R. Pence Gm•enwr Thomas W. Easterly C

omm i ssio ner



### 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

Re: MOBILE6.0 to MOVES MVEB Replacement Update to the Maintenance Plan for the 1997 8
- Hour Ozone Standard for Vigo County , Indiana The Indiana Department of Environmental Management (IDEM) submits the e nclosed MOBILE6

. 0 to Motor V e hicl e Emissions Simulator (MOVES) Motor Vehicle Emissions Budget (MVEB) replacem e nt update to the maintenance plan for the 1997 8
- hour ozone standard for Vigo County , Indiana

. The United States Environmental Protection Agency (U.S. EPA) approved the Request for Redesignation and M

a inten a nce Plan for Ozone Attainm ent in the 8-Hour Ozon e Basic Nonatt a inment Area, for Vigo County, Indiana , submitted by IDEM on July , 5, 2005, with an effective date of February 6, 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 th e mainte nan ce plan for th e 1 9 97 8-hour o z on e st a ndard for Vigo County , Indiana, if a public hearing request was received by June 12, 2013. A hearing was scheduled for June 19, 2013. No request for a public hearing was received and the hearing was cancelled

. IDEM received no public c omments during the public notice process. Documents related to the public participation process are included in Appendix C of this submittal. This MOBILE6

. 0 to MOVES MVEB replacement update incorporates onroad emission estimates and revised MVEBs using U

. S. EPA's recently adopted MOVES m o del. The onroad emission estimates were c alculated using the MOVES-based emission factors and data extracted from the Vigo County , Indiana , area's travel
demand mod e l.

A

n E q ua l O ppo rtu n ity E m p l o yer 

# 0

A Sta te**th at~**  

### (i) R e cycl e d Pape r

### Ms. Hedman Page 2 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 MOBILE6.0, 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 onroad safety margins applied to mobile sources, the Vigo County, 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 Vigo County, 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, 

# ;<_.J.A_ 0

**(V~r"")** Keith Baugues Assistant Commissioner Office of Air Quality

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

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) Ron Hinsenkamp, WCIEDD (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 Vigo County, Indiana, Maintenance Area under the 1997 8- Hour Ozone Standard
FINAL July 2013

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### Introduction On July 5, 2005, the Indiana Department of Environmental Management (IDEM) submitted a 

### Requestfor Redesignation and Maintenance Planfor Ozone Attainment in the 8-How· Ozone Basic Nonattainment Area, for Vigo County, Indiana. The United States Environmental Protection Agency (U.S. EPA) subsequently approved the Indiana redesignation ofVigo County, Indiana, to attai1m1ent for the 1997 8-hour ozone standard on January 5, 2006 with an effective date of Febmary 6, 2006 (71 FR 541 ). Onroad emissions for the July 5, 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 Vigo County, Indiana, ozone maintenance area that incorporates MOVES-based omoad emissions. 

### Emission Inventory
Table 4.1 was included without title in Appendix B of the original Redesignation Petition and Maintenance Plan. Table 4.1 -A (to be considered a replacement of the table included in Appendix B) has been revised to incorporate updated onroad emission estimates for nitrogen oxides (NOx) 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, Vigo County 1997 8-Hour Ozone Nonattainment Area (MOBILE6.0-based Onroad Emissions) Sector 2002 NOx 2010 NOx 2015 NOx

Area 1.30 1.40 1.43 Non-road 2.53 2.01 1.53

Mobile 

### ++.-1-G fr.+6**~**



### Point 33.63 12.91 12.93 

### Total 4&S()**~** 

### l9.B Sector 2002 

# voc 2010VOC 2015VOC

Area 8.56 9.89 10.83 Non-road 2.80 1.93 1.67

Mobile +.46 :h84 

### gg

Point 6.52 7.24 8.42 

### Total**~** 

### n.9ll :g£l



### 1

### Table 4.1

- A Comparison of2002, 2010, and 2015 Emission Estimates in Ton s Per S ummer Day, Vigo County 1997 8-Hour Ozone Maintenance Area (MOVES

- ba sed Onroad Emi ss ion s ) Sector 2002 NOx 2010 NOx 2015 NOx

Area 1.30 1.40 1 .43 Nonroad 2.53 2.01 1.53 Onroad 14. 8 7 7.49 4.4 1

P oint 33.63 12.9 1 12.9 3 Total 52.3 3 23

. 81 2 0. 3 Sector 2002 

## voc 2010 

## voc 2015 

## voc

Area 8.56 9 .8 9 10. 83 Nonroad 2.80 1. 93 1. 67

Onroad 5.79 3

. 06 1.88

Point 6.52 7.24 8.42 Total 23

. 6 7 22.12 22

. 8
Onroad em i ss ion es timates in Tab le 4.1- A were calculated u s in g U.S

. EPA's MOVES mod e lproduced emiss ion factor s and data ext racted from t h e area's travel-demand model. The MOVES mod e l implements a significantly diff ere nt approach to em iss io n s estim a tion than th e previou s mode l (MOBILE6.0). Preliminary u se of the MOVES m odel indi ca tes that emi ss ion estimate s can be con s iderably di ffe rent than s imilar calculations usin g MOBILE6.0, whi ch was u sed to create the original MVEBs for the Vi go Co u nty, Indiana, 1997 8 -hour ozo n e non attainm ent area. A general s ummary of the MOVES m etho do l ogy us ed in thi s area can be fo und in Appendix A

. In addition, MOVES input a nd outp ut file s are being provided electronically w ith thi s s ubmitta l. Growth and control strategy assu mp ti o ns for n on -mo bil e so urce s (i.e. are a, nomoad , and point) from the original submittal for th e years 2002, 2010, and 2 015 were deve loped before the eco nomic challenges of the last several year s . B ecause of this, the factors inc luded in the o ri g inal submitta l may project more growth than w ill actua lly occu r in the future

. As a result, the growth and contro l st rategy ass umptions for the non -mob il e sources for t h e year s 2002, 20 10 , and 2015 continue to be va lid and do not affect the overall conclusions ofthe plan

. Onroad safety margins have been includ ed for onroad emi ssion estim ates to accommodate the wide array of ass umption s th at are facto red into the calcul ation proces s . Since assumptio n s change over tim e, it is neces sary to h ave an onroad safety margin that will accommodate the imp ac t ofrefined assu mptio n s in the p rocess. The plan continues to meet all applicable Clean Air Act (CAA) requirem ents as th e revised emiss io n inventories clearly illustrate that total NOx and VOC emission s in the V igo County, Indi an a, 1997 8-hour o zo ne maintenance area w ill co ntinue to decline l eading to local reduction s between 2002 (b ase year) and 2010 (main tenance plan interim bud get yea r) , as we ll as 2 002 (base yea r) and 2 01 5 (m a inte nan ce plan hori zo n budget year).

2

### Transportation Conformity Budgets Table 5.1 was included on Page 18 ofthe original Redesignation Petition and Maintenance Plan for the Vigo County , Indiana, 1997 8-hour ozone maintenance area . Table 5

. 1

- A (to b e considered a replacement of Table 5

. 1) has been revised to incorporate U.S. EPA 's MOVES model-produced emis s ion factors and data extracted from the region 's travel-demand model. Table 5.1 Emission Estimations for On - Road Mobile Sources for the Vigo County, Indiana, 1997 8 - Hour Ozone Nonattainment Area (MOBILE6.0 - based Onroad Emissions)
2 002 2010 2015 2015 Margin of
VMT (mile s/ day) 3 ,5 06 ,57 0 3,669,020 3 ,76 4,676 VOC (tons/day) 

### +.46**~ ~**  

### NOx (ton s/day) -l--h-l-0**~** 

### +.M
Table 5.1- A Emission Estimations for Onroad Mobile Sources for the Vigo County, Indiana, 1997 8 - Hour Ozone Nonattainment Area (MOVES-based Onroad E missions) 2002 2010 2015 VO C (ton s/day) 5.79 3. 06 1.88 NO x (ton s/day) 14 .87 7.49 4.41 Safety

10

. 07% 9.88%

Table 5.2 was also inc lud ed on P age 19 ofthe original Redesignation Petition and M aintenance Plan for the Vigo Co unty , Indiana, 1997 8-hour ozone maintenanc e area. Table 5 .2

- A (to b e considered a repla ce ment of T ab le 5.2) h as been revi s ed to incorp orate MVEB s calculated u s ing U.S. EPA's MOVES mod el-produced emission factors and data extracted from the re g ion 's traveldemand mod el as detail ed in Table 5.1

- A. Table 5.2 Motor Vehicle Emission Bud gets (MOBILE6.0-based Onroad Emissions) 2015 tons/day 

## voc**~** 

### NO x**~**



### 3

### Table 5.2- A Motor Vehicle Emission Budgets for the Vigo County, Indiana, 1997 8-Hour Ozone Maintenance Area (MOVES-based Onroad Emissions) 2015 VOC (tons/summer day) 2. 1 7 NOx (tons/summer day) 5.07 Through the interagency consultation process, i t was determi ned that a maintenance p lan horizon year budget of20 1 5, would be approp ri ate. The interagency consultation group approved onroad margins of safety of fifteen per cent ( 1 5%) for both VOC and NOx onroad emi ss ion estimates fo r the year 2015. A s unm1ary of thi s interagency consultation discussion can be found in Appendix B. These revised emission inventories clearly illu strate that omoad VOC and NOx emi ssions in the Vigo County, Indiana, 199 7 8-hour ozone maintenance area will c ontinu e to decline leading to local reductions between 2002 (base year) and 2015 (maintenance plan horizon budget year)

. Furthermore, wh en compared to the overall safety margin as defin ed in the Code of Federal Regulations (CFR) at 40 CFR 93 .I 01, it is evident the onroad safety margin allocation i s reasonable and approp riate. More specifically, even with the allocation of an onroad safety margin to mobile so urces, emi ss ion s will continue to rem ain well below the overall safety margin for all so urce s as detailed in Table 4.1

- A. MVEBs are constrained to ensure that the total emissions (i. e., all source catego rie s) do not exceed the 2002 attainment year emissions of either VOC or NOx, thereby ensur ing co ntinued maintenance of the 1 997 8-hour ozone standard. Conclusion This MOBILE6 .0 to MOVES replacement upd ate to the previously submitted R equest for R edesignation and Maintenance Plan for Ozone Attainment in the 8-Ho · w· Ozone Basic Nona ttain ment Area, 

### for Vigo Cou nty, Indiana inc orporates omoad emission estimates and a revised MVEB using U.S. EPA's recently adopted MOVES model. MVEBs have been revised in anticipation of the mandatory use ofthe MOVES model in f uture transportation confo rmity detenninations. The onroad emission estimates wer e calculated using the MOVES -based emiss ion facto r s and data extracte d from the area's travel-demand model. Onroad safety margins for VOCs and NOx, established throu gh the in teragency co n sultation process, are included in order to account for the wide array of assumption s that are factored into the calcul ation process. MVEBs are also constrained to ensu re that total VOC and NOx emissions (i .e., all source categories) do not exceed attainment year (2002) e mi ss ions to ensure continued maintenance ofthe 1997 8-hour ozone standard

. With the add ition of MOVES-based onroad safety marg in s applied to mobile sources, the Vigo Cou nty, Indi a na, ozone maintenance area will continue to remain we ll below the overall safety margins for all sources into the future. As s uch, the 1997 8-hour ozone maintenance p lan for Vigo County, Indiana, continues to meet all applicab le CAA requirements.



### 4

# Appendix A Vigo County, Indiana, Maintenance Area MOVES Methodology

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# Terre Haute MOVES2010a Input Data and Parameters INDOT P l ann ing 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- MOVES2010a Input Settings and Assumptions Appendix B- Vehicle Age Distributions for Vigo County Appendix C- Vehicle Populations for Vigo County Appendix D- Meteorological Data for Vigo County 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 Terre Haute 8-hour Ozone Maintenance 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 (INDOT). 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. MOVES2010a 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, MOVES2010a 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 Vigo County 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 LOT 4). 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.

2Table 3: Distribution of MO BILE6.2 Light Duty 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 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 metropolitan planning organization (MPO) for Terre Haute- Vigo County 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 source types using the MAR method were discarded and the observed data were used instead.

3Future 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 Vigo County 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 Redesignation and Maintenance Plan for Ozone Attainment in the 8-hour Ozone Basic Nonattainment Area, Appendix C, developed by the Indiana Department of Environmental Management in October, 2005. The MOVES formatted meteorological data for Vigo County 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 9/1/1 0 GARY LAKE I 80 /I 94 MM 6.0 4 Only 2010 data passed QC LAPORTE LAPORTE SR2 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 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 SR67RM 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 SR66 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 of Runs:

Input Item Ozone Years 2002, 2010, 2015, 2020, 2025,2030, 2035,2040 Pollutants/ Volatile Processes Organic Compound (VOC), NOx, and supporting Meteorology Summer #ofMOVES 8 runsGeneral Parameters: MOVES Input Item Screen Ozone Description Description User Choice Scale Doma in/Scale County Calculation Type Emission Rate Time Spans Time Hour Aggregation Level Year 2002, 2010 , 2015, 2020 , 2025, 2030 , 2035,2040 Months July Days Weekday Hours Select All Geographic Geographi c Vigo County Bounds Bounds Vehicles Vehicles All Gas and Diesel Combinations Road Type Road Type Select All Pollutants/ Pollutants/ VOC, NOx , and Processes Processes supporting General Database N ame Vi go Ozone Output Units Select "Grams" and "Mi les" and "Million BTU" Activity Distance , Population Output On Road Select "Source Emissions Use Type" and Detail "Road T ype "

### C 

### t D 

### t M 

# • County Data Excel Sheet Tab Manager Input Name Ozone Source (Vehicle) sourceTypeYear Local Registration for Source Types 21, 31, and Type Population 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. Vehicle Type HPMSVTypeYear Statewide default vehicle distributions across VMT (by 13 road types developed by INDOT using an MOVES Vehicle analysis of permanent count station data from a Types) 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. Hou rVMTF raction Statewide default hourly fractions developed by INDOT using an analysis of permanent count station data from a statewide data set. Average Speed avgSpeed National defaults. Distribution (% Distribution of VHT in each 5 mph speed bin) Road Type roadType Calculated from local VMT data. Use travel Distribution Distribution demand model base year distributions for all (VMT by 5 years. MOVES Road Types) Age Distribution sourceTypeAge Local age distributions developed from vehicle (Vehicle Distribution registration data for source types 21, 31, and 32. Population by Default MOVES age distributions for all other Age of Vehicle) source types. Ramp Fraction RoadType Based on local travel demand model. Meteorology ZoneMonthHour MOBILE6 Summer Met Data Converted to Data MOVES format Fuel(% of FueiFormulation MOVES Defaults Market Share by FueiSupply Vigo County MOVES Defaults for Summer Fuel Type) (check if varies among counties) liM Program IMCoverage No ProgramAppendix B Viao Countv Vehicle Aae Distributions tor Viao Countv: Source Types aaeid 11 21 31 32 41 42 43 51 52 53 54 61 62 0 0.2109690540 0.0212253419 0.0081779159 0.0207930917 0.0643023355 0.0545743076 0.0622220643 0.0494240790 0.0588526168 0.0787544027 0.0615095870 0.0535634660 0.0670845256 1 0.1921154969 0.0452075694 0.0354869745 0.0502215657 0.0626728412 0.0531913309 0.0606452875 0.0481716155 0.0573612230 0.0767586735 0.0599508636 0.0535634660 0.0670845256 2 0.1573471585 0.0488477289 0.0404455299 0.0557891149 0.0624853859 0.0530322328 0.0604638952 0.0480275345 0.0571896519 0.0765290827 0.0597715492 0.0541045093 0.0677621447 3 0.1359771581 0.0455822917 0.0384103020 0.0466992387 0.0624229593 0.0529792497 0.0604034894 0.0479795509 0.0571325186 0.0764526251 0.0597118340 0.0575579884 0.0720873878 4 0.1058454735 0.0506945746 0.0610938425 0.0648789910 0,0617369906 0.0523970560 0.0597397140 0.0474523026 0.0565046834 0.0756124785 0.0590556596 0.0564182312 0.0706599203 5 0.0750909142 0.0544953294 0.0599837182 0.0656743552 0.0559170498 0.0474575929 0.0541080614 0.0429789769 0.0511779950 0.0684845018 0.0534884926 0.0489290859 0.0612802835 6 0.0476805323 0.0564492385 0.0628700414 0.05851607'17 0.0468365056 0.0397508123 0.0453212873 0.0359994879 0.0428670388 0.0573630896 0.0448023279 0.036603441,1 0.0458432683 7 0.0331026886 0.0630068788 0.0694937833 0.0676059539 0.0425786431 0.0361370941 0.0412011709 0.0327268079 0.0389700355 0.0521482660 0.0407293873 0.0340742206 0.0426755959 8 0.0197278356 0.0613473943 0.0600207223 0.0580615839 0.0468268516 0.0397426124 0.0453119367 0.0359920640 0.0428582007 0.0573512681 0.0447930981 0.0358093100 0.0448486759 9 0.0118473747 0.0728299564 0.0640171699 0.0665833428 0.0534377006 0.0453533365 0.0517089150 0.0410733035 0.0489087668 0.0654479137 0.0511168252 0.0526288382 0.0659139597 10 0.0053251777 0.0676106100 0.0640911782 0.0587433246 0.0532712252 0.0452120443 0.0515478328 0.0409453420 0.0487564067 0.0652440247 0.0509575859 0.0624520143 0.0782168041 11 0.0025378610 0.0521934638 0.0564683245 0.0572662197 0.0407951886 0.0536203440 0.0411075833 0.0313560350 0.0391491717 0.0523881239 0.0302729398 0.0478258601 0.0598985955 12 0.0013011470 0.0540135435 0.0538780343 0.0451085104 0.0331924560 0.0489936472 0.0382933197 0.0255124310 0.0294483131 0.0394065607 0.0466101866 0.0389128550 ,0.0487354179 13 0,0006124019 0.0461443752 0.0408525755 0.0342006590 0.0277347637 0.0456089741 0.0333751020 0.0545980574 0.0316399801 0.0194774783 0.0291673253 0.0325145854 0.0462990441 14 0.0002476898 0.0488477289 0.0435538780 0.0363595046 0.0364294706 0.0377746681 0.0430863640 0.0632656498 0.0364439725 0.0194691525 0.0347804437 0.0427077419 ' 0.0462072388 15 0.0001527705 0.0375525280 0.0415556542 0.0381774798 0.0283511969 0.0332950401 0.0210164622 0.0395649332 0.0357887614 0.0311848083 0.0335202065 0.0332372597 0.0300444032 16 0.0000668536 0.0339659003 0.0335257549 0.0278377457 0.0235884296 0.0279132162 0.0253671498 0.0341566540 0.0259987277 0.0230196849 0.0233151075 0.0276536739 0.0230524492 17 0.0000299603 0.0284521292 0.0257918887 0.0254516532 0.0175637044 0.0244970846 0.0206833627 0.0146346390 0.0197956396 0.0052258132 0.0206748599 0.0205906442 0.0138452217 18 0.0000127409 0.0223495088 0.0235346359 0.0178388819 0.0201192241 0.0250480695 0.0266888558 0.0401958334 0.0193740288 0.0037212159 0.0155464816 0.0235865809 0.0100066460 19 0.0000055369 0.0173442895 0.0180210184 0.0137484377 0.0225790392 0.0366610768 0.0301447753 0.0342277190 0.0227335396 0.0175775477 0.0203628520 0.0264703224 0.0098603738 20 0.0000022027, 0.0152297851 0.0181690349 0.0159072833 0.0226407923 0.0281971934 0.0173882093 0.0270081845 0.0289395633 0.0183874556 0.0265944575 0.0265427,135 0.0095755112 21 0.0000010015 0.0106528198 0.0172809355 0.0149982956 0.0212965445 0.0224413685 0.0209032932 0.0367430589 0.0255089927 0.0121624816 0.0238465850 0.0249667984 0.0083402541 22 0.0000005320 0.0089665694 0.0116933097 0.0120440859 0.0221366577 0.0207614938 0.0211741003 0.0294241579 0.0211707159 0.0029207200 0.0232916866 0.0259516972 Q0021970287 23 0.0000002372 0.0070661920 0.0112862641 0.0090898762 0.0187753208 0.0176845935 0.0186862600 0.0367365508 0.0255742899 0.0006595597 0.0173635700 0.0220110680 0.0022815392 24 0.0000001072 0.0058081957 0.0088069864 0.0089762527 0,0165801584 0.0153441343 0.0162223474 0.0195371739 0.0181341022 0.0013228019 0.0186391363 0.0194375881 0.0028947085 25 0.0000000515 0.0040951795 0.0066607460 0.0056811726 0.0130464803 0.0119613578 0.0125269842 0.0202862884 0.0101534224 0.0013255722 0.0189070434 0.0152949162 0.0014963357 25 0.0000000201 0.0023018656 0.0042184725 0.0042040677 0.0052066606 0.0114707358 0.0046276161 0.0058785937 0.0158244798 0.0000000000 0.0123859355 0.0061039775 0.0003051544 27 0.0000000084 0.0015256551 0.0029603316 0.0036359505 0.0044375500 0.0062552616 0.0034269422 0.0066192300 0.0082431519 0.0005853113 0.0073123264 0.0052023202 0.0002365920 28 0.0000000046 0.0016327186 0.0021832445 0.0031814567 0.0038534093 0.0027153367 0.0040227141 0.0058648852 0.0078447522 0.0004224309 0.0040199156 0.0045175071 0.0007539156 29 0.0000000027 0.0015256551 0.0007770870 0.0004544938 0.0050202650 0.0073813428 0.0039557847 0.0014702211 0.0082910352 0.0000000000 0.0005297244 0.0058854602 0.0002483418 30 0.0000000060 0.0130349830 0.0146906454 0.0122713328 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 Vigo County for source types 21, 32, and 32, MDVES2010a default distributions for all other source types.Appendix C Vfoo Countv Vehicle Pooulations: Vehicle Populations Source Types 11 21 31 32 41 42 43 51 52 53 54 61 62 Annual Populations 2008 1,652 39,546 29,031 8,888 31 16 214 9 640 82 148 722 864 2009 1,651 39,528 29,018 8,884 31 16 213 9 640 82 148 722 863 2010 1,651 39,510 29,005 8,880 31 16 213 9 639 82 148 721 863 2011 1,650 39,493 28.992 8,876 31 16 213 9 639 82 148 721 863 2012 1,649 39,475 28,979 8,873 31 16 213 9 639 82 148 721 862 2013 1,648 39,457 28,967 8,869 31 16 213 9 638 82 148 720 862 2014 1,648 39,440 28,954 8,865 31 16 213 9 638 82 148 720 861 2015 1,647 39,422 28.941 8,861 31 16 213 9 638 82 148 720 861 2016 1,646 39,404 28,928 8,857 31 16 213 9 638 82 147 719 861 2017 1,645 39,387 28,915 8,853 31 16 213 9 637 82 147 719 860 2018 1,645

. 39,369 28.902 8,849 31 16 213 9 637 82 147 719 860 ······ 2019 1,644 39,351 28,889 8,845 31 16 212 9 637 82 147 718 860 2020 _1,643 39,334 28,876 8,841 31 16 212 9 637 82 147 718 859 2021 1,642 39,316 28,863 8,837 31 16 212 9 636 82 147 718 859 2022 1,642 39,299 28,850 8,833 31 16 212 9 636 82 147 718 858 2023 1,641 39,281 28.837 8,829 31 16 212 9 636 82 147 717 858 2024 1,640 39,283 28,824 8,825 31 16 212 9 635 82 147 717

. 858

.... 2025 1,640 39,246 28,811 8,821 31 16 212 9 635 82 147 717 857 2026 1,639 39,228 28,798 8,817 31 16 212 9 635 82 147 716 857 2027 1,638 39,211 28,786 8,813 31 16 212 9 635 82 147 716 857 2028 1,637 39,193 28,773 8,809 31 16 212 9 634 82 147 716 856 2029 1,637 39,176 28,760 8,805 31 16 212 9 634 81 147 715 856 2030 1,636 39,158 28,747 8,801 31 16 211 9 634 81 147 715 855 2031 1,635 39,141 28,734 8,797 31 16 211 9 633 81 146 715 855 2032 1,634 39,123 28,721 8,793 31 16 211 9 633 81 148 714 855 2033 1,634 39,106 28,708 8,790 31 16 211 9 633 81 146 714 854 2034 1,633 39,088 28,696 8,786 31 16 211 9 633 81 146 714 854 2035 1,632 39,071 28,683 8,782 31 16 211 9 632 81 146 713 854 2036 1,631 39,053 28,670 8,778 31 16 211 9 632 81 146 713 853 2037 1,631 39,036 28,657 8,774 31 16 211 9 632 81 146 713 853 2038 1,630 39,018 28,644 8,770 31 16 211 9 632 81 146 713 852 2039 1.629 39,001 28,631 8,766 31 16 211 9 631 81 146 712 852 2040 1,629 38,983 28,619 8,762 31 16 211 9 631 81 146 712 852 Source: Quality assured vehicle registratiorJ data for Vigo County 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 

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### a a: monthiD zoneiD HouriD temperature reiHumidity 7 181670 1 69.8 87.2 7 181670 2 68.5 91.2 7 181670 3 67.5 94.4 7 181670 4 66.8 96.9 7 181670 5 66.2 98.8 7 181670 6 65.6 100.0 7 181670 7 65.0 100.0 7 181670 8 65.5 100.0 7 181670 9 68.3 92.1 7 181670 10 72.7 79.1 7 181670 11 77.3 67.9 7 181670 12 81.2 59.7 7 181670 13 84.6 53.4 7 181670 14 86.5 50.4 7 181670 15 87.1 49.3 7 181670 16 87.3 49.0 7 181670 17 86.8 49.8 7 181670 18 85.5 51.9 7 181670 19 83.3 55.7 7 181670 20 80.4 61.2 7 181670 21 77.5 67.3 7 181670 22 75.0 73.1 7 181670 23 73.3 77.6 7 181670 24 71.5 82.4
Source: Mobile 6.2 reported meteorological data from Appendix C of the Request for Redesignation and Maintenance Plan for Ozone Attainment in the 8-Hour Ozone Basic Nonattainment Area, Vigo County, Indiana prepared by IDEM on October, 2005 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 Indiana Default Hourly Distribution Factors for Road Tvpe 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 0.0174195788 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 0.071111 0358 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 0.07 46488056 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 0.0847160034 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.Indiana Default Hourlv Distribution Factors for Road Tvoe 3- Rural Unrestricted 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 0.0046485153 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 0.0118584575 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 0.01,36(31866 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 Indiana Department of Transportation traffic count data.Indiana Default Hourly Distribution Factors for Road Type 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 0.0790728466 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 0.0795090490 0.0795090490 0.0795000490 0.0573429674 0.0573429674 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 0.0821371575 0.0821371575 0.0577256909 0.0577256909 0.0577256909 0.0563364761 0.0563364761 0.0563364761 0.0563364761 0.0551911545 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 0.0450990958 0.0450990958 0.0450990958 0.0249336618 0.0249336618 0.0249336618 0.0.249336618 0.0487199307 0.0487199307 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 0.0293181427 0.0293181427 0.0322318571 0.0322318571 0.0322318571 0.0162446774 0,0162446774 0.0162446774 0.0162446774 0.0390319248 0.0390319248 22 0.0316564842 0.0313403787 0.0249971308 0.0249971308 0.0282046747 0.0282046747 0.0282046747 0.0142456600 0.0142456600 0.0142456600 0.0142456600 0.0355118446 0.0355118446 23 0.0245992722'' 0.0251562568 0.0203505544 0.0203505544 0.0242700475 0.0242700475 0.0242700475 0.0124474.209 0.0124474209 0.0124474209 0.0124474209 0.0317711657 o.o31n11s57 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: StateVIIide averages developed from Indiana Department of Transportation traffic count data.fndiana Default Hourly Distribution Factors for Road Type 5 -Urban Unrestricted Access: Source Types 

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

## 115 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 0.0775387708 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 0.0310667712 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 Indiana Department of Transportation traffic count data.Appendix G 

### 1 d. 

## o i 11 

## o ., o· t ·b 

## r F 

### t n tana e au anv 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 Monthlv Distribution Factors: monthiD monthVMTFraction 0. 073342401 0 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 Vigo County Ramp Fractions:

Road Type 2 4 Ramp Fraction 0% 5.73% Source: Analysis of VHT from the Terre Haute travel demand model.

# Appendix B
Vigo, Indiana, Maintenance 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 Vigo County, Indiana, Maintenance Area under the 1997 8-Hom· Ozone Standard
ICG Conference Call Date and Time
• February 13, 2013 at 1 pm Eastern


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


### ICG Discussion Topics and Conclusions
1. For the PM 2

_ 5 

### 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 NO, 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

# Appendix C Vigo County, Indiana, Maintenance AreaPublic 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 Budget Replacement Update to the Maintenance Plan for the 1997 8-Hour Ozone S tandard for Vigo County, Indiana Notice is hereby given under 40 CFR 5 1.1 02 that the Indiana Department of Environmen tal Management (IDEM) i s 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 Vigo County, Indiana. Omoad emission s for the original s ubmittal were calculated u sing 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 Em issions Simulator (MOVES) mobile model. All interested persons are invited and will be given reasonable opportunity to express their views concerning the submittal of the proposed MVEB replac ement update to the Vi go County, Indiana , maintenance area for the 1997 8-hour ozone standard. The purpose of this notice is to solicit public comment on Indi ana's proposed MVEB replacement update. Vigo County, Indiana, was designated as nonattainment for the 19 97 8-hour ozone standard and is subject to the requirements of Section 172 ofthe C lean Air Act (CAA). One ofthe compliance requirements mandated by Section 175A(b) of the CAA, is the development of a plan demonstrating that maintenance areas will co ntinu e to meet the 1997 8-hour ozo ne stand ard for the n ext ten years, whi ch includes MVEBs for onroad sources, beyond the curren t maintenance period. Thi s s ubmittal ofthe proposed MVEB replacement update to the 

### R eques t for Redesignalion and Maintenance Plan for Ozone Allainmen t in the 8-Hour Ozone Basic Nonallainment Area for Vigo County, Indiana, maintenance area that was originally submitted on July 5, 2005 , is being drafted and submitted consistent with U.S. EPA guid a nce. Upon comp letion ofthis public notice proce ss, the MOBILE6.2-based to MOVE S

-bas e d MVEB replacement update will be submitted to U.S. EPA for approval into the State Implementation Plan. Cop ies of the draft documents w i 11 be available on or before May 1 7, 2013, to any perso n upon reque st and at the following locations:

• Indiana Depmiment of E nvironmental Management, Office of Air Quality,

Indiana Government Center North, 100 North Senate Avenue , Room N1 003, Indianapo li s, Indiana.

• Vigo County Public Library , One Librm·y Square (7 111 

### and Poplar) , Terre Haute,

Indiana. The draft documents w ill a lso be avai lab le on the following web page: http: //www. in. gov/ idem/airguali ty/2392 .htm



## c- 1

### An electronic vers ion of all MOVES mobil e model input an d o utput fil es will be available at the public hearin g, if held , or upon re quest. Any p ers on may submi t written comments o n the MVEB replace ment upd ate to the Vigo Co unty , Indian a , 1 997 8-hour oz one m aintenance ar ea on or befor e Jun e 2 1 , 201 3

. Written c omment s s hould be directed to Mr. Shaw n S eal s, M ail Co de 61-50 , Office of A ir Quality , Indi ana D e p artment of E nvironmental M anagement , 100 N orth Senate Ave nue , Indianapoli s, Indiana 46204 ; or f ax (317) 2 33

- 596 7 ; or email at SS eals@ ide m.in. go v . Interested pmties m ay a lso pr es ent oral o r written co mments at the publi c hearing, if held. Oral state ments will b e hear d, but fo r the accuracy o fthe record , s tatem ents s ho uld be submitte d in writing . Written s tatements may b e s ubm itted t o the attenda nt des ignate d to rece ive w ritten commen ts at the public hearing. A publi c hearin g on the MVEB repl ace ment update to th e maintena nce pl an fo r the 1997 8-hour ozone stand ard for Vigo County , Indi ana will be held if a publi c he arin g request i s recei ved b y June 12,2 013

. A he arin g has b een scheduled fo r June 19 ,20 1 3. The meeting will convene at 6 :00p.m. (l oc al t ime) at the Vi go County Publ ic Library, One Librar y S qu are (7 111 

### and P opl ar) , Ten e H a ute, Indi ana , 47 8 07. If a request fo r a publi c hea ring is not rec eived by June 12, 20 13, the he aring will be cance lle d. Interes t ed pmti es can check the online ID EM calendar at http: //www .in. gov/idem /5474. htm or contact Mr. Shawn Seal s at (3 17) 2 33-0425 , after June 12 , 2 013 , to see ifthe hearin g h as been can ce ll e d or will convene . A tra nscript of th e hearin g a nd all written s ubmi ssi on s provided at the pu bl i c he aring s hall be op en to pu bli c in sp ecti o n at ID EM and cop ies may be m ade avail ab le to any p e r son up o n payment of repro duction c o sts
. Any per s on h eard o r represented at the hearin g or requesting noti ce s hall be given written noti ce o f acti on s res ultin g fro m the he arin g . For additional in fo rm ation c ontact Mr. Shawn S eals, at the Indi an a D epartment of En vironm en ta l M an agement , O ffice o f Air Qu ali ty , Ro om N l OO l , Ind iana Govern ment Ce nter N mth , 100 North Senate Avenue , Indi anapo li s , IN 462 04 or ca ll (3 1 7) 233

- 0425 or ( 800) 4 5 1 -6 027 ext. 3 -0425 (in Indiana)

. 

## *********************************************** * ** ** ***** ** ** * ****** *** * In div idu als req uiring reaso na ble accomm oda tions fo r par t idpation in this hearh1 g, 

## ! f held, should contact the I DEMA m ericans w ith D isabili tie s Act (ADA) coordinator at: 

### Attn: ADA Coo rdinator Indi an a D epartment of E nviro nmenta l M anagem ent

- Mail Code 5 0-10 1

00 N o rth S ena te Avenue I ndian apoli s, IN 4 62 04-22 5 1 Or call (3 1 7 ) 233 -1 785 (vo ice) o r (3 1 7) 232

- 6565 (I' DD ). P leas e provide a minimum of 7

2 h ou r s no tificatio n.



## c- 2

### IDEM WEBMASTER CERTIFICATION OF LEGAL NOTICE PUBLICATION
May 22 , 2 013



### CERTIFICATE OF PUBLICATION This i s to certify that the Indian a Department of Envirmm1ental Management (IDEM) No tice ofthe opportunity for a Publi c Hearing regarding the followin g:

• Motor Vehicle Emission B ud get (MVEB) Rep l acement Update to the Maintenance Plan for the 1997 8-Hour Ozone S tandard for Vigo Co unty , Indiana

was published on IDEM 's web s ite o n May 1 3, 2013

. It 

### is expected that it w ill remain po s ted on the s ite until at least Jun e 2 1, 2013. The notice in full was avail able o nlin e at the fo ll ow ing web address, under " Wes tern ". http: //www . in .gov/idem / 5474. htm

Web publication ofthe notice was at the reque s t of Scott D eloney, Branch C hi ef, Program s Branch, Office of Air Quality , ID EM.

Attachment s: Copy of web page as pub li shed. By:

Mike Finkles tein ID EM Webmaster



## c- 3

### SCREENSHOT VERIFICATION OF LEGAL NOTICE POSTING ON IDEM W E BSITE

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