## Monday,

May 22, 2000



# Part III



# Environmental Protection Agency

40 CFR Part 261
Regulatory Determination on Wastes from the Combustion of Fossil Fuels; Final

Rule


### 32214 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

ENVIRONMENTAL PROTECTION
AGENCY

40 CFR Part 261

[FRL–6588–1]

RIN 2050–AD91

Notice of Regulatory Determination on
Wastes From the Combustion of Fossil

Fuels

AGENCY: Environmental Protection Agency.

ACTION : Regulatory determination.

SUMMARY : This document explains
EPA’s determination of whether regulation of fossil fuel combustion
wastes is warranted under subtitle C of
the Resource Conservation and Recovery Act (RCRA). Today’s action applies to all remaining fossil fuel combustion wastes other than high
volume coal combustion wastes generated at electric utilities and independent power producing facilities and managed separately, which were addressed by a 1993 regulatorydetermination. These include: Largevolume coal combustion wastes generated at electric utility and independent power producing facilities that are co-managed together with certain other coal combustion wastes; coal combustion wastes generated by non-utilities; coal combustion wastes generated at facilities with fluidized bed combustion technology; petroleum coke combustion wastes; wastes from the
combustion of mixtures of coal and other fuels (i.e. , co-burning); wastes from the combustion of oil; and wastes from the combustion of natural gas.

The Agency has concluded these wastes do not warrant regulation under subtitle C of RCRA and is retaining the hazardous waste exemption under RCRA section 3001(b)(3)(C). However,
EPA has also determined national regulations under subtitle D of RCRA
are warranted for coal combustion wastes when they are disposed in landfills or surface impoundments, and that regulations under subtitle D of RCRA (and/or possibly modifications to existing regulations established under authority of the Surface Mining Control and Reclamation Act (SMCRA)) are
warranted when these wastes are used to fill surface or underground mines.

So that coal combustion wastes are consistently regulated across all waste management scenarios, the Agency also
intends to make these national regulations for disposal in surface impoundments and landfills and minefilling applicable to coal combustion wastes generated at electric utility and independent powerproducing facilities that are not comanaged with low volume wastes,.

The Agency has concluded that no additional regulations are warranted for
coal combustion wastes that are used beneficially (other than for minefilling) and for oil and gas combustion wastes. We do not wish to place any unnecessary barriers on the beneficial
use of fossil fuel combustion wastes so that they can be used in applications
that conserve natural resources and reduce disposal costs. Currently, about one-quarter of all coal combustion
wastes are diverted to beneficial uses. We support increases in these beneficial uses, such as for additions to cement and concrete products, waste
stabilization and use in construction products such as wallboard.

DATES : Comments in response to data and information requests in this document are due to EPA on September

19, 2000.

ADDRESSES : Public comments and supporting materials are available for viewing in the RCRA Information Center (RIC). In addition to the data and
information that was included in the docket to support the RTC on FFC waste and the Technical Background Documents, the docket also includes the following document: Responses to Public Comments on the Report To Congress, Wastes from the Combustion
of Fossil Fuels. The RIC is located at Crystal Gateway I, First Floor, 1235 Jefferson Davis Highway, Arlington, VA.
The Docket Identification Number is F– 2000–FF2F–FFFFF. The RIC is open from 9 a.m. to 4 p.m., Monday through Friday, excluding federal holidays. To review docket materials, we recommend that the public make an appointment by calling 703 603–9230. The public may copy a maximum of 100 pages from any regulatory docket at no charge. Additional copies cost $0.15/page. The index and some supporting materials are available electronically. See the

SUPPLEMENTARY INFORMATION section for information on accessing them.

Commenters must send an original and two copies of their comments referencing docket number F–2000– FF2F–FFFFF to: (1) If using regular US
Postal Service mail: RCRA Docket Information Center, Office of Solid Waste (5305G), U.S. Environmental Protection Agency Headquarters (EPA, HQ), Ariel Rios Building, 1200 Pennsylvania Avenue, NW., Washington, DC 20460–0002; or (2) if using special delivery, such as overnight express service: RCRA Docket Information Center (RIC), Crystal Gateway One, 1235 Jefferson Davis Highway, First Floor, Arlington, VA 22202. Comments may also be submitted electronically through the

Internet to: rcra-docket@epa.gov

. Comments in electronic format should also be identified by the docket number
F–2000–FF2F–FFFFF and must be submitted as an ASCII file avoiding the use of special characters and any form of encryption.

Commenters should not submit electronically any confidential business information (CBI). An original and two copies of CBI must be submitted under separate cover to: RCRA CBI Document Control Officer, Office of Solid Waste (5305W), U.S. EPA, Ariel Rios Building, 1200 Pennsylvania Avenue, NW., Washington, DC 20460–0002.

FOR FURTHER INFORMATION CONTACT: For general information, contact the RCRA
Hotline at 800 424–9346 or TDD 800 553–7672 (hearing impaired). In the Washington, DC, metropolitan area, call

703 412–9810 or TDD 703 412–3323.

For more detailed information on specific aspects of this regulatory determination, contact Dennis Ruddy, Office of Solid Waste (5306W), U.S. Environmental Protection Agency, Ariel Rios Building, 1200 Pennsylvania Avenue, NW, Washington, DC 20460– 0002, telephone (703) 308–8430, e-mail
address ruddy.dennis@epa.gov

.
SUPPLEMENTARY INFORMATION : The index and several of the primary supporting
materials are available on the Internet.
You can find these materials at <http:/ /www.epa.gov/epaoswer/other/fossil/
index.htm

.

The official record for this action will be kept in paper form. Accordingly, EPA
will transfer all comments received electronically into paper form and place them in the official record, which will
also include all comments submitted directly in writing. The official record is the paper record maintained at the
address in ADDRESSES at the beginning
of this notice.

EPA will not immediately reply to commenters electronically other than to
seek clarification of electronic comments that may be garbled in transmission or during conversion to paper form, as discussed above.

The contents of today’s notice are listed in the following outline:

1. General Information

A. What action is EPA taking today? B. What is the statutory authority for this

action?

C. What was the process EPA used in making today’s decision?

D. What is the significance of ‘‘uniquely
associated wastes’’ and what wastes does EPA consider to be uniquely associated

wastes?


### 32215 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

E. Who is affected by today’s action and how are they affected?

F. What additional actions will EPA take after this regulatory determination regarding coal, oil and natural gas combustion wastes?

2. What Is the Basis for EPA’s Regulatory

Determination for Coal Combustion Wastes?

A. What is the Agency’s decision regarding the regulatory status of coal combustion wastes and why did EPA make that decision?

B. What were EPA’s tentative decisions as presented in the Report to Congress?

C. How did commenters react to EPA’s

tentative decisions and what was EPA’s analysis of their comments?

D. What is the basis for today’s decisions? E. What approach will EPA take in developing national regulations?

3. What Is the Basis for EPA’s Regulatory

Determination for Oil Combustion Wastes?

A. What is the Agency’s decision regarding the regulatory status of oil combustion wastes and why did EPA make that decision?

B. What were EPA’s tentative decisions as presented in the Report to Congress?

C. How did commenters react to EPA’s

tentative decisions and what was EPA’s analysis of their comments?

D. What is the basis for today’s decisions?

4. What Is the Basis for EPA’s Regulatory

Determination for Natural Gas Combustion

Wastes?

A. What is the Agency’s decision regarding the regulatory status of natural gas combustion wastes and why did EPA make

that decision?

B. What was EPA’s tentative decision as presented in the Report to Congress?

C. How did commenters react to EPA’s

tentative decisions?

D. What is the basis for today’s decisions?

5. What Is the History of EPA’s Regulatory

Determinations for Fossil Fuel Combustion

Wastes?

A. On what basis is EPA required to make regulatory decisions regarding the regulatory

status of fossil fuel combustion wastes?

B. What was EPA’s general approach in making these regulatory determinations?

C. What happened when EPA failed to issue its determination of the regulatory status of the large volume utility combustion wastes in a timely manner?

D. When was the Part 1 regulatory decision made and what were EPA’s findings?

6. Executive Orders and Laws Addressed in Today’s Action

A. Executive Order 12866—Determination of Significance.

B. Regulatory Flexibility Act, as amended. C. Paperwork Reduction Act (Information Collection Requests).

D. Unfunded Mandates Reform Act.

E. Executive Order 13132: Federalism. F. Executive Order 13084: Consultation

and Coordination with Indian Tribal

Governments.

G. Executive Order 13045: Protection of

Children from Environmental Health Risks and Safety Risks.

H. National Technology Transfer and

Advancement Act of 1995.

I. Executive Order 12898: Environmental Justice.

J. Congressional Review Act.

7. How To Obtain more Information

1. General Information

A. What Action Is EPA Taking Today?

In today’s action, we are determining that regulation of fossil fuel combustion (FFC) wastes under subtitle C of the Resource Conservation and Recovery Act (RCRA) is not warranted. This determination covers the following

wastes:

• Large-volume coal combustion wastes generated at electric utility and independent power producing facilities that are co-managed together with certain other coal combustion wastes;

• Coal combustion wastes generated at non-utilities;

• Coal combustion wastes generated
at facilities with fluidized bed combustion technology;

• Petroleum coke combustion wastes;

• Wastes from the combustion ofmixtures of coal and other fuels (i.e., coburning of coal with other fuels where coal is at least 50% of the total fuel);

• Wastes from the combustion of oil;
and

• Wastes from the combustion of natural gas.

While these wastes remain exempt from subtitle C, we have further decided to establish national regulations under subtitle D of RCRA (RCRA sections 1008(a) and 4004(a)) for coal combustion wastes that are disposed in landfills or surface impoundments or used to fill surface or underground
mines. For coal combustion wastes used as minefill, we will consult with the Office of Surface Mining in the Department of the Interior and thoroughly assess whether equivalent protectiveness could be achieved by using regulatory authorities available under the Surface Mining Control and Reclamation Act (SMCRA), as well as
those afforded under the Resource Conservation and Recovery Act. We will
consider whether RCRA subtitle D or
SMCRA authorities or some
combination of both are most appropriate to regulate the disposal of
coal combustion wastes when used for minefill in surface and underground mines to ensure protection of human
health and the environment. These standards will be developed through notice and comment rulemaking and in
consultation with states and other stakeholders. These regulations will, in EPA’s view, ensure that the trend towards improved management of coal combustion wastes over recent years
will accelerate and will ensure a consistent level of protection of human health and the environment is put in place across the United States.

If, as a result of comments in response to this notice; the forthcoming analyses identified in this notice; or additional information garnered in the course of developing these national regulations;
we find that there is a need for regulation under the authority of RCRA subtitle C, the Agency will revise this determination accordingly.

We recognize our decision to develop regulations under RCRA subtitle D (or, for minefilling, possibly under SMCRA)
for the above-listed coal combustion wastes was not specifically identified as an option in our March 31, 1999 Report to Congress. Our final determination reflects our consideration of public comments received on the Report to Congress and other analyses that we
conducted.

Today’s decision was, in the Agency’s view, a difficult one, given the many competing considerations discussed throughout today’s notice. After considering all of the factors specified in RCRA section 8002(n), we have decided as discussed further below, that
the decisive factors are the trends in present disposal and utilization practices (section 8002 (n)(2)), the current and potential utilization of the wastes (Section 8002 (n)(8), and the admonition against duplication of efforts by other federal and state agencies.

As described in the Report to Congress, the utility industry has made significant improvements in its waste management practices over recent years, and most state regulatory programs are similarly improving. For example, in the utility industry the use of liners and groundwater monitoring at landfills and surface impoundments has increased substantially over the past 15 years as indicated in the following table.


### 32216 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

P ERCENT OF 

### U TILITY 

### COAL 

### COMBUSTION 

### WASTE 

### MANAGEMENT 

### U NITS 

### W ITH 

### CONTROLS IN 

### 1995

Waste management unit Liners Groundwater monitoring

Percent of

all units Percent of
new units * Percent of
all units Percent of
new units *

Landfills ...................................................................................................................... ...... 57 75 85 88 Surface Impoundments .................................................................................................... 26 60 38 65

* New units constructed between 1985–1995. Source: USWAG, EPRI 1995.

Public comments and other analyses, however, have convinced us that these wastes could pose risks to human health and the environment if not properly managed, and there is sufficient evidence that adequate controls may not be in place—for example, while most states can now require newer units to include liners and groundwater monitoring, 62% of existing utility surface impoundments do not have groundwater monitoring. This, in our view, justifies the development of national regulations. We note, however, that some waste management units may not warrant liners and/or groundwater monitoring, depending on site-specific
characteristics.

New information we received in public comments includes additional documented damage cases, as well as cases indicating at least a potential for damage to human health and the environment. We did not independently investigate these damage cases; rather,
we relied on information contained in
state files. While the absolute number of documented damage cases is not large,
we have considered the evidence of proven and potential damage in light of the proportion of facilities that lack basic environmental controls (e.g., groundwater monitoring). We acknowledge, moreover, that our inquiry into the existence of damage cases was focused primarily on a subset
of states—albeit states that account for almost 20 percent of coal fired utility electricity generation capacity. Given
the volume of coal combustion wastes generated nationwide (115 million tons)
and the numbers of facilities that currently lack some basic environmental controls, especially groundwater monitoring, other cases of proven and potential damage are likely to exist.
Because EPA did not use a statistical sampling methodology to evaluate the potential for damage, the Agency is
unable to determine whether the identified cases are representative of the conditions at all facilities and, therefore, cannot quantify the extent and magnitude of damages at the national
level. Since the Report to Congress, we have conducted additional analyses of the potential for the constituents of coal
combustion wastes to leach in dangerous levels into ground water. Based on a comparison of drinking water and other appropriate standards
to leach test data from coal combustion waste samples, we identified a potential
for risks from arsenic that we cannot
dismiss at this time. This conclusion is based on possible exceedences of a range of values that EPA is currently considering for a revised arsenic MCL. Once a new arsenic MCL is established, additional groundwater modeling may be required to evaluate the likelihood of exceeding that MCL.

As discussed further below, in light of
certain comments received on the Report to Congress, we are not relying on a quantitative groundwater risk assessment to assess potential risks to
human health or the environment. In the absence of a more complete groundwater risk assessment, we are unable at this time to draw quantitative conclusions regarding the risks due to arsenic or other contaminants posed by improper waste management. Once we have completed a review of our groundwater model and made any necessary changes, we will reevaluate groundwater risks and take appropriate regulatory actions. We will specifically assess new modeling results as they relate to any promulgated changes in the

arsenic MCL.

We acknowledge that, even without federal regulatory action, many facilities in the utility industry have either voluntarily instituted adequate
environmental controls or have done so at the direction of states that regulate these facilities. In addition, we found that for the proven damage cases, the states (and in two cases, EPA under the Superfund program) have taken action to mitigate risk and require corrective action. However, in light of the evidence of actual and potential environmental releases of metals from these wastes; the large volume of wastes generated from coal combustion; the proportion of existing and even newer units that do not currently have basic controls in place; and the presence of hazardous constituents in these wastes; we believe, on balance, that the best means of ensuring that adequate controls are imposed where needed is to develop national subtitle D regulations. As we develop and issue the national regulations, we will try to minimize disruptions to operation of existing waste management units.

In taking today’s action, we carefully considered whether to develop national regulations under RCRA subtitle D or subtitle C authorities. One approach we considered was to promulgate regulations pursuant to subtitle C authority, similar to recently proposed regulations applicable to cement kiln dust. Under this approach, EPA would have established national management
standards for coal combustion wastes managed in landfills and surface impoundments and used for minefilling,
as well as a set of tailored subtitle C requirements, promulgated pursuant to RCRA section 3004(x). If wastes were properly managed in accordance with subtitle D-like standards, they would
not be classified as a hazardous waste. If wastes were not properly managed, they would become listed hazardous wastes subject to tailored subtitle C standards. This approach would give EPA enforcement authority in states following their adoption of the contingent management listing.

We believe, however, for the reasons described below, the better approach at this time to ensuring adequate management of FFC wastes is to develop national regulations under subtitle D
rather than subtitle C. EPA has reached this conclusion in large part based on consideration of ‘‘present disposal and utilization practices.’’ RCRA § 8002(n). As noted above, present disposal practices in landfills and surface impoundments are significantly better than they have been in the past in terms of imposing basic environmental controls such as liners and groundwater monitoring. This trend is the result of increasing regulatory oversight by states of the management of these wastes as well as voluntary industry improvements. In the 1980’s, only 11


### 32217 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

states had authority to require facilities to install liners, and 28 states had the authority to require facilities to conduct groundwater monitoring at landfills. As of 1995, these rates were significantly higher, with 43 states having the authority to require liners and 46 states having the authority to require groundwater monitoring at landfills. When authority under state groundwater and drinking water regulations are considered, some commenters have suggested that nearly all states can address the management of these wastes. Thus, with the exception of relatively few states, the regulatory infrastructure is generally in place at the state level to ensure adequate management of these wastes.

While the trend both in terms of state regulatory authorities and the imposition of controls at these facilities has been positive, between 40 and 70 percent of sites lacked controls such as liners and/or groundwater monitoring as of 1995. This gap is of environmental concern given the potential for risks posed by mismanagement of coal
combustion wastes in certain circumstances. Nonetheless, given most of the states’ current regulatory capabilities and the evidence that basic controls are increasingly being put in place by the states and facilities (see RCRA section 8002(n), which directs
EPA to consider actions of state and other federal agencies with a view to avoiding duplication of effort), EPA
believes that subtitle D controls will provide sufficient clarity and incentive for states to close the remaining gaps in coverage, and for facilities to ensure that their wastes are managed properly.

For minefilling, although we have
considerable concern about certain current practices (e.g., placement directly into groundwater) we have not yet identified a case where placement of
coal wastes can be determined to have actually caused increased damage to ground water. In addition, there is a federal regulatory program—SMCRA— expressly designed to address
environmental risks associated with coal mines. Finally, given that states have been diligent in expanding and upgrading programs, as they have done for surface impoundments and landfills, we believe they will be similarly responsive in addressing environmental concerns arising from this emerging practice. In short, we arrive at the same conclusions, for substantially the same reasons, for this practice as we did for landfills and surface impoundments: that subtitle D controls, or upgraded
SMCRA controls or a combination of the two, should provide sufficient clarity and incentive to ensure proper handling of this waste. Having determined that subtitle C regulation is not warranted for all other management practices, EPA
does not see a basis in the record for carving this one practice out for separate regulatory treatment.

Once these regulations are effective, facilities would be subject to citizen suits for any violation of the standards. If EPA were addressing wastes that had not been addressed by the states (or the federal government) in the past, or an industry with wide evidence of irresponsible solid waste management practices, EPA may well conclude that
the additional incentives for improvement and compliance provided by the subtitle C scheme—the threat of federal enforcement and the stigma associated with improper management
of RCRA subtitle C waste—were necessary. But the record before us
indicates that the structure and the
sanctions associated with a subtitle D approach (or a SMCRA approach if EPA determines it is equivalent) should be
sufficient.

We also see a potential downside to pursuing a subtitle C approach. Section 8002(n)(8) directs us to consider, among other factors, ‘‘the current and potential utilization of such materials.’’ Industry commenters have indicated that they believe subjecting any coal combustion wastes to a subtitle C regime would place a significant stigma on these wastes, the most important effect being that it would adversely impact beneficial reuse. As we understand it, the concern is that, even though beneficially reused waste would not be hazardous under the contemplated subtitle C approach, the link to subtitle C would nonetheless tend to discourage purchase and re-use of the waste. We do not wish to place any unnecessary
barriers on the beneficial uses of these wastes, because they conserve natural resources, reduce disposal costs and
reduce the total amount of waste destined for disposal. States and industry have also expressed concern that regulation under subtitle C could
cause a halt in the use of coal
combustion wastes to reclaim
abandoned and active mine sites. We recognize that when done properly, minefilling can lead to substantial
environmental benefits. EPA believes the contingent management scheme we discussed should diminish any stigma that might be associated with the subtitle C link. Nonetheless, we acknowledge the possibility that the approach could have unintended consequences. We would be particularly concerned about any adverse effect on
the beneficial re-use market for these wastes because more than 23 percent (approximately 28 million tons) of the total coal combustion waste generated each year is beneficially reused and an additional eight percent (nine million tons) is used for minefilling. EPA
believes that such reuse when performed properly, is by far the environmentally preferable destination for these wastes, including when minefilled. Normally, concerns about stigma are not a deciding factor in EPA’s decisions under RCRA, given the central concern under the statute for protection
of human health and the environment. However, given our conclusion that the subtitle D approach here should be fully effective in protecting human health and the environment, and given the large and salutary role that beneficial reuse plays for this waste, concern over stigma is a factor supporting our decision today that subtitle C regulation is unwarranted in light of our decision to pursue a subtitle D approach.

Additionally, in a 1993 regulatory determination, EPA previously addressed large volume coal combustion wastes generated at electric utility and independent power producing facilities that manage the wastes separately from certain other low volume and uniquely associated coal combustion wastes (see 58 FR 42466; August 9, 1993). Our 1993 regulatory determination maintained the exemption of these large volume coal combustion wastes from being regulated as hazardous wastes when managed separately from other wastes (e.g., in monofills). We intend that the national subtitle D regulations we develop for the coal combustion wastes subject to today’s regulatory determination will also be applicable to the wastes covered in the 1993 regulatory determination for the reasons listed below, so that all coal combustion wastes are consistently regulated for placement in landfills, surface impoundments, and minefills.

• The co-managed coal combustion wastes that we studied extensively in making today’s regulatory determination derive their characteristics largely from these large-volume wastes and not from the other wastes that are co-managed
with them.

• We believe that the risks posed by the co-managed coal combustion wastes result principally from the large-volume

wastes.

• These large-volume coal combustion wastes, account for over 20% of coal combustion wastes.

As we proceed with regulation development, we will also take
enforcement action under RCRA section 7003 when we identify cases of
imminent and substantial endangerment. We will also use Superfund remedial and emergency


### 32218 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

1 The consent decree entered into by EPA (Frank Gearhart, et al. v. Browner, et al., No. 91–2435 (D.D.C.) for completing the studies and regulatory

determination for fossil fuel combustion wastes used the term ‘‘remaining wastes’’ to differentiate the wastes to be covered in today’s decision from the large-volume utility coal combustion wastes that were covered in the August 1993 regulatory determination (see 58 FR 42466). response authorities under the Comprehensive Environmental Response Compensation and Liabilities Act (CERCLA), as appropriate, to address damages that result in risk to
human health and the environment.

However, as stated above, this
decision was a difficult one and EPA believes that, absent our conclusions regarding the current trends in management of this waste, the waste might present sufficient potential threat
to human health and the environment to justify subtitle C regulation. There are several factors that might cause us to rethink our current determination. First, and perhaps most importantly, if current trends toward protective management do not continue, EPA may well determine that subtitle C regulation
is warranted for this waste. As we have stated, we do not believe the current gaps in the basic controls are acceptable,
and our determination that subtitle C regulation is not warranted is premised to a large extent on our conclusion that subtitle D regulation will be sufficient to close these gaps. If this conclusion turns out not to be warranted, we would be
inclined to re-examine our current
decision.

Second, EPA will continue to examine available information and, as a result of the ongoing review, may
conclude over the next several months
that this decision should be revised. Our ongoing review will include consideration of: (1) The extent to
which fossil fuel combustion wastes have caused actual or potential damage to human health or the environment; (2) the environmental effects of filling underground and surface coal mines with fossil fuel combustion wastes; and (3) the adequacy of existing state and/ or federal regulation of these wastes. Finally, the agency will consider the results of a report of the National Academy of Sciences regarding the
adverse human health effects of mercury, one of the constituents in
fossil fuel combustion wastes. EPA believes that this report will enhance our understanding of the risks due to exposure to mercury. All of these efforts may result in a subsequent revision of today’s regulatory determination.

Finally, relating to oil combustion wastes, we will work with relevant stakeholders so that any necessary
measures are taken to ensure that oil combustion wastes currently managed in the two known remaining unlined surface impoundments are managed in a manner that protects human health
and the environment. B. What Is the Statutory Authority for
This Action?

We are issuing today’s notice under the authority of RCRA section 3001 (b) (3) (C), as amended. This section exempts certain wastes, including fossil fuel combustion wastes, from hazardous waste regulation until the Agency completes a Report to Congress mandated by RCRA section 8002 (n) and maintains the exemption, unless the
EPA Administrator makes a determination that subtitle C (hazardous waste) regulation is warranted. RCRA section 3004 (x) provides the Agency with flexibility in developing subtitle C standards. If appropriate, these formerly exempted wastes may not be subjected to full subtitle C requirements in areas such as treatment standards, liner design requirements and corrective

action.

C. What Was the Process EPA Used in Making Today’s Decision?

1. What Approach Did EPA Take to Studying Fossil Fuel Combustion

Wastes?

We conducted our study of wastes generated by the combustion of fossil fuels in two phases. The first phase, called the Part 1 determination, covered high volume coal combustion wastes ( e.g., bottom ash and fly ash) generated at electric utility and independent power producing facilities (non-utility electric power producers that are not engaged in any other industrial activity) and managed separately from other fossil fuel combustion wastes. In 1993, EPA issued a regulatory determination that exempted Part 1 wastes from regulation as hazardous wastes (see 58 FR 42466; August 9, 1993). Today’s regulatory determination is the second phase of our effort, or the Part 2
determination. It covers all other fossil
fuel combustion wastes not covered in Part 1. This includes high volume, utility-generated coal combustion wastes when co-managed with certain
low volume wastes that are also generated by utility coal burners; coal combustion wastes generated by industrial, non-utility, facilities; and
wastes from the combustion of oil and gas. Under court order, we are required to complete the Part 2 regulatory determination by April 25, 2000. 1 2. What Statutory Requirements Does EPA Have To Meet in Making Today’s Regulatory Determinations?

RCRA section 8002(n) specifies eight study factors that we must take into account in our decision-making. These

are:

1. The source and volumes of such materials generated per year.

2. Present disposal practices. 3. Potential danger, if any, to human
health and the environment from the disposal of such materials.

4. Documented cases in which danger
to human health or the environment has been proved.

5. Alternatives to current disposal
methods.

6. The costs of such alternatives. 7. The impact of those alternatives on
the use of natural resources.

8. The current and potential
utilization of such materials.

Additionally, in developing the Report to Congress, we are directed to
consider studies and other actions of other federal and State agencies with a view toward avoiding duplication of effort (RCRA section 8002(n)). In addition to considering the information contained in the Report, EPA is required to base its regulatory determination on information received in public hearings and comments submitted on the Report to Congress (RCRA section 3001(b)(3)(C)).

3. What Were the Agency’s Sources of
Information and Data That Serve as the
Basis for This Decision?

We gathered publicly available information from a broad range of sources, including federal and state agencies, industry trade groups, environmental organizations, and open literature searches. We requested information from all stakeholder groups on each of the study factors Congress requires us to evaluate. For many of the study factors, very limited information existed prior to this study. We worked closely with the Edison Electric Institute (EEI), Utility Solid Waste Activities Group (USWAG), the Electric Power Research Institute (EPRI), and the
Council of Industrial Boiler Owners (CIBO) as those organizations developed new information. Because other ongoing EPA projects currently focus on portions of the FFC waste generator universe, we also leveraged data collection efforts conducted for air, industrial waste, and hazardous waste programs. In addition,
we obtained information from environmental organizations regarding
beneficial uses of some FFC wastes and methods for characterizing the risks
associated with FFC wastes.


### 32219 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

Specifically, we gathered and analyzed the following information from industry, states and environmental

groups:

• Published and unpublished
materials obtained from state and federal agencies, utilities and trade industry groups, and other knowledgeable parties on the volumes and characteristics of coal, oil, and natural gas combustion wastes and the corresponding low-volume and uniquely associated wastes (see the following section for a description of ‘‘uniquely associated wastes’’).

• Published and unpublished materials on waste managementpractices (including co-disposal and reuse) associated with FFC wastes and the corresponding low-volume and uniquely associated wastes.

• Published and unpublished materials on the potential environmental impacts associated with

FFC wastes.

• Published and unpublished materials on trends in utility plant operations that may affect waste
volumes and characteristics. We gathered specific information on
innovations in scrubber use and the potential impacts of the 1990 Clean Air
Act Amendments on waste volumes and
characteristics.

• Energy Information Agency (EIA), Department of Energy, data on utility operations and waste generation
obtained from EIA’s Form 767 database.
These data are submitted to EIA annually by electric utilities.

• Site visit reports and accompanyingfacility submittals for utility and nonutility plants we visited during the study.

• Materials obtained from public files maintained by State regulatory agencies.
These materials focus on waste characterization, waste management, and environmental monitoring data, along with supporting background
information.

We visited five states to gather specific information about state regulatory programs, FFC waste generators, waste management practices and candidate damage cases related to
fossil fuel combustion. The five states we examined in great detail were: Indiana, Pennsylvania, North Carolina, Wisconsin, and Virginia. These five states account for almost 20 percent of coal-fired utility electrical generation capacity.

We also performed a variety of analyses, including human health and ecological risk assessments, analyses of existing federal and state regulatory programs, and economic impact analyses. We discussed and shared these results with all of our
stakeholders. We also conducted an external peer review of our risk analysis.

4. What Process Did EPA Follow To Obtain Comments on the Report to Congress?

RCRA requires that we publish a Report to Congress (RTC) evaluating the above criteria. Further, within six months of submitting the report, we must, after public hearings and opportunity for comment, decide whether to retain the exemption from hazardous waste requirements or whether regulation as hazardous waste is warranted. On March 31, 1999, we issued the required RTC on those fossil fuel combustion wastes (coal, oil and gas) not covered in the Part 1 regulatory determination, which are also known as the ‘‘remaining wastes’’ (see footnote 1).

We asked the public to comment on the Report and the appropriateness of regulating fossil fuel wastes under
subtitle C of RCRA. To ensure that all interested parties had an opportunity to present their views, we held a public meeting with stakeholders on May 21, 1999. The April 28, 1999 Federal Register notice provided a 45-day public comment period, until June 14, 1999. We received over 150 requests to extend the public comment period by up to six months. However, we were obligated by a court-ordered deadline to issue our official Regulatory Determination by October 1, 1999. (See 64 FR 31170; June 10, 1999.) In response to requests for an extension, we entered into discussions with the parties to
consider an extension of the comment period to ensure that all interested members of the public had sufficient time to complete their review and submit comments. Subsequently, the plaintiffs in Gearhart v. Reilly moved to modify the consent decree to reopen the comment period and to allow EPA until March 10, 2000 to complete the Regulatory Determination. We supported the motion, and on September 2, 1999, the Court granted the motion. In compliance with the court order, on September 20, 1999, we announced that public comments would be accepted through September 24, 1999 (64 FR 50788; Sept. 20, 1999). We have
since received two extensions to the
date for the final determination. Currently, EPA is directed to issue the Part 2 regulatory determination by April

25, 2000.

We received about 220 comments on the RTC from the public hearing and our Federal Register requests for comments. The docket for this action (Docket No. F–99–FF2P–FFFFF) contains all individual comments presented in the public meetings and hearing, and a transcript from the public hearing, and
all written comments. The docket is available for public inspection. Today’s decision is based on the RTC, its underlying data and analyses, public comments, and EPA analyses of these

comments.

The comments covered a wide variety of topics discussed in the Report to Congress, such as fossil fuel combustion waste generation and characteristics; current and alternative practices for managing FFC waste; documented damage cases and potential danger to human health and the environment; existing regulatory controls on FFC waste management; cost and economic impacts of alternatives to current management practices; FFC beneficial use practices; and our review of applicable state and federal regulations.

D. What Is the Significance of ‘‘Uniquely
Associated Wastes’’ and What Wastes Does EPA Consider To Be ‘‘Uniquely
Associated Wastes?’

Facilities that burn fossil fuels generate combustion wastes and also generate other wastes from processes
that are related to the main fuel combustion processes. Often, as a general practice, facilities co-dispose these wastes with the large volume wastes that are subject to the RCRA section 3001 (b) (3) (C) exemption. Examples of these related wastes are:

• Precipitation runoff from the coal storage piles at the facility.

• Waste coal or coal mill rejects that are not of sufficient quality to burn as
fuel.

• Wastes from cleaning the boilers used to generate steam.

There are numerous wastes like these, collectively known as ‘‘low-volume’’wastes. Further, when one of these lowvolume wastes, during the course of generation or normal handling at the facility, comes into contact with either fossil fuel (e.g., coal, oil) or fossil fuel combustion waste (e.g., coal ash or oil ash) and it takes on at least some of the
characteristics of the fuel or combustion waste, we call it a ‘‘uniquely associated’’ waste. When uniquely associated wastes are co-managed with fossil fuel combustion wastes, they fall within the coverage of today’s regulatory determination. When managed separately, uniquely associated wastes are subject to regulation as hazardous waste if they are listed wastes or exhibit
the characteristic of a hazardous waste (see 40 CFR 261.20 and 261.30, which specify when a solid waste is considered to be a hazardous waste).

The Agency recognizes that determining whether a particular waste


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is uniquely associated with fossil fuel
combustion involves an evaluation of the specific facts of each case. In the Agency’s view, the following qualitative
criteria should be used to make such determinations on a case-by-case basis:

(1) Wastes from ancillary operations are not ‘‘uniquely associated’’ because they are not properly viewed as being
‘‘from’’ fossil fuel combustion.

(2) In evaluating a waste from nonancillary operations, one must consider the extent to which the waste originates or derives from the fossil fuels, the combustion process, or combustion residuals, and the extent to which these operations impart chemical
characteristics to the waste.

The low-volume wastes that are not uniquely associated with fossil fuel combustion would not be subject to today’s regulatory determination. That is, they would not be accorded an exemption from RCRA subtitle C, whether or not they were co-managed with any of the exempted fossil fuel combustion wastes. Instead, they would be subject to the RCRA characteristic standards and hazardous waste listings. The exemption applies to mixtures of an exempt waste with a non-hazardous waste, but when an exempt waste is mixed with a hazardous waste, the mixture is not exempt.

Based on our identification and
review of low volume wastes associated with the combustion of fossil fuels, we are considering offering the following guidance concerning which low volume wastes are uniquely associated with and which are not uniquely associated with
fossil fuel combustion. Unless there are some unusual site-specific circumstances, we would generally consider that the following lists of lowvolume wastes are uniquely and nonuniquely associated wastes:

Uniquely Associated

• Coal Pile Runoff

• Coal Mill Rejects and Waste Coal

• Air Heater and Precipitator Washes

• Floor and Yard Drains and Sumps

• Wastewater Treatment Sludges

• Boiler Fireside Chemical Cleaning

Wastes

Not Uniquely Associated

• Boiler Blowdown

• Cooling Tower Blowdown and

Sludges

• Intake or Makeup Water Treatment

and Regeneration Wastes

• Boiler Waterside Cleaning Wastes

• Laboratory Wastes

• General Construction and Demolition

Debris

• General Maintenance Wastes

Moreover, we do not generally consider spillage or leakage of materials used in the processes that generate these non-uniquely associated wastes, such as boiler water treatment chemicals, to be uniquely associated wastes, even if they occur in close proximity to the fossil fuel wastes covered by this regulatory
determination.

An understanding of whether a waste is uniquely associated can be important
in one circumstance. If a waste is not uniquely associated and is a hazardous waste, co-managment with a Bevill
waste will result in loss of the Bevill exemption. As a general matter, the wastes identified above as potentially not uniquely associated do not tend to be hazardous. This issue may therefore not be critical. The Agency, however, must still define appropriate boundaries for the Bevill exemption, because there is no authority to grant Bevill status to wastes that are not uniquely associated—the exemption was not
intended as an umbrella for wastes that
other industries must treat as hazardous.

EPA solicits comment on this discussion of uniquely associated
wastes in the context of fossil fuel
combustion and will issue final guidance after reviewing and evaluating
information we receive as a result of this request.

E. Who Is Affected by Today’s Action and How Are They Affected?

As explained above, fossil fuel combustion wastes generated from the combustion of coal, oil and natural gas will continue to remain exempt from being regulated as hazardous wastes under RCRA. No party is affected by today’s determination to develop regulations applicable to coal combustion wastes when they are land disposed or used to fill surface or underground mines because today’s action does not impose requirements. However, if such regulations are promulgated, they would affect coal combustion wastes subject to today’s regulatory determination as well as wastes covered by the Part 1 regulatory determination when they are disposed in landfills and surface impoundments,
or when used to fill surface or underground mines.

While we do not intend that national subtitle D regulations would be applicable to oil combustion wastes, we
intend to work with relevant stakeholders so that any necessary
measures are taken to ensure that oil combustion wastes currently managed in the two known remaining unlined surface impoundments are managed in a manner that protects human health
and the environment. F. What Additional Actions Will EPA Take After this Regulatory Determination Regarding Coal, Oil and
Natural Gas Combustion Wastes?

To ensure that entities who generate and/or manage fossil fuel combustion wastes provide long-term protection of human health and the environment, we plan several actions:

• We will review comments submitted in response to today’s notice on uniquely associated wastes and on the adequacy of the guidance developedby the utility industry on comanagement of mill rejects (pyrites) with large volume coal combustion

wastes.

• We will work with the State of
Massachusetts and the owners and operators of the remaining two oil combustion facilities that currently manage their wastes in unlined surface impoundments to ensure that any necessary measures are taken so these wastes are managed in a manner that protects human health and the environment (described in section 3.D. of this document).

• We are evaluating the groundwater model and modeling methods that were
used in the RTC to estimate risks for these wastes. This review may result in a re-evaluation of the potential groundwater risks posed by the management of fossil fuel combustion
wastes and action to revise our Part 1 and Part 2 determinations if appropriate (see section 2.C. of this document).

• There are a number of ongoing and evolving efforts underway at EPA to improve our understanding of the human health impacts of wastes used in agricultural settings. We expect to
receive substantial comments and new
scientific information based on a risk
assessment of the use of cement kiln dust as a substitute for agricultural lime (see 64 FR 45632; August 20, 1999) and other Agency efforts. As a result, we may refine our methodology for assessing risks related to the use of wastes in agricultural settings. If these
efforts lead us to a different understanding of the risks posed by
fossil fuel combustion wastes when used as a substitute for agricultural lime, we will take appropriate action to reevaluate today’s regulatory determination (see section 2.C. of this document).

• We will review the findings and
recommendations of the National Academy of Sciences upcoming report on mercury and assess its implications on risks due to exposure to mercury. We will ensure that the regulations we develop as a result of today’s regulatory determination address any additional


### 32221 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

risks posed by these wastes if hazardous constituent levels exceed acceptable
levels

• We will reevaluate risk posed by managing coal combustion solid wastes if levels of mercury or other hazardous constituents change due to any future Clean Air Act air pollution control requirements for coal burning utilities (see section 2.C. of this document).

• We will continue EPA’s partnership with the states to finalize voluntary industrial solid waste management guidance that identifies baseline protective practices for industrial waste management units, including fossil fuel combustion waste management units.
We will use relevant information and knowledge that we obtain as a result of this effort to assist us in developing national regulations applicable to coal
combustion wastes.

2. What Is the Basis for EPA’s Regulatory Determination for Coal
Combustion Wastes?

A. What Is the Agency’s Decision Regarding the Regulatory Status of Coal Combustion Wastes and Why Did EPA
Make That Decision?

We have determined at this time that regulation of coal combustion wastes
under subtitle C is not warranted. However, we have also decided that it is appropriate to establish national regulations under non-hazardous waste
authorities for coal combustion wastes that are disposed in landfills and surface impoundments. We believe that subtitle D regulations are the most appropriate mechanism for ensuring that these wastes disposed in landfills and surface impoundments are managed safely.

EPA’s conclusion that some form of national regulation is warranted to
address these wastes is based on the following considerations: (a) The composition of these wastes could present danger to human health and the environment under certain conditions, and ‘‘potential’’ damage cases identified by EPA and commenters, while not definitively demonstrating damage from coal combustion wastes, may indicate that these wastes have the potential to pose such danger; (b) we have identified eleven documented cases of proven damages to human health and the environment by improper management
of these wastes in landfills and surface impoundments; (c) present disposal practices are such that, in 1995, these wastes were being managed in 40 percent to 70 percent of landfills and surface impoundments without reasonable controls in place, particularly in the area of groundwater monitoring; and (d) while there have been substantive improvements in state regulatory programs, we have also identified gaps in state oversight.

When we considered a tailored subtitle C approach, we estimated the potential costs of regulation of coal combustion wastes (including the utility
coal combustion wastes addressed in the 1993 Part 1 determination) to be $1 billion per year. While large in absolute terms, we estimate that these costs are less than 0.4 percent of industry sales. To improve our estimates we solicit public comment on the potential compliance costs to coal combustion waste generators as well as the indirectcosts to users of these combustion byproducts.

We have also decided that it is appropriate to establish national regulations under RCRA non-hazardous waste authorities (and/or possibly modifications to exiting regulations established under authority of SMCRA) applicable to the placement of coal
combustion wastes in surface or underground mines. We have reached this decision because (a) we find that
these wastes when minefilled could present a danger to human health and
the environment under certain circumstances, and (b) there are few states that currently operate comprehensive programs that specifically address the unique circumstances of minefilling, making it more likely that damage to human health or the environment could go
unnoticed.

With the exception of minefilling as described above, we have decided that national regulation under subtitle C or subtitle D is not warranted for any of the
other beneficial uses of coal combustion
wastes. We have reached this decision because: (a) We have not identified any other beneficial uses that are likely to present significant risks to human health or the environment; and (b) no documented cases of damage to human
health or the environment have been identified. Additionally, we do not want to place any unnecessary barriers on the
beneficial uses of coal combustion wastes so they can be used in applications that conserve natural resources and reduce disposal costs.

B. What Were EPA’s Tentative Decisions as Presented in the Report to Congress?

On March 31, 1999, EPA indicated a preliminary decision that disposal of
coal combustion wastes should remain exempt from regulation under RCRA subtitle C. We also presented our
tentative view that most beneficial uses of these wastes should remain exempt from regulation under RCRA subtitle C. However, in the RTC we identified three situations where we had particular concerns with the disposition or uses of
these wastes.

First, we indicated some concern with the co-management of mill rejects (‘‘pyrites’’) with coal combustion wastes which, under certain circumstances, could cause or contribute to ground
water contamination or other localized environmental damage. We indicated that the utility industry responded to our concern by implementing a voluntary education and technical guidance program for the proper management of these wastes. We expressed satisfaction with the industry program and tentatively concluded that additional regulation in this area was not necessary. We explained that we were committed to overseeing industry’s progress on properly managing pyritic wastes, and would revisit our regulatory
determination relative to comanagement of pyrites with large
volume coal combustion wastes at a later date, if industry progress was
insufficient in this area.

Second, in the RTC we identified potential human health risks from
arsenic when these wastes are used for agricultural purposes (e.g., as a lime substitute). To address this risk, we indicated our preliminary view that Subtitle C regulations may be appropriate for this management practice. We explained that an example
of such controls could include regulation of the content of these materials such that, when used for agricultural purposes, the arsenic level could be no higher than that found in agricultural lime. As an alternative to subtitle C regulation, we indicated that EPA could engage the industry to implement a voluntary program to address the risk, for example, by limiting the level of arsenic in coal combustion wastes when using them for agricultural purposes. Moreover, we
indicated that a decision to establish hazardous waste regulations applicable to agricultural uses of co-managed coal combustion wastes would likely affect the regulatory status of the Part 1 wastes (i.e., electric utility high volume coal combustion wastes managed separately from other coal combustion wastes) when used for agricultural purposes.
This is because the source of the
identified risk was the arsenic content of the high volume coal combustion wastes and not other materials that may be co-managed with them.

Third, we expressed concern with potential impacts from the expanding practice of minefilling coal combustion wastes (i.e., backfilling the wastes into mined areas) and described the


### 32222 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

difficulties we had with assessing the impacts and potential risks of this practice. We explained that these
difficulties include:

• Determining if elevated contaminants in ground water are due to minefill practices or pre-existing conditions resulting from mining operations,

• Trying to model situations that may be more complex than our groundwater models can accommodate,

• The lack of long-term experience with the recent practice of minefilling,
which limits the amount of environmental data for analysis, and

• The site-specific nature of these operations.

Accordingly, we did not present a
tentative decision in the RTC for this practice. We indicated that subtitle C regulation would remain an option for minefilling, but that we needed additional information prior to making a final decision. Rather, we solicited
additional information from commenters on these and other aspects of minefilling practices and indicated we would carefully consider that
information in the formulation of today’s decision.

C. How Did Commenters’ React to EPA’s
Tentative Decisions and What Was EPA’s Analysis of Their Comments?

Commenter’s provided substantial input and information on several aspects of our overall tentative decision to retain the exemption for these wastes from RCRA subtitle C regulation. These aspects are: modeling and risk assessment for the groundwater pathway, documented damage cases, the potential for coal combustion waste characteristics to change as a result of possible future Clean Air Act regulations, proper management of mill rejects (pyrites), agricultural use of coal combustion wastes, the practice of minefilling coal combustion wastes, and our assessment of existing State programs and industry waste management practices.

1. How Did Commenters React to the Groundwater Modeling and Risk Assessment Analyses Conducted by EPA To Support its Findings in the Report to Congress?

Comments. Industry and public interest group commenters submitted detailed critiques of the groundwater model, EPACMTP, that we used for our risk analysis. Industry commenters
believe that the model will overestimate the levels of contaminants that may migrate down-gradient from disposed wastes. Environmental groups expressed the opposite belief; that is, that the model underestimates down-gradient chemical concentrations and, therefore, underestimates the potential risk posed by coal combustion wastes.

The breadth and potential implications of the numerous technical
comments on the EPACMTP model are significant. Examples of the comments include issues relating to:

• The thermodynamic data that are the basis for certain model calculations,

• The model’s ability to account for
the effects of oxidation-reduction potential,

• The model’s ability to account for competition between multiple contaminants for adsorption sites,

• The model’s algorithm for selecting adsorption isotherms,

• The impact of leachate chemistry on adsorption and aquifer chemistry,
and

• The model’s inherent assumptions about the chemistry of the underlying aquifer.

EPA’s Analysis of the Comments. We have been carefully reviewing all of the
comments on the model. We determined that the process of thoroughly investigating all of the comments will take substantially more time to complete
than is available within the court deadline for issuing this regulatory determination. At this time, we are
uncertain of the overall outcome of our analysis of the issues raised in the comments. Accordingly, we have
decided not to use the results of our groundwater pathway risk analysis in support of today’s regulatory
determination on fossil fuel combustion wastes. As explained below, in making today’s regulatory determination, we have relied in part on other information related to the potential danger that may result from the management of fossil
fuel combustion wastes.

Meanwhile, we will continue with our analysis of comments on the groundwater model and risk analysis.This may involve changing or restructuring various aspects of the model, if appropriate. It may also include additional analyses to determine whether any changes to the model or modeling methodology would materially affect the groundwater risk analysis results that were reported in the RTC. If our investigations reveal that a re-analysis of groundwater risks is appropriate, we will conduct the analysis and re-evaluate today’sdecisions as warranted by the reanalysis.

In addition to our ongoing review of comments on the groundwater model,
one element of the model—the metals partitioning component called ‘‘MINTEQ’’—has been proposed for additional peer review. When additional peer review is completed, we will take the findings and recommendations intoaccount in any overall decision to reevaluate today’s regulatory
determination.

While not relying on the EPACMTP groundwater modeling as presented in the RTC, we have since conducted a general comparison of the metals levels
in leachate from coal combustion wastes to their corresponding hazardous waste toxicity characteristic levels. Fossil fuel wastes infrequently exceed the
hazardous waste characteristic. For comanaged wastes, 2% (1 of 51 samples)
exceeded the characteristic level. For individual wastes streams, 0% of the coal bottom ash, 2% of the coal fly ash, 3% of the coal flue gas desulfurization, and 7% of the coal boiler slag samples
that were tested exceeded the characteristic level. Nevertheless, once we have completed a review of our groundwater model and made any necessary changes, we will reevaluate groundwater risks and take appropriate regulatory actions. We will specifically assess new modeling results as they relate to any promulgated changes in the

arsenic MCL.

We also compared leach
concentrations from fossil fuel wastes to the drinking water MCLs. In the case of arsenic, we examined a range of values because EPA expects to promulgate a new arsenic drinking water regulation by January 1, 2001. This range includes the existing arsenic MCL (50 ug/l), a lower health based number presented in the FFC Report to Congress (RTC) (0.29 ug/l), and two assumed values in between (10 and 5 ug/l). We examined this range of values because of our desire to bracket the likely range of values that EPA will be considering in
its effort to revise the current MCL for
arsenic. The National Research Council’s 1999 report on Arsenic in Drinking Water indicated that the current MCL is not sufficiently protective and should be revised downward as soon as possible. For this reason, we selected the current MCL of 50 ug/L for the high end of the range because EPA is now considering lowering the current MCL and does not anticipate that the current MCL would be revised to any higher value. We
selected the health-based number presented in the Report to Congress for the low end of the range because we believe this represents the lowest
concentration that would be considered in revising the current MCL. Because at this time we cannot project a particular value as the eventual MCL, we also
examined values in between these lowend and high-end values, a value of 5


### 32223 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

2 The Part 1 determination identified six cases of documented damages. Upon further reveiw, we determined that two of these cases involve utility coal ash monofills which are covered by the Part 1 determination. However, the other four cases involved remaining wastes that are covered by today’s determination. ug/L and a value of 10 ug/L, for our analyses supporting today’s regulatory
determination. The choice of these midrange values for analyses does not predetermine the final MCL for arsenic.

Those circumstances where the leach
concentrations from the wastes exceed the drinking water criteria have the greatest potential to cause significant risks. This ‘‘potential’’ risk, however, may not occur at actual facilities.
Pollutants in the leachate of the wastes undergo dilution and attenuation as they migrate through the ground. The primary purpose of models such as EPACMTP is to account for the degree of dilution and attenuation that is likely to occur, and to obtain a realistic
estimate of the concentration of contaminants at a groundwater receptor. To provide a view of potential groundwater risk, we tabulated the
number of occurrences where the waste
leachate hazardous metals concentrations were: (a) Less than the criteria, (b) between 1 and 10 times the criteria, (c) between 10 and 100 times the criteria, and (d) greater than 100
times the criteria. Groundwater models that we currently use, when applied to large volume monofill sources of metals, frequently predict that dilution and
attenuation will reduce leachate levels
on the order of a factor of 10 under reasonable high end conditions. This multiple is commonly called a dilution and attenuation factor (DAF). For this
reason and because lower dilution and attenuation factors (e.g., 10) are often associated with larger disposal units such as those typical at facilities where coal is burned, we assessed the frequency of occurrence of leach
concentrations for various hazardous metals which were greater than 10 times the drinking water criteria. Based on current MCLs, there was only one exceedence (for cadmium). However,
when we considered the arsenic health based criterion from the RTC, we found that a significant percentage (86%) of available waste samples had leach
concentrations for arsenic that were greater than ten times the health-based criterion. Even considering intermediate values closer to the current MCL, a significant percentage of available waste samples had leach concentrations for arsenic that were greater than ten times the criteria (30% when the criterion was assumed to be 5 ug/l, and 14% when the criterion was assumed to be 10 ug/l).
Similar concerns also occurred when comparing actual groundwater samples
associated with FFC waste units and this range of criteria for arsenic. We believe this is an indication of potential
risks from arsenic. For the above analysis, we used a value equal to half the detection level to
deal with those situations where analyses resulted in ‘‘less than
detection’’ values that exceeded the
MCL criteria. The actual concentration may be as low as zero or up to the detection level. To illustrate the impact of this assumption, an analysis was performed setting the ‘‘less than detection’’ values to zero, and an arsenic criteria at 50 ug/l. While 30% of the
values exceeded 10 times the criteria when using half the detection level, exceedences dropped to 13% when
‘‘less than detection’’ values were set to

zero.

The comparison of the leachate levels to 10 times MCL criteria is a screening level analysis that supports our concerns, which are primarily based on damage cases and the lack of installed controls (liners and groundwater monitoring). We recognize, however, that prior to issuing a regulation the Agency expects to address the issues raised on the groundwater model and complete a comprehensive groundwater modeling effort. Furthermore, we anticipate that uncertainty regarding
whether the arsenic MCL will be amended and to what level, will be more settled prior to regulation of these wastes. These factors could heighten or reduce concerns with regard to the need for Federal regulation of fossil fuel
combustion wastes.

2. How Did Commenters React to EPA’s Assessment of Documented Damage Cases Presented in the Report to Congress?

Prior to issuing the RTC, we sought and reviewed potential damage cases related to these particular wastes. The
activities included:

• A re-analysis of the potential damage cases identified during the Part 1 determination,

• A search of the CERCLA Information System for instances of these wastes being cited as causes or contributors to damages,

• Contacts and visits to regulatory agencies in five states with high rates of coal consumption to review file
materials and discuss with state officials the existence of damage cases,

• A review of information provided by the Utility Solid Waste Act Group
and the Electric Power Research Institute on 14 co-management sites,
and

• A review of information provided by the Council of Industrial Boiler Owners on eight fluidized bed combustion (FBC) facilities.

These activities yielded three damage
case sites in addition to the four cases initially identified in the Part 1
determination. 2 Five of the damage cases involved surface impoundments
and the two other cases involved landfills. The waste management units in these cases were all older, unlined
units. The releases in these cases were confined to the vicinity of the facilities and did not affect human receptors. None of the damages impacted human health. We did not identify any damage
cases that were associated with beneficial use practices.

Comments. Public interest group commenters criticized our approach to identifying damage cases associated with the management of fossil fuel combustion (FFC) wastes, stating that EPA did not use the same procedure used to identify damage cases for the cement kiln dust (CKD) Report to Congress. These commenters believed
that we were too conservative in our interpretation and determination of FFC damage cases and dismissed cases that
commenters believe are relevant instances of damage. For example, these commenters indicated that EPA, in the RTC, did not consider cases where the only exceedences of ground water standards were for secondary MCLs (Maximum Contaminant Levels as established by EPA for drinking water standards). They further indicated that the states often require ground water monitoring only for secondary MCL
constituents and that elevated levels of the secondary MCL constituents are an indication of future potential for more serious, health-based standards to be
exceeded for other constituents in the wastes, such as toxic metals. Additionally, these commenters stated that the Agency’s analysis for damage cases was incomplete and they provided information on 59 possible damage cases involving these wastes, mostly at utilities. Additionally, commenters submitted seven cases of ecological damage that allege damage to mammals, amphibians, fish, benthic layerorganisms and plants from comanagement of coal combustion wastes in surface impoundments.

Industry commenters cited EPA’s finding of so few damage cases as important support for our tentative conclusion to exempt these wastes from hazardous waste regulation. Further, some of the industry commenters indicated that the few damage cases that EPA identified do not represent current


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utility industry management practices, but rather reflect less environmentally protective management practices at older facilities that pre-date the
numerous state and federal requirements that are now in effect for managing these wastes.

EPA’s Analysis of the Comments

. Regarding ecological damage, while we did not identify any ecological damage
cases in the RTC associated with management of coal combustion wastes,
we reviewed the information on ecological damage submitted by commenters and agree that four of the
seven submitted are documented damage cases that involve FFC wastes.
All of these involve some form of discharge from waste management units to nearby lakes or creeks. These confirm our risk modeling conclusions as presented in the RTC that there could be adverse impacts on amphibians, birds, or mammals if they were subject to the
elevated concentrations of selected
chemicals that had been measured in some impoundments. However, no
information was submitted in comments
that would lead us to alter our
conclusion that these threats are not substantial enough to cause large scale, system level ecological disruptions. These damage cases, attributable to runoff or overflow that is already subject to Clean Water Act discharge or stormwater regulations, are more appropriately addressed under the existing Clean Water Act requirements.

Regarding our assessment of damage to ground water, we believe our approach to FFC damage cases in the RTC was consistent with the approach we used for identifying CKD damage cases. For CKD, we established two categories of damage cases—‘‘proven’’ damage cases and ‘‘potential’’ damage cases. Proven damage cases were those
with documented MCL exceedences that were measured in ground water at a
sufficient distance from the waste management unit to indicate that hazardous constituents had migrated to the extent that they could cause human health concerns. Potential damage cases
were those with documented MCL
exceedences that were measured in ground water beneath or close to the waste source. In these cases, the
documented exceedences had not been
demonstrated at a sufficient distance from the waste management unit to
indicate that waste constituents had migrated to the extent that they could
cause human health concerns. We do not believe that it would be appropriate to consider an exceedence directly beneath a waste management unit or very close to the waste boundary to be a documented, proven damage case. State regulations typically use a compliance procedure that relies on measurement at a receptor site or in ground water at a point beyond the waste boundary (e.g., 150 meters). While our CKD analysis did not distinguish between primary and secondary MCL exceedences, most CKD damage cases involved a primary MCL constituent. Our principal basis for determining that CKD when managed in land-based units would no longer remain exempt from being regulated as a hazardous waste was our concern about generally poor management practices characteristic of that industry. Our conclusion was further supported by the extremely high percentage of proven damage cases occurring at active CKD sites for which groundwater monitoring data were
available.

For FFC, we used the same test of proof to identify possible damage cases. Our FFC analysis drew a distinction between primary and secondary MCL
exceedences because we believe this factor is appropriate in weighing the seriousness of FFC damage in terms of indicating risk to human health and the environment. For FFC, in the RTC, we reported only the ‘‘proven’’ damage (i.e.,
exceedence of a health-based standard such as a primary MCL and measurement in ground water or surface water). As was done in the CKD analysis, we also identified a number of potential FFC damage cases (eleven) which were included in the background documents that support the RTC.

Unlike the primary MCLs, secondary
MCLs are not based on human health considerations. (Examples are dissolved solids, sulfate, iron, and chloride for which groundwater standards have been
established because of their effect on taste, odor, and color.) While some
commenters believe that elevated levels of some secondary MCL parameters such as soluble salts are likely precursors or indicators of future
hazardous constituent exceedences that
could occur at coal combustion facilities, we are not yet able and will not be able to test their hypothesis until we complete our analysis of all comments received on our groundwater model and risk analysis, which will not be concluded until next year.

Of the 59 damage cases reported by commenters, 11 cases appear to involve exceedences of primary MCLs or other
health-based standards as measured either in off-site ground water or in nearby surface waters, the criteria we used in the RTC to identify proven damage cases. Of these eleven cases,
two are coal ash monofills which were included in the set of damage cases described by EPA in its record supporting the Part 1 regulatory determination. The remaining nine cases involve the co-management of large volume coal combustion wastes with other low volume and uniquely
associated coal combustion wastes. We had already identified five of these nine cases in the RTC. Thus, only four of these eleven damage cases are newly identified to us. Briefly, the four new
cases involve:

• Exceedence of a state standard for lead in downgradient ground water at a coal fly ash landfill in New York. There were also secondary MCL exceedences for sulfate, dissolved solids, and iron.

• Primary MCL exceedences for arsenic and selenium in downgradient monitoring wells for a coal ash impoundment at a power plant in North Dakota. There were also secondary MCL
exceedences for sulfate and chloride.

• Primary MCL exceedences for
fluoride and exceedence of a state standard for boron in downgradient monitoring wells at a utility coal combustion waste impoundment in Wisconsin. There was also a secondary
MCL exceedence for sulfate.

• Exceedence of a state standard for boron and the secondary MCL for sulfate and manganese in downgradient monitoring wells at a utility coal
combustion landfill in Wisconsin.

We found that in nine of the 11 proven damage cases (including one Superfund site), states took appropriate action to require or conduct remedial
activities to reduce or eliminate the
cause of contamination. EPA took action in the remaining two cases under the Superfund program

Nineteen of the candidate damage cases submitted by commenters involve
either on-site or off-site exceedences of secondary MCLs, but not primary MCLs
or other health-based standards. Consistent with our CKD analysis, we
consider these cases to be indicative of a potential for damage to occur at these sites because they demonstrate that there has been a release to ground water from the waste management unit.

Regarding the remaining 29 cases submitted by commenters:

• Six involve primary MCL exceedences, but measurements were in ground water either directly beneath the waste or very close to the waste boundary, i.e. , no off-site ground water or receptor measurements indicated that ground water standards had been exceeded. Consistent with our analysis of damage cases for cement kiln dust,
we consider these six cases to be indicative of a potential for damage to occur at these sites because they
demonstrate that there has been a


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release to ground water from the waste management unit..

• Eighteen case summary
submissions contained insufficient documentation and data for us to verify
and draw a conclusion about whether we should consider these to be potential or proven damage cases. Of these 18 cases, commenters claimed that 11 cases involve primary MCL exceedences, and another two involve secondary MCLs, but not primary MCLs. The other five
cases lacked sufficient information and
documentation to determine whether primary or secondary MCLs are involved. Examples of information critical to assessing and verifying candidate damage cases that was not available for these particular cases include: Identification of the pollutants causing the contamination;
identification of where or how the damage case information was obtained ( e.g. , facility monitoring data, state monitoring or investigation, third party study or analysis); monitoring data used to identify levels of contaminants; and/
or sufficient information to determine whether the damages were actually
attributable to fossil fuel combustion wastes; and/or location of the identified contamination (i.e. , directly beneath the unit or very close to the waste boundary or at a point some distant (e.g. , 150 meters) from the unit boundary).

• Three case submissions are cases
we identified in the Part 1
determination and involve monofilled utility coal ash wastes. However, as explained in the Report to Congress for the Part 1 determination, EPA
determined that there was insufficient
evidence to consider them to be documented damage cases.

• One case did not involve fossil fuel
combustion wastes.

• One case involved coal combustion
wastes and other unrelated wastes in an illegal, unpermitted dump site. This site was handled by the state as a hazardous waste cleanup site.

Our detailed analysis of the damage cases submitted by commenters is available in the public docket for this regulatory determination.

In summary, based on damage case information presented in the RTC and our review of comments, we conclude that there are 11 proven damage cases associated with wastes covered by today’s regulatory determination. We identified seven of these damage cases in the RTC, so there are four new proven damage cases that were identified by
commenters. All of the sites were at older, unlined units, with disposal occurring prior to 1993. For all 11 of the proven damage cases, either the state or EPA provided adequate follow-up to require or else undertake corrective action. Although these damage cases
indicate that coal combustion wastes can present risks to human health and the environment, they also show the effectiveness of states’ responses when damages were identified. None of these cases involved actual human exposure.

Additionally, we determined that
another 25 of the commenter submitted cases are potential damage cases for the reasons described above. Thus, including the 11 potential damage cases that we identified in the background documents that support the RTC, we are aware of 36 potential damage cases.
While we do not believe the latter 36 cases satisfy the statutory criteria of documented, proven damage cases because damage to human health or the environment has not been proven, we believe that these cases may indicate that these wastes pose a ‘‘potential’’ danger to human health and the

environment in some circumstances.

In conclusion, while the absolute number of documented, proven damage cases is not large, we believe that the evidence of proven and potential damage should be considered in light of the proportion of new and existing facilities, particularly surface impoundments, that today lack basic
environmental controls such as liners and groundwater monitoring. Approximately one-third of coal combustion wastes are managed in surface impoundments. We note that controls such as liners may not bewarranted at some facilities, due to sitespecific conditions. We acknowledge, however, that our inquiry into the existence of damage cases was focused primarily on a subset of states. Given
the volume of coal combustion wastes generated nationwide and the number of facilities that lacked groundwater monitoring as of 1995, there is at least
a substantial likelihood other cases of actual and potential damage likely exist.
Because we did not use a statistical sampling methodology to evaluate the potential for damage, we are unable to
determine whether the identified cases are representative of the conditions at all facilities and, therefore, cannot quantify the extent and magnitude of damages at the national level.

3. What Concerns Did Commenters Express About the Impact of Potential Future Regulation of Hazardous Air
Pollutants Under the Clean Air Act on Today’s Regulatory Determination?

Comments. In both public hearing testimony and written comments, public interest groups expressed concern about potential changes in the characteristics of these wastes when new air pollution controls are established under the Clean
Air Act. The commenters referred to the possible future requirement for hazardous air pollutant controls at coal burning electric utility power plants,
which could result in an increased level of metals and possibly other hazardous
constituents in coal combustion wastes.
The commenters indicated that these increased levels, in turn, could have serious implications for cross-media environmental impacts such as leaching to groundwater and volatilization to the air. The commenters argued that the Agency should include these factors in its current decision making on the regulatory status of coal combustion
under the Resource Conservation and Recovery Act.

EPA’s Analysis of the Comments. We have carefully considered the issue of cross-media impacts and the commenters’ specific concerns that future air regulations could have an adverse impact on the characteristics of
coal combustion wastes. We have concluded that it is premature to consider the possible future impact of such new air pollution controls on the wastes that are subject to today’s regulatory determination. The Agency plans to issue a regulatory determination in the latter part of 2000 regarding hazardous air pollutant (HAP) controls at coal-burning, power generating facilities. If EPA decides to initiate a rulemaking process, final rulemaking under the Clean Air Act is projected to occur in 2004. Thus, no final decision has been made on what, if any, constituents will be regulated by future air pollution control requirements. Additionally, the regulatory levels of the those specific pollutants that might be controlled and the control technologies needed to attain any regulatory requirements have not yet been identified. Therefore, we
believe there is insufficient information at this time for evaluating the characteristics and potential environmental impacts of solid wastes that would be generated as a result of new Clean Air Act requirements.

When any rulemaking under the Clean Air Act proceeds to a point where we can complete an assessment of the likely changes to the character of coal combustion wastes, we will evaluate the implications of these changes relative to today’s regulatory determination and take appropriate action.

4. How Did Commenters React to the Findings Presented in the Report to Congress Related to Proper Management of Mill Rejects (Pyrites)?

The RTC explained that we identified situations where pyrite-bearing


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materials such as mill rejects (a low volume and uniquely associated waste) that are co-managed with coal combustion wastes may cause or

contribute to risks or environmental damage if not managed properly. These materials when managed improperly with exposure to air and water can generate acid. The acid, in turn, can

mobilize metals contained in the comanaged combustion wastes. The RTC also explained that the Agency engaged the utility industry in a voluntary program to ensure appropriate management of these wastes. The industry responded by developing technical guidance and a voluntary industry education program on proper management of these wastes.

Comments. Utility industry commenters supported our tentative decision to continue the exemption for coal combustion wastes co-managed with mill rejects from regulation as a hazardous waste. Their position is based primarily on the industry’s voluntary implementation of an education program and technical guidance on the proper management of these wastes, as

described in the RTC.

Public interest groups and other commenters disagreed with our tentative decision, explaining their belief that such voluntary controls or programs are inadequate. They

indicated that coal combustion wastes should be subject to hazardous waste regulations.

EPA’s Analysis of the Comments. We remain encouraged by the utility industry program to educate and inform its members by implementing guidance on the proper management of coal mill rejects. However, as pointed out by commenters, there is no assurance that

facilities where coal combustion wastes co-managed with pyritic wastes will follow the guidance developed by industry. In light of the number of demonstrated and potential damage cases identified to date, we are concerned that simply relying on voluntary institution of necessary controls would not adequately ensure the protection of human health and the environment. At this time, to ensure

that we are aware of all stakeholders views on the adequacy of the control approaches described in the guidance to protect human health and the environment, we are soliciting public

comment on the final version of the industry coal mill rejects guidance. This guidance is available in the docket supporting today’s decisions. 5. How Did Commenters React to the Findings Presented in the Report to Congress Related to Agricultural Use of
Coal Combustion Wastes?

In the RTC, we presented findings on
the human health risks associated with agricultural use of coal wastes as an agricultural lime substitute. The pathway examined embodies risks from ingestion of soil and inhalation, and from ingestion of contaminated dairy, beef, fruit and vegetable products. The resultant ‘‘high end’’ cancer risk reported in the RTC was 1 × 10

¥ 5 (one in one hundred thousand exposed population), for the child of a farmer. The variables held at high end for this
calculation were contaminant
concentration and children’s soil ingestion. With all variables set to central tendency values, the risk was
calculated to be 1 × 10

¥ 7 (one in ten million exposed population). We didnot identify the presence of any noncancer hazard of concern. Based on the high end risk, the Agency raised the possibility in the RTC of developing Subtitle C controls or seeking commitments from industry to a voluntary program.

Comments. A number of industry, academic, and federal agency commenters disagreed with our
tentative conclusion that some level of regulation may be appropriate for coal
combustion wastes when used as an agricultural soil supplement. They indicated that EPA used unrealistically conservative levels for four key inputs used in our risk analysis and that use of a realistic level for any one of these inputs would result in a risk level less
than 1 × 10

¥ 6. The four inputs identified by the commenters are: application rate of the wastes to the land, the rate of soil ingestion by children, the bioavailability of arsenic and the phytoavailability of arsenic.

These commenters further recommended that EPA not regulate, but rather encourage voluntary restrictions
because:

• Agricultural use of coal combustion
wastes creates no adverse environmental impacts and EPA identified no damage cases associated with this practice;

• Agricultural use of these wastes has significant technical and economic benefits;

• Federal controls would be unnecessarily costly and would create a barrier for research and development on the practice;

• Existing regulatory programs are sufficient to control any risks from this practice; and

• The limits suggested in the RTC for
arsenic levels in coal combustion wastes are inconsistent with limits applied to other materials used in agriculture.

Public interest groups stated their belief that a voluntary approach would not be sufficiently protective of human health and the environment. They believe the Agency should apply
restrictions on the use of these wastes in agriculture because the Agency’s analyses of the risks and benefits of this practice were inadequate. They further recommended that EPA should prohibit the land application of coal combustion wastes generated by conventional boilers, and make the arsenic limitation of EPA’s sewage sludge land application regulations applicable to the land application of coal combustion wastes generated by fluidized bed combustors, which add lime as part of the combustion process.

EPA’s Analysis of Comments. After reviewing these comments and supporting information provided by the commenters, we concluded that a revised input into the model for children’s soil ingestion rate is appropriate. Based on further review of the Agency’s Exposure Factors Handbook (EFH), we decided to model a children’s soil ingestion rate of 0.4 grams per day instead of the 1.4 grams per day that underlay the results given
in the RTC.

Many studies have been conducted to estimate soil ingestion by children. Early studies focused on dirt present on children’s hands. More recently, studies have focused on measuring trace
elements in soil and then in feces as a function of internal absorption. These
measurements are used to estimate amounts of soil ingested over a specified time period. The EFH findings for children’s soil ingestion are based on seven key studies and nine other relevant studies that the Agency reviewed on this subject. These studies
showed that mean values for soil ingestion ranged from 39 mg/day to 271 mg/day with an average of 146 mg/day.
These results are characterized for studies that were for short periods with little information reported for pica behavior. To account for longer periods of time, the EFH reviewed the upper percentile ranges of the data studied and found ingestion rates that ranged from 106 mg/day to 1,432 mg/day with an average of 383 mg/day for soil ingestion. Rounding to one significant figure, the EFH recommended an upper percentile children’s soil ingestion rate of 400 mg/ day. The Agency believes that this
recommendation is the best available
information to address children’s exposure through the soil ingestion route. Reducing the ingestion rate to the
EFH handbook recommended level of


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400 mg/day reduced the calculated risk

to 3.4 × 10–6 for this one child risk situation and suggests that agricultural
use of FFC wastes does not cause a risk
of concern.

EPA believes its inputs for phytoavailability are accurate, although there are studies that suggest phytoavailability will decrease over time. Arsenic bioavailability is a
function of all sources of arsenic and
EPA believes it has characterized this accurately. However, as noted elsewhere, arsenic toxicity is now being studied by the Agency in conjunction with a proposed new arsenic MCL and may necessitate re-visiting today’s judgement on agricultural use.

Our technical analysis that resulted in revised risk is explained in a document titled Reevaluation of Non-groundwater Pathway Risks from Agricultural Use of Coal Combustion Wastes, which is
available in the docket for this action.

The comment on inappropriateness of application frequency was caused by a misunderstanding of the language in the RTC. The rate used was actually every two or three years, not two or three times per year.

Two ongoing studies of wastes of potential use as agricultural soil supplements relate to the use of FFC wastes for this purpose. Although these did not play a direct role in EPA’s decision regarding FFC wastes, they are summarized below and may play a role in any future review of today’s decision.

(1) On August 20, 1999, the agency proposed risk-based standards for cement kiln dust when used as a liming agent (see 64 FR 45632; August 20, 1999). This analysis was completed in 1998 just prior to our completion of the analysis of FFC wastes when used as agricultural supplements. The CKD analysis underwent a special peer review by a standing committee that is used by the Department of Agriculture. We were not able to respond to the peer
review comments in either the CKD proposal or in our assessment for fossil fuel combustion wastes prior to publication of today’s regulatory determination. The comment period for the CKD proposal closed on February 17, 2000, and we will soon begin our review and analyses of the public and peer review comments.

(2) In December 1999, EPA proposed
new risk based standards for the use of municipal sewage sludge under section 503 of the Clean Water Act (the ‘‘503 standards’’). It is important to note that municipal sludge has unique properties, application rates, and uses. This makes it inappropriate to transfer the 503 standards directly. Even though the standards cannot be used directly, there may be interest in the risk assessment methodologies used to support the development of these standards. We disagree that it is appropriate to
establish an arsenic limitation for coal
combustion ash when used for agricultural purposes equivalent to that contained in the EPA sewage sludge land application regulations. The organic nature of sewage sludge makes it behave very differently from inorganic
wastes such as coal combustion wastes.

We conclude at this time that arsenic
levels in coal combustion wastes do not pose a significant risk to human health when used for agricultural purposes. We expect to continue to review and refine
the related risk assessments noted above, and will consider comments on the Agency’s CKD and municipal sludge proposals, as well as new scientific developments related to this issue such as additional peer review of the EPA MINTEQ model that was used as a component of our risk analysis. If these
efforts lead us to a different understanding of the risks posed by coal
combustion wastes when used as a substitute for agricultural lime, we will take appropriate action to reevaluate today’s regulatory determination.

6. How Did Commenters React to the Findings Presented in the Report to Congress Related to Minefilling of Coal
Combustion Wastes?

In the RTC, we explained that we had insufficient information to adequately
assess the risks associated with the use
of coal combustion wastes to fill surface and underground mines, whether the
mines are active or abandoned. Accordingly, we did not present a
tentative conclusion in the RTC with respect to the use of coal combustion wastes for disposal in active mines or for reclamation of mines. However, we did indicate that regulation of minefilling under hazardous waste rulemaking authority would remain an option for minefilling, but that we needed additional information prior to making a final decision. Thus, we
solicited additional information on specific minefilling techniques, problems that may be inherent in this management practice, risks posed by this practice, existing state regulatory requirements, and environmental monitoring data. We indicated that we would consider any comments and new information on minefilling received in
comments and would address this management practice in today’s regulatory determination.

Comments. A number of commenters responded to our request by providing reports on individual case studies, including minefilling in underground as well as in surface mines, descriptions of current state regulatory requirements that address this practice, monitoring data, and information about risk analysis techniques.

Industry commenters and one federal agency supported our decision to study the issue further and not attempt to estimate the risks posed by this practice using existing methods. Further, numerous industry, academic, state agency, and federal agency commenters encouraged EPA not to adopt national regulations or voluntary restrictions on minefilling because: (a) Nationwide
standards would not be conducive to the site-specific evaluations needed to appropriately control these operations; (b) minefilling creates no adverse environmental impacts and EPA identified no damage cases associated with this practice; (c) existing state and federal regulatory programs and industry practices are sufficient to control any risks from this practice, and (d) federal standards would be an
unreasonable interference with states’
authorities.

Additionally, several industry representatives, legislators, and state mining and environmental agencies mentioned that this practice, when used to remediate abandoned mine lands, will produce considerably greater
environmental benefits than risks. Further, they maintained that minefilling is a relatively inexpensive means to stop or even reverse the environmental damage caused by old mining practices. They indicated that through remediation by minefilling, these lands frequently can be returned to productive use. These commenters recommended no additional regulation of this practice.

Public interest groups and others believe we should regulate minefilling under RCRA subtitle C or prohibit it for several reasons including weaknesses in existing state and federal regulatory programs, the poor practices and performance at existing minefilling operations, and potential impacts on potable water sources. Commenters stated that state programs effectively allow open dumps without any design
or construction standards. For minefilling, one commenter urged EPA to defer to state regulations only if the Agency specifically found existing state regulations to be adequate.

EPA’s Analysis of Comments. We agree with commenters that it is inappropriate to estimate the risks posed by minefilling using the existing methods that we employed to conduct risk analyses for disposal of coal
combustion wastes in landfills and impoundments. We found that the


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groundwater models available to us are unsuitable for estimating risks from minefills because, for example, they are
not able to account for conditions such as fractured flow that are typical of the hydrogeology associated with mining operations. In addition, as explained above, EPA’s primary groundwater model, EPACMTP, is now undergoing
careful review on the basis of comments received on the Report to Congress.

We are aware that the use of coal
combustion wastes to conduct remediation of mine lands can improve conditions caused by mining activities. We also recognize that this often is the lowest cost option for conducting these remediation activities. We generally encourage the practice of remediating
mine lands with coal combustion wastes when minefilling is conducted properly and when there is adequate oversight of
the remediation activities. We are also aware that relatively few states currently operate regulatory or other programs that specifically address minefilling, and that many states where this practice is occurring do not have programs in place. Based on our review of information on existing state minefill programs, we find serious gaps such as a lack of adequate controls and restrictions on unsound practices, e.g.
, no requirement for groundwater monitoring and no control or prohibitions on waste placement in the aquifer.

At this time, we cannot reach
definitive conclusions about the adequacy of minefilling practices employed currently in the United States and the ability of government oversight agencies to ensure that human health and the environment are being adequately protected. For example, it is often impossible to determine if existing groundwater quality has been impacted by previous mining operations or as a
result of releases of hazardous
constituents from the coal combustion wastes used in the minefilling applications. Additionally, data and information submitted during the public comment period indicate that if the chemistry of the mine relative to the chemistry of the coal combustion wastes is not properly taken into account, the
addition of coal combustion wastes to certain environmental settings can lead
to an increase in hazardous metals
released into the environment. This phenomena has been substantiated by data available to the Agency that show when pyrites, which can cause acidgeneration, have been improperly comanaged with coal combustion wastes, high levels of metals, especially arsenic,
have leached from the wastes. Finally, we concluded in our recent study of disposal of cement kiln dust that placement of cement kiln dust directly in contact with ground water led to a substantially greater release of
hazardous metal constituents than we predicted would occur when such placement in ground water did not
occur. We are aware of situations where coal combustion wastes are being placed in direct contact with ground water in both underground and surface mines.
This could lead to increased releases of
hazardous metal constituents as a result of minefilling. Thus, if the complexities related to site-specific geology, hydrology, and waste chemistry are not properly taken into account when minefilling coal combustion wastes, we believe that certain minefilling practices have the potential to degrade, rather than improve, existing groundwater quality and can pose a potential danger
to human health and the environment. Subsequent impacts on human health would depend in part on the proximity of drinking water wells, if any, to
elevated levels of metals in the water. To date we are unaware of any proven damage cases resulting from minefilling operations.

7. How Did Commenters React to EPA’s Tentative Reliance on State Programs and Voluntary Industry Implementation of Improved Management Practices To Mitigate Potential Risks From Coal Combustion Waste Management?

In the RTC, EPA considered retaining the exemption for coal combustion wastes disposed in surface impoundments and landfills and for mill rejects (pyrites) that are managed with those wastes. The Agency cited a reliance on state programs that have improved substantially over the past 10 to 15 years and continue to improve, combined with voluntary industry implementation of guidance for improved management practices to mitigate risk. In addition, we stated that
we would continue to work with industries and states to promote and monitor improvements.

To assess the adequacy of state programs and the potential for voluntary implementation of improved practices,
we looked at the current number of facilities with liners and groundwater monitoring (which may reflect voluntary industry upgrading as well as state requirements), and the number of state programs that currently have authority to require a broad range of
environmental controls. For units operating as of 1995, we found that among utilities, slightly more than half of the disposal units were surface impoundments. Of these impoundments, 38 percent had groundwater monitoring and 26 percent had liners. Eighty-five percent of the utility landfills had groundwater monitoring and 57 percent had liners. For non-utility landfills, 94 percent had groundwater monitoring, and between 16 percent and 52 percent had liners. Between 1985 and 1995, 75 percent of new landfills and 60 percent of new surface impoundments within the utility sector had been lined. We have no information regarding the percentage of units built since 1995 (the date when the study we have relied on ended) that have liners or groundwater monitoring

programs.

In looking at state programs, we found that for landfills, more than 40 states have the authority to require permits, siting restrictions, liners, leachate collection, groundwater monitoring, closure controls, and cover/dust controls. Forty-three states can require liners and 46 can require groundwater monitoring compared to 11 and 28 states, respectively, in the 1980’s. For surface impoundments, more than 40 states have authority to require permits, siting restrictions, liners, groundwater monitoring, and closure control; 33 can require leachate collection (there is no earlier comparison data for surface impoundments). Forty-five states can require liners and 44 can require groundwater monitoring for impoundments.

Comments. Industry and state agency commenters generally stated that the Agency presented an accurate and comprehensive analysis of state programs and that existing state regulations are adequate. Public interest commenters raised many concerns about the adequacy of state programs: Either they do not have provisions to cover all elements of a protective program; they do not consistently impose the requirements for which they have authority; and/or enforcement is
lax. Evidence commenters cited for the inadequacy of state programs included grandfathering for older management units and an apparent lack of controls for surface impoundments. For these reasons, some found EPA’s review of state programs inaccurate or incomplete.

Public interest commenters were also skeptical of programs or efforts that rely on voluntary industry implementation because adherence to guidance is not guaranteed. Several commenters, primarily from industry, urged theAgency not to regulate pyrite comanagement because of the voluntary, industry-developed guidance.

EPA’s Analysis of Comments. We believe that state programs have, in fact, substantially improved over the last 15


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years or so. A high percentage of states have authority to impose protective management standards on surface impoundments and landfills, especially for groundwater monitoring, liners, and leachate collection, which mitigate potential risks posed by these units. Over 40 states today have these authorities (33 states have authority to require leachate collection in surface impoundments). When authority under state groundwater and drinking water regulations are considered, some commenters have suggested that nearly all states can address the management of these wastes. In addition, we believe
that the trend to line and install groundwater monitoring for new surface impoundments and landfills is positive. However, as some commenters noted, we acknowledge that our state program
review looked at the authorities
available to states and their overall regulatory requirements, not the specific requirements applied to given facilities, which could be more or less stringent. In addition, we recognize that individual state programs may have some gaps in coverage, as indicated below, so that some controls may not now be required at coal combustion waste impoundments and landfills. We would expect to see some differences in the application of requirements, depending on site-specific conditions.

One consistent trend that raises concern for the Agency is that controls
are much less common at surface impoundment than at landfills. Even for newer units at utilities (constructed between 1985 and 1995), liners are used at 75 percent of landfills and only 60 percent of surface impoundments. Also at newer units, groundwater monitoring is implemented at 88 percent of landfills and at only 65 percent of surfaceimpoundments. Approximately onethird of coal combustion wastes were managed in surface impoundments in 1995. Hydraulic pressure in a surface impoundment increases the likelihood of releases. We believe that groundwater monitoring, at a minimum, in existing as well as new impoundments, is a reasonable approach to monitor performance of the unit and a critical first step to addressing groundwater damage that may be caused by the unit. As of 1995, 38 percent of currently operating utility surface impoundments had groundwater monitoring and only 26 percent had liners.

While liners and groundwater monitoring are applied more frequently at landfills, there are still many utility and non-utility landfills that do not have liners. In addition, 15 percent of utility landfills do not have groundwater monitoring, and some six percent of non-utility landfills do not have groundwater monitoring, based on a limited survey.

The utility industry through its trade
associations has demonstrated a willingness to work with EPA to develop protective management practices, and individual companies have committed to upgrading their own practices. However, the Agency recognizes that participation in voluntary programs is not assured. Also, individual facilities and companies may not implement protective management practices and controls, for a variety of reasons, in spite of their endorsement by industry-wide groups.

We see a trend toward significantly improving state programs and voluntary industry investment in liners and groundwater monitoring that we believe can mitigate potential risks over time. However, we identified significant gaps in controls already in place and, in particular, requirements that may be lacking in some states, either in authority to impose the requirements or potentially in exercising that authority. In response to comments, we further analyzed risks posed by coal combustion wastes taking into account waste characteristics and potential and actual damage cases. Based on these analyses, we concluded that coal combustion wastes, in certain circumstances, could unnecessarily
increase risks to human health and the environment, and that a number of proven damages have been documented, and that more are likely if we had been able to conduct a more thorough search
of available state records and if groundwater monitoring data were available for all units. We recognize there will probably continue to be some gaps in practices and controls and are concerned at the possibility that these will go unaddressed. We also believe the time frame for improvement of current practices is likely to be longer in the absence of federal regulations.

D. What Is the Basis for Today’s

Decisions?

Based on our collection and analysis of information reflecting the criteria in section 8002(n) of RCRA that EPA must consider in making today’s regulatory determination, materials developed in preparing the RTC and supportive background materials, existing state and federal regulations and programs that affect the management of coal combustion wastes, and comments received from the public on the findings we presented in the RTC, we have concluded the following: 1. Beneficial Uses

To the extent coal combustion wastes are used for beneficial purposes, we believe they should continue to remain exempt from being regulated as
hazardous wastes under RCRA. Beneficial purposes include waste stabilization, beneficial construction applications ( e.g., cement, concrete, brick and concrete products, road bed, structural fill, blasting grit, wall board, insulation, roofing materials), agricultural applications (e.g., as a substitute for lime) and other applications (absorbents, filter media, paints, plastics and metals manufacture, snow and ice control, waste stabilization). For the reasons presented in section 3 below, we are separately addressing the use of coal combustion wastes to fill surface or underground

mines.

For beneficial uses other than minefilling, we have reached this decision because: (a) We have not identified any beneficial uses that are likely to present significant risks to human health or the environment; and (b) no documented cases of damage to
human health or the environment have been identified. Additionally, we do not want to place any unnecessary barriers
on the beneficial use of coal combustion wastes so that they can be used in applications that conserve natural resources and reduce disposal costs.

Disposal can be burdensome and fails to take advantage of beneficial
characteristics of fossil fuel combustion wastes. About one-quarter of the coal combustion wastes now generated are diverted to beneficial uses. Currently, the major beneficial uses of coal
combustion wastes include: Construction (including building products, road base and sub-base, blasting grit and roofing materials) accounting for approximately 21%; sludge and waste stabilization and acid neutralization accounting for approximately 3%; and agricultural use accounting for 0.1%. Based on our
conclusion that these beneficial uses of coal combustion wastes are not likely to pose significant risks to human health and the environment, we support
increases in these beneficial uses of coal
combustion wastes.

Off-site uses in construction, including wallboard, present low risk due to the coal combustion wastes being bound or encapsulated in the
construction materials or because there is low potential for exposure. Use in waste and sludge stabilization and in acid neutralization are either regulated (under RCRA for hazardous waste stabilization or when placed in


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municipal solid waste landfills, or
under the Clean Water Act in the case of municipal sewage sludge or wastewater neutralization), or appear to present low risk due to low exposure potential. While in the RTC, we expressed concern over risks presented by agricultural use, we now believe our previous analysis assumed unrealistically high-end conditions, and that the risk, which we now believe to
be on the order of 10–6, does not warrant national regulation of coal combustion wastes that are used in agricultural applications.

In the RTC, we were not able to identify damage cases associated with these types of beneficial uses, nor do we
now believe that these uses of coal combustion wastes present a significant
risk to human health or the
environment. While some commenters disagreed with our findings, no data or other support for the commenters’ position was provided, nor was any information provided to show risk or damage associated with agricultural use. Therefore, we conclude that none of the
beneficial uses of coal combustion wastes listed above pose risks of

concern.
2. Disposal in Landfills and Surface Impoundments

In this section, we discuss available information regarding the potential risks
to human health and the environment from the disposal of coal combustion
wastes into landfills and impoundments. In sum, our conclusion is these wastes can pose significant risks when mismanaged and, while significant improvements are being made in waste management practices due to increasing state oversight, gaps in the current regulatory regime remain.

We have determined that the establishment of national regulations is
warranted for coal combustion wastes when they are disposed in landfills and surface impoundments, because: (a) The composition of these wastes has the potential to present danger to human
health and the environment under some circumstances and ‘‘potential’’ damage cases identified by EPA and commenters, while not definitively demonstrating damage from coal combustion wastes, lend support to our
conclusion that these wastes have the potential to pose such danger; (b) we have identified eleven cases of proven damage to human health and the environment by improper management of these wastes when land disposed; (c) while industry management practices have improved measurably in recent years, there is sufficient evidence these wastes are currently being managed in a significant number of landfills and surface impoundments without proper controls in place, particularly in the area of groundwater monitoring; and (d)
while there have been substantive improvements in state regulatory programs, we have also identified significant gaps either in states’ regulatory authorities or in their exercise of existing authorities. Moreover, we believe that the costs of complying with regulations that specifically address these problems, while large in absolute terms, are only a small percentage of industry revenues.

When we considered a tailored subtitle C regulatory approach, we estimated the potential costs of regulation of coal combustion wastes (including the utility coal combustion
wastes addressed in the 1993 Part 1 determination) to be $1 billion per year. While large in absolute terms, we
estimate that these costs are less than 0.4 percent of industry sales. Our preliminary estimate of impact on profitability is a function of facility size, among other factors. For the largerfacilities, we estimate that reported pretax profit margins of about 13 percent may be reduced to about 11 percent. For smaller facilities, margins may be reduced from about nine percent to about seven percent.

We identified that the constituents of concern in these wastes are metals, particularly hazardous metals. We
further identified that leachate from various large volume wastes generated
at coal combustion facilities infrequently exceed the hazardous waste toxicity characteristic, for one or more of the following metals: arsenic, cadmium, chromium, lead, and mercury. Additionally, when we compared waste leachate concentrations
for hazardous metals to their corresponding MCLs (or potential MCLs in the case of arsenic), we found that there was a potential for risk as a result of arsenic leaching from these wastes.
The criteria we examined included the existing arsenic MCL, a lower health based number presented in the RTC,
and two assumed values in between. We examined this range of values because, as explained earlier in this notice, EPA is in the process of revising the current
MCL for arsenic to a lower value as a result of a detailed study of arsenic in drinking water and we wanted to assess the likely range of values that would be under consideration by EPA. Once we have completed a review of our groundwater model and made necessary changes, we will reevaluate the potential risks from metals in coal combustion wastes and compare any projected groundwater contamination to
the MCLs that exist at that time.

We also identified situations where the improper management of mill rejects, a low volume and uniquely associated waste, with high volume coal combustion wastes has the potential to cause releases of higher quantities of
hazardous metals. When these wastes are improperly managed, the mill rejects
can create an acidic environment which enhances leachability and can lead to the release of hazardous metals in high concentrations from the co-managed wastes to ground water or surface waters. Thus, our analysis of the
characteristics of coal combustion
wastes leads us to conclude that these wastes have the potential to pose risk to
human health and the environment. We also plan to address such waste management practices in our subsequent rulemaking.

Additionally, we identified 11 proven damage cases that documented disposal
of coal combustion wastes in unlined landfills or surface impoundments that involved exceedences of primary MCLs
or other health-based standards in ground water or drinking water wells. Three of the proven damage cases were on the EPA Superfund National Priorities List. Although these damage
cases indicate that coal combustion wastes can present risks to human health and the environment, they also
show the effectiveness of states’ responses when damages were identified. All of the sites were at older, unlined units, with disposal occurring prior to 1993. None of these cases involved actual human exposure. Given the large number of facilities that do not now conduct groundwater monitoring,
we have a concern that additional cases of damage may be undetected.

As detailed in the RTC and explained earlier in this notice, we identified that the states and affected industry have made considerable progress in recent years toward more effective management of coal combustion wastes. We also identified that the ability for most states to impose specific regulatory
controls for coal combustion wastes has increased almost three-fold over the past 15 years. Forty-three states can now impose a liner requirements at landfills whereas 15 years ago, 11 had the same authority. In addition to regulatory permits, the majority of states now have authority to require siting controls, liners, leachate collection, groundwater monitoring, closure controls, and other controls and requirements for surface impoundments and landfills.

Nonetheless, we have concluded that there are still gaps in the actual application of these controls and


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requirements, particularly for surface impoundments. While most states now have the appropriate authorities and regulations to require liners and groundwater monitoring that would
reduce or minimize the risks that we have identified, we have also identified
numerous situations where these controls are not being applied. For example, only 26 percent of utility surface impoundments and 57 percent of utility landfills have liner systems in place. We have insufficient information
to determine whether the use of these controls is significantly different for non-utility disposal units, due to a small sample size.

While many of these unlined units may be subject to grandfathering provisions that allow them to continue to operate without being lined, or may not need to be lined due to site-specific conditions, we are especially concerned
that a substantial number of units do not employ groundwater monitoring to ensure that if significant releases occur from these unlined units, they will be detected and controlled. In 1995, groundwater was monitored at only 38 percent of utility surface impoundments. While monitoring is more frequent at landfills, there are still many units at which releases of hazardous metals could go undetected. For example, of the approximately 300 utility landfills, 45 newer landfills (15%) do not monitor ground water. We
are concerned that undetected releases could cause exceedences of drinking
water or other health-based standards that may threaten public health or groundwater and surface water resources. Thus, we conclude that national regulations would lead to substantial improvements in the management of coal combustion wastes.

3. Minefilling

We have determined that the establishment of national regulations is
warranted for coal combustion wastes when they are placed in surface or underground mines because: (a) We
wind that these wastes when minefilled have the potential to present a danger to human health and the environment, (b) minefilling of these wastes has been an expanding practice and there are few states that currently operate comprehensive programs that specifically address the unique circumstances of minefilling, making it more likely that any damage to human health or the environment would go unnoticed or unaddressed, and (c) we believe that the cost of complying with regulations that address these potential dangers may not have a substantial impact on this practice because minefilling continues to grow in those few states that already have comprehensive programs.

We recognize that at this time, we cannot quantify the nature of damage that may be occurring or may occur in the future as a result of using coal
combustion wastes as minefill. It is often impossible to determine if existing groundwater quality has been impacted by previous mining operations or as a
result of releases of hazardous
constituents from the coal combustion wastes used in minefilling applications. We have not as yet identified proven damage cases resulting from the use of coal combustion wastes for minefilling.

We also acknowledge that when the complexities related to site-specific geology, hydrology, waste chemistry and interactions with the surrounding matrix, and other relevant factors are properly taken into account, coal
combustion wastes used as minefill can provide significant benefits. However, when not done properly, minefilling has the potential to contaminate ground water to levels that could damage
human health and the environment. Based on materials submitted during the public comment period, coal
combustion wastes used as minefill can
lead to increases in hazardous metals released into ground water if the acidity
within the mine overwhelms the capacity of the coal combustion wastes
to neutralize the acidic conditions. This is due to the increased leaching of
hazardous metals from the wastes. The potential for this to occur is further supported by data showing that management of coal combustion wastes in the presence of acid-generating pyritic wastes has caused metals to
leach from the combustion wastes at much higher levels than are predicted by leach test data for coal combustion wastes when strongly acidic conditions are not present. Such strongly acidic conditions often exist at mining sites.

Although we have identified no damage cases involving minefilling, we
are also aware of situations where coal combustion wastes are being placed in direct contact with ground water in both surface and underground mines. We concluded in our recent study of cement kiln dust management practices that placement of cement kiln dust in direct contact with ground water led to a substantially greater release of hazardous metals than we predicted would occur when the waste was placed above the water table. For this reason, we find that there is a potential for
increased releases of hazardous metals as a result of placing coal combustion
wastes in direct contact with groundwater. Also, there are damage cases associated with coal combustion wastes in landfills. The Agency believes
it is reasonable to be concerned when similar quantities of coal combustion wastes are placed in mines, which often are not engineered disposal units and in some cases involve direct placement of wastes into direct contact with ground

water.

We are concerned that government oversight is necessary to ensure that minefilling is done appropriately to protect human health and the environment, particularly since minefilling is a recent, but rapidly expanding use of coal combustion wastes. Government oversight has not yet ‘‘caught up’’ with the practice consistently across the country. There are some states that have programs that specifically address minefilling practices. We are likely to find that their programs or certain elements of their programs could serve as the basis for a comprehensive, flexible set of national management standards that ensure protection of human health and the
environment. We also believe that these state programs will provide valuable experience in coordinating with SMCRA program requirements. However, at this time, few of the programs are comprehensive. Commenters pointed out, and we agree, there are significant gaps in other states. We believe that additional requirements for long-term groundwater monitoring, and controls on wastes placed directly into groundwater might be prudent.

E. What Approach Will EPA Take in Developing National Regulations?

We will not promulgate any regulations for beneficial uses other than minefilling. We do not wish to place any unnecessary barriers on the
beneficial use of fossil fuel combustion wastes so that they can be used in applications that conserve natural resources and reduce disposal costs.

Once we concluded there is a need for some form of national regulation of coal combustion wastes disposed in landfills and surface impoundments and used as minefill, we considered two approaches. One approach would involve promulgating subtitle D regulations, pursuant to sections 1008 and 4004(a) of RCRA, that would contain criteria defining landfills and impoundments that would constitute ‘‘sanitary landfills.’’ Any facility that failed to
meet the standards would constitute an open dump, which is prohibited by section 4005(a) of RCRA. Such
standards would set a consistent baseline for protective management throughout the country. We would also work with the Department of Interior,


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Office of Surface Mining to evaluate whether equivalent protectiveness for minefilling could be afforded by relying on revision of existing SMCRA regulations or by relying on a
combination of RCRA and SMCRA
authorities.

The second approach was to promulgate regulations pursuant to Subtitle C of RCRA, that would have been similar to our recent proposed regulation of cement kiln dust. Following this approach, EPA would develop national management standards based on the Subtitle D open dump criteria as discussed above, as well as a set of tailored Subtitle C requirements promulgated pursuant to RCRA section 3004(x). If the wastes were properly managed in accordance with the subtitle D-like standards, they would not be
classified as hazardous wastes. When they were not properly managed, they
would become listed hazardous wastes subject to tailored subtitle C standards.
This scheme would be effective in each
state authorized for the hazardous waste program when that state modified its hazardous waste program to incorporate the listing.

Under this approach, after states have adopted the contingent listing, facilities that have egregious or repeated violations of the management standards
would be moved into the subtitle C program (subject to the tailored RCRA 3004 (x) requirements, rather than to the full set of subtitle C requirements). Thus, EPA would have authority to enforce the management standards.

The decision whether to establish regulations under subtitle C or D of RCRA for disposal of coal combustion
wastes in landfills and surface impoundments and when minefilled was a difficult one. EPA believes that, in this case, either approach would ensure adequate protection of public
health and the environment. Either subtitle C or D provides EPA with the authority to prescribe protective standards for the management of these wastes. Moreover, as described above, the standards that EPA would adopt under either regime, because of the flexibility provided by section 3004 (x), would be substantively the same. Also, under either approach, a facility that fails to comply with the standards is in
violation of RCRA—in the case of subtitle C, the facility would be in
violation of the tailored standards promulgated under section 3004(x). In the case of subtitle D, the facility would be in violation of the prohibition in section 4005(a) of RCRA against ‘‘open dumping.’’ The prohibition against open dumping is, however, enforceable only by private citizens and states, not EPA. Management standards established under the authority of subtitle C (including tailored section 3004(x) standards) are also enforceable by EPA. It appears that more than 40 states already have sufficient authority to implement most, if not all of the national standards we contemplate would be appropriate for surface impoundments and landfills. One difference between the two regimes may
be that states could cite revised subtitle D standards as a basis for exercising their existing authorities more vigorously, potentially promoting swifter adoption of appropriate controls for surface impoundments and landfills. In addition, subtitle D standards would be applicable and enforceable by
citizens as soon as the federal rule
becomes effective. subtitle C standards in contrast, would not apply until incorporated into state subtitle C programs. For minefilling, we would also explore SMCRA as a possible mechanism to speed implementation,
even if we relied on subtitle D to establish protective standards, because minefilling operations already are subject to SMCRA permitting authority.

Taking into account the common and
distinct features of these alternative approaches, EPA believes at this time, based on the current record, that subtitle D regulations are the more appropriate
mechanism for a number of reasons. In view of the very substantial progress that states have made in regulating disposal of fossil fuel combustion wastes in surface impoundments and landfills in recent years, as well as the active role that this industry has played recently in facilitating responsible waste disposal practices, EPA believes that subtitle D controls will provide sufficient clarity and incentive for states to close the remaining gaps in coverage,
and for facilities to ensure that their wastes are managed properly.

For minefilling, although we have
considerable concern about certain current practices (e.g., placement directly into groundwater), we have not yet identified a case where placement of
coal wastes can be determined to have actually caused increased damage to ground water. In addition, there is a federal regulatory program—SMCRA— expressly designed to address
environmental risks associated with coal mines. Finally, given that states have been diligent in expanding and upgrading programs for surface impoundments and landfills, we believe they will be similarly responsive in addressing environmental concerns arising from this emerging practice. In short, we arrive at the same conclusions, for substantially the same reasons, for this practice as we did for landfills and surface impoundments: that subtitle D controls, or upgraded SMCRA controls or a combination of the two, should provide sufficient clarity and incentive to ensure proper handling of this waste when minefilled. Having determined that subtitle C regulation is not warranted for all other management practices, EPA does not see a basis in the record for carving this one practice out for separate regulatory treatment.

Once these subtitle D regulations are effective, facilities would be subject to citizen suits for any violation of the standards. If EPA were addressing wastes that had not been addressed by the states (or the federal government) in the past, or an industry with wide evidence of irresponsible solid waste management practices, EPA may well
conclude that the additional incentives for improvement and compliance provided by the subtitle C scheme—the
threat of federal enforcement and the stigma associated with improper management of RCRA subtitle C waste— were necessary. But the record before us
indicates that the structure and the
sanctions associated with a subtitle D approach (or a SMCRA approach if EPA determines it is equivalent) should be
sufficient.

We also see a potential downside to pursuing a subtitle C approach. Section 8002(n)(8) directs us to consider, among other factors, ‘‘the current and potential utilization of such materials.’’ Industry commenters have indicated that they believe subjecting any coal combustion wastes to a subtitle C regime would place a significant stigma on these wastes, the most important effect being that it would adversely impact beneficial reuse. As we understand it, the concern is that, even though beneficially reused waste would not be hazardous under the contemplated subtitle C approach, the link to subtitle C would nonetheless tend to discourage purchase and re-use of the wastes or products made from the wastes. We do not wish to place any unnecessary
barriers on the beneficial uses of these wastes, because they conserve natural resources, reduce disposal costs and
reduce the total amount of waste destined for disposal. States and industry have also expressed concern that regulation under subtitle C could
cause a halt in the use of coal
combustion wastes to reclaim
abandoned and active mine sites. If this were to occur, it would be unfortunate in that when done properly, we recognize this practice can lead to
substantial environmental benefits. EPA believes the contingent management
scheme we discussed should diminish


### 32233 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

any stigma that might be associated with the subtitle C link. Nonetheless, we acknowledge the possibility that the approach could have unintended consequences. We would be particularly concerned about any adverse effect on

the beneficial re-use market for these wastes because more than 23 percent (approximately 28 million tons) of the total coal combustion waste generated each year is beneficially reused and an additional eight percent (nine million tons) is used for minefilling. EPA

believes that such reuse when performed properly, is by far the environmentally preferable destination for these wastes, including when minefilled. Normally, concerns about stigma are not a deciding factor in EPA’s decisions under RCRA, given the central concern under the statute for protection

of human health and the environment. However, given our conclusion that the subtitle D approach here should be fully effective in protecting human health and the environment, and given the large and salutary role that beneficial reuse plays for this waste, concern over stigma is a factor supporting our decision today that subtitle C regulation is unwarranted in light of our decision to pursue a subtitle D approach.

As we proceed with regulation development, we will also take

enforcement action under RCRA section 7003 when we identify cases of

imminent and substantial endangerment. We will also use Superfund remedial and emergency response authorities under the Comprehensive Environmental Response Compensation and Liabilities Act (CERCLA), as appropriate, to address damages that result in risk to

human health and the environment. We

will also take into account new

information as it becomes available. We are awaiting a National Academy of Sciences report scheduled to be released in June 2000. This report will present a comprehensive review of mercury and recommendations on appropriate

adverse health effects levels for this constituent. We believe that this report will enhance our understanding of the risks due to exposure to mercury, and

we will review and assess its implications for today’s decision on

fossil fuel combustion wastes. These efforts may result in a re-evaluation of the risks posed by managing coal

combustion wastes. 3. What Is the Basis for EPA’s Regulatory Determination for Oil
Combustion Wastes?

A. What Is the Agency’s Decision Regarding the Regulatory Status of Oil Combustion Wastes and Why Did EPA
Make This Decision?

We have determined that it is not appropriate to issue regulations under subtitle C of RCRA applicable to oil combustion wastes because: (a) We have not identified any beneficial uses that are likely to present significant risks to human health or the environment; and (b) except for a limited number of unlined surface impoundments, we have not identified any significant risks
to human health and the environment associated with any waste management practices.

We intend to work with the State of
Massachusetts and the owners and operators of the remaining two oil combustion facilities that currently manage their wastes in unlined surface impoundments to ensure that their wastes are managed in a manner that protects human health and the

environment.

B. What Were EPA’s Tentative Decisions as Presented in the Report to Congress and Why Did EPA Make That Decision?

In the Report to Congress, we stated that the only management scenario for which we found risks posed by management of oil combustion wastes
was when oil combustion wastes are managed in unlined surface impoundments. The Report to Congress further explained that we were considering two approaches to address these identified risks. One approach was to regulate using RCRA subtitle C authority. The other approach was to encourage voluntary changes so that no oil combustion wastes are managed in unlined surface impoundments. This voluntary approach is based on recent industry and state regulatory trends to line oil combustion waste disposal units and implement groundwater monitoring.

We also tentatively decided that the existing beneficial uses of oil
combustion wastes should remain exempt from RCRA subtitle C. There are few existing beneficial uses of these wastes, which include use in concrete products, structural fill, roadbed fill, and vanadium recovery. We determined that no significant risks to human health
exist for the beneficial uses of these
wastes. For the case of facilities that accept these wastes to recover vanadium from them, we explained that if the wastes resulting from the metal recovery processes are hazardous, they will be subject to existing hazardous waste requirements.

We found in most cases that OCW, whether managed alone or co-managed, are rarely characteristically hazardous. Additionally, we identified no significant ecological risks posed by land disposal of OCW. We identified only one documented damage case involving OCW in combination with coal combustion wastes, and it did not affect human receptors.

Although most of the disposed oil combustion wastes are managed in lined surface impoundments, we did identify six utility sites where wastes are managed in unlined units. We expressed particular concern with management of these wastes in unlined settling basins and impoundments that are designed and operated to discharge the aqueous portion of the wastes to ground water. Our risk analysis indicated that, in these situations, three metals—arsenic, nickel, and vanadium—may pose potential risk by the groundwater pathway.

C. How Did Commenters React to EPA’s
Tentative Decisions and What Was EPA’s Analysis of Their Comments?

Because we were able to identify so few unlined surface impoundments, the only management scenario for which we found risks, the primary focus of the comments regarding oil combustion
wastes was on the six unlined surface impoundments that we identified. In addition, there were extensive comments on our modeling and risk assessment methodology for the groundwater pathway that are applicable to our assessment of risks posed by oil combustion wastes.

1. How Did Commenters React to the
Six Unlined Oil Combustion Waste Surface Impoundments That We
Identified?

Comments. Industry commenters supported the approach to encourage voluntary changes in industry practices on a site-specific basis, and explained why they believed hazardous waste regulations are unnecessary. The environmental community supported the development of hazardous waste regulations.

EPA’s Analysis of Comments. In the RTC, we identified that our only
concern about oil combustion wastes was based on the potential for migration of arsenic, nickel, and vanadium from unlined surface impoundments. We requested information on this issue and did not receive any additional data and/
or information to refute our tentative finding stated in the RTC that these


### 32234 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

unlined surface impoundments could pose a significant risk.

As stated in the RTC, there are only six sites involving two companies that have unlined surface impoundments.
Four of the sites are in Florida and are operated by one company. The company operating the four unlined impoundments in Florida is undertaking projects to mitigate potential risks posed by their unlined management units. At a May 21, 1999 public hearing, the company announced its plans to remove all the oil ash and
basin material from its unlined impoundments and to line or close the units. The company informed us in January 2000 that it had completed the lining of all the units. Based on this information, we do not believe that these units pose a significant risk to
human health and the environment.

The other two sites with unlined impoundments are operated by one utility in Massachusetts. Both sites are permitted under Massachusetts’ ground water discharge permit program and have monitoring wells around the
unlined basins. Arsenic is monitored for compliance with state regulations. Although the company expressed no plans to line their impoundments, they are preparing to implement monitoring for nickel and vanadium in ground water around the waste management units. We have been working with the State and the company to obtain
additional information to evaluate these two management units. We will
continue this effort and will work with the company and the State to ensure that any necessary measures are taken so that these wastes are managed in a manner that protects human health and
the environment.

2. How Did Commenters React to the Groundwater Modeling and Risk Assessment Analyses Conducted by EPA to Support Its Findings in the Report to Congress?

Comments. Industry and public interest group commenters submitted detailed critiques of the ground water model, EPACMTP, that we used for our risk analysis. Industry commenters
believe that the model will overestimate the levels of contaminants that may migrate down-gradient from disposed wastes. Environmental groups expressed the opposite belief; that is, that the model underestimates down-gradient chemical concentrations and, therefore, underestimates the potential risk posed by oil combustion wastes.

EPA’s Analysis of the Comments. We are carefully reviewing all of the
comments on the model and have determined that the process of thoroughly investigating all of the comments will take substantially more time to complete than is available within the court deadline for issuing this regulatory determination. At this time, we are uncertain of the overall outcome of our analysis of the issues raised in the comments. Accordingly,
we have decided not to use the results of our ground water pathway risk analysis in support of today’s regulatory
determination on fossil fuel combustion wastes. As explained above, we believe
that actions have been taken or are under way by specific companies and/
or the State of Massachusetts to address potential risks at the six impoundments that we have been able to identify.
Therefore we believe that further groundwater analysis is unnecessary at
this time.

Meanwhile, we will continue with our analysis of comments on the groundwater model and risk analysis. This may involve changing or restructuring various aspects of the model, if appropriate. It may also include additional analyses to determine whether any changes to the model or modeling methodology would materially affect the groundwater risk analysis results that were reported in the RTC. If our investigations reveal that a reanalysis of groundwater risks is appropriate, we will conduct the analysis and reevaluate today’s decisions as appropriate.

In addition to our ongoing review of comments on the groundwater model,
one element of the model—the metals partitioning component called ‘‘MINTEQ’’—has been proposed for additional peer review. When this additional peer review is completed, we will take the findings and recommendations into account in any overall decision to re-evaluate today’s regulatory determination.

D. What Is the Basis for Today’s

Decisions?

We have determined that it is not appropriate to establish national regulations applicable to oil combustion wastes because: (a) We have not identified any beneficial uses that are likely to present significant risks to human health or the environment; and (b) except for two remaining unlined surface impoundments, we have not identified any significant risks to human
health and the environment associated with any waste management practices. As explained in the previous section,
we intend to work with the State of
Massachusetts and the owners and operators of the remaining two oil combustion facilities that currently manage their wastes in unlined surface impoundments to ensure that any necessary measures are taken so that their wastes are managed in a manner that protects human health and the

environment. Given the limited number of sites at issue and our ability to adequately address risks from thesewaste management units through sitespecific response measures, we see no need for issuing regulations under

subtitle C or D of RCRA.

4. What Is the Basis for EPA’s Regulatory Determination for Natural

Gas Combustion Wastes?

A. What Is the Decision Regarding the Regulatory Status of Natural Gas

Combustion Wastes?

For the reasons described in the Report to Congress (pages 7–1 to 7–3), EPA has decided that regulation of natural gas combustion wastes as

hazardous wastes under RCRA subtitle C or D is not warranted. The burning of natural gas generates virtually no solid

waste.

B. What Was EPA’s Tentative Decision as Presented in the Report to Congress?

The Agency’s tentative decision was to retain the subtitle C exemption for natural gas combustion because virtually no solid waste is generated.

C. How Did Commenters React to EPA’s

Tentative Decision?

No commenters on the RTC disagreed with EPA’s findings or its tentative decision to continue the exemption for natural gas combustion wastes.

Specific comments on this issue supported our tentative decision to retain the exemption for natural gas combustion waste. One industry association encouraged us to foster the use of natural gas as a substitute for other fossil fuels. While some public interest group commenters disagreed broadly with our tentative conclusions to retain the exemption for fossil fuel combustion wastes, they did not specifically address natural gas

combustion wastes.

D. What Is the Basis for Today’s

Decision?

The burning of natural gas generates virtually no solid waste. We, therefore,

believe that there is no basis for EPA developing subtitle C or D regulations applicable to natural gas combustion

wastes.


### 32235 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

5. What Is the History of EPA’s Regulatory Determinations for Fossil
Fuel Combustion Wastes?

A. On What Basis Is EPA Required To Make Regulatory Determinations Regarding the Regulatory Status of
Fossil Fuel Combustion Wastes?

Section 3001(b)(3)(C) of the Resource Conservation and Recovery Act (RCRA) as amended requires that, after completing a Report to Congress mandated by section 8002(n) of RCRA,
the EPA Administrator must determine whether Subtitle C (hazardous waste) regulation of fossil fuel combustion
wastes is warranted.

B. What Was EPA’s General Approach in Making These Regulatory

Determinations?

We began our effort to make our determination of the regulatory status of fossil fuel combustion wastes by studying high volume coal combustion wastes managed separately from other
fossil fuel combustion wastes that are generated by electric utilities. In February 1988, EPA published the Report to Congress on Wastes from the Combustion of Coal by Electric Utility Power Plants. The report addressed four large-volume coal combustion wastes generated by electric utilities and independent power producers when managed alone. The four wastes are fly ash, bottom ash, boiler slag, and flue gas desulfurization (FGD) wastes. The report did not address co-managed utility coal combustion wastes (UCCWs), other fossil fuel wastes generated by utilities, or wastes from non-utility boilers burning any type of fossil fuel. Because of other priorities at the time, we did not immediately complete a determination of the regulatory status of these large-volume
coal combustion wastes.

C. What Happened When EPA Failed To Issue Its Determination of the Regulatory Status of the Large Volume Utility Combustion Wastes in a Timely

Manner?

In 1991, a suit was filed against EPA for not completing a regulatory
determination on fossil fuel combustion wastes ( Gearhart v. Reilly, Civil No. 91– 2345 (D.D.C.)). On June 30, 1992, the Agency entered into a Consent Decree
that established a schedule for us to complete the regulatory determination
for all fossil fuel combustion wastes in two phases:

• The first phase covers fly ash, bottom ash, boiler slag, and flue gas
emission control wastes from the combustion of coal by electric utilities and independent commercial power producers. These are the four large volume wastes that were the subject of the 1988 Report to Congress described
above. We refer to this as the Part 1 regulatory determination.

• The second phase covers all of the ‘‘remaining’’ fossil fuel combustion
wastes not covered in the Part 1 regulatory determination. We refer to this as the Part 2 regulatory determination, which is the subject oftoday’s action. Under the current courtorder, EPA was directed to issue the Part 2 regulatory determination by April

25, 2000.

D. When Was the Part 1 Regulatory
Decision Made and What Were EPA’s Findings?

In 1993, EPA issued the Part 1 regulatory determination, in which we retained the exemption for Part 1 wastes (see 58 FR 42466; August 9, 1993). The four Part 1 large-volume utility coal combustion wastes (UCCWs) are also addressed in the Part 2 regulatorydetermination when they are comanaged with low-volume fossil fuel
combustion wastes not covered in the
Part 1 determination.

6. Executive Orders and Laws Addressed in Today’s Action

A. Executive Order 12866— Determination of Significance

Under Executive Order 12866, (58 FR 51735, Oct. 4, 1993) we must determine whether the regulatory action is ‘‘significant’’ and therefore subject to review by the Office of Management and Budget (OMB) and the requirements of
the Executive Order. The Order defines ‘‘significant regulatory action’’ as one that is likely to result in a rule that may:

• Have an annual effect on the economy of $100 million or more or adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, public health or safety, or State, local, or tribal governments or communities;

• Create a serious inconsistency or
otherwise interfere with an action taken or planned by another agency;

• Materially alter the budgetary impact of entitlements, grants, user fees, or loan programs or the rights and obligations of recipients thereof; or

• Raise novel legal or policy issues arising out of legal mandates, the President’s priorities, or the principles
in the Executive Order.’’

Under Executive Order 12866, this is a ‘‘significant regulatory action.’’ Thus,
we have submitted this action to OMB for review. Changes made in response to OMB suggestions or recommendations are documented in the public record. B. Regulatory Flexibility Act (RFA), as Amended by the Small Business Regulatory Enforcement Fairness Act of 1996 (SBREFA), 5 U.S.C. 601 et seq.

Today’s action is not subject to the RFA, which generally requires an agency to prepare a regulatory flexibility analysis for any rule that will have a significant economic impact on a
substantial number of small entities. The RFA applies only to rules subject to notice-and-comment rulemaking requirements under the Administrative Procedure Act (APA) or any other statute. This action is not subject to notice and comment requirements under the APA or any other statute. Today’s action is being taken pursuant to section 3001(b)(3)(C) of the Resource Conservation and Recovery Act. This provision requires EPA to make a determination whether to regulate fossil
fuel combustion wastes after submission of its Report to Congress and public hearings and an opportunity for comment. This provision does not require the publication of a notice of proposed rulemaking and today’s action is not a regulation. See American
Portland Cement Alliance v. E.P.A., 101 F.3d 772 (D.C.Cir. 1996).

C. Paperwork Reduction Act Information Collection Requests

Today’s final action contains no information collection requirements.

D. Unfunded Mandates Reform Act

Today’s action is not subject to the requirements of sections 202 and 205 of
the Unfunded Mandates Reform Act of 1995 (UMRA), Public Law 104–4. Title II of UMRA establishes requirements for federal agencies to assess the effects of their regulatory actions on state, local, and tribal governments and the private sector. Under section 202 of the UMRA, EPA generally must prepare a written statement, including a cost-benefit analysis, for proposed and final rules with ‘‘federal mandates’’ that may result in expenditures to state, local, and tribal governments, in the aggregate, or to the private sector, of $100 million or more in any one year.

Before we issue a rule for which a written statement is needed, section 205 of the UMRA generally requires us to identify and consider a reasonable number of regulatory alternatives andadopt the least costly, most costeffective, or least burdensome
alternative that achieves the rule’s objectives. Section 205 doesn’t apply when it is inconsistent with applicable law. Moreover, section 205 allows us to adopt an alternative other than the least costly, most cost-effective, or least


### 32236 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

burdensome alternative if the final rule explains why that alternative was not adopted. Before we establish any regulatory requirements that may significantly affect small governments, including tribal governments, we must have developed under section 203 of the UMRA a small-government-agency plan. The plan must provide for notifying potentially affected small governments, enabling them to have meaningful and timely input in the developing EPA regulatory proposals with significant federal intergovernmental mandates, and informing, educating, and advising small governments on compliance with the regulatory requirements.

Today’s final action contains no federal mandates (under the regulatory provisions of Title II of the UMRA) for state, local, or tribal governments or the private sector. Today’s final action imposes no enforceable duty on any state, local or tribal governments or the private sector.

In addition, we have determined this
action contains no federal mandate that may result in expenditures of $100 million or more for state, local, and tribal governments, in the aggregate, or the private sector in any one year.

E. Executive Order 13132: Federalism

Executive Order 13132, entitled Federalism (64 FR 43255, August 10, 1999) requires us to develop an accountable process to ensure meaningful and timely input by state and local officials in the development of regulatory policies that have federalism implications. The executive order defines policies that have federalism implications to include regulations that
have substantial direct effects on the states, on the relationship between the national government and the states, or on the distribution of power and responsibilities among the various levels of government.

Under section 6 of Executive Order 13132, we may issue a regulation that has federalism implications, that imposes substantial direct compliance costs, and that isn’t required by statute, only if the federal government provides funds the direct compliance costs incurred by state and local governments,
or if EPA consults with state and local officials early in the development of the proposed regulation. Also, EPA may issue a regulation that has federalism implications and that preempts state law, only if we consult with state and local officials early in the development of the proposed regulation.

If EPA complies by consulting, Executive Order 13132 requires us to provide OMB, in a separately identified section of the rule’s preamble, a federalism summary impact statement (FSIS). The FSIS must describe the extent of our prior consultation with state and local officials, summarizing
the nature of their concerns and our position supporting the need for the regulation, and state the extent to which
the concerns of state and local officials have been met. Also, when we transmit
a draft final rule with federalism implications to OMB for review under Executive Order 12866, our federalism
official must include a certification that EPA has met the requirements of Executive Order 13132 in a meaningful and timely manner.

Today’s final action does not have federalism implications. It will not have a substantial direct affect on the States, on the relationship between the national government and the States, or on the distribution of power and responsibilities among the various levels of government, as specified in
Executive Order 13132. This is because no requirements are imposed by today’s action, and EPA is not otherwise mandating any state or local government actions. Thus, the requirements of
section 6 of the Executive Order do not apply to this final action.

F. Executive Order 13084: Consultation
and Coordination With Indian Tribal

Governments

Under Executive Order 13084, EPA may take an action that isn’t required by statute, that significantly or uniquely
affects the communities of Indian tribal governments, and that imposes substantial direct compliance costs on those communities, only if the federal government provides the funds necessary to pay the direct compliance costs incurred by the tribal governments
or EPA consults with those governments. If EPA complies by consulting, Executive Order 13084 requires us to describe in a separately identified section of the preamble to the rule the extent of our prior consultation with representatives of affected tribal governments, summarizing of the nature of their concerns, and state the need for the regulation. Also, Executive Order 13084 requires EPA to develop an effective process permitting elected officials and other representatives of Indian tribal governments ‘‘to provide meaningful and timely input in the development of regulatory policies on matters that significantly or uniquely
affect their communities.’’

Today’s final action does not significantly or uniquely affect the
communities of Indian tribal governments. This is because today’s action by EPA involves no regulations or other requirements that significantly or uniquely affect Indian tribal governments. So, the requirements of section 3(b) of Executive Order 13084 do not apply to this action.

G. Executive Order 13045: Protection of

Children From Environmental Health Risks and Safety Risks

‘‘Protection of Children from Environmental Health Risks and Safety Risks’’ (62 FR 19885, April 23, 1997) applies to any rule that: (1) Is ‘‘economically significant’’ as defined under Executive Order 12866, and (2)

concerns an environmental health or safety risk that EPA has reason to believe may have a disproportionate effect on children. If the regulatory action meets both criteria, we must

evaluate the environmental health or safety effects of the planned rule on children and explain why the planned regulation is preferable to other potentially effective and reasonably feasible alternatives considered by the Agency.

Today’s final action isn’t subject to

the Executive Order because it is not economically significant as defined in Executive Order 12866, and because we

have no reason to believe the environmental health or safety risks addressed by this action present a disproportionate risk to children. Risks were thoroughly evaluated during the course of developing today’s decision

and were determined not to disproportionately affect children.

H. National Technology Transfer and Advancement Act of 1995

As noted in the proposed rule, section 12(d) of the National Technology

Transfer and Advancement Act of 1995 (‘‘NTTAA’’), Public Law. No. 104–113, section12(d) (15 U.S.C. 272 note) directs EPA to use voluntary-consensus standards in its regulatory activities unless doing so would be inconsistent with applicable law or otherwise impractical. Voluntary-consensus standards are technical standards (such as materials specifications, test methods, sampling procedures, and business practices) that are developed or adopted by voluntary-consensus

standards bodies. The NTTAA directs us to explain to Congress, through OMB,

when we decide not to use available and applicable voluntary-consensus

standards.

Today’s final action involves no technical standards. So, EPA didn’t consider using any voluntary-consensus

standards.


### 32237 Federal Register / Vol. 65, No. 99 / Monday, May 22, 2000 / Rules and Regulations

I. Executive Order 12898: Environmental Justice

EPA is committed to addressing environmental justice concerns and is assuming a leadership role in environmental justice initiatives to enhance environmental quality for all populations in the United States. The Agency’s goals are to ensure that no segment of the population, regardless of race, color, national origin, or income bears disproportionately high and
adverse human health or environmental impacts as a result of EPA’s policies, programs, and activities, and that all people live in safe and healthful environments. In response to Executive Order 12898 and to concerns voiced by many groups outside the Agency, EPA’s Office of Solid Waste and Emergency Response formed an Environmental Justice Task Force to analyze the array of environmental justice issues specific to waste programs and to develop an overall strategy to identify and address these issues (OSWER Directive No. 9200.317).

J. Congressional Review Act

The Congressional Review Act, 5

U.S.C. 801 et seq., as added by the Small Business Regulatory Enforcement Fairness Act of 1996, does not apply
because this action is not a rule for purposes of 5 U.S.C. 804(3). Rather, this action is an order as defined by 5 U.S.C. 551(6).

7. How To Obtain More Information

Documents related to this regulatory determination, including EPA’s response to the public comments, are available for inspection in the docket.
The relevant docket numbers are: F–99– FF2D–FFFFF for the regulatory determination, and F–99–FF2P–FFFFF
for the RTC. The RCRA Docket Information Center (RIC), is located at Crystal Gateway I, First Floor, 1235 Jefferson Davis Highway, Arlington, VA. The RIC is open from 9 a.m. to 4 p.m., Monday through Friday, excluding Federal holidays. To review docket materials, it is recommended that the public make an appointment by calling 703-603–9230. The public may copy a maximum of 100 pages from any regulatory docket at no charge. Additional copies cost $0.15/page. The index and some supporting materials are available electronically. See the Supplementary Information section for information on accessing them.

List of Subjects in 40 CFR Part 261

Fossil fuel combustion waste, Coal combustion, Gas combustion, Oil combustion, Special wastes, Bevill exemption

Dated: April 25, 2000.

Carol M. Browner,

Administrator.

[FR Doc. 00–11138 Filed 5–19–00; 8:45 am]

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