Idling Vehicle Emissions for Passenger
Cars, Light-Duty Trucks, and Heavy-
Duty Trucks
The amount of pollution that a vehicle emits is dependent on many
factors. The U.S. Environmental Protection Agency (EPA) has
developed a series of computer models that estimate the average emis-
sions for different types of highway vehicles. This fact sheet is one of
a series on highway vehicle emission factors. It presents average emis-
sion rates for passenger cars, light-duty trucks, (e.g., pickup trucks,
sport-utility vehicles), heavy-duty trucks (semi tractor-trailers), and
motorcycles when they are idling.
I-L.
Introduction
There are a number of factors that affect the rate at which any vehicle emits air pol'
lutants, whether the vehicle is being driven or is at idle (engine running, but vehicle
not moving). Some of the most important are:
• vehicle type/size (passenger cars, light-duty trucks, heavy-duty trucks, motor-
cycles)
• vehicle age and accumulated mileage
• fuel used (gasoline, diesel, others)
• ambient weather conditions (temperature, precipitation, wind)
• maintenance condition of the vehicle (well maintained, in need of maintenance,
presence and condition of pollution control equipment)
The most current version of the computer model that EPA uses to estimate average
in-use emissions from highway vehicles is MOBILE6.2. EPA, the States, and others
use this model to estimate total emissions of pollutants generated by highway vehicles
in various geographic areas and over specific time periods. The idle emission rates or
"emission factors" presented in this fact sheet are based on national data representing
the in-use fleet as of July 2008,
United States
Environmental Protection
Agency
Office of Transportation and Air Quality
EPA420-F-08-025
October 2008
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The emission rates of hydrocarbons
(both volatile organic compounds
[VOCs] and Total Hydrocarbons
[THC]), carbon monoxide (CO),
and nitrogen oxides (NOx) for idling
vehicles are presented in the follow'
ing tables. In addition, the emission
rates of particulate matter (PM1C
and PM ,) are provided for heavy-
CO:
g/hr:
g/min:
GVW:
Ib:
NOx:
PM,
10-
PM
2.5'
ppm:
psi:
RVP:
THC:
VMT:
VOC:
Abbreviations and Acronyms Used
Carbon monoxide; a regulated pollutant
Carbon dioxide; the primary byproduct
of all fossil fuel combustion
gram(s)
grams per hour
grams per minute
Gross Vehicle Weight
pound
Nitrogen oxides; a regulated pollutant
Particulate matter under 10 microns
diameter; a regulated pollutant
Particulate matter under 2.5 microns
diameter, sometimes referred to as
"fine particulate"
parts per million
pounds per square inch
Reid vapor pressure; a standardized
method for expressing the volatility,
or tendency to evaporate, of gasoline
Total hydrocarbons
Vehicle miles traveled
Volatile organic compounds; equivalent
to THC plus aldehydes minus both
methane and ethane
duty diesel vehicles only because the
MOBILE model does not include PM
for the other vehicle categories dur-
ing idle operation. 1 These emission
factors assume an "average" properly
maintained vehicle, operating on
typical gasoline or diesel fuel, on a
warm summer day. Emission rates
can be higher in very hot weather
(especially HC) or in very cold
weather (especially CO),
National average values are used
for registration distributions by age
(what fraction of all cars, or light
trucks, in use today are of the cur-
rent model year, are one to two years
old, 2 to 3 years old, and so forth up
to 25 years old) and annual mileage
accumulation rates by age (newer
vehicles tend to be driven more miles
per year than do older vehicles). Some of the other primary assumptions incorporated in these
emission factors are:
Ambient temperatures:
Nominal gasoline volatility:
Weathered fuel volatility:
Gasoline sulfur content:
Diesel sulfur content:
Inspection/maintenance program:
Reformulated gasoline:
72 to 92 °F day time range
9.0 psi Reid vapor pressure (RVP)
8.6 psi RVP
30 ppm
330 ppm
No
No
Note that these emission rates are applicable for relatively short periods of idle time, as observed
in drive-thru lanes, at toll gates, at stop lights, and in very heavily congested traffic. These idle
emission rates are not applicable to "hoteling" situations for heavy-duty diesel trucks, where
the truck engine may be idling for periods of hours at a time with many accessories being oper-
ated from the engine power. EPA is currently studying the issue of emissions from heavy-duty
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diesel trucks during "hoteling" situations; more information on this subject is available on EPA's
SmartWay Transport Partnership Program web site at: www.epa.gov/smartway/idling.htm.
These emission rates also are not applicable for buses (urban transit buses and school buses).
Average idle emission estimates for urban and school buses are provided in the fact sheet
"Average In-Use Emission Factors for Urban Buses and School Buses" (EPA420'F'08'026),
Idle Emission Rates
The following tables present idle emission factors expressed as grams per hour (g/hr) and grams
per minute (g/min) of idle time. Table 1 presents idling emission rates for gasoline-fueled and
diesel cars, light-duty trucks, and heavy-duty vehicles, and motorcycles.
Definitions of Vehicle Types
(Gross Vehicle Weight)
LDGV: Light-duty gasoline-fueled vehicles, up to 6000 Ib GVW (gasoline-fueled passenger
cars)
LDGT: Light-duty gasoline-fueled trucks, up to 8500 Ib GVW (includes pick-up trucks,
minivans, passenger vans, sport-utility vehicles, etc.)
HDGV Heavy-duty gasoline-fueled vehicles, over 8500 Ib GVW (gasoline-fueled heavy-duty
trucks)
LDDV Light-duty diesel vehicles, up to 6000 Ib GVW (diesel engine passenger cars)
LDDT: Light-duty diesel trucks, up to 8500 Ib GVW (diesel engine light-duty trucks)
HDDV Heavy-duty diesel vehicles, over 8500 Ib GVW (diesel engine heavy-duty trucks)
MC: Motorcycles (only those certified for highway use; all are gasoline-fueled)
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The HDDV column represents the average of all diesel engine vehicles over 8,500 Ib gross ve-
hicle weight (GVW); this category is dominated by the heaviest HDDVs (GVW Classes Villa
and VHIb) which exceed 33,000 Ib GVW.
Table 1: Average Idle Emission Rates by Pollutant and Vehicle Type2
Pollutant
VOC
THC
CO
NOx
PM25
PM:o
Units
g/hr
g/min
g/hr
g/min
g/hr
g/min
g/hr
g/min
g/hr
g/min
g/hr
g/min
LDGV
2.683
0.045
3.163
0.053
71.225
1.187
3.515
0.059
N/A1
N/A1
N/A1
N/A1
LDGT
4.043
0.067
4.838
0.081
72.725
1.212
4.065
0.068
N/A1
N/A1
N/A1
N/A1
HDGV
6.495
0.108
7.260
0.121
151.900
2.532
5.330
0.089
N/A1
N/A1
N/A1
N/A1
LDDV
1.373
0.023
1.353
0.023
7.018
0.117
2.690
0.045
N/A1
N/A1
N/A1
N/A1
LDDT
2.720
0.045
2.680
0.045
5.853
0.098
3.705
0.062
N/A1
N/A1
N/A1
N/A1
HDDV
3.455
0.058
3.503
0.058
25.628
0.427
33.763
0.563
1.100
0.018
1.196
0.020
MC
19.153
0.319
21.115
0.352
301.075
5.018
1.625
0.027
N/A1
N/A1
N/A1
N/A1
Table 2 presents HDDV idle emission rates by weight class. The GVW weight classes are:
Heavy-Duty Diesel Vehicle Classifications
(Gross Vehicle Weight)
lib: 8,501-10,000 Ib (e.g., full-size pick-up trucks, very large passenger vans)
III: 10,001-14,000 Ib (e.g., panel trucks, small enclosed delivery trucks)
IV: 14,001-16,000 Ib (e.g., city delivery trucks, landscape utility trucks)
V 16,001-19,500 Ib (e.g., bucket utility trucks, large walk-in delivery trucks)
VI: 19,501-26,000 Ib (e.g., rack trucks, single axle vans)
VII: 26,001-33,000 Ib (e.g., tow trucks, garbage collection trucks)
Villa: 33,001-60,000 Ib (e.g., long-haul semi-tractor trailer rigs)
VHIb: > 60,000 Ib (e.g., long-haul semi-tractor trailer rigs)
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Table 2: Average Idle Emission Rates for Heavy-Duty Diesel Vehicles by GVW Class3
Pollutant
voc
THC
CO
NOx
PM25
PM10
Units
g/hr
g/min
g/hr
g/min
g/hr
g/min
g/hr
g/min
g/hr
g/min
g/hr
g/min
lib
1.465
0.024
1.498
0.025
9.305
0.155
12.668
0.211
1.103
0.018
1.199
0.020
III
1.555
0.026
1.580
0.026
10.068
0.168
13.530
0.226
1.010
0.017
1.098
0.018
IV
2.025
0.034
2.055
0.034
12.898
0.215
17.850
0.298
1.065
0.018
1.157
0.019
V
2.120
0.035
2.150
0.036
13.183
0.220
18.655
0.311
1.008
0.017
1.095
0.018
VI
2.820
0.047
2.865
0.048
15.163
0.253
24.325
0.405
1.069
0.018
1.162
0.019
VII
3.503
0.058
3.553
0.059
19.055
0.318
30.343
0.506
1.093
0.018
1.188
0.020
Villa
3.518
0.059
3.565
0.059
26.548
0.442
35.758
0.596
1.070
0.018
1.163
0.019
VIHb
4.218
0.070
4.270
0.071
34.473
0.575
42.345
0.706
1.114
0.019
1.211
0.020
For More Information
The other fact sheets in this series and additional information are available on the Office of
Transportation and Air Quality's Web site at:
Emission factor fact sheets:
Modeling and estimating vehicle emissions:
Fuel economy:
Improving fuel economy and reducing emissions:
Finding the "greenest" vehicle:
www.epa.gov/otaq/consumer.htm
www.epa.gov/otaq/models.htm
www.epa.gov/fueleconomy
www.fueleconomy.gov/
www.epa.gov/epahome/trans.htm
www.fueleconomy.gov/feg/drive.shtml
www.epa.gov/greenvehicles
Endnotes
1. The MOBILE model includes PM estimates for heavy-duty diesel vehicles only during idle
operation because there has been insufficient emission testing of PM for gasoline-fueled vehicles
of the type necessary to develop emission rates for these vehicles at idle, since the PM
contribution to ambient air quality from gasoline vehicles and the few light duty diesel cars and
trucks in the fleet is normally negligible.
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2. Figures presented in this fact sheet are averages only. Individual vehicles can differ
substantially in the amount of pollution emitted while idling from the values indicated here.
Emission rates may differ slightly from original sources due to rounding,
3. All of the emission estimates provided in this document are consistent, in terms of assumptions
made and modeling methodology, with those provided in the other fact sheets in this series:
"Average Annual Emissions and Fuel Consumption for Gasoline-Fueled Passenger Cars and
Light Trucks" (EPA420'F-08-024), "Average In-Use Emissions from Heavy-Duty Trucks"
(EPA420'F'08'027), and "Average In-Use Emission Factors for Urban Buses and School Buses"
(EPA420-F-08-026).
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