United States
Environmental Protection
Agency
National Risk Management
Research Laboratory
CINCINNATI, OH 45268
Research and Development
EPA/600/SR-98/097   August 1998
Project Summary
A  CIS-Based  Modal  Model  of
Automobile  Exhaust Emissions
William H. Bachman
  Suburban sprawl, population growth,
and auto-dependency have been linked,
along with other factors, to air pollution
problems in U.S. metropolitan  areas.
Addressing  these problems becomes
difficult when trying to accommodate
the needs of a growing population and
economy while simultaneously  lower-
ing or maintaining levels of ambient pol-
lutants.  Growing urban areas  must,
therefore, continually develop creative
strategies to curb increased  pollutant
production.
  The report presents progress toward
the development of a  computer  tool
called MEASURE, the Mobile Emission
Assessment System  for Urban  and
Regional Evaluation. The tool works to-
ward a goal of providing researchers
and planners with a way to assess new
mobile emission mitigation strategies.
The model  is  based on a geographic
information system  (GIS) and  uses
modal emission rates, varying emis-
sions according to vehicle technologies
and modal operation (acceleration, de-
celeration, cruise, and idle). Estimates
of spatially  resolved fleet composition
and activity are  combined with situa-
tion-specific emission  rates to predict
engine start and running exhaust emis-
sions. The  estimates are provided at
user-defined spatial scales. A demon-
stration of modal operation is  provided
using a 100 km2 study area in Atlanta,
Georgia. Future mobile emissions mod-
eling research needs are developed
from an analysis of the sources of
model error.
  This Project Summary was developed
by the National Risk Management Re-
search Laboratory's Air Pollution Pre-
vention and Control Division, Research
Triangle Park, NC, to announce key find-
ings of the research project that is fully
documented in a separate report of the
same title (see Project Report ordering
information at back).

Introduction
  Suburban sprawl,  population  growth,
and auto-dependency have been linked,
along with  other factors, to air  pollution
problems in U.S metropolitan areas. Ac-
cordingly,  the  Clean Air Act and  other
federal legislation and regulations require
metropolitan areas to develop strategies
for reducing air pollution where air quality
standards are  exceeded. An emissions
'budget' is established in metropolitan ar-
eas that provides a benchmark for com-
paring new emission-generating activity,
and presumably not exceeded.  Such a
goal becomes difficult when trying to ac-
commodate the needs of a growing popu-
lation and economy while simultaneously
lowering or maintaining  levels of ambient
pollutants. Growing  urban  areas, there-
fore,  must continually  develop  creative
strategies to curb increased pollutant pro-
duction. Because the largest contributor
of pollutant emissions in urban areas has
most often been transportation (or mobile)
sources, transportation is targeted for new
control strategies.
  Developing measures of effectiveness
and subsequent predictions of overall
impact for  control  strategies require an
understanding of the relationship  between
observable transportation system charac-
teristics and emission production. Quan-
tifying this effectiveness requires modeling

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these relationships. According to published
research, motor vehicle emission rates are
correlated to a variety of vehicle charac-
teristics (weight, engine size, emission con-
trol equipment, etc.), operating modes (idle,
cruise, acceleration, and deceleration), and
transportation  system conditions  (road
grade, pavement condition, etc.). Exhaust
emissions are produced when a vehicle is
started and while  it is operating.  Pollut-
ants produced from starting a vehicle can
be predicted using vehicle characteristics.
Running  exhaust  emissions additionally
require estimates of dynamic engine con-
ditions that result from how the vehicle is
driven. Estimating motor vehicle emissions
requires the ability to predict or measure
these parameters for an entire  region at a
level of spatial and temporal aggregation
fitting the scope of control strategies. Cur-
rent modeling approaches, however, can-
not provide these estimates.

Emission Modeling
  Today's motor vehicle emission model-
ing process  is based on four  separate
models:  a  travel  demand forecasting
model, a  mobile emission model, a photo-
chemical model (for emission  inventory),
and  a microscale  model (for  analyzing
transportation improvements). The  travel
demand forecasting model uses charac-
teristics of the transportation system and
socioeconomic data to develop estimates
of road-specific traffic volumes  and aver-
age speeds. Mobile emission models use
these travel demand estimates, operating
fleet model  year distributions,  and envi-
ronmental conditions to develop estimates
of mobile  source  pollutant  production.
                   These estimates are fed into photochemi-
                   cal models (along  with stationary source
                   estimates and data regarding atmospheric
                   conditions) and are used to predict ambi-
                   ent  pollutant levels in space and  time.
                   These mobile source estimates can then
                   be used by microscale models to predict
                   pollutant  levels near specific transporta-
                   tion facilities.
                     Several  problems with the four-model
                   system limit effective evaluation of motor
                   vehicle emission control strategies.  First,
                   the  estimates  of vehicle activity (vehicle
                   miles traveled and average speed)  lack
                   the accuracy and spatial resolution needed
                   to evaluate control  measures. Second, the
                   mobile source emission rate modeling pro-
                   cess uses highly aggregate fleet average
                   emission  rates which are not specific for
                   the  fleet  in operation,  mode  of vehicle
                   operation, or grade of the highway facility.
                   As a consequence, the  current modeling
                   system has limited capabilities for meet-
                   ing the modeling  requirements of trans-
                   portation planners. Transportation planners
                   and environmental assessment and con-
                   trol officials have need for improved  mod-
                   els  that  help  identify  the  impacts of
                   standard  transportation  system improve-
                   ments (e.g., lane additions, signal timing,
                   peak-hour smoothing).
                     While many researchers agree that new
                   models and processes need to be devel-
                   oped to overcome these problems, they
                   disagree over the best approach. The U.S.
                   Environmental  Protection Agency and the
                   Federal  Highway  Administration  held  a
                   workshop  in Ann Arbor,  Michigan, in May
                   1997, to identify and discuss current emis-
                   sion modeling  research  efforts. After the
                                       workshop, it was clear that defining ap-
                                       propriate model aggregation levels is im-
                                       portant in defining how and what research
                                       should be conducted. A point of departure
                                       between the largest vehicle emissions re-
                                       search efforts  (University of California  at
                                       Riverside, and the Georgia  Institute  of
                                       Technology) and the currently mandated
                                       approach (MOBILESa) is the  level of ag-
                                       gregation required.  Figure  1  shows the
                                       spectrum of possible approaches. It shows
                                       that highly aggregate approaches limit ex-
                                       planatory power, but  have  reduced data
                                       intensity. Disaggregate models have the
                                       most explanatory power, but  the  highest
                                       data needs.  An  added dimension  of the
                                       issue  is that estimates must  be spatially
                                       and temporally resolved, suggesting that
                                       an undefined level of spatial and temporal
                                       aggregation must also be defined. In fact,
                                       the level of spatial and temporal aggrega-
                                       tion of mobile source emissions needed
                                       by photochemical models may help define
                                       the minimum level of model  aggregation
                                       currently being debated.
                                         The  report presents a research model
                                       that can guide future mobile emissions
                                       model  development efforts. A major ob-
                                       jective  of the model is to incorporate the
                                       latest  transportation / air quality findings
                                       at  a low level  of spatial aggregation (re-
                                       stricted only  by data availability). Creating
                                       a model under these guidelines develops
                                       information  that leads to the  maximum
                                       level of disaggregation given  user needs
                                       and data availability. The research model
                                       will be comprehensive, flexible, and user
                                       oriented. It  includes enhanced  vehicle
                                       activity measures: starts, idle, cruise, ac-
                                       celeration, and deceleration. Vehicle tech-
                                                        Emission Rates
     Average Fleet
        (g/trip)
  Vehicle Class
 Average Speed
     (g/mi)
Tech Groups'
Vehicle Mode
   (g/sec)
Tech Groups'
Vehicle Mode
   (g/sec)
Individual Vehicles
  Vehicle Mode
     (g/sec)
Individual Vehicles
  Engine Mode
     (g/sec)
                 Aggregate
    Total Trips/Day
  Vehicle Class
     VMTb
Mean Link Speeds
 Tech Group
Speed/Accel.
   Profiles
 Tech Group
 Traffic Flow
 Simulation
                                                        Vehicle Activity
a Tech groups refer to sets of vehicles with similar emission characteristics.
b Vehicle miles traveled.
                                                                           Disaggregate
    Vehicle
    Activity
   Simulation
 Vehicle/Engine
    Activity
   Simulation
Figure 1.    Spectrum of modeling approaches.

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nology characteristics (model year, engine
size, etc.) and operating conditions (road
grade, traffic flow, etc.) are developed at
a large scale  (small zones and road seg-
ments). Flexibility is achieved  through  a
modular  design that separates emission
production based on  thresholds determined
in background research. Due to  large gaps
in the state of knowledge, technology, and
practice regarding travel behavior, emis-
sion rates, and the  urban  system inven-
tory, the accuracy  of the  model results
remains  unvalidated and  therefore  un-
known. However, the model contributes to
transportation and air quality research in
that it aids research and software devel-
opment.
  The intended model users include emis-
sion science  experts, model developers,
transportation  planners, policy makers, and
government researchers. Each user group
has specific modeling interests that define
how the  model should  be designed and
presented.  Central to the model design is
a geographic  information system (CIS).
  GISs are widely  used computer tools
that allow geographically referenced data
to  be organized and manipulated. Both
transportation and air quality vary in spa-
tial  dimensions. Thus, GISs have the con-
ceptual  capability to  manage the
relationships  between transportation  ac-
tivity  and  resulting  air  quality changes
based on their spatial characteristics. Fur-
ther, GISs are already used by most plan-
ning  organizations  in   government
institutions. Thus, a  CIS-based  emissions
modeling framework fits the character of
emission science as well as the technical
environment of the expected users.
  The variables included in the  proposed
research model are  those whose relation-
ship to vehicle activity and  emission rates
has been defined in  research and is avail-
able to public agencies. They can be cat-
egorized as:
  Spatial Character:
  •  U.S. Census block  boundaries
  •  Land use boundaries
  •  Traffic analysis zone boundaries (from
    travel demand forecasting model)
  •  Grid cell boundaries (defined by user)
  •  Road segments (by classification)
  •  Travel demand  forecasting  network
    links
  •  Grade school and university locations
  Temporal Character:
  •  Hour of the day
  Vehicle Technology:
  •  Model year
  •  Engine size
  •  Vehicle weight
  •  Emission control equipment
  •  Fuel injection type
  Modal Activity:
  •  Idle
  •  Cruise
  •  Acceleration
  •  Deceleration
  Trip Generation:
  •  Home-based work trips
  •  Home-based shopping trips
  •  Home-based university trips
  •  Home-based grade school trips
  •  Home-based other trips
  •  Non-home-based trips
  Road Geometries:
  •  Number of lanes
  •  Grade
  Socioeconomic Characteristics (for spa-
tial allocation only):
  •  Housing units
  •  Land use  (residential,  nonresidential,
    and commercial)

Summary of Contributions to
Research
  •  An  automobile  exhaust  emissions
    model is developed maximizing com-
    prehensiveness, flexibility, and  user
    friendliness.
  Comprehensiveness is ensured by in-
cluding  variables  and procedures identi-
fied  in  the  literature as  significant  to
emission  rate modeling.  Flexibility  is
achieved by organizing  the  model com-
ponents by geographic location,  and by
maintaining a  modular program  design.
User friendliness  is  achieved  by  includ-
ing  only current data available to plan-
ning agencies,  and by  using   a  CIS
framework.
  •  A research tool is provided that al-
    lows for testing variable levels of mo-
    tor  vehicle  emission  model  spatial
    aggregation.
  By having the flexibility to use a variety
of spatial entities, the model  can become
a testbed for determining the spatial reso-
lution needed  for future  models. This in-
formation is valuable in identifying future
research needs,  costs of  emission  esti-
mation, model development, maintenance,
and operation. A question this model could
be used to help answer would  be,  "Given
the  current state  of research, does a  1
km2 aggregation of ozone precursors pro-
vide enough  resolution to predict ozone
formation, or  would a 4 km2 aggregation
be better?"
  •  The benefits of using GIS  for emis-
    sions modeling are demonstrated.
  GISs provide the ability to organize data
by location, in turn providing the  capability
to develop relationships with new or exist-
ing  spatial datasets. This  allows the de-
velopment of creative alternatives to model
construction  and  provides the  ability  to
prioritize emission control strategies based
on location.
  •  Research and data  needs for im-
    proved spatial and temporal emissions
    modeling are identified.
  A study of background research into
emissions  modeling, coupled  with an
analysis of data  available  in Atlanta, will
determine gaps  in important  emission-
specific  variables. Further, a  prioritization
of the data  needs based on  balancing
explanatory  power and cost will  guide
future model  development.

Report Organization
  Chapter 1  presents an  introduction to
the  report and provides an  overview of
the  research being presented to the  reader.
Chapter 2 discusses background research
significant to   automobile  exhaust  emis-
sion modeling, vehicle activity  modeling,
and  GISs.  It  also  identifies a  research
foundation of  knowledge that is used to
develop model parameters. Chapter 3 pre-
sents a  conceptual model  design that
serves as the foundation of the research
approach. Accuracy, comprehensiveness,
user needs, and enterprise awareness are
important considerations in  developing this
conceptual model. Chapter 4 provides  a
physical model structure that  can be  used
as a research tool. The  model will reside
in a UNIX operating system and use Make,
the  C programming language, and ARC/
INFO. A step-by-step guide to model use
is also provided. Chapters 5 and  6 present
and analyze a model implementation for a
100 km2 area  in  Atlanta. Each module of
the  system  is studied  using  sensitivity
analysis or a comparison  of observed  data.
Chapter 7 discusses data needs and pre-
sents final conclusions.  An expanded
model diagram demonstrates how future
vehicle  types  and operating modes can
be added to  the system. Chapter 8 lists
references cited in the report, and Appen-
dix A is  a data dictionary.

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   I/I/ Bachman is with the School of Civil and Environmental Engineering, Georgia
     Institute of Technology, Atlanta, GA 30332.
   Carl T. Ripberger is the EPA Project Officer (see below).
   The complete report,  entitled "A GIS-Based Modal Model of Automobile Exhaust
     Emissions," (Order No. PB98-165145; Cost: $44.00, subject to change) will be
     available only from:
           National Technical Information Service
           5285 Port Royal Road
           Springfield, VA 22161
           Telephone:  703-487-4650
   The EPA Project Officer can be contacted at:
           Air Pollution Prevention and Control Division
           National Risk Management Research Laboratory
           U.S. Environmental Protection Agency
           Research Triangle Park,  NC 27711
United States
Environmental Protection Agency
CenterforEnvironmental Research Information
Cincinnati, OH 45268
      BULK RATE
POSTAGE & FEES PAID
        EPA
   PERMIT No. G-35
Official Business
Penalty for Private Use
$300
EPA/600/SR-98/097

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