### IDEM INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT

Mitchell E. DanielsJr. Governor
Thomas W Easterly Commissioner



### Ms. Susan Hedman Regional Administrator We ProtectHoosiers andOurEnvironment.

June 15, 2012 100 North Senate Avenue Indianapolis, Indiana 46204 (317) 232-8603 Toll Free (800) 451-6027 www.idem.IN.gov



### U.S. Environmental Protection Agency Region 5 

# UUN 1'J 

# 2012
77 West Jackson Boulevard Chicago, IL 60604-3950
Dear Ms

. Hedman:
Re: Request to Parallel Process the Draft MOBILE6.2 to MOVES MVEB Replacement Update to the Delaware County Maintenance Area underthe 1997 8-Hour Ozone Standard
The Indiana Department of Environmental Management (IDEM) submits the enclosed MOBILE6.2 to MotorVehicle Emissions Simulator (MOVES) MotorVehicle Emissions Budget (MVEB) replacement update for the Delaware County Maintenance Area underthe 1997 8-hour ozone standard. IDEM requests thatthe United States Environmental Protection Agency (U.S. EPA) parallel process this draft submittal for approval into Indiana's State Implementation Plan.
IDEM is providing an opportunityfor a public hearing on the MVEB replacement update to the Delaware County maintenance area ifa public hearing request is received by July 11, 2012. A hearing has been scheduled for July 18, 2012. Ifa request for a public hearing is not received by July 11, 2012, the hearing will be cancelled. The final submittal ofthe MVEB update for the Delaware County maintenance area will document the public review process, including a detailed summary of and response to substantive comments.
This MOBILE6.2 to MOVES MVEB replacement update incorporates onroad emission estimates and revised MVEBs using U.S. EPA's recently adopted MOVES model. The onroad emission estimates were calculated using the MOVES-based emission factors and data extracted from the Delaware County area's travel-demand model.
MVEBs are being revised in anticipation ofthe mandatory use ofthe MOVES model in future transportation conformity determinations. Preliminary use ofthe new model indicates that emission estimates can be considerably differentthan similar

RecycledPaper 

### <i) An Equal Opportunity Employer Please Recycle 

### 0

### Ms. Hedman Page 2
calculations using MOBILE6.2, which was used to create the MVEBs in the original 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 orderto accountfor the wide array ofassumptions that are factored into the calculation process. With the addition ofonroad safety margins applied to mobile sources, the Delaware County maintenance area will continue to remain well belowthe 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 ofthe 1997 8-hour ozone standard.
This submittal consists ofone (1) hard copy ofthe required documentation. An electronic version ofthe submittal in PDF format that is identical to the hard copy has been sentto Pamela Blakley, Chiefof U.S. EPA Region 5's Control Strategies Section.
IDEM respectfully requests that U.S. EPA proceed with preliminary review ofthe MOBILE6.2 to MOVES MVEB replacement update and revised transportation conformity budgets and approval into Indiana's State Implementation Plan for the Delaware County Maintenance Area underthe 1997 8-hour ozone standard. Ifyou have any questions or need additional information, please contact Scott Deloney, Chief, Air Programs Branch, at (317) 233-5694.

KB/sad/sms
Enclosure: Sincerely, 

### I!

- .... l 

## a. /}LA»'- u) GAA-txtUy._,J G 

### Keith Baugues Assistant Commissioner Office ofAir Quality

Onroad Emissions MOBILE6.2 to MOVES Replacement Submittal for the Delaware County, Indiana Maintenance Area underthe 1997 8-Hour Ozone Standard
Cc: Doug Aburano, U.S. EPA Region 5 (w/ enclosures) Ed Doty, U.S. EPA Region 5 (w/ enclosures) Pamela Blakley, U.S. EPA Region 5 (w/ enclosures) Pat Morris, U.S. EPA Region 5 (w/ enclosures)

RecycledPaper 

### (i)Steve Rosenthal, U.S. EPA Region 5 (no enclosures) Marta Moody, DMMPC (w/ enclosures) Scott Deloney, IDEM (no enclosures) Christine Pedersen, IDEM (no enclosures) Shawn Seals, IDEM (w/ enclosures)

An Equal OpportunityEmployer Please Recycle 

## O

# OnroadEmissions MOBILE6.2 to MOVES Replacement Submittal

Forthe Delaware County MaintenanceAreaunderthe 1997 8-HourOzone Standard

DRAFT June 2012

### This pageintentionallyleftblank

### Introduction
OnAugust25,2005, the IndianaDepartmentofEnvironmental Management (IDEM) submitted a Request forRedesignation andMaintenance Plan for OzoneAttainmentin the 8-Hour Ozone NonattainmentArea, Delaware County, Indiana. The United States Environmental Protection Agency (U.S. EPA) subsequently approvedthe Indianaredesignation ofthe Delaware CountyArea to attainmentfor ozone onNovember 16, 2005 (70 FR69443). Onroademissions for the August 25, 2005, submittal were calculatedusingMOBILE6.2. U.S. EPAhas encouragedmobile source stakeholdersto transitiontothe newMotorVehicleEmissions Simulator (MOVES) model as expeditiously as possible. Therefore, IDEMis providingthis MOBILE6.2 to MOVES replacement update to thepreviously submitted 8-hourozonemaintenanceplanforthe Delaware CountyArea thatincorporatesMOVES-basedonroad emissions.


### EmissionInventory

The table, "Delaware CountyArea" was includedwithouttitleinAppendixF ofthe original RedesignationPetitionandMaintenancePlan. Thetable, "DelawareCountyArea- A" (to be considered areplacement ofthetable includedinAppendix F) hasbeenrevisedto incorporate updated onroademissionestimates for nitrogenoxides (NOx) andvolatile organic compounds (VOCs) for the years 2002, 2010, and 2015 andresults in a different overall safetymarginfor the
area.

Sector Area Nonroad Onroad

Point Total Sector Area Nonroad Onroad

Point Total 

### DelawareCountyArea (MOBILE6.2-based OnroadEmissions)

2002NOx 2010NOx 1.43 1.54 4.11 3.29**~ ~**  0.35 0.37 -l-9-.18 Y.8(i 2002

## voc 2010VOC 9.79 11.48 9.23 5.43 8-J-9 4.49 0.83 1.00**~ ~** 



### 1 2015NOx 1.58 2.74**~** 0.39 9-.J() 2015VOC12.67 5.28**~** 1.17**~**

### DelawareCountyArea - A (MOVES-based OnroadEmissions)

Sector 2002 NO, 2010 NO, Area 1.43 1.54 Nonroad 4.11 3.29 Onroad 20

.28 10

.53

Point 0.35 0.37 Total 26.17 15.73 Overall SafetyMargin NA NA Sector 2002

### voc 2010

### voc Area 9.79 11.48 Nonroad 9.23 5.43 Onroad 6.23 3.45

Point 0.83 1.00 Total 26.08 21.36 Overall SafetyMargin NA NA 2015NOx 1.58 2.74 6

.10 0.39 10.81 15.36 2015

### voc 12.67 5.28 2.20 1.17 21.32

4

.76



### Onroad emission estimates intable "Delaware CountyArea- A"were calculatedusingU.S. EPA'sMOVES model-producedemissionfactors and dataextracted from the area'straveldemandmodel. TheMOVES model implements a significantlydifferent approachto emissions estimationthanthepreviousmodel (MOBILE6.2). Preliminaryuse ofthe MOVES model indicatesthat emissionestimates canbe considerably differentthan similarcalculationsusing MOBILE6.2, whichwas usedto createthe original MotorVehicleEmissionBudgets (MVEBs) for theDelaware CountyArea. A general summaryofthe MOVES methodologyused inthis
areacanbe found inAppendixA. 

### In addition, MOVES inputand outputfiles are beingprovided electronicallywiththis submittal. Growth and control strategy assumptions for non-mobile
sources (i.e. area, nonroad, andpoint) from the original submittalfor the years 2002, 2010, and 2015 were developedbeforethe economic challenges ofthe last several years. Because ofthis, the factors included inthe original submittal mayprojectmore growththan will actually occurin the future. As aresult, the growth andcontrol strategy assumptions for the non-mobile sources for the years 2002, 2010, and 2015 continuetobevalid and do not affectthe overall conclusions oftheplan.
Onroad safetymarginshavebeenincludedfor onroademissionestimatesto accommodatethe wide array ofassumptionsthat are factored into the calculationprocess. Since assumptions change overtime, itis necessaryto have anonroad safetymarginthatwill accommodatethe impactofrefined assumptions intheprocess. Theplancontinuesto meet all applicable Clean AirAct (CAA) requirements as therevised emissioninventories clearlyillustratethattotalNOx and VOC emissions inthe Delaware County Areawill continueto decline leadingto local reductionsbetween2002 (base year) and 2015 (maintenanceplanhorizon).

2

### Transportation ConformityBudgets


### Table 5.1 was included onPage 19 ofthe original RedesignationPetition andMaintenancePlan for the Delaware County Area. Table 5.1 -A (to beconsidered areplacement ofTable 5.1) has beenrevisedto incorporateU.S. EPA'sMOVES model-produced emissionfactors and data extractedfromtheregion'stravel-demandmodel.

Table5.1 EmissionEstimations for On-RoadMobile Sources (MOBILE6.2-based OnroadEmissions)

2002 2010 2015
VMT (miles/day) 4,410,000 4,822,355 13,282,621 VOC (tons/day) 8.19 4.69 3.33 NOx(tons/day) 13.89 7.66 4.59



### Table5.1- A EmissionEstimates for OnroadMobile Sources (MOVES-based OnroadEmissions)
2002 2010 2015 VOC (tons/day) 6.23 3.45 2.20 NOx(tons/day) 20.28 10.53 6.10 2015Margin of Safety

5.1% 5.0%



### Table 5.2 was included onPage 19 ofthe original RedesignationPetition and MaintenancePlan for the Delaware County Area. Table 5.2- A (to be considered areplacement ofTable 5.2) has beenrevisedto incorporateMVEBs calculatedusing U.S. EPA'sMOVES model-produced emissionfactors and dataextractedfrom theregion'stravel-demand model as detailed inTable 5.1 -A. Table5.2 MobileVehicleEmissionBudgets (MOBILE6.2-based OnroadEmissions)
2015 VOC (tons/day) 3.50 NOx(tons/day) 4.82



### Table5.2- A MotorVehicleEmissionBudgets (MOVES-based OnroadEmissions)
2015 VOC (tons/day) 2.53 NOx(tons/day) 7.02



### 3

### Throughthe interagencyconsultationprocess, itwas determinedthat a maintenanceplanhorizon yearbudget of2015,wouldbe appropriate. The interagency consultationgroup approved omoad margins ofsafety offifteenpercent (15%) forbothVOC andNOx omoademissionestimatesfor theyear2015. A summary ofthis interagencyconsultationdiscussion canbe found inAppendix B. Theserevised emissioninventories clearlyillustratethat omoadVOC andNOx emissionsinthe Delaware CountyAreawill continueto decline leadingto local reductionsbetween2002 (base year) and 2015 (maintenanceplanhorizon). Furthermore, whencomparedto the overall safetymargin as defined inthe Code ofFederal Regulations (CFR) at40 CFR93.101, itis evidentthe omoad safetymargin allocationis reasonable and appropriate. More specifically, evenwiththe allocationofanomoad safetymargin to mobile sources, emissions will continueto remainwell belowthe overall safetymarginfor all
sources as detailed intable, "Delaware CountyArea- A"

. MVEBs are constrainedto ensurethat thetotal emissions (i.e., all source categories) do notexceedthe 2002 attainmentyearemissions of eitherVOC orNOx, thereby ensuring continuedmaintenance ofthe 1997 8-hourozone standards.
Conclusion


### ThisMOBILE6.2to MOVES replacementupdate to thepreviously submitted 8-hourozone maintenanceplanfor the Delaware CountyAreaincorporates omoademissionestimates and a revisedMVEBusingU.S. EPA'srecently adopted MOVES model. MVEBshave beenrevised in anticipation ofthe mandatoryuse ofthe MOVES model infuture transportation conformity determinations. The omoademissionestimates were calculatedusingthe MOVES-based emission factors and dataextractedfrom the area'stravel-demandmodel. Omoad safetymargins for VOCs andNOx, establishedthroughthe interagencyconsultationprocess, are includedinorderto account forthe wide array ofassumptions that are factored into the calculationprocess. MVEBs are also constrainedto ensurethattotal VOC andNOx emissions (i.e., all source categories) do notexceed attainmentyear (2002) emissionsto ensure continuedmaintenance ofthe 1997 8-hourozone standard. Withthe addition ofMOVES-based omoad safetymargins appliedto mobile sources, theDelaware CountyAreawill continueto remainwell belowthe overall safetymargins for all
sourcesinto the future. As such, the 8-hour ozonemaintenanceplanfor the Delaware CountyArea continuesto meet all applicable CAArequirements.

4

# AppendixA

Delaware County MOVES Methodology

### Thispage leftintentionallyblank

# Delaware County MOVES2010a Input Data and Parameters

INDOT Planning Contract



# Final Report June 14, 2012Table 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: MOVES201Oa 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 Delaware County Appendix C- Vehicle Populations for Delaware County Appendix D- Meteorological Data for Delaware 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 1- Ramp FractionsOverview: This report is being written to document the input parameters for a set of MOVES201Oa runs for the Delaware County 8-hour Ozone Maintenance Area. This report contains a discussion on the intended input settings used in MOVES201Oa and the development of the input datasets. These MOVES2010a 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 ofTransportation (INDOT). Throughout this report references are made to MOVES 201Oa 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: MOVES201Oa 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 UnitShort-haulTruck 

### 53 Single Unit Long-haul Truck 

### 54 Motor Home 

### 61 Combination Short-haul Truck 

### 62 Combination Long-haul Truck
Table 2: MOVES201Oa 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 ofage distributions was provided in both MOBILE6 and MOVES formats. The MOVES formatted data will be used forthese MOVES201Oa 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, MOVES201Oa 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 Delaware County are shown in Appendix B ofthis report.
Vehicle Population: The vehicle populations for source types 21, 31, and 32 were developed directly from the vehicle registration data. All valid records that were identified from the vehicle registration data set were used to determine the number of vehicles for each of these three source types. The VIN decoded data provided to INDOT contained vehicle types according to MOBILE6.2 vehicle categories. There is a direct correlation between MOVES source type 21 (cars) and the MOBILE6.2 vehicle type LDV. All valid LDV records (those records not excluded from the vehicle age distribution analysis due to errors as was described in the section on Vehicle Age Distribution in this report) were counted in the vehicle population.
There is not a direct correlation between MOVES source types 31 (passenger trucks) and 32 (light commercial vehicles) and the MOBILE6.2 light truck vehicle types (LDT1, LDT2, LDT3, and LDT4). All valid records from the vehicle registration data set for MOBILE6.2 light duty trucks were counted in the vehicle populations. The light duty trucks were distributed between MOVES source types 31 and 32 as per the Environmental Protection Agency's (EPA) guidance documented in Table A.1 of the appendix of the Technical Guidance on the Use of MOVES2010 for Emission Inventory Preparation in State Implementation Plans and Transportation Conformity. The guidance provides two sets of factors for distributing MOBILE6.2 light trucks between MOVES source types 31 and 32. These are based on fuel type and are shown in Table 3.

2Table 3: Distribution of MOBILES 2 L" ht D t T k . to MOVES Source Types IQ my rue s 

### m

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 ofdiesel 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 ofthe erroneous records that were discarded from the analysis actually belonged to these source types. The nature ofthese 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 adjustthe vehicle populations calculated from vehicle registration data to compensate for these discarded records. Based on an analysis of the error rate reported by ERG, vehicle populations for source types 21, 31, and 32 were increased by 5.8 percent.
Vehicle populations were not able to be developed directly from the vehicle registration data for some source types. This was due to the limitations in the VIN decoder used by ERG to process the vehicle registration data. Vehicle populations for all other source types (motorcycles and heavy vehicles) were derived by applying the Mileage Accumulation Rate (MAR) method documented in EPA's Technical Guidance on the Use of MOVES2010 for Emission 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 yearfor 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 Delaware-Muncie Metropolitan Plan Commission (DMMPC), which is the metropolitan planning organization (MPO) for Delaware 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 yearvehicle 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 Delaware 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 G, developed by the Indiana Department of Environmental Management in August, 2005. The MOVES formatted meteorological data for Delaware County are presented in Appendix D of this report.
DefaultVMT 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 ofthe 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 ofthe 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 ofVMT by vehicle type was calculated for each road type by taking each vehicle type's percentage oftotal 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 SR 332 RM 0.5 3 Closed since 9/26/2006. No data. CARMEL HAMILTON US 31 RM 125.7 5 Good INDYWEST MARION 1465 MM 10.0 4 Closed since 9/1/10 GARY LAKE I 80 II 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 VIGO 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 FORTWAYNE ALLEN 1-69 0.53 mi N of 4 Good SR3 MUNCIE DELAWARE US 35 RM 44.5 5 Good DALEVILLE DELAWARE 169 MM 31.4 2 Good-built in 12/10/2007 SOUTH BEND ST. JOSEPH US 20 RM 77.1 4 Good INDY SOUTH MARION SR 37 RM 143.5 5 Good-closed 5/22/09-6/1/09 MARTINSVILLE MORGAN SR 67 RM 80.6 3 Good SEYMOUR JACKSON 165 MM 47.0 2 Good HAZLETON GIBSON SR 56 RM 0.6 3 Good DUBOIS DUBOIS SR 56 RM 53.3 3 Good- closed 10/16/08- 3/20/09 EVANSVILLE VANDERBURGH SR 66 RM 23.5 5 Good 170 MARION 170 MM 83.5 4 Closed 5/17/06-3/24/08
Default Hourly Distributions: The same set of twenty permanent traffic count locations discussed in the section on Default VMT Distributions was analyzed to develop a set of hourly distribution factors. These factors were calculated by road type, by HPMS vehicle type. Hourly factors were only calculated for the average weekday. The hourly distribution pattern for each traffic count location was reviewed. Any data that appeared to reflect either an error in the data or an outlier of behavior were removed to prevent bias in the data. The following data were excluded from the analysis:

• Bus data from count stations 0105 and 0603 were excluded due to abnormal midnight peaks in the data; • An abnormal relationship between passenger cars and light duty trucks at count station 4500 prompted the exclusion of all data from this location due to questions of reliability; • Peak spreading behavior observed at count station 4000 from traffic related to Chicago was considered to be too unique to be included in a default statewide data set; and,

5• Combination truck traffic from station 3200 was excluded due to too much overnighttraffic when compared to othervehicles and otherstations. Furthermore, traffic patterns reported by those count stations corresponding to road type 3 (3000, 4500, 0105, 0201, 0502, 0602, and 0603) had a tendency to over represent long distance travel. This was most likely the result of statewide permanent count stations focusing primarily on higher order facilities. Rural collectors and local streets are less likely to reflect long distance travel. The hourly distributions for road type 3 (rural unrestricted access) were adjusted to better account for traffic behavior on lower order facilities in rural areas. A sample oftraffic 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 ofall 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 INDOT'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 ofVMT is occurring on weekdays and what percentage is occurring on weekends. The monthly distribution factors determine what percentage ofannual 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 ofVHT occurring on ramps reported by the base year travel demand model. These ramp fractions are reported in Appendix I.

6AppendixA
NumberofRuns:

Input Item Ozone Years 2002, 2010, 2015, 2020, 2025,2030, 2035,2040 Pollutants/ Volatile Processes Organic Compound (VOC), NOx, and supporting Meteorology Summer #of MOVES 8 runsGeneralParameters: MOVES Input Item Screen Ozone Description Description UserChoice Scale Domain/Scale County Calculation Type Emission Rate Time Spans Time Hour Aggregation Level Year 2002,2010, 20.15, 2020, 2025,2030, 2035,2040 Months July Days Weekday Hours SelectAll Geographic Geographic Delaware County Bounds Bounds Vehicles Vehicles All Gas and Diesel Combinations RQad Type Road Type SelectAll Pollutants/ Pollutants/ VOC, NOx, and Processes Processes supporting General Database Name Delaware Ozone Output Units Select "Grams" and "Miles" and "Million BTU" Activity Distance, Population Output On Road Select "Source Emissions Use Type" and Detail "Road Type"

### C tDtMar 

# • County Data Excel Sheet Tab Manager Input Name

Source (Vehicle) sourceTypeYear Type Population

. Vehicle Type HPMSVTypeYear

VMT (by 13 MOVESVehicle Types) Ozone Local Registration for Source Types 21 I 31 I and 32; Estimated population using default MOVES mileage accumulation rates and local VMTforall othersource types. Futureyearvehicle populations based on population growth rates for source types 11 I 21 I 31 I and 32. Employment growth used for all othersource types

. Statewide defaultvehicle distributions across road types developed by INDOT usingan analysis ofpermanent count station.data from a statewide data set. MonthVMTFraction Statewide default monthlyfractions developed by INDOT using an analysis ofpermanent count station data from a statewide data set.

···bayVNJTFraction Statewidedefaultdailyfractionsdevelopedby INDOTusing an analysis ofpermanentcount station data from 

### a statewide dataset.

. HourVMTFraction Statewide default hourlyfractions developed by INDOT using an analysis of permanent count station datafrom a statewide data set.

·**Aver~geSpeed**

Distribution (% ofVHT in each 5 mph speed bin) Road Type roadType Distribution Distribution (VMT by5 MOVES Road Types) Age Distribution sourceTypeAge (Vehicle Distribution Population by Age ofVehicle) Ramp Fraction RoadType
Meteorology ZoneMonthHour Data ·

Fuel (% of FueiFormulation Market Share by Fuel Type) FuelSupply
JIM Program IMCoverage Calculated from local VMT data. Usetravel demand model base yeardistributions for all years.

Local age.distributions developed fromvehicle registration dataforsourcetypes 21 I 31 I and 32. Default MOVES age distributionsforall other source types. Based on local travel demand model.

MOBILE6 Summer Met Data Convertedto MOVES format

MOVES Defaults Delaware County MOVES Defaults for Summer (check ifvaries among counties) No ProgramAppendix 8
Vehicle Age Distributions forDelaware County: SourceTypes aqeid 11 21 31 32 41 42 43 51 52 53 54 61 62 0 0.2109690540 0.0270887127 0.0099403579 0.0275038352 0.0643023355 0.0545743076 0.0622220643 0.0494240790 0.0588526168 0.0787544027 0.0615095870 0.0535634660 0.0670845256 1 0.1921154969 0.0463389893 0.0404938788 0.0513916283 0.0626728412 0.0531913309 0.0606452875 0.0481716155 0.0573612230 0.0767586735 0.0599508636 0.0535634660 0.0670845256 2 0.1573471585 0.0519181114 0.0469812703 0.0622397545 0.0624853859 0.0530322328 0.0604638952 0.0480275345 0.0571896519 0.0765290827 0.0597715492 0.0541045093 0.0677621447 3 0.1359771581 0.0490363335 0.0414704754 0.0464606618 0.0624229593 0.0529792497 0.0604034894 0.0479795509 0.0571325186 0.0764526251 0.0597118340 0.0575579884 0.0720873878 4 0.1058454735 0.0534396902 0.0599909316 0.0567609029 0.0617369906 0.0523970560 0.0597397140 0.0474523026 0.0565046834 0.0756124785 0.0590556596 0.0564182312 0.0706599203 5 0.0750909142 0.0551226485 0.0572355342 0.0592811747 0.0559170498 0.0474575929 0.0541080614 0.0429789769 0.0511779950 0.0684845018 0.0534884926 0.0489290859 0.0612802835 6 0.0476805323 0.0539007746 0.0620487601 0.0535831690 0.0468365056 0.0397508123 0.0453212873 0.0359994879 0.0428670388 0.0573630896 0.0448023279 0.0366034411 0.0458432683 7 0.0331026886 0.0590188122 0.0643507377 0.0569800570 0.0425786431 0.0361370941 0.0412011709 0.0327268079 0.0389700355 0.0521482660 0.0407293873 0.0340742206 0.0426755959 8 0.0197278356 0.0571744744 0.0562240592 0.0515012053 0.0468268516 0.0397426124 0.0453119367 0.0359920640 0.0428582007 0.0573512681 0.0447930981 0.0358093100 0.0448486759 9 0.0118473747 0.0648976392 0.0674549196 0.0706771861 0.0534377006 0.0453533365 0.0517089150 0.0410733035 0.0489087688 0.0654479137 0.0511168252 0.0526288382 0.0659139597 10 0.0053251777 0.0617853191 0.0657458756 0.0585141354 0.0532712252 0.0452120443 0.0515478328 0.0409453420 0.0487564067 0.0652440247 0.0509575859 0.0624520143 0.0782168041 11 0.0025378610 0.0539929915 0.0564333298 0.0535831690 0.0407951886 0.0536203440 0.0411075833 0.0313560350 0.0391491717 0.0523881239 0.0302729398 0.0478258601 0.0598985955 12 0.0013011470 0.0545001844 0.0512364410 0.0481043173 0.0331924560 0.0489936472 0.0382933197 0.0255124310 0.0294483131 0.0394065607 0.0466101866 0.0389128550 0.0487354179 13 0.0006124019 0.0458548506 0.0440166021 0.0398860399 0.0277347637 0.0456089741 0.0333751020 0.0545980574 0.0316399801 0.0194774783 0.0291673253 0.0325145854 0.0462990441 14 0.0002476898 0.0466386942 0.0419587737 0.0414201183 0.0364294706 0.0377746681 0.0430863640 0.0632656498 0.0364439725 0.0194691525 0.0347804437 0.0427077419 0.0462072388 15 0.0001527705 0.0386158244 0.0387499564 0.0355029586 0.0283511969 0.0332950401 0.0210164622 0.0395649332 0.0357887614 0.0311848083 0.0335202065 0.0332372597 0.0300444032 16 0.0000668536 0.0327369974 0.0303442503 0.0284900285 0.0235884296 0.0279132162 0.0253671498 0.0341566540 0.0259987277 0.0230196849 0.0233151075 0.0276536739 0.0230524492 17 0.0000299603 0.0298321653 0.0247985770 0.0249835634 0.0175637044 0.0244970846 0.0206833627 0.0146346390 0.0197956396 0.0052258132 0.0206748599 0.0205906442 0.0138452217 18 0.0000127409 0.0225700848 0.0212060968 0.0197238659 0.0201192241 0.0250480695 0.0266888558 0.0401958334 0.0193740288 0.0037212159 0.0155464816 0.0235865809 0.0100066460 19 0.0000055369 0.0178900775 0.0166718984 0.0150120535 0.0225790392 0.0366610768 0.0301447753 0.0342277190 0.0227335396 0.0175775477 0.0203628520 0.0264703224 0.0098603738 20 0.0000022027 0.0162301734 0.0203341355 0.0177514793 0.0226407923 0.0281971934 0.0173882093 0.0270081845 0.0289395633 0.0183874556 0.0265944575 0.0265427135 0.0095755112 21 0.0000010015 0.0121956842 0.0180321579 0.0169844401 0.0212965445 0.0224413685 0.0209032932 0.0367430589 0.0255089927 0.0121624816 0.0238465850 0.0249667984 0.0083402541 22 0.0000005320 0.0091755810 0.0125562415 0.0118343195 0.0221366577 0.0207614938 0.0211741003 0.0294241579 0.0211707159 0.0029207200 0.0232916866 0.0259516972 0.0021970287 23 0.0000002372 0.0079537071 0.0107425622 0.0105193951 0.0187753208 0.0176845935 0.0186862600 0.0367365508 0.0255742899 0.0006595597 0.0173635700 0.0220110680 0.0022815392 24 0.0000001072 0.0062476946 0.0081266785 0.0088757396 0.0165801584 0.0153441343 0.0162223474 0.0195371739 0.0181341022 0.0013228019 O.D186391363 0.0194375881 0.0028947085 25 0.0000000515 0.0045647363 0.0062781207 0.0056980057 0.0130464803 0.0119613578 0.0125269842 0.0202862884 0.0101534224 0.0013255722 0.0189070434 0.0152949162 0.0014963357 26 0.0000000201 0.0024206935 0.0035924802 0.0027394258 0.0052066606 0.0114707358 0.0046276161 0.0058785937 0.0158244798 0.0000000000 0.0123859355 0.0061039775 0.0003051544 27 0.0000000084 0.0013832534 0.0024066130 0.0036160421 0.0044375500 0.0062552616 0.0034269422 0.0066192300 0.0082431519 0.0005853113 0.0073123264 0.0052023202 0.0002365920 28 0.0000000046 0.0017982294 0.0022670992 0.0032873110 0.0038534093 0.0027153367 0.0040227141 0.0058648852 0.0078447522 0.0004224309 0.0040199156 0.0045175071 0.0007539156 29 0.0000000027 0.0014293619 0.0004534198 0.0007670392 0.0050202650 0.0073813428 0.0039557847 0.0014702211 0.008291 0352 0.0000000000 0.0005297244 0.0058854602 0.0002483418 30 0.0000000060 0.0142475101 0.0178577657 0.0163269779 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 Delaware County forsourcetypes 21, 32, and 32, MOVES201Oa default distributions for all other source types.Appendix C
01 eaware County e tce Popu attons: Vehicle Populations Source Types 11 21 31 32 41 42 43 51 52 53 54 61 62 AnnualPopulations 2008 2,743 45,696 30,485 9,333 51 27 346 16 1,079 139 250 1,667 1,994 2009 2,755 45,892 30,616 9,373 51 27 349 16 1,086 140 251 1,678 2,007 2010 2,767 46,089 30,747 9,414 52 27 351 16 1,093 141 253 1,689 2,021 2011 2,779 46,286 30,879 9,454 52 27 353 16 1,101 141 255 1,700 2,034 2012 2,791 46,485 31,011 9,495 52 27 356 16 1,108 142 256 1,711 2,047 2013 2,802 46,684 31,144 9,535 53 28 358 16 1,115 143 258 1,723 2,061 2014 2,814 46,884 31,278 9,576 53 28 360 16 1,123 144 260 1,734 2,075 2015 2,827 47,085 31,412 9,617 53 28 363 17 1,130 145 261 1,746 2,089 2016 2,839 47,287 31,546 9,658 54 28 365 17 1,138 146 263 1,757 2,102 2017 2,851 47,489 31,682 9,700 54 28 368 17 1,145 147 265 1,769 2,116 2018 2,863 47,693 31,817 9,741 55 29 370 17 1,153 148 267 1,781 2,130 2019 2,875 47,897 31,954 9,783 55 29 373 17 1,161 149 268 1,793 2,145 2020 2,888 48,103 32,091 9,825 55 29 375 17 1,168 150 270 1,805 2,159 2021 2,900 48,309 32,228 9,867 56 29 378 17 1,176 151 272 1,817 2,173 2022 2,912 48,516 32,367 9,909 56 29 380 17 1,184 152 274 1,829 2,188 2023 2,925 48,724 32,505 9,952 56 29 383 17 1,192 153 276 1,841 2,202 2024 2,937 48,933 32,645 9,995 57 30 385 18 1,200 154 277 1,853 2,217 2025 2,950 49,143 32,785 10,037 57 30 388 18 1,208 155 279 1,865 2,232 2026 2,963 49,353 32,925 10,081 57 30 390 18 1,216 156 281 1,878 2,246 2027 2,975 49,565 33,066 10,124 58 30 393 18 1,224 157 283 1,890 2,261 2028 2,988 49,777 33,208 10,167 58 30 395 18 1,232 158 285 1,903 2,276 2029 3,001 49,991 33,350 10,211 59 31 398 18 1,240 159 287 1,915 2,291 2030 3,014 50,205 33,493 10,254 59 31 401 18 1,248 160 289 1,928 2,307 2031 3,027 50,420 33,637 10,298 59 31 403 18 1,257 162 291 1,941 2,322 2032 3,040 50,637 33,781 10,343 60 31 406 18 1,265 163 293 1,954 2,337 2033 3,053 50,854 33,926 10,387 60 32 409 19 1,273 164 294 1,967 2,353 2034 3,066 51,072 34,071 10,431 61 32 411 19 1,282 165 296 1,980 2,368 2035 3,079 51,291 34,217 10,476 61 32 414 19 1,290 166 298 1,993 2,384 2036 3,092 51,510 34,364 10,521 61 32 417 19 1,299 167 300 2,006 2,400 2037 3,105 51,731 34,511 10,566 62 32 420 19 1,307 168 302 2,020 2,416 2038 3,119 51,953 34,659 10,611 62 33 422 19 1,316 169 304 2,033 2,432 2039 3,132 52,176 34,808 10,657 63 33 425 19 1,325 170 306 2,046 2,448 2040 3,146 52,399 34,957 10,703 63 33 428 19 1,334 171 308 2,060 2,464
Source: Quality assured vehicle registration data for Delaware 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 forecastsAppendix D
D I

e aware 

### C t M t
. I D ountv e eoro og1ca at a: monthiD zoneiD HouriD temperature reiHumidity 7 180350 1 68.5 91.2 7 180350 2 67.3 95.1 7 180350 3 66.4 98.3 7 180350 4 65.7 100.0 7 180350 5 65.1 100.0 7 180350 6 64.5 100.0 7 180350 7 64.0 100.0 7 180350 8 64.4 100.0 7 180350 9 67.0 96.0 7 180350 10 71.2 83.1 7 180350 11 75.5 72.0 7 180350 12 79.2 63.8 7 180350 13 82.4 57.4 7 180350 14 84.1 54.3 7 180350 15 84.7 53.2 7 180350 16 84.9 52.9 7 180350 17 84.5 53.7 7 180350 18 83.2 55.8 7 180350 19 81.2 59.8 7 180350 20 78.5 65.3 7 180350 21 75.8 71.4 7 180350 22 73.4 77.2 7 180350 23 71.8 81.7 7 180350 24 70.1 86.4

Source: Mobile 6.2 reported meteorological data from Appendix G ofthe RequestforRedesignation and Maintenance Plan for Ozone Attainmentin the 8-Hour Ozone Basic NonattainmentArea, Delaware County, Indiana prepared by IDEM on August25, 2005 converted using EPA data converter.Appendix E
Indiana Default VMTDistributions by Vehicle Type andRoad 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 ofTransportation traffic count data.Appendix F
Indiana Default HourlvDistribution Factors forRoad Type 2- RuralRestrictedAccess: SourceTypes 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 0.0711110358 0.0711110358 0.0517738130 0.0517738130 11 0.0559204481 0.0513700269 0.0575854739 0.0575854739 0.0576707709 0.0576707709 0.0576707709 0.0730230234 0.0730230234 0.0730230234 0.0730230234 0.0557712484 0.0557712484 12 0.0572822100 0.0533048469 0.0582753930 0.0582753930 0.0549541212 0.0549541212 0.0549541212 0.0731872952 0.0731872952 0.0731872952 0.0731872952 0.0571435296 0.0571435296 13 0.0592008057 0.0551586141 0.0599414146 0.0599414146 0.0541541840 0.0541541840 0.0541541840 0.0739324454 0.0739324454 0.0739324454 0.0739324454 0.0567014536 0.0567014536 14 0.0615145144 0.0595500442 0.0635019874 0.0635019874 0.0570747392 0.0570747392 0.0570747392 0.0746488056 0.0746488056 0.0746488056 0.0746488056 0.0567500887 0.0567500887 15 0.0647783324 0.0662712693 0.0683897966 0.0683897966 0.0551925339 0.0551925339 0.0551925339 0.0704234655 0.0704234655 0.0704234655 0.0704234655 0.0578234055 0.0578234055 16 0.0713500739 0.0764876319 0.0772110428 0.0772110428 0.0551956709 0.0551956709 0.0551956709 0.0628601912 0.0628601912 0.0628601912 0.0628601912 0.0577540296 0.0577540296 17 0.0754978425 0.0847160034 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: Statewlde averages developed from lndlana Department ofTransportation traffic count data.Indiana Default HourlvDistribution Factors forRoad Tvoe 3- Rural UnrestrictedAccess: SourceTypes 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 O.Q061663979 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 Indiana Department ofTransportation traffic count data.Indiana DefaultHourlvDistribution Factors forRoad Tvoe 4-Urban RestrictedAccess: SourceTypes 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 O.D117453229 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 0.0795090490 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 0.0249336618 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 0,0124474209 0.0124474209 0.0124474209 0.0124474209 0.0317711657 0.0317711657 24 0.0198157539 0.0189063955 0.0154623663 0.0154623663 0.0217813392 0.0217813392 0.0217813392 0.0110419727 0.0110419727 0.0110419727 0.0110419727 0.0278292477 0.0278292477
Source: Statewide averages developed from Indiana Department ofTransportation traffic count data.Indiana DefaultHourlvDistribution Factors forRoad Tvoe 5-Urban UnrestrictedAccess: 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 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
Indiana DefaultDailyDistribution Factors: dayiD monthiD 2 5 1 0.2325411725 0.7674588275 2 0.2380547378 0.7619452622 3 0.2393402049 0.7606597951 4 5 0.2396052454 0.2484757701 0.7603947546 0.7515242299 6 0.2489743665 0.7510256335 7 0.2481153021 0.7518846979 8 0.2527028648 0.7472971352 9 0.2496078420 0.7503921580 10 0.2462808693 0.7537191307 11 0.24397 42406 0.7560257594 12 0.2258784720 0.7741215280

Source: Statewide averages developed from Indiana Department ofTransportation traffic count data.Appendix H
Indiana DefaultMonthlyDistribution 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 ofTransportation traffic count data.Appendix I
Delaware CountyRamp Fractions: Ramp Road Type Fraction 2 4 1.3% 12.3%

Source: Analysis ofVHT from the Muncie travel demand model.

# Appendix B

Delaware CountyArea Interagency Consultation Group MeetingMinutes/Summary

### Thispageleftintentionallyblank

### Interagency Consultation Group (ICG) Conference CallMinutes

Forthe MOBILE6.2 to MOVES MVEB ReplacementUpdate Related to the Delaware CountyMaintenanceArea underthe 1997 8-HourOzone Standard

ICG Conference CallDate and Time


### • May 30, 2012 at lOam Eastern

ICG Attendees


### • Shawn Seals (IDEM), PatriciaMorris (EPA), Steve Smith (INDOT), Larry Heil (FHWA), Greg Katter (INDOT), Hugh Smith (DMMPC), MartaMoody (DMMPC), and Jay Mitchell (INDOT)

ICG Discussion Topics and Conclusions 

### 1. Forthe Ozone MVEB Replacement submittal, various mobile source margins of safety were discussed. A. After discussion, the consensus ofthe ICGwasthat as long as the a 15% mobile source marginofsafetyfor VOC andNOx emissions does notresultin
an exceedance oftheall sources margins ofsafety, itwas reasonable and appropriate for inclusioninMVEB Replacement submittal. The attached spreadsheetdemonstrates that a 15%mobile source margin ofsafety for VOC andNOx emissions fall wellbelowthe all sources margins ofsafety and, as such, will be reflected inthe OzoneMVEB Replacement submittal.

B-1