Hazardous Waste Management System; Identification and Listing of Hazardous Waste; Direct Final Rule, 60052-60055 [2015-24459]
Download as PDF
60052
Federal Register / Vol. 80, No. 192 / Monday, October 5, 2015 / Rules and Regulations
CALIFORNIA—PM–10
Designation
Classification
Designated area
Date
*
*
*
Mono County
Mammoth Lakes planning area .............................
Includes the following sections:
a. Sections 1–12, 17, and 18 of Township
T4S, R28E;
b. Sections 25–36 of Township T3S, R28E;
c. Sections 25–36 of Township T3S, R27E;
d. Sections 1–18 of Township T4S, R27E;
and,
e. Sections 25 and 36 of Township T3S,
R26E.
*
*
*
*
*
*
*
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 261
[EPA–R07–RCRA–2014–0452; FRL–9934–
78–Region 7]
Hazardous Waste Management
System; Identification and Listing of
Hazardous Waste; Direct Final Rule
Environmental Protection
Agency (EPA).
ACTION: Direct final rule.
AGENCY:
The Environmental Protection
Agency (EPA) is taking direct final
action to revise delisting levels for the
hazardous waste exclusion granted to
John Deere Des Moines Works (John
Deere) of Deere & Company, in Ankeny,
Iowa to exclude or ‘‘delist’’ up to 600
tons per calendar year of F006/F019
wastewater treatment sludge. The
wastewater treatment sludge is a filter
cake generated by John Deere’s Ankeny,
Iowa, facility wastewater treatment
system was conditionally excluded from
the list of hazardous wastes on
November 25, 2014. This direct final
rule responds to a request submitted by
John Deere to increase certain delisting
levels and eliminate certain delisting
levels for the excluded waste. After
careful analysis and use of the Delisting
Risk Assessment Software (DRAS), EPA
has concluded the request may be
granted.
DATES: This direct final rule is effective
on December 4, 2015, without further
notice, unless EPA receives adverse
comment by November 4, 2015. If EPA
receives adverse comment, we will
mstockstill on DSK4VPTVN1PROD with RULES
SUMMARY:
VerDate Sep<11>2014
16:55 Oct 02, 2015
*
Jkt 238001
*
*
I. Why is EPA using a direct final rule?
II. Does this action apply to me?
III. Background
A. What is a delisting petition?
B. How did EPA act on John Deere’s
delisting petition?
C. What are the changes John Deere is
requesting?
D. How did EPA evaluate John Deere’s
request?
E. How does this final rule affect states?
IV. Statutory and Executive Order Reviews
Frm 00026
Fmt 4700
*
Attainment ........................
publish a timely withdrawal in the
Federal Register informing the public
that this rule will not take effect.
ADDRESSES: EPA has established a
docket for this action under Docket ID
No. EPA–R07–RCRA–2014–0452. All
documents in the docket are listed on
the www.regulations.gov Web site.
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, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
www.regulations.gov or in by contacting
the further information contact below.
The public may copy material from any
regulatory docket at no cost for the first
100 pages and at a cost of $0.15 per page
for additional copies.
FOR FURTHER INFORMATION CONTACT:
Kenneth Herstowski, Waste
Remediation and Permits Branch, Air
and Waste Management Division, EPA
Region 7, 11201 Renner Boulevard,
Lenexa, KS 66219; telephone number
(913) 551–7631; email address:
herstowski.ken@epa.gov.
SUPPLEMENTARY INFORMATION: The
information in this section is organized
as follows:
PO 00000
Date
*
November 4, 2015 ............
*
[FR Doc. 2015–25165 Filed 10–2–15; 8:45 am]
Type
Sfmt 4700
Type
*
........................
*
*
I. Why is EPA using a direct final rule?
The EPA is publishing this rule
without a prior proposed rule because
we view this as a non-controversial
amendment and anticipate no adverse
comment. This action narrowly changes
the delisting levels for the F006/F019
wastewater treatment sludge generated
at the John Deere Des Moines facility in
Ankeny, Iowa. If the EPA receives
adverse comment, we will publish a
timely withdrawal in the Federal
Register informing the public that this
direct final rule will not take effect. In
that case, we may issue a proposed rule
to propose the changes and would
address public comments in any
subsequent final rule based on the
proposed rule.
II. Does this action apply to me?
This action only applies to the F006/
F019 wastewater treatment sludge
generated at the John Deere Des Moines
facility in Ankeny, Iowa.
III. Background
A. What is a delisting petition?
A delisting petition is a request from
a generator to EPA or to an authorized
state to exclude or delist, from the
RCRA list of hazardous wastes, waste
the generator believes should not be
considered hazardous under RCRA.
B. How did EPA act on John Deere’s
delisting petition?
After evaluating the delisting petition
submitted by John Deere, EPA proposed,
on August 20, 2014 (79 FR 49252), to
exclude the waste from the lists of
hazardous waste under § 261.31. EPA
issued a final rule on November 25,
2014 (79 FR 70108) granting John
Deere’s delisting petition to have up to
600 tons per year of the F006/F019
wastewater treatment sludge generated
E:\FR\FM\05OCR1.SGM
05OCR1
Federal Register / Vol. 80, No. 192 / Monday, October 5, 2015 / Rules and Regulations
at the John Deere Des Moines, Ankney,
Iowa, facility excluded, or delisted, from
the definition of a hazardous waste,
once it is disposed in a Subtitle D
landfill.
mstockstill on DSK4VPTVN1PROD with RULES
C. What are the changes John Deere is
requesting?
John Deere requests removal of Table
1 item 1(C)—the requirement to conduct
analysis of verification samples using
EPA SW–846 Method 1313 Extraction at
pH 2.88, 7 and 13 and the requirement
not to exceed hexavalent chromium
level in the resulting [Method 1313]
extracts.
John Deere requests increases in
delisting levels in Table 1 item 1(D) as
follows: Cadmium to 25.5 milligrams
per kilogram (mg/kg), chromium (total)
to 51,000 mg/kg, chromium (hexavalent)
to 41 mg/kg, copper to 2877 mg/kg,
nickel to 3030 mg/kg, zinc to 10,170,
cyanide (total) to 9 mg/kg, and oil and
grease to 64,500 mg/kg.
John Deere requests the removal of
delisting levels in Table 1 item 1(D) for
antimony, arsenic, barium, beryllium,
cobalt, lead, mercury, selenium, silver,
thallium, tin, vanadium, acetone, and
methyl ethyl ketone.
To support the request, John Deere
submitted analytical data from
verification testing events conducted
since the exclusion was finalized. John
Deere generated the sampling data
under a Sampling Plan and Quality
Assurance Project Plan (June 2012
Revision).
D. How did EPA evaluate John Deere’s
request?
EPA evaluated the proposed increases
in the delisting levels against the listing
criteria and factors cited in
§ 261.11(a)(2) and (a)(3). EPA evaluated
the proposed increases in the delisting
levels with respect to other factors or
criteria to assess whether there is a
reasonable basis to believe that such
additional factors could cause the
wastes to be hazardous. EPA considered
whether the waste is acutely toxic, the
concentrations 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.
For this delisting determination, we
assumed that the waste would be
disposed in a Subtitle D landfill and we
considered transport of waste
constituents through groundwater,
surface water and air. We evaluated
John Deere’s petitioned waste using the
Agency’s Delisting Risk Assessment
VerDate Sep<11>2014
16:55 Oct 02, 2015
Jkt 238001
Software (DRAS) described in 65 FR
58015 (September 27, 2000), 65 FR
75637 (December 4, 2000), and 73 FR
28768 (May 19, 2008) to predict the
maximum allowable concentrations of
hazardous constituents that may be
released from the petitioned waste after
disposal and determined the potential
impact of the disposal of John Deere’s
petitioned waste on human health and
the environment. 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 EPA’s Composite Model
for Leachate Migration and
Transformation Products (EPACMTP).
From a release to groundwater, the
DRAS considers routes of exposure to a
human receptor of 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 included in
the docket.
At a benchmark cancer risk of one in
one hundred thousand (1×10¥5) and a
benchmark hazard quotient of 1.0, the
DRAS program determined maximum
allowable concentrations for each
constituent in both the waste and the
leachate at an annual waste volume of
1000 cubic yards disposed in a landfill
for 20 years after which time the landfill
is closed. We used the maximum
reported total and TCLP leachate
concentrations as inputs to estimate the
constituent concentrations in the
groundwater, soil, surface water and air.
The maximum allowable total COC
concentrations in the Filter Cake as
determined by the DRAS are as follows:
milligrams per kilogram (mg/kg)
Barium—2.85 × 107; Copper—5.34 ×
106; Chromium (III)—4.56 × 1010;
Hexavalent Chromium—1.36 × 104;
Cyanide—2.99 × 106; Lead—1.09 × 107;
Mercury—1.86 × 101; Nickel—4.76 ×
106; Vanadium—1.52 × 108; Zinc—1.38
× 107; Acetone—3.63 × 108; and Methyl
Ethyl Ketone—1.45 × 109. The
maximum allowable leachate COC
PO 00000
Frm 00027
Fmt 4700
Sfmt 4700
60053
concentrations in the Filter Cake as
determined by the DRAS are as follows:
Milligrams per liter
(mg/l) Copper—1.78 × 102; Hexavalent
Chromium—1.38 × 101; Cyanide—2.27 ×
101; Lead—4.18 × 100; Nickel—9.78 ×
101; Vanadium—2.47 × 101; Zinc—1.48
× 103; and Acetone—3.84 × 103. The
maximum allowable leachate COC
concentrations in the Filter Cake as
determined by TCLP are as follows:
Milligrams per liter (mg/l) Barium—100;
Chromium (total)—5; Mercury—0.2; and
Methyl Ethyl Ketone—200.
The concentrations of all constituents
in both the waste and the leachate are
below the allowable concentrations. The
requested changes in delisting levels are
below the allowable concentrations.
EPA’s decision to grant the requested
changes by John Deere is based on the
information submitted in support of this
direct final rule, and other information
in the docket.
E. How does this final rule affect states?
EPA is issuing this exclusion under
the Federal RCRA delisting program.
Thus, upon the exclusion being
finalized, the wastes covered will be
removed from Subtitle C control under
the Federal RCRA program. This will
mean, first, that the wastes will be
delisted in any State or territory where
the EPA is directly administering the
RCRA program (e.g., Iowa, Indian
Country). However, whether the wastes
will be delisted in states which have
been authorized to administer the RCRA
program will vary depending upon the
authorization status of the States and
the particular requirements regarding
delisted wastes in the various states.
Some other generally authorized
states have not received authorization
for delisting. Thus, the EPA makes
delisting determinations for such states.
However, RCRA allows states to impose
their own regulatory requirements that
are more stringent than EPA’s, under
Section 3009 of RCRA. These more
stringent requirements may include a
provision that prohibits a Federally
issued exclusion from taking effect in
the state, or that requires a state
concurrence before the Federal
exclusion takes effect, or that allows the
state to add conditions to any Federal
exclusion. We urge the petitioner to
contact the state regulatory authority in
each state to or through which it may
wish to ship its wastes to establish the
status of its wastes under the state’s
laws.
EPA has also authorized some states
to administer a delisting program in
place of the Federal program, that is, to
make state delisting decisions. In such
states, the state delisting requirements
E:\FR\FM\05OCR1.SGM
05OCR1
60054
Federal Register / Vol. 80, No. 192 / Monday, October 5, 2015 / Rules and Regulations
operate in lieu of the Federal delisting
requirements. Therefore, this exclusion
does not apply in those authorized
states unless the state makes the rule
part of its authorized program. If John
Deere transports the federally excluded
waste to or manages the waste in any
state with delisting authorization, John
Deere must obtain a delisting
authorization from that state before it
can manage the waste as non-hazardous
in that state.
mstockstill on DSK4VPTVN1PROD with RULES
IV. Statutory and Executive Order
Reviews
Under Executive Order 12866,
‘‘Regulatory Planning and Review’’ (58
FR 51735, October 4, 1993) and 13563
(76 FR 3821, January 21, 2011), this rule
is not of general applicability and
therefore is not a regulatory action
subject to review by the Office of
Management and Budget (OMB). This
rule 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
applies to a particular facility only.
Because this rule is of particular
applicability relating to a particular
facility, it is not subject to the regulatory
flexibility provisions of the Regulatory
Flexibility Act (5 U.S.C. 601 et seq.), or
to Sections 202, 204, and 205 of the
Unfunded Mandates Reform Act of 1995
(UMRA) (Pub. L. 104–4). Because this
rule will affect only a particular facility,
it will not significantly or uniquely
affect small governments, as specified in
Section 203 of UMRA. Because this rule
will affect only a particular facility, this
final rule 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, as specified in
Executive Order 13132, ‘‘Federalism,’’
(64 FR 43255, August 10, 1999). Thus,
Executive Order 13132 does not apply
to this rule. Similarly, because this rule
will affect only a particular facility, this
final rule does not have tribal
implications, as specified in Executive
Order 13175, ‘‘Consultation and
Coordination with Indian Tribal
Governments’’ (65 FR 67249, November
9, 2000). Thus, Executive Order 13175
does not apply to this rule. This rule
VerDate Sep<11>2014
16:55 Oct 02, 2015
Jkt 238001
also is not subject to Executive Order
13045, ‘‘Protection of Children from
Environmental Health Risks and Safety
Risks’’ (62 FR 19885, April 23, 1997),
because it is not economically
significant as defined in Executive
Order 12866, and because the Agency
does not have reason to believe the
environmental health or safety risks
addressed by this action present a
disproportionate risk to children. The
basis for this belief is that the Agency
used the DRAS program, which
considers health and safety risks to
children, to calculate the maximum
allowable concentrations for this rule.
This rule is not subject to Executive
Order 13211, ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355, May 22, 2001), because it is
not a significant regulatory action under
Executive Order 12866. This rule does
not involve technical standards; thus,
the requirements of Section 12(d) of the
National Technology Transfer and
Advancement Act of 1995 (15 U.S.C.
272 note) do not apply. As required by
Section 3 of Executive Order 12988,
‘‘Civil Justice Reform,’’ (61 FR 4729,
February 7, 1996), in issuing this rule,
EPA has taken the necessary steps to
eliminate drafting errors and ambiguity,
minimize potential litigation, and
provide a clear legal standard for
affected conduct.
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report which includes a
copy of the rule to each House of the
Congress and to the Comptroller General
of the United States. Section 804
exempts from Section 801 the following
types of rules (1) Rules of particular
applicability; (2) rules relating to agency
management or personnel; and (3) rules
of agency organization, procedure, or
practice that do not substantially affect
the rights or obligations of non-agency
parties (5 U.S.C. 804(3)). EPA is not
required to submit a rule report
regarding today’s action under Section
801 because this is a rule of particular
applicability. Executive Order (EO)
12898 (59 FR 7629 (February 16, 1994))
establishes Federal executive policy on
environmental justice. Its main
PO 00000
Frm 00028
Fmt 4700
Sfmt 4700
provision directs Federal agencies, to
the greatest extent practicable and
permitted by law, to make
environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has determined that this final
rule will not have disproportionately
high and adverse human health or
environmental effects on minority or
low-income populations because it does
not affect the level of protection
provided to human health or the
environment. The Agency’s risk
assessment did not identify risks from
management of this material in a
Subtitle D landfill. Therefore, EPA
believes that any populations in
proximity of the landfills used by this
facility should not be adversely affected
by common waste management
practices for this delisted waste.
List of Subjects in 40 CFR Part 261
Environmental protection, Hazardous
waste, Recycling, Reporting and
recordkeeping requirements.
Authority: Sec. 3001(f) RCRA, 42 U.S.C.
6921(f).
Dated: September 14, 2015.
Mark Hague,
Acting Regional Administrator, Region 7.
For the reasons set out in the
preamble, EPA amends 40 CFR part 261
as follows:
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. In the second Table 1 of Appendix
IX to part 261, ‘‘Wastes Excluded From
Non-Specific Sources’’, in the entry for
‘‘John Deere Des Moines Works of Deere
& Company, Ankeny, IA’’, revise entry
‘‘1. Delisting Levels’’ to read as follows:
■
Appendix IX to Part 261—Wastes
Excluded Under §§ 260.20 and 260.22
*
E:\FR\FM\05OCR1.SGM
*
*
05OCR1
*
*
60055
Federal Register / Vol. 80, No. 192 / Monday, October 5, 2015 / Rules and Regulations
TABLE 1—WASTES EXCLUDED FROM NON-SPECIFIC SOURCES
Facility
Address
*
*
John Deere Des Moines
Ankeny, IA.
Works of Deere Company.
Waste description
*
*
*
*
*
*
*
*
*
*
*
BILLING CODE 6560–50–P
DEPARTMENT OF HEALTH AND
HUMAN SERVICES
Centers for Medicare & Medicaid
Services
42 CFR Part 412
[CMS–1632–CN]
RIN 0938–AS41
Medicare Program; Hospital Inpatient
Prospective Payment Systems for
Acute Care Hospitals and the LongTerm Care Hospital Prospective
Payment System Policy Changes and
Fiscal Year 2016 Rates; Revisions of
Quality Reporting Requirements for
Specific Providers, including Changes
Related to the Electronic Health
Record Incentive Program; Extensions
of the Medicare-Dependent, Small
Rural Hospital Program and the LowVolume Payment Adjustment for
Hospitals; Correction
Centers for Medicare &
Medicaid Services (CMS), HHS.
ACTION: Final rule and interim final rule
with comment period; correction.
AGENCY:
This document corrects
technical and typographical errors in
the final rule and interim final rule with
comment period that appeared in the
Federal Register on August 17, 2015
titled ‘‘Medicare Program; Hospital
Inpatient Prospective Payment Systems
for Acute Care Hospitals and the LongTerm Care Hospital Prospective
Payment System Policy Changes and
Fiscal Year 2016 Rates; Revisions of
Quality Reporting Requirements for
Specific Providers, including Changes
SUMMARY:
VerDate Sep<11>2014
17:39 Oct 02, 2015
Jkt 238001
*
*
*
I. Background
In FR Doc. 2015–19049 which
appeared in the August 17, 2015
Federal Register, titled ‘‘Medicare
Program; Hospital Inpatient Prospective
Payment Systems for Acute Care
Hospitals and the Long-Term Care
Hospital Prospective Payment System
Policy Changes and Fiscal Year 2016
Rates; Revisions of Quality Reporting
Requirements for Specific Providers,
including Changes Related to the
Electronic Health Record Incentive
Program; Extensions of the MedicareDependent, Small Rural Hospital
Program and the Low-Volume Payment
Adjustment for Hospitals’’ (hereinafter
referred to as the FY 2016 IPPS/LTCH
PPS final rule), there were a number of
technical and typographical errors that
are identified and corrected in section
IV. of this correcting document. The
provisions in this correction document
are effective as if they had been
included in the document that appeared
in the August 17, 2015 Federal Register.
Accordingly, the corrections are
effective October 1, 2015.
II. Summary of Errors
A. Summary of Errors in the Preamble
On page 49412, we made a
typographical error with regards to an
MS–DRG code. We made inadvertent
and technical errors related to the
employment cost index (ECI) used in
the wage index, the MS–DRG
PO 00000
*
*
*
*
*
*
1. Delisting Levels: (A) The WWTS Filter Cake shall not exhibit any of the ‘‘Characteristics of
Hazardous Waste’’ in 40 CFR part 261, subpart C. (B) All TCLP leachable concentrations
(40 CFR 261.24(a)) for the following constituents must not exceed the following levels
(mg/L for TCLP): Nickel—32.4. (C) Reserved. (D) All total concentrations for the following
constituents must not exceed the following levels (mg/kg): Cadmium—25.5; Chromium
(total)—51,000; Chromium (hexavalent)—41; Copper—2877; Nickel—3030; Zinc—10,170;
Cyanide—9, Oil and Grease—64,500.
Related to the Electronic Health Record
Incentive Program; Extensions of the
Medicare-Dependent, Small Rural
Hospital Program and the Low-Volume
Payment Adjustment for Hospitals.’’
DATES: This document is effective
October 1, 2015.
FOR FURTHER INFORMATION CONTACT:
Donald Thompson, (410) 786–4487.
SUPPLEMENTARY INFORMATION:
*
[FR Doc. 2015–24459 Filed 10–2–15; 8:45 am]
mstockstill on DSK4VPTVN1PROD with RULES
*
Frm 00029
Fmt 4700
Sfmt 4700
*
*
reclassification and recalibration budget
neutrality adjustment factor (as
discussed in section II.B. of this
correcting document), and the MGCRB
reclassification status of certain
providers (as discussed in section II.B.
of this correcting document), each of
which resulted in additional conforming
corrections. Specifically, on page 49492,
we inadvertently miscalculated the
estimated percentage change in the ECI
for compensation for the 30-day
increment after March 14, 2013 and
before April 15, 2013 for private
industry hospital workers from the
Bureau of Labor Statistics’ (BLS’)
‘‘Compensation and Working
Conditions.’’ The ECI is used to adjust
a hospital’s wage data to calculate the
wage index, and is based on the
midpoint of a cost reporting period.
On page 49498, we are making
conforming changes to the number of
hospitals in New Jersey that will be
receiving the imputed rural floor and to
the FY 2016 rural floor value for Nevada
as a result of correcting the ECI error,
the technical error in the calculation of
the MS–DRG reclassification and
recalibration budget neutrality
adjustment factor (discussed in section
II.B. of this correcting document), and
the error in the reclassification status of
50 providers (discussed in section II.B.
of this correcting document).
On page 49619, consistent with the
conforming corrections to the IPPS
outlier fixed-loss cost threshold for FY
2016 discussed in section II.B. of this
correcting document, we are making
further conforming corrections to the FY
2016 outlier fixed-loss amount for site
neutral cases in the context of our
discussion regarding LTCH PPS highcost outliers.
B. Summary of Errors in the Addendum
On page 49776, we are correcting the
MS–DRG reclassification and
E:\FR\FM\05OCR1.SGM
05OCR1
Agencies
[Federal Register Volume 80, Number 192 (Monday, October 5, 2015)]
[Rules and Regulations]
[Pages 60052-60055]
From the Federal Register Online via the Government Publishing Office [www.gpo.gov]
[FR Doc No: 2015-24459]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 261
[EPA-R07-RCRA-2014-0452; FRL-9934-78-Region 7]
Hazardous Waste Management System; Identification and Listing of
Hazardous Waste; Direct Final Rule
AGENCY: Environmental Protection Agency (EPA).
ACTION: Direct final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is taking direct
final action to revise delisting levels for the hazardous waste
exclusion granted to John Deere Des Moines Works (John Deere) of Deere
& Company, in Ankeny, Iowa to exclude or ``delist'' up to 600 tons per
calendar year of F006/F019 wastewater treatment sludge. The wastewater
treatment sludge is a filter cake generated by John Deere's Ankeny,
Iowa, facility wastewater treatment system was conditionally excluded
from the list of hazardous wastes on November 25, 2014. This direct
final rule responds to a request submitted by John Deere to increase
certain delisting levels and eliminate certain delisting levels for the
excluded waste. After careful analysis and use of the Delisting Risk
Assessment Software (DRAS), EPA has concluded the request may be
granted.
DATES: This direct final rule is effective on December 4, 2015, without
further notice, unless EPA receives adverse comment by November 4,
2015. If EPA receives adverse comment, we will publish a timely
withdrawal in the Federal Register informing the public that this rule
will not take effect.
ADDRESSES: EPA has established a docket for this action under Docket ID
No. EPA-R07-RCRA-2014-0452. All documents in the docket are listed on
the www.regulations.gov Web site. 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, is not placed on the Internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available either electronically through
www.regulations.gov or in by contacting the further information contact
below. The public may copy material from any regulatory docket at no
cost for the first 100 pages and at a cost of $0.15 per page for
additional copies.
FOR FURTHER INFORMATION CONTACT: Kenneth Herstowski, Waste Remediation
and Permits Branch, Air and Waste Management Division, EPA Region 7,
11201 Renner Boulevard, Lenexa, KS 66219; telephone number (913) 551-
7631; email address: herstowski.ken@epa.gov.
SUPPLEMENTARY INFORMATION: The information in this section is organized
as follows:
I. Why is EPA using a direct final rule?
II. Does this action apply to me?
III. Background
A. What is a delisting petition?
B. How did EPA act on John Deere's delisting petition?
C. What are the changes John Deere is requesting?
D. How did EPA evaluate John Deere's request?
E. How does this final rule affect states?
IV. Statutory and Executive Order Reviews
I. Why is EPA using a direct final rule?
The EPA is publishing this rule without a prior proposed rule
because we view this as a non-controversial amendment and anticipate no
adverse comment. This action narrowly changes the delisting levels for
the F006/F019 wastewater treatment sludge generated at the John Deere
Des Moines facility in Ankeny, Iowa. If the EPA receives adverse
comment, we will publish a timely withdrawal in the Federal Register
informing the public that this direct final rule will not take effect.
In that case, we may issue a proposed rule to propose the changes and
would address public comments in any subsequent final rule based on the
proposed rule.
II. Does this action apply to me?
This action only applies to the F006/F019 wastewater treatment
sludge generated at the John Deere Des Moines facility in Ankeny, Iowa.
III. Background
A. What is a delisting petition?
A delisting petition is a request from a generator to EPA or to an
authorized state to exclude or delist, from the RCRA list of hazardous
wastes, waste the generator believes should not be considered hazardous
under RCRA.
B. How did EPA act on John Deere's delisting petition?
After evaluating the delisting petition submitted by John Deere,
EPA proposed, on August 20, 2014 (79 FR 49252), to exclude the waste
from the lists of hazardous waste under Sec. 261.31. EPA issued a
final rule on November 25, 2014 (79 FR 70108) granting John Deere's
delisting petition to have up to 600 tons per year of the F006/F019
wastewater treatment sludge generated
[[Page 60053]]
at the John Deere Des Moines, Ankney, Iowa, facility excluded, or
delisted, from the definition of a hazardous waste, once it is disposed
in a Subtitle D landfill.
C. What are the changes John Deere is requesting?
John Deere requests removal of Table 1 item 1(C)--the requirement
to conduct analysis of verification samples using EPA SW-846 Method
1313 Extraction at pH 2.88, 7 and 13 and the requirement not to exceed
hexavalent chromium level in the resulting [Method 1313] extracts.
John Deere requests increases in delisting levels in Table 1 item
1(D) as follows: Cadmium to 25.5 milligrams per kilogram (mg/kg),
chromium (total) to 51,000 mg/kg, chromium (hexavalent) to 41 mg/kg,
copper to 2877 mg/kg, nickel to 3030 mg/kg, zinc to 10,170, cyanide
(total) to 9 mg/kg, and oil and grease to 64,500 mg/kg.
John Deere requests the removal of delisting levels in Table 1 item
1(D) for antimony, arsenic, barium, beryllium, cobalt, lead, mercury,
selenium, silver, thallium, tin, vanadium, acetone, and methyl ethyl
ketone.
To support the request, John Deere submitted analytical data from
verification testing events conducted since the exclusion was
finalized. John Deere generated the sampling data under a Sampling Plan
and Quality Assurance Project Plan (June 2012 Revision).
D. How did EPA evaluate John Deere's request?
EPA evaluated the proposed increases in the delisting levels
against the listing criteria and factors cited in Sec. 261.11(a)(2)
and (a)(3). EPA evaluated the proposed increases in the delisting
levels with respect to other factors or criteria to assess whether
there is a reasonable basis to believe that such additional factors
could cause the wastes to be hazardous. EPA considered whether the
waste is acutely toxic, the concentrations 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.
For this delisting determination, we assumed that the waste would
be disposed in a Subtitle D landfill and we considered transport of
waste constituents through groundwater, surface water and air. We
evaluated John Deere's petitioned waste using the Agency's Delisting
Risk Assessment Software (DRAS) described in 65 FR 58015 (September 27,
2000), 65 FR 75637 (December 4, 2000), and 73 FR 28768 (May 19, 2008)
to predict the maximum allowable concentrations of hazardous
constituents that may be released from the petitioned waste after
disposal and determined the potential impact of the disposal of John
Deere's petitioned waste on human health and the environment. 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 EPA's Composite Model for Leachate
Migration and Transformation Products (EPACMTP). From a release to
groundwater, the DRAS considers routes of exposure to a human receptor
of 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 included in the docket.
At a benchmark cancer risk of one in one hundred thousand
(1x10-5) and a benchmark hazard quotient of 1.0, the DRAS
program determined maximum allowable concentrations for each
constituent in both the waste and the leachate at an annual waste
volume of 1000 cubic yards disposed in a landfill for 20 years after
which time the landfill is closed. We used the maximum reported total
and TCLP leachate concentrations as inputs to estimate the constituent
concentrations in the groundwater, soil, surface water and air.
The maximum allowable total COC concentrations in the Filter Cake
as determined by the DRAS are as follows: milligrams per kilogram (mg/
kg) Barium--2.85 x 10\7\; Copper--5.34 x 10\6\; Chromium (III)--4.56 x
10\10\; Hexavalent Chromium--1.36 x 10\4\; Cyanide--2.99 x 10\6\;
Lead--1.09 x 10\7\; Mercury--1.86 x 10\1\; Nickel--4.76 x 10\6\;
Vanadium--1.52 x 10\8\; Zinc--1.38 x 10\7\; Acetone--3.63 x 10\8\; and
Methyl Ethyl Ketone--1.45 x 10\9\. The maximum allowable leachate COC
concentrations in the Filter Cake as determined by the DRAS are as
follows: Milligrams per liter (mg/l) Copper--1.78 x 10\2\; Hexavalent
Chromium--1.38 x 10\1\; Cyanide--2.27 x 10\1\; Lead--4.18 x 10\0\;
Nickel--9.78 x 10\1\; Vanadium--2.47 x 10\1\; Zinc--1.48 x 10\3\; and
Acetone--3.84 x 10\3\. The maximum allowable leachate COC
concentrations in the Filter Cake as determined by TCLP are as follows:
Milligrams per liter (mg/l) Barium--100; Chromium (total)--5; Mercury--
0.2; and Methyl Ethyl Ketone--200.
The concentrations of all constituents in both the waste and the
leachate are below the allowable concentrations. The requested changes
in delisting levels are below the allowable concentrations. EPA's
decision to grant the requested changes by John Deere is based on the
information submitted in support of this direct final rule, and other
information in the docket.
E. How does this final rule affect states?
EPA is issuing this exclusion under the Federal RCRA delisting
program. Thus, upon the exclusion being finalized, the wastes covered
will be removed from Subtitle C control under the Federal RCRA program.
This will mean, first, that the wastes will be delisted in any State or
territory where the EPA is directly administering the RCRA program
(e.g., Iowa, Indian Country). However, whether the wastes will be
delisted in states which have been authorized to administer the RCRA
program will vary depending upon the authorization status of the States
and the particular requirements regarding delisted wastes in the
various states.
Some other generally authorized states have not received
authorization for delisting. Thus, the EPA makes delisting
determinations for such states. However, RCRA allows states to impose
their own regulatory requirements that are more stringent than EPA's,
under Section 3009 of RCRA. These more stringent requirements may
include a provision that prohibits a Federally issued exclusion from
taking effect in the state, or that requires a state concurrence before
the Federal exclusion takes effect, or that allows the state to add
conditions to any Federal exclusion. We urge the petitioner to contact
the state regulatory authority in each state to or through which it may
wish to ship its wastes to establish the status of its wastes under the
state's laws.
EPA has also authorized some states to administer a delisting
program in place of the Federal program, that is, to make state
delisting decisions. In such states, the state delisting requirements
[[Page 60054]]
operate in lieu of the Federal delisting requirements. Therefore, this
exclusion does not apply in those authorized states unless the state
makes the rule part of its authorized program. If John Deere transports
the federally excluded waste to or manages the waste in any state with
delisting authorization, John Deere must obtain a delisting
authorization from that state before it can manage the waste as non-
hazardous in that state.
IV. Statutory and Executive Order Reviews
Under Executive Order 12866, ``Regulatory Planning and Review'' (58
FR 51735, October 4, 1993) and 13563 (76 FR 3821, January 21, 2011),
this rule is not of general applicability and therefore is not a
regulatory action subject to review by the Office of Management and
Budget (OMB). This rule 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 applies to a particular facility only.
Because this rule is of particular applicability relating to a
particular facility, it is not subject to the regulatory flexibility
provisions of the Regulatory Flexibility Act (5 U.S.C. 601 et seq.), or
to Sections 202, 204, and 205 of the Unfunded Mandates Reform Act of
1995 (UMRA) (Pub. L. 104-4). Because this rule will affect only a
particular facility, it will not significantly or uniquely affect small
governments, as specified in Section 203 of UMRA. Because this rule
will affect only a particular facility, this final rule 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, as specified in Executive Order 13132,
``Federalism,'' (64 FR 43255, August 10, 1999). Thus, Executive Order
13132 does not apply to this rule. Similarly, because this rule will
affect only a particular facility, this final rule does not have tribal
implications, as specified in Executive Order 13175, ``Consultation and
Coordination with Indian Tribal Governments'' (65 FR 67249, November 9,
2000). Thus, Executive Order 13175 does not apply to this rule. This
rule also is not subject to Executive Order 13045, ``Protection of
Children from Environmental Health Risks and Safety Risks'' (62 FR
19885, April 23, 1997), because it is not economically significant as
defined in Executive Order 12866, and because the Agency does not have
reason to believe the environmental health or safety risks addressed by
this action present a disproportionate risk to children. The basis for
this belief is that the Agency used the DRAS program, which considers
health and safety risks to children, to calculate the maximum allowable
concentrations for this rule. This rule is not subject to Executive
Order 13211, ``Actions Concerning Regulations That Significantly Affect
Energy Supply, Distribution, or Use'' (66 FR 28355, May 22, 2001),
because it is not a significant regulatory action under Executive Order
12866. This rule does not involve technical standards; thus, the
requirements of Section 12(d) of the National Technology Transfer and
Advancement Act of 1995 (15 U.S.C. 272 note) do not apply. As required
by Section 3 of Executive Order 12988, ``Civil Justice Reform,'' (61 FR
4729, February 7, 1996), in issuing this rule, EPA has taken the
necessary steps to eliminate drafting errors and ambiguity, minimize
potential litigation, and provide a clear legal standard for affected
conduct.
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report which includes a copy of the rule to
each House of the Congress and to the Comptroller General of the United
States. Section 804 exempts from Section 801 the following types of
rules (1) Rules of particular applicability; (2) rules relating to
agency management or personnel; and (3) rules of agency organization,
procedure, or practice that do not substantially affect the rights or
obligations of non-agency parties (5 U.S.C. 804(3)). EPA is not
required to submit a rule report regarding today's action under Section
801 because this is a rule of particular applicability. Executive Order
(EO) 12898 (59 FR 7629 (February 16, 1994)) establishes Federal
executive policy on environmental justice. Its main provision directs
Federal agencies, to the greatest extent practicable and permitted by
law, to make environmental justice part of their mission by identifying
and addressing, as appropriate, disproportionately high and adverse
human health or environmental effects of their programs, policies, and
activities on minority populations and low-income populations in the
United States.
EPA has determined that this final rule will not have
disproportionately high and adverse human health or environmental
effects on minority or low-income populations because it does not
affect the level of protection provided to human health or the
environment. The Agency's risk assessment did not identify risks from
management of this material in a Subtitle D landfill. Therefore, EPA
believes that any populations in proximity of the landfills used by
this facility should not be adversely affected by common waste
management practices for this delisted waste.
List of Subjects in 40 CFR Part 261
Environmental protection, Hazardous waste, Recycling, Reporting and
recordkeeping requirements.
Authority: Sec. 3001(f) RCRA, 42 U.S.C. 6921(f).
Dated: September 14, 2015.
Mark Hague,
Acting Regional Administrator, Region 7.
For the reasons set out in the preamble, EPA amends 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. In the second Table 1 of Appendix IX to part 261, ``Wastes Excluded
From Non-Specific Sources'', in the entry for ``John Deere Des Moines
Works of Deere & Company, Ankeny, IA'', revise entry ``1. Delisting
Levels'' to read as follows:
Appendix IX to Part 261--Wastes Excluded Under Sec. Sec. 260.20 and
260.22
* * * * *
[[Page 60055]]
Table 1--Wastes Excluded From Non-Specific Sources
----------------------------------------------------------------------------------------------------------------
Facility Address Waste description
----------------------------------------------------------------------------------------------------------------
* * * * * * *
John Deere Des Moines Works of Deere Ankeny, IA....................
Company.
* * * * * * *
1. Delisting Levels: (A) The WWTS Filter
Cake shall not exhibit any of the
``Characteristics of Hazardous Waste''
in 40 CFR part 261, subpart C. (B) All
TCLP leachable concentrations (40 CFR
261.24(a)) for the following
constituents must not exceed the
following levels (mg/L for TCLP):
Nickel--32.4. (C) Reserved. (D) All
total concentrations for the following
constituents must not exceed the
following levels (mg/kg): Cadmium--
25.5; Chromium (total)--51,000;
Chromium (hexavalent)--41; Copper--
2877; Nickel--3030; Zinc--10,170;
Cyanide--9, Oil and Grease--64,500.
* * * * * * *
----------------------------------------------------------------------------------------------------------------
* * * * *
[FR Doc. 2015-24459 Filed 10-2-15; 8:45 am]
BILLING CODE 6560-50-P