United States
Environmental Protection
#»Agency

Office of Land and Emergency Management (5203)
EPA 542-F-23-001	March 2023 Update

Green Remediation Best Management Practices:
Cleaner Fuels and Air Emissions for Site
Cleanups

A fact sheet about the concepts and tools for using best management practices to
reduce the environmental footprint of fuel consumption and associated air emissions
during site investigation and remediation

Overview	Page 1

Advanced Emission Control Technologies	Page 2
for Vehicles and Engines

Operation and Maintenance	Page 3

Transportation Plans	Page 4

Energy

The U.S. Environmental Protection Agency (EPA) Principles for Greener Cleanups outline the Agency's policy for evaluating and
minimizing the environmental footprint of activities involved in cleaning up contaminated sites.1 Best management practices (BMPs)
of green remediation involve specific activities to address the core elements of greener cleanups:

~	Reduce total energy use and increase the percentage of energy from renewable resources.

~	Reduce air pollutants and greenhouse gas (GHG) emissions.

Reduce water use and preserve water quality.

*¦ Conserve material resources and reduce waste.

~	Protect land and ecosystem services.	Water

Materials
& Waste

Core

Land & Elements Air &
Ecosystems	Atmosphere

BMPs focused on the core elements concerning energy consumption and air quality may also help mitigate and adapt to ongoing
climate change.

Overview

Environmental investigation and remediation at hazardous waste sites can involve significant consumption of fossil fuels such as
gasoline and diesel by vehicles and mobile or stationary equipment that may act as non-point sources of air pollution. Minimizing
emission of air pollutants such as GHGs and particulate matter (PM) resulting from cleanup activities is a core element of green
remediation strategies. Efforts to reduce these emissions during site investigation, remedial or corrective actions, and long-term
operation and maintenance (O&M) of site remedies must meet Clean Air Act (CAA) requirements and state air quality standards as
well as relevant requirements of federal and state cleanup programs. The CAA specifies ground-level ozone, PM, carbon monoxide,
nitrogen dioxide, sulfur dioxide and lead as the nation's criteria air pollutants. EPA's air quality criteria and national ambient air
quality standards (NAAQS) for criteria pollutants must be met in all state implementation plans.

Burning of fossil fuels results in significant emission of carbon dioxide (CO2), a
GHG that disturbs the earth's natural carbon cycle and greatly contributes to
climate changes.2 Ongoing EPA analyses indicate that CO2 accounted for 79.5
percent of the GHGs emitted in the United States in 2021.3 Related EPA studies
of GHG emissions by U.S. economic sectors indicate that the transportation
sector and electric power sector are the two largest contributors to CO2 emissions
resulting from the combustion of petroleum, coal and natural gas. The majority
of fossil fuel directly consumed during site cleanup results from using onroad and offroad
vehicles and stationary or mobile equipment powered by internal combustion engines.

The use of fossil fuels also increases production of ground-level ozone, which can trigger
human health problems such as aggravated asthma and reduced lung function. As of
late 2020, EPA analyses indicate that about 22 percent of the U.S. population lives within
three miles of a Superfund remedial site.5 Additionally, airborne pollutants are among the
impacts that disproportionally affect communities with environmental justice concerns,
including those regarding local Superfunds sites; hazardous waste treatment, storage and
disposal facilities; and brownfields.6 EPA is accordingly collecting air quality data in such
communities to support improved compliance with state and federal air quality standards.

Green remediation BMPs focused on air quality can reduce the environmental footprints
of cleanup projects while improving their public health outcomes and helping mitigate
climate change. BMPs relating to air quality also help meet goals of the Diesel Emissions
Reduction Act, which prioritizes environmental justice and emissions reductions in areas

EPA's Green Remediation Best Management
Practices: Integrating Renewable Energy fact
sheet provides information about applying solar
electric and other renewable energy
technologies to avoid or offset the Use of grid
electricity produced from fossil fuels>

EPA's Spreadsheets for Environmental
Footprint Analysis (SEFA) tool was
used to estimate fuel consumption
and air emissions involved in
corrective action at the Bay Road
Holdings LLC site in East Palo Alto,
California.7


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2

Green Remediation BMPs: Cleaner Fuels and Air Emissions for Site Cleanups

receiving disproportionate impacts from diesel fleets. EPA's Web-based EJScreen provides information and mapping on
socioeconomic demographics and environmental indicators such as Superfund site proximity and diesel PM within a given
geographic area.8

Fleets of transportation and construction vehicles deployed for site cleanup typically encompass a range of vehicle types. Light-duty
vehicles with a gross vehicle weight rating (GVWR) below 8,500 pounds (such as sport-utility vehicles, light-duty trucks and medium-
duty passenger vehicles) are commonly used to transport workers, small equipment and small quantities of supplies. Heavy-duty
commercial vehicles such as cargo vans or light-duty trucks rated above 8,500 pounds GVWR are often deployed to transport
heavier loads and serve as a platform for field equipment such as hollow-stem auger drill rigs needed for collection of subsurface
environmental samples.

Nonroad vehicles such as bulldozers, excavators and graders are used for purposes such as demolishing buildings, constructing
remedies such as landfill caps, or contouring disturbed ground surfaces. Additionally, tractor trailers may be intermittently required
to transport heavy construction equipment or materials to and from the site or to transfer contaminated waste to an offsite facility.

Diesel Consumption and Estimated CO2 Emissions in an Illustrative Excavation and Soil Amendment Project



Diesel

CO2

Activity

Consumption

Emission



(gallons)

(tons)*

Removing 35,000 cubic yards of contaminated soil by way of an excavator

4,000

89,800

Hauling excavated soil to a hazardous waste disposal facility 1 00 miles away byway of tractor trailers

11,666

261,902

Importing wood milling and agricultural waste from sources 50 miles away by way of dump trucks

2,400

53,880

Applying soil amendments and contouring ground surfaces byway of a grader

288

6,465

Using two medium-duty pickup trucks for site preparation and remedy construction over six months

500

1 1,225

Total diesel consumption and associated air emissions

18.854

423,272

*Based on an emission coefficient of 22.45 pounds per gallon, https://www.eia.gov/environment/emissions/co2_vol_mass.php

Advanced Emission Control Technologies for Vehicles and Engines

Reductions in PM, nitrogen oxides (NOx) and other air pollutants from vehicles and
mobile or stationary equipment can be achieved through BMPs such as:

~	Replace older vehicles and older equipment engines with newer ones meeting the
most recent emission control standards.

~	Use newer emission control components to rebuild engines.

~	Retrofit diesel engines with exhaust aftertreatment devices.

EPA continues to update fuel economy and emission standards that must be met by
manufacturers of onroad and offroad vehicles deployed in the United States. The "Tier
3" emission and fuel standards finalized in 2014 apply to passenger cars, light-duty
trucks, medium-duty passenger vehicles, and some heavy-duty vehicles.9 Vehicles
meeting Tier 3 standards are equipped with emission reduction technologies as well as
engines that have been calibrated to optimize fuel consumption while minimizing
emissions.

"Tier 4" emission standards apply to nonroad compression-ignition (diesel) engines used
in machines such as the drill rigs, excavators, pumps and compressors commonly required
for site characterization, remedy construction or remedial operations. Tier 4 standards
also apply to nonroad spark-ignition engines used in equipment such as generators and
forklifts fueled by propane, gasoline or natural gas.10

EPA and the California Air Resources Board maintain lists of relevant technologies that
have been verified to reduce the harmful impacts of diesel exhaust. '* Technologies
commonly integrated in newer vehicles and engines include diesel oxidation catalysts
(DOCs) and diesel particulate filters (DPFs). Information about installing DOCs and DPFs
in older vehicles is available in EPA technical bulletins.Ij

Offroad vehicles equipped with
diesel-electric power trains and Tier 4
compliant engines were used to
minimize fuel consumption and air
emissions during remedy construction
at the Elizabeth Mine Superfund site in
Vermont. Use of a bulldozer with an
electric power train, for example,
decreased its fuel consumption by
about 30 percent and increased its
productivity by about 1 0 percent.
Deployment of excavators powered by
Tier 4 engines over six months was
estimated to reduce PM emissions by
90 percent and NOx by 50 percent
and improve fuel efficiency by 5
percent.14


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Green Remediation BMPs: Cleaner Fuels and Air Emissions for Site Cleanups

Another technology that has been integrated in newer vehicles and engines involves selective catalytic reduction (SCR) systems,
which reduce the excess NOx formed by a lean-burn engine. EPA conducted a modeling study of the potential changes in local air
quality attributable to applying SCR technology in mobile equipment such as diesel-fired generators and in onroad or offroad
vehicles deployed for Superfund remedy construction. Results showed a 65 percent reduction of NOx emission could be achieved
over a five-day period, leading to a 49 percent reduction in ground-level ozone formation over the same period.1: The findings are
particularly relevant in areas where NAAQS are exceeded (non-attainment areas) and to populations that are disproportionately
exposed to ground-level ozone or other air pollutants and consequently suffer associated health problems. Ground-level ozone
also reduces respiration and associated photosynthesis in trees and other vegetation providing communities with ecosystem services
such as air purification and flood control.

Requirements for emission reduction and tracking are increasingly integrated in contracts for site investigative or remedial services
and associated purchase or rental agreements. EPA's Motor Vehicle Emission Simulator (MOVES) can be used to estimate air
pollution emissions for criteria air pollutants, GHGs and air toxics associated with onroad vehicle and nonroad fleets.16 Decisions
regarding vehicle or engine replacements may be informed by EPA's Power Profiler, which describes the type and amount of
emissions associated with electricity production in specific regions of the United
States.1' In certain applications, government funding under the Diesel Emissions
Reductions Act may be available to help cover the costs of replacing diesel
vehicles and engines with ones fueled by electricity, which is considered an
alternative fuel under the Energy Policy Act.18

Operation arid Maintenance

Site management plans and service or product procurements can specify other BMPs
relevant to onsite driving and in some cases offsite driving. The manners in which vehicles
and equipment are operated and maintained directly affect their performance and fuel
efficiency; the harder an engine must work, the more fuel it requires. As a result, many
BMPs focused on O&M can help decrease fuel-related project costs.

Eliminating unnecessary vehicle engine idle can significantly reduce fuel consumption and
associated air emissions. For example, a Class 6 medium-duty commercial truck is often
used to transport large quantities of supplies. A single hour of idling by this type of vehicle
during loading or unloading would typically consume approximately 0.84 gallons of
gasoline20 and emit an estimated 16.5 pounds of CO2 equivalent.21 Similarly, heavy
nonroad vehicles are often used for remedy construction activities such as excavating
contaminated materials and building subsurface pipelines. Manufacturers estimate that
such vehicles conventionally idle an average of 28 to 38 percent of their operating
times.22

In addition to unnecessarily burning fuel, excessive idling also shortens engine service
lives, poses health and safety risks to vehicle and cab occupants if emission leaks occur,
and increases noise pollution in local communities. Relevant BMPs include:

~	Manually shut down engines of vehicles not actively engaged for more than 1 0
seconds, except for work requiring intermittent engine use or when in traffic.20

~	Engage automatic shut-down devices, which typically can be programmed to cut
an engine after as little as five consecutive minutes of idling.

~	Install a direct-fired air heater, which consumes only a small amount of a vehicle's
fuel supply and eliminates the need for idling to heat an engine or a cab interior.

~	Improve a vehicle engine's cold-weather startup ease by installing a coolant
heater in the engine compartment or adding a waste-heat recovery system.

~	Deploy energy storage batteries in the back of a truck that provides power take-off for auxiliary equipment.

~	Recharge laptop computers and mobile devices in vehicles that are in active motion rather than idling.

Fuel conservation can also be maximized by properly maintaining all onroad and offroad vehicles to avoid overworking their
engines. Routine maintenance should include practices such as:

~	Ensure sufficient inflation and tread and proper alignment of tires, to minimize rolling resistance. For example, a 1 0 percent
reduction in rolling resistance would improve fuel economy by about 3 percent for light- and heavy-duty vehicles. Additional
efficiency may be gained by replacing worn tires with models that are SmartWay verified for low rolling resistance.2

~	Use the vehicle manufacturer's recommended grade of motor oil, which can impact fuel economy up to 2 percent.

To evaluate replacement and upgrade options
for heavy-duty diesel engines in greater detail,
access EPA's web-based Diesel Emissions
Quantifier.?'

Application of the ASTM Standard
Guide for Greener Cleanups
(E2893)24 to plan bioremediation
activities at Travis Air Force Base in
Solano County, California, indicated
that minimizing Usage of
transportation fuel and related air
emissions was a high priority. Bulk
quantities of the selected biological
reagent (emulsified vegetable oil)
were shipped to the site via rail lines
rather than trucks. Locomotive
engines meeting Tier 4 emission
standards are estimated to produce
about two-thirds less GHG than
typical truck engines. Additionally, the
reagents were injected into the
subsurface via hydraulic pressure
instead of fuel-fired hydraulic
pumps.35


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Green Remediation BMPs: Cleaner Fuels and Air Emissions for Site Cleanups

~	Replace filters in air and fuel systems in accordance with the vehicle manufacturer's recommended frequencies, which
typically distinguish between a normal-duty cycle versus a severe-duty cycle that accounts for usage conditions such as
unpaved roads or high levels of dust or pollen.

~	Clean emission control systems such as SCR systems and DPFs on a regular basis to prevent plugging, remove
contaminants, and reduce engine back pressure.

~	Check brake parts such as calipers and pads and promptly replace worn parts to avoid brake drag.

~	Clean mass airflow sensors to assure the proper air-fuel mixture is entering the engines.

~	Replace engine oil on a timely basis to avoid worn piston rings that reduce engine efficiency.

~	Secure prompt interim maintenance when the vehicle's "check engine" light becomes illuminated.

Other BMPs focus on sources of air pollutants attributable to diesel, gasoline, propane or natural gas consumed by stationary or
mobile equipment deployed in site characterization or in groundwater, soil or sediment treatment systems. For example:

~	Use solar or wind energy resources instead of diesel to generate electricity for
equipment such as water pumps that recirculate, extract or transfer contaminated
groundwater. Any excess energy produced from these renewable resources can be
stored in transportable battery banks that could power additional equipment,
recharge electric vehicles or provide emergency backup power.

~	Use hydrogen fuel cells to operate critical equipment or provide additional backup
power. Fuel cell generators are twice as efficient as diesel generators and emit
little or no emissions.27

~	Maintain diesel-fueled compression engines in equipment such as air compressors
and blowers in accordance with manufacture recommendations, and retrofit or
replace such equipment as needed to meet Tier 4 emission standards.

~	Integrate heat exchangers in groundwater treatment systems involving heated
fluids, to beneficially use the systems' waste heat. A heat exchange process can
eliminate or reduce the use of fuel-fired equipment for purposes such as pre-
heating cold fluids entering the treatment stream.

~	Replace aged equipment supporting onsite building operations, such as material
chilling units and water heaters, with newer models meeting the latest energy-
efficiency standards set by the U.S. Department of Energy (DOE).28

~	Replace gasoline engines with diesel engines meeting Tier 4 emission standards,
which are typically equipped with SCR and DPF technologies that reduce NOx and
PM by more than 90%.

~	Ensure the leak detection systems of pressurized equipment such as propane
storage tanks and natural gas pipelines operate at all times, to avoid fugitive emission of methane and other GHGs. Leaky
valves and seals typically account for a significant portion of fugitive emissions from an industrial process.

~	Downsize energy-intensive equipment that has become oversized as cleanup progresses.

Green remediation BMPs specific to pump and
treat technology, bioremediation, soil vapor
extraction and other frequently used
remediation technologies are described in
companion EPA fact sheets.d2

Transportation Plans

Transportation planning for a site cleanup project can specify strategies to minimize fuel consumption and related air emissions
throughout the project's life. General BMPs include:

~	Choose the nearest offsite site laboratories, material vendors and waste facilities, to reduce shipping distances.

~	Import supplies and export wastes via full rather than partial vehicle loads whenever feasible.

~	Facilitate staff carpooling opportunities, to minimize travel to and from the site or other destinations on a given day.

~	Deploy plug-in or hybrid electric vehicles to the greatest extent possible as the U.S. transition to electric vehicles continues.

~	Schedule heavy shipping or construction activities to occur during spring or autumn, to avoid contributing to ground-level
ozone formation that is typically higher during summer due to higher air temperatures and humidity levels.

~	Purchase lower carbon fuels where available, such as El 5 for gasoline vehicles or E85 for flex-fuel vehicles. Diesel-fueled
equipment can often use diesel blends containing up to 20% biodiesel (B20), and renewable diesel (an advanced renewable
fuel) can be used safely in diesel engines in any amount.33

~	Choose material or waste haulers that use SmartWay designated trailers and tractors and SmartWay verified technologies
relating to low rolling resistance tires, idling reduction and aerodynamic devices.34

Operation of photovoltaic systems at
the Frontier Fertilizer Superfund site in
Davis, California, avoids an estimated
147,500 pounds in CO2 (equivalent)
emissions each year. The systems
involve a ground-mounted solar array
as well as a roof-mounted solar array
that together offset 1 00 percent of the
grid electricity used to pump and treat
the site's contaminated
groundwater.29

The California Air Resources Board offers a list of verified diesel emission control
devices applying to stationary engines.30 Related compliance requirements
issued by EPA may be used to guide selection and retrofitting of stationary
engines at area sources of hazardous air pollutants.3'


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Green Remediation BMPs: Cleaner Fuels and Air Emissions for Site Cleanups

Transportation plans can encourage offsite drivers to reduce fuel consumption through sensible driving techniques. Also, certain
techniques help reduce local noise pollution attributed to operating transport vehicles. BMPs include:

~	Use a suitably sized vehicle for the task at hand. For example, use of an oversized truck to transfer a small amount of waste
to a disposal facility results in wasted fuel.

~	Combine trips to avoid unnecessary stopping and starting of engines. Multiple short trips can use twice as much fuel as one
long, multi-purpose trip that covers the same distance while the engine is warm and at its most fuel-efficient temperature.

~	Reduce vehicle loads by offloading any unneeded items, and avoid using rooftop cargo carriers.

~	Use overdrive gearing whenever feasible to reduce an engine's speed, which in turn reduces fuel consumption, extends
engine life, and lessens engine noise.

~	Avoid rapid acceleration, excessive speed and repetitive hard braking, which lowers gas mileage by as much as 30 percent.

~	Refrain from using a jake brake in or near residential neighborhoods and other sensitive communities.

~	Use a reliable navigation system that enables selecting the shortest route to destinations and avoiding traffic events that may
trigger vehicle idling.

References

1	U.S. EPA. Greener Cleanups. Principles for Greener Cleanups, https://www.epa.gov/greenercleanups

2	National Research Council. Climate Change: Evidence and Causes. Update 2020. http://nap.nationalacademies.org/25733

3	U.S. EPA. Draft Inventory of U.S. Greenhouse Gas Emissions and Sinks: 1990-2021. https://www.epa.gov/ghgemissions/inventory-us-greenhouse-gas-
emissions-and-sinks

4	U.S. EPA. Green Remediation Best Management Practices: Integrating Renewable Energy. EPA 542-F-22-01. March 2022. https://clu-
in.org/greenremediation/docs/GR_fact_sheet_renewable_energy.pdf

5	U.S. EPA. Population Surrounding 7,857 Superfund Remedial Sites. September 2020. https://www.epa.gov/sites/default/files/2015-
09/documents/webpopulationrsuperfundsites9.28.15.pdf

6	U.S. EPA. EJ Action Plan: Building Up Environmental Justice in EPA's Land Protection and Cleanup Programs. EPA 502/P-21/001. September 2022.
https://www.epa.gov/environmentaljustice/environmental-iustice-action-plan-epas-land-protection-and-cleanup-programs

7	U.S. EPA. Environmental Footprint Analysis of Three Potential Remedies: Former Romic Environmental Technologies Corporation Facility/ East Palo Alto,
California. May 1 1, 2010. https://clu-in.org/greenremediation/romic/docs/romic_report_rev_051 1 10.pdf

8	U.S. EPA. EJScreen: Environmental Justice Screening and Mapping Tool, https://www.epa.gov/ejscreen

9	U.S. EPA. Final Rule for Control of Air Pollution from Motor Vehicles: Tier 3 Motor Vehicle Emission and Fuel Standards, https://www.epa.gov/regulations-
emissions-vehicles-and-engines/final-rule-control-air-pollution-motor-vehicles-tier-3

10	U.S. EPA. Regulations for Emissions from Heavy Equipment with Compression-Ignition (Diesel) Engines, https://www.epa.gov/regulations-emissions-vehicles-
and-engines/ regulations-emissions-heavy-equipment-compression

11	U.S. EPA. Verified Technologies List for Clean Diesel, https://www.epa.gov/verified-diesel-tech/verified-technologies-list-clean-diesel

12	California Air Resources Board. Verification Procedures: Currently Verified, https://ww2.arb.ca.gov/diesel/verdev/vt/cvt.htm

13	U.S. EPA. Information on Diesel Particulate Filters and Diesel Oxidation Catalysts, https://www.epa.gov/verified-diesel-tech/information-diesel-particulate-
filters-and-diesel-oxidation-catalysts

14	U.S. EPA CLU-IN Green Remediation Focus. Green Remediation Profile: Elizabeth Mine, https://clu-in.org/greenremediation/profiles/elizabethmine

15	U.S. EPA. Analysis of the Benefits of Green Remediation Best Management Practices for Local Air Quality. Prepared by Charlene V. Lawson. December 201 2.
https://clu-in.org/greenremediation/docs/Analysis_of_the_Benefits_of_GR_BMPs_for_Local_Air_Quality_201 2.pdf

16	U.S. EPA. Latest Version of Motor Vehicle Emission Simulator (MOVES), https://www.epa.gov/moves/latest-version-motor-vehicle-emission-simulator-moves

17	U.S. EPA. Power Profiler, https://www.epa.g0v/egrid/power-profiler#/

18	U.S. EPA. Diesel Emissions Reduction Act (DERA) Funding, https://www.epa.gov/dera

19	U.S. EPA. Diesel Emissions Quantifier, https://cfpub.epa.gov/quantifier/index.cfm?action = main.home

20	Argonne National Laboratory. Idling Reduction Savings Calculator, https://www.anl.gov/sites/www/files/2018-02/idling_worksheet.pdf

21	U.S. EPA. Greenhouse Gas Equivalencies Calculator, https://www.epa.gov/energy/greenhouse-gas-equivalencies-calculator

22	Construction Equipment. How to Manage Engine Idling for Efficiency. March 24, 2020. https://www.constructionequipment.com/topical/green-
resources/article/1 07571 22/how-to-manage-engine-idling-for-efficiency

23	U.S. DOE. Idle Reduction, https://afdc.energy.gov/conserve/idle_reduction_medium.html

24	ASTM International. Standard Guide for Greener Cleanups. ASTM E2893-1 6. https://www.astm.org/e2893-16e01 .html

25	U.S. EPA. CLU-IN Green Remediation Focus. Green Remediation Profile: Travis Air Force Base, https://clu-in.org/greenremediation/profiles/travisafb

26	U.S. EPA. SmartWay Verified List for Low Rolling Resistance (LRR) New and Retread Tire Technologies, https://www.epa.gov/verified-diesel-tech/smartway-
verified -1 ist- low- ro I ling -resistance-1 rr-new-and- retread-tire

27	U.S. DOE. Fuel Cells, https://www.energy.gov/eere/fuelcells/fuel-cells

28	U.S. DOE. Energy Efficiency & Renewable Energy. Buildings: Standards and Test Procedures, https://www.energy.gov/eere/buildings/standards-and-test-
procedures

29	U.S. EPA. CLU-IN Green Remediation Focus. Green Remediation Profile: Frontier Fertilizer Superfund Site. https://clu-
i n .org/ g ree n rem ed iatio n/prof i les/f ro ntie rferti I ize r

30	California Air Resources Board. Diesel Certifications, Verifications, and Related Links, https://ww2.arb.ca.gov/diesel/verdev/vt/stationary.htm

31	U.S. EPA. Compliance Requirements for Stationa 17 Engines, https://www.epa.gov/stationary-engines/compliance-requirements-stationary-engines

32	U.S. EPA. Best Management Practices. https://clu-in.org/greenremediation/BMPs

33	U.S. Department of Energy, Alternative Fuels Data Center, Renewable Hydrocarbon Biofuels, https://afdc.energy.gov/fuels/emerging_hydrocarbon.html

34	U.S. EPA. SmartWay Technology, https://www.epa.gov/verified-diesel-tech/smartway-technology

This fact sheet provides an update on information compiled in the August 2010
"Best Management Practices: Clean Fuel & Emission Technologies for Site Cleanup"' fact sheet (EPA 542-F-l 0-008),
in collaboration with the Greener Cleanups Subcommittee of the U.S. EPA Technical Support Project's Engineering Forum.
To view BMP fact sheets on other topics, visit CLU-IN Green Remediation Focus: www.clu-in.org/greenremediation.


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