United States
Environmental Protection
Agency
Using Coal Ash in Highway Construction:
A Guide to Benefits and Impacts
'
'INTERNATIONAL!
EPA-530-K-05-002
April 2005
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Acknowledgments
This document was prepared by the U.S. Environmental Protection Agency (EPA),
in cooperation with the following agencies and associations:
Department of Energy (DOE)
Federal Highway Administration (FHWA)
The American Coal Ash Association (ACAA)
The Utility Solid Waste Activities Group (USWAG)
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III PC11C1I13
Alkali-Silicate Reactivity: The reaction between the alkalies (sodium and potassi-
um) in Portland cement with certain siliceous rocks and minerals, such as opaline
chert, strained quartz, and acidic volcanic glass, present in some aggregates; the
products of the reaction can cause abnormal expansion and cracking of concrete in
service. Class F fly ash is used in concrete to reduce the occurrence of alkali-silica
reactivity.
Attenuation: The reduction in mass or concentration of a compound in ground
water over time or distance from the source of constituents of concern due to nat-
urally occurring physical, chemical, and biological processes, such as biodegreda-
tion, dispersion, dilution, adsorption, and volatilization.
Beneficial Uses: The use of byproducts in such a manner that the material serves a
beneficial function, while not adversely impacting human health or the environ-
ment. Beneficial uses of byproducts include construction applications (e.g., brick
and concrete products, road bed, blasting grit, wall board, insulation, roofing mate-
rials), agricultural applications (e.g., as a substitute for lime) and other applications
(e.g., absorbents, filter media, paints, plastics and metals manufacture, snow and
ice control, waste stabilization).
Borrow Pit: An area from which soil is excavated for use as a fill material in a high-
way application.
Cement Clinker: The fused particles or pellets produced from the sintering or burn-
ing zone (2200° F to 2700° F) of a rotary kiln in the cement manufacturing process.
Raw materials (limestone, shale, iron ore, sand) are proportioned and ground to a
powder and blended before being processed through the rotary kiln.
Coal Combustion Products (CCPs): Residues from coal burning, including bottom
ash, fly ash, boiler slag, and flu gas desulfurization materials (FGD), which can be
used beneficially. (The use of the term "coal combustion products" in this docu-
ment does not change the legal definition of solid waste as defined in RCRA 42
U.S.C. 6903(27).)
Concrete: A construction material consisting primarily of aggregates, Portland
cement, and water. Certain coal ashes can be used as a replacement for a portion
of the Portland cement.
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Engineered Application: Use of a byproduct that has been specifically designed and
engineered (for example, a road design that incorporates appropriate run-off con-
trol and provides adequate strength for the required use).
Fill: Material such as dirt, gravel, or coal ash used to build up an area of land.
Flowable Fill: A fill material that flows like a liquid, is self-leveling, requires no com-
paction or vibration to achieve maximum density, hardens to a predetermined
strength, and is sometimes used as a controlled low-strength material.
Flue Gas Desulfurization Materials (FGD): The materials created during the process
of removing gaseous sulfur dioxide from boiler exhaust gas. FGD materials often
are used as a replacement for gypsum in wallboard.
Heat of Hydration: Heat evolved by chemical reactions with water such as during
the setting and hardening of Portland cement.
Leachate: The liquid, including any suspended components in the liquid, that has
percolated through or drained from a pile or cell of solid materials; the liquid
stream that issues from a pile or cell of solid materials and that contains water,
dissolved solids, and decomposition products of the solids.
Maximum Contaminant Level (MCL): The highest level of a contaminant that is
allowed in drinking water.
Portland Cement: A hydraulic cement made by heating a mixture of limestone and
clay containing oxides of calcium, aluminum, iron, and silicon in a kiln and pulveriz-
ing the resulting clinker.
Pozzolanic Properties: The phenomenon of strength development that occurs when
lime and certain aluminosilicates react at ambient temperatures in the presence of
water.
Sulfate Attack: Either a chemical or physical reaction (or both) between sulfates,
usually in soil or ground water, and concrete and mortar. The chemical reaction is
primarily with calcium aluminate hydrates in the cement-paste matrix and can
cause deterioration of the cement product.
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In ancient times, the Romans added
volcanic ash to concrete to strengthen
structures such as the Roman Pantheon
and the Coliseum—both of which still
stand today.
The first major use of coal fly ash in con-
crete in the United States occurred in
1942 to repair a tunnel spillway at the
Hoover Dam.
One of the most impressive concrete
structures in the country, the Hungry
Horse Dam near Glacier National Park
in Montana, was constructed from 1948
to 1952, with concrete containing
coal fly ash.
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In Washington, DC, both the metropol-
itan area subway system (Metro) and
the new Ronald Reagan Building and
International Trade Center were built
with concrete containing coal fly ash.
Other significant structures utilizing
coal fly ash in concrete include the
"Big Dig" in Boston and the decks
and piers of Tampa Bay's Sunshine
Skyway Bridge.
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Using Coal in
A to nl
The U.S. Environmental Protection Agency (EPA) encourages the use of
coal combustion products (CCPs) in highway construction projects such
as in concrete, road base, embankments, flow/able fill, and other benefi-
cial applications. The increased use of these materials, which would otherwise be
discarded as waste, can reduce greenhouse gases in the atmosphere, reduce
energy consumption, and conserve natural resources. Some applications, such as
road embankments and other non-encapsulated (loose) uses, may require the eval-
uation of local hydrogeological conditions to ensure protection of human health and
the environment.
To encourage the increased use of coal combustion products, EPA, the Department
of Energy, and the Federal Highway Administration, along with the American Coal
Ash Association and the Utility Solid Waste Activities Group, are co-sponsoring the
Coal Combustion Products Partnership (C2P2). The purpose of C2P2 is to foster the
beneficial uses of coal combustion products. This booklet is intended to help users
and the public understand both the environmental benefits and potential impacts
of using coal combustion products in various applications. EPA and the National
Academy of Sciences are evaluating the use of coal combustion products as mine-
fill and will address this issue separately.
;•%€'
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Background Basics 3
What Are Coal Combustion Products? 3
How Are Coal Combustion Products Used? 4
How Are Coal Combustion Products Used in Highway Applications? 6
What Are the Engineering Performance Standards for Using Coal Ash in Highway
Construction? 8
Are There State Requirements for Using Coal Ash in Highway Construction?.... 9
Performance and Cost Benefits 12
In Concrete 12
In Embankments 13
In Flowable Fill 13
In Stabilized Base Course 14
In Asphalt Pavements 14
In Grouts for Pavement Subsealing 14
Environmental Benefits 16
Greenhouse Gas Emissions and Energy Reductions 16
Resource Conservation 18
Solid Waste Reduction 19
Environmental and Health Cautions Associated with Concrete
(Encapsulated) Uses 20
Environmental and Health Cautions Associated with
Unencapsulated Uses 21
Water Issues: Groundwater/Surface Water Health and Human Ingestion 22
Vegetation and Food Chain Issues 26
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Air Issues: Air Quality and Inhalation 26
Occupational Issues: Inhalation and Skin Contact 27
EPA's Position on the Use of Coal Combustion Products 30
Regulatory Determinations 30
Procurement Policy 31
Case Studies 32
Concrete Pavement:
Cold In-Place Recycling of Asphalt Pavement, Jackson County, Missouri 32
Boston Central Artery/Tunnel Project, Massachusetts 33
Road Base:
State Route 22 Project, Georgia 34
Embankments:
Route 213/301 Overpass Project, Maryland 34
Access Ramp Project, Delaware 35
Flowable Fill:
McGee Creek Aqueduct Pipe Bedding Project, Oklahoma 36
References and Other Sources 37
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Background Basics
The concentrations of naturally
occurring elements found in many
fly ashes are similar to those
found in naturally occurring soil.
Background Basics
What Are Coal Combustion Products?
When coal is burned in a power plant to generate electricity, it leaves
behind residues that can be used as products or raw materials, pri-
marily in the construction industry. These materials are known as coal
combustion products, or CCPs. Power plants generate a variety of CCPs, namely bot-
tom ash, fly ash, boiler slag, and flue gas
desulfurization (FGD) materials. EPA and
industry refer to the larger ash particles
that fall to the bottom of a furnace as
bottom ash, and ash that is carried
upward by the hot combustion gases of the furnace as fly ash. Boiler slag is formed
instead of bottom ash when combustion occurs in a wet boiler, and FGD materials
are produced from scrubbers used to remove sulfur from air emissions.
The concentrations of naturally occurring elements found in many fly ashes are
similar to those found in naturally occurring soil. A mineral analysis of coal combus-
tion products from coal-fired power plants indicates that they are composed of 95
percent iron oxides, aluminum, and silica. They also contain oxidized forms of other
naturally occurring elements found in coal, such as arsenic, barium, cadmium,
chromium, copper, lead, mercury, selenium, and zinc. The exact chemical composi-
tion of coal combustion products varies depending on the type of coal burned, the
extent to which the coal is prepared before it is burned, and the operating condi-
tions for combustion.
Figure 1: Typical Steam Generating System
Note: SCR-Selective Catalytic
Reduction DeNOx System FGD-Flue
Gas Desulfurization System
FGD Byproduct
Gypsum
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Using Coal Ash in Highway Construction
A Guide to Benefits and Impacts
How Are Coal Combustion Products Used?
According to the American Coal Ash Association's annual coal combustion product
survey, almost 122 million tons of coal combustion residues were generated in 2003,
and more than 46 million tons were used as products in such beneficial applications
as concrete, roofing tiles and shingles, bricks and blocks for building construction,
wallboard, and specialty uses such as filler in carpet and bowling balls. Figure 2
shows the top uses of coal combustion products, and Figure 3 shows the top uses
of coal fly ash specifically for the reporting year 2003. These figures show that the
number one use of coal combustion products collectively, and coal fly ash specifical-
ly, is in cement, concrete products, and grout. Figure 4 presents the total coal com-
bustion product generation and use in 2003 by type of material. This figure shows
Figure 2: Top Uses of Coal Combustion Products, 2003
Snowand Ice Control
788,184 Tons
Blasting Grit/
Roofing Granules
1,497,744 Tons
Road Base/Sub-base/
Pavement
l,661,388Tons
Mining Applications
2,330,032 Tons
Cement/Raw
FeedforClinker
3,956,973 Tons
Waste Stabilization/
Solidification
3,999,623 Tons
Soil Modification/Stabilization 773,076Tons
Aggregate 687,839 Tons
Other 2,042,037 Tons
Wallboard
7,780,906 Tons
Concrete/Concrete
Products/Grout
12,679,134 Tons
Structural Fill/
Embankments
8,187,469 Tons
* EPA and the National Academy of Sciences are evaluating the use of coal combus-
tion products as minefill and will address this issue separately.
Source: American Coal Ash Association. 2004.
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Background Basics
that for most coal combustion materials, the United States is beneficially using only
about a third of the material generated, with the exception of boiler slag, which
shows a 95 percent usage rate.
Coal combustion products have also been used as minefill material. EPA and the
National Academy of Sciences are evaluating the use of these materials as minefill.
Figure 3: Top Uses of Coal Fly Ash, 2003
Road Base/Sub-base/Pavement
493,487 Tons
Soil Modification/Stabilization
515,552 Tons
Mining Applications
683,925 Tons
Cement/Raw
FeedforClinker
3,024,930 Tons
L Aggregate 137,171 Tons
FlowableFilll36,618Tons
Mineral Filler in Asphalt 52,608 Tons
Other410,218Tons
Concrete/Concrete
Products/Grout
12,265,169 Tons
Waste Stabilization/
Solidification
3,919,898 Tons
Structural Fill/
Embankments
5,496,948 Tons
* EPA and the National Academy of Sciences are evaluating the use of coal combus-
tion products as minefill and will address this issue separately.
Source: American Coal Ash Association. 2004.
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Using Coal Ash in Highway Construction
A Guide to Benefits and Impacts
Figure 4: Coal Combustion Product Generation and Use (Short Tons), 2003
75,000,000
Percent Used
Fly Ash 38.7%
60,000,000
« Bottom Fly Ash 45.6%
o
Boiler Slag 95.6%
45,000,000 • —FGD Material 29.1%
Other 33.1%
30,000,000
15,000,000
0
Total Production Total Use
Source: American Coal Ash Association. 2004.
How Are Coal Combustion Products
Used in Highway Applications?
The two types of coal combustion products used most often in highway construc-
tion are fly ash and bottom ash. Fly ash can be used as a replacement for Portland
cement in concrete and grout, as a fill material in embankments, as aggregate for
highway subgrades and road base, and in flowable fill. Bottom ash can be used as
aggregate in concrete and in cold mixed asphalt, and as a structural fill for
embankments and cement stabilized bases for highway construction. Figure 5
presents details on coal combustion product use for the 2003 year, with highway
applications shaded.
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Background Basics
Figure 5: Details of Coal Combustion Product Use (Short Tons), 2003
Highway Applications are shaded.
^^B^^^^B
Concrete/concrete
products/grout
Structural fills/embankments
Cement/raw feed for cement
clinker
Road base/sub-base/pavement
Snow and ice control
Aggregate
Flow/able Fill
Mineral filler in asphalt
Wall board
Waste stabilization/solidification
Mining applications**
Blasting grit/roofing granules
Soil modification/stabilization
Miscellaneous/other
Total
Fly Ash Bottom Ash Boiler Slag
12,265,169
5,496,948
3,024,930
493,487
1,928
137,171
136,618
52,608
0
3,919,898
683,925
0
515,552
408,290
27,136,524
298,181
2,443,206
493,765
1,138,101
683,556
512,769
20,327
0
0
30,508
1,184,927
42,604
67,998
1,331,331
8,247,273
15,907
11,074
15,766
29,800
102,700
31,600
0
31,402
0
0
59,800
1,455,140
0
2,815
1,756,004
Hji^^^H^H
99,877
236,241
422,512
0
0
6,299
9,184
0
7,780,906
0
390,331
0
818
34,813
8,980,981
Source: American Coal Ash Association. 2004.
* Flue gas desulfurization materials include FGD gypsum, FGD material wet scrubbers, FGD materi-
al dry scrubbers and FGD other.
** EPA and the National Academy of Sciences are evaluating the use of coal combustion products
as minefill and will address this issue separately.
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The American Society for Testing and Materials (ASTM) and the American
Association of State Highway and Transportation Officials (AASHTO) have issued
numerous standards that describe the proper use of bottom and fly ash in engi-
neering activities.
The standard for using fly ash in Portland cement concrete—the most common
type of coal combustion product used in highway construction and the most com-
mon usage—is ASTM C 618, or the very similar AASHTO M 295. Two classes of
fly ash are defined in ASTM C618: Class F and Class C. These classifications are
related to the amount of free lime or calcium oxide in the ash and the grade of
coal. Both Class F and Class C fly ash have pozzolanic properties—in other words,
they react with water and free lime (calcium oxide) to produce a cement-like com-
pound. Class F fly ash typically contains from 2 to 6 percent calcium oxide and
requires additional lime to obtain self-hardening properties. Class C fly ash typically
contains between 15 and 35 percent calcium oxide and does not require additional
lime for self-hardening properties.
8
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The Standard Guide for Design and Construction of Coal Ash Structural Fills, ASTM
E2277-03, addresses the second largest use of coal fly ash. This document
includes guidelines on using coal ash for structural fill applications (road embank-
ments and other uses), site characterization considerations such as geologic and
hydrologic investigations, laboratory test procedures, design considerations and
methods, and construction considerations. This guide replaces ASTM E 1861-97.
For more information concerning the ASTM and AASHTO standards that apply to
coal ash use in highway construction see the Federal Highway Administration's
June 2003 document, Fly Ash Facts for Highway Engineers.
States with CCP Laws, Regulations,
Policies, or Guidance
Many states have laws, regulations, policies, or guidance authorizing or allowing at
least limited use of coal combustion products in highway construction. For
instance, Wisconsin's Department of Natural Resources has developed a largely
self-implementing regulation (NR 538
Wis. Adm. Code), which includes a
five-category system to allow for bene-
ficial use of industrial byproduct materi-
al, including coal ash.1 (See sidebar on
page 10.) The Texas Natural Resource
Conservation Commission issued guid-
ance in 1995 that defined coal combus-
tion products as "co-products" instead
of waste when used in certain applica-
tions in accordance with industry stan-
dards. Many other state regulations
adopt by reference the federal regula-
tion, which exempts coal combustion
products from classification as haz-
ardous waste. For additional informa-
tion on applicable regulations, contact
your local and state authorities.
Alabama
Alaska
Arkansas
California
Connecticut
Colorado
Delaware
Florida
Georgia
Illinois
Iowa
Kentucky
Maine
Maryland
Massachusetts
Michigan
Missouri
Nebraska
New Hampshire
New Jersey
New Mexico
New York
North Carolina
North Dakota
Ohio
Oklahoma
Pennsylvania
Tennessee
Texas
Utah
Vermont
Virginia
West Virginia
Wisconsin
' See .
9
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Wisconsin's Beneficial Use of Industrial
Byproducts Waste Management Program
Wisconsin's Beneficial Use of Industrial Byproducts
Program is a state-authorized voluntary environmental
program that encourages the beneficial use of coal ash,
boiler slag, paper mill sludge, foundry sand, and foundry slag as
alternatives to placing these materials in the state's solid waste
landfills. For the reporting year 2000, the Wisconsin Department
of Natural Resources (WDNR) showed that participating genera-
tors generated more than 1.4 million tons of coal ash and boiler
slag and beneficially used more than 1.1 million tons (81 per-
cent). WDNR also estimated that, statewide (including facilities
not participating in the program), nearly 72 percent of coal ash
and boiler slag generated in the state is beneficially used. In
contrast, the American Coal Ash Association reported that only
29 percent of the coal ash generated nationally in 2000 was ben-
eficially used.
Wisconsin's beneficial use program began in 1985 when the
state legislature gave WDNR authority to issue landfill exemp-
tions for low-hazard wastes. In 1995, this authority was expand-
ed to allow WDNR to develop a program and rule for certain
industrial byproducts. The result was enactment of State Law NR
538, "Beneficial Use of Industrial Byproducts." The law includes
five different categories of industrial byproducts, determined by
the chemical characteristics of the materials, defines acceptable
end uses for each category, and provides 12 pre-approved bene-
ficial uses for the materials.
For small private projects (<5,000 cu. yds. of material), genera-
tors may use their byproducts in a pre-approved beneficial use
without contacting WDNR. For large private or public projects,
generators must notify WDNR of the nature of the project and
provide information about the material characteristics. WDNR
reserves the right to review any of these projects, but no permit
process beyond notification is required.
1O
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To ensure success, WDNR used a technical advisory committee to
help develop the program, including WDNR representatives from
all of the district offices, representatives from the generator
community, the Department of Transportation, Sierra Club and
other environmental groups, and a number of general contrac-
tors that perform aggregate construction work. Because most of
the affected entities were part of the development process, the
program was not challenged in public hearings or in court. In
addition, the rule was coordinated with Department of
Transportation requirements, and liability issues were addressed.
Another key to the success of the program is that it is largely
self-implementing. Generators can conduct their own material
testing and can proceed without state approval for uses covered
by the law. The self-implementing aspect of the program was
important to the generator groups on the committee; these
groups were willing to balance the advantages of self-implemen-
tation with the disadvantages of recordkeeping and reporting
requirements included in the law.
NR 538 became effective in June 1998. Its success can be meas-
ured by the high percentage of coal ash and slag use throughout
the state, compared to the national average. In addition, no
environmental issues or problems have been associated with the
implementation of the program. ,
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Using Coal Ash in Highway Construction
A Guide to Benefits and Impacts
Performance and Cost Benefits
Why Is Coal Fly Ash Useful?
The physical properties of coal fly ash—
specifically, the unique spherical shape
and particle size distribution—make it a
good mineral filler in hot-mix asphalt
applications, improve the fluidity of flow-
able fill and grout, and reduce the perme-
ability of concrete.
I sing coal combustion products
in highway construction yields
a number of performance and
cost benefits, which can lead to environ-
mental benefits as well. Performance
benefits can be realized from the use of
coal ash in concrete mixtures, embank-
ments, in flowable fill, as a stabilized
base course, in asphalt pavements, and
in grouts for pavement subsealing.
In Concrete
Coal ash can be used to create superior products because of its inherent cementi-
tious properties. Mixing fly ash with Portland cement mixtures can produce
stronger and longer lasting roads and bridges than concrete made with only
Portland cement as the binder (glue). The following are notable performance bene-
fits from using coal fly ash in concrete:
Figure 6: Strength Gain of Fly Ash Concrete
12
Improved workability of concrete due to the nature and shape of the ash particles
Reduced water demand
Reduced bleeding at the edges of pavement
Increased ultimate strength of the concrete
Reduced permeability to moisture, improving long-term durability of the concrete
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»> Decreased heat of hydration during concrete curing
i» Greater concrete resistance to various forms of deterioration
»> Reduced concrete shrinkage
I7/:
Fly ash can be used as a borrow material for highway embankments. When fly ash
is compacted, a structural fill can be constructed that can support highways. The
performance benefits associated with this use include:
*> Elimination of the need to purchase, permit, and operate a borrow pit
»> Placement over low-bearing-strength soils
*> Ease of handling and compaction, which reduces
construction time and equipment costs
Flowable fill made with coal fly ash can be used in place of conventional backfill
materials and alleviates problems and restrictions generally associated with the
placement of those materials. Benefits include:
*> Placement in any weather, including under freezing conditions
»> 100 percent density with no compactive effort
*!* Ability to fill around and under structures inaccessible
to conventional fill placement techniques
<» Increased soil-bearing capacity
»*» Prevention of post-fill settlement problems
<» Increased speed and ease of backfilling operations
»*» Decreased variability in the density of backfilled
materials
i» Improved on-the-job safety and reduced labor and
excavation costs
»> Easy excavation later when properly designed
13
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^truction
m
Fly ash and lime can be combined with aggregate to produce a quality stabilized base
course. These road bases are referred to as pozzolanic-stabilized mixtures and are
advantageous over other base materials because they provide:
»> A strong durable mixture
»t» Reduced costs
»> Autogenous healing
»t» Increased energy efficiency
Fly ash also can be used as a mineral filler in
asphalt pavements. Mineral fillers increase the
stiffness of the asphalt mortar mix, improve
the rutting resistance of pavements, and
improve the durability of the mix. Other bene-
fits include:
# Reduced potential for asphalt stripping
•> Reduced cost compared to other
mineral fillers
Grouts for pavement subsealing are proportioned mixtures of fly ash, water, and other
materials used to fill voids under a pavement system without raising the slabs by
drilling and injecting grout under specified areas of the pavement. In these applica-
tions, the performance benefits include:
»> Quick correction of concrete pavements
«t» Minimal traffic disturbance
«> Development of high ultimate strength
14
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Cost
In addition to these performance benefits, many coal combustion products are less
costly to use than the materials they
replace. At the same time, the durabili-
ty benefits from using coal ash con-
crete can reduce the cost of maintain-
ing the nation's road systems. This
enhanced performance also provides additional environmental benefits by reducing
the need for new concrete to replace aging roads and bridges, thereby significantly
reducing future energy consumption and greenhouse gas emissions.
The California Department of
Transportation requires the use of
concrete containing fly ash in all of
its roadways to improve durability.
Over the past 15 years, the Federal Highway Administration (FHWA) and its partners in
state highway agencies, universities, and the pavement industry have achieved tremen-
dous advances in pavement technology. The FHWA's Office of Pavement Technology
has been focusing on combining recent technical advances to develop long-life pave-
ment systems that can last up to 50 years for roads—twice the lifetime of conventional
pavements. These long-life pavements will reduce the costs of maintaining the nation's
highway systems and also result in decreased material needs. Coal fly ash and other
recycled materials are common components of these high-performance Portland
cement pavements.
15
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Using Coal Ash in Highway Construction
A Guide to Benefits and Impacts
Environmental Benefits
The use of coal combustion products in highway construction provides
significant short- and long-term environmental benefits. Specifically,
using coal combustion products in lieu of other materials, such as
Portland cement, reduces energy use and greenhouse gas emissions and con-
serves natural resources. In addition, it prevents the disposal of a valuable
resource, reducing the need for landfills and surface impoundments. Finally, the
inherent performance benefits of concrete made from coal ash actually leads to
additional environmental benefits. Highways and bridges made with coal ash con-
crete are more durable than those made without it and, therefore, do not need to
be repaired and replaced as often.
Greenhouse Gas Emissions and Energy
Reductions
Producing cement involves many steps, including grinding and blending raw ingre-
dients (such as limestone, shells or chalk, and shale, clay, sand, or iron ore), heat-
ing those ingredients to very high temperatures in a kiln, cooling and mixing those
ingredients with gypsum, then grinding down the mixture to form cement powder.
Figure 7: Generic Cement Production Process
Water—»• Slurry—>• Grinding
Blending
Emissions
2500-3000°F
Cement
Clinker
Coo"nS
Gypsum
• Mix
Grinding
Portland
Cement
Dry Raw Materials
This energy-intensive process typically emits nearly one ton of greenhouse gases
for each ton of cement created and requires the equivalent of a barrel of oil per
16
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K; ^ ?? 8 3'C K ?f:ii *!i 11 ta i
ton. Using fly ash—which would other-
wise be disposed of—in concrete has
the potential to significantly reduce the
quantity of greenhouse gases emitted
and the amount of fuel used. Typically,
between 15 to 30 percent of Portland
cement in concrete can be replaced
with fly ash.
The Federal Highway Administration
reports that roads and bridges made
with high-performance coal ash con-
crete can last years longer than those
made with Portland cement as the only
binding agent. Thus, using coal ash
concrete reduces the need to produce
new concrete, which consequently
What Are Greenhouse Gas
Emissions?
The Earth's atmosphere acts like an
immense greenhouse, trapping heat from
the sun to warm the planet to create
habitable conditions. This "greenhouse
effect" occurs when solar radiation is
absorbed by greenhouse gases in the
atmosphere. Most greenhouse gases,
such as carbon dioxide, nitrous oxide, and
other trace gases like methane, occur
naturally. Human activities may intensify
this natural phenomenon. Burning fossil
fuels to power cars, homes, and industry
releases carbon dioxide and increases con-
centrations of other greenhouse gases in
the atmosphere.
means further reductions in future
greenhouse gas emissions, energy use, and natural resources. For some locations,
coal combustion products are a locally available construction material that requires
less transportation costs and fuel usage
for trucking the material to the con-
struction site.
In 2002, the American Coal Ash
Association estimated that 12.6 million
tons of fly ash were used as a substi-
tute for Portland cement in the United
States. The industry set a goal to
increase its use to 20 million tons by
2010. EPA estimates that this would
reduce the future generation of green-
house gasses by more than 6.5 million
tons a year.2
Conserves enough landfill space to
hold about 1,200 pounds of waste, or
the amount of solid waste produced
by one American over 270 days.
Reduces the equivalent of two
months of an automobile's carbon
dioxide emissions.
Saves enough energy to provide elec-
tricity to an average American home
for 19 days.
2 Estimated using EPA's Waste Reduction Model, Solid Waste Management and
Greenhouse Gases, Second Edition, EPA 530-R-02-006, Office of Solid Waste, June 2002.
17
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• ,;• ' K,.r
Because coal ash can be used as a replacement for many materials in highway
construction, its use reduces the need to quarry or excavate virgin materials and
therefore helps to reduce the environ-
mental impacts associated with these
activities. Reducing these operations
helps prevent habitat destruction, pro-
tect scenic waterways, reduce water
runoff and air emissions, and reduce
energy use. In addition, each ton of
coal ash used beneficially reduces the
need for one ton of virgin resources.
Coal combustion products can be substi-
tuted for many virgin resources that
would otherwise have to be quarried or
excavated, such as:
Limestone and clay to make concrete
Gypsum to make wallboard
Sand and gravel to make road beds
Soil for road embankments
18
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Environmental Benefits
Solid Waste Reduction
Although many U.S. industries are using coal combustion products, the United
States continues to dispose of more than 80 million tons of this material in landfills
and surface impoundments annually.
Using coal ash as a substitute for
cement in highway construction and
other applications could reduce this
waste. Typically, a ton of coal ash com-
pacted to 70 pounds per cubic foot
takes up approximately 28 cubic feet of
landfill space. Every million tons of coal
combustion products beneficially used
instead of disposed of reduces the need for 656 acre-feet of landfill space. Figure 8
shows U.S. trends in the generation and use of coal combustion products over the
past several years. These data indicate that while the beneficial use of coal com-
bustion products is increasing slowly, so has the generation of these materials.
Figure 8. Production and Use of Coal Combustion Products, 1996-2003
140,000
120,000
<2 100,000
I Production
re
a>
=
o
80,000
1996 1997 1998 1999 2000 2001 2002 2003
Usage
Percentage 24.9% 27.8% 29.0% 30.8% 29.1% 31.5% 35.4% 38.1%
19
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' -: !/, ;•;'hen coal ash is used in concrete for building roads and bridges, its
"«;• " . ' ;;<•' constituents—such as heavy metals—are bound (encapsulated) in
' -'' x"1 < 5- >
'• " '• the matrix of the concrete and are very stable. Leaching of these
constituents for all practical purposes does not occur.3
Occupational issues associated with coal
ash use in concrete include the handling of
dry coal ash prior to or during its inclusion in
a concrete mix or exposures during demoli-
tion of concrete structures. In these cases,
work inhalation and skin contact precautions
should be observed, as described on page
27 in the section called Occupational Issues:
Inhalation and Skin Contact.
U.S. Environmental Protection Agency. March 1999.
2O
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;•"".''" tudies and research conducted or supported by Electric Power and
''•"'.„.„'\ Research Institute (EPRI), government agencies, and universities4 indicates
• '"•••'":,/ •- 'that the beneficial uses of coal combustion products in highway construc-
tion have not been shown to present significant risks to human health or the envi-
ronment. But, as with many other common substances, precautions and sound
management practices should be applied when using coal ash in unencapsulated
uses. Water and air are the two media most likely to be affected by coal ash or
coal ash constituents.
Ingestion, inhalation, and skin contact are the ways that humans and other living
things could be exposed to coal ash. Other issues that may need to be addressed
are leaching of elements such as mercury and metals into ground water, contami-
nation of vegetation and the impact of other elements on the food chain, and air-
borne dust. In most cases, however, the way that coal ash is used, the engineering
requirements for that use, and the handling and management methods applied
minimizes exposure to the ash.
EPRI. May 1990, December 1990, February 1991, November 1993, June 1995, March
1998, and 1998; Hassett, David J., et al 2001; Pflughoseft-Hassett, D.F., et al. 1993; U.S.
Environmental Protection Agency. August 9, 1993.
21
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Using Coal Ash in Highway Construction
A Guide to Benefits and Impacts
Mercury
Although mercury in coal ash can potentially be released into the environment through
leachate in water or as emissions to the ambient air, studies conducted by the University
of North Dakota Energy and Environmental Research Center and the University of
Nevada, which tested bituminous, subbituminous, and lignite coals, have shown that
mercury releases from coal ash to the environment are negligible.s Results from water
leachate tests showed that mercury was very stable in coal fly ash and leached less than
1 percent of the initial mercury concentrations. Studies on the release of mercury from
coal ash to the ambient air show only minute losses to the environment.
EPA has proposed a new regulation, called the Clean Air Mercury Rule (CAMR), that
would require reductions in mercury emissions from coal-fired power plants. This pro-
posed regulation might affect the amount of mercury found in coal ash, but whether
this regulation will increase mercury concentrations in coal ash or not is not clear at this
time because this is the first time ever that EPA has regulated mercury emissions from
power plants. EPA's conclusions in this document are based on the regulations currently
affecting power plants. EPA will reassess its position, if it appears that there is a signifi-
cant increase in the level of mercury in coal ash, when the CAMR is promulgated.
Water Issues: Groundwater/Surface
Water Health and Human Ingestion
Several studies6 over the past 10
years have shown that the use of
coal ash in highway construction
projects has resulted in little to no
impact on groundwater and
surface water quality, but some
precautions are necessary.
Road Beds and Embankments: Coal ash used as a fill for road beds and embank-
ments, unlike that used in concrete, requires greater care to ensure its safe use.
The use of engineering standards and guidelines pertaining to coal ash will help
ensure that the use of these materials will not negatively impact the environment.
Hassett, David J., et al. 1999.
EPRI. May 1990, December 1990, February 1991, November 1993, June 1995, March
1998, 1998; Hassett, David J., et a/200/; Pflughoseft-Hassett, D.F., et al. 1993; U.S.
Environmental Protection Agency. August 9, 1993.
22
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C.: TI v:' if ®- IT mi ;'?• ii t a 1
Environmental issues in these cases are largely determined by local circumstances,
such as groundwater depth and proximity to drinking water wells. The studies
mentioned above show that while
leaching of coal ash constituents is Precautionary Measures
possible from unencapsulated uses, Associated until Jtaencapsulted
it does not occur in practice at high
concentrations and has not been • Assess hydrogeologic characteristics of
shown to migrate far from the site the sitei
when appropriate engineering prac- • Mitigate leaching through engineering and
tices are followed design practices and follow proper construc-
tion techniques.
Despite the relative safety of using . Unencapsu|ated coa, asn can be used wnen
coal combustion products in unen- an assessment indicates it will not affect
Capsulated highway construction gr0und or surface waters. An assessment is
projects, Some preventive and Cau- particularly important in areas with sandy
tionary measures Should be taken soils, shallow ground water or in close prox-
(See Town Of Pines Case Study On imity to drinking water aquifers
page 24):
1) Conduct an evaluation of local groundwater conditions prior to using coal com-
bustion products as a fill material. Numerous groundwater models are available,
such as EPA's Industrial Waste Evaluation Model (IWEM), a groundwater fate
and transport risk assessment model in EPA's Guide for Industrial Waste
Management, and HYDRUS 2D.7
2) Consult with your state regulatory agency for information on the applicable test
procedures, water quality standards, and other requirements.
3) Once you determine that a site is appropriate for coal ash use, mitigate the
leaching of coal ash constituents by assuring adequate compaction and grading
to promote surface water runoff, and daily proof-rolling of the finished subgrade
to impede infiltration. When construction is finished, a properly seeded soil
cover will also help. Two helpful sources of construction information are state
highway departments and the Federal Highway Administration's June 2003
document, Fly Ash Facts for Highway Engineers.
IWEM model available at www.epa.gov/epaoswer/non-hw/industd/iwem.htm; HYDRUS
2D model available at www.hydrus2d.com.
23
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••"" , " '," -' ". '
.:, '."I! 10
The Town of Pines, Indiana, provides a cautionary lesson on
waste disposal and the use of coal ash as general fill in
vulnerable areas. It is primarily a story about the groundwater
contamination that arose because of poor early disposal
practices. It demonstrates several lessons on the need for good
coal combustion product construction practices and site charac-
terization when the material is not encapsulated—specifically,
assessing potential groundwater impacts.
Pines is located about two miles south of Lake Michigan,
adjacent to Dunes National Lakeshore. The town's drinking
water comes from shallow residential wells typically drawing
ground water from 25 to 50 feet below ground level. The native
soils are sandy, unconsolidated, and highly acidic, with a high
organic content overlying a less permeable clay-rich layer.
Since 1983, more than a million tons of coal ash and other mate-
rials have been disposed of at a local landfill or used around
town as a fill material. The landfill was originally located in a
swampy area only 300 feet from the nearest drinking water well
and has recently closed. The direction of groundwater flow is to
the east/northeast with a small northerly component that affect-
ed the main portion of the Town of Pines. Coal ash was also
used throughout the town to fill in low lying areas—up to eight
feet in some places—and to build roads that were often left
uncovered and exposed to the elements. The shallowness of
Pines's drinking water aquifer makes it susceptible to contami-
nation of all types.
In May 2000, the Indiana Department of Environmental
Management (IDEM) began an investigation of the town's water
after a resident complained that it tasted foul. IDEM found sev-
eral volatile organic compounds (VOCs) in the water, including
24
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Environmental and Health Cautions
benzene. In January 2001, IDEM also found elevated levels of
methyl-tertiary-butyl-ether (MTBE). Both benzene and MTBE are
associated with gasoline and are not associated with the landfill
or coal ash. Later investigations discovered high levels of boron,
manganese, and molybdenum in the drinking water, which are
associated with coal ash. In short, the shallowness of the drink-
ing water wells, the porosity of the overlying sands, the location
of the landfill, and the improper use of coal ash all contributed
to the contamination of the town's drinking water.
Several important lessons can be learned from Pines:
Take care when using or disposing of any material in a hydroge-
ologically vulnerable area.
Before using coal ash as a fill material, conduct an assessment
of its potential groundwater impacts.
Follow proper engineering requirements when using unencap-
sulated coal ash.
The environmental problems in the Town of Pines should not dis-
courage the beneficial use of fly ash at other locations for fill,
road base, or embankments. But, these problems do highlight
the need for properly assessing and addressing potential
groundwater impacts. '*
25
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*,.,*
lit!
EPA, in 2000, determined that the use of coal ash as a highway fill material or even
as a substitute for lime in agricultural applications did not pose a risk of concern. In
addition, several EPRI (Electric Power Research lnstitute)studies8 have shown that
the use of coal ash in unencapsulated highway construction projects poses limited
risk to roadside vegetation. Studies of road construction projects in Arizona,
Arkansas, Georgia, Illinois, and Kansas indicate that while metal constituents from
coal fly ash and bottom ash might enter plant tissues
through absorption, the concentrations of these elements
are found to be well below the toxic limits.
In addition, studies examining the effects of ingestion of
fly ash constituents by animals have not suggested any
associated health problems.9 Some tests showed slightly
elevated levels of some elements in blood and various
organs, while other tests found no constituent increases.
These results indicate little potential for coal ash ele-
ments from highway construction projects to accumulate in soil and increase in
concentration by food chain biomagnification (the process by which animals feed-
ing on affected plants can, in turn, accumulate the same constituents and build up
these constituents in their tissues).
In
n in -
IIV
I
t III i- •
III "III
Air inhalation of coal ash dust is primarily a worker safety issue. Nevertheless, proper
precautions should be taken to protect the public from dusting during delivery and
construction, when coal ash is first laid down. Dust is not an issue when coal ash is
used in concrete or in a slurry form.
Coal ash can become airborne during storage and
processing of ash, from traffic on roads, and
through wind erosion during ash placement. Like
other nuisance dust, however, specific controls
can address these exposure methods to prevent
air pollution and inhalation:
Electric Power Research Institute. June 1995.
Electric Power Research Institute. 1998.
26
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:nviron _
High-calcium, self-hardening ash
should be stored dry in silos, while
low-calcium ash can be stockpiled
onsite if the ash is kept moist and
covered to prevent dusting and
erosion.
Dry fly ash should be transported in
covered or pneumatic tanker trucks.
Wind erosion of coal ash should be
mitigated in highway construction application by moistening the ash during
the construction phase or by using the material in slurry form.
Coal ash used in road construction should be compacted and covered to
minimize dusting.
Inhalation
Workers involved with dry ash handling, concrete grinding, or
demolition activities can come in contact with fugitive dust con-
taining coal ash. Health risks associated with the inhalation of
these fugitive dusts in occupational settings can be limited by
following Occupational Safety and Health Administration (OSHA)
standards and practices. These standards and practices are
applicable whether or not coal ash is used in concrete. Workers
should request Material Safety Data Sheets (MSDS) from coal
combustion product suppliers when they are not sure of the
proper precautions.
In addition, workers can minimize inhalation through a number
of actions:
«J» Cleaning work areas regularly by wet sweeping or vacuuming.
*> Wearing basic personal protection such as safety goggles with side shields to pro-
tect the eyes from dust.
27
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ii
»> Wearing a suitable particulate respirator (i.e., approved for particulates by the
National Institute for Occupational Safety and Health—NIOSH) to prevent particu-
late inhalation.
»> Adding water to the ash to prevent fly ash from blowing during handling.
<» Using standard dust filters on vehicles and silos.
»> Using mechanical ventilation or extraction in areas where dust could escape into
the work environment.
<» Using closed pumping systems for bulk deliveries.
An EPRI study to determine potential health effects of workers in frequent contact
with coal fly ash concluded that routine operating activities did not produce hazardous
exposures.10 In addition, occupational health records for these types of workers do not
show a higher incidence of respiratory problems than those of power plant workers
who do not work as closely with fly ash. In some occupational settings, however,
Coal contains naturally occurring radioactive elements. After combustion, these ele-
ments and their decay products can remain in coal combustion ash. EPA has classified
coal fly ash as a diffuse, naturally occurring radioactive material, which is EPA's most
benign radioactive classification.
Studies have shown that the level of radioactivity in coal combustion products is
about the same as the level found in surface rocks and soil.* A long-term Tennessee
Valley Authority study of a 42-acre site that used more than 1 million cubic yards of
fly ash in structural fill indicated that ambient radon levels measured directly over
the fly ash fill were comparable to the levels
measured in control areas without fly ash.
Studies have also shown that radon releas-
es from concrete blocks manufactured
using coal fly ash are well below EPA's
radon action levels. "
Electric Power Research Institute.
U.S. Environmental Protection Agency.
October 1998.
' Electric Power Research Institute. 1998.
28
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iitiental
Issues
such as maintenance activities or in an accident, some power plant workers can be
exposed to higher concentrations of fly ash particles. In these cases, potential health
problems related to either the presence of particles in the lungs or to specific sub-
stances in the ash (e.g., metals or quartz) can occur from direct inhalation of higher
concentrations of coal fly ash.
Another study11 reviewed the toxicity and health hazards of coal fly ash compared to
coal mine dust, which is known to cause pneumoconiosis and emphysema.
Researchers concluded that exposure to high concentrations of coal fly ash can cause
chronic bronchitis and air flow obstruction—typical of the common effects seen after
inhaling a variety of different types of dusts. However, the study found no evidence
that coal fly ash can induce pneumoconiosis and emphysema. Exposures to high con-
centrations of coal fly ash can be minimized or prevented by following the guidelines
presented earlier in this section and by observing OSHA requirements regarding nui-
sance dust.
Skin Contact
Power plant workers and people involved in producing cement, concrete, or other ash-
based products can have skin contact with coal fly ash. In highway applications, skin
contact is likely limited to construction workers working with dry ash. When construc-
tion is finished, the road bed and a properly seeded soil cover will reduce any chance
of skin contact. While most contact with coal ash can be controlled by proper han-
dling and construction safety practices, if contact does occur, coal ash can cause skin
irritation or contact dermatitis.
Workers can minimize skin contact through a number of spe-
cific actions:
*> Wearing gloves or applying a barrier hand cream.
•I* Wearing loose, comfortable clothing that protects the
skin and washing work clothes regularly.
*> Washing any exposed skin thoroughly with mild soap and
water prior to eating and at the end of work activities.
Others exposed to coal ash should wash exposed skin with
mild soap and water and launder soiled clothing.
Borm, P.J.A., December 1997.
29
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• i)•?•)'-!PA supports and encourages the beneficial use of coal combustion products
|S': Wv jn highway construction applications for several reasons. First, coal combus-
"5M>.\!( a tjon products are a significant component of the U.S. solid waste stream. The
United States produced over 121 million tons of this material in 2003. Second, coal
combustion products can be benefi-
cially used in highway applications
instead of being land disposed. This
beneficial use has many environ-
mental benefits, including reduced
energy consumption, greenhouse
gases, need for additional landfill
space, and raw material consump-
tion. Third, using coal combustion products in highway construction applications does
not result in environmental harm or human health problems if proper management
practices are followed.
EPA conducted two regulatory determinations on the management and use of coal
combustion products, in 1993 and in 2000. As part of these regulatory determina-
tions, EPA evaluated the following eight factors:
*i" The source and volume of coal combustion products generated per year
<- Current disposal practices.
*i" Potential danger, if any, to human health or the environment from the disposal of
coal combustion products.
* Documented cases in which danger to human health or the environment has
been proved.
•5* Alternatives to current disposal methods.
<• The costs of such alternatives.
•5* The impact of those alternatives on the use of natural resources.
3O
-------
'!*-"u ll>-. ,,:: rr-f< •"
*> The current and potential utilization of coal combustion products.
In conducting these two regulatory determinations, EPA did not identify any environ-
mental harm associated with the beneficial use of coal combustion products in high-
way construction applications and concluded in both determinations that these
materials did not warrant regulation as a hazardous waste. The beneficial use of coal
combustion products can include both encapsu-
lated and unencapsulated applications. EPA rec-
ognizes that unencapsulated uses of coal com-
bustion product require proper hydrogeologic
evaluation to ensure adequate groundwater
protection.
The 2000 regulatory determination recommend-
ed a separate review addressing the use of coal
combustion wastes as fill for surface or under-
ground mines, which is currently underway.
EPA also has provided guidelines to the federal government for purchasing cement
and concrete products containing fly ash.12 In 1983, EPA promulgated the first fed-
eral procurement guideline that required agencies using federal funds to implement
a preference program favoring the purchase of cement and concrete containing fly
ash. EPA also endorses the use of pozzolans, such as coal ash, as the preferred
method for stabilizing certain metal-bearing wastes. EPA published a summary of
information pertaining to coal combustion products use in an environmental fact
sheet, Guideline for Purchasing Cement and Concrete Containing Fly Ash (EPA530-
SW-91-086, January 1992).
In addition, Executive Order 12873, Federal Acquisition, Hecycling, and Waste
Prevention, signed on October 20,1993, directs federal agencies to develop affir-
mative procurement programs for environmentally preferable products. It also
requires EPA to issue guidance on principles that agencies should follow in making
determinations for the preference and purchase of these products. In 1995, EPA
issued the Comprehensive Procurement Guideline, designating items that can be
made with recovered materials, including coal fly ash. EPA also further clarified
that flowable fill from the combustion of coal can be used as a recovered material.
12 U.S. Environmental Protection Agency. January 28, 1983.
31
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'•< :.. '.If, III
jhe following case studies provide examples of how coal combustion
"tags)-' ........ ° I- i-
jjjjjjjjjjjj products have been used successfully in a variety of highway construc-
ts tion applications nationwide over the past few decades.
Cold In-Place Recycling of Asphalt Pavement, Jackson County, Missouri
A Jackson County, Missouri innovative partnership rehabilitated 2.36 miles of deteri-
orating rural roads, resulting in an environmentally sound and superior road surface at
significant cost savings to the County.
The "Jackson County Partnership" included the County's Depart-
ment of Public Works, Lafarge-North America, Kansas City Power &
Light and the University of Missouri-Kansas City (UMKC). The part-
nership developed a process in which the full depth of asphalt and
base material were pulverized and mixed with fly ash and water.
These constituents were re-compacted to form a strong, economi-
cal sub-base and then covered with a new asphalt wear surface.
In this project, an independent researcher and students from UMKC assisted in the
development of County specifications and evaluated the finished product. The
removal of the old asphalt and processing on site minimized the environmental
impact of the project including use of nearly 1,700 tons of Class C fly ash donated by
KCP&L and Lafarge-NA. The project to rehabilitate the road with fly ash cost about
one-third less than it would have to remove and replace the entire road. California
Bearing Ratio values, a measurement of strength, averaged 52 after 24 to 48 hours
of curing. This stronger road base permitted a thinner (less expensive) layer of
asphalt to be applied as the final wear surface.
On-site recycling of the old pulverized pavement with locally provided fly ash,
reduced overall energy consumption, equipment and hauling costs
and emission pollution, as well as truck traffic. This project also
eliminated landfill requirements, excavation, and depletion of
newly quarried rock and dredged sand. The partnership demon-
strates not only the value of innovative cooperation among organi-
zations, but also exemplifies the goals of the Coal Combustion
Products Partnership.
32
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Storrow Drive Connector
Studies
Boston Central Artery/Tunnel Project Massachusetts
Approximately 3.8 million yards of concrete con-
taining a 30 percent coal fly ash mix is being
used in the sprawling Boston Central Artery/
Tunnel project—one of the largest and most
technologically challenging highway projects in
the United States. Coal fly ash is being used as
part of the concrete design and specification
because of its resistence to alkali reactivity and
low heat of hydration. At the same time, the fly
ash used in place of cement will prevent approx-
imately 335,000 tons of greenhouse gases from
being released.
The project has two major components:
1. The replacement of a six-lane elevated highway with an eight- to 10-lane under-
ground expressway directly beneath the existing road, culminating in a two-
bridge crossing of the Charles River (the Cable Stayed Bridge and the Storrow
Drive Connector).
2. The extension of I-90 (the Massachusetts Turnpike) from its current terminus
south of downtown Boston through a tunnel beneath South Boston and Boston
Harbor to Logan Airport. The first link in this new connection—the four-lane Ted
Williams Tunnel under the harbor—was finished in December 1995.
The concrete mixes used on the project
were designed to meet rigid project spec-
ifications. Using these mix-designs allows
for the elimination of construction joints,
which in turn helps the construction
schedule, saves on labor-intensive costs,
and allows for very large placements—up
to 1,400 cubic yards in a single pour.
Ted Williams Tunnel
33
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State Route 22 Project Georgia
Post-construction environmental and performance testing determined that using
coal fly ash as a base course along part of Georgia State Route 22 has resulted in
negligible environmental impacts and has shown sustainable high performance.
This test project was a joint venture of the Georgia Department of Transportation
(GDOT), Southern Company Services, and the Georgia Power Company, with fund-
ing from the Electric Power Research Institute,
which promotes ash utilization in large volume
applications. The testing area was constructed
along a two-lane bypass section of Route 22,
near Crawfordville, Georgia, approximately 90
miles east of Atlanta. Both coarse and fine ash
were used to compare with the typical con-
struction materials replaced by fly ash. Site preparations began in fall 1984, and
construction of the ash layers was completed in July 1985.
Class F fly ash supplied from Southern Electric System was used in three applica-
tions: 1) a lime-fly ash (LEA) stabilized sub-base, 2) a cement-stabilized fly ash
(CFA) base course, and 3) a cement stabilized pond ash (CPA) base course, each
of which were each placed in 1,000-foot-long test sections.
Post-construction monitoring evaluated strength, road surface conditions, pavement
deflections, groundwater quality from four groundwater monitoring wells and multi-
ple leachate collection pipes, and environmental effects resulting from the use of fly
ash. Results indicate that the performance of all test sections surpassed that of the
control section and exceeded GDOT requirements. Environmental monitoring results
indicate that the environmental impact of the test sections has been negligible.
Route 213/301 Overpass Project Maryland
Sixty thousand tons of Class F fly ash from the Baltimore Gas and Electric and the
Delmarva Power plant were provided to the Maryland State Highway
Administration in 1993 and 1994 to create the highway embankments for the
Route 213 overpass over Route 301 on Maryland's eastern shore. A study of the
34
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Case Studies
overpass was initiated in March 1999 by the Maryland Department of Natural
Resources Power Plant Research Program to assess groundwater quality impacts
and promote the beneficial use of coal combustion products generated in
Maryland. Groundwater data collected during May, June, and July of 1999 indicate
that the leachate from the fly ash has had no discernable impact on the groundwa-
ter quality at the site.
The site embankments were constructed using a base layer of silty sand, with the
placement of sandy clay berms to contain the sides of the fly ash, and placement
and compaction of fly ash in 8-inch lifts. The fly ash was moistened to about 20
percent prior to compaction and covered with 2 feet of sandy clay. The portions
beneath the road were covered with a stone base and asphalt pavement.
The groundwater study for this site involved using lysimeters, monitoring wells,
and soil moisture probes in and through the fly ash fill on the shoulder of Route
213. Samples were collected to provide infor-
mation on the embankment material's physical
and chemical properties and were used to
assess the factors impacting the attenuation of
constituents. Pore and groundwater samples
collected at the site were analyzed for dissolved
trace elements, major cations and anions, and
alkalinity. Water quality results indicated elevat-
ed concentrations of several trace elements and
major ions in the fly ash pore water, indicating
that leachate is forming within the fly ash fill. The data also indicate, however, that
these constituents are being attenuated in underlying soils and ground water
beneath the embankments. The water quality data indicate that the use of fly ash
for highway embankments can adequately protect groundwater quality.
Access Ramp Project Delaware
Nearly 10,000 tons of stockpiled fly ash from Delmarva Power and Light Company's
Edge Moor Station were used to construct the main access ramps for a new inter-
change to Interstate 495 near Wilmington, Delaware. This project was conducted
during June 1987 and, during the two-year monitoring period that followed, showed
no significant environmental effects, but did show high performance characteristics.
35
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lO
Environmental analysts studied the short-term effects of the project on local
groundwater quality by evaluating four monitoring wells and four permeate collec-
tion drains, and by collecting and analyzing runoff and leachate in the vicinity of
the ash fill area. In addition, monitoring of post-construction performance showed
that in-place soil had the same characteristics as a well-compacted granular soil.
Less than one-eighth of an inch of settlement was measured at each of the set-
tlement plate locations, indicating that the fly ash fill performed as well as con-
ventional materials.
McGee Creek Aqueduct Pipe Bedding Project Oklahoma
Not only did the use of fly ash allow the entire McGee Creek Aqueduct Pipe
Bedding project to proceed on a faster schedule, but it also resulted in a 40 per-
cent cost savings. The 1984 construction of this 16.6-mile aqueduct near Ferris,
Oklahoma, by the U.S. Bureau of Land Reclamation reused 8,000 tons of fly ash.
This ash was used to make a flowable fly ash grout mix, which was used instead
of compacted crushed stone for the pipe bedding.
The pipeline contractor selected flowable fly ash grout for bedding to increase the
speed of bedding placement, reduce labor and equipment costs, and provide a
more uniform bedding. The flowable grout mix contained 11 percent Class C fly
ash by weight, as well as sand, water, and R-7 chemical retarder. The fly ash, sup-
plied by Oklahoma Gas and Electric Company, had self-cementing and flash-setting
properties, and the chemical retarding agent was used to control the flash-setting
characteristics.
The performance of both the fly ash grout and a Portland cement grout, which was
also used on the project, was compared by visual inspection. The fly ash grout
exhibited the least amount of segregation, bleeding, and shrinkage. The fly ash
grout also set up in the trench faster than the cement grout, allowing the second
lift to be placed sooner and the entire operation to proceed more quickly than if
conventional cement grout had been used. The material cost analysis indicated
that the use of Class C fly ash and retarder in place of Portland cement resulted in
the significant cost savings. In addition, the use of the fly ash grout for this project
resulted in a reduced need for crushed stone.
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American Coal Ash Association. 1998. Innovative Applications of Coal Combustion
Products (CCPs).
American Coal Ash Association. 2002. Annual Survey of Coal Combustion Products
Production and Use.
American Coal Ash Association. 2003. Annual Survey of Coal Combustion Products
Production and Use.
American Coal Ash Association. 2004. Annual Survey of Coal Combustion Products
Production and Use.
ASTM C 618-03. (Also, AASHTO M 295). Standard Specification for Coal Fly Ash
and Raw or Calcined Natural Pozzolan for Use as a Mineral Admixture in Concrete.
ASTM E 2277-03. Standard Guide for Design and Construction of Coal Ash in
Structural Fills.
Borm, PJ.A. December 1997. Toxicity and Occupational Health Hazards of Coal Fly
Ash. A Review of Data and Comparison to Coal Mine Dust. Annals of Occupational
Hygiene, Vol. 41, No. 6, 659-676.
Department of Energy. July 1994. Barriers to the Increased Utilization of Coal
Combustion/Desulfurization Byproducts by Governmental and Commercial Sectors.
Office of Fossil Energy.
Department of Energy/Energy Information Administration. 1998. 1997 Annual
Energy Review, Appendix A. Washington DC.
Electric Power Research Institute (EPRI). May 1990. Environmental Performance
Assessment of Coal Ash Use Sites: Little Canada Structural Ash Fill, EPRI Report
No. EN-6532. Palo Alto, CA.
Electric Power Research Institute (EPRI). December 1990. Environmental
Performance Assessment of Coal Ash Use Sites: Waukegan Ash Embankment,
EPRI Report No. EN-6533. Palo Alto, CA.
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; >•'• MI
Electric Power Research Institute (EPRI). February 1991. Use of Coal Ash in
Highway Construction: Michigan Demonstration Project- Interim Report; EPRI GS-
7175, Project 2422-7.
Electric Power Research Institute (EPRI). August 1993. Fly Ash Exposure in Coal
Fired Power Plants, EPRI TR-102576.
Electric Power Research Institute (EPRI). November 1993. Environmental
Performance Assessments of Coal Ash Use Sites. EPRI Report No. RP-2796. Palo
Alto, CA.
Electric Power Research Institute (EPRI). June 1995. Environmental Performance
Assessment of Coal Combustion Byproduct Use Sites; Road Construction
Applications, EPRI TR-105127.
Electric Power Research Institute (EPRI). March 1998. High-Volume Fly Ash
Utilization Projects in the United States and Canada, EPRI CS-4446, Second Edition,
Project 2422-2.
Electric Power Research Institute (EPRI). 1998. Coal Ash: Its Origin, Disposal, Use,
and Potential Health Issues, EPRI Environmental Focus Issue Paper.
Electric Power Research Institute (EPRI). 2002. Mercury Release from Coal Fly Ash.
Palo Alto, CA. 1005259.
Energy Information Administration. 2000. Voluntary Reporting of Greenhouse Gases
2000, Report # DOE/EIA-0608.
Federal Highway Administration (FHWA). June 2003. Fly Ash Facts for Highway
Engineers, FHWA-IF-03-019.
Fly Ash Resource Center. Fly Ash Material Safety Data Sheet.
www.geocities.com/capecanaveral/launchpad/2095/msds.html.
Hassett, David J., Debra F Pflughoeft-Hassett, Dennis L. Laudal, and John H.
Pavlish. 1999. Mercury Release from Coal Combustion Byproducts to the
Environment, www.flyash.org/1999/ashpdf (then click on Hasset21.pdf)
Hassett, David J., Loreal V Heebink. 2001. Release of Mercury Vapor from Coal
Combustion Ash. From the 2001 International Ash Utilization Symposium held
October 22-24, 2001, Lexington, KY.
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Heebink, Loreal V. and David J. Hassett. 2001. Coal Fly Ash Trace Element Mobility
in Soil Stabilization. From the 2001 Ash Utilization Symposium held October 22-24,
2001, Lexington, KY.
Kalyoncu, Rustu S. 2000. U.S. Geological Survey Minerals Yearbook—2000, Coal
Combustion Products.
Meij, Ruud and Henk te Winkel. 2001. Health Aspects of Coal Fly Ash. From the
2001 Ash Utilization Symposium held October 22-24, 2001, Lexington, KY.
Pflughoseft-Hassett, D.F, D.J. Hassett, and B.A. Dockter. 1993. High Volume Fly
Ash Utilization and the Effects on Groundwater in North Dakota in High-Volume
Uses/Concrete Applications. From Proceedings of the 10th International Ash Use
Symposium held January 18-21, 1993, Orlando, FL,. EPRI TR-101774, Project 3176,
Vol.1.
Sutton, Michael E., Thomas E. Schmaltz, Cheri Miller, and Kathy J. Harper. 2001.
Radon Emissions from a High Volume Coal Fly Ash Structural Fill Site. From the
2001 International Ash Utilization Symposium held October 22-24, 2001,
Lexington, KY.
U.S. Environmental Protection Agency. January 28,1983. Guidelines for
Procurement of Products Containing Cement and Concrete, Federal Register
Notice. 48 FR 4230.
U.S. Environmental Protection Agency. August 9,1993. Notice of Regulatory
Determination on Four Large-Volume Wastes from the Combustion of Coal by
Electric Utility Power Plants, Federal Register Notice. 58 FR 42466.
U.S. Environmental Protection Agency. 1997. Annual Emissions and Fuel
Consumption for an "Average" Passenger Car.
U.S. Environmental Protection Agency. October 1998. Supplemental Report to
Congress on Remaining Wastes from Fossil Fuel Combustion—Technical
Background Document: Beneficial Use of Fossil Fuel Combustion (FCC) Wastes.
Office of Solid Waste.
U.S. Environmental Protection Agency. March 1999. Report to Congress: Wastes
from the Combustion of Fossil Fuels—Volume II, EPA 530-S-99-010. Office of Solid
Waste.
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U.S. Environmental Protection Agency. 2000. Municipal Solid Waste in the United
States: 2000 Facts and Figures.
U.S. Environmental Protection Agency. June 2002. Solid Waste Management and
Greenhouse Gases, A Life-Cycle Assessment of Emissions and Sinks, Second
Edition, EPA530-R-02-006. Office of Solid Waste.
U.S. Environmental Protection Agency. February 2003. Guide for Industrial Waste
Management, EPA 530-R-03-001. Office of Solid Waste.
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U.S. Environmental Protection Agency, Coal Combustion Products Partnership
www.epa.gov/c2p2/index.htm
American Coal Ash Association
www.acaa-usa.org
Utility Solid Waste Activities Group
www.uswag.org
Federal Highway Administration, Pavement Technology
www.fhwa.dot.gov/pavement/
Department of Energy
www.doe.gov
The Fly Ash Resource Center
www.geocities.com/CapeCanaveral/Launchpad/2095/flyash.html
Electric Power Research Institute (EPRI)
www.epri.com/destinations
U.S. Environmental Protection Agency, Comprehensive Procurement Guidelines,
Cement and Concrete Specifications
www.epa.gov/cpg/products/cemspecs.htm
University of New Hampshire, Recycled Materials Research Center
www.rmrc.unh.edu/
EERC/University of North Dakota, Coal Ash Resource Center
www.eerc.und.nodak.edu/carrc/index.html
UWMilwaukee, Center for By-Products Utilization
ww.uwm.edu/Dept/CBU
Center for Applied Energy Research at the University of Kentucky
www.flyash.org
Ohio State University, Coal Combustion Product Extension Program
ccpohio.eng.ohio-state.edu/ccpohio
West Virginia University, Combustion Byproduts Recycling Consortium
wvri.nrcce.wvu.edu/programs/cbrc/index.cfm
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