### IDEM INDIANA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT We Protect Hoosiers and Our Environment. Michael R. Pence Governor

Thomas W. Easterly Commissioner



### Ms. Susan Hedman Regional Administrator U.S. Environmental Protection Agency Region 5 77 West Jackson Boulevard Chicago, IL 60604-3950
Dear Ms. Hedman: May 14, 2013 100 North Senate Avenue Indianapolis, Indiana 46204 (317) 232-8603 Toll Free (800) 451-6027 www.idem.IN.gov



### Re: Request to Parallel Process the Draft MOBILE6.2 to MOVES MVEB Replacement Update to the Maintenance Plan for the 1997 Annual Fine Particles Standard for the Southwestern Indiana 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 to the maintenance plan for the annual fine particles standard for the Southwestern Indiana Area, which includes Dubois, Vanderburgh, and Warrick counties, Montgomery Township in Gibson County, Ohio Township in Spencer County , and Washington Township in Pike County. The United States Environmental Protection Agency (U.S. EPA) approved the Request for Redesignation and Maintenance Plan Under the Annual National Ambient Air Quality Standard for Fine Particles, for the Southwestern Indiana Area, submitted by IDEM on April 8, 2011, with an effective date of October 27 , 2011. IDEM requests that U.S. EPA parallel process this draft MVEB replacement submittal for approval into Indiana's State Implementation Plan.
IDEM is providing an opportunity for a public hearing on the MVEB replacement update to the maintenance plan for the annual fine particles standard for the Southwestern Indiana Area, if a public hearing request is received by June 12, 2013. A hearing has been scheduled for June 20, 2013

. If a request for a public hearing is not received by June 12, 2013, the hearing will be cancelled. IDEM is providing a 30 day comment period on this update, with the public comment period ending on June 21, 2013. The final submittal of the MVEB update for the maintenance plan for the annual fine particles standard for the Southwestern Indiana Area will document the public review process, including a detailed summary of and response to substantive comments.

RecycledPaper 

## ® An Equal Opportunity Employer Ple ase R ecy cl

e 

### O

### Ms. Hedman Page 2
This MOBILE6.2 to MOVES MVEB replacement update incorporates onroad emission estimates and revised MVEBs using U.S. EPA's recently adopted MOVES model. The on road emission estimates were calculated using the MOVES-based emission factors and data extracted from the Southwestern 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 particles standard maintenance plan.
Onroad safety margins, established through the interagency consultation process, are included for nitrogen oxides (NOx) and fine particles (PMz.s). These onroad safety margins are allocated to on road 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 Southwestern Indiana Area annual fine particles standard maintenance area will continue to remain well below the overall safety margins for all sources. MVEBs are also constrained to ensure that total NOx and PMz.s emissions (i.e., all source categories) do not exceed attainment year emissions to ensure continued maintenance of the annual fine particles standard. Although there is a increase in direct PM2.5 emissions in the Southwestern Indiana Area, this increase is outweighed by the significant regional reductions in NOx and S02 

### that have occurred and will continue to occur in the future.
This submittal consists of one (1) hard copy of the required documentation. An electronic version of the submittal in PDF format, that is identical to the hard copy, has been sent to Pamela Blakley, Chief of U.S. EPA Region 5's Control Strategies Section.

IDEM respectfully requests that U.S. EPA proceed with preliminary review of the MOBILE6.2 to MOVES MVEB replacement update and revised transportation conformity budgets and approval into Indiana's State Implementation Plan for the Southwestern Indiana maintenance area under the annual fine particles standard. If you have any questions or need additional information, please contact Scott Deloney, Chief, Air Programs Branch, at (317) 233-5694.

KB/sad/sms
Enclosures: Sincerely, 

# y
. '') 1\_.v.J:l._ 

# bMj"' Keith Baugues Assistant Commissioner Office of Air Quality

Request for Redesignation and Maintenance Plan Under the Annual National Ambient Air Quality Standard for Fine Particles, for the Southwestern Indiana Area, and Appendices.

### Ms. Hedman Page 3
Electronic MOVES-based modeling input and output data files.

cc: John Mooney, U.S. EPA Region 5 (no enclosures) Doug Aburano, U.S. EPA Region 5 (w/ enclosures) Steve Rosenthal, U.S. EPA Region 5 (no enclosures) Pam Blakley, U.S. EPA Region 5 (no enclosures) Anthony Maietta, U.S. EPA Region 5 (no enclosures) Seyed Shokouhzadeh, EMPO (w/ enclosures) Keith Baugues, IDEM 

### (no enclosures) Scott Deloney, IDEM (no enclosures) Shawn Seals, IDEM (w/ enclosures)

### LEGAL NOTICE OF PUBLIC HEARING

Motor Vehicle Emission Budgets Replacement Update to the Maintenance Plans for the 1997 Annual Fine Particles Standard for the Southwestern Indiana Area

Notice is hereby given under 40 CPR 51.102 that the Indiana Department of Environmental Management (IDEM) is accepting written comment and providing an opportunity for public hearing regarding the Motor Vehicle Emission Budget (MVEB) replacement update to the maintenance plan for the 1997 annual fine particles standard for Dubois, Vanderburgh, and Warrick counties, Montgomery Township in Gibson County, Ohio Township in Spencer County, and Washington Township in Pike County (herein referred to as the "Southwestern Indiana Area"). Onroad emissions for the original submittal were calculated using the United States Environmental Protection Agency's (U.S. EPA's) MOBILE6.2 mobile model and are now being replaced with U.S. EPA's recently adopted Motor Vehicle Emissions Simulator (MOVES) mobile model. All interested persons are invited and will be.given reasonable oppotiunity to express their views concerning the submittal ofthe proposed MVEB replacement update to the maintenance plan for the 1997 annual fine pmticles standard for the Southwestern Indiana Area.

The purpose ofthis notice is to solicit public comment on Indiana's proposed MVEB replacement update. The Southwestern Indiana Area was designated as nonattainment for the 1997 annual fine pmiicles standard and is subject to the requirements of Section 172 ofthe Clean Air Act (CAA). One ofthe compliance requirements mandated by Section 175A(b) ofthe CAA, is the development ofa plan demonstrating that maintenance areas will continue to meet the 1997 annual fine pmiicles standmd for the next ten years, which includes MVEBs for omoad sources, beyond the cmTent maintenance period. This submittal ofthe proposed MVEB replacement update to the Request for Redesignation andMaintenance Plan Under the Annual National AmbientAir Quality Standard for Fine Particles for the Southwestern Indiana Area was originally submitted on April 8, 2011is being drafted and submitted consistent with U.S. EPA guidance. Upon completion ofthis public notice process, the MOBILE6.2-based to MOVES-based MVEB replacement update will be submitted to U.S. EPA for approval into the State Implementation Plan. Copies ofthe draft documents will be available on or before May 22, 2013, to any person upon request and at the following locations:

• Indiana Depmiment ofEnvironmental Management, Office ofAir Quality,

Indiana Government Center Nmih, 100 Nmih Senate Avenue, Room Nl003, Indianapolis, Indiana.

• Indiana Department ofEnvironmental Management, Southwest Regional Office, 1120 Nmih Vincennes Avenue, Petersburg, Indiana.

I

### • Evansville Vanderburgh Public Library, Central Branch, 200 SE Martin Luther King Jr. Boulevard, Evansville, Indiana.

• Boonville-Warrick County Public Library, 61 1 West Main Street, Boonville,

Indiana.

• Jasper Public Library, 1116 Main Street, Jasper, Indiana.

• Pike County Public Library, 1104 Main Street, Petersburg, Indiana.

• Spencer County Public Library, 210 Walnut Street, Rockport, Indiana.

The draft documents will also be available on the following web page: http://www
.in

.gov/idem /5474.htm
An 

### electronic version ofall MOVES mobile model input and output files will be
available at the public hear ing, ifheld, or upon request. Any person may submit written conunents on the MVEB replacement update to the maintenance plan for the 1997 annual fine particles standard for the Southwestern Indiana Area on or before June 21, 2013. Written comments should be directed to Mr. Shawn Seals, Mail Code 61-50, Office ofAir Quality, Indiana Department of Environmental Management, 100 Nmth Senate Avenue, Indianapolis, Indiana 46204; or fax (317) 233

-5967; or email at SSeals @ idem.in.gov

. Interested parties may also present oral or written comments at the public hearing, ifheld

. Oral statements will be heard, but for the accuracy ofthe record, statements should be submitted in writing. Written statements may be submitted to the attendant designated to receive written comments at the public hearing.

A public hearing on the MVEB replacement update to the maintenance plan for the 1997 annual fine pmticles standard for the Southwestern Indiana Area will be held if
a public hearing request is received by June 12, 2013. A hearing has been scheduled for June 20, 2013. The meeting will convene at 6:00p.m. (local time) at the Evansville Vanderburgh Public Library, Central Branch, 200 SE Martin Luther King Jr. Boulevard, Evansville, Indiana, 47713. Ifa request for a public hearing is not received by June 12, 2013, the hearing will be cancelled. Interested parties can check the online IDEM calendar at http://www.in

.gov/idem /5 390.htm or contact Mr. Shawn Seals at (317) 233- 0425, after June 12, 2013, to see ifthe hearing has been cancelled or will convene.
A transcript ofthe hearing and all written submissions provided at the public hearing shall be open to public inspection at IDEM and copies may be made available to any person upon payment ofreproduction costs. Any person heard or represented at the hearing or requesting notice shall be given written notice ofactions resulting from the hearing. ·

2

### For additional information contact Mr. Shawn Seals, at the Indiana Department of Environmental Management, Office ofAir Quality, Room N1001, Indiana Govemment Center North, 100 North Senate Avenue, Indianapolis, IN 46204 or call (317) 233-0425
or (800) 451-6027 ext. 3-0425 (in Indiana). 

## ************************************************************************ Individuals requiring reasonable accommodationsforparticipation in this hearing, 

## if held, should contact the IDEMAmericans with DisabilitiesAct (ADA) coordinator at:
Attn: ADA Coordinator Indiana Department ofEnvironmental Management- Mail Code 50-1 0 100 North Senate Avenue Indianapolis, IN 46204-2251



### Or call (3I7) 233-1785 (voice) or (317) 232-6565 (TDD). Pleaseprovide a minimum of 72 hours nofification.

3

# DRAFT Onroad Emissions MOBILE6.2 to

MOVES Replacement Submittal

For 

# the

# Sdtlth;~~~**~=~~~ha :;:,;~ji;:~;A** **<~** :;:::

..**~;~:;~~~::::::.** . ·\:.:.::.:;:;:;:;,, 

# Maintenance**~r~a;und~r.** 

# the 1997

May 2013

### This page intentionally left blank

### Introduction



### On April 8, 2011, the Indiana Department ofEnvironmental Management (IDEM) submitted a 

### Requestfor Redesignation andMaintenance Plan Under the Annual National AmbientAir Quality Standard for Fine Particles, for Dubois, Vanderburgh, and Warrick counties, Montgomery Township in Gibson County, Ohio Township in Spencer County, and Washington Township in Pike County (herein referred to as "Southwestem Indiana" or the "Southwestem Indiana Area"). The United States Environmental Protection Agency (U.S. EPA) subsequently redesignated the Southwestern Indiana Area to attainment for the 1997 annual national ambient air quality standard for fine particles on September 27, 2011 (76 FR 

### 59527) with an**eft~~tive** 

### date ofOctober 27, 2011. Onroad emissions for the April 8, 2011 submittal were calculate&U$1ng MOBILE6.2. U.S. EPA has encouraged mobile source stakeholders to transition to

### tM:!fi~y{Motor Vehicle Emissions Simulator (MOVES) model as expeditiously as**possible.,,,~~liJH9:\:~:JDEM** 

### is providing this MOBILE6.2 to MOVES replacement update to the**pr~yjotfsly subimtt~d**  

### 1997 annual fine particles maintenance plan for the Southwestern Indiana

### maj_nJM~b.ce area

### thaf{il~qrporates MOVES-based onroad emissions. 

## :::t

Emission Inventory



### The tables titled, 2005 Base Year

# Emi~~f&~$I1wentor;,~B~S~~~~::dary**Validat::~~ear** Emissions Inventory, 2015 Projected Emissions,

### 20~QPi'ilj~"J)t~d**Emissiilfi~;!lnd** 2022 Projected Emissions
were included in Appendix E ofthe

### origirtaJRed6~ig"i):(!1ion PetiH\?fi<)nd Maintenance Plan. The consolidated table titled, 

## Tql?)s1J- A,**20d5)~Q08, 2tJ1~;gQ20,** **at(f1~Q22** 

### Southwestern Indiana Maintenance Area,**A114,!j(!Jf]Jp'i5i}~l;z!f** 

### Source:liitto**be.!)~)lsitl~\:~4a** 

### repHicement ofthe existing separate 2005, 2008, 2<)l2j2020, ari\tgp22**tabf&~~<,J,f,[u"fi& patif6i~~(PMzs)**  

### and nitrogen oxides (NOx) included in**Appd'i'(jj~~** 

### as**det~JI~d** 

### above**)'1j~~been** 

### revised to incorporate updated onroad emission estimates for**the"Jg~rs.200~(:."2Q08, 20!5,"'~~:i\O,**  

### and 2022 and results in a different overall Sa"ety .,,,,,,,,,, .,,,., · :·,;::·>:;·;::;:c::;.:;..... •
..· ..·. 11 '<<<-> >>:< ;.· ·::'.<'.' • .".·:.::.·•.**--~~:.·.·,,,','···',.·.,** .•.. ·•• 

### . :·;'··.· •••.·.·.. •.: . --- ,•, --- ,-, '·

-**"/<::.;:;;:~::::;~:;>,·.,** ·>;•.-,-.·



### ,.-::> -.·,**"<;<::~:;:;:~:::::>** 

### ·<1-;i;:;::>. 

# <

# 1~~>

1

### 2005 Base Year Emissions Inventory (MOBILE6.2-based Onroad Emissions)

2005 Southwestern Indiana Area (Tons Per Year)

NO,



### 2 e,l4e.73

### 2008 Secondary Validation Year Emissions Inventory (MOBILE6.2-based Onroad Emissions)

2008 Southwestern Indiana Area (Tons Per Year)

Direct PM2
.5

NO,



### 3

### 2015 Projected Emissions (MOBILE6.2-based Onroad Emissions)

2015 Southwestern Indiana Area (Tons Per Year)

Direct PM 2
.5



### 2015 Southwestern Indiana Area (Tons Per Year)

NO,



### 4

### 2020 Projected Emissions (MOBILE6.2-based Onroad Emissions)

2020 Southwestern Indiana Area (Tons Per Year)

NO,



### 5 2,968.17

### 2022 Projected Emissions (MOBILE6.2-based Onroad Emissions)

2022 Southwestern Indiana Area (Tons Per Year)

IN

NO,



### 6 2,J67.98

### Table 4.1-A 2005, 2008, 2015, 2020, and 2022 Southwestern Indiana Maintenance Area, All Anthropogenic Sources (MOVES-based Onroad Emissions)

(Tons per Day)

Secto•· 2005 PM 2.s 2008PM2.s 2015 PM2.s 2020 PM2

.s 2022PM2 .s Area 37.44 37.22 35.54 34.72 34.05 Nonroad 337.06 275.19 179.91 142.59 111.57

EGU 8,240

.09 11,362.99 12,403.95 12,403.94 11,253.01 Onroad 440.28 360.35 1 73.85 I 12.07 87.35

Point 1,427.40 1,278.38 1,2 18.43 1,2 13.29 1,156.50 Total 10,482.27 13,314

. 13 14,011

.68 13,906.61 12,642.48 Overall Safety NA NA (3,529.42) 

### NA (2,160.2 1) Margin
Sector 2005 NO. 2008 NO. 2015 NOx 2020 NO, 2022 NOx Area 1,624.28 3,648

.59 1,619.59 1,601.05 1,601.97 Nonroad 5,675.84 4 ,580.86 3,107.58 2,553.46 2,010.02

EGU 85,319.54 60,278.80 51,931.67 51,931.55 45 ,862.13 Onroad 12,3 36.7 1 10,107.77 4,906.91 3,372

.83 2,759.20 Point 773.96 760.57 735.15 724.68 710.78 Total 105,730

.33 79,376.59 62,300.90 60,183.57 52,944.10 Overall Safety 

### NA NA 43,429.43 

### NA 52,786.23 Marg in**~.** 

## . .. 

### ··..

### ·.····.· ··········**~.· .·;-;•,•,•,•,**  

### .......,•.•,•,•;•.•.

### ~{::::;:;::::···**'':<:~~~::~. '<{f::** **:.:t~[;~~W'' '···=:::::~;~l~tl:** **:: ·**  Onroad emission**estim~ites** 

### in Table:i4 .1

- A**·~f ~·** **aa 1cul** **ated** 

### using U.S

. EPA' s MOVES modelproduced emissi?n

## fac**tbf ;;** **~9f ?~** **~% ~~~c** **te~ fr** **8~ tp** **e** area's

## tr**vel-?e~and** m?del: The Mo-yEs

### I:JS:?:$~**:?W .B!.~ments** **:: ~(.** **gm P,oa~W** **r:A~ fere~** **~R proach**  to emtsst?ns. estlmatwn

### th~n.the**prevwu .:** **®9:del '(1\ifQ..~~~** **E6.2 J.)** **hmmary ~.se** **.9ftij~ :·** **MOVES** 

### model mdtcates that ermsswn

### estimat**mi ~**  be consfd'6n ibly dif.t H ent than

### fffiii~i~**.· c~lculations**  using MOBILE6.2, which was**-~~~:::~:::::..** • • •

..**~·:·:::·:::•.. '~**  ;...;:;.. ..,. •' 0 0 

### used to · cte.a te the ongmal: MYEBs fdi".the Southwestern Indiana 1997 annual fine particles

## nonattai**nili= ~~k** **~u·ea .**  A

## gen**~% umn** **;~ 0£the**  MOVES methodology used in this area can be found in

### Ap**~~ a~** **t?5 .**  A. In

### add**ft~ ~r~**  MOVEs ·· input and output files are being provided electronically

## 'H~**tNs submitt~J** **{W ;p** **rowth** and control strategy assumptions for non-mobile
sources (i.e. area,**if(j~ ~~?:** **d, elec.** **~#,ip generating**  

### units, and point) from the original submittal for the years 2005, 2008,

## · 2:

0

:1::§.,**202 m;** **md** 

### 2022 were developed before the economic challenges of the last several years.

### ~tan~~**!(f.f** this, the factors included in the original submittal may project ·.·.·······y' 

### more growth than will actuaiTy occur in the future. As a result, the growth and control strategy assumptions for the non-mobile sources for the years 2005, 2008 , 2015, 2020, and 2022 continue to be valid and do not affect the overall conclusions ofthe plan.

Omoad safety margins have been included for onroad emission estimates to accommodate the wide array ofassumptions 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 ofrefined assumptions in the process. The plan continues to meet all applicable Clean Air Act (CAA) r equirements as the revised emission inventories clearly illustrate that total PM2
.5



### 7

### and NOxemissions in the Southwestern Indiana 1997 annual fine patiicles maintenance area will continue to decline leading to local reductions between 2005 (base year) and 2015 (maintenance plan interim budget year) and 2005 (base year) and 2022 (maintenance plan horizon budget year)

. Although there is an increase in direct PM2 .s 

### emissions in the Southwestern Indiana Area, this increase is outweighed by the significant regional reductions in NOx and S02that have occurred and will continue to occur in the future. Transportation Conformity Budgets

Table 5.1 was included on Page 28 ofthe original Redesignation) ?etition and Maintenance Plan for the Southwestern Indiana, 1997 annual fine particles

## maiq**~i)2\** m·ea
. Table 5.1 -A (to be considered a replacement ofTable 5.1) has been revised**to J.~£.9~J>** **orate** 

### U.S. EPA's MOVES model-produced emission factors and data extracted froutJhf 1 : egis m's travel-demand model.
Ta

# J~**i~ ~:-:v··** **·:.::;~::[it[[~~;····--::**..

Direct PM2.s

(tons/year) NOx (tons/year)



### ········ ;.**··;~::(;;:**••• < 

### PM2.s 

## ··.. (tons/year) NOx (tons/ year) Emission Estimations for**Oiii O'ad**  

### Mobile Sources for the**(;:•:·:·;·;·:..:-~** '•:· 

### ·. •. 

### Southweste r"

[f

j lndiana Area**·. ,\.::::~::** 

### ..

## (MOBILE6**base~ fQ~r** **!:lad ~mJ** **ions) ··** **:.::~:~ls::::**

## ..

·:·!· • •**·:::!;~~~~ ~~j::** !:.,**,.:::~mj ~:~:** **~~;::::..** 

### . · ..**::~~;: ~::** **::~:·.** 

### 2005 2022
117.67

1,699.86

,..,.,,., ··:·:·:·:·:·... 

### 2005

## '\~f

# \**2'0 ::::.**  2015 2020 2022
440.28 360.35 173

.85 112

.07 87.35

12,336 .71 10, 107. 77 4,906 .9 1 3,372.83 2,759.20

• •>**~**.• 

### Table 5

.2 was also included on Page 28 ofthe original Redesignation Petition and Maintenance Plan for the Southwestern Indiana Area

. Table 5.2

- A (to be considered a replacement ofTable 5

.2) has been revised to incorporate MVEBs calculated using U.S. EPA' s MOVES modelproduced emission factors and data extracted from the region' s travel-demand model as detailed in Table 5

. 1 -A.

8

### Table 5.2 Mobile Vehicle Emission Budgets (MOBILE6.2-based Onroad Emissions)

2015 2022 PM2.s (tons/year)**~ ~**  

### NOx (tons/year)**:6,6:68.~~** 

### 1,869.84



### Table 5.2

- A**/)~.** 

### Motor Vehicle Emission**Budget ·.** **:f91 ·**  

### the Southwestern**Indiana "'** **:i tre~** **··** 

### (MOVES-based

### Onroa**lEMi sirin~)**  ,.·:·.:-_·· .:::·· ··:··:::··:"::



### .. ao'Oo:o•, ·.· 

### ·. 

## ·. 

# .;:-: ioi:s-

. ·.,.;/ 

## 2022:
.. ··:· 

### ··. PM2.s (tons/year) 199

.93 100.45 NOx (tons/year) 5,642.95 3,173.08 

## :t:

... Through the interagency

# consultation**\; ·.o** **6~s~ ,** **~~** was

# ~~**~i~~r.~; ··** **that** a main

# ten**·**plan interim budget year of2015, and a horizon**budg~ .i'.** **ea{ ~022,**  

### wol.11a} Q

. Yappropriate. The interagency consultation group approved onroad margins

### of**at~ tY.** **o[fifte ai** **:: P.** **ent** (15%) for both PM2.s and

. :..

. 

## . ... 

## .. .... ·. 

### ·. ,••, 

### ·.·.··.·.····

NOx onroad emission**esti~at~s fqr**  

### the yeat \ 2

. 015 arid.202g

.. A**:i'tmn ~ry**  

### of this interagency
consultation

### discussiory**:: f>** **fo ~{il~_in** **App 11,di~**  B

.

### .T**l}~ s~** **vi s~** **d**l ltission inventories clearly**illu~trate** 

### tha.t omoad**P-¥ ·~** **. a~d** **No ·.** **rpi sions** **th~**

### ..**uthwest((iil Indi** **~a** 

### 1997 annual fine parttcles mamtenance area
.:Will contmue to declme ; leadmg to local reductions between 2005 (base year) and 2015 (maintena £ eplan interim budget

## i·), as well as between 2005 (base year) and 2022

## (maintyv.**anc~ ::** **J>.I.aQ; hori** **on** q: udget year)

. . ':: ·· 

## .;:;:}?{>·::;;.:.**···:-.:::;:::;:~t?~:\..** 

# ''<.. ·,·•.

. · .....; :·

..\·.:)**Furtherri1 ;**  

### when**comp l:i** **(.l,:to** 

### th e ·o.verall safet{ rnargin as defined in the Code ofFederal**~~h ~~y-** **~.** 

### Regulatim1 s':;(Q f.R) at 40 CFR;2}. 1 01 ,' it )s evident the onroad safety margin allocation is reasonable andJ P.P.ropriate.**Mo ::** **~pecificfilJy,** 

### even with the allocation of an onroad safety margin to mobile

### sourc**e~ ·/** **missions wil** **@~ .ptinue**  

# t6 remain well below the overall safety margin for all
sources as**detailed .'** **tl:: ~ble**  

### 4.1

- !,:)tMVEBs are constrained to ensure that the total emissions

·.·.··········**;•.·.·.·,·~** 

### (i.e. , all source**categ6N****~*-)A****o n~** **tM ceed**  

### the 2005 attainment year emissions ofeither PM2.s or NOx, thereby ensuring**c6 h!** **~.BH ~~Qji~** **intenance** 

### ofthe 1997 annual fine particles standard. As stated previously, although there**ii ~D'** **increase** 

### in direct PM2.5 

### emissions in the Southwestern Indiana Area, this increase is outweigli

. ed by 

### the significant regional reductions in NOx

### and S02 

### that have occurred and will continue to occur in the future.


### Conclusion

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

### Request for Red e

signation andMaintenance Plan Under the AnnualNational AmbientAir Quality Standard for Fine Particles for the Southwestern Indiana Area incorporates omoad emission estimat es and a revi sed MVEB using U.S. EPA's recently adopted MOVES model. MVEBs have been revised in

9

### anticipation ofthe mandatory use ofthe 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 NO" established through the interagency consultation process, are included in order to account for the wide array ofassumptions that are factored into the calculation process. MVEBs are also constrained to ensure that total PM2
.5 

### and NOx emissions (i.e., all source categories) do not exceed attainment year (2005) emissions to ensure continued maintenance ofthe 1997 annual fine particles standard, even considering the increase in direct PM2.5 emissions that will be otiset by current and future regional and national reductions. With the addition ofMOVES-based onroad safety margins applied to mobile sources, the Southwestem Indi<),l)l;l,annual fine particles maintenance area will continue to remain well below the**overaJ@~fety** 

### margins for all sources into the future. As such, the 1997 annual fine particles

### mainten,'!Jj'\f~j.[if~n for the Southwestern Indiana Area continues to meet all applicable CAA**requirement~(:::::::?:::::,:,:,:,:-:**



### 10

# Appendix A

Southwestern Indiana Area MOVES Methodology

### This page left intentionally blank

# Vanderburgh and Warrick Counties MOVES2010a Input Data and Parameters

INDOT Planning Contract



# Final Report October 4, 2012



# CDMth Sm1Table of Contents Overview

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

....................................................................................................... 1 Vehicle Population

................................................................................................................ 2 Meteorological Data

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

..................................................................................................... 4 Default Hourly Distributions

.................................................................................................. 5 Default Daily and Monthly Distributions

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

.................................................................................................................... 6

LIST OF TABLES

Table 1: MOVES2010a Source Type Codes

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

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

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

....................................................................... 5

LIST OF APPENDICES
Appendix A- MOVES2010a Input Settings and Assumptions Appendix B- Vehicle Age Distributions for Vanderburgh and Warrick Counties Appendix C- Vehicle Populations for Vanderburgh and Warrick Counties Appendix D- Meteorological Data for Vanderburgh and Warrick Counties Appendix E- Default Statewide Factors Appendix F- Statewide Default Hourly Distribution Factors Appendix G- Statewide Default Daily Distribution Factors Appendix H- Statewide Default Monthly Distribution Factors Appendix I

- Ramp FractionsOverview: This report is being written to document the input parameters for a set of MOVES201 Oa runs for the Vanderburgh and Warrick Counties 8-hour Ozone Maintenance Area and the Vanderburgh and Warrick Counties PM 2.5 non-attainment area. This report contains a discussion on the intended input settings used in MOVES201 Oa and the development of the input datasets. These MOVES201 Oa runs are intended to develop a default set of emission rates that can be used for conformity determination and is part of a statewide effort being conducted by the Indiana Department of Transportation (INDOT). Throughout this report references are made to MOVES 201 Oa codes for two types of data. The values for the source type codes are shown in Table 1. The values for the road type codes are shown in Table 2. MOVES2010a input settings and assumptions for this effort are shown in Appendix A.
Table 1: MOVES2010a Source Type Codes sourcetypeid Description 

### 11 Motorcycles 

### 21 Passenger Car 

### 31 Passenger Truck 

### 32 Light Commercial Truck 

### 41 Intercity Bus 

### 42 Transit Bus 

### 43 School Bus 

### 51 Refuse Truck 

### 52 Single Unit Short-haul Truck 

### 53 Single Unit Long-haul Truck 

### 54 Motor Home 

### 61 Combination Short-haul Truck 

### 62 Combination Long-haul Truck
Table 2: MOVES2010a Road Type Codes roadtypeid

Vehicle Age Distribution: 1 2 3 4 5 Description Off Network Rural Restricted Access Rural Unrestricted Access Urban Restricted Access Urban Unrestricted Access

The vehicle age distributions for MOVES source types 21, 31, and 32 (cars, passenger trucks, and light commercial vehicles respectively) were developed through an analysis of Indiana's 2009 vehicle registration data. The analysis was performed by Eastern Research Group (ERG) under contract to the Lake Michigan Air Directors Consortium (LADCO). ERG was provided with vehicle identification numbers (VIN) for vehicles in Indiana.There were approximately 6.37 million VINs in the statewide data set. Out of these, approximately 1.3 million returned errors. Of these, approximately 200,000 errors were deemed non-critical. This means that the model year and vehicle type assigned to the records were most likely correct despite there being an error in the VIN decoding. These records were included in ERG's analysis. The remaining errors were considered critical enough to call into question the accuracy of the model year and vehicle types. These critical errors were excluded from ERG's analysis.
In all, approximately 5.2 million VINs from around the state were used in the analysis. Each VIN was associated to a specific "county. ERG then developed age distributions for each county in the state along with seven combination areas comprised of two or more counties each. Additional information on the methodology used to develop the vehicle age distributions can be found in a May 28, 2010 report written by ERG for LADCO titled MOBILE6 and MOVES Registration Distribution Calculations for Indiana Registration Data. Each set of age distributions was provided in both MOBILE6 and MOVES formats. The MOVES formatted data will be used for these MOVES201 Oa runs.
Due to limitations in ERG's VIN decoder, it was not possible to develop vehicle age distributions for any source types other than 21, 31, and 32 from the vehicle registration data. For all other source types, MOVES201 Oa default vehicle age distributions specific to each source types were used. This includes motorcycles and all heavy vehicles. Vehicle age distributions for all source types were kept constant for all future years. The vehicle age distributions for Vanderburgh and Warrick Counties as a combined area are shown in Appendix B of this report.
Vehicle Population: The vehicle populations for source types 21, 31, and 32 were developed directly from the vehicle registration data. All valid records that were identified from the vehicle registration data set were used to determine the number of vehicles for each of these three source types. The VIN decoded data provided to INDOT contained vehicle types according to MOBILE6.2 vehicle categories. There is a direct correlation between MOVES source type 21 (cars) and the MOBILE6.2 vehicle type LDV. All valid LDV records (those records not excluded from the vehicle age distribution analysis due to errors as was described in the section on Vehicle Age Distribution in this report) were counted in the vehicle population.
There is not a direct correlation between MOVES source types 31 (passenger trucks) and 32 (light commercial vehicles) and the MOBILE6.2 light truck vehicle types (LDT1, LDT2, LDT3, and LOT4). All valid records from the vehicle registration data set for MOBILE6.2 light duty trucks were counted in the vehicle populations. The light duty trucks were distributed between MOVES source types 31 and 32 as per the Environmental Protection Agency's (EPA) guidance documented in Table A.1 of the appendix of the Technical Guidance on the Use of MOVES2010 for Emission lnventorv Preparation in State Implementation Plans and Transportation Conformity. The guidance provides two sets of factors for distributing MOBILE6.2 light trucks between MOVES source types 31 and 32. These are based on fuel type and are shown in Table 3.

2Table 3: Distribution of MOBILES 2 Light Duty Trucks into MOVES Source Types Source Types Fuel 

### 31 32 Gas 78% 22% Diesel 42% 58%
As per ERG's assumption documented in MOBILE6 and MOVES Registration Distribution Calculations for Indiana Registration Data, all light duty trucks that did not have a fuel type identified were counted as diesel trucks. This was to prevent an underestimation of diesel trucks and their related emissions.
Since only valid records from the vehicle registration data were used to calculate vehicle populations for source types 21, 31, and 32, it is reasonable to assume that some of the erroneous records that were discarded from the analysis actually belonged to these source types. The nature of these errors is not that the vehicle does not exist. Rather, it is that the vehicle could not be properly identified with any sense of certainty. It was therefore necessary to adjust the vehicle populations calculated from vehicle registration data to compensate for these discarded records. Based on an analysis of the error rate reported by ERG, vehicle populations for source types 21, 31, and 32 were increased by 5.8 percent.
Vehicle populations were not able to be developed directly from the vehicle registration data for some source types. This was due to the limitations in the VIN decoder used by ERG to process the vehicle registration data. Vehicle populations for all other source types (motorcycles and heavy vehicles) were derived by applying the Mileage Accumulation Rate (MAR) method documented in EPA's Technical Guidance on the Use of MOVES201 0 for Emission Inventory Preparation in State Implementation Plans and Transportation Conformity, Section 3.3 Source Type Population.
The default MARs were extracted from MOVES by running MOVES for a single pollutant and a single year for all vehicles, fuels, months, days, and hours. The activity output was set to report both distance and population. A ratio of population to vehicle-miles-traveled (VMT) was calculated from these outputs. The ratios were calculated for each source type.
The Evansville MPO, which is the metropolitan planning organization (MPO) for Vanderburgh and Warrick Counties, provided VMT by MOVES road types extracted from their travel demand model's base year. Since the default MARs in MOVES vary by year (but not by location), the MOVES run that was executed to extract the MARs was run for a year consistent with the travel demand model's base year. This resulted in MARs that could be applied directly to the validated VMTs reported by the travel demand model. The travel demand model VMTs were converted into annual VMT and distributed by vehicle types using statewide default VMT distribution factors documented in this report in the section on Default VMT Distributions. The MARs were then applied to the annual vehicle type VMTs. The result was an estimated vehicle population for each source type for the travel demand model's base year. Since the vehicle populations for source types 21, 31, and 32 were developed directly from the vehicle registration data, the population

3estimates derived for those source types using the MAR method were discarded and the observed data were used instead.
Future year vehicle populations were developed base on socioeconomic growth rates for the maintenance area. The MPO provided base year and horizon year population and employment data for the area. Annual growth rates were calculated for population growth and employment growth individually. Population growth rates were then used to grow the light vehicle populations (source types 11, 21, 31, and 32). Employment growth rates were used to grow the heavy vehicle populations (source types 41, 42, 43, 51, 52, 53, 54, 61, and 62). Vehicle populations were calculated for every year from 2008 to 2040. These vehicle populations for Vanderburgh and Warrick Counties as a combined area are shown in Appendix C. Meteorological Data: The default set of hourly temperatures and hourly relative humidity was developed using EPA's data converters for changing MOBILE6.2 minimum 

### I maximum temperatures and absolute humidity to the MOVES equivalent formats. The values for the MOBILE6.2 inputs were taken from the Request for Redesignation and Maintenance Plan for Ozone Attainment in the 8-hour Ozone Basic Nonattainment Area, Appendix D, developed by Indiana Department of Environmental Management in June 2, 2005 and the draft Request for Redesiqnation and Maintenance Plan under the Annual National Ambient Air Quality Standard for Fine Particles, Appendix F, developed by the Indiana Department of Environmental Management in January, 2011. Meteorological data reflect average annual conditions for the PM 2.5 runs. The MOBILE6.2 meteorological input data for each of the twelve months of the years were averaged together to create average annual temperatures and humidity. These were then passed through the data converters. The data reflect summer conditions for ozone using MOBILE6.2 inputs for July. The MOVES formatted meteorological data for Vanderburgh and Warrick Counties as a combined area are presented in Appendix D of this report.
Default VMT Distributions: As part of this effort, INDOT developed a default set of VMT distribution factors by Highway Performance Monitoring System (HPMS) vehicle type and by MOVES road type. These distribution factors were developed by analyzing four consecutive years of continuous traffic count data ending in 2010 for twenty permanent traffic count stations throughout Indiana. The stations were selected to provide a spread of locations corresponding to each of the four MOVES road types. Furthermore, these stations were selected from among sites that were concentrated in nonattainment and maintenance areas. In some cases, data from the requested site were either partially or completely unavailable. An inventory of the sites used to develop the distributions is shown in Table 

### 4.
The vehicle counts reported at each station were provided by vehicle class. These were aggregated into the six basic HPMS vehicle types: motorcycle, passenger car, light truck, bus, single-unit heavy truck, and combination heavy truck. The distribution of VMT by vehicle type was calculated for each road type by taking each vehicle type's percentage of total traffic. These default statewide factors are shown in Appendix E.

4Table 4 Inventory of Permanent Count Stations SiteiD City County Location Road Type Data Quality
3000 MUNCIE DELAWARE HAMILTON MARION LAKE LAPORTE SR 332 RM 0.5 3 Closed since 9/26/2006. No data. 3200 CARMEL US 31 RM 125.7 5 Good 3300 INDY WEST 1465 MM 10.0 4 Closed since 9/1/10 4000 GARY I 80 /I 94 MM 6.0 4 Only 2010 data passed QC Good 4500 LAPORTE SR2 RM 65.2 3 5600 6100 SELLERSBURG CLARK EVANSVILLE GIBSON 0105 TERRE HAUTE VIGO 0201 0210 0303 0327 0403 0501 0502 0507 0602 MIDDLEBURY FORT WAYNE MUNCIE DALEVILLE SOUTH BEND INDY SOUTH MARTINSVILLE SEYMOUR HAZLETON ELKHART ALLEN DELAWARE DELAWARE ST. JOSEPH MARION MORGAN JACKSON GIBSON 165 MM 8.0 164 MM 27.9 US 41 RM 104.2 

### 4 2 3 SR 120 RM 13.9 3 1-69 0.53 mi N of 4 SR3 US 35 RM 44.5 5 169MM31.4 2 US 20 RM 77.1 4 SR 37 RM 143.5 5 SR 67 RM 80.6 3 165 MM 47.0 2 SR 56 RM 0.6 3 Bad sensors. Not usable. Good Good-closed 5/13/09 11/13/08-
Good- closed .8/3/10-12/6/10 Good Good Good-built in 12/10/2007 Good Good-closed 5/22/09-6/1/09 Good Good Good 0603 DUBOIS DUBOIS SR 56 RM 53.3 3 

### 5 

### 4 Good- closed 10/16/08- 3/20/09 0608 EVANSVILLE VANDERBURGH SR 66 RM 23.5 Good 1315 I 70 MARION 170 MM 83.5 Closed 5/17/06-3/24/08
Default Hourly Distributions: The same set of twenty permanent traffic count locations discussed in the section on Default VMT Distributions was analyzed to develop a set of hourly distribution factors. These factors were calculated by road type, by HPMS vehicle type. Hourly factors were only calculated for the average weekday. The hourly distribution pattern for each traffic count location was reviewed. Any data that appeared to reflect either an error in the data or an outlier of behavior were removed to prevent bias in the data. The following data were excluded from the analysis:

• Bus data from count stations 0105 and 0603 were excluded due to abnormal midnight peaks in the data; • An abnormal relationship between passenger cars and light duty trucks at count station 4500 prompted the exclusion of all data from this location due to questions of reliability; • Peak spreading behavior observed at count station 4000 from traffic related to Chicago was considered to be too unique to be included in a default statewide data set; and, • Combination truck traffic from station 3200 was excluded due to too much overnight traffic when compared to other vehicles and other stations.

5Furthermore, traffic patterns reported by those count stations corresponding to road type 3 (3000, 4500, 0105, 0201, 0502, 0602, and 0603) had a tendency to over represent long distance travel. This was most likely the result of statewide permanent count stations focusing primarily on higher order facilities. Rural collectors and local streets are less likely to reflect long distance travel. The hourly distributions for road type 3 (rural unrestricted access) were adjusted to better account for traffic behavior on lower order facilities in rural areas. A sample of traffic count data from Morgan County, IN was used to introduce more local traffic behavior in the road type 3 hourly distributions. An analysis of the Morgan County data showed a pattern more consistent with AM and PM peaking characteristics reflecting local commuting traffic on collectors and local streets for passenger cars and light duty trucks. The Morgan County data for passenger cars and light duty trucks on collectors and local streets were weighted and added to the road type 3 data set. This analysis assumed that rural collectors and local streets accounted for 20 percent of all VMT for road type 3.
The statewide default hourly distribution factors are presented in Appendix F.
Default Daily and Monthly Distributions: Default daily and monthly distribution factors were calculated from IN DOT's official count adjustment factors which are more commonly used to develop AADT from raw traffic counts. These factors are based on the set of daily traffic counts collected from all permanent count stations throughout the state. The daily distribution factors determine what percentage of VMT is occurring on weekdays and what percentage is occurring on weekends. The monthly distribution factors determine what percentage of annual VMT is occurring in each month of the year. The statewide default daily distribution factors are shown in Appendix G. The statewide default monthly distribution factors are shown in Appendix H. Ramp Fractions: The ramp fractions represent the percentage of vehicle-hours-traveled (VHT) for road types 2 (rural restricted access) and 4 (urban restricted access) occurring on the ramps associated with those road types. These fractions were calculated based on the percentage of VHT occurring on ramps reported by the base year travel demand model. These ramp fractions are reported in Appendix 

### I.

6Appendix A
Number ofRuns:

Input Item Ozone PM 2

.5 Years 2002,2010 , 2008,2010 , 2015 , 2020, 2015, 2020, 2025 , 2030 , 2022,2030, 2035,2040 2035 , 2040 Pollutants/ Volatile PM 2

.5 with all Processes Organic subspecies ; Compound NOx (VOC) , NOx, and supporting Meteorology Summer Average Annual #of MOVES 8 8 runsGeneral Parameters: MOVES Input Item Screen Ozone PM 2.5 Description Scale

Time Spans

Geographic Bounds Vehicles

Road Type Pollutants/ Processes General Output

Output Emissions Detail Description Domain/Scale Calculation Type Time Aggregation Level Year

Months Days Hours Geographic Bounds Vehicles

Road Type Pollutants/ Processes Database Name Units

Activity

On Road User Choice County Emission Rate Hour Hour

2002, 2010, 2008, 2010, 2015, 2020, 2016, 2020, 2025 , 2030, 2022,2030, 2035, 2040 2035, 2040 July April Weekday Weekday Select All Select All Vanderburgh Vanderburgh County* County*

All Gas and Diesel Combinations

Select All VOC, NOx, and supporting Evansville Ozone PM 2.5 with all subspecies; NOx Evansville PM Select "Grams" and "Miles" and "Million BTU"

Distance, Population

Select "Source Use Type" and "Road Type"

*Re prese nts both Vanderburgh and Warri ck Counties

.

### C t D t M 

# • County Data Excel Sheet Tab Manager Input Name
Ozone PM 2

.5 Source (Vehicle) source Type Year Local Registration for Source Types 21 , 31, and 32; Type Population Estimated population using default MOVES mileage accumulation rates and local VMT for all other source types. Future year vehicle populations based on population growth rates for source types 11, 21 , 31, and 32

. Employment growth used for all other source types.

Vehicle Type HPMSVTypeYear Statewide default vehicle distributions across road types VMT (by 13 developed by INDOT using an analysis of permanent count MOVES Vehicle station data from a statewide data set. Types) MonthVMTFraction Statewide default monthly fractions developed by IN DOT using an analysis of permanent count station data from a statewide data set. DayVMTFraction Statewide default daily fractions developed by IN DOT using an analysis of permanent count station data from a statewide data set. HourVMTFraction Statewide default hourly fractions developed by INDOT using an analysis of permanent count station data from a statewide data set. Average Speed avgSpeed National defaults

. Distribution (% Distribution of VHT in each 5 mph speed bin) Road Type roadType Calculated from local VMT data

. Use travel demand model Distribution Distribution base year distributions for all years

. (VMT by 5 MOVES Road Types) Age Distribution sourceTypeAge Local age distributions developed from vehicle registration (Vehicle Distribution data for source types 21, 31, and 32. Default MOVES age Population by distributions for all other source types

. Age of Vehicle) Ramp Fraction RoadType Based on local travel demand model.

Meteorology ZoneMonthHour MOBILE6 Summer Met Data MOBILE6 12 month Met Data Converted to MOVES format Data Converted to MOVES format and averaged to annual meteorology Fuel(% of FueiFormulation MOVES Defaults Market Share by FueiSupply Vanderburgh County MOVES Vanderburgh County MOVE S Fuel Type) Defaults for Summer (check if Defaults for annual (check if varies among counties) varies among counties) 1/M Program 1MCoverage No ProgramAppendix B
Vehicle Age Distributions for Vanderburgh and Warrick Counties: Source Types aqeid 11 21 31 32 41 42 43 51 52 53 54 61 62 0 0.2109690540 0.0254913494 0,0108613399 0.0283536975 0.0643023355 0.0545743076 0.0622220643 0.0494240790 0.0588526168 0.0787544027 0.0615095870 0.0535634660 0.06'7:0845256 1 0.1921154969 0.0471761977 0.0455523407 0.0691813189 0.0626728412 0.0531913309 0.0606452875 0.0481716155 0.0573612230 0.0767586735 0.0599508636 0.0535634660 0.0670845256 2 0.1573471585 0.0580075242 0.0532532087 0.07143769_42 _Q.0624853859 0.0530322328

. _0.0604638952'"**_q.IJ4~0275345 0.05718965~9**  0.0765290827 0.0597715492 0.0541045093 0.0677621447 3 0.1359771581 0.0527361307 0.0471399955 0.0603686832 0.0624229593 0.0529792497 0.0604034894 0.0479795509 0.0571325186 0.0764526251 0.0597118340 0.0575579884 0.0720873878 4 0.1058454735 0.0539901675 0.07:13109281.**0.07~771.~_2?**... 0,0617369906 0,0523970560 0.0597397140 0.0474523026 0.0565046834 0.07561,24785 0.0590556596 0.0564182312 0.0706599203 5 0.0750909142 0.0553551809 0.0640255212 0.0718634254 0.0559170498 0.0474575929 0.0541080614 0.0429789769 0.0511779950 0.0684845018**0.05348~926** 0.0489290859 0.0612802835 6 0.0476605323 0.0577522:778 'Q_.Q7_26_61_1(66 0.0639022521 0,0468365056 0.0397508_1_23

. 0.0_453212873 0.0359994879. 0.0428670388 0.0573630896 0.0448023279 0.0366034411 0,0458432683 7 0.0331026886 0.06257_'97645 0.0709548186 0.0653071651 0.0425786431 0.0361370941 0.0412011709 0.0327268079 0.0389700355 0.0521482660 0.0407293873 0.0340742206 0.042_67559_59 8

. 0.0197278356 0.0632456247 0.061.6514578_ _0.0567.92541_2_ 0.0468268516 0.0397426124 0.045311936( 0.0359920640

. 0,0428582007 0.0573512681**0.044793098~** 0.0358093100 0,0448486759 9 0.0118473747 0.0721570542 0.0623636768 0.0628379241 0.0534377006 0.0453533365 0.0517089150_ 0.04_10733035 0.0489087688 0.0654479137 0.0511168252 0.0526288382 0.0659139597 10-

--- 0.0053251777, 0,0654096705' 0.0604S44261 0.0567073950 0.0532712252 0.0452120443 0.0515478328 0.0409453420 0.0487564067 0.0652440247 _·0.0509575859 0.0624520143 0.078216804) 11 0.0025378610 0.0559211621 0.0512946064 0.0461492614 0.0407951886 0.0536203440 0.0411075833 0.0313560350 0.0391491717 0.0523881239 0.0302729398 0.0478258601 0.0598985955 12

. 0.0013011470 0.0508939174 0.0480747830 0.(1399335859 0.0:331924560 0.0489936472 0.0382933197 0.0255124310 0.0294483131 0.0394065607 0.0466101866 ,0.0389128550 0.0487354179 13 0.0006124019 0.0430811573 0.0375695526 0.0292051599 0.0277347637 0.0456089741 0.0333751020 0.0545980574 0.0316399801 0.0194774783 0.0291673253 0.0325145854 0.0462990441 14 0.0002476898 o:o433142083**0.036~154388** 0.0285665631 0.0364294706**o.o3m:~·6681** 0.0430863640 0.0632656498 0.0364439725 0.0194691525 0.0347804437

. 0.0427077,4_19 0.0462072388 15 0.0001527705_ 0.0346136346 0.0357444914 0.0309932309 0.0283511969 0.0332950401 0.0210164622 0.0395649332 0.0357887614 0.0311848083 0.0335202065 0.0332372597 0.0300444032 15 0.0000668536 0.0300081013 (1.0257882632 0.0210311210 0.0235884296 0.0279132162 0.0253671498 0.0341566540 0.0259987277 0.0230196849 0,02331_51_075 0.0276536739 0.0230524492 17 0.0000299603 0.0235936477 0.0221233029 0.0179658564 0.0175637044 0.0244970846 0.0206833627 0.0146346390 0.0197956396 0.0052258132 0.0206748599 0.0205906442 0.0138452217 18 0.0000127409 0.0196650723 0.018473_1805 0.0145600068 0.0201192241 0.02504;80695 0.0266888558 0.0401958334 0.0193740288 0.0037212159 0.0155464816 0.0235865809 o._o_1,ooo_664_(5_o :_ 19 0.0000055369 0.0160361340 0.0154017360 0.0115798885 0.0225790392 0.0366610768 0.0301447753 0.0342277190 0.0227335396 0.0175775477 0.0203628520 0.0264703224 0.0098603738 20 0.0000022027 0.0141717254. 0.0150307886 0.0129848014 0.0226407923 '0.0281971934 0.0173882093**0.027008~_845_** 0.0289395633 0.01'83874556 0.0265944575 0,02654271_35

_ o.oo95Z55112d 21 0.0000010015 0.0106315684 0.0149120855 0.0124739240 0.0212965445 0.0224413685 0.0209032932 0.0367430589 0.0255089927 0.0121624816 0.0238465850 0.0249667984 0.0083402541 22 0.0000005320 0. 0082566669 0,0097633356 0,0079611733 0.0221366577 0.0207614938 0.0211741003 0.0294241579 0.0211707159 0.0029207200 0.0232916866 0.0259516972 0.0021970287 23 0.0000002372 0.0061814025 0.0097781735 0.0078334540 0.0187753208 0.0176845935 0.0186862600 0.0367365508 0.0255742899 0.0006595597 0.0173635700 0.0220110680 0.0022815392 24 0.0000001072 0.0051493192 0.0086653313**0.007:961~733** 0.0165801584 0.0153441343 0.0162223474 0.019537_1739 0,0181341022 0.0013228019 0.0186391363**0.019437588~** 0.0028947085 25 0.0000000515 0.0038065010 0.0056235626 0.0052364937 0.0130464803 0.0119613578 0.0125269842 0.0202862884 0.0101534224 0.0013255722 0.0189070434 0.0152949162 0.0014963357 26 0.0000000201 0.0022417295**0.003S43015~** 0.0030226915 0.0052066606 0.01__14707358 0.0046276161 0.0058785937 0.0158244798 0.0000000000 0.0123859$55 0.0061039775 0.0003051544 27 0.0000000084 0.0014426972 0.0025817939 0.0022989484 0.0044375500 0.0062552616 0.0034269422 0.0066192300 0.0082431519 0.0005853113 0.0073123264 0.0052023202 0.0002365920 28 0.0000000046 0.0013983065 0.0019586023 0.0012771936 0.0038534093 0.0027153367 0.0040227141 0.0058648852 0.0078447522 0.0004224309 0.0040199156 0.0045175071 .0.0007539'156 29 0.0000000027 0.0016979436 0.0006825432 0.0005108774 0.0050202650 0.0073813428 0.0039557847 0.0014702211 0.0082910352 0.0000000000 0.0005297244 0.0058854602 0.0002483418 30 0.0000000060 0.0139941626 0.0163365235 0.0133253864 0.0041641999 0.0025473919 0.0046291194 0.0021486392 0.0093642209 0.0005969550 0.0069720059 0.0048818593 0.0002S41374-

Source: Quality assured vehicle registration data for the combined Vanderburgh County and Warrick County area for source types 21, 32, and 32, MOVES2010a default distributions for all other source types.Appendix C
Vanderbu h and Warrick Counties Vehicle Po ulations: Vehicle Populations

Annual Populations 2008 2009 2010 2011 2012 2013 2014 2015 2016 2017**201S_~··** 2019 2020_ 2021 2022 2023 2024,--·" 2025 2026 2027 2026 2029 2030 2031 2032 2033 2034 2035 2036

__ 2037 2038 2039 2040 11

4,425 4,446 4,466 4,487 4,508 4,529 4,550 4,572, 4,:S93 4,614 4,636 4,657**-~,679** 4,701

4,745

.. 4,7.67 4,789 4,812 4,834 4,857 4,879 4,902 4,925 4,948, 4,971 4,994 5,018 5,04,1' 5,065 5,088 5,112 5,130 21

''94,893

95,335 '' 95,780'

96,227 96,'676 '97,127 97,580 ',.,98,035

98,493 98,952 99,414 99,878 J.00,344," 100,812

- }01 ,755 ' "" .102,229, 102,706 103,1_86 103,667 104,,1_51 104,637 105;125 105,615 -106,108, 106,603_ 10?',100 107,600 1,08_,102, 108,606 109,113_ 109,622 110,134 31

73,275 73,616 73,960 74,305" 74,652 _75,000 75,350 75,701 76,055 76,409 76,766 77,124 7_7,484

__:, 77,845

- 78,209

- 78,573 78,940_, 79,308 79,678 80,050 80,424 80,799 81,176 81,554 81,935 82,317 82,701 83,087 83,475 83,864 84,255 84,649 85,043 32

22,434 22,539 22,-644, 22,750 22,856 ' 22,962

23,069 23,177 23,285 23,394 23,503 23,613 23,723

__ 23,834

_ 23,945 24,056 24,169 _24,281 24,395 24,509 24,623 24,738 24,853 24,969 25,086, 25,203 25,320 25,438 25,557

- 25,676 25;796 '25,916 26,037 41

83 83 84 84 85 85 88 87 87 88 '. ,88_

89 "

__90

__

90 ;91 92 .92 93 94 94 95 96 96 97 ,,.98

98 99 100 '' 100

101 102 _102 103 42

43 43 44 44 44 45 45 45 46 46 _46,. 47 .47 47

.. 48.

48 48 49 49 49 50 50 50 51 51 51 52 52 53 53 53 54 54 Source Types 43 51

560 22 564 22 568 22 572 22 576 23 580 23 594 23 588

__ 23 592 23 597

. _601

605 "

____ 609 613 618 622 '626

__ -

631 635 640 644 649 _653 658 662 667 672' 677 661 _686 691 696 23 '

.... 24

24 24 24 24 24

___ 25

25 25 25 25 25 26 26 26 26 26 27 ,27' 27 27 27 27 52

1,503 1,513 1,524 1,535 1,545 1,556 1,567 1,578 1_,589 1,600

---- J,6_12 1,623 ,1,634

---- 1,6:46

__

__ 1,657

___

1,669 J,68L 1,692 1,704 1,716 1,728 1,741 1,753 1,765 1,77_7 1,790 1,802 1,815 1,828 1,841**~.854** _1,867 1,880 53

193 194 ,.196 197 199 200 201 203 204 206

. ' 20?.

...

209 210 212 213 215 '_216'

218 219 221 222 224 225 227 228 230 232 233 235. 237 238 240 54

348 350 352 355 357 360 362 365 368 370 _373_ 375 378 381 383, 386 -,389 "" 39_1

..

394 397 400 402 405 408 ,411 414 417: 420 423 _426 429 432 61

2,21,0 2,225 2,241 2,257 2,272 2,288 2,304 2,321 2,337 2,353 2,370 2,386 2,403 2,420 2,437

__2,454

2,47:1**2,~9** ___ 2,506 2,524 2,541 2,559 2,577, 2,595 2,614 2,632 ,2,650 2,669 2,698 2,707 2,726 2,745 2,764 62

2,644 2,662**2,68~'** 2,700 2,719 2,738 2,757 2,776 2,796 2,815 2,835 2,855 _2,875 2,895

__**2,9~5** 2,936- 2,957

...... 2.9T7

__ _ 2,998 3,019 3,040_ 3,062 3,083 3,105 3,127, 3,149**3,17~** 3,193 3,215 3,238 3,261 3,284 3,307 Source: Quality assured vehicle registration data for the combined Vanderburgh County and Warrick County area for source types 21, 32, and 32, MOVES201 oa default mileage accumulation rates for all olher source types.**Popula~on** growth factors are taken from local socioeconomic data forecasts.Appendix D


### V: d b h dW:

. kG f M 

### t

. I D 

## t

an**e~** ur.qr an arne oun1es e eoro omca 

### a a: Ozone PM2.5 monthiD zoneiD HouriD temperature reiHumiditv monthiD zoneiD HouriD temperature reiHumidity 7 181730 1 72.6 63.9 4 181730 1 49.9 100.0 7 181730 2 71.3 66.6 4 181730 2 48.7 100.0 7 181730 3 70.4 68.8 4 181730 3 47.7 100.0 7 181730 4 69.7 70.5 4 181730 4 47.0 100.0 7 181730 5 69.1 71.8 4 181730 5 46.5 100.0 7 181730 6 68.5 73.3 4 181730 6 45.8 100.0 7 181730 7 68.0 74.6 4 181730 7 45.3 100.0 7 181730 8 68.4 73.5 4 181730 8 45.7 100.0 7 181730 9 71.1 67.2 4 181730 9 48.4 100.0 7 181730 10 75.3 58.3 4 181730 10 52.7 97.4 7 181730 11 79.6 50.6 4 181730 11 57.1 83.1 7 181730 12 83.2 44.9 4 181730 12 60.8 72.7 7 181730 13 86.5 40.5 4 181730 13 64.1 64.7 7 181730 14 88.2 38.3 4 181730 14 65.9 60.8 7 181730 15 88.8 37.6 4 181730 15 66.5 59.5 7 181730 16 89.0 37.4 4 181730 16 66.7 59.1 7 181730 17 88.6 37.9 4 181730 17 66.3 60.0 7 181730 18 87.3 39.4 4 181730 18 65.0 62.7 7 181730 19 85.2 42.1 4 181730 19 62.9 67.6 7 181730 20 82.5 45.9 4 181730 20 60.1 74.5 7 181730 21 79.8 50.2 4 181730 21 57.3 • 82.3 7 181730 22 77.5 54.2 4 181730 22 54.9 89.8 7 181730 23 75.8 57.3 4 181730 23 53.2 95.5 7 181730 24 74.1 60.6 4 181730 24 51.5 100.0
Source: Mobile 6.2 reported meteorological data from Request for Redesignation and Maintenance Plan for Ozone Attainment in the 8-hour Ozone Basic Nonattainment Area. Appendix D, developed by Indiana Department of Environmental Management in June 2, 2005 and the draft Request for Redesignation and Maintenance Plan under the Annual National AmbientAir Quality Standard for Fine Particles, Appendix F, developed by the Indiana Department of Environmental Management in January, 2011 converted using EPA data converter.Appendix E
Indiana Default VMT Distributions by Vehicle Type and Road Type:

Road Light Duty Single Unit Combination Type Motorcycle Passenqer Car Truck Bus Truck Truck 2 0.007033832 0.506408086 0.163786651 0.004174166 0.007773053 0.310824213 3 0.001733929 0.659751199 0.225767175 0.000793168 0.010963315 0.100991214 4 0.003973041 0.569953374 0.254198647 0.002831718 0.009082816 0.159960404 5 0.002785022 0.702754695 0.245240087 0.001402085 0.009764356 0.038053756

Source: Statewide averages developed from Indiana Department of Transportation traffic count data.Appendix F
Indiana Default Hourtv J tstTI utton actors or Road Tvoe 2- Rural Restricted Access: Source Types Hour 11 21 31 32 41 42 43 51 52 53 54 61 62 1 0.0125903247 0.0101219844 0.0084967341 0.0084967341 0.0254913340 0.0254913340 0.0254913340 0.0126607789 0.0126607789 0.0126607789 0.0126607789 0.0197906895 0.0197906895 2 0.0104070951 0.0069241973 0.0066421955 0.0066421955 0.0269500431 0.0269500431 0.0269500431 0.0114617645 0.0114617645 0.0114617645 0.0114617645 0.0212124099 0.0212124099 3 0.0098043179 0.0056567534 0.0061275627 0.0061275627 0.0231103443 0.0231103443 0.0231103443 0.0107741941 0.0107741941 0.0107741941 0.0107741941 0.0201622890 0.0201622890 4 0.0140329469 0.0069658232 0.0084286563 0.0084286563 0.0234460042 0.0234460042 0.0234460042 0.0128724692 0.0128724692 0.0128724692 0.0128724692 0.0213065902 0.0213065902 5 0.0165212405 0.0100941552 0.0134026652 0.0134026652 0.0244090660 0.0244090660 0.0244090660 0,0174195788 0,0174195788 0.0174195788 0.0174195788 0.0250478552 0.0250478552 6 0.0312047458 0.0241732202 0.0316551315 0.0316551315 0.0322923692 0.0322923692 0.0322923692 0.0261005783 0.0261005783 0.0261005783 0.0261005783 0.0304976568 0.0304976568 7 0.0399082603 " 0.0390974746 0.0481531313 0.0481531313 0.0302344914 0.0302344914 0.0302344914 0.0420450985 0.0420450985 0.0420450985 0.0420450985 0.0339947725 0.0339947725 6 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 0.054.1442978 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 0.0575654739 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 0.066271.2693 0.0683897966 0.0683897966 0.0551925339 0.0551925339 0.0551925339 0.0704234655 0.0704234655 0.0704234655 0.0704234655 0.0578234055 0.0578234055 16 0.0713500739 0.0764876319 0.0772110428 0.0772110428 0.0551956709 0.0551956709 0.0551956709 0.0628601912 0.0628601912 0.0628601912 0.0628601912 0.0577540296 0.0577540296 17 0.0754978425 0.084"(1_60034 0.0792545794 0.0[92545794 0.0557979766 0.0557979766 0.0557979766 0.0534712990- 0.0534712990 0.0534712990 0.0534712990 _0.05629108_1.4 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 0.0372595,462 ' 0.03110'15284 0.0311015284**0.04~8602463** 0.0418602463 0,0418602463 0.0261242877 0.0261242877 0.0261242877 0.0261242877

u**0.04213,1,104~**.. 0.0421311043 22 0.0294294934- 0.0312744978 0.0249803003 0.0249803003 0.0366496745 0.0366496745 0.0366496745 0.0215822567**0.02~5822587** 0.0215822587 0.0215822587 0.0381387483 0.0381387483 23 0.0223450238 0. 0235734666 0.0182964081 0.0182964081 0.0347517842 0.0347517842 0.0347517842 0.0189759266 0.0189759266 0.0189759266 0,0189759266 0.0342326572 0.0342326572 24 0.0179418099 0.0169198902 0.0133194323 0.0133194323 0.0310595247 0.0310595247 0.0310595247 0.0157396039 0.0157396039 0.0157396039 0.0157396039 0.0307625891 0.0307625891

Source: Statewide averages developed from Indiana Department ofTransportation traffic count data.Indiana Default Hourly Distribution Factors for Road Type 3- Rural UnrestrictedAccess: Source Types Hour 11 21 31 32 41 42 43 51 52 53 54 61 62 1 0.0040299464 0.0073183989 0.0054636028 0.0054636028 0.0036998387 0.0036998387 0.0036998387 0.0043986387 0.0043986387 0.0043986387 0.0043986387 0.0164160879 0.0164160879 2 0.0040299464 0.0041131835 0.0034619242 0.0034619242 0.0045536477 0.0045536477 0.0045536477 0.0041872686 0.0041872686 0.0041872686 0.0041872686 0.0167510731 0.0167510731 3 0.0041817017 0.0032797517 0.0030691885 0.0030691885 0.0046485153 0.0046485153 0.0046485153 0.0073497934 0.0073497934 0.0073497934 0.0073497934 0.0165479051 0.0165479051 4 0.0053114356 0.0057247729 0.0048082254 0.0048082254 0.0039844417 0.0039844417 0.0039844417 0.0084039684 0.0084039684 0.0084039684 0.0084039684 0.0195836328 0.0195836328 5 0.0140963815 0.0151258840

.. 0.0143177758 0.0143177758 0.0082534864 0.0082534864 0.0082534864 0.0153176438 0.0153176438 0.0153176438 0.0153176438 o. 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 0.10492363,5 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**0.0444~83487_** 0.0568454275 0.0568454275 0.1186794422 0.11.86794422 0.1186794422 0.0886336394 0.0886336394 0.0886336394 0.0886336394 0.0633505956

.. 0.0633505956 12



### ...... 0.0563855259 0.0512966366 0.0618918527 0.0618918527 0.115453941_8- 0.1154539418 0.1154539418 0.0859045570 0.0859045570 0.0859045570 0.0859045570 0.0635864154 0.0635864154 13 0.0638721209 0.0537246907 0.061081821.1 '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**0.077~51039** 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

.. 0.0916098179 0.087:1890696 0.0796014405 0.0796014405 0.0317806660 0.0317806660 0.0317806660 0.0433522764 0.0433522764 0.0433522764 0:0433522764 0.0517440242 0.051.7440242 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

.**0.054527275~** 0.0545272751

. 0.0120481928

. 0.0120481928 0.0120481928**0.0187,7448~5** 0.0187744815 0:0187144815 0.0187744815 0.0413186686**0.0~._1_31_86_686** 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 o:o106166656 0.0106166656 0.0318882915 0.0318882915 22 0.0217853168 0.0289018238 0.0218457686 0.0218457686 0.0061663979 0.0061663979 0.0061663979 0.0079972816 0.0079972816 0.0079972816 0.0079972816 0.0290264055 0.0290264055

...... ... 23:.

.... 0.011.9380838, 0.0205028665

. .0.0136731866 0.0136731866 0.0048382506 0.0048382506 0.0048382506 0.0061564888 0.0061564-888 0.0061564888'

..0.0061564888. 0.0255574344' 0.025557:4344_, 24 0.0061882440 0.0127827290 0.0079763402 0.0079763402 0.0035101034 0.0035101034 0.0035101034 0.0050809093 0.0050809093 0.0050809093 0.0050809093 0.0225579868 0.0225579868

Source: Statewide averages developed from Indiana Department ofTransportation traffic count data.Indiana Default Hourly Distribution Factors for Road Type 4 Urban Restdcted Access: Source Types Hour 11 21 31 32 41 42 43 51 52 53 54 61 62 1 0.0114838630 0.0104500369 0.0090397680 0.0090397680 0.0186488577 0.0186488577 0.0186488577 0.0090968023 0.0090968023 0.0090968023 0.0090968023 0.0194173119 0.0194173119 2 0.0071800855 0.0062500477 0.0056304309 0.0056304309 0.0163411464 0.0163411464 0.0163411464 0.0080102618 0.0080102618 0.0080102618 0.0080102618 0.0198708197 0.0198708197 3 0.0063691205 0,0049689741 0.0046493622 0.0046493622 0.0157775876 0.0157775876 0.0157775876

. 0.0078361983 0.0078361983 0.0078361983 0.0078361983 0.0186489893 0.0186489893 4 0.0073777516 0.0058427101 0.0058801326 0.0058801326 0.0161766037 0.0161766037 0.0161766037 0.0086827231 0.0086827231 0.0086827231 0.0086827231 0.0198231326 0.0198231326 5

. 0.0108139353 _0.0098545059 0.0108999000 0.0108999000 0.0221330492 0.0221330492 0.0221330492 0.0117453229 0.0117453229 0.0117453229 0.0117453229 0.0232515449 0.0232515449 6 0.0235457656 0.0231603609 0.0263517526 0.0263517526 0.0299755654 0.0299755654 0.0299755654 0.0204013312 0.0204013312 0.0204013312 0.0204013312 0.0294638153 0.0294638153

... 7 0.0461747881 0.0495085217 0.0542414568 0.0542414568 0.0393812372 0.0393812372 0.0393812372 0.0435263184 0.0435263184 0.0435263184 0.0435263184 0.0375553768 0.0375553768 8 0.0567226756 0.0788353145 0.0674512195 0.0674512195 0.0503870867 0.0503870867 0.0503870867 0.0659533819 0.0659533819 0.0659533819 0.0659533819 0.0446175773 0.0446175773 9

.. 0.04931.1_1440 0.06382?:9223 · .. 0.0614111771**0.061,41,1~771** 0.0589556475 0.0589556475 0.0589556475 0.0756333F8 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 o:o51.2594850 0.0616027281 0.0616027281 0.0616027281 0.0824723032 0.0824?:23032 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 0.057342$674 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_ O.OS38541123 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 ....•**0.06~5951265** 0.0604364374 0.0543673700 ,0.0543673700 0.0450990958 0.0450990958 0.0450990958 0.0249336618 0.024933661.8 0.0249336618 0.0249336618 0.0487199307**0.0~87199307** 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 0.032231857J 0.0162446774 0.0162446774 0.0162446774 0.0162446774 0:0390319248 0.0390319248 22 0.0316564842 0.0313403787**0.02~9971308** 0.0249971308 0.0282046747 0.0282046747 0.0282046747 0.0142456600 0.0142456600 0.0142456600 0.0142456600**0.03551184~6** 0.0355118446 23 ····· 0.0245992722

..0.0251-562568 0.0203505544 0.0203505544 0.02427,0047'5 0.0242700475.**_0.02~2700475** 0.0124474209

. 9.0124474209 0.0124474209 0.0124474209. 0.0317_711657:_.**0.03177.1~657,-** 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 Default Hour! Distribution Factors for Road 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 _D.0087215410**0.0~53898606** 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,()418068371 '0.0418068371 0.0418068371**0.04~8068371** 0.0436775030 0.0436775030 8

........ 0.0602121997 0.0721456866 0.0675347974 0.0675347974 0.0691895946 0.0691895946 0.0691895946**0.0~31482386** 0.0731482386 0.0731482386 0.0731482386 0.0588646976 0.0588646976 9

... 0.0556311148 0.0567013667 0.0643660182 0.0643660182 0.07_47959425. 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 ,0.0637:S49687_" • ,0.0526386278 '. _0.05263862(8_

.. 0.0285090860 0.0285090860 0.0285090860

..0.01,73341_336 0.01733;41336**0.017334~336** 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 _0.007661,5_624 0.0076615624 0.0076515624, 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 0.005327_'6381 0.0053276381 0,0053276381 ; 0.0,193?:51364 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 ofTransportation traffic count data.AppendixG
Indiana Default Daily Distribution Factors: dayiD monthiD 2 5 1 0.2325411725 0.7674588275 2 0.2380547378 0.7619452622 3 0.2393402049 0.7606597951 4 0.2396052454 0.7603947546 5 0.2484757701 0.7515242299 6 0.2489743665 0.7510256335 7 0.2481153021 0.7518846979 8 0.2527028648**0.747297135~** 9 0.2496078420 0.7503921580 10 0.2462808693 0.7537191307 11 0.2439742406 0.7560257594 12 0.2258784720 0.7741215280

Source: Statewide averages developed from Indiana Department of Transportation traffic count data.Appendix H
Indiana Default Monthlv Distribution Factors: monthiD monthVMTFraction 1 0.0733424010 2 0.0693661929 3 0.0827036024 4 0.0831789580 5 0.0891346903 6 0.0888150873 7 0.0907968617 8 0.0918542094 9 0.0854175366 10 0.0875162272 11 0.0812354405 12 0.0766387926

Source: Statewide averages developed from Indiana Department of Transportation traffic count data.Appendix I Vanderburgh and Warrick Counties Ramp Fractions: Ramp Road Tvoe Fraction 2 4 2% 13%

Source: Analysis of VHT from the Evansville MPO travel demand model.

# Appendix B

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

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

### This page left intentionally blank

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

For the MOBILE6.2 to MOVES MVEB Replacement Update Related to the 1997 8-Hour Ozone Standard for Vanderburgh and Warrick Counties, Indiana, and the 1997 Annual Fine Particles Standar·d for the Southwestern Indiana Area

ICG Conference Call Date and Time

• February 

### 13,2013 at lpm Eastern Standard Time

ICG Attendees

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

ICG Discussion Topics and Conclusions 1. For the Ozone MVEB Replacement submittal, various mobile source margins of safety were discussed. 

### A. After discussion, the consensus ofthe ICG was that as long as the a 15% mobile source margin of safety for VOC and NOx emissions does not result in
an exceedance ofthe all sources margins of safety, it was reasonable and appropriate for inclusion in the MVEB replacement submittal.



### 2. For the PM2

.5 

### MVEB Replacement submittal, various mobile source margins of safety were discussed. A. After discussion, the consensus ofthe ICG was that as long as the a 15% mobile source margin of safety for NOx and PM2.s emissions does not result in
an exceedance ofthe all sources margins of safety, it was reasonable and appropriate for inclusion in the MVEB replacement submittal.

B-1