Project XL Site-Specific Rulemaking for the Ortho-McNeil Pharmaceutical, Inc. Facility in Spring House, PA Involving On-Site Treatment of Mixed Wastes, 36850-36858 [05-12658]
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[FR Doc. 05–12657 Filed 6–24–05; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 261
[RCRA–2001–0021; FRL–7928–8]
RIN 2090–AA14
Project XL Site-Specific Rulemaking
for the Ortho-McNeil Pharmaceutical,
Inc. Facility in Spring House, PA
Involving On-Site Treatment of Mixed
Wastes
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: The Environmental Protection
Agency (EPA) is today finalizing this
rule to implement a pilot project under
the Project XL program, providing sitespecific regulatory flexibility under the
Resource Conservation and Recovery
Act (RCRA), as amended, for the OrthoMcNeil Pharmaceutical, Inc. facility in
Spring House, Pennsylvania (OMP
Spring House). The principal objective
of this XL project is to obtain
information helpful to determining
whether regulatory oversight by the
Nuclear Regulatory Commission (NRC),
or NRC Agreement States, under
authority of the Atomic Energy Act
(AEA) is sufficient to ensure protection
of human health and the environment
regarding the management of certain
small volumes of mixed wastes (i.e.,
RCRA hazardous wastes that also
contain radioactive materials) that are
both generated and treated in an NRClicensed pharmaceutical research and
development laboratory. If, as a result of
this XL project, the Agency determines
that certain small volumes of low-level
mixed wastes (LLMW) generated and
managed under NRC oversight need not
also be subject to RCRA hazardous
waste regulations to ensure protection of
human health and the environment,
EPA may consider adopting the
approach on a national basis.
DATES: Effective Date: This final rule is
effective on June 27, 2005.
ADDRESSES: EPA has established a
docket for this action under Docket ID
No. RCRA–2001–0021. All documents
in the docket are listed in the EDOCKET
index at https://www.epa.gov/edocket.
Although listed in the index, some
information is not publicly available,
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i.e., 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 in
EDOCKET or in hard copy at the RCRA
Docket, EPA/DC, EPA West, Room
B102, 1301 Constitution Ave., NW.,
Washington, DC. The Public Reading
Room is open from 8:30 a.m. to 4:30
p.m., Monday through Friday, excluding
legal holidays. The telephone number
for the Public Reading Room is (202)
566–1744, and the telephone number for
the RCRA Docket is (202) 566–0270.
FOR FURTHER INFORMATION CONTACT: Mr.
Charles Howland, U.S. Environmental
Protection Agency, Region III (3OR00),
1650 Arch Street, Philadelphia, PA,
19103–2029. Mr. Howland can be
reached at (215) 814–2645 (or
howland.charles@epa.gov).
SUPPLEMENTARY INFORMATION:
Outline of Today’s Rule
The information presented in this
preamble is organized as follows:
I. Authority
II. Overview of Project XL
III. Overview of the OMP Spring House XL
Pilot Project
A. To Which Facilities Does the Final Rule
Apply?
B. What Problems Does the OMP Spring
House XL Project Attempt To Address?
1. Current Regulatory Status of Mixed
Wastes
2. Site-Specific Considerations at the OMP
Spring House Facility
C. What Solution Is Being Tested by the
OMP Spring House XL Project?
D. What Regulatory Changes Are Being
Made to Implement this Project?
E. Why is EPA Promulgating This
Approach To Removing RCRA
Regulatory Controls Over a Mixed
Waste?
F. How Have Various Stakeholders Been
Involved in this Project?
G. Response to Major Comments Received
on the Proposed Rule
H. How Will This Project Result in Cost
Savings and Paperwork Reduction?
I. What Are the Terms of the OMP Spring
House XL Project and How Will They Be
Enforced?
J. How Long Will This Project Last and
When Will It Be Completed?
IV. RCRA & Hazardous and Solid Waste
Amendments of 1984
A. Applicability of Rules in Authorized
States
B. Effect on Pennsylvania Authorization
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
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E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act of 1995
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
K. Executive Order 12988: Civil Justice
Reform
L. Congressional Review Act
I. Authority
EPA is publishing this regulation
under the authority of sections 2002,
3001, 3002, 3003, 3006, 3007, 3010,
3013, and 7004 of the Solid Waste
Disposal Act of 1970, as amended by the
Resource Conservation and Recovery
Act, as amended (42 U.S.C. 6912, 6921,
6922, 6923, 6926, 6927, 6930, 6934, and
6974).
II. Overview of Project XL
The Final Project Agreement (FPA)
sets forth the intentions of EPA,
Pennsylvania Department of
Environmental Protection (PADEP), and
the OMP Spring House facility with
regard to a project developed under
Project XL, an EPA initiative that allows
regulated entities to achieve better
environmental results with additional
regulatory flexibility. This final
regulation, along with the FPA
(contained in the docket for this rule
under Docket ID No. RCRA–2001–0021),
will facilitate implementation of the
project. Project XL —‘‘eXcellence and
Leadership’’— was announced on
March 16, 1995, as a central part of the
Agency’s effort to reinvent
environmental protection. See 60 FR
27282 (May 23, 1995). Project XL
provides a limited number of private
and public regulated entities an
opportunity to develop their own pilot
projects to request regulatory flexibility
that will result in environmental
protection that is superior to what
would be achieved through compliance
with current and reasonably-anticipated
future regulations. For more information
about the XL Program in general, and
XL project criteria and project
development processes in detail, readers
should refer to https://www.epa.gov/
projectxl/. Additional background
information on the proposed OMP
Spring House Project XL site-specific
rulemaking published is available at
https://www.epa.gov/projectxl/ortho/
index.htm and published in the Federal
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Register, specifically: July 24, 2001 (66
FR 38396), two descriptive documents
published in the Federal Register (60
FR 27282, May 23, 1995 and 62 FR
19872, April 23, 1997), and the
December 1, 1995 ‘‘Principles for
Development of Project XL Final Project
Agreements’’ document. For further
discussion as to how the OMP Spring
House XL project addresses the XL
criteria, readers should refer to the Final
Project Agreement available from the
EPA RCRA docket (Docket ID No.
RCRA–2001–0021; see ADDRESSES
section of today’s preamble).
III. Overview of the OMP Spring House
XL Pilot Project
Today’s final rule will facilitate
implementation of the FPA that has
been developed by EPA, PADEP, the
OMP Spring House facility, and other
stakeholders. Today’s final rule will
become effective under Pennsylvania
State law in accordance with the
Commonwealth’s hazardous waste
program, as described further in section
IV of this preamble.
To implement this XL project, today’s
final rule provides a site-specific
exemption from the regulatory
definition of hazardous waste for the
mixed wastes generated and treated in
OMP’s Spring House research and
development laboratory. The terms of
the overall XL project are contained in
an FPA which is included in the docket
for today’s final rule. A draft version of
the FPA was the subject of a Notice of
Availability published in the Federal
Register on September 1, 2000 in which
EPA solicited comment. The FPA was
signed on September 22, 2000 by
representatives of EPA, the
Pennsylvania Department of
Environmental Protection (PADEP), and
Ortho-McNeil Pharmaceutical. The
exemption from the regulatory
definition of hazardous waste of the
mixed wastes generated at the OMP
Spring House facility will remain in
effect only for the five-year term of this
XL project, and begins upon the
effective date of this final rule.
A. To Which Facilities Does the Final
Rule Apply?
This final rule will apply only to the
OMP Spring House facility. Thus, mixed
wastes generated in other
pharmaceutical research and
development facilities remain subject to
current Resource Conservation and
Recovery Act (RCRA) Subtitle C
regulations. (The Agency notes that the
term ‘‘RCRA Subtitle C regulations’’
includes the exemptions and exclusions
specific to mixed wastes that have been
promulgated as part of the regulatory
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program.) Further, the regulatory
modification will only affect the mixed
waste that is the focus of this XL project;
hazardous wastes resulting from any
other operations at the OMP Spring
House facility are not affected by today’s
final rule.
B. What Problems Will the OMP Spring
House XL Project Attempt To Address?
The OMP Spring House facility does
not believe the RCRA Subtitle C
regulatory controls, as applied to the
low-level mixed wastes (LLMW) it
generates and treats, provide any
additional environmental protection
than is otherwise provided by the
Atomic Energy Act (AEA) oversight, and
indeed believes that RCRA Subtitle C
regulatory controls serve as a major
disincentive to environmentally
protective on-site treatment of the small
volume of mixed wastes generated at the
facility.
While limited commercial off-site
treatment for such wastes is available,
the on-site, bench-scale, hightemperature catalytic oxidation unit
OMP Spring House will use to treat the
mixed wastes has been demonstrated to
be more efficient in preventing the
emission of radioactivity to the
atmosphere and at least as efficient, if
not more, at destroying the organic
components than available commercial
treatment. (The on-site treatment of
OMP Spring House’s mixed wastes has
been tested under a ‘‘treatability study’’
exemption provided in 40 CFR 261.4(f),
and granted by PADEP.) According to
OMP Spring House, it has not sought a
RCRA hazardous waste treatment permit
for the catalytic oxidation unit because
the costs of permitting cannot be
justified from a business standpoint for
the small volume of LLMW generated.
Nor does OMP Spring House intend to
become a commercial mixed waste
treatment facility, receiving mixed
wastes from off-site facilities which
might enable it to recover the costs of
a RCRA permit. Finally, OMP Spring
House has asserted (as have many of
those who commented on EPA’s July,
2001 proposed rule) that the costs of
existing off-site commercial treatment
for the small volume of mixed wastes
typically generated in the
pharmaceutical research industry are
very high and therefore hinder the
research and development of new
pharmaceuticals.
1. Current Regulatory Status of Mixed
Wastes
Mixed waste comprises radioactive
hazardous waste, subject to two
statutory authorities: (1) The RCRA as
implemented by EPA (or States
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authorized by EPA) with jurisdiction
over the hazardous waste component;
and (2) the AEA as implemented by
either the Department of Energy (DOE),
or the Nuclear Regulatory Commission
(NRC) (or its Agreement States) with
jurisdiction over the radioactive
component of the waste. Therefore,
absent today’s regulatory modification,
the management of the mixed wastes
that are the subject of this XL pilot
project would continue to be subject to
both RCRA permitting and NRC
licensing requirements and regulatory
oversight from the point the waste is
generated through to its final disposal.
Members of the regulated community
have raised concerns that this dual
regulatory oversight of LLMW is unduly
burdensome, duplicative and costly,
without providing any additional
protection of human health and the
environment beyond that achieved
under one regulatory regime. In
response to these concerns, on April 30,
2001, EPA Administrator Christine
Todd Whitman signed a final mixed
waste rule modifying the existing
regulatory framework to provide
flexibility related to the storage,
treatment (of certain types),
transportation and disposal for LLMW
(see 66 FR 27217, May 16, 2001). This
rule became effective on November 13,
2001 (‘‘Mixed Waste Rule’’).
In developing the Mixed Waste Rule,
EPA assessed NRC regulations for
storage, treatment, transportation and
disposal of low-level wastes (LLW) and
compared them with EPA’s regulations
for hazardous waste storage, treatment,
transportation and disposal applicable
to LLMW. The Agency found that given
NRC’s regulatory controls, protection of
human health and the environment
from chemical risks would not be
compromised by deferral to NRC’s LLW
management requirements under the
circumstances set forth in the Mixed
Waste Rule. Accordingly, through the
Mixed Waste Rule, the Agency adopted
a conditional exemption from certain
RCRA hazardous waste management
requirements for NRC-licensed
generators of LLMW, in specified
circumstances.
Basically, the Mixed Waste Rule
allows generators of LLMW to claim a
conditional exemption from the RCRA
regulatory definition of hazardous waste
for mixed wastes stored, treated,
transported or disposed of under the
NRC regulatory regime, acknowledging
the protectiveness of NRC regulations
for LLW (of which LLMW is a part). (For
the complete text of the Mixed Waste
Rule, see 66 FR 27217, May, 16, 2001.)
More specifically, the conditional
exemption allows, among other things,
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a generator to treat LLMW generated
under a single NRC or NRC Agreement
State license, in tanks or containers,
without having to obtain a RCRA
treatment permit, provided the form of
treatment is allowed under its NRC or
NRC Agreement State license. The
conditional exemption for storage and
treatment is only available to generators
of LLMW that are licensed by the NRC
or NRC Agreement States. In addition,
the Mixed Waste Rule provides that
LLMW that meets the applicable Land
Disposal Restrictions (LDR) standards
(either as generated or through
treatment) may be transported and
disposed of as LLW at an NRC or NRC
Agreement State licensed low-level
radioactive waste disposal facility
(LLRWDF), which need not also possess
a RCRA treatment, storage, or disposal
permit.
2. Site-Specific Considerations at the
OMP Spring House Facility
OMP Spring House conducts research
and development of pharmaceuticals/
drugs at its Spring House, Pennsylvania
facility. As part of this work, OMP
Spring House develops and utilizes
radiolabeled compounds to study the
bioabsorption and metabolism of the
drugs, in compliance with Food and
Drug Administration (FDA)
requirements. The radiolabeled
compounds typically consist of an
isotopically-labeled organic compound
and a solvent (the specific solvent varies
with the research being conducted). The
solvent is mixed with a radioisotope
(typically carbon-14 (14C) or tritium
(3H)), yielding both the desired
radiolabeled compound, and a waste
mixture that consists of radioactive
materials (over which NRC has
jurisdiction) and a hazardous organic
component (over which EPA has
jurisdiction). This radioactive/
hazardous organic waste mixture is the
LLMW that is the focus of this XL pilot
project. The estimated volume of mixed
waste produced per batch by OMP
Spring House ranges from less than 50
milliliters to several liters, with an
annual total volume of less than 50
liters.
OMP Spring House has developed an
innovative bench-scale treatment
process (using high-temperature
catalytic oxidization), which oxidizes
the mixed waste, thereby destroying its
hazardous waste components (yielding
water and CO2 ) and capturing the
radioactivity in the aqueous residuals or
as radioactive CO2. In this process the
liquid LLMW is completely reacted with
oxygen or air at high temperature in the
presence of an oxidation catalyst. [For a
general physical description of the
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bench-scale high-temperature catalytic
oxidizing unit and how it operates, the
reader is referred to the July 24, 2001
proposed rule (see 66 FR at 38399). For
a more complete technical description
of the unit, operations parameters and
analytical methodology, the reader is
referred to the document titled ‘‘A
Prototype High-Temperature Catalytic
Oxidation Process For Mixed Waste In
A Pharmaceutical Research Laboratory,’’
available in the docket for today’s final
rule under Docket ID No. RCRA–2001–
0021.]
OMP Spring House’s treatment of
carbon-14 labeled compounds generates
radioactive CO2 (which is subsequently
converted to potassium carbonate) and
the treatment of tritium labeled
compounds generates radioactive (i.e.,
tritiated) water (3H). These residual lowlevel wastes could then be sent off-site
for stabilization, recycling, or disposal
under NRC or NRC Agreement State
regulation. [The Agency notes that
because the treatment process yields
one of two residuals from a variety of
LLMW, they are more amenable to
recycling (e.g., recovery of tritium).
However, recycling the small volumes
of residuals being generated at the OMP
Spring House facility is not currently
economically viable. OMP Spring House
has been working to support efforts to
facilitate the recovery of radioactivity
from residuals like those it generates in
its high-temperature catalytic
oxidization process.] For tritium
containing compounds, the volume of
the treatment residual is generally the
same volume as the wastestream being
treated. For carbon-14 containing
compounds, the volume of the treatment
residuals is generally slightly higher
than the volume of the original
wastestream being treated. The yearly
estimated volume of the treatment
residuals generated by the hightemperature catalytic oxidation of
LLMW at OMP Spring House is 50 liters
per year, which is about the same as the
volume of the original LLMW.
OMP Spring House has been
operating this innovative catalytic
oxidation process for the treatment of
the mixed wastes it generates since 1996
under a ‘‘treatability study exemption’’
approved by the PADEP, which is
authorized to carry out portions of the
RCRA hazardous waste program in
Pennsylvania. This treatability study
has been conducted to evaluate the
performance of the catalytic oxidation
process on the organic component of
these mixed wastes and the capture of
the radioactive components.
The treatment technology being
employed by OMP Spring House is not
included under the 2001 Mixed Waste
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Rule because it is not conducted within
a ‘‘tank’’ or ‘‘container,’’ as those terms
are defined in RCRA. The Agency
determined that more specific controls
(as are presently provided under RCRA)
are generally more appropriate for
certain forms of treatment, such as
thermal treatment (including
incineration) which take place outside
of a ‘‘tank’’ or ‘‘container,’’ due to the
complexity and variety of such
processes and the specificity of RCRA
requirements. This XL pilot project
affords the Agency an opportunity to
test whether a defined subset of LLMW
(e.g., small volumes of research and
development laboratory-generated
mixed wastes being treated within the
NRC-licensed laboratory in which the
wastes are generated) may safely be
treated outside of a tank or container
(e.g., use of a bench-scale high
temperature catalytic oxidation process)
without RCRA regulatory controls (i.e.,
a treatment permit pursuant to Subtitle
C of RCRA), instead relying on AEA
regulations implemented by the NRC.
Thus, this pilot project is intended to
assess the appropriateness of the dual
oversight (i.e., concurrent RCRA and
AEA regulatory controls) exerted over
the small volumes of mixed wastes
generated and treated at this
pharmaceutical research and
development facility, and to
characterize those factors that could
inform EPA’s decision whether mixed
wastes generated and treated in similar
circumstances should also be exempted
from the regulatory definition of
hazardous wastes (and thus, RCRA
regulatory control) on a national basis
(in effect, deferring regulatory oversight
of these specific types of mixed wastes
to NRC or NRC Agreement States). The
pilot project will also provide the
Agency additional data regarding the
performance of the on-site, bench-scale
high-temperature catalytic oxidation
unit used to treat the mixed wastes,
which will also be considered as part of
any future determination regarding
possible changes to the types of units
included in RCRA’s May 2001 Mixed
Waste Rule.
To date, OMP Spring House’s
treatability study has yielded extremely
positive results, demonstrating that the
full range of organics used to produce
radiolabeled compounds are effectively
eliminated (routinely achieving
destruction and removal efficiencies
(DRE) of 99.999% to 99.99999%) by the
high-temperature catalytic oxidation
process. The treatment process exceeds
Land Disposal Restricitons (LDR)
treatment standards for organics, and
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releases only negligible amounts of
radioactivity11.
The catalytic oxidation unit is housed
in a laboratory fume hood within OMP
Spring House’s radiosynthesis
laboratory suite. All seven fume hoods
in the lab suite are connected to a
dedicated stack for air emissions. This
air pollution control system employs
high efficiency particulate arresting
(HEPA) filtration to capture any fugitive
dusts or particulate matter. No other
pharmaceutical research operations, or
other processes performed at the facility
are tied into this system. Air emissions
monitoring for radioactivity is
performed whenever the process is
operating. The monitoring is of the
consolidated non-turbulent air stream
within the ventilation system after the
juncture of the seven hoods and prior to
emissions into the atmosphere via the
dedicated stack.
C. What Solution Is Being Tested by the
OMP Spring House XL Project?
OMP Spring House originally
proposed that EPA address its LLMW in
one of three ways:
—Exempt the bench-scale treatment of
mixed wastes from permitting
requirements,
—Provide permit-by-rule exemptions for
the bench-scale treatment of mixed
wastes, or
—De-list post-oxidation wastes pursuant
to 40 CFR 260.20 and 260.22 to allow
the treatment of the LLMW.
Under each of these alternatives, OMP
Spring House noted that the laboratory
in which the wastes are generated and
treated would continue to be subject to
an NRC license, which it believed
would be sufficient to protect human
health and the environment during the
generation and treatment of its LLMW,
especially considering the very small
volumes of wastes being generated and
treated, the small size of the treatment
unit, the proximity of the treatment unit
to the point of generation (the wastes are
both generated and treated within the
same laboratory room), the sophisticated
level of expertise of the technicians that
work in the lab, and the protective
controls (e.g., emission limits) required
by the NRC license.
1 During calendar year 2003, air emissions
monitoring revealed an annual average
concentration of 7.54E–11 uCi/mL for tritium and
2.09E–11 uCi/mL for carbon-14 for all operations
(i.e., not just emissions from the high-temperature
catalytic oxidation process). These annual average
concentrations of radionuclides in effluent air are
less than 0.08% of the limits specified by NRC in
10 CFR Part 20 for allowable concentrations in
effluent air (i.e., 1 × 10E–7 mCi/mL for tritium and
3 × 10E–7 uCi/mL for carbon-14 (present as carbon
dioxide-14C)). Note that these units are expressed in
microcuries (10 E–6 curies)/milliliter.
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EPA and the PADEP agreed that
applicability of OMP Spring House’s
NRC license conditions was likely
sufficient to ensure that OMP Spring
House’s high-temperature catalytic
oxidation would be operated so as to be
protective of human health and the
environment absent RCRA regulatory
controls, and EPA determined that the
most appropriate mechanism to confirm
this was by exempting OMP Spring
House’s LLMW from RCRA’s definition
of hazardous waste, as discussed below.
D. What Regulatory Changes Are Being
Made To Implement This Project?
To allow for this XL project to be
implemented, the Agency proposed on
July 24, 2001 to provide a site-specific
exemption in 40 CFR 261.4(b) (i.e.,
‘‘Solid wastes which are not hazardous
wastes’’) for the mixed wastes generated
and treated in OMP Spring House’s
pharmaceutical research and
development (R&D) laboratory (see 66
FR 38396). The Agency is today
finalizing this site-specific rule, albeit
clarifying that it comprises an
exemption to RCRA’s definition of
hazardous waste, not an exclusion to
RCRA’s definition of solid waste.2 The
effect of this exemption, assuming all
the conditions are met, is to remove
these wastes from RCRA Subtitle C
regulation at the point of their
generation. Further, because the
residuals resulting from the catalytic
oxidation treatment process will not be
derived from hazardous wastes, no
‘‘delisting’’ is required for these
residuals (since the original wastestream
will no longer comprise a RCRA
‘‘listed’’ waste). The Agency believes
2 In its July, 2001 proposal, EPA characterized the
regulatory flexibility to be offered under this XL
Project as comprising a
‘‘site specific exclusion in 40 CFR 261.4(b) (i.e.
‘Solid wastes which are not hazardous wastes’) for
the mixed wastes generated and treated in OMP
Spring House’s pharmaceutical research and
development (R&D) laboratory. The effect of this
exclusion, assuming all the conditions are met, will
be to exclude these wastes from RCRA Subtitle C
regulation at the point of generation, * * * Instead
of being considered ‘mixed wastes,’ these wastes
will simply be considered low-level wastes (LLWs)
subject to NRC or NRC Agreement State regulation.’’
66 FR at 38400–01.
EPA has determined that its use of the word
‘‘exclusion’’ (which generally applies to materials
excluded from RCRA’s definition of solid waste
under 40 CFR 261.4(a) rather than materials
exempted from RCRA’s definition of hazardous
waste under 40 CFR 261.4(b)), and the potential
implication that this regulatory change would result
in clarification. In this final rule, EPA makes plain
that the effect of this regulatory change is to
conditionally exempt OMP Spring House’s LLMW
from RCRA’s definition of hazardous waste under
40 CFR 261.4(b) (and thus from its hazardous waste
regulations). OMP Spring House’s LLMW remains
a solid waste under RCRA and thus, is subject to
EPA’s enforcement authority under Section 7001 of
RCRA.
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that this regulatory mechanism is the
most efficient way to provide OMP
Spring House with the regulatory
outcome it seeks and implement the XL
pilot project.
The site-specific exemption being
finalized today is conditioned on
various reporting requirements intended
to provide the Agency with the data
necessary to determine whether this XL
pilot project is a success and obtain the
information to help it decide whether
the regulatory change should be
‘‘transferred’’ to the national program
(which, if it occurs, would happen
through normal rulemaking procedures).
The specific conditions are further
discussed in section III.I.
E. Why Is EPA Supporting This
Approach To Removing RCRA
Regulatory Controls Over a Mixed
Waste?
The Agency agrees with OMP Spring
House that this XL project has merit and
has the potential to result in significant
environmental and efficiency benefits
should the regulatory change be adopted
on a national basis. While the Agency
adopted the Mixed Waste Rule to
generically address the regulation of
some mixed wastes, Project XL offers
the Agency the opportunity to test
alternative approaches, in this case, an
alternative approach tailored to a
specific subset of the generic category of
mixed wastes not covered by the Mixed
Waste Rule. The Agency believes this is
the type of ‘‘test’’ that Project XL is
intended to facilitate. The information
and data gathered throughout the course
of this XL project will provide the
Agency with the ability to make a more
informed determination regarding the
appropriate regulatory controls for
‘‘mixed waste’’ generally, as well as
certain discrete subsets of ‘‘mixed
waste’’ that may be amenable to an
alternative regulatory approach.
F. How Have Various Stakeholders Been
Involved in This Project?
During the developmental stages of
this XL pilot project, OMP Spring House
cultivated stakeholder involvement
from the local community and local
environmental groups in a variety of
ways. These methods included
communicating through the local news
media, announcements at Township
meetings, public meetings and direct
contact with interested parties. For a
more detailed description of the
methods used to involve stakeholders
and the meetings held with the local
community to discuss the pilot project,
the reader is referred to the July 24,
2001 proposed rulemaking (see 66 FR at
38401).
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OMP Spring House understands that
stakeholder involvement is an integral
part of the XL process and will continue
to hold public meetings with the local
community to provide updates and
information on this XL pilot project, as
needed.
G. Response to Major Comments
Received on the Proposed Rule
The Agency received 65 comments in
response to the July 24, 2001 proposed
rule. Detailed responses to all of these
comments is presented in the document
titled ‘‘Response to Comments on the
OMP Spring House XL Project NPRM’’
contained in the docket for today’s final
rulemaking under Docket ID No. RCRA–
2001–0021. The vast majority of these
comments were very supportive and
generally encouraged the Agency to
move quickly to consider similar
regulatory flexibility on a national scale.
However, two commenters submitted
adverse comments, and several
commenters provided editorial
suggestions and requests for
clarification.
The two commenters which opposed
the proposed rule were both commercial
LLMW treatment facilities, capable of
treating OMP Spring House’s’s LLMW.
(EPA does note that several other
treatment facilities offered comments
that were supportive of the proposal.)
These two commenters questioned the
merits of reducing regulatory oversight
for such wastes (with the potential for
increased risks); the impact of such an
exemption on the existing commercial
mixed waste treatment industry (which
has invested substantial resources to
obtain the necessary permits and
licenses), and, (if the regulatory
flexibility is adopted on a national scale
for research and development
laboratories) the advisability of having
many facilities generating radioactive
residuals (even if they are small in
volume and recyclable) rather than a
small number of commercial facilities
generating such residuals (albeit in
larger quantities).
The Agency has considered the
concerns expressed by these
commenters; however, it believes this
pilot project should go forward. The
Agency believes that the NRC license
provides sufficient protections, at least
in this specific situation, such that a
RCRA permit is not necessary. Thus, we
disagree with the commenter who
argues that the facility would be
‘‘unlicensed/unpermitted.’’ We also
disagree with the commenter who
suggested that this rulemaking would
reduce the treatment standards for this
waste. As has been demonstrated, the
high-temperature catalytic oxidation
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unit utilized by OMP Spring House
meets or exceeds the existing treatment
standards that these wastes are subject
to. Thus, we believe that the rule will
not pose additional risks to workers or
the public. Moreover, the Agency notes
that since OMP Spring House’s waste
stream will remain a solid waste under
RCRA, it retains the authority to require
OMP Spring House to address any threat
which it determines presents an
imminent threat to the public health or
the environment. See 42 U.S.C. 6973(a).
Further, a core goal of EPA’s XL
initiative is to promote innovation,
which includes considering whether
new approaches are better able to
protect the public health and the
environment than existing regulatory
requirements, even where the latter are
long-established and required
significant investment by facilities to
comply. Therefore, while EPA
understands the concerns expressed by
these commercial mixed waste
treatment facilities, the Agency does not
believe that these concerns are sufficient
to preclude the exploration of other
approaches or, in this specific case,
testing the proposition that an NRC
license provides sufficient protections
for the thermal treatment of small
volumes of research and development
LLMW in the same laboratory where the
wastes are generated. (The Agency notes
that these commenters did not suggest
any specific RCRA regulatory
requirement that they thought is
necessary to protect human health and
the environment at OMP Spring House’s
NRC-licensed facility.)
H. How Will This Project Result in Cost
Savings and Paperwork Reduction?
OMP Spring House has stated that if
it became required to obtain a RCRA
permit to operate its catalytic oxidation
unit, it would instead send its small
volume of mixed wastes generated to a
commercial treatment facility.3 For
mixed wastes, commercial treatment
costs are typically based primarily upon
the level of radioactivity (i.e., number of
curies) being treated, as well as the
volume of the waste. The costs range
from approximately $20,000–$35,000
per curie, with an average cost of
$30,000/curie. This represents a
3 OMP Spring House believes that the current
RCRA permitting requirements are intended to
apply primarily to commercial hazardous waste
treatment facilities, and that it would be difficult to
justify investing the costs of obtaining and
maintaining a RCRA Subtitle C permit unless it
could recoup such costs through commercial
activities (i.e., treating wastes generated by other
generators for a fee). OMP Spring House has stated
that it neither is nor intends to be in the commercial
waste treatment business, and therefore it would
not seek such a permit.
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$300,000/year cost for OMP Spring
House, which generates up to 10 curies
of mixed waste per year. OMP Spring
House has stated that other cost savings,
such as reduced transportation costs
and administrative/paperwork savings
resulting from no longer having its
LLMW be defined as a RCRA hazardous
waste, are relatively minor compared
with the costs of commercial LLMW
treatment.
EPA understands that pharmaceutical,
medical, and academic research
activities, such as the radiolabeling
which generates OMP Spring House’s
mixed wastes, are often limited by the
high costs of waste management.
Because waste management costs are
such a major factor in the budgets
allocated to such R&D activities, the
high cost of waste management can
significantly reduce the money actually
spent on R&D. With more cost-effective
treatment (such as OMP Spring House’s
on-site bench-scale catalytic oxidation
unit), more money could be spent on the
actual research and development of
pharmaceuticals.
I. What Are the Terms of the OMP
Spring House XL Project and How Will
They Be Enforced?
To implement this XL pilot project,
EPA is today modifying 40 CFR 261.4(b)
by providing a site-specific exemption
from the regulatory definition of
hazardous waste for OMP Spring
House’s LLMW generated and treated in
their radiosynthesis laboratory, which is
subject to a ‘‘Type A Broad Scope’’ NRC
license for research and development. In
accordance with 25 Pa. Code section
261a.1 of Pennsylvania’s RCRAauthorized hazardous waste program,
EPA’s exemption of OMP Spring
House’s mixed waste from the
regulatory definition of hazardous waste
under RCRA is automatically
incorporated in Pennsylvania’s
hazardous waste regulations because the
State hazardous waste regulations
incorporate 40 CFR 261.4(b) by
reference, including any modification or
additions made to that section by the
Federal program.
Through the development of the Final
Project Agreement (FPA), OMP Spring
House had agreed to comply with
several conditions for this exemption,
which were included in the regulatory
text that was proposed on July 24, 2001
and are being finalized today. These
conditions focus on demonstrating the
efficacy of the treatment technology,
and to gather the data and other
information that will allow the Agency
to make a determination regarding the
possible future adoption of this site-
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specific exemption as a nationwide
generic exemption.
The site-specific exemption is limited
to a total volume of 50 liters/year of
mixed waste and only applies to mixed
wastes that are generated and treated
using OMP Spring House’s hightemperature catalytic oxidation process
within the OMP Spring House facility’s
radiosynthesis laboratory. In addition,
the exemption is further conditioned
such that OMP Spring House must
report, on a semi-annual basis, the
following:
(1) Analysis demonstrating the
destruction and removal efficiencies for
all organic components of the exempted
wastes subject to treatment.
(2) Analysis demonstrating the
capture efficiencies for the radioactive
component of the exempted wastes
subject to treatment, and an estimate of
the amount of radioactivity that was
released during the reporting period.
(3) Analyses of the constituent
concentrations, including inorganic
constituents, present and radioactivity
of the exempted wastes prior to, and
after, treatment.
(4) The volume of exempted wastes
treated per batch, as well as a total for
the duration of the reporting period.
(5) The final disposition of the
radioactive residuals from the treatment
of the exempted wastes.
In addition, OMP Spring House
commits to work with other companies,
organizations and research institutes to:
(1) Further develop a standard, benchscale off-the-shelf treatment unit, based
on its high-temperature catalytic
oxidation technology, to be made
available to any company or institution
that generates similar R&D quantities of
mixed wastes, and (2) further develop
the technology and market for the
recycling and reuse of the radioactive
component of the LLMW (i.e., the LLW
residuals resulting from the treatment of
the LLMW).
As part of meeting this commitment,
OMP Spring House will prepare (and
submit to EPA for review and comment)
a proposed plan summarizing how it
will accomplish this goal. Because these
two commitments involve the
participation of other companies and
entities outside OMP Spring House’s
control and thus are much less certain
than the conditions discussed above,
these commitments have not been made
conditions of the exemption. However,
in evaluating the success of this XL
project, these ‘‘non-enforceable’’
commitments will be considered by
EPA and the PADEP.
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J. How Long Will This Project Last and
When Will It Be Completed?
This project will be in effect for five
years from the date that this final
rulemaking becomes effective, unless it
is terminated earlier or extended by all
project signatories (if the FPA and rule
are extended, this will be done through
a rulemaking seeking the comments and
input of stakeholders and the public).
Any project signatory may terminate its
participation in this project at any time
in accordance with the procedures set
forth in the FPA. The project will be
completed at the conclusion of the fiveyear anniversary of today’s final
rulemaking or at a time earlier or later
as agreed to by the parties involved.
IV. RCRA & Hazardous and Solid
Waste Amendments of 1984
A. Applicability of Rules in Authorized
States
Under section 3006 of RCRA, EPA
may authorize qualified States to
administer and enforce the RCRA
program for hazardous waste within the
State. (See 40 CFR Part 271 for the
standards and requirements for
authorization.) States with final
authorization administer their own
hazardous waste programs in lieu of the
Federal program. Following
authorization, a state continues to have
enforcement responsibility under its
State law to pursue violations of its
hazardous waste program. EPA
continues to have independent
enforcement authority under sections
3007, 3008, 3013 and 7003 of RCRA.
After authorization, Federal rules
issued under RCRA provisions that
predate the Hazardous and Solid Waste
Amendments of 1984 (HSWA), no
longer apply in the authorized state.
New Federal requirements imposed by
non-HSWA rules do not take effect in an
authorized State until the State adopts
the requirements as State law.
In contrast, under section 3006(g) of
RCRA, new requirements and
prohibitions imposed by HSWA take
effect in authorized States at the same
time they take effect in nonauthorized
States. EPA is directed to carry out
HSWA requirements and prohibitions in
authorized States until the State is
granted authorization to do so.
B. Effect on Pennsylvania Authorization
Today’s final rule is promulgated
pursuant to non-HSWA authority.
Pennsylvania initially received
authority from EPA to implement its
base hazardous waste program effective
January 30, 1986 (see 51 FR 1791,
January 15, 1986). Because EPA clarified
that the hazardous waste component of
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36855
mixed waste was subject to RCRA after
Pennsylvania received its initial RCRA
base authorization (see 51 FR 24504,
July 3, 1986), mixed waste was not
initially included within Pennsylvania’s
authorized base program. Pennsylvania
subsequently applied to EPA, seeking
approval that its hazardous waste
program, as revised (including its
adoption of regulations governing mixed
waste), complied with RCRA. Under the
terms of the Commonwealth’s
hazardous waste program, subsequent
modifications and additions to EPA’s
RCRA regulations as published in the
Code of Federal Regulations (with
certain exceptions not relevant here) are
automatically incorporated into the
Commonwealth’s hazardous waste
program. See 29 Pa. Bull. 2367, 2370
(May 1, 1999), 65 FR at 57734 and
57736 (September 26, 2000).
On September 26, 2000, EPA
published notice of Final Authorization
of Pennsylvania’s hazardous waste
program, including specifically its
regulation of mixed waste, effective
November 27, 2000. See 65 FR 57734
and 57736 (September 26, 2000). EPA
did not receive any adverse comments,
and thus EPA’s authorization of
Pennsylvania’s hazardous waste
program (including mixed wastes)
became effective on November 27, 2000.
This XL project was undertaken and
developed (by EPA, PADEP, and OMP
Spring House) with the assumption that
Pennsylvania would receive
authorization for mixed wastes,
necessitating the regulatory flexibility
on the part of PADEP to implement the
XL project. Since Pennsylvania has had
RCRA authorization for mixed wastes
since November 27, 2000, and because
Pennsylvania’s definition of hazardous
waste under the Pennsylvania Solid
Waste Management Act (PaSWMA),
including its exclusions and
exemptions, incorporates RCRA’s
analogous provisions upon their
promulgation, this rule will have the
effect of exempting OMP Spring House’s
mixed wastes from regulation by the
Commonwealth as a hazardous waste
under its hazardous waste program,
which in turn allows Pennsylvania to
implement this XL project.
V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735), the Agency must determine
whether this regulatory action is
‘‘significant’’ and therefore subject to
formal review by the Office of
Management and Budget (OMB) and to
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the requirements of the Executive Order,
which include assessing the costs and
benefits anticipated as a result of this
regulatory action. The Order defines
‘‘significant regulatory’’ action as one
that is likely to result in a rule that may:
(1) Have an annual effect on the
economy of $100 million or more or
adversely affect in a material way the
economy, a sector of the economy,
productivity, competition, jobs, the
environment, public health or safety, or
State, local, or tribal governments or
communities; (2) create a serious
inconsistency or otherwise interfere
with an action taken or planned by
another agency; (3) materially alter the
budgetary impact of entitlements,
grants, user fees, or loan programs or the
rights and obligations of recipients
thereof; or (4) raise novel legal or policy
issues arising out of legal mandates, the
President’s priorities, or the principles
set forth in the Executive Order.
Because this rule affects only one
facility, it is not a rule of general
applicability and therefore is not subject
to OMB review and Executive Order
12866.
B. Paperwork Reduction Act
This action does not impose an
information collection burden under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq., since it
applies to only one facility. It is exempt
from OMB review under the Paperwork
Reduction Act because it is a sitespecific rule, directed to fewer than ten
persons. 44 U.S.C. 3502(3), (10); 5 CFR
1320.3(c), 1320.4 and 1320.5.
Burden means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, or disclose
or provide information to or for a
Federal agency. This includes the time
needed to review instructions; develop,
acquire, install, and utilize technology
and systems for the purposes of
collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
An agency may not conduct or
sponsor, and a person is not required to
respond to a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR part 9.
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C. Regulatory Flexibility Act
Pursuant to the Regulatory Flexibility
Act (5 U.S.C. 601 et seq., as amended by
the Small Business Regulatory
Enforcement Fairness Act (SBREFA) of
1996), whenever an Agency is required
to publish a notice for any proposed or
final rule, it must prepare and make
available for public comment a
regulatory flexibility analysis that
describes the effect of the rule on small
entities (i.e., small businesses, small
organizations, and small governmental
jurisdictions). However, no regulatory
flexibility analysis is required if the
head of an agency certifies the rule will
not have a significant economic impact
on a substantial number of small
entities. SBREFA amended the
Regulatory Flexibility Act to require
Federal agencies to provide a statement
of the factual basis for certifying that a
rule will not have a significant
economic impact on a substantial
number of small entities. This rule will
not have a significant impact on a
substantial number of small entities
because it only affects the OMP Spring
House facility, and it is not a small
entity.
Based on the foregoing discussion, I
hereby certify that this rule will not
have a significant adverse economic
impact on a substantial number of small
entities. Consequently, the Agency has
determined that preparation of a formal
Regulatory Flexibility Analysis is
unnecessary.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
federal agencies to assess the effects of
their regulatory actions on state, local,
and tribal governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘federal mandates’’ that may result
in expenditures by state, local, and
tribal governments, in the aggregate, or
to the private sector, of $100 million or
more in any one year.
Before promulgating a rule for which
a written statement is needed, section
205 of the UMRA generally requires
EPA to identify and consider a
reasonable number of regulatory
alternatives and adopt the least costly,
most cost-effective or least burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply when they are
inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the least
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costly, most cost-effective, or least
burdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted. Before EPA establishes
any regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments, it must have developed
under section 203 of the UMRA a small
government agency plan. The plan must
provide for notifying potentially
affected small governments, enable
officials of affected small governments
to have meaningful and timely input in
the development of EPA regulatory
proposals with significant federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
As noted above, this rule is applicable
only to one facility in Pennsylvania.
EPA has determined that this rule
contains no regulatory requirements that
might significantly or uniquely affect
small governments. EPA has also
determined that this rule does not
contain a Federal mandate that may
result in expenditures of $100 million or
more for State, local, and tribal
governments, in the aggregate, or the
private sector in any one year. Thus,
today’s rule is not subject to the
requirements of sections 202 and 205 of
the UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications. ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the states, on the relationship
between the National Government and
the states, or on the distribution of
power and responsibilities among the
various levels of government.’’
This rule does not have federalism
implications. It will not have a
substantial direct effect on States, on the
relationship between the National
Government and the States, or on the
distribution of powers and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. Today’s rule
will only affect one facility, providing
regulatory flexibility applicable to this
specific site. Thus, Executive Order
13132 does not apply to this rule.
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F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 6, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ ‘‘Policies that have tribal
implications’’ is defined in the
Executive Order to include regulations
that have ‘‘substantial direct effects on
one or more Indian tribes, on the
relationship between the Federal
Government and the Indian tribes, or on
the distribution of power and
responsibilities between the Federal
Government and Indian tribes.’’
This final rule, does not have tribal
implications. It will not have substantial
direct effects on tribal governments, on
the relationship between the Federal
Government and Indian tribes, or on the
distribution of power and
responsibilities between the Federal
Government and Indian tribes, as
specified in Executive Order 13175.
EPA is currently unaware of any Indian
tribes located in the vicinity of the
facility. Thus, Executive Order 13175
does not apply to this rule.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
Executive Order 13045, ‘‘Protection of
Children From Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997) applies to any rule that
EPA determines (1) is ‘‘economically
significant’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
the Agency must evaluate the
environmental health or safety effects of
the planned rule on children and
explain why the planned regulation is
preferable to other potential effective
and reasonably feasible alternatives
considered by the Agency.
This rule is not subject to Executive
Order 13045 because it is not an
economically significant rule as defined
by Executive Order 12866, and because
the Agency believes that the
environmental health or safety risks
addressed by this action do not present
a disproportionate risk to children.
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H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not a ‘‘significant energy
action’’ as defined in Executive Order
13211, ‘‘Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355, May
22, 2001) because it is not likely to have
a significant adverse effect on the
supply, distribution, or use of energy. It
will not result in increased energy
prices, increased cost of energy
distribution, or an increased
dependence on foreign supplies of
energy.
I. National Technology Transfer and
Advancement Act of 1995
36857
Today’s rule applies to one facility in
Pennsylvania. Overall, no
disproportional impacts to minority or
low income communities are expected.
Today’s rule applies to one facility in
Pennsylvania. Overall, no
disproportional impacts to minority or
low income communities are expected.
K. Executive Order 12988: Civil Justice
Reform
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, as
required by section 3 of Executive Order
12988, entitled Civil Justice Reform (61
FR 4729, February 7, 1996).
L. Congressional Review Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA,’’ Public Law
104–113, section 12(d) (15 U.S.C. 272
note) directs EPA to use voluntary
consensus standards in its regulatory
activities unless to do so would be
inconsistent with applicable law or
otherwise impractical. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by voluntary consensus
standards bodies. The NTTAA directs
EPA to provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards. Today’s
rule does not establish technical
standards. Therefore, EPA did not
consider the use of any voluntary
consensus standards.
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. EPA is not required to submit a
rule report regarding today’s action
under section 801 because this is a rule
of particular applicability.
J. Executive Order 12898: Federal
Actions to Address Environmental
Justice in Minority Populations and
Low-Income Populations
Environmental protection, Hazardous
materials, Waste treatment and disposal.
Executive Order 12898, ‘‘Federal
Actions to Address Environmental
Justice in Minority Populations and
Low-Income Populations’’ (February 11,
1994) is designed to address the
environmental and human health
conditions of minority and low-income
populations. EPA is committed to
addressing environmental justice
concerns and has assumed a leadership
role in environmental justice initiatives
to enhance environmental quality for all
citizens of the United States. The
Agency’s goals are to ensure that no
segment of the population, regardless of
race, color, national origin, income, or
net worth bears disproportionately high
and adverse human health and
environmental impacts as a result of
EPA’s policies, programs, and activities.
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List of Subjects in 40 CFR Part 261
Dated: June 20, 2005.
Stephen L. Johnson,
Administrator.
For the reasons set forth in the
preamble, title 40, chapter I of the Code
of Federal Regulations is amended as
follows:
I
PART 261—IDENTIFICATION AND
LISTING OF HAZARDOUS WASTE
1. The authority citation for part 261
continues to read as follows:
I
Authority: 42 U.S.C. 6905, 6912(a), 6921,
6922, 6924(y), and 6938.
Subpart A—General
2. Section 261.4 is amended by adding
paragraph (b)(17) to read as follows:
I
§ 261.4
*
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(b) * * *
(17) Solid waste that would otherwise
meet the definition of low-level mixed
wastes (LLMW) pursuant to § 266.210 of
this chapter that is generated at the
Ortho-McNeil Pharmaceutical, Inc.
(OMP Spring House) research and
development facility in Spring House,
Pennsylvania and treated on-site using a
bench-scale high temperature catalytic
oxidation unit is not a hazardous waste
provided that:
(i) The total volume of LLMW
generated and treated is no greater than
50 liters/year, (ii) OMP Spring House
submits a written report to the EPA
Region III office once every six months
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beginning six months after June 27,
2005, that must contain the following:
(A) Analysis demonstrating the
destruction and removal efficiency of
the treatment technology for all organic
components of the wastestream,
(B) Analysis demonstrating the
capture efficiencies of the treatment
technology for all radioactive
components of the wastestream and an
estimate of the amount of radioactivity
released during the reporting period,
(C) Analysis (including
concentrations of constituents,
including inorganic constituents,
present and radioactivity) of the
wastestream prior to and after treatment,
PO 00000
Frm 00050
Fmt 4700
Sfmt 4700
(D) Volume of the wastestream being
treated per batch, as well as a total for
the duration of the reporting period, and
(E) Final disposition of the radioactive
residuals from the treatment of the
wastestream.
(iii) OMP Spring House makes no
significant changes to the design or
operation of the high temperature
catalytic oxidation unit or the
wastestream.
(iv) This exclusion will remain in
affect for 5 years from June 27, 2005.
*
*
*
*
*
[FR Doc. 05–12658 Filed 6–24–05; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\27JNR1.SGM
27JNR1
Agencies
[Federal Register Volume 70, Number 122 (Monday, June 27, 2005)]
[Rules and Regulations]
[Pages 36850-36858]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-12658]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 261
[RCRA-2001-0021; FRL-7928-8]
RIN 2090-AA14
Project XL Site-Specific Rulemaking for the Ortho-McNeil
Pharmaceutical, Inc. Facility in Spring House, PA Involving On-Site
Treatment of Mixed Wastes
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) is today finalizing
this rule to implement a pilot project under the Project XL program,
providing site-specific regulatory flexibility under the Resource
Conservation and Recovery Act (RCRA), as amended, for the Ortho-McNeil
Pharmaceutical, Inc. facility in Spring House, Pennsylvania (OMP Spring
House). The principal objective of this XL project is to obtain
information helpful to determining whether regulatory oversight by the
Nuclear Regulatory Commission (NRC), or NRC Agreement States, under
authority of the Atomic Energy Act (AEA) is sufficient to ensure
protection of human health and the environment regarding the management
of certain small volumes of mixed wastes (i.e., RCRA hazardous wastes
that also contain radioactive materials) that are both generated and
treated in an NRC-licensed pharmaceutical research and development
laboratory. If, as a result of this XL project, the Agency determines
that certain small volumes of low-level mixed wastes (LLMW) generated
and managed under NRC oversight need not also be subject to RCRA
hazardous waste regulations to ensure protection of human health and
the environment, EPA may consider adopting the approach on a national
basis.
DATES: Effective Date: This final rule is effective on June 27, 2005.
ADDRESSES: EPA has established a docket for this action under Docket ID
No. RCRA-2001-0021. All documents in the docket are listed in the
EDOCKET index at https://www.epa.gov/edocket. Although listed in the
index, some information is not publicly available, i.e., 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 in
EDOCKET or in hard copy at the RCRA Docket, EPA/DC, EPA West, Room
B102, 1301 Constitution Ave., NW., Washington, DC. The Public Reading
Room is open from 8:30 a.m. to 4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone number for the Public Reading
Room is (202) 566-1744, and the telephone number for the RCRA Docket is
(202) 566-0270.
FOR FURTHER INFORMATION CONTACT: Mr. Charles Howland, U.S.
Environmental Protection Agency, Region III (3OR00), 1650 Arch Street,
Philadelphia, PA, 19103-2029. Mr. Howland can be reached at (215) 814-
2645 (or howland.charles@epa.gov).
SUPPLEMENTARY INFORMATION:
Outline of Today's Rule
The information presented in this preamble is organized as follows:
I. Authority
II. Overview of Project XL
III. Overview of the OMP Spring House XL Pilot Project
A. To Which Facilities Does the Final Rule Apply?
B. What Problems Does the OMP Spring House XL Project Attempt To
Address?
1. Current Regulatory Status of Mixed Wastes
2. Site-Specific Considerations at the OMP Spring House Facility
C. What Solution Is Being Tested by the OMP Spring House XL
Project?
D. What Regulatory Changes Are Being Made to Implement this
Project?
E. Why is EPA Promulgating This Approach To Removing RCRA
Regulatory Controls Over a Mixed Waste?
F. How Have Various Stakeholders Been Involved in this Project?
G. Response to Major Comments Received on the Proposed Rule
H. How Will This Project Result in Cost Savings and Paperwork
Reduction?
I. What Are the Terms of the OMP Spring House XL Project and How
Will They Be Enforced?
J. How Long Will This Project Last and When Will It Be
Completed?
IV. RCRA & Hazardous and Solid Waste Amendments of 1984
A. Applicability of Rules in Authorized States
B. Effect on Pennsylvania Authorization
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act of 1995
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Executive Order 12988: Civil Justice Reform
L. Congressional Review Act
I. Authority
EPA is publishing this regulation under the authority of sections
2002, 3001, 3002, 3003, 3006, 3007, 3010, 3013, and 7004 of the Solid
Waste Disposal Act of 1970, as amended by the Resource Conservation and
Recovery Act, as amended (42 U.S.C. 6912, 6921, 6922, 6923, 6926, 6927,
6930, 6934, and 6974).
II. Overview of Project XL
The Final Project Agreement (FPA) sets forth the intentions of EPA,
Pennsylvania Department of Environmental Protection (PADEP), and the
OMP Spring House facility with regard to a project developed under
Project XL, an EPA initiative that allows regulated entities to achieve
better environmental results with additional regulatory flexibility.
This final regulation, along with the FPA (contained in the docket for
this rule under Docket ID No. RCRA-2001-0021), will facilitate
implementation of the project. Project XL --``eXcellence and
Leadership''-- was announced on March 16, 1995, as a central part of
the Agency's effort to reinvent environmental protection. See 60 FR
27282 (May 23, 1995). Project XL provides a limited number of private
and public regulated entities an opportunity to develop their own pilot
projects to request regulatory flexibility that will result in
environmental protection that is superior to what would be achieved
through compliance with current and reasonably-anticipated future
regulations. For more information about the XL Program in general, and
XL project criteria and project development processes in detail,
readers should refer to https://www.epa.gov/projectxl/. Additional
background information on the proposed OMP Spring House Project XL
site-specific rulemaking published is available at https://www.epa.gov/
projectxl/ortho/index.htm and published in the Federal
[[Page 36851]]
Register, specifically: July 24, 2001 (66 FR 38396), two descriptive
documents published in the Federal Register (60 FR 27282, May 23, 1995
and 62 FR 19872, April 23, 1997), and the December 1, 1995 ``Principles
for Development of Project XL Final Project Agreements'' document. For
further discussion as to how the OMP Spring House XL project addresses
the XL criteria, readers should refer to the Final Project Agreement
available from the EPA RCRA docket (Docket ID No. RCRA-2001-0021; see
ADDRESSES section of today's preamble).
III. Overview of the OMP Spring House XL Pilot Project
Today's final rule will facilitate implementation of the FPA that
has been developed by EPA, PADEP, the OMP Spring House facility, and
other stakeholders. Today's final rule will become effective under
Pennsylvania State law in accordance with the Commonwealth's hazardous
waste program, as described further in section IV of this preamble.
To implement this XL project, today's final rule provides a site-
specific exemption from the regulatory definition of hazardous waste
for the mixed wastes generated and treated in OMP's Spring House
research and development laboratory. The terms of the overall XL
project are contained in an FPA which is included in the docket for
today's final rule. A draft version of the FPA was the subject of a
Notice of Availability published in the Federal Register on September
1, 2000 in which EPA solicited comment. The FPA was signed on September
22, 2000 by representatives of EPA, the Pennsylvania Department of
Environmental Protection (PADEP), and Ortho-McNeil Pharmaceutical. The
exemption from the regulatory definition of hazardous waste of the
mixed wastes generated at the OMP Spring House facility will remain in
effect only for the five-year term of this XL project, and begins upon
the effective date of this final rule.
A. To Which Facilities Does the Final Rule Apply?
This final rule will apply only to the OMP Spring House facility.
Thus, mixed wastes generated in other pharmaceutical research and
development facilities remain subject to current Resource Conservation
and Recovery Act (RCRA) Subtitle C regulations. (The Agency notes that
the term ``RCRA Subtitle C regulations'' includes the exemptions and
exclusions specific to mixed wastes that have been promulgated as part
of the regulatory program.) Further, the regulatory modification will
only affect the mixed waste that is the focus of this XL project;
hazardous wastes resulting from any other operations at the OMP Spring
House facility are not affected by today's final rule.
B. What Problems Will the OMP Spring House XL Project Attempt To
Address?
The OMP Spring House facility does not believe the RCRA Subtitle C
regulatory controls, as applied to the low-level mixed wastes (LLMW) it
generates and treats, provide any additional environmental protection
than is otherwise provided by the Atomic Energy Act (AEA) oversight,
and indeed believes that RCRA Subtitle C regulatory controls serve as a
major disincentive to environmentally protective on-site treatment of
the small volume of mixed wastes generated at the facility.
While limited commercial off-site treatment for such wastes is
available, the on-site, bench-scale, high-temperature catalytic
oxidation unit OMP Spring House will use to treat the mixed wastes has
been demonstrated to be more efficient in preventing the emission of
radioactivity to the atmosphere and at least as efficient, if not more,
at destroying the organic components than available commercial
treatment. (The on-site treatment of OMP Spring House's mixed wastes
has been tested under a ``treatability study'' exemption provided in 40
CFR 261.4(f), and granted by PADEP.) According to OMP Spring House, it
has not sought a RCRA hazardous waste treatment permit for the
catalytic oxidation unit because the costs of permitting cannot be
justified from a business standpoint for the small volume of LLMW
generated. Nor does OMP Spring House intend to become a commercial
mixed waste treatment facility, receiving mixed wastes from off-site
facilities which might enable it to recover the costs of a RCRA permit.
Finally, OMP Spring House has asserted (as have many of those who
commented on EPA's July, 2001 proposed rule) that the costs of existing
off-site commercial treatment for the small volume of mixed wastes
typically generated in the pharmaceutical research industry are very
high and therefore hinder the research and development of new
pharmaceuticals.
1. Current Regulatory Status of Mixed Wastes
Mixed waste comprises radioactive hazardous waste, subject to two
statutory authorities: (1) The RCRA as implemented by EPA (or States
authorized by EPA) with jurisdiction over the hazardous waste
component; and (2) the AEA as implemented by either the Department of
Energy (DOE), or the Nuclear Regulatory Commission (NRC) (or its
Agreement States) with jurisdiction over the radioactive component of
the waste. Therefore, absent today's regulatory modification, the
management of the mixed wastes that are the subject of this XL pilot
project would continue to be subject to both RCRA permitting and NRC
licensing requirements and regulatory oversight from the point the
waste is generated through to its final disposal.
Members of the regulated community have raised concerns that this
dual regulatory oversight of LLMW is unduly burdensome, duplicative and
costly, without providing any additional protection of human health and
the environment beyond that achieved under one regulatory regime. In
response to these concerns, on April 30, 2001, EPA Administrator
Christine Todd Whitman signed a final mixed waste rule modifying the
existing regulatory framework to provide flexibility related to the
storage, treatment (of certain types), transportation and disposal for
LLMW (see 66 FR 27217, May 16, 2001). This rule became effective on
November 13, 2001 (``Mixed Waste Rule'').
In developing the Mixed Waste Rule, EPA assessed NRC regulations
for storage, treatment, transportation and disposal of low-level wastes
(LLW) and compared them with EPA's regulations for hazardous waste
storage, treatment, transportation and disposal applicable to LLMW. The
Agency found that given NRC's regulatory controls, protection of human
health and the environment from chemical risks would not be compromised
by deferral to NRC's LLW management requirements under the
circumstances set forth in the Mixed Waste Rule. Accordingly, through
the Mixed Waste Rule, the Agency adopted a conditional exemption from
certain RCRA hazardous waste management requirements for NRC-licensed
generators of LLMW, in specified circumstances.
Basically, the Mixed Waste Rule allows generators of LLMW to claim
a conditional exemption from the RCRA regulatory definition of
hazardous waste for mixed wastes stored, treated, transported or
disposed of under the NRC regulatory regime, acknowledging the
protectiveness of NRC regulations for LLW (of which LLMW is a part).
(For the complete text of the Mixed Waste Rule, see 66 FR 27217, May,
16, 2001.) More specifically, the conditional exemption allows, among
other things,
[[Page 36852]]
a generator to treat LLMW generated under a single NRC or NRC Agreement
State license, in tanks or containers, without having to obtain a RCRA
treatment permit, provided the form of treatment is allowed under its
NRC or NRC Agreement State license. The conditional exemption for
storage and treatment is only available to generators of LLMW that are
licensed by the NRC or NRC Agreement States. In addition, the Mixed
Waste Rule provides that LLMW that meets the applicable Land Disposal
Restrictions (LDR) standards (either as generated or through treatment)
may be transported and disposed of as LLW at an NRC or NRC Agreement
State licensed low-level radioactive waste disposal facility (LLRWDF),
which need not also possess a RCRA treatment, storage, or disposal
permit.
2. Site-Specific Considerations at the OMP Spring House Facility
OMP Spring House conducts research and development of
pharmaceuticals/drugs at its Spring House, Pennsylvania facility. As
part of this work, OMP Spring House develops and utilizes radiolabeled
compounds to study the bioabsorption and metabolism of the drugs, in
compliance with Food and Drug Administration (FDA) requirements. The
radiolabeled compounds typically consist of an isotopically-labeled
organic compound and a solvent (the specific solvent varies with the
research being conducted). The solvent is mixed with a radioisotope
(typically carbon-14 (\14\C) or tritium (\3\H)), yielding both the
desired radiolabeled compound, and a waste mixture that consists of
radioactive materials (over which NRC has jurisdiction) and a hazardous
organic component (over which EPA has jurisdiction). This radioactive/
hazardous organic waste mixture is the LLMW that is the focus of this
XL pilot project. The estimated volume of mixed waste produced per
batch by OMP Spring House ranges from less than 50 milliliters to
several liters, with an annual total volume of less than 50 liters.
OMP Spring House has developed an innovative bench-scale treatment
process (using high-temperature catalytic oxidization), which oxidizes
the mixed waste, thereby destroying its hazardous waste components
(yielding water and CO2 ) and capturing the radioactivity in
the aqueous residuals or as radioactive CO2. In this process
the liquid LLMW is completely reacted with oxygen or air at high
temperature in the presence of an oxidation catalyst. [For a general
physical description of the bench-scale high-temperature catalytic
oxidizing unit and how it operates, the reader is referred to the July
24, 2001 proposed rule (see 66 FR at 38399). For a more complete
technical description of the unit, operations parameters and analytical
methodology, the reader is referred to the document titled ``A
Prototype High-Temperature Catalytic Oxidation Process For Mixed Waste
In A Pharmaceutical Research Laboratory,'' available in the docket for
today's final rule under Docket ID No. RCRA-2001-0021.]
OMP Spring House's treatment of carbon-14 labeled compounds
generates radioactive CO2 (which is subsequently converted
to potassium carbonate) and the treatment of tritium labeled compounds
generates radioactive (i.e., tritiated) water (\3\H). These residual
low-level wastes could then be sent off-site for stabilization,
recycling, or disposal under NRC or NRC Agreement State regulation.
[The Agency notes that because the treatment process yields one of two
residuals from a variety of LLMW, they are more amenable to recycling
(e.g., recovery of tritium). However, recycling the small volumes of
residuals being generated at the OMP Spring House facility is not
currently economically viable. OMP Spring House has been working to
support efforts to facilitate the recovery of radioactivity from
residuals like those it generates in its high-temperature catalytic
oxidization process.] For tritium containing compounds, the volume of
the treatment residual is generally the same volume as the wastestream
being treated. For carbon-14 containing compounds, the volume of the
treatment residuals is generally slightly higher than the volume of the
original wastestream being treated. The yearly estimated volume of the
treatment residuals generated by the high-temperature catalytic
oxidation of LLMW at OMP Spring House is 50 liters per year, which is
about the same as the volume of the original LLMW.
OMP Spring House has been operating this innovative catalytic
oxidation process for the treatment of the mixed wastes it generates
since 1996 under a ``treatability study exemption'' approved by the
PADEP, which is authorized to carry out portions of the RCRA hazardous
waste program in Pennsylvania. This treatability study has been
conducted to evaluate the performance of the catalytic oxidation
process on the organic component of these mixed wastes and the capture
of the radioactive components.
The treatment technology being employed by OMP Spring House is not
included under the 2001 Mixed Waste Rule because it is not conducted
within a ``tank'' or ``container,'' as those terms are defined in RCRA.
The Agency determined that more specific controls (as are presently
provided under RCRA) are generally more appropriate for certain forms
of treatment, such as thermal treatment (including incineration) which
take place outside of a ``tank'' or ``container,'' due to the
complexity and variety of such processes and the specificity of RCRA
requirements. This XL pilot project affords the Agency an opportunity
to test whether a defined subset of LLMW (e.g., small volumes of
research and development laboratory-generated mixed wastes being
treated within the NRC-licensed laboratory in which the wastes are
generated) may safely be treated outside of a tank or container (e.g.,
use of a bench-scale high temperature catalytic oxidation process)
without RCRA regulatory controls (i.e., a treatment permit pursuant to
Subtitle C of RCRA), instead relying on AEA regulations implemented by
the NRC. Thus, this pilot project is intended to assess the
appropriateness of the dual oversight (i.e., concurrent RCRA and AEA
regulatory controls) exerted over the small volumes of mixed wastes
generated and treated at this pharmaceutical research and development
facility, and to characterize those factors that could inform EPA's
decision whether mixed wastes generated and treated in similar
circumstances should also be exempted from the regulatory definition of
hazardous wastes (and thus, RCRA regulatory control) on a national
basis (in effect, deferring regulatory oversight of these specific
types of mixed wastes to NRC or NRC Agreement States). The pilot
project will also provide the Agency additional data regarding the
performance of the on-site, bench-scale high-temperature catalytic
oxidation unit used to treat the mixed wastes, which will also be
considered as part of any future determination regarding possible
changes to the types of units included in RCRA's May 2001 Mixed Waste
Rule.
To date, OMP Spring House's treatability study has yielded
extremely positive results, demonstrating that the full range of
organics used to produce radiolabeled compounds are effectively
eliminated (routinely achieving destruction and removal efficiencies
(DRE) of 99.999% to 99.99999%) by the high-temperature catalytic
oxidation process. The treatment process exceeds Land Disposal
Restricitons (LDR) treatment standards for organics, and
[[Page 36853]]
releases only negligible amounts of radioactivity\1\1.
---------------------------------------------------------------------------
\1\ During calendar year 2003, air emissions monitoring revealed
an annual average concentration of 7.54E-11 uCi/mL for tritium and
2.09E-11 uCi/mL for carbon-14 for all operations (i.e., not just
emissions from the high-temperature catalytic oxidation process).
These annual average concentrations of radionuclides in effluent air
are less than 0.08% of the limits specified by NRC in 10 CFR Part 20
for allowable concentrations in effluent air (i.e., 1 x 10E-7 mCi/mL
for tritium and 3 x 10E-7 uCi/mL for carbon-14 (present as carbon
dioxide-\14\C)). Note that these units are expressed in microcuries
(10 E-6 curies)/milliliter.
---------------------------------------------------------------------------
The catalytic oxidation unit is housed in a laboratory fume hood
within OMP Spring House's radiosynthesis laboratory suite. All seven
fume hoods in the lab suite are connected to a dedicated stack for air
emissions. This air pollution control system employs high efficiency
particulate arresting (HEPA) filtration to capture any fugitive dusts
or particulate matter. No other pharmaceutical research operations, or
other processes performed at the facility are tied into this system.
Air emissions monitoring for radioactivity is performed whenever the
process is operating. The monitoring is of the consolidated non-
turbulent air stream within the ventilation system after the juncture
of the seven hoods and prior to emissions into the atmosphere via the
dedicated stack.
C. What Solution Is Being Tested by the OMP Spring House XL Project?
OMP Spring House originally proposed that EPA address its LLMW in
one of three ways:
--Exempt the bench-scale treatment of mixed wastes from permitting
requirements,
--Provide permit-by-rule exemptions for the bench-scale treatment of
mixed wastes, or
--De-list post-oxidation wastes pursuant to 40 CFR 260.20 and 260.22 to
allow the treatment of the LLMW.
Under each of these alternatives, OMP Spring House noted that the
laboratory in which the wastes are generated and treated would continue
to be subject to an NRC license, which it believed would be sufficient
to protect human health and the environment during the generation and
treatment of its LLMW, especially considering the very small volumes of
wastes being generated and treated, the small size of the treatment
unit, the proximity of the treatment unit to the point of generation
(the wastes are both generated and treated within the same laboratory
room), the sophisticated level of expertise of the technicians that
work in the lab, and the protective controls (e.g., emission limits)
required by the NRC license.
EPA and the PADEP agreed that applicability of OMP Spring House's
NRC license conditions was likely sufficient to ensure that OMP Spring
House's high-temperature catalytic oxidation would be operated so as to
be protective of human health and the environment absent RCRA
regulatory controls, and EPA determined that the most appropriate
mechanism to confirm this was by exempting OMP Spring House's LLMW from
RCRA's definition of hazardous waste, as discussed below.
D. What Regulatory Changes Are Being Made To Implement This Project?
To allow for this XL project to be implemented, the Agency proposed
on July 24, 2001 to provide a site-specific exemption in 40 CFR
261.4(b) (i.e., ``Solid wastes which are not hazardous wastes'') for
the mixed wastes generated and treated in OMP Spring House's
pharmaceutical research and development (R&D) laboratory (see 66 FR
38396). The Agency is today finalizing this site-specific rule, albeit
clarifying that it comprises an exemption to RCRA's definition of
hazardous waste, not an exclusion to RCRA's definition of solid
waste.\2\ The effect of this exemption, assuming all the conditions are
met, is to remove these wastes from RCRA Subtitle C regulation at the
point of their generation. Further, because the residuals resulting
from the catalytic oxidation treatment process will not be derived from
hazardous wastes, no ``delisting'' is required for these residuals
(since the original wastestream will no longer comprise a RCRA
``listed'' waste). The Agency believes that this regulatory mechanism
is the most efficient way to provide OMP Spring House with the
regulatory outcome it seeks and implement the XL pilot project.
---------------------------------------------------------------------------
\2\ In its July, 2001 proposal, EPA characterized the regulatory
flexibility to be offered under this XL Project as comprising a
``site specific exclusion in 40 CFR 261.4(b) (i.e. `Solid wastes
which are not hazardous wastes') for the mixed wastes generated and
treated in OMP Spring House's pharmaceutical research and
development (R&D) laboratory. The effect of this exclusion, assuming
all the conditions are met, will be to exclude these wastes from
RCRA Subtitle C regulation at the point of generation, * * * Instead
of being considered `mixed wastes,' these wastes will simply be
considered low-level wastes (LLWs) subject to NRC or NRC Agreement
State regulation.''
66 FR at 38400-01.
EPA has determined that its use of the word ``exclusion'' (which
generally applies to materials excluded from RCRA's definition of
solid waste under 40 CFR 261.4(a) rather than materials exempted
from RCRA's definition of hazardous waste under 40 CFR 261.4(b)),
and the potential implication that this regulatory change would
result in clarification. In this final rule, EPA makes plain that
the effect of this regulatory change is to conditionally exempt OMP
Spring House's LLMW from RCRA's definition of hazardous waste under
40 CFR 261.4(b) (and thus from its hazardous waste regulations). OMP
Spring House's LLMW remains a solid waste under RCRA and thus, is
subject to EPA's enforcement authority under Section 7001 of RCRA.
---------------------------------------------------------------------------
The site-specific exemption being finalized today is conditioned on
various reporting requirements intended to provide the Agency with the
data necessary to determine whether this XL pilot project is a success
and obtain the information to help it decide whether the regulatory
change should be ``transferred'' to the national program (which, if it
occurs, would happen through normal rulemaking procedures). The
specific conditions are further discussed in section III.I.
E. Why Is EPA Supporting This Approach To Removing RCRA Regulatory
Controls Over a Mixed Waste?
The Agency agrees with OMP Spring House that this XL project has
merit and has the potential to result in significant environmental and
efficiency benefits should the regulatory change be adopted on a
national basis. While the Agency adopted the Mixed Waste Rule to
generically address the regulation of some mixed wastes, Project XL
offers the Agency the opportunity to test alternative approaches, in
this case, an alternative approach tailored to a specific subset of the
generic category of mixed wastes not covered by the Mixed Waste Rule.
The Agency believes this is the type of ``test'' that Project XL is
intended to facilitate. The information and data gathered throughout
the course of this XL project will provide the Agency with the ability
to make a more informed determination regarding the appropriate
regulatory controls for ``mixed waste'' generally, as well as certain
discrete subsets of ``mixed waste'' that may be amenable to an
alternative regulatory approach.
F. How Have Various Stakeholders Been Involved in This Project?
During the developmental stages of this XL pilot project, OMP
Spring House cultivated stakeholder involvement from the local
community and local environmental groups in a variety of ways. These
methods included communicating through the local news media,
announcements at Township meetings, public meetings and direct contact
with interested parties. For a more detailed description of the methods
used to involve stakeholders and the meetings held with the local
community to discuss the pilot project, the reader is referred to the
July 24, 2001 proposed rulemaking (see 66 FR at 38401).
[[Page 36854]]
OMP Spring House understands that stakeholder involvement is an
integral part of the XL process and will continue to hold public
meetings with the local community to provide updates and information on
this XL pilot project, as needed.
G. Response to Major Comments Received on the Proposed Rule
The Agency received 65 comments in response to the July 24, 2001
proposed rule. Detailed responses to all of these comments is presented
in the document titled ``Response to Comments on the OMP Spring House
XL Project NPRM'' contained in the docket for today's final rulemaking
under Docket ID No. RCRA-2001-0021. The vast majority of these comments
were very supportive and generally encouraged the Agency to move
quickly to consider similar regulatory flexibility on a national scale.
However, two commenters submitted adverse comments, and several
commenters provided editorial suggestions and requests for
clarification.
The two commenters which opposed the proposed rule were both
commercial LLMW treatment facilities, capable of treating OMP Spring
House's's LLMW. (EPA does note that several other treatment facilities
offered comments that were supportive of the proposal.) These two
commenters questioned the merits of reducing regulatory oversight for
such wastes (with the potential for increased risks); the impact of
such an exemption on the existing commercial mixed waste treatment
industry (which has invested substantial resources to obtain the
necessary permits and licenses), and, (if the regulatory flexibility is
adopted on a national scale for research and development laboratories)
the advisability of having many facilities generating radioactive
residuals (even if they are small in volume and recyclable) rather than
a small number of commercial facilities generating such residuals
(albeit in larger quantities).
The Agency has considered the concerns expressed by these
commenters; however, it believes this pilot project should go forward.
The Agency believes that the NRC license provides sufficient
protections, at least in this specific situation, such that a RCRA
permit is not necessary. Thus, we disagree with the commenter who
argues that the facility would be ``unlicensed/unpermitted.'' We also
disagree with the commenter who suggested that this rulemaking would
reduce the treatment standards for this waste. As has been
demonstrated, the high-temperature catalytic oxidation unit utilized by
OMP Spring House meets or exceeds the existing treatment standards that
these wastes are subject to. Thus, we believe that the rule will not
pose additional risks to workers or the public. Moreover, the Agency
notes that since OMP Spring House's waste stream will remain a solid
waste under RCRA, it retains the authority to require OMP Spring House
to address any threat which it determines presents an imminent threat
to the public health or the environment. See 42 U.S.C. 6973(a).
Further, a core goal of EPA's XL initiative is to promote innovation,
which includes considering whether new approaches are better able to
protect the public health and the environment than existing regulatory
requirements, even where the latter are long-established and required
significant investment by facilities to comply. Therefore, while EPA
understands the concerns expressed by these commercial mixed waste
treatment facilities, the Agency does not believe that these concerns
are sufficient to preclude the exploration of other approaches or, in
this specific case, testing the proposition that an NRC license
provides sufficient protections for the thermal treatment of small
volumes of research and development LLMW in the same laboratory where
the wastes are generated. (The Agency notes that these commenters did
not suggest any specific RCRA regulatory requirement that they thought
is necessary to protect human health and the environment at OMP Spring
House's NRC-licensed facility.)
H. How Will This Project Result in Cost Savings and Paperwork
Reduction?
OMP Spring House has stated that if it became required to obtain a
RCRA permit to operate its catalytic oxidation unit, it would instead
send its small volume of mixed wastes generated to a commercial
treatment facility.\3\ For mixed wastes, commercial treatment costs are
typically based primarily upon the level of radioactivity (i.e., number
of curies) being treated, as well as the volume of the waste. The costs
range from approximately $20,000-$35,000 per curie, with an average
cost of $30,000/curie. This represents a $300,000/year cost for OMP
Spring House, which generates up to 10 curies of mixed waste per year.
OMP Spring House has stated that other cost savings, such as reduced
transportation costs and administrative/paperwork savings resulting
from no longer having its LLMW be defined as a RCRA hazardous waste,
are relatively minor compared with the costs of commercial LLMW
treatment.
---------------------------------------------------------------------------
\3\ OMP Spring House believes that the current RCRA permitting
requirements are intended to apply primarily to commercial hazardous
waste treatment facilities, and that it would be difficult to
justify investing the costs of obtaining and maintaining a RCRA
Subtitle C permit unless it could recoup such costs through
commercial activities (i.e., treating wastes generated by other
generators for a fee). OMP Spring House has stated that it neither
is nor intends to be in the commercial waste treatment business, and
therefore it would not seek such a permit.
---------------------------------------------------------------------------
EPA understands that pharmaceutical, medical, and academic research
activities, such as the radiolabeling which generates OMP Spring
House's mixed wastes, are often limited by the high costs of waste
management. Because waste management costs are such a major factor in
the budgets allocated to such R&D activities, the high cost of waste
management can significantly reduce the money actually spent on R&D.
With more cost-effective treatment (such as OMP Spring House's on-site
bench-scale catalytic oxidation unit), more money could be spent on the
actual research and development of pharmaceuticals.
I. What Are the Terms of the OMP Spring House XL Project and How Will
They Be Enforced?
To implement this XL pilot project, EPA is today modifying 40 CFR
261.4(b) by providing a site-specific exemption from the regulatory
definition of hazardous waste for OMP Spring House's LLMW generated and
treated in their radiosynthesis laboratory, which is subject to a
``Type A Broad Scope'' NRC license for research and development. In
accordance with 25 Pa. Code section 261a.1 of Pennsylvania's RCRA-
authorized hazardous waste program, EPA's exemption of OMP Spring
House's mixed waste from the regulatory definition of hazardous waste
under RCRA is automatically incorporated in Pennsylvania's hazardous
waste regulations because the State hazardous waste regulations
incorporate 40 CFR 261.4(b) by reference, including any modification or
additions made to that section by the Federal program.
Through the development of the Final Project Agreement (FPA), OMP
Spring House had agreed to comply with several conditions for this
exemption, which were included in the regulatory text that was proposed
on July 24, 2001 and are being finalized today. These conditions focus
on demonstrating the efficacy of the treatment technology, and to
gather the data and other information that will allow the Agency to
make a determination regarding the possible future adoption of this
site-
[[Page 36855]]
specific exemption as a nationwide generic exemption.
The site-specific exemption is limited to a total volume of 50
liters/year of mixed waste and only applies to mixed wastes that are
generated and treated using OMP Spring House's high-temperature
catalytic oxidation process within the OMP Spring House facility's
radiosynthesis laboratory. In addition, the exemption is further
conditioned such that OMP Spring House must report, on a semi-annual
basis, the following:
(1) Analysis demonstrating the destruction and removal efficiencies
for all organic components of the exempted wastes subject to treatment.
(2) Analysis demonstrating the capture efficiencies for the
radioactive component of the exempted wastes subject to treatment, and
an estimate of the amount of radioactivity that was released during the
reporting period.
(3) Analyses of the constituent concentrations, including inorganic
constituents, present and radioactivity of the exempted wastes prior
to, and after, treatment.
(4) The volume of exempted wastes treated per batch, as well as a
total for the duration of the reporting period.
(5) The final disposition of the radioactive residuals from the
treatment of the exempted wastes.
In addition, OMP Spring House commits to work with other companies,
organizations and research institutes to: (1) Further develop a
standard, bench-scale off-the-shelf treatment unit, based on its high-
temperature catalytic oxidation technology, to be made available to any
company or institution that generates similar R&D quantities of mixed
wastes, and (2) further develop the technology and market for the
recycling and reuse of the radioactive component of the LLMW (i.e., the
LLW residuals resulting from the treatment of the LLMW).
As part of meeting this commitment, OMP Spring House will prepare
(and submit to EPA for review and comment) a proposed plan summarizing
how it will accomplish this goal. Because these two commitments involve
the participation of other companies and entities outside OMP Spring
House's control and thus are much less certain than the conditions
discussed above, these commitments have not been made conditions of the
exemption. However, in evaluating the success of this XL project, these
``non-enforceable'' commitments will be considered by EPA and the
PADEP.
J. How Long Will This Project Last and When Will It Be Completed?
This project will be in effect for five years from the date that
this final rulemaking becomes effective, unless it is terminated
earlier or extended by all project signatories (if the FPA and rule are
extended, this will be done through a rulemaking seeking the comments
and input of stakeholders and the public). Any project signatory may
terminate its participation in this project at any time in accordance
with the procedures set forth in the FPA. The project will be completed
at the conclusion of the five-year anniversary of today's final
rulemaking or at a time earlier or later as agreed to by the parties
involved.
IV. RCRA & Hazardous and Solid Waste Amendments of 1984
A. Applicability of Rules in Authorized States
Under section 3006 of RCRA, EPA may authorize qualified States to
administer and enforce the RCRA program for hazardous waste within the
State. (See 40 CFR Part 271 for the standards and requirements for
authorization.) States with final authorization administer their own
hazardous waste programs in lieu of the Federal program. Following
authorization, a state continues to have enforcement responsibility
under its State law to pursue violations of its hazardous waste
program. EPA continues to have independent enforcement authority under
sections 3007, 3008, 3013 and 7003 of RCRA.
After authorization, Federal rules issued under RCRA provisions
that predate the Hazardous and Solid Waste Amendments of 1984 (HSWA),
no longer apply in the authorized state. New Federal requirements
imposed by non-HSWA rules do not take effect in an authorized State
until the State adopts the requirements as State law.
In contrast, under section 3006(g) of RCRA, new requirements and
prohibitions imposed by HSWA take effect in authorized States at the
same time they take effect in nonauthorized States. EPA is directed to
carry out HSWA requirements and prohibitions in authorized States until
the State is granted authorization to do so.
B. Effect on Pennsylvania Authorization
Today's final rule is promulgated pursuant to non-HSWA authority.
Pennsylvania initially received authority from EPA to implement its
base hazardous waste program effective January 30, 1986 (see 51 FR
1791, January 15, 1986). Because EPA clarified that the hazardous waste
component of mixed waste was subject to RCRA after Pennsylvania
received its initial RCRA base authorization (see 51 FR 24504, July 3,
1986), mixed waste was not initially included within Pennsylvania's
authorized base program. Pennsylvania subsequently applied to EPA,
seeking approval that its hazardous waste program, as revised
(including its adoption of regulations governing mixed waste), complied
with RCRA. Under the terms of the Commonwealth's hazardous waste
program, subsequent modifications and additions to EPA's RCRA
regulations as published in the Code of Federal Regulations (with
certain exceptions not relevant here) are automatically incorporated
into the Commonwealth's hazardous waste program. See 29 Pa. Bull. 2367,
2370 (May 1, 1999), 65 FR at 57734 and 57736 (September 26, 2000).
On September 26, 2000, EPA published notice of Final Authorization
of Pennsylvania's hazardous waste program, including specifically its
regulation of mixed waste, effective November 27, 2000. See 65 FR 57734
and 57736 (September 26, 2000). EPA did not receive any adverse
comments, and thus EPA's authorization of Pennsylvania's hazardous
waste program (including mixed wastes) became effective on November 27,
2000.
This XL project was undertaken and developed (by EPA, PADEP, and
OMP Spring House) with the assumption that Pennsylvania would receive
authorization for mixed wastes, necessitating the regulatory
flexibility on the part of PADEP to implement the XL project. Since
Pennsylvania has had RCRA authorization for mixed wastes since November
27, 2000, and because Pennsylvania's definition of hazardous waste
under the Pennsylvania Solid Waste Management Act (PaSWMA), including
its exclusions and exemptions, incorporates RCRA's analogous provisions
upon their promulgation, this rule will have the effect of exempting
OMP Spring House's mixed wastes from regulation by the Commonwealth as
a hazardous waste under its hazardous waste program, which in turn
allows Pennsylvania to implement this XL project.
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
Under Executive Order 12866 (58 FR 51735), the Agency must
determine whether this regulatory action is ``significant'' and
therefore subject to formal review by the Office of Management and
Budget (OMB) and to
[[Page 36856]]
the requirements of the Executive Order, which include assessing the
costs and benefits anticipated as a result of this regulatory action.
The Order defines ``significant regulatory'' action as one that is
likely to result in a rule that may: (1) Have an annual effect on the
economy of $100 million or more or adversely affect in a material way
the economy, a sector of the economy, productivity, competition, jobs,
the environment, public health or safety, or State, local, or tribal
governments or communities; (2) create a serious inconsistency or
otherwise interfere with an action taken or planned by another agency;
(3) materially alter the budgetary impact of entitlements, grants, user
fees, or loan programs or the rights and obligations of recipients
thereof; or (4) raise novel legal or policy issues arising out of legal
mandates, the President's priorities, or the principles set forth in
the Executive Order.
Because this rule affects only one facility, it is not a rule of
general applicability and therefore is not subject to OMB review and
Executive Order 12866.
B. Paperwork Reduction Act
This action does not impose an information collection burden under
the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et seq.,
since it applies to only one facility. It is exempt from OMB review
under the Paperwork Reduction Act because it is a site-specific rule,
directed to fewer than ten persons. 44 U.S.C. 3502(3), (10); 5 CFR
1320.3(c), 1320.4 and 1320.5.
Burden means the total time, effort, or financial resources
expended by persons to generate, maintain, retain, or disclose or
provide information to or for a Federal agency. This includes the time
needed to review instructions; develop, acquire, install, and utilize
technology and systems for the purposes of collecting, validating, and
verifying information, processing and maintaining information, and
disclosing and providing information; adjust the existing ways to
comply with any previously applicable instructions and requirements;
train personnel to be able to respond to a collection of information;
search data sources; complete and review the collection of information;
and transmit or otherwise disclose the information.
An agency may not conduct or sponsor, and a person is not required
to respond to a collection of information unless it displays a
currently valid OMB control number. The OMB control numbers for EPA's
regulations in 40 CFR are listed in 40 CFR part 9.
C. Regulatory Flexibility Act
Pursuant to the Regulatory Flexibility Act (5 U.S.C. 601 et seq.,
as amended by the Small Business Regulatory Enforcement Fairness Act
(SBREFA) of 1996), whenever an Agency is required to publish a notice
for any proposed or final rule, it must prepare and make available for
public comment a regulatory flexibility analysis that describes the
effect of the rule on small entities (i.e., small businesses, small
organizations, and small governmental jurisdictions). However, no
regulatory flexibility analysis is required if the head of an agency
certifies the rule will not have a significant economic impact on a
substantial number of small entities. SBREFA amended the Regulatory
Flexibility Act to require Federal agencies to provide a statement of
the factual basis for certifying that a rule will not have a
significant economic impact on a substantial number of small entities.
This rule will not have a significant impact on a substantial number of
small entities because it only affects the OMP Spring House facility,
and it is not a small entity.
Based on the foregoing discussion, I hereby certify that this rule
will not have a significant adverse economic impact on a substantial
number of small entities. Consequently, the Agency has determined that
preparation of a formal Regulatory Flexibility Analysis is unnecessary.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), Public
Law 104-4, establishes requirements for federal agencies to assess the
effects of their regulatory actions on state, local, and tribal
governments and the private sector. Under section 202 of the UMRA, EPA
generally must prepare a written statement, including a cost-benefit
analysis, for proposed and final rules with ``federal mandates'' that
may result in expenditures by state, local, and tribal governments, in
the aggregate, or to the private sector, of $100 million or more in any
one year.
Before promulgating a rule for which a written statement is needed,
section 205 of the UMRA generally requires EPA to identify and consider
a reasonable number of regulatory alternatives and adopt the least
costly, most cost-effective or least burdensome alternative that
achieves the objectives of the rule. The provisions of section 205 do
not apply when they are inconsistent with applicable law. Moreover,
section 205 allows EPA to adopt an alternative other than the least
costly, most cost-effective, or least burdensome alternative if the
Administrator publishes with the final rule an explanation why that
alternative was not adopted. Before EPA establishes any regulatory
requirements that may significantly or uniquely affect small
governments, including tribal governments, it must have developed under
section 203 of the UMRA a small government agency plan. The plan must
provide for notifying potentially affected small governments, enable
officials of affected small governments to have meaningful and timely
input in the development of EPA regulatory proposals with significant
federal intergovernmental mandates, and informing, educating, and
advising small governments on compliance with the regulatory
requirements.
As noted above, this rule is applicable only to one facility in
Pennsylvania. EPA has determined that this rule contains no regulatory
requirements that might significantly or uniquely affect small
governments. EPA has also determined that this rule does not contain a
Federal mandate that may result in expenditures of $100 million or more
for State, local, and tribal governments, in the aggregate, or the
private sector in any one year. Thus, today's rule is not subject to
the requirements of sections 202 and 205 of the UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled ``Federalism'' (64 FR 43255, August
10, 1999), requires EPA to develop an accountable process to ensure
meaningful and timely input by State and local officials in the
development of regulatory policies that have federalism implications.
``Policies that have federalism implications'' is defined in the
Executive Order to include regulations that have ``substantial direct
effects on the states, on the relationship between the National
Government and the states, or on the distribution of power and
responsibilities among the various levels of government.''
This rule does not have federalism implications. It will not have a
substantial direct effect on States, on the relationship between the
National Government and the States, or on the distribution of powers
and responsibilities among the various levels of government, as
specified in Executive Order 13132. Today's rule will only affect one
facility, providing regulatory flexibility applicable to this specific
site. Thus, Executive Order 13132 does not apply to this rule.
[[Page 36857]]
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
Executive Order 13175, entitled ``Consultation and Coordination
with Indian Tribal Governments'' (65 FR 67249, November 6, 2000),
requires EPA to develop an accountable process to ensure ``meaningful
and timely input by tribal officials in the development of regulatory
policies that have tribal implications.'' ``Policies that have tribal
implications'' is defined in the Executive Order to include regulations
that have ``substantial direct effects on one or more Indian tribes, on
the relationship between the Federal Government and the Indian tribes,
or on the distribution of power and responsibilities between the
Federal Government and Indian tribes.''
This final rule, does not have tribal implications. It will not
have substantial direct effects on tribal governments, on the
relationship between the Federal Government and Indian tribes, or on
the distribution of power and responsibilities between the Federal
Government and Indian tribes, as specified in Executive Order 13175.
EPA is currently unaware of any Indian tribes located in the vicinity
of the facility. Thus, Executive Order 13175 does not apply to this
rule.
G. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
Executive Order 13045, ``Protection of Children From Environmental
Health Risks and Safety Risks'' (62 FR 19885, April 23, 1997) applies
to any rule that EPA determines (1) is ``economically significant'' as
defined under Executive Order 12866, and (2) concerns an environmental
health or safety risk that EPA has reason to believe may have a
disproportionate effect on children. If the regulatory action meets
both criteria, the Agency must evaluate the environmental health or
safety effects of the planned rule on children and explain why the
planned regulation is preferable to other potential effective and
reasonably feasible alternatives considered by the Agency.
This rule is not subject to Executive Order 13045 because it is not
an economically significant rule as defined by Executive Order 12866,
and because the Agency believes that the environmental health or safety
risks addressed by this action do not present a disproportionate risk
to children.
H. Executive Order 13211: Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use
This rule is not a ``significant energy action'' as defined in
Executive Order 13211, ``Actions Concerning Regulations That
Significantly Affect Energy Supply, Distribution, or Use'' (66 FR
28355, May 22, 2001) because it is not likely to have a significant
adverse effect on the supply, distribution, or use of energy. It will
not result in increased energy prices, increased cost of energy
distribution, or an increased dependence on foreign supplies of energy.
I. National Technology Transfer and Advancement Act of 1995
Section 12(d) of the National Technology Transfer and Advancement
Act of 1995 (``NTTAA,'' Public Law 104-113, section 12(d) (15 U.S.C.
272 note) directs EPA to use voluntary consensus standards in its
regulatory activities unless to do so would be inconsistent with
applicable law or otherwise impractical. Voluntary consensus standards
are technical standards (e.g., materials specifications, test methods,
sampling procedures, and business practices) that are developed or
adopted by voluntary consensus standards bodies. The NTTAA directs EPA
to provide Congress, through OMB, explanations when the Agency decides
not to use available and applicable voluntary consensus standards.
Today's rule does not establish technical standards. Therefore, EPA did
not consider the use of any voluntary consensus standards.
J. Executive Order 12898: Federal Actions to Address Environmental
Justice in Minority Populations and Low-Income Populations
Executive Order 12898, ``Federal Actions to Address Environmental
Justice in Minority Populations and Low-Income Populations'' (February
11, 1994) is designed to address the environmental and human health
conditions of minority and low-income populations. EPA is committed to
addressing environmental justice concerns and has assumed a leadership
role in environmental justice initiatives to enhance environmental
quality for all citizens of the United States. The Agency's goals are
to ensure that no segment of the population, regardless of race, color,
national origin, income, or net worth bears disproportionately high and
adverse human health and environmental impacts as a result of EPA's
policies, programs, and activities.
Today's rule applies to one facility in Pennsylvania. Overall, no
disproportional impacts to minority or low income communities are
expected.
Today's rule applies to one facility in Pennsylvania. Overall, no
disproportional impacts to minority or low income communities are
expected.
K. Executive Order 12988: Civil Justice Reform
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, as required by
section 3 of Executive Order 12988, entitled Civil Justice Reform (61
FR 4729, February 7, 1996).
L. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, 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. EPA is not required to submit a rule
report regarding today's action under section 801 because this is a
rule of particular applicability.
List of Subjects in 40 CFR Part 261
Environmental protection, Hazardous materials, Waste treatment and
disposal.
Dated: June 20, 2005.
Stephen L. Johnson,
Administrator.
0
For the reasons set forth in the preamble, title 40, chapter I of the
Code of Federal Regulations is amended 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.
Subpart A--General
0
2. Section 261.4 is amended by adding paragraph (b)(17) to read as
follows:
Sec. 261.4 Exclusions.
* * * * *
[[Page 36858]]
(b) * * *
(17) Solid waste that would otherwise meet the definition of low-
level mixed wastes (LLMW) pursuant to Sec. 266.210 of this chapter
that is generated at the Ortho-McNeil Pharmaceutical, Inc. (OMP Spring
House) research and development facility in Spring House, Pennsylvania
and treated on-site using a bench-scale high temperature catalytic
oxidation unit is not a hazardous waste provided that:
(i) The total volume of LLMW generated and treated is no greater
than 50 liters/year, (ii) OMP Spring House submits a written report to
the EPA Region III office once every six months beginning six months
after June 27, 2005, that must contain the following:
(A) Analysis demonstrating the destruction and removal efficiency
of the treatment technology for all organic components of the
wastestream,
(B) Analysis demonstrating the capture efficiencies of the
treatment technology for all radioactive components of the wastestream
and an estimate of the amount of radioactivity released during the
reporting period,
(C) Analysis (including concentrations of constituents, including
inorganic constituents, present and radioactivity) of the wastestream
prior to and after treatment,
(D) Volume of the wastestream being treated per batch, as well as a
total for the duration of the reporting period, and
(E) Final disposition of the radioactive residuals from the
treatment of the wastestream.
(iii) OMP Spring House makes no significant changes to the design
or operation of the high temperature catalytic oxidation unit or the
wastestream.
(iv) This exclusion will remain in affect for 5 years from June 27,
2005.
* * * * *
[FR Doc. 05-12658 Filed 6-24-05; 8:45 am]
BILLING CODE 6560-50-P