INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT 

( WiProtect Hoosiers' and lJur' Enrironment. 

Mitchell E. Daniels Jr.(.; ~; f 100 North Senate Avenue 

Governor · / , :\1 ~ Indianapolis, Indiana 46204 

i . ;,, I (317) 232-8603 

Thomas W Easterly 1 'DEC - L1 2012 I Toll Free (800) 451-6027 

Commissioner f. 1 l 'd IN 1 .' ;,"J www.1 em. .gov ·~ .... j; '1 .~ ~ ., ~·j ,; . .' ,: . ·. ·. - . ··-·-· -- .. ·.··: ---~'; 'g~ - 'November 2s· 20f2 I 

Ms. Susan Hedman 

Regional Administrator 

U.S. Environmental Protection Agency 

Region 5 

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 Request for 

Redesignation Petition and Maintenance 

Plan Under the Annual National Ambient 

Air Quality Standard for Fine Particles for 

the Central Indiana Nonattainment Area 

The Indiana Department of Environmental Management (IDEM) submits the 

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

Emissions Budget (MVEB) replacement update for the Request for Redesignation 

Petition and Maintenance Plan Under the Annual National Ambient Air Quality Standard 

for Fine Parlicles for the Central Indiana Nonattainment Area. The Indianapolis, Indiana 

nonattainment area includes Hamilton, Hendricks, Johnson, Marion, and Morgan 

counties. This request for redesignation was submitted to the United States 

Environmental Protection Agency (U.S. EPA) on May 31, 2011, and has not yet been 

acted upon. IDEM requests that U.S. EPA parallel process this draft MVEB replacement 

submittal for approval into Indiana's previously submitted request for redesignation under 

the annual fine particles standard. 

IDEM is providing an opportunity for a public hearing on the MVEB replacement 

update to the Indianapolis, Indiana nonattainment area if a public hearing request is 

received by January 2, 2013. A hearing has been scheduled for January 9, 2013. If a 

request for a public hearing is not received by January 2, 2013, the hearing will be 

cancelled. IDEM is providing a 38 day comment period on this update, with the public 

comment period ending on January 11, 2013. The final submittal of the MVEB update for 

the Indianapolis, Indiana nonattainment area will document the public review process, 

including a detailed summary of and response to substantive comments. 

Recycled Paper @ An Equal Opportunity Employer Please Recycle 0 
Ms. Hedman 

Page 2 

This MOBILE6.2 to MOVES MVEB replacement update incorporates onroad 

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

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

emission factors and data extracted from the Indianapolis, Indiana area's travel-demand 

model. 

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

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

model indicates that emission estimates can be considerably different than similar 

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

annual fine particle redesignation request. 

Onroad safety margins, established through the interagency consultation process, 

are included for fine particulate matter (PM25) and nitrogen oxides (NOx). 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 Indianapolis, Indiana 

area will continue to remain well below the overall safety margins for all sources. MVEBs 

are also constrained to ensure that total PM2.s and NOx emissions (i.e., all source 

categories) do not exceed attainment year emissions, to ensure continued maintenance 

of the annual national ambient air quality standard for fine particles. 

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. 

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

MOBILE6.2 to MOVES MVEB replacement update and revised transportation conformity 

budgets and approval of Indiana's Request to Parallel Process the Draft MOBILE6.2 to 

MOVES MVEB Replacement Update to the Request for Redesignation Petition and 

Maintenance Plan Under the Annual National Ambient Air Quality Standard for Fine 

Particles for the Central Indiana Nonattainment Area of May 31, 2011. If you have any 

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

Programs Branch, at (317) 233-5694. 

Sincerely, 

~ o.~o Keith Baugues 

Assistant Commissioner 

Office of Air Quality 

KB/sad/sms 

Enclosure: 

Recycled Paper (i) 

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

Redesignation Petition and Maintenance Plan Under the Annual National Ambient 

Air Quality Standard (NAAQS) for Fine Particles for the Central Indiana 

Nonattainment Area 

An Equal Opportunity Employer Please Recycle O 
Ms. Hedman 

Page 3 

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) 

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

John Summerhays, U.S. EPA Region 5 (w/ enclosures) 

Philip Roth, IMPO (w/ enclosures) 

Jerry Bridges, MCCOG (w/ enclosures) 

Scott Deloney, IDEM (no enclosures) 

Christine Pedersen, IDEM (no enclosures) 

Shawn Seals, IDEM (w/ enclosures) 

Recycled Paper (!) An Equal Opportunity Employer Please Recycle O 

DRAFT 

Onroad Emissions MOBILE6.2 to 

MOVES Replacement Submittal ~,!:cn1·i~!hl(0> 

·~''··:~~~·~~,i>~ .. 

For the Indiatti$olis,lfld!ana 

Maintenance ·~;lanl1tt.~t~r th~~~nnual <~~~l~~;~l··· '<<;~]~~ . 

N atio11:~J All\p r~~t.~l:~,~.Quality _4:~~:~~i:_~-~~::\]jf;~~ff;:::;-:.-. ·<it~0;~;::-__ /~~~~~;;~:[!~~;~~" _ ·<:::~tE+ 

Staf:fiiara. fortDlthe'~articles 
This page intentionally left blank 
Introduction 

emiSSIOnS. 

Emission Inventory 

The tables titled, 2008 Central Indiana Area, 2015 f:?f'.J:~a. 2020' ~~htral Indiana 

Area, and 2025 Central Indiana Area, included 

Petition and Maintenance Plan. The table 

of the originlit~designation 

2015, 2020, and 2025 Central 

Indiana Area All Anthropogenic SO\JrC()S~)l\, r;mast•deJ·ect a replacement of the 

existing separate 2008, 2015,2020, and Lv~:~;}a[ 

been and nitrogen revised to oxides i~;~~i~~~~~~~~~~~~~~:s 

overall safety margin 

are included in the 

1 

~RI'l:~ndix E as detailed above) has 

,:,. matter (PMz.s) 

· · results in a different 

dioxide (S02) emissions 

federal1mplementation rule for fine 

be a significant contributor to fine 

constitutes less than 1.2% of the area's 

not included in the table titled, 2008, 

bp1Jge:nic Sources in Tons Per Year. 
2008 Central Indiana Area (Tons Per Year)- (MOBILE6.2-based Onroad Emissions) 

ONROAD NONROAD AREA EGU POINT TOTAL w/o ONROAD 

HAMILTON COUNTY 202.68 7.29 3.32 8.99 222.28 

Direct HENDRICKS COUNTY 115.34 5.01 0.00 30.31 150.66 

PM2.5 JOHNSON COUNTY 4(&..6+ 69.93 4.54 0.00 0.44 74.91 

MARION COUNTY 378.65 61.52 1,535.20 677.02 2,652.39 

MORGAN COUNTY 38.82 7.00 427.97 126.29 600.08 

40Mi'7 805.42 85.36 843.05 

ALw/ONROAD 4,103.99 

so, 

NO, 

2 
2015 Central Indiana Area (Tons Per Year)- (MOBILE6.2-based Onroad Emissions) 

ONROAD NONROAD AREA EGU POINT TOTAL w/o ONROAD 

HAMILTON COUNTY 133.61 7.06 0.13 9.19 149.99 

Direct HENDRICKS COUNTY 69.92 4.91 0.00 29.28 104.11 

PM2.5 JOHNSON COUNTY ~ 45.46 4.40 0.00 0.42 50.28 

MARION COUNTY 260.03 58.63 2,007.70 636.70 2,963.06 

MORGAN COUNTY 28.74 6.77 560.01 147.15 742.67 

~ 537.76 81.77 822.74 

4,299.78 

so, 

NO, 

3 
2020 Central Indiana Area (Tons Per Year)- (MOBILE6.2-based Onroad Emissions) 

ONROAD NONROAD AREA EGU POINT TOTAL w/o ONROAD 

HAMILTON COUNTY 93.73 6.88 0.13 8.94 109.68 

Direct HENDRICKS COUNTY 44.83 4.81 0.00 28.81 78.45 

PMz.s JOHNSON COUNTY ~ 31.41 4.29 0.00 0.42 36.12 

MARION COUNTY 191.29 56.42 2,007.69 623.48 2,878.88 

MORGAN COUNTY 22.75 6.57 560.01 144.52 733.85 

~ 384.01 78.97 806.17 

4,112.09 

4 
2025 Central Indiana Area (Tons Per Year)- (MOBILE6.2-based Onroad Emissions) 

ONROAD NONROAD AREA EGU POINT TOTAL w/o ONROAD 

HAMILTON COUNTY 67.50 6.70 0.13 8.70 83.03 

Direct HENDRICKS COUNTY 29.93 4.71 0.00 28.34 62.98 

PM2.5 JOHNSON COUNTY UlB4 22.32 4.18 0.00 0.42 26.92 

MARION COUNTY 143.54 54.32 2,007.67 610.60 2,816.13 

MORGAN COUNTY 18.23 6.39 560.01 141.95 726.58 

UllM 281.52 76.30 2,567.81 790.01 

w/ONROAD 3,976.18 

5 
2008, 2015, 2020, and 2025 Central Indiana Area All Anthropogenic Sources in Tons Per 

Year- (MOVES-based Onroad Emissions) 

Sector 2008PM2.5 2015PM2•5 2020 PM2•5 2025PM2•5 

Area 85.36 81.77 78.97 76.30 

Nonroad 805.42 537.76 384.01 281.52 

Onroad 1,463.72 742.40 571.28 400.16 

Point 843.05 822.74 806.17 790.01 

Total 3,197.55 2,184.67 1,840.43 1,547.99 

Overall Safety 1,012.88 1,357.12 1,649.56 Margin 

Sector 2008NOx 2015 NO, 2020NOx 2025N0x 

Area 4,885.91 4,808.82 4,726.75 4,646.40 

Nonroad 10,953.68 7,146.72 4,961.21 3,544.70 

On road 43,388.93 22,012.60 16,818.74 11,624.87 

Point 6,259.45 ':- 6,267.98 "·~,182.66 6,098.76 

Total 65,487.97 40,236.12 32,689.36 25,914.73 

Overall Safety 25,251.85 32,798.61 39,573.24 Margin 'R ··~ .. :• <'" '-:· .,~Hi" ·:.. ,_., "".;; ' <. , x:+',mf~ ~.. '<• '··· · ~. 

Onroad emission estimates in the taB\~\itfed 2008, 201S}:2020, and 2025 Central Indiana Area ~~: ... ~ .. ·~ ... ...... ~~ ·~···, 

All Anthropogenic Sources in Tons Pe\ Year, wer~ calculate _;\! ng U.S. EPA's MOVES modelproduced emission factors and data extra~ted frb:inj h_r ~ea's tr~~e~~demand model. The 

MOVES model implem~nts":@.:: ~ignifi.cantly different''apj)l'oach to''eg}is.sions estimation than the ~:-· · . ..••. .• , ... ,., ' .. ·:~ . ... • ,._ ·! .•• 

pre.vious model (M~~JLp62):.}~r.~~iminary ~se.oft~ MO<'ES fl~'del indicates that e~ssion 

estimates can be cons&~~:rably difftr~p.t than tt.mlar calculati'on~,usmg MOBILE6.2, whtch was 

used to create the origina1 ·Motor V.~l$cle Emission Budgets (MVEBs) for the Central Indiana '7. l .<•.\ " .... 

Area. A gen~~~ ummary ~f:the,~MQYES methodol<;>gy used in this area can be found in 

Appendix ~ In ll;ddit~on, MOVE.S mput.arid outp~tJUes are being provided electronically with / •;:' ,.._._ ~· ,r, ... •••o: ;,: ,•,,,, ~·~'> 

this submittat Growth and control strategy ass\imptltfns for non-mobile sources (i.e. area, ~ .~ ''v. _\S, "~·····;~~..;'2i 

nonroad, and point) from the,original ·submittal fO"r the years 2008, 2015, 2020, and 2025 were 

developed before the do~'tl,un in the economy over the last several years. Because of this, the 

factors inci~8_~ n the origi~ ll submitta] may project more growth than will actually occur in the ·'\?~~;)~' .. ~ ~ 

future. As a res~lt,-J~e growth ~~? control strategy assumptions for the non-mobile sources for 

the year.s 2008, 20lS~220, andi~P?5 continue to be valid and do not affect the overall 

conclusiOns of the pla~;;h.... .."">;:~~~ 

~.::~,.,., ~~~"~;-~;:~~::;·· 

Onroad safety margins haveJ:,"een included for onroad emission estimates to accommodate the 

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

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

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

Air Act (CAA) requirements as the revised emission inventories clearly illustrate that total PM2.5 

and NOx emissions in the Central Indiana Area will continue to decline leading to local 

reductions between 2008 (attainment/base year), 2015 (interim year), and 2025 (maintenance 

plan horizon year). 

6 
Transportation Conformity Budgets 

Table 5.2 was included on Page 26 of the original Redesignation Petition and Maintenance Plan. 

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

MVEBs calculated using U.S. EPA's MOVES model-produced emission factors and data extracted 

from the region's travel-demand model. 

Table 5.2 

Motor Vehicle Emission Budgets for the Central Indiana Area 

(MOBILE6.2-based Onroad i(_ms) 

Year 

.. .• ,....---~,....------,':'::---'-~-----' .... · ~ .. \~· ' :-!• ' ,1' ~,., .. , ~ . .. ..... ~ : ~ .... ,.~ 

it-.wa~ O.etermiried.Jhat an interim budget year of 

·v ,u.UI",''-'' year ~f2025, would be appropriate. The interagency 

pere~nt (15<%) fuargin of safety for onroad PM2.5 and NOx .. ,;-..:.,.:.,\' ... (' '*i'• 

and gQ~?· A s~ary ofthis interagency consultation 

Th;se i.~i' xd emission inventories clearly illustrate that 

Iri1iiana Area will continue to decline leading to 

year), 2015 (interim year), and 2025 (maintenance 

overall safety margin as defined in the Code of Federal 

, it is evident the onroad safety margin allocation is 

'""'""'·T, , even with the allocation of an onroad safety margin 

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

sources in the Central Indiana Area as detailed in the table titled, 2008, 2015, 2020, and 2025 

Central Indiana Area All Anthropogenic Sources in Tons Per Year. MVEBs are constrained to 

ensure that the total emissions (i.e., all source categories) do not exceed the 2008 attainment/base 

year emissions of either PM2.s or NOx, thereby ensuring continued maintenance of the annual 

national ambient standard for fine particles. 

7 
Conclusion 

This MOBILE6.2 to MOVES replacement update to the previously submitted Requestfor 

Redesignation and Maintenance Plan Under the Annual National Ambient Air Quality Standard 

for Fine Particles for the Central Indiana Area incorporates onroad 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 of the MOVES model in future transportation conformity 

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

factors and data extracted from the area's travel-demand model. Onroad safety margins for PM2.s 

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

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

constrained to ensure that total PM2.5 and NOx emissions categories) do not exceed 

attaimnent/base year (2008) emissions to ensure of the annual national 

ambient standard for fine particles. With the onroad safety margins 

applied to mobile sources, the Central Indiana well below the overall 

safety margins for all sources into the future. and 

Maintenance Plan Under the Annual National 

the Central Indiana Area continues to meet all 

8 
Appendix A 

Central Indiana 

MOVES Methodology 
This page left intentionally blank 
- - - - -CAMBRIDGE-- - - - SYSTEMATICS 

Update of Indianapolis MPO Travel Demand 

Model Air Quality Pre- and Post-Processor to 

Reflect MOVES 

technical 

Memorandum 

Final Draft 

prepared for 

Indianapolis Metropolitan Planning Organization 

prepared by 

Cambridge Systematics, Inc. 

Error! Unknown document property name. www.camsys.com 
technicalnienwrnndiLm 

Update of Indianapolis MPO Travel 

Demand Model Air Quality Preand Post-Processor to Reflect 

MOVES 

prepared for 

Indianapolis Metropolitan Planning Organization 

prepared by 

Cambridge Systematics, Inc. 

100 CambridgePark Drive, Suite 400 

Cambridge, MA 02140 

dote 

December 1, 2011 
Table of Contents 

Introduction ...................................................................................................................... ! 

1.0 MOVES Input Data and Planning Assumptions .......................................... l-1 

1.1 Air Quality Analysis Years ........................................................................ 1-1 

1.2 MOVE Inputs ............................................................................................... 1-3 

2.0 TDM Pre- and Post-Processor ........................................................................... 2-1 

2.1 Included Counties ....................................................................................... 2-3 

2.2 Air Quality Module Script Structure (Macros) ....................................... 2-3 

A. Appendix: User's Guide to Running TDM Air Quality Module .............. 14 

State of Indiana 

Error! Unknown document property uame. 

List of Tables 

Table 1.1 General Parameter Inputs in MOVES2010a .......................................... 1-3 

Table 1.2 County Data Manager Inputs in MOVES2010a ................................... 1-4 

Table 2.1 HPMS Functional Class Codes Assigned Based on Area 

Type and Facility Type Combinations .................................................. 2-6 

Table 2.2 Description of Input files and Array Variables .................................... 2-7 

Table 2.3 HPMS Functional Class to MOVES Road Type Equivalency 

Table ........................................................................................................... 2-9 

Table 2.4 Hours Within Each Time Period ............................................................ 2-9 

Table 2.5 Speed Ranges Within Each Speed Bin ................................................. 2-10 

Table 2.6 Field Descriptions of the Link Database (EMIS_Daily.bin) .............. 2-11 

Table 2.7 Emissions by HPMS Functional Class ................................................. 2-13 

Table 2.8 Emissions by County ............................................................................. 2-13 

State of Indiana iii 

List of Figures 

Figure 1.1 Indianapolis MPO Air Quality Analysis Years .................................... 1-2 

Figure 2.1 Overview of Emissions Calculation Process ......................................... 2-1 

Figure 2.2 Flow Chart of Emissions Calculation Process ...................................... 2-2 

Figure 2.3 Flow Diagram of GISDK Script for Air Quality Module .................... 2-5 

Figure 2.4 Process for Calculating Daily Running Emissions ............................ 2-12 

State of Indiana v 
Introduction 

State of Indiana 

The purpose of the air quality pre- and post-processor update was to transition 

from the current MOBILE6.2 based emissions module within the Indianapolis 

travel demand model (TDM) to MOVES2010a, the U.S. Environmental Protection 

Agency's (EPA) Motor Vehicle Emissions Simulator (MOVES) model. Further 

detail on the input data and planning assumptions used to run MOVES2010a, as 

well as the sh·ucture of the air quality pre- and post-processor (air quality 

module) within the TDM, are provided below. A user's guide to running the 

TDM air quality module is included as an appendix. 

1-1 
1.0 MOVES Input Data and 

Planning Assumptions 

In order to automate the calculation of ozone and PM2.semissions within the TDM 

post-processor, MOVES2010a was run in emission rate mode providing emission 

rates that were used as input files into the TDM post-processor and then applied to 

pre-processed travel activity data within the TDM to calculate emissions. Unless 

inputs into MOVES change, fm example, fuel formulation data or a new inspection 

and maintenance (I/M) program in the Indianapolis area, it should not be 

necessary to run MOVES again until the next full update of the Indianapolis LongRange Transportation Plan (LRTP) or every five years at a minimum. 

1.1 AIR QUALITY ANALYSIS YEARS 

State of Indiana 

Since the base validation year of the Indianapolis TDM is 2010, MOVES2010a 

was run for 2015, 2020, and 2025 representing future year runs necessary to 

created MOVES-based emissions for input into the PM2.s and Ozone Motor 

Vehicle Emissions Budgets (MVEB) as part of the State Implementation Plans 

(SIP). MOVES-based emissions for air quality years required prior to the base 

year of the model (i.e., 2002, 2005, 2006, and 2008) will be calculated off-model by 

the Indianapolis MPO. Figure 1.1 illustrates why each of the air quality analysis 

years were chosen. It should be noted that year 2035 is the current LRTP horizon 

year and as such, the Indianapolis MPO will be required to run MOVES at a later 

time fm the purpose of the regional emissions analysis to complete their 

conformity determination. 

1-1 
Figure 1.1 Indianapolis MPO Air Quality Analysis Years 

State of Indiana 1-2 
1.2 MOVE INPUTS 

State of Indiana 

Table 1.1 demonstrates the general parameter inputs for MOVES, while Table 1.2 

demonstrates the county data manager inputs, as agreed upon during 

interagency consultation in May and June of 2011'. 

Table1.1 General Parameter Inputs in MOVES2010a 

MOVES Screen Input Item Ozone PM2.o 

Description Description User Choice 

Domain/Scale County 

Scale 

Calculation Type Emission Rate 

Time Aggregation Hour Hour Level 

Yeara 2002, 2005, 2006, 2008,2015,2025 

Time Spans 2015,2020,2035' 

Months July April 

Days Weekday Weekday 

Hours Select All Select All 

Geographic Bounds Geographic Bounds' Marion Marion 

Vehicles Vehicles All Gas and Diesel Combinations 

Road Type Road Type Select All 

Pollutants Pollutants VOC, NO,, and PM, with all 

Processes Processes supporting subspecies; NO, 

Database Name Marion Ozone Marion PM2.o 

General Output Units Select "Grams" and "Miles" and "Million BTU" 

Activity No Selections Required 

Output Emissions Detail On Road Select "Source Use Type" 

Run future years first 

A MOVES run for Marion County will represent the entire Central Indiana Maintenance and 

Non attainment Areas. 

1 It should be noted that while emission rate mode was chosen early in the course of the project, the project 

team later became aware of some bugs in EPA's MOVES emission rate calculations associated with the VOC 

refueling process and PM2.5 tirewear process. While these calculation errors internal to MOVES are believed 

to result in only slightly different emissions results than if MOVES were run in Inventory mode, the exact size 

of the differences are unknovvn at this point. 

1-3 
' 2035 was run as an internal check to verify a reasonable margin of safety for mobile sources. 

Table 1.2 County Data Manager Inputs in MOVES2010a 

County Data Manager Input Excel Sheet Tab Name Ozone PM2.s 

2009 Light-Duty 2009 Light-Duty 

Registration Data for 9 Registration Data for 5 

Source (Vehicle) Counties; MOVES Counties; MOVES 

source Type Year Tech guidance method Tech guidance method Type Population for heavy duty; human for heavy duty; human 

population to forecast population to forecast 

future years future years 

Model VMT with Model VMT with vehicle vehicle split from split from INDOT 18 HPMSVTypeYear INDOT 18 

Nonattainment ATR Nonattainment ATR 

Vehicle Type VMT (by 13 data data 

MOVES Vehicle Types) 

Month VMTF raction IN DOT Statewide ATR Data 

DayVMTFraction IN DOT Statewide ATR Data 

HourVMTFraction IN DOT 18 Nonattianment ATR Data 

Average Speed Distribution Not Needed for Emission (percentage of VHT in each 5 avgSpeed Distribution Rate Mode (Dummy Inputs) mph speed bin) 

Road Type Distribution (VMT roadType Distribution Not Needed for Emission 

by 5 MOVES Road Types) Rate Mode (Dummy Inputs) 

Age Distribution (Vehicle sourceTypeAge 2009 Light-Duty Registration Data for 9 

Population by Age of Vehicle) Distribution Counties; MOVES default age distributions for 

heavy-duty+ motorcycles 

Ramp Fraction RoadType Local TDM results (2% rural, 8% urban). 

MOBILE6 Met Data for 

MOBILE6 Summer each of 4 seasons 

Meteorology Data ZoneMonthHour Met Data Converted to 

converted to MOVES 

format and then MOVES format averaged to represent 

entire year. 

FueiFormulation National Defaults 

Marion County Marion County MOVES Fuel (Percentage of Market MOVES Defaults for 

Share by Fuel Type) Fuel Supply Summer (check if Defaults for annual 

varies among (check if varies among 

counties) counties) 

State of Indiana 1-4 
liM Program 1M Coverage No Program 

State of Indiana 1-5 
2.0 

State of Indiana 

TOM Pre- and Post-Processor 

Emission rates generated by MOVES are used as inputs to the TDM postprocessor. The TDM air quality model, or emissions module, which contains 

both the TDM pre- and post-processor can be run from the MPO model interface 

by checking the "Air Quality" option in the "Assigmnent" stage of the TDM's 

user interface. The entire process takes approximately 10 to 15 minutes to run 

depending on the computer system's specifications. 

The TDM pre-processor provides some inputs to MOVES, such as VMT and road 

type distribution. Once emission factors are generated from MOVES, the 

emission factors are reformatted within the TDM in order to streamline the 

reading of the factors within the GISDK script and to get them in the format 

needed to apply to the travel activity data. The TDM pre-processor prepares the 

travel activity data on the model links in order to apply these factors and then 

the TDM post-processor calculates and summarizes both the running and nonrunning ermsswns. Figure 2.1 illustrates the overall emissions calculation 

process, while Figure 2.2 illustrates additional detail within each step. 

Figure 2.1 Overview of Emissions Calculation Process 

Run MOVES 

2-1 
Figure 2.2 Flow Chart of Emissions Calculation Process 

Process for Calculating Emissions in the 

Indy MPO Model Air Quality Postprocessor 

Run MOVES Run MOVES 

Emissions rates for 

each analysis year 

9-County 

Emission Rates 

Qnclude inputs for 9 

counties and output 1 

set of rates )I 

PM15 

Ozone 

(NO., VOCs) 

(run as average 

summer day for 9 

(run as annual 

average for 5 counties) 

NO,& VOC 

Running Emission Rates by 

MOVES Source (Vehicle) Type, 

Road Type, Speed Bin, and Hour' 

Reformat Emission 

Factors 

counties) 

J. - .>: ·lt ·'I 

. . . :_ . ·-~ 

NO,& VOC 

Nonrunning Hourly Emission 

Rates by MOVES Source 

(Vehicle) Type and Hour'·' 

~ ...... ....,.. ~ --- ... ~- · · ~r~r·~,-· r. r-~ ..... ·· 

... r -:-:...:~ ... ~- .... ··-· ~~.;-:.... ~ ;......: i . . . - . . 

- - - . . - ~---

Calculate 

Emissions 

PM15 

Running Hourly Emission Rates 

by MOVES Source (Vehicle) 

Type, Road Type, Speed Bin, 

and Hour' 

PM15 

Nonrunning Hourly Emission 

Rates by MOVES Source 

(Vehicle) Type and Hour'·' 

t The five counties in the Indy PM2.5 Nonaltainment A!ea Include Hamiton, Hendricks, Johnson, Marion. and Morgan Counties. The 9 counties in the Indy Ozone Nonattainment A!ea include the 

above fwe counties plus Hancock, Shelby, Boone, and Madison Counties. Madison County is included in the Anderson MPO travel demand model. As a resull running emissions for Mad'oson County 

wil be calculated sepa<ately from the Indy MPO travel demand model. However, VMT from the Anderson MPO travel demand model are input into MOVES to calculate emissions factors that will be 

applied to the Madison MPO model travel activity data It is anticipated that Madison County emissions will be added back in to the regional emissions outside the Indy air quality postprocessor. 

' Oisaggregated by poUutanl process, source type (vehicle type), hour, road type, speed. 

J Nonrunning emissions factors are output as two tables- rate per vehicle, rate per profile. 

' Disaggregated by pollutanl process, soorce type (vehicle type). 5 Weighted emissions factors are created by first calculating the percent ofVMT by MOVES source (vehicle) type using MOVES national defaults. The emissions factors for each of the 13 MOVES 

vehicle types are then aggregated to the 6 HPMS vehicle type categories by applying the weighted average to the rate. Total VMT from the Indy model is disaggregated to the 6 HPMS vehicle type 

categories by using the percent of VMT by vehicle type from HPMS data for the County. The weighted average emissions factor at the HPMS level is then applied to the disaggregated model VMT by 

HPMS vehicle type. 

' HPMS adjustment factors are calculated separately for each County. 

State of Indiana 

l egend 

MOVES J 

8/19/11 

2-2 
2.1 INCLUDED COUNTIES 

The TDM air quality model generates daily running emissions at the county level and at the Highway 

Performance Monitoring System (HPMS) functional class level. It generates the non-running daily emissions 

at the regional level based on vehicle population data. The counties included within the Indianapolis MPO 

boundary are: Marion, Hamilton, Johnson, Hendricks, Hancock, Shelby, Boone, Morgan, and Madison. The 

Anderson MPO TDM generates daily running emissions for Madison County. Historically, running emissions 

for Madison County have been calculated off-model by the Anderson MPO using MOBILE6.2 emission rates 

provided by the Indianapolis MPO. Similarly with MOVES, the Indianapolis MPO will provide the Anderson 

MPO with MOVES emission rates for the Anderson MPO to calculate Madison County running emissions and 

provide back to the Indianapolis MPO for inclusion in the overall Conformity Determination Report (CDR) for 

the entire Indianapolis nonattainment areas. The Indianapolis MPO will calculate non-running emissions for 

Madison County using vehicle populations from IN DOT and the same non-running emissions rates used for 

the other counties. As a result, the TDM air quality module does not output running emissions for Madison 

County, but does output non-running emissions for Madison County. 

The Ozone nonattainment area includes all nine counties and the PM2.5 nonattainment area includes 

Hamilton, Hendricks, Johnson, Marion, and Morgan Counties. Therefore, PM2.5 emissions output from 

the TDM air quality module for the other four counties (Hancock, Shelby, Boone, and Madison Counties) 

are set to zero. 

2.2 AIR QUALITY MODULE SCRIPT STRUCTURE 

(MACROS) 

The air quality post-processing script was written in GISDK to make it 

compatible with the other components of the TransCAD model. The air quality 

module script is embedded in the macro titled "AQ" within the overall model 

sh·eam script. It calls the following macros: 

• Set_HPMS: Sets the HPMS functional class code in the line layer of the 

model network based on specified Facility Type and Area Type combinations 

on each link. 

• ReadFiles: Reads the input files and stores the input data in arrays. 

• Calculate_NonRunning_Emissions: Calculates the daily non-running 

emissions based on emission rates generated by MOVES and the vehicle 

population within the MPO model boundary. 

• Create_MOVES_RD_TYPE: Populates each network link with a MOVES 

road type code based on an HPMS functional class code equivalency table. 

• CalculateintrazonalVMT: Calculates inh·azonal Vehicle Miles Traveled 

(VMT) based on intrazonal travel distance and intrazonal trips. The 

intrazonal VMT includes all travel activity that begin and end within the 

State of Indiana 2-3 
State of Indiana 

same traffic analysis zone and it is calculated for each time period and for 

both AB and BA directions. 

• Calculatejlpms_adj_factor: Calculates adjustment factors based on the ratio of 

HPMS VMT to the model VMT. The adjustment factors are calculated for each 

of the HPMS functional class codes and for each of the nine counties. Based on 

previous interagency consultation discussions, HPMS adjustment factors are not 

currently used by the Indianapolis MPO and as such, these factors are set to 1.0. 

• Calculate_Speed_Bin: Sets the speed bins for each network link based on 

congested model speeds for different times of day. It uses the five mile per 

hour (mph) speed bin ranges defined in MOVES to determine the speed bins 

for the network links. 

• Calculate_Running_Emissions: This macro calculates the daily running emissions 

by applying the emission rates generated by MOVES to the weighted VMT. 

• Summary: Summarizes the daily emissions by functional class and county. 

Figure 2.3 illustrates the flow diagram of GISDK script for the air quality module. 

2-4 
Figure 2.3 Flow Diagram of GISDK Script for Air Quality Module 

Rate per profile 

(rateperproflle.csv) 

Vehicle population 

(vehlclepopulalioJt.5Country.csv 

Emlssion_by_Country.csv 

Emlssion_by _HPMS_Functional_ 

Class_by _Country.csv 

Emission/mile for 

each network link 

0 Input File 0 Storage Array • Process 0 Output 

The following subsections provide further detail on each macro, or subroutine. 

Setting the HPMS Functional Classification 

The air quality module sets the HPMS functional class code for each network link 

based on its area type and facility type combination. Table 2.1lists each of these 

combinations and their assigned HPMS functional classification code. 

State of Indiana 2-5 
Table 2.1 HPMS Functional Class Codes Assigned Based on Area 

Type and Facility Type Combinations 

HPMS Functional Class Area Type Facility Type 

5 1, 7, 8, 9, 10, 11,12 

2 5 2,4,6 

6 5 3 

9 5 5 

11 1,2,3,4 1.~~~ 10, 11,12 

12 1, 2, 3, 4 2 

14 1,2,3,4 4,6 

16 1,2,3,4 3 

19 1, 2, 3, 4 5 

The assignment of HPMS Functional Class codes to each link in the network provides: 

State of Indiana 

1. An equivalency ath·ibute for MOVES road type codes, and 

2. The ability to calculate HPMS adjustment factors by HPMS functional class if 

desired. 

Reading Input Data 

The air quality module reads the input files and stores the input data in 

multidimensional arrays. Table 2.2 provides a description of the input data. 

2-6 
State of Indiana 

Table 2.2 Description of Input files and Array Variables 

Pollutantindex is the position of the pollutant ID in the array of pollutants, poll_seq = [3,87, 110,116, 117] 

2 Process index is the position of process ID in the array of processes, proc_seq = 

[1 ,2,9, 10, 11, 12,13, 15, 16,17, 18, 19,90] 

3 

4 

5 

Source type index is the position of 

source type ID in the array of MOVES 

source types, veh_seq = 

[11 ,21 ,31 ,32,41 ,42,43,51 ,52,53,54,61 ,62] 

Road type index is the position of 

MOVES road type ID in the array of 

MOVES road types, road_seq = [2,3,4,5] 

County index is the position of county ID 

in the array, county = [1 ,2,3,4,5,6, 7,8,9] 

Input File Name 

rateperdistance_ 

PM2.5.csv 

rateperdistance_ 

Oz.csv 

File Content 

PM2., Emission rate by pollutant 

process, by speed bin, by sour< 

by MOVES road type and by ho 

day 

Ozone Emission rate by polluta 

process, by speed bin, by sour< 

by MOVES road type and by ho 

day 

6 HPMS vehicle class index is the position of HPMS vehicle class in the array of HPMS vehicle classes 

[10, 20, 30, 40, 50,60] 

7 HPMS functional class index is the position of HPMS functional class in the array of HPMS functional classes 

8 The array [rateperdistance], [ratepervehicle] and [rateperprofile] in embedded into the array of emission 

rate types, Emis_Array = [rateperdistance, ratepervehicle, rateperprofile] 

Calculate Non-Running Emissions 

The non-running emissions are produced by - vehicles when they are not in 

motion. The calculation process uses [ratepervehicle], [rateperprofile] and the 

vehicle population as input. It calculates the emission based on the following 

equations: 

Daily non-running emissions by pollutant = emission from rate per vehicle by 

pollutant + emission from rate per profile by pollutant 

emission from rate per vehicle by pollutant = L,hourL,source2)rocess 

ratepervehicle* vehicle population 

emission from rate per profile by pollutant = L,lwurL,source rateperprofile* 

vehicle population 

In order to calculate Ozone emission which includes NOx and VOC, it uses the 

total vehicle population in all nine counties. PM2.s rates are applied to the vehicle 

population of five counties. The non-running emissions are stored in the array 

variable, NREmissions[pollutant index]. 

Create MOVES Road Type 

The MOVES road type is set based on the functional class. Below is the script 

that provides the criteria for assigning MOVES road type codes: 

2-7 
State of Indiana 

IfHPMS = 11 or HPMS= 12 then MOVES_TYPE = 4 where MOVES_TYPE 

= 4 for urban restricted access 

If HPMS = 1 or (HPMS= 2 and facilih; h;pe =2) then MOVES_TYPE = 2 

where MOVES_TYPE = 2for rural resb·icted access 

If HPMS > 12 then MOVES_TYPE = 5 where MOVES_TYPE = 5 for urban 

unrestricted access 

If (HPMS >2 and HPMS <=9) or (HPMS = 2 and FACILTY_TYPE<>2) where 

MOVES_TYPE = 3 for rural unrestricted access 

It was noticed in the model network that the roadways with an HPMS 

functional class code = 2 can be both restricted-access and unrestricted-access 

roadways. Therefore, the attribute "facility type" is used to differentiate 

between the roadways with restricted-access and the roadways with 

um·estricted-access. 

Table 2.3 illustrates the HPMS Functional Class to MOVES Road 

Type equivalency table. 

2-8 
State of Indiana 

Table 2.3 HPMS Functional Class to MOVES Road Type Equivalency Table 

MOVES Road Types HPMS Functional Class 

Out of network 

Period 

a.m. 

p.m. 

Off-peak 6 p 

2 1, 2 

3 6,9 

4 11,12 

5 14, 16, 19 

Calculate Intrazonal VMT 

The air quality module calculates the model VMT by using assigned flow and the 

length of the network links. The model generates assigned flow table for three 

different time periods: a.m., p.m. and off-peak. Table 2.4 demonstrates the time 

spans of each time period. 

Table 2.4 Hours Within Each Time Period 

The intrazonal VMT at each TAZ is calculated from the time of day trip tables 

and the inh·azonal distance skim. The intrazonal distance skim is generated from 

the shortest path based on congested travel time. In order to get the intrazonal 

skim, the average distance to the three nearest neighboring zones were 

multiplied by a factor of 0.5. The intrazonal VMT at each TAZ is distributed to 

the cenh·oid connectors based on their share of the assigned VMT. The 

intrazonal VMT on each link connector is calculated from the following 

equations: 

ABjBA InmzonalVMT for centroid connector i= IntrazonalVMT at TAZ *share 

of assigned VMT at i 

share of assigned VMT at i = (AB/BA assigned flow)j(sum of the assigned flow 

at each centroid connectors of the TAZ) 

2-9 
T11e calculated intrazonal VMT at each link are then added to the assigned VMT 

of that link. The daily VMT on each link is being calculated by adding the VMTs 

of three time of day periods. 

Calculate HPMS Adjustment Factor 

The model VMT gets adjusted by the HPMS VMT. The HPMS VMTs are 

pmvided by INDOT. The HPMS 

VMTs are available by counties 

and by HPMS functional classes. 

The air quality module sets the 

HPMS adjustment factors for each 

of the network links by using the 

county and the HPMS functional 

class attribute of that link. The 

default value of HPMS 

adjustment factor is 1. HPMS 

adjustment factor is calculated by 

using the following equation: 

avgSpeedBiniD 

2 

3 

4 

5 

6 

HPMS_ADJ_FACT for county c and HPMS functional class h ~ (HPMS VMT 

for c and h)/( sum of model VMT for c and h) 

Calculate Speed Bin 

The air quality module sets the speed for each network link based their 

congested speeds. The congested speed for each link is calculated from the link 

length and the congested travel time. The congested travel time is generated by 

the highway assignment component of the model. The speed varies by time of 

day periods and by the direction of flow. Therefore, speed bin is determined for 

each time of day periods and for each of AB and BA direction. The speed bin for 

each link is being set by using the following criteria identified in Table 2.5. 

Table2.5 Speed Ranges Within Each Speed Bin 

Calculate Running Emissions 

The running emissions are generated from the moving vehicles. The running 

emission is calculated from rate per distance, travel data and the network 

attributes. It uses the following equation to calculate running emission for each 

of the network link: 

Daily running emission by pollutant ~ "LJwuri,HPMS Veh Class (hourly 

adjusted vmt * I,process rateperdistance) 

Where rate per distance depends on speed bins and MOVES road h;pe 

State of Indiana 2-10 
State of Indiana 

In order to facilitate the calculation pwcess, the air quality module creates a 

database titled EMIS_daily.bin. Each record in this file can be identified by 

network link Ids. Table 2.6 describes the fields in the database EMIS_Daily.bin. 

Table2.6 Field Descriptions of the Link Database (EMIS_Daily.bin) 

Table 2.6 

Table2.6 

Field Descriptions 

of the Link Database 

(EMIS_Daily.bin) 

(continued) 

Field Descriptions 

of the Link Database 

(EMIS_Daily.bin) 

(continued) 

The running emission is calculated 

Fields 

i!ll!kltiiiEIIilM'vl'iit_factor TBAl~ 

l'll&_l'.'fi1EIIil~ifit_factor Dlti!tli!Bl1MQ_Mli'FIAI 

L~~~-eVMT +I 

for each of the network links from rate per distance and the adjusted VMT. The 

rate per distance varies with hours of day, MOVES source type, MOVES road 

types, speed bins, emission processes and pollutants. The emission rate is 

calculated for each of the HPMS vehicle type categories. In order to do that, the 

program aggregates the rates by 13 MOVES source types to the rates by 6 HPMS 

vehicle classes be using a weighting factor. The factor is calculated from the 

array variable, MOVES_Frac, as described earlier in Table 2.2. This array stores 

the fraction of VMT by MOVES road type and MOVES source (vehicle) type. As 

a result, the weighting factor varies with MOVES road types and MOVES vehicle 

types. The factor is calculated by using the following equation: 

The weighting factor ~ MOVES_Fmc[road h;pe index4][HPMS vehicle class 

index6][2nd digit of source h;pe]fLMOVES_Frac[road h;pe index4][HPMS 

vehicle class index6] 

For each link of the network, the air quality module looks up the emission rates 

from the array variable, rateperdistance, by using the attributes such as the speed 

bins and road types for each MOVES source (vehicle) type, emission process, 

pollutant and hour of the day. The following flow chart (Figure 2.4) describes 

the process of calculating daily emissions by pollutant by HPMS vehicle classes. 

The air quality module populates three new fields in the network's line layer: 

Daily_NOx_per _mile, Daily_ VOC_per _mile, and DAILY _PM25_per _mile. These 

fields show the running emissions per mile for each link. 

2-11 
Figure 2.4 Process for Calculating Daily Running Emissions 

Loop: MOVES Rd 

Type Index, 1 to 4 

Loop: Speed Bins, 

1 to16 

Loop: Hours, 

1 to24 

If hour= 7,8,9then use AM 

Speed bin, if hours = 

16,17,18then use PM speed 

bins, otherwise use 

MOVES source type= HPMS veh index *10 + 

second digit of source type 

MOVES Total= sum of VMTfrac from MOVES_ 

frac for each HPMS veh type r----~ 

w = number of source types that belong to 

each HPMSveh type 

Get the selection set from 

the table emis_daily.bin 

for MOVE road type and 

speed bin 

hourly VMT for each HPMS veh ype = 

daily adjusted VMT • weighted hourly 

vmt fraction • fraction of VMT by 

HPMS veh class 

Calculate emission by pollutant: 

emission = emission + hourly VMT by HMPS veh 

*Weighted emission by pollutant 

State of Indiana 

MOVES weight = VMT 

fraction for source type/ 

MOVES Total 

Weighted hourly VMT fraction = 

weighted hourly VMTfraction + 

VMT frac from Hourly _trac for 

each HPMS veh type * MOVES 

weight 

2-12 
EmlsslonTvne 

Runni-;;-

Runnin" 

Runni-;;-

RunninP 

Runnin~-

Runni~ 

Runnin" 

Runni-;;-

Running 

Runnin" 

Runnin<> 

Non-runni-;;-;;-

State of Indiana 

Summary Macro 

The air quality module stores the emission summaries in two separate files: 

1. Emission_ by _HPMS_Functinal_ Class_by _County .csv 

2. Emission_by_County.csv 

The first file reports the daily runnmg emissions by HPMS functional class and 

County. The second file reports the daily running emissions by County. Both of 

the files report daily non-running emissions for the region. Sample output is 

illustrated below in Tables 2.7 and 2.8. 

Table 2.7 Emissions by HPMS Functional Class 

HPMS Functional 

lrounru 

Daily NOx for DallyNOxfor 

Class Ozone PM2.5 Dail voc ailvPM2.5-

Rural Interstate Marion 229821 238420 12988 7738 

Rural Interstate Hamilton 800571 830630 46146 27349 

Rural Interstate ohnson 1062221 1102078 60897 36176 

Rural Interstate Hendricks 1123555 1165610 63782 38139 

Rural Interstate Hancock 24519 0 1886 0 

Rural Interstate he~ 1384248 0 78751 0 

Rural Interstate Boone 2494053 0 141698 0 

Rural Interstate M~;an 642205 666237 36355 21690 

Rural Principal 

Arterial Marion 0 0 0 0 

Rural Principal 

Arterial Hamilton 1082530 1099509 119769 38927 

Rural Principal 

Arterial ohnson 825039 834039 97108 33886 

-

- - - II Counties 22989168 19350230 20697327 237064 

Table 2.8 Emissions by County 

EmlsslonTvne Countv Dailv NOx for Ozone Dal\vNOxforPM-2.5 , oanvvot .· ........... DailvPM2.s 

Runnine: Marion 28055166 28388483 3904938 1231216 

Runnin" Hamilton 7361642 7416047 1047001 322120 

Runnin" Johnson 4054185 4106645 490529 163288 

Runnina Hendricks 4548314 4597461 572896 185621 

Runnina Hancock 2571251 0 318755 0 

Runnina 5helbv 2682064 0 245505 0 

Runnina Boone 4120728 0 357362 0 

Runnina Mor.aan 2694182 2724933 310788 106299 

Runnin" AilS Counties 56087532 47233569 7247774 2008543 

Non-runntn.a- All Counties 22989168 19350230 20697327 237064 

Appendix A mcludes a user's guide on how to run the air quality module with 

the Indianapolis MPO TDM. 

2-13 
A. Appendix: User's Guide to 

Running TDM Air Quality 

Module 

Running air quality module from the Model 

Interface: 

Step 1: 

Open the model interface, select the scenario and click on the setup button to 

open the scenario manager window. 

my; &J.SJ.t ttA~-· .......__ __ 

• 

Scenarios 

lrtl 

2035AQ 

No Project 1 nonTOD •• - • • 0 0 ---

p, Stop alter stage ~....----------. 

r. Dry Run _ ___.=· ==Se=tu::p =~ 

=~~ Trip Generation .. 1 

II, ~ Trip Distribution 1 (ill Preassignment ~1 

rJ'J ~ Build Transit Net 1 

~ 1!1 6i) Mode Choice 1 

EI9R Assignment 1 Quit I y 20100419 

State of Indiana 14 
Step 2: 

In the model scenario manager win dow, select "Assignment" from the list and 

click on the Input Files tab. Click on the button "Change File" to select file from 

the file browser window. All the files in the list must be available to the user. 

=!lr§lii~ BIIr!I=~I~BI,I! .81 ·I 

~~ Scenatio 1 Foldel 1 Dote ~ Steps 

. ·-,,.. ""': !"'~'""'""~"" "'f'" ~"' T~Gene1ation ::!J 

I Base YoadRTIP 2035 C:llndyTC5<3\DEIS NoB<M pln Co Too Dec 09 20" ;o ~~Diwwion :' ,;:' outignment l :;~~ . ' ~~~~~~7~ ---- ~~~~~~ ~llldT1anslNel ·:_..:! .. '-todo Choice d I Kfitijf o!\lflo'i\20is::Ao\- -- ri.Ooec 2820' 

! 1f'tXAn r~~------ -y:;::-- :::~'iii= J' .:.J ~, Scen~ios I~ F ... l 0~ nul PotMlOie<sl 

i N..,. I Path I Stotu. I Doset"""' I 

lllli.TJMMUWIM q:M'vatepecchlance_Oz..cJv Mfu i1g Em~ton rete J>ef cldance fOf Ozone 

'I MOVES_Iatepe~cillance_PM qu\totope~ci tanco_PM.csv M~oi>g EIMsion late pe1 ~loncof01 PM2.5 

MOVES _latepetVetocio_Oz qu\totepetvetoclo_Oz.csv M~ilo EtNosion ; 1110 pt1 vol1clo 101 Ozone 

I MOVES_IIIepelvotocio_PM irl><A\tatepeovehiclo_PM.csv M;,.;,g EtNosion 1alo pol votoclo 101 PM2.5 : I MOVES_Ial-ptofle qu\tal-prolilo.csv Mitoi>g EtNosion 1alo pe1 ptolle 

ve/uloPUoliorLPM25_nonaU qu\v~!iCo<riy.cs• M~ ilg VetOcle popUotion n PM2.5 ,.,.oil air 

vetu>oP<latiOf\.O~;_nOf>aUai irl><A\vet0cle~9Comty.cs• Missilg VetOcle popUotion n Ozone ,.,.altair : I VMT~we qu\VMTbyvoiW:Iolype.ctv Miuilg VMT ltedicn by MOVES vehiclo \)'pot 

' HPMS_Fraclioo\.INStatewido irlU\HPMS_F1ac6orUNStotewido.c Mitmg VMT f1edicn by HPMSvohiclo l,ypes o 

I Hoo.r~-VMT_IIoction qu\Hoo.r_fraclioo\.deld.csv M~;,g H~VMT flection by HPMS clau 

I 

HPMS_VMT_B....., irl><A\HPMS_ VMT _Boono.csv Mistilg T otaiVMT by HPMS class n Boone 

i HPMS_VMT_H ... on irl><A\HPMS_VMT_Hdonctv Mitsilg T otaiVMT by HPMS class n Ho_.on 

HPMS_VMT_Honcock qu\HPMS_ VMT_Hancock.csv M~ T otaiVMT by HPMS class n Honcocl 

HPMS_VMT_Hondoicks irl><A\HPMS_ VMT _Hondoickt.csv M~;,g T otaiVMT by HPMS class n Hondo 

! HPMS_VMT_Jolnson irl><A\HPMS_VMT_Jomsoncsv Mitlilo TotaiVMT byHPMS class i>Jolnson 

HPMS_VMT_Mocison qu\HPMS_ VMT _Mocisoncsv Mitoi>g T otaiVMT by HPMS clau n Mocison 

·I HPMS_VMT_M.,ion i>p.A\HPMS_ VMT_Marion.csv M~ilg TotaiVMT byHPMS clau n MOiion 

HPMS_ VMT_t-401gan irlU\HPMS_VMT_MOigancsv M~ T otaiVMT by HPMS class n M01gan 

HPMS_VMT_ShoiJy irl><A\HPMS_ VMT _Shelly.csv M~ilg T otaiVMT by HPMS class n Shelly 

.,1 

' 

Chango no I Chango Foldel I Open I i! OK I ' Cancel I 

Step 3: 

The air quality module script includes the code to calculate HPMS adjustment 

factors based on HPMS_ VMT_ *.csv. Currently, this block of code is commented 

out in the script since the Indianapolis MPO currently does not use HPMS 

adjustment factors based on previous interagency consultation. Since the model 

table will look for these files, the user needs to create a dummy set of csv files 

(HPMS_ VMT_*.csv) for each of the counties in the following format: 

State of Indiana 15 
n; 

fll 

~I 

HPMS CLASS HPMS VMT DEFINITION 

1 372202 Rural Principal Arterial Interstate 

2 18942 Ru ral Principal Arterial Other 

6 82512 Rural Minor Arterial 

9 0 Rural Local 

11 646109 Urban Principal Arterial Interstate 

12 0 Urban Principal Arterial Other Freeway 

14 34486 Urban Principal Arterial Other 

16 549584 Urban Minor Arterial 

19 324050 Urban Local 

Step 4: 

In the Parameters tab of the scenario manager, set the parameter to 

"MOVES_ANALYSIS_YEAR" and then click the button "ok." 

". i!!l 

Scenorio 1 Foldof !Dolo I ;j Stope 

,_,~.,, ... ~ ... '"'"''"'.~""'"'"""~"I Tri>G.,..tlion .!.I Tr1>0isbbAion e.,, Y<MIRTIP 2035 C:\l,q,TC!ir3\0EIS NoBI.id plJt Co Tt.. Doc 09 20" rreaso9vnent B01oYtlll 0:\INDY\BueYHI\--··· friDec 0201~ ~ojd rwiNel ,, 2015AQ G:\INOYTCl0\2015>\Q\ TuoOec 28 20" .....J koc~o Choice 

liltU D:\INOY\2025_,AQ\ T uo Doc 28 ro:~ ?n.,..An ft"'.\'1n')II;An\ T,..,.I\ ...... "'I"W'r G:J .=.] 

Scenarios lt..,u Fies l O<Apo.t ne.s p.,emetett) 

N1m0 !Vabo Otsai>tion 

l01o_end 1200 Mtx f"naltssigvnelt lettlions 

lirill'l111!1111111• 2025 Alr~~~l'NI 

AO_I~folde< 

-I ~ - -- I..,U foldof l01 .0 qJOily ~sis 

AQ_OIApU._fcldet - OIApul folder 101 .0 q>08y ~sis 

-

'i 

:i 

OK I c..col I 

State of Indiana 16 
Step 5: 

In the model user interface, click on the button Eif9 l next to the button " Assignment." Check the 

option "Air Quality Model" and click the button "ok. " Then click on the button "Assignment. " 

Stage Step Settings : · 

Run Macro 

D Final Highwa.Y Assignment 

D 

D 

State of Indiana 

OK Cancel 

17 

AppendixB 

Central Indiana 

Interagency Consultation Group 

Meeting Minutes/Summary 
This page left intentionally blank 
Interagency Consultation Group (ICG) Conference Call Minutes 

For the MOBILE6.2 to MOVES MVEB Replacement Update 

Related to the Indianapolis, Indiana Maintenance Area under the 1997 8-Hour Ozone 

Standard 

ICG Conference Call Date and Time 

• January 18,2012 at lpm Eastern 

ICG Attendees 

• Shawn Seals (IDEM), Gale Ferris (IDEM), Patricia Morris (EPA), Steve Smith 

(INDOT), Laurence Brown (INDOT), LatTy Heil (FHWA), Stephanie Belch (Indy 

MPO), Catherine Schoenherr (Indy MPO), Philip Roth (Indy MPO), Steve 

Cum1ingham (Indy MPO) and Vince Bernardin (BLA) 

ICG Discussion Topics and Conclusions 

I. The question of whether or not non-rulliling emissions should be included in 

MVEBs as we move forward was raised. 

A. It was determined by consensus of the ICG that both running and non-running 

emissions were appropriate for inclusion in the MVEBs. 

B. A revised ICG discussion spreadsheet was subsequently developed to include 

an additional line of totals with both running and non-running emissions that 

are included as the baseline for the mobile source margins of safety and the all 

source margin of safety discussions. 

2. The question of using one allilual run, or four seasonal runs was raised. 

A. After discussion of the I CG, the consensus was the one allilualtun was 

reasonable and appropriate for MOVES runs. 

3. For the PM2.5 MVEB Replacement submittal, various mobile source margins of 

safety were discussed. 

A. The originally submitted PM2.5 SIP submittal included a 22% mobile source 

margin of safety that was inflated for the purpose of accommodating the 

uncertainties of the transition from 2004 to 2009 Indiana vehicle fleet mix. 

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

PM2.5 and NOx mobile source margin of safety did not result in an 

exceedance of the all sources margin of safety, it was reasonable and 

appropriate for inclusion in MVEB Replacement submittal. The subsequent 

spreadsheet mentioned above demonstrated that a 15% mobile source margin 

of safety falls well below the all sources margin of safety and, as such, will be 

reflected in the PM2.5 MVEB Replacement submittal. 

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

safety were discussed. 

B-1 
A. The originally submitted Ozone SIP submittal included a 12% mobile source 

margin of safety for VOC, with a 10% margin of safety for NOx. 

B. After discussion, the consensus of the ICG was that as long as the existing 

12% for VOC and 10% for NOx mobile source margins of safety do not result 

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

appropriate for inclusion in MVEB Replacement submittal. The attached 

spreadsheet demonstrates that a 12% for VOC and 10% for NOx mobile 

source margins of safety fall well below the all sources margins of safety and, 

as such, will be reflected in the Ozone MVEB Replacement submittal. 

C. After further study, Indy MPO requested additional time to conduct a 2035 

MOVES-based emissions projection to confirm that the recommended mobile 

source margins of safety for the Ozone SIP submittal will be adequate farther 

into the future. After the 2035 projection was complete, it was confirmed that 

the recommended mobile source margins of safety for the submittal would be 

adequate. 

B-2