# APPENDIX D

Onroad Sources

Bureau of Air Quality Department of Environmental Protection

## [ This page intentionally left blank

. ]

# APPENDIX D

Technical Support Document Mobile Source Highway Emissions Inventory

Executive Summary

July 20 14 Prepared for:

Mobile Sources Section, Bureau of Air Quality Pennsylvania Department of Environmental Protection PO Box 8468 Harrisburg, PA 17105-8468

Prepared by:

Michael Baker, Jr., Inc. 1304 Concourse Drive Linthicum, MD 21090 410-689-3400

## Mobile Source Emissions Inventory Executive Summary July 2014



# Exhibit of Contents

SUMMARY

................................................................................................ .................................................................. 1

E MISSIONS 

### I NVENTORY



### ................................................................................................ ............................................. 2 A NALYSIS 

### M ETHODOLOGY



### ................................................................................................ ........................................ 3

DATA SOURCES AND ANA LYSIS TOOLS

........................................................................................................... 4

A NALYSIS 

### T OOLS



### ................................................................................................ ...................................................... 4 T RAFFIC 

### D ATA 

### S OURCE 

### /F LEET 

### D ATA 

### I NPUTS



### ........................................................................................................... 5 I/M AND 

### F UEL 

### P ARAMETERS



### ................................................................................................ ..................................... 6 M ETEOROLOGY 

### D ATA



### ................................................................................................ ............................................... 7 V EHICLE 

### T ECHNOLOGY 

### P ROGRAMS



### .......................................................................................................................... 7

RESOURCES

................................................................................................ ............................................................... 9



# List of Exhibits

E XHIB IT 

### 1: S UMMARY OF 

### A PPENDICES



### ........................................................................................................................... 1 E XHIBIT 

### 2: M OTOR 

### V EHICLE 

### E MISSIONS 

### U SING 

### MOVES2010 B



### .................................................................................... 2 E XHIBIT 

### 3: S UMMARY OF 

### A NALYSIS 

### T OOLS



### ................................................................................................................... 4 E XHIBIT 

### 4: PPSUITE P ROCESS



### ................................................................................................ ...................................... 5



# Summary of Appendices

Appendix D

- 1: Explanation of Methodology

Appendix D

- 2: Emission Results for VOC, NOx, and CO (By Road Type

, Source Type and Process )

Appendix D -3: MO VE S S ample Input Files

### Mobile Source Emissions Inventory : Executive Summary 1 

# SUMMARY

This technical appendix supports the ozone S tate Implementation Plan (SIP) for the following nonattainment areas:

• Allentown -Bethlehem- Easton a rea , consisting of:  Lehigh County,  Northampton County, and  Carbon County.

• Lancaster area, consisting of Lancaster County

• Philadelphia, Pennsylvania portion of the Philadelphia-Wilmington- Atlantic City, PA

- NJ

- MD

- DE Area , consisting of:  Bucks County,  Chester County,  Delaware County,  Montgomery County, and  Philadelphia County.

• Pittsburgh- Beaver Valley area , consisting of:  Allegheny County,  Armstrong County,  Beaver County,  Butler County,  Fayette County,  Washington County, and  Westmoreland County.

• Reading area , consisting of Berks County.

To meet emission inventory requirements of section 172(c)(3) of the Clean Air Act, a regional mobile source highway inventory has been prepared for the ozone e missions. Emissions are estimated for the 2011 analysis year

. The pollutants included in the inventory are for ozone precursors, volatile organic compounds (VOC) and the n itrogen oxides (NOx), and carbon monoxide (CO).

Appendix D has been provided to su mmarize the methodology and analysis results for the motor vehicle emissions inventory using MOVES2010b. To complement this executive summary, attachments have been provided with additional detail regarding the analysis methodology, the MOVES input parameters, and the output vehicle miles of travel ( VMT ) and emission results for the region . These include:



## E xhibit 1 : Summary of Appendices
Appendix Title Description

D-1 Explanation of Methodology Provides a detailed summary of the methodology used to calculate the VMT and emissions.



### D-2 VOC, NOx, and CO Emission Results Provides annual emission exhibits by county, road type

, source type and process categories in 20 11

. 

### D-3 MOVES Sample Input File Provides examples of the MOVES input files.

### Mobile Source Emissions Inventory : Executive Summary 2 

# Emissions Inventory

A summary of the motor vehicle emissions for the nonattainment a rea s is provided in Exhibit 2

. The emission estimates for all pollutants have been developed using the MOVES2010b emission model an d latest planning assumptions. Emissions have been estimated for the 2011 analysis year

.



## Exhibit 2 : Motor Vehicle Emissions Using MOVES2010b

Pollutants Area County VOC NOx CO

July Weekday ( **Short Tons/Day)** Allentown Lehigh 8.24 17.13 85.53 Northampton 7.00 14.04 65.30 Carbon 1.94 4.39 21.76 Area Total 17.18 35.56 172.59

Lancaster Lancaster 11.99 24.42 121.03 Area Total 11.99 24.42 121.03

Philadelphia Bucks 11.47 22.55 119.86 Chester 9.29 20.29 102.86 Delaware 8.68 17.25 88.68 Montgomery 14.50 28.89 159.89 Philadelphia 16.63 34.40 160.42 Area Total 60.58 123.39 631.69

Pittsburgh Allegheny 20.40 41.15 208.35 Armstrong 1.61 3.33 15.76

Beaver 3.22 6.45 32.45 Butler 4.44 9.64 46.20 Fayette 2.91 5.31 27.66 Washington 4.02 8.71 42.75 Westmoreland 6.95 14.26 73.47

Area Total 43.54 88.85 446.64
Reading Berks 9.86 22.11 98.88 Area Total 9.86 22.11 98.88

Annual ( **Short Tons/Year)** Allentown Lehigh 2,938.97 6,154.43 37,317.95 Northampton 2,524.35 5,086.83 30,028.04 Carbon 706.66 1,592.35 9,454.14 Area Total 6,169.98 12,833.61 76,800.12

Lancaster Lancaster 4,233.63 8,879.12 52,716.37 Area Total 4,233.63 8,879.12 52,716.37

Philadelphia Bucks 4,120.01 8,292.77 49,954.81 Chester 3,309.73 7,413.67 41,456.81 Delaware 3,097.85 6,222.26 37,084.67 Montgomery 5,156.21 10,458.00 64,680.67 Philadelphia 5,814.04 11,482.34 66,678.77 Area Total 21,497.83 43,869.04 259,855.73

Pittsburgh Allegheny 7,755.25 14,865.96 98,535.36 Armstrong 611.63 1,223.02 7,454.79

Beaver 1,232.52 2,365.83 15,550.01 Butler 1,672.83 3,527.63 21,200.51 Fayette 1,114.77 1,950.20 13,397.21 Washington 1,540.23 3,197.99 20,163.87 Westmoreland 2,657.30 5,229.77 34,579.73

Area Total 16,584.53 32,360.40 210,881.48
Reading Berks 3,479.35 8,073.19 43,022.47 Area Total 3,479.35 8,073.19 43,022.47

### Mobile Source Emissions Inventory : Executive Summary 3 

# Analysis Methodology

Guidance documents from EPA were used to develop the base and future year emissions inventories for the region . They include:

• Policy Guidance on the Use of MOVES2010 and Subsequent Minor Revisions for State Implementation Plan Development, Transportation Conformity, and Other Purposes

, US EPA Office of Transportation and Air Quality , EPA -420-B-12-010, April 2012.

• Using MOVES to Prepare Emission Inventories in State Implementation Plans and Transportation Conformity: Technical Guidance for MOVES2010, 2010a and 2010b

. US EPA Office of Transportation and Air Quality , EPA -420-B-12-028, April 2012.

• Motor Vehicle Emission Simulator (MOVES)
– User Guide for MOVES2010b, US EPA Office of Transportation and Air Quality, EPA -420-B-12-001b, June 2012.

The highway m obile source emission inventory was developed using available travel data and EPA’s MOVES2010b emission model. The methodologies used to produce the emission data conform to the recommendations provided in EPA’s Technical G uidance . A mix of local data and national default (internal to MOVES2010b ) data has been used for this submission. Local data has been used for the primary data items that have a significant impact on emissions. These include:

• Vehicle miles of travel ( VMT ) by vehicle type

.

• Average speed d istribution

.

• Vehicle type mixes

.

• Source t ype p opulation (for light -duty vehicles).

• Vehicle age distribution

.

• Hourly distributions

.

• Meteorology data

.

• Inspection/Maintenance p rogram

.

• Fuel supply.

M ost local data inputs to the analysis process reflect the latest planning assumptions based on 20 11 data obtained from the Pennsylvania Department of Transportation (PennDOT), the Bureau of Motor Vehicles

, and other local/national sources

. N ewer data was availa ble and was use d for control strategies (e.g. Inspection- Maintenance programs) , vehicle age distributions and fuel characteristics.

The analysis methodology is consistent with past statewide inventory efforts including the 20 11 National Emissions Inventory (NEI) submission. This includes the use of custom post processing software to calculate hourly speeds and prepare key traffic input files to the MOVES2010b emission model. A detailed methodology is provided in Appendix D -1

. The following sections address the key input data sources and analysis tools used for the emissions inventory for the Allentown

- Bethlehem

- Easton Area

.

### Mobile Source Emissions Inventory : Executive Summary 4 

# DATA SOURCES AND ANALYSIS TOOLS

This section provides a summary of the key input data and analys is tools used for producing the emission s inventory. The key elements to the modeling protocol are described in the sections below. A more detailed description of the analysis process and tools is provided in the methodology report s in Appendix D-1 through D-3

.


# Analysis Tools

The mobile vehicle emissions inventory analysis utilizes several key software/programs for producing the county emissions totals. These tools are outlined in Exhibit 3

.



## Exhibit 3 : Summary of Analysis Tools

Tool Purpose

MOVES2010b Produces emission rates for the emissions of VOC, NOx, and CO

PPSUITE Processes the highway data ; Calculates hourly congested speeds for each state roadway segment ; Prepares MOVES2010b input files ; Processes MOVES2010b output files into a summary report

.

CENTRAL Provides a batch menu driven process to execute PPSUITE, MOVES2010b and other MYSQL steps.

The inventory reflects the highway mobile source emission estimations using EPA’s MOVES2010b emission model releas ed on June 2012

. The MOVES2010b model provides a more robust estimate of emissions as compared to its predecessor MOBILE6.2. MOVES2010b has been integrated with local traffic, vehicle fleet, environmental, fuel, and control strategy data to estimate emissions

.

PPSUITE represents an enhanced version of the Post Processor for Air Quality (PPAQ) software system that has been used for previo us inventory and conformity submissions in Pennsylvania. The software has under gone significant revision s to ensure consistency with the MOVES2010b . PPSUITE was used to calculate hourly congested speeds for each roadway link, apply vehicle type fractions , aggregate VMT, prepare MOVES2010b traffic

- related input files and process MOVES2010b outputs.

The PPSUITE software and process methodologies are consistent with that used for state inventories and transportation conformity analyses throughout Pennsylv ania. Exhibit 4 summarizes the key functions of PPSUITE.

CENTRAL is a menu

- driven software platform that executes the PPSUITE and MOVES2010b processes in batch mode. The software allows users to execute runs for a variety of input options and integrates custom MYSQL steps into the process. CENTRAL provides important quality control and assurance steps including file naming and storage automation.

### Mobile Source Emissions Inventory : Executive Summary 5 

# Traffic Data Source/Fleet Data Inputs

Traffic Volume Data : The PennDOT Roadway Management System (RMS) data serves as the primary highway data source for the county and functional class VMT estimates. The data source is used to provide a “snapshot” of the regional roadway system and traffic volumes in 2011 (consistent with past triennial updates of traffic data). The 20 11 data is also integrated with traffic signal locations. The data includes the average annual daily traffic (AADT) volumes for all state roadways in Pennsylvania. To account for additional local roadway VMT and to ensure consistency with reported Highway Performance Monitoring System ( HPMS ) VMT totals, the V MT totals estimated from PennDOT’s RMS are adjusted to match the annual 2011 HPMS VMT totals , as reported to FHWA.

Seasonal Adjustment s : Within MOVES, annual VMT is split to monthly sub- totals and then to weekdays and weekends using seasonal factors

. The monthly seasonal factors are developed from data contained in the document, 2011 Pennsylvania Traffic Data

, prepared by PennDOT’s Bureau of Planning and Research (BPR). The seasonal and daily factors provided in this document are b ased on statistical analyses of 2011 traffic counts taken at permanent and in

- pavement ATR (automatic traffic recorder) locations throughout the state.

Congested Speeds : B ased on the average annual daily traffic, a single set of hourly speed distributions are estimated by the PPSUITE post processing system and input to MOVES. To disaggregate the daily RMS volumes to hourly volumes, auto and truck hourly pattern data from PennDOT’s 2011 Pennsylvania Traffic Data report is used to determine the tempora l variations in traffic volumes

. 

## Exhibit 4 : PPSUITE Process

### Mobile Source Emissions Inventory : Executive Summary 6 

### Vehicle Population : Vehicle population is a key input that has an important impact on start and evaporative emissions. MOVES2010b requires the number of vehicles by 13 source types to determin e evaporative emissions. State 2011 vehicle registration data (consistent with past triennial updates of traffic data) was used to estimate vehicle popula tion for light

- duty vehicles

, school buses and transit buses . The data was split to source types using MOVES default population data. For all other heavy

duty vehicles, PPSUITE calculates vehicle population based on the analysis year VMT for each source type and default MOVES ratio s of VMT and source type population (e.g. the number of miles per vehicle by source type).

VMT by Source Type : The total VMT is disaggregated to the 13 MOVES source types. For this inventory, the vehicle mix was calculated for each county and functiona l class grou ping utilizing a combination of:

• 2011 RMS truck percentages

• 2011 school bus registration data

• 2011 PennDOT transit data

EPA’s MOVES default distribution of VMT by source type was used to determine the remaining source type VMT percentages. The development of vehicle type pattern data input to the MOVES2010b software is described in more detail in Appendix D -1

. Vehicle Age Distribution : Vehicle age distributions are required to be input by 13 source types . The distributions reflect the percentage of vehicles in the fleet up to 31 years old

. A recent 201 1 registration download from PennDOT’s Bureau of Motor Vehicles Registration Database has indicated a substantially older fleet than recorded in the 2002-2008 period

. As a result, t he 20 11 vehicle age distributions have been used for this inventory

. Due to insufficient data, only data for light

- duty vehicles are used as local inputs ; and , heavy

- duty vehicles use the MOVES2010 national default age distribution

. The registration data download is based on M OBILE6.2 vehicle categories . T he data was converted to source types using the EPA convertor spreadsheets provided with the MOVES emission model.



# I/M and Fuel Parameters

I/M Program: The inspection m aintenanc e (I/M) program inputs to the MOVES model are based on past and current programs within each county (all Pennsylvania I/M programs are based on county boundaries). All analysis year s include Pennsylvania’s statewide program . The default I/M program parameters included in MOVES model were examined for each county and necessary changes made to the defaults to match the actual local program.

In order to assure that emission controls are working properly, vehicle inspection and m aintenance (I/M) programs have been adopted in some nonattainment areas. These programs have the added benefit of improving the fuel efficiency of vehicles

. The Pennsylvania inspection and maintenance (I/M) program was upgraded and expanded throughout th e state with a phase

- in period starting in September 2003 and fully implemented by June 2004.

The program requirements vary by region (five regions) and include on

- board diagnostics (OBD) technology that uses the vehicle’s computer for model years 1996 and newer to identify potential engine and exhaust system problems that could a ffect emissions. The program, named PAOBDII, is implemented by region, as follows:

• Philadelphia Region - Bucks, Chester, Delaware, Montgo mery and Philadelphia Counties

• Pittsb urgh Region - Allegheny, Beaver, Washin gton and Westmoreland Counties

### Mobile Source Emissions Inventory : Executive Summary 7 

### • South Central and Lehigh Valley Region - Berks , Cumberland, Dauphin, Lancaster, Lebanon, Lehigh, Northampton and York Counties

• North Region - Blair, Cambria, Centre, Erie, Lackawanna, Lu zerne , Lycoming, and Mercer Counties

The OBDII program is implemented in Philadelphia and Pittsburgh along with tailpipe (idle in Pittsburgh and idle and ASM in Philadelphia) and gas cap tests. Tests in other regions include:

• Subject vehicles registered in the South Central and Lehigh Valley counties receive the visual, OBD and gas cap tests.

• Subject vehicles registered in the North region receive a gas cap test and visual inspection.

• Subject vehicles registered in the other 42 counties (67 total counties) receive a visual inspection as part o f the annual safety inspection.

Fuel Assumptions : The MOVES2010b default fuel formulation and fuel supply data were reviewed and updated based on available local volumetric fuel propert y information. The gas ohol market penetration values and RVP values were updated but MOVES 2010b default data was used for the remaining parameters. Key assumptions included:

• Philadelphia Region :  Using MOVES default RVP (6.96 for summer months).  10% ethanol used throughout the year for analysis year 2011.

• Pittsburgh Region:  A low RVP (7.8) fuel program for summer months.  10% ethanol used throughout the year for analysis year 2011.

• Other PA Regions:  8.7 RVP used for summer months.  10% ethanol used throughout the year for analysis year 2011.



# Meteorolog y Data

Updated weather information has been obtained from WeatherBank, Inc. ( www.weatherbank.com ). The 10- year (1998-2008) average minimum and maximum monthly temperature and relative humidity values were obtained for each of the 9 airport locations in Pennsylvania.

The MOVES2010b model requires temperature and relative humidity data for each hour of the day and for all the 12 months for the annual analysis. EPA’s data converters were used to convert minimum and maximum daily temperatures to an hourly temperature profile that could be input to MOVES2010b. These assumptions are consistent with the 20 11 NEI inventory submission.



# Vehicle Tec hnology Programs

Federal Programs

Current f ederal vehicle emissions control and fuel programs are incorporated into the MOVES2010b software. The se include the National Program standards covering model year vehicles through 2016. Modifications of default emission rates are required to reflect the early implementation of the National Low Emission Vehicle Program (NLEV) program in Pennsylvania. To reflect these impacts, EPA has

### Mobile Source Emissions Inventory : Executive Summary 8 

### released instructions and input files that can be used to model these impacts. This inventory utilized the August 2010 version of the files ( http://www.epa.gov/oms/models/moves/tools.htm ).

St ate Programs

The Pennsylvania Clean Vehicles (PCV) Program, adopted in 1998, incorporated the California Low Emission Vehicle Program (CA LEVII) by reference

, although it allowed automakers to comply with the NLEV program as an alternative to this Penn sylvania program until MY 2006. Beginning with MY 2008, “new” passenger cars and light

- duty trucks with a gross vehicle weight rating (GVWR) of 8,500 pounds or less that are sold or leased and titled in Pennsylvania must be certified by the California Air Resources Board (CARB) or be certified for sale in all 50 states. For this program, a “new” vehicle is a qualified vehicle with an odometer reading less than 7,500 miles. Pa DEP and PennDOT worked with the automobile manufacturers, dealers and other interested business partners and finalized procedures for complying with these new requirements. DEP focus es its outreach effort with the manufacturers and dealers regarding what vehicles can be offered for sale and how to certify that the vehicles are complia nt. PennDOT’s role is to ensure licensing and registration records include these certifications of compliance or that the vehicle owner qualifies for an exemption to the requirements. In all cases, DEP will use information obtained during PennDOT’s title and registration process to oversee and audit, as needed, certain vehicle title transactions to determine compliance to the program.

The impacts of this program are modeled for all analysis years beyond 2008 using the same instructions and tools as down loaded for the early NLEV analysis. EPA provided input files to reflect the CAL LEVII program. Modifications to those files were made to reflect a 2008 start date for Pennsylvania.

### Mobile Source Emissions Inventory : Executive Summary 9 

# RESOURCES

2011 Pennsylvania Traffic Data, PennDOT Bureau of Planning a nd Research, 2011.

Policy Guidance on the Use of MOVES2010 and Subsequent Minor Revisions for State Implementation Plan Development, Transportation Conformity, and Other Purposes , US EPA Office of Transportation and Air Quality , EPA -420-B-12-010, April 2012.

Using MOVES to Prepare Emission Inventories in State Implementation Plans and Transportation Conformity: Technical Guidance for MOVES2010, 2010a and 2010b

. US EPA Office of Transportation and Air Quality , EPA -420-B-12- 028, April 2012.

Motor Vehicl e Emission Simulator (MOVES) – User Guide for MOVES2010b , US EPA Office of Transportation and Air Quality, EPA-420-B-12-001b, June 2012.

Metrological Data from Weather Bank, Inc., www.weatherbank.com

# APPENDIX D-1

Explanation of Methodology

### An Explanation of Methodology 

## Explanation of Methodology July 2014



# TABLE OF CONTENTS

INTRODUCTION

................................................................................................ ....................................................... 1

O VERVIEW OF 

### E MISSIONS 

### I NVENTORIES



### .................................................................................................................... 1 H IGHWAY 

### V EHICLE 

### E MISSION 

### I NVENTORIES



### ............................................................................................................. 1

WHERE DOES PENNSYLVANIA OBTAIN ITS DATA?

..................................................................................... 4

S UMMARY OF 

### MOVES I NPUTS



### ................................................................................................ .................................. 4 V EHICLE 

### M ILES OF 

### T RAVEL 

### (VMT)

.......................................................................................................................... 5 A DJUSTMENTS TO 

### R OADWAY 

### D ATA



### .......................................................................................................................... 8 V EHICLE 

### T YPE 

### P ROCESSING



### ................................................................................................ ...................................... 9 V EHICLE 

### F LEET AND 

### P OPULATION 

### D ATA



### ................................................................................................................ 10 E NVIRONMENTAL 

### , F UEL AND 

### T ECHNOLOGY 

### A SSUMPTIONS



### .................................................................................... 10

SPEED/EMISSION ESTIM ATION PROCEDURE

.............................................................................................. 12

V OLUME 

### /VMT D EVELOPMENT



### ............................................................................................................................... 12 S PEED 

### /D ELAY 

### D ETERMINATION



### .............................................................................................................................. 15 HPMS AND 

### VMT A DJUSTMENTS



### ............................................................................................................................ 16 MOVES E MISSIONS 

### R UN



### ................................................................................................ ........................................ 17

RESOURCES

................................................................................................ ............................................................. 18

HIGHWAY VEHICLE INVE NTORY GLOSSARY

............................................................................................. 19



# List of Exhibits

E XHIBIT 

### 1: S UMMARY OF 

### PPSUITE P ROCESS



### ................................................................................................................ 3 E XHIBIT 

### 2: MOVES L OCAL 

### D ATA 

### I NPUT 

### S UMMARY



### ..................................................................................................... 4 E XHIBIT 

### 3: P ENN 

### DOT U RBAN 

### /R URAL AND 

### F UNCTIONAL 

### C LASS 

### C ODES



### ....................................................................... 6 E XHIBIT 

### 4: E MISSION 

### F ACTOR VS



### . S PEED 

### V ARIANCES 

### (NO X 

### )

........................................................................................ 7 E XHIBIT 

### 5: MOVES S OURCE 

### T YPES AND 

### HPMS V EHICLE 

### G ROUPS



### .............................................................................. 9 E XHIBIT 

### 6: PPSUITE S PEED 

### / E MISSION 

### E STIMATION 

### P ROCEDURE



### .............................................................................. 13

### Appendix D

- 1 1 

# INTRODUCTION

The purpose of this document is to explain how the Pennsylvania Department of Environmental Protection (Department) estimates emissions from highway vehicles for inclusion in its emission inventories and State Implementation Plans.


# Overview of Emissions Inventories

The Department’s inventories generally categorize emissions into four categories:

• H ighway vehicles

.

• Po int sources (major industrial, commercial and utility sources)

.

• Non -point sources (smaller industrial/commercial sources, consumer products)

.

• N onroad mobile sources (including construction and agricultural equipment, lawn and garden equipment).

An evaluation of emissions from point, area, and mobile sources is needed to develop a complete inventory needed for a maintenance demonstration plan. This documentation addresses the mobile source activity and emissions for base and future years used to support su ch a demonstration.

Of all of the sources of air pollution, only the emissions of some stationary sources are measured directly and continuously through instrumentation. Emissions from all other sources must be modeled based on available local data , including those from highway vehicles. In their very simplest form, estimates of emissions follow the following pattern:

Emission rate x activity level = emissions per time period (usually day or year)

Most emission rates have been developed by the U .S. Environmental Protection Agency ( EPA ) , in cooperation with industry and states, and are compiled and documented in to key references or emission models. These include Compilation of Air Pollution Emission Factors (AP -42), the Motor Vehicle Emission Simula tor (MOVES) model, and the NONROAD model. Adding up the products of the emission rates and activity levels for all sources of a given pollutant constitutes the emission inventory for that pollutant.


# Highway Vehicle Emission Inventories

Highway vehicles c ontribute significantly to air pollution, particularly to ground

- level ozone, which is the most persistent air pollutant in Pennsylvania. Ground

- level 

## o zone is not emitted directly to the atmosphere, but is formed by photochemical reactions between volatile organic compounds (VOCs) and oxides of nitrogen (NO x 

## ) in the presence of sunlight. The long, hot, humid days of summer are particularly conducive to ozone formation, so ozone levels are of concern primarily during the months of May through September. Both VOCs and NOx are emitted from highway vehicles. Pennsylvania’s ozone

- related emission inventory efforts focus on these two types of pollutants.

Obviously, direct measurement of emission levels from all vehicles in use is impossible. In comparison
t o highway vehicles, estimating residential heating emissions is a fairly simple calculation because there is a constant emission rate and a fairly simple measure of activity. However, f or highway vehicles

### Appendix D

- 1 2 

### estimating the emission rate and activity levels of all vehicles on the road during a typical summer day is a complicated endeavor.

If every vehicle emitted the same amount of pollution all the time, one could simply multiply those emission standards (emission rate in grams of pollution per mile) times the vehicle miles traveled ( VMT ) to estimate total emissions. But emission rates from all vehicles vary over the entire range of conditions under which they operate. These variables include air temperature, speed, traffic conditions, o perating mode and fuel characteristics . The inventory must also account for non- exhaust or evaporative emissions. In addition, the fleet is composed of several generations and types of vehicles with different emission control technologies. This requires the estimation algorithm include the composition of the fleet (vehicle ages and types)

.

In order to e stimate both the rate at which emissions are being generated and to calculate vehicle miles traveled (activity level), Pennsylvania examines its road network and fleet to estimate vehicle activity. For ozone- related inventories, this is done for a typical summer weekday. For carbon monoxide (CO) and
p articulate m atter (PM) emission inventories, this may be done for a typical winter weekday , summer weekday and/ or annual conditions. Not only must this be done for a baseline year, but it must also be projected into the future. This process involves a large quantity of data and is extremely complex.

Computer models have been developed to perform these calc ulations by simulating the travel of vehicles on the Commonwealth’s roadway system. The models also generate emission s rates (also called emission factors) for different vehicle types for area

- specific conditions

, and then combine them in summary form. T he area

- specific conditions include vehicle and highway data, plus control measure characteristics and future year projections of all variables. The key models used to generate this mobile source emissions inventory are:

MO VES : EPA’s MOVES 2010b model , release in June 2012, was used for this mobile source inventory as approved by EPA. The MOVES model provides a more robust estimate of emissions as compared to its predecessor MOBILE6.2. MOVES calculates average in

- use fleet emission s for each of thirt een categories of vehicles under various conditions affecting in

- use emission levels (e.g., ambient temperatures, average traffic speeds, gasoline volatility) as specified by the model user.

MOVES can be used to estimate national, state, and county level inventories of criteria air pollutants,
precursors, greenhouse gas emissions, and some mobile source air toxics from highway vehicles. Additionally, MOVES can make projections for energy cons umption (total, petroleum

- based, and fossil

based).

PPSUITE : For the Department’s highway emissions inventory, a post processor named PPSUITE (formerly named PPAQ - Post Processor for Air Quality) is used, which consists of a set of programs that perform the following functions:

• Analyzes highway operating conditions.

• Calculates highway speeds

.

• Compiles vehicle miles of travel (VMT) and vehicle type mix data

.

• Prepares MO VES runs and processes MOVES outputs.

PPSUITE is a widely used and accepted tool for estimating speeds and processing emission s rat es. The software is based upon accepted transportation engineering methodologies. For example, PPSUITE uses speed and delay estimation procedures based on planning methods provided in the Highway Capacity Manual , a report prepared by the Transportation Research Board (TRB) summarizing current knowledge and analysis techniques for capacity and level -of- service analyses of the transportation system.

### Appendix D

- 1 3 

### The PPSUITE process is integral to producing key input file s to the MOVES emission model. Exhibit 1 summarizes the key functions of PPSUITE and the traffic

- related input files prepared for the MOVES County Data Manager (CDM).



## Exhibit 1: Summary of PPSUITE Process

The following sections summarize the key data and methodologies used to produce the mobile source emissions inventory. This includes a summary of local data sources and a step

- by

- step review of the speed calculation process. The emission data and pro cess has been developed according to recommendations provided by EPA in key policy and technical guidance as provided below:

• Policy Guidance on the Use of MOVES2010 and Subsequent Minor Revisions for State Implementation Plan Development, Transportation Conformity, and Other Purposes

, US EPA Office of Transportation and Air Quality , EPA -420-B-12-010, April 2012.

• Using MOVES to Prepare Emission Inventories in State Implementation Plans and Transportation Conformity: Technical Guidance for MOVES2010, 2010a and 2010b

. US EPA Office of Transportation and Air Quality , EPA -420-B-12-028, April 2012.

The process has focused on developing an emissions inventory using the available tools and data to its fullest extent. This includes the use of available local data for items that have a significant impact on emissions and applying a robust calculation process to estimate hourly traffic speeds.

### Appendix D

- 1 4 

# WHERE DOES PENNSYLVANIA OBTAIN ITS DATA?

Summary of MOVES Inputs

A large number of inputs to MO VES are needed to fully account for the numerous vehicle and environmental parameters that affect emissions . These include traffic flow characteristics (as determined from the PPSUITE software), vehicle descriptions, fuel parameters, inspection/maintenance p rogram parameters, and environmental varia bles

. MOVES includes a default national database of meteorology, vehicle fleet, vehicle activity, fuel, and emission control program data for every county ; but EPA cannot certify that the default data is the most current or best available information for any specific area

. As a result, local data is recommended for use for analyses supporting s tate implementation p lans (SIPs)

.

A mix of local and default data is used for this inventory. Local data sources are used for all inputs that have a significant impact on calculated emission rates. Exhibit 2 summarizes Pennsylvania- specific inputs assembled and used for this inventory

. These data items are discussed in the following sections.



## Exhibit 2 : MOVES Local Data Input Summary

Traffic Vehicle Fuel Inspection Environmental

Data D escriptions Parameters Maintenance Variables

Vehicle Type Vehicle Type RVP Start Year H ourly VMT Mix Model Year s Temperatures

Vehicle Vehicle Age Sulfur T est Standards

, Population Distribution Level Source Types, Humidity Frequency

VMT Average Speeds Ethanol Stringency, Fractions (PPSUITE) Volume Waiver Rate, (PPSUITE) Compliance

Road Type Hourly Refueling Distribution Distributions Controls (PPSUITE)

R amp Fraction (PPSUITE)

Emission Rates

### Appendix D

- 1 5 

# Vehicle Miles of Travel (VMT)

The VMT input to emissions calculations for Pennsylvania is based on information from the Roadway Management System (RMS) maintained by the Pennsylvania Department of Transportation’s (Penn DOT’s ) Bureau of Planning and Research (BPR) . P ennD OT obtains this information from periodic visual and electronic traffic counts. RMS data is dynamic

, since it is continually reviewed and updated from new traffic coun ts and field visits conducted by PennDOT. Information on roadways included in the National Highway System is reviewed at least annually, while information on other roadways is reviewed at least biennially.

On a triennial basis, a current “snapshot” of t he RMS database is taken and downloaded to provide an up

to

- date record of the Commonwealth’s highway system for estimating emissions. This emissions inventory is based on the most current snapshot of the RMS data.

The RMS database contains all state hi ghways, including the Pennsylvania Turnpike, divided into segments approximately 0.5 miles in length. These segments are usually divided at important intersections or locations where there is a change in the physical characteristics of the roadway (e.g. t he number of lane s changes). There are approximately 120 ,000 state highway segments for the 67 Pennsylvania counties contained in the RMS. Each of these segments contains an abundance of descriptive data, but only the following information is extracted f or emission calculations:

• Lanes

.

• Distances

.

• Volumes representing Average Annual Daily Traffic (AADT)

.

• Truck percentages

.

• Penn DOT urban/rural classifications

.

• Penn DOT functional class codes

.

• Number of signals (based on linkage to PennDOT GIS signal location data).

RMS volumes and distances are used in calculating highway VMT totals for each county. As discussed in the next section, adjustments are needed to convert the volumes to an average summer weekday, winter weekday, and monthly day. In addition, the traffic volumes must be forecast to support future year emission inventories. Lane values and traffic signals are an important input for determining the congestion and speeds for individual highway segments. Truck percentages are used in the spe ed determination process and are used to split volumes to individual vehicle types used by the MO VES software.

R oad segments are classified by function, as well as whether it is located in an urban, small urban or rural area, as indicated below in Exhibit 3 . The P enn DOT urban/rural (UR) and functional classes (FC) are important indicators of the type and function of each roadway segment. The variables provide insights into other characteristics not contained in the RMS data that are used for speed and emission calculations.

### Appendix D

- 1 6 

## Exhibit 3 : PennDOT Urban/Rural and Functional Class Codes

Urban/Rural Code 1=Rural 2=Small Urban 3=Urban

Functional Class Rural Functional Classes Used Urban Functional Classes Used For Rural Areas For Small Urban and Urban Areas

------------------------------------- ------------------------------------------ 1=Rural Freeway 11=Urban Freeway 2=Rural Other Principal Arterial 12=Urban Expressway 6=Rural Minor Arterial 14=Urban Principal Arterial 7=Rural Major Collector 16=Urban Minor Arterial 8=Rural Minor Collector 17=Urban Collector 9=Rural Local 19=Urban Local



### Additional Network Information: The PPSUITE software system allows for many additional variables other than those available in the RMS database. Using these variables improves the ability of the Department to incorporate real roadway conditions into its estimates. The variables include information regarding free

- flow speeds and capacities, signal characteristics and other physical roadway features that can affect a roadway’s calculated congested speed. This data can be determined from lookup tables based on a road way segment’s urban/rural code and functional class. Much of the lookup table data was developed from i nformation contained in the Highway Capacity Manua l

, PennDOT information on speeds and signal densities , and other engineering judgment.

MOVES Traffic Inputs: The PPSUITE software uses RMS traffic data to prepare key inputs to the MOVES emission model including :

• VMT

.

• T ravel speeds

.

• Road type distributions.

• Ramp fractions.

VMT is the primary traffic input that affects emission results. The roadway segment distances and traffic volumes are used to prepare estimates of VMT. PPSUITE performs these calculations and outputs the MOVES annual VMT input file to the CDM.

Emissions for many pollutants (including both VOC and NOx ) vary significantly with travel speed. While VOCs generally decrease as speed increases, NOx decreases at the low speed range and increases at higher speeds

, as illustrated in Exhibit 4

. To obtain the best estimate of vehicle speeds

, the Department uses the PPSUITE set of progra ms, whose primary function is to calculate speeds and to organize and simplify the handling of large amounts of data needed for calculating speeds and for preparing MOVES input files . The PPSUITE software prepares the MOVES vehicle hours of travel (VHT) b y speed bin file which summarizes the distribution of speeds across all links into each of 16 MOVES speed bins for each hour of the day. This robust process ensures that MOVES emission rates are used to the fullest extent and is consistent with the method s and recommendations provided in EPA’s 

## Using MOVES to Prepare Emission Inventories in State Implementation Plans and Transportation Conformity: Technical Guidance for MOVES2010, 2010a and 2010b

.

### Appendix D

- 1 7 

## Exhibit 4: Emission Factor vs. S peed Variances (NOx)

In MOVES, typical drive cycles and associated operating conditions vary by the type of roadway. MOVES defines five different road types as follows:

1 Off

- Network

. 2 Rural Restricted Access

. 3 Rural Unrestricted Access

. 4 Urban Restricted Access

. 5 Urban Unrestrict ed Access

.

The off

- network road type includes emissions from vehicle starts, extended idle activity, and evaporative emissions. Off

- network activity in MOVES is primarily determined by the Source Type Population input, as discussed in a following section

. The remaining distribution among road types is determined by equating the PennDOT functional class with each MOVES road type as follows:

• MOVES Road Type (2) = PennDOT Functional Class (1).

• MOVES Road Type (3) = PennDOT Functional Class (2,6,7,8,9).

• MOVES Road Type (4) = PennDOT Functional Class (11,12).

• MOVES Road Type (5) = PennDOT Functional Class (14,16,17,19).

For this inventory, the MOVES road type distribution file is automatically generated by PPSUITE using the defined equivalencies.

Since r amps are not directly represented within the RMS database information, it is assumed that 8% of the Freeway V H T is Ramp V H T. This is consistent with the recommendations provided in EPA’s
t echnical guidance. Source: Figure 3 from Implications of the MOVES2010 Model on Mobile Source Emission Estimates, Air & Waste Management Association, July 2010.

### Appendix D

- 1 8 

# Adjustments to Roadway Data

Before the RMS data can be used by PPSUITE for speed and emission calculations, several adjustments and additions must be made to the roadway data. These adjustments are summarized below.

HPMS Adjustments : According to EPA guidance, baseline inventory VMT computed from the RMS highway segment volumes must be adjusted to be consistent with Highway Performance Monitoring System (HPMS) VMT totals. The HPMS VMT reported for Pennsylvania is a subsystem of the RMS established to meet the data reporting requirements of the Fede ral Highway Administration (FHWA) and to serve as P enn DOT’s official source of highway information. Although it has some limitations, the HPMS system is currently in use in all 50 states and is being improved under FHWA direction.

Although the HPMS VMT and the roadway data used for an inventory emissions analysis are both based on data from the RMS system, differences do exist between them and include the following. First, the HPMS and inventory roadway data are “snapshots” of the RMS data taken at different times. Since the RMS is dynamic, changing constantly due to new data, differences will result between the data used for calculating HPMS VMT totals and the inventory data used for an emissions analysis. Second

, since the RMS does not contain many of the local roadways, local road estimates of HPMS VMT are obtained through alternative procedures developed by P enn DOT

. To account for such differences, adjustment factors are calculated and used to adjust the inventory roadway data to the reported HPMS VMT totals submitted to FHWA. The VMT contained in the HPMS reports are considered to represent average annual daily traffic (AADT).

Adjustment factors are calculated which adjust the base year RMS download VMT to the reported HPMS totals for that year. These factors are developed for each county and functional class combination and are also applied to all future year runs. Adjustments for the “higher” functional classes (e.g. Freeway, Arterials - major routes) are close to 1.000 since HPMS VMT is deriv ed from RMS information, and the only difference in the data is that the “snapshot” for the emission calculations is taken at a different time than for the HPMS. “Lower” classes (e.g. local roads) require greater adjustment since a large part of the local system is not under state jurisdiction and is not in the RMS database. There is, of course, a significant amount of local road mileage in the state. It is assumed that those local streets that are in RMS are representative of all local streets in their a rea with respect to volume and speed, so that roadway mileage adjustment is appropriate.

Seasonal Adjustments to Volumes : The RMS contains AADT volumes that are an average of all days in the year

, including weekends and holi days. An ozone emission analysis, however, is based on a typical July or summer weekday. PM and CO analyses require volumes representing a typical summer or winter weekday and monthly average conditions (needed for producing annual totals). Therefore, the RMS volumes must be seasonally adjusted. Seasonal factors were developed for each functional class and urban/rural code based on yearly count information prepared by P enn DOT’s B PR . These factors are applied to the existing RMS AADT volumes to produc e the July volumes. The same factors are also use d to develop the MOVES daily and monthly VMT fraction files.

Hourly Adjustments : Speeds and emissions vary considerably depending on the time of day

. Therefore, it is important to estimate the pattern by which roadway volume varies by hour of the day. The 24- hour pattern data provides PPSUITE with information used to split the daily roadway segment volumes to each of the 24 hours in a day. Pattern data is in the form of a percentage of the daily volumes for each hour. Distributions are provided for each county and functional class grouping. This data is developed from 24

- hour count data compiled by PennDOT’s B PR , according to the process in the agencies annual traffic data reports. The same factors are also used to develop the MOVES hourly fraction file.

### Appendix D

- 1 9 

# Vehicle Type Processing

Emission rates within MOVES vary significantly by the type of vehicle. The MOVES model produces emissions and rates by thirteen MOVES vehicle source types. However, VMT is in put to MOVES by six HPMS vehicle groups. Exhibit 5 summarizes the distinction between each classification scheme.



## Exhibit 5 : MOVES Source Types and HPMS Vehicle Groups

SOURCE TYPES HPMS Class Groups 11 Motorcycle 10 M otorcycle 21 Passenger Car 20 Passenger Car 31 Passenger Truck 30 Passenger/Light Truck 32 Light Commercial Truck 40 Buses 41 Intercity Bus 50 Single Unit Trucks 42 Transit Bus 60 Combination Trucks 43 School bus 51 Refus e 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



### The process used for this inventory includes a method to disaggregate the RMS traffic volumes to the thirteen source types and then to recombine the estimates to the six HPMS vehicle classes. V ehicle type pattern data is used by PPSUITE to divide the hou rly roadway segment volumes to the thirteen MOVES source types. Similar to the 24

- hour pattern data, this data contains percentage splits to each source type for every hour of the day. The vehicle type pattern data for this inventory is developed from se veral sources of information:

• Penn DOT truck percentages from the RMS database

.

• Hourly distributions for trucks and total traffic compiled by PennDOT’s B PR

.

• Transit data from PennDOT and the N ational T ransit D atabase

.

• S chool bus registration data from Penn DOT’s Bureau of Motor Vehicles Registration Database

. The vehicle type pattern data is developed for each county and functional class combination. First, RMS truck percentages are averaged for all roadways within a county and functional class grouping. Using this percentage data, the total roadway volume for any segment is divided to auto and truck vehicle type categories. The transit data and school bus data is used to further disaggregate trucks

, resulting in four vehicle groups (light -duty, school, transit, and other heavy -duty).

From these groups, MO VES default Pennsylvania county VMT distribution s by source type are used to divide the four groups into each of the MO VES source type s. P enn DOT hourly distr ibutions for trucks and total traffic are used to create source type percentage breakdowns for each hour of the day.

Vehicle Type Capacity Analysis Factors : Vehicle type percentages are provided to the capacity analysis section of PPSUITE to adjust the speeds in response to trucks. That is, a given number of larger trucks take up more roadway space than a given number of cars, and this is accounted for in the speed estimation process by adjusting capacity using information from the Highway Capacity Man ual

.

### Appendix D

- 1 10 

# Vehicle Fleet and Population Data

The information on the vehicle fleet including the number and age of vehicles has a significant impact on forecasted start and evaporative emissions within MOVES. The MOVES Model requires the population of vehicles by the thirteen source type categories

. Pennsylvania county vehicle registration data is used to estimate vehicle populat ion for light

- duty vehicles, school buses and transit buses . The data is split to source types using MOVE S default P ennsylvania county population data . O ther heavy

- duty vehicle population values are based on VMT for each source type using the vehicle mix and pattern data discussed previously. The PPSUITE software automatically applies default MOVES ratios o f VMT and source type population (e.g. the number of mi les per vehicle by source type) to the local VMT estimates to produce vehicle population.

Vehicle Age : Vehicle age distributions are input to MO VES for each county by the thirteen source types. The distributions reflect the percentage of vehicles in the fleet up to 31 years old. The most recent available registration download from PennDOT’s Bureau of Motor Vehicles Registration Database has been used for the inventory. Due to insufficient dat a, only information for light

- duty vehicles are used as local inputs; and, heavy

- duty vehicles use the MOVES2010 national default age distribution . The registration data download is based on MOBILE6.2 vehicle categories. As a result, the data was
convert ed to source types using the EPA convertor spreadshe ets provided with the MOVES emission model.



# Environmental, Fuel and Technology Assumptions

Information on environmental, fuel, vehicle technology and other control strategy assumptions were determined based on a review of MOVES 2010b default information by the PaDEP.

Fuel Parameters : The same vehicle will produce different emissions using a different type of gasoline. Fuel control strategies can be powerful emission reduction mechanisms

. The MOVES2010b default fuel formulation and fuel supply data were reviewed and updated based on available local volumetric fuel property information. The gasohol market penetration and RVP values were updated but MOVES 2010b default data was used for the remaining para meters.

Refueling Emissions : MO VES also allows users to calculate refueling emissions, the emissions created when vehicles are refueled at service stations. Pennsylvania includes refueling emissions in its area source inventory and not in its highway v ehicle inventory. R efueling emissions are not included in the highway emissions inventory.

Vehicle Emission Inspection/Maintenance (I/M) Parameters : MO VES allows users to vary inputs depending on the I/M program in place for the area. The inputs includ e:

• P rogram start year

.

• S tringency level

.

• F irst and last model years subject to the program

.

• W aiver rates

.

• Co mpliance rates

.

• P rogram type (test -only, test-and- repair, etc.) and effectiveness

.

• F requency of inspection (annual, biennial)

.

• V ehicle type coverage

.

• T est type (idle, loaded, etc.)

### Appendix D

- 1 11 

### The MOVES default P ennsylvania assumptions were reviewed and modifications were made per actual program parameters.

Environmental Variables : Ambient temperature and humidity are known to have a significant impact on most pollutant processes for on

- road vehicles. In MOVES2010, temperature and humidity affect emissions through three mechanisms: 1) direct effect via a temperature adjustment on emission rates; 2) direct effect via a humidity correction factor for NOx; 3) indirect effect via an air conditioning adjustment for which temperature and relative humidity are used to populate a heat index which in turn is used to calculate the fraction of v ehicle fleet with air conditioning turned on. Hourly temperatures have been compiled for each county based on information from WeatherBank, Inc. to specify temperatures from nine airports within the state

. Ozone analysis temperature and humidity values were determined using the procedures documented in EPA’s technical guidance. Minimum and maximum temperatures for each month were converted to hourly temperatures using EPA convertors supplied with the MOVES model.

A summary of the MO VES related inputs u sed for the inventory and future year estimates are attached with the submission.

### Appendix D

- 1 12 

# SPEED/EMISSION ESTIMATION PROCEDURE

The previous sections have summarized the input data used for computing speeds and emission s for Pennsylvania. This section explains how PPSUITE and MO VES uses that input data to produce emission estimates. Exhibit 6 summarizes PPSUITE’s analysis procedure used for each of the RMS highway segments in the state.

Producing an emissions inventory with PPSUITE requires a process of disaggregation and aggregation. Data is available and used on a very small scale

-- individual 1⁄2 mile roadway segments 24 hours of the day. This data needs to be processed individually to determine the distribution of vehicle hours of travel (VHT) by speed and then aggregated by vehicle class to determine input VMT to the MOVES emission model.



# Volume/VMT Development

Before speeds can be calculated and MO VES run, volumes acquired from RMS must be adjusted and disaggregated. Such adjustments include factoring to future years, seasonal adjustments, and disaggregating daily volumes to each hour of the day and to each of the thirteen MO VES source types.

Determine Future Year Volumes : The RMS database contains up

- to

- date current year volumes. However, t o conduct a future year analysis, these volumes must be factored to the year being analyzed. Growth factors have been prepared for each county and functional class grouping. These growth factors are applied to the base year RMS volumes to obtain future year estimates that can be utilized by PPSUITE. For this base year inventory, forecasting was not required.

Example:

A typical freeway link in the RMS database is I

- 80 segment 2500 in Luzerne County, Pennsylvania . This link has an urban/rural code=1 which indicates the link is in a rural area, and a functional class=1 indicating a rural freeway.

The average annual daily traffic (AADT) from the RMS database for this link in 200 8 is 12,077 vehicles/day.

Growth factors have been developed to factor the 200 8 volume to future years. For example, to factor the 200 8 volume to the year 20 14 , a growth factor of 1.282 would yield:

2014 volume = 12,077 vehicles/day x 1.282 = 15,483 vehicles/day

### Appendix D

- 1 13 

## Exhibit 6 : PPSUITE Speed / Emission Estimation Procedure

Data From PPSUITE Input Files PPSUITE Analysis Process Data from Roadway Source (RMS)

The Following is Performed For Each RMS Roadway Segment

Percent Pattern Distributions Expand to 24 hourly volumes RMS AWDT Adjusted Volumes

Apply VMT Adjustments Adjust Volumes for Peak Spreading (V/C thresholds for spreading)

Vehicle Type Patterns Disaggregate to Vehicle Type RMS Truck Percentages

T ransit D ata School Bus Data
Calculate Link & Signal Capacities Roadway Attributes (Lanes, FC code, UR code) Speed/Capacity Lookup Table Calculate Link Calculate Midblock Speed Approach Delay

Apply Post Speed VMT Adjustments

Prepare MOVES CDM Files

VHT by Annual Road Type Source Type Hourly Ramp Speed Bin V MT Fractions Population Fractions Fractions Per VMT < Default >

< Trucks >



### Off

- line File Preparation

Vehicle Age Distribution

Hourly Run MOVES Importer Temps/Humidity to convert county input data into MYSQL data format I/M / Fuel Parameters

Source Type

Population Run MOVES Month/Day VMT Fractions

### Appendix D

- 1 14 

### Seasonal Adjustments : PPSUITE takes the input daily volumes from RMS ( which represent s annual average daily traffic ( AADT )) and seasonally adjusts the volumes to an average weekday in July. This adjustment utilizes factors developed for each functional class and urban/rural code. VMT can then be calculated for each link using the adjusted weekday volumes.

Example:

A gain, assume the rural freeway link: I

- 80 segment 2500 in Luzerne County, Pennsylvania. The AADT for this link in 2008 is 12,077 vehicles/day.

Seasonal factors have been developed for urban/rural code and functional class combinations. For an urban/ rural code=1 and a functional class=1, the factor to convert from AADT to an average weekday in July is = 1.15

.
Average Weekday July Volume = 12,077 x 1.15 = 13,889 vehicles/day

.
Total VMT (daily) for this link is calculated as volume x distance. The distance of this link as obtained from RMS is 0.2 9 6 miles.

2008 VMT = 13,889 vehicles/day x 0.296 miles = 4,111 vehicle

- miles / day

.



### Disaggregation to 24 Hours : After seasonally adjusting the link volume, the volume is split to each hour of the day. T his allows for more accurate speed calculations (effects of congested hours) and allows PPSUITE to prepare the hourly VMT and speeds for input to the MOVES model.

Example:

To support speed calculations and emission estimates by time of day, the July weekday volume is disaggregated to 24 hourly volumes. Temporal patterns were previously developed from P enn DOT count data and input to PPSUITE. For the I

- 80 rural freeway link with morning peak volumes similar to evening peak hours (neutral), the followi ng temporal pattern is applied:

0 1 2 3 4 5 6 7 8 9 101357911131517192123 Hour of DayPercent of Daily



### Using the I

- 80 segment, typical hourly volumes which result include: 8- 9 a.m. 6.0% x (4,111 vehicle miles/ 0.296mi.) = 833 vehicles/hour (vph) 12

- 1 p.m. 5.0% x (4,111 vehicle .miles/ 0.296mi.) = 694 vph 5- 6 p.m. 6.3% x (4,111 vehicle miles/ 0.296mi.) = 875 vph

### Appendix D

- 1 15 

### After dividing the daily volumes to each hour of the day, PPSUITE identifies hours that are unreasonably congested. For those hours, PPSUITE then spreads a portion of the volume to other hours within the same peak period, thereby approximating the “peak spreading” that normally occurs in such over- capacity conditions.

Disaggregation to Vehicle Type : EPA requires VMT estimates to be prepared by source type, reflecting
spec ific local characteristics. As a result, for Pennsylvania’s emission inventory runs, the hourly volumes are disaggregated to the thirteen MOVES source types based on count data assembled by P enn DOT in combination with MOVES defaults.

Example:

Disaggreg ation of the total I

- 80 VMT to the various source types would include the following:

Total Volume 8

- 9 am = 833 vph

Source Type Volume 8

- 9 am: Motorcycle 11 0.5% 4 vph Passenger Car 21 54.7% 456 vph Passenger Truck 31 27.9% 232 vph Light Commercial Truck 32 9.3% 78 vph Intercity Bus 41 0.1% 1 vph Transit Bus 42 0.1% 1 vph School bus 43 0.1% 1 vph Refuse Truck 51 0.0% 0 vph Single Unit Short

- haul Truck 52 2.2% 19 vph Single Unit Long

- haul Truck 53 0.3% 2 vph Motor Home 54 0.1% 1 vph Combination Short

- haul Truck 61 1.9% 16 vph Combination Long

- haul Truck 62 2.6% 22 vph



# Speed/Delay Determination

EPA recognizes that the estimation of vehicle speeds is a difficult and complex process. Because emissions are so sensitive to speeds, it recommends special attention be given to developing reasonable and consistent speed estimates; it also recommends that VMT be disaggregated into subsets that have roughly equal speed, with separate emission factors for each subset. At a minimum, speeds should be estimated separately by road type.

The computational framework used for this analysis meets and exceeds that recommendation. Speeds are individually calculated for each roadway segment and hour and include the delays encountered at signals. Rather than accumulating the roadway segments into a particular road type and calculating an average
spe ed, each individual link hourly speed is represented in the MOVES vehicle hours of travel (VHT) by speed bin file. This MOVES input file allows the specificat ion of a distribution of hourly speeds.

For example, if 5% of a county’s arterial V H T operate s at 5 mph during the AM peak hour and the remaining 95% operate s at 65 mph, this can be represented in the MOVES speed input file. For the model runs, distributions of speeds are input to MOVES by road type and source type by each hour of the day; VMT and VHT is accumulated by the same groupings for the application of the emission factors to produce resulting emission totals.

### Appendix D

- 1 16 

### To calculate speeds, PPSUITE first obtains initial capacities (how much volume the roadway can serve before heavy congestion) and fr ee

- flow speeds (speeds assuming no congestion) from the speed/capacity lookup data. As described in previous sections, this data contains default roadway information indexed by the urban/rural code and functional class. For areas with known characteristi cs, values can be directly coded to the RMS database and the speed/capacity data can be overridden. However, for most areas where known information is not available, the speed/capacity lookups provide valuable default information regarding speeds, capacit ies, signal characteristics, and other capacity adjustment information used for calculating congested delays and speeds. An effort has been made to enhance the RMS data with traffic signal locations using other GIS signal data available from PennDOT’s Bur eau of Highway Safety and Traffic Engineering.

Example:

The speed/capacity lookup table is used to obtain important data used for link speed calculations. For the I

- 80 link with an urban/rural code = 1 (rural) and a functional class = 1 (freeway), the lookup table provides information including the following:

freeflow speed = 65 mph capacity = 1800 vph per lane number of signals = 0 (per RMS linkage to GIS traffic signal locations)

This information is used along with the physical characteristics of the roadway to calculate the delay (including congestion) to travel this link during each hour of the day:

For example: The I

- 80 link is calculated to have a travel time, including delay of 17.76 seconds for the 8

- 9am hour

.
Total travel time, in vehic le hours, for the 8

- 9am hour is calculated as:

VHT (8

- 9am) = 17.76 seconds x 833vph / 3600 sec/hr = 4.12 vehicle hours

.



### The result of this process is an estimated average travel time for each hour of the day for each highway segment. The average ti me can be multiplied by the volume to produce vehicle hours of travel (VHT).



# HPMS and VMT Adjustments

Volumes must also be adjusted to account for differences with the HPMS VMT totals, as described previously. VMT adjustment factors are provided as input to PPSUITE, and are applied to each of the roadway segment volumes. These factors were developed from the latest HPMS download (conducted triennially) ; however, they are also applied to any future year runs. The VMT added or subtracted to the RMS database assumes the speeds calculated using the original volumes for each roadway segment for each hour of the day.

### Appendix D

- 1 17 Example:

Using the Luzerne County I

- 80 rural freeway link example, the daily assigned volume is adjusted to account for reconciliation with the HPMS VMT. RMS VMT (in AADT) for Luzerne County rural freeways totals 962,559 vehicle miles in 2008. HPMS VMT (in AADT) as supplied by P enn DOT and reported to FHWA totals to 990,088 vehicle miles for the rural freeways. A factor is developed by dividing the HPMS VMT by the RMS VMT:

HPMS adjustment factor for Luzerne County rural freeways = 990,088 / 9 62,559 = 1.029

.
This factor is held constant in all future years. As an example, this adjustment is made to the I- 80 freeway link VMT for the 8

- 9am hour after speed calculations are made, and produces the final July weekday VMT for this hour used for Ozone runs.

I- 80 Link VMT (8

- 9am) = 833vph x 0.296 miles x 1.029 = 254 vehicle miles /hour

.



# MO VES Emissions Run

After computing speeds and aggregating VMT and VHT, PPSUITE prepares traffic

- related inputs needed to run EPA’s MOVES software, which i s used to estimate emission factors in grams of pollutant per vehicle mile and to produce total emissions based on input VMT to the model. The process uses MOVES2010b, the officially released emissions model that was obtained directly from EPA.

The MOV ES inputs prepared by PPSUITE include the following:

• Vehicle Type VMT

.

• Vehicle Population

.

• VMT fractions

.

• Average speed distributions

.

• Road Type Distribution

.

• Ramp Fractions

.

These files are text formatted files with a *.csv extension. The files are provided as input s within the MOVES county data importer. In addition the remaining MOVES input data including temperatures, I/M programs, fuel and vehicle ages are prepared manually outside of the PPSUITE process.

The MOVES county importer is run in batch mode. This program converts all data files into the MYSQL formats used by the MOVES model. At that point a MOVES run specification file (*.mrs) is created which specifies options and key data locations for the run. MOVES is then executed in batch mode.

MOVES can be executed using either the inventory or rate -based approaches. For this highway emissions inventory, MOVES is applied using the inventory- based approach. Under this method, actual VMT and population are provided as input s to the model ; MOVES is responsible for producing the total emissions for the region. Under the rate

- based approach, MOVES would produce emission factors , after which PPSUITE would apply the emission factors to the link data and calculate total regional emissions.

### Appendix D

- 1 18 

# RESOURCES

MO VES model

Modeling Page within EPA’s Office of Mobile Sources Website (http://www.epa.gov/omswww/models.htm) contains a downloadable model, MO VES users guide and other information.

Policy Guidance on the Use of MOVES2010 and Subsequent Minor Revisions for State Implementation Plan Development, Transportation Conformity, and Other Purposes , US EPA Office of Transportation and Air Quality , EPA -420-B-12-010, April 2012.

Using MOVES to Prepare Emission Inventories in State Implementation Plans and Transportation Conformity: Technical Guidance for MOVES2010, 2010a and 2010b . US EPA Office of Transportation and Air Quality , EPA -420-B-12- 028, April 2012.

Motor Vehicle Emission Simulator (MOVES) – User Guide for MOVES2010b , US EPA Office of Transportation and Air Quality, EPA-420-B-12-001b, June 2012.

Traffic Engineering

Highway Capacity Manual, Transportation Research Board, presents current knowledge and techniques for analyzing the transportation system.

Traffic Data Collection and Factor Development Report, 2011 Data, Pennsylvania Department of Transportation, Bureau of Planning and Research.

### Appendix D

- 1 19 

# Highway Vehicle Inventory Glossary

AADT: Average Annual Daily Traffic, average of ALL days.

AWDT: Average Weekday Daily Traffic

.

Basic em ission rates: MOBILE emission rates based on the applicable Federal emission standards and the emission control technologies characterizing the fleet in various model years.

Emission rate or factor: Expresses the amount of pollution emitted per unit of activity. For highway vehicles, usually in grams of pollutant emitted per mile driven.

FC: Functional code, applied in data management to road segments to identify their type (freeway, local, etc.)

.
Fuel volatility: The ability of fuel components to evaporate, thus entering the atmosphere as pollution. Fuel volatility is usually measured as Reid Vapor Pressure (RVP) in pounds per square inch. The lower the RVP, the less volatile the fuel.

Growth factor: Factor used to convert volumes to future years.

HPMS: Highway Performance Monitoring System, PENNDOT’s official source of highway information and a subset of RMS.

I/M: Vehicle emissions inspection/maintenance programs ensure that vehicle emission controls are in good working order throughout the life of the vehicle. The programs require vehicles to be tested for emissions. Most vehicles that do not pass must be repaired.

MOBILE: The model EPA has developed and which Pennsylvania uses to estimate emissions from highway vehicles.

MOVES: The latest model EPA has developed with which Pennsylvania uses to estimate emissions from highway vehicles.

Pattern data: Extrapolations of traffic patterns (such as how traffic volume on road segment types varies by time of day, or what kinds of vehicles tend to use a road segment type) from segments with observed data to similar segments.

PPSUITE: Post

- Processor for Air Quality, a set of programs that estimate speeds and processes MOBILE emission rates.

R MS: Roadway Management System, a database maintained by PENNDOT from traffic counts and field visits

.
Segment (also referred to as link) : Di vision of roadway in the PENNDOT Roadway Management System. Usually represents 0.5 mile segments of roadway.

UR: Urban/rural code, applied in data management to identify whether a road segment is urban, small urban or rural.

### Appendix D

- 1 20 

### VHT: V ehicle hours traveled

.

VMT: V ehicle miles traveled. In modeling terms, it is the simulated traffic volumes times link length

.
Vehicle Type : One of eight types, distinguished primarily by fuel type and/or weight, used in MOBILE modeling.

Source Type : One of thirteen types, distinguished primarily by weight, used in MOVES modeling.

Road Type: Functional code, applied in data management to road segments to identify their type (rural/urban highways, rural/urban arterials, etc.)

County Data Manager: U ser interface developed to simplify importing specific local data for a single county or a user-defined custom domain without requiring direct interaction with the underlying MySQL database.

# APPENDIX D-2

Emission Results

# APPENDIX D-2-1 Allentown-Bethlehem-Easton Area Emission Summary Tables

Appendix D-2-1-1 2011 July Weekday Emissions

Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process



## Appendix D-2-1-2 2011 Annual Emissions

Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process

## Appendix D-2-1-1
2011 Allentown-Bethlehem-Easton Area Area Emission Summary
Summer Weekday (Tons/Day)

County VMT Speed (mph) VOC NOX CO

Lehigh 9,251,839 40.9 8.24 17.13 85.53 Northampton 6,306,177 39.7 7.00 14.04 65.30 Lehigh Valley MPO 15,558,016

- 15.24 31.17 150.83

Carbon 2,387,690 46.3 1.94 4.39 21.76

Appendix D-2-1 2

### Appendix D-2-1-1 2011 Allentown-Bethlehem-Easton Area Emission Summar y

b y Road T yp e Summer Weekday (Tons/Day)

Count y Road Type V MT Speed (mph) V OC NOX CO Lehigh Off-Network - - 5.39 3.62 30.65 Rural Restricted Access 298,962 64.82348912 0.08 0.68 1.87 Rural Unrestricted Access 648,919 42.59254052 0.19 0.92 3.41 Urban Restricted Access 3,316,660 56.08611836 0.87 4.96 21.46 Urban Unrestricted Access 4,987,297 33.81275214 1.71 6.95 28.15 Tota l 9,251,83 9 8.24 17.1 3 85.5 3

Count y Road Type V MT Speed (mph) V OC NOX CO Northampton Off-Network - - 4.97 3.36 28.33 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 763,892 46.56189936 0.21 1.09 3.91 Urban Restricted Access 2,227,709 56.8719825 0.62 4.85 13.93 Urban Unrestricted Access 3,314,576 32.15179852 1.19 4.74 19.12 Tota l 6,306,17 7 7.0 0 14.04 65.3 0

Count y Road Type V MT Speed (mph) V OC NOX CO Carbon Off-Network - - 1.25 0.85 7.16 Rural Restricted Access 1,113,829 64.89380015 0.28 1.68 7.40 Rural Unrestricted Access 799,013 37.1415114 0.26 1.19 4.47 Urban Restricted Access 31,845 59.79114797 0.01 0.04 0.21 Urban Unrestricted Access 443,003 35.70416377 0.15 0.63 2.51 Tota l 2,387,69 0 1.94 4.3 9 21.7 6

Appendix D-2-1 3Appendix D-2-1-1 2011 Allentown-Bethlehem-Easton Area Emission Summar y b y Source T y

pe Summer Weekday (Tons/Day)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Lehigh Motorcycle 49,795 0.5% 0.29 3.5% 0.04 0.2% 0.81 1.0% Passenger Car 5,016,615 54.2% 2.12 25.8% 3.11 18.1% 22.08 25.8% Passenger Truck 2,640,306 28.5% 3.98 48.3% 6.01 35.1% 43.14 50.4% Light Commercial Truck 893,392 9.7% 1.28 15.6% 2.25 13.2% 13.95 16.3% Intercity Bus 6,210 0.1% 0.00 0.0% 0.09 0.5% 0.03 0.0% Transit Bus 13,641 0.1% 0.01 0.1% 0.15 0.9% 0.13 0.2% School Bus 5,605 0.1% 0.01 0.1% 0.04 0.2% 0.12 0.1% Refuse Truck 4,595 0.0% 0.00 0.0% 0.04 0.2% 0.02 0.0% Single Unit Short-haul Truck 202,859 2.2% 0.19 2.3% 0.89 5.2% 3.18 3.7% Single Unit Long-haul Truck 28,540 0.3% 0.02 0.3% 0.11 0.7% 0.32 0.4% Motor Home 12,229 0.1% 0.02 0.3% 0.06 0.4% 0.38 0.4% Combination Short-haul Truck 157,402 1.7% 0.07 0.9% 1.52 8.9% 0.44 0.5% Combination Long-haul Truck 220,650 2.4% 0.23 2.8% 2.82 16.5% 0.93 1.1% Total 9,251,839 100.0% 8.24 100.0% 17.13 100.0% 85.53 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Northampton Motorcycle 32,628 0.5% 0.25 3.6% 0.02 0.2% 0.54 0.8% Passenger Car 3,287,114 52.1% 1.79 25.6% 2.26 16.1% 16.04 24.6% Passenger Truck 1,730,056 27.4% 3.33 47.6% 4.37 31.1% 32.44 49.7% Light Commercial Truck 585,384 9.3% 1.07 15.2% 1.63 11.6% 10.65 16.3% Intercity Bus 7,950 0.1% 0.00 0.1% 0.11 0.8% 0.03 0.1% Transit Bus 11,370 0.2% 0.01 0.1% 0.13 0.9% 0.11 0.2% School Bus 6,257 0.1% 0.01 0.1% 0.05 0.3% 0.11 0.2% Refuse Truck 4,775 0.1% 0.00 0.0% 0.04 0.3% 0.02 0.0% Single Unit Short-haul Truck 208,999 3.3% 0.19 2.8% 0.90 6.4% 3.27 5.0% Single Unit Long-haul Truck 29,437 0.5% 0.02 0.3% 0.12 0.8% 0.33 0.5% Motor Home 12,599 0.2% 0.02 0.3% 0.06 0.5% 0.39 0.6% Combination Short-haul Truck 162,231 2.6% 0.07 1.0% 1.53 10.9% 0.45 0.7% Combination Long-haul Truck 227,376 3.6% 0.23 3.2% 2.83 20.1% 0.92 1.4% Total 6,306,177 100.0% 7.00 100.0% 14.04 100.0% 65.30 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Carbon Motorcycle 12,933 0.5% 0.06 3.2% 0.01 0.2% 0.22 1.0% Passenger Car 1,302,961 54.6% 0.54 27.6% 0.88 20.1% 6.16 28.3% Passenger Truck 685,917 28.7% 0.92 47.5% 1.56 35.6% 10.70 49.2% Light Commercial Truck 231,887 9.7% 0.29 15.2% 0.57 13.0% 3.39 15.6% Intercity Bus 1,012 0.0% 0.00 0.0% 0.01 0.3% 0.00 0.0% Transit Bus 1,899 0.1% 0.00 0.1% 0.02 0.5% 0.02 0.1% School Bus 792 0.0% 0.00 0.1% 0.01 0.1% 0.02 0.1% Refuse Truck 1,088 0.0% 0.00 0.0% 0.01 0.2% 0.00 0.0% Single Unit Short-haul Truck 48,676 2.0% 0.04 2.3% 0.21 4.8% 0.75 3.5% Single Unit Long-haul Truck 6,871 0.3% 0.00 0.2% 0.03 0.6% 0.08 0.3% Motor Home 2,931 0.1% 0.01 0.3% 0.02 0.3% 0.09 0.4% Combination Short-haul Truck 37,769 1.6% 0.02 0.8% 0.37 8.5% 0.10 0.5% Combination Long-haul Truck 52,953 2.2% 0.05 2.7% 0.69 15.6% 0.21 1.0% Total 2,387,690 100.0% 1.94 100.0% 4.39 100.0% 21.76 100.0% County Sourcetype County Sourcetype

County Sourcetype

Appendix D-2-1 4

### Appendix D-2-1-1 2011 Allentown-Bethlehem-Easton Area Emission Summar y

b y Proces s Summer Weekday (Tons/Day)

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Lehigh Running Exhaust 2.13 25.8% 13.51 78.8% 54.87 64.2% Start Exhaust 3.09 37.5% 3.03 17.7% 30.36 35.5% Evap Permeation 0.75 9.1% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 1.59 19.3% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.48 5.9% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.03 0.4% 0.00 0.0% 0.01 0.0%

Crankcase Start Exhaust 0.04 0.5% 0.00 0.0% 0.00 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.13 1.5% 0.60 3.5% 0.29 0.3% Total 8.24 100.0% 17.13 100.0% 85.53 100.0%

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Northampton Running Exhaust 1.53 21.8% 10.68 76.0% 36.96 56.6% Start Exhaust 2.84 40.5% 2.78 19.8% 28.05 43.0% Evap Permeation 0.68 9.8% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 1.35 19.3% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.41 5.9% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.02 0.3% 0.00 0.0% 0.01 0.0%

Crankcase Start Exhaust 0.04 0.5% 0.00 0.0% 0.00 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.12 1.8% 0.58 4.1% 0.28 0.4% Total 7.0 0 100.0 % 14.04 100.0 % 65.3 0 100.0 %

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct.
Carbon Running Exhaust 0.54 27.6% 3.54 80.6% 14.60 67.1%
Start Exhaust 0.76 39.2% 0.71 16.2% 7.10 32.6% Evap Permeation 0.15 7.6% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 0.35 17.9% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.10 5.4% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.01 0.4% 0.00 0.0% 0.00 0.0%

Crankcase Start Exhaust 0.01 0.5% 0.00 0.0% 0.00 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.03 1.5% 0.14 3.2% 0.06 0.3% Total 1.94 100.0 % 4.3 9 100.0 % 21.7 6 100.0 % County Emission Process

County Emission Process County Emission Process

Appendix D-2-1 5

## Appendix D-2-1-2 2011 Allentown-Bethlehem-Easton Area Area Emission Summar y Annual (Tons/Year)

County VMT Speed (mph) VOC NOX CO

Lehigh 2,988,096,138 42.1 2938.97 6154.43 37317.95 Northampton 2,046,098,683 40.5 2524.35 5086.83 30028.04 Lehigh Valley MPO 5,034,194,821

- 5463.32 11241.26 67345.98

Carbon 772,100,241 46.3 706.66 1592.35 9454.14

Appendix D-2-1 6

### Appendix D-2-1-2 2011 Allentown-Bethlehem-Easton Area Emission Summar y

b y Road T ype Annual (Tons/Year)

Count y Road Type V MT Speed (mph) V OC NOX CO Lehigh Off-Network - - 2,048.92 1,402.04 19,416.77 Rural Restricted Access 96,314,786 64.91911342 24.94 246.79 611.17 Rural Unrestricted Access 210,428,358 42.85132497 60.98 328.90 1,126.01 Urban Restricted Access 1,055,992,705 57.69505107 268.36 1,778.58 6,901.82 Urban Unrestricted Access 1,625,360,287 35.08715246 535.77 2,398.12 9,262.17 Tota l 2,988,096,138 2,938.97 6,154.43 37,317.95

Count y Road Type V MT Speed (mph) V OC NOX CO Northampton Off-Network - - 1,885.77 1,304.33 17,870.29 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 248,441,874 46.79265469 67.55 388.09 1,292.72 Urban Restricted Access 709,330,489 57.67880162 194.82 1,743.32 4,505.19 Urban Unrestricted Access 1,088,326,320 33.09706451 376.21 1,651.09 6,359.84 Tota l 2,046,098,683 2,524.35 5,086.83 30,028.04

Count y Road Type V MT Speed (mph) V OC NOX CO Carbon Off-Network - - 484.27 329.15 4,541.11 Rural Restricted Access 358,846,806 64.89525101 88.22 606.53 2,467.58 Rural Unrestricted Access 258,650,742 37.21297761 84.06 419.14 1,520.83 Urban Restricted Access 10,138,855 59.79114174 2.46 12.62 70.11 Urban Unrestricted Access 144,463,838 36.00571544 47.65 224.92 854.51 Tota l 772,100,241 706.66 1,592.35 9,454.14

Appendix D-2-1 7Appendix D-2-1-2 2011 Allentown-Bethlehem-Easton Area Emission Summar y b y Source T y

p e Annual (Tons/Year)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Lehigh Motorcycle 16,085,844 0.5% 80.48 2.7% 15.09 0.2% 398.27 1.1% Passenger Car 1,620,586,580 54.2% 844.85 28.7% 1,112.77 18.1% 11,251.83 30.2% Passenger Truck 852,934,440 28.5% 1,388.42 47.2% 2,136.88 34.7% 17,927.42 48.0% Light Commercial Truck 288,604,969 9.7% 449.98 15.3% 793.16 12.9% 5,833.32 15.6% Intercity Bus 1,816,899 0.1% 1.14 0.0% 29.25 0.5% 7.85 0.0% Transit Bus 4,527,742 0.2% 3.37 0.1% 56.95 0.9% 43.69 0.1% School Bus 1,860,327 0.1% 2.71 0.1% 16.20 0.3% 42.00 0.1% Refuse Truck 1,478,506 0.0% 0.72 0.0% 13.94 0.2% 6.84 0.0% Single Unit Short-haul Truck 65,322,029 2.2% 58.02 2.0% 323.96 5.3% 1,108.15 3.0% Single Unit Long-haul Truck 9,199,039 0.3% 6.56 0.2% 41.41 0.7% 117.56 0.3% Motor Home 3,935,589 0.1% 7.05 0.2% 23.55 0.4% 147.80 0.4% Combination Short-haul Truck 50,692,787 1.7% 23.09 0.8% 548.50 8.9% 141.14 0.4% Combination Long-haul Truck 71,051,388 2.4% 72.58 2.5% 1,042.78 16.9% 292.06 0.8% Total 2,988,096,138 100.0% 2,938.97 100.0% 6,154.43 100.0% 37,317.95 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Northampton Motorcycle 10,597,056 0.5% 67.65 2.7% 9.99 0.2% 278.41 0.9% Passenger Car 1,067,612,490 52.2% 726.69 28.8% 817.64 16.1% 8,967.40 29.9% Passenger Truck 561,899,430 27.5% 1,175.06 46.5% 1,561.63 30.7% 14,168.03 47.2% Light Commercial Truck 190,124,980 9.3% 378.87 15.0% 579.23 11.4% 4,669.84 15.6% Intercity Bus 2,348,746 0.1% 1.44 0.1% 37.34 0.7% 9.76 0.0% Transit Bus 3,796,036 0.2% 2.79 0.1% 48.19 0.9% 35.86 0.1% School Bus 2,088,938 0.1% 2.71 0.1% 17.77 0.3% 40.46 0.1% Refuse Truck 1,522,472 0.1% 0.73 0.0% 14.14 0.3% 6.91 0.0% Single Unit Short-haul Truck 67,247,719 3.3% 58.82 2.3% 331.32 6.5% 1,141.99 3.8% Single Unit Long-haul Truck 9,470,230 0.5% 6.64 0.3% 42.52 0.8% 121.58 0.4% Motor Home 4,053,974 0.2% 7.16 0.3% 24.30 0.5% 152.87 0.5% Combination Short-haul Truck 52,187,207 2.6% 23.27 0.9% 554.26 10.9% 142.19 0.5% Combination Long-haul Truck 73,149,406 3.6% 72.52 2.9% 1,048.50 20.6% 292.74 1.0%
Total 2,046,098,683 100.0% 2,524.35 100.0% 5,086.83 100.0% 30,028.04 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Carbon Motorcycle 4,181,966 0.5% 17.11 2.4% 4.12 0.3% 104.57 1.1% Passenger Car 421,317,211 54.6% 214.91 30.4% 319.88 20.1% 3,022.59 32.0% Passenger Truck 221,793,563 28.7% 328.41 46.5% 562.51 35.3% 4,453.85 47.1% Light Commercial Truck 74,981,666 9.7% 105.57 14.9% 204.41 12.8% 1,424.78 15.1% Intercity Bus 305,127 0.0% 0.19 0.0% 5.05 0.3% 1.38 0.0% Transit Bus 632,083 0.1% 0.49 0.1% 8.15 0.5% 6.53 0.1% School Bus 263,736 0.0% 0.47 0.1% 2.51 0.2% 7.97 0.1% Refuse Truck 353,046 0.0% 0.17 0.0% 3.43 0.2% 1.63 0.0% Single Unit Short-haul Truck 15,747,875 2.0% 13.70 1.9% 77.91 4.9% 264.24 2.8% Single Unit Long-haul Truck 2,220,764 0.3% 1.54 0.2% 9.90 0.6% 27.86 0.3% Motor Home 950,613 0.1% 1.65 0.2% 5.77 0.4% 36.27 0.4% Combination Short-haul Truck 12,211,006 1.6% 5.43 0.8% 134.83 8.5% 33.49 0.4% Combination Long-haul Truck 17,141,586 2.2% 17.00 2.4% 253.88 15.9% 68.98 0.7% Total 772,100,241 100.0% 706.66 100.0% 1,592.35 100.0% 9,454.14 100.0% County Sourcetype

County Sourcetype County Sourcetype

Appendix D-2-1 8Appendix D-2-1-2 2011 Allentown-Bethlehem-Easton Area Emission Summary by Process Annual (Tons/Year)

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Lehigh Running Exhaust 668.01 22.7% 4,751.48 77.2% 17,897.48 48.0% Start Exhaust 1,499.46 51.0% 1,163.71 18.9% 19,324.03 51.8% Evap Permeation 136.35 4.6% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 399.67 13.6% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 165.89 5.6% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 9.29 0.3% 0.91 0.0% 3.70 0.0%

Crankcase Start Exhaust 19.81 0.7% 0.04 0.0% 2.52 0.0% Crankcase Extended Idle Exhaust 0.61 0.0% 0.07 0.0% 0.16 0.0% Extended Idle Exhaust 39.88 1.4% 238.22 3.9% 90.06 0.2% Total 2,938.97 100.0% 6,154.43 100.0% 37,317.95 100.0%

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Northampton Running Exhaust 484.06 19.2% 3,781.64 74.3% 12,154.84 40.5% Start Exhaust 1,375.80 54.5% 1,068.67 21.0% 17,778.56 59.2% Evap Permeation 124.95 4.9% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 331.71 13.1% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 142.64 5.7% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 6.88 0.3% 0.87 0.0% 2.91 0.0%

Crankcase Start Exhaust 18.18 0.7% 0.04 0.0% 2.33 0.0% Crankcase Extended Idle Exhaust 0.61 0.0% 0.07 0.0% 0.16 0.0% Extended Idle Exhaust 39.52 1.6% 235.55 4.6% 89.24 0.3% Tota l 2,524.35 100.0% 5,086.83 100.0% 30,028.04 100.0%

VOC NOX CO
Emissions Pct. Emissions Pct. Emissions Pct. Carbon Running Exhaust 171.50 24.3% 1,262.98 79.3% 4,912.08 52.0% Start Exhaust 368.77 52.2% 273.29 17.2% 4,519.54 47.8% Evap Permeation 27.28 3.9% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 86.51 12.2% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 35.93 5.1% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 2.37 0.3% 0.22 0.0% 0.95 0.0%

Crankcase Start Exhaust 4.87 0.7% 0.01 0.0% 0.59 0.0% Crankcase Extended Idle Exhaust 0.14 0.0% 0.02 0.0% 0.04 0.0% Extended Idle Exhaust 9.28 1.3% 55.83 3.5% 20.95 0.2% Tota l 706.66 100.0% 1,592.35 100.0% 9,454.14 100.0% County Emission Process County Emission Process

County Emission Process

Appendix D-2-1 9

# APPENDIX D-2-2 Lancaster County Emission Summary Tables

Appendix D-2-2-1 2011 July Weekday Emissions

Emission Summary Emission Summary by Road Type Emission Summary by Source Type

Emission Summary by Process



### Appendix D-2-2-2 2011 Annual Emissions

Emission Summary Emission Summary by Road Type Emission Summary by Source Type

Emission Summary by Process

## Appendix D-2-2-1 2011 Lancaster County Emission Summary Summer Weekday (Tons/Day)

Count y V MT Speed ( mph ) V OC NOX CO

Lancaster 12,789,519 43.2 11.99 24.42 121.03

Appendix D-2-2 2

### Appendix D-2-2-1 2011 Lancaster County Emission Summary by Road Type Summer Weekday (Tons/Day)

Count y Road Typ e V MT Speed (mph) V OC NO X CO Lancaster Off-Network

- - 8.15 5.43 45.08 Rural Restricted Access 1,504,295 65.0 0.35 1.48 10.45 Rural Unrestricted Access 3,154,301 46.5 0.89 4.95 16.50 Urban Restricted Access 2,629,352 53.9 0.72 4.40 17.54 Urban Unrestricted Access 5,501,572 35.3 1.87 8.18 31.47 Tota l 12,789,519 11.99 24.42 121.03

Appendix D-2-2 3Appendix D-2-2-1 2011 Lancaster County Emission Summary by Source Type Summer Weekday (Tons/Day)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Lancaster Motorcycle 68,232 0.5% 0.43 3.5% 0.05 0.2% 1.12 0.9% Passenger Car 6,874,134 53.7% 3.08 25.7% 4.30 17.6% 30.64 25.3% Passenger Truck 3,617,944 28.3% 5.76 48.1% 8.36 34.2% 61.02 50.4% Light Commercial Truck 1,224,187 9.6% 1.85 15.4% 3.11 12.7% 19.82 16.4% Intercity Bus 8,475 0.1% 0.01 0.0% 0.12 0.5% 0.04 0.0% Transit Bus 15,047 0.1% 0.01 0.1% 0.15 0.6% 0.14 0.1% School Bus 4,434 0.0% 0.01 0.1% 0.03 0.1% 0.10 0.1% Refuse Truck 7,194 0.1% 0.00 0.0% 0.06 0.2% 0.03 0.0% Single Unit Short-haul Truck 316,435 2.5% 0.30 2.5% 1.34 5.5% 4.89 4.0% Single Unit Long-haul Truck 44,555 0.3% 0.03 0.3% 0.17 0.7% 0.49 0.4% Motor Home 19,074 0.1% 0.04 0.3% 0.09 0.4% 0.56 0.5% Combination Short-haul Truck 245,620 1.9% 0.11 0.9% 2.32 9.5% 0.70 0.6% Combination Long-haul Truck 344,188 2.7% 0.36 3.0% 4.33 17.7% 1.47 1.2% Total 12,789,519 100.0% 11.99 100.0% 24.42 100.0% 121.03 100.0% County Sourcetype

Appendix D-2-2 4

### Appendix D-2-2-1 2011 Lancaster County Emission Summary by Process Summer Weekday (Tons/Day)

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Lancaster Running Exhaust 2.90 24.2% 18.99 77.8% 75.94 62.7% Start Exhaust 4.58 38.2% 4.51 18.4% 44.61 36.9% Evap Permeation 1.20 10.0% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 2.30 19.2% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.70 5.8% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.04 0.3% 0.00 0.0% 0.02 0.0%

Crankcase Start Exhaust 0.06 0.5% 0.00 0.0% 0.01 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.20 1.7% 0.92 3.8% 0.46 0.4% Total 11.9 9 100.0 % 24.4 2 100.0 % 121.0 3 100.0 % County Process

Appendix D-2-2 5

## Appendix D-2-2-2 2011 Lancaster County Emission Summary Annual (Tons/Year)

Count y V MT Speed ( mph ) V OC NOX CO

Lancaster 4,150,294,966 44.2 4233.63 8879.12 52716.37

Appendix D-2-2 6

### Appendix D-2-2-2 2011 Lancaster County Emission Summary by Road Type Annual (Tons/Year)

Count y Road Typ e V MT Speed (mph) V OC NO X CO Lancaster Off-Network

- - 3,028.27 2,109.23 28,380.46 Rural Restricted Access 484,659,822 65.0 109.99 537.79 3,284.87 Rural Unrestricted Access 1,021,743,499 47.0 282.86 1,771.59 5,328.99 Urban Restricted Access 837,239,063 56.4 220.36 1,556.24 5,508.16 Urban Unrestricted Access 1,806,652,583 36.2 592.16 2,904.26 10,213.90 Tota l 4,150,294,966 4,233.63 8,879.12 52,716.37

Appendix D-2-2 7Appendix D-2-2-2 2011 Lancaster County Emission Summary by Source Type Annual (Tons/Year)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Lancaster Motorcycle 22,145,858 0.5% 116.19 2.7% 21.14 0.2% 554.97 1.1% Passenger Car 2,231,110,112 53.8% 1205.57 28.5% 1,551.72 17.5% 15,666.19 29.7% Passenger Truck 1,174,261,600 28.3% 1992.59 47.1% 2,993.74 33.7% 25,309.56 48.0% Light Commercial Truck 397,329,550 9.6% 643.87 15.2% 1,104.88 12.4% 8,273.06 15.7% Intercity Bus 2,519,853 0.1% 1.62 0.0% 39.32 0.4% 11.15 0.0% Transit Bus 5,048,422 0.1% 3.63 0.1% 59.36 0.7% 47.81 0.1% School Bus 1,487,526 0.0% 2.26 0.1% 12.38 0.1% 36.13 0.1% Refuse Truck 2,338,866 0.1% 1.17 0.0% 21.36 0.2% 10.87 0.0% Single Unit Short-haul Truck 102,459,700 2.5% 91.64 2.2% 496.33 5.6% 1,711.08 3.2% Single Unit Long-haul Truck 14,427,396 0.3% 10.37 0.2% 63.16 0.7% 180.90 0.3% Motor Home 6,175,313 0.1% 11.06 0.3% 35.55 0.4% 221.54 0.4% Combination Short-haul Truck 79,522,500 1.9% 36.93 0.9% 852.17 9.6% 225.20 0.4% Combination Long-haul Truck 111,468,270 2.7% 116.74 2.8% 1,628.03 18.3% 467.91 0.9% Total 4,150,294,966 100.0% 4,233.63 100.0% 8,879.12 100.0% 52,716.37 100.0% County Sourcetype

Appendix D-2-2 8

### Appendix D-2-2-2 2011 Lancaster County Emission Summary by Process Annual (Tons/Year)

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Lancaster Running Exhaust 914.44 21.6% 6,768.53 76.2% 24,330.65 46.2% Start Exhaust 2,183.46 51.6% 1,729.97 19.5% 28,230.70 53.6% Evap Permeation 217.31 5.1% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 571.10 13.5% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 240.08 5.7% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 12.82 0.3% 1.35 0.0% 5.27 0.0%

Crankcase Start Exhaust 28.85 0.7% 0.06 0.0% 3.68 0.0% Crankcase Extended Idle Exhaust 0.99 0.0% 0.12 0.0% 0.26 0.0% Extended Idle Exhaust 64.57 1.5% 379.08 4.3% 145.82 0.3% Total 4,233.6 3 100.0 % 8,879.1 2 100.0 % 52,716.3 7 100.0 % County

Appendix D-2-2 9

# APPENDIX D-2-3 Philadelphia Area Emission Summary Tables

Appendix D-2-3-1 2011 July Weekday Emissions

Emission Summar y Emission Summary by Road Type Emission Summary by Source Typ e Emission Summary by Proces s



## Appendix D-2-3-2 2011 Annual Emissions

Emission Summar y Emission Summary by Road Type Emission Summary by Source Typ e Emission Summary by Proces s

## Appendix D-2-3-1 2011 Philadelphia Area Emission Summar y Summer Weekday (Tons/Day)

Count y V MT Speed ( mph ) V OC NOX CO

Bucks 14,614,068 45.9 11.47 22.55 119.86 Chester 13,198,835 44.8 9.29 20.29 102.86 Delaware 10,324,285 39.7 8.68 17.25 88.68 Montgomery 20,134,609 42.6 14.50 28.89 159.89 Philadelphia 16,521,773 23.8 16.63 34.40 160.42 Philadelphia MPO 74,793,570

- 60.58 123.39 631.69

Appendix D-2-3 2

### Appendix D-2-3-1 2011 Philadelphia Area Emission Summar y

b y Road T y

p e Summer Weekday (Tons/Day)

Count y Road Typ e V MT Speed (mph) V OC NO X CO Bucks Off-Network - - 8.23 5.84 48.93 Rural Restricted Access 386,283 65 0.07 0.30 2.24 Rural Unrestricted Access 1,208,420 48 0.26 1.58 5.31 Urban Restricted Access 3,782,921 57 0.77 4.42 21.50 Urban Unrestricted Access 9,236,445 42 2.15 10.42 41.89 Tota l 14,614,06 8 11.47 22.55 119.8 6

Count y Road Typ e V MT Speed (mph) V OC NO X CO Chester Off-Network - - 6.29 4.62 37.78 Rural Restricted Access 615,179 65 0.11 0.48 3.56 Rural Unrestricted Access 1,558,477 45 0.37 2.27 6.91 Urban Restricted Access 3,614,348 56 0.74 4.21 20.65 Urban Unrestricted Access 7,410,831 40 1.78 8.72 33.95 Tota l 13,198,835 9.2 9 20.2 9 102.8 6

Count y Road Typ e V MT Speed (mph) V OC NO X CO Delaware Off-Network - - 6.12 4.39 36.38 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 0 N/A 0.00 0.00 0.00 Urban Restricted Access 3,346,976 52 0.74 4.65 18.96 Urban Unrestricted Access 6,977,309 36 1.82 8.21 33.34 Tota l 10,324,285 8.6 8 17.25 88.6 8

Count y Road Typ e V MT Speed (mph) V OC NO X CO Montgomery Off-Network - - 9.86 6.98 58.46 Rural Restricted Access 181,449 65 0.03 0.14 1.05 Rural Unrestricted Access 260,156 50 0.06 0.33 1.14 Urban Restricted Access 7,153,004 52 1.49 7.55 40.95 Urban Unrestricted Access 12,539,999 39 3.07 13.88 58.28 Tota l 20,134,60 9 14.5 0 28.8 9 159.8 9

Count y Road Typ e V MT Speed (mph) V OC NO X CO Philadelphia Off-Network - - 10.66 7.88 62.87 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 0 N/A 0.00 0.00 0.00 Urban Restricted Access 4,936,996 29 1.60 9.52 30.52 Urban Unrestricted Access 11,584,776 22 4.37 17.00 67.02 Tota l 16,521,77 3 16.6 3 34.4 0 160.4 2

Appendix D-2-3 3Appendix D-2-3-1 2011 Philadelphia Area Emission Summar y b y Source T y

pe Summer Weekday (Tons/Day)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Bucks Motorcycle 79,407 0.5% 0.43 3.8% 0.06 0.3% 1.28 1.1% Passenger Car 7,999,936 54.7% 3.09 26.9% 4.05 18.0% 31.73 26.5% Passenger Truck 4,214,568 28.8% 5.40 47.1% 7.86 34.8% 59.19 49.4% Light Commercial Truck 1,420,579 9.7% 1.80 15.7% 3.08 13.6% 20.17 16.8% Intercity Bus 11,333 0.1% 0.01 0.1% 0.15 0.7% 0.05 0.0% Transit Bus 17,592 0.1% 0.01 0.1% 0.18 0.8% 0.15 0.1% School Bus 17,963 0.1% 0.02 0.2% 0.12 0.5% 0.31 0.3% Refuse Truck 6,287 0.0% 0.00 0.0% 0.05 0.2% 0.03 0.0% Single Unit Short-haul Truck 276,140 1.9% 0.25 2.2% 1.12 5.0% 4.22 3.5% Single Unit Long-haul Truck 38,897 0.3% 0.03 0.2% 0.14 0.6% 0.42 0.4% Motor Home 16,640 0.1% 0.03 0.3% 0.08 0.3% 0.48 0.4% Combination Short-haul Truck 214,375 1.5% 0.09 0.8% 1.99 8.8% 0.60 0.5% Combination Long-haul Truck 300,351 2.1% 0.30 2.6% 3.68 16.3% 1.23 1.0% Total 14,614,068 100.0% 11.47 100.0% 22.55 100.0% 119.86 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Chester Motorcycle 71,431 0.5% 0.35 3.7% 0.05 0.3% 1.15 1.1% Passenger Car 7,196,442 54.5% 2.46 26.4% 3.50 17.3% 27.49 26.7% Passenger Truck 3,791,275 28.7% 4.31 46.4% 6.77 33.4% 50.04 48.6% Light Commercial Truck 1,277,889 9.7% 1.45 15.6% 2.68 13.2% 16.92 16.5% Intercity Bus 8,883 0.1% 0.01 0.1% 0.12 0.6% 0.04 0.0% Transit Bus 17,906 0.1% 0.01 0.1% 0.18 0.9% 0.16 0.2% School Bus 11,979 0.1% 0.01 0.2% 0.08 0.4% 0.24 0.2% Refuse Truck 6,046 0.0% 0.00 0.0% 0.05 0.2% 0.03 0.0% Single Unit Short-haul Truck 266,562 2.0% 0.25 2.7% 1.10 5.4% 4.10 4.0% Single Unit Long-haul Truck 37,530 0.3% 0.03 0.3% 0.14 0.7% 0.41 0.4% Motor Home 16,069 0.1% 0.03 0.3% 0.08 0.4% 0.47 0.5% Combination Short-haul Truck 206,936 1.6% 0.09 1.0% 1.94 9.6% 0.59 0.6% Combination Long-haul Truck 289,888 2.2% 0.30 3.2% 3.60 17.7% 1.22 1.2% Total 13,198,835 100.0% 9.29 100.0% 20.29 100.0% 102.86 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Delaware Motorcycle 55,760 0.5% 0.32 3.7% 0.04 0.2% 0.88 1.0% Passenger Car 5,617,611 54.4% 2.32 26.8% 3.02 17.5% 23.46 26.5% Passenger Truck 2,959,494 28.7% 4.06 46.8% 5.80 33.6% 43.50 49.1% Light Commercial Truck 997,542 9.7% 1.36 15.7% 2.31 13.4% 14.87 16.8% Intercity Bus 12,978 0.1% 0.01 0.1% 0.18 1.1% 0.05 0.1% Transit Bus 25,628 0.2% 0.02 0.2% 0.28 1.6% 0.22 0.3% School Bus 17,906 0.2% 0.02 0.2% 0.12 0.7% 0.24 0.3% Refuse Truck 4,715 0.0% 0.00 0.0% 0.04 0.2% 0.02 0.0% Single Unit Short-haul Truck 206,420 2.0% 0.20 2.3% 0.89 5.2% 3.27 3.7% Single Unit Long-haul Truck 29,046 0.3% 0.02 0.3% 0.11 0.7% 0.33 0.4% Motor Home 12,437 0.1% 0.02 0.3% 0.06 0.4% 0.39 0.4% Combination Short-haul Truck 160,247 1.6% 0.07 0.9% 1.53 8.9% 0.46 0.5% Combination Long-haul Truck 224,499 2.2% 0.24 2.8% 2.86 16.6% 0.97 1.1% Total 10,324,285 100.0% 8.68 100.0% 17.25 100.0% 88.68 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Montgomery Motorcycle 110,966 0.6% 0.55 3.8% 0.08 0.3% 1.77 1.1% Passenger Car 11,179,424 55.5% 3.92 27.0% 5.54 19.2% 43.78 27.4% Passenger Truck 5,889,612 29.3% 6.88 47.4% 10.65 36.9% 79.21 49.5% Light Commercial Truck 1,985,158 9.9% 2.31 15.9% 4.23 14.7% 26.80 16.8% Intercity Bus 9,717 0.0% 0.01 0.0% 0.13 0.5% 0.04 0.0% Transit Bus 31,087 0.2% 0.02 0.1% 0.32 1.1% 0.28 0.2% School Bus 14,460 0.1% 0.02 0.1% 0.10 0.3% 0.29 0.2% Refuse Truck 6,711 0.0% 0.00 0.0% 0.05 0.2% 0.03 0.0% Single Unit Short-haul Truck 296,083 1.5% 0.28 2.0% 1.26 4.3% 4.62 2.9% Single Unit Long-haul Truck 41,692 0.2% 0.03 0.2% 0.16 0.6% 0.46 0.3% Motor Home 17,850 0.1% 0.03 0.2% 0.09 0.3% 0.54 0.3% Combination Short-haul Truck 229,809 1.1% 0.11 0.7% 2.19 7.6% 0.66 0.4% Combination Long-haul Truck 322,040 1.6% 0.34 2.4% 4.09 14.2% 1.39 0.9%
Total 20,134,609 100.0% 14.50 100.0% 28.89 100.0% 159.89 100.0% County Sourcetype

County Sourcetype

County Sourcetype

County Sourcetype

Appendix D-2-3 4VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Philadelphia Motorcycle 89,170 0.5% 0.61 3.7% 0.05 0.2% 1.44 0.9% Passenger Car 8,983,566 54.4% 4.39 26.4% 5.96 17.3% 42.61 26.6% Passenger Truck 4,732,768 28.6% 7.71 46.3% 11.12 32.3% 78.21 48.8% Light Commercial Truck 1,595,244 9.7% 2.62 15.7% 4.77 13.9% 27.04 16.9% Intercity Bus 22,154 0.1% 0.02 0.1% 0.36 1.0% 0.12 0.1% Transit Bus 224,167 1.4% 0.21 1.3% 2.89 8.4% 2.18 1.4% School Bus 38,308 0.2% 0.05 0.3% 0.33 0.9% 0.47 0.3% Refuse Truck 6,166 0.0% 0.00 0.0% 0.06 0.2% 0.03 0.0% Single Unit Short-haul Truck 270,860 1.6% 0.34 2.0% 1.48 4.3% 4.74 3.0% Single Unit Long-haul Truck 38,153 0.2% 0.04 0.2% 0.19 0.6% 0.48 0.3% Motor Home 16,325 0.1% 0.04 0.2% 0.10 0.3% 0.58 0.4% Combination Short-haul Truck 210,284 1.3% 0.14 0.8% 2.35 6.8% 0.77 0.5% Combination Long-haul Truck 294,608 1.8% 0.48 2.9% 4.75 13.8% 1.76 1.1% Total 16,521,773 100.0% 16.63 100.0% 34.40 100.0% 160.42 100.0% County Sourcetype

Appendix D-2-3 5

### Appendix D-2-3-1 2011 Philadel p hia Area Emission Summar y

b y Proces s Summer Weekday (Tons/Day)

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Bucks Running Exhaust 2.39 20.8% 16.71 74.1% 70.91 59.2% Start Exhaust 4.65 40.5% 5.08 22.5% 48.55 40.5% Evap Permeation 1.40 12.2% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 2.05 17.9% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.72 6.3% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.03 0.3% 0.00 0.0% 0.02 0.0%

Crankcase Start Exhaust 0.06 0.5% 0.00 0.0% 0.01 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.17 1.4% 0.76 3.3% 0.38 0.3% Total 11.4 7 100.0 % 22.5 5 100.0 % 119.8 6 100.0 %

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Chester Running Exhaust 2.21 23.8% 15.67 77.2% 65.06 63.3% Start Exhaust 3.54 38.1% 3.86 19.0% 37.39 36.4% Evap Permeation 1.07 11.5% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 1.65 17.8% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.57 6.2% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.03 0.3% 0.00 0.0% 0.01 0.0%

Crankcase Start Exhaust 0.05 0.5% 0.00 0.0% 0.01 0.0%
Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.17 1.8% 0.76 3.7% 0.38 0.4% Total 9.2 9 100.0 % 20.2 9 100.0 % 102.8 6 100.0 %

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Delaware Running Exhaust 1.86 21.5% 12.85 74.5% 52.29 59.0% Start Exhaust 3.45 39.8% 3.77 21.9% 36.06 40.7% Evap Permeation 1.04 12.0% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 1.57 18.1% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.55 6.3% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.03 0.3% 0.00 0.0% 0.01 0.0%

Crankcase Start Exhaust 0.05 0.5% 0.00 0.0% 0.01 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.14 1.6% 0.62 3.6% 0.31 0.3% Total 8.6 8 100.0 % 17.2 5 100.0 % 88.6 8 100.0 %

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Montgomery Running Exhaust 3.37 23.2% 21.91 75.8% 101.40 63.4% Start Exhaust 5.58 38.5% 6.10 21.1% 58.02 36.3% Evap Permeation 1.69 11.6% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 2.64 18.2% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.91 6.3% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.05 0.3% 0.00 0.0% 0.02 0.0%

Crankcase Start Exhaust 0.07 0.5% 0.00 0.0% 0.01 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.19 1.3% 0.88 3.0% 0.44 0.3% Total 14.5 0 100.0 % 28.8 9 100.0 % 159.8 9 100.0 % County Process

County Process

County Process

County Process

Appendix D-2-3 6V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Philadelphia Running Exhaust 4.13 24.8% 26.52 77.1% 97.52 60.8% Start Exhaust 6.02 36.2% 6.58 19.1% 62.22 38.8% Evap Permeation 1.82 11.0% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 3.16 19.0% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 1.07 6.5% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.06 0.4% 0.01 0.0% 0.03 0.0%

Crankcase Start Exhaust 0.08 0.5% 0.00 0.0% 0.01 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.29 1.7% 1.30 3.8% 0.64 0.4% Total 16.6 3 100.0 % 34.4 0 100.0 % 160.4 2 100.0 % County Process

Appendix D-2-3 7

## Appendix D-2-3-2 2011 Philadelphia Area Emission Summar y Annual (Tons/Year)

Count y V MT Speed ( mph ) V OC NOX CO

Bucks 4,727,714,740 46.3 4,120.01 8,292.77 49,954.81 Chester 4,277,234,661 45.3 3,309.73 7,413.67 41,456.81 Delaware 3,336,447,774 40.9 3,097.85 6,222.26 37,084.67 Montgomery 6,505,446,210 43.9 5,156.21 10,458.00 64,680.67 Philadelphia 5,344,510,485 25.7 5,814.04 11,482.34 66,678.77 Philadelphia MPO 24,191,353,871

- 21,497.83 43,869.04 259,855.73

Appendix D-2-3 8

### Appendix D-2-3-2 2011 Philadel p hia Area Emission Summar y

b y Road T ype Annual (Tons/Year)

County Road Type V MT Speed (mph) V OC NOX CO Bucks Off-Network

- - 3,103.30 2,284.90 29,066.23 Rural Restricted Access 124,437,780 65 21.34 108.67 646.71 Rural Unrestricted Access 391,585,306 48 83.56 562.74 1,588.12 Urban Restricted Access 1,204,522,245 58 236.20 1,585.11 6,213.62 Urban Unrestricted Access 3,007,169,409 42 675.61 3,751.37 12,440.14 Total 4,727,714,74 0 4,120.01 8,292.7 7 49,954.81

County Road Type V MT Speed (mph) V OC NOX CO Chester Off-Network

- - 2,369.42 1,813.02 22,234.46 Rural Restricted Access 198,173,354 65 33.98 173.14 1,029.97 Rural Unrestricted Access 507,158,668 45 115.99 809.92 2,089.71 Urban Restricted Access 1,150,850,483 56 228.65 1,507.76 5,975.00 Urban Unrestricted Access 2,421,052,155 41 561.70 3,109.83 10,127.67 Total 4,277,234,661 3,309.7 3 7,413.6 7 41,456.81

County Road Type V MT Speed (mph) V OC NOX CO Delaware Off-Network

- - 2,307.41 1,713.92 21,597.24 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 0 N/A 0.00 0.00 0.00 Urban Restricted Access 1,065,709,327 56 221.05 1,645.70 5,523.18 Urban Unrestricted Access 2,270,738,447 36 569.39 2,862.64 9,964.25 Total 3,336,447,77 4 3,097.8 5 6,222.2 6 37,084.6 7

County Road Type V MT Speed (mph) V OC NOX CO Montgomery Off-Network

- - 3,722.39 2,726.89 34,850.29 Rural Restricted Access 58,452,519 65 10.03 51.07 303.82 Rural Unrestricted Access 84,085,637 50 17.40 118.72 339.45 Urban Restricted Access 2,277,629,193 55 443.42 2,632.85 11,826.25 Urban Unrestricted Access 4,085,278,861 39 962.98 4,928.47 17,360.87 Total 6,505,446,21 0 5,156.21 10,458.0 0 64,680.6 7

County Road Type V MT Speed (mph) V OC NOX CO Philadelphia Off-Network

- - 4,026.99 3,051.04 37,549.13 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 0 N/A 0.00 0.00 0.00 Urban Restricted Access 1,571,998,035 35 441.67 2,958.63 8,887.03 Urban Unrestricted Access 3,772,512,450 23 1,345.39 5,472.66 20,242.62 Total 5,344,510,48 5 5,814.0 4 11,482.3 4 66,678.7 7

Appendix D-2-3 9Appendix D-2-3-2 2011 Philadelphia Area Emission Summary by Source Type Annual (Tons/Year)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Bucks Motorcycle 25,689,051 0.5% 125.07 3.0% 24.36 0.3% 575.93 1.2% Passenger Car 2,588,072,036 54.7% 1,230.10 29.9% 1,499.53 18.1% 15,354.74 30.7% Passenger Truck 1,363,461,076 28.8% 1,893.46 46.0% 2,862.63 34.5% 23,559.03 47.2% Light Commercial Truck 459,573,695 9.7% 634.39 15.4% 1,111.72 13.4% 8,014.21 16.0% Intercity Bus 3,338,919 0.1% 2.05 0.0% 51.17 0.6% 13.77 0.0% Transit Bus 5,850,837 0.1% 3.92 0.1% 68.01 0.8% 51.53 0.1% School Bus 5,974,469 0.1% 7.09 0.2% 46.45 0.6% 102.10 0.2% Refuse Truck 2,029,899 0.0% 0.98 0.0% 18.15 0.2% 8.92 0.0% Single Unit Short-haul Truck 89,304,860 1.9% 76.63 1.9% 417.38 5.0% 1,369.11 2.7% Single Unit Long-haul Truck 12,578,824 0.3% 8.63 0.2% 53.19 0.6% 144.09 0.3% Motor Home 5,381,833 0.1% 9.11 0.2% 29.95 0.4% 177.40 0.4% Combination Short-haul Truck 69,327,968 1.5% 31.13 0.8% 729.41 8.8% 190.58 0.4% Combination Long-haul Truck 97,131,273 2.1% 97.44 2.4% 1,380.82 16.7% 393.40 0.8% Tota l 4,727,714,740 100.0% 4,120.01 100.0% 8,292.77 100.0% 49,954.81 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Chester Motorcycle 23,149,433 0.5% 100.56 3.0% 21.70 0.3% 505.87 1.2% Passenger Car 2,332,217,366 54.5% 967.54 29.2% 1,279.93 17.3% 12,644.10 30.5% Passenger Truck 1,228,672,880 28.7% 1,503.01 45.4% 2,443.06 33.0% 19,376.18 46.7% Light Commercial Truck 414,137,170 9.7% 506.35 15.3% 955.28 12.9% 6,554.18 15.8% Intercity Bus 2,622,789 0.1% 1.65 0.0% 40.34 0.5% 11.20 0.0% Transit Bus 5,956,207 0.1% 4.06 0.1% 68.91 0.9% 53.83 0.1% School Bus 3,984,592 0.1% 5.25 0.2% 31.69 0.4% 78.93 0.2% Refuse Truck 1,963,847 0.0% 0.96 0.0% 17.66 0.2% 8.75 0.0% Single Unit Short-haul Truck 86,310,360 2.0% 75.49 2.3% 409.96 5.5% 1,334.66 3.2% Single Unit Long-haul Truck 12,149,896 0.3% 8.52 0.3% 52.18 0.7% 140.37 0.3% Motor Home 5,200,483 0.1% 8.98 0.3% 29.23 0.4% 173.23 0.4% Combination Short-haul Truck 67,001,309 1.6% 30.68 0.9% 711.02 9.6% 187.19 0.5% Combination Long-haul Truck 93,868,330 2.2% 96.67 2.9% 1,352.71 18.2% 388.32 0.9%
Tota l 4,277,234,661 100.0% 3,309.73 100.0% 7,413.67 100.0% 41,456.81 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Delaware Motorcycle 18,023,707 0.5% 93.36 3.0% 16.27 0.3% 400.77 1.1% Passenger Car 1,815,818,800 54.4% 920.04 29.7% 1,091.67 17.5% 11,410.60 30.8% Passenger Truck 956,617,900 28.7% 1,418.79 45.8% 2,066.53 33.2% 17,406.79 46.9% Light Commercial Truck 322,442,350 9.7% 476.36 15.4% 811.62 13.0% 5,931.64 16.0% Intercity Bus 3,775,297 0.1% 2.36 0.1% 59.83 1.0% 15.59 0.0% Transit Bus 8,502,848 0.3% 5.88 0.2% 103.09 1.7% 74.13 0.2% School Bus 5,940,709 0.2% 6.25 0.2% 47.20 0.8% 79.65 0.2% Refuse Truck 1,522,534 0.0% 0.76 0.0% 14.18 0.2% 6.93 0.0% Single Unit Short-haul Truck 66,493,530 2.0% 59.72 1.9% 327.42 5.3% 1,055.02 2.8% Single Unit Long-haul Truck 9,355,999 0.3% 6.76 0.2% 41.84 0.7% 111.31 0.3% Motor Home 4,008,710 0.1% 7.18 0.2% 23.31 0.4% 140.22 0.4% Combination Short-haul Truck 51,615,030 1.5% 24.02 0.8% 555.81 8.9% 146.38 0.4% Combination Long-haul Truck 72,330,360 2.2% 76.36 2.5% 1,063.49 17.1% 305.64 0.8% Tota l 3,336,447,774 100.0% 3,097.85 100.0% 6,222.26 100.0% 37,084.67 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Montgomery Motorcycle 35,852,438 0.6% 159.36 3.1% 32.94 0.3% 779.06 1.2% Passenger Car 3,611,994,900 55.5% 1,537.46 29.8% 2,007.12 19.2% 20,123.30 31.1% Passenger Truck 1,902,894,242 29.3% 2,388.38 46.3% 3,816.70 36.5% 30,686.86 47.4% Light Commercial Truck 641,391,605 9.9% 804.73 15.6% 1,495.95 14.3% 10,374.41 16.0% Intercity Bus 2,848,271 0.0% 1.81 0.0% 44.65 0.4% 12.37 0.0% Transit Bus 10,257,634 0.2% 7.18 0.1% 120.40 1.2% 93.93 0.1% School Bus 4,771,373 0.1% 6.44 0.1% 38.68 0.4% 96.34 0.1% Refuse Truck 2,184,470 0.0% 1.09 0.0% 20.10 0.2% 9.92 0.0% Single Unit Short-haul Truck 95,676,583 1.5% 85.44 1.7% 463.69 4.4% 1,499.30 2.3% Single Unit Long-haul Truck 13,467,829 0.2% 9.67 0.2% 59.08 0.6% 157.79 0.2% Motor Home 5,766,570 0.1% 10.21 0.2% 32.85 0.3% 196.09 0.3% Combination Short-haul Truck 74,258,624 1.1% 34.59 0.7% 798.39 7.6% 211.07 0.3% Combination Long-haul Truck 104,081,671 1.6% 109.85 2.1% 1,527.47 14.6% 440.20 0.7%
Tota l 6,505,446,210 100.0% 5,156.21 100.0% 10,458.00 100.0% 64,680.67 100.0% County Sourcetype

County Sourcetype

County Sourcetype

County Sourcetype

Appendix D-2-3 10VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Philadelphia Motorcycle 28,853,973 0.5% 175.29 3.0% 22.61 0.2% 650.52 1.0% Passenger Car 2,906,927,384 54.4% 1,698.76 29.2% 1,938.64 16.9% 20,560.74 30.8% Passenger Truck 1,531,442,380 28.7% 2,647.10 45.5% 3,597.89 31.3% 31,206.07 46.8% Light Commercial Truck 516,193,200 9.7% 899.05 15.5% 1,487.22 13.0% 10,709.20 16.1% Intercity Bus 6,369,057 0.1% 5.02 0.1% 113.64 1.0% 31.81 0.0% Transit Bus 72,957,860 1.4% 64.93 1.1% 1,012.96 8.8% 687.95 1.0% School Bus 12,467,769 0.2% 15.37 0.3% 116.45 1.0% 154.63 0.2% Refuse Truck 1,985,896 0.0% 1.30 0.0% 21.25 0.2% 10.63 0.0% Single Unit Short-haul Truck 87,215,260 1.6% 99.40 1.7% 525.26 4.6% 1,530.50 2.3% Single Unit Long-haul Truck 12,278,738 0.2% 11.62 0.2% 67.25 0.6% 162.43 0.2% Motor Home 5,256,358 0.1% 11.92 0.2% 35.09 0.3% 206.64 0.3% Combination Short-haul Truck 67,691,680 1.3% 41.61 0.7% 831.46 7.2% 236.50 0.4% Combination Long-haul Truck 94,870,930 1.8% 142.66 2.5% 1,712.62 14.9% 531.14 0.8% Tota l 5,344,510,485 100.0% 5,814.04 100.0% 11,482.34 100.0% 66,678.77 100.0% County Sourcetype

Appendix D-2-3 11Appendix D-2-3-2 2011 Philadelphia Area Emission Summar y

b y Process Annual (Tons/Year)

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Bucks Running Exhaust 749.00 18.2% 6,006.66 72.4% 20,883.90 41.8% Start Exhaust 2,234.69 54.2% 1,972.63 23.8% 28,941.78 57.9% Evap Permeation 257.72 6.3% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 535.08 13.0% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 249.32 6.1% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 10.53 0.3% 1.22 0.0% 4.68 0.0%

Crankcase Start Exhaust 29.52 0.7% 0.07 0.0% 3.77 0.0% Crankcase Extended Idle Exhaust 0.82 0.0% 0.10 0.0% 0.21 0.0% Extended Idle Exhaust 53.34 1.3% 312.10 3.8% 120.46 0.2% Tota l 4,120.0 1 100.0 % 8,292.7 7 100.0 % 49,954.8 1 100.0 %

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Chester Running Exhaust 693.77 21.0% 5,599.48 75.5% 19,217.96 46.4% Start Exhaust 1,698.33 51.3% 1,501.29 20.3% 22,111.03 53.3% Evap Permeation 195.93 5.9% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 437.40 13.2% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 197.99 6.0% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 9.79 0.3% 1.16 0.0% 4.39 0.0%

Crankcase Start Exhaust 22.44 0.7% 0.05 0.0% 2.92 0.0%
Crankcase Extended Idle Exhaust 0.82 0.0% 0.10 0.0% 0.21 0.0% Extended Idle Exhaust 53.27 1.6% 311.58 4.2% 120.29 0.3% Tota l 3,309.7 3 100.0 % 7,413.6 7 100.0 % 41,456.8 1 100.0 %

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Delaware Running Exhaust 577.01 18.6% 4,507.37 72.4% 15,483.82 41.8% Start Exhaust 1,660.13 53.6% 1,465.40 23.6% 21,498.55 58.0% Evap Permeation 191.52 6.2% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 407.97 13.2% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 188.11 6.1% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 8.15 0.3% 0.97 0.0% 3.60 0.0%

Crankcase Start Exhaust 21.93 0.7% 0.05 0.0% 2.80 0.0% Crankcase Extended Idle Exhaust 0.65 0.0% 0.08 0.0% 0.17 0.0% Extended Idle Exhaust 42.39 1.4% 248.40 4.0% 95.72 0.3% Tota l 3,097.8 5 100.0 % 6,222.2 6 100.0 % 37,084.6 7 100.0 %

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Montgomery Running Exhaust 1,041.90 20.2% 7,729.70 73.9% 29,824.18 46.1% Start Exhaust 2,685.78 52.1% 2,369.78 22.7% 34,707.88 53.7% Evap Permeation 310.04 6.0% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 693.17 13.4% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 313.49 6.1% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 14.45 0.3% 1.41 0.0% 6.19 0.0%

Crankcase Start Exhaust 35.48 0.7% 0.08 0.0% 4.50 0.0% Crankcase Extended Idle Exhaust 0.94 0.0% 0.11 0.0% 0.24 0.0% Extended Idle Exhaust 60.96 1.2% 356.91 3.4% 137.66 0.2% Tota l 5,156.2 1 100.0 % 10,458.0 0 100.0 % 64,680.6 7 100.0 % County Process County Process

County Process

County Process

Appendix D-2-3 12VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Philadelphia Running Exhaust 1,246.77 21.4% 8,429.32 73.4% 29,122.18 43.7% Start Exhaust 2,897.37 49.8% 2,556.62 22.3% 37,353.56 56.0% Evap Permeation 334.91 5.8% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 831.90 14.3% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 361.45 6.2% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 17.77 0.3% 1.98 0.0% 7.47 0.0%

Crankcase Start Exhaust 38.28 0.7% 0.09 0.0% 4.86 0.0% Crankcase Extended Idle Exhaust 1.30 0.0% 0.15 0.0% 0.34 0.0% Extended Idle Exhaust 84.30 1.4% 494.18 4.3% 190.37 0.3% Tota l 5,814.0 4 100.0 % 11,482.3 4 100.0 % 66,678.7 7 100.0 % County Process

Appendix D-2-3 13

# APPENDIX D-2-4 Pittsburgh-Beaver Valley Area Emission Summary Tables

Appendix D-2-4-1 2011 July Weekday Emissions

Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process



## Appendix D-2-4-2 2011 Annual Emissions

Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process

Appendix D-2-4 1

## Appendix D-2-4-1 2011 Pittsbur g h-Beaver Valle y Area Emission Summar y Summer Weekday (Tons/Day)

Count y V MT Speed ( mph ) V OC NOX CO

Allegheny 25,509,480 35.7 20.40 41.15 208.35 Armstrong 1,793,743 45.1 1.61 3.33 15.76

Beaver 4,066,807 39.3 3.22 6.45 32.45 Butler 5,437,667 44.9 4.44 9.64 46.20 Fayette 2,928,750 45.1 2.91 5.31 27.66 Washington 5,382,187 45.6 4.02 8.71 42.75 Westmoreland 9,523,496 42.6 6.95 14.26 73.47

SPC MPO 54,642,130

- 43.54 88.85 446.64

Appendix D-2-4 2

### Appendix D-2-4-1 2011 Pittsbur g h-Beaver Valle y Area Emission Summar y

b y Road T ype Summer Weekday (Tons/Day)

Count y Road Type V MT Speed (mph) V OC NOX CO Allegheny Off-Network - - 13.61 9.75 86.73 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 233,881 48 0.05 0.29 0.96 Urban Restricted Access 6,603,764 58 1.33 7.78 34.19 Urban Unrestricted Access 18,671,835 31 5.41 23.34 86.48 Tota l 25,509,480 20.40 41.15 208.35

Count y Road Type V MT Speed (mph) V OC NOX CO Armstrong Off-Network - - 1.16 0.79 7.09 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 1,012,522 47 0.25 1.49 4.75 Urban Restricted Access 127,360 56 0.03 0.21 0.76 Urban Unrestricted Access 653,862 41 0.17 0.84 3.15 Tota l 1,793,743 1.61 3.33 15.76

Count y Road Type V MT Speed (mph) V OC NOX CO Beaver Off-Network - - 2.21 1.58 14.07 Rural Restricted Access 161,653 65 0.03 0.13 0.85 Rural Unrestricted Access 929,198 41 0.22 1.20 3.92 Urban Restricted Access 547,157 60 0.11 0.61 2.81 Urban Unrestricted Access 2,428,798 35 0.65 2.93 10.81 Tota l 4,066,807 3.22 6.45 32.45

Count y Road Type V MT Speed (mph) V OC NOX CO Butler Off-Network - - 3.08 2.12 18.80 Rural Restricted Access 597,848 65 0.14 1.20 3.49 Rural Unrestricted Access 2,049,834 46 0.50 2.83 9.64 Urban Restricted Access 579,540 59 0.13 0.90 3.40 Urban Unrestricted Access 2,210,445 38 0.59 2.59 10.87 Tota l 5,437,667 4.44 9.64 46.20

Count y Road Type V MT Speed (mph) V OC NOX CO Fayette Off-Network - - 2.19 1.44 13.14 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 1,441,378 47 0.35 1.97 6.76 Urban Restricted Access 422,490 55 0.10 0.50 2.57 Urban Unrestricted Access 1,064,882 40 0.28 1.40 5.18 Tota l 2,928,750 2.91 5.31 27.66

Count y Road Type V MT Speed (mph) V OC NOX CO Washington Off-Network - - 2.79 1.99 17.90 Rural Restricted Access 1,040,639 65 0.20 1.32 5.40 Rural Unrestricted Access 1,481,866 43 0.35 1.99 6.19 Urban Restricted Access 964,436 59 0.19 1.16 4.97 Urban Unrestricted Access 1,895,246 37 0.49 2.25 8.28 Tota l 5,382,187 4.02 8.71 42.75

Count y Road Type V MT Speed (mph) V OC NOX CO Westmoreland Off-Network - - 4.72 3.36 30.10 Rural Restricted Access 347,301 65 0.06 0.30 1.82 Rural Unrestricted Access 1,949,271 46 0.44 2.52 8.01 Urban Restricted Access 2,269,473 59 0.43 2.07 11.75 Urban Unrestricted Access 4,957,450 36 1.29 6.00 21.80 Tota l 9,523,496 6.95 14.26 73.47

Appendix D-2-4 3Appendix D-2-4-1 2011 Pittsbur g h-Beaver Valle y Area Emission Summar y b y Source T y

pe Summer Weekday (Tons/Day)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 139,314 0.5% 0.79 3.9% 0.10 0.2% 2.26 1.1% Passenger Car 14,035,297 55.0% 5.16 25.3% 7.15 17.4% 54.60 26.2% Passenger Truck 7,398,111 29.0% 9.78 48.0% 14.42 35.0% 103.16 49.5% Light Commercial Truck 2,488,333 9.8% 3.27 16.0% 5.73 13.9% 35.10 16.8% Intercity Bus 18,239 0.1% 0.01 0.1% 0.27 0.7% 0.08 0.0% Transit Bus 94,859 0.4% 0.07 0.3% 1.02 2.5% 0.83 0.4% School Bus 35,265 0.1% 0.04 0.2% 0.25 0.6% 0.59 0.3% Refuse Truck 9,552 0.0% 0.01 0.0% 0.08 0.2% 0.05 0.0% Single Unit Short-haul Truck 421,073 1.7% 0.45 2.2% 1.97 4.8% 6.95 3.3% Single Unit Long-haul Truck 59,277 0.2% 0.05 0.2% 0.25 0.6% 0.70 0.3% Motor Home 25,376 0.1% 0.05 0.3% 0.13 0.3% 0.81 0.4% Combination Short-haul Truck 326,859 1.3% 0.17 0.8% 3.34 8.1% 1.03 0.5% Combination Long-haul Truck 457,924 1.8% 0.56 2.7% 6.43 15.6% 2.20 1.1% Total 25,509,480 100.0% 20.40 100.0% 41.15 100.0% 208.35 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 9,480 0.5% 0.05 3.4% 0.01 0.2% 0.16 1.0% Passenger Car 955,088 53.2% 0.41 25.6% 0.54 16.2% 4.00 25.4% Passenger Truck 503,424 28.1% 0.77 47.5% 1.05 31.6% 7.69 48.8% Light Commercial Truck 169,339 9.4% 0.25 15.3% 0.40 11.9% 2.57 16.3% Intercity Bus 1,638 0.1% 0.00 0.1% 0.02 0.7% 0.01 0.0% Transit Bus 9,156 0.5% 0.01 0.4% 0.09 2.8% 0.08 0.5% School Bus 5,983 0.3% 0.01 0.4% 0.04 1.2% 0.11 0.7% Refuse Truck 1,028 0.1% 0.00 0.0% 0.01 0.2% 0.00 0.0% Single Unit Short-haul Truck 45,227 2.5% 0.04 2.6% 0.18 5.5% 0.69 4.4% Single Unit Long-haul Truck 6,360 0.4% 0.00 0.3% 0.02 0.7% 0.07 0.4% Motor Home 2,729 0.2% 0.00 0.3% 0.01 0.4% 0.08 0.5% Combination Short-haul Truck 35,124 2.0% 0.02 1.0% 0.33 10.0% 0.10 0.6% Combination Long-haul Truck 49,167 2.7% 0.05 3.1% 0.62 18.5% 0.20 1.3% Total 1,793,743 100.0% 1.61 100.0% 3.33 100.0% 15.76 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 22,169 0.5% 0.12 3.9% 0.02 0.3% 0.36 1.1% Passenger Car 2,233,402 54.9% 0.82 25.3% 1.11 17.2% 8.37 25.8% Passenger Truck 1,177,233 28.9% 1.54 47.9% 2.26 35.1% 16.11 49.6% Light Commercial Truck 395,973 9.7% 0.51 15.9% 0.89 13.8% 5.50 17.0% Intercity Bus 2,238 0.1% 0.00 0.0% 0.03 0.5% 0.01 0.0% Transit Bus 6,886 0.2% 0.00 0.1% 0.07 1.1% 0.06 0.2% School Bus 2,882 0.1% 0.00 0.1% 0.02 0.3% 0.06 0.2% Refuse Truck 1,692 0.0% 0.00 0.0% 0.01 0.2% 0.01 0.0% Single Unit Short-haul Truck 73,166 1.8% 0.07 2.3% 0.33 5.1% 1.17 3.6% Single Unit Long-haul Truck 10,317 0.3% 0.01 0.3% 0.04 0.6% 0.12 0.4% Motor Home 4,411 0.1% 0.01 0.3% 0.02 0.3% 0.13 0.4% Combination Short-haul Truck 56,861 1.4% 0.03 0.9% 0.57 8.8% 0.17 0.5% Combination Long-haul Truck 79,579 2.0% 0.09 2.9% 1.08 16.7% 0.37 1.1% Total 4,066,807 100.0% 3.22 100.0% 6.45 100.0% 32.45 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 28,915 0.5% 0.15 3.4% 0.02 0.2% 0.49 1.1% Passenger Car 2,913,026 53.6% 1.13 25.6% 1.59 16.5% 12.08 26.1% Passenger Truck 1,535,484 28.2% 2.11 47.5% 3.08 31.9% 22.50 48.7% Light Commercial Truck 516,447 9.5% 0.68 15.4% 1.17 12.1% 7.43 16.1% Intercity Bus 4,708 0.1% 0.00 0.1% 0.07 0.7% 0.02 0.0% Transit Bus 9,945 0.2% 0.01 0.1% 0.11 1.1% 0.09 0.2% School Bus 5,840 0.1% 0.01 0.2% 0.04 0.4% 0.12 0.2% Refuse Truck 3,143 0.1% 0.00 0.0% 0.03 0.3% 0.01 0.0% Single Unit Short-haul Truck 137,065 2.5% 0.12 2.8% 0.57 5.9% 2.13 4.6% Single Unit Long-haul Truck 19,308 0.4% 0.01 0.3% 0.07 0.7% 0.21 0.5% Motor Home 8,261 0.2% 0.02 0.3% 0.04 0.4% 0.25 0.5% Combination Short-haul Truck 106,401 2.0% 0.05 1.0% 1.01 10.5% 0.29 0.6% Combination Long-haul Truck 149,125 2.7% 0.14 3.2% 1.85 19.2% 0.59 1.3%
Total 5,437,667 100.0% 4.44 100.0% 9.64 100.0% 46.20 100.0% County Sourcetype

County Sourcetype County Sourcetype

County Sourcetype

Appendix D-2-4 4VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 15,724 0.5% 0.10 3.5% 0.01 0.2% 0.27 1.0% Passenger Car 1,584,084 54.1% 0.77 26.3% 0.94 17.8% 7.16 25.9% Passenger Truck 834,981 28.5% 1.41 48.5% 1.83 34.5% 13.82 50.0% Light Commercial Truck 280,845 9.6% 0.45 15.6% 0.69 12.9% 4.61 16.7% Intercity Bus 2,062 0.1% 0.00 0.0% 0.03 0.5% 0.01 0.0% Transit Bus 6,757 0.2% 0.00 0.1% 0.07 1.3% 0.06 0.2% School Bus 2,458 0.1% 0.00 0.1% 0.02 0.3% 0.05 0.2% Refuse Truck 1,511 0.1% 0.00 0.0% 0.01 0.2% 0.01 0.0% Single Unit Short-haul Truck 65,366 2.2% 0.06 2.1% 0.27 5.1% 1.01 3.6% Single Unit Long-haul Truck 9,185 0.3% 0.01 0.2% 0.03 0.6% 0.10 0.4% Motor Home 3,935 0.1% 0.01 0.2% 0.02 0.4% 0.11 0.4% Combination Short-haul Truck 50,750 1.7% 0.02 0.8% 0.48 9.1% 0.14 0.5% Combination Long-haul Truck 71,090 2.4% 0.07 2.5% 0.90 16.9% 0.30 1.1% Total 2,928,750 100.0% 2.91 100.0% 5.31 100.0% 27.66 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 29,076 0.5% 0.15 3.9% 0.02 0.3% 0.49 1.2% Passenger Car 2,929,272 54.4% 1.02 25.3% 1.45 16.6% 11.07 25.9% Passenger Truck 1,544,040 28.7% 1.91 47.6% 2.96 34.0% 21.03 49.2% Light Commercial Truck 519,335 9.6% 0.63 15.7% 1.14 13.1% 7.08 16.6% Intercity Bus 3,680 0.1% 0.00 0.1% 0.05 0.6% 0.02 0.0% Transit Bus 12,996 0.2% 0.01 0.2% 0.14 1.6% 0.12 0.3% School Bus 5,674 0.1% 0.01 0.2% 0.04 0.5% 0.11 0.3% Refuse Truck 2,479 0.0% 0.00 0.0% 0.02 0.2% 0.01 0.0% Single Unit Short-haul Truck 109,509 2.0% 0.10 2.5% 0.46 5.3% 1.72 4.0% Single Unit Long-haul Truck 15,426 0.3% 0.01 0.3% 0.06 0.7% 0.17 0.4% Motor Home 6,597 0.1% 0.01 0.3% 0.03 0.4% 0.20 0.5% Combination Short-haul Truck 84,932 1.6% 0.04 0.9% 0.82 9.4% 0.24 0.6% Combination Long-haul Truck 119,170 2.2% 0.12 3.0% 1.52 17.4% 0.49 1.1%
Total 5,382,187 100.0% 4.02 100.0% 8.71 100.0% 42.75 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 52,241 0.5% 0.27 3.9% 0.04 0.3% 0.87 1.2% Passenger Car 5,263,078 55.3% 1.77 25.4% 2.54 17.8% 19.31 26.3% Passenger Truck 2,774,201 29.1% 3.34 48.1% 5.19 36.4% 36.59 49.8% Light Commercial Truck 933,104 9.8% 1.11 16.0% 2.02 14.1% 12.36 16.8% Intercity Bus 3,662 0.0% 0.00 0.0% 0.05 0.4% 0.02 0.0% Transit Bus 7,810 0.1% 0.01 0.1% 0.08 0.6% 0.07 0.1% School Bus 2,854 0.0% 0.00 0.1% 0.02 0.1% 0.08 0.1% Refuse Truck 3,567 0.0% 0.00 0.0% 0.03 0.2% 0.02 0.0% Single Unit Short-haul Truck 157,595 1.7% 0.16 2.2% 0.68 4.8% 2.49 3.4% Single Unit Long-haul Truck 22,180 0.2% 0.02 0.2% 0.09 0.6% 0.25 0.3% Motor Home 9,499 0.1% 0.02 0.3% 0.05 0.3% 0.28 0.4% Combination Short-haul Truck 122,255 1.3% 0.06 0.8% 1.20 8.4% 0.36 0.5% Combination Long-haul Truck 171,449 1.8% 0.19 2.7% 2.28 16.0% 0.76 1.0% Total 9,523,496 100.0% 6.95 100.0% 14.26 100.0% 73.47 100.0% County Sourcetype

County Sourcetype County Sourcetype

Appendix D-2-4 5

### Appendix D-2-4-1 2011 Pittsbur g h-Beaver Valle y Area Emission Summar y

b y Proces s Summer Weekday (Tons/Day)

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Allegheny Running Exhaust 5.02 24.6% 31.40 76.3% 121.60 58.4% Start Exhaust 8.29 40.7% 8.23 20.0% 85.99 41.3% Evap Permeation 1.83 9.0% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 3.54 17.3% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 1.21 5.9% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.07 0.3% 0.01 0.0% 0.03 0.0%

Crankcase Start Exhaust 0.11 0.5% 0.00 0.0% 0.01 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.32 1.6% 1.52 3.7% 0.72 0.3% Total 20.4 0 100.0 % 41.1 5 100.0 % 208.3 5 100.0 %

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Armstrong Running Exhaust 0.35 21.8% 2.54 76.3% 8.66 55.0% Start Exhaust 0.74 45.8% 0.66 19.8% 7.03 44.6% Evap Permeation 0.14 8.5% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 0.26 16.1% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.08 5.2% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.00 0.3% 0.00 0.0% 0.00 0.0%

Crankcase Start Exhaust 0.01 0.6% 0.00 0.0% 0.00 0.0%
Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.03 1.7% 0.13 3.9% 0.06 0.4% Total 1.61 100.0 % 3.3 3 100.0 % 15.7 6 100.0 %

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Beaver Running Exhaust 0.75 23.4% 4.87 75.5% 18.38 56.6% Start Exhaust 1.34 41.8% 1.33 20.7% 13.95 43.0% Evap Permeation 0.30 9.2% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 0.55 17.2% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.19 5.9% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.01 0.3% 0.00 0.0% 0.00 0.0%

Crankcase Start Exhaust 0.02 0.6% 0.00 0.0% 0.00 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.05 1.6% 0.25 3.8% 0.12 0.4% Total 3.2 2 100.0 % 6.45 100.0 % 32.4 5 100.0 %

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Butler Running Exhaust 1.06 23.9% 7.52 78.0% 27.39 59.3% Start Exhaust 1.95 44.0% 1.75 18.1% 18.62 40.3% Evap Permeation 0.36 8.1% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 0.72 16.1% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.23 5.2% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.01 0.3% 0.00 0.0% 0.01 0.0%

Crankcase Start Exhaust 0.03 0.6% 0.00 0.0% 0.00 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.08 1.8% 0.37 3.8% 0.18 0.4% Total 4.44 100.0 % 9.64 100.0 % 46.2 0 100.0 % County Process

County Process

County Process

County Process

Appendix D-2-4 6V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Fayette Running Exhaust 0.56 19.3% 3.87 72.9% 14.51 52.5% Start Exhaust 1.40 48.0% 1.25 23.5% 13.05 47.2% Evap Permeation 0.26 8.9% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 0.48 16.3% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.15 5.3% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.01 0.3% 0.00 0.0% 0.00 0.0%

Crankcase Start Exhaust 0.02 0.6% 0.00 0.0% 0.00 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.04 1.4% 0.19 3.6% 0.09 0.3% Total 2.91 100.0 % 5.31 100.0 % 27.6 6 100.0 %

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Washington Running Exhaust 0.94 23.4% 6.71 77.1% 24.84 58.1% Start Exhaust 1.69 42.2% 1.68 19.3% 17.75 41.5% Evap Permeation 0.37 9.3% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 0.67 16.8% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.23 5.8% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.01 0.3% 0.00 0.0% 0.01 0.0%

Crankcase Start Exhaust 0.02 0.6% 0.00 0.0% 0.00 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.07 1.6% 0.31 3.6% 0.15 0.3% Total 4.0 2 100.0 % 8.71 100.0 % 42.7 5 100.0 %

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Westmoreland Running Exhaust 1.67 24.0% 10.90 76.4% 43.36 59.0% Start Exhaust 2.88 41.4% 2.86 20.0% 29.85 40.6% Evap Permeation 0.63 9.1% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 1.19 17.1% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.41 5.9% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.02 0.3% 0.00 0.0% 0.01 0.0%

Crankcase Start Exhaust 0.04 0.5% 0.00 0.0% 0.00 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.11 1.5% 0.51 3.6% 0.24 0.3% Total 6.95 100.0 % 14.2 6 100.0 % 73.4 7 100.0 % County Process

County Process County Process

Appendix D-2-4 7

## Appendix D-2-4-2 2011 Pittsbur g h-Beaver Valle y Area Emission Summar y Annual (Tons/Year)

Count y V MT Speed ( mph ) V OC NOX CO

Allegheny 8,276,510,090 36.6 7,755.25 14,865.96 98,535.36 Armstrong 582,533,915 45.2 611.63 1,223.02 7,454.79

Beaver 1,320,804,219 39.4 1,232.52 2,365.83 15,550.01 Butler 1,765,362,008 45.2 1,672.83 3,527.63 21,200.51 Fayette 948,403,927 45.2 1,114.77 1,950.20 13,397.21 Washington 1,745,736,483 45.6 1,540.23 3,197.99 20,163.87 Westmoreland 3,087,663,074 42.8 2,657.30 5,229.77 34,579.73

SPC MPO 17,727,013,716 - 16,584.53 32,360.40 210,881.48

Appendix D-2-4 8

### Appendix D-2-4-2 2011 Pittsbur g h-Beaver Valle y Area Emission Summar y

b y Road T ype Annual (Tons/Year)

Count y Road Type V MT Speed (mph) V OC NOX CO Allegheny Off-Network

- - 5,596.01 3,817.82 57,782.90 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 76,304,105 48 16.35 103.73 323.38 Urban Restricted Access 2,102,755,624 58 420.14 2,792.85 11,223.50 Urban Unrestricted Access 6,097,450,361 32 1,722.75 8,151.57 29,205.58 Tota l 8,276,510,090 7,755.25 14,865.96 98,535.36

Count y Road Type V MT Speed (mph) V OC NOX CO Armstrong Off-Network

- - 467.20 309.39 4,546.56 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 329,141,567 47 80.15 535.16 1,600.15 Urban Restricted Access 40,554,754 56 9.72 74.24 250.90 Urban Unrestricted Access 212,837,594 41 54.55 304.23 1,057.17 Tota l 582,533,915 611.63 1,223.02 7,454.79

Count y Road Type V MT Speed (mph) V OC NOX CO Beaver Off-Network

- - 907.03 620.74 9,364.19 Rural Restricted Access 52,114,209 65 9.25 47.46 279.95 Rural Unrestricted Access 302,407,892 41 72.44 431.00 1,327.59 Urban Restricted Access 174,268,783 60 33.91 221.10 922.13 Urban Unrestricted Access 792,013,335 35 209.89 1,045.52 3,656.16 Tota l 1,320,804,219 1,232.52 2,365.83 15,550.01

Count y Road Type V MT Speed (mph) V OC NOX CO Butler Off-Network

- - 1,235.95 827.15 12,028.92 Rural Restricted Access 192,595,513 65 44.64 435.79 1,159.45 Rural Unrestricted Access 666,158,379 46 161.03 1,012.35 3,244.99 Urban Restricted Access 184,551,412 59 41.90 321.73 1,117.33 Urban Unrestricted Access 722,056,703 39 189.31 930.61 3,649.81 Tota l 1,765,362,008 1,672.83 3,527.63 21,200.51

Count y Road Type V MT Speed (mph) V OC NOX CO Fayette Off-Network

- - 882.16 561.71 8,542.33 Rural Restricted Access 0 N/A 0.00 0.00 0.00 Rural Unrestricted Access 466,633,805 47 111.63 706.40 2,266.81 Urban Restricted Access 134,579,593 55 30.22 178.83 842.49 Urban Unrestricted Access 347,190,529 40 90.75 503.25 1,745.57 Tota l 948,403,927 1,114.77 1,950.20 13,397.21

Count y Road Type V MT Speed (mph) V OC NOX CO Washington Off-Network

- - 1,143.41 782.63 11,838.96 Rural Restricted Access 335,237,080 65 64.57 480.61 1,790.10 Rural Unrestricted Access 482,635,851 43 112.99 713.01 2,096.10 Urban Restricted Access 307,097,934 59 61.22 414.77 1,630.27 Urban Unrestricted Access 620,765,618 37 158.04 806.97 2,808.44 Tota l 1,745,736,483 1,540.23 3,197.99 20,163.87

Count y Road Type V MT Speed (mph) V OC NOX CO Westmoreland Off-Network

- - 1,941.11 1,319.27 20,046.30 Rural Restricted Access 111,904,248 65 20.16 110.88 600.00 Rural Unrestricted Access 634,377,842 46 141.39 905.87 2,707.69 Urban Restricted Access 722,653,599 59 136.36 746.73 3,845.86 Urban Unrestricted Access 1,618,727,385 36 418.30 2,147.02 7,379.88 Tota l 3,087,663,074 2,657.30 5,229.77 34,579.73

Appendix D-2-4 9Appendix D-2-4-2 2011 Pittsburgh-Beaver Valley Area Emission Summary by Source Type Annual (Tons/Year)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 45,198,949 0.5% 232.00 3.0% 39.66 0.3% 1,132.85 1.1% Passenger Car 4,553,616,638 55.0% 2,242.87 28.9% 2,598.57 17.5% 31,114.65 31.6% Passenger Truck 2,400,246,642 29.0% 3,623.47 46.7% 5,153.29 34.7% 46,109.58 46.8% Light Commercial Truck 807,316,054 9.8% 1,210.09 15.6% 2,024.28 13.6% 15,609.06 15.8% Intercity Bus 5,326,741 0.1% 3.63 0.0% 88.44 0.6% 24.28 0.0% Transit Bus 31,264,111 0.4% 22.92 0.3% 373.87 2.5% 277.58 0.3% School Bus 11,622,979 0.1% 15.22 0.2% 96.23 0.6% 207.39 0.2% Refuse Truck 3,110,997 0.0% 1.73 0.0% 30.71 0.2% 15.83 0.0% Single Unit Short-haul Truck 136,638,527 1.7% 137.69 1.8% 723.75 4.9% 2,437.96 2.5% Single Unit Long-haul Truck 19,240,454 0.2% 15.73 0.2% 92.12 0.6% 256.89 0.3% Motor Home 8,236,889 0.1% 16.56 0.2% 49.93 0.3% 319.31 0.3% Combination Short-haul Truck 106,071,345 1.3% 54.65 0.7% 1,210.44 8.1% 328.99 0.3% Combination Long-haul Truck 148,619,765 1.8% 178.69 2.3% 2,384.68 16.0% 701.01 0.7% Tota l 8,276,510,090 100.0% 7,755.25 100.0% 14,865.96 100.0% 98,535.36 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 3,079,443 0.5% 16.12 2.6% 3.07 0.3% 81.96 1.1% Passenger Car 310,241,820 53.3% 177.01 28.9% 200.19 16.4% 2,303.52 30.9% Passenger Truck 163,527,528 28.1% 284.06 46.4% 382.56 31.3% 3,453.34 46.3% Light Commercial Truck 55,006,607 9.4% 92.15 15.1% 143.88 11.8% 1,152.40 15.5% Intercity Bus 484,609 0.1% 0.30 0.0% 7.46 0.6% 2.03 0.0% Transit Bus 3,009,291 0.5% 2.08 0.3% 34.98 2.9% 26.88 0.4% School Bus 1,966,442 0.3% 2.60 0.4% 15.55 1.3% 39.02 0.5% Refuse Truck 331,064 0.1% 0.16 0.0% 2.96 0.2% 1.51 0.0% Single Unit Short-haul Truck 14,643,106 2.5% 12.86 2.1% 68.20 5.6% 241.59 3.2% Single Unit Long-haul Truck 2,063,678 0.4% 1.44 0.2% 8.65 0.7% 25.40 0.3% Motor Home 884,431 0.2% 1.52 0.2% 4.92 0.4% 30.58 0.4% Combination Short-haul Truck 11,353,989 1.9% 5.17 0.8% 120.76 9.9% 31.50 0.4% Combination Long-haul Truck 15,941,907 2.7% 16.16 2.6% 229.85 18.8% 65.03 0.9%
Tota l 582,533,915 100.0% 611.63 100.0% 1,223.02 100.0% 7,454.79 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 7,198,525 0.5% 36.77 3.0% 6.59 0.3% 183.16 1.2% Passenger Car 725,223,630 54.9% 357.60 29.0% 411.16 17.4% 4,884.80 31.4% Passenger Truck 382,267,450 28.9% 574.87 46.6% 820.72 34.7% 7,279.02 46.8% Light Commercial Truck 128,579,118 9.7% 191.55 15.5% 319.90 13.5% 2,471.18 15.9% Intercity Bus 667,793 0.1% 0.45 0.0% 10.77 0.5% 3.07 0.0% Transit Bus 2,287,686 0.2% 1.63 0.1% 26.12 1.1% 20.64 0.1% School Bus 957,375 0.1% 1.43 0.1% 7.86 0.3% 21.51 0.1% Refuse Truck 551,538 0.0% 0.30 0.0% 5.28 0.2% 2.74 0.0% Single Unit Short-haul Truck 23,840,668 1.8% 23.23 1.9% 121.15 5.1% 413.21 2.7% Single Unit Long-haul Truck 3,352,050 0.3% 2.64 0.2% 15.35 0.6% 43.31 0.3% Motor Home 1,436,152 0.1% 2.77 0.2% 8.38 0.4% 52.93 0.3% Combination Short-haul Truck 18,511,428 1.4% 9.27 0.8% 207.35 8.8% 56.04 0.4% Combination Long-haul Truck 25,930,807 2.0% 30.01 2.4% 405.18 17.1% 118.41 0.8% Tota l 1,320,804,219 100.0% 1,232.52 100.0% 2,365.83 100.0% 15,550.01 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 9,392,426 0.5% 44.58 2.7% 9.16 0.3% 242.09 1.1% Passenger Car 946,250,980 53.6% 481.56 28.8% 586.43 16.6% 6,587.58 31.1% Passenger Truck 498,778,320 28.3% 778.76 46.6% 1,119.85 31.7% 9,838.77 46.4% Light Commercial Truck 167,759,780 9.5% 253.26 15.1% 421.73 12.0% 3,255.60 15.4% Intercity Bus 1,387,813 0.1% 0.84 0.1% 21.91 0.6% 5.74 0.0% Transit Bus 3,293,723 0.2% 2.29 0.1% 40.15 1.1% 30.48 0.1% School Bus 1,934,035 0.1% 2.60 0.2% 16.14 0.5% 40.39 0.2% Refuse Truck 1,014,713 0.1% 0.48 0.0% 9.36 0.3% 4.59 0.0% Single Unit Short-haul Truck 44,216,371 2.5% 38.09 2.3% 208.56 5.9% 737.98 3.5% Single Unit Long-haul Truck 6,230,653 0.4% 4.26 0.3% 26.55 0.8% 77.75 0.4% Motor Home 2,665,833 0.2% 4.57 0.3% 15.37 0.4% 97.90 0.5% Combination Short-haul Truck 34,321,242 1.9% 15.03 0.9% 365.98 10.4% 92.55 0.4% Combination Long-haul Truck 48,116,118 2.7% 46.51 2.8% 686.45 19.5% 189.10 0.9%
Tota l 1,765,362,008 100.0% 1,672.83 100.0% 3,527.63 100.0% 21,200.51 100.0% County Sourcetype

County Sourcetype County Sourcetype

County Sourcetype

Appendix D-2-4 10VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 5,090,795 0.5% 29.54 2.6% 5.10 0.3% 139.19 1.0% Passenger Car 512,878,190 54.1% 330.42 29.6% 350.83 18.0% 4,233.51 31.6% Passenger Truck 270,341,610 28.5% 526.64 47.2% 666.95 34.2% 6,302.79 47.0% Light Commercial Truck 90,929,110 9.6% 170.26 15.3% 249.88 12.8% 2,103.38 15.7% Intercity Bus 605,297 0.1% 0.38 0.0% 9.35 0.5% 2.60 0.0% Transit Bus 2,237,720 0.2% 1.58 0.1% 26.13 1.3% 20.49 0.2% School Bus 814,142 0.1% 1.17 0.1% 6.59 0.3% 18.01 0.1% Refuse Truck 485,626 0.1% 0.24 0.0% 4.36 0.2% 2.23 0.0% Single Unit Short-haul Truck 21,217,131 2.2% 18.86 1.7% 99.95 5.1% 352.17 2.6% Single Unit Long-haul Truck 2,981,275 0.3% 2.12 0.2% 12.64 0.6% 36.91 0.3% Motor Home 1,279,627 0.1% 2.23 0.2% 7.17 0.4% 44.62 0.3% Combination Short-haul Truck 16,480,171 1.7% 7.59 0.7% 176.03 9.0% 46.11 0.3% Combination Long-haul Truck 23,063,232 2.4% 23.74 2.1% 335.23 17.2% 95.20 0.7% Tota l 948,403,927 100.0% 1,114.77 100.0% 1,950.20 100.0% 13,397.21 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 9,431,002 0.5% 45.69 3.0% 9.22 0.3% 244.77 1.2% Passenger Car 950,137,200 54.4% 446.46 29.0% 537.20 16.8% 6,310.57 31.3% Passenger Truck 500,824,170 28.7% 714.28 46.4% 1,077.84 33.7% 9,389.21 46.6% Light Commercial Truck 168,451,120 9.6% 236.85 15.4% 412.99 12.9% 3,154.03 15.6% Intercity Bus 1,084,098 0.1% 0.67 0.0% 17.31 0.5% 4.60 0.0% Transit Bus 4,299,279 0.2% 3.03 0.2% 52.21 1.6% 39.82 0.2% School Bus 1,877,130 0.1% 2.59 0.2% 15.75 0.5% 39.95 0.2% Refuse Truck 816,172 0.0% 0.40 0.0% 7.64 0.2% 3.78 0.0% Single Unit Short-haul Truck 35,499,638 2.0% 31.55 2.0% 171.61 5.4% 600.73 3.0% Single Unit Long-haul Truck 4,998,783 0.3% 3.54 0.2% 21.82 0.7% 63.23 0.3% Motor Home 2,138,229 0.1% 3.79 0.2% 12.48 0.4% 79.60 0.4% Combination Short-haul Truck 27,579,440 1.6% 12.45 0.8% 298.27 9.3% 76.40 0.4% Combination Long-haul Truck 38,600,223 2.2% 38.92 2.5% 563.64 17.6% 157.17 0.8%
Tota l 1,745,736,483 100.0% 1,540.23 100.0% 3,197.99 100.0% 20,163.87 100.0%

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 16,935,055 0.5% 80.05 3.0% 16.06 0.3% 430.73 1.2% Passenger Car 1,706,141,922 55.3% 772.77 29.1% 939.84 18.0% 10,908.77 31.5% Passenger Truck 899,318,290 29.1% 1,244.31 46.8% 1,885.61 36.1% 16,259.96 47.0% Light Commercial Truck 302,486,201 9.8% 414.24 15.6% 728.77 13.9% 5,478.07 15.8% Intercity Bus 1,087,104 0.0% 0.73 0.0% 17.37 0.3% 5.06 0.0% Transit Bus 2,617,401 0.1% 1.96 0.1% 30.52 0.6% 25.10 0.1% School Bus 956,631 0.0% 1.64 0.1% 8.14 0.2% 26.35 0.1% Refuse Truck 1,169,548 0.0% 0.61 0.0% 10.98 0.2% 5.65 0.0% Single Unit Short-haul Truck 51,207,845 1.7% 48.35 1.8% 253.29 4.8% 873.53 2.5% Single Unit Long-haul Truck 7,207,246 0.2% 5.47 0.2% 32.11 0.6% 91.66 0.3% Motor Home 3,086,215 0.1% 5.74 0.2% 17.75 0.3% 111.43 0.3% Combination Short-haul Truck 39,750,979 1.3% 19.37 0.7% 438.75 8.4% 117.26 0.3% Combination Long-haul Truck 55,698,637 1.8% 62.06 2.3% 850.59 16.3% 246.14 0.7% Tota l 3,087,663,074 100.0% 2,657.30 100.0% 5,229.77 100.0% 34,579.73 100.0% County Sourcetype

County Sourcetype County Sourcetype

Appendix D-2-4 11Appendix D-2-4-2 2011 Pittsbur g h-Beaver Valle y Area Emission Summar y

b y Process Annual (Tons/Year)

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Allegheny Running Exhaust 1,608.95 20.7% 11,045.92 74.3% 40,743.48 41.3% Start Exhaust 4,268.72 55.0% 3,209.05 21.6% 57,544.54 58.4% Evap Permeation 342.62 4.4% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 936.59 12.1% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 415.95 5.4% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 22.40 0.3% 2.21 0.0% 8.99 0.0%

Crankcase Start Exhaust 56.37 0.7% 0.12 0.0% 7.43 0.0%
Crankcase Extended Idle Exhaust 1.57 0.0% 0.19 0.0% 0.41 0.0% Extended Idle Exhaust 102.08 1.3% 608.47 4.1% 230.52 0.2% Tota l 7,755.2 5 100.0 % 14,865.9 6 100.0 % 98,535.3 6 100.0 %

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Armstrong Running Exhaust 113.57 18.6% 913.42 74.7% 2,907.52 39.0% Start Exhaust 361.22 59.1% 256.82 21.0% 4,525.96 60.7% Evap Permeation 25.53 4.2% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 66.96 10.9% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 29.00 4.7% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 1.62 0.3% 0.21 0.0% 0.70 0.0%

Crankcase Start Exhaust 4.77 0.8% 0.01 0.0% 0.60 0.0%
Crankcase Extended Idle Exhaust 0.14 0.0% 0.02 0.0% 0.04 0.0% Extended Idle Exhaust 8.84 1.4% 52.54 4.3% 19.97 0.3% Tota l 611.6 3 100.0 % 1,223.0 2 100.0 % 7,454.7 9 100.0 %

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Beaver Running Exhaust 244.19 19.8% 1,744.74 73.7% 6,184.45 39.8% Start Exhaust 691.15 56.1% 519.45 22.0% 9,324.53 60.0% Evap Permeation 55.47 4.5% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 146.13 11.9% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 65.80 5.3% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 3.40 0.3% 0.35 0.0% 1.37 0.0%

Crankcase Start Exhaust 9.13 0.7% 0.02 0.0% 1.20 0.0% Crankcase Extended Idle Exhaust 0.26 0.0% 0.03 0.0% 0.07 0.0% Extended Idle Exhaust 17.00 1.4% 101.24 4.3% 38.38 0.2% Tota l 1,232.5 2 100.0 % 2,365.8 3 100.0 % 15,550.0 1 100.0 %

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Butler Running Exhaust 342.51 20.5% 2,699.89 76.5% 9,169.52 43.3% Start Exhaust 954.41 57.1% 677.44 19.2% 11,970.42 56.5% Evap Permeation 67.57 4.0% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 186.14 11.1% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 79.21 4.7% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 4.82 0.3% 0.58 0.0% 2.07 0.0%

Crankcase Start Exhaust 12.61 0.8% 0.02 0.0% 1.57 0.0% Crankcase Extended Idle Exhaust 0.39 0.0% 0.05 0.0% 0.10 0.0% Extended Idle Exhaust 25.17 1.5% 149.65 4.2% 56.83 0.3% Tota l 1,672.8 3 100.0 % 3,527.6 3 100.0 % 21,200.5 1 100.0 % County Process

County Process

County Process

County Process

Appendix D-2-4 12VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Fayette Running Exhaust 181.83 16.3% 1,388.20 71.2% 4,853.80 36.2% Start Exhaust 684.72 61.4% 484.05 24.8% 8,511.73 63.5% Evap Permeation 48.41 4.3% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 121.58 10.9% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 53.40 4.8% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 2.55 0.2% 0.29 0.0% 1.08 0.0%

Crankcase Start Exhaust 9.04 0.8% 0.02 0.0% 1.09 0.0% Crankcase Extended Idle Exhaust 0.20 0.0% 0.02 0.0% 0.05 0.0% Extended Idle Exhaust 13.04 1.2% 77.62 4.0% 29.46 0.2% Tota l 1,114.7 7 100.0 % 1,950.2 0 100.0 % 13,397.2 1 100.0 %

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Washington Running Exhaust 304.13 19.7% 2,414.86 75.5% 8,323.06 41.3% Start Exhaust 870.85 56.5% 655.74 20.5% 11,789.21 58.5% Evap Permeation 69.83 4.5% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 177.07 11.5% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 80.94 5.3% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 4.26 0.3% 0.50 0.0% 1.84 0.0%

Crankcase Start Exhaust 11.50 0.7% 0.02 0.0% 1.54 0.0% Crankcase Extended Idle Exhaust 0.33 0.0% 0.04 0.0% 0.09 0.0% Extended Idle Exhaust 21.31 1.4% 126.83 4.0% 48.13 0.2% Tota l 1,540.2 3 100.0 % 3,197.9 9 100.0 % 20,163.8 7 100.0 %

VOC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Westmoreland Running Exhaust 540.36 20.3% 3,909.77 74.8% 14,530.38 42.0% Start Exhaust 1,480.31 55.7% 1,111.96 21.3% 19,964.97 57.7% Evap Permeation 118.83 4.5% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 314.15 11.8% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 141.26 5.3% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 7.49 0.3% 0.73 0.0% 3.05 0.0%

Crankcase Start Exhaust 19.55 0.7% 0.04 0.0% 2.56 0.0% Crankcase Extended Idle Exhaust 0.54 0.0% 0.06 0.0% 0.14 0.0% Extended Idle Exhaust 34.82 1.3% 207.21 4.0% 78.63 0.2% Tota l 2,657.3 0 100.0 % 5,229.7 7 100.0 % 34,579.7 3 100.0 % County Process County Process

County Process

Appendix D-2-4 13

# APPENDIX D-2-5 Berks County Emission Summary Tables

Appendix D-2-5-1 2011 July Weekday Emissions

Emission Summary Emission Summary by Road Type Emission Summary by Source Type

Emission Summary by Process



### Appendix D-2-5-2 2011 Annual Emissions

Emission Summary Emission Summary by Road Type Emission Summary by Source Type

Emission Summary by Process

## Appendix D-2-5-1 2011 Berks County Emission Summary Summer Weekday (Tons/Day)

Count y V MT Speed ( mph ) V OC NOX CO

Berks 10,470,736 44.1 9.86 22.11 98.88

Appendix D-2-5 2

### Appendix D-2-5-1 2011 Berks County Emission Summary by Road Type Summer Weekday (Tons/Day)

Count y Road Typ e V MT Speed (mph) V OC NO X CO Berks Off-Network

- - 6.71 4.60 37.84 Rural Restricted Access 1,414,342 64.9 0.39 3.73 8.89 Rural Unrestricted Access 2,632,956 43.2 0.78 3.98 14.05 Urban Restricted Access 2,000,510 55.5 0.55 3.58 13.19 Urban Unrestricted Access 4,422,928 37.2 1.44 6.22 24.90 Tota l 10,470,736 9.86 22.11 98.88

Appendix D-2-5 3Appendix D-2-5-1 2011 Berks County Emission Summary by Source Type Summer Weekday (Tons/Day)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Berks Motorcycle 53,974 0.5% 0.34 3.5% 0.04 0.2% 0.89 0.9% Passenger Car 5,437,643 51.9% 2.48 25.1% 3.39 15.3% 24.26 24.5% Passenger Truck 2,861,906 27.3% 4.63 47.0% 6.60 29.9% 48.48 49.0% Light Commercial Truck 968,363 9.2% 1.49 15.1% 2.46 11.1% 15.78 16.0% Intercity Bus 13,116 0.1% 0.01 0.1% 0.18 0.8% 0.05 0.1% Transit Bus 22,121 0.2% 0.01 0.1% 0.24 1.1% 0.20 0.2% School Bus 11,810 0.1% 0.01 0.1% 0.08 0.4% 0.22 0.2% Refuse Truck 8,101 0.1% 0.00 0.0% 0.07 0.3% 0.03 0.0% Single Unit Short-haul Truck 356,843 3.4% 0.32 3.3% 1.47 6.7% 5.47 5.5% Single Unit Long-haul Truck 50,247 0.5% 0.03 0.3% 0.19 0.8% 0.55 0.6% Motor Home 21,507 0.2% 0.04 0.4% 0.11 0.5% 0.66 0.7% Combination Short-haul Truck 277,044 2.6% 0.12 1.2% 2.58 11.7% 0.74 0.8% Combination Long-haul Truck 388,060 3.7% 0.37 3.7% 4.70 21.2% 1.53 1.5% Total 10,470,736 100.0% 9.86 100.0% 22.11 100.0% 98.88 100.0% County Sourcetype

Appendix D-2-5 4

### Appendix D-2-5-1 2011 Berks County Emission Summary by Process Summer Weekday (Tons/Day)

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Berks Running Exhaust 2.42 24.5% 17.51 79.2% 61.02 61.7% Start Exhaust 3.75 38.0% 3.69 16.7% 37.38 37.8% Evap Permeation 0.98 9.9% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 1.86 18.9% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 0.57 5.7% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 0.03 0.3% 0.00 0.0% 0.02 0.0%

Crankcase Start Exhaust 0.05 0.5% 0.00 0.0% 0.01 0.0% Crankcase Extended Idle Exhaust 0.00 0.0% 0.00 0.0% 0.00 0.0% Extended Idle Exhaust 0.20 2.0% 0.91 4.1% 0.45 0.5% Total 9.8 6 100.0 % 22.11 100.0 % 98.8 8 100.0 % County Process

Appendix D-2-5 5

## Appendix D-2-5-2 2011 Berks County Emission Summary Annual (Tons/Year)

Count y V MT Speed ( mph ) V OC NOX CO

Berks 3,381,679,051 44.7 3,479.35 8,073.19 43,022.47

Appendix D-2-5 6

### Appendix D-2-5-2 2011 Berks County Emission Summary by Road Type Annual (Tons/Year)

Count y Road Typ e V MT Speed (mph) V OC NO X CO Berks Off-Network

- - 2,487.41 1,795.63 23,447.90 Rural Restricted Access 455,630,812 64.9 122.95 1,366.70 2,858.36 Rural Unrestricted Access 850,765,567 43.6 246.35 1,420.02 4,527.45 Urban Restricted Access 636,983,988 57.1 169.32 1,287.24 4,158.49 Urban Unrestricted Access 1,438,298,684 37.8 453.31 2,203.61 8,030.28 Tota l 3,381,679,051 3,479.35 8,073.19 43,022.47

Appendix D-2-5 7Appendix D-2-5-2 2011 Berks County Emission Summary by Source Type Annual (Tons/Year)

VMT VOC NOX CO Miles Pct. Emissions Pct. Emissions Pct. Emissions Pct. Berks Motorcycle 17,438,221 0.5% 93.54 2.7% 16.65 0.2% 439.03 1.0% Passenger Car 1,756,833,196 52.0% 972.43 27.9% 1,231.13 15.2% 12,510.13 29.1% Passenger Truck 924,645,260 27.3% 1604.56 46.1% 2,374.32 29.4% 20,193.82 46.9% Light Commercial Truck 312,865,900 9.3% 518.27 14.9% 876.38 10.9% 6,614.15 15.4% Intercity Bus 3,853,491 0.1% 2.30 0.1% 60.93 0.8% 15.76 0.0% Transit Bus 7,365,809 0.2% 5.12 0.1% 91.96 1.1% 69.06 0.2% School Bus 3,932,516 0.1% 5.00 0.1% 33.45 0.4% 77.74 0.2% Refuse Truck 2,603,985 0.1% 1.20 0.0% 24.11 0.3% 11.65 0.0% Single Unit Short-haul Truck 114,896,970 3.4% 97.00 2.8% 547.58 6.8% 1,907.60 4.4% Single Unit Long-haul Truck 16,177,425 0.5% 10.87 0.3% 69.77 0.9% 201.90 0.5% Motor Home 6,924,108 0.2% 11.90 0.3% 40.77 0.5% 259.28 0.6% Combination Short-haul Truck 89,172,150 2.6% 38.42 1.1% 944.92 11.7% 237.61 0.6% Combination Long-haul Truck 124,970,020 3.7% 118.73 3.4% 1,761.22 21.8% 484.74 1.1% Total 3,381,679,051 100.0% 3,479.35 100.0% 8,073.19 100.0% 43,022.47 100.0% Sourcetype

Appendix D-2-5 8

### Appendix D-2-5-2 2011 Berks County Emission Summary by Process Annual (Tons/Year)

V OC NOX CO Emissions Pct. Emissions Pct. Emissions Pct. Berks Running Exhaust 761.05 21.9% 6,276.10 77.7% 19,569.84 45.5% Start Exhaust 1784.51 51.3% 1,419.28 17.6% 23,299.82 54.2% Evap Permeation 177.43 5.1% 0.00 0.0% 0.00 0.0% Evap Fuel Vapor Venting 461.93 13.3% 0.00 0.0% 0.00 0.0% Evap Fuel Leaks 194.92 5.6% 0.00 0.0% 0.00 0.0% Crankcase Running Exhaust 10.86 0.3% 1.46 0.0% 4.74 0.0%

Crankcase Start Exhaust 23.59 0.7% 0.05 0.0% 3.12 0.0% Crankcase Extended Idle Exhaust 0.99 0.0% 0.12 0.0% 0.26 0.0% Extended Idle Exhaust 64.07 1.8% 376.19 4.7% 144.70 0.3% Total 3,479.3 5 100.0 % 8,073.1 9 100.0 % 43,022.4 7 100.0 %

\ County Process

Appendix D-2-5 9

# APPENDIX D-3
MOVES Sample Input FilesAppendix D-3 1 

# July Weekday MOVES Run Specification File Settings

Sample xml file format

<moves> <importer mode="county" > <filters> <geographicselections> <geographicselection type="COUNTY" key="42025" description="PENNSYLVANIA - Carbon County"/> </geographicselections> <timespan> <year key="2011"/> <month id="07"/> <day id="2"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateBy key="Hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="62" sourcetypename="Combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="61" sourcetypename="Combination Short- haul Truck"/> <onroadvehicleselect ion fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="41" sourcetypename="Intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="32" sourcetypename="Light Commercial Truck"/>

< onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="54" sourcetypename="Motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="11" sourcetypename="Motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="21" sourcetypename="Passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="31" sourcetypename="Passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="51" sourcetypename="Refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="43" sourcetypename="School Bu s"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="53" sourcetypename="Single Unit Long- haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="52" sour cetypename="Single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="42" sourcetypename="Transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" so urcetypeid="62" sourcetypename="Combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="61" sourcetypename="Combination Short- haul Truck"/> <onroadvehicleselection fueltype id="1" fueltypedesc="Gasoline" sourcetypeid="41" sourcetypename="Intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="32" sourcetypename="Light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="54" sourcetypename="Motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="11" sourcetypename="Motorcycle"/> <onroadvehicleselecti on fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="21" sourcetypename="Passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="31" sourcetypename="Passenger Truck"/>

< onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="51" sourcetypename="Refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="43" sourcetypename="School Bus"/>

< onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="53" sourcetypename="Single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="52" sourcetypename="Single Unit Short- haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="42" sourcetypename="Transit Bus"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="Off-Network"/> <roadtype roadtypeid="2" roadtypename="Rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="Rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="Urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="Urban Unrestricted Access"/> </roadtypes> </filters> <databaseselection servername="localhost" databasename="42025_2011_07_05_JulWkd_OZ_CO_mi"/> <agedistribution> <description><![CDATA[]]></description> <parts>Appendix D-3 2 <sourceTypeAgeDistribution> <filename>C:\PAMOVES11\MOVESInputs\AgeDistribution\11Reg_RepCty\2011\ 42035_2011_SourceTypeAgeDistribution.csv</filename> </sourceTypeAgeDistribution> </parts> </agedistribution>

<avgspeeddistribution> <description><![CDATA[]]></description> <parts> <avgSpeedDistribution> <filename>C:\PAMOVES11\Out\PA_2011_Julwkd_OZ_CO\\42025_2011_07_05_JulWkd_OZ_CO\CDM\ avgSpeedDistribution.csv</filename> </avgSpeedDistribution> </parts> </avgspeeddistribution>

<imcoverage> <description><![CDATA[]]></description> <parts> <imcoverage> <filename>C:\PAMOVES11\MOVESInputs\IM\42000_2011_IMCoverage.csv</filename> </imcoverage> </parts> </imcoverage>

<fuel> <description><![CDATA[]]></description> <parts> <FuelSupply> <filename>C:\PAMOVES11\MOVESInputs\Fuel\MOVES2010a\42000_2011_FuelSupply.csv</filename> </FuelSupply> <FuelFormulation> <filename>C:\PAMOVES11\MOVESInputs\Fuel\42000_FuelFormulation_MOVES2010a.csv</filename> </FuelFormulation> </parts> </fuel>

<zonemonthhour> <description><![CDATA[]]></description> <parts> <zoneMonthHour> <filename>C:\PAMOVES11\MOVESInputs\Meteorology\2008\42025_2008_met.csv</filename> </zoneMonthHour> </parts> </zonemonthhour>

<roadtypedistribution> <description><![CDATA[]]></description> <parts> <roadTypeDistribution> <filename>C:\PAMOVES11\Out\PA_2011_Julwkd_OZ_CO\\42025_2011_07_05_JulWkd_OZ_CO\CDM\ roadTypeDistribution.csv</filename> </roadTypeDistribution> </parts> </roadtypedistribution>

<sourcetypepopulation> <description><![CDATA[]]></description> <parts> <sourceTypeYear> <filename>C:\PAMOVES11\Out\PA_2011_Julwkd_OZ_CO\\42025_2011_07_05_JulWkd_OZ_CO\CDM\ SourceTypePopulation.csv</filename> </sourceTypeYear> </parts> </sourcetypepopulation>

<rampfraction> <description><![CDATA[]]></description> <parts> <roadType> <filename>C:\PAMOVES11\MOVESInputs\RampFraction\rampfraction_defaults.csv</filename>Appendix D-3 3 </roadType> </parts> </rampfraction>

<vehicletypevmt> <description><![CDATA[]]></description> <parts> <hpmsVTypeYear> <filename>C:\PAMOVES11\Out\PA_2011_Julwkd_OZ_CO\\42025_2011_07_05_JulWkd_OZ_CO\ CDM\hpmsVTypeYear.csv</filename> </hpmsVTypeYear> <monthvmtfraction> <filename>C:\PAMOVES11\MOVESInputs\MonthDayHourFractions\2011_MonthFraction\ 42025_2011_MonthVMTFraction.csv</filename> </monthvmtfraction> <dayvmtfraction> <filename>C:\PAMOVES11\MOVESInputs\MonthDayHourFractions\2011_DayFraction\ 42025_2011_dayvmtfraction.csv</filename> </dayvmtfraction> <hourvmtfraction> <filename>C:\PAMOVES11\Out\PA_2011_Julwkd_OZ_CO\\42025_2011_07_05_JulWkd_OZ_CO\CDM\ hourvmtfraction.csv</filename> </hourvmtfraction> </parts> </vehicletypevmt> <avft> <description><![CDATA[]]></description> <parts> <avft> <filename></filename> </avft> </parts> </avft> </importer> </moves>



## Sample mrs file format

<runspec> <description><![CDATA[MOVES2010 RunSpec Created by CENTRAL4 Scenario: CARB 2011 JULWKD JulWkd_OZ_CO Emission Inventory with u ser's data]]></description> <modelscale value="INV"/> <modeldomain value="SINGLE"/> <geographicselections> <geographicselection type="COUNTY" key="42025" description="PENNSYLVANIA - Carbon County"/> </geographicselections> <timespan> <year key="2011"/> <month id="07"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateBy key="Hour"/> </timespan> <onroadvehicleselections>

<onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="Motorcyc le"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="Passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="Passeng er Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="Light Co mmercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="11" sourcetypename="Motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="21" sourcetypename="Passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="31" sourcetypename="Passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="32" sourcetypename="Light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="11" sourcetypename="Motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="21" sourcetypename="Passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="31" sourcetypename="Passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="32" sourcetypename="Light Commercial Truck"/>Appendix D-3 4 <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="Intercit y Bus"/> <onroadvehicleselection fueltypeid="3" fueltypede sc="Compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="Transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="School B us"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="41" sourcetypename="Intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="42" sourcetypename="Transit Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="43" sourcetypename="School Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="41" sourcetypename="Intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="42" sourcetypename="Transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="43" sourcetypename="School Bus"/>

<onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="Refuse T ruck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="Single U nit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="53 " sourcetypename="Single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="Motor Ho me"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="Combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="Combinat ion Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="51" sourcetypename="Refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="52" sourcetypename="Single Unit Short- haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="53" sourcetypename="Single Unit Long- haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="54" sourcetypename="Motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="61" sourcetypename="Combination Short- haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="62" sourcetypename="Combination Long- haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="51" sourcetypename="Refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="52" sourcetypename="Single Unit Short- haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="53" sourcetypename="Single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="54" sourcetypename="Motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="61" sourcetypename="Combination Short- haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="62" sourcetypename="Combination Long-haul Truck"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="Off-Network"/> <roadtype roadtypeid="2" roadtypename="Rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="Rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="Urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="Urban Unrestricted Access"/> </roadtypes> <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey="1" processname="Running Exhaus t"/> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey="15" processname="Crankcase Run ning Exhaust"/> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey= "16" processname="Crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey="17" processname="Crankcase Ext ended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="2" pollutantname="Car bon Monoxide (CO)" processkey="90" processname="Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="1" processname="Running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="15" processname="Crankcase Runni ng Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="16" processname="Crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="17" processname="Crankcase Exten ded Idle Exhaust"/> <pollutantprocessass ociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="90" processname="Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="1" processname="Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="11" processname="Evap Permeation"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="12" processname="Evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non-Methane Hydrocarbons" processkey="13" p rocessname="Evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="15" processname="Crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non-Methane Hydro carbons" processkey="16" processname="Crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="17" processname="Crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="90" processname="Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="1" processname="Running Exhaust"/> <pollut antprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="11" processname="Evap Pe rmeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="12" processname="Evap Fu el Vapor Venting"/>Appendix D-3 5 <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="13 " processname="Evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="15" processname="Crankca se Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="16" processname="Crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="17" processname="Crankca se Extended Idle Exhaust"/> <pollutantprocessassociation poll utantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="90" processname="Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="1" processname="Running Exhaust"/> <pollutan tprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="11" processname="Evap P ermeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="12" processname="Evap F uel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey=" 13" processname="Evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="15" processname="Crankc ase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile O rganic Compounds" processkey="16" processname="Crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="17" processname="Crankc ase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="90" processname="Extended Idle Exhaust"/>

</pollutantprocessassociations> <databaseselections> <databaseselection servername="localhost" databasename="early_NLEV" description=""/> <databaseselection servername="localhost" databasename="calevii08" description=""/> </databaseselections> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="0" numberofsimulations="0"/> <geographicoutputdetail description="COUNTY"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <emissionprocess selected="true"/> <onroadoffroad selected="true"/> <roadtype selected="true"/> <sourceusetype selected="true"/> <movesvehicletype selected="false"/> <onroadscc selected="false"/> <offroadscc selected="false"/> <estimateuncertainty selected="false" numberOfIterations="2" keepSampledData="false" keepIterations="false"/> <sector selected="false"/> <engtechid selected="false"/> <hpclass selected="false"/> </outputemissionsbreakdownselection> <outputdatabase servername="localhost" databasename="42025_2011_07_05_JulWkd_OZ_CO_mo" description=""/>> <outputtimestep value="Hour"/> <outputvmtdata value="true"/> <outputsho value="true"/> <outputsh value="true"/> <outputshp value="true"/> <outputshidling value="true"/> <outputstarts value="true"/> <outputpopulation value="true"/> <scaleinputdatabase servername="localhost" databasename="42025_2011_07_05_JulWkd_OZ_CO_mi" description=""/> <pmsize value="0"/> <outputfactors> <timefactors selected="true" units="Hours"/> <distancefactors selected="false" units="Miles"/> <massfactors selected="false" units="Grams" energyunits="Million BTU"/> </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="false" truncateactivity="false"/> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.Rat eOfProgressStrategy"><![CDATA[
useParameters No

]]></internalcontrolstrategy> </internalcontrolstrategies> </runspec>Appendix D-3 6 

# Annual MOVES Run Specification File Settings

Sample xml file format

<moves> <importer mode="county" > <filters> <geographicselections> <geographicselection type="COUNTY" key="42025" description="PENNSYLVANIA - Carbon County"/> </geographicselections> <timespan> <year key="2011"/> <month id="00"/> <day id="2"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateBy key="Hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="62" sourcetypename="Combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="61" sourcetypename="Combination Short- haul Truck"/> <onroadvehicleselect ion fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="41" sourcetypename="Intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="32" sourcetypename="Light Commercial Truck"/>

< onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="54" sourcetypename="Motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="11" sourcetypename="Motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="21" sourcetypename="Passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="31" sourcetypename="Passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="51" sourcetypename="Refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="43" sourcetypename="School Bu s"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="53" sourcetypename="Single Unit Long- haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="52" sour cetypename="Single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="42" sourcetypename="Transit Bus"/>

< onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="62" sourcetypename="Combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="61" sourcetypename="Combination Short- haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="41" sourcetypename="Intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="32" sourcetypenam e="Light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="54" sourcetypename="Motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="11" sourcetypename="Motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="21" sourcetypename="Passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="31" so urcetypename="Passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="51" sourcetypename="Refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="43" sourcetypename="School Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="53" sourcetypename="Single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="52" sourcetypename="Single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="42" sourcetypename="Transit Bus"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="Off-Network"/> <roadtype roadtypeid="2" roadtypename="Rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="Rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="Urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="Urban Unrestricted Access"/> </roadtypes> </filters> <databaseselection servername="localhost" databasename="42025_2011_00_25_Ann_OZ_CO_mi"/> <agedistribution> <description><![CDATA[]]></description>Appendix D-3 7 <parts> <sourceTypeAgeDistribution> <filename>C:\PAMOVES11\MOVESInputs\AgeDistribution\11Reg_RepCty\2011\ 42035_2011_SourceTypeAgeDistribution.csv</filename> </sourceTypeAgeDistribution> </parts> </agedistribution>

<avgspeeddistribution> <description><![CDATA[]]></description> <parts> <avgSpeedDistribution> <filename>C:\PAMOVES11\Out\PA_2011_Ann_OZ_CO\\42025_2011_00_25_Ann_OZ_CO\CDM\ avgSpeedDistribution.csv</filename> </avgSpeedDistribution> </parts> </avgspeeddistribution>

<imcoverage> <description><![CDATA[]]></description> <parts> <imcoverage> <filename>C:\PAMOVES11\MOVESInputs\IM\42000_2011_IMCoverage.csv</filename> </imcoverage> </parts> </imcoverage>

<fuel> <description><![CDATA[]]></description> <parts> <FuelSupply> <filename>C:\PAMOVES11\MOVESInputs\Fuel\MOVES2010a\42000_2011_FuelSupply.csv</filename> </FuelSupply> <FuelFormulation> <filename>C:\PAMOVES11\MOVESInputs\Fuel\42000_FuelFormulation_MOVES2010a.csv</filename> </FuelFormulation> </parts> </fuel>

<zonemonthhour> <description><![CDATA[]]></description> <parts> <zoneMonthHour> <filename>C:\PAMOVES11\MOVESInputs\Meteorology\2008\42025_2008_met.csv</filename> </zoneMonthHour> </parts> </zonemonthhour>

<roadtypedistribution> <description><![CDATA[]]></description> <parts> <roadTypeDistribution> <filename>C:\PAMOVES11\Out\PA_2011_Ann_OZ_CO\\42025_2011_00_25_Ann_OZ_CO\CDM\ roadTypeDistribution.csv</filename> </roadTypeDistribution> </parts> </roadtypedistribution>

<sourcetypepopulation> <description><![CDATA[]]></description> <parts> <sourceTypeYear> <filename>C:\PAMOVES11\Out\PA_2011_Ann_OZ_CO\\42025_2011_00_25_Ann_OZ_CO\CDM\ SourceTypePopulation.csv</filename> </sourceTypeYear> </parts> </sourcetypepopulation>

<rampfraction> <description><![CDATA[]]></description> <parts> <roadType>Appendix D-3 8 <filename>C:\PAMOVES11\MOVESInputs\RampFraction\rampfraction_defaults.csv</filename> </roadType> </parts> </rampfraction>

<vehicletypevmt> <description><![CDATA[]]></description> <parts> <hpmsVTypeYear> <filename>C:\PAMOVES11\Out\PA_2011_Ann_OZ_CO\\42025_2011_00_25_Ann_OZ_CO\CDM\ hpmsVTypeYear.csv</filename> </hpmsVTypeYear> <monthvmtfraction> <filename>C:\PAMOVES11\MOVESInputs\MonthDayHourFractions\2011_MonthFraction\420 25_2011_MonthVMTFraction.csv</filename> </monthvmtfraction> <dayvmtfraction> <filename>C:\PAMOVES11\MOVESInputs\MonthDayHourFractions\ dayvmtfraction_avgday.csv</filename> </dayvmtfraction> <hourvmtfraction> <filename>C:\PAMOVES11\Out\PA_2011_Ann_OZ_CO\\42025_2011_00_25_Ann_OZ_CO\CDM\ hourvmtfraction.csv</filename> </hourvmtfraction> </parts> </vehicletypevmt> <avft> <description><![CDATA[]]></description> <parts> <avft> <filename></filename> </avft> </parts> </avft>

</importer> </moves>



## Sample mrs file format

<runspec> <description><![CDATA[MOVES2010 RunSpec Created by CENTRAL4 Scenario: CARB 2011 ANNAVG Ann_OZ_CO Emission Inventory with user 's data]]></description> <modelscale value="INV"/> <modeldomain value="SINGLE"/> <geographicselections> <geographicselection type="COUNTY" key="42025" description="PENNSYLVANIA - Carbon County"/> </geographicselections> <timespan> <year key="2011"/>

<month id="1"/> <month id="2"/> <month id="3"/> <month id="4"/> <month id="5"/> <month id="6"/> <month id="7"/> <month id="8"/> <month id="9"/> <month id="10"/> <month id="11"/> <month id="12"/> <day id="2"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateBy key="Hour"/> </timespan>Appendix D-3 9 <onroadvehicleselections>

<onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="Motorcyc le"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="Passenge r Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="Passe nger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="Light Co mmercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="11" sourcetypename="Motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="21" sourcetypename="Passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="31" sourcetypename="Passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="32" sourcetypename="Light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="11" sourcetypename="Motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="21" sourcetypename="Passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="31" sourcetypename="Passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="32" sourcetypename="Light Commercial Truck"/>

<onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="Intercit y Bus"/> <onroadvehicleselection fueltypeid="3" fueltype desc="Compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="Transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="School B us"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="41" sourcetypename="Intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="42" sourcetypename="Transit Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="43" sourcetypename="School Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="41" sourcetypename="Intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="42" sourcetypename="Transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="43" sourcetypename="School Bus"/>

<onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="Refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="Single U nit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="Single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="Motor Ho me"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compres sed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="Combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="Compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="Combinat ion Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="51" sourcetypename="Refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="52" sourcetypename="Single Unit Short- haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="53" sourcetypename="Single Unit Long- haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="54" sourcetypename="Motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="61" sourcetypename="Combination Short- haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="Diesel Fuel" sourcetypeid="62" sourcetypename="Combination Long- haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="51" sourcetypename="Refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="52" sourcetypename="Single Unit Short- haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="53" sourcetypename="Single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="54" sourcetypename="Motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="61" sourcetypename="Combination Short- haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="Gasoline" sourcetypeid="62" sourcetypename="Combination Long-haul Truck"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="Off-Network"/> <roadtype roadtypeid="2" roadtypename="Rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="Rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="Urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="Urban Unrestricted Access"/> </roadtypes> <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey="1" processname="Running Exhaus t"/> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey="15" processname="Crankcase Run ning Exhaust"/> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey="16" processname="Crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="2" pollutantname="Carbon Monoxide (CO)" processkey="17" processname="Crankcase Ext ended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="2" polluta ntname="Carbon Monoxide (CO)" processkey="90" processname="Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="1" processname="Running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="15" processname="Crankcase Runni ng Exhaust"/> <pollutantprocessassociation pollut antkey="3" pollutantname="Oxides of Nitrogen" processkey="16" processname="Crankcase Start Exhaust"/>Appendix D-3 10 <pollutantprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="17" processname="Crankcase Exten ded Idle Exhaust"/> <pollutan tprocessassociation pollutantkey="3" pollutantname="Oxides of Nitrogen" processkey="90" processname="Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="1" processname="Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non-Methane Hydrocarbons" processkey="11" processname="E vap Permeation"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="12" processname="Evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non-Methane Hydrocarbons" proces skey="13" processname="Evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="15" processname="Crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non-Me thane Hydrocarbons" processkey="16" processname="Crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="17" processname="Crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="Non- Methane Hydrocarbons" processkey="90" processname="Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="1" processname="Running Exhaust"/> <pollu tantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="11" processname="Evap Pe rmeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="12" processname="Evap Fu el Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="1 3" processname="Evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="15" processname="Crankca se Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="16" processname="Crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="17" processname="Crankca se Extended Idle Exhaust"/> <pollutantprocessassociation pol lutantkey="1" pollutantname="Total Gaseous Hydrocarbons" processkey="90" processname="Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="1" processname="Running Exhaust"/> <polluta ntprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="2" processname="Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="11" processname="Evap P ermeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="12" processname="Evap F uel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey= "13" processname="Evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="15" processname="Crankc ase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="16" processname="Crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="17" processname="Crankc ase Extended Idle Exhaust"/> <pollutantprocessassociatio n pollutantkey="87" pollutantname="Volatile Organic Compounds" processkey="90" processname="Extended Idle Exhaust"/>

</pollutantprocessassociations> <databaseselections> <databaseselection servername="localhost" databasename="early_NLEV" description=""/> <databaseselection servername="localhost" databasename="calevii08" description=""/> </databaseselections> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="0" numberofsimulations="0"/> <geographicoutputdetail description="COUNTY"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <emissionprocess selected="true"/> <onroadoffroad selected="true"/> <roadtype selected="true"/> <sourceusetype selected="true"/> <movesvehicletype selected="false"/> <onroadscc selected="false"/> <offroadscc selected="false"/> <estimateuncertainty selected="false" numberOfIterations="2" keepSampledData="false" keepIterations="false"/> <sector selected="false"/> <engtechid selected="false"/> <hpclass selected="false"/> </outputemissionsbreakdownselection> <outputdatabase servername="localhost" databasename="42025_2011_00_25_Ann_OZ_CO_mo" description=""/>> <outputtimestep value="Month"/> <outputvmtdata value="true"/> <outputsho value="true"/> <outputsh value="true"/> <outputshp value="true"/> <outputshidling value="true"/> <outputstarts value="true"/> <outputpopulation value="true"/> <scaleinputdatabase servername="localhost" databasename="42025_2011_00_25_Ann_OZ_CO_mi" description=""/> <pmsize value="0"/> <outputfactors> <timefactors selected="true" units="Hours"/> <distancefactors selected="false" units="Miles"/> <massfactors selected="false" units="Grams" energyunits="Million BTU"/>Appendix D-3 11 </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="false" truncateactivity="false"/> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.Rat eOfProgressStrategy"><![CDATA[
useParameters No

]]></internalcontrolstrategy> </internalcontrolstrategies> </runspec>