Hazardous Waste Management System; Identification and Listing of Hazardous Waste Proposed Rule, 4120-4128 [2023-00835]
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Federal Register / Vol. 88, No. 15 / Tuesday, January 24, 2023 / Proposed Rules
40 CFR Part 70
Environmental protection,
Administrative practice and procedure,
Air pollution control, Intergovernmental
relations, Operating permits, Reporting
and recordkeeping requirements.
Dated: January 12, 2023.
Meghan A. McCollister,
Regional Administrator, Region 7.
40 CFR parts 52 and 70 as set forth
below:
Subpart Q—Iowa
2. In § 52.820, the table in paragraph
(c) is amended by revising the entries
‘‘567–20.2’’, ‘‘567–21.1’’ and ‘‘567–22.1’’
to read as follows:
■
PART 52—APPROVAL AND
PROMULGATION OF
IMPLEMENTATION PLANS
§ 52.820
1. The authority citation for part 52
continues to read as follows:
■
*
Authority: 42 U.S.C. 7401 et seq.
For the reasons stated in the
preamble, the EPA proposes to amend
Identification of plan.
*
*
(c) * * *
*
*
EPA-APPROVED IOWA REGULATIONS
Iowa citation
State effective
date
Title
EPA approval date
Explanation
Iowa Department of Natural Resources Environmental Protection Commission [567]
Chapter 20—Scope of Title–Definitions
*
567–20.2 ...............
*
Definitions .....
*
*
5/11/22
*
*
*
[Date of publication of the final rule in the
Federal Register], [Federal Register citation of the final rule].
*
*
*
*
The definitions for ‘‘anaerobic lagoon,’’
‘‘odor,’’ ‘‘odorous substance,’’ ‘‘odorous
substance source’’ are not SIP approved.
*
*
*
*
*
*
*
Chapter 21—Compliance
567–21.1 ...............
Compliance
Schedule.
*
5/11/22
*
[Date of publication of the final rule in the
Federal Register], [Federal Register citation of the final rule]..
*
*
*
Chapter 22—Controlling Pollution
567–22.1 ...............
Permits Required for
New or Existing Stationary
Sources.
*
*
*
5/11/22
*
*
*
[Date of publication of the final rule in the
Federal Register], [Federal Register citation of the final rule]..
*
*
PART 70—STATE OPERATING PERMIT
PROGRAMS
3. The authority citation for part 70
continues to read as follows:
■
*
*
22.105(2) and 567–22.128(4) on June 3, 2022.
The state effective date is May 11, 2022. The
proposed revision effective date is [date 30
days after date of publication of the final rule
in the Federal Register].
ENVIRONMENTAL PROTECTION
AGENCY
*
[EPA–R06–RCRA–2022–0780; FRL–10237–
01–Region 6]
*
*
*
*
[FR Doc. 2023–00928 Filed 1–23–23; 8:45 am]
Authority: 42 U.S.C. 7401, et seq.
4. Appendix A to part 70 is amended
by adding paragraph (y) under ‘‘Iowa’’
to read as follows:
BILLING CODE 6560–50–P
Hazardous Waste Management
System; Identification and Listing of
Hazardous Waste Proposed Rule
■
tkelley on DSK125TN23PROD with PROPOSALS
40 CFR Part 261
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
Appendix A to Part 70—Approval
Status of State and Local Operating
Permits Programs
AGENCY:
*
SUMMARY:
*
*
*
*
*
*
*
*
The Environmental Protection
Agency (EPA) is proposing to grant an
exclusion from the list of hazardous
wastes to ExxonMobil Baytown Refinery
(EMBR or Petitioner) located in
Baytown, Texas. This action responds to
Iowa
*
(y) The Iowa Department of Natural
Resources submitted for program approval
revisions to rules 567–22.105(1), 567–
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Federal Register / Vol. 88, No. 15 / Tuesday, January 24, 2023 / Proposed Rules
a petition to exclude (or ‘‘delist’’) up to
730 cubic yards per year of sludges
removed from the wastewater treatment
plant (WWTP) from the list of federal
hazardous wastes when disposed of in
a Subtitle D landfill under the Resource
Conservation Recovery Act (RCRA). The
EPA is proposing to grant the petition
based on an evaluation of waste-specific
information provided by Petitioner.
DATES: Comments on this proposed
exclusion must be received by February
23, 2023.
ADDRESSES: Submit your comments by
one of the following methods:
• Federal eRulemaking Portal:
https://www.regulations.gov. Follow the
on-line instructions for submitting
comments.
• Email: shah.harry@epa.gov.
Instructions: The EPA must receive
your comments by February 23, 2023.
Direct your comments to Docket ID
Number EPA–R06–RCRA–2022–0780.
The EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI), or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or email. The
Federal regulations.gov website is an
‘‘anonymous access’’ system, which
means the EPA will not know your
identity or contact information unless
you provide it in the body of your
comment. If you send an email
comment directly to the EPA without
going through regulations.gov, your
email address will be automatically
captured and included as part of the
comment that is placed in the public
docket and made available on the
internet. If you submit an electronic
comment, the EPA recommends that
you include your name and other
contact information in the body of your
comment with any CBI you submit. If
the EPA cannot read your comment due
to technical difficulties and cannot
contact you for clarification, the EPA
may not be able to consider your
comment. Electronic files should avoid
the use of special characters, any form
of encryption and be free of any defects
or viruses.
Docket: The index to the docket for
this action is available electronically at
www.regulations.gov. Although listed in
the index, some information is not
publicly available, e.g., CBI or other
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information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy.
You can view and copy the delisting
petition and associated publicly
available docket materials either
through www.regulations.gov or at: EPA,
Region 6, 1201 Elm Street, Suite 500,
Dallas, Texas 75270. The EPA facility is
open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding
Federal holidays and facility closures
due to COVID–19. The EPA recommend
that you telephone Harry Shah, at (214)
665–6457, before visiting the Region 6
office. Interested persons wanting to
examine these documents should make
an appointment with the office.
FOR FURTHER INFORMATION CONTACT:
Harry Shah, (214) 665–6457,
shah.harry@epa.gov. Out of an
abundance of caution for members of
the public and our staff, the EPA Region
6 office may be closed to the public to
reduce the risk of transmitting COVID–
19. The EPA encourages the public to
submit comments via https://
www.regulations.gov, as there will be a
delay in processing mail and no courier
or hand deliveries will be accepted.
Please call or email the contact listed
above if you need alternative access to
material indexed but not provided in
the docket.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Overview Information
II. Background
A. What is the history of the delisting
program?
B. What is a delisting petition, and what
does it require of a petitioner?
C. What factors must the EPA consider in
deciding whether to grant a delisting
petition?
D. Environmental Justice Evaluation
III. The EPA’s Evaluation of the Waste
Information and Data
A. What waste did the Petitioner petition
the EPA to delist?
B. How did the Petitioner generate the
waste?
C. How did the Petitioner sample and
analyze the petitioned waste?
D. What factors did the EPA consider in
deciding whether to propose to grant the
delisting petition?
E. How did the EPA evaluate the risk of
delisting this waste?
F. What did the EPA conclude?
IV. Conditions for Exclusion
A. How will the Petitioner manage the
waste if it is delisted?
B. What are the maximum allowable
concentrations of hazardous constituents
in the waste?
C. How frequently must the Petitioner test
the waste?
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D. What data must the Petitioner submit?
E. What happens if the Petitioner fails to
meet the conditions of the exclusion?
F. What must the Petitioner do if the
process changes?
V. When would the EPA finalize the
proposed delisting exclusion?
VI. How would this action affect states?
VII. Statutory and Executive Order Reviews
I. Overview Information
The EPA is proposing to grant a May
2021 petition (‘‘F037 Delisting
Petition’’) request submitted by EMBR
in Baytown, Texas to exclude (or
‘‘delist’’) up to 730 cubic yards per year
of F037 WWTP sludge from the list of
federal hazardous waste set forth in 40
CFR 261.3 (hereinafter, all sectional
references are to 40 CFR unless
otherwise indicated) for offsite disposal.
The Petitioner claims that the petitioned
wastes do not meet the criteria for
which the EPA listed it, and that there
are no additional constituents or factors
which could cause the waste to be
hazardous. Based on our review
described in section III, the EPA
propose to approve the petition request,
and allow the delisted waste to be
disposed in a Subtitle D landfill. A copy
of the May 2021 petition is located in
the docket to this proposal action.
II. Background
A. What is the history of the delisting
program?
The EPA published an amended list
of hazardous wastes from non-specific
and specific sources on January 16,
1981, as part of its final and interim
final regulations implementing section
3001 of RCRA. The EPA has amended
this list several times and codifies the
list in §§ 261.31 and 261.32.
The EPA lists the Petitioner’s wastes
as hazardous because: (1) the wastes
typically and frequently exhibit one or
more of the characteristics of hazardous
wastes identified in subpart C of part
261 (that is, ignitability, corrosivity,
reactivity, and toxicity), (2) the wastes
meet the criteria for listing contained in
§ 261.11(a)(2) or (3), or (3) the wastes are
mixed with or derived from the
treatment, storage or disposal of such
characteristic and listed wastes and
which therefore become hazardous
under § 261.3(a)(2)(iv) or (c)(2)(i),
known as the ‘‘mixture’’ or ‘‘derivedfrom’’ rules, respectively.
Individual waste streams may vary,
however, depending on raw materials,
industrial processes, and other factors.
Thus, while a waste described in these
part 261 regulations or resulting from
the operation of the mixture or derivedfrom rules generally is hazardous, a
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Federal Register / Vol. 88, No. 15 / Tuesday, January 24, 2023 / Proposed Rules
specific waste from an individual
facility may not be hazardous.
For this reason, 40 CFR 260.20 and
260.22 provide an exclusion procedure,
called delisting, which allows persons
to prove that the EPA should not
regulate a specific waste from a
particular generating facility as a
hazardous waste.
B. What is a delisting petition, and what
does it require of a petitioner?
A delisting petition is a request from
a facility to the EPA or an authorized
state to exclude wastes from the list of
hazardous wastes. The facility petitions
the EPA because it does not consider the
waste as hazardous under RCRA
regulations.
In a delisting petition, the petitioner
must show that wastes generated at a
particular facility do not meet any of the
criteria for which the waste was listed.
The criteria for which the EPA lists a
waste are in 40 CFR part 261 and further
explained in the background documents
for the listed waste in the June 30, 1992
publication of the ‘‘Final Best
Demonstrated Available Technology
(BDAT) Background Document for
Newly Listed Refinery Wastes F037 and
F038’’ (https://nepis.epa.gov/Exe/
ZyNET.exe/
P100VUGS.TXT?ZyActionD=
ZyDocument&Client=EPA&
Index=1991+Thru+1994&
Docs=&Query=&Time=
&EndTime=&SearchMethod=1&
TocRestrict=n&Toc=&TocEntry=&
QField=&QFieldYear=&QFieldMonth=
&QFieldDay=&IntQ
FieldOp=0&ExtQField
Op=0&XmlQuery=&File=D%3A%5
Czyfiles%5CIndex%20Data%5
C91thru94%5CTxt%5C00000035
%5CP100VUGS.txt&
User=ANONYMOUS&
Password=anonymous&
SortMethod=h%7C-&
MaximumDocuments=
1&FuzzyDegree=0&
ImageQuality=r75g8/r75g8/x150
y150g16/i425&
Display=hpfr&DefSeekPage=x&
SearchBack=
ZyActionL&Back=ZyActionS
&BackDesc=Results%20page
&MaximumPages=1&ZyEntry=1&Seek
Page=x&ZyPURL).
In addition, under 40 CFR 260.22, a
petitioner must prove that the waste
does not exhibit any of the hazardous
waste characteristics (that is,
ignitability, reactivity, corrosivity, and
toxicity) and must present sufficient
information for the EPA to decide
whether factors other than those for
which the waste was listed warrant
retaining it as a hazardous waste.
Generators remain obligated under
RCRA to confirm whether their waste
remains non-hazardous based on the
hazardous waste characteristics even if
the EPA has ‘‘delisted’’ the waste.
C. What factors must the EPA consider
in deciding whether to grant a delisting
petition?
Besides considering the criteria in 40
CFR 260.22(a) and 3001(f) of RCRA, 42
U.S.C. 6921(f), and in the background
documents for the listed wastes, the
EPA must consider any factors
(including additional constituents) aside
from those for which the EPA listed the
waste, if a reasonable basis exists that
these additional factors could cause the
waste to be hazardous.
The EPA must also consider
hazardous waste mixtures containing
listed hazardous wastes and wastes
derived from treating, storing, or
disposing of listed hazardous waste. See
§ 261.3(a)(2)(iii) and (iv) and (c)(2)(i),
called the ‘‘mixture’’ and ‘‘derivedfrom’’ rules, respectively. These wastes
are also eligible for exclusion and
remain hazardous wastes until
excluded. See 66 FR 27266 (May 16,
2001).
D. Environmental Justice Evaluation
To better meet the EPA’s
‘‘responsibilities related to the
protection of public health and the
environment, the EPA has developed a
new environmental justice (EJ) mapping
and screening tool called EJ Screen’’
that reports values as a percentile when
compared to a state or the nation. ‘‘It is
based on nationally consistent data and
an approach that combines
environmental and demographic
indicators in maps and reports,’’
(https://www.epa.gov/ejscreen). The
EPA is providing analysis of
environmental justice associated with
this action. The EPA are doing so for the
purpose of providing information to the
public, not as a basis of our final action.
The EPA utilized EJ Screen to
evaluate potential environmental justice
concerns in communities at one-, three, and five-mile radiuses around the
Baytown facility. The EPA considers the
potential for EJ concerns in a
community when one or more of the 12
EJ indices is at or above the 80th
percentile when compared to the rest of
the USA. At the one-mile radial
measurement, all 12 EJ indices exceeded
the 80th percentile, at the three-mile
measurement, 11 out of the 12 EJ
indices exceeded the 80th percentile,
and at the five-mile radial measurement,
four EJ indices exceeded the 80th
percentile. This information is provided
in Table 1. More information on EJ
Screen, including an explanation of the
12 EJ indices can be found at
www.epa.gov/ejscreen/what-ejscreen.
TABLE 1—EJ INDICES AT ONE-, THREE-, AND FIVE-MILE RADIUSES AROUND THE FACILITY
1 Mile radius
around
the facility
tkelley on DSK125TN23PROD with PROPOSALS
EJ index
(USA percentile)
EJ
EJ
EJ
EJ
EJ
EJ
EJ
EJ
EJ
EJ
EJ
EJ
Index
Index
Index
Index
Index
Index
Index
Index
Index
Index
Index
Index
for
for
for
for
for
for
for
for
for
for
for
for
VerDate Sep<11>2014
Particulate Matter 2.5 ..............................................................................................
Ozone ......................................................................................................................
2017 Diesel Particulate Matter ...............................................................................
2017 Air Toxics Cancer Risk ..................................................................................
2017 Air Toxics Respiratory HI ...............................................................................
Traffic Proximity ......................................................................................................
Lead Paint ...............................................................................................................
Superfund Proximity ................................................................................................
RMP Facility Proximity ............................................................................................
Hazardous Waste Proximity ...................................................................................
Underground Storage Tanks ..................................................................................
Wastewater Discharge ............................................................................................
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86
82
86
95
88
83
84
87
97
86
86
90
24JAP1
3 Mile radius
around
the facility
81
77
82
89
82
81
82
87
94
81
85
87
5 Mile radius
around
the facility
74
72
77
79
75
78
79
84
88
74
81
85
Federal Register / Vol. 88, No. 15 / Tuesday, January 24, 2023 / Proposed Rules
III. The EPA’s Evaluation of the Waste
Information and Data
A. What waste did the Petitioner
petition the EPA to delist?
In May 2021, EMBR petitioned the
EPA to exclude from the list of
hazardous wastes contained in § 261.31,
WWTP solids (F037) generated from its
facility located in Baytown, Texas. The
waste falls under the classification of
listed waste pursuant to § 261.31.
Specifically, in its petition, EMBR
requested that the EPA grant a standard
exclusion for 730 cubic yards per year
of the WWTP solids for offsite disposal.
B. How did the Petitioner generate the
waste?
Per the definition provide in 40 CFR
261.31, an F037 listed hazardous waste
is any sludge generated from the
gravitational separation of oil/water/
solids during the storage or treatment of
process wastewaters and oily cooling
wastewaters from petroleum refineries.
Such sludges also include sludge
generated from gravitational separation
in stormwater units receiving dry
weather flow. The preseparators receive
industrial wastewater generated at the
ExxonMobil Baytown Complex,
comprised of the Baytown Olefins Plant,
Baytown Chemical Plant, and the
Baytown Refinery, as part of the WWTP.
The sludge separates from the process
wastewaters in the primary treatment/
storage systems, making it an F037
waste stream by definition. Under
routine operating conditions, the
primary separation sludge is generated
at the preseparators; however, during
infrequent and isolated times of nonroutine elevated wastewater flows,
temporary storage/conveyance of dry
weather industrial wastewater may
occur in the stormwater impoundments
(e.g. Upper Outfall Canal or Stormwater
Retention Basin) where primary
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separation will occur. The sludge is
collected in the units for removal and
disposal.
C. How did the Petitioner sample and
analyze the petitioned waste?
A total of twelve (3 samples per
month for 4 months) acceptable sample
results were provided by Petitioner to
support the petition. The EPA
considered all 12 samples of the WWTP
solids and the disposal scenario of the
landfill was modeled using the Delisting
Risk Assessment Software. The worstcase scenario of the constituents’
concentrations for the F037 sludge were
used as input in the model to determine
if it would meet the hazardous waste
criteria for which it was listed. The
maximum total and leachate
concentrations for the inorganic and
organic constituents which were found
in the analytical data provided by
Petitioner are presented in Table 2.
TABLE 2—MAXIMUM TOTAL AND TCLP CONCENTRATIONS
Maximum total
concentration
(mg/kg)
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Chemical Name
Acenaphthene ..........................................................................................................................................
Acenapthylene .........................................................................................................................................
Acetone (2-propanone) ............................................................................................................................
Aniline (benzeneamine) ...........................................................................................................................
Anthracene ...............................................................................................................................................
Antimony ..................................................................................................................................................
Arsenic .....................................................................................................................................................
Barium ......................................................................................................................................................
Benz(a)anthracene ..................................................................................................................................
Benzene ...................................................................................................................................................
Benzo(a)pyrene .......................................................................................................................................
Benzo(b)fluoranthene ..............................................................................................................................
Benzo(ghi)perylene ..................................................................................................................................
Benzo(k)fluoranthene ...............................................................................................................................
Beryllium ..................................................................................................................................................
Bis(2-ethylhexyl)phthalate ........................................................................................................................
Cadmium ..................................................................................................................................................
Chromium (III) (Chromic Ion) ...................................................................................................................
Chrysene ..................................................................................................................................................
Cobalt .......................................................................................................................................................
Copper .....................................................................................................................................................
Cresol m- .................................................................................................................................................
Cresol o- ..................................................................................................................................................
Cresol p- ..................................................................................................................................................
DDD .........................................................................................................................................................
DDE .........................................................................................................................................................
DDT p,p′- .................................................................................................................................................
Dibenz(a,h)anthracene ............................................................................................................................
Dibenzofuran ............................................................................................................................................
Dieldrin .....................................................................................................................................................
Dimethylphenol, 2,4- ................................................................................................................................
Diphenylamine .........................................................................................................................................
Endosulfan (Endosulfan I and II,mixture) ................................................................................................
Endrin .......................................................................................................................................................
Ethyl methacrylate ...................................................................................................................................
Ethylbenzene ...........................................................................................................................................
Fluoranthene ............................................................................................................................................
Fluorene ...................................................................................................................................................
HCH, alpha- (Hexachlorocyclohexane alpha-BHC) ................................................................................
HCH, beta- (Hexachlorocyclohexane beta-BHC) ....................................................................................
Heptachlor ................................................................................................................................................
Heptachlor epoxide ..................................................................................................................................
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3.6
2.3
0.12
4.5
0.14
3.17
11.9
221
8.1
0.54
6.9
9.9
4.1
5.8
1.12
0.45
0.494
62.4
11
5.61
127
6.1
16
16
0.013
0.013
0.031
1.1
21
0.0085
3.6
0.47
0.03664
0.025
0.11
2.2
35
27
0.0022
0.32
0.00068
0.033
24JAP1
Maximum TCLP
concentration
(mg/l)
0.0037
0.0003
0.046
0.0014
0.0008
0.0362
0.0486
0.862
0.0003
0.012
0.0004
0.0004
0.0003
0.0007
0.0002
0.0008
0.002
0.151
0.0008
0.0236
0.308
0.026
0.055
0.055
2.00E–05
2.00E–05
2.50E–05
0.0006
0.0015
3.00E–05
0.016
0.01
1.10E–05
3.00E–05
0.02
0.013
0.0004
0.0036
4.90E–05
1.00E–05
1.10E–05
1.00E–05
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Federal Register / Vol. 88, No. 15 / Tuesday, January 24, 2023 / Proposed Rules
TABLE 2—MAXIMUM TOTAL AND TCLP CONCENTRATIONS—Continued
Maximum total
concentration
(mg/kg)
Chemical Name
Indeno (1,2,3-cd) pyrene .........................................................................................................................
Lead .........................................................................................................................................................
Mercury (Fish Pathway Only) ..................................................................................................................
Mercury (Total) ........................................................................................................................................
Methoxychlor ............................................................................................................................................
Methylnapthalene 2- ................................................................................................................................
Naphthalene .............................................................................................................................................
Nickel .......................................................................................................................................................
Nitrosodiphenylamine N- .........................................................................................................................
Phenanthrene ..........................................................................................................................................
Phenol ......................................................................................................................................................
Pyrene ......................................................................................................................................................
Pyridine ....................................................................................................................................................
Selenium ..................................................................................................................................................
Silver ........................................................................................................................................................
Styrene .....................................................................................................................................................
Tetrachlorodibenzo-p-dioxin (TCDD) 2,3,7,8- .........................................................................................
Tin ............................................................................................................................................................
Toluene ....................................................................................................................................................
Trinitrobenzene (Trinitrobenzene 1,3,5-) sym- ........................................................................................
Vanadium .................................................................................................................................................
Xylenes (total) ..........................................................................................................................................
Zinc ..........................................................................................................................................................
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D. What factors did the EPA consider in
deciding whether to propose to grant the
delisting petition?
In reviewing this petition, the EPA
considered the original listing criteria
and the additional factors required by
the Hazardous and Solid Waste
Amendments of 1984 (HSWA). See
section 222 of HSWA, 42 U.S.C. 6921(f),
and 40 CFR 260.22(d)(2) through (4).
The EPA evaluated the petitioned
wastes against the listing criteria and
factors cited in § 261.11(a)(2) and (3).
In addition to the criteria in 40 CFR
260.22(a), 261.11(a)(2) and (3), 42 U.S.C.
6921(f), and in the background
documents for the listed wastes, the
EPA also considered factors (including
additional constituents) other than those
for which the EPA listed the waste to
determine if these additional factors
could cause the waste to be hazardous
(See the background documents).
Our proposed decision to grant the
May 2021 petition to delist the waste
from the Petitioner’s facility in
Baytown, Texas is based on our
evaluation of the wastes for factors or
criteria which could cause the waste to
be hazardous. These factors included:
(1) whether the waste is considered
acutely toxic; (2) the toxicity of the
constituents; (3) the concentration of the
constituents in the waste; (4) the
tendency of the constituents to migrate
and to bioaccumulate; (5) the
persistence in the environment of any
constituents once released from the
waste; (6) plausible and specific types of
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management of the petitioned waste; (7)
the quantity of waste produced; and (8)
waste variability.
The EPA must also consider as
hazardous wastes mixtures containing
listed hazardous wastes and wastes
derived from treating, storing, or
disposing of listed hazardous waste. See
40 CFR 261.3(a)(2)(iv) and (c)(2)(i),
called the ‘‘mixture’’ and ‘‘derivedfrom’’ rules, respectively. Mixture and
derived-from wastes are also eligible for
exclusion but remain hazardous until
excluded.
E. How did the EPA evaluate the risk of
delisting this waste?
For this proposed delisting
determination, the EPA evaluated the
risk that the waste would be disposed of
as a non-hazardous waste in a landfill.
The EPA considered transport of waste
constituents through groundwater,
surface water and air. The EPA
evaluated the Petitioner’s analysis of the
petitioned waste using the Delisting
Risk Assessment Software (DRAS) to
predict the concentration of hazardous
constituents that might be released from
the petitioned waste and to determine if
the waste would pose a threat to human
health and the environment. The DRAS
software and associated documentation
can be found at www.epa.gov/hw/
hazardous-waste-delisting-riskassessment-software-dras.
To predict the potential for release to
groundwater from landfilled wastes and
subsequent routes of exposure to a
receptor, the DRAS uses dilution
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94.3
1.95
1.95
0.0035
55
63
464
0.47
72
20
30
0.43
1.86
0.0688
0.39
2.00E–07
15.1
9.7
0.5
1110
21
871
Maximum TCLP
concentration
(mg/l)
0.0006
0.0747
0.000642
0.000642
0.00015
0.042
0.023
3.38
0.01
0.0051
0.029
0.0003
0.0003
0.0254
0.002
0.01
4.10E–06
0.0289
0.093
0.0006
36.1
0.096
1.61
attenuation factors derived from the
EPA’s Composite Model for leachate
migration with transformation products.
From a release to groundwater, the
DRAS considers routes of exposure to a
human receptor through ingestion of
contaminated groundwater, inhalation
from groundwater while showering and
dermal contact from groundwater while
bathing.
From a release to surface water by
erosion of waste from an open landfill
into storm water run-off, DRAS
evaluates the exposure to a human
receptor by fish ingestion and ingestion
of drinking water. From a release of
waste particles and volatile emissions to
air from the surface of an open landfill,
DRAS considers routes of exposure of
inhalation of volatile constituents,
inhalation of particles, and air
deposition of particles on residential
soil and subsequent ingestion of the
contaminated soil by a child. The
technical support document and the
user’s guide to DRAS are available at
https://www.epa.gov/hw/hazardouswaste-delisting-risk-assessmentsoftware-dras.
F. What did the EPA conclude?
Petitioner stated in its petition that
the petitioned waste meets the criteria
of F037 for which the EPA listed it.
Petitioner also stated that no additional
constituents or factors could cause the
waste to be hazardous. Petitioner also
stated that disposal in a landfill will not
adversely impact human health and the
environment. The EPA’s review of this
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petition included consideration of the
original listing criteria, and the
additional factors required by the
Hazardous and Solid Waste
Amendments of 1984 (HSWA). See
section 3001(f) of RCRA, 42 U.S.C.
6921(f), and § 260.22 (d)(1) through (4).
In making the initial delisting
determination, the EPA evaluated the
petitioned waste against the listing
criteria and factors cited in
§ 261.11(a)(2) and (3). Based on this
review, the EPA agrees with the
Petitioner that the petitioned waste is
nonhazardous with respect to the
original listing criteria. (If the EPA had
found, based on this review, that the
waste remained hazardous based on the
factors for which the waste was
originally listed, the EPA would
propose to deny the petition.) The EPA
evaluated the waste with respect to
other factors or criteria to assess
whether there is a reasonable basis to
believe that such additional factors
could cause the waste to be hazardous.
The EPA considered whether the waste
is acutely toxic, the concentration of the
constituents in the waste, their tendency
to migrate and to bioaccumulate, their
persistence in the environment once
released from the waste, plausible and
specific types of management of the
petitioned waste, the quantities of waste
generated, and waste variability. The
EPA believes that the petitioned waste
does not meet the listing criteria and
thus, should not be a listed waste. The
EPA’s proposed decision to delist the
waste from the Petitioner’s facility is
based on the information submitted in
support of this proposed rule, including
descriptions of the wastes and analytical
data from the Baytown, Texas facility,
and that is contained in the Petition and
attachments, all of which are included
in the docket to this action.
IV. Conditions for Exclusion
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A. How will the Petitioner manage the
waste if it is delisted?
If the petitioned wastes are delisted as
proposed, the Petitioner must dispose of
them in a Subtitle D landfill which is
permitted, licensed, or registered by a
state to manage industrial waste.
B. What are the maximum allowable
concentrations of hazardous
constituents in the waste?
The EPA notes that in some instances
the maximum allowable total
constituent concentrations provided by
the DRAS model exceed 100% of the
waste—these DRAS results are an
artifact of the risk calculations that do
not have physical meaning. In instances
where DRAS predicts a maximum
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constituent greater than 100 percent of
the waste (that is, greater than 1,000,000
mg/kg or mg/L, respectively, for total
and TCLP concentrations), the EPA is
not proposing to require the Petitioner
to perform sampling and analysis for
that constituent and sampling type (total
or TCLP).
C. How frequently must the Petitioner
test the waste?
The testing approach for this waste
stream will be conducted annually
during the second calendar quarter.
Petitioner must conduct annual
sampling and analysis as described in
the delisting sampling and analysis plan
and ensure that the wastes do not
exceed the delisting parameters. If any
measured constituent concentration
exceeds the delisting levels set forth in
Table 2, ExxonMobil must collect an
additional representative sample within
10 business days of being made aware
of the exceedance and test it
expeditiously for the constituent(s)
which exceeded delisting levels in the
original annual sample. If compliance
with the delisting parameters is
demonstrated with analytical testing
(TCLP analysis), the Petitioner may
dispose of the WWTP sludge as a nonhazardous waste. The annual amount of
sludge disposed as delisted waste may
not exceed 730 cubic yards. The annual
sampling report shall include the
volume of sludge disposed of in the
landfill, as well as annual testing event
data. The petitioner should monitor and
report increasing trends of constituents
which will affect the overall compliance
with the discharge permit.
D. What data must the Petitioner
submit?
The Petitioner must submit the data
obtained through verification testing to
U.S. EPA Region 6, Office of Land,
Chemicals and Redevelopment Division,
1201 Elm Street, Suite 500, M/C 6LCR–
RP, Dallas, Texas 75270–2102, within
30 business days after receiving the final
results from the laboratory. These
results may be submitted electronically
to Harry Shah, shah.harry@epa.gov. The
Petitioner must make those records
available for inspection. All data must
be accompanied by a signed copy of the
certification statement in 40 CFR
260.22(i)(12).
E. What happens if the Petitioner fails
to meet the conditions of the exclusion?
If this Petitioner violates the terms
and conditions established in the
exclusion, the EPA may start procedures
to withdraw the exclusion.
Additionally, the terms of the exclusion
provide that ‘‘[a]ny waste volume for
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4125
which representative composite
sampling does not reflect full
compliance with the exclusion criteria
must continue to be managed as
hazardous.’’
If the testing of the waste does not
demonstrate compliance with the
delisting concentrations described in
section IV.C above, or other data
(including but not limited to leachate
data or groundwater monitoring data
from the final land disposal facility)
relevant to the delisted waste indicates
that any constituent is at a
concentration in waste above specified
delisting verification concentrations in
Table 2, the Petitioner must notify the
EPA within 10 business days, or such
later date as the EPA may agree to in
writing, after receiving the final
verification testing results from the
laboratory or of first possessing or being
made aware of other relevant data. The
EPA may require the Petitioner to
conduct additional verification
sampling to better define the particular
volume of wastes within the affected
unit that does not fully satisfy delisting
criteria. For any volume of wastes for
which the corresponding representative
sample(s) do not reflect full compliance
with delisting exclusion levels, the
exclusion by its terms does not apply,
and the waste must be managed as
hazardous.
The EPA has the authority under
RCRA and the Administrative
Procedures Act, 5 U.S.C. 551 (1978) et
seq. to reopen a delisting decision if the
EPA receive new information indicating
that the conditions of this exclusion
have been violated or, are otherwise not
being met.
F. What must the Petitioner do if the
process changes?
Any process changes or additions
implemented at Petitioner’s facility
which would significantly impact the
constituent concentrations of the waste
must be reported to the EPA in
accordance with Condition VI. of the
exclusion language.
V. When would the EPA finalize the
proposed delisting exclusion?
HSWA specifically requires the EPA
to provide notice and an opportunity for
public comment before granting or
denying a final exclusion. Thus, the
EPA will not make a final decision or
grant an exclusion until it has addressed
all timely public comments, including
any at public hearings. Upon receipt
and consideration of all comments, the
EPA will publish its final determination
as a final rule. Since this proposed rule
would reduce the existing requirements
for persons generating hazardous
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wastes, the regulated community does
not need a six-month period to come
into compliance in accordance with
section 3010 of RCRA, as amended by
HSWA.
VI. How would this action affect states?
Because the EPA is proposing to issue
this exclusion under the federal RCRA
delisting regulations, only states subject
to federal RCRA delisting provisions
will be affected. This exclusion may not
be effective in states which have
received authorization from the EPA to
make their own delisting decisions.
RCRA allows states to impose more
stringent regulatory requirements than
RCRA’s under 3009 of RCRA. These
more stringent requirements may
include a provision that prohibits a
federally-issued exclusion from taking
effect in the state. The EPA urge
Petitioners to contact the state
regulatory authority to establish the
status of its wastes under the state law.
The EPA has also authorized some
states to administer a delisting program
in place of the federal program, that is,
to make state delisting decisions.
Therefore, this exclusion does not apply
in those states. If the Petitioner manages
the wastes in any state with delisting
authorization, the Petitioner must obtain
delisting authorization or other
determination from the receiving state
before it can manage the waste as
nonhazardous in that state.
VII. Statutory and Executive Order
Reviews
Additional information about these
statutes and Executive Orders can be
found at https://www2.epa.gov/lawsregulations/laws-and-executive-orders.
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory Review
This proposed action is exempt from
review by the Office of Management and
Budget because it is a rule of particular
applicability, not general applicability.
The proposed action approves a
delisting petition under RCRA for the
petitioned waste at a particular facility.
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B. Executive Order 13771: Reducing
Regulations and Controlling Regulatory
Costs
This proposed action is not an
Executive Order 13771 regulatory action
because actions such as approval of
delisting petitions under RCRA are
exempted under Executive Order 13771
C. Paperwork Reduction Act
This proposed action does not impose
an information collection burden under
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the provisions of the Paperwork
Reduction Act of 1995 (44 U.S.C. 3501
et seq.) because it only applies to a
particular facility.
I. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution or Use
D. Regulatory Flexibility Act
This proposed action is not subject to
Executive Order 13211, because it is not
a significant regulatory action under
Executive Order 13211.
Because this proposed rule is of
particular applicability relating to a
particular facility, it is not subject to the
regulatory flexibility provision of the
Regulatory Flexibility Act (5 U.S.C. 601
et seq.).
E. Unfunded Mandates Reform Act
This proposed action does not contain
any unfunded mandate as described in
the Unfunded Mandates Reform Act (2
U.S.C. 1531–1538) and does not
significantly or uniquely affect small
governments. The action imposes no
new enforceable duty on any state,
local, or tribal governments or the
private sector.
F. Executive Order 13132: Federalism
This proposed action does not have
federalism implications. It will not 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.
G. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
This proposed action does not have
tribal implications as specified in
Executive Order 13175. This proposed
action applies only to a particular
facility on non-tribal land. Thus,
Executive Order 13175 does not apply
to this action.
H. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
This proposed action is not subject to
Executive Order 13045 because it is not
economically significant as defined in
Executive Order 13045 and because the
EPA does not believe the environmental
health or safety risks addressed by this
action present a disproportionate risk to
children. This proposed action’s health
and risk assessments using the EPA’s
Delisting Risk Assessment Software
(DRAS), which considers health and
safety risks to children, are described in
section III.E above. The technical
support document and the user’s guide
for DRAS are included in the docket.
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J. National Technology Transfer and
Advancement Act
This proposed action does not involve
technical standards as described by the
National Technology Transfer and
Advancement Act of 1995 (15 U.S.C.
272 note).
K. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 (59 FR 7629,
Feb. 16, 1994) directs Federal agencies
to identify and address
‘‘disproportionately high and adverse
human health or environmental effects’’
of their actions on minority populations
and low-income populations to the
greatest extent practicable and
permitted by law. The EPA defines
environmental justice (EJ) as ‘‘the fair
treatment and meaningful involvement
of all people regardless of race, color,
national origin, or income with respect
to the development, implementation,
and enforcement of environmental laws,
regulations, and policies.’’ The EPA
further defines the term fair treatment to
mean that ‘‘no group of people should
bear a disproportionate burden of
environmental harms and risks,
including those resulting from the
negative environmental consequences of
industrial, governmental, and
commercial operations or programs and
policies,’’ (https://www.epa.gov/
environmentaljustice/learn-aboutenvironmental-justice).
The EPA believes that this proposed
action does not have disproportionately
high and adverse human health or
environmental effects on minority
populations, low-income populations,
and/or indigenous peoples. The EPA
has determined that this proposed
action will not have disproportionately
high and adverse human health or
environmental effects on minority or
low-income populations because the
petitioned wastes do not meet the
criteria that determines what constitutes
a hazardous waste and there are no
additional constituents or factors which
could cause the waste to be hazardous.
The EPA’s risk assessment, as described
in section III.E above, did not identify
risks from management of this material
in an authorized, solid waste landfill
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(e.g., RCRA Subtitle D landfill,
commercial/industrial solid waste
landfill, etc.). Therefore, the EPA
believes that any populations in
proximity of the landfill(s) used by the
Baytown facility should not be
adversely affected by common waste
management practices for this delisted
waste.
L. Congressional Review Act
This proposed action is exempt from
the Congressional Review Act (5 U.S.C.
801 et seq.) because it is a rule of
particular applicability.
List of Subjects in 40 CFR Part 261
Environmental protection, Hazardous
waste, Recycling, Reporting and
recordkeeping requirements.
Dated: January 9, 2023.
Ronald Crossland,
Director, Land, Chemicals and
Redevelopment Division.
4127
PART 261—IDENTIFICATION AND
LISTING OF HAZARDOUS WASTE
1. The authority citation for part 261
continues to read as follows:
■
Authority: 42 U.S.C. 6905, 6912(a), 6921,
6922, 6924(y) and 6938.
2. Amend Table 1 of Appendix IX to
Part 261 by adding the entry
‘‘ExxonMobil Baytown Refinery’’ in
alphabetical order to read as follows:
■
For the reasons set out in the
preamble, the EPA proposes to amend
40 CFR part 261 as follows:
Appendix IX to Part 261 Wastes
Excluded Under §§ 260.20 and 260.22
TABLE 1—WASTES EXCLUDED FROM NON-SPECIFIC SOURCES
Facility
Address
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*
ExxonMobil Baytown
Refinery.
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Baytown, Texas
16:51 Jan 23, 2023
Waste description
*
*
*
*
*
Wastewater Treatment Plant Sludge (the EPA Hazardous Waste No. F037) maximum delisted amount of 730 cubic
yards per calendar year after (date rule finalized) and disposed in a Subtitle D landfill. ExxonMobil must implement a
verification program that meets the following Paragraphs:
(1) Delisting Levels: All leachable constituent concentrations must not exceed the following levels. The petitioner must
use the method specified in 40 CFR 261.24 to measure constituents in the waste leachate (mg/L). Wastewater Treatment Plant Solids Leachate: Acenaphthene-107; Acetone-5220; Aniline-19.8; Anthracene-260; Antimony-1.23; Arsenic-0.129; Barium-100; Benz(a) anthracene-5.13; Benzene-0.5; Benzo(a)pyrene-1930; Beryllium-1.43; Cadmium1.0; Chromium (III)-5.0; Chrysene-513; Cobalt-2.71; Copper-88.1; Cresol (total)-200; Dibenzofuran-5.91; 2,4Dimethylphenol-114; Diphenylamine-387; Endosulfan-35.9; Endrin-0.05; Ethyl Methacrylate-2030; Ethylbenzene-7.88;
Fluoranthrene-24.7; Fluorene-49.2; Beta HCH-0.0636; Heptachlor-0.008; Heptachlor epoxide-0.008; Lead-5.0; Mercury-0.2; 2-Methylnapthalene-7.29; Naphthalene-0.947; Nickel-136; N-Nitrosodiphenylamine-11.5; Phenol-1740; Pyrene-44.6; Pyridine-5; Selenium-1.0; Silver-5.0; Styrene-15.2; TCDD-467; Toluene-152; 1,3,5-Trinitrobenzene-174;
Vanadium-41.7; Xylenes (total)–86.1; Zinc-1980.
(2) Waste Holding and Handling:
(A) Wastewater treatment plant sludge must be tested annually to assure they have met the concentrations described
in Paragraph (1). Solids that do not meet the concentrations in the original and retest representative sample must be
disposed of as hazardous waste.
(B) Levels of constituents measured in the samples of the solids that do not exceed the levels set forth in Paragraph
(1) are non-hazardous. ExxonMobil can manage and dispose the non-hazardous WWTP solids according to all applicable solid waste regulations.
(C) ExxonMobil must maintain a record of the actual volume of the WWTP solids to be disposed in the Subtitle D landfill according to the requirements in Paragraph (4).
(3) Testing Requirements:
(A) ExxonMobil must test a representative sample of the WWTP sludge for all constituents listed in paragraph (1) at
least once per calendar year. If any measured constituent concentration exceeds the delisting levels set forth in paragraph (1), ExxonMobil must collect an additional representative sample within 10 business days of being made aware
of the exceedance and test it expeditiously for the constituent(s) which exceeded delisting levels in the original annual sample.
(B) The annual testing report should include the total amount of delisted waste in cubic yards disposed during the calendar year.
(4) Changes in Operating Conditions: If ExxonMobil significantly changes the process described in its petition or starts
any processes that may or could affect the composition or type of waste generated as established under Paragraph
(1) (by illustration, but not limitation, changes in equipment or operating conditions of the treatment process), they
must notify the EPA in writing during the annual report; they may no longer handle the wastes generated from the
new process as nonhazardous until the test results of the wastes meet the delisting levels set in Paragraph (1).
(5) Data Submittals: ExxonMobil must submit the information described below. If ExxonMobil fails to submit the required
data within the specified time or maintain the required records on-site for the specified time, the EPA, at its discretion, will consider this sufficient basis to reopen the exclusion as described in Paragraph 5. ExxonMobil must:
(A) Submit the data obtained through Paragraph 3 to the Chief, RCRA Permits & Solid Waste Section, Mail Code,
(6LCR–RP) US EPA Region 6, 1201 Elm Street, Suite 500, Dallas, TX 75270 within the time specified. Data may be
submitted via email to the technical contact for the delisting program.
(B) Compile records of operating conditions and analytical data from Paragraph (3), summarized, and maintained onsite for a minimum of five years.
(C) Furnish these records and data when the EPA or the State of Texas request them for inspection.
(D) Send along with all data, a signed copy of the following certification statement, to attest to the truth and accuracy of
the data submitted: ‘‘Under civil and criminal penalty of law for the making or submission of false or fraudulent statements or representations (pursuant to the applicable provisions of the Federal Code, which include, but may not be
limited to, 18 U.S.C. 1001 and 42 U.S.C. 6928), I certify that the information contained in or accompanying this document is true, accurate and complete. As to the (those) identified section(s) of this document for which I cannot personally verify its (their) truth and accuracy, I certify as the company official having supervisory responsibility for the
persons who, acting under my direct instructions, made the verification that this information is true, accurate and
complete. If any of this information is determined by the EPA in its sole discretion to be false, inaccurate or incomplete, and upon conveyance of this fact to the company, I recognize and agree that this exclusion of waste will be
void as if it never had effect or to the extent directed by the EPA and that the company will be liable for any actions
taken in contravention of the company’s RCRA and CERCLA obligations premised upon the company’s reliance on
the void exclusion.’’
(6) Reopener:
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Federal Register / Vol. 88, No. 15 / Tuesday, January 24, 2023 / Proposed Rules
TABLE 1—WASTES EXCLUDED FROM NON-SPECIFIC SOURCES—Continued
Facility
Address
Waste description
(A) If, any time after disposal of the delisted waste, ExxonMobil possesses or is otherwise made aware of any environmental data (including but not limited to leachate data or ground water monitoring data) or any other data relevant to
the delisted waste indicating that any constituent identified for the delisting verification testing is at level higher than
the delisting level allowed by the Division Director in granting the petition, then the facility must report the data, in
writing, to the Division Director within 10 days of first possessing or being made aware of that data.
(B) If the verification testing of the waste does not meet the delisting requirements in Paragraph 1, ExxonMobil must report the data, in writing, to the Division Director within 10 days of first possessing or being made aware of that data.
(C) If ExxonMobil fails to submit the information described in paragraphs (5), (6)(A) or (6)(B) or if any other information
is received from any source, the Division Director will make a preliminary determination as to whether the reported information requires EPA action to protect human health or the environment. Further action may include suspending, or
revoking the exclusion, or other appropriate response necessary to protect human health and the environment.
(D) If the Division Director determines that the reported information does require EPA action, the Division Director will
notify the facility, in writing, of the actions the Division Director believes are necessary to protect human health and
the environment. The notice shall include a statement of the proposed action and a statement providing the facility
with an opportunity to present information as to why the proposed EPA action is not necessary. The facility shall
have 10 business days from the date of the Division Director’s notice to present such information.
(E) Following the receipt of information from the facility described in paragraph (6)(D) or (if no information is presented
under paragraph (6)(D)) the initial receipt of information described in paragraphs (5), (6)(A) or (6)(B), the Division Director will issue a final written determination describing the EPA actions that are necessary to protect human health
or the environment. Any required action described in the Division Director’s determination shall become effective immediately, unless the Division Director provides otherwise.
(6) Notification Requirements: ExxonMobil must do the following before transporting the delisted waste: Failure to provide this notification will result in a violation of the delisting petition and a possible revocation of the decision.
(A) Provide a one-time written notification to any State Regulatory Agency to which, or through which they will transport
the delisted waste described above for disposal, 60 days before beginning such activities. If ExxonMobil transports
the excluded waste to or manages the waste in any state with delisting authorization, ExxonMobil must obtain
delisting authorization from that state before it can manage the waste as nonhazardous in the state.
(B) Update the one-time written notification if they ship the delisted waste to a different disposal facility.
(C) Failure to provide the notification will result in a violation of the delisting variance and a possible revocation of the
exclusion.
*
*
*
[FR Doc. 2023–00835 Filed 1–23–23; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[Docket No. FWS–R4–ES–2022–0098;
FF09E21000 FXES111109FEDR 234]
RIN 1018–BG85
Endangered and Threatened Wildlife
and Plants; Designation of Critical
Habitat for the Sickle Darter
Fish and Wildlife Service,
Interior.
ACTION: Proposed rule.
AGENCY:
We, the U.S. Fish and
Wildlife Service (Service), propose to
designate critical habitat for the sickle
darter (Percina williamsi) under the
Endangered Species Act of 1973 (Act),
as amended. In total, approximately 104
river miles (168 river kilometers) in
Bledsoe, Blount, Morgan, and Roane
Counties, Tennessee, and Scott, Smyth,
and Washington Counties, Virginia, fall
within the boundaries of the proposed
critical habitat designation. If we
finalize this rule as proposed, it would
extend the Act’s protections to this
species’ critical habitat. We also
announce the availability of a draft
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SUMMARY:
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*
*
economic analysis of the proposed
designation of critical habitat for the
sickle darter.
DATES: We will accept comments
received or postmarked on or before
March 27, 2023. Comments submitted
electronically using the Federal
eRulemaking Portal (see ADDRESSES,
below) must be received by 11:59 p.m.
Eastern Time on the closing date. We
must receive requests for a public
hearing, in writing, at the address
shown in FOR FURTHER INFORMATION
CONTACT by March 10, 2023.
ADDRESSES: Written comments: You may
submit comments by one of the
following methods:
(1) Electronically: Go to the Federal
eRulemaking Portal:
https://www.regulations.gov. In the
Search box, enter FWS–R4–ES–2022–
0098, which is the docket number for
this rulemaking. Then, click on the
Search button. On the resulting page, in
the panel on the left side of the screen,
under the Document Type heading,
check the Proposed Rule box to locate
this document. You may submit a
comment by clicking on ‘‘Comment.’’
(2) By hard copy: Submit by U.S. mail
to: Public Comments Processing, Attn:
FWS–R4–ES–2022–0098, U.S. Fish and
Wildlife Service, MS: PRB/3W, 5275
Leesburg Pike, Falls Church, VA 22041–
3803.
We request that you send comments
only by the methods described above.
PO 00000
Frm 00038
Fmt 4702
Sfmt 4702
*
*
We will post all comments on https://
www.regulations.gov. This generally
means that we will post any personal
information you provide us (see
Information Requested, below, for more
information).
Availability of supporting materials:
For the proposed critical habitat
designation, the coordinates or plot
points or both from which the maps are
generated are included in the decision
file for this critical habitat designation
and are available at https://
www.regulations.gov at Docket No.
FWS–R4–ES–2022–0098 and on the
Service’s website at https://
www.fws.gov/office/tennesseeecological-services. Additional
supporting information that we
developed for this critical habitat
designation will be available on the
Service’s website, at https://
www.regulations.gov, or both.
FOR FURTHER INFORMATION CONTACT:
Daniel Elbert, Field Supervisor, U.S.
Fish and Wildlife Service, Tennessee
Ecological Services Field Office, 446
Neal Street, Cookeville, TN 38501;
telephone 931–528–6481. Individuals in
the United States who are deaf,
deafblind, hard of hearing, or have a
speech disability may dial 711 (TTY,
TDD, or TeleBraille) to access
telecommunications relay services.
Individuals outside the United States
should use the relay services offered
within their country to make
E:\FR\FM\24JAP1.SGM
24JAP1
]]>Agencies
[Federal Register Volume 88, Number 15 (Tuesday, January 24, 2023)]
[Proposed Rules]
[Pages 4120-4128]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2023-00835]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 261
[EPA-R06-RCRA-2022-0780; FRL-10237-01-Region 6]
Hazardous Waste Management System; Identification and Listing of
Hazardous Waste Proposed Rule
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is proposing to
grant an exclusion from the list of hazardous wastes to ExxonMobil
Baytown Refinery (EMBR or Petitioner) located in Baytown, Texas. This
action responds to
[[Page 4121]]
a petition to exclude (or ``delist'') up to 730 cubic yards per year of
sludges removed from the wastewater treatment plant (WWTP) from the
list of federal hazardous wastes when disposed of in a Subtitle D
landfill under the Resource Conservation Recovery Act (RCRA). The EPA
is proposing to grant the petition based on an evaluation of waste-
specific information provided by Petitioner.
DATES: Comments on this proposed exclusion must be received by February
23, 2023.
ADDRESSES: Submit your comments by one of the following methods:
Federal eRulemaking Portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments.
Email: [email protected].
Instructions: The EPA must receive your comments by February 23,
2023. Direct your comments to Docket ID Number EPA-R06-RCRA-2022-0780.
The EPA's policy is that all comments received will be included in the
public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI), or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://www.regulations.gov or email. The Federal regulations.gov website is an
``anonymous access'' system, which means the EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an email comment directly to the EPA without
going through regulations.gov, your email address will be automatically
captured and included as part of the comment that is placed in the
public docket and made available on the internet. If you submit an
electronic comment, the EPA recommends that you include your name and
other contact information in the body of your comment with any CBI you
submit. If the EPA cannot read your comment due to technical
difficulties and cannot contact you for clarification, the EPA may not
be able to consider your comment. Electronic files should avoid the use
of special characters, any form of encryption and be free of any
defects or viruses.
Docket: The index to the docket for this action is available
electronically at www.regulations.gov. Although listed in the index,
some information is not publicly available, e.g., CBI or other
information whose disclosure is restricted by statute. Certain other
material, such as copyrighted material, will be publicly available only
in hard copy.
You can view and copy the delisting petition and associated
publicly available docket materials either through www.regulations.gov
or at: EPA, Region 6, 1201 Elm Street, Suite 500, Dallas, Texas 75270.
The EPA facility is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding Federal holidays and facility closures due to COVID-
19. The EPA recommend that you telephone Harry Shah, at (214) 665-6457,
before visiting the Region 6 office. Interested persons wanting to
examine these documents should make an appointment with the office.
FOR FURTHER INFORMATION CONTACT: Harry Shah, (214) 665-6457,
[email protected]. Out of an abundance of caution for members of the
public and our staff, the EPA Region 6 office may be closed to the
public to reduce the risk of transmitting COVID-19. The EPA encourages
the public to submit comments via https://www.regulations.gov, as there
will be a delay in processing mail and no courier or hand deliveries
will be accepted. Please call or email the contact listed above if you
need alternative access to material indexed but not provided in the
docket.
SUPPLEMENTARY INFORMATION:
Table of Contents
I. Overview Information
II. Background
A. What is the history of the delisting program?
B. What is a delisting petition, and what does it require of a
petitioner?
C. What factors must the EPA consider in deciding whether to
grant a delisting petition?
D. Environmental Justice Evaluation
III. The EPA's Evaluation of the Waste Information and Data
A. What waste did the Petitioner petition the EPA to delist?
B. How did the Petitioner generate the waste?
C. How did the Petitioner sample and analyze the petitioned
waste?
D. What factors did the EPA consider in deciding whether to
propose to grant the delisting petition?
E. How did the EPA evaluate the risk of delisting this waste?
F. What did the EPA conclude?
IV. Conditions for Exclusion
A. How will the Petitioner manage the waste if it is delisted?
B. What are the maximum allowable concentrations of hazardous
constituents in the waste?
C. How frequently must the Petitioner test the waste?
D. What data must the Petitioner submit?
E. What happens if the Petitioner fails to meet the conditions
of the exclusion?
F. What must the Petitioner do if the process changes?
V. When would the EPA finalize the proposed delisting exclusion?
VI. How would this action affect states?
VII. Statutory and Executive Order Reviews
I. Overview Information
The EPA is proposing to grant a May 2021 petition (``F037 Delisting
Petition'') request submitted by EMBR in Baytown, Texas to exclude (or
``delist'') up to 730 cubic yards per year of F037 WWTP sludge from the
list of federal hazardous waste set forth in 40 CFR 261.3 (hereinafter,
all sectional references are to 40 CFR unless otherwise indicated) for
offsite disposal. The Petitioner claims that the petitioned wastes do
not meet the criteria for which the EPA listed it, and that there are
no additional constituents or factors which could cause the waste to be
hazardous. Based on our review described in section III, the EPA
propose to approve the petition request, and allow the delisted waste
to be disposed in a Subtitle D landfill. A copy of the May 2021
petition is located in the docket to this proposal action.
II. Background
A. What is the history of the delisting program?
The EPA published an amended list of hazardous wastes from non-
specific and specific sources on January 16, 1981, as part of its final
and interim final regulations implementing section 3001 of RCRA. The
EPA has amended this list several times and codifies the list in
Sec. Sec. 261.31 and 261.32.
The EPA lists the Petitioner's wastes as hazardous because: (1) the
wastes typically and frequently exhibit one or more of the
characteristics of hazardous wastes identified in subpart C of part 261
(that is, ignitability, corrosivity, reactivity, and toxicity), (2) the
wastes meet the criteria for listing contained in Sec. 261.11(a)(2) or
(3), or (3) the wastes are mixed with or derived from the treatment,
storage or disposal of such characteristic and listed wastes and which
therefore become hazardous under Sec. 261.3(a)(2)(iv) or (c)(2)(i),
known as the ``mixture'' or ``derived-from'' rules, respectively.
Individual waste streams may vary, however, depending on raw
materials, industrial processes, and other factors. Thus, while a waste
described in these part 261 regulations or resulting from the operation
of the mixture or derived-from rules generally is hazardous, a
[[Page 4122]]
specific waste from an individual facility may not be hazardous.
For this reason, 40 CFR 260.20 and 260.22 provide an exclusion
procedure, called delisting, which allows persons to prove that the EPA
should not regulate a specific waste from a particular generating
facility as a hazardous waste.
B. What is a delisting petition, and what does it require of a
petitioner?
A delisting petition is a request from a facility to the EPA or an
authorized state to exclude wastes from the list of hazardous wastes.
The facility petitions the EPA because it does not consider the waste
as hazardous under RCRA regulations.
In a delisting petition, the petitioner must show that wastes
generated at a particular facility do not meet any of the criteria for
which the waste was listed. The criteria for which the EPA lists a
waste are in 40 CFR part 261 and further explained in the background
documents for the listed waste in the June 30, 1992 publication of the
``Final Best Demonstrated Available Technology (BDAT) Background
Document for Newly Listed Refinery Wastes F037 and F038'' (https://nepis.epa.gov/Exe/ZyNET.exe/P100VUGS.TXT?ZyActionD=ZyDocument&Client=EPA&Index=1991+Thru+1994&Docs=&Query=&Time=&EndTime=&SearchMethod=1&TocRestrict=n&Toc=&TocEntry=&QField=&QFieldYear=&QFieldMonth=&QFieldDay=&IntQFieldOp=0&ExtQFieldOp=0&XmlQuery=&File=D%3A%5Czyfiles%5CIndex%20Data%5C91thru94%5CTxt%5C00000035%5CP100VUGS.txt&User=ANONYMOUS&Password=anonymous&SortMethod=h%7C-&MaximumDocuments=1&FuzzyDegree=0&ImageQuality=r75g8/r75g8/x150y150g16/i425&Display=hpfr&DefSeekPage=x&SearchBack=ZyActionL&Back=ZyActionS&BackDesc=Results%20page&MaximumPages=1&ZyEntry=1&SeekPage=x&ZyPURL).
In addition, under 40 CFR 260.22, a petitioner must prove that the
waste does not exhibit any of the hazardous waste characteristics (that
is, ignitability, reactivity, corrosivity, and toxicity) and must
present sufficient information for the EPA to decide whether factors
other than those for which the waste was listed warrant retaining it as
a hazardous waste.
Generators remain obligated under RCRA to confirm whether their
waste remains non-hazardous based on the hazardous waste
characteristics even if the EPA has ``delisted'' the waste.
C. What factors must the EPA consider in deciding whether to grant a
delisting petition?
Besides considering the criteria in 40 CFR 260.22(a) and 3001(f) of
RCRA, 42 U.S.C. 6921(f), and in the background documents for the listed
wastes, the EPA must consider any factors (including additional
constituents) aside from those for which the EPA listed the waste, if a
reasonable basis exists that these additional factors could cause the
waste to be hazardous.
The EPA must also consider hazardous waste mixtures containing
listed hazardous wastes and wastes derived from treating, storing, or
disposing of listed hazardous waste. See Sec. 261.3(a)(2)(iii) and
(iv) and (c)(2)(i), called the ``mixture'' and ``derived-from'' rules,
respectively. These wastes are also eligible for exclusion and remain
hazardous wastes until excluded. See 66 FR 27266 (May 16, 2001).
D. Environmental Justice Evaluation
To better meet the EPA's ``responsibilities related to the
protection of public health and the environment, the EPA has developed
a new environmental justice (EJ) mapping and screening tool called EJ
Screen'' that reports values as a percentile when compared to a state
or the nation. ``It is based on nationally consistent data and an
approach that combines environmental and demographic indicators in maps
and reports,'' (https://www.epa.gov/ejscreen). The EPA is providing
analysis of environmental justice associated with this action. The EPA
are doing so for the purpose of providing information to the public,
not as a basis of our final action.
The EPA utilized EJ Screen to evaluate potential environmental
justice concerns in communities at one-, three-, and five-mile radiuses
around the Baytown facility. The EPA considers the potential for EJ
concerns in a community when one or more of the 12 EJ indices is at or
above the 80th percentile when compared to the rest of the USA. At the
one-mile radial measurement, all 12 EJ indices exceeded the 80th
percentile, at the three-mile measurement, 11 out of the 12 EJ indices
exceeded the 80th percentile, and at the five-mile radial measurement,
four EJ indices exceeded the 80th percentile. This information is
provided in Table 1. More information on EJ Screen, including an
explanation of the 12 EJ indices can be found at www.epa.gov/ejscreen/what-ejscreen.
Table 1--EJ Indices at One-, Three-, and Five-Mile Radiuses Around the Facility
----------------------------------------------------------------------------------------------------------------
1 Mile radius 3 Mile radius 5 Mile radius
EJ index (USA percentile) around the around the around the
facility facility facility
----------------------------------------------------------------------------------------------------------------
EJ Index for Particulate Matter 2.5............................. 86 81 74
EJ Index for Ozone.............................................. 82 77 72
EJ Index for 2017 Diesel Particulate Matter..................... 86 82 77
EJ Index for 2017 Air Toxics Cancer Risk........................ 95 89 79
EJ Index for 2017 Air Toxics Respiratory HI..................... 88 82 75
EJ Index for Traffic Proximity.................................. 83 81 78
EJ Index for Lead Paint......................................... 84 82 79
EJ Index for Superfund Proximity................................ 87 87 84
EJ Index for RMP Facility Proximity............................. 97 94 88
EJ Index for Hazardous Waste Proximity.......................... 86 81 74
EJ Index for Underground Storage Tanks.......................... 86 85 81
EJ Index for Wastewater Discharge............................... 90 87 85
----------------------------------------------------------------------------------------------------------------
[[Page 4123]]
III. The EPA's Evaluation of the Waste Information and Data
A. What waste did the Petitioner petition the EPA to delist?
In May 2021, EMBR petitioned the EPA to exclude from the list of
hazardous wastes contained in Sec. 261.31, WWTP solids (F037)
generated from its facility located in Baytown, Texas. The waste falls
under the classification of listed waste pursuant to Sec. 261.31.
Specifically, in its petition, EMBR requested that the EPA grant a
standard exclusion for 730 cubic yards per year of the WWTP solids for
offsite disposal.
B. How did the Petitioner generate the waste?
Per the definition provide in 40 CFR 261.31, an F037 listed
hazardous waste is any sludge generated from the gravitational
separation of oil/water/solids during the storage or treatment of
process wastewaters and oily cooling wastewaters from petroleum
refineries. Such sludges also include sludge generated from
gravitational separation in stormwater units receiving dry weather
flow. The preseparators receive industrial wastewater generated at the
ExxonMobil Baytown Complex, comprised of the Baytown Olefins Plant,
Baytown Chemical Plant, and the Baytown Refinery, as part of the WWTP.
The sludge separates from the process wastewaters in the primary
treatment/storage systems, making it an F037 waste stream by
definition. Under routine operating conditions, the primary separation
sludge is generated at the preseparators; however, during infrequent
and isolated times of non-routine elevated wastewater flows, temporary
storage/conveyance of dry weather industrial wastewater may occur in
the stormwater impoundments (e.g. Upper Outfall Canal or Stormwater
Retention Basin) where primary separation will occur. The sludge is
collected in the units for removal and disposal.
C. How did the Petitioner sample and analyze the petitioned waste?
A total of twelve (3 samples per month for 4 months) acceptable
sample results were provided by Petitioner to support the petition. The
EPA considered all 12 samples of the WWTP solids and the disposal
scenario of the landfill was modeled using the Delisting Risk
Assessment Software. The worst-case scenario of the constituents'
concentrations for the F037 sludge were used as input in the model to
determine if it would meet the hazardous waste criteria for which it
was listed. The maximum total and leachate concentrations for the
inorganic and organic constituents which were found in the analytical
data provided by Petitioner are presented in Table 2.
Table 2--Maximum Total and TCLP Concentrations
------------------------------------------------------------------------
Maximum total Maximum TCLP
Chemical Name concentration (mg/ concentration (mg/
kg) l)
------------------------------------------------------------------------
Acenaphthene.................... 3.6 0.0037
Acenapthylene................... 2.3 0.0003
Acetone (2-propanone)........... 0.12 0.046
Aniline (benzeneamine).......... 4.5 0.0014
Anthracene...................... 0.14 0.0008
Antimony........................ 3.17 0.0362
Arsenic......................... 11.9 0.0486
Barium.......................... 221 0.862
Benz(a)anthracene............... 8.1 0.0003
Benzene......................... 0.54 0.012
Benzo(a)pyrene.................. 6.9 0.0004
Benzo(b)fluoranthene............ 9.9 0.0004
Benzo(ghi)perylene.............. 4.1 0.0003
Benzo(k)fluoranthene............ 5.8 0.0007
Beryllium....................... 1.12 0.0002
Bis(2-ethylhexyl)phthalate...... 0.45 0.0008
Cadmium......................... 0.494 0.002
Chromium (III) (Chromic Ion).... 62.4 0.151
Chrysene........................ 11 0.0008
Cobalt.......................... 5.61 0.0236
Copper.......................... 127 0.308
Cresol m-....................... 6.1 0.026
Cresol o-....................... 16 0.055
Cresol p-....................... 16 0.055
DDD............................. 0.013 2.00E-05
DDE............................. 0.013 2.00E-05
DDT p,p'-....................... 0.031 2.50E-05
Dibenz(a,h)anthracene........... 1.1 0.0006
Dibenzofuran.................... 21 0.0015
Dieldrin........................ 0.0085 3.00E-05
Dimethylphenol, 2,4-............ 3.6 0.016
Diphenylamine................... 0.47 0.01
Endosulfan (Endosulfan I and 0.03664 1.10E-05
II,mixture)....................
Endrin.......................... 0.025 3.00E-05
Ethyl methacrylate.............. 0.11 0.02
Ethylbenzene.................... 2.2 0.013
Fluoranthene.................... 35 0.0004
Fluorene........................ 27 0.0036
HCH, alpha- 0.0022 4.90E-05
(Hexachlorocyclohexane alpha-
BHC)...........................
HCH, beta- 0.32 1.00E-05
(Hexachlorocyclohexane beta-
BHC)...........................
Heptachlor...................... 0.00068 1.10E-05
Heptachlor epoxide.............. 0.033 1.00E-05
[[Page 4124]]
Indeno (1,2,3-cd) pyrene........ 3.8 0.0006
Lead............................ 94.3 0.0747
Mercury (Fish Pathway Only)..... 1.95 0.000642
Mercury (Total)................. 1.95 0.000642
Methoxychlor.................... 0.0035 0.00015
Methylnapthalene 2-............. 55 0.042
Naphthalene..................... 63 0.023
Nickel.......................... 464 3.38
Nitrosodiphenylamine N-......... 0.47 0.01
Phenanthrene.................... 72 0.0051
Phenol.......................... 20 0.029
Pyrene.......................... 30 0.0003
Pyridine........................ 0.43 0.0003
Selenium........................ 1.86 0.0254
Silver.......................... 0.0688 0.002
Styrene......................... 0.39 0.01
Tetrachlorodibenzo-p-dioxin 2.00E-07 4.10E-06
(TCDD) 2,3,7,8-................
Tin............................. 15.1 0.0289
Toluene......................... 9.7 0.093
Trinitrobenzene (Trinitrobenzene 0.5 0.0006
1,3,5-) sym-...................
Vanadium........................ 1110 36.1
Xylenes (total)................. 21 0.096
Zinc............................ 871 1.61
------------------------------------------------------------------------
D. What factors did the EPA consider in deciding whether to propose to
grant the delisting petition?
In reviewing this petition, the EPA considered the original listing
criteria and the additional factors required by the Hazardous and Solid
Waste Amendments of 1984 (HSWA). See section 222 of HSWA, 42 U.S.C.
6921(f), and 40 CFR 260.22(d)(2) through (4). The EPA evaluated the
petitioned wastes against the listing criteria and factors cited in
Sec. 261.11(a)(2) and (3).
In addition to the criteria in 40 CFR 260.22(a), 261.11(a)(2) and
(3), 42 U.S.C. 6921(f), and in the background documents for the listed
wastes, the EPA also considered factors (including additional
constituents) other than those for which the EPA listed the waste to
determine if these additional factors could cause the waste to be
hazardous (See the background documents).
Our proposed decision to grant the May 2021 petition to delist the
waste from the Petitioner's facility in Baytown, Texas is based on our
evaluation of the wastes for factors or criteria which could cause the
waste to be hazardous. These factors included: (1) whether the waste is
considered acutely toxic; (2) the toxicity of the constituents; (3) the
concentration of the constituents in the waste; (4) the tendency of the
constituents to migrate and to bioaccumulate; (5) the persistence in
the environment of any constituents once released from the waste; (6)
plausible and specific types of management of the petitioned waste; (7)
the quantity of waste produced; and (8) waste variability.
The EPA must also consider as hazardous wastes mixtures containing
listed hazardous wastes and wastes derived from treating, storing, or
disposing of listed hazardous waste. See 40 CFR 261.3(a)(2)(iv) and
(c)(2)(i), called the ``mixture'' and ``derived-from'' rules,
respectively. Mixture and derived-from wastes are also eligible for
exclusion but remain hazardous until excluded.
E. How did the EPA evaluate the risk of delisting this waste?
For this proposed delisting determination, the EPA evaluated the
risk that the waste would be disposed of as a non-hazardous waste in a
landfill. The EPA considered transport of waste constituents through
groundwater, surface water and air. The EPA evaluated the Petitioner's
analysis of the petitioned waste using the Delisting Risk Assessment
Software (DRAS) to predict the concentration of hazardous constituents
that might be released from the petitioned waste and to determine if
the waste would pose a threat to human health and the environment. The
DRAS software and associated documentation can be found at www.epa.gov/hw/hazardous-waste-delisting-risk-assessment-software-dras.
To predict the potential for release to groundwater from landfilled
wastes and subsequent routes of exposure to a receptor, the DRAS uses
dilution attenuation factors derived from the EPA's Composite Model for
leachate migration with transformation products. From a release to
groundwater, the DRAS considers routes of exposure to a human receptor
through ingestion of contaminated groundwater, inhalation from
groundwater while showering and dermal contact from groundwater while
bathing.
From a release to surface water by erosion of waste from an open
landfill into storm water run-off, DRAS evaluates the exposure to a
human receptor by fish ingestion and ingestion of drinking water. From
a release of waste particles and volatile emissions to air from the
surface of an open landfill, DRAS considers routes of exposure of
inhalation of volatile constituents, inhalation of particles, and air
deposition of particles on residential soil and subsequent ingestion of
the contaminated soil by a child. The technical support document and
the user's guide to DRAS are available at https://www.epa.gov/hw/hazardous-waste-delisting-risk-assessment-software-dras.
F. What did the EPA conclude?
Petitioner stated in its petition that the petitioned waste meets
the criteria of F037 for which the EPA listed it. Petitioner also
stated that no additional constituents or factors could cause the waste
to be hazardous. Petitioner also stated that disposal in a landfill
will not adversely impact human health and the environment. The EPA's
review of this
[[Page 4125]]
petition included consideration of the original listing criteria, and
the additional factors required by the Hazardous and Solid Waste
Amendments of 1984 (HSWA). See section 3001(f) of RCRA, 42 U.S.C.
6921(f), and Sec. 260.22 (d)(1) through (4). In making the initial
delisting determination, the EPA evaluated the petitioned waste against
the listing criteria and factors cited in Sec. 261.11(a)(2) and (3).
Based on this review, the EPA agrees with the Petitioner that the
petitioned waste is nonhazardous with respect to the original listing
criteria. (If the EPA had found, based on this review, that the waste
remained hazardous based on the factors for which the waste was
originally listed, the EPA would propose to deny the petition.) The EPA
evaluated the waste with respect to other factors or criteria to assess
whether there is a reasonable basis to believe that such additional
factors could cause the waste to be hazardous. The EPA considered
whether the waste is acutely toxic, the concentration of the
constituents in the waste, their tendency to migrate and to
bioaccumulate, their persistence in the environment once released from
the waste, plausible and specific types of management of the petitioned
waste, the quantities of waste generated, and waste variability. The
EPA believes that the petitioned waste does not meet the listing
criteria and thus, should not be a listed waste. The EPA's proposed
decision to delist the waste from the Petitioner's facility is based on
the information submitted in support of this proposed rule, including
descriptions of the wastes and analytical data from the Baytown, Texas
facility, and that is contained in the Petition and attachments, all of
which are included in the docket to this action.
IV. Conditions for Exclusion
A. How will the Petitioner manage the waste if it is delisted?
If the petitioned wastes are delisted as proposed, the Petitioner
must dispose of them in a Subtitle D landfill which is permitted,
licensed, or registered by a state to manage industrial waste.
B. What are the maximum allowable concentrations of hazardous
constituents in the waste?
The EPA notes that in some instances the maximum allowable total
constituent concentrations provided by the DRAS model exceed 100% of
the waste--these DRAS results are an artifact of the risk calculations
that do not have physical meaning. In instances where DRAS predicts a
maximum constituent greater than 100 percent of the waste (that is,
greater than 1,000,000 mg/kg or mg/L, respectively, for total and TCLP
concentrations), the EPA is not proposing to require the Petitioner to
perform sampling and analysis for that constituent and sampling type
(total or TCLP).
C. How frequently must the Petitioner test the waste?
The testing approach for this waste stream will be conducted
annually during the second calendar quarter. Petitioner must conduct
annual sampling and analysis as described in the delisting sampling and
analysis plan and ensure that the wastes do not exceed the delisting
parameters. If any measured constituent concentration exceeds the
delisting levels set forth in Table 2, ExxonMobil must collect an
additional representative sample within 10 business days of being made
aware of the exceedance and test it expeditiously for the
constituent(s) which exceeded delisting levels in the original annual
sample. If compliance with the delisting parameters is demonstrated
with analytical testing (TCLP analysis), the Petitioner may dispose of
the WWTP sludge as a non-hazardous waste. The annual amount of sludge
disposed as delisted waste may not exceed 730 cubic yards. The annual
sampling report shall include the volume of sludge disposed of in the
landfill, as well as annual testing event data. The petitioner should
monitor and report increasing trends of constituents which will affect
the overall compliance with the discharge permit.
D. What data must the Petitioner submit?
The Petitioner must submit the data obtained through verification
testing to U.S. EPA Region 6, Office of Land, Chemicals and
Redevelopment Division, 1201 Elm Street, Suite 500, M/C 6LCR-RP,
Dallas, Texas 75270-2102, within 30 business days after receiving the
final results from the laboratory. These results may be submitted
electronically to Harry Shah, [email protected]. The Petitioner must
make those records available for inspection. All data must be
accompanied by a signed copy of the certification statement in 40 CFR
260.22(i)(12).
E. What happens if the Petitioner fails to meet the conditions of the
exclusion?
If this Petitioner violates the terms and conditions established in
the exclusion, the EPA may start procedures to withdraw the exclusion.
Additionally, the terms of the exclusion provide that ``[a]ny waste
volume for which representative composite sampling does not reflect
full compliance with the exclusion criteria must continue to be managed
as hazardous.''
If the testing of the waste does not demonstrate compliance with
the delisting concentrations described in section IV.C above, or other
data (including but not limited to leachate data or groundwater
monitoring data from the final land disposal facility) relevant to the
delisted waste indicates that any constituent is at a concentration in
waste above specified delisting verification concentrations in Table 2,
the Petitioner must notify the EPA within 10 business days, or such
later date as the EPA may agree to in writing, after receiving the
final verification testing results from the laboratory or of first
possessing or being made aware of other relevant data. The EPA may
require the Petitioner to conduct additional verification sampling to
better define the particular volume of wastes within the affected unit
that does not fully satisfy delisting criteria. For any volume of
wastes for which the corresponding representative sample(s) do not
reflect full compliance with delisting exclusion levels, the exclusion
by its terms does not apply, and the waste must be managed as
hazardous.
The EPA has the authority under RCRA and the Administrative
Procedures Act, 5 U.S.C. 551 (1978) et seq. to reopen a delisting
decision if the EPA receive new information indicating that the
conditions of this exclusion have been violated or, are otherwise not
being met.
F. What must the Petitioner do if the process changes?
Any process changes or additions implemented at Petitioner's
facility which would significantly impact the constituent
concentrations of the waste must be reported to the EPA in accordance
with Condition VI. of the exclusion language.
V. When would the EPA finalize the proposed delisting exclusion?
HSWA specifically requires the EPA to provide notice and an
opportunity for public comment before granting or denying a final
exclusion. Thus, the EPA will not make a final decision or grant an
exclusion until it has addressed all timely public comments, including
any at public hearings. Upon receipt and consideration of all comments,
the EPA will publish its final determination as a final rule. Since
this proposed rule would reduce the existing requirements for persons
generating hazardous
[[Page 4126]]
wastes, the regulated community does not need a six-month period to
come into compliance in accordance with section 3010 of RCRA, as
amended by HSWA.
VI. How would this action affect states?
Because the EPA is proposing to issue this exclusion under the
federal RCRA delisting regulations, only states subject to federal RCRA
delisting provisions will be affected. This exclusion may not be
effective in states which have received authorization from the EPA to
make their own delisting decisions.
RCRA allows states to impose more stringent regulatory requirements
than RCRA's under 3009 of RCRA. These more stringent requirements may
include a provision that prohibits a federally-issued exclusion from
taking effect in the state. The EPA urge Petitioners to contact the
state regulatory authority to establish the status of its wastes under
the state law.
The EPA has also authorized some states to administer a delisting
program in place of the federal program, that is, to make state
delisting decisions. Therefore, this exclusion does not apply in those
states. If the Petitioner manages the wastes in any state with
delisting authorization, the Petitioner must obtain delisting
authorization or other determination from the receiving state before it
can manage the waste as nonhazardous in that state.
VII. Statutory and Executive Order Reviews
Additional information about these statutes and Executive Orders
can be found at https://www2.epa.gov/laws-regulations/laws-and-executive-orders.
A. Executive Order 12866: Regulatory Planning and Review and Executive
Order 13563: Improving Regulation and Regulatory Review
This proposed action is exempt from review by the Office of
Management and Budget because it is a rule of particular applicability,
not general applicability. The proposed action approves a delisting
petition under RCRA for the petitioned waste at a particular facility.
B. Executive Order 13771: Reducing Regulations and Controlling
Regulatory Costs
This proposed action is not an Executive Order 13771 regulatory
action because actions such as approval of delisting petitions under
RCRA are exempted under Executive Order 13771
C. Paperwork Reduction Act
This proposed action does not impose an information collection
burden under the provisions of the Paperwork Reduction Act of 1995 (44
U.S.C. 3501 et seq.) because it only applies to a particular facility.
D. Regulatory Flexibility Act
Because this proposed rule is of particular applicability relating
to a particular facility, it is not subject to the regulatory
flexibility provision of the Regulatory Flexibility Act (5 U.S.C. 601
et seq.).
E. Unfunded Mandates Reform Act
This proposed action does not contain any unfunded mandate as
described in the Unfunded Mandates Reform Act (2 U.S.C. 1531-1538) and
does not significantly or uniquely affect small governments. The action
imposes no new enforceable duty on any state, local, or tribal
governments or the private sector.
F. Executive Order 13132: Federalism
This proposed action does not have federalism implications. It will
not 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.
G. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
This proposed action does not have tribal implications as specified
in Executive Order 13175. This proposed action applies only to a
particular facility on non-tribal land. Thus, Executive Order 13175
does not apply to this action.
H. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
This proposed action is not subject to Executive Order 13045
because it is not economically significant as defined in Executive
Order 13045 and because the EPA does not believe the environmental
health or safety risks addressed by this action present a
disproportionate risk to children. This proposed action's health and
risk assessments using the EPA's Delisting Risk Assessment Software
(DRAS), which considers health and safety risks to children, are
described in section III.E above. The technical support document and
the user's guide for DRAS are included in the docket.
I. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution or Use
This proposed action is not subject to Executive Order 13211,
because it is not a significant regulatory action under Executive Order
13211.
J. National Technology Transfer and Advancement Act
This proposed action does not involve technical standards as
described by the National Technology Transfer and Advancement Act of
1995 (15 U.S.C. 272 note).
K. Executive Order 12898: Federal Actions To Address Environmental
Justice in Minority Populations and Low-Income Populations
Executive Order 12898 (59 FR 7629, Feb. 16, 1994) directs Federal
agencies to identify and address ``disproportionately high and adverse
human health or environmental effects'' of their actions on minority
populations and low-income populations to the greatest extent
practicable and permitted by law. The EPA defines environmental justice
(EJ) as ``the fair treatment and meaningful involvement of all people
regardless of race, color, national origin, or income with respect to
the development, implementation, and enforcement of environmental laws,
regulations, and policies.'' The EPA further defines the term fair
treatment to mean that ``no group of people should bear a
disproportionate burden of environmental harms and risks, including
those resulting from the negative environmental consequences of
industrial, governmental, and commercial operations or programs and
policies,'' (https://www.epa.gov/environmentaljustice/learn-about-environmental-justice).
The EPA believes that this proposed action does not have
disproportionately high and adverse human health or environmental
effects on minority populations, low-income populations, and/or
indigenous peoples. The EPA has determined that this proposed action
will not have disproportionately high and adverse human health or
environmental effects on minority or low-income populations because the
petitioned wastes do not meet the criteria that determines what
constitutes a hazardous waste and there are no additional constituents
or factors which could cause the waste to be hazardous. The EPA's risk
assessment, as described in section III.E above, did not identify risks
from management of this material in an authorized, solid waste landfill
[[Page 4127]]
(e.g., RCRA Subtitle D landfill, commercial/industrial solid waste
landfill, etc.). Therefore, the EPA believes that any populations in
proximity of the landfill(s) used by the Baytown facility should not be
adversely affected by common waste management practices for this
delisted waste.
L. Congressional Review Act
This proposed action is exempt from the Congressional Review Act (5
U.S.C. 801 et seq.) because it is a rule of particular applicability.
List of Subjects in 40 CFR Part 261
Environmental protection, Hazardous waste, Recycling, Reporting and
recordkeeping requirements.
Dated: January 9, 2023.
Ronald Crossland,
Director, Land, Chemicals and Redevelopment Division.
For the reasons set out in the preamble, the EPA proposes to amend
40 CFR part 261 as follows:
PART 261--IDENTIFICATION AND LISTING OF HAZARDOUS WASTE
0
1. The authority citation for part 261 continues to read as follows:
Authority: 42 U.S.C. 6905, 6912(a), 6921, 6922, 6924(y) and
6938.
0
2. Amend Table 1 of Appendix IX to Part 261 by adding the entry
``ExxonMobil Baytown Refinery'' in alphabetical order to read as
follows:
Appendix IX to Part 261 Wastes Excluded Under Sec. Sec. 260.20 and
260.22
Table 1--Wastes Excluded From Non-Specific Sources
----------------------------------------------------------------------------------------------------------------
Facility Address Waste description
----------------------------------------------------------------------------------------------------------------
* * * * * * *
ExxonMobil Baytown Refinery...... Baytown, Texas............. Wastewater Treatment Plant Sludge (the EPA
Hazardous Waste No. F037) maximum delisted
amount of 730 cubic yards per calendar year
after (date rule finalized) and disposed in a
Subtitle D landfill. ExxonMobil must implement
a verification program that meets the following
Paragraphs:
(1) Delisting Levels: All leachable constituent
concentrations must not exceed the following
levels. The petitioner must use the method
specified in 40 CFR 261.24 to measure
constituents in the waste leachate (mg/L).
Wastewater Treatment Plant Solids Leachate:
Acenaphthene-107; Acetone-5220; Aniline-19.8;
Anthracene-260; Antimony-1.23; Arsenic-0.129;
Barium-100; Benz(a) anthracene-5.13; Benzene-
0.5; Benzo(a)pyrene-1930; Beryllium-1.43;
Cadmium-1.0; Chromium (III)-5.0; Chrysene-513;
Cobalt-2.71; Copper-88.1; Cresol (total)-200;
Dibenzofuran-5.91; 2,4-Dimethylphenol-114;
Diphenylamine-387; Endosulfan-35.9; Endrin-
0.05; Ethyl Methacrylate-2030; Ethylbenzene-
7.88; Fluoranthrene-24.7; Fluorene-49.2; Beta
HCH-0.0636; Heptachlor-0.008; Heptachlor
epoxide-0.008; Lead-5.0; Mercury-0.2; 2-
Methylnapthalene-7.29; Naphthalene-0.947;
Nickel-136; N-Nitrosodiphenylamine-11.5; Phenol-
1740; Pyrene-44.6; Pyridine-5; Selenium-1.0;
Silver-5.0; Styrene-15.2; TCDD-467; Toluene-
152; 1,3,5-Trinitrobenzene-174; Vanadium-41.7;
Xylenes (total)-86.1; Zinc-1980.
(2) Waste Holding and Handling:
(A) Wastewater treatment plant sludge must be
tested annually to assure they have met the
concentrations described in Paragraph (1).
Solids that do not meet the concentrations in
the original and retest representative sample
must be disposed of as hazardous waste.
(B) Levels of constituents measured in the
samples of the solids that do not exceed the
levels set forth in Paragraph (1) are non-
hazardous. ExxonMobil can manage and dispose
the non-hazardous WWTP solids according to all
applicable solid waste regulations.
(C) ExxonMobil must maintain a record of the
actual volume of the WWTP solids to be disposed
in the Subtitle D landfill according to the
requirements in Paragraph (4).
(3) Testing Requirements:
(A) ExxonMobil must test a representative sample
of the WWTP sludge for all constituents listed
in paragraph (1) at least once per calendar
year. If any measured constituent concentration
exceeds the delisting levels set forth in
paragraph (1), ExxonMobil must collect an
additional representative sample within 10
business days of being made aware of the
exceedance and test it expeditiously for the
constituent(s) which exceeded delisting levels
in the original annual sample.
(B) The annual testing report should include the
total amount of delisted waste in cubic yards
disposed during the calendar year.
(4) Changes in Operating Conditions: If
ExxonMobil significantly changes the process
described in its petition or starts any
processes that may or could affect the
composition or type of waste generated as
established under Paragraph (1) (by
illustration, but not limitation, changes in
equipment or operating conditions of the
treatment process), they must notify the EPA in
writing during the annual report; they may no
longer handle the wastes generated from the new
process as nonhazardous until the test results
of the wastes meet the delisting levels set in
Paragraph (1).
(5) Data Submittals: ExxonMobil must submit the
information described below. If ExxonMobil
fails to submit the required data within the
specified time or maintain the required records
on-site for the specified time, the EPA, at its
discretion, will consider this sufficient basis
to reopen the exclusion as described in
Paragraph 5. ExxonMobil must:
(A) Submit the data obtained through Paragraph 3
to the Chief, RCRA Permits & Solid Waste
Section, Mail Code, (6LCR-RP) US EPA Region 6,
1201 Elm Street, Suite 500, Dallas, TX 75270
within the time specified. Data may be
submitted via email to the technical contact
for the delisting program.
(B) Compile records of operating conditions and
analytical data from Paragraph (3), summarized,
and maintained on-site for a minimum of five
years.
(C) Furnish these records and data when the EPA
or the State of Texas request them for
inspection.
(D) Send along with all data, a signed copy of
the following certification statement, to
attest to the truth and accuracy of the data
submitted: ``Under civil and criminal penalty
of law for the making or submission of false or
fraudulent statements or representations
(pursuant to the applicable provisions of the
Federal Code, which include, but may not be
limited to, 18 U.S.C. 1001 and 42 U.S.C. 6928),
I certify that the information contained in or
accompanying this document is true, accurate
and complete. As to the (those) identified
section(s) of this document for which I cannot
personally verify its (their) truth and
accuracy, I certify as the company official
having supervisory responsibility for the
persons who, acting under my direct
instructions, made the verification that this
information is true, accurate and complete. If
any of this information is determined by the
EPA in its sole discretion to be false,
inaccurate or incomplete, and upon conveyance
of this fact to the company, I recognize and
agree that this exclusion of waste will be void
as if it never had effect or to the extent
directed by the EPA and that the company will
be liable for any actions taken in
contravention of the company's RCRA and CERCLA
obligations premised upon the company's
reliance on the void exclusion.''
(6) Reopener:
[[Page 4128]]
(A) If, any time after disposal of the delisted
waste, ExxonMobil possesses or is otherwise
made aware of any environmental data (including
but not limited to leachate data or ground
water monitoring data) or any other data
relevant to the delisted waste indicating that
any constituent identified for the delisting
verification testing is at level higher than
the delisting level allowed by the Division
Director in granting the petition, then the
facility must report the data, in writing, to
the Division Director within 10 days of first
possessing or being made aware of that data.
(B) If the verification testing of the waste
does not meet the delisting requirements in
Paragraph 1, ExxonMobil must report the data,
in writing, to the Division Director within 10
days of first possessing or being made aware of
that data.
(C) If ExxonMobil fails to submit the
information described in paragraphs (5), (6)(A)
or (6)(B) or if any other information is
received from any source, the Division Director
will make a preliminary determination as to
whether the reported information requires EPA
action to protect human health or the
environment. Further action may include
suspending, or revoking the exclusion, or other
appropriate response necessary to protect human
health and the environment.
(D) If the Division Director determines that the
reported information does require EPA action,
the Division Director will notify the facility,
in writing, of the actions the Division
Director believes are necessary to protect
human health and the environment. The notice
shall include a statement of the proposed
action and a statement providing the facility
with an opportunity to present information as
to why the proposed EPA action is not
necessary. The facility shall have 10 business
days from the date of the Division Director's
notice to present such information.
(E) Following the receipt of information from
the facility described in paragraph (6)(D) or
(if no information is presented under paragraph
(6)(D)) the initial receipt of information
described in paragraphs (5), (6)(A) or (6)(B),
the Division Director will issue a final
written determination describing the EPA
actions that are necessary to protect human
health or the environment. Any required action
described in the Division Director's
determination shall become effective
immediately, unless the Division Director
provides otherwise.
(6) Notification Requirements: ExxonMobil must
do the following before transporting the
delisted waste: Failure to provide this
notification will result in a violation of the
delisting petition and a possible revocation of
the decision.
(A) Provide a one-time written notification to
any State Regulatory Agency to which, or
through which they will transport the delisted
waste described above for disposal, 60 days
before beginning such activities. If ExxonMobil
transports the excluded waste to or manages the
waste in any state with delisting
authorization, ExxonMobil must obtain delisting
authorization from that state before it can
manage the waste as nonhazardous in the state.
(B) Update the one-time written notification if
they ship the delisted waste to a different
disposal facility.
(C) Failure to provide the notification will
result in a violation of the delisting variance
and a possible revocation of the exclusion.
* * * * * * *
----------------------------------------------------------------------------------------------------------------
[FR Doc. 2023-00835 Filed 1-23-23; 8:45 am]
BILLING CODE 6560-50-P
