Standards Applicable to Generators of Hazardous Waste; Subpart K-Standards Applicable to Academic Laboratories, 29712-29752 [06-4654]
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Federal Register / Vol. 71, No. 99 / Tuesday, May 23, 2006 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 261 and 262
[EPA–HQ–RCRA–2003–0012; FRL–8171–5]
RIN 2050–AG18
Standards Applicable to Generators of
Hazardous Waste; Subpart K—
Standards Applicable to Academic
Laboratories
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
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AGENCY:
SUMMARY: Today, EPA is proposing
alternative generator requirements
applicable to college and university
laboratories as defined in this proposed
rule. The proposal provides a flexible
and protective set of regulations that
address the specific nature of hazardous
waste generation in college and
university laboratories. The flexibility in
today’s proposed rule will allow
colleges and universities the discretion
to determine the most appropriate and
effective method of compliance with
today’s proposed requirements. This
preamble will refer to this flexible
approach as a ‘‘performance-based’’
approach. Additionally, this proposed
rule grants colleges and universities the
choice to manage their hazardous
wastes in accordance with today’s
alternative set of regulations or remain
subject to the existing generator
regulations.
DATES: EPA will accept public
comments on this proposed rule until
August 21, 2006.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
RCRA 2003–0012 or EPA–2050 AG 18
RCRA–2003–0012, by one of the
following methods:
• https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
• E-mail: Comments may be sent by
electronic mail (e-mail) to [‘‘RCRA–
docket@epamail.epa.gov’’], Attention
Docket ID No. EPA–HQ–RCRA–2003–
0012 or EPA–2050 AG 18 RCRA–2003–
0012.
• Fax: Fax comments to: 202–566–
0270, Attention Docket ID. No. EPA–
HQ–RCRA–2003–0012 or EPA–2050 AG
18 RCRA–2003–0012.
• Mail: Send comments to: OSWER
Docket, EPA Docket Center Mailcode:
5305T, Environmental Protection
Agency, 1200 Pennsylvania Ave., NW.,
Washington, DC 20460, Attention
Docket ID Number EPA–HQ–RCRA–
2003–0012 or EPA–2050 AG 18 RCRA–
2003–0012. In addition, please mail a
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copy of your comments on the
information collection provisions to the
Office of Information and Regulatory
Affairs, Office of Management and
Budget (OMB), Attn: Desk Officer for
EPA, 725 17th Street NW., Washington,
DC 20503.
• Hand Delivery: Deliver comments
to: Environmental Protection Agency,
EPA Docket Center, Room B102, 1301
Constitution Avenue, NW., Washington,
DC, Attention Docket ID Number EPA–
HQ–RCRA–2003–0012 or EPA–2050 AG
18 RCRA–2003–0012. Such deliveries
are only accepted during the Docket’s
normal hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–RCRA–2003–
0012 or EPA–2050 AG 18 RCRA–2003–
0012. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available on-line at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or e-mail. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an e-mail comment directly
to EPA without going through https://
www.regulations.gov, your e-mail
address will be automatically captured
and included as part of the comment
that is placed in the public docket and
made available on the Internet. If you
submit an electronic comment, EPA
recommends that you include your
name and other contact information in
the body of your comment and with any
disk or CD–ROM you submit. If EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
special characters, any form of
encryption, and be free of any defects or
viruses. For additional information
about EPA’s public docket, visit the EPA
Docket Center homepage at https://
www.epa.gov/epahome/dockets/htm.
For additional instructions for
submitting comment, comment go to
section B of the SUPPLEMENTARY
INFORMATION section of this document.
Docket: All documents in the docket
are listed in the https://
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www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at
the at the OSWER Docket in the EPA
Docket Center (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) 566–1774, and the telephone
number for the OSWER Docket is (202)
566–0270. Copies cost $0.15/page.
FOR FURTHER INFORMATION CONTACT: For
general information, contact EPA’s Web
site at https://www.epa.gov/epaoswer/
osw/comments.htm. For general
information regarding lab wastes for
educational institutions, contact https://
www.epa.gov/epaoswer/osw/specials/
labwaste/. For further
information regarding specific aspects of
this notice, contact Patricia Mercer,
Hazardous Waste Identification
Division, Office of Solid Waste (5304W),
U.S. Environmental Protection Agency,
1200 Pennsylvania Avenue,
Washington, DC 20460; (703) 308–8408;
fax number (703) 308–0514; e-mail
address: mercer.patricia@epa.gov.
SUPPLEMENTARY INFORMATION:
General Information
A. Entities Potentially Affected by This
Proposed Rule
Entities potentially affected by this
proposed action are generators of
unwanted materials, as defined in this
proposal, from college and university
laboratories. College and university
laboratories, as defined under this
proposal, include laboratories
associated with a private or public, postsecondary, degree-granting, academic
institution that is accredited by an
accrediting agency listed annually by
the U.S. Department of Education. Only
those colleges and universities which
have laboratories on their campuses
would be covered by this alternate
approach; laboratories not located at
colleges or universities would not be
covered. This proposed action is
optional in that colleges and
universities may elect to have their
laboratories remain regulated under
current RCRA generator regulations as
set forth in 40 CFR 262.11 and
262.34(c), or may choose to manage
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their hazardous wastes according to this
alternative regulatory approach. (In
RCRA authorized states, today’s
proposed action would be an option
once it has been adopted by the state in
which the college or university resides.)
To determine whether a college or
university laboratory is covered by this
action, interested parties should
examine 40 CFR part 262 subpart K
carefully. If there are questions
regarding the applicability of the
proposed rule to a particular entity,
consult the person listed in the section
of this preamble entitled FOR FURTHER
INFORMATION CONTACT.
B. What To Consider When Preparing
Comments for EPA
1. Submitting CBI. Do not submit this
information to EPA through https://
www.regulations.gov or e-mail. Clearly
mark part of all of the information that
you claim to be CBI. For CBI
information in a disk or CD ROM that
you mail to EPA, mark the outside of the
disk or CD ROM as CBI and then
identify electronically within the disk or
CD ROM the specific information that is
claimed as CBI. In addition to one
complete version of the comment that
includes information claimed as CBI, a
copy of the comment that does not
contain the information claimed as CBI
must be submitted for inclusion in the
public docket. Information so marked
will not be disclosed, except in
accordance with procedures set forth in
40 CFR part 2.
2. Tips for Preparing Your Comments.
When submitting comments, remember
to:
• Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
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• Follow directions—The Agency
may ask for commenters to respond to
specific questions or organize comments
by referencing a Code of Federal
Regulations (CFR) part or section
number.
• Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• If estimating potential burden or
costs, explain methods used to arrive at
the estimate in sufficient detail to allow
for it to be reproduced.
• Provide specific examples to
illustrate any concerns and suggest
alternatives.
• Make sure to submit comments by
the comment period deadline identified
above.
LIST OF ACRONYMS
ACE ...........................
APA ...........................
APPA .........................
BR ..............................
C2E2 ..........................
CAA ...........................
CAS ...........................
CESQG ......................
CFR ...........................
CSHEMA ...................
EH&S .........................
EMP ...........................
EMS ...........................
HHMI .........................
HSWA ........................
ICR ............................
LDR ...........................
LMP ...........................
LQG ...........................
NACUBO ...................
NGO ..........................
NTTAA .......................
OMB ..........................
PRA ...........................
Project XL ..................
RCRA ........................
RFA ...........................
SAA ...........................
SIC .............................
SQG ...........................
SWDA ........................
TRI .............................
TSDF .........................
UMRA ........................
American Council on Education.
Administrative Procedures Act.
Association of Higher Education Facilities Officers.
Biennial Report.
Campus Consortium for Environmental Excellence.
Central Accumulation Area.
Chemical Abstract Service.
Conditionally Exempt Small Quantity Generator.
Code of Federal Regulations.
Campus Safety, Health and Environmental Management Association.
Environmental Health and Safety.
Environmental Management Plan.
Environmental Management System.
Howard Hughes Medical Institute.
Hazardous and Solid Waste Amendments of 1984.
Information Collection Request.
Land Disposal Restrictions.
Laboratory Management Plan.
Large Quantity Generator.
National Association of College and University Business Officers.
Non-Governmental Organization.
National Technology Transfer Advancement Act.
Office of Management and Budget.
Paperwork Reduction Act.
eXcellence and Leadership.
Resource Conservation and Recovery Act.
Regulatory Flexibility Act.
Satellite Accumulation Area.
Standard Industrial Code.
Small Quantity Generator.
Solid Waste Disposal Act.
Toxics Release Inventory.
Treatment, Storage or Disposal Facility.
Unfunded Mandates Reform Act.
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Preamble Outline
I. Statutory Authority
II. Background
A. Intent of Today’s Proposed Rule
B. History
C. Agency’s College and University
Initiatives
D. Overview of College and University
Laboratory Operations
1. Generation of Hazardous Wastes—Types
and Quantities
a. Data Sources
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b. Summary of College and University
Hazardous Waste Generation Activities
i. Summary of College and University
Laboratory Hazardous Waste Generation
ii. Summary of Type and Volume of
Laboratory Hazardous Waste Generation
at College and University LQGs and
SQGs
2. Summary of Current RCRA Generator
Regulations
a. Who May Determine Whether a Waste Is
Hazardous?
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b. Generators That Treat Hazardous Waste
On-Site
c. Land Disposal Restrictions
d. Applicability of Today’s Proposal to
Conditionally Exempt Small Quantity
Generators (CESQGs)
III. Overview of Today’s Proposed Rule
IV. Detailed Discussion of Today’s Proposed
Rule
A. Discussion of Proposed Definitions
B. Scope of Laboratories at Colleges and
Universities Covered Under This
Proposed Rule
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1. Laboratories in Colleges and Universities
2. Alternative Regulations
3. Notification
C. Specific Requirements Under the
Alternative Regulations
1. Making the Hazardous Waste
Determination
2. Container Standards
3. Labeling Standards
4. Training and Instruction Requirements
5. Removal Frequency of Unwanted
Materials
a. Reactive Acutely Hazardous Unwanted
Materials
b. Other Unwanted Materials That Are
Potentially Acutely Hazardous Waste
6. Where and When To Make the
Hazardous Waste Determination—
Transferring Unwanted Materials or
Hazardous Wastes From the Laboratory
to an On-Site CAA or On-Site TSDF
7. Making the Hazardous Waste
Determination in the Laboratory
8. Making the Hazardous Waste
Determination at an On-Site Central
Accumulation Area
9. Making the Hazardous Waste
Determination at an On-Site TSDF
10. Laboratory Clean-Outs
11. Laboratory Management Plan
D. Recordkeeping
E. Implementation and Enforcement
V. State Authorization
A. Applicability of Rules in Authorized
States
B. Effect on State Authorization
VI. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
1. Economic Analysis
2. Summary of Proposed Rule Findings:
Costs, Economic Impacts, Benefits
B. Paperwork Reduction Act (ICR)
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 Usage
I. National Technology Transfer
Advancement Act Attachment A
I. Statutory Authority
These regulations are proposed under
the authority of Sections 2002, 3001,
3002, and 3004 of the Solid Waste
Disposal Act (SWDA) of 1970, as
amended by the Resource Conservation
and Recovery Act (RCRA) of 1976, as
amended by the Hazardous and Solid
Waste Amendments of 1984 (HSWA), 42
U.S.C. 6921, 6922, 6923, and 6924.
II. Background
A. Intent of Today’s Proposed Rule
The intent of today’s proposed rule is
to establish an alternative set of
generator requirements for college and
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university laboratories that is better
suited to their specific circumstances,
and promotes environmental protection
and public health through safer
management of laboratory hazardous
wastes. While the Agency has been
investigating these issues for a number
of years, starting in 2002, EPA
conducted a series of outreach activities
to generators of hazardous waste with
laboratories to obtain information
regarding the differences between how
hazardous waste is generated and
managed at college and university
laboratory operations as compared with
production operations of industrial
generators and other non-college or
university laboratory generators. The
information collected by the Agency
indicates that college and university
laboratory operations differ from both
industrial laboratories and industrial
production facilities that generate
hazardous waste, warranting
development of an alternative set of
regulations for college and university
laboratories.
Relative to industrial production
facilities, laboratories generally have a
large number of points of generation (i.e.
points where waste is originally
generated) such as multiple laboratory
benchtops within a single laboratory
and laboratories located at several areas
on a single campus. Laboratories also
tend to generate a relatively small
volume of hazardous waste at each of
these points of generation. In contrast,
industrial generators tend to generate
only a few wastestreams in large
quantities at relatively few generation
points. Additionally, while most
individuals involved in hazardous
waste generation activities at both
industrial production facilities and
other non-college or university
laboratories are employees who are
professionally trained in managing
hazardous wastes, students often
generate hazardous waste at college and
university laboratories.
EPA recognizes that hazardous waste
management operations vary widely
among campuses and some colleges and
universities have developed programs
that have proven to be successful, and
thus may be reluctant to change from
the regulation under which they are
currently operating. Therefore, today’s
proposal is an optional, alternative set
of requirements to the existing generator
regulations at §§ 262.11 and 262.34(c).
Those colleges or universities that
choose to continue to manage their
laboratory hazardous waste under the
current hazardous waste regulations
may do so. Colleges or universities that
would like the additional flexibility of
today’s rule may choose to manage their
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laboratory hazardous waste according to
this new set of generator regulations.
This proposal was developed with
performance-based standards in part to
account for the diversity among college
and university operations and practices,
curricula, and goals. The term
‘‘performance-based standards’’ means a
flexible approach that will allow
colleges or universities the discretion to
determine the most appropriate and
effective method of compliance with the
requirements of today’s proposed rule.
This diversity in programs for managing
wastes, including hazardous waste, is
also reflective of logistical
considerations including campus size,
space, personnel, and other resource
differences among colleges and
universities.
EPA has heard from college and
university stakeholders that the greatest
difficulty they face in managing their
laboratory hazardous waste under the
existing regulations is making the RCRA
hazardous waste determination
pursuant to 40 CFR 262.11 (i.e.
determining whether their solid waste is
hazardous waste) in the laboratory when
individuals in the laboratory generating
the solid waste and other materials are
students, often untrained and
unqualified to make a hazardous waste
determination.
Additionally, stakeholders have
pointed out that it is difficult to make
hazardous waste determinations in
college and university laboratories
because in a college and university
setting there are numerous individual
points of generation. This can make it
difficult for an Environmental Health
and Safety (EH&S) (or other similarly
qualified) staff member to be present
when the waste is generated. Since any
individual laboratory chemical hood (as
one example) can be considered a point
of generation, and any college or
university with a substantial science
department can have over a thousand
such hoods located in many laboratories
throughout a campus, it can be
extremely impractical to have such
qualified individuals present at each
point.
Today’s proposal addresses this issue
by providing flexibility in 40 CFR
262.209 with regard to where the
hazardous waste determination can be
made (i.e. in the laboratory, at an on-site
central accumulation area (CAA) or at
an on-site TSDF), provided all
unwanted materials (as defined in
Section IV. A. of this preamble) that are
generated in the laboratory are managed
according to the provisions described
below. If the unwanted materials are
sent to an on-site CAA (or on-site TSDF)
at the college or university for
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hazardous waste determination by
EH&S personnel (or other RCRA trained
individuals), the hazardous waste
determination must be made within four
calendar days of arriving at the on-site
CAA or TSDF. Additionally, today’s
rule allows for the hazardous waste
determination to be made by RCRAtrained individuals in the laboratory
before unwanted materials are removed
from the laboratory. The proposed
provisions would apply to all unwanted
materials in the laboratory that have the
potential for being RCRA hazardous
wastes, including those which are later
determined not to be RCRA hazardous
waste by EH&S or other qualified
personnel. Colleges or universities with
laboratories that generate hazardous
waste that choose not to be subject to
today’s proposal would remain subject
to the current generator requirements set
forth in §§ 262.11 and 262.34(c).
Today’s proposal would not alter or
move the point of generation of any
hazardous waste, but merely allow the
hazardous waste determination to be
made at an on-site central accumulation
area or TSDF, or allow the hazardous
waste determination to be made in the
laboratory, but at a point in time after
initial generation of the waste. The
point of generation of the hazardous
waste would continue to be the location
and time at which the hazardous waste
is first created.
Because the specific issues which are
faced by colleges and universities with
regard to waste management are specific
to hazardous wastes generated in
laboratories, it is only the hazardous
waste generated in the laboratory that
may be managed under subpart K.
Hazardous wastes generated at other
parts of the college and university will
remain subject to the existing hazardous
waste regulations.
EPA believes that a performancebased approach will allow colleges and
universities greater flexibility and
ensure better environmental results.
EPA also recognizes that performancebased standards inherently lack
specificity. Therefore, EPA is proposing
a planning component to help ensure
that a college or university throughly
considers its specific circumstances,
and provides the details needed to
ensure safe management of its unwanted
materials. Therefore, under today’s
proposal, colleges and universities must
develop, implement and retain a
Laboratory Management Plan (LMP).
This plan would describe how a college
or university will meet the required
provisions in this proposal (i.e. the
performance-based standards). Subpart
K will require that the LMP contain
certain elements; however, how an
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individual college or university chooses
to comply with these requirements (i.e.
the specifics of the LMP) will be left to
its discretion. For example, while the
labeling standards for containers require
the words ‘‘unwanted material’’ to be
either affixed to or physically
accompany the container, the Agency is
providing flexibility to colleges and
universities to use their discretion to
meet the labeling standard for providing
sufficient information to alert
emergency responders to the hazards of
the contents of the container. In this
instance, the Agency is proposing
performance-based language for
container labeling and is not mandating
specific terms or information to be used
for defining ‘‘sufficient information.’’
The same is true for the propose
requirements for container management
standards (i.e., while containers must be
maintained and kept in good condition,
EPA is not prescribing precisely how
the containers are managed) and
training/instruction (i.e., depending on
a college or university’s generator status
and the duties of individual workers,
colleges and universities may determine
the level of training needed for an
individual to perform their assigned
duties). These elements must be
addressed in detail in an LMP. It would
be a violation of subpart K for a college
or university laboratory (choosing to
operate under subpart K) not to have an
LMP that addresses the required
elements in a way which would meet
the performance standards. EPA is
proposing two options for enforceability
of the provisions contained within the
LMP. Under one option, it would not be
a violation of subpart K for a college or
university to deviate from its LMP,
provided the performance-based
standards are met. Under the second
option, it would be a violation of
subpart K for a college or university to
deviate from its LMP.
EPA believes that today’s proposal
will lead to safe management of
unwanted materials and greater
environmental protection by facilitating
RCRA hazardous waste determinations,
requiring that they be performed by
specifically trained personnel, rather
than by untrained students in college
and university laboratories. EPA also
believes that today’s proposal will
promote the protection of human health
and the environment by ensuring that
all unwanted materials which may, in
whole or in part, be RCRA hazardous
wastes are safely managed while in the
laboratory prior to the time that the
hazardous waste determination is made.
In addition, EPA believes that the
requirement in today’s proposal to
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develop and implement an LMP will
improve a college or university’s
coordination and integration of
hazardous waste management
procedures and enhance environmental
awareness among researchers and
students at colleges and universities,
leading to a transfer of good
environmental management practices to
the larger community.
EPA strongly encourages colleges and
universities to go beyond developing an
LMP that addresses only the required
elements, and examine their waste
generation and management practices
college or university-wide, with a
particular eye toward finding
opportunities for waste minimization
and pollution prevention. For example,
opportunities may exist for developing
systems that would facilitate and
encourage redistribution and reuse of
unwanted materials throughout the
institution. To that end, EPA actively
encourages colleges and universities to
consider the implementation of an
Environmental Management System
(EMS), a system of management
practices and related documentation,
procedures, and work practices that are
put in place to manage an institution’s
overall environmental impacts. More
information on EMSs at colleges and
universities can be found at: https://
www.epa.gov/ne/assistance/univ/
emsguide.html and https://
www.campusEMS.org/.
B. History
EPA has led and participated in
several efforts to gain a better
understanding of the challenges
associated with managing hazardous
wastes in college and university
laboratories. Pursuant to Congressional
direction in the Hazardous and Solid
Waste Amendments of 1984 (HSWA),
the Environmental Protection Agency
(EPA) undertook a study of challenges
associated with the accumulation,
storage and disposal of hazardous
wastes from college and university
laboratories. The study culminated in a
Report to Congress (Report) in April
1989, outlining the then current
regulatory requirements for college and
university laboratories managing
hazardous waste, the current practices
at these laboratories, and the problems
confronting college and university
laboratories. The challenges for college
and university laboratories highlighted
in the Report included a lack of
awareness about hazardous wastes and
the applicable regulations due to the
transient nature of the student
population, the highly variable
wastestreams generated, resource
constraints on hazardous waste
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management, and general difficulty in
complying with the hazardous waste
regulations.
In 1999, EPA initiated a pilot program
for three colleges and universities,
providing the regulatory flexibility
necessary for the participating
institutions to be able to experiment
with potentially promising regulatory
approaches to hazardous waste
management in college and university
laboratories. This program was
developed under the Agency’s Project
XL, which stands for ‘‘eXcellence and
Leadership,’’ an initiative to allow
regulated entities to achieve better
environmental results at less cost by
increasing awareness of EPA regulations
and environmental performance through
the use of tools such as Environmental
Management Plans (EMPs). The goals of
the EPA University Laboratories Project
XL were to develop a more effective
approach for regulating university
laboratories, develop programs to
enhance laboratory safety, and illustrate
better systems to manage laboratory
environmental impacts.
In 2001, Congress endorsed EPA’s
participation in a pilot project in
collaboration with ten major academic
research institutions, the Howard
Hughes Medical Institute (HHMI) and
state regulatory officials and directed
EPA to subsequently report to Congress
on the HHMI project. The project was
intended to evaluate a performancebased approach in order to provide
regulatory flexibility, reduce burdens
and yield superior compliance, and
thus, environmental protection. EPA
encouraged state regulators to provide
the maximum flexibility under the
current regulations to program
participants so that they could
implement the consensus best practices
developed through the program. In
2002, EPA issued a Report to Congress
(Report) on the HHMI project,
recognizing that college and university
laboratories may have difficulty
complying with the RCRA hazardous
waste regulations largely due to the
regulations’ industry-oriented
framework. In the Report, EPA also
indicated that regulatory changes may
be necessary in some cases and that the
regulatory process would allow EPA to
consider views from diverse
stakeholders and promote national
consistency through the public noticeand-comment process.
EPA subsequently developed a threephased approach to address the issues
identified in the 2002 Report to
Congress: (1) Outreach to stakeholders
to gather information to help EPA
understand the specific nature of the
issues, (2) guidance to clarify issues
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raised by stakeholders not needing
regulatory changes, and (3) regulatory
changes, where appropriate, to provide
flexibility. Such an approach allowed
EPA to first identify the specific issues
involved, and quickly address, through
guidance, those issues that would not
necessarily require rulemaking. Those
issues that are more complex, and that
are best served by the rulemaking
process, were to be addressed at a later
time.
In June 2003, as part of the first phase,
EPA held a public meeting in order to
solicit input from stakeholders on
approaches to address the issues
concerning hazardous waste
management in college and university
laboratories. Topics discussed at the
meetings included: Where and when to
make the hazardous waste
determination; waste labeling
requirements; personnel training
requirements; satellite area
accumulation; and types of treatment
performed in laboratories. In March
2004, as part of the second phase, EPA
issued a guidance memorandum,
answering certain frequently asked
questions regarding satellite
accumulation area regulations. Because
most laboratories in colleges and
universities would be considered
satellite accumulation areas, this
memorandum helped resolve many of
the issues faced by college and
university laboratories. Today’s rule
constitutes phase three of the threephased approach, and addresses several
of the issues which require a
rulemaking.
As a parallel effort, in May 2003,
colleges and universities were selected
to become a partner in EPA’s Sector
Strategies Program. The Sector
Strategies Program seeks industry-wide
environmental gains through innovative
actions taken with a number of
manufacturing and service sectors. EPA
is working with six college and
university Sector Partners (Howard
Hughes Medical Institute (HHMI);
American Council on Education (ACE);
APPA: The Association of Higher
Education Facilities Officers; Campus
Consortium for Environmental
Excellence (C2E2); Campus Safety
Health and Environmental Management
Association (CSHEMA); and National
Association of College and University
Business Officers (NACUBO)) to
develop sector-specific approaches to
assist colleges and universities to
advance the use of environmental
management systems, reduce regulatory
performance barriers, and measure
environmental progress.
In May, June and August 2004, the
College and University Sector Program
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Partners shared their thoughts in a
series of proposals suggesting
alternative approaches for developing a
RCRA program that addresses the
specific problems faced by college and
university laboratories. Their suggested
changes to existing requirements
focused on tailoring new regulations for
college and university laboratories that
are different from the standards required
of other generators and operators of
treatment, storage and disposal
facilities, similar to the current ‘‘satellite
accumulation area’’ regulations, and
included provisions for providing
flexibility for the point at which the
hazardous waste determination is made,
training of laboratory workers, labeling,
container management standards, and
provisions for bench-scale treatment of
waste in the laboratory. (See the docket
for today’s rulemaking for copies of
proposals submitted to EPA.)
C. Agency’s College and University
Initiatives
Today’s proposed rule is just one of
the many efforts EPA is pursuing to
assist colleges and universities in
reducing risks and costs by developing
tools to better manage chemicals and
waste; reducing use of resources; and
promoting better overall environmental
stewardship. These efforts on behalf of
colleges and universities rely on
voluntary and tool-based approaches, as
well as regulations designed to achieve
better environmental performance at
less cost and burden. The Agency also
has developed funding mechanisms to
promote the development of new, more
environmentally friendly experiments
and technologies. The goals of all these
programs are to improve environmental
performance and environmental health
where students, educators, and college
or university personnel learn, teach and
work.
Through its Colleges and Universities
Sector Strategies Program, described
above, the Agency is partnering with
college and universities and their trade
associations to overcome potential
regulatory barriers, promote
environmental management systems,
and develop measures of environmental
performance. More specifically, EPA is
working with the college and university
sector to incorporate sound sustainable
practices to improve environmental
safety practices, provide a baseline for
measuring change, identify priorities for
continual improvement and minimize
overall environmental impacts. To learn
more about EPA’s College and
University Sector Strategy Program,
visit: https://www.epa.gov/sectors/
colleges/.
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Three of these efforts focus
specifically on reducing waste. First,
there is an Agency partnership, called
WasteWise, which is a voluntary
program helping U.S. organizations
eliminate costly municipal and solid
waste, improving economic and
environmental sustainability. The
WasteWise program is supporting
RecycleMania, an intercollegiate
competition involving colleges and
universities across the U.S. in an annual
recycling competition. The goal of the
competition is to increase student
awareness of campus recycling.
Founded in 2001 by two of EPA’s
WasteWise partners, the number of
competing schools increased from 2 in
2001 to 47 in 2005. The total pounds
recycled per student across all
participating schools increased from 74
pounds in 2001 to 1,117 pounds in
2005.
Second, in 2002, EPA funded
Chemical Management Services (CMS)
pilots at two universities—the
University of New Hampshire and
Dartmouth College. CMS, which has
been used successfully in the
automotive, microelectronic and
aerospace industries, restructures the
relationship between buyers of
chemicals and their suppliers. Chemical
suppliers and waste service providers
bring their expertise directly to the
college or university to help manage
chemicals and waste streams, allowing
the colleges and universities to focus on
their core function—education. More
information about the results of the
pilots can be found at https://
www.epa.gov/epaoswer/hazwaste/
minimize/pdfs/cms-broch.pdf.
Third, is EPA’s Green Chemistry
Program. Green Chemistry, a proven
pollution prevention approach toward
environmentally sustainable
manufacturing, is the design of chemical
products and processes that reduce or
eliminate the use or generation of
hazardous substances. To promote this
goal, EPA’s Green Chemistry Program
supports a variety of educational and
research efforts in which colleges and
universities have participated. One
element of EPA’s Green Chemistry
Program is the development of
curricular materials and experiments
that incorporate the principles of green
chemistry. These materials are primarily
aimed at undergraduate and graduate
chemistry students. Another element of
EPA’s Green Chemistry program is
awarding grants for research that
advances the development and use of
innovative technologies and approaches
directed at avoiding or minimizing the
use or generation of hazardous
substances. A third element is the
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Presidential Green Chemistry Challenge
Awards Program, which provides
national recognition of outstanding
chemical technologies that incorporate
the principles of green chemistry into
chemical design, manufacture, and use.
To learn more about EPA’s Green
Chemistry Program, visit: https://
www.epa.gov/greenchemistry/
index.html.
In 2003, EPA launched another award
program: the P3 Award—A Student
Design Competition for Sustainability.
P3 focuses on the three components of
sustainability: People, prosperity and
the planet. Only colleges and
universities are eligible to participate in
this annual competition. The
competition has two phases. Initially,
student teams compete for $10,000
grants to use for researching and
developing their design projects. The P3
award, which includes additional
funding of up to $75,000, is given to the
highest-rated student designs, which
gives the students the opportunity to
further develop their designs for
sustainability, implement their projects
in the field, and move them to the
marketplace. One of the 2005 P3
winners was designing and developing
solar ovens to be mass-produced at low
cost, for use in the developing world. To
learn more about EPA’s P3 Awards,
visit: https://es.epa.gov/ncer/p3/
index.html.
There are two efforts within EPA that
focus specifically on laboratories. First,
in 2003, EPA awarded a cooperative
agreement to Iowa State University to
develop a website, called Labs
Achieving Better Stewardship (LABS)
Central, which is a web-based
clearinghouse of information of interest
to laboratories, at colleges and
universities and elsewhere, dedicated to
the pursuit of enhanced environmental
performance. This site brings together
existing information about innovative
approaches to waste management and
resource conservation that may be
helpful to laboratories interested in
regulatory compliance and
environmental stewardship. LABS
Central guides visitors to web-based
information about regulatory
compliance, environmental
performance, advanced waste
management techniques and waste
reduction. LABS Central can be found
at: https://www.labscentral.info.
Second, the Agency’s Laboratories for
the 21st Century (Labs21) Partnership
Program encourages the development of
sustainable, high-performance, and lowenergy consumption laboratories.
Labs21 is a voluntary program whose
partners set goals to reduce energy and
water use and take a ‘‘whole-building’’
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approach to laboratory design or
retrofitting. Labs21 partners are
demonstrating that a holistic approach
to laboratory design can result in higher
efficiencies, cost savings, reduced
emissions, and improved health and
safety conditions. Currently 16 of 23
private sector partners in Labs21 are
colleges and universities. To learn more
about Labs21, visit https://
www.labs21century.gov.
ENERGY STAR is another program
that is demonstrating that better energy
management, in this case across a
college or university campus, can yield
cost savings. Colleges and universities
spend close to $2 billion each year on
energy. ENERGY STAR is a voluntary
EPA program that gives institutions the
power to reduce the pollution that
causes global warming, while enhancing
their financial value. EPA’s ENERGY
STAR program encourages colleges and
universities to become ENERGY STAR
partners and adopt a strategic approach
to energy management that can lower
energy bills by 30% or more. By
partnering with ENERGY STAR, an
organization demonstrates
environmental leadership, improves its
energy efficiency, saves money, and
receives recognition. ENERGY STAR is
a proven energy management strategy to
distinguish an institution as an
environmental leader and save money
for repair and renovation, hiring of new
faculty, new construction, and other
core activities. To learn more about
ENERGY STAR or becoming an
ENERGY STAR partner, visit: https://
www.energystar.gov/
index.cfm?c=higher_ed.bus_
highereducation.
Recognizing that universities have a
significant impact on the built and
natural environment, EPA continues to
pursue a series of projects that promote
smart growth implementation to achieve
increased viability of the campus and
the surrounding neighborhood in an
environmentally sustainable manner.
These activities include: Co-hosting the
1st Annual Smart and Sustainable
Campuses Conference at the University
of Maryland in November 2005, funding
the publication of ‘‘Partnerships for
Smart Growth: University-Community
Collaboration for Better Public Spaces,’’
compiling a list of smart growth course
prospectuses, developing a list of
resources of best practices and contacts
at universities, providing input on the
P3 project and providing information
and tools to the public. To learn more
about EPA’s Smart Growth Program,
visit: https://www.epa.gov/smartgrowth.
Finally, EPA has sponsored
partnerships with industry, academic
institutions, environmental groups, and
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other agencies to launch sector-specific
Compliance Assistance Centers
(Centers). Through web sites, telephone
assistance lines, fax-back systems, and
e-mail discussion groups, the Centers
are helping businesses, local
governments, and federal facilities
understand federal environmental
requirements and save money through
pollution prevention techniques. The
Agency is in the early stages of
developing a new compliance assistance
center dedicated to the education sector.
Existing compliance assistance centers
may be viewed at: https://
www.assistancecenters.net.
D. Overview of College and University
Laboratory Operations
While Agency data sources and
information gained through site visits
and comments indicate that other areas
of colleges and universities generate
hazardous waste, today’s proposal only
addresses hazardous waste generated
and accumulated in college and
university laboratories. Other areas
within the college or university do not
face the same specific situations as
laboratories and the current RCRA
requirements are effectively dealing
with waste generation and management
in those areas. Agency information
gathering and outreach efforts also
indicate the primary differences
between laboratories and the other areas
in the college or university and more
traditional industrial settings include
the number of wastestreams generated,
the variability and volume of any
individual wastestream generated, the
number of individuals involved in
waste generation and management, their
employment status (e.g. employee vs.
student) and the stability of that
workforce (e.g. transient nature of
students, visiting professors etc.
involved in waste generation and
management vs. relatively constant
workforce in an industrial setting or
other non-college or university
laboratory setting).
In traditional industrial settings,
generally the waste output is known in
advance. Relatively large volumes of
each waste type are generated, and there
are relatively few wastestreams per
facility, with little variability over time.
Furthermore, industrial facilities,
including industrial laboratories,
maintain a relatively steady workforce
and include environmental health and
safety experts on staff. In contrast, the
waste generated within a laboratory at a
college or university is generated in
relatively small quantities (beakerful
versus barrelful), and the exact character
and composition of the waste may not
be known in advance. Additionally, the
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number of different wastestreams
generated by a single laboratory may be
quite high due to the nature of research
and teaching activities. Each college or
university may have a very large
number of individual laboratories, each
generating different wastestreams and
operating under different management
or supervision. The most striking
difference is that at colleges and
universities, much of the hazardous is
generated by students who are either in
instructional settings (such as a
chemistry class) or are conducting
research, but who are not employees of
the college or university.
A great deal of variability also exists
in hazardous waste generation and
management procedures from laboratory
to laboratory at colleges and universities
depending on the type of activity being
conducted and the size of the
laboratory. However, there are some
general practices that can be identified,
and are discussed below.
There are two primary activities that
occur in college and university
laboratories and that generate hazardous
waste. The first is the routine use of
chemicals in instruction and research.
Over the course of a typical month, the
majority of waste generated by college
and university laboratories is generated
during such routine use. During
instruction or research, chemicals are
mixed to produce reactions, and the
resulting mixtures may qualify as
hazardous waste upon completion of the
experiment. In other instances, solvents,
a major wastestream from laboratories,
are used as extractants (to help isolate
and extract a wanted chemical from a
mixture), or in cleaning laboratory
glassware. In addition, certain
laboratory equipment used in analyzing
samples discharge the chemical sample
and any chemical carrier as waste at the
end of the analysis. Hazardous waste
generated in this way may be of a very
small volume (beakerful or less), and
any given experiment may generate
multiple wastes. Often the exact
chemical makeup of such a waste is
unknown to the researcher, particularly
in research experiments involving
synthesizing new chemicals.
A researcher or student in a college or
university laboratory generally generates
the hazardous wastes through routine
use under a laboratory hood, a
contained area equipped with
ventilation and drainage, as part of the
experiment he/she is conducting.
Typically, these hazardous wastes are
collected in a container directly under
the hood. At the end of an experiment,
or the end of the day, the waste is
transferred to a container in a specially
designated area nearby. When a
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container of hazardous waste is filled
(usually well before the 55 gallon limit
is exceeded, according to college and
university representatives), the
environmental health and safety staff (or
waste management company under
contract to the college or university) are
contacted by the researcher or
laboratory manager. In some cases, the
environmental health and safety staff
come directly to the laboratory to make
a hazardous waste determination
(identifying the appropriate RCRA
hazardous waste code), and to transport
the waste either to an on-site central
accumulation area, or in some cases,
directly to an on-site or off-site
permitted treatment, storage or disposal
facility.
The second activity at college and
university laboratories that generates
hazardous wastes is laboratory cleanouts. Laboratory clean-outs are
relatively infrequent events that may
generate larger volumes of hazardous
waste over a relatively short period of
time. Unlike routine laboratory
operations, the primary wastes
generated during a clean-out event are
not chemicals that have been used
during an experiment, but rather
expired laboratory standard solutions
and unused reagents. Generally, the
term ‘‘reagent’’ is used to describe the
chemicals in their ‘‘original’’ state, as
purchased from a manufacturer, rather
than when the chemicals are the result
of a chemical reaction. However, the
result of a chemical reaction can also
become a reagent in a new reaction.
Most laboratories have a large inventory
of various reagents used for conducting
experiments. Because researchers at
colleges and universities may require a
particular reagent on very short notice
in the development of an experimental
procedure, they tend to maintain a large
inventory in the laboratory, rather than
obtain each chemical from a central
location or from a chemical distributor.
Reagents generally are used infrequently
and only in small amounts at any one
particular time. Therefore, researchers
and/or professors at colleges and
universities may store those reagents for
long periods of time. When a researcher
and/or professor retires or otherwise
leaves the college or university, the
laboratory may be cleaned out of all
unused reagents. A laboratory clean-out
may also occur when a building is
renovated, or on occasion, as the result
of a college or university-wide effort to
identify and remove excess chemicals.
During a laboratory clean-out, reagents
often are assessed to determine if they
should be kept for further use. If
retained, the reagents are not considered
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solid or hazardous wastes. However,
when accumulated for long periods of
time, for example, such unused reagents
may be considered solid or hazardous
wastes if it can be determined that they
are no longer usable for their intended
purpose.
Laboratory clean-outs are relatively
infrequent. One reason for this is that
during a laboratory clean-out, fairly
large volumes of hazardous waste,
including those listed as acutely
hazardous, may be generated at one time
(as compared with the baseline of
generation for that laboratory).
Currently, college and university
laboratories generally operate as satellite
accumulation areas under 40 CFR
262.34(c), and therefore must promptly
(within 3 days) remove any acutely
hazardous waste that exceeds one quart
in volume. Furthermore, a generator’s
status (as large quantity generator, small
quantity generator, or conditionally
exempt small quantity generator) is
determined, in part, by the volume of
acutely hazardous waste it generates in
a calendar month. During a laboratory
clean-out, it is common for college and
university laboratories to generate
acutely hazardous wastes in relatively
large quantities, since many unused
bottles of reagents are deemed to be no
longer needed (the hazard is not
increased in this instance, because the
amount of the substances is not
increasing, merely its status is changing
from unused product to hazardous
waste). This increase in generation of
acutely hazardous waste is problematic
for small quantity generators that
generate quantities exceeding one quart
during a laboratory clean-out and
thereby forcing them into large quantity
generator status with shorter on-site
accumulation time and additional
requirements and recordkeeping
burden.
Hazardous wastes generated in college
and university laboratories either during
routine laboratory operation, or during
laboratory clean-out events are then
removed from the laboratory and
transferred to another location for
treatment, storage or disposal. Some
colleges and universities have on-site
central accumulation areas or treatment
storage and disposal facilities (TSDF),
while others transport their hazardous
waste to off-site TSDFs.
1. Generation of Hazardous Waste—
Types and Quantities
This section describes the estimated
hazardous waste quantities and
hazardous waste types generated by
college and university large and small
quantity generators. Specifically, this
section discusses the overall hazardous
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waste generation activities at college
and university laboratories, and the
hazardous waste generated from
colleges and universities with art
programs.
a. Data Sources
The information on colleges and
universities contained in this section
was obtained from the following agency
data sources: 2001 Biennial Report (BR)
data and additional data from the
RCRAInfo (Resources Conservation and
Recovery Act Information) database, and
the 2001 Toxics Release Inventory data
files. To supplement data not obtainable
from EPA databases, EPA used public
information to fill data gaps or to
improve data quality. The Art School
and Program Directory (https://
www.artschools.com) was used to assist
with identifying colleges and
universities that have an art program,
and the list of U.S. universities and list
of community colleges developed by the
University of Texas (available at:
https://www.utexas.edu/world/univ/)
was used to identify small quantity
generator sites. These data sources
provided the most recent and reliable
data available to the agency for
finalizing this proposed rule.
b. Summary of College and University
Hazardous Waste Generation Activities 1
A summary of quantities and types of
hazardous wastes generated at colleges
and universities by large quantity
generator (LQG) and small quantity
generator (SQG) four-year college,
university and professional schools;
two-year junior colleges/technical
institutes; and vocational schools
(which include ‘‘all other miscellaneous
schools and instruction,’’ ‘‘fine arts
schools’’ and ‘‘other technical and trade
schools’’) follows.
Assuming college and university
hazardous waste generation remains
fairly stable over time, college and
university generators account for a
relatively small quantity of overall
hazardous waste generation (i.e., in
2001, over 40,800,000 tons of hazardous
wastes were generated by the total
generator reporting universe compared
to the 35,742 tons generated by colleges
and universities). Specifically, in 2001,
there were a total of 1,304 college and
university LQGs and SQGs generating
hazardous waste. These entities
generated 35,742 tons of hazardous
wastes. Of these totals, 333 colleges and
universities are LQGs generating a total
of 33,789 tons of hazardous wastes and
1 Hazardous waste quantities exclude remedial
waste generation and types and quantities of
hazardous waste generated by medical facilities
affiliated with a college or university hospital.
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971 2 colleges and universities are SQGs
generating a total of 1,953 tons of
hazardous wastes.
Information also indicates that
colleges and universities generate
relatively small quantities of many
different types of hazardous
wastestreams. For example, in 2001,
colleges and universities generated 12
distinct hazardous waste type categories
or wastestreams: lab packs; heavy metal
and cyanide; dioxin pesticide; ignitable,
corrosive and/or reactive characteristic;
inorganic metal; listed discarded
commercial chemical products (‘‘P’’ and
‘‘U’’ listed); mixtures from non-specific
sources; mixtures of toxic characteristic;
pesticide; organic; spent solvents; and
‘‘unknowns.’’ Hazardous waste
generated for any one particular
wastestream by college and university
LQGs ranged from approximately 3,158
tons generated by 268 colleges/
universities to less than one ton
generated by one college/university
generator (with the exception of one
vocational school generating over
25,000 tons of inorganic metal
hazardous wastes). To further illustrate
the small quantities of hazardous waste
generated by college and university
large and small quantity generators, a
significant number of colleges and
universities generate less than one ton
per generator for a particular waste type
(e.g., 2.3 tons of dioxin pesticides
wastes were generated in 2001 by 27
four-year colleges or universities which
averages to approximately .08 tons per
college or university).
In addition, while the majority of
college and university hazardous waste
generators are SQGs (roughly two-thirds
of the college and university generator
universe), LQGs account for over 90% of
the hazardous waste generated by
colleges and universities. Furthermore,
in 2001, LQGs generated an average of
approximately 75 tons of hazardous
waste per school and SQGs generated an
average of approximately 2 tons per
school.
i. Summary of College and University
Laboratory Hazardous Waste
Generation 3
As can be expected, laboratory
hazardous waste generated by colleges
and universities is a small percentage of
overall hazardous waste generation
because colleges and universities
2 EPA does not have hazardous waste quantity
information for 517 SQGs. Therefore, these SQG
estimates are excluded and hazardous waste
generation quantities for SQGs may be underestimated.
3 For purposes of this analysis, a hazardous waste
was considered a laboratory waste if the Biennial
Report waste description contained the word ‘‘lab.’’
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represent only a portion of the total
generator universe and laboratory waste
is only a portion of college and
university hazardous waste. In addition,
not all colleges and universities
generating hazardous waste reported
generating laboratory waste. However,
laboratory waste represents a small
portion of the hazardous waste
generated at colleges and universities, as
well. For instance, 246 of the 333
college and university LQGs and 309 of
the 971 SQGs reported generating
relatively small quantities of laboratory
hazardous wastes. For LQGs, laboratory
waste generation only amounts to
approximately 9% (or 2,939 tons) of the
total hazardous waste generated by
colleges and universities, while SQGs
reported generating approximately 334
tons of laboratory hazardous waste,
which on average equates to
approximately 1 ton of laboratory
hazardous waste per SQG.
Art studios/programs at colleges and
universities are included in the universe
of college and university laboratories in
this proposal, while some types of
laboratories are not included (e.g.,
hazardous waste generated by medical
facilities associated with a college or
university). In considering the effect of
hazardous waste generation by college
and university art programs, it is
interesting to note its comparison to
hazardous waste generation by other
laboratories in the scope of today’s
proposal at colleges and universities.
Schools with art programs generated an
estimated 21% of the total hazardous
waste generated by college and
university LQGs. Another interesting
comparison is that more college and
university SQGs reported having art
programs than those generating
laboratory hazardous wastes.
ii. Summary of Type and Volume of
Laboratory Hazardous Waste Generation
at College and University LQGs and
SQGs
College and university LQGs
generated approximately 2,939 tons of
laboratory hazardous waste in 2001.
This represents approximately 9% of
the hazardous waste generated by these
college and university LQGs. Four-year
schools comprise the vast majority of
schools generating laboratory waste (235
of 246 LQGs generating laboratory
hazardous waste were four-year schools)
and account for approximately 8.5% of
the 9% of the laboratory hazardous
waste generated. Vocational schools
reported generating a minute amount of
laboratory hazardous waste (about
.01%). The hazardous waste type
comprising the highest percentage
generated by both four-year and two-
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year schools generating laboratory
hazardous waste is lab packs, generated
by 114 out of a total of 235 four-year
schools, and 3 out of a total of 8 twoyear schools reporting. Of the total
number of vocational schools reporting
(3), the largest percentage of laboratory
hazardous waste generated is by one
fine arts school for inorganic (metal)
wastes.
Approximately 73% of college and
university SQGs that generated
laboratory hazardous waste in 2001 are
four-year colleges and universities.
These four-year schools generated about
285 tons of laboratory hazardous wastes
which represents approximately 14% of
the all hazardous waste generated by
college and university SQGs. Four-year
SQGs generated the majority of
laboratory hazardous waste for all
college and university SQGs reporting
(∼ 85%). Lab packs are the largest
contributor to the quantity of laboratory
hazardous waste generated and
represents ∼ 73 tons of waste generated
by approximately 79 SQGs. Spent
solvents is the second largest type of
hazardous waste generated (∼ 51.7 tons
generated by ∼ 91 SQGs), followed by
ignitable, corrosive, and/or reactive
characteristic hazardous wastes with an
approximate 44.2 tons of laboratory
hazardous waste generated by an
estimated 92 four-year college and
university SQGs.
College and university LQGs with art
programs have a modest impact on
laboratory hazardous waste generation.
In 2001, an estimated 239 of 333 college
and university LQGs reported having an
art program. These schools generated an
estimated total of 7,167 tons of
hazardous wastes (or 21% of the total
hazardous waste generated by college
and university LQGs). College and
university SQGs with art programs
account for approximately 19% of the
total hazardous waste generated by
SQGs. Notably, SQGs with art programs
account for the majority of hazardous
waste generated by college and
university SQGs (approximately 62% of
the 953 tons of hazardous waste
generated).
2. Summary of Current RCRA Generator
Regulations
Colleges and universities that generate
hazardous waste are subject to the
RCRA generator regulations at 40 CFR
part 262. Colleges and universities
generate hazardous waste at many
locations and facilities throughout their
campuses, including laboratories, but
also including operations and
maintenance facilities, construction and
renovation activities, vehicle
maintenance facilities, and photo
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processing facilities. The institution(s
generator status depends on the total
amount of hazardous waste generated at
the entire site in a calendar month.
Many colleges and universities are
LQGs of hazardous waste, generating
(1000 kg/month; or >1 kg of acute
hazardous waste/month. LQGs may
comply with the regulations in 40 CFR
262.34(a) when accumulating hazardous
waste on-site. Hazardous wastes
generated by LQGs also may be
accumulated on-site without interim
status or a permit for 90 days or less
provided the hazardous waste is
accumulated in certain types of units.
Many other colleges and universities are
SQGs, generating >100 kg/month but
<1000 kg/month of hazardous waste.
SQGs may comply with 40 CFR
262.34(d) for the accumulation of
hazardous waste on-site. However,
hazardous wastes generated by SQGs
may be accumulated on-site without
interim status or a permit for 180 days
or less provided the hazardous waste is
accumulated in certain types of units. In
addition, if the hazardous waste needs
to travel more than 200 miles, it can be
stored on-site without interim status or
a permit for up to 270 days, provided
the SQG complies with 262.34(d).
Additionally some colleges and
universities are conditionally exempt
small quantity generators (CESQGs ),
generating < 100 kg/month of hazardous
waste, or < 1 kg of acutely hazardous
waste/month. While CESQGs are not
subject to the requirement to obtain an
EPA ID number, comply with
accumulation and storage requirements,
manifest their wastes, or meet
recordkeeping and reporting
requirements, they are subject to limited
generator waste management standards.
CESQGs also may be subject to
Department of Transportation
requirements. Specifically, CESQGs
must identify their hazardous waste,
comply with storage limit requirements
(no more than 1000 kg of hazardous
waste stored in any one calendar
month), and ensure hazardous waste
treatment or disposal occurs at a facility
that is on-site or off-site and is one of
the following:
• Permitted hazardous waste TSDF.
• Interim status hazardous waste
TSDF.
• Facility authorized to manage
hazardous waste by a state with an
approved hazardous waste program.
• Licensed, registered, or permitted
by the state to manage municipal solid
waste.
• Licensed, registered, or permitted
by the state to manage non-municipal
non-hazardous solid waste.
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• Facility that beneficially uses,
reuses, recycles or reclaims its waste; or
treats its waste prior to beneficial use,
reuse, recycling, or reclamation, or
• Universal waste facility.
(See 40 CFR 261.5(f)(3) or 261.5(g)(3).)
Because generator status is
determined on a monthly basis, it is
possible that a generator(s status can
change from one month to the next,
depending on the amount of hazardous
waste generated in a particular month.
This is commonly referred to as
‘‘episodic generation.’’ If a generator’s
status does in fact change, the generator
is required to comply with the
respective regulatory requirements for
that class of generators for the
hazardous waste generated in that
particular month (i.e. LQG, SQG,
CESQG).
Many of the hazardous wastes
managed at colleges and universities are
generated and initially accumulated in
laboratories. The satellite accumulation
provisions of 40 CFR 262.34(c) allow for
reduced requirements for hazardous
waste accumulated in containers at or
near any point of generation. Both LQGs
and SQGs may take advantage of the
reduced requirements while hazardous
waste is in satellite accumulation areas,
such as laboratories, provided the waste
is managed in accordance with the
provisions at 40 CFR 262.34(c).
Appendix I contains a comparison table
of current regulations and the proposed
regulations in Subpart K.
Regardless of the generator’s status, or
whether the waste is generated in a
satellite accumulation area, all
generators of hazardous wastes are
required to make a hazardous waste
determination according to § 262.11.
Proper hazardous waste determination
is essential to the success of the RCRA
program. The determination process can
be simplified into several basic steps:
1. Is the material in question a solid
waste (as defined in 40 CFR 261.2)?
2. Is the solid waste excluded from
regulation as a hazardous waste under
§ 261.4?
3. Is it or does it contain a hazardous
waste listed in Subpart D of Part 261?
4. Does it exhibit any of the
characteristics defined in Subpart C of
Part 261 (ignitability, corrosivity,
reactivity or toxicity)?
a. Who May Determine Whether a
Waste is Hazardous?
40 CFR 262.11 states, ‘‘A person who
generates a solid waste...must determine
if that waste is a hazardous waste...’’ A
‘‘person’’ is defined in § 260.10 as ‘‘an
individual, trust, firm, joint stock
company, Federal Agency, corporation
(including a government corporation),
partnership, association, State,
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municipality, commission, political
subdivision of a State, or any interstate
body’’ (40 CFR 260.10). Therefore, a
‘‘person’’ is not limited to a specific
individual, but may also be an entity.
Therefore, any individual who is part an
entity that meets the definition of
‘‘person’’ and can act on behalf of that
entity may make a hazardous waste
determination. The hazardous waste
determination is not limited to the
individual who actually generates a
solid waste. For example,
Environmental, Health & Safety (EH&S)
personnel may make a hazardous waste
determination for a waste generated by
an individual professor, as long as the
EH&S personnel and the professor are
part of the same ‘‘person’’ (e.g., colleges
and universities). This regulatory
interpretation has been previously
stated in a memo from Elizabeth
Cotsworth, Director, Office of Solid
Waste to RCRA Senior Policy Advisors
and EPA Regions, dated August 16,
2002, a copy of which has been placed
in the docket for today’s proposal.
EPA’s objective under § 262.11
(Hazardous Waste Determination) is to
ensure that the hazardous waste is
accurately identified. Proper hazardous
waste determination is important in
order to allow the generator to comply
with the applicable hazardous waste
management requirements and to
protect public health and the
environment. In short, it is the
‘‘person’s’’ responsibility to ensure that
the individuals within the organization
who are making the hazardous waste
determination obtain all the necessary
information from appropriate sources so
that they can make a proper hazardous
waste determination. In practice, a
hazardous waste determination in a
laboratory setting would likely be made
by the laboratory staff or staff member,
or would be a collaborative effort
between the individual researcher at a
college or university who generates the
waste and EH&S personnel who may
make the hazardous waste
determination. In the latter instance,
EH&S personnel making a hazardous
waste determination will need
sufficiently accurate and detailed
information about the waste from the
laboratory staff to ensure an accurate
hazardous waste determination.
b. Generators That Treat Hazardous
Waste On-Site
EPA has consistently interpreted its
existing hazardous waste regulations to
allow generators to non-thermally treat
hazardous waste in their accumulation
tanks and containers, without obtaining
a permit or having interim status (51 FR
10168, March 24, 1986). This is true for
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both LQGs and SQGs. Of course, all
generators are allowed to treat only the
hazardous waste that is generated onsite. A permit would be required to store
and/or treat hazardous waste that is
consolidated from off-site locations.
Examples of treatment that may be
conducted in accumulation tanks and
containers without a permit or interim
status include precipitating heavy
metals from solutions and oxidation/
reduction reactions. It should be noted,
however, that thermal treatment by
generators is not allowed without a
permit.
c. Land Disposal Restrictions
The land disposal restrictions (LDRs)
of part 268 also apply to generators of
hazardous waste, including college and
university laboratories. The LDRs
require that hazardous waste must be
treated by a specified method or to a
specified constituent concentration
level before it (or its residue) may be
placed in or on the land. The generator
must know the treatment standard
applicable to his/her hazardous waste
and either treat (non-thermally and in
tanks and containers) to meet the
treatment standard or send it to an
interim-status or permitted hazardous
waste treatment facility to do so.
The hazardous waste becomes subject
to the LDR requirements at the point the
waste is generated. Therefore, if the
hazardous waste is being treated on-site
and the treatment residue is destined to
be land disposed, the generator still has
responsibilities under the LDR program
with regard to the treatment residues. In
addition, generators who treat
hazardous waste on-site to meet a
treatment standard must prepare a waste
analysis plan if treatment occurs in
units that do not require a RCRA permit
(see 40 CFR 262.34(a)(4) for LQGs, and
40 CFR 262.34(d)(4) for SQGs).
Additionally, there are some generator
reporting and recordkeeping
requirements associated with the LDRs
(40 CFR 268.7(a)). More information
about the LDR program may be found in
‘‘Land Disposal Restrictions: Summary
of Requirements’’ at https://
www.epa.gov/epaoswer/hazwaste/ldr/
new.htm.
d. Applicability of Today’s Proposal to
Conditionally Exempt Small Quantity
Generators (CESQGs)
Conditionally exempt small quantity
generators are generators of hazardous
waste that generate less than 100 kg/
month of hazardous waste and less than
1 kg of acutely hazardous waste/month.
Although, like all generators of
hazardous wastes, CESQGs are required
to make a hazardous waste
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determination at the time the waste is
generated, under the existing hazardous
waste regulations, CESQGs are not
required to comply with many of the
requirements that apply to LQGs and
SQGs. Because CESQGs are not
currently subject to the controls that
apply to satellite accumulation areas,
many of the provisions set forth in
today’s proposal would be more
stringent than those to which they
currently are subject. For this reason,
today’s proposed alternative regulations
would not apply to college and
university laboratories that are CESQGs.
Nevertheless, EPA does not wish to
preclude CESQGs from taking advantage
of any of the benefits which could be
gained by this proposed approach and is
considering whether it would be
appropriate to include CESQGs under
this rule. EPA therefore is, requesting
comment on whether to include
CESQGs in this rule, whether CESQGs
would in fact benefit from this
alternative program, and whether they
would elect to manage their hazardous
wastes in accordance with its
provisions. EPA also is soliciting
comment on what portions of today’s
proposal would be appropriate for
CESQGs if colleges and universities that
are CESQGs are interested in complying
with Subpart K. Specifically, EPA is
requesting comment on whether it
would be appropriate to allow colleges
and universities that are CESQGs to take
advantage of the proposed regulatory
incentives for conducting laboratory
clean-outs.
III. Overview of Today’s Proposal
A college or university which chooses
to manage the unwanted materials
generated in its laboratories according to
the alternative regulations proposed
today, would be required to send a
notice to the EPA Regional
Administrator or, in a state authorized
for this rule, the State Director,
informing them of its intent to follow
the alternative set of regulations, as
finalized. The college or university also
would have to develop a Laboratory
Management Plan (LMP), which
describes the procedures that will be
used by the laboratory(ies) at the college
or university for implementing the
performance-based requirements of
these regulations.
Under the provisions of today’s
alternative set of regulations, all
laboratory workers must be trained and
students must be instructed
commensurate with his/her duties. All
persons working in a laboratory must
determine whether any material they
generate is unwanted and has the
potential of being a RCRA hazardous
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waste. They must then place the
unwanted material in an appropriate
container for subsequent removal. The
container must be safely managed to
prevent leaks, spills, emissions to the
air, and adverse chemical reactions
while in the laboratory. Containers also
must be properly labeled with the
appropriate information to make a
hazardous waste determination. The
date that the initial amount of unwanted
material was placed in the container
must be associated in some manner with
the container, and if the volume of
unwanted material exceeds 55 gallons
or the volume of one of the seven
reactive acutely hazardous unwanted
materials (as defined in today’s
proposal) exceeds one quart, the date on
which either volume limit is exceeded
must also be associated with the
container. Additionally, laboratory
workers or students must provide
sufficient information to allow a RCRAtrained individual to properly make a
RCRA hazardous waste determination at
a later time. Like the date, this
information must be associated with the
waste, but need not physically be
attached to the waste container. For
example, this information may be
entered into a computer tracking system
and a bar code placed on the container.
In this example, the information is not
physically on the container, but is
associated with it via the bar code. A
college or university must determine a
schedule for removal of unwanted
materials from its laboratories and
specify the schedule in its LMP. The
removal of unwanted materials must
occur at least once every six months.
However, if the volume limits of 55
gallons of unwanted materials or one
quart of reactive acutely hazardous
unwanted materials are exceeded, all of
the unwanted material must be removed
within 10 calendar days, or the next
regularly scheduled removal time,
whichever occurs first.
At the time of a removal, a RCRAtrained individual must either make a
RCRA hazardous waste determination in
the laboratory, or else remove the
material to an on-site central
accumulation area or on-site TSDF. If
the hazardous waste determination is
made in the laboratory, the RCRA
hazardous waste can be taken to a
regulated unit on-site or transported to
an off-site TSDF, and must comply with
the existing hazardous waste
regulations, including the manifest
requirements. If, however, the
hazardous waste determination is not
made in the laboratory, then the
unwanted material must be taken to an
on-site central accumulation area or on-
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site TSDF. The college or university has
four calendar days from the time that
the unwanted material arrives at the onsite central accumulation area or TSDF
within which to make the RCRA
hazardous waste determination. EPA
expects that the time that the unwanted
material is in transport on-site from the
laboratory to the central accumulation
area or TSDF would be relatively short.
However, to ensure that the unwanted
material does not stay in transport for
long periods of time, the rule requires
that the unwanted material be taken
directly from the laboratory(ies) to the
on-site central accumulation area or onsite TSDF. Once an unwanted material
is determined to be RCRA hazardous
waste, it is subject to full RCRA
hazardous waste regulation.
IV. Detailed Discussion of Today’s
Proposed Rule
EPA is today proposing optional,
alternative regulations (40 CFR part 262,
subpart K) for the management of
unwanted materials generated in college
and university laboratories.
This section discusses in detail the
major features of and rationale for the
proposal. The Agency also presents
other options that are being considered
in developing the proposed rule. EPA
welcomes comments on all aspects of
this proposed rule, and on the options
under consideration. Throughout this
section, EPA requests comments on
specific options and on specific issues,
but comments are welcome on all
provisions of this proposal. EPA’s
request for comments on specific
options and specific issues means that
EPA is considering those options and
issues in developing the final rule.
A. Discussion of Proposed Definitions
All the definitions that appear in
today’s proposal are for the purposes of
part 262, subpart K only. Therefore, the
definitions are relevant only to colleges
and universities that have laboratories
and that take part in today’s proposed
alternative regulations.
Central Accumulation Area—Today’s
proposal defines ‘‘central accumulation
area’’ as:
an on-site hazardous waste accumulation
area subject to either § 262.34(a) of this Part
(large quantity generators) or § 262.34(d) of
this Part (small quantity generators). A
central accumulation area at a college or
university that chooses to be subject to this
Subpart also must comply with § 262.211
when accumulating unwanted materials.
Under existing regulations, large
quantity generators may accumulate
hazardous waste on-site without a
permit for up to 90 days provided they
comply with § 262.34(a) and small
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quantity generators may do the same for
up to180 days, provided they comply
with § 262.34(d).4 EPA is proposing to
codify the term ‘‘central accumulation
area’’ solely for the purposes of this rule
to distinguish these types of
accumulation areas from satellite
accumulation areas or laboratories.
Today’s proposal does not change the
existing regulations in §§ 262.34(a) and
262.34(d); it merely codifies a term for
the sake of convenience and clarity,
within today’s rule. Colleges and
universities that choose to operate
under the provisions of today’s
alternative regulations must comply
with 262.34(a) or (d) at the central
accumulation area, if and when,
unwanted materials are brought from
laboratories to a central accumulation
area, as well as proposed § 262.211.
College or University—Today’s
proposal defines ‘‘college or university’’
as:
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a private or public, post-secondary, degreegranting, academic institution, that is
accredited by an accrediting agency listed
annually by the U.S. Department of
Education.
Regardless of whether an institution has
the word ‘‘college’’ or ‘‘university’’ in its
title, for a generator to be eligible to
operate under the provisions of Subpart
K, the generator must meet the criteria
in the definition. Aside from the
obvious academic institutions, some of
the institutions that EPA intends to
include under this definition are postsecondary military academies, two-year
community colleges, and postsecondary vocational or technical
schools that admit high school
graduates or GED recipients. Therefore,
EPA does not intend for vocational or
technical high schools, which are not
post-secondary, to be eligible to
participate in this proposed Subpart.
Similarly, the Agency does not intend
for laboratories at hospitals that are
affiliated with a college or university to
be included in the definition of college
or university. The Agency believes that
although hospitals affiliated with
colleges or universities have
laboratories, the waste generation
pattern at these hospital laboratories
differs substantially from the research or
teaching laboratories at a college or
university, such as chemistry
laboratories. The number of different
wastestreams from research or teaching
laboratories at a college or university is
4 Small quantity generators that must send their
hazardous waste more than 200 miles for off-site
treatment, storage, or disposal are allowed to
accumulate hazardous waste on-site without a
permit for 270 days or less, provided the conditions
of § 262.34(d) are met (see § 262.34(e)).
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expected to be higher and the variability
of the wastes greater than from hospital
laboratories. Furthermore, the turnover
of hospital personnel is expected to be
lower than at other types of laboratories
within a college and university.
Given the importance of this
definition to today’s proposal, the
Agency requests comment on a number
of areas. First, the Agency would like to
know if the proposed definition of
‘‘college’’ or ‘‘university’’ captures and
excludes the types of institutions that
are discussed above. Second, is it
appropriate to include and/or exclude
those institutions described above in the
definition of college and university?
Third, what types of institutions grant
certificates, rather than degrees and is it
appropriate to extend participation in
these new alternative regulations to
those institutions? Fourth, the Agency is
seeking comment on whether it is
appropriate to include in the definition
of college and university the
requirement that the institution be
accredited and if so, whether it is
appropriate to limit accredited schools
to those whose accreditation was
granted by agencies approved by the
U.S. Department of Education. The
Department of Education publishes its
list of approved agencies annually in the
Federal Register. It is EPA’s
understanding that the purpose of the
Department of Education’s list of
accreditation agencies is to determine
eligibility for participation in federal
financial aid programs. That is, a college
or university that is accredited by an
agency that is identified by the
Department of Education is allowed to
participate in federal financial aid
programs. For those commenters that
believe it is important for a college or
university to be accredited to be able to
participate in this new Subpart, EPA
requests comment on whether there are
alternative approaches for defining what
institutions may bestow accreditation.
Laboratory—Today’s proposal defines
‘‘laboratory’’ as:
an area within a college or university where
relatively small quantities of chemicals and
other substances are used on a nonproduction basis for teaching or research
purposes and are stored and used in
containers that are easily manipulated by one
person. An area where the same hazardous
wastes are routinely generated, such as photo
processing, is not a laboratory.
Today’s proposed definition of
laboratory has its basis in the OSHA
Laboratory Standard (29 CFR 1910.1450)
and in EPA’s University Laboratory XL
rule (40 CFR part 262, subpart J). EPA
has combined elements of the
definitions of laboratory and laboratoryscale into a single definition. EPA is
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including phrases that both OSHA and
the University Laboratory rule use such
as ‘‘non-production basis’’ and
‘‘containers that are easily manipulated
by one person’’ to make it clear that the
rule is not intended for non-academic,
commercial operations that may occur
in areas sometimes referred to as
laboratories. Commercial-scale
laboratory operations tend to differ in
their waste generation patterns, by using
only a few chemicals, but in large
quantities. Therefore, laboratories that
use or produce commercial quantities of
chemicals are not considered
laboratories for purposes of this subpart.
EPA intends to include laboratories
where teaching or research occur, that
are associated with a college or
university, and where chemicals are
used in small quantities. Of course,
small quantities of many wastes can add
up to large quantities overall, and it is
not EPA’s intent to exclude laboratories
at colleges and universities that are large
quantity generators from participating in
this proposed set of regulations. The
intent is for subpart K to apply to those
laboratories where each individual
chemical is used in relatively small
quantities.
Those areas that are typically referred
to or considered as laboratories include
chemistry and biology laboratories, for
example. However, other areas within a
college or university will also be
considered laboratories. Generally, areas
where large numbers of different
wastestreams are generated in small
volumes will be considered laboratories.
For example, art studios will be
considered laboratories under this
proposal, despite the fact that they are
rarely referred to as laboratories,
because they have similar waste
generation patterns to chemistry
laboratories. On the other hand, it is
possible that some areas that are
typically referred to as laboratories will
not be considered laboratories under
subpart K. For example, photography
laboratories, which generate a few
predictable wastestreams, would not be
considered laboratories under today’s
proposal. Likewise, computer
laboratories would not be considered
laboratories under today’s proposal.
Similarly, automotive maintenance
facilities, whether they are teaching
facilities, or for the maintenance of
college or university motor pools, will
not be considered laboratories. This is
because auto shops tend to generate a
few predictable waste streams in large
volumes.
Under the existing regulations,
laboratories usually initially accumulate
the hazardous waste they generate in
satellite accumulation areas. EPA is
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proposing that laboratories operating
under these proposed alternative
regulations will no longer be subject to
the satellite accumulation area
provisions. Instead, laboratories at
colleges and universities electing to
participate in this new set of regulations
will be subject to regulations in new
subpart K in part 262, which have been
developed specifically for the way these
laboratories operate.
EPA is requesting comment on the
proposed definition of laboratory and
whether it is appropriate to include
and/or exclude the types of laboratories
discussed and whether there are
additional types of laboratories that the
Agency needs to consider. For example,
the Agency seeks comment on whether
field laboratories that are associated
with colleges and universities should be
included in the definition of laboratory
and be eligible for the alternative
regulations. Specifically, EPA is
interested in whether the waste
generation patterns of field laboratories
that are associated with a college or
university are similar to those of
laboratories located at a college or
university, and whether the alternative
regulations proposed today would be
suitable for their operations. The
Agency expects that many field
laboratories would be conditionally
exempt small quantity generators, but
seeks comment on whether this is the
case and whether field laboratories
associated with colleges and
universities would fit the criteria of
today’s proposed alternative regulations.
In addition, EPA is seeking comment
on whether to expand the scope of this
alternative set of regulations to include
other laboratories outside of colleges
and universities that have similar
hazardous waste generation patterns.
For example, this could include
government and private laboratories that
generate large numbers of different
waste streams, each in relatively small
quantities that are stored and used in
containers that can be easily
manipulated by one person. Such an
expansion in scope would not include
production scale manufacturing
laboratories, as they do not have the
similar production patterns and unique
circumstances that this rulemaking is
intended to address. EPA is particularly
interested in comments that provide
data showing similarities or differences
between college and university
laboratories and laboratories at other
institutions, with regard to hazardous
waste generation patterns and
challenges. Additionally, EPA seeks
comments on whether such an
expansion of scope might lead to
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unintended, adverse consequences for
human health or the environment.
If the Agency were to conclude that
certain other laboratories should be
included within the scope of this
rulemaking, it would alter the definition
to reflect those laboratories covered by
the final rule to ensure that the specific
types of non-academic laboratories that
EPA has determined meet the same
criteria are provided the same options
that academic laboratories are provided.
EPA envisions that the revised
definition of laboratory might be ‘‘an
area where relatively small quantities
and a wide variety of chemicals and
other substances are used on a nonproduction basis for teaching or
research purposes and are stored and
used in containers that are easily
manipulated by one person. An area
where the same hazardous wastes are
routinely generated, such as photo
processing, is not a laboratory.’’ (See
discussion under section IV.B.1.)
Laboratory Clean-out—Today’s
proposal defines ‘‘laboratory clean-out’’
as:
EPA does not intend to limit laboratory
clean-outs to the removal of unused
chemicals and may include other
unwanted materials as well.
During a laboratory clean-out, some of
the chemicals that are evaluated may
turn out not to be unwanted materials.
That is, the chemicals may end up back
on the laboratory shelf for further use.
Those chemicals that are unwanted
materials may include chemicals that
are subsequently redistributed to other
laboratories. However, the bulk of
unwanted materials generated during
laboratory clean-outs is expected to be
disposed of as solid or hazardous waste.
Laboratory Worker—Today’s proposal
defines ‘‘laboratory worker’’ as:
An evaluation of the inventory of chemicals
and other materials in a laboratory that are
no longer needed or have expired and the
subsequent removal of those chemicals or
other unwanted materials from the
laboratory. A clean-out may occur for several
reasons. It may be on a routine basis (e.g., at
the end of a semester or academic year) or
as a result of a renovation, relocation, or a
change in laboratory supervisor/occupant. A
regularly scheduled pick-up of unwanted
materials as required by § 262.208 does not
qualify as a laboratory clean-out.
The reason for defining laboratory
worker is to identify who in a laboratory
must receive training under this
subpart. The definition is intended to
include any person who performs duties
in a laboratory, regardless of whether
that person is paid or is an employee of
the college or university. EPA is
proposing that students, whether
undergraduate or graduate, will not be
considered laboratory workers if their
activities in the laboratory are limited to
experimentation or other classwork. The
Agency proposes to exclude students
from the definition of laboratory worker
for two reasons. First, EPA expects that
students in a classroom setting will be
under the direct supervision of an
instructor or professor who would be
considered a laboratory worker and
would thus receive training under these
new regulations. Second, given the large
number and high turnover of students,
EPA recognizes the impracticability of
requiring training for students.
However, EPA proposes that students in
a classroom setting receive some form of
instruction regarding the proper
procedures for handling unwanted
materials generated in the laboratory.
Under the proposed definition, a
student may be considered a laboratory
worker if that student conducts research
activities outside of those required for a
specific class. For example,
undergraduate students that conduct
research for extra credit, for honors
projects or to earn money, would be
considered laboratory workers.
Similarly, EPA expects that most
EPA is proposing a definition for
‘‘laboratory clean-out’’ to distinguish it
from regularly scheduled pick-ups of
unwanted materials. Under the
proposal, laboratory clean-outs are more
comprehensive than the regularly
scheduled pick-ups of unwanted
materials. Although EPA does not
intend to limit regularly scheduled pickups to used chemicals, EPA expects that
regularly scheduled pick-ups will
mainly consist of unwanted materials
that are routinely generated in the
course of laboratory operations and
experiments, many of which will be
used chemicals. A laboratory clean-out,
on the other hand, includes an
assessment of the inventory of unused
chemicals and other materials in a
laboratory that may have expired or are
no longer needed and the subsequent
removal of those chemicals or other
materials. It is a process of sorting and
evaluating to determine what should be
eliminated from the laboratory’s
inventory. But just as EPA does not
intend to limit regularly scheduled pickups to the removal of used chemicals,
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a person who handles chemicals and/or
unwanted materials in a laboratory and may
include, but is not limited to, faculty, staff,
post-doctoral fellows, graduate students,
interns, researchers, technicians, supervisors/
managers, and principal investigators. A
person does not need to be paid or otherwise
compensated for his/her work in the
laboratory to be considered a laboratory
worker. Students in a supervised classroom
setting are not laboratory workers.
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graduate students would be considered
laboratory workers, because their
research is outside the classroom setting
and may be unsupervised. It is not
uncommon for colleges and universities
to have guest researchers, or summer
interns that are not employees of the
college or university, that conduct
research at the college or university.
Therefore, the Agency proposes that it is
not necessary for a person to be an
employee of the college or university in
order to be considered a laboratory
worker.
EPA is requesting comment on the
definition of laboratory worker.
Specifically, EPA requests comments on
whether there are additional types of
work arrangements that EPA has not
anticipated in this discussion and that
may require clarification.
RCRA-Trained Individual—Today’s
proposal defines ‘‘RCRA-trained
individual’’ as:
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a person who has completed the applicable
RCRA training requirements of § 265.16 for
large quantity generators, or
§ 262.34(d)(5)(iii) for small quantity
generators. A RCRA-trained individual may
be an employee of the college/university or
may be a contractor or vendor.
The primary reason for today’s proposal
is to allow a RCRA-trained individual to
make the hazardous waste
determination instead of the laboratory
worker or student that generates the
unwanted material. Today’s proposal
will allow laboratory workers and
students to concentrate on proper
materials management without having
to be trained in the RCRA generator
requirements. It will also allow a college
or university to concentrate its resources
on providing RCRA training to those
individuals who will be responsible for
using the information provided by the
laboratory workers regarding the
unwanted materials and translating that
information into solid and hazardous
waste determinations, as well as
identifying any appropriate RCRA waste
codes.
In some cases, a RCRA-trained
individual will be an employee or
student of the college or university. In
other cases, the RCRA-trained
individual that makes the hazardous
waste determinations for a college or
university may be an off-site vendor or
contractor. If the RCRA-trained
individual is an employee of the college
or university, the RCRA-trained
individual must have RCRA training
appropriate to the generator status for
the facility. That is, RCRA-trained
individuals at colleges and universities
that are small quantity generators must
have training that complies with
§ 262.34(d)(5)(iii), while RCRA-trained
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individuals at colleges and universities
that are large quantity generators must
have training in compliance with
§ 265.16. RCRA-trained individuals that
are not employees of the college or
university must have training that
complies with the large quantity
generator regulations.
The Agency is requesting comment on
the extent to which colleges and
universities currently rely on
individuals that are not employees of
the college or university to make the
hazardous waste determination on their
behalf. EPA seeks comment on allowing
such individuals to make the hazardous
waste determination on their behalf.
EPA notes that a college or university
that allows a non-employee to make the
hazardous waste determination on its
behalf could still be held liable in the
event that a non-employee makes
mistaken determinations that lead to
mismanagement of hazardous waste.
Reactive Acutely Hazardous
Unwanted Material—Today’s proposal
defines ‘‘reactive acutely hazardous
unwanted material’’ as:
29725
consists of the commercially pure grade
of the chemical, any technical grades of
the chemical that are produced or
marketed, and all formulations in which
the chemical is the sole active
ingredient.’’ Only unused chemicals are
considered commercial chemical
products that could carry a ‘‘P-listed’’
waste code. Once a reactive chemical
that is on the P-list has been used, it is
not considered a commercial chemical
product. Therefore, it cannot be a
reactive acutely hazardous unwanted
material, nor an acute hazardous waste.
It may, however, still be a hazardous
waste because it meets the criteria of
another listing, or one of the four
characteristics.
Unwanted Material—Today’s
proposal defines ‘‘unwanted material’’
as:
an unwanted material that is one of the
acutely hazardous commercial chemical
products listed in § 261.33(e) for reactivity
and toxicity.
any chemical, mixtures of chemicals,
products of experiments, or other materials
from a laboratory that are no longer needed,
wanted or usable in the laboratory and which
are destined for hazardous waste
determination by a RCRA-trained individual.
Unwanted materials include reactive acutely
hazardous unwanted materials. Unwanted
materials include materials that may
eventually be determined not to be solid
waste pursuant to § 261.2 or a hazardous
waste pursuant to § 261.3.
A reactive acutely hazardous unwanted
material is an unwanted material that
also is a commercial chemical product
listed in § 261.33(e) (known as the ‘‘Plist’’) for reactivity and toxicity.
Reactive acutely hazardous unwanted
materials are a subset of unwanted
materials and they currently include the
following seven commercial chemical
products:
(1) P006 (CAS Number: 20859–73–8)
Aluminum phosphide;
(2) P009 (CAS Number: 131–74–8)
Ammonium picrate; Phenol, 2,4,6trinitro-, ammonium salt;
(3) P042 (CAS Number: 51–43–4) 1,2Benzenediol, 4-[1-hydroxy-2(methylamino)ethyl]-;
(4) P065 (CAS Number: 628–86–4)
Fulminic Acid, mercury(2+) salt;
Mercury fulminate;
(5) P081 (CAS Number: 55–63–0)
Nitroglycerine; 1,2,3-Propanetriol,
trinitrate;
(6) P112 (CAS Number: 509–14–8)
Methane, tetranitro-; Tetranitromethane;
and
(7) P122 (CAS Number: 1314–84–7)
Zinc phosphide Zn3P2 when present at
concentrations greater than 10%.
The language in the regulations at
§ 261.33(d) states: ‘‘the phrase
‘‘commercial chemical product’’ * * *
refers to a chemical substance which is
manufactured or formulated for
commercial or manufacturing use which
As discussed above, one of the main
purposes of today’s proposal is to
provide a college or university the
discretion to make the hazardous waste
determination for unwanted materials
generated in the laboratory at a location
other than the laboratory and at a time
after its initial generation. Therefore, the
Agency is proposing that chemicals or
other materials that are no longer
needed, wanted or usable in the
laboratory be referred to as unwanted
materials. The Agency prefers this term
over the term laboratory waste, which
was used in the University Laboratories
XL rule, published as a final rule in the
Federal Register (64 FR 460696, July 27,
1999), because some fraction of the
unwanted materials may turn out not to
be solid or hazardous waste.
Stakeholders have frequently told EPA
that putting a ‘‘waste’’ label on a
container stigmatizes the material so
that it is difficult to redistribute.
Likewise, EPA has been told that
generators are concerned about the
legality of removing a hazardous waste
label from a container, even if the label
is in error. For example, sometimes
chemicals are mistakenly identified as
hazardous waste or a hazardous waste
label is put on a container of unused
material that is no longer wanted in one
laboratory, but is otherwise eligible for
redistribution to another laboratory for
further legitimate use at the college or
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university. EPA proposes to resolve
these concerns by using the term
unwanted materials. EPA believes this
will remove any regulatory barriers that
may exist to the redistribution of
unused chemicals and promote the
legitimate reuse of laboratory chemicals.
Increased chemical redistribution and
reuse will decrease costs associated
with purchasing new chemicals, reduce
the volume of hazardous waste
generation, and avoid waste disposal
costs.
EPA is proposing that the term
unwanted materials include all
chemicals or other materials in a
laboratory that are no longer needed,
wanted or usable in the laboratory. To
this extent, the laboratory worker or
student has made the decision that the
material serves no useful purpose in the
laboratory where it originated.
Unwanted materials may be used or
unused, new or expired, pure or
mixtures, products of an experiment, or
newly synthesized in the laboratory.
Any chemical or other material that has
the potential to be a solid and hazardous
waste will be considered to be an
unwanted material at the time that it is
determined by a laboratory worker or
RCRA-trained individual that it is no
longer needed, wanted or usable in the
laboratory. Many unwanted materials
will later be determined to be solid and
hazardous wastes. EPA emphasizes that
the point of generation of those solid
and hazardous wastes is in the
laboratory, even though the formal
RCRA hazardous waste code
determination may be made at a later
date, and outside the laboratory where
it was generated.
The definition of unwanted materials
includes reactive acutely hazardous
unwanted materials, as defined above.
In other words, reactive acutely
hazardous unwanted materials are a
subset of unwanted materials.
EPA requests comments on the
definition of unwanted material and
whether the definition appropriately
captures the items EPA has indicated it
intends to include or whether certain
materials should be excluded from the
definition. EPA asks that commenters
provide specific examples of materials
that may require additional clarification.
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B. Scope of Laboratories at Colleges or
Universities Covered Under This
Proposed Rule
1. Laboratories in Colleges and
Universities
Today’s proposed alternative
regulations would apply only to
laboratories at colleges and universities
that generate unwanted and that choose
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to be subject to these proposed
regulations instead of the existing
regulations governing the generation of
hazardous waste. Other parts of the
college or university, and laboratories
located outside of colleges and
universities, that generate hazardous
wastes would not be eligible for today’s
proposed rule, but rather are and will
continue to be subject to the existing
hazardous waste regulations.
As stated above, EPA has a long
history of working with colleges and
universities on the management of
hazardous waste generated in
laboratories. EPA has worked with
colleges and universities since the early
1980s to more fully understand the
difficulties they face in complying with
the existing RCRA hazardous waste
regulations. Projects such as the Howard
Hughes Medical Institute pilot program
and the EPA’s University Laboratories
Project XL Pilot Project, which provides
flexibility to colleges and universities,
have focused on how hazardous wastes
are generated and accumulated in
laboratories. EPA has met with
stakeholders, held a public meeting,
gone on site visits, and attended
meetings and conferences with
associations representing various
colleges and universities and
laboratories. Through these various
activities, EPA has developed a good
understanding of the operational
practices in laboratories at colleges and
universities and the challenges they face
in complying with the RCRA hazardous
waste requirements. Therefore, EPA has
decided to develop separate, alternative
hazardous waste regulations, primarily
as it relates to where the hazardous
waste determination for laboratories at
colleges and universities can be made.
Nevertheless, EPA is taking comment
on whether to expand the scope of this
alternative set of regulations to include
other laboratories with similar
hazardous waste generation patterns.
Specifically, this could include
government and private laboratories that
generate large numbers of different
waste streams, each in relatively small
quantities, that are stored and used in
containers that can be easily
manipulated by one person. EPA also
requests comment on whether
laboratories in hospitals owned by or
affiliated with colleges or universities
should be included in the scope of this
alternative set of regulations, regardless
of any other expansion in scope.
As stated above, college and
university representatives have
commented that laboratories located in
colleges and universities have specific
hazardous waste generation patterns.
However, in comments submitted in
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response to EPA’s public meeting in
2003, several commenters indicated that
laboratories in government and industry
share similar processes, use of
chemicals, and hazardous waste
generation patterns. Specifically, like
laboratories at colleges and universities,
many industry, utility, and government
laboratories generate relatively small
amounts of a large variety of hazardous
wastes.
Therefore, EPA seeks comment on
whether the proposed alternative
regulations should be limited solely to
college and university laboratories or
whether other institutions with
laboratories having similar hazardous
waste generation patterns as those in
colleges and universities should also be
given the option of complying with this
alternative set of regulations. EPA is
interested in comments with data that
show similarities or differences between
college and university laboratories and
laboratories at other institutions, with
regard to hazardous waste generation
patterns and challenges.
If the Agency were to conclude that
non-academic laboratories should be
included within the scope of this
rulemaking, it would alter the definition
to reflect those laboratories covered by
the final rule to ensure that the specific
types of non-academic laboratories
which EPA has determined meet the
same criteria are provided the same
options that academic laboratories are
provided.
2. Alternative Regulations
Today’s proposal would allow
colleges and universities the flexibility
to manage unwanted materials
generated in their laboratories in a more
efficient manner, based on their specific
circumstances, while still meeting the
goals of the RCRA hazardous waste
program: management of hazardous
waste that is protective of human health
and the environment. EPA believes that
a regulatory option that is more tailored
to the college and university laboratory
setting will allow them to achieve better
environmental performance. EPA also
believes that today’s proposed
alternative set of regulations are as
protective as the existing hazardous
waste regulations. Therefore, EPA
believes that allowing college and
university laboratories to manage their
hazardous waste under today’s proposal
will best meet the goals of the RCRA
statute.
At the same time, it should be noted
that laboratories in colleges and
universities can operate quite differently
from one another. For instance, there is
tremendous variety among colleges and
universities with regard to the number
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of laboratories on campus, the dispersal
of those laboratories over a large area
and in a number of separate buildings,
and the management and organizational
structure of the institution. This high
degree of variability among colleges and
universities argues against a ‘‘one-sizefits-all’’ approach. In fact, certain
colleges and universities may have
developed internal procedures for
identifying, handling, and storing
hazardous waste such as computer
tracking systems or contracts with waste
haulers which allow them to more
easily comply with the current
requirements at their individual
laboratories. For these college and
university laboratories, the difficulty in
transitioning to an alternative set of
regulations for unwanted materials
management may be greater than the
benefit derived.
Additionally, because today’s
proposed alternative regulations apply
only to colleges or universities that
generate hazardous wastes in
laboratories, and not to colleges or
universities that generate hazardous
wastes elsewhere on-site, a college or
university choosing to be regulated
under today’s proposal could be subject
to two different sets of requirements for
waste management: 40 CFR part 262,
subpart K for unwanted materials it
generates in its laboratories, and all
other applicable requirements in 40 CFR
part 262 for hazardous wastes it
generates elsewhere at the college or
university. Therefore, some colleges or
universities may find it easier to simply
manage all of their hazardous wastes
according to one set of regulations, and
therefore remain subject to existing
regulations, and therefore remain
subject to 40 CFR part 262.
For these reasons, EPA believes that
providing the option for colleges and
universities to comply with either the
existing hazardous waste regulations or
the proposed alternative regulations
better serves the intentions and goals of
both the Agency and the college and
university community.
Although today’s proposed alternative
set of regulations does give colleges and
universities the option to select between
the existing hazardous waste regulations
or the proposed alternative regulations,
EPA does not intend for colleges and
universities to make this decision on a
laboratory-by-laboratory basis. All
laboratories in the college or university
(covered under a single EPA ID number)
must operate under the same set of
regulations.
Finally, it should be noted that
because EPA authorizes qualified states
to administer their own hazardous
waste programs in lieu of the federal
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program within the state, colleges and
universities located in authorized states
wishing to have their laboratories be
subject to subpart K do not have this
option until and unless their state has
adopted the finalized rule.
3. Notification
Because EPA’s proposal provides the
option for colleges and universities to
choose to manage their hazardous
wastes from laboratories under the
existing regulations or alternatively
their laboratories’ unwanted materials
under today’s proposed provisions, it is
important that EPA, or the authorized
state, know to which set of regulations
a college or university’s laboratories are
subject.
Today’s proposal, therefore, requires
that a college or university choosing the
proposed alternative regulations for
unwanted materials over the existing
regulations for regulation of hazardous
wastes generated in its laboratories must
notify the appropriate EPA Regional
Administrator or, when appropriate,
State Director in authorized states that
have adopted the final rule. A single
notice may apply to multiple ID
numbers, however, all laboratories
within one EPA ID number must
comply with the same set of regulations
(in other words, the alternative
approach can not be applied to only one
or a few laboratories within that ID
number, but must apply to all or none).
The reason for this is that EPA believes
it would be difficult for a college or
university to adequately keep track of
which set of regulations apply to which
laboratory or group of laboratories.
Furthermore, it would be extremely
difficult for states or regions to keep
track of the applicable set of regulations
if, within a single EPA ID number,
different laboratories are complying
with different requirements. No
mechanism currently exists at EPA or
the states to track such distinctions. The
notice must be submitted to the
appropriate EPA Regional Administrator
or State Director in authorized states
that have adopted the final rule. At all
times, a college or university’s
laboratories must comply with either
the existing regulations or the
alternative regulations. If a college or
university decides that its laboratories
will remain subject to the existing
regulations, no notification is necessary.
It is also possible that once a college
or university has chosen to manage its
unwanted materials under the
alternative regulations, it may decide
that this approach is not meeting the
needs of the college or university, and
that it would prefer to return to
regulation under existing applicable
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29727
generator regulations. Under today’s
proposal, a college or university that
chooses to no longer manage its
unwanted materials under the proposed
alternative regulations would be
required to submit another notice to the
EPA Regional Administrator (or State
Director in authorized states). The
notice must indicate the date upon
which the college or university’s
laboratories will no longer be subject to
subpart K and would be subject to the
existing applicable generator
regulations.
The intent of today’s proposed
notification requirement is to provide
basic information to regulatory agencies
concerning which set of regulations the
college or university has chosen to
govern the management of the
hazardous wastes or unwanted materials
generated in its laboratories. The
Agency is not proposing any specific
format for these notices, but that the
notification must include the name and
address of the college or university, the
EPA ID number(s), the name and phone
number of a contact person at the
college or university, and the date that
the college or university will comply
with or withdraw from the alternative
regulations.
EPA requests comment on whether
the information required in the
notification to the EPA Regional
Administrator (or State Director, in
authorized states) is sufficient to
unambiguously identify and monitor
which colleges and universities are
managing their hazardous waste or
unwanted materials under which set of
regulations. EPA would also like input
into whether the Subtitle C Site
Identification Form [EPA Form 8700–
12] or the comparable state form should
be used to provide this notice, and
whether the forms should therefore be
modified to include a checkbox to
indicate which set or regulations the
college or university is choosing to
manage the unwanted materials
generated in its laboratories.
Additionally, EPA seeks comment on
whether the Regional Administrator (or
State Director, in authorized states)
should provide the college or university
with a written receipt of the one-time
notice.
C. Specific Requirements Under the
Alternative Regulations
Today’s proposed alternative
regulations would allow laboratories in
colleges and universities to send
unwanted material that is generated in
the laboratory to an on-site central
accumulation area or an on-site TSDF
before making the hazardous waste
determination for the unwanted
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material, or to make the hazardous
waste determination in the laboratory
prior to removal. However, the college
or university laboratory must meet
certain requirements as described
below.
1. Making the Hazardous Waste
Determination
Currently, under the existing
hazardous waste regulations in 40 CFR
262.11, any individual generating a
solid waste is required to determine if
that solid waste is hazardous, that is,
determining whether a waste is ‘‘listed’’
and/or ‘‘characteristic’’ (as described in
section II.D.2 of this preamble). Under
40 CFR 262.34(c), generators are
allowed to accumulate up to 55 gallons
of hazardous waste (or one quart of
acutely hazardous waste) in containers
at or near the point where the waste was
generated without a permit or interim
status and without complying with
certain other hazardous waste generator
requirements. This point is generally
known as a ‘‘satellite accumulation
area,’’ (SAA). The SAA must be ‘‘under
the control of the operator’’ generating
the hazardous waste [40 CFR
262.34(c)(1)]. Although the generator
requirements for hazardous wastes
managed in the satellite accumulation
area are a more streamlined set of
requirements, the requirement to
determine if the solid waste is
hazardous still applies. Because most
hazardous waste generated in a college
or university laboratory is generated in
small quantities (rarely do college or
university laboratories accumulate up to
the 55 gallon limit before removing their
waste), laboratories generally manage
their hazardous wastes according to the
requirements of the ‘‘satellite
accumulation area.’’
Typically, college and university
laboratories do not have one central
location where hazardous wastes are
generated, but may have many
independent and widely dispersed
points where hazardous waste is
generated, including many different
points of generation within a single
laboratory. Hazardous wastes generated
in colleges and university laboratories
are characterized by a wide variability
in wastestreams, generally small
quantities of each individual
wastestream, and a large number of
individuals involved in hazardous
waste generation and management,
many of whom are students, an
inherently transient population. Due to
this dynamic, under the current
regulations, a large number of
potentially constantly changing
individuals must be able to make proper
hazardous waste determinations (per 40
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CFR 262.11) for large numbers of ever
changing wastes. Colleges and
universities have explained to EPA that
it is a challenge to provide sufficient
RCRA training to all these individuals.
However, the potentially large number
of laboratories at colleges and
universities where such hazardous
waste is generated makes the hazardous
waste determination extremely difficult
for the limited EH&S staff employed at
these institutions. Scheduling an
individual trained in RCRA regulations
to be present at every laboratory
location where hazardous waste
generation occurs is impractical and
difficult to achieve. Therefore, EPA is
proposing today that colleges and
universities be provided the flexibility
to make the hazardous waste
determination in the laboratory before it
is removed from the laboratory or
within four days of arriving at an on-site
CAA or TSDF, provided certain
provisions are met. Specifically these
provisions are: (1) Any unwanted
material that is generated is labeled in
the laboratory, (2) the RCRA hazardous
waste determination is made by a
RCRA-trained individual before the
unwanted material is removed from the
laboratory or within four calendar days
of arriving at an on-site CAA or TSDF,
and (3) that while the unwanted
material is in the laboratory certain
other standards are met, as described in
other sections of this preamble.
With the flexibility to make the
hazardous waste determination in the
laboratory, in an on-site central
accumulation area or on-site TSDF, the
individual in the laboratory generating
the waste does not need to be familiar
with the RCRA hazardous waste
determination procedures. However, it
is important to note that while the
actual hazardous waste determination
does not need to be made at the time
that unwanted materials are generated
in the laboratory, any unwanted
material identified later as hazardous
waste will be considered to have been
generated in the laboratory, and the
unwanted material must be properly
managed from the moment of its
generation and comply with the
requirements of today’s proposal. To
ensure that any RCRA hazardous wastes
that may be generated in the laboratory
are properly managed, today’s proposal
would require that all unwanted
materials generated in the laboratory be
managed in accordance with the
provisions set forth in today’s proposal
(even if ultimately they are determined
not to be RCRA solid or hazardous
waste). This provision is designed to
ensure that persons properly and
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thoroughly trained in the RCRA
hazardous waste regulations be able to
make hazardous waste determinations
for all unwanted materials generated at
the laboratory, rather than relying on a
great many individual researchers or
students attempting to do this. EPA
believes that this will reduce the
chances of either an improper
hazardous waste determination or no
hazardous waste determination at all for
the unwanted material, and thus the
possibility of hazardous wastes being
improperly managed. It also will allow
EH&S personnel at the college or
university to determine, campus-wide,
whether any of the chemicals or other
materials generated in one laboratory
may continue to be used in another
laboratory and thus, reduce the amount
of waste, whether hazardous or not, that
is generated in the first place.
EPA’s authority to impose
requirements in today’s proposal on
college and university laboratories that
generate unwanted materials, including
unwanted materials that are ultimately
determined not to be RCRA hazardous
waste, is based on RCRA section 3002.
This provision allows EPA to
promulgate regulations for generators of
hazardous waste. Historically, college
and university laboratories have been
generators of hazardous waste. College
or university laboratories that decide to
comply with subpart K of part 262 know
that hazardous wastes typically
constitute most of the unwanted
materials generated in these
laboratories. In this rulemaking, EPA is
using its authority in Section 3002 to
cover unwanted materials that may, in
fact, be hazardous waste even though
the formal determination is not required
until such time that the unwanted
material is removed from the laboratory,
or until such time the unwanted
material reaches the on-site central
accumulation area or on-site TSDF. By
making the determination of hazardous
waste at a time subsequent to the initial
generation of the unwanted materials,
the laboratory assumes the
responsibility for managing all of the
unwanted materials in accordance with
the provisions of today’s proposal until
such time as each wastestream is
determined to be a hazardous waste, a
non-hazardous solid waste or another
material not regulated pursuant to
RCRA.
2. Container Standards
The Agency is proposing
performance-based requirements for the
management of containers of unwanted
material while they are being
accumulated in the laboratory. Today’s
proposal would require that containers
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be properly managed for safe storage, to
prevent spills, and to avoid dangerous
situations in which adverse chemical
reactions occur. Additionally, the
Agency is proposing to require the
following regulations for proper
container management: management to
prevent spills, leaks, or adverse
environmental releases, including
minimizing loss of unwanted materials
via emissions into the air; practices to
ensure containers are kept in good
condition and damaged containers are
replaced; and management to ensure
that unwanted materials are compatible
with their containers to avoid reactions
between the contents and its container.
The proposed rule would not specify
the manner in which college or
university laboratories would achieve
these standards, thus providing
flexibility for each laboratory to
determine the most suitable approach,
although in all cases, the unwanted
materials would have to be properly
controlled within the container.
Under the existing satellite
accumulation area regulations, the
container management standards are
more specific, requiring that containers
be in good condition with no structural
defects or leaks, that the waste be
compatible with the containers, and that
containers holding hazardous waste
always be closed during storage, except
when adding or removing waste.
The proposed container management
requirements provide laboratories with
more flexibility than the current specific
regulatory requirements, since each
college or university laboratory is able
to determine the most appropriate way
to meet the standards in the rule. For
example, the flexibility in the proposed
rule allows laboratories to decide how
to safely manage their in-line wastes, as
opposed to the current regulations,
which require that containers be closed
at all times, except when adding or
removing wastes. EPA believes that by
allowing this flexibility, laboratories
will be able to establish methods which
are most appropriate for their
institutions, thereby obtaining better
environmental results.
One alternative the Agency is
considering including in the regulation
is the concept of a ‘‘working container.’’
A working container would be defined
as a small container (of one gallon or
less), managed under the control of a
laboratory worker and used at a bench
or work station, whose contents are
emptied into a container of unwanted
material at the end of the procedure.
Under this alternative, a more specific
provision would be added to the
proposed performance-based container
management standards, requiring that
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any container of unwanted materials
that does not fit the definition of a
working container be closed at all times,
except when it is necessary to add or
remove unwanted materials. This
alternative option would provide
flexibility for laboratory workers to
leave working containers open during
ongoing experiments, but would ensure
that all other containers remain safely
closed when not in use.
A second alternative option the
Agency is considering is to explicitly
include specific container management
requirements in the regulation. This
option would be similar to the current
container management standards for
laboratories, requiring that containers be
in good condition, that the waste be
compatible with other materials and the
containers, and that containers holding
hazardous waste always be closed
during storage. As opposed to the more
performance-based proposal, this option
would contain regulatory language
requiring that an institution ‘‘must at all
times’’ keep containers: closed except
when adding or removing materials and,
in cases for in-line collection, provide
assurance of no spillage from overflow;
maintained to prevent leaks or spills
and, if the container becomes impaired,
immediately transfer materials to a
container in good condition; and
compatible with materials to prevent
adverse reactions or container
impairment and stored a safe distance
from other incompatible containers. In
addition, this option could impose
minimum requirements for what
constitutes a ‘‘safe distance from’’ and
what constitutes a ‘‘container in good
condition.’’ This option also could
include specific requirements for
assuring that no spills from overflow
occur for in-line collections by
mechanisms such as secondary
containment, equipment monitoring or
shut down of equipment in certain
instances. The Agency has proposed
performance-based standards for
container management as opposed to
more specific requirements because the
Agency believes such flexibility is
appropriate and will lead to greater
environmental protection, considering
the specific circumstances at
laboratories. As a result, laboratory
personnel will be able to apply their
institutional knowledge and experience
to determining the most effective and
safest container management standards
for each laboratory.
The Agency requests comments on
the proposed performance-based
standards for container management.
Specifically, EPA is seeking comment
on whether the proposed standards
provide for protection of human health
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and the environment, while providing
flexibility to the laboratories. EPA also
seeks comment on the ease of
determining compliance with the
performance-based standards. EPA
requests comments on the concept
requiring that all containers be closed at
all times, except ‘‘working containers.’’
EPA specifically requests comment on
the definition of ‘‘working container’’
and its applicability in college and
university laboratories. Additionally,
EPA is seeking comment on whether the
alternative option of specific container
management requirements should be in
the regulations, and, if so, what these
regulations should contain.
3. Labeling Standards
The labeling requirements in today’s
proposal include two sets of
performance-based requirements. First,
in order to demonstrate compliance
with the proposed rule, to alert
individuals handling the materials, and
to ensure proper handling, a label must
be affixed to or physically
accompanying the container of
unwanted material. This cautionary
compliance label must include
sufficient information to alert
emergency response personnel and
transporters to the material’s hazards
and/or identity. For example, this might
include the possible hazardous
properties of the unwanted material or
its constituents. Once the RCRA-trained
individual makes the hazardous waste
determination, whether it is in the
laboratory or an on-site CAA or TSDF,
the hazardous waste code(s) must be
added to the cautionary compliance
label that is affixed to or physically
accompanying the container. Requiring
that the hazardous waste code(s) be
placed onto the cautionary compliance
label will ensure that inspectors can
confirm that the hazardous waste
determination has been made and that
there is no confusion as to the contents
of the container so that employees of the
college or university or contractors
consolidating the waste can easily verify
that incompatible wastes are not labpacked together.
The second proposed standard
requires that the RCRA-trained
individual who makes the hazardous
waste determination receives sufficient
information regarding the unwanted
material so that the hazardous waste
determination can be properly made.
This information may be affixed to, but
at a minimum, must in some way be
associated with each container in order
to allow this individual to properly
identify whether an unwanted material
is a hazardous waste and to assign a
proper hazardous waste code(s).
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Examples of the types of information
that may be associated with the
container are: a description of the
chemical composition of the material;
whether the unwanted material has
been used or is unused; a description of
the manner in which the unwanted
material was used (i.e., used as a
solvent); and a description of the
possible hazardous properties of the
unwanted material (i.e., toxic, reactive,
corrosive or ignitable). This information
may be physically affixed or attached to
the container of unwanted material, but
need not be. The information must be
received by the RCRA-trained
individual making the hazardous waste
determination so that this individual is
able to correlate the information
received with the container of unwanted
material to which it refers.
Additionally, the date the unwanted
materials began accumulating in the
laboratory must be associated with (but
need not be affixed to) the container in
order to track the interval when
materials must be removed as specified
in a college or university’s LMP, which
must not exceed six months. If the
volume of unwanted materials in a
laboratory exceeds 55 gallons (or 1 quart
of acutely hazardous reactive waste), an
additional date must be recorded in
order to determine whether the 10
calendar days for removing the
unwanted materials from the laboratory
has elapsed. These dates—the date that
the unwanted material began
accumulating in the container in the
laboratory and the date that the
container exceeds 55 gallons of
unwanted materials (or one quart of
acutely hazardous reactive wastes)—
may be on the label affixed to the
container, or otherwise added to the
label associated with the container.
A laboratory might meet the second
proposed labeling standard by devising
a system that, for example, numbers the
containers of unwanted material and
creates a spreadsheet containing
sufficient information to identify the
material for each of the numbered
containers of unwanted material. The
spreadsheet could then be sent
electronically to the RCRA-trained
individual so the information is
available to that individual when the
hazardous waste determination is made.
Alternatively, laboratories could affix a
bar code to each container that, when
scanned, would provide the information
necessary for proper determination of
the unwanted material. Laboratories
might also choose to include with the
containers a printed inventory of the
unwanted materials and the associated
information each time the containers are
removed from the laboratory and the
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RCRA-trained individual makes the
hazardous waste determination. The
second labeling requirement is meant to
provide the laboratory with flexibility in
determining the most efficient manner
in which to provide the RCRA-trained
individual with the information they
need to accurately and easily identify
whether the unwanted materials are
RCRA hazardous wastes.
Proposing two distinct labeling
standards ensures that the RCRA-trained
individual will be able to make an
accurate hazardous waste determination
of the status of the unwanted materials
that are generated by students and
laboratory workers. The central
accumulation area or TSDF at a college
or university may be receiving
unwanted materials from dozens of
laboratories, in addition to other sources
on campus, and the RCRA-trained
individual responsible for identifying
and managing the unwanted materials
may not be aware of the origins of this
material, unless sufficiently informed by
the generators in the laboratories.
The Agency is also considering a
labeling option (concerning the second
labeling requirement) that would
require specific information be
associated with the container of
unwanted materials, as opposed to the
performance-based requirements
described above. Under this approach,
specific labeling requirements would be
specified in the regulatory language. For
example, the rule would specifically
require, among other things, that
containers have associated labels that
include a chemical description of the
unwanted material, whether the
material is used or unused, the manner
in which the chemicals were used, and
a description of the possible hazardous
properties of the material. The Agency
is proposing the performance-based
requirements and requesting comment
on the specific labeling requirements
option since EPA believes that the
performance-based labeling
requirements will allow college and
university laboratories more flexibility
in finding the most appropriate labeling
method for their laboratory that will
ensure the unwanted materials are
labeled in such a way that they are
properly handled, as well as easily and
accurately identified, whether that is in
the laboratory or at an on-site central
accumulation area or TSDF.
The Agency requests comments on
the proposed performance-based
labeling requirements and the more
prescriptive alternative option described
above. Specifically, EPA is seeking
comment on whether the proposed
standards provide sufficient flexibility.
Additionally, EPA is seeking comment
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on whether it is more appropriate to
require specific standards for labeling
and, if so, what information should be
required on the container labels.
4. Training and Instruction
Requirements
Today’s proposal includes
performance-based standards for
training workers and instructing
students in laboratories at participating
colleges and universities. The proposal
maximizes flexibility in both the
content and method of instruction for
students or training for workers in order
to meet the proposed standards. Under
this proposal, the regulation requires
that colleges and universities provide
laboratory workers with training
commensurate with the laboratory
workers’ duties. Students working in
laboratories must receive instruction
relevant to their activities in the
laboratory. A college or university is
required to document in its Laboratory
Management Plan (LMP) how it will
meet the training and instruction
standards of the proposed regulation
(e.g., who will be trained/instructed,
what are the minimal requirements for
completing the training/instruction).
EPA believes training should be
commensurate with an individual’s
assigned duties, the degree of
involvement with the management of
the unwanted materials, and the
transportation of potentially hazardous
waste until the ultimate hazardous
waste determination and treatment,
storage or disposal of such hazardous
waste is made. Therefore, EPA
maintains it is sufficient for students to
be instructed in the applicable
laboratory chemical and unwanted
materials management standards and
practices of today’s proposal to enable
them to perform learning and
enrichment activities customarily
performed by students in the laboratory.
Laboratory workers, including graduate
students, must be trained in accordance
with their job function. EPA is
including graduate students in the same
category for training as laboratory
workers, as explained in the definition
sections (section IV.A of this preamble
and § 262.200 of subpart K), since
graduate students often perform many of
the same chemical or unwanted
materials management functions as
laboratory workers employed by, or
otherwise in service to, a college or
university.
EPA distinguishes training from
instruction to correspond with the level
of knowledge or practical application
needed by individuals to perform their
assigned functions or fulfill their job or
enrollment classification (i.e., professor,
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EH&S, graduate student) within a
college or university laboratory. EPA
believes instruction constitutes
familiarization or transference of
knowledge to perform tasks and
assignments in a safe and
environmentally sound manner. For
example, students conducting
experiments will come in contact with
and use a variety of chemicals which
may potentially become hazardous
waste following experimentation or may
react adversely if incorrectly stored or
managed. These potentially hazardous
wastes must be stored in containers to
minimize risk and labeled to alert
individuals that the contents of the
container should be managed in a
certain manner. There is also the
potential for dangerous or hazardous
situations such as explosions, fires,
spills, or other hazards from
mishandling of chemicals or unwanted
materials which require emergency
response actions by qualified personnel.
It is not necessary that students have the
capability of an emergency response
coordinator or other qualified
individual to respond and perform
emergency procedures and other
remedial actions. Rather, it is sufficient
for students to know how to correctly
handle and manage potentially
hazardous wastes to avoid dangerous or
hazardous situations and in case of an
emergency, the correct information or
procedures to follow such as contact
information and evacuation procedures.
Conversely, the Agency considers
training as more formalized or technical
instruction whereby upon completion of
training, personnel are qualified to
perform the functions of their job
descriptions or assigned duties. To
illustrate, current RCRA personnel
training for LQGs under 40 CFR
265.16(a)(1) describes required training
as classroom or on-the-job training. It
also requires personnel to complete a
training program that teaches them to
perform their duties in a way which
ensures compliance with the
regulations. Therefore, for the purpose
of subpart K, laboratory workers must
receive formalized training or technical
instruction commensurate with their
duties (which is dependent on an
individuals job description or
assignments), be able to supervise or
instruct students in the laboratory and
generally perform duties which fulfill
responsibilities contained in their job
description or assigned duties, which
may include conducting chemical
analysis, preparing containers for
transport, emergency response duties or
other duties, as appropriate. It is
required that personnel conducting the
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hazardous waste determination or
transporting unwanted materials on-site
be RCRA-trained according to the
generator status of the college or
university. In the case of laboratory
workers, the level of training needed by
workers is dependent on their
individual duties and may not require
these individuals to be RCRA-trained to
the same degree as required for
individuals involved in the on-site
transport of unwanted materials or
making the hazardous waste
determination if these duties are not
assigned to them.
Under this proposal, colleges and
universities choosing to be subject to
this new set of alternative regulations
have the flexibility to determine the
appropriate subject matter for
instructing their students and training
laboratory workers and to tailor the
training to individual needs according
to function, duties and tasks. For
example, to meet the requirement that
all laboratory workers must receive
training in accordance with their
functions, a college or university may
develop training that includes proposed
laboratory practices and standards for
unwanted materials management. As
with personnel training for individuals
not making the hazardous waste
determination or transporting unwanted
materials on-site, EPA is not mandating
specific subject matter, materials or
methods for instructing students.
However, the Agency believes
appropriate instruction for students
would cover such information as
unwanted materials management
standards and practices sufficient to
enable students to manage unwanted
materials safely and in an
environmentally sound manner, while
working in the laboratory. Both training
of laboratory workers and instruction of
students must ensure that appropriate
and accurate information is conveyed to
the RCRA-trained individual in order
for that individual to make accurate
hazardous waste determinations and to
safely transport unwanted materials onsite, if appropriate.
EPA believes it is necessary for
individuals involved in the on-site
transportation of potentially hazardous
wastes and individuals making the
hazardous waste determination (either
in the laboratory, on-site CAA or on-site
TSDF) to receive the full complement of
RCRA training in accordance with the
college or university’s generator status
as found in 40 CFR 262.34(a)(4) and
265.16 for LQGs, and 262.34(d)(5)(iii)
for SQGs. EPA is requiring that
individuals involved in the on-site
transportation of unwanted materials
receive this level of training due to the
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potential of a release or spill directly to
the environment (e.g., soil, air, water) or
risks from an explosion or other
accident, while potentially hazardous
wastes or other materials are in route
during on-site transport. EPA also
believes that individuals making the
hazardous waste determination must be
aware of all applicable RCRA
requirements in order to be able to
classify the unwanted materials as solid
and hazardous wastes and identify the
RCRA hazardous waste code(s) for
proper hazardous waste or unwanted
materials management or re-use.
Therefore, §§ 262.207(c) and (d),
262.209, 262.210(a) and (e), 262.211(a)
and (c), and 262.212(a) and (c) of
subpart K require that a RCRA-trained
individual accompany on-site transport
of unwanted materials and hazardous
wastes and only RCRA-trained
individuals may make the hazardous
waste determination. EPA also is
requiring in today’s proposal that
contractors employed by the college or
university involved in laboratory
management of unwanted materials or
hazardous waste as contained in subpart
K must be RCRA-trained per LQG
requirements regardless of a college or
universities generator status. To
summarize, the existing training
requirements relevant to RCRA-trained
individuals cited above:
1. LQG regulations under 40 CFR
265.16 set a minimum of required
elements (much of which pertain to
emergency response) as follows:
a. Personnel must successfully
complete a program of classroom
instruction or on-the-job training that
teaches them to perform their duties in
a way that ensures compliance and must
include hazardous waste management
procedures (including contingency plan
implementation) relevant to their
employment position. Personnel who
have not successfully completed
training must not work in unsupervised
conditions.
b. The training program must be
directed by an individual trained in
hazardous waste management. At a
minimum, training must be designed to
ensure that personnel are able to
effectively respond to emergencies by
familiarizing them with emergency
procedures, equipment and systems.
Where applicable, personnel are
required to become familiar with the
procedures and information of
§ 265.16(a)(3)(i)–(vi), such as responses
to fires or explosions, or groundwater
contamination incidents.
In addition, LQG training
requirements of 40 CFR 265.16 require
that personnel take part in an annual
review of training (§ 265.16(c)) and must
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maintain training records including a
written description of the types and
amount of training completed in
accordance with job descriptions
(§ 626.16(d)).
2. SQG training requirements of 40
CFR 262.34(d)(5)(iii) require the
generator to ensure all employees are
thoroughly familiar with proper waste
handling and emergency procedures,
relevant to their responsibilities during
normal college or university operations
and emergencies.
For purposes of Subpart K, training
records for RCRA-trained individuals at
college or university large quantity
generators must be kept as currently
required by 40 CFR 265.16. Both large
and small quantity generators must
address training standards for RCRAtrained individuals in their LMP as
required by subpart K (see details in
preamble section IV.D for recordkeeping
and section IV.C.11 for LMP
requirements associated with today’s
proposed rule).
As stated earlier, EPA is not
proposing specific types of training
methods for laboratory workers or
instruction requirements for students.
Rather, each college or university
choosing to be subject to subpart K may
determine the best training or
instruction method to meet their
circumstances and operations. For
example, training methods may consist
of a variety of approaches, including
formal classroom or electronic training,
on-the-job training, or instruction to
students by professors or other qualified
personnel before or during an
experiment. Professors may choose to
simulate an emergency event as a
method to instruct students on proper
emergency contact or evacuation
procedures, or choose to post
information or procedures in the
laboratory and/or test the students on
these procedures as part of regular
exams. Regardless of the method used,
a college or university is required to
address the training and instruction
standards found in today’s proposed
rule and must document the training
methods in its LMP. In addition,
training or instruction must be sufficient
to enable individuals to carry out their
duties in an environmentally safe and
sound manner and in accordance with
other appropriate regulations.
The Agency is also considering an
alternative option to today’s proposal.
This option is a more prescriptive
regulatory approach than the proposed
performance-based option. Like the
proposed option, this option requires
that training/instruction be
commensurate with the duties of
laboratory workers and students based
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on the degree of involvement with
handling and management of unwanted
materials, and transportation of
potentially hazardous waste. Also, as
with the proposal, laboratory workers
and graduate students would receive
training, while students are required to
receive instruction in appropriate areas.
Colleges and universities would tailor
the training/instruction to the
individuals’ functions and would
determine training and instruction
methods that best fit the college or
university’s environment (see examples
in the proposal above). However, with
this alternative, EPA would set certain
minimum training requirements for
laboratory workers and students.
Specifically, EPA would require that: (1)
Students receive instruction in proper
container management and labeling
(§ 262.206), collection procedures for
unwanted materials (§ 262.208), and
emergency procedures (as added, if
appropriate); and (2) laboratory workers
must be trained in the same subject
matter as students, and any additional
training necessary to perform their
individual duties. For instance,
laboratory workers may need to receive
more technical or extensive training in
the same areas as students to be able to
teach, supervise or otherwise assist
students in laboratory chemical and
unwanted materials management
practices. In addition, further training
maybe required beyond what is
sufficient to be able to supervise
students in the laboratory if laboratory
workers perform other duties such as
chemical inventories, laboratory cleanouts, emergency response or other
duties not required of students. These
additional duties would require training
in the areas not required of students.
Furthermore, as with the proposed
option, only RCRA-trained individuals
may be tasked with on-site
transportation of unwanted materials
(see summary of RCRA training
requirements in the proposed option
above for LQGs and SQGs) and colleges
and universities must address the
required training standards in their
LMP.
The Agency requests comments on
the proposed performance-based
training and instruction requirements
and the alternative option offered. The
proposed option grants maximum
flexibility to colleges and universities in
meeting the training requirements. The
alternative option sets minimum
standards which colleges and
universities would be required to meet.
In both cases, training must be
documented in the college and
university’s LMP. Additionally, the
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Agency is interested in receiving
comment on training requirements
under other regulations that institutions
may use to fulfill the requirements of
today’s proposed option.
5. Removal Frequency of Unwanted
Materials
Typically, laboratories initially
accumulate hazardous wastes within the
laboratory before sending the hazardous
wastes to an on-site or off-site location.
As the initial accumulation area for
hazardous wastes, the laboratory
generally manages the hazardous waste
in a satellite accumulation area (see
§ 262.34(c)). Under the current
regulations, the removal of hazardous
waste from satellite accumulation areas
is dependent on the volume of
hazardous waste. That is, once more
than 55 gallons of hazardous waste (or
more than 1 quart of acutely hazardous
waste) is accumulated in a satellite
accumulation area, a generator has three
days to remove the excess hazardous
waste from the satellite accumulation
area and transfer it to an area that
complies with § 262.34(a) for large
quantity generators, or § 262.34(d) for
small quantity generators. Of course, the
hazardous waste from the laboratory
may also be sent to an on-site TSDF or
off-site TSDF. Large quantity generators
are allowed to accumulate hazardous
waste for up to 90 days on-site without
a permit, provided the standards of
§ 262.34(a) are met. Similarly, small
quantity generators are allowed to
accumulate hazardous waste for up to
180 days on-site without a permit,
provided the standards of § 262.34(d)
are met.5 The hazardous waste
management standards in §§ 262.34(a)
and 262.34(d) are more comprehensive
than the regulations for accumulating
hazardous waste in satellite
accumulation areas in § 262.34(c). The
satellite accumulation regulations of
§ 262.34(c)(2) require that once 55
gallons of hazardous waste is exceeded,
only the excess of 55 gallons of
hazardous waste must be removed (or
the excess of 1 quart of acutely
hazardous waste) from the satellite
accumulation area.
Colleges and universities have told
EPA that they rarely accumulate 55
gallons in a laboratory, except during a
laboratory clean-out, which occurs, for
example, when faculty retire or when
buildings are renovated. Thus, under
the existing hazardous waste
5 Small quantity generators that must send their
hazardous waste more than 200 miles for off-site
treatment, storage or disposal are allowed to
accumulate hazardous waste for 270 days or less
on-site without a permit, provided the conditions
of § 262.34(d) are met (see § 262.34(e)).
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regulations, the hazardous waste can
remain in the laboratory for long periods
of time, provided that no more than 55
gallons of hazardous waste (or 1 quart
of acutely hazardous waste) is
accumulated, since there is no time
limit for how long a satellite
accumulation area can take to
accumulate 55 gallons. However, once
55 gallons is exceeded, the excess must
be removed within three days. Colleges
and universities have commented that
the three-day time limit is insufficient
for EH&S personnel to respond to
individual waste removal requests at
laboratories that are sometimes spread
out over extensive grounds of a college
or university campus.
Today, EPA is proposing to regulate
the removal of unwanted materials from
laboratories at colleges and universities
primarily by time, and secondarily by
volume of unwanted materials
(including reactive acutely hazardous
unwanted materials). EPA is proposing
that unwanted materials, including
reactive acutely hazardous unwanted
materials, generated in laboratories at
colleges and universities must be
removed from the laboratory at a regular
interval that is specified in the college
or university’s Laboratory Management
Plan. However, the regular interval for
routine removal of unwanted materials
must not exceed six months. If a
laboratory accumulates more than 55
gallons of unwanted materials, or one
quart of reactive acutely hazardous
reactive unwanted material, prior to the
regularly scheduled removal specified
in the college or university’s Laboratory
Management Plan, then all of the
unwanted materials, including the
reactive acutely hazardous unwanted
materials, must be removed from the
laboratory within 10 calendar days of
exceeding 55 gallons or one quart of
acutely hazardous reactive materials, or
at the next regularly scheduled removal,
whichever occurs first. Colleges and
universities that do not have an on-site
central accumulation area or on-site
TSDF will have to ensure that
laboratories do not exceed 55 gallons, or
be prepared to arrange for transportation
off-site to a designated facility within 10
calendar days of exceeding 55 gallons.
EPA is proposing this alternative
regulation for two reasons. First, it is
rare for a laboratory to accumulate 55
gallons of hazardous waste (other than
during laboratory clean-outs); therefore,
hazardous waste can accumulate in
laboratories for extended periods of
time. The Agency believes a time-driven
schedule for removal of hazardous
waste from laboratories is more
appropriate for the way laboratories
operate and generate hazardous waste.
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Second, regularly scheduled removals of
unwanted materials will provide
additional protection for laboratory
workers and students, as well as the
environment, since the regular removal
of unwanted materials will result in
accumulation of lower volumes of
unwanted materials in the laboratory for
shorter periods of time.
Colleges and universities will be
required to identify in their LMP the
frequency of removals of all unwanted
materials. The Agency is proposing to
impose a maximum time of six months
that may elapse between removals.
Colleges and university representatives
have told EPA that tying the removal of
wastes with the academic calendar
would facilitate removal of wastes that
accumulate during the course of the
semester with a minimum of disruption.
The Agency believes that six months is
an appropriate length of time to allow
colleges and universities to schedule
removals of unwanted materials at the
end of each semester. The Agency
realizes that many colleges and
universities have more than the
traditional two semesters; however, the
Agency is not aware of any college or
university that has a semester exceeding
six months. EPA is requesting comment
on whether six months is an appropriate
maximum interval for regularly
scheduled removal of unwanted
materials or whether another time
interval may be more appropriate.
Colleges and universities are certainly
free to schedule the removal of
unwanted materials from their
laboratories at a shorter interval, if that
best suits their schedule. However, EPA
does not believe that allowing unwanted
materials to accumulate for longer than
six months would provide the benefits
to human health and the environment
that are anticipated from moving to a
time-driven rather than volume-driven
approach.
Although many commenters have told
EPA that laboratories rarely accumulate
55 gallons of hazardous waste, the
Agency is maintaining the current
volume-driven removal approach as a
secondary measure to prevent
laboratories from accumulating
unnecessary volumes of unwanted
materials. Today’s proposal differs from
the current satellite accumulation area
regulations, which are also volumedriven, in two ways. First, rather than
being required to remove just the excess
of 55 gallons of hazardous waste (or one
quart of acutely hazardous waste), EPA
is proposing that if a laboratory
accumulates more than 55 gallons of
unwanted materials or one quart of
reactive acutely hazardous unwanted
materials, all the unwanted materials
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must be removed from the laboratory.
The Agency believes that if a RCRAtrained individual is called upon for
removal of unwanted materials, it makes
sense to remove all the containers of
unwanted materials, rather than leave
up to 55 gallons of potentially
hazardous waste or one quart of reactive
acutely hazardous unwanted materials
behind, while removing only the excess
of unwanted materials. Secondly, the
Agency is proposing to extend from
three days to ten calendar days the time
that a college or university has to
remove unwanted materials from a
laboratory when that laboratory exceeds
55 gallons of unwanted materials or one
quart of reactive acutely hazardous
unwanted materials. Under the current
regulations, if a college or university has
a schedule for waste removal from
laboratories and a laboratory requests
that waste be removed due to an
exceedance of the specific thresholds, it
may be difficult for EH&S staff to
respond to the request within three
days. For example, when removal
requests are made just prior to
weekends or holidays, three days will
likely not provide sufficient time to
respond to the request, and to continue
routine waste removals. Commenters
have suggested to EPA that extending
the period from three days to ten
calendar days will provide enough
flexibility to allow colleges and
universities to respond to what is
expected to be an unusual occurrence of
exceeding 55 gallons of unwanted
materials or one quart of reactive
acutely hazardous unwanted materials
in a laboratory, while maintaining the
requirement for regular waste removal
from laboratories.
Currently, when a generator
accumulates more than 55 gallons of
hazardous waste (or 1 quart acutely
hazardous waste) in a satellite
accumulation area, the generator has
three days to remove the excess
hazardous waste from the satellite
accumulation area to another location.
The Agency has received numerous
inquiries regarding the definition of
‘‘three days’’ in the current satellite
accumulation area regulations. The
Agency has interpreted ‘‘three days’’ to
mean ‘‘three calendar days’’ (see memo
from Robert Springer, Director, OSW to
EPA Regional Directors, 3–17–04, a
copy of which is included in the docket
for today’s proposed rule). For clarity, in
today’s proposal, the Agency is
including the word ‘‘calendar’’ in the
regulatory language that allows ten days
to remove unwanted materials that
exceed 55 gallons (or 1 quart of reactive
acutely hazardous unwanted materials).
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That is, once a laboratory accumulates
more than 55 gallons of unwanted
material (or 1 quart of reactive acutely
hazardous unwanted materials), all of
the unwanted material (or reactive
acutely hazardous unwanted material)
must be removed within 10 calendar
days. EPA is requesting comment on
whether 10 calendar days is an
appropriate length of time for removing
all of the unwanted material (or reactive
acutely hazardous unwanted material)
from the laboratory, once 55 gallons (or
1 quart) is exceeded in the laboratory.
1. Reactive Acutely Hazardous
Unwanted Materials
EPA recognizes the higher risk from
reactive acutely hazardous unwanted
materials (as defined in section IV.A. of
this preamble), and has determined that
there is justification for treating these
materials somewhat differently from
other unwanted materials, including
others that are potentially acutely
hazardous waste. The Agency has
decided that these seven reactive
acutely hazardous unwanted materials
should be subject to a lower volume
limit for accumulation in the laboratory.
These reactive chemicals pose extreme
danger to laboratory personnel when
they are stored for long periods and
become unstable. When they become
unstable, these reactive chemicals have
the potential to cause significant harm
to individuals and property. Reactive
acutely hazardous unwanted materials
must be removed from the laboratory
during regularly scheduled pick-ups,
along with all unwanted materials. But,
the Agency is proposing that if a
laboratory exceeds 1 quart of these
acutely reactive unwanted materials
prior to a regularly schedule removal,
then all the acutely reactive unwanted
materials must be removed from the
laboratory within 10 calendar days of
exceeding 1 quart, or at the next
regularly scheduled removal, whichever
occurs first. Because these reactive
acutely hazardous unwanted materials
are, by definition, unused commercial
chemical products, and there are
currently only seven such chemicals,
they will be easily identifiable by a
laboratory worker or student, and could
therefore be collected separately from
other unwanted materials. By
segregating reactive acutely hazardous
unwanted materials from other
materials, the student or laboratory
worker could easily determine when the
one quart limit is reached.
b. Other Unwanted Materials That Are
Potentially Acutely Hazardous Waste
Other than the reactive unwanted
materials listed as acutely hazardous in
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261.33(e), the remainder of unwanted
materials that may eventually be
determined to be acutely hazardous
waste will not be subject to the lower
accumulation volumes. Current
requirements for managing hazardous
wastes in satellite accumulation areas
allow for the accumulation of up to one
quart of acutely hazardous wastes and
require the removal (within three days)
of any excess over one quart. There is
currently no requirement to remove the
initial quart of acutely hazardous waste.
Because today’s proposal does not
require that the hazardous waste
determination be made until the
unwanted material is removed from the
laboratory or within 4 calendar days of
arriving at an on-site central
accumulation area or on-site TSDF,
there is no way to distinguish in the
laboratory between unwanted materials
that may be acutely hazardous waste
and those that may be non-acutely
hazardous waste. Therefore, under
today’s proposal, except for the reactive
acutely hazardous unwanted materials,
unwanted material which may later be
determined to be acutely hazardous
waste is subject to the same
requirements as other unwanted
material generated in the laboratory, and
may potentially accumulate in the
laboratory in volumes greater than one
quart. However, unlike the current
generator regulations, today’s proposal
requires all unwanted material
accumulated in the laboratory to be
removed at a regular interval not to
exceed six months. Furthermore, when
55 gallons of unwanted materials or one
quart of reactive acutely hazardous
unwanted materials is exceeded, all
unwanted materials must be removed
from the laboratory, not merely the
excess of 55 gallons, as is required
currently.
EPA believes that the risk associated
with acutely hazardous waste is reduced
in the laboratory by requiring unwanted
material to be removed from the
laboratory at least every six months and
requiring that all of the unwanted
materials be removed at regularly
scheduled pick-ups, as well as when
maximum volumes are exceeded.
Additionally, today’s proposed
alternative regulations contain
provisions, such as training
requirements for laboratory workers,
instruction for students, and the
Laboratory Management Plan, which
includes planning for emergency
response, which the Agency believes
will improve management of unwanted
materials, while in the laboratory.
Improved management will limit the
potential for human exposure and spills
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from all unwanted materials, including
those which may later be determined to
be acutely hazardous wastes. For these
reasons, EPA does not propose to treat
potentially acutely hazardous waste,
with the exception of reactive acutely
hazardous unwanted materials,
differently from other potentially
hazardous waste that is generated in the
laboratory.
6. Where and When To Make the
Hazardous Waste Determination
In today’s proposal, the Agency is
providing maximum flexibility for
colleges and universities with respect to
where the hazardous waste
determination may be made, while still
providing protection of human health
and the environment. Section 262.209
in today’s proposal, requires colleges
and universities to make the hazardous
waste determination under § 262.11 on
unwanted materials generated in
laboratories in one of three places: (1) In
the laboratory before the unwanted
materials are removed from the
laboratory (see § 262.210), (2) within 4
calendar days of arriving at an on-site
central accumulation area (see
§ 262.211), or (3) within 4 calendar days
of arriving at an on-site TSDF (see
§ 262.212). Regardless of where the
hazardous waste determination is made,
all of the standards that EPA is
proposing today for managing unwanted
materials in the laboratory would apply,
while the unwanted materials remain in
the laboratory, including training/
instruction, labeling, and container
management. Also, regardless of where
the hazardous waste determination is
made, an unwanted material that is
determined to be a hazardous waste is
subject to all applicable hazardous
waste regulations from that point,
including the land disposal restrictions
of part 268, all requirements for the onsite management of hazardous waste,
and any applicable requirements
pertaining to off-site transportation.
As with all hazardous waste
determinations, if a RCRA-trained
individual determines that an unwanted
material is suitable and intended for
direct use or reuse at another laboratory
or location at the college or university,
or does not meet the definition of solid
waste in 40 CFR 261.2, then the
unwanted material will not become
subject to the hazardous waste
regulations. Likewise, if a RCRA-trained
individual determines that an unwanted
material is a solid waste, but not a
hazardous waste, the unwanted material
is no longer subject to the hazardous
waste regulations, including part 262.
However, the non-hazardous solid
wastes must be managed and disposed
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of according to applicable State and
local solid waste management
requirements.
Transferring Unwanted Materials or
Hazardous Wastes From the Laboratory
to an On-Site Central Accumulation
Area, or On-Site TSDF
Currently, when hazardous waste is
removed from a laboratory that manages
it in a satellite accumulation area, it can
be brought to an on-site generator
accumulation area (sometimes called a
<90 or <180 day area), an on-site TSDF,
or picked up for transport to an off-site
designated facility, such as an off-site
TSDF. EPA’s policy has been that
hazardous waste in a satellite
accumulation area may not be
transferred to another satellite
accumulation area (see memo from
Robert Springer, Director, OSW to EPA
Regional Directors; 3–17–04, a copy of
which is in the docket for today’s
proposal). Today’s proposal maintains
all the same options and prohibitions
for the removal of unwanted materials
from the laboratory and for the removal
of hazardous wastes from the laboratory
if the hazardous waste determination is
made in the laboratory.
Many of the unwanted materials that
will be transferred from laboratories to
an on-site central accumulation area or
an on-site TSDF will ultimately be
determined to be hazardous wastes.
Therefore, EPA believes it is appropriate
to keep the existing level of protection
for the on-site movement of unwanted
materials. EPA’s interpretation of
existing regulations is that any
personnel responsible for the on-site
movement of hazardous waste must
receive the level of training appropriate
to the college or university’s generator
status, as specified by § 262.34(d)(5)(iii)
for small quantity generators and
§ 265.16 for large quantity generators
(see memo from Robert Springer,
Director, OSW to EPA Regional
Directors; 3–17–04, a copy of which is
in the docket for today’s proposal). EPA
is proposing to codify this regulatory
interpretation for the on-site movement
of unwanted materials at colleges and
universities.
To ensure that unwanted materials
removed from the laboratory are brought
promptly to their next destination, the
Agency is proposing to require that
when unwanted materials are removed
from a laboratory, they must be brought
‘‘directly’’ from the laboratory(ies) to an
on-site central accumulation area or an
on-site TSDF. Without such a
requirement, the Agency is concerned
that the unwanted material or hazardous
wastes could be held in on-site transport
for days or longer (without any specific
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controls) before it is delivered to its next
destination.
The Agency realizes that in certain
cases, the RCRA-trained individual will
remove the unwanted material from a
single laboratory and deliver it
immediately to the central accumulation
area, while in other instances, the
RCRA-trained individual will remove
the unwanted material from a number of
laboratories before it is delivered to the
central accumulation area. In both cases,
this would meet the intent of the
regulation. On the other hand, if a
RCRA-trained individual that is
collecting unwanted materials from
laboratories leaves the unwanted
materials on a cart in the hallway
overnight, this would not meet the
intent of the regulations. In general, if
the unwanted materials are sent from
the laboratory to its next destination
within the same work day, this would
meet the intent of today’s requirement
to bring unwanted materials or
hazardous wastes ‘‘directly’’ from the
laboratory to an on-site central
accumulation area, or on-site TSDF.
EPA is seeking comment on whether it
is necessary to define ‘‘directly’’ or to
replace it with a more specific timeframe, such as a same day requirement.
7. Making the Hazardous Waste
Determination in the Laboratory
Any college or university that chooses
to comply with today’s new set of
alternative regulations for unwanted
materials generated in laboratories will
have the option of making the
hazardous waste determination in the
laboratory before the unwanted
materials are removed from the
laboratory. The Agency believes that
this option will be most useful for those
colleges and universities that do not
have on-site central accumulation areas
or on-site TSDFs. EPA expects that
smaller colleges and universities are less
likely to have on-site central
accumulation areas or on-site TSDFs
and will be the most likely to benefit
from making the hazardous waste
determination in the laboratory before
the unwanted materials are removed
from the laboratory. Nonetheless, the
Agency would like to extend the added
flexibility of this option to colleges and
universities that have on-site central
accumulation areas or on-site TSDFs, as
well. Some colleges or universities with
on-site central accumulation areas or
on-site TSDFs may elect to make the
hazardous waste determination in the
laboratory in order to avoid bringing
non-hazardous wastes to its on-site
central accumulation area or on-site
TSDF. Regardless of whether a college
or university has an on-site central
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29735
accumulation area, or on-site TSDF, if a
college or university identifies in its
Laboratory Management Plan that the
hazardous waste determination will be
made in the laboratory, EPA is
proposing that the hazardous waste
determination may be made in the
laboratory at any time, but must be
made before the unwanted materials are
removed from the laboratory.
Commenters have told EPA that there
are a number of reasons a college or
university may choose not to build and
maintain an on-site central
accumulation area. First, some colleges
and universities choose not to have a
central accumulation area because they
lack the extra resources needed to have
an emergency coordinator available at
all times to be either on-site or on call,
as required for both small and large
quantity generators (see
§§ 262.34(d)(5)(i) and 265.55,
respectively). Secondly, some colleges
and universities do not have the
physical space to build a central
accumulation area and the cost of
acquiring space can be prohibitive.
Thirdly, complying with local fire codes
associated with a central accumulation
area can also make the cost prohibitive.
It is clear, from these comments, that
many colleges and universities that do
not currently operate central
accumulation areas are unlikely to do so
in the future. Therefore, as noted
previously, EPA is proposing that the
hazardous waste determination for
unwanted materials generated in
laboratories at colleges and universities
may be made before the unwanted
materials are removed from the
laboratory.
In many cases, EPA expects that the
hazardous waste determination will not
be made by an employee of the college
or university, but rather by a contractor
or vendor. This practice is acceptable,
since the proposed definition of RCRAtrained individual includes contractors
and vendors, provided the contractor or
vendor has received RCRA training.
Regardless of who makes the hazardous
waste determination in this scenario, it
must be made on all unwanted materials
before the unwanted materials may be
removed from the laboratory. In
addition, regardless of whether an
employee or non-employee makes the
hazardous waste determination, the
college or university could still be
responsible if the hazardous waste
determination is not made correctly and
for any mismanagement of hazardous
waste.
When an unwanted material has been
determined to be a hazardous waste
prior to its removal from the laboratory,
it remains subject to subpart K for as
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long as it remains in the laboratory. This
is to avoid having the laboratory being
dually regulated as a satellite
accumulation area for the unwanted
materials that have been determined to
be hazardous wastes and as a laboratory
under subpart K. For those unwanted
materials that are determined to be
hazardous wastes in the laboratory, the
appropriate hazardous waste code(s)
and the words ‘‘hazardous waste’’ must
be placed on the container label that is
affixed to the container prior to
removing it from the laboratory. Upon
removal from the laboratory, an
unwanted material that has been
determined to be a hazardous waste is
subject to all applicable hazardous
waste regulations, including the land
disposal restrictions. Additionally, an
unwanted material that is determined to
be a hazardous waste must be counted
toward the college or university’s
generator status. If an RCRA-trained
individual determines that an unwanted
material is not a solid or hazardous
waste, then it would no longer be
subject to part 262, including subpart K.
Many commenters representing
colleges and universities have suggested
that EPA create a new type of
accumulation area to allow for the
consolidation of hazardous wastes from
laboratories. Under the existing
regulations, generators may accumulate
hazardous waste in two types of areas
without having a permit or interim
status: (1) satellite accumulation areas
and (2) generator accumulation areas
(<90 or <180 day areas).6 EPA believes
that today’s proposal provides sufficient
flexibility for colleges and universities
to manage the unwanted materials that
are generated in their laboratories.
Nevertheless, the Agency is soliciting
comment on whether such an additional
category should be created. (See section
below for specific request for comment.)
Under the current satellite
accumulation area regulations,
hazardous wastes must be accumulated
at or near the point of generation. In
addition, it has been EPA’s regulatory
interpretation that hazardous wastes can
not be moved from one satellite
accumulation area to another (see memo
from Robert Springer, Director, OSW to
EPA Regional Directors; 3–17–04, a
copy of which is in the docket for
today’s proposal). Although many
commenters suggested EPA create a new
type of consolidation area, one
commenter suggested a specific type of
6 Small quantity generators that must send their
hazardous waste more than 200 miles for off-site
treatment, storage, or disposal are allowed to
accumulate hazardous waste for 270 days or less
on-site without a permit, provided the conditions
of § 262.34(d) are met (see § 262.34(e)).
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consolidation area—a ‘‘super satellite
area’’—whereby hazardous wastes could
be consolidated in a common area that
is outside of the laboratory (i.e, not at or
near the point of generation), but the
current satellite accumulation area
regulations, including volume limits,
would continue to apply to the
consolidated wastes. The commenter’s
primary goal was to enhance the safety
of laboratory personnel by removing
hazardous wastes from the laboratory as
quickly as possible in order to prevent
accidents. EPA believes that this
concept would only be practical for
laboratories generating relatively low
volumes of waste, since combining
hazardous wastes from multiple
laboratories could result in quickly
exceeding 55 gallons of unwanted
materials or one quart of reactive
acutely hazardous unwanted materials,
which would require frequent removals.
Thus, EPA is not proposing to establish
a ‘‘super satellite area,’’ as suggested by
the commenter. However, the Agency is
soliciting comment on this concept, and
specifically, the Agency requests
comment on why this approach is
needed and what additional safeguards
should be imposed, if any.
In summary, EPA is requesting
comment on whether today’s proposal
will enable colleges and universities
without central accumulation areas to
take advantage of the intended benefits
of today’s rule. EPA is requesting
comment on our proposal or other
alternative approaches for allowing
colleges and universities without central
accumulation areas to benefit from this
rule. Specifically, EPA is requesting
comment on the creation of a third
category of accumulation area—such as
a consolidation area or ‘‘super satellite
area.’’ The Agency encourages
commenters to be as specific as possible
about what management standards
would apply to consolidation areas and
how those conditions would differ from
those required in the current two types
of accumulation areas. The Agency also
requests that commenters address
whether creating a new type of category
of accumulation area would eliminate
the concerns that have been raised to
EPA by colleges and universities which
do not operate an on-site central
accumulation area.
8. Making the Hazardous Waste
Determination at an On-Site Central
Accumulation Area
Based on the information that EPA
received from college and university
representatives, including from a public
meeting in June 2003, receiving nearly
50 written comments to the associated
docket, and participating in many
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meetings, EPA has come to expect that
most colleges and universities will
remove their unwanted materials from
laboratories to an on-site central
accumulation area. Under the existing
hazardous waste regulations, when
hazardous wastes are removed from the
laboratory to an on-site central
accumulation area, the waste has
already been identified as a hazardous
waste and is subject to the applicable
requirements, including the requirement
to identify the hazardous waste code.
EPA is proposing that when a RCRAtrained individual removes containers
of unwanted materials from the
laboratory and the unwanted material is
brought to an on-site central
accumulation area, the hazardous waste
determination must be made within four
calendar days after the unwanted
material arrives at the on-site central
accumulation area. The Agency has
selected four calendar days for making
the hazardous waste determination to
allow sufficient time to make a
hazardous waste determination when
unwanted materials are removed from a
laboratory at the end of the work week.
Since the unwanted materials will be
fully regulated upon arrival in the
central accumulation area, with the
exception of the ‘‘hazardous waste’’
label and hazardous waste code, the
Agency believes that allowing four
calendar days for the hazardous waste
determination does not compromise
protection of human health and the
environment.
EPA is proposing that from the time
the unwanted material arrives in the
central accumulation area, it will be
subject to the full central accumulation
area regulations of § 262.34(a) or
§ 262.34(d). Among other things, these
existing generator regulations require
that containers must be dated upon
arrival in the central accumulation area.
Under the existing generator
regulations, this date is used to calculate
when the maximum accumulation time
for generators has elapsed (either 90,
180 or 270 days). Under today’s
proposal, the date of arrival at the
central accumulation area will also be
used to calculate when the four calendar
days for making the hazardous waste
determination have elapsed. That is,
EPA is proposing that the four calendar
days allowed for making the hazardous
waste determination will be part of the
90 or 180 (or 270) days of maximum
accumulation time, not in addition to it.
EPA is proposing that containers in the
central accumulation area will not be
required to be labeled with the words
‘‘hazardous waste,’’ as required by
§ 262.34(a)(3), until after a hazardous
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waste determination has been made.
When a RCRA-trained individual
determines that an unwanted material is
a hazardous waste, the appropriate
hazardous waste code(s) and the words
‘‘hazardous waste’’ must be added to the
label that is affixed to the container.
EPA is requesting comment on
whether four calendar days is an
appropriate timeframe for making the
hazardous waste determination for
unwanted materials in the central
accumulation area (or at an on-site
TSDF), or whether another time period
is more suitable. EPA also seeks
comment on whether the four day
period in which to make the hazardous
waste determination should be added to
the 90 or 180 (or 270) days of
accumulation in the central
accumulation area. Under today’s
proposal, by including the four calendar
days as part of the 90/180/270 days, the
date of arrival at the central
accumulation area would be used for
two purposes: (1) Calculating the four
calendar days allotted for making the
hazardous waste determination and (2)
calculating the maximum accumulation
time in the central accumulation area.
Under this scenario, the total maximum
accumulation time in the central
accumulation area would be 90/180/270
days, which is the same as the current
regulations. Under today’s proposal, the
hazardous waste determination would
also have to be made within the first
four calendar days of the on-site
accumulation time. If, however, the four
calendar days is in addition to the 90/
180/270 days, then additional dating
would be required after the hazardous
waste determination is made. That is,
the date of arrival at the central
accumulation area would be used for
calculating the four calendar days
allotted for making a hazardous waste
determination and a second date would
be required after the hazardous waste
determination is made for calculating
the maximum accumulation time in the
central accumulation area. Under this
scenario, the total maximum
accumulation time would increase from
90/180/270 days to 94/184/274 days.
The Agency seeks comment on whether
the benefit of an additional four
calendar days of accumulation time
warrants an additional dating
requirement.
9. Making the Hazardous Waste
Determination at an On-Site TSDF
In a few cases, colleges and
universities have on-site permitted (or
interim status) storage or treatment
facilities. In such cases, a college or
university may choose to make the
hazardous waste determination in the
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laboratory before the unwanted
materials are removed or bring
unwanted materials to their on-site
TSDF for the hazardous waste
determination. EPA is proposing to
allow colleges and universities to have
the flexibility of choosing whichever
option works best for them.
Under today’s proposal, there will be
many operational similarities between a
college or university that makes the
hazardous waste determination at an onsite central accumulation area and a
college or university that makes the
hazardous waste determination at an onsite TSDF. For example, colleges and
universities that choose to make the
hazardous waste determination at their
on-site TSDF must bring their unwanted
materials directly from the
laboratory(ies) to the on-site TSDF and
must make the hazardous waste
determination within four calendar days
of arriving at the on-site TSDF. The
Agency does not intend to add any new
dating requirements for colleges or
universities that operate on-site TSDFs.
Therefore, in order to calculate when
the four calendar days have elapsed,
EPA will rely on the requirement for
dating containers upon arrival at a TSDF
that already exists in the storage
prohibition regulations of part 268 [see
§ 268.50(a)(2)(i)]. In order to implement
the storage prohibition, EPA requires
that containers of hazardous waste must
be labeled with the date accumulation
begins at a TSDF. This requirement will
now have the secondary purpose of
determining when four calendar days
have elapsed for colleges and
universities that make the hazardous
waste determination in an on-site TSDF.
10. Laboratory Clean-Outs
While today’s proposal does not
require periodic laboratory clean-outs,
EPA strongly encourages that such
clean-outs be conducted in laboratories
at colleges and universities. EPA
inspections and enforcement cases at
colleges and universities have revealed
that used and unused chemicals, but
particularly unused chemicals, have
remained in laboratories for years and
even decades and can have the potential
to cause significant harm to human
health and the environment. Regular
removals of unwanted materials will
help remove some materials from the
laboratory, but may not address the
problem of ‘‘legacy’’ chemicals. These
legacy chemicals often accumulate over
many years in a laboratory as
researchers purchase chemicals for new
projects without using or disposing of
chemicals from previous projects. Other
times, EPA has been told that chemicals
are purchased in much larger quantities
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than are necessary for an experiment,
because it is less expensive to buy in
bulk, and the excess remains in the
laboratory. In other cases, chemicals
accumulate in laboratories when the
management of an individual laboratory
changes, such as when professors retire
or move to another institution. In some
of these cases, chemicals are left behind
in the laboratory by a previous
occupant, the new laboratory occupant
may not know the contents of the
containers, and the chemicals remain in
the laboratory unidentified.
In the definitions section of today’s
proposal, the definition of ‘‘laboratory
clean-out’’ is described. In short, EPA
envisions laboratory clean-outs as more
comprehensive than the regularly
scheduled removals of unwanted
materials. It is a process of sorting and
evaluating to determine what should be
eliminated from the laboratory’s
inventory.
EPA has been told that the current
satellite accumulation area regulations
are a barrier to conducting clean-outs of
laboratories. Specifically, when
laboratory clean-outs are conducted, it
is likely that more than 55 gallons of
chemicals, whether used or unused, will
be generated. The existing satellite
accumulation area rules require that
once 55 gallons of hazardous waste (or
one quart of acutely hazardous waste) is
exceeded, the excess of 55 gallons must
be removed within three days.
Commenters have told EPA that the
current requirement to move the excess
of 55 gallons of hazardous waste (or one
quart of acutely hazardous waste)
within three days is an impediment to
comprehensive laboratory clean-outs,
because it does not provide enough time
to sort through and evaluate the many
chemicals that can be part of a
laboratory clean-out. Under today’s
proposal, when 55 gallons of unwanted
materials (or one quart of reactive
acutely hazardous unwanted materials)
is exceeded in a laboratory, the college
or university has 10 calendar days to
remove all of the unwanted materials
from the laboratory. EPA believes that
even 10 calendar days may not be a
sufficient amount of time to conduct a
thorough evaluation of the inventory of
unused chemicals in a laboratory.
Therefore, in an effort to encourage
laboratory clean-outs, EPA is proposing
certain modifications to the hazardous
waste regulations that are designed to
make it more advantageous for colleges
and universities to conduct clean-outs.
Specifically, EPA is proposing that
during a laboratory clean-out only, a
college or university will have up to 30
calendar days to sort through unwanted
materials from the laboratory. EPA has
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chosen 30 calendar days for the
duration of a clean-out because college
and university representatives have
indicated that this would allow
sufficient time to complete a thorough
laboratory clean-out. EPA hopes that the
extra time that EPA is including in
today’s proposal for laboratory cleanouts, will remove an existing regulatory
obstacle for conducting laboratory
clean-outs at colleges and universities.
During the course of a laboratory
clean-out, as chemicals are evaluated
and sorted, the determination about
whether a chemical or other material is
an unwanted material will be made. No
doubt, some chemicals that are
evaluated during a laboratory clean-out
will end up not being unwanted
materials. Once it has been determined
that a chemical is, indeed, an unwanted
material, as opposed to a chemical or
other material that can be kept in the
laboratory for further use, then the
unwanted material becomes subject to
subpart K.
If, at the conclusion of a laboratory
clean-out, the total volume of unwanted
materials in the laboratory does not
exceed 55 gallons and the total volume
of reactive acutely hazardous unwanted
materials does not exceed one quart, the
unwanted materials may remain in the
laboratory until the next regularly
scheduled removal of unwanted
material. However, EPA would
encourage colleges and universities that
generate unwanted materials during a
laboratory clean-out to remove the
unwanted materials promptly to an onsite central accumulation area, an onsite TSDF or an off-site designated
facility, even if 55 gallons is not
exceeded. When determining whether
55 gallons of unwanted materials has
been exceeded in a laboratory, EPA does
not intend for routinely generated
unwanted materials to be counted
separately from unwanted materials
generated at laboratory clean-outs.
If, however, the volume of unwanted
materials generated during a laboratory
clean-out exceeds 55 gallons, at the end
of the 30-day laboratory clean-out, all
unwanted materials must be removed
from the laboratory, regardless of
whether it was generated during the
clean-out or during routine laboratory
activities. As with other unwanted
materials in today’s proposal, unwanted
materials generated during a laboratory
clean-out must be brought directly to an
on-site central accumulation area, onsite TSDF, or an off-site TSDF. If the
unwanted materials generated during a
laboratory clean-out will be transferred
to an on-site central accumulation area
or on-site TSDF, the hazardous waste
determination, which must be done by
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a RCRA-trained individual, may be
made in the laboratory during the cleanout, but must be made no later than four
calendar days after arriving at an on-site
central accumulation area, or on-site
TSDF. If the unwanted materials from a
laboratory clean-out are not destined for
further on-site management in a central
accumulation area or on-site TSDF, the
hazardous waste determination must be
made in the laboratory and the
hazardous waste sent off-site by the
conclusion of the 30-day laboratory
clean-out.
EPA has been told that another barrier
to conducting laboratory clean-outs is
the possibility that the volume of
hazardous waste generated during a
laboratory clean-out would be sufficient
to change the college or university’s
generator status. This change in
generator status would add additional
regulatory burden, such as fewer days
for on-site accumulation in a central
accumulation area, or a requirement to
have a contingency plan. Therefore,
EPA is proposing that the hazardous
waste generated during a laboratory
clean-out will not be counted toward
calculating the amount of hazardous
waste generated per month when
determining a college or university’s
generator status. Under the existing
hazardous waste regulations, all
hazardous wastes generated during a
laboratory clean-out would be counted
toward the college or university’s
generator status (unless it meets one of
the exclusions in § 261.5(c) or (d)). EPA
believes adding this flexibility will
allow colleges and universities that are
small quantity generators to undertake
laboratory clean-outs without changing
their generator status.
The Agency believes that both of
these changes, allowing 30 calendar
days for a laboratory clean-out and not
counting hazardous wastes from
laboratory clean-outs in calculating
generator status, should encourage
routine laboratory clean-outs. The
Agency believes that laboratory cleanouts will go a long way toward
addressing unused ‘‘legacy’’ chemicals
that pose a threat to human health and
the environment.
Nevertheless, while EPA wants to
encourage laboratory clean-outs at
colleges and universities, the Agency is
also concerned that by providing these
two incentives, EPA may be
inadvertently encouraging colleges and
universities to retain unwanted
materials that are generated in the
laboratory on a routine basis and
remove them only during laboratory
clean-outs. Therefore, EPA feels that it
must limit the frequency with which
colleges and universities can take
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advantage of the two incentives for
laboratory clean-outs to once per 12month period per laboratory. Without
such a safeguard, a college or university
that is currently a large quantity
generator could become a conditionally
exempt small quantity generator by
claiming that it is conducting monthly
laboratory clean-outs since it is not
required to count the hazardous waste
toward its generator status. EPA is
proposing that for each 12-month period
each laboratory may have 30 calendar
days to conduct a laboratory clean-out
with the hazardous waste generated
during that laboratory clean-out
excluded from the college or
university’s monthly waste quantity
determination. The Agency has selected
a ‘‘12-month period,’’ rather than
‘‘calendar year’’ because selecting
‘‘calendar year’’ could allow a
laboratory clean-out to occur once in
November of one calendar year and
again in January of the following
calendar year, and this was not EPA’s
intent. EPA wants to ensure that there
will be at least one regularly scheduled
removal of unwanted materials between
laboratory clean-outs. Therefore, each
laboratory may take advantage of the
incentives for laboratory clean-outs only
once per 12-month period.
Unwanted materials generated prior
to a laboratory clean-out that are still in
the laboratory at the time a laboratory
clean-out begins must be counted
toward the college or university’s
generator status. The proposed labeling
standards requires that laboratories
must identify the date that unwanted
materials begin accumulating in a
container. Therefore, any containers
with dates that pre-date the onset of a
laboratory clean-out are not considered
part of the laboratory clean-out and
must be counted toward the college or
university’s generator status.
EPA emphasizes that it is not limiting
the number of laboratory clean-outs a
college or university may conduct, only
the frequency with which a college or
university laboratory may take
advantage of the proposed regulatory
incentives. If a laboratory has conducted
a laboratory clean-out within the past 12
months, EPA does not expect a
subsequent laboratory clean-out to yield
an excess of 55 gallons of unwanted
materials. However, if a laboratory
conducts a subsequent laboratory cleanout within the same 12-month period
and generates an excess of 55 gallons of
unwanted materials, the unwanted
materials would have to be removed
from the laboratory within 10 calendar
days, in conformance with the
requirements proposed for exceeding 55
gallons on a routine basis and that
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amount would have to be counted in
determining the generator status of the
college or university.
EPA also emphasizes that any
hazardous waste that is not counted
toward generator status during a
laboratory clean-out is still a hazardous
waste and is subject to all applicable
regulations, including the land disposal
regulations, and the regulations for onsite and off-site management,
transportation, and treatment and
disposal of hazardous waste. The
incentive that the Agency is proposing
to provide for hazardous wastes
generated during a laboratory clean-out
affects only the length of time that
hazardous wastes are stored on-site and
other associated regulations of 40 CFR
262.34 pertaining to generator status,
such as biennial reporting and
contingency plans.
Because EPA is reluctant to impose
barriers to laboratory clean-outs, it does
not want to require overly burdensome
recordkeeping for laboratory clean-outs.
However, the Agency believes that it
must require some minimal
recordkeeping related to laboratory
clean-outs to ensure compliance with
the proposed requirements. The
recordkeeping requirements would only
apply if the college or university intends
to take advantage of the laboratory
clean-out incentives. A participating
college or university that conducts a
laboratory clean-out must keep records
that identify the laboratory that has been
cleaned out, the date the clean-out
began and was completed, and the
volume of hazardous waste generated
during the laboratory clean-out. The
Agency believes these records are
necessary to ensure that a college or
university is in compliance with the
proposed requirements. The records
identifying which laboratory is being
cleaned out and the date the clean-out
begins should be created at the onset of
the laboratory clean-out. All records
pertaining to laboratory clean-outs must
be maintained for as long as the college
or university operates under this new
subpart.
A college or university may also want
to implement a system for
distinguishing between hazardous
wastes that are counted and hazardous
wastes that are not counted toward
generator status. Such a system could
consist of labels on individual
containers, or separate storage areas, or
records in a log book. EPA is not
proposing to require such a mandatory
tracking system, in order to provide
colleges and universities with maximum
flexibility.
EPA requests comments on the
provisions related to laboratory clean-
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outs. First, the Agency seeks comment
on whether laboratory clean-outs should
be required, rather than simply
encouraged. In responding to this
request, the Agency would appreciate
any information or data that would
support that such clean-outs should be
required. Second, the Agency requests
comment on whether 30 calendar days
is an appropriate length of time for
conducting a laboratory clean-out.
Third, the Agency seeks comment on
whether the proposal provides
appropriate mechanisms for
encouraging laboratory clean-outs or
whether there might be a better
incentive that EPA could provide.
Fourth, EPA is requesting comment on
whether limiting these incentives to
once per 12-month period per laboratory
is appropriate or whether a different
interval, or no limit, would be more
appropriate. Fifth, the Agency seeks
comment on whether it would be
appropriate to allow a college or
university to take advantage of the
incentives for laboratory clean-outs if
the clean-out occurred in a chemical
stock room that is not itself a laboratory,
but that supplies laboratories with new
or redistributed chemicals.
11. Laboratory Management Plan
Today’s proposal would require
colleges and universities choosing to be
subject to the proposed alternative
regulations to develop a Laboratory
Management Plan (LMP).
Under today’s proposed rule, the
performance-based standards set the
framework for managing unwanted
materials generated in a college or
university laboratory, while the LMP is
the mechanism for implementing those
performance-based standards. A college
or university is required to develop an
LMP which articulates how it plans to
comply with the performance-based
requirements for safely managing the
unwanted materials generated in
laboratories. Specifically, the LMP must
describe how the college or university
proposes to meet the standards for
regularly scheduled removal of
unwanted materials from the laboratory,
container management, labeling
requirements, the requirements for
instructing students and training
laboratory workers, the requirements to
ensure safe transportation of unwanted
material or hazardous waste from the
laboratory to an on-site accumulation
area, on-site TSDF or an off-site TSDF,
and emergency preparedness and
response procedures. Additionally,
although laboratory clean-outs are
voluntary, if a laboratory conducts
clean-outs, the college or university
must also describe its laboratory clean-
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out procedures in the LMP. EPA is
requiring an LMP as part of this
proposal to ensure that a college or
university seeking flexibility in
managing the unwanted materials from
their laboratories will do so in a
thoughtful manner by documenting
their practices in an LMP. The LMP
replaces the ‘‘one-size-fits all’’
provisions of the current regulations
with the option for a college or
university to develop their own system
for managing unwanted materials from
the laboratory. EPA has found that the
written environmental management
plan was a key component to the
positive changes seen during the EPA
University Laboratories XL Project.
While today’s proposed rule would
only require the above elements to be
addressed in a college or university’s
Laboratory Management Plan, EPA
envisions and encourages that
additional elements could be
incorporated into the LMP or that the
LMP could form the basis for, or be
incorporated as part of, a larger effort to
‘‘green’’ a campus. The LMP could help
colleges and universities to go beyond
compliance with today’s proposed
regulations by developing a program
addressing all of their waste issues. The
college or university could design a
campus-wide recycling program or
develop waste minimization programs
for implementation. EPA envisions that
the LMP will present an opportunity for
colleges or universities to address all
aspects of their waste management
programs in a holistic manner.
While the development of an LMP is
required under today’s proposed rule,
EPA is proposing two options regarding
the enforceability of the LMP. The first
option requires that an LMP be
developed and that specific elements of
today’s proposal be contained in the
LMP, but under this option the college
or university would have some
flexibility in how it implemented the
specific provisions in its LMP. Provided
the college or university meets the
performance-based standards set forth
in the rule, it would be in compliance
with today’s rule. The requirement to
develop an LMP would, however, be
enforceable and the failure to develop a
plan would be a violation of this
requirement.
As an example, under this option, an
individual college or university may
decide to meet the requirement that
containers of unwanted materials have
certain information associated with
them by using a particular computer
tracking system, and indicate this in its
LMP. While EPA would expect the
computer tracking system to be used as
stated, if for some reason that system is
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not functioning, and the university
tracks the information manually,
provided the information included with
the unwanted materials meets the
requirements of the regulation (i.e. it
provides sufficient information to allow
a RCRA-trained individual to make the
hazardous waste determination), EPA
would consider the college or university
to be in compliance with the
performance-based standards.
Under the second proposed option, as
in the previous option, colleges and
universities would be required to
develop an LMP, and address all the
specific elements of today’s proposal.
The LMP, however, would be
enforceable. Therefore, a college or
university would need to follow the
specific provisions in its LMP, to be in
compliance with this requirement. Only
the parts of the LMP that are developed
to satisfy the requirements of this
subpart would be enforceable. If a
college or university chooses to include
elements not required by this proposal,
resulting in a broader LMP, those other
elements contained in the LMP would
not be enforceable.
As an example, under this option, an
individual college or university may
decide to meet the requirement that
containers of unwanted materials have
certain information associated with
them by using a particular computer
tracking system, and indicate this in its
LMP. EPA would expect the college or
university to utilize the computer
tracking system as described in the
LMP. If the college or university fails to
use this computer tracking system, EPA
would consider the college or university
to be in violation of these regulations.
As described elsewhere, today’s
proposed alternative regulations allow
colleges and universities flexibility to
tailor their laboratory operations to fit
their individual circumstances, and
remain protective of human health and
the environment. Performance-based
standards for management of unwanted
materials generated in laboratories
provide a better opportunity for colleges
and universities to evaluate their overall
hazardous waste management program,
and tailor it in such a way that
facilitates efficient and safe management
of its hazardous waste, and minimizes
burden, while at the same time maintain
a high standard of protection of human
health and the environment. Both of
today’s proposed options would help
each college or university centralize and
coordinate its chemical management
practices and demonstrate
environmental performance.
EPA realizes that many colleges and
universities may already have plans that
address some of the provisions of the
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LMP proposed today. It is not EPA’s
intent for colleges or universities to
develop a separate document or plan in
such a situation. Therefore, both of
today’s options allow a college or
university to revise an existing plan to
address the specific LMP provisions
described above. In this way, colleges
and universities that have existing
plans, such as the Chemical Hygiene
Plan required under OSHA, may use
this plan as a basis for meeting the LMP
provision of today’s proposal, making
only those modifications and/or
additions which would address the
specific provisions required to be
addressed in today’s proposed LMP.
This would avoid the development of
largely redundant plans, while still
ensuring that all provisions are
adequately considered. It is EPA’s belief
that thoughtful, documented planning
will result in better management of
hazardous wastes, and the LMP
requirements can be incorporated into
existing mechanisms to achieve that
end.
Finally, under both proposed options,
the proposed rule would require
colleges and universities to revise the
LMP and improve it as new information
becomes available. EPA envisions the
LMP will evolve and change in
accordance with changes in operations
at the college or university.
In addition to the two options
described above, EPA is also
considering not requiring the
development of an LMP as a condition
of eligibility for this alternative
regulation. In this case, rather than the
‘‘performance-based’’ requirements for
container management, labeling, and
training, etc., more specific
requirements would likely be included
in the regulatory language. (These
specific requirements are discussed in
sections IV. C. 2–4 above.)
Although many stakeholders have
commented that the variability among
colleges and universities makes a ‘‘onesize-fits all’’ approach impractical, and
have stated that a more performancebased approach is preferable, EPA has
learned from others that performancebased standards, by their very nature,
are less specific than more prescriptive
types of regulations. This less
prescriptive form of regulation has the
potential for differing interpretations
regarding whether the standards have
been met. Some stakeholders have
expressed concern regarding
compliance decisions in situations
where one interpretation of a
performance-based standard may differ
from another. For such a college or
university, complying with more
specific regulatory conditions for the
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management of unwanted materials in
the laboratory may be preferable to
having performance-based requirements
accompanied by the requirement to
develop an LMP.
While EPA believes that the
development of an LMP will provide
colleges and universities with an
opportunity to thoroughly examine the
hazardous waste management
operations and practices in a holistic
manner and identify areas of savings
and improved management, the Agency
is mindful of the additional burden.
Therefore, EPA is taking comment on
whether the Final Rule should require
the development of an LMP. The
process of developing an LMP can be
lengthy and resource intensive for a
college or university. For the LMP to be
an effective and beneficial tool, we
recommend that a college or university
evaluate its current hazardous waste
management practices and identify
areas for improvement, as well as any
barriers to meeting the performancebased standards. While EPA is
proposing that a college or university
may modify an existing plan to meet the
requirement of an LMP (rather than
developing a separate plan), many
colleges and universities may not have
a pre-existing plan to build upon. For
these colleges and universities, the
added burden of developing an LMP
may discourage them from taking
advantage of the benefits of today’s
proposal. However, EPA believes that
colleges and universities can greatly
benefit from the development of a
comprehensive LMP and strongly
encourages colleges and universities to
develop a plan regardless of whether it
is a mandatory requirement in the final
rule or not.
EPA is requesting comment on
whether the proposed approach of
combining performance-based standards
with a requirement for an LMP is
practical, or whether it would be
preferable to have more specific
regulatory conditions for the
management of unwanted materials in
the laboratory due to the burden of
developing an LMP.
D. Recordkeeping
Today’s proposal requires that every
college and university choosing to
comply with this alternative set of
regulations maintain certain records.
Specifically, colleges and universities
must maintain the following records: (1)
Notification(s) to the appropriate EPA
Regional Administrator (or State
Director, in authorized states) of its
participation in or subsequent
withdrawal from subpart K; (2) a
Laboratory Management Plan (LMP) (an
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existing plan may be modified to
address the specific requirements of this
alternative regulation, as finalized); (3)
training records for RCRA-trained
individuals and laboratory workers as
defined in 40 CFR 262.200 of this
subpart; and (4) documentation of
laboratory clean-out activities
identifying the laboratory being cleaned
out, the date the clean-out begins and is
completed, and the volume of waste
accumulated during a clean-out if a
college or university chooses to conduct
such clean-outs.
In today’s proposal, EPA is requiring
that the college or university maintain a
copy of its notification to participate in
subpart K on file for the duration the
college or university remains subject to
subpart K. Additionally, the college or
university must maintain a copy of its
notification to withdrawal from today’s
proposal, as finalized, on file for three
(3) years.
Also, in today’s proposal, EPA is
requiring that the most recent copy of
the college or university’s LMP be
retained on file at the college or
university for the duration that it is
regulated under 40 CFR part 262,
subpart K. Furthermore, the LMP must
be dated and accessible by anyone
involved in the management of
unwanted materials, including students
in the laboratory. The college or
university must determine how best to
meet the requirements of this proposal.
Further, since EPA envisions that an
LMP will be revised periodically, the
college or university must determine
how best to maintain it, keep records,
make revisions, etc. It is important to
note that subpart K does not supersede
or in any way alter the requirements of
existing plans used or modified to
comply with subpart K.
Today’s proposal also requires that
training records for RCRA-trained
individuals (individuals conducting the
hazardous waste determination or
transporting unwanted materials onsite) and for laboratory workers are
maintained in accordance with existing
applicable training requirements
pertaining to a college or university’s
generator status. SQG training
requirements at 40 CFR 262.34(d)(5)(iii))
do not require retention of training
records. Since EPA proposes no changes
to the existing recordkeeping
requirements for compliance with
today’s proposal, RCRA-trained
individuals at large quantity generators
must comply with recordkeeping
requirements found at 40 CFR 265.16(e).
For laboratory workers at LQG colleges
and universities, training records that
are sufficient to indicate whether the
laboratory worker has received adequate
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training commensurate with their duties
that ensures understanding the
requirements of complying with this
alternative regulation must be
maintained (e.g., if laboratory workers
are tasked with making the hazardous
waste determination or transporting
unwanted materials on-site then these
employees would need to be RCRAtrained (see definitions in § 262.200).
Under existing LQG recordkeeping
provisions for training, these records
must be kept until the institution closes
or for three years after departure of a
laboratory worker. In addition, it is
sufficient for college and university
laboratories that maintain training
records required under existing
regulations (i.e., LQGs) to cite in its
LMP where existing training
requirements and records are
maintained for RCRA-trained
individuals and laboratory workers.
Today’s proposal would require a
second labeling or information
requirement, other than currently
required by 40 CFR 262.34(c).
Specifically, the following labels are
required for containers for college and
university laboratories choosing to be
regulated under subpart K: (1) A
precautionary label that must be affixed
or physically accompany the container
and (2) a second label (or other media
such as a computer system that contains
the required information) that may
either be affixed or somehow associated
with the container that contains the date
unwanted materials began accumulating
in the laboratory and sufficient
information for a RCRA-trained
individual to make the hazardous waste
determination. At a minimum, these
labels must be affixed or otherwise
associated with their containers until
the hazardous waste determination is
made. However, it is left to the best
judgement of each college or university
to determine if labels should be kept
longer.
Additionally, this alternative
regulation includes a new
recordkeeping provision for laboratory
clean-out events at colleges and
universities. Section 262.213 of today’s
proposal requires colleges and
universities to document their clean-out
activities. EPA is not mandating a
particular record format or media.
Instead, colleges and universities may
determine the most appropriate type of
record to maintain that best suits their
individual capabilities and
recordkeeping systems (e.g., filed hard
copy, electronic copy). However, the
documentation must contain certain
specific information and be retained at
the college or university, while the
college or university laboratories are
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regulated under 40 CFR part 262,
subpart K. Specifically, this
documentation must include the date
the activity began and the date the
clean-out was complete, the particular
laboratory that is being cleaned out, and
the volume of hazardous waste
generated during the clean-out. This
documentation is particularly relevant
since a laboratory may only utilize the
waiver from counting hazardous wastes
toward generator status and the 30-day
allowance for removal once per 12month period per laboratory.
Additionally, clean-out records must be
easily accessible by inspectors and other
relevant college and university
personnel.
Today’s proposal strives to reduce or
minimize additional recordkeeping
requirements on colleges and
universities choosing to be subjected to
subpart K. As an example, EPA believes
colleges and universities will revise
current planning documents required by
relevant regulations such as OSHA’s
Chemical Hygiene Plan (CHP), where
practicable. In this instance, a CHP, as
revised, is required to be kept under
OSHA laboratory standard regulations at
29 CFR 1910.1450 and, therefore, no
additional recordkeeping requirement
would be associated with an LMP.
However, EPA also understands that
this may not be true in all cases. While
EPA does not expect this to be the case,
where planning documents suitable for
modification to comply with subpart K
are not kept as a current requirement for
a particular college or university, an
additional recordkeeping requirement
would be associated with maintaining
an LMP since colleges and universities
may need to develop this document to
comply with this subpart.
EPA also believes utilizing existing
generator regulatory provisions for
training records associated with today’s
proposal is another example of how the
Agency is minimizing burden.
Specifically, today’s proposal requires
that college and university laboratories
comply with the same requirements that
currently apply to its generator status
for maintaining training records for
RCRA-trained individuals and
laboratory workers. However, as is the
case for an LMP, if training records do
not exist, college and university
laboratories would need to maintain
pertinent records to comply with this
proposal.
EPA is considering whether
maintenance of other records or
reporting requirements not included in
the paragraphs above should be required
under today’s alternative regulation for
purposes of improving implementation
and compliance monitoring and
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assistance by the relevant regulatory
authority or for program
implementation. However, it is not
EPA’s intention to place such additional
recordkeeping or reporting burden on
colleges and universities as to make
subpart K unattractive or otherwise too
burdensome. Therefore, EPA seeks
comment on whether records are
needed to assure compliance with
subpart K requirements such as the
retention of container labels for a
specified length of time or if specific
reporting requirements are needed for
program implementation. The Agency is
also requesting comment on whether
other types of recordkeeping or
reporting should be required to ensure
compliance with today’s proposed
regulation, to measure program success,
or if existing reporting requirements
exist which may further reduce burden
on colleges and universities.
Specifically, EPA is requesting comment
on whether maintenance of training
records for RCRA-trained or laboratory
workers at SQGs should be required, or
if other additional records or
information are needed to assure college
and university laboratories are
conducting clean-outs or managing
unwanted materials in the laboratory
according to requirements of this
subpart (e.g., retention of labels with
unwanted materials accumulation and
removal dates for specified period of
time after the hazardous waste
determination is made such as
electronic labels accompanying
containers, or records on container
maintenance). In addition, EPA is
considering using the RCRA Subtitle C
Site Identification Form [EPA Form 87–
12] in the Notification of Waste Activity
Instructions and Form Booklet or the
required state form as a substitute for
the proposed notification process.
Therefore, EPA is seeking comment on
whether the alternative notification
option contained in today’s proposal of
utilizing the RCRA Subtitle C Site
Identification Form should be required
instead of the proposed requirement to
submit a separate notice to the
appropriate EPA Regional Administrator
(or State Director, in authorized states)
to enter or withdraw from subpart K.
Specifically, instead of submitting a
written notification to enter or exit
regulation under subpart K, colleges and
universities would notify the
appropriate state (in authorized states
that have adopted the final rule) or EPA
authority of their regulatory status by
submitting a Subsequent Notification of
Regulated Waste Activity. The college or
university laboratory generator would
complete the RCRA Subtitle C Site
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Identification Form [EPA Form 87–12]
in the Notification of Waste Activity
Instructions and Form Booklet or the
required state form. Data from the form
is maintained in the agency’s RCRAInfo
system. EPA also requests comment on
whether using this method would
reduce burden on colleges and
universities. In lieu of requiring
notification using EPA Form 87–12,
EPA is seeking comment on whether to
include a requirement for the
appropriate EPA Regional Administrator
(or State Director, in authorized states)
to send an acknowledgment of receipt to
colleges and universities submitting a
notification to either enter or withdraw
from regulation under subpart K. EPA is
also seeking comment on whether
colleges and universities would still
choose to be subject to subpart K if
additional recordkeeping or reporting
requirements are necessarily imposed
and when it would be too burdensome.
E. Implementation and Enforcement
Colleges and universities with
laboratories that are subject to the
existing hazardous waste regulations of
40 CFR 262.11 and 262.34(c) must
comply with either those existing
regulations or with today’s proposed
subpart K of part 262, as finalized.
Today’s proposal co-proposes two
enforcement options for the Laboratory
Management Plan (LMP) requirement.
Under proposed option one, colleges
and universities must develop,
implement and maintain an LMP.
However, how a college or university
chooses to meet the required rule
standards in the LMP is not enforceable.
Proposed option two, as with option
one, requires colleges and universities
to develop, implement and maintain an
LMP; however, the college or university
must comply with the procedures
described in their LMP. Only colleges
and universities with eligible
laboratories, as defined in this proposal,
may choose to manage their wastes
according to subpart K. All laboratories
sharing a single identification number
(ID) must comply with either the
existing generator regulations of 40 CFR
262.11 and 262.34(c) or with subpart K
of 40 CFR part 262. Specifically, a
college or university may not decide to
manage the unwanted materials from
some of its laboratories or campuses
under the existing hazardous waste
regulations and then manage unwanted
materials from other laboratories with
that same ID number under today’s
proposed alternative regulations.
However, colleges and universities may
choose which set of regulations (i.e., 40
CFR subpart K or 40 CFR 262.11 and
262.34(c)) to comply with on a case-by-
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case basis for laboratories or campuses
with unique RCRA ID numbers.
In addition, since today’s proposal is
optional, it is possible that eligible
colleges and universities could be
subject to two different sets of
requirements for waste management: 40
CFR part 262, subpart K for unwanted
materials generated in its laboratories
and 40 CFR part 262, subpart C for all
other applicable wastes generated by the
college or university. Further, the
regulatory status of laboratories sharing
the same RCRA ID number may
fluctuate periodically since colleges and
universities have the option to enter or
exit regulation under subpart K at their
discretion. As a result, implementers
will need to determine a college or
university’s laboratory regulatory status
at any given time for compliance
monitoring and assistance.
Colleges and universities regulated
under subpart K of part 262 must adhere
to the requirements and standards set
forth therein for notifying the
appropriate State or EPA Administrator
of its participation or subsequent
withdrawal from subpart K (§§ 262.203–
262.204), making the hazardous waste
determination (§§ 262.209–262.212), the
container management and labeling
requirements (§ 262.206), the training
requirements (§ 262.207), and the
requirement to develop and maintain an
LMP which under proposed option one
addresses the required performancebased elements of § 262.214 of the rule,
or under proposed option two address
and complies with the measures
developed by the college or university
and contained in their LMP to meet the
performance-based elements of
§ 262.214 of today’s proposed rule. In
addition, colleges and universities must
adhere to the quantity limits and
removal frequencies for unwanted
materials both in the laboratory and at
other on-site locations (§ 262.208), and
the safe movement of unwanted
materials from laboratories to other onor off-site destinations (§§ 262.210,
262.211 and 262.212). Further, the
college or university must make its LMP
available to students, laboratory
workers, others at the college or
university who request it and
inspectors, and the LMP must be
reviewed and revised as needed. Failure
to comply with the requirements of the
rule, including the performance-based
requirements and standards set forth in
the rule, may subject a college or
university to an enforcement action. To
comply with the LMP requirement of
proposed option one, colleges and
universities must meet the performancebased standards requirements set forth
in the proposed rule; however, how a
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college or university chooses to describe
its procedures in the LMP or how the
LMP is implemented is not an
enforceable action. For a college or
university to comply with the coproposed option two for the LMP
requirement, a college or university
must implement the measures contained
in their LMP to meet the performancebased standards. For example,
minimum standards exist in the rule
with which colleges and universities are
required to comply, including a
requirement for an LMP and a
requirement to document in a college or
university’s LMP how it will meet the
standards of the rule. Specifically, an
LMP must describe how a college or
university will meet the required
standards for: (1) Container labeling and
management in accordance with
§ 262.206(a) and (b); (2) training of
laboratory workers, other appropriate
faculty, and environmental health and
safety personnel, commensurate with
their duties in accordance with
§ 262.207(a); (3) instructing students in
accordance with § 262.207(b); (4)
ensuring the safe movement of
unwanted materials from the laboratory
to an on-site central accumulation area;
an on-site interim status/permitted
treatment, storage, or disposal facility;
or an off-site interim status/permitted
treatment, storage, or disposal facility in
accordance with § 262.207(c); (5)
developing a regular schedule for
identifying and removing unwanted
materials from its laboratories in
accordance with § 262.208, (6) making
the hazardous waste determination,
including where the determination will
be made in accordance with § 262.209
and (7) conducting laboratory clean-outs
in accordance with § 262.213, if a
college or university chooses to conduct
these events. If these required standards
are not addressed in an LMP, the college
or university is in violation and an
enforcement action may ensue.
However, under the proposed option it
is the intent of the proposed rule that if
a college or university does not comply
precisely with the terms of its LMP, that
no enforcement action can be levied
against it, provided the college or
university meets the performance-based
requirements. As an example, colleges
and universities must describe in a LMP
how it will instruct students. If the
college or university LMP contains an
instruction program that includes a
specific number of hours of classroom
training for students, but students
receive either a different number of
hours, or a different type of training,
such as video instruction, the college or
university would not be in violation of
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subpart K, as long as the students are
instructed and meet the performancebased standards. However, it is the
intent of co-proposed option two to
require that a college or university’s
LMP is enforceable. Specifically, while
the college or university may tailor the
approach or measures developed to
meet the required standards of the rule
in order for a college or university to be
in compliance with co-proposed option
two, the college or university must
implement those measures as developed
and described in their LMP.
Further, under subpart K, colleges and
universities are required to maintain
and retain certain records as specified in
section D of this preamble and the
appropriate sections of this proposed
rule. Specifically, colleges and
universities must maintain the
following records: (1) Notifications to
enter or exit participation in subpart K,
(2) an LMP, (3) training records for
RCRA-trained individuals and
laboratory workers, and (4) laboratory
clean-outs.
In summary, colleges and universities
with laboratories must either comply
with the existing regulations found at 40
CFR 262.11 and 262.34(c), or with
today’s proposal, as finalized. Colleges
and universities with eligible
laboratories electing to be regulated
under subpart K must comply with the
requirements set forth in today’s
proposal. Failure to comply with these
requirements or to meet the
performance-based standards of this
proposed rule may result in an
enforcement action. As referenced above
and specified in the rule language, a
violation may occur if colleges or
universities fail to notify the appropriate
EPA Regional Administrator or State
Director of their election to participate
or withdrawal from regulation under
subpart K and to include the required
information in the notice; do not
develop or revise an existing plan to
meet the LMP requirements of this
proposal; fail to meet required container
labeling and management standards; do
not maintain required records, such as
training records for RCRA-trained
individuals at LQGs, clean-out
documentation and notifications to
enter or withdrawal from subpart K; do
not instruct students and train
laboratory workers and other relevant
faculty commensurate with their duties;
do not comply with the requirement
that only RCRA-trained individuals may
make the hazardous waste
determination or transport unwanted
materials on- or off-site; and do not
comply with the rule requirements for
making the hazardous waste
determination in the laboratory, or on-
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site CAA, or TSDF, including such
requirements as frequencies for
removing unwanted materials from the
laboratory or on-site CAA, or TSDF;
quantity limits for accumulating
unwanted materials or chemicals in the
laboratory; providing dates for
unwanted material accumulation and
removal in the laboratory or other areas
where the hazardous waste
determination is made or for laboratory
clean-outs. In essence, while this
summary is not exhaustive, failure to
adhere to or comply with any of the
requirements as found in today’s
proposal or failure to meet any of the
performance-based standards of this
proposal may result in an enforcement
action.
In addition, today’s proposed rule
would not affect the college and
university’s obligation to promptly
respond to any releases of hazardous
wastes that may occur, including
releases in the laboratory, as they may
later prove to be hazardous wastes once
the hazardous waste determination is
made. Any management of released
material not in compliance with
applicable Federal and State hazardous
waste requirements could result in an
enforcement action. For example, an
individual who spilled or released a
hazardous waste and failed to
immediately clean it up could
potentially be subject to enforcement for
illegal disposal of the hazardous wastes.
See, for example, 40 CFR 264.1(g)(8). In
addition, solid and hazardous waste
releases could potentially be addressed
through enforcement orders, such as
orders under RCRA sections 3013 and
7003.
V. State Authorization
A. Applicability of the Rule in
Authorized States
Under section 3006 of RCRA, EPA
may authorize qualified states to
administer their own hazardous waste
programs in lieu of the federal program
within the state. Following
authorization, EPA retains enforcement
authority under sections 3008, 3013,
and 7003 of RCRA, although authorized
states have primary enforcement
responsibility. The standards and
requirements for state authorization are
found at 40 CFR part 271.
Prior to enactment of the Hazardous
and Solid Waste Amendments of 1984
(HSWA), a State with final RCRA
authorization administered its
hazardous waste program entirely in
lieu of EPA administering the federal
program in that state. The federal
requirements no longer applied in the
authorized state, and EPA could not
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issue permits for any facilities in that
state, since only the state was
authorized to issue RCRA permits.
When new, more stringent federal
requirements were promulgated, the
state was obligated to enact equivalent
authorities within specified time frames.
However, the new federal requirements
did not take effect in an authorized state
until the state adopted the Federal
requirements as state law.
In contrast, under RCRA section
3006(g) (42 U.S.C. 6926(g)), which was
added by HSWA, new requirements and
prohibitions imposed under HSWA
authority take effect in authorized states
at the same time that they take effect in
unauthorized states. EPA is directed by
the statute to implement these
requirements and prohibitions in
authorized states, including the
issuance of permits, until the state is
granted authorization to do so. While
states must still adopt HSWA related
provisions as state law to retain final
authorization, EPA implements the
HSWA provisions in authorized states
until the states do so.
Authorized states are required to
modify their programs only when EPA
enacts Federal requirements that are
more stringent or broader in scope than
existing Federal requirements. RCRA
section 3009 allows the states to impose
standards more stringent than those in
the Federal program (see also 40 CFR
271.1). Therefore, authorized states may,
but are not required to, adopt Federal
regulations, both HSWA and nonHSWA, that are considered less
stringent than previous Federal
regulations.
B. Effect on State Authorization
Today’s notice proposes regulations
that would not be promulgated under
the authority of HSWA. Thus, the
standards proposed today would be
applicable on the effective date only in
those states that do not have final
authorization. Moreover, authorized
states are required to modify their
program only when EPA promulgates
Federal regulations that are more
stringent or broader in scope than the
authorized state regulations. For those
changes that are less stringent or reduce
the scope of the Federal program, states
are not required to modify their
program. This is a result of section 3009
of RCRA, which allows states to impose
more stringent regulations than the
Federal program. Today’s proposal,
however, is considered to be neither
more nor less stringent than the current
standards. Therefore, authorized states
would not be required to modify their
programs to adopt regulations consistent
with and equivalent to today’s proposed
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standards. Nevertheless, because EPA
believes that today’s proposal will
increase the ability of colleges and
universities to comply with the RCRA
hazardous waste generator regulations,
which would likely lead to greater
environmental protection, EPA strongly
encourages States to adopt today’s
proposed rule, once it is finalized.
Colleges and universities located in
authorized states wishing to be subject
to subpart K do not have this option
until their state has adopted the final
rule.
VI. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
1. Economic Analysis
Under Executive Order 12866 (58 FR
51735 (October 4, 1993), the Agency, in
conjunction with OMB’s Office of
Information and Regulatory Affairs
(OIRA), must determine whether a
regulatory action is ‘‘significant’’ and
therefore subject to OMB review and the
full requirements of the Executive
Order. 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.
Pursuant to the terms of Executive
Order 12866, it has been determined
that this rule is a ‘‘significant regulatory
action.’’ The proposed rule raises novel
legal or policy issues. The proposed rule
is unlikely to result in any significant
university lab waste management costs
or cost savings. Thus, the $100 million
threshold for economic significance, as
established under point number one
above, is not relevant to this action. In
addition, this rule is not expected to
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. Thus, this rule is not
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considered to be an economically
significant action. This rule is also not
considered significant under points two
through three of the Order. Finally,
while economic benefits have not been
quantified or monetized for this
proposal, we believe such benefits to be
well below the $100 million threshold.
We have prepared an economic
assessment in support of today’s
proposal. This document is entitled:
Assessment of Costs, Benefits, and
Other Impacts For the Proposed Revised
Standards Applicable to Generators of
Hazardous Waste; Subpart K—
Academic Laboratories. Findings from
this document are summarized below.
This document, and any changes made
in response to OMB review, are
maintained in the RCRA docket
established for today’s action. Interested
persons are encouraged to read and
comment on all aspects of this
document.
2. Summary of Proposed Rule Findings:
Costs, Economic Impacts, Benefits
This section summarizes the findings
from our Assessment document, as
identified above. A detailed review of
our analytical methodology, data
sources, findings, and limitations are
presented in the full Assessment
document.
The Agency has identified a total of
1,811 colleges and universities in
operation in the U.S. Of this total
number of colleges and universities, we
estimate that 333 are large quantity
generators (LQGs) and 1,478 are small
quantity generators (SQGs).
The total quantity of hazardous waste
generated by the affected colleges and
universities, excluding remediation
wastes was estimated based on 2001
biennial reporting data. In total, the
affected colleges and universities
generated a total of 11,628 tons of
hazardous waste during 2001. Of this
waste quantity, laboratory hazardous
wastes are estimated to range from
approximately 3,400 to 6,000 tons per
year. Only the management of
laboratory-generated hazardous wastes
are affected by the proposed
rulemaking.
The proposed rule is optional, which
means that individual colleges and
universities may choose to be regulated
under subpart K, or continue to operate
under existing regulations. Furthermore,
because the rule is optional, states with
authority to administer the RCRA
program may adopt the proposed rule
(when it is finalized) or continue to rely
on existing rules. Because the rule is
optional, we believe only some states
will adopt the rule. Additionally, we
believe that colleges and universities
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will only choose to be subject to the rule
if it is deemed to be in their interest. For
purposes of the EA, it is assumed that
only colleges and universities that
would experience a reduction in
hazardous waste management costs
would choose to be subject to the rule.
The aggregate annualized cost savings
associated with the proposed rule are
estimated to range from $0.6 to $2.9
million for all colleges and universities
that choose to be subject to subpart K.
The proposed regulations have
numerous benefits. There are many
economic gains through efficient waste
management practices, waste
minimization and waste coordination
activities. The structured nature of the
Laboratory Management Plan (LMP) will
result in safer laboratory practices and
increased awareness of waste
management. This would minimize
exposure of hazardous substances to
humans and the environment.
Ultimately, the proposed changes would
improve the way universities coordinate
and integrate waste management
activities and enhance awareness about
proper handling techniques.
In addition to the LPM, the proposed
rule specifies training requirements for
students, laboratory workers,
individuals involved in the on-site
transportation of potentially hazardous
wastes and individuals making the
hazardous waste determination. The
requirements for training are expected
to reduce the potential for release of
hazardous materials. For example, waste
generated through experimentation may
react adversely if incorrectly stored or
managed; training requirements for
laboratory workers will ensure workers
are knowledgeable in the storage and
compatibility of waste materials, as well
as reagents.
The Agency believes that the
proposed rule will also encourage more
frequent clean-outs of unwanted
material, including unused reagents
from laboratories. Over time, storage of
unused material stored in the laboratory
can suffer from deteriorating labels and
containers, increasing the chances that a
long-stored reagent will be accidently or
mistakenly released into the
environment. More frequent clean-outs
of laboratories will help to reduce this
potential.
The Agency did not complete a formal
RCRA 3007 survey of college and
university laboratories. Consequently,
for this assessment it was necessary to
rely on publicly available data which
resulted in numerous limitations.
Furthermore, this analysis may not
capture all of the variables that affect a
generator’s decision to manage
hazardous wastes under the proposed
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rule. College and university laboratories
manage hazardous wastes with
substantial variations in procedures and
staff making hazardous waste
determinations, in regarding laboratory
clean-outs, use of subcontractors and
other factors which could not all be
modeled. Additionally, this analysis
relies on biennial reporting data which
does not include hazardous waste
quantities for a number of SQGs.
Furthermore, it is difficult to determine
whether hazardous waste reported is
generated in college and university
laboratories or other college and
university operations.
B. Paperwork Reduction Act (ICR)
The information collection
requirements in this proposed rule have
been submitted for approval to the
Office of Management and Budget
(OMB) under the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. The
Information Collection Request (ICR)
document prepared by EPA has been
assigned EPA ICR Number 0820.10.
EPA is proposing an alternative set of
generator regulations for college and
university laboratories under the
authority of sections 2002, 3001, 3002,
and 3004 of RCRA as amended by the
Hazardous and Solid Waste
Amendments of 1984 (HSWA). Section
2002 authorizes EPA to prescribe
regulations as are necessary to carry out
the requirements under the RCRA
statute. Section 3001 authorizes EPA to
develop and promulgate criteria for
identifying the characteristics of
hazardous waste, and for listing
hazardous waste, which would be
subject to the hazardous waste program.
Sections 3002(a) and 3004(a) direct EPA
to establish requirements for hazardous
waste generators and TSDFs respecting,
among other things, recordkeeping
practices for hazardous wastes.
As stated above, this proposed rule
establishes an alternative set of
generator requirements for eligible
college and university laboratories. It is
important that EPA or the authorized
states know which set of regulations a
college or university is subject to.
Therefore, EPA has determined at
proposed 40 CFR 262.203 and 262.204
that it is necessary to require colleges
and universities to submit a notification
to the EPA Regional Administrator or
State Director, in authorized states
indicating that they are electing to be
subject to or withdrawing from subpart
K for all laboratories under the same
EPA ID number.
Under proposed 40 CFR 262.206,
262.208, 262.10, 262.11, and 262.12
colleges and universities must label
containers of unwanted materials as
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29745
specified. These labeling requirements
are necessary to: demonstrate
compliance with subpart K, alert
individuals handling the containers of
its contents to ensure proper handling,
assist RCRA-trained individuals in
making the hazardous waste
determination and assigning the
appropriate hazardous code(s) and for
enforcement and monitoring purposes.
Proposed 40 CFR 262.207 requires
training or instruction for all
individuals working in a laboratory
commensurate with their duties. This
training/instruction is necessary to
ensure that unwanted materials are
handled safely and in an
environmentally sound manner and in
compliance with the proposal. In
addition, colleges and universities that
are LQGS must maintain training
records for laboratory workers to ensure
compliance with the proposed
requirements.
Under proposed 40 CFR 262.313
colleges and universities must develop
and maintain documentation on
laboratory clean-outs to ensure
compliance with the proposed
requirement.
Under proposed 40 CFR 262.214
colleges and universities are required to
develop, implement and maintain a
laboratory management plan to
document their practices for complying
with the performance-based
requirements of subpart K.
Section 3007(b) of RCRA and 40 CFR
part 2, subpart B, which defines EPA’s
general policy on public disclosure of
information, contain provisions for
confidentiality. However, the Agency
does not anticipate that businesses will
assert a claim of confidentiality covering
all or part of the proposed rule. If such
a claim were asserted, EPA must and
will treat the information in accordance
with the regulations cited above. EPA
also will assure that this information
collection complies with the Privacy
Act of 1974 and OMB Circular 108.
According to the estimates provided
in the ICR for this proposed rule, the
average annual incremental burden to
respondents as a result of the proposed
requirements is approximately 59,136
hours and $2.08 million. 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
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existing ways to comply with any
previously applicable instructions and
requirements; train personnel 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.
To comment on the Agency’s need for
this information, the accuracy of the
provided burden estimates, and any
suggested methods for minimizing
respondent burden, including the use of
automated collection techniques, EPA
has established a public docket for this
rule, which includes this ICR, under
Docket ID number EPA–HQ–RCRA–
2003–0012 or EPA–2050 AG 18 RCRA–
2003–0012. Submit any comments
related to the ICR for this proposed rule
to EPA and OMB. See ADDRESSES
section at the beginning of this notice
for where to submit comment to EPA.
Send comments to OMB at the Office of
Information and Regulatory Affairs,
Office of Management and Budget, 725
17th Street, NW., Washington, DC
20503, Attention: Desk Officer for EPA.
Since OMB is required to make a
decision concerning the ICR between 30
and 60 days after May 23, 2006, a
comment to OMB is best assured of
having its full effect if OMB receives it
by June 22, 2006. The final rule will
respond to any OMB or public
comments on the information collection
requirements contained in this proposal.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA),
as amended by the Small Business
Regulatory Enforcement Fairness Act of
1996 (SBREFA), 5 U.S.C. 601 et seq.,
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For purposes of assessing the impacts
of today’s proposed rule on small
entities, small entity is defined as: (1) A
small business as defined by the Small
Business Administration’s (SBA)
regulations at 13 CFR 121.201; (2) a
small governmental jurisdiction that is a
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government of a city, county, town,
school district or special district with a
population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise that is independently
owned and operated and is not
dominant in its field.
In determining whether a rule has a
significant economic impact on a
substantial number of small entities, the
impact of concern is any significant
adverse economic impact on small
entities, since the primary purpose of
the regulatory flexibility analysis is to
identify and address regulatory
alternatives ‘‘which minimize any
significant economic impact of the
proposed rule on small entities.’’ 5
U.S.C. 603 and 604. Thus, an agency
may certify that a rule will not have a
significant economic impact on a
substantial number of small entities if
the rule relieves regulatory burden, or
otherwise has a positive economic effect
on all of the small entities subject to the
rule.
Because this proposed rule is
performance-based, colleges and
universities with qualifying laboratories
have increased flexibility to manage
materials and hazardous wastes in a
manner best suited to the operations at
their individual institutions. The
Agency believes that hazardous waste
management costs for both small and
large entities will be reduced or
minimized. In addition, since facilities
may choose to either opt into the new
requirements in today’s proposal or to
remain subject to the existing part 262
requirements, EPA believes facilities
will only opt into today’s proposal if
they are more cost effective or otherwise
beneficial to the facility. EPA has
therefore concluded that today’s
proposed rule will relieve regulatory
burden for all small entities.
Because this proposal will not have a
significant impact on a substantial
number of small entities, EPA
nonetheless has tried to reduce the
impact of this proposal on small
entities. In addition to the economic
analysis, we conducted outreach
activities to ensure that small business
interests were informed of our potential
actions, and to solicit input from
representatives of small entities during
the development of the proposal. We
continue to be interested in the
potential impacts of the proposed rule
on small entities and welcome
comments on issues related to such
impacts.
After considering the economic
impacts of today’s proposed rule on
small entities, we have concluded that
this proposed rule will not have a
significant economic impact on a
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substantial number of small entities. For
the reasons discussed above, I certify
that this action will not have a
significant economic impact on a
substantial number of small entities.
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 to State, local,
and tribal governments, in the aggregate,
or to the private sector, of $100 million
or more in any one year. Before
promulgating an EPA 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 costeffective 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, enabling
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.
EPA has 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
to the private sector in any one year.
This is because this final rule imposes
no enforceable duty on any State, local
or tribal governments. EPA also has
determined that this rule contains no
regulatory requirements that might
significantly or uniquely affect small
governments. Thus, today’s rule is not
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Federal Register / Vol. 71, No. 99 / Tuesday, May 23, 2006 / Proposed Rules
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 proposed rule does not have
federalism implications. It will not have
substantial direct effects on the States,
on the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. This proposed
rulemaking directly affects primarily
generators of ‘‘unwanted materials’’ and
hazardous wastes from college and
university laboratories, as defined in
this proposal. There are no state and
local government bodies that incur
direct compliance costs by this
rulemaking. State and local government
implementation expenditures are
expected to be a minimum of $2,126 in
any one year. The $2,126 cost does not
include one-time-only costs of $23,917
for reviewing notifications from schools
and a cost of $10,632 for initial
inspector training (refer to the economic
background document to this proposed
rule for more information). Thus,
Executive Order 13132 does not apply
to this proposed rule.
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 9, 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.’’
EPA has concluded that this proposed
rule may have tribal implications to the
extent that qualifying academic
institutions with laboratories affiliated
with tribal lands could be affected.
However, this proposed rule will
neither impose substantial direct
compliance costs on tribal governments
or preempt tribal law.
EPA did not consult directly with
representatives of Tribal governments
early in the process of developing this
proposal. However, EPA did conduct an
extensive outreach process with
industry. Thus, EPA believes it has
captured concerns that also would have
been expressed by representatives of
Tribal governmental. EPA solicits
additional comments on this proposed
rule from Tribal officials.
G. Executive Order 13045: Protection of
Children From Environmental Health
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:
(1) is determined to be ‘‘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
29747
preferable to other potentially effective
and reasonably feasible alternatives
being considered by the Agency.
This proposed rule is not subject to
the Executive Order because it is not
economically significant as defined in
Executive Order 12866, and because the
Agency does not have reason to believe
the environmental health or safety risks
addressed by this action present a
disproportionate risk to children.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Usage
This rule is not a ‘‘significant energy
action’’ as defined in Executive Order
13211, ‘‘Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Usage’’ (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.
I. National Technology Transfer
Advancement 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. This
proposed rule does not involve
technical standards. Therefore, EPA is
not considering the use of any voluntary
consensus standards.
Attachment A
TABLE 1.—COMPARISON OF CURRENT AND PROPOSED REGULATIONS FOR LABORATORIES
Proposed regulations subpart K
name of accumulation area ...............................
materials regulated ............................................
satellite accumulation area ...............................
hazardous wastes & acute hazardous wastes
hazardous waste determination .........................
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Current regulations § 262.34(c)
must make hazardous waste determination: ...
• in satellite accumulation area ................
• when hazardous waste is generated ....
maximum accumulation time in lab ...................
none (unless 55 gallons hazardous waste or 1
quart acute hazardous waste is exceeded).
laboratory.
unwanted materials & reactive acutely hazardous unwanted materials.
RCRA-trained individual must make hazardous waste determination:
• in laboratory, before unwanted material
is removed, or
• within 4 days of arriving at on-site central accumulation area or on-site TSDF.
six months (unless 55 gallons hazardous
waste or 1 quart reactive acutely hazardous
waste is exceeded).
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TABLE 1.—COMPARISON OF CURRENT AND PROPOSED REGULATIONS FOR LABORATORIES—Continued
Current regulations § 262.34(c)
Proposed regulations subpart K
maximum accumulation volume ........................
• 55 gallons of hazardous waste ....................
• 1 quart of acute hazardous waste ................
maximum number of days that lab can exceed
maximum volume.
labeling on container .........................................
3 days ...............................................................
• 55 gallons of unwanted material
• 1 quart of reactive acutely hazardous unwanted material.
10 calendar days.
information associated with container ...............
none ..................................................................
training of laboratory personnel .........................
none ..................................................................
container management ......................................
• containers must be in good condition ..........
• hazardous waste must be compatible with
container.
• containers must be kept closed except
when adding or removing waste.
Laboratory Management Plan ...........................
none ..................................................................
incentives for non-mandatory laboratory cleanouts (limited to 1x per 12-month period per
lab).
none ..................................................................
notification ..........................................................
notification to indicate generator status ...........
List of Subjects
§ 261.5 Special requirements for
hazardous waste generated by conditionally
exempt small quantity generators.
40 CFR Part 261
‘‘hazardous waste’’ or ‘‘other words that identify the contents of the container’’.
Environmental protection, Exports,
Hazardous materials transportation,
Hazardous waste, Imports, Labeling,
Packaging and containers, Reporting
and recordkeeping requirements.
*
*
*
*
(c) * * *
(7) Is generated solely as a result of a
laboratory clean-out conducted at a
college or university pursuant to
§ 262.213. For purposes of this
provision, the term college or university
shall have the meaning as defined in
§ 262.200 of part 262.
*
*
*
*
*
Dated: May 12, 2006.
Stephen L. Johnson,
Administrator.
PART 262—STANDARDS APPLICABLE
TO GENERATORS OF HAZARDOUS
WASTE
Environmental protection, Hazardous
waste, Recycling, Reporting and
recordkeeping requirements.
40 CFR Part 262
For the reasons set out in the
preamble, parts 261 and 262 of title 40,
Chapter I of the Code of Federal
Regulations are proposed to be amended
as follows:
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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.
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Jkt 208001
3. The authority citation for part 262
continues to read as follows:
Authority: 42 U.S.C. 6906, 6912, 6922–
6925, 6937, and 6938.
Subpart A—General
PART 261—IDENTIFICATION AND
LISTING OF HAZARDOUS WASTE
2. Section 261.5 is amended by
adding paragraph (c)(7) to read as
follows:
*
4. Section 262.10 is amended by
adding paragraph (l) to read as follows:
§ 262.10
Purpose, scope, and applicability.
*
*
*
*
*
(l) The laboratories located at a
college or university that chooses to be
subject to the requirements of subpart K
of this part are not subject to the
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• ‘‘unwanted material’’ and
• sufficient information to alert emergency responders to hazards of contents.
• sufficient information to allow a RCRAtrained individual to make a hazardous
waste determination.
• date accumulation begins.
• training for laboratory workers commensurate with duties.
• instruction for students.
• containers must be properly managed to assure safe storage of unwanted materials to
prevent spillage, or adverse chemical reactions or other dangerous situations that may
result in harm to laboratory workers or the
environment.
• containers must be in good condition.
• unwanted material must be compatible
with container.
required to describe specifics of implementing
performance-based standards.
• do not have to count hazardous waste generated during lab clean-out toward generator status.
• have 30 calendar days to complete cleanout.
notification to indicate decision to exercise option to comply with part 262 subpart K.
requirements of § 262.11 or § 262.34(c),
except as provided in subpart K. For
purposes of this provision, the terms
‘‘laboratory’’ and ‘‘college’’ and
‘‘university’’ shall have the meaning as
defined in § 262.200 of subpart K of this
part.
5. Part 262 is amended by adding
subpart K to read as follows:
Subpart K—Alternative Requirements
for Hazardous Waste Determination
and Accumulation of Unwanted
Material for Laboratories Located at
Colleges/Universities
Sec.
262.200 Definitions for this subpart.
262.201 Applicability of this subpart.
262.202 This subpart is optional.
262.203 How a college or university
indicates it will be subject to the
requirements of this subpart.
262.204 How a college or university
indicates it will withdraw from the
requirements of this subpart.
262.205 Summary of the requirements of
this subpart.
262.206 Labeling and management
standards for containers of unwanted
material in the laboratory.
262.207 Training and instruction.
262.208 When must containers of unwanted
material be removed from the laboratory?
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262.209 Where and when to make the
hazardous waste determination and
where to send containers of unwanted
material upon removal from the
laboratory.
262.210 Making the hazardous waste
determination in the laboratory before
the unwanted material is removed from
the laboratory.
262.211 Making the hazardous waste
determination at an on-site central
accumulation area.
262.212 Making the hazardous waste
determination at an on-site interim status
or permitted treatment, storage or
disposal facility.
262.213 Laboratory clean-outs.
262.214 Laboratory management plan.
262.215 Unwanted material that is not solid
or hazardous waste.
262.216 Non-laboratory hazardous waste
generated at a college/university.
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§ 262.200
Definitions for this subpart.
The following definitions apply to
this subpart:
Central Accumulation Area means an
on-site hazardous waste accumulation
area subject to either § 262.34(a) of this
Part (large quantity generators) or
§ 262.34(d) of this Part (small quantity
generators). A central accumulation area
at a college or university that chooses to
be subject to this subpart must also
comply with § 262.211 when
accumulating unwanted material.
College/University means a private or
public, post-secondary, degree-granting,
academic institution, that is accredited
by an accrediting agency listed annually
by the U.S. Department of Education.
Laboratory means an area within a
college or university where relatively
small quantities of chemicals and other
substances are used on a nonproduction basis for teaching or
research purposes and are stored and
used in containers that are easily
manipulated by one person. An area
where the same hazardous waste is
routinely generated, such as photo
processing, is not a laboratory.
Laboratory Clean-out means an
evaluation of the inventory of chemicals
and other materials in a laboratory that
are no longer needed or that have
expired and the subsequent removal of
those chemicals or other unwanted
material from the laboratory. A cleanout may occur for several reasons. It
may be on a routine basis (e.g., at the
end of a semester or academic year) or
as a result of a renovation, relocation, or
change in laboratory supervisor/
occupant. A regularly scheduled
removal of unwanted material as
required by § 262.208 does not qualify
as a laboratory clean-out.
Laboratory Worker means a person
who handles chemicals and/or
unwanted material in a laboratory and
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may include, but is not limited to
faculty, staff, post-doctoral fellows,
interns, researchers, technicians,
supervisors/managers, and principal
investigators. A person does not need to
be paid or otherwise compensated for
his/her work in the laboratory to be
considered a laboratory worker.
Undergraduate and graduate students in
a supervised classroom setting are not
laboratory workers.
RCRA-Trained Individual means a
person who has completed the
applicable RCRA training requirements
of § 265.16 for large quantity generators,
or § 262.34(d)(5)(iii) for small quantity
generators. A RCRA-trained individual
may be an employee of the college/
university or may be a contractor or
vendor.
Reactive Acutely Hazardous
Unwanted Material means an unwanted
material that is one of the acutely
hazardous commercial chemical
products listed in § 261.33(e) for
reactivity and toxicity.
Unwanted Material means any
chemical, mixtures of chemicals,
products of experiments or other
material from a laboratory that are no
longer needed, wanted or usable in the
laboratory and that are destined for
hazardous waste determination by a
RCRA-trained individual. Unwanted
material includes reactive acutely
hazardous unwanted materials.
Unwanted material includes material
that may eventually be determined not
to be solid waste pursuant to § 261.2 or
a hazardous waste, pursuant to § 261.3.
§ 262.201
Applicability of this subpart.
This subpart provides optional,
alternative requirements to the
requirements in §§ 262.11 and 262.34(c)
for the hazardous waste determination
and accumulation of hazardous waste in
laboratories located at colleges and
universities that choose to be subject to
this subpart and that complete the
notification requirements of § 262.203.
This subpart does not apply to
laboratories at colleges or universities
that are conditionally exempt small
quantity generators (CESQGs) under
§ 261.5.
§ 262.202
This subpart is optional.
Colleges and universities have the
option of complying with this subpart
with respect to its laboratories, as an
alternative to the requirements of
§§ 262.11 and 262.34(c).
§ 262.203 How a college or university
indicates it will be subject to the
requirements of this subpart.
(a) A college or university must notify
the appropriate EPA Regional
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29749
Administrator in writing that it is
electing to be subject to the
requirements of this Subpart for all
laboratories located at the college or
university under the same EPA
Identification Number. In the
notification, a college or university must
include:
(1) The name, address and EPA
Identification number of the college or
university
(2) Contact information for an
appropriate representative of the college
or university, and
(3) The date on which the laboratories
at the college or university will become
subject to this subpart.
(b) A college or university must keep
a copy of the notification on file at the
college or university while its
laboratories are subject to this subpart.
§ 262.204 How a college or university
indicates it will withdraw from the
requirements of this subpart.
(a) A college or university must notify
the appropriate EPA Regional
Administrator in writing that it is
electing to no longer be subject to the
requirements of this subpart for all
laboratories located at the college or
university under the same EPA
Identification Number. In the
withdrawal notification, a college or
university must include:
(1) The name, address and EPA
Identification number of the college or
university
(2) Contact information for an
appropriate representative of the college
or university, and
(3) The date on which the laboratories
at the college or university will no
longer be subject to this subpart.
(b) A college or university must keep
a copy of the withdrawal notice on file
at the college or university for three
years from the date of the letter.
§ 262.205 Summary of the requirements of
this subpart.
This subpart provides optional,
alternative requirements for the
hazardous waste determination and
accumulation of unwanted material in
laboratories located at colleges and
universities that choose to be subject to
this subpart and that complete the
notification requirements of § 262.203.
Under this subpart, a participating
college or university must manage the
unwanted material in its laboratories in
accordance with §§ 262.206–262.208
(container labeling, container
management standards, training/
instruction, regular removal from the
laboratory) from the point of generation
of unwanted materials in the laboratory.
For purposes of this subpart, the
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hazardous waste determination
pursuant to § 262.11 for unwanted
material must be made by a RCRAtrained individual in the laboratory
before the unwanted material is
removed from the laboratory, or within
4 calendar days of arriving at an on-site
central accumulation area, or on-site
treatment, storage or disposal facility in
accordance with the applicable
provisions of §§ 262.210, 262.211, or
262.212. A college or university that
chooses to be subject to subpart K is not
required to have interim status or a
permit for the accumulation of
hazardous waste in the laboratory,
provided the laboratories comply with
the provisions of this subpart and the
college or university has a Laboratory
Management Plan (LMP) in accordance
with § 262.214 that describes how the
college or university laboratories will
comply with the requirements of
subpart K.
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§ 262.206 Labeling and management
standards for containers of unwanted
material in the laboratory.
A college or university must manage
containers of unwanted material while
in the laboratory in accordance with the
requirements in this section.
(a) Labeling: Label unwanted material
as follows:
(1) The following information must be
affixed to or physically accompany the
container:
(i) The words ‘‘unwanted material’’
and
(ii) Sufficient information to alert
emergency responders to the hazards or
the contents of the container.
(2) The following information must be
associated with the container:
(i) The date that unwanted material
first began accumulating in the
container.
(ii) Information sufficient to allow a
RCRA-trained individual to properly
identify whether an unwanted material
is a solid and hazardous waste and to
assign a proper hazardous waste code(s),
pursuant to § 262.11. For example, the
following information may be associated
with the container:
(A) The name and/or description of
the chemical contents or composition of
the unwanted material, or, if known, the
product of the chemical reaction.
(B) Whether the unwanted material
has been used or is unused
(C) A description of the manner in
which the chemical was processed, if
applicable.
(b) Management of Containers in the
Laboratory: A college or university must
properly manage containers to assure
safe storage of the unwanted material, to
prevent leaks, spills, emissions to the
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air, adverse chemical reactions, and to
prevent dangerous situations that may
result in harm to human health or the
environment. Proper container
management must include the
following:
(1) Containers are maintained and
kept in good condition and damaged
containers are replaced.
(2) Containers are compatible with
their contents to avoid reactions
between the contents and the container;
and are made of, or lined with, material
that is compatible with the unwanted
material so that the container’s integrity
is not impaired.
§ 262.207
Training and instruction.
A college or university must provide
training or instruction to all individuals
working in a laboratory at that college
or university, as follows:
(a) For laboratory workers: Training
for laboratory workers must be
commensurate with their duties so they
understand the requirements in this
subpart and implement them such that
it ensures the laboratories’ compliance
with the requirements of this subpart.
(1) A college or university that is a
large quantity generator must maintain
training records for laboratory workers:
(i) That are sufficient to determine
whether laboratory workers have been
trained.
(ii) For the durations specified in
§ 265.16(e).
(2) [Reserved]
(b) For students: Students in a
laboratory where unwanted material is
generated must receive instruction
relevant to their activities in the
laboratory. For example, instruction
may include proper container labeling,
collection procedures for unwanted
material, and emergency response
procedures.
(c) For on-site transportation: Only
RCRA-trained individuals may transport
unwanted material and hazardous waste
on-site.
(d) For hazardous waste
determination: Only RCRA-trained
individuals may make hazardous waste
determinations, pursuant to § 262.11, for
unwanted material
(e) A college or university can provide
training and instruction for laboratory
workers and students in a variety of
ways, including, but not limited to:
(1) Instruction by the professor/
manager before or during an
experiment.
(2) Formal classroom training.
(3) Electronic/written training.
(4) On-the-job training.
(5) Written or oral exams.
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§ 262.208 When must containers of
unwanted material be removed from the
laboratory?
(a) A college or university must
remove all containers of unwanted
material and acutely reactive unwanted
material from each laboratory on a
regular interval, not to exceed 6 months.
The college or university must specify
in its Laboratory Management Plan a
regular interval for removal of unwanted
material and acutely reactive unwanted
material.
(b) If a laboratory accumulates more
than 55 gallons of unwanted material
(including reactive acutely hazardous
unwanted material) before the regularly
scheduled removal, the college or
university must ensure that all
containers of unwanted material
(including reactive acutely hazardous
unwanted material) are:
(1) Labeled with the date that 55
gallons is exceeded; and
(2) Removed from the laboratory
within 10 calendar days of the date that
55 gallons was exceeded, or at the next
regularly scheduled removal, whichever
comes first.
(c) If a laboratory accumulates more
than 1 quart of reactive acutely
hazardous unwanted material before the
regularly scheduled removal, then the
college or university must ensure that
all containers of reactive acutely
hazardous unwanted material are:
(1) Labeled with the date that 1 quart
is exceeded; and
(2) Removed from the laboratory
within 10 calendar days of the date that
1 quart was exceeded, or at the next
regularly scheduled removal, whichever
comes first.
§ 262.209 Where and when to make the
hazardous waste determination and where
to send containers of unwanted material
upon removal from the laboratory.
A college or university must ensure
that a RCRA-trained individual makes a
hazardous waste determination,
pursuant to § 262.11, for unwanted
material in one of the following areas:
(a) In the laboratory before the
unwanted material is removed from the
laboratory, in accordance with
§ 262.210, or
(b) Within 4 calendar days of arriving
at an on-site central accumulation area,
in accordance with § 262.211, or
(c) Within 4 calendar days of arriving
at an on-site treatment, storage or
disposal facility, in accordance with
§ 262.212.
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§ 262.210 Making the hazardous waste
determination in the laboratory before the
unwanted material is removed from the
laboratory.
If a college or university makes the
hazardous waste determination,
pursuant to § 262.11, for unwanted
material in the laboratory before the
unwanted material is removed from the
laboratory, it must comply with the
following:
(a) A RCRA-trained individual must
determine, pursuant to § 262.11, if the
unwanted material is a hazardous waste
before the unwanted material is
removed from the laboratory.
(b) If an unwanted material is a
hazardous waste, the college or
university must place the appropriate
hazardous waste code(s) and the words
‘‘hazardous waste’’ on the container
label that is affixed to or physically
accompanies the container, before the
hazardous waste may be transferred to
an on-site central accumulation area, an
on-site interim status or permitted
treatment, storage or disposal facility, or
transported off-site to a designated
facility.
(c) If an unwanted material is a
hazardous waste, the college or
university must count the hazardous
waste toward the college or university’s
generator status, pursuant to § 261.5.
(d) An unwanted material that is a
hazardous waste, is subject to all
applicable hazardous waste regulations
when it is removed from the laboratory.
(e) Unwanted material and hazardous
waste that is transferred from the
laboratory to an on-site central
accumulation area or on-site interim
status or permitted treatment, storage or
disposal facility must be accompanied
by a RCRA-trained individual.
rwilkins on PROD1PC63 with PROPOSAL_2
§ 262.211 Making the hazardous waste
determination at an on-site central
accumulation area.
If a college or university makes the
hazardous waste determination,
pursuant to § 262.11, for unwanted
material at an on-site central
accumulation area, it must comply with
the following:
(a) Unwanted material and hazardous
waste that is transferred from the
laboratory to an on-site central
accumulation area must be
accompanied by a RCRA-trained
individual.
(b) Unwanted material must be taken
directly from the laboratory(ies) to the
on-site central accumulation area.
(c) A RCRA-trained individual must
determine, pursuant to § 262.11, if the
unwanted material is a hazardous waste
within 4 calendar days of arriving at the
on-site central accumulation area.
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Jkt 208001
(d) The unwanted material becomes
subject to the generator accumulation
regulations of § 262.34(a) for large
quantity generators or § 262.34(d) for
small quantity generators as soon as it
arrives in the central accumulation area,
except for the ‘‘hazardous waste’’
labeling requirements of § 262.34(a)(3).
(e) If the unwanted material is a
hazardous waste, the college or
university must place the appropriate
hazardous waste code(s) and the words
‘‘hazardous waste’’ on the container
label that is affixed to the container,
before the hazardous waste may be
transferred to another on-site central
accumulation area or on-site interim
status or permitted treatment, storage or
disposal facility, or transported off-site
to a designated facility.
(f) If the unwanted material is a
hazardous waste, the college or
university must count the hazardous
waste toward the college or university’s
generator status, pursuant to § 261.5 and
is subject to all applicable hazardous
waste regulations.
§ 262.212 Making the hazardous waste
determination at an on-site interim status or
permitted treatment, storage or disposal
facility.
If a college or university makes the
hazardous waste determination,
pursuant to § 262.11, for unwanted
material at an on-site treatment, storage
or disposal facility, it must comply with
the following:
(a) Unwanted material and hazardous
waste that is transferred from the
laboratory to an on-site interim status or
permitted treatment, storage or disposal
facility must be accompanied by a
RCRA-trained individual.
(b) Unwanted material must be taken
directly from the laboratory(ies) to the
on-site interim status or permitted
treatment, storage or disposal facility.
(c) A RCRA-trained individual must
determine, pursuant to § 262.11, if the
unwanted material is a hazardous waste
within 4 calendar days of arriving at an
on-site interim status/permitted
treatment, storage or disposal facility.
(d) The unwanted material becomes
subject to the terms of the college or
university’s hazardous waste permit or
interim status as soon as it arrives in the
on-site treatment, storage or disposal
facility.
(e) If the unwanted material is a
hazardous waste, the college or
university must place the appropriate
hazardous waste code(s) and the words
‘‘hazardous waste’’ on the container
label that is affixed to or physically
accompanies the container, before the
hazardous waste may be transferred to
another interim status or permitted
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Fmt 4701
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29751
treatment, storage or disposal facility or
transported off-site to a designated
facility.
(f) If the unwanted material is a
hazardous waste, the college or
university must count the hazardous
waste toward the college or university’s
generator status, pursuant to § 261.5 and
is subject to all applicable hazardous
waste regulations.
§ 262.213
Laboratory clean-outs.
(a) One time per 12 month period per
laboratory, a college or university may
opt to conduct a laboratory clean-out
that is subject to all the applicable
requirements of this subpart, except
that:
(1) If the volume of unwanted
material in the laboratory exceeds 55
gallons (or 1 quart of reactive acutely
hazardous unwanted material), the
college or university is not required to
remove all unwanted materials from the
laboratory within 10 calendar days of
exceeding 55 gallons (or 1 quart of
reactive acutely hazardous unwanted
material), as required by § 262.208.
Instead, the college or university must
remove all unwanted materials from the
laboratory within 30 calendar days from
the start of the laboratory clean-out,
including those already in the
laboratory prior to the beginning of the
laboratory clean-out, and
(2) A college or university is not
required to count hazardous waste
generated solely during the laboratory
clean-out toward its hazardous waste
generator status, pursuant to § 261.5(c)
and (d). An unwanted material that is
generated prior to the beginning of the
laboratory clean-out and is still in the
laboratory at the time the laboratory
clean-out commences, must be counted
toward hazardous waste generator
status, pursuant to § 261.5(c) and (d), if
it is determined to be hazardous waste,
and
(3) A college or university must
document the activities of the laboratory
clean-out. The documentation must, at a
minimum, identify the laboratory being
cleaned out, the date the laboratory
clean-out begins and ends, and the
volume of hazardous waste generated
during the laboratory clean-out. The
college or university must maintain the
records for a period of three years from
the date the clean-out ends.
(b) For all other laboratory clean-outs
conducted during the same 12-month
period, a college or university is subject
to all the applicable requirements of this
subpart, including, but not limited to:
(1) If the volume of unwanted
material in the laboratory exceeds 55
gallons (or 1 quart of reactive acutely
hazardous unwanted material), the
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college or university is required to
remove all unwanted materials from the
laboratory within 10 calendar days of
exceeding 55 gallons (or 1 quart of
reactive acutely hazardous unwanted
material), as required by § 262.208, and
(2) A college or university must count
hazardous waste generated during the
laboratory clean-out toward its
hazardous waste generator status,
pursuant to § 261.5(c) and (d).
§ 262.214
Laboratory management plan.
rwilkins on PROD1PC63 with PROPOSAL_2
option 1 for paragraph (a):
(a) A college or university must
develop, implement, and retain on-site
a Laboratory Management Plan, or
revise an existing plan, that describes
how the college/university will comply
with paragraphs (a)(1) through (9) of this
section:
option 2 for paragraph (a):
(a) A college or university must
develop, implement, and retain on-site
a Laboratory Management Plan, or
revise an existing plan, that describes
how the college/university will comply
with paragraphs (a)(1) through (9) of this
section. The college or university must
comply with the specific provisions
contained in its Laboratory Management
Plan.
(1) Container management in
accordance with § 262.206.
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Jkt 208001
(2) Container labeling in accordance
with § 262.206, including identifying
where the labeling information will be
located.
(3) Training for laboratory workers
commensurate with their duties in
accordance with § 262.207(a).
(4) Instruction for students in
accordance with § 262.207(b).
(5) Training to ensure safe on-site
movement of unwanted material and
hazardous waste in accordance with
§ 262.207(c).
(6) Develop a regular schedule for
identifying and removing unwanted
material from laboratories in accordance
with § 262.208.
(7) Make hazardous waste
determinations for unwanted material,
in accordance with § 262.209.
(8) Conduct laboratory clean-outs in
accordance with § 262.213, if the college
or university elects to conduct
laboratory clean-outs.
(9) Emergency prevention,
notification and response procedures
appropriate to the hazards in the
laboratory.
(b) A college or university must make
its Laboratory Management Plan
available to laboratory workers,
students, or others at the college or
university who request it.
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(c) A college or university must
review and revise its Laboratory
Management Plan, as needed.
§ 262.215 Unwanted material that is not
solid or hazardous waste.
(a) If a RCRA-trained individual
determines that an unwanted material
does not meet the definition of solid
waste in § 261.2, it is no longer subject
to this subpart or to RCRA Subtitle C.
(b) If a RCRA-trained individual
determines that an unwanted material
does not meet the definition of
hazardous waste in § 261.3, it is no
longer subject to this subpart or to
RCRA Subtitle C, but may be subject to
RCRA Subtitle D.
§ 262.216 Non-laboratory hazardous waste
generated at a college/university.
A college or university that generates
hazardous waste outside of a laboratory
is not eligible to manage that hazardous
waste under subpart K and remains
subject to the generator requirements of
§§ 262.11, 262.34(c) (if the hazardous
waste is managed in a satellite
accumulation area) and all other
applicable generator requirements of 40
CFR part 262, with respect to that
hazardous waste.
[FR Doc. 06–4654 Filed 5–22–06; 8:45 am]
BILLING CODE 6560–50–P
E:\FR\FM\23MYP2.SGM
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Agencies
[Federal Register Volume 71, Number 99 (Tuesday, May 23, 2006)]
[Proposed Rules]
[Pages 29712-29752]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 06-4654]
[[Page 29711]]
-----------------------------------------------------------------------
Part II
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Parts 261 and 262
Standards Applicable to Generators of Hazardous Waste; Subpart K--
Standards Applicable to Academic Laboratories; Proposed Rule
Federal Register / Vol. 71, No. 99 / Tuesday, May 23, 2006 / Proposed
Rules
[[Page 29712]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 261 and 262
[EPA-HQ-RCRA-2003-0012; FRL-8171-5]
RIN 2050-AG18
Standards Applicable to Generators of Hazardous Waste; Subpart
K--Standards Applicable to Academic Laboratories
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: Today, EPA is proposing alternative generator requirements
applicable to college and university laboratories as defined in this
proposed rule. The proposal provides a flexible and protective set of
regulations that address the specific nature of hazardous waste
generation in college and university laboratories. The flexibility in
today's proposed rule will allow colleges and universities the
discretion to determine the most appropriate and effective method of
compliance with today's proposed requirements. This preamble will refer
to this flexible approach as a ``performance-based'' approach.
Additionally, this proposed rule grants colleges and universities the
choice to manage their hazardous wastes in accordance with today's
alternative set of regulations or remain subject to the existing
generator regulations.
DATES: EPA will accept public comments on this proposed rule until
August 21, 2006.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
RCRA 2003-0012 or EPA-2050 AG 18 RCRA-2003-0012, by one of the
following methods:
https://www.regulations.gov: Follow the on-line
instructions for submitting comments.
E-mail: Comments may be sent by electronic mail (e-mail)
to [``RCRA-docket@epamail.epa.gov''], Attention Docket ID No. EPA-HQ-
RCRA-2003-0012 or EPA-2050 AG 18 RCRA-2003-0012.
Fax: Fax comments to: 202-566-0270, Attention Docket ID.
No. EPA-HQ-RCRA-2003-0012 or EPA-2050 AG 18 RCRA-2003-0012.
Mail: Send comments to: OSWER Docket, EPA Docket Center
Mailcode: 5305T, Environmental Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460, Attention Docket ID Number EPA-HQ-
RCRA-2003-0012 or EPA-2050 AG 18 RCRA-2003-0012. In addition, please
mail a copy of your comments on the information collection provisions
to the Office of Information and Regulatory Affairs, Office of
Management and Budget (OMB), Attn: Desk Officer for EPA, 725 17th
Street NW., Washington, DC 20503.
Hand Delivery: Deliver comments to: Environmental
Protection Agency, EPA Docket Center, Room B102, 1301 Constitution
Avenue, NW., Washington, DC, Attention Docket ID Number EPA-HQ-RCRA-
2003-0012 or EPA-2050 AG 18 RCRA-2003-0012. Such deliveries are only
accepted during the Docket's normal hours of operation, and special
arrangements should be made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-RCRA-
2003-0012 or EPA-2050 AG 18 RCRA-2003-0012. EPA's policy is that all
comments received will be included in the public docket without change
and may be made available on-line at https://www.regulations.gov,
including any personal information provided, unless the comment
includes information claimed to be Confidential Business Information
(CBI) or other information whose disclosure is restricted by statute.
Do not submit information that you consider to be CBI or otherwise
protected through https://www.regulations.gov or e-mail. The https://
www.regulations.gov Web site is an ``anonymous access'' system, which
means EPA will not know your identity or contact information unless you
provide it in the body of your comment. If you send an e-mail comment
directly to EPA without going through https://www.regulations.gov, your
e-mail address will be automatically captured and included as part of
the comment that is placed in the public docket and made available on
the Internet. If you submit an electronic comment, EPA recommends that
you include your name and other contact information in the body of your
comment and with any disk or CD-ROM you submit. If EPA cannot read your
comment due to technical difficulties and cannot contact you for
clarification, EPA may not be able to consider your comment. Electronic
files should avoid the use of special characters, any form of
encryption, and be free of any defects or viruses. For additional
information about EPA's public docket, visit the EPA Docket Center
homepage at https://www.epa.gov/epahome/dockets/htm. For additional
instructions for submitting comment, comment go to section B of the
SUPPLEMENTARY INFORMATION section of this document.
Docket: All documents in the docket are listed in the https://
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the at the OSWER
Docket in the EPA Docket Center (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)
566-1774, and the telephone number for the OSWER Docket is (202) 566-
0270. Copies cost $0.15/page.
FOR FURTHER INFORMATION CONTACT: For general information, contact EPA's
Web site at https://www.epa.gov/epaoswer/osw/ comments. htm. For
general information regarding lab wastes for educational institutions,
contact https://www.epa.gov/epaoswer/osw/specials/ labwaste/index.
html. For further information regarding specific aspects of this
notice, contact Patricia Mercer, Hazardous Waste Identification
Division, Office of Solid Waste (5304W), U.S. Environmental Protection
Agency, 1200 Pennsylvania Avenue, Washington, DC 20460; (703) 308-8408;
fax number (703) 308-0514; e-mail address: mercer.patricia@epa.gov.
SUPPLEMENTARY INFORMATION:
General Information
A. Entities Potentially Affected by This Proposed Rule
Entities potentially affected by this proposed action are
generators of unwanted materials, as defined in this proposal, from
college and university laboratories. College and university
laboratories, as defined under this proposal, include laboratories
associated with a private or public, post-secondary, degree-granting,
academic institution that is accredited by an accrediting agency listed
annually by the U.S. Department of Education. Only those colleges and
universities which have laboratories on their campuses would be covered
by this alternate approach; laboratories not located at colleges or
universities would not be covered. This proposed action is optional in
that colleges and universities may elect to have their laboratories
remain regulated under current RCRA generator regulations as set forth
in 40 CFR 262.11 and 262.34(c), or may choose to manage
[[Page 29713]]
their hazardous wastes according to this alternative regulatory
approach. (In RCRA authorized states, today's proposed action would be
an option once it has been adopted by the state in which the college or
university resides.) To determine whether a college or university
laboratory is covered by this action, interested parties should examine
40 CFR part 262 subpart K carefully. If there are questions regarding
the applicability of the proposed rule to a particular entity, consult
the person listed in the section of this preamble entitled FOR FURTHER
INFORMATION CONTACT.
B. What To Consider When Preparing Comments for EPA
1. Submitting CBI. Do not submit this information to EPA through
https://www.regulations.gov or e-mail. Clearly mark part of all of the
information that you claim to be CBI. For CBI information in a disk or
CD ROM that you mail to EPA, mark the outside of the disk or CD ROM as
CBI and then identify electronically within the disk or CD ROM the
specific information that is claimed as CBI. In addition to one
complete version of the comment that includes information claimed as
CBI, a copy of the comment that does not contain the information
claimed as CBI must be submitted for inclusion in the public docket.
Information so marked will not be disclosed, except in accordance with
procedures set forth in 40 CFR part 2.
2. Tips for Preparing Your Comments. When submitting comments,
remember to:
Identify the rulemaking by docket number and other
identifying information (subject heading, Federal Register date and
page number).
Follow directions--The Agency may ask for commenters to
respond to specific questions or organize comments by referencing a
Code of Federal Regulations (CFR) part or section number.
Explain why you agree or disagree; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If estimating potential burden or costs, explain methods
used to arrive at the estimate in sufficient detail to allow for it to
be reproduced.
Provide specific examples to illustrate any concerns and
suggest alternatives.
Make sure to submit comments by the comment period
deadline identified above.
List of Acronyms
--------------------------------------------------------------------------------------------------------------------------------------------------------
--------------------------------------------------------------------------------------------------------------------------------------------------------
ACE......................................... American Council on Education.
APA......................................... Administrative Procedures Act.
APPA........................................ Association of Higher Education Facilities Officers.
BR.......................................... Biennial Report.
C2E2........................................ Campus Consortium for Environmental Excellence.
CAA......................................... Central Accumulation Area.
CAS......................................... Chemical Abstract Service.
CESQG....................................... Conditionally Exempt Small Quantity Generator.
CFR......................................... Code of Federal Regulations.
CSHEMA...................................... Campus Safety, Health and Environmental Management Association.
EH&S........................................ Environmental Health and Safety.
EMP......................................... Environmental Management Plan.
EMS......................................... Environmental Management System.
HHMI........................................ Howard Hughes Medical Institute.
HSWA........................................ Hazardous and Solid Waste Amendments of 1984.
ICR......................................... Information Collection Request.
LDR......................................... Land Disposal Restrictions.
LMP......................................... Laboratory Management Plan.
LQG......................................... Large Quantity Generator.
NACUBO...................................... National Association of College and University Business Officers.
NGO......................................... Non-Governmental Organization.
NTTAA....................................... National Technology Transfer Advancement Act.
OMB......................................... Office of Management and Budget.
PRA......................................... Paperwork Reduction Act.
Project XL.................................. eXcellence and Leadership.
RCRA........................................ Resource Conservation and Recovery Act.
RFA......................................... Regulatory Flexibility Act.
SAA......................................... Satellite Accumulation Area.
SIC......................................... Standard Industrial Code.
SQG......................................... Small Quantity Generator.
SWDA........................................ Solid Waste Disposal Act.
TRI......................................... Toxics Release Inventory.
TSDF........................................ Treatment, Storage or Disposal Facility.
UMRA........................................ Unfunded Mandates Reform Act.
--------------------------------------------------------------------------------------------------------------------------------------------------------
Preamble Outline
I. Statutory Authority
II. Background
A. Intent of Today's Proposed Rule
B. History
C. Agency's College and University Initiatives
D. Overview of College and University Laboratory Operations
1. Generation of Hazardous Wastes--Types and Quantities
a. Data Sources
b. Summary of College and University Hazardous Waste Generation
Activities
i. Summary of College and University Laboratory Hazardous Waste
Generation
ii. Summary of Type and Volume of Laboratory Hazardous Waste
Generation at College and University LQGs and SQGs
2. Summary of Current RCRA Generator Regulations
a. Who May Determine Whether a Waste Is Hazardous?
b. Generators That Treat Hazardous Waste On-Site
c. Land Disposal Restrictions
d. Applicability of Today's Proposal to Conditionally Exempt
Small Quantity Generators (CESQGs)
III. Overview of Today's Proposed Rule
IV. Detailed Discussion of Today's Proposed Rule
A. Discussion of Proposed Definitions
B. Scope of Laboratories at Colleges and Universities Covered
Under This Proposed Rule
[[Page 29714]]
1. Laboratories in Colleges and Universities
2. Alternative Regulations
3. Notification
C. Specific Requirements Under the Alternative Regulations
1. Making the Hazardous Waste Determination
2. Container Standards
3. Labeling Standards
4. Training and Instruction Requirements
5. Removal Frequency of Unwanted Materials
a. Reactive Acutely Hazardous Unwanted Materials
b. Other Unwanted Materials That Are Potentially Acutely
Hazardous Waste
6. Where and When To Make the Hazardous Waste Determination--
Transferring Unwanted Materials or Hazardous Wastes From the
Laboratory to an On-Site CAA or On-Site TSDF
7. Making the Hazardous Waste Determination in the Laboratory
8. Making the Hazardous Waste Determination at an On-Site
Central Accumulation Area
9. Making the Hazardous Waste Determination at an On-Site TSDF
10. Laboratory Clean-Outs
11. Laboratory Management Plan
D. Recordkeeping
E. Implementation and Enforcement
V. State Authorization
A. Applicability of Rules in Authorized States
B. Effect on State Authorization
VI. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
1. Economic Analysis
2. Summary of Proposed Rule Findings: Costs, Economic Impacts,
Benefits
B. Paperwork Reduction Act (ICR)
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 Usage
I. National Technology Transfer Advancement Act Attachment A
I. Statutory Authority
These regulations are proposed under the authority of Sections
2002, 3001, 3002, and 3004 of the Solid Waste Disposal Act (SWDA) of
1970, as amended by the Resource Conservation and Recovery Act (RCRA)
of 1976, as amended by the Hazardous and Solid Waste Amendments of 1984
(HSWA), 42 U.S.C. 6921, 6922, 6923, and 6924.
II. Background
A. Intent of Today's Proposed Rule
The intent of today's proposed rule is to establish an alternative
set of generator requirements for college and university laboratories
that is better suited to their specific circumstances, and promotes
environmental protection and public health through safer management of
laboratory hazardous wastes. While the Agency has been investigating
these issues for a number of years, starting in 2002, EPA conducted a
series of outreach activities to generators of hazardous waste with
laboratories to obtain information regarding the differences between
how hazardous waste is generated and managed at college and university
laboratory operations as compared with production operations of
industrial generators and other non-college or university laboratory
generators. The information collected by the Agency indicates that
college and university laboratory operations differ from both
industrial laboratories and industrial production facilities that
generate hazardous waste, warranting development of an alternative set
of regulations for college and university laboratories.
Relative to industrial production facilities, laboratories
generally have a large number of points of generation (i.e. points
where waste is originally generated) such as multiple laboratory
benchtops within a single laboratory and laboratories located at
several areas on a single campus. Laboratories also tend to generate a
relatively small volume of hazardous waste at each of these points of
generation. In contrast, industrial generators tend to generate only a
few wastestreams in large quantities at relatively few generation
points. Additionally, while most individuals involved in hazardous
waste generation activities at both industrial production facilities
and other non-college or university laboratories are employees who are
professionally trained in managing hazardous wastes, students often
generate hazardous waste at college and university laboratories.
EPA recognizes that hazardous waste management operations vary
widely among campuses and some colleges and universities have developed
programs that have proven to be successful, and thus may be reluctant
to change from the regulation under which they are currently operating.
Therefore, today's proposal is an optional, alternative set of
requirements to the existing generator regulations at Sec. Sec. 262.11
and 262.34(c). Those colleges or universities that choose to continue
to manage their laboratory hazardous waste under the current hazardous
waste regulations may do so. Colleges or universities that would like
the additional flexibility of today's rule may choose to manage their
laboratory hazardous waste according to this new set of generator
regulations. This proposal was developed with performance-based
standards in part to account for the diversity among college and
university operations and practices, curricula, and goals. The term
``performance-based standards'' means a flexible approach that will
allow colleges or universities the discretion to determine the most
appropriate and effective method of compliance with the requirements of
today's proposed rule. This diversity in programs for managing wastes,
including hazardous waste, is also reflective of logistical
considerations including campus size, space, personnel, and other
resource differences among colleges and universities.
EPA has heard from college and university stakeholders that the
greatest difficulty they face in managing their laboratory hazardous
waste under the existing regulations is making the RCRA hazardous waste
determination pursuant to 40 CFR 262.11 (i.e. determining whether their
solid waste is hazardous waste) in the laboratory when individuals in
the laboratory generating the solid waste and other materials are
students, often untrained and unqualified to make a hazardous waste
determination.
Additionally, stakeholders have pointed out that it is difficult to
make hazardous waste determinations in college and university
laboratories because in a college and university setting there are
numerous individual points of generation. This can make it difficult
for an Environmental Health and Safety (EH&S) (or other similarly
qualified) staff member to be present when the waste is generated.
Since any individual laboratory chemical hood (as one example) can be
considered a point of generation, and any college or university with a
substantial science department can have over a thousand such hoods
located in many laboratories throughout a campus, it can be extremely
impractical to have such qualified individuals present at each point.
Today's proposal addresses this issue by providing flexibility in
40 CFR 262.209 with regard to where the hazardous waste determination
can be made (i.e. in the laboratory, at an on-site central accumulation
area (CAA) or at an on-site TSDF), provided all unwanted materials (as
defined in Section IV. A. of this preamble) that are generated in the
laboratory are managed according to the provisions described below. If
the unwanted materials are sent to an on-site CAA (or on-site TSDF) at
the college or university for
[[Page 29715]]
hazardous waste determination by EH&S personnel (or other RCRA trained
individuals), the hazardous waste determination must be made within
four calendar days of arriving at the on-site CAA or TSDF.
Additionally, today's rule allows for the hazardous waste determination
to be made by RCRA-trained individuals in the laboratory before
unwanted materials are removed from the laboratory. The proposed
provisions would apply to all unwanted materials in the laboratory that
have the potential for being RCRA hazardous wastes, including those
which are later determined not to be RCRA hazardous waste by EH&S or
other qualified personnel. Colleges or universities with laboratories
that generate hazardous waste that choose not to be subject to today's
proposal would remain subject to the current generator requirements set
forth in Sec. Sec. 262.11 and 262.34(c). Today's proposal would not
alter or move the point of generation of any hazardous waste, but
merely allow the hazardous waste determination to be made at an on-site
central accumulation area or TSDF, or allow the hazardous waste
determination to be made in the laboratory, but at a point in time
after initial generation of the waste. The point of generation of the
hazardous waste would continue to be the location and time at which the
hazardous waste is first created.
Because the specific issues which are faced by colleges and
universities with regard to waste management are specific to hazardous
wastes generated in laboratories, it is only the hazardous waste
generated in the laboratory that may be managed under subpart K.
Hazardous wastes generated at other parts of the college and university
will remain subject to the existing hazardous waste regulations.
EPA believes that a performance-based approach will allow colleges
and universities greater flexibility and ensure better environmental
results. EPA also recognizes that performance-based standards
inherently lack specificity. Therefore, EPA is proposing a planning
component to help ensure that a college or university throughly
considers its specific circumstances, and provides the details needed
to ensure safe management of its unwanted materials. Therefore, under
today's proposal, colleges and universities must develop, implement and
retain a Laboratory Management Plan (LMP). This plan would describe how
a college or university will meet the required provisions in this
proposal (i.e. the performance-based standards). Subpart K will require
that the LMP contain certain elements; however, how an individual
college or university chooses to comply with these requirements (i.e.
the specifics of the LMP) will be left to its discretion. For example,
while the labeling standards for containers require the words
``unwanted material'' to be either affixed to or physically accompany
the container, the Agency is providing flexibility to colleges and
universities to use their discretion to meet the labeling standard for
providing sufficient information to alert emergency responders to the
hazards of the contents of the container. In this instance, the Agency
is proposing performance-based language for container labeling and is
not mandating specific terms or information to be used for defining
``sufficient information.'' The same is true for the propose
requirements for container management standards (i.e., while containers
must be maintained and kept in good condition, EPA is not prescribing
precisely how the containers are managed) and training/instruction
(i.e., depending on a college or university's generator status and the
duties of individual workers, colleges and universities may determine
the level of training needed for an individual to perform their
assigned duties). These elements must be addressed in detail in an LMP.
It would be a violation of subpart K for a college or university
laboratory (choosing to operate under subpart K) not to have an LMP
that addresses the required elements in a way which would meet the
performance standards. EPA is proposing two options for enforceability
of the provisions contained within the LMP. Under one option, it would
not be a violation of subpart K for a college or university to deviate
from its LMP, provided the performance-based standards are met. Under
the second option, it would be a violation of subpart K for a college
or university to deviate from its LMP.
EPA believes that today's proposal will lead to safe management of
unwanted materials and greater environmental protection by facilitating
RCRA hazardous waste determinations, requiring that they be performed
by specifically trained personnel, rather than by untrained students in
college and university laboratories. EPA also believes that today's
proposal will promote the protection of human health and the
environment by ensuring that all unwanted materials which may, in whole
or in part, be RCRA hazardous wastes are safely managed while in the
laboratory prior to the time that the hazardous waste determination is
made. In addition, EPA believes that the requirement in today's
proposal to develop and implement an LMP will improve a college or
university's coordination and integration of hazardous waste management
procedures and enhance environmental awareness among researchers and
students at colleges and universities, leading to a transfer of good
environmental management practices to the larger community.
EPA strongly encourages colleges and universities to go beyond
developing an LMP that addresses only the required elements, and
examine their waste generation and management practices college or
university-wide, with a particular eye toward finding opportunities for
waste minimization and pollution prevention. For example, opportunities
may exist for developing systems that would facilitate and encourage
redistribution and reuse of unwanted materials throughout the
institution. To that end, EPA actively encourages colleges and
universities to consider the implementation of an Environmental
Management System (EMS), a system of management practices and related
documentation, procedures, and work practices that are put in place to
manage an institution's overall environmental impacts. More information
on EMSs at colleges and universities can be found at: https://
www.epa.gov/ne/assistance/univ/emsguide.html and https://
www.campusEMS.org/.
B. History
EPA has led and participated in several efforts to gain a better
understanding of the challenges associated with managing hazardous
wastes in college and university laboratories. Pursuant to
Congressional direction in the Hazardous and Solid Waste Amendments of
1984 (HSWA), the Environmental Protection Agency (EPA) undertook a
study of challenges associated with the accumulation, storage and
disposal of hazardous wastes from college and university laboratories.
The study culminated in a Report to Congress (Report) in April 1989,
outlining the then current regulatory requirements for college and
university laboratories managing hazardous waste, the current practices
at these laboratories, and the problems confronting college and
university laboratories. The challenges for college and university
laboratories highlighted in the Report included a lack of awareness
about hazardous wastes and the applicable regulations due to the
transient nature of the student population, the highly variable
wastestreams generated, resource constraints on hazardous waste
[[Page 29716]]
management, and general difficulty in complying with the hazardous
waste regulations.
In 1999, EPA initiated a pilot program for three colleges and
universities, providing the regulatory flexibility necessary for the
participating institutions to be able to experiment with potentially
promising regulatory approaches to hazardous waste management in
college and university laboratories. This program was developed under
the Agency's Project XL, which stands for ``eXcellence and
Leadership,'' an initiative to allow regulated entities to achieve
better environmental results at less cost by increasing awareness of
EPA regulations and environmental performance through the use of tools
such as Environmental Management Plans (EMPs). The goals of the EPA
University Laboratories Project XL were to develop a more effective
approach for regulating university laboratories, develop programs to
enhance laboratory safety, and illustrate better systems to manage
laboratory environmental impacts.
In 2001, Congress endorsed EPA's participation in a pilot project
in collaboration with ten major academic research institutions, the
Howard Hughes Medical Institute (HHMI) and state regulatory officials
and directed EPA to subsequently report to Congress on the HHMI
project. The project was intended to evaluate a performance-based
approach in order to provide regulatory flexibility, reduce burdens and
yield superior compliance, and thus, environmental protection. EPA
encouraged state regulators to provide the maximum flexibility under
the current regulations to program participants so that they could
implement the consensus best practices developed through the program.
In 2002, EPA issued a Report to Congress (Report) on the HHMI project,
recognizing that college and university laboratories may have
difficulty complying with the RCRA hazardous waste regulations largely
due to the regulations' industry-oriented framework. In the Report, EPA
also indicated that regulatory changes may be necessary in some cases
and that the regulatory process would allow EPA to consider views from
diverse stakeholders and promote national consistency through the
public notice-and-comment process.
EPA subsequently developed a three-phased approach to address the
issues identified in the 2002 Report to Congress: (1) Outreach to
stakeholders to gather information to help EPA understand the specific
nature of the issues, (2) guidance to clarify issues raised by
stakeholders not needing regulatory changes, and (3) regulatory
changes, where appropriate, to provide flexibility. Such an approach
allowed EPA to first identify the specific issues involved, and quickly
address, through guidance, those issues that would not necessarily
require rulemaking. Those issues that are more complex, and that are
best served by the rulemaking process, were to be addressed at a later
time.
In June 2003, as part of the first phase, EPA held a public meeting
in order to solicit input from stakeholders on approaches to address
the issues concerning hazardous waste management in college and
university laboratories. Topics discussed at the meetings included:
Where and when to make the hazardous waste determination; waste
labeling requirements; personnel training requirements; satellite area
accumulation; and types of treatment performed in laboratories. In
March 2004, as part of the second phase, EPA issued a guidance
memorandum, answering certain frequently asked questions regarding
satellite accumulation area regulations. Because most laboratories in
colleges and universities would be considered satellite accumulation
areas, this memorandum helped resolve many of the issues faced by
college and university laboratories. Today's rule constitutes phase
three of the three-phased approach, and addresses several of the issues
which require a rulemaking.
As a parallel effort, in May 2003, colleges and universities were
selected to become a partner in EPA's Sector Strategies Program. The
Sector Strategies Program seeks industry-wide environmental gains
through innovative actions taken with a number of manufacturing and
service sectors. EPA is working with six college and university Sector
Partners (Howard Hughes Medical Institute (HHMI); American Council on
Education (ACE); APPA: The Association of Higher Education Facilities
Officers; Campus Consortium for Environmental Excellence (C2E2); Campus
Safety Health and Environmental Management Association (CSHEMA); and
National Association of College and University Business Officers
(NACUBO)) to develop sector-specific approaches to assist colleges and
universities to advance the use of environmental management systems,
reduce regulatory performance barriers, and measure environmental
progress.
In May, June and August 2004, the College and University Sector
Program Partners shared their thoughts in a series of proposals
suggesting alternative approaches for developing a RCRA program that
addresses the specific problems faced by college and university
laboratories. Their suggested changes to existing requirements focused
on tailoring new regulations for college and university laboratories
that are different from the standards required of other generators and
operators of treatment, storage and disposal facilities, similar to the
current ``satellite accumulation area'' regulations, and included
provisions for providing flexibility for the point at which the
hazardous waste determination is made, training of laboratory workers,
labeling, container management standards, and provisions for bench-
scale treatment of waste in the laboratory. (See the docket for today's
rulemaking for copies of proposals submitted to EPA.)
C. Agency's College and University Initiatives
Today's proposed rule is just one of the many efforts EPA is
pursuing to assist colleges and universities in reducing risks and
costs by developing tools to better manage chemicals and waste;
reducing use of resources; and promoting better overall environmental
stewardship. These efforts on behalf of colleges and universities rely
on voluntary and tool-based approaches, as well as regulations designed
to achieve better environmental performance at less cost and burden.
The Agency also has developed funding mechanisms to promote the
development of new, more environmentally friendly experiments and
technologies. The goals of all these programs are to improve
environmental performance and environmental health where students,
educators, and college or university personnel learn, teach and work.
Through its Colleges and Universities Sector Strategies Program,
described above, the Agency is partnering with college and universities
and their trade associations to overcome potential regulatory barriers,
promote environmental management systems, and develop measures of
environmental performance. More specifically, EPA is working with the
college and university sector to incorporate sound sustainable
practices to improve environmental safety practices, provide a baseline
for measuring change, identify priorities for continual improvement and
minimize overall environmental impacts. To learn more about EPA's
College and University Sector Strategy Program, visit: https://
www.epa.gov/sectors/colleges/.
[[Page 29717]]
Three of these efforts focus specifically on reducing waste. First,
there is an Agency partnership, called WasteWise, which is a voluntary
program helping U.S. organizations eliminate costly municipal and solid
waste, improving economic and environmental sustainability. The
WasteWise program is supporting RecycleMania, an intercollegiate
competition involving colleges and universities across the U.S. in an
annual recycling competition. The goal of the competition is to
increase student awareness of campus recycling. Founded in 2001 by two
of EPA's WasteWise partners, the number of competing schools increased
from 2 in 2001 to 47 in 2005. The total pounds recycled per student
across all participating schools increased from 74 pounds in 2001 to
1,117 pounds in 2005.
Second, in 2002, EPA funded Chemical Management Services (CMS)
pilots at two universities--the University of New Hampshire and
Dartmouth College. CMS, which has been used successfully in the
automotive, microelectronic and aerospace industries, restructures the
relationship between buyers of chemicals and their suppliers. Chemical
suppliers and waste service providers bring their expertise directly to
the college or university to help manage chemicals and waste streams,
allowing the colleges and universities to focus on their core
function--education. More information about the results of the pilots
can be found at https://www.epa.gov/epaoswer/hazwaste/minimize/pdfs/cms-
broch.pdf.
Third, is EPA's Green Chemistry Program. Green Chemistry, a proven
pollution prevention approach toward environmentally sustainable
manufacturing, is the design of chemical products and processes that
reduce or eliminate the use or generation of hazardous substances. To
promote this goal, EPA's Green Chemistry Program supports a variety of
educational and research efforts in which colleges and universities
have participated. One element of EPA's Green Chemistry Program is the
development of curricular materials and experiments that incorporate
the principles of green chemistry. These materials are primarily aimed
at undergraduate and graduate chemistry students. Another element of
EPA's Green Chemistry program is awarding grants for research that
advances the development and use of innovative technologies and
approaches directed at avoiding or minimizing the use or generation of
hazardous substances. A third element is the Presidential Green
Chemistry Challenge Awards Program, which provides national recognition
of outstanding chemical technologies that incorporate the principles of
green chemistry into chemical design, manufacture, and use. To learn
more about EPA's Green Chemistry Program, visit: https://www.epa.gov/
greenchemistry/.
In 2003, EPA launched another award program: the P3 Award--A
Student Design Competition for Sustainability. P3 focuses on the three
components of sustainability: People, prosperity and the planet. Only
colleges and universities are eligible to participate in this annual
competition. The competition has two phases. Initially, student teams
compete for $10,000 grants to use for researching and developing their
design projects. The P3 award, which includes additional funding of up
to $75,000, is given to the highest-rated student designs, which gives
the students the opportunity to further develop their designs for
sustainability, implement their projects in the field, and move them to
the marketplace. One of the 2005 P3 winners was designing and
developing solar ovens to be mass-produced at low cost, for use in the
developing world. To learn more about EPA's P3 Awards, visit: https://
es.epa.gov/ncer/p3/.
There are two efforts within EPA that focus specifically on
laboratories. First, in 2003, EPA awarded a cooperative agreement to
Iowa State University to develop a website, called Labs Achieving
Better Stewardship (LABS) Central, which is a web-based clearinghouse
of information of interest to laboratories, at colleges and
universities and elsewhere, dedicated to the pursuit of enhanced
environmental performance. This site brings together existing
information about innovative approaches to waste management and
resource conservation that may be helpful to laboratories interested in
regulatory compliance and environmental stewardship. LABS Central
guides visitors to web-based information about regulatory compliance,
environmental performance, advanced waste management techniques and
waste reduction. LABS Central can be found at: https://
www.labscentral.info.
Second, the Agency's Laboratories for the 21st Century (Labs21)
Partnership Program encourages the development of sustainable, high-
performance, and low-energy consumption laboratories. Labs21 is a
voluntary program whose partners set goals to reduce energy and water
use and take a ``whole-building'' approach to laboratory design or
retrofitting. Labs21 partners are demonstrating that a holistic
approach to laboratory design can result in higher efficiencies, cost
savings, reduced emissions, and improved health and safety conditions.
Currently 16 of 23 private sector partners in Labs21 are colleges and
universities. To learn more about Labs21, visit https://
www.labs21century.gov.
ENERGY STAR is another program that is demonstrating that better
energy management, in this case across a college or university campus,
can yield cost savings. Colleges and universities spend close to $2
billion each year on energy. ENERGY STAR is a voluntary EPA program
that gives institutions the power to reduce the pollution that causes
global warming, while enhancing their financial value. EPA's ENERGY
STAR program encourages colleges and universities to become ENERGY STAR
partners and adopt a strategic approach to energy management that can
lower energy bills by 30% or more. By partnering with ENERGY STAR, an
organization demonstrates environmental leadership, improves its energy
efficiency, saves money, and receives recognition. ENERGY STAR is a
proven energy management strategy to distinguish an institution as an
environmental leader and save money for repair and renovation, hiring
of new faculty, new construction, and other core activities. To learn
more about ENERGY STAR or becoming an ENERGY STAR partner, visit:
https://www.energystar.gov/index.cfm?c=higher_ed. bus--
highereducation.
Recognizing that universities have a significant impact on the
built and natural environment, EPA continues to pursue a series of
projects that promote smart growth implementation to achieve increased
viability of the campus and the surrounding neighborhood in an
environmentally sustainable manner. These activities include: Co-
hosting the 1st Annual Smart and Sustainable Campuses Conference at the
University of Maryland in November 2005, funding the publication of
``Partnerships for Smart Growth: University-Community Collaboration for
Better Public Spaces,'' compiling a list of smart growth course
prospectuses, developing a list of resources of best practices and
contacts at universities, providing input on the P3 project and
providing information and tools to the public. To learn more about
EPA's Smart Growth Program, visit: https://www.epa.gov/smartgrowth.
Finally, EPA has sponsored partnerships with industry, academic
institutions, environmental groups, and
[[Page 29718]]
other agencies to launch sector-specific Compliance Assistance Centers
(Centers). Through web sites, telephone assistance lines, fax-back
systems, and e-mail discussion groups, the Centers are helping
businesses, local governments, and federal facilities understand
federal environmental requirements and save money through pollution
prevention techniques. The Agency is in the early stages of developing
a new compliance assistance center dedicated to the education sector.
Existing compliance assistance centers may be viewed at: https://
www.assistancecenters.net.
D. Overview of College and University Laboratory Operations
While Agency data sources and information gained through site
visits and comments indicate that other areas of colleges and
universities generate hazardous waste, today's proposal only addresses
hazardous waste generated and accumulated in college and university
laboratories. Other areas within the college or university do not face
the same specific situations as laboratories and the current RCRA
requirements are effectively dealing with waste generation and
management in those areas. Agency information gathering and outreach
efforts also indicate the primary differences between laboratories and
the other areas in the college or university and more traditional
industrial settings include the number of wastestreams generated, the
variability and volume of any individual wastestream generated, the
number of individuals involved in waste generation and management,
their employment status (e.g. employee vs. student) and the stability
of that workforce (e.g. transient nature of students, visiting
professors etc. involved in waste generation and management vs.
relatively constant workforce in an industrial setting or other non-
college or university laboratory setting).
In traditional industrial settings, generally the waste output is
known in advance. Relatively large volumes of each waste type are
generated, and there are relatively few wastestreams per facility, with
little variability over time. Furthermore, industrial facilities,
including industrial laboratories, maintain a relatively steady
workforce and include environmental health and safety experts on staff.
In contrast, the waste generated within a laboratory at a college or
university is generated in relatively small quantities (beakerful
versus barrelful), and the exact character and composition of the waste
may not be known in advance. Additionally, the number of different
wastestreams generated by a single laboratory may be quite high due to
the nature of research and teaching activities. Each college or
university may have a very large number of individual laboratories,
each generating different wastestreams and operating under different
management or supervision. The most striking difference is that at
colleges and universities, much of the hazardous is generated by
students who are either in instructional settings (such as a chemistry
class) or are conducting research, but who are not employees of the
college or university.
A great deal of variability also exists in hazardous waste
generation and management procedures from laboratory to laboratory at
colleges and universities depending on the type of activity being
conducted and the size of the laboratory. However, there are some
general practices that can be identified, and are discussed below.
There are two primary activities that occur in college and
university laboratories and that generate hazardous waste. The first is
the routine use of chemicals in instruction and research. Over the
course of a typical month, the majority of waste generated by college
and university laboratories is generated during such routine use.
During instruction or research, chemicals are mixed to produce
reactions, and the resulting mixtures may qualify as hazardous waste
upon completion of the experiment. In other instances, solvents, a
major wastestream from laboratories, are used as extractants (to help
isolate and extract a wanted chemical from a mixture), or in cleaning
laboratory glassware. In addition, certain laboratory equipment used in
analyzing samples discharge the chemical sample and any chemical
carrier as waste at the end of the analysis. Hazardous waste generated
in this way may be of a very small volume (beakerful or less), and any
given experiment may generate multiple wastes. Often the exact chemical
makeup of such a waste is unknown to the researcher, particularly in
research experiments involving synthesizing new chemicals.
A researcher or student in a college or university laboratory
generally generates the hazardous wastes through routine use under a
laboratory hood, a contained area equipped with ventilation and
drainage, as part of the experiment he/she is conducting. Typically,
these hazardous wastes are collected in a container directly under the
hood. At the end of an experiment, or the end of the day, the waste is
transferred to a container in a specially designated area nearby. When
a container of hazardous waste is filled (usually well before the 55
gallon limit is exceeded, according to college and university
representatives), the environmental health and safety staff (or waste
management company under contract to the college or university) are
contacted by the researcher or laboratory manager. In some cases, the
environmental health and safety staff come directly to the laboratory
to make a hazardous waste determination (identifying the appropriate
RCRA hazardous waste code), and to transport the waste either to an on-
site central accumulation area, or in some cases, directly to an on-
site or off-site permitted treatment, storage or disposal facility.
The second activity at college and university laboratories that
generates hazardous wastes is laboratory clean-outs. Laboratory clean-
outs are relatively infrequent events that may generate larger volumes
of hazardous waste over a relatively short period of time. Unlike
routine laboratory operations, the primary wastes generated during a
clean-out event are not chemicals that have been used during an
experiment, but rather expired laboratory standard solutions and unused
reagents. Generally, the term ``reagent'' is used to describe the
chemicals in their ``original'' state, as purchased from a
manufacturer, rather than when the chemicals are the result of a
chemical reaction. However, the result of a chemical reaction can also
become a reagent in a new reaction. Most laboratories have a large
inventory of various reagents used for conducting experiments. Because
researchers at colleges and universities may require a particular
reagent on very short notice in the development of an experimental
procedure, they tend to maintain a large inventory in the laboratory,
rather than obtain each chemical from a central location or from a
chemical distributor. Reagents generally are used infrequently and only
in small amounts at any one particular time. Therefore, researchers
and/or professors at colleges and universities may store those reagents
for long periods of time. When a researcher and/or professor retires or
otherwise leaves the college or university, the laboratory may be
cleaned out of all unused reagents. A laboratory clean-out may also
occur when a building is renovated, or on occasion, as the result of a
college or university-wide effort to identify and remove excess
chemicals. During a laboratory clean-out, reagents often are assessed
to determine if they should be kept for further use. If retained, the
reagents are not considered
[[Page 29719]]
solid or hazardous wastes. However, when accumulated for long periods
of time, for example, such unused reagents may be considered solid or
hazardous wastes if it can be determined that they are no longer usable
for their intended purpose.
Laboratory clean-outs are relatively infrequent. One reason for
this is that during a laboratory clean-out, fairly large volumes of
hazardous waste, including those listed as acutely hazardous, may be
generated at one time (as compared with the baseline of generation for
that laboratory). Currently, college and university laboratories
generally operate as satellite accumulation areas under 40 CFR
262.34(c), and therefore must promptly (within 3 days) remove any
acutely hazardous waste that exceeds one quart in volume. Furthermore,
a generator's status (as large quantity generator, small quantity
generator, or conditionally exempt small quantity generator) is
determined, in part, by the volume of acutely hazardous waste it
generates in a calendar month. During a laboratory clean-out, it is
common for college and university laboratories to generate acutely
hazardous wastes in relatively large quantities, since many unused
bottles of reagents are deemed to be no longer needed (the hazard is
not increased in this instance, because the amount of the substances is
not increasing, merely its status is changing from unused product to
hazardous waste). This increase in generation of acutely hazardous
waste is problematic for small quantity generators that generate
quantities exceeding one quart during a laboratory clean-out and
thereby forcing them into large quantity generator status with shorter
on-site accumulation time and additional requirements and recordkeeping
burden.
Hazardous wastes generated in college and university laboratories
either during routine laboratory operation, or during laboratory clean-
out events are then removed from the laboratory and transferred to
another location for treatment, storage or disposal. Some colleges and
universities have on-site central accumulation areas or treatment
storage and disposal facilities (TSDF), while others transport their
hazardous waste to off-site TSDFs.
1. Generation of Hazardous Waste--Types and Quantities
This section describes the estimated hazardous waste quantities and
hazardous waste types generated by college and university large and
small quantity generators. Specifically, this section discusses the
overall hazardous waste generation activities at college and university
laboratories, and the hazardous waste generated from colleges and
universities with art programs.
a. Data Sources
The information on colleges and universities contained in this
section was obtained from the following agency data sources: 2001
Biennial Report (BR) data and additional data from the RCRAInfo
(Resources Conservation and Recovery Act Information) database, and the
2001 Toxics Release Inventory data files. To supplement data not
obtainable from EPA databases, EPA used public information to fill data
gaps or to improve data quality. The Art School and Program Directory
(https://www.artschools.com) was used to assist with identifying
colleges and universities that have an art program, and the list of
U.S. universities and list of community colleges developed by the
University of Texas (available at: https://www.utexas.edu/world/univ/)
was used to identify small quantity generator sites. These data sources
provided the most recent and reliable data available to the agency for
finalizing this proposed rule.
b. Summary of College and University Hazardous Waste Generation
Activities \1\
---------------------------------------------------------------------------
\1\ Hazardous waste quantities exclude remedial waste generation
and types and quantities of hazardous waste generated by medical
facilities affiliated with a college or university hospital.
---------------------------------------------------------------------------
A summary of quantities and types of hazardous wastes generated at
colleges and universities by large quantity generator (LQG) and small
quantity generator (SQG) four-year college, university and professional
schools; two-year junior colleges/technical institutes; and vocational
schools (which include ``all other miscellaneous schools and
instruction,'' ``fine arts schools'' and ``other technical and trade
schools'') follows.
Assuming college and university hazardous waste generation remains
fairly stable over time, college and university generators account for
a relatively small quantity of overall hazardous waste generation
(i.e., in 2001, over 40,800,000 tons of hazardous wastes were generated
by the total generator reporting universe compared to the 35,742 tons
generated by colleges and universities). Specifically, in 2001, there
were a total of 1,304 college and university LQGs and SQGs generating
hazardous waste. These entities generated 35,742 tons of hazardous
wastes. Of these totals, 333 colleges and universities are LQGs
generating a total of 33,789 tons of hazardous wastes and 971 \2\
colleges and universities are SQGs generating a total of 1,953 tons of
hazardous wastes.
---------------------------------------------------------------------------
\2\ EPA does not have hazardous waste quantity information for
517 SQGs. Therefore, these SQG estimates are excluded and hazardous
waste generation quantities for SQGs may be under-estimated.
---------------------------------------------------------------------------
Information also indicates that colleges and universities generate
relatively small quantities of many different types of hazardous
wastestreams. For example, in 2001, colleges and universities generated
12 distinct hazardous waste type categories or wastestreams: lab packs;
heavy metal and cyanide; dioxin pesticide; ignitable, corrosive and/or
reactive characteristic; inorganic metal; listed discarded commercial
chemical products (``P'' and ``U'' listed); mixtures from non-specific
sources; mixtures of toxic characteristic; pesticide; organic; spent
solvents; and ``unknowns.'' Hazardous waste generated for any one
particular wastestream by college and university LQGs ranged from
approximately 3,158 tons generated by 268 colleges/universities to less
than one ton generated by one college/university generator (with the
exception of one vocational school generating over 25,000 tons of
inorganic metal hazardous wastes). To further illustrate the small
quantities of hazardous waste generated by college and university large
and small quantity generators, a significant number of colleges and
universities generate less than one ton per generator for a particular
waste type (e.g., 2.3 tons of dioxin pesticides wastes were generated
in 2001 by 27 four-year colleges or universities which averages to
approximately .08 tons per college or university).
In addition, while the majority of college and university hazardous
waste generators are SQGs (roughly two-thirds of the college and
university generator universe), LQGs account for over 90% of the
hazardous waste generated by colleges and universities. Furthermore, in
2001, LQGs generated an average of approximately 75 tons of hazardous
waste per school and SQGs generated an average of approximately 2 tons
per school.
i. Summary of College and University Laboratory Hazardous Waste
Generation \3\
---------------------------------------------------------------------------
\3\ For purposes of this analysis, a hazardous waste was
considered a laboratory waste if the Biennial Report waste
description contained the word ``lab.''
---------------------------------------------------------------------------
As can be expected, laboratory hazardous waste generated by
colleges and universities is a small percentage of overall hazardous
waste generation because colleges and universities
[[Page 29720]]
represent only a portion of the total generator universe and laboratory
waste is only a portion of college and university hazardous waste. In
addition, not all colleges and universities generating hazardous waste
reported generating laboratory waste. However, laboratory waste
represents a small portion of the hazardous waste generated at colleges
and universities, as well. For instance, 246 of the 333 college and
university LQGs and 309 of the 971 SQGs reported generating relatively
small quantities of laboratory hazardous wastes. For LQGs, laboratory
waste generation only amounts to approximately 9% (or 2,939 tons) of
the total hazardous waste generated by colleges and universities, while
SQGs reported generating approximately 334 tons of laboratory hazardous
waste, which on average equates to approximately 1 ton of laboratory
hazardous waste per SQG.
Art studios/programs at colleges and universities are included in
the universe of college and university laboratories in this proposal,
while some types of laboratories are not included (e.g., hazardous
waste generated by medical facilities associated with a college or
university). In considering the effect of hazardous waste generation by
college and university art programs, it is interesting to note its
comparison to hazardous waste generation by other laboratories in the
scope of today's proposal at colleges and universities. Schools with
art programs generated an estimated 21% of the total hazardous waste
generated by college and university LQGs. Another interesting
comparison is that more college and university SQGs reported having art
programs than those generating laboratory hazardous wastes.
ii. Summary of Type and Volume of Laboratory Hazardous Waste Generation
at College and University LQGs and SQGs
College and university LQGs generated approximately 2,939 tons of
laboratory hazardous waste in 2001. This represents approximately 9% of
the hazardous waste generated by these college and university LQGs.
Four-year schools comprise the vast majority of schools generating
laboratory waste (235 of 246 LQGs generating laboratory hazardous waste
were four-year schools) and account for approximately 8.5% of the 9% of
the laboratory hazardous waste generated. Vocational schools reported
generating a minute amount of laboratory hazardous waste (about .01%).
The hazardous waste type comprising the highest percentage generated by
both four-year and two-year schools generating laboratory hazardous
waste is lab packs, generated by 114 out of a total of 235 four-year
schools, and 3 out of a total of 8 two-year schools reporting. Of the
total number of vocational schools reporting (3), the largest
percentage of laboratory hazardous waste generated is by one fine arts
school for inorganic (metal) wastes.
Approximately 73% of college and university SQGs that generated
laboratory hazardous waste in 2001 are four-year colleges and
universities. These four-year schools generated about 285 tons of
laboratory hazardous wastes which represents approximately 14% of the
all hazardous waste generated by college and university SQGs. Four-year
SQGs generated the majority of laboratory hazardous waste for all
college and university SQGs reporting (~ 85%). Lab packs are the
largest contributor to the quantity of laboratory hazardous waste
generated and represents ~ 73 tons of waste generated by approximately
79 SQGs. Spent solvents is the second largest type of hazardous waste
generated (~ 51.7 tons generated by ~ 91 SQGs), followed by ignitable,
corrosive, and/or reactive characteristic hazardous wastes with an
approximate 44.2 tons of laboratory hazardous waste generated by an
estimated 92 four-year college and university SQGs.
College and university LQGs with art programs have a modest impact
on laboratory hazardous waste generation. In 20