Proposed Rule2025-24134

No-Migration Variance From Land Disposal Restrictions for Clean Harbors Grassy Mountain, Utah

Primary source

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Published
December 31, 2025

Issuing agencies

Environmental Protection Agency

Abstract

The U.S. Environmental Protection Agency (EPA) is proposing to grant, with conditions, no-migration variances for four categories/ groups of wastes, containing up to 250 temporary disposal units ("put piles") at any one time, from the Resource Conservation and Recovery Act (RCRA) Land Disposal Restrictions (LDR) standards at Clean Harbors' Grassy Mountain (Clean Harbors) commercial treatment, storage and disposal facility (TSDF) in Tooele County, UT. These variances will allow Clean Harbors to temporarily store treated hazardous wastes that are awaiting LDR compliance verification in put piles within their Subtitle C (hazardous waste) landfill. The petitioner demonstrated, to a reasonable degree of certainty, that there will be no migration of hazardous constituents from the disposal units for as long as the wastes remain hazardous. Additionally, once LDR compliance is verified, the put piles will be disposed within the onsite RCRA hazardous waste Landfill area and will be subject to the conditions set out in the Compliance Monitoring Plan section of this document.

Full Text

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<title>Federal Register, Volume 90 Issue 247 (Wednesday, December 31, 2025)</title>
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[Federal Register Volume 90, Number 247 (Wednesday, December 31, 2025)]
[Proposed Rules]
[Pages 61356-61361]
From the Federal Register Online via the Government Publishing Office [<a href="http://www.gpo.gov">www.gpo.gov</a>]
[FR Doc No: 2025-24134]


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Proposed Rules
                                                Federal Register
________________________________________________________________________

This section of the FEDERAL REGISTER contains notices to the public of 
the proposed issuance of rules and regulations. The purpose of these 
notices is to give interested persons an opportunity to participate in 
the rule making prior to the adoption of the final rules.

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Federal Register / Vol. 90, No. 247 / Wednesday, December 31, 2025 / 
Proposed Rules

[[Page 61356]]



ENVIRONMENTAL PROTECTION AGENCY

40 CFR Part 268

[EPA-R08-RCRA-2025-0420; FRL-12863-01-R8]


No-Migration Variance From Land Disposal Restrictions for Clean 
Harbors Grassy Mountain, Utah

AGENCY: Environmental Protection Agency (EPA).

ACTION: Notice of proposal to grant.

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SUMMARY: The U.S. Environmental Protection Agency (EPA) is proposing to 
grant, with conditions, no-migration variances for four categories/
groups of wastes, containing up to 250 temporary disposal units (``put 
piles'') at any one time, from the Resource Conservation and Recovery 
Act (RCRA) Land Disposal Restrictions (LDR) standards at Clean Harbors' 
Grassy Mountain (Clean Harbors) commercial treatment, storage and 
disposal facility (TSDF) in Tooele County, UT. These variances will 
allow Clean Harbors to temporarily store treated hazardous wastes that 
are awaiting LDR compliance verification in put piles within their 
Subtitle C (hazardous waste) landfill. The petitioner demonstrated, to 
a reasonable degree of certainty, that there will be no migration of 
hazardous constituents from the disposal units for as long as the 
wastes remain hazardous. Additionally, once LDR compliance is verified, 
the put piles will be disposed within the onsite RCRA hazardous waste 
Landfill area and will be subject to the conditions set out in the 
Compliance Monitoring Plan section of this document.

DATES: Comments must be received on or before January 30, 2026.

ADDRESSES: You may send comments, identified by EPA-R08-RCRA-2025-0420, 
by any of the following methods:
    <bullet> Federal eRulemaking portal: <a href="https://www.regulations.gov/">https://www.regulations.gov/</a> 
(our preferred method). Follow the online instructions for submitting 
comments.
    <bullet> Email: <a href="/cdn-cgi/l/email-protection#c4aaa1b3a8a5aaa0eaaea1b7b7a184a1b4a5eaa3abb2"><span class="__cf_email__" data-cfemail="264843514a474842084c435555436643564708414950">[email&#160;protected]</span></a>.
    <bullet> Mail, hand delivery or courier: Deliver your comments to 
Jesse Newland, Land, Chemicals and Redevelopment Division, EPA Region 
8, 1595 Wynkoop Street, Denver, Colorado 80202-1129, Mail Code: 8LCR-
RC-P, telephone number: (303) 312-6353. Courier or hand deliveries are 
only accepted during the Regional Office's normal hours of operation. 
The public is advised to call in advance to verify the business hours. 
Special arrangements should be made of deliveries of boxed information.
    <bullet> Instructions: All submissions received must include the 
Docket ID No. EPA-R08-RCRA-2025-0420 for this rulemaking. Comments 
received may be posted without change to <a href="https://www.regulations.gov">https://www.regulations.gov</a>, 
including any personal information provided. For detailed instructions 
on sending comments and additional information, see the ``Public 
Participation'' heading of the SUPPLEMENTARY INFORMATION section of 
this document.

FOR FURTHER INFORMATION CONTACT: Jesse Newland, Land, Chemicals and 
Redevelopment Division, EPA Region 8, 1595 Wynkoop Street, Denver, 
Colorado 80202-1129, mail code: 8LCR-RC-P, telephone number: (303) 312-
6353, email address: <a href="/cdn-cgi/l/email-protection#d3bdb6a4bfb2bdb7fdb9b6a0a0b693b6a3b2fdb4bca5"><span class="__cf_email__" data-cfemail="91fff4e6fdf0fff5bffbf4e2e2f4d1f4e1f0bff6fee7">[email&#160;protected]</span></a>.

SUPPLEMENTARY INFORMATION:

I. Public Participation

A. Docket

    EPA has established a docket for this action under Docket ID No. 
EPA-R08-RCRA-2025-0420. All documents in the docket are listed in the 
<a href="https://www.regulations.gov">https://www.regulations.gov</a> index.

B. Written Comments

    Submit your comments, identified by Docket ID No. EPA-R08-RCRA-
2025-0420, at <a href="https://www.regulations.gov">https://www.regulations.gov</a> (our preferred method), or 
the other methods identified in the ADDRESSES section. Once submitted, 
comments cannot be edited or removed from the docket. EPA may publish 
any comment received to its public docket. Do not submit electronically 
any information you consider to be Confidential Business Information 
(CBI) or other information whose disclosure is restricted by statute. 
Multimedia submissions (audio, video, etc.) must be accompanied by a 
written comment. The written comment is considered the official comment 
and should include discussion of all points you wish to make. EPA will 
generally not consider comments or comment contents located outside of 
the primary submission (i.e., on the web, cloud, or other file sharing 
system). For additional submission methods, the full EPA public comment 
policy, information about CBI or multimedia submissions, and general 
guidance on making effective comments, please visit <a href="https://www.epa.gov/dockets/commenting-epa-dockets">https://www.epa.gov/dockets/commenting-epa-dockets</a>.

C. Submitting CBI

    Do not submit information that you consider to be CBI 
electronically through <a href="https://www.regulations.gov">https://www.regulations.gov</a> or email. Send or 
deliver information identified as CBI to only the following address: 
RCRA Document Control Officer Andy Woodward, 1595 Wynkoop Street, 
Denver, CO 80202-1129, Mail Code: 8ECA-RO-E, Email: 
<a href="/cdn-cgi/l/email-protection#2f5840404b584e5d4b014e414b566f4a5f4e01484059"><span class="__cf_email__" data-cfemail="a0d7cfcfc4d7c1d2c48ec1cec4d9e0c5d0c18ec7cfd6">[email&#160;protected]</span></a>, Attn: Docket ID No. EPA-R08-RCRA-2025-0420.
    Clearly mark the part or all of the information that you claim to 
be CBI. For CBI information in a disk or CD-ROM that you mail to EPA, 
mark the outside of the disk or CD-ROM as CBI and then identify 
electronically within the disk or CD-ROM the specific information that 
is claimed as CBI. In addition to one complete version of the comment 
that includes information claimed as CBI, a copy of the comment that 
does not contain the information claimed as CBI must be submitted for 
inclusion in the public docket. If you submit a CD-ROM or disk that 
does not contain CBI, mark the outside of the disk or CD-ROM clearly 
that it does not contain CBI. Information marked as CBI will not be 
disclosed except in accordance with procedures set forth in 40 Code of 
Federal Regulations (CFR) part 2.

II. General Information

A. Does this document apply to me?

    This action applies only to Clean Harbors' Grassy Mountain facility 
(Clean Harbors) located in Tooele County, Utah.

B. What action is the Agency taking?

    On July 16, 2024, Clean Harbors submitted to EPA a no-migration 
variance (NMV) petition, in accordance with 40 CFR 268.6, seeking an

[[Page 61357]]

exemption from the Land Disposal Restrictions (LDR) prohibition on land 
placement of hazardous waste that does not meet the prescribed LDR 
standards of 40 CFR 268.40. Because the petition demonstrated to a 
reasonable degree of certainty that, for as long as the wastes remain 
hazardous, there will be no migration of hazardous constituents from 
the disposal units, EPA proposes to grant, with conditions, Clean 
Harbors' variance from the LDR prohibition for up to 250 put piles at 
any one time. If granted, the term of this NMV shall be no longer than 
the term of the RCRA Subtitle C permit for the permitted Landfill.

C. What is the Agency's authority for taking this action?

    Sections 3004(d) through (g) of the Resource Conservation and 
Recovery Act (RCRA), 42 U.S.C. 6294(d)-(g), prohibit the land disposal 
of hazardous wastes unless such wastes meet the LDR treatment standards 
(``treatment standards'') established by EPA (``Agency'').
    However, RCRA 3004(d)(1),\1\ and its implementing regulations found 
at 40 CFR 268.6, provide an option for land disposal of hazardous waste 
that does not meet the applicable treatment standards where EPA has 
approved an NMV petition. Specifically, the regulations in 40 CFR 
268.6(a) describe the components that a demonstration must address; 40 
CFR 268.6(b) specifies certain criteria that must be satisfied for that 
demonstration, and 40 CFR 268.6(c) describes the monitoring program 
that will be used to verify that the conditions of the NMV are being 
met.
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    \1\ RCRA 3004(d)(1)(c) states: ``. . . For the purposes of this 
paragraph, a method of land disposal may not be determined to be 
protective of human health and the environment for a hazardous waste 
referred to in paragraph (2) . . . unless, upon application by an 
interested person, it has been demonstrated to the Administrator, to 
a reasonable degree of certainty, that there will be no migration of 
hazardous constituents from the disposal unit or injection zone for 
as long as the wastes remain hazardous.''
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III. Background

A. No-Migration Variances and Guidance

    An NMV is a formal decision that can be rendered by the EPA in 
response to a petition filed with the Agency, to allow land disposal 
within a particular disposal unit, of specific prohibited waste when it 
has been demonstrated, ``to a reasonable degree of certainty, that 
there will be no migration of hazardous constituents from the disposal 
unit . . . for as long as the wastes remain hazardous.'' \2\ It must be 
demonstrated, to a reasonable degree of certainty, that hazardous 
constituents will not exceed Agency-approved human health-based levels 
(or environmentally protective levels, if they are appropriate) beyond 
the boundary of the disposal unit.\3\ In most cases, the disposal unit 
boundary is defined as the outermost limit of engineered components.\4\
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    \2\ See 51 FR at 40578, November 7, 1986.
    \3\ 57 FR 35941, August 11, 1992.
    \4\ Id.
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    The regulatory requirements for an NMV under the RCRA LDRs were 
codified in 40 CFR 268.6 in 1986,\5\ and EPA issued guidance on these 
requirements in 1992. The 1992 guidance is applicable to landfills, 
surface impoundments, and waste piles. While the 1992 guidance 
acknowledged temporary placement of waste under an approved NMV, it did 
not address the temporary placement of treated waste piles awaiting LDR 
compliance verification within the boundary of a RCRA-permitted 
Subtitle C (hazardous waste) landfill. In this situation, once a 
treated waste pile is confirmed to meet the LDR, it is moved to the 
``working face'' \6\ of the Landfill for final disposal; however, if 
there is an exceedance of an LDR standard, the waste pile is returned 
to the treatment process for further treatment.
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    \5\ 51 FR 40572, November 7, 1986.
    \6\ The working face of a landfill is the area within a specific 
cell where waste is currently being placed and compacted. It is the 
designated section where waste is unloaded and daily cover is 
applied at the end of each working day.
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    Any instance where a waste pile does not meet the applicable LDR 
standards and an NMV has not been granted would violate LDR 
requirements--hazardous waste either must meet the LDR standards or 
have an approved NMV in place. To provide guidance specific to this 
circumstance, the EPA issued ``Information for Petitioners Seeking a 
No-Migration Variance Under the RCRA Land Disposal Restrictions for 
Temporary Placement of Treated Hazardous Waste Within a Permitted 
Subtitle C Landfill'' (88 FR 10894, February 22, 2023) (``2023 
Guidance'') and posted it online at <a href="https://rcrapublic.epa.gov/files/14952.pdf">https://rcrapublic.epa.gov/files/14952.pdf</a>.
    The 2023 guidance acknowledges the need for unique considerations 
when a no migration demonstration for put piles occurs within a 
Subtitle C Landfill prior to permanent disposal in the Landfill. ``EPA 
expects that petitioners will be able to take advantage of existing 
facility information (e.g., existing monitoring, inspections, 
engineered barriers, waste analyses), where appropriate, as part of any 
demonstration . . . For example, the use of temporary barriers, such as 
plastic covers above and below the piles; visual monitoring and prompt 
responses to possible releases; and generally good housekeeping 
practices that ensure the treated waste remains in the pile during the 
temporary storage period would be elements to consider. Attributes of 
the permitted Landfill cell (e.g., design, existing controls, 
monitoring) in which the pile or piles are located should also be 
considered to the extent that they support the demonstration criteria 
being applied to the piles themselves.'' (86 FR 5192, January 19, 
2021).
    Approval of an NMV petition is delegated to the EPA Regional 
Administrator for the EPA Region in which the waste management unit is 
located. States are not authorized to implement the NMV authority; 
however, the EPA consulted with Utah prior to proposing to grant this 
NMV. The final decision will be published in the Federal Register. If 
granted, the term of an NMV may be no longer than the term of the 
existing RCRA Subtitle C permit for the Landfill. Any petitions to 
renew an NMV must undergo notice and comment procedures. An NMV that 
has been issued can be revoked for cause, including any migration of 
hazardous constituents.
    40 CFR 268.6(e) acknowledges the potential for post-approval 
changes in conditions at the no migration unit(s) and/or the 
environment around the no migration unit(s). For purposes of these 
variances, these changes must be reported to the Regional Administrator 
of Region 8 (Region 8 Administrator) if these changes significantly 
depart from the conditions described in the variances and affect the 
potential for migration of hazardous constituents from the units as 
follows:
    1. If Clean Harbors plans to make changes to the unit(s)' design, 
construction, or operation, such a change must be proposed, in writing, 
and include a demonstration to the Region 8 Administrator at least 30 
days prior to making the change. The Region 8 Administrator will 
determine whether the proposed change invalidates the terms of the 
approved variance and will determine the appropriate response. Any 
change must be approved by the Region 8 Administrator prior to being 
made.
    2. If Clean Harbors discovers that a condition at the site which 
was modeled or predicted in the petition does not occur as predicted, 
this change must be reported, in writing, to the Region 8 Administrator 
within 10 days of discovering the change. The Region 8 Administrator 
will determine whether the reported change from the terms of

[[Page 61358]]

the variance requires further action, which may include termination of 
waste acceptance and revocation of the petition, petition 
modifications, or other responses.

B. Clean Harbors' Petition for No Migration Variances

    On July 16, 2024, Clean Harbors' Grassy Mountain facility (Clean 
Harbors) in Tooele County, Utah, submitted an NMV petition to the EPA 
seeking an exemption from the LDR prohibition on placing hazardous 
waste on the ground, if that waste does not meet the prescribed LDR 
standards of 40 CFR 268.40, by demonstrating that for as long as the 
waste remains hazardous, there will be no migration of hazardous 
constituents from the disposal units. Clean Harbors' no migration 
demonstration applies to 250 put piles at any one time located within 
the facility's Subtitle C Landfill cell, known as ``Cell 8,'' Clean 
Harbors also requested that this variance proactively apply to future 
put piles of identical waste characteristics that would be staged in 
future proposed and permitted Subtitle C Landfill cells, known as 
``Cells 9 to 13.''
    While this Notice of Proposal to Grant applies only to those put 
piles placed within existing Landfill Cell 8, upon permit approval of 
Landfill Cells 9, 10, 11, 12, and/or 13, Clean Harbors may submit to 
the Agency, an addendum to this petition to expand this NMV and all of 
its conditions and requirements, to the put piles within the new 
landfill cell(s) if:
    1. Clean Harbors is in compliance with the approved NMV,
    2. The new landfill cell(s) use the same disposal unit engineered 
controls concept (e.g., landfill cell interior berms for run-on and 
run-off control) as approved in this variance,
    3. The duration of temporary placement must remain at six (6) 
months or less and comply with the conditions established herein,
    4. The waste categories remain the same, and
    5. The monitoring program (e.g., groundwater monitoring) is 
expanded to include the new landfill cells.
    In response to EPA requests following the original July 2024 
submission, Clean Harbors provided supplemental information for the 
Agency's evaluation of Clean Harbors' no-migration demonstration. The 
original petition and the response to Agency information requests 
(together referred to as ``the petition'') can be found in the docket 
(EPA-R08-RCRA-2025-0420).
    Clean Harbors' petition included the following components: (a) 
facility description, (b) site characterization, (c) identification and 
characterization of the affected wastes, (d) disposal unit engineered 
controls, (e) duration of temporary staging, (f) air pathway 
mitigation, (g) monitoring program, and (h) uncertainty analysis. These 
are discussed below.

IV. Basis for the EPA's Proposed Determination

A. Components of the Petition

1. Facility Description
    Clean Harbors' Grassy Mountain facility (EPA ID Number: 
UTD991301748) is located three miles East and seven miles north of 
Knolls, Tooele County, Utah. The mean annual precipitation in the 
region is approximately 7.9 inches and 0.5 inches for rain and snow, 
respectively. The permitted facility, which covers an area of 
approximately 640 acres, with an additional 0.5-mile buffer along the 
perimeter, is expected to be in operation for more than ten years. A 
RCRA Part B Permit (hazardous waste permit) was issued by the EPA in 
1998 and later transferred to the State of Utah for subsequent 
renewals. The latest renewal (signed on October 4, 2023) for a 10-year 
term, was issued by the Utah Division of Waste Management and Radiation 
Control.
    Clean Harbors' hazardous waste permit authorizes the facility to 
manage liquid, solid or semisolid hazardous waste and non-hazardous 
industrial waste. The facility has three active hazardous waste 
Landfill cells, two of which are also authorized for disposal of PCB 
waste. Waste treatment services provided at the facility include 
solidification, stabilization and macro/microencapsulation of hazardous 
waste and evaporation of non-hazardous wastewater. Solid, liquid, and 
sludge wastes are accepted in containerized or bulk loads (e.g., roll-
off containers); however, the wastes that would generally be covered 
under this NMV are received as bulk loads.
2. Site Characterization/Unit Description
    Currently, all put piles are temporarily stored in Landfill Cell 8 
until LDR compliance has been confirmed, then compliant piles are moved 
to the working face of Landfill Cell 8. Put piles that fail to meet LDR 
standards are retreated and subsequently returned to a put pile in 
Landfill Cell 8. It is important to note that this variance, if 
approved, will apply to the each put pile and not to Landfill Cell 8. 
As stated in the 2023 guidance, where multiple piles contain the same 
or similar wastes, the petition can address these units as a group 
where such piles are effectively being managed as a single unit. As 
such, the Agency proposes that each of the four categories/groups of 
treated wastes described in the Waste Characterization section below 
will have its own variance; however, each put pile within each 
category/group will be assigned its own unit boundary.
    Each put pile (approximately 35-cubic yards) is placed on a 
polyethylene barrier sheet (20-mil minimum thickness) within Landfill 
Cell 8. Because wastes are treated and presumed to meet LDR standards 
prior to placement in Landfill Cell 8, and storage in the petitioned 
units is temporary, the Agency has established unit boundaries (i.e., 
points of compliance for no-migration purposes) for each of the 
petitioned units to account for existing Landfill controls and 
appropriate deviations from the waste pile liner design standards of 40 
CFR 264.251.
    The Agency proposes that the unit boundaries extend vertically one 
inch below the 20-mil thick polyethylene liner and laterally one foot 
short of the outermost surface edges of the 20-mil thick polyethylene 
liner. Air dispersion compliance will be demonstrated at the outer 
thickness of the Posi-Shell[supreg] liner.
3. Waste Characterization
    In accordance with 40 CFR 268.6(a)(1), Clean Harbors indicated that 
the following four categories/groups of hazardous wastes and their 
underlying hazardous constituents (UHCs) found at 40 CFR 268.48 could 
be temporarily placed in the put piles after treatment to meet LDR 
standards: (1) general metals (D002, D004-D011); (2) cyanide/sulfide 
with metals (D002, D004 through D011, F006 through F012, F019); (3) 
high-chromium wastes (D002, D004 through D011, F006); and (4) ammonia 
(D002, D004-D011). These four waste categories/groups may be stabilized 
via treatment with any combination of the following reagents to prevent 
leaching: cement kiln dust, water, calcium polysulfide, ferrous 
sulfate, and sodium hypochlorite. The stabilization processes performed 
include the LDR technology standards for chemical oxidation (CHOXD), 
neutralization (NEUTR), chemical reduction (CHRED) and deactivation 
(DEACT).
    Clean Harbors' hazardous waste treatment process for the four waste 
categories/groups is found in section 7, ``Waste Treatment Process'' of 
the facility's Waste Analysis Plan (WAP) dated July 25, 2025, available 
on the Utah Department of Environmental

[[Page 61359]]

Quality website at <a href="https://deq.utah.gov/businesses-facilities/rcra-part-b-hazardous-waste-permit-clean-harbors-grassy-mountain-llc">https://deq.utah.gov/businesses-facilities/rcra-part-b-hazardous-waste-permit-clean-harbors-grassy-mountain-llc</a>. The 
following summary cites directly from this WAP. The hazardous waste 
treatment processes include solidification, stabilization and/or 
oxidation/reduction. Solidification is performed on wastes containing 
free liquids. Pozzolans and other appropriate materials are used to 
chemically fix the liquid. This process may also be used to neutralize 
a waste stream and meet the LDR technology standard of neutralizing and 
deactivating. Pre-treatment analyses of the wastes are required to 
determine compatibility with the pozzolanic reactant. The initial 
analysis, including fingerprint analysis, and compatibility testing is 
done prior to treatment. A post-treatment analysis using a paint filter 
test is performed to ensure that all free liquids have been chemically 
reacted, and the mixture is suitable for disposal in the Landfill.
4. Uncertainty Analysis
    40 CFR 268.6(b)(5) requires the petitioner to include an analysis 
to identify and quantify any aspects of the demonstration that 
contribute significantly to uncertainty. The analysis must include an 
evaluation of the consequences of predictable future events, including, 
but not limited to, earthquakes, floods, severe storm events, droughts, 
or other natural phenomena. This analysis has already been performed in 
conjunction with Clean Harbors' approved RCRA Part B permit for the 
broader landfill and as such, the Agency accepts Clean Harbors' 
uncertainty analysis as presented in the petition located in the 
docket.
5. No-Migration Demonstration
    The bases for the EPA's proposed conclusion that Clean Harbors has 
demonstrated to a reasonable degree of certainty that no hazardous 
constituents will migrate from the put piles for as long as the wastes 
remain hazardous are discussed in this section. Although wastes are 
treated with the intent of meeting the RCRA LDR standards prior to 
being placed in put piles, this NMV is a safeguard to ensure that any 
temporary storage of treated hazardous waste complies with statutory 
and regulatory standards, particularly in those instances where a 
treated hazardous waste placed in a temporary waste pile does not meet 
LDR standards. This NMV is conditioned upon the temporary nature of the 
put piles within Landfill Cell 8 and is intended for situations where 
the temporary waste piles are used as part of an overall strategy to 
confirm consistent and compliant treatment that meets the applicable 
LDR treatment standards.
    Where reasonable, the Agency considered existing landfill design 
and operating requirements (40 CFR 264.301) that include run-on and 
run-off controls to prevent the migration of hazardous constituents 
beyond the designated unit boundary. Additional information including 
monitoring data and discussions regarding the temporary nature of these 
put piles (i.e., duration of storage), testing for verification of 
treatment effectiveness, retreatment protocols and engineered controls, 
as referenced in this section, is available in the petition or 
supplemental information in the RCRA regulatory docket for today's 
document.
    i. Treatment effectiveness. As required by 40 CFR 268.6(a)(2), 
Clean Harbors characterized the subject wastes, post-treatment, to 
determine if LDR standards were met. Analytical data was provided for 
January 2022 through March 2024 for each category of hazardous waste. 
Analyses were performed for compliance with the 40 CFR 268.48 Universal 
Treatment Standards (UTS) for all UHCs, including antimony (Sb), 
arsenic (As), barium (Ba), beryllium (Be), cadmium (Cd), chromium (Cr), 
lead (Pb), nickel (Ni), selenium (Se), silver (Ag), thallium (Tl), 
vanadium (V), zinc (Zn), mercury (Hg), and cyanides (CN).
    Clean Harbors provided analytical data indicating that 
approximately 95% of all waste treated met the LDR standards following 
the first treatment procedure, without the need for additional 
treatment; however, in the early 2020's the passing rate decreased, due 
to some wastes having higher than expected concentrations of certain 
constituents. Clean Harbors reanalyzed incoming waste streams to adjust 
their treatment recipe/methods. Continued improvement in treatment 
effectiveness was demonstrated from 2022 to the present. In 2022, 316 
waste piles were treated and analyzed and 282 met post-treatment LDR 
standards, resulting in a net ``pass rate'' of 89.2%. In 2023, 345 
waste piles were treated and analyzed and 317 met post-treatment LDR 
standards (91.9%). From January to March of 2024, 113 waste piles were 
treated and analyzed and 108 met post-treatment LDR standards (95.6%). 
By the end of March 2024, 126 waste piles were treated and analyzed and 
121 met post-treatment LDR standards (96%). The results of these waste 
analyses are summarized in table A-1 of the petition located in the 
docket for today's document.
    The sampling methodology used by Clean Harbors to verify compliance 
with LDR standards for the wastes post-treatment was deemed adequate 
for this NMV because: (1) verification samples were collected in 
accordance with the facility's approved WAP that requires sample(s) be 
collected from each batch of treated waste (see section 7.1 of the WAP: 
one batch is generally equivalent to the volume of one put pile; (2) 
the samples were collected and analyzed over extended periods of time 
to demonstrate long-term compliance history; (3) the treated wastes 
were analyzed for compliance with UTS for UHCs likely to be found in 
the wastes; and (4) pass or fail determinations for LDR compliance were 
presented for all wastes sampled and net pass rates were calculated 
from these determinations as described in the preceding paragraph. The 
current pass rate for temporarily staged subject waste piles exceeds 
95%, demonstrating that these put piles do not routinely receive 
treated wastes that do not meet applicable LDR standards, thereby 
supporting the ``temporary'' nature of storage for each waste category. 
The Agency concludes that Clean Harbors has provided sufficient waste 
characterization information in its petition to support the conclusion 
of treatment effectiveness.
    ii. Duration of temporary storage. When the LDR standard is 
confirmed to ``pass,'' the put pile is moved to the working face of 
Landfill Cell 8 for final disposal generally within 45 days of initial 
placement of the put pile. If the LDR standard ``fails,'' the RCRA 
permit requires the put pile to either be resampled or retreated 
immediately. Resampling consists of two grab samples per batch of waste 
to verify the results of the initial sample. If one or both resamples 
fail, the waste is retreated. If both samples pass, the put pile is 
moved to the working face of Landfill Cell 8 for final disposal. 
Alternatively, after an LDR ``fail,'' Clean Harbors may choose to 
retreat the waste without re-sampling to verify the initial result. 
However, if the failed sample indicates that the concentrations of the 
UHCs are decreasing, possibly due to additional curing, a third 
confirmation sample is collected and analyzed. The end result of a 
multi-stage process for sampling and retreating is that a few waste 
piles may remain temporarily staged even after an LDR fail if the 
analytical data indicates additional curing time is appropriate. Clean 
Harbors requested up to six (6) months duration for temporary staging 
of a put pile to account for the retreatment and curing process. The 
Agency concludes

[[Page 61360]]

that Clean Harbors has provided sufficient analytical data to justify a 
six (6)-month duration for storage of a put pile from the time the pile 
is first staged until final disposal in the working face of the 
Landfill Cell 8.
    iii. Disposal unit engineered controls. This section describes 
existing and proposed put pile liners, put pile covers, and run-off/
run-on controls. Man-made barriers or engineered systems (e.g., liner 
systems) alone generally will not meet the ``no migration'' standard. 
This is not the case for temporary land-based storage of treated waste 
as is being considered in this document. The containment of hazardous 
waste within engineered barriers is considered in making the ``no 
migration'' demonstration for waste awaiting the results of 
verification sampling after treatment, provided that wastes are to be 
removed after a reasonably short storage period that may be 
conservatively projected to be well before the failure of the 
engineered barrier system.\7\ Because Clean Harbors' temporary storage 
for each put pile must not exceed six (6) months, and the lifespan of 
the engineered barriers described below extends into multiple decades 
with appropriate operational controls to prevent rips or tears, 
excluding the Posi-Shell[supreg] system which remains for the duration 
of temporary storage, the Agency concurs that Clean Harbors' use of the 
following barriers will prevent migration of hazardous constituents via 
infiltration, lateral migration (e.g., erosion/surface water 
interaction or movement of infiltration), and air dispersion/
particulate loss.
---------------------------------------------------------------------------

    \7\ No Migration Variances to the Hazardous Waste Land Disposal 
Prohibitions: A Guidance Manual for Petitioners, at 4, EPA Office of 
Solid Waste, July 1992, EPA-530-R92-023.
---------------------------------------------------------------------------

    The put piles will be encapsulated (liner below and Posi-
Shell[supreg] atop) by the unit-specific engineered barriers discussed 
below to prevent migration of hazardous constituents beyond the waste 
pile boundary. These unit-specific barriers are distinct from the 
existing landfill controls, such as run-on and run-off controls, that 
were considered in the overall prevention of migration of hazardous 
constituents.
Liners
    A liner of at least 20-mil thickness polyethylene geomembrane must 
be used as a barrier to vertical and lateral migration for the put 
piles. The liner beneath the pile will provide a barrier for vertical 
migration. The Agency agrees that a minimum of 20-mil thickness barrier 
is sufficient for this temporary application that will last six (6) 
months or less. Because the layout of the put piles is accommodated 
within the standard width of a pre-fabricated geomembrane roll, the 
liner must be one solid piece without the need for welding of seams. 
The lack of seams lends to additional assurance that migration of 
hazardous constituents will not migrate through a broken seam. The 
Agency concludes that a liner of at least 20-mil thickness, in 
conjunction with the inspection program described in the Compliance 
Monitoring Program section, is appropriate for use in this temporary 
disposal scenario; however, there must always be at least 12 inches of 
the liner visible on all sides of the waste pile to prevent potential 
migration of the waste from the edge of the liner.
Covers
    Clean Harbors will use a Posi-Shell[supreg] cover to act as a rain 
and wind barrier for put piles, to ensure no migration of hazardous 
constituents from the waste piles occurs via lateral migration or air 
pathways. Posi-Shell[supreg] is a spray-applied mortar applied as a 
coating to the surface of the put piles, with a minimum cover thickness 
of \3/8\-inch. Because Posi-Shell[supreg] is a mortar, curing is 
necessary to allow it to harden. Curing typically occurs within 12-24 
hours in dry weather, forming a relatively impermeable thin layer of 
durable, hardened mortar. However, if moderate to heavy rainfall occurs 
unexpectedly or is imminent, or if sustained freezing temperatures are 
expected for more than one day or if the temperature falls below 30 
[deg]F, the Posi-Shell[supreg] will not harden sufficiently. During 
these times of inclement weather, Clean Harbors must temporarily cover 
the put piles with polyethylene sheeting of at least 20-mil thickness, 
anchored with sandbags around its edges, until the adverse weather 
conditions abate, and the Posi-Shell[supreg] coating can be applied. 
Within twenty-four (24) hours of weather conditions amenable to Posi-
Shell[supreg] application, Clean Harbors must apply the coating.
    To ensure Posi-Shell[supreg] is appropriate for put pile covering, 
the Agency reviewed several case studies provided by Clean Harbors 
where Posi-Shell[supreg] was demonstrated to prevent erosion, air 
dispersion, infiltration of rainwater, and overall migration of wastes. 
Table 2 in the petition located in the docket summarizes these case 
studies.
    The Agency concludes that Posi-Shell[supreg], or under the limited 
inclement weather circumstances described above, a minimum 20-mil 
polyethylene sheeting cover, will serve as an appropriate barrier to 
protect the put pile from wind dispersion, erosion and rainwater 
infiltration.
Run-On/Run-Off Controls
    Before placing the put piles in the temporary storage area of 
Landfill Cell 8, Clean Harbors must grade the temporary storage area 
where waste piles will be located. The grading must be relatively flat 
but with a slight positive grade to preclude ponding of water on the 
polyethylene liners. If one does not yet exist, a diversion berm of 
sufficient height/width to direct run-on away from the area must be 
constructed upgradient of the staging area. As Landfill Cell 8 is 
filled, if the waste grade changes adjacent to the put pile temporary 
storage area, additional diversion berms must be added, where 
necessary, to divert stormwater run-on and run-off to isolate the 
staging area on the working face of Landfill Cell 8. To control run-
off, in addition to the Posi-shell[supreg] coating, Clean Harbors will 
include depressions in the waste and ditches around the inside 
perimeter of Landfill Cell 8 embankments. In combination with General 
Surrounding Area Engineered Controls described below, these controls 
must be constructed and operated to contain the water volume of a 24-
hour, 100-year storm event.
    iv. General surrounding area engineered controls. All put piles are 
temporarily stored in a designated area of Landfill Cell 8 until LDR 
compliance has been confirmed. The put piles are then moved to the 
working face of Landfill Cell 8. Landfill Cell 8 has a liner system 
consisting of: (1) a bottom 60-mil textured high density polyethylene 
(HDPE) liner atop a 3-foot-thick compacted clay layer with a hydraulic 
conductivity of less than 1.7 x 10-7 cm/sec; (2) a double-sided 
geocomposite leak detection system drainage layer; (3) a top composite 
liner consisting of geosynthetic clay between two 80-mil textured HDPE 
liners; (4) a double-sided geocomposite leak collection system; and (5) 
a 2-foot thick cover layer. Stormwater run-on controls include 
diversion channels and embankments up-gradient and within active 
portions of the Landfill designed to contain a 24-hour, 100-year 
rainfall event.
    v. Groundwater monitoring. Clean Harbors has a groundwater 
monitoring well network at the facility that currently includes four 
(4) upgradient monitoring wells and 56 downgradient monitoring wells. 
In particular, Landfill Cell 8 has five (5) downgradient monitoring 
wells in its proximity. The wells are monitored semi-annually

[[Page 61361]]

under the RCRA detection monitoring program in the facility's RCRA Part 
B permit for the analytes set forth in Attachment VII-3. This 
attachment is in the docket. The Utah Department of Environmental 
Quality reviewed Clean Harbors' groundwater monitoring data and advised 
EPA that no hazardous constituents have been detected above their 
respective health-based levels within the permit cycle.
    vi. Compliance monitoring plan. 40 CFR 268.6(a)(4) requires a 
petition to include a monitoring plan to verify continued compliance 
with the conditions of the NMV. The monitoring plan must be designed to 
detect migration ``at the earliest practicable time.'' The plan must 
include frequent visual monitoring and prompt responses to possible 
releases; and generally good housekeeping practices that ensure the 
treated waste remains in the pile during the temporary storage 
period.\8\ The monitoring plan must also include a discussion of the 
sampling and analysis of the treated waste that determines when the 
temporary waste pile will be moved to the working face of the landfill 
for final disposal.
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    \8\ Information for Petitioners Seeking a No-Migration Variance 
Under the RCRA Land Disposal Restrictions for Temporary Placement of 
Treated Hazardous Waste Within a Permitted Subtitle C Landfill EPA 
Office of Resource Conservation and Recovery, February 2023, <a href="https://rcrapublic.epa.gov/files/14952.pdf">https://rcrapublic.epa.gov/files/14952.pdf</a>.
---------------------------------------------------------------------------

    Clean Harbors must maintain at the facility a put pile monitoring 
plan that includes, at a minimum, components (1-15) below, many of 
which were included by Clean Harbors in the petition and the Agency 
adopts as proposed.
    Deficiencies identified during inspection must be remedied/repaired 
to ensure no migration of hazardous constituents occurs. Deficiencies 
may include but are not limited to: cracking, breakdown or insufficient 
application of the Posi-Shell cover; gaps, tears or holes in plastic 
sheeting utilized for the management of the unit; presence of 
stormwater run-on flow and/or ponded water; visibly exposed waste; poor 
overall pile condition. Deficiencies must be remedied within one (1) 
week of discovery and remedies must be recorded in the facility's 
operating record.
    Deficiencies described by this section must be remedied regardless 
of whether Clean Harbors determines that a migration of hazardous 
constituents has occurred or may have occurred, if LDR compliance 
analyses of the waste in the unit is not yet available. If Clean 
Harbors determines that there has been a migration of hazardous 
constituents from any of the units, or is unable to remedy any 
deficiency within one (1) week of discovery, Clean Harbors must 
immediately suspend receipt of prohibited waste at the put pile and 
notify the Region 8 Administrator, in writing, within ten (10) days of 
the determination that a release has occurred.
    1. Review and tracking of LDR standard ``pass rates'' for put 
piles. To ensure that the waste piles are only being ``temporarily 
stored,'' as described in the February 2023 guidance, if the failure 
rate of the initial verification test for treated put piles exceeds 5% 
in a calendar month, Clean Harbors must conduct a root cause analysis 
and adjust the treatment protocol for the affected category of waste.
    2. Inspection of the temporary staging area for put piles prior to 
deploying the 20-mil polyethylene liner. The underlying area must be 
free of large or rigid objects that may damage the liner.
    3. Observing that the liner is not displaced or damaged during 
placement of the waste piles on the liner to confirm the integrity of 
the liner beneath a waste pile. A damaged liner must be replaced with a 
new liner.
    4. Daily inspection of covered waste piles to verify integrity of 
the liner, cover, and overall pile condition. Inspectors must, at a 
minimum, check for (1) signs of stormwater run-on flow that has or is 
migrating towards a put pile, or other signs of potential for put pile 
erosion, undermining, or washout of the waste encapsulation barriers; 
(2) damage from strong winds, heavy rain, or other extreme weather 
events (e.g., in particular, causing holes, uplift, or other breaches 
in the Posi-Shell[supreg] cover) within 24 hours of such event; (3) 
visible exposed waste; (4) releases of waste (washout/undermining, 
displacement/movement of pile such as shifting or slumping, windblown 
waste particles, etc.); (5) other indications of potential for 
migration or actual observed migration of hazardous constituents from 
the pile (e.g., liquid seeps on the waste pile slopes or emanating from 
its base); and (6) cracks in the Posi-Shell[supreg].
    5. Appropriate Posi-Shell[supreg] application. Adhering to 
inclement weather application prohibitions as recommended by the 
manufacturer. If a waste pile is unable to be immediately covered with 
a Posi-Shell[supreg] (e.g., moderate to heavy rainfall occurs 
unexpectedly or is imminent), the waste pile must be temporarily 
covered with polyethylene sheeting of at least 20-mil thickness and 
anchored with sandbags around its edges until the adverse weather 
conditions abate and the Posi-Shell[supreg] coating can then be 
applied. Posi-Shell[supreg] should not be applied when sustained 
freezing temperatures are expected for more than one day or during 
temperatures below 30 [deg]F.
    6. Verify 100% coverage of Posi-Shell[supreg] is achieved over the 
entire waste pile (no bare or thin spots).
    7. Confirm that the minimum \3/8\-in. thickness of Posi-
Shell[supreg] is achieved.
    8. Confirm that the Posi-Shell[supreg] cover is sufficiently set 
(hardened) before a moderate to heavy rainfall event.
    9. Promptly re-apply Posi-Shell[supreg] cover if any deficiencies 
are identified during application, including but not limited to lack of 
coverage, thickness, or hardening.
    10. Checking for loss of 100% coverage of Posi-Shell[supreg], or 
other signs of cover degradation (imminent potential for loss of 
effectiveness or thickness).
    Landfill Cell 8-specific remediation requirements:
    11. Remove ponded water on the landfill surface that could affect 
the put piles.
    12. Modify, as needed, run-on controls to continue to divert 
surface water around the waste pile staging area.
    13. Maintain or alter, as appropriate, landfill grading to prevent 
put pile run-on.
    14. Isolate the four categories/groups of put piles from each 
other.
    15. Maintain landfill equipment.

V. Conclusion

    The Agency proposes that Clean Harbors has successfully 
demonstrated, to a reasonable degree of certainty, that there will be 
no migration of hazardous constituents beyond the unit boundary for 
treated hazardous wastes temporarily stored in put piles within their 
permitted Subtitle C hazardous waste Landfill Cell 8 while awaiting LDR 
compliance verification.
    Therefore, EPA proposes to grant, with conditions, no-migration 
variances for the four categories/groups of wastes designated herein, 
containing up to 250 put piles at any one time at Clean Harbors' Grassy 
Mountain TSD.

Cyrus M. Western,
Regional Administrator, Region 8.
[FR Doc. 2025-24134 Filed 12-30-25; 8:45 am]
BILLING CODE 6560-50-P


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