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                                 EXECUTIVE SUMMARY          £,PA/53C?-S W-
530SW88002                                                    8»-oo.a.A.l

       The Environmental . Protection Agency (EPA) has prepared this report on

    fossil fuel combustion wastes pursuant to the requirements of Section 8002 (n)

    of the Resource Conservation and Recovery Act (RCRA) ,  as amended in 1980 .

    These amendments to the Act added Section 8002 (n) ,  which directed the

    Administrator of EPA to


            conduct a detailed and comprehensive study and submit a
            report on the adverse effects on human health and the
            environment, if any, of the disposal and utilization of fly
            ash waste, bottom ash waste, slag waste, flue gas emission
            control waste, and other by-product materials generated
            primarily from the combustion of coal or other fossil fuels.


        Pending the completion of this  study, fossil fuel combustion wastes were

    exempted from the hazardous waste requirements established under RCRA.  Under

    Section 3001(b) (3) (A) , EPA is prohibited from regulating these wastes until at

    least  six  months after this report  is submitted to Congress.



        If EPA determines that fossil fuel combustion wastes are hazardous under

    RCRA,  and  therefore subject to  regulation under Subtitle C, EPA has  some

    flexibility to  promulgate regulations that take into account the unique

    characteristics of these wastes.  Section 3004(x) states  ...
             If ...  fly ash waste, bottom ash waste, slag waste and flue
             gas emission control waste generated primarily from the
             combustion of coal or other fossil fuels ... is subject to
             regulation under this subtitle, the Administrator is
             authorized to modify the requirements of subsections (c),
             (d),  (e), (f), (g), (o) and (u) and section 3005(j) ...  to
             take into account the special characteristics of such wastes,
             the practical difficulties associated with implementation of
             such requirements, and site-specific characteristics ... so
             long as such modified requirements assure protection of human
             health  and the environment.

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     This  report  examines  only  those wastes generated  from  the  combustion  of  coal




 by the electric  utility industry.  These wastes  account  for  approximately 90




 percent of all wastes  generated from  the combustion of fossil  fuels.   EPA has




 deferred study of the  disposal of wastes generated by the  combustion of other




 fossil fuels and from  coal combustion in industries other  than the electric




 utility industry until a later date.








     Coal-fired power plants produce  substantial quantities of wastes.  In 1984




' about 69 million tons of ash and 16  million tons of flue gas desulfurization




 wastes were generated.  Because of increasing reliance on coal for producing




 electricity, by the year 2000 the amount of ash waste is expected to increase by




 about 75 percent to about 120 million tons annually;  production of FGD wastes is




 expected  to triple to  about 50 million tons annually.1  In  addition  to the




 high-volume ash and flue  gas  desulfurization wastes,  coal-fired power  plants




 also  generate several  lower-volume waste streams  as  a result  of equipment




 maintenance and cleaning activities.








      About one-fifth of all  waste generated  at  coal-fired  electric utility power




 plants is currently  reused;  the remaining four-fifths are typically disposed  in




  surface impoundments  or landfills.   The recycled wastes,  usually  fly ash, bottom




  ash, or boiler  slag,  have been used primarily  as cement additives, high-volume




  road construction material, and blasting  grit.   There is  some potential for




  increased use of these wastes in such applications.   However, barring the






       1 It is possible that advances in coal combustion technology will alter




  the  amount and types  of coal-combustion wastes produced in the future.  An




  analysis  of  these technological advances is beyond  the scope of  this  report.

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                                    ES-3
development of new utilization techniques, or major changes in combustion and




environmental control technologies, the proportion of coal combustion wastes




that are reused is unlikely to change significantly.









    While utility waste management sites are currently exempt from RCRA




hazardous waste requirements, they are subject to state and local level solid




waste laws and regulations.  There is substantial variation in the




state-mandated disposal requirements.









    Most utility waste management facilities were not designed to provide a high




level of protection against leaching.  Only about 25 percent of all facilities




have liners to reduce off-site migration of leachate, although 40 percent of the




generating units built since 1975 have liners.  Additionally, only about 15




percent have leachate collection systems; about one-third of all facilities have




ground-water monitoring systems to detect potential leachate problems.  Both




leachate collection and ground-water monitoring systems are more common at newer




facilities.









    The primary concern regarding  the disposal of wastes from coal-fired power




plants is the potential for waste  leachate to cause ground-water contamination.




Although most of the materials found in these wastes do not cause much concern




(for example, over 95 percent of ash is composed of oxides of silicon, aluminum,




iron, and calcium), small  quantities of other constituents that could




potentially damage human health and  the environment may also be present.  These




constituents  include arsenic, barium, cadmium, chromium, lead, mercury, and




selenium.  At certain concentrations, these  elements have  toxic effects.

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    To assess the potential threat to health and the environment posed by these




wastes and to document any specific damage cases,  EPA,  other agencies, and




various private organizations sponsored several studies.   The main research




efforts cited in this Report to Congress are a 1985 study by Arthur D. Little,




Inc. for EPA, which -characterized the environmental effects of waste disposal at




several utility disposal sites, and a series of reports submitted to the Agency




in  1982 by the Utility Solid Waste Activities Group, the Edison Electric




Institute, and the National Rural Electric Cooperative Association.









    The findings of  these various research efforts  indicate that most  coal




combustion wastes do not exhibit any  of the  four hazardous characteristics




defined in RCRA  Subpart C.  The results of a substantial number of  extraction




procedure tests  were examined; these  tests  indicated that metals do not




generally leach  out  of coal combustion wastes at  levels  classified  as hazardous




under RCRA.   The only metals  which were found in  any ash or  sludge  samples  at




 "hazardous"  levels were cadmium  and arsenic.  For boiler cleaning wastes,




 chromium and lead were sometimes  found at levels  classified as hazardous under




 RCRA.  This waste stream  was  also found to be corrosive  in a number of samples.




 Results of EP Tests performed on co-disposed high and  low volume wastes




 indicate,  however,  that boiler cleaning wastes do not  exhibit hazardous




 characteristics when co-disposed with ash.









     While most of the laboratory results indicated that coal combustion wastes




 do not possess RCRA hazardous characteristics, in  some instances,  data on actual




 field observations  indicate  that migration  of potentially hazardous  constituents




 from utility waste  disposal  sites has occurred.   For example, observed

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                                     ES-5
concentrations of contaminants found in ground water downgradient from the sites

exceed the Primary Drinking Water Standards about 5 percent of the time.

Although the magnitude of the PDWS exceedances are typically not many times

greater than the standard, a large number of disposal facilities report at least

one PDWS exceedance at some time.


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    While a causal connection cannot always be made between the utility waste

disposal site and the presence of contaminants at concentrations in excess of

these standards, the available information indicates that some ground-water

contamination from utility disposal sites is indeed occurring.  The actual

potential for exposure of human and ecological populations is likely to be

limited, however, since ground water in the vicinity of utility waste disposal

sites is not typically used for drinking water; the concentrations of

contaminants in the ground water also tend to be diluted in nearby surface water

bodies.  These surface water bodies are typically used by electric utilities in

the power plants for cooling and other purposes.



    The electric utility industry currently spends about $800 million annually

to dispose of its coal-fired combustion wastes.  Under current practices, costs

for waste management at most basic facilities range from as little as $2 per ton

to as much as $31 per ton.  Mitigative measures to control potential

leaching include installation of liners, leachate collection systems, and

ground-water monitoring systems and corrective action to clean up ground-water

contamination.  These mitigative measures, which are currently used at some

utility waste disposal sites, may reduce the likelihood of ground-water

contamination, but may also substantially increase disposal costs.  For example,

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                                    ES-6
the incremental cost of new waste disposal practices,  excluding corrective .




action costs or higher recycling costs,  could range up to $70 per to-n, or $3.7




billion annually if all wastes were listed as hazardous.  While substantial on a




total cost basis, these increases would be unlikely to significantly affect the




rate at which existing power plants consume coal.  Due to the competitiveness of




alternative fuels for electricity generation at future power plants, however,




any increase in disposal costs could potentially slow the growth in electric




utility coal consumption in future years.  Moreover, if new disposal standards




require corrective action measures as set forth in 40 CFR 264.100, the costs  to




utilities could be extremely high and could have a substantial effect on  the




utility industry.









    Based on  the  findings from  this Report to Congress,  the Agency presents




 three  preliminary recommendations  for those wastes  included  in the  scope  of  this




 study.  The recommendations are subject  to change based on continuing




 consultations with other  government agencies  and new  information submitted




 through the public hearings and comments on  this report.  Pursuant  to the




 process outlined in RCRA  3001(b)(3)(C),  EPA  will announce its regulatory




 determination within six  months after  submitting this report to  Congress.









     First.  EPA has concluded  that coal  combustion  waste streams  generally do not




 exhibit hazardous characteristics under current RCRA regulations.	EPA does not




 intend to regulate under Subtitle C flv ash, bottom ash, boiler slag, and flue




 gas desulfurization wastes.   EPA's tentative conclusion is  that current waste




 management practices appear to be adequate for protecting human health and the




 environment.   The Agency prefers that these wastes remain under Subtitle D

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authority.  EPA will use section 7003 of RCRA and sections 104 and 106 of CERCIA




to seek relief in any cases where wastes from coal combustion waste disposal




sites pose substantial threats or imminent hazards to human health and the




environment.  Coal combustion waste problems can also be addressed under RCRA




Section 7002, which authorizes citizen lawsuits for violations of Subtitle D




requirements in 40 CFR Part 257.









    Second. EPA is concerned that several other wastes from coal-fired utilities




may exhibit the hazardous characteristics of corrosivity or EP toxicitv and




merit regulation under Subtitle C.  EPA intends to consider whether these waste




streams should be regulated under Subtitle C of RCRA based on further study and




information obtained durine the public comment period.  The waste streams of




most concern appear to be those produced during equipment maintenance and water




purification, such as metal and boiler cleaning wastes.  The information




available to the Agency at this time does not allow EPA to determine the exact




quantity of coal combustion wastes that may exhibit RCRA Subtitle C




characteristics.  However, sufficient information does exist to indicate that




some equipment maintenance and water purification wastes do occasionally exhibit




RCRA hazardous characteristics, and therefore, may pose a danger to human health




and the environment.  These wastes are similar to wastes produced by other




industries  that are subject to Subtitle C.regulation, and waste management




practices for coal combustion wastes are often similar to waste management




practices employed by other industries.  EPA is considering removing the




exemption for all coal-fired utility wastes other than those identified in the




first recommendation.  The effect would be to apply Subtitle C regulation to any




of those wastes that are hazardous by the RCRA characteristic tests.  EPA

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                                    ES-8
believes there are various treatment options available for these wastes that




would render them nonhazardous without major costs or disruptions to the




utilities.








    Third. EPA encourages the utilization of coal combustion wastes as one




method for reducing the amount of these wastes that need to be disposed to the




extent such utilization can be done in an environmentally safe manner.  From the




information available to the Agency at this time, current waste utilization




practices appear  to be done in an environmentally safe manner.  The Agency




supports voluntary efforts by industry to investigate additional possibilities




for utilizing coal combustion wastes.








    Through  its own analysis, evaluation of public  comments,  and consultation




with  other agencies,  the Agency  will  reach a  regulatory  determination within six




months  of submission  of  this Report  to Congress.  In so  doing,  it  will consider




 and evaluate a broad  range  of management control  options consistent with




 protecting human  health  and the  environment.   Moreover,  if  the  Agency determines




 that Subtitle C regulation  is warranted,  in  accordance with Section 3004(x)  EPA




 will take into  account the  "special  characteristics of  such waste, the practical




 difficulties associated with implementation of such requirements,  and




 site-specific characteristics .  .  .," and will comply with the requirements of




 Executive Orders  12291 and 12498 and the Regulatory Flexibility Act.

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