Revisions to: The Requirements for Transboundary Shipments of Wastes Between OECD Countries, the Requirements for Export Shipments of Spent Lead-Acid Batteries, the Requirements on Submitting Exception Reports for Export Shipments of Hazardous Wastes, and the Requirements for Imports of Hazardous Wastes, 58388-58416 [E8-22536]
Download as PDF
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Federal Register / Vol. 73, No. 194 / Monday, October 6, 2008 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 262, 264, 265, 266, and
271
[EPA–HQ–RCRA–2005–0018; FRL–8720–3]
RIN 2050–AE93
Revisions to: The Requirements for
Transboundary Shipments of Wastes
Between OECD Countries, the
Requirements for Export Shipments of
Spent Lead-Acid Batteries, the
Requirements on Submitting
Exception Reports for Export
Shipments of Hazardous Wastes, and
the Requirements for Imports of
Hazardous Wastes
Environmental Protection
Agency.
ACTION: Proposed rule.
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AGENCY:
SUMMARY: This rule proposes to amend
certain existing regulations promulgated
under the hazardous waste provisions of
the Resource Conservation and
Recovery Act (RCRA) regarding the
export and import of hazardous wastes
from and into the United States.
Specifically, we are proposing to
modify: The requirements to implement
the OECD framework concerning the
transboundary movement of hazardous
waste among countries belonging to the
Organization for Economic Cooperation
and Development (OECD), including
reducing the number of control levels,
exempting qualifying shipments sent for
laboratory analyses from certain
paperwork requirements, requiring
recovery facilities to submit a certificate
of recovery, adding provisions for the
return or re-export of wastes subject to
the Amber control procedures, and
clarifying certain existing provisions
that were identified as potentially
ambiguous to the regulated community;
the regulations regarding the
management of spent lead-acid batteries
being reclaimed to require appropriate
notice and consent for those batteries
intended for reclamation in a foreign
country; the exception reporting
requirements for hazardous waste
exports to specify that all exception
reports submitted to EPA be sent to the
Office of Enforcement and Compliance
Assurance’s Office of Federal Activities
in Washington, DC rather than to the
Administrator; and the hazardous waste
import requirements such that U.S.
importers would give the initial
transporter a copy of the EPA-provided
documentation confirming EPA’s
consent to the import when they
provide the RCRA hazardous waste
manifest, and that the documentation
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would be submitted by the U.S.
receiving facility to EPA along with the
RCRA hazardous waste manifest within
thirty days of import shipment delivery.
Finally, separate from this proposed
rule, EPA is publishing in https://
www.epa.gov/epawaste/hazard/
international/oecd-slab-rule.htm a draft
guidance document on how U.S.
receiving facilities may request EPA to
identify them as pre-approved facilities
to receive hazardous waste from OECD
Member countries.
DATES: Comments must be received on
or before December 5, 2008. Under the
Paperwork Reduction Act, comments on
the information collection provisions
must be received by OMB on or before
November 5, 2008.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
RCRA–2005–0018, by one of the
following methods:
• https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
• E-mail: rcra-docket@epa.gov,
Attention Docket No. EPA–HQ–RCRA–
2005–0018.
• Fax: (202) 566–9744, Attention
Docket No. EPA–HQ–RCRA–2005–0018.
• Mail: RCRA Docket No. EPA–HQ–
RCRA–2005–0018, Environmental
Protection Agency, Mail Code: 2822T,
1200 Pennsylvania Avenue, NW.,
Washington, DC 20460. Please include a
total of 2 copies. 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 St. NW., Washington, DC
20503.
• Hand Delivery: RCRA Docket No.
EPA–HQ–RCRA–2005–0018, EPA West
Building, Room 3334, 1301 Constitution
Ave., NW., Washington DC 20004. 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–2005–
0018. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or e-mail. The
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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.
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 RCRA Docket, EPA/DC, EPA West,
Room 3334, 1301 Constitution Avenue,
NW., Washington, DC. The Public
Reading Room is open from 8:30 a.m. to
4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone
number for the Public Reading Room is
(202) 566–1744 and the telephone
number for the RCRA Docket is (202)
566–0270.
FOR FURTHER INFORMATION CONTACT:
Laura Coughlan, Hazardous Waste
Identification Division, Office of Solid
Waste (5304P), Environmental
Protection Agency, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460;
telephone number: (703) 308–0005; fax
number: (703) 308–0514; e-mail:
coughlan.laura@epa.gov.
The
information presented in this preamble
is organized as follows:
SUPPLEMENTARY INFORMATION:
I. General Information
A. List of Acronyms Used in This Proposed
Rule
B. What are the statutory authorities for
this proposed rule?
C. Does this proposed rule apply to me?
D. What is the purpose of this proposed
rule?
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II. Background
A. OECD Revisions
B. SLAB Revisions
C. Exception Report Revisions for Exports
Under Subparts E and H of 40 CFR Part
262
D. Import Revisions
III. Summary of This Proposed Rule and
Changes
A. Changes to 40 CFR Part 262, Subpart E
B. Changes to 40 CFR 262.60(e), Subpart F
C. Changes to 40 CFR Part 262, Subpart H
D. Changes to 40 CFR 264.12(a)(2) and 40
CFR 265.12(a)(2)
E. Changes to 40 CFR 264.71(a)(3) and 40
CFR 265.71(a)(3)
F. Changes to 40 CFR 266.80(a)
G. Changes to 40 CFR 271.1
IV. Costs and Benefits of the Proposed Rule
A. Introduction
B. Analytical Scope
C. Cost Impacts
D. Benefits
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
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act of 1995
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
Risks and Safety Risks
H. Executive Order 13211: Actions
Concerning Regulations that
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer
Advancement Act
J. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
I. General Information
A. List of Acronyms Used in This
Proposed Rule
Acronym
BCI ...........
CBI ...........
CERCLA ..
CFR .........
EPA .........
FR ............
HSWA ......
LAB ..........
NAICS ......
NTTAA .....
NAFTA .....
OECD ......
OMB ........
OSWER ...
RCRA ......
RFA .........
SIC ...........
SLAB .......
Acronym
Meaning
SBREFA ..
Small Business Regulatory Enforcement Fairness Act
Toxics Release Inventory
Unfunded Mandates Reform Act
TRI ...........
UMRA ......
B. What are the statutory authorities for
this proposed rule?
The authority to propose this rule is
found in sections 1006, 1007, 2002(a),
3001–3010, 3013–3015, and 3017 of the
Battery Council International
Solid Waste Disposal Act, as amended
Confidential Business Informaby the Resource Conservation and
tion
Comprehensive Environmental Recovery Act (RCRA), and as amended
Response, Compensation, and by the Hazardous and Solid Waste
Amendments, 42 U.S.C. 6905, 6906,
Liability Act
6912, 6921–6930, 6934–6936, and 6938.
Code of Federal Regulations
Meaning
U.S. Environmental Protection
Agency
Federal Register
Hazardous and Solid Waste
Amendments
Lead-Acid Battery
North American Industrial Classification System
National Technology Transfer
and Advancement Act
North American Free Trade
Agreement
Organization for Economic Cooperation and Development
Office of Management and
Budget
Office of Solid Waste and Emergency Response
Resource Conservation and Recovery Act
Regulatory Flexibility Act
Standard Industrial Classification
Spent Lead-Acid Battery
C. Does this proposed rule apply to me?
1. OECD Revisions
The OECD revisions in this proposed
rule affect all persons who export or
import hazardous waste, export or
import universal waste, or export spent
lead-acid batteries (SLABs) destined for
recovery operations in countries
belonging to the Organization for
Economic Cooperation and
Development (OECD), except for Mexico
and Canada. Any transboundary
movement of hazardous wastes between
the United States and either Mexico or
Canada will continue to be regulated by
their respective bilateral agreements and
applicable regulations. Potentially
affected entities may include, but are
not limited to:
Industry sector
NAICS
Utilities .............................................................................................................................................................................
Petroleum and Coal Products Manufacturing .................................................................................................................
Chemical Manufacturing ..................................................................................................................................................
Primary Metal Manufacturing ...........................................................................................................................................
Fabricated Metal Product Manufacturing ........................................................................................................................
Machinery Manufacturing ................................................................................................................................................
Computer and Electronic Product Manufacturing ...........................................................................................................
Electrical Equipment, Appliance, and Component Manufacturing ..................................................................................
Transportation Equipment Manufacturing .......................................................................................................................
Miscellaneous Manufacturing ..........................................................................................................................................
Scrap and Waste Materials .............................................................................................................................................
Materials Recovery Facilities ...........................................................................................................................................
2. SLAB Revisions
The SLAB revisions in this proposed
rule affect all persons who export
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NAICS
Hazardous Waste Collectors ...........................................................................................................................................
Recyclable Material Hauling, Long-Distance ...................................................................................................................
Batteries, automotive, merchant wholesalers ..................................................................................................................
Lead-acid storage batteries, manufacturing ....................................................................................................................
Automotive Parts, Accessories, and Tire Stores .............................................................................................................
Tire Dealers .....................................................................................................................................................................
All other General Merchandise Stores ............................................................................................................................
New Car Dealers .............................................................................................................................................................
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SLABs for reclamation in any foreign
country. Potentially affected entities
may include, but are not limited to:
Industry sector
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Industry sector
NAICS
Recyclable Material Wholesaler ......................................................................................................................................
Other Waste Collection ....................................................................................................................................................
Recyclable Material Collection Services, Solid Waste Collection ...................................................................................
Marinas ............................................................................................................................................................................
General Freight Trucking, Long-Distance, TL .................................................................................................................
General Freight Trucking, Long-Distance, LTL ...............................................................................................................
Specialized Freight Trucking ...........................................................................................................................................
Freight Carriers (except air couriers), Air Scheduled ......................................................................................................
Freight Charter Services, Air ...........................................................................................................................................
Freight Railways, Line-Haul .............................................................................................................................................
Freight Transportation, Deep Sea, to and from Domestic Ports ....................................................................................
Freight Transportation, Deep Sea, to or from Foreign Ports ..........................................................................................
3. Exception Report Revisions for
Exports Under Subparts E and H of 40
CFR Part 262
The exception report change to 40
CFR part 262, subpart E and subpart H
NAICS
Utilities .............................................................................................................................................................................
Petroleum and Coal Products Manufacturing .................................................................................................................
Chemical Manufacturing ..................................................................................................................................................
Primary Metal Manufacturing ...........................................................................................................................................
Fabricated Metal Product Manufacturing ........................................................................................................................
Machinery Manufacturing ................................................................................................................................................
Computer and Electronic Product Manufacturing ...........................................................................................................
Electrical Equipment, Appliance, and Component Manufacturing ..................................................................................
Transportation Equipment Manufacturing .......................................................................................................................
Miscellaneous Manufacturing ..........................................................................................................................................
Scrap and Waste Materials .............................................................................................................................................
The import revisions in this proposed
rule affect all persons importing
hazardous waste from a foreign country
that must comply with 40 CFR part 262,
subpart F, and all facilities receiving
imported hazardous waste from a
foreign country that must comply with
either 264.71(a)(3) or 265.71(a)(3). This
NAICS
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Hazardous Waste Collectors ...........................................................................................................................................
Recyclable Material Hauling, Long-Distance ...................................................................................................................
Recyclable Material Wholesaler ......................................................................................................................................
Other Waste Collection ....................................................................................................................................................
Recyclable Material Collection Services, Solid Waste Collection ...................................................................................
General Freight Trucking, Long-Distance, TL .................................................................................................................
Scrap and Waste Materials .............................................................................................................................................
Materials Recovery Facilities ...........................................................................................................................................
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D. What is the purpose of this proposed
rule?
1. OECD Revisions
This proposed rule is intended to
implement the OECD’s ‘‘Decision of the
Council C(2001)107/FINAL, Concerning
the Control of Transboundary
Movements of Wastes Destined for
Recovery Operations, as amended by
C(2004)20’’ (hereinafter referred to as
the Amended 2001 OECD Decision),
which amended the OECD Decision
(1992) on the same subject. The purpose
of these revisions was to encourage
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includes those hazardous waste import
shipments originating in OECD
countries, as well as in non-OECD
countries. Potentially affected entities
may include, but are not limited to:
Industry sector
The lists of potentially affected
entities in the above tables may not be
exhaustive. The Agency’s aim is to
provide a guide for readers regarding
those entities that potentially could be
affected by this action. However, this
action may affect other entities not
listed in these tables. If you have
questions regarding the applicability of
this proposed rule to a particular entity,
consult the person listed in the
preceding section entitled FOR FURTHER
INFORMATION CONTACT.
5093
4212
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of this proposed rule affect all persons
who export hazardous waste, universal
waste, or SLABs to any foreign country.
Potentially affected entities may
include, but are not limited to:
Industry sector
4. Import Revisions
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consistency and harmonization between
the OECD and the Basel Convention,1
which in turn, promotes economic
1 The Basel Convention on the Control of
Transboundary Movements of Hazardous Wastes
and their Disposal is a comprehensive global
environmental agreement on hazardous and other
wastes. The Convention has 170 Member countries,
also known as Parties, and aims to protect human
health and the environment against the adverse
effects resulting from the generation, management,
transboundary movements and disposal of
hazardous and other wastes. More information on
the Basel Convention may be found at https://
www.basel.int.
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efficiency and the recovery of waste in
an environmentally sound manner.
The Amended 2001 OECD Decision
was supported by the United States and
imposes legally binding commitments
on the United States pursuant to
Articles 5(a) and 6 of the OECD
Convention. By consenting to the
Decision, the United States Government
has agreed to promulgate regulations
necessary to ensure that the United
States can uphold the agreement.
Further, this proposed rule clarifies
certain regulations to articulate more
explicitly EPA’s original intent in those
regulations and to eliminate any
confusion on the part of the regulated
community.
2. SLAB Revisions
EPA also proposes to amend the
RCRA hazardous waste regulations for
SLABs specified in 40 CFR part 266,
subpart G by requiring notification and
consent for the export of SLABs in order
to ensure that SLABs are sent to
reclamation facilities in countries that
can manage them in an environmentally
sound manner. The notification and
consent requirements are intended to:
(1) Reduce potential risk to human
health and the environment, including
potential risk from the transboundary
movement of pollution from other
countries to the U.S., and (2) harmonize
the notice and consent procedures with
international practice (see II.B.4) and
with the RCRA universal waste
regulations for the export of SLABs,
resulting in a more uniform practice for
notification and consent for SLABs.
Notification of potential exports of
hazardous waste destined for recovery
in another country is a key component
of multilateral environmental systems
for appropriate governmental oversight
to ensure proper management of the
waste. The notification mechanism
allows for all concerned countries (i.e.,
exporting, importing, and transit) to
determine whether the hazardous waste
can be handled safely based on the
requirements of their waste management
systems. Specifically, the importing
country has the opportunity to confirm
that the particular facility that is
designated to receive the waste is
qualified to manage it in a safe and
environmentally sound manner, and has
all appropriate approvals, permits, or
licenses. Furthermore, the notice and
consent process is the fundamental tool
that is employed in transboundary
waste arrangements to provide business
certainty for legitimate trade.
Risks to human health and the
environment derived from improper
SLAB recycling techniques are of major
concern internationally. The Basel
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Convention has developed two guidance
documents 2 3 to assist governments,
transporters, and recyclers to achieve
environmentally sound management of
SLABs. Indeed, the Basel Convention
considers transboundary movement of
SLABs to be ‘‘illegal traffic’’ if it occurs
without prior notification. Similar
guidance was developed by the
Commission for Environmental
Cooperation 4 (CEC) for use by North
American countries to promote sound
management of SLABs.5 A 1996 OECD
Ministerial Declaration on risk
reduction from lead called on Member
countries to take domestic and
international action to reduce human
exposure to lead from a variety of
sources.6 Further, the Report of the
Special Rapporteur of the U.N.
Commission on Human Rights 7
expressed concerns that ‘‘the United
States system does not impose export
regulations on SLABs destined for
recycling,’’ and suggests that ‘‘the
recycling of lead-acid batteries is one of
the greatest potential sources of risk,
especially for exposed workers in the
informal sector in many developing
countries.’’
For economic and efficiency reasons,
some highly industrialized countries
may ship their SLABs to less
industrialized countries for SLAB
breaking, draining, component
separation, slag generation and lead
refining. Human health and
environmental risk issues can arise
when these recycling processes are
performed with insufficient human
health or environmental safety controls.
The results could include: (1)
Significant increases in elevated blood
lead levels in facility workers and their
2 Basel Convention Training Manual: National
Management Plans for Used Lead Acid Batteries,
SBC No. 2004/5, 2004.
3 Technical Guidelines for the Environmentally
Sound Management of Waste Lead-acid Batteries,
SBC No. 2003/9, 2003.
4 The Commission for Environmental Cooperation
is an international organization created by Canada,
Mexico and the United States under the North
American Agreement on Environmental
Cooperation (NAAEC). The CEC was established to
address regional environmental concerns, help
prevent potential trade and environmental conflicts,
and to promote the effective enforcement of
environmental law. The Agreement complements
the environmental provisions of the North
American Free Trade Agreement (NAFTA).
5 Practices and Options for Environmentally
Sound Management of Spent Lead-acid Batteries
within North America, Commission for
Environmental Cooperation, December 2007.
6 The Global Pursuit of the Sound Management of
Chemicals, The World Bank, February 2004.
7 Adverse effects of the illicit movement and
dumping of toxic and dangerous products and
wastes on the enjoyment of human rights, U.N.
Commission on Human Rights, Economic and
Social Council, E/CN.4/2003/56/Add.1, 10 January
2003, p. 17.
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58391
families; (2) increases in uncontrolled
releases of lead-laden slag to soil,
surface water and ground water sources;
and (3) lead air-emissions from lead
smelting without the proper airemissions controls.
EPA would like to focus on the use of
preventative measures to decrease the
proportionate risks to human health and
the global environment. There are
inherent human health and
environmental hazards associated with
a significant amount of SLABs being
exported across borders without the
knowledge and consent of receiving
countries and/or SLABs being exported
to countries with substandard smelting
infrastructures. Amending the current
RCRA hazardous waste regulations to
include the notification and consent
requirements would help ensure that
SLABs are exported to countries with
the capacity to handle them in an
environmentally sound manner and to
aid countries with tracking the
movements and life-cycle management
of SLABs inside their borders. EPA
believes that the notification and
consent approach is an effective way of
preventing the export of SLABs to
countries and to facilities that do not
have the capability of safely managing
the SLABs by providing the receiving
country with the necessary information
about the proposed shipment and
requiring its consent before the export
can proceed. In addition, by providing
the receiving country with this
information, they can monitor and track
the export and the facility’s
management of the SLABs for safe
management. The purpose of the
notification and consent requirements
for SLABs destined for reclamation in
this proposed rule is consistent with the
purpose of the notification and consent
requirements in RCRA section 3017.
Congress, in enacting section 3017,
considered it important to require
notification and consent for exports of
hazardous wastes. The legislative
history for section 3017 indicates that
Congress felt that prior notification of an
export to the receiving country would
allow that country to make an informed
decision as to whether it would accept
the waste and, if so, how it would safely
manage that waste. Congress noted that
problems, such as harm to human
health and the environment arise when
wastes are sent to countries that do not
want to receive them, or lack sufficient
information to manage them properly.
EPA believes that the potential
reduction in risk to human health and
the environment with this proposed
modification will outweigh the
incremental increase in burden to SLAB
exporters. Moreover, because the
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notification and consent requirements
are intended to ensure that the receiving
country has the necessary advance
knowledge of a proposed shipment of
SLABs to a facility in that country, the
country can properly consent (or object)
to this shipment based on its knowledge
of the capabilities of the particular
facility and its ability to manage the
batteries in a safe and environmentally
sound manner.
3. Exception Report Revisions for
Exports Under Subparts E and H of 40
CFR Part 262
EPA proposes to amend the exception
reporting requirements in 40 CFR part
262, subparts E and H, to specify that all
exception reports be submitted to the
Office of Enforcement and Compliance
Assurance’s Office of Federal Activities
in Washington, DC rather than to the
Administrator.8 The Agency proposes
this change because it believes that a
more specific address should assist in
proper delivery of the exception report
to the appropriate EPA office. The more
general requirement in the existing
regulation to send this report to the
‘‘Administrator’’ may have not provided
sufficiently specific instruction for those
exporters trying to notify EPA of
returned shipments, which could
reduce EPA’s ability to provide
oversight on such exports. Directing that
all exception reports submitted to EPA
pursuant to the requirements in 40 CFR
part 262, subparts E and H, be sent to
a specific address should ensure better
oversight of (1) return shipments into
the U.S. and (2) compliance with the
exception report requirements without
additional regulatory burden.
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4. Import Revisions
Finally, EPA proposes to amend the
import requirements specified in 40
CFR part 262, subpart F. This change
would require that the U.S. importer
provide the transporter with a copy of
documentation provided by EPA,
confirming EPA’s consent to the
hazardous waste import under a specific
notice. This documentation would then
accompany each RCRA hazardous waste
manifested import shipment and be
submitted by the receiving facility in the
U.S. to EPA along with the RCRA
hazardous waste manifest in accordance
with §§ 264.71(a)(3) and 265.71(a)(3).
While EPA currently requires that
receiving facilities in the U.S. submit a
copy of the hazardous waste manifest to
EPA to document individual import
8 The Office of Enforcement and Compliance
Assurance is the office within EPA that implements
the notice and consent scheme for hazardous waste
transboundary shipments.
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shipments, it has been difficult for EPA
to match an individual manifest for a
hazardous waste import shipment with
the related notice of intent to export
from a foreign country for which EPA
has provided consent. One major reason
for this difficulty is because a given
destination facility in the U.S. could be
receiving the same hazardous waste
from the same foreign exporter under
more than one notice. Adding this
requirement will enable EPA to better
match the individual import shipments
against the related notice from the
foreign exporting country for which
EPA has provided consent, and facilitate
our oversight of such imports.
II. Background
A. OECD Revisions
1. What is the OECD?
The OECD is an international
organization established in 1960 to
assist Member countries in achieving
sustainable economic growth,
employment, and an increased standard
of living, while simultaneously ensuring
the protection of human health and the
environment. OECD Member countries
are concerned with a host of
international socio-economic and
political issues, including
environmental issues. To address these
issues, the OECD Council may negotiate
Council Decisions, which are
international agreements that create
binding commitments on the United
States under the terms of the OECD
Convention, unless otherwise provided
in the Articles of the 1960 Convention.
One such Council Decision addresses
the transboundary movement of waste,
which is the subject of this proposed
rule. There are currently thirty OECD
Member countries: Australia, Austria,
Belgium, Canada, the Czech Republic,
Denmark, Finland, France, Germany,
Greece, Hungary, Iceland, Ireland, Italy,
Japan, Luxembourg, Mexico, the
Netherlands, New Zealand, Norway,
Poland, Portugal, the Slovak Republic,
South Korea, Spain, Sweden,
Switzerland, Turkey, the United
Kingdom, and the United States. The
OECD country Web site for each
Member country may be found at
https://www.oecd.org/infobycountry/.
2. What OECD Decision formed the
basis for the existing regulations in 40
CFR part 262, subpart H?
On March 30, 1992, the OECD
Council adopted the ‘‘Decision of the
Council C(92)39/FINAL Concerning the
Control of Transfrontier Movements of
Wastes Destined for Recovery’’
(hereinafter referred to as the 1992
Decision), which applied to the
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transboundary movements of wastes
destined for recovery operations
between OECD Member countries. The
1992 Decision provided a framework for
OECD Member countries to control the
transboundary movement of recoverable
wastes in an environmentally sound and
economically efficient manner.
3. Why did EPA establish the existing
regulations in 40 CFR part 262, subpart
H?
Due to the legally binding nature of
the 1992 Decision, the United States, as
an OECD Member country, was required
to implement the terms of the decision
in accordance with Articles 5(a) and 6
of the OECD Convention. (A copy of the
OECD Convention is included in the
docket to this proposed rule.) In order
to implement the specific provisions of
the 1992 Decision, EPA published a
final rule in the Federal Register
entitled, ‘‘Imports and Exports of
Hazardous Waste: Implementation of
OECD Council Decision C(92)39
Concerning the Control of Transfrontier
Movements of Wastes Destined for
Recovery Operations’’ (61 FR 16289,
April 12, 1996)(hereafter referred to as
EPA’s OECD rule). These regulations
appear primarily in 40 CFR part 262,
subpart H.
4. What OECD Decisions form the basis
of the revisions in this proposed rule?
On June 14, 2001, the OECD Council
amended the 1992 Decision by passing
‘‘Revision of Decision C(92)30/FINAL
on the Control of Transboundary
Movement of Wastes Destined for
Recovery Operations’’ (hereafter referred
to as the 2001 OECD Decision). The goal
of the 2001 OECD Decision was to
harmonize the procedures and
requirements of the OECD with those of
the Basel Convention and to eliminate
duplicative activities between the two
international organizations as much as
practical. These changes include
significant revisions to the original
established framework (such as
reducing the levels of control from a
three-tiered system to a two-tiered
system), while also adding entirely new
provisions (for example, the new
certificate of recovery requirement).
Subsequent to the 2001 OECD Decision,
an addendum, C(2001)107/ADD1
(hereafter referred to as the 2001 OECD
Addendum), which consists of revised
versions of the notification and
movement documents and the
instructions to complete them, was
adopted by the OECD Council on
February 28, 2002. The addendum was
incorporated into the 2001 OECD
Decision as section C of Appendix 8,
and the combined version was issued in
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May 2002 as C(2001)107/FINAL.
Finally, on March 30, 2004, the OECD
Council adopted C(2004)20 (hereafter
referred to as the 2004 OECD
Amendment), which updated the OECD
waste lists, entitled ‘‘Appendix 3: List of
Wastes Subject to the Green Control
Procedure’’ (hereafter referred to as the
Green list) and ‘‘Appendix 4: List of
Wastes Subject to the Amber Control
Procedure’’ (hereafter referred to as the
Amber List). To the extent possible, the
Green and Amber Lists were revised
based on the amendments made to
Annexes II, VIII, and IX of the Basel
Convention in November 2003. The
OECD Council decisions are collectively
referred to as the Amended 2001 OECD
Decision.
5. How does EPA propose to revise the
existing regulations to implement the
latest OECD Decisions?
This rule proposes to amend EPA’s
OECD rule to reflect the procedural and
substantive amendments in the 2001
OECD Decision, the applicable changes
to the new notification and movement
documents presented in the 2001 OECD
Addendum, and the changes to the
OECD waste lists as presented in the
2004 OECD Amendment, collectively
referred to as the Amended 2001 OECD
Decision. This proposed rule also seeks
to clarify certain existing regulatory
provisions that have been identified as
potentially ambiguous to the regulated
community.
As noted previously, OECD Council
Decisions are international agreements
that create binding commitments on the
United States, unless otherwise
provided in the Articles to the 1960
Convention. Therefore, by consenting to
the Amended 2001 OECD Decision, the
United States Government has agreed to
establish legal measures necessary to
ensure that the United States can
uphold the agreement. EPA believes that
RCRA contains adequate authority to
promulgate the requirements of the
Amended 2001 OECD Decision.
It is important to recognize that the
OECD Decision allows a Member
country to determine if a waste on an
OECD list is hazardous based on its
‘‘national procedures.’’ EPA has
determined that a waste is hazardous
under U.S. ‘‘national procedures’’—and
therefore subject to the OECD provisions
of Subpart H—if the waste meets the
following requirements under RCRA: (a)
Meets the Federal definition of
hazardous waste in 40 CFR 261.3; and
(b) is subject to either the Federal
hazardous waste manifesting
requirements in 40 CFR 262, or to the
universal waste management standards
of 40 CFR part 273, or to State
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requirements analogous to Part 273.
This determination was set forth in
§ 262.89(a), and additional discussion
on how this provision impacts
transboundary movements of wastes
subject to RCRA exemptions, exclusions
and recycling provisions can be found
in the April 12, 1996, preamble to the
original OECD rule (61 FR 16290–
16316).
6. How does EPA propose to implement
future OECD revisions?
(a) Changes to OECD Member Country
List
Qualified countries may be invited to
accede to the OECD Convention as new
Members. The OECD Convention
defines qualified countries as those that
have demonstrated the basic values
shared by all Members: An open market
economy, democratic pluralism, and
respect for human rights. Any decision
to invite a new country to become a
Member of the OECD must be
unanimous, although abstentions may
be allowed. Thus, no new Member may
be admitted over the objection of the
United States (or any other Member).
In order to accommodate changes in
OECD membership as quickly as
possible, EPA intends to publish in the
Federal Register any future
amendments to the list of OECD
Member countries set forth in
§ 262.58(a)(1), as the OECD adds new
Member countries or otherwise amends
its list in the future. EPA intends to
publish notices of these future
amendments to § 262.58(a)(1) as a final
rule without prior notice and
opportunity for comment. EPA believes
that the Agency would be able to make
a ‘‘good cause’’ finding under the
Administrative Procedure Act (APA) (5
U.S.C. 553(b)(3)(B)) to make these future
amendments without prior notice and
comment. EPA believes notice and an
opportunity for comment on future
amendments to § 262.58(a)(1) to reflect
the updates to the OECD list of Member
countries would be unnecessary,
because the United States, as an OECD
Member country, is legally obligated to
implement OECD Decisions with
respect to all OECD Member countries.
58393
able to make a ‘‘good cause’’ finding
under the Administrative Procedure Act
(APA) (5 U.S.C. 553(b)(3)(B)) to make
these future amendments without prior
notice and comment because the
purpose of § 262.89(d) is solely
informational—to provide an up-to-date
reference of the OECD list. Public
comment on such updates is
unnecessary, as EPA would have no
discretion to modify the OECD list. As
discussed above, U.S. national
procedures, rather than the OECD list,
ultimately determine the applicability of
Subpart H, recognizing that the OECD
list will be relevant for exports to other
OECD members.
B. SLAB Revisions
1. What are SLABs?
Lead-acid batteries are secondary, wet
cell batteries that contain liquid and can
be recharged for many uses. They are
the most widely used rechargeable
batteries in the world and are mainly
used as starting, lighting, and ignition
(SLI) power batteries found in
automobiles and other vehicles. A
rechargeable SLAB is spent if it no
longer performs effectively and cannot
be recharged. Battery failure is most
commonly attributed to water loss and
grid corrosion during normal use.
SLABs are considered both solid and
hazardous wastes under Subtitle C of
RCRA, because they are classified as
spent materials that exhibit the toxicity
characteristic for lead, and the
corrosivity characteristic for the sulfuric
acid electrolyte in the battery.
Lead-acid batteries are typically
composed of an outside plastic casing
and six inner cells containing lead strips
and positive and negative lead
terminals. Each cell is made up of two
lead frameworks, the positive plate
being lead dioxide and the negative
plate being spongy lead (a metallic lead
in a high-surface-area porous structure).
Each cell is filled with sulfuric acid as
the electrolyte. When the battery is in
use, the spongy lead, sulphuric acid,
and lead dioxide react to produce an
electrical current. Both electrodes are
converted to lead sulfate, a process
which is reversed during recharge.
(b) Changes to OECD Waste List
2. How are SLABs currently managed?
The OECD waste list is incorporated
by reference and cited in § 262.89(d). If
the OECD amends its waste list in the
future by decision of the OECD Council
(with the concurrence of the United
States), EPA intends to publish notices
of these amendments in the Federal
Register as a final rule without prior
notice and an opportunity for comment.
EPA believes that the Agency would be
Currently, SLABs are either reclaimed
for their lead value or disposed of. The
Battery Council International (BCI)
reported a 99.2 percent domestic SLAB
reclamation rate for the years 1999–
2003, making lead-acid batteries one of
the most recycled consumer products.
When a SLAB is collected, it is sent to
a reclaimer where the SLABs are
cracked through various means, such as
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a hammermill in order to separate out
the lead, battery casing, plate separators,
and sulfuric acid components into
recycling streams and disposal streams.
Specifically, the lead plates, lead oxide
paste and other lead parts are cleaned
and then melted together in smelting
furnaces to produce lead ingots along
with residual lead dross and slag. The
residual lead dross and slag may be
reclaimed further or disposed of in a
landfill. Used sulphuric acid can be (1)
Sent for acid regeneration, where the
acid is cleaned for re-use as electrolyte
in the battery manufacturing process, (2)
neutralized and released into a public
sewer system once it meets Clean Water
Act standards, or (3) converted into
sodium sulfate, an odorless white
powder that’s used in laundry detergent,
glass and textile manufacturing. If it is
a plastic-cased battery, the plastic is
either cleaned and recycled as new
battery casings or disposed of at a
landfill. If the battery casing is made of
rubber or other materials, it can be used
as a fuel at the smelter. Other materials
from batteries are either recycled or
disposed of in a landfill.
Lead is a highly toxic heavy metal
naturally occurring in the environment.
For this reason, proper management of
lead and lead-containing products is
essential to the protection of human
health and the environment. In the U.S.,
the Occupational Safety and Health
Administration (OSHA) has developed
standards to address and minimize
workplace exposure to lead (29 CFR
§ 1910.1025). These standards establish
permissible exposure limits; exposure
monitoring, respiratory protection and
safety procedures; and proper warning
and sign-age requirements for facilities
processing lead. Proper ventilation,
training and safety procedures also are
necessary. In less developed countries,
these precautions may be overlooked,
leading to dangerous conditions. (See
‘‘A Study of the Lead-Acid Battery
Industry and Spent Lead-Acid Battery
Exports,’’ June 2003, a copy of which is
included in the RCRA docket
established for this proposed rule.)
Recent data show that the primary
factors influencing decisions to export
SLABs from the United States include
the price of scrap lead, worldwide
supply and demand for lead, and the
relative price of virgin lead compared to
the price of scrap lead. BCI estimates
that in 1995, approximately 1,078,674
tons of recoverable lead was available
from batteries consumed domestically.
BCI also reports that, based on
Department of Commerce data,
approximately 104,614 tons of battery
scrap lead were exported in 1995. In
contrast, approximately 269,171 metric
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tons of SLABs were exported in 2006
based on more recent data from the
International Trade Commission,
Environment Canada, and Secretaria de
Medio Ambiente y Recursos Naturales
(SEMARNAT). Such a large increase in
exports may be in large part due to
recent increases in the domestic and
international price of lead.
According to the annual ‘‘Mineral
Commodity Summaries’’ published by
the U.S. Geological Survey (USGS), the
average price of lead for North
American producers increased by 77%
from 43.7 cents/pound in 1999 to 77.8
cents/pound in 2006. The average price
as reported on the London Metal
Exchange increased by 154% during
those same years from 22.8 cents/pound
to 58.0 cents/pound. In addition, while
export shipments destined for locations
in many countries are subject to duties
or tariffs on any exported SLABs,
Canadian and Mexican importers are
allowed, under the conditions of the
North American Free Trade Agreement
(NAFTA), to import SLABs without the
usual surcharge. Indeed, data show that
Canada and Mexico are the major
destination countries to which U.S.
SLABs have been exported in recent
years. For example, in 2006 U.S. SLAB
exports to Mexico and Canada were
estimated to be 199,000 metric tons and
66,000 metric tons, respectively (based
on data from Mexican and Canadian
government sources). Comparing this
information to data from the U.S.
International Trade Commission, it is
estimated that only 1.8% of SLAB
exports are destined for countries other
than Mexico or Canada. (See the EPA
Cost Assessment 9 prepared in support
of this proposed action.)
3. How are SLABs currently regulated in
the United States?
Under the current Federal hazardous
waste regulations established pursuant
to RCRA, SLABs are hazardous wastes
if the batteries exhibit one or more of
the characteristics of hazardous waste
provided in 40 CFR 261, subpart C (e.g.,
corrosivity (D001), or toxicity for lead
(D008)). SLABs typically exhibit the
toxicity characteristic for lead and,
therefore, are defined as hazardous
wastes.
regulations, which could include the
part 273 universal waste rules.
However, in all instances, SLABs that
are disposed of must be managed at a
RCRA Subtitle C disposal facility and
are subject to the Land Disposal
Restriction requirements of 40 CFR part
268.
The universal waste regulations,
promulgated on May 11, 1995, were
created to provide a streamlined set of
management regulations governing the
collection and management of certain
widely generated hazardous wastes,
such as spent batteries. For the purposes
of the universal waste regulations, the
definition of ‘‘battery’’ includes SLABs.
While SLABs managed as universal
waste may be drained of sulphuric acid,
the battery casings must be intact.
SLABs that have partially or wholly
crushed casings cannot be managed as
universal waste.
A universal waste handler is required
to ensure that the SLABs do not spill or
leak and that they are stored in a
structurally sound container. In
addition, depending upon the amount of
SLABs that are accumulated, a battery
handler may be required to track
shipments of the SLABs sent off-site for
reclamation or other management.
Universal waste handlers are not
allowed to treat their waste; however,
they can conduct certain activities (e.g.,
sorting, regeneration 10, etc.) provided
the battery casings remain intact.
Other general provisions to which all
universal waste handlers are subject
include labeling/marking, accumulation
time limits, employee training, and
response to releases of hazardous waste.
Off-site shipments of universal wastes
do not require a hazardous waste
manifest, provided they are sent to
another universal waste handler or a
specified destination facility, and are
shipped by an authorized universal
waste transporter.
(b) SLABs Sent for Reclamation Within
the United States
(a) SLABs Sent for Disposal Within the
United States
If a generator disposes, rather than
reclaims, SLABs, the SLABs would need
to be managed in compliance with the
Subtitle C hazardous waste management
When reclaimed, SLABs are exempt
from most of the RCRA Subtitle C
hazardous waste regulations, but are
subject to the regulations in part 266,
subpart G. (See 40 CFR § 261.6(a)(2)(iv).)
Alternatively, they can also be managed
as a universal waste and subject to the
universal waste regulations in 40 CFR
part 273. Thus, generators that send
SLABs off-site for reclamation may
choose to manage their SLABs either as
a universal waste, in accordance with
9 Cost Assessment for the Proposed Rule on
Exports and Imports of Hazardous Waste Destined
for Recovery Among OECD Countries and Exports
of Spent Lead-Acid Batteries from the U.S.
10 Regeneration under 40 CFR part 266, subpart G,
includes only replacing drained electrolyte fluids
and replacing ‘‘bad’’ battery cells. (See 48 FR at
14496.)
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the management standards in 40 CFR
part 273, or in accordance with the
management standards in 40 CFR part
266, subpart G.
Under the provisions of 40 CFR part
266, subpart G, persons who generate,
collect, transport, or store SLABs for
direct regeneration or reclamation are
exempt from the bulk of the RCRA
hazardous waste regulations (40 CFR
parts 262 through 266, 270, 124 and the
EPA notification and identification
number requirements). However, 40
CFR part 266, subpart G imposes certain
requirements on reclaimers of SLABs
who do not store prior to reclamation,
and on facilities that store SLABs
destined for reclamation, but do not
conduct any reclamation. In addition,
owners or operators of facilities that
both store and reclaim SLABs are
required to comply with the EPA
notification and identification number
requirements and all applicable
hazardous waste management facility
provisions in parts 264/265, 270, and
124, and are subject to 40 CFR parts 261,
§ 262.11, and applicable provisions
under part 268.
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4. What international agreements apply
to the export of SLABs?
There are two major international
agreements that expressly address the
export of SLABs: (1) The Basel
Convention on the Control of
Transboundary Movements of
Hazardous Wastes and Their Disposal
(Basel Convention); and (2) the
Amended 2001 OECD Decision (see
II.A.4 for more information). This
proposal would harmonize the EPA
SLAB export requirements with both of
these international agreements.
As noted in footnote 1, the Basel
Convention is a multilateral
international agreement governing the
transboundary movements of hazardous
wastes. Among other things, the Basel
Convention includes a requirement for
notice and written consent for
transboundary movements of hazardous
waste between trading countries. SLABs
are covered under the Basel Convention
as a hazardous waste and are thus
subject to the notice and consent
requirements of the Basel Convention.
The United States is a signatory to the
Convention, but has not yet ratified it
and is therefore not legally bound to its
requirements.
The Amended 2001 OECD Decision
regulates the transboundary movements
of hazardous wastes (e.g. wastes subject
to Amber control procedures) destined
for recovery within OECD Member
countries. The Amended 2001 OECD
Decision lists SLABs, whether whole or
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crushed, as subject to the Amber control
procedures.
Currently, under the RCRA hazardous
waste regulations, SLABs can be
managed either in accordance with the
special regulations under 40 CFR part
266, subpart G or in accordance with the
universal waste regulations, as
discussed above. Under part 266,
subpart G, SLABs that are destined for
reclamation are currently exempt from
the RCRA export requirements in 40
CFR part 262, subpart E and subpart H
(including the notice and consent
requirements).
On the other hand, under the
universal waste regulations, exporters of
SLABs for reclamation are subject to the
export requirements in 40 CFR part 273
(including the notice and consent
requirements) or, if the SLABs will be
exported to an OECD Member country
for recovery, the export requirements
(including notice and consent) in 40
CFR part 262, subpart H, apply. In
addition, even in situations where U.S.
exporters are not subject to the notice
and consent requirements, U.S.
exporters may still be required to notify
the importing OECD Member country of
their intention to export batteries,
pursuant to contracts with foreign
consignees. This is because SLABs,
identified by the Amended 2001 OECD
Decision as wastes subject to Amber
control procedures, are generally
considered to be hazardous waste under
the national procedures of the importing
Member countries.
5. How does EPA propose to revise the
SLAB regulations under 40 CFR part
266, subpart G?
EPA proposes to amend the SLAB
regulations under 40 CFR part 266,
subpart G, to require that exporters and
transporters handling SLABs destined
for reclamation in a foreign country to
comply with the same requirements
specified in the universal waste
regulations under 40 CFR part 273.
Specifically, an exporter who sends the
SLABs to a foreign destination other
than to those OECD countries specified
in 40 CFR 262.58(a)(1) would have to:
(a) Comply with the requirements
applicable to a primary exporter in 40
CFR 262.53, 262.56(a) (1) through (4),
(6), 262.56(b) and 262.57; (b) export
such SLABs only upon consent of the
receiving country and in conformance
with the EPA Acknowledgement of
Consent as defined in subpart E of 40
CFR part 262 of this chapter; and (c)
provide a copy of the EPA
Acknowledgment of Consent for the
shipment to the transporter transporting
the shipment for export. In addition, a
transporter transporting a shipment of
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SLABs to a foreign destination other
than to those OECD countries specified
in 40 CFR 262.58(a)(1) would not be
able to accept a shipment if the
transporter knew the shipment does not
conform to the EPA Acknowledgment of
Consent, and would have to ensure that:
(a) a copy of the EPA Acknowledgment
of Consent accompanies the SLAB
export shipment; and (b) the shipment
is delivered to the facility designated by
the person initiating the SLAB export
shipment.
For SLABs destined for reclamation in
OECD countries specified in 40 CFR
262.58(a)(1), exporters and transporters
would be subject to the requirements of
40 CFR part 262, subpart H, the
requirements governing hazardous
waste shipments to OECD countries.
C. Exception Report Revisions for
Exports Under Subparts E and H of 40
CFR Part 262
EPA proposes to replace ‘‘EPA
Administrator’’ with ‘‘the Office of
Enforcement and Compliance
Assurance, Office of Federal Activities,
International Compliance Assurance
Division (2254A), Environmental
Protection Agency, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460’’
in both § 262.55 and in § 262.87(b).
By providing a specific address for the
submission of all exception reports
required by 40 CFR part 262, subparts
E and H, EPA can ensure better
oversight of (1) return shipments to the
U.S. and (2) compliance with the
exception reporting requirements
without any additional regulatory
burden for U.S. exporters. In this
proposed rule, EPA is making very clear
that submission of these export
exception reports must be to the same
specific EPA address that receives all
export notifications and export annual
reports, and with no substitution for
comparable State agencies. States that
are interested in receiving a parallel
copy of the exception report will still be
able to require the submission of a copy
to their State Director in addition to
sending it to the above federal address.
D. Import Revisions
EPA proposes to amend the import
requirements specified in § 262.60(e) to
require that the U.S. importer provide
the transporter with a copy of the
documentation confirming EPA’s
consent to the hazardous waste import,
specified under a notice submitted by
the competent authority of the country
of export. This documentation must
accompany each RCRA hazardous waste
shipment and be submitted by the U.S.
receiving facility to EPA along with the
RCRA hazardous waste manifest as
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required under §§ 264.71(a)(3) and
265.71(a)(3).
While EPA currently requires that
U.S. receiving facilities submit a copy of
the hazardous waste manifest to EPA to
document individual hazardous waste
import shipments, it has proved
difficult to match individual hazardous
waste import shipments against a given
approved notice of intent to export from
a foreign country. In part, this is because
a given destination facility in the United
States could be receiving the same
hazardous waste from the same foreign
exporter under more than one approved
notice. Adding this requirement will
enable EPA to match the submitted
RCRA hazardous waste manifests for
individual import shipments against the
approved import notice that typically
covers the twelve months of imports.
Being able to do so will enable EPA to
determine when any import shipments
claiming coverage under that specific
notice would or would not be in
accordance with the terms of the
approved notice, thus improving our
oversight of such imports.
EPA currently responds to specific
notices of intent to export hazardous
waste from a foreign country into the
United States with either a written
response (e.g., written consent or
objection) or a tacit consent. Tacit
consents are allowable for imports
subject to EPA’s OECD regulations, as
specified in 40 CFR part 262, subpart H.
For such imports, the exporting country
may assume tacit consent to the
proposed shipments by EPA if no
written response from EPA has been
received by the exporting country thirty
working days from the date EPA sends
the exporting country a letter
acknowledging receipt of the notice.
Because EPA’s consents are currently
either tacit or sent in writing only to the
competent authority of the exporting
country, EPA will need to provide or
otherwise make available to U.S.
importers documentation confirming
the Agency’s consent. EPA is
considering and soliciting comments on
what would provide adequate
documentation of the Agency’s written
or tacit consent to a specific notice, and
how best to provide that information to
U.S. importers.
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III. Summary of This Proposed Rule
and Changes
A. Changes to 40 CFR Part 262, Subpart
E
This proposed rule amends the
exception reporting requirements in
§ 262.55 to specify that all exception
reports be submitted to the Office of
Enforcement and Compliance
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Assurance’s Office of Federal Activities
in Washington, DC, rather than to the
Administrator. In addition, the proposal
also updates § 262.58(a) to reflect that
export shipments of SLABs being
managed under 40 CFR part 266,
subpart G that are destined for recovery
in one of the OECD Member countries
listed in § 262.58(a)(1) are subject to the
requirements of subpart H. Finally, the
proposal adds language in § 262.58(b) of
subpart E to clarify that hazardous waste
exports subject to subpart E and
hazardous waste imports subject to
subpart F are not subject to subpart H
in order to reduce confusion for U.S.
exporters and importers.
B. Changes to 40 CFR 262.60(e), Subpart
F
This proposed rule includes the
requirement that a U.S. importer
provide the transporter a copy of the
documentation confirming EPA’s
consent to the import of hazardous
waste when the importer provides the
transporter with an additional copy of
the manifest.
C. Changes to 40 CFR Part 262, Subpart
H
All but the last three changes listed
below are necessary to conform to the
revisions in the Amended 2001 OECD
Decision. These changes range from
substantive revisions and amendments
to changes in terminology to simple
editorial changes. Collectively, these
changes serve to implement the
Amended 2001 OECD Decision, as well
as clarify certain sections that were
previously ambiguous to the regulated
community. Changes to 40 CFR part
262, subpart H include:
1. Changes in Terminology
In the Amended 2001 OECD Decision,
the OECD Council updated several
terms and definitions used in the 1992
Decision. EPA believes that these
changes do not result in substantive
changes to the intent of the
requirements, but merely bring them in
line with current terminology used in
practice and in other international
agreements. To limit any unnecessary
confusion between the U.S. regulations
and those of other OECD Member
countries and to promote consistency
with the Amended 2001 OECD
Decision, this proposed rule adopts
these changes in terminology. Thus,
EPA proposes to change the following
terminology:
(a) ‘‘Transfrontier’’ to
‘‘transboundary’’;
(b) ‘‘Tracking document’’ to
‘‘movement document’’;
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(c) ‘‘Amber-list controls’’ to ‘‘Amber
control procedures’’;
(d) ‘‘Notifier’’ to ‘‘exporter’’; and
(e) ‘‘Consignee’’ to ‘‘importer.’’ 11
2. The Number of Different Levels of
Control Is Reduced From Three (Green,
Amber, and Red) to Two (Green and
Amber) and the Waste Lists Have Been
Updated
The 2001 OECD Decision replaced the
OECD three-tier waste list (Green,
Amber, Red) system with a two-tiered
system (Green and Amber) to conform to
the Basel Convention waste lists more
closely. Further, the revised OECD
waste lists, as provided by the 2004
OECD Amendment, better correspond to
those of the Basel Convention.
Accordingly, we are proposing to make
these same conforming changes to EPA’s
OECD rule.
Wastes subject to the Green control
procedures are those wastes listed in
Parts I and II of Appendix 3 to the
Amended 2001 OECD Decision. Part I
contains wastes listed in Annex IX of
the Basel Convention, to which the
OECD has made and noted adjustments,
as appropriate. Part II contains
additional wastes subject to the Green
control procedures, which the OECD
has assessed as not posing any risk to
human health or the environment under
its risk criteria.
Wastes subject to the Amber control
procedures are those wastes listed in
Parts I and II of Appendix 4 to the
Amended 2001 OECD Decision. Part I
contains wastes listed in Annexes II and
VIII of the Basel Convention, to which
the OECD has made and noted
adjustments, as appropriate. Part II
contains additional wastes subject to the
Amber control procedures, which the
OECD has assessed as posing a risk to
human health or the environment under
its risk criteria. Further, all wastes
formerly appearing on the Red list
would be subject to the Amber control
procedures.
U.S. importers and exporters of
hazardous waste subject to the subpart
H requirements of 40 CFR part 262
should be aware that wastes listed in
Part I of both the new OECD Amber and
Green waste lists have not retained their
OECD waste codes. Consequently, the
relevant Basel waste codes should be
used instead. However, wastes listed in
Part II of both the new OECD Amber and
Green waste lists do retain their original
OECD waste codes, as listed in the 1992
Decision. This two-part system is
11 The change from ‘‘consignee’’ to ‘‘importer’’ is
only being made in 40 CFR part 262 subpart H, and
does not affect the use of consignee in 40 CFR part
262 subpart E.
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necessary to ensure that wastes not yet
explicitly listed under the Basel
Convention will continue to have the
same level of control applied to them
when destined for recovery under the
Amended 2001 OECD Decision.
Both the Green waste list and the
Amber waste list are cited in § 262.89.
This rule proposes to amend § 262.89(d)
to incorporate by reference the most
current OECD waste lists from the
Amended 2001 OECD Decision. Further,
the elimination of the Red list allows for
the consolidation of the provisions
currently found in § 262.89(b) and (c),
which appears in the new proposed
§ 262.89(b).
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3. References to Unlisted Wastes Have
Been Eliminated in Favor of ‘‘Wastes
Not Covered in Appendices 3 and 4 of
the OECD Decision’’
Section 262.83(d) currently addresses
the general notification requirements for
unlisted wastes. This rule first proposes
to renumber this section to § 262.83(c)
since the current § 262.83(c) addresses
‘‘red-list wastes’’ and is no longer
needed. This proposal also replaces the
term ‘‘unlisted wastes’’ with ‘‘wastes not
covered in Appendices 3 and 4 of the
OECD Decision, 12’’ so that wastes not
on these lists are not automatically
subject to the Amber control
procedures. Rather, ‘‘wastes not covered
in Appendices 3 and 4 of the OECD
Decision’’ will be subject to the
domestic rules and regulations of the
countries of concern.
4. Transboundary Movements May Now
Qualify for a Laboratory Analysis
Exemption
The 1992 Decision and EPA’s OECD
rule did not include a provision that
would exempt waste samples destined
for laboratory analyses. The Amended
2001 OECD Decision, however, would
allow Member countries to decide
through their domestic laws and
regulations that waste samples normally
subject to the Amber control procedures
will only be subject to the Green control
procedures if such samples are destined
for laboratory analyses to assess its
physical or chemical characteristics, or
to determine its suitability for recovery
operations. Therefore, we are proposing
that if the waste sample is destined for
laboratory analyses and meets certain
specified conditions, then the waste is
subject to the Green control procedures
12 Section 262.81(j) in the proposed revisions to
the regulatory text in 40 CFR part 262, subpart H
defines ‘‘OECD Decision’’ as ‘‘Decision of the
Council C(2001)107/FINAL, Concerning the Control
of Transboundary Movements of Wastes Destined
for Recovery Operations, as Amended by
C(2004)20’’ for the purposes of the subpart.
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(e.g., the existing controls normally
applied in commercial transactions).
The Amended 2001 OECD Decision
provides that the amount of waste
qualifying for this exemption shall not
be more than the minimum quantity
reasonably needed to perform the
analyses adequately in each particular
case, but can never exceed twenty-five
kilograms (25 kg /55 lbs). Analytical
samples also must be appropriately
packaged and labeled and must be
carried out under the terms of all
applicable international transport
agreements. Furthermore, any
transboundary movement of such
samples through non-OECD Member
countries shall be subject to
international law and to all applicable
national laws and regulations. Thus, the
proposed rule allows for waste samples
that are sent for laboratory analyses to
be exempt from the Amber control
procedures provided they meet the same
conditions as set forth in the Amended
2001 OECD Decision.
Information on exemptions and any
other national requirements concerning
movements of waste for laboratory
analyses is available to the public via a
Web site with information compiled by
the OECD Environment Directorate,
which can be accessed at https://
www.oecd.org/env/waste/.
U.S. exporters should also be aware
that even if their shipments qualify for
the laboratory analyses exemption, some
Member countries may elect to apply
the Amber control procedures to such
shipments, requiring the exporter of a
waste sample for laboratory analyses to
inform the competent authorities of
such a movement. U.S. exporters should
check with the competent authorities of
each country to find out if they require
the Amber control procedures for a
sample that would qualify for the
laboratory analyses exemption.
5. Recovery Facilities Must Submit a
Certificate of Recovery
This proposed rule would implement
the Amended 2001 OECD Decision’s
requirement that a duly authorized
representative of the recovery facility
submit a certificate of recovery to all
interested parties (e.g., exporter, country
of export, country of import), ensuring
recovery of the waste has been
completed. A valid certificate of
recovery is defined as a written and
dated statement that affirms that the
waste materials were recovered and that
any residuals generated from the
recovery operation have been disposed
of in the manner agreed to by the parties
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to the contract.13 This proposed rule
also requires, as does the Amended
2001 OECD Decision, that the recovery
facility send the certificate of recovery
as soon as possible, but no later than
thirty (30) days after the completion of
recovery and no later than one (1)
calendar year following the receipt of
waste by the recovery facility. Finally,
this proposed rule requires that the
recovery facility must send copies of the
certificate of recovery to the exporter
and competent authorities of the
countries of export and import by mail,
e-mail followed by mail, or fax followed
by mail. This proposed rule
incorporates the certificate of recovery
provisions of the Amended 2001 OECD
Decision in § 262.83(e).
The Amended 2001 OECD Decision
states that the completion of block 18 of
the OECD movement document, and the
submission of signed copies to the
exporter and relevant competent
authorities, fulfils the certificate of
recovery requirement. Although the
OECD movement document is
recommended, the Amended 2001
OECD Decision does not require
recovery facilities to use it.
While some recovery facilities may
not be subject to the import and other
requirements because they are not
handling RCRA hazardous waste, these
entities should be aware that the
competent authorities of the exporting
Member countries may still impose the
conditions outlined in the OECD
Council Decisions before the
transactions can be completed. Thus, if
the waste is considered non-hazardous
in the United States, EPA would not
require a certificate of recovery from a
facility. However, the competent
authority of the country of export may
require a certificate of recovery, and
may require that the exporter include
such a requirement in the contract
between the exporter and importer.
13 Under both the 1992 Decision and the
Amended 2001 OECD Decision, transboundary
movements of wastes subject to the Amber control
procedures may only occur under the terms of a
valid written contract, or chain of contracts, or
equivalent arrangements between facilities
controlled by the same legal entity, starting with the
exporter and terminating at the recovery facility.
The contracts must: (a) Clearly identify the
generator of each type of waste, each person who
shall have legal control of the wastes and the
recovery facility; (b) provide that relevant
requirements of the OECD Decisions are taken into
account and binding on all parties; and (c) specify
which party to the contract shall assume
responsibility for ensuring alternative management
of the wastes including, if necessary, the return of
the wastes.
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6. Amendments to Notification
Requirements
The Amended 2001 OECD Decision
introduced a series of notification
requirements that require EPA to make
conforming amendments to its OECD
regulations. Specifically, this proposed
rule would amend § 262.83(e) (which
would be renumbered as § 262.83(d)) by
incorporating several new items that
must be included in the notification,
including:
(a) Exporter and importing recovery
facility e-mail address;
(b) E-mail address for importer (if
different from the importing recovery
facility);
(c) Address, telephone, fax, and email of intended transporter(s);
(d) Means of transport envisioned;
and
(e) Specification of the type of
recovery operation(s) that will be used.
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7. Amendments to Procedures for
Exports to Pre-Approved Facilities
Under the Amended 2001 OECD
Decision, a pre-approved recovery
facility (also known as a pre-consented
recovery facility) is one that has been
identified in advance by the competent
authority having jurisdiction over that
facility as acceptable for receiving
hazardous waste imports. For these
facilities, the competent authority must
inform the OECD secretariat that the
facility is pre-approved, and the waste
types that are acceptable for recovery.
This allows for simplified and
accelerated notification procedures. Preapproval may be granted for a specific
time frame and may be revoked at any
time by the relevant competent
authority.
The Amended 2001 OECD Decision
established a consideration period for
objection to transboundary movements
to pre-approved facilities and
lengthened the allowable coverage
period for notifications. Specifically, the
Decision established a consideration
period of seven (7) working days during
which time relevant competent
authorities may object to transboundary
movements of waste to pre-approved
facilities. The Decision also established
that the allowable coverage period for
general notifications may extend up to
three (3) years. Today’s proposed rule
amends the current regulations to
incorporate these changes in
§ 262.83(b)(2)(ii) to reflect the seven (7)
day consideration period and in
§ 262.83(b)(2)(i) to reflect the allowable
coverage period for notifications.
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8. New Procedures for the Pretreatment
of Hazardous Wastes at R12/R13
Recovery Facilities
The Amended 2001 OECD Decision
imposed new requirements for R12 and
R13 recovery facilities, which we are
proposing to incorporate in this
proposal. R12 and R13 recovery
facilities are transfer and storage
facilities, respectively, that do not
recover the wastes themselves. Because
hazardous wastes destined for recovery
may have to undergo treatment before a
R1–R11 14 recovery facility actually
recovers them, the OECD considers R12
and R13 facilities as ‘‘intermediate or
temporary operations.’’ The primary
reason for the new requirements is to
ensure that the subsequent R1–R11
recovery operation receives the waste
and completes its recovery in an
environmentally sound manner.
When the notification document lists
an R12/R13 recovery facility, we are
proposing that the exporter must
indicate in the same notification
document the recovery facility or
facilities where the subsequent R1–R11
recovery operation takes place or may
take place.
The R12/R13 recovery facility shall
certify the receipt of the hazardous
waste by sending a copy of the duly
completed movement document within
three (3) working days of the receipt of
such wastes to the exporter and all
competent authorities concerned. In
addition, the R12/R13 recovery facility
must retain the original movement
document for three (3) years. Similarly,
the R12/R13 recovery facility has to
certify the completion of the R12/R13
recovery operation by submitting a
certificate of recovery as soon as
possible, but no later than thirty (30)
days after the completion of the R12/
R13 recovery operation at that facility
and no later than one (1) calendar year
following the receipt of the waste by the
R12/R13 recovery facility. The R12/R13
recovery facility must send the
certificate of recovery to the exporter
and to the competent authorities of the
countries of export and import by either
14 Recovery operations R1 through R11 are
defined as the following: R1, use as a fuel (other
than in direct incineration) or other means to
generate energy; R2, solvent reclamation/
regeneration; R3, recycling/reclamation of organic
substances which are not used as solvents; R4,
recycling/reclamation of metals and metal
compounds; R5, recycling/reclamation of other
inorganic materials; R6, regeneration of acids or
bases; R7, recovery of components used for
pollution abatement; R8, recovery of components
used from catalysts; R9, used oil re-refining or other
reuses of previously used oil; R10, land treatment
resulting in benefit to agriculture or ecological
improvement; and, R11, uses of residual materials
obtained from any of the operations numbered R1–
R10.
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mail, e-mail followed by mail, or by fax
followed by mail.
The control procedures applied to
transboundary movements of hazardous
waste from an R12/R13 recovery facility
to a subsequent R1–R11 recovery facility
vary depending on whether these
facilities are located within the same
Member country or in a different
Member country.
When the subsequent R1–R11
recovery facility is located within the
same country, we are proposing that the
R12/R13 recovery facility must obtain
from the subsequent R1–R11 recovery
facility a certification that the ‘‘final’’
recovery of the hazardous waste at that
facility has been completed within one
(1) calendar year following the delivery
of the hazardous waste to the R1–R11
facility. The format of the certification
of recovery is not fixed, but it must, at
a minimum, identify the code number of
the notification document and serial
number of the movement documents to
which it pertains. The R12/R13 recovery
facility must then transmit the
certification document prepared by the
R1–R11 recovery facility to the
competent authorities of the countries of
import and export as soon as possible,
but no later than one (1) calendar year
following the delivery of the hazardous
waste to the R1–R11 recovery facility.
When the subsequent R1–R11 facility
is not located in the same Member
country as the R12/R13 facility, we are
proposing that a new notification must
be made for the transboundary
movement of hazardous waste by the
R12/R13 recovery facility. The
applicable procedures differ, however,
depending upon the country where the
final recovery operation occurs. In
particular, if the final R1–R11 recovery
facility is located in the initial country
of export, then the normal Amber
control procedures shall apply. In this
case, the R12/R13 facility must submit
a new notification document to its
competent authority and obtain consent
from its competent authority and from
the initial country of export to the
export of the hazardous waste back to
that country for final recovery. If,
however, the final R1–R11 recovery
facility is located in a country different
from the initial country of export, then
the Amber control procedures shall also
apply, but the movement will in effect
be treated as a ‘‘re-export’’ of waste to
a third country. In this case, not only is
a new notification document required,
but the competent authority of the
initial country of export must also be
notified of the transboundary
movement, and consent must be
obtained from the original country of
export and the new countries of import,
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export, and transit. For example, if a
hazardous waste is exported from the
United States to a R12/R13 facility in
France, and then will be sent to a
subsequent R1–R11 recovery facility in
Germany, the R12/R13 facility in France
must submit a notification to and obtain
consent from France (the new country of
export), the United States (the original
country of export) and Germany (the
new country of import for final
recovery).
This proposed rule incorporates all of
these requirements in § 262.82(f).
9. New Provisions Regarding Mixtures
of Hazardous Wastes
The Amended 2001 OECD Decision
contains controls and provisions related
to the mixture of hazardous waste.
Specifically, the Amended 2001 OECD
Decision defines a mixture of hazardous
waste as one that results from the
intentional or unintentional mixing of
two or more different hazardous wastes.
However, under the Amended 2001
OECD Decision, a single shipment of
hazardous wastes, consisting of two or
more wastes, where each is separated, is
not considered a mixture of hazardous
waste.
The Amended 2001 OECD Decision
also provides that:
• A mixture of two or more Green
wastes should be subject to the Green
control procedures. However, the
regulated community should be aware
that some OECD Member countries may
require, by domestic law, that mixtures
of different Green wastes be subject to
the Amber control procedures.
• A mixture consisting of a Green
waste and more than a ‘‘de minimis’’
amount of Amber waste is subject to the
Amber control procedures. In the
absence of internationally accepted
criteria, the term ‘‘de minimis’’ should
be defined according to national
regulations and procedures.
• A mixture containing two or more
Amber wastes is subject to the Amber
control procedures.
In this proposed rule, EPA has revised
the text in § 262.82(a) to clarify that only
those wastes and waste mixtures
considered hazardous under U.S.
national regulations will be subject to
the Amber control procedures within
the United States. This is consistent
with longstanding EPA policy, and
should minimize confusion for the
regulated community. For example,
under the existing RCRA hazardous
waste regulations, any mixture of an
Amber waste that exhibits one or more
of the hazardous characteristics of
ignitability, corrosivity, reactivity, or
toxicity under RCRA with a Green waste
shall be considered an Amber waste if
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the mixture still exhibits one or more of
the RCRA hazardous waste
characteristics and, thus, be subject to
the Amber control procedures.
Conversely, if the resulting mixture no
longer exhibits one or more of the RCRA
hazardous characteristics, it will instead
be considered a Green waste, and be
subject to the Green control procedures.
Because other OECD Member
countries may require that the mixtures
listed above (that the U.S. sometimes
considers subject to the Green control
procedures) be subject to Amber control
procedures, the proposed rule includes
notes stating that other OECD Member
countries may subject such mixtures to
the Amber control procedures. In such
cases, U.S. importers and exporters
should be prepared to follow the Amber
control procedures within those OECD
Member countries.
Finally, the Amended 2001 OECD
Decision requires that notification for a
transboundary movement of a mixture
of hazardous wastes falling under the
Amber control procedures should be
made by the person performing the
mixing activity (the generator of the
mixture) or any other person acting as
an exporter in place of the person
performing the mixing activity. In the
notification, relevant information on
each fraction of the waste, including its
code numbers, has to be given in order
of importance. This proposed rule
would impose these requirements.
10. New Provisions Regarding the
Return and Re-Export of Hazardous
Wastes Subject to the Amber Control
Procedures
This proposed rule proposes to adopt
the Amended 2001 OECD Decision’s
more precise provisions (than the earlier
1992 Decision) on measures to be taken
in case a transboundary movement of
hazardous waste that is subject to the
Amber control procedures cannot be
completed as intended (e.g., not in
accordance with the notification,
consents given by the competent
authorities, or the terms of the contract).
There may be a number of reasons for
this non-completion, for example, an
accident during the transport of the
waste, improper notification, or any
illegal action taken by someone
involved with the movement of the
hazardous waste.
The Amended 2001 OECD Decision
provides that if this uncompleted
movement of hazardous waste (hereafter
referred to as the ‘‘incident’’), takes
place in the country of import, the
competent authority of that country
shall immediately inform the competent
authority of the country of export. The
competent authorities of the concerned
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countries are to cooperate in resolving
the incident by making all necessary
arrangements to ensure the best
alternative management of the
hazardous waste. If alternative
arrangements cannot be made to recover
these wastes in an environmentally
sound manner in the country of import,
the hazardous waste must be returned to
the country of export or re-exported to
a third country.
(a) Return of Hazardous Waste to
Country of Export
Under the Amended 2001 OECD
Decision, the return of the hazardous
waste to the country of export is to take
place within ninety (90) days from the
time when the country of export was
informed of the incident, or such other
period of time to which all concerned
countries agree. The competent
authorities of both countries of export
and transit (if applicable) are to be
informed about the return of the
hazardous waste and the reasons for its
return. These authorities are prohibited
from opposing or preventing the return
of the hazardous waste to the country of
export, so long as the movement
complies with the requirements set out
by the country of export’s domestic law.
If the waste is returned through a new
country of transit, the competent
authority of that country is to be
notified and consent obtained in
accordance with the normal Amber
control procedures.
(b) Re-Export of Hazardous Waste From
the Country of Import to a Third
Country
Under the Amended 2001 OECD
Decision, the re-export from the country
of import to a third country is
considered a new transboundary
movement of hazardous waste. As a
result, the Amber control procedures are
applicable. The initial importer becomes
the new exporter and, consequently,
assumes all responsibilities as an
exporter. In addition, the notification
must also include the competent
authority of the initial country of export
who, in accordance with the Amber
control procedures, may object to the reexport if the movement does not comply
with the requirements set out by its
domestic law.
(c) Return of Hazardous Waste From
Country of Transit to Country of Export
If the incident takes place in the
country of transit, the exporter should
make arrangements so that the
hazardous waste still can be recovered
in an environmentally sound manner in
the recovery facility of the importing
country to where it was originally
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destined. The competent authority of
the country of transit is to immediately
inform the competent authorities of the
countries of export and import and any
other countries of transit. If the exporter
is unable to arrange for the recovery of
the hazardous waste in an
environmentally sound manner at the
recovery facility to where it was
originally destined, the hazardous waste
should be returned, adhering to
subsection (a) above, to the country of
export within ninety (90) days from the
time when the country of export was
informed of the incident or such other
period of time as the concerned
countries agree. The competent
authorities of the country of export and
the countries of transit are to be
informed of the return, but they are
prohibited from opposing or preventing
the return of the hazardous wastes to the
country of export, so long as the
movement complies with the
requirements set out by the country of
export’s domestic law. This proposal
sets forth these re-export and return
provisions of the Amended 2001 OECD
Decision in §§ 262.82(c), 262.82(d), and
262.82(e).
11. SLABs Are Now Covered by EPA’s
OECD Rule
This proposed rule updates
§ 262.80(a) to reflect that export
shipments of SLABs being managed
under 40 CFR part 266, subpart G that
are destined for recovery in one of the
OECD countries listed in § 262.58(a)(1)
are subject to 40 CFR part 262, subpart
H.
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12. Technical Corrections to EPA’s
OECD Rule
This proposed rule makes several
technical corrections to EPA’s current
OECD rule, including corrections to
capitalization, syntax, and punctuation
errors. In these changes, EPA is not
making any substantive revisions, but is
seeking to eliminate any confusion on
the part of the regulated community by
striving for consistency both within the
regulations and with the terms of the
Amended 2001 OECD Decision. Some
prevalent examples of these types of
revisions include changing ‘‘Subpart’’ to
‘‘subpart,’’ ‘‘OECD member’’ to ‘‘OECD
Member,’’ and ‘‘thirty days’’ to ‘‘thirty
(30) days.’’
13. Change to the Submittal Address for
Exception Reports
This proposed rule amends the
exception reporting requirements in
§ 262.87(b) to specify that all exception
reports are to be submitted to the Office
of Enforcement and Compliance
Assurance’s Office of Federal Activities
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in Washington, DC rather than the
Administrator.
D. Changes to 40 CFR 264.12(a)(2) and
40 CFR 265.12(a)(2)
This proposed rule also amends
§§ 264.12(a)(2) and 265.12(a)(2) by,
among other things, requiring owners or
operators of recovery facilities to submit
a certificate of recovery as soon as
possible after the recovery is completed,
but no later than thirty (30) days after
the completion of recovery and no later
than one (1) calendar year following the
receipt of the hazardous waste.
E. Changes to 40 CFR 264.71(a)(3) and
40 CFR 265.71(a)(3)
This proposed rule also amends
§§ 264.71(a)(3) and 265.71(a)(3) by
requiring owners or operators of
facilities receiving imported hazardous
wastes to submit to EPA the written
documentation of EPA’s consent to the
import along with a copy of the RCRA
hazardous waste manifest for the
shipment that they are currently
required to submit to EPA within thirty
(30) days of shipment delivery. This
will enable EPA to match the individual
shipment manifest to the consent for an
annual notice from a foreign exporter.
F. Changes to 40 CFR 266.80(a)
The existing regulations at 40 CFR
part 266, subpart G, ‘‘Spent Lead-Acid
Batteries Being Reclaimed,’’ exempt
exporters of SLABs destined for
reclamation from the export
requirements of 40 CFR part 262. EPA
proposes to amend the table located at
40 CFR 266.80 by including two
additional rows to the current table.
These additional rows will effectively
require that exporters and transporters
of SLABs being sent to a foreign country
for reclamation will need to meet the
universal waste requirements
concerning the export of SLABs for
reclamation.
Specifically, exporters would need to
either comply with the requirements in
40 CFR part 262, subpart H when the
shipments are destined to one of the
OECD Member countries listed in
§ 262.58(a)(1), or with the following
requirements when the shipments are
destined for any country not listed in
§ 262.58(a)(1):
• Comply with the requirements
applicable to a primary exporter in 40
CFR 262.53, 262.56(a)(1) through (4),
(6), and (b) and 262.57;
• Export such SLABs only upon
consent of the receiving country and in
conformance with the EPA
Acknowledgement of Consent as
defined in subpart E of 40 CFR part 262
of this chapter; and
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• Provide a copy of the EPA
Acknowledgment of Consent for the
shipment to the transporter transporting
the shipment for export.
The transporter of SLABs being sent
to a foreign country for reclamation
would need to comply with the
applicable requirements in 40 CFR part
262, subpart H when the shipments are
destined to one of the OECD Member
countries listed in § 262.58(a)(1). For
export shipments of SLABs not destined
for one of the OECD Member countries
listed in § 262.58(a)(1), the transporter
would not be able to accept a shipment
if the transporter knows the shipment
does not conform to the EPA
Acknowledgment of Consent, and
would have to ensure that:
• A copy of the EPA
Acknowledgment of Consent
accompanies the shipment; and
• The shipment is delivered to the
foreign facility designated by the person
initiating the shipment.
EPA proposes to amend the table
located at 40 CFR 266.80 in order to
ensure greater protection of human
health and the environment through
notification, tracking, and management
of SLABs. In addition to harmonizing
the RCRA hazardous waste regulations
for SLABs with the notification and
consent requirements in the RCRA
universal waste rules, today’s proposed
rule would harmonize the export
requirements for SLABs with the
Amended 2001 OECD Decision and the
Basel Convention. (Note that the
exemption from the manifest
requirements for exporters and
transporters of SLABs for reclamation
will continue to remain in effect.)
The table located at 40 CFR 266.80
describes the various kinds of SLAB
handlers and their respective legal
requirements. Some SLAB handlers may
find that more than one description
located in the table applies to their
SLAB management activities. It is the
SLAB handler’s responsibility to read
all seven descriptions and carefully
consider any and all requirements
which may apply.
1. Export Shipments of SLABs to OECD
Member Countries
We are proposing that exporters and
transporters of SLABs destined for
reclamation in one of the OECD Member
countries listed in § 262.58(a)(1) would
have to comply with all applicable
sections of 40 CFR part 262, subpart H
for wastes subject to the Amber control
procedures. For a complete listing of the
proposed requirements, exporters and
transporters should consult the
regulatory text for 40 CFR part 262,
subpart H in this proposal. In addition
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to the proposed changes to subpart H
discussed in earlier sections, the
applicable Amber control procedures
include, but are not limited to, the
following:
(a) Notification of Intent To Export
Exporters of SLABs destined for
reclamation would be required to
comply with the Amber control
procedures in § 262.83. Under the
Amber control procedures, an exporter
must submit a complete notification of
its intent to export to EPA at least 45
days before the export is scheduled to
leave the United States (or at least ten
days if the shipment is going to a preapproved facility in the country of
import). The notification can cover
export activities spanning a period of up
to and including 12 months (or up to
three years if the shipment is going to
a pre-approved facility in the country of
import).
A complete notification includes, but
is not limited to:
• Contact information and EPA ID
number (if applicable) for the exporter;
• Point of departure from country of
export;
• A waste description and quantity of
the hazardous waste being exported;
• The RCRA waste code(s) (if
applicable), United Nations number,
and OECD waste code for the hazardous
waste (SLABs are classified as Amber
waste A1160 under the Amended 2001
OECD Decision);
• Planned mode(s) of transportation;
• Contact information for all intended
transporters;
• Contact information and the OECD
recovery operation code(s) (e.g., R1–
R13) for both the importer and the final
recovery facility (if different sites);
• The requested period of
exportation;
• A list of all transit countries, along
with points of entry and departure,
through which the hazardous waste will
be sent, and
• A certification by the exporter that
a contract or chain of contracts or
equivalent arrangements among all
parties to the proposed shipment are in
place and are legally enforceable in all
concerned countries.
If the notification is complete, EPA
will forward it to the importing country
and any transit country(ies). Within
three working days of receiving the
notification, the importing country must
send either an Acknowledgement of
Receipt or a list of items that the
notification lacks directly to U.S. EPA,
to the exporter, and to any countries of
transit. The countries of import and
transit have thirty (30) days from the
date on the Acknowledgement of
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Receipt (seven days for shipments going
to pre-approved facilities) to object or
consent explicitly to the proposed
shipment. Any explicit objection or
consent by the country of import or
transit will be sent simultaneously to
U.S. EPA, the exporter, and any other
interested country (e.g., of import or
transit). If no objections are submitted
within the thirty day (30) period (seven
days for shipments going to preapproved facilities), under the
provisions of the Amended 2001 OECD
Decision, tacit (or implied) consent is
assumed and the movement of the
hazardous wastes may commence.
(b) Shipment Tracking
Under § 262.84, export shipments of
SLABs must be accompanied by a
movement document from the initiation
of the shipment until it reaches the final
recovery facility. Exporters must
provide the initial transporter with the
movement document. Transporters are
prohibited from accepting a shipment of
SLABs without such a movement
document, and are required to ensure
that the movement document
accompanies the shipment from the
initiation of the shipment until it
reaches the final recovery facility. The
movement document must include all
the information from the notification
and the following:
• Date movement commenced;
• Name (if not the exporter), address,
telephone and fax numbers, and e-mail
of person originating the movement
document (Note that this person is
equivalent to the primary exporter
under 40 CFR part 262, subpart E);
• Company name and EPA ID number
(if applicable) of all transporters;
• Identification (license, registered
name or registration number) of means
of transport, including types of
packaging envisaged;
• Any special precautions to be taken
by transporter(s) during transportation;
• Certification/declaration signed by
the exporter that no objection to the
shipment has been lodged; and
• Appropriate signatures for each
custody transfer (e.g., transporter,
importer, and owner or operator of the
recovery facility).
(c) Annual Reporting
Under § 262.87(a), any person
exporting SLABs who meets the
definition of primary exporter in
§ 262.51 or who initiates the movement
documentation under § 262.84 will have
to submit to the Office of Enforcement
and Compliance Assurance’s Office of
Federal Activities in Washington, DC,
an annual report summarizing the types,
quantities, frequency, and ultimate
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58401
destination of all SLABs exported
during the previous calendar year.
Reports are due by March 1st of every
year.
(d) Exception Reporting
Under § 262.87(b), any person
exporting SLABs who meets the
definition of primary exporter in
§ 262.51 or who initiates the movement
documentation under § 262.84 must file
an exception report with the Office of
Enforcement and Compliance
Assurance, Office of Federal Activities,
International Compliance Assurance
Division (2254A), Environmental
Protection Agency, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460, if
any of the following occurs:
• He has not received a copy of the
RCRA hazardous waste manifest signed
by the transporter and noting the date
and point of departure of the waste from
the United States, within forty-five (45)
days from the date it was accepted by
the initial transporter;
• Within ninety (90) days from the
date the waste was accepted by the
initial transporter, the exporter has not
received written confirmation from the
recovery facility that the hazardous
waste was received;
• The waste is returned to the United
States.
(e) Recordkeeping
Under § 262.87(c), any person
exporting SLABs who meets the
definition of primary exporter in
§ 262.51 or who initiates the movement
documentation under § 262.84 must
keep the following records:
• A copy of each notification of intent
to export and all written consents
obtained from the competent authorities
of countries concerned (e.g., export,
transit, and import) for a period of at
least three (3) years from the date the
hazardous waste was accepted by the
initial transporter;
• A copy of each annual report for a
period of at least three (3) years from the
due date of the report;
• A copy of any exception reports and
a copy of each confirmation of delivery
(i.e., movement documentation) sent by
the recovery facility to the exporter for
at least three (3) years from the date the
hazardous waste was accepted by the
initial transporter or received by the
recovery facility, whichever is
applicable; and
• A copy of each confirmation of
recovery sent by the recovery facility to
the exporter for at least three (3) years
from the date that the recovery facility
completed the processing of the SLAB
shipment.
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(a) Notification of Intent To Export
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2. Export Shipments of SLABs to
Countries Not Listed in § 262.58(a)(1)
We are proposing that exporters of
SLABs must provide a copy of the EPA
Acknowledgment of Consent for the
SLAB shipment to the transporter
transporting the shipment for export.
Transporters are prohibited from
accepting a SLAB export shipment if the
transporter knows the shipment does
not conform to the EPA
Acknowledgment of Consent. In
addition the transporter must ensure
that:
• A copy of the EPA
Acknowledgment of Consent
accompanies the SLAB export
shipment; and
• The SLAB export shipment is
delivered to the facility designated by
the person initiating the shipment.
Unlike SLAB export shipments that
must comply with 40 CFR part 262,
subpart H, SLAB export shipments
destined for countries not listed in
§ 252.58(a)(1) do not have any shipment
tracking documentation requirements or
exception reporting requirements
because SLAB shipments are exempt
from the RCRA hazardous waste
manifest requirements.
We are proposing that exporters of
SLABs destined for reclamation in
countries not listed in § 262.58(a)(1)
would be required to comply with the
primary exporter notification
requirements in § 262.53, and export the
SLABs only upon consent of the
receiving country and in conformance
with the EPA Acknowledgement of
Consent, as defined in 40 CFR part 262,
subpart E. Specifically, the exporter
would have to submit a complete
notification of its intent to export to
EPA at least 60 days before the export
is scheduled to leave the United States.
The notification can cover export
activities spanning a period of up to and
including 12 months. This complete
notification contains:
• Contact information and EPA ID
number (if applicable) for the primary
exporter;
• A description and quantity of the
SLABs to be exported;
• The RCRA waste code(s) (if
applicable), U.S. DOT proper shipping
name, hazard class, and United Nations
number as identified in 49 CFR parts
171 through 177;
• Planned mode(s) of transportation
and type(s) of containers;
• A description of the manner in
which the SLABs will be treated, stored,
or disposed of (including recovery) in
the receiving country;
• The planned frequency and time
period of exportation;
• A list of all transit countries
through which the SLABs will be sent,
and a description of the approximate
length of time the hazardous waste will
remain in each country and the nature
of its handling while there;
• All points of entry to and departure
from each foreign country through
which the SLABs will pass; and
• The name and site address of the
consignee 15 and any alternate
consignee.
If after proper notification, the
receiving country consents to the receipt
of the hazardous waste, EPA will
forward an EPA Acknowledgment of
Consent to the exporter. If, on the other
hand, the receiving country objects to
the receipt of the hazardous waste or
withdraws a prior consent, EPA will
notify the exporter in writing. EPA will
also notify the exporter of any responses
from transit countries.
15 As noted previously, this is equivalent to
‘‘importer’’ in the proposed revisions to 40 CFR part
262, subpart H.
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(c) Annual Reporting
We are proposing that exporters of
SLABs must follow the requirements
applicable to a primary exporter
detailed in § 262.56 ‘‘Annual reports’’
(a)(1) through (4), (6), and (b).
Specifically, exporters will have to file
with the EPA Administrator an annual
report summarizing the types,
quantities, frequency, and ultimate
destination of all SLABs exported
during the previous calendar year.
Reports are due by March 1st of every
year.
(d) Recordkeeping
Under § 262.57, we are proposing that
exporters of SLABs must keep the
following records:
• A copy of each notification of intent
to export for at least three years from the
date the SLAB export shipment was
accepted by the initial transporter;
• A copy of each EPA
Acknowledgment of Consent for at least
three years from the date the SLAB
export shipment was accepted by the
initial transporter;
• A copy of each confirmation of
delivery of the SLAB shipment from the
consignee for at least three years from
the date the SLAB export shipment was
accepted by the initial transporter; and
• A copy of each annual report for at
least three years from the due date of the
report.
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G. Changes to 40 CFR 271.1
This proposed rule amends Table 1
and Table 2 of § 271.1 by adding
references to the revisions which amend
40 CFR part 262, subpart E to reflect that
subpart E implements the Hazardous
and Solid Waste Amendments of 1984.
IV. Costs and Benefits of the Proposed
Rule
A. Introduction
The value of any regulatory action is
traditionally measured by the net
change in social welfare that it
generates. The Agency’s economic
assessment conducted in support of this
proposed action evaluates costs, cost
savings, benefits, and other impacts,
such as environmental justice,
children’s health, unfunded mandates,
regulatory takings, and small entity
impacts. To conduct this analysis, we
developed and implemented a
methodology for examining impacts,
and followed appropriate guidelines
and procedures for examining equity
considerations, children’s health, and
other impacts.
B. Analytical Scope
This analysis assesses the proposed
integration of various OECD Council
Decisions into existing U.S. regulations
governing shipments (export/import/
transit) of hazardous wastes destined for
recovery between the U.S. and other
OECD Member countries. In addition,
we assess the newly proposed export
regulations for SLABs to OECD and nonOECD countries. Also incorporated into
the analysis is the proposed
requirements that importers of
hazardous waste subject to 40 CFR part
262, subpart F, provide to the initial
transporter documentation necessary to
confirm EPA’s consent to the import to
accompany such manifested import
shipments, and that the receiving
facility submit to EPA a copy of that
documentation when it submits to EPA
the RCRA hazardous waste manifest for
the import shipment. Finally, this action
proposes a revision to the current
language in §§ 262.55 and 262.87(b) that
will require exception reports to be
submitted directly to the Director,
International Compliance and
Assurance Division (ICAD), of the Office
of Enforcement and Compliance
Assurance (OECA), EPA Headquarters,
rather than to the EPA Administrator.
There is no discernable cost impact
associated with this proposed
requirement for exception reports to be
submitted directly to the Director.
First, we assess all potential cost
impacts (positive and negative) of the
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proposed revisions to the OECD rule,
including:
• Exemptions for wastes destined for
laboratory analyses,
• The requirement to provide a
certificate of recovery,
• Information collection requirements
associated with exchange and
accumulation recovery operations, and
• The notification requirements
related to the return of wastes.
Next, we assess all potential cost
impacts (positive and negative) of the
proposed revisions to the SLAB
regulations, including:
• Notification requirements for SLAB
exporters,
• The renotification requirements
associated with any changes to the
original SLAB export notification,
• The annual reporting requirements,
• Additional reporting requirements
(if requested by EPA), and
• SLAB exporter recordkeeping
requirements.
Finally, we analyze the proposed
requirements that importers of
hazardous waste subject to 40 CFR part
262, subpart F, provide to the initial
transporter documentation necessary to
confirm EPA’s consent to the import to
accompany such manifested import
shipments, and that the receiving
facility submit to EPA a copy of that
documentation when it submits to EPA
the RCRA hazardous waste manifest for
the import shipment.
We also include an estimate for
potentially affected entities to read the
regulation, which is, by default, a
necessary requirement for
understanding the regulation. Cost
impacts associated with reading the
regulation are assessed for exporters,
importers, and transporters.
C. Cost Impacts
The total incremental cost for the
OECD portion of the proposed rule
during the first year of implementation
(i.e., including reading the rule) is
estimated to be $14,472. This is a net
impact estimate that includes a total net
incremental cost increase to the
regulated community of $13,634, and a
total net cost increase to EPA of $838.
The total incremental annual net cost
for the OECD portion after the first year
of implementation (i.e., excluding
reading the rules) is estimated to be
$9,678.
The total incremental cost for the
SLAB portion of the proposed rule
during the first year of implementation
(i.e., including reading the rule) is
estimated at $851,000. The first year
total incremental cost is expected to be
about $780,000 for the affected U.S.
industry and about $71,000 for EPA.
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The total incremental annual cost after
the first year of implementation (i.e.,
excluding reading the rules) is estimated
to be $404,000.
The combined total cost of the
proposed rule (OECD portion, plus
SLAB portion, plus import consent
documentation portion) is estimated at
$919,000 for the first year.
Approximately 92.5% of this total is
attributable to the SLAB portion of the
proposal, followed by the EPA import
consent documentation requirements
representing about 5.9% of the total.
The OECD portion accounts for about
1.6% of the total first year cost of the
proposal. After the first year, the total
incremental cost of the proposed
rulemaking, omitting the cost of reading
the rules, is estimated at $468,000.
Cost estimates presented in this
section are based on our estimates for
the number of potentially affected
importers, exporters, and transporters.
Numerous data sources were used in the
derivation of these estimates, including:
RCRAInfo, the Waste International
Tracking System (WITS), industry
consultations, the Biennial Report, the
International Trade Commission (ITC),
Environment Canada, and
SEMARNAT 16 data. A full explanation
of the data sources, analytical
methodology, assumptions, and
limitations associated with the findings
presented above is presented in our Cost
Assessment 17 document prepared in
support of this proposed action. This
document is available in the docket.
Interested stakeholders are encouraged
to read and comment on the analysis
and findings presented in this
document.
D. Benefits
We have prepared a qualitative
assessment of the benefits anticipated
from this action. Overall, this action is
expected to result in improved
regulatory efficiency of the affected
materials, while ensuring improved data
collection and enhanced enforcement
capabilities. Specific benefits include
the following:
• The U.S. would meet its legal
obligations to implement the Amended
2001 OECD Decision.
• Increased regulatory efficiency by
implementing provisions in the
Amended 2001 OECD Decision that
were meant to clarify the scope of
control and make the control procedures
more precise.
16 Secretarıa de Medio Ambiente y Recursos
´
Naturales (SEMARNAT).
17 Cost Assessment for the Proposed Rule on
Exports and Imports of Hazardous Waste Destined
for Recovery Among OECD Countries and Exports
of Spent Lead-Acid Batteries from the U.S.
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• Helping to improve market
efficiency by allowing exporters to ship
wastes more quickly and store for
shorter periods of time.
• Encouraging the environmentally
sound recovery of hazardous wastes,
thereby reducing the risks associated
with treatment and disposal.
• Providing for the improved ability
to acquire information regarding the
quantities of SLABs exported from the
U.S. and the destination facilities to
which the SLABs are exported.
V. State Authorization
A. Applicability of Rules 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
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
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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
non-HSWA, that are considered less
stringent than previous federal
regulations.
B. Effect on State Authorization
Because of the Federal government’s
special role in matters of foreign policy,
EPA cannot authorize States to
administer Federal import/export
functions in any section of the RCRA
hazardous waste regulations. This
promotes national coordination,
uniformity and the expeditious
transmission of information between the
United States and foreign countries.
Although States do not receive
authorization to administer the Federal
government’s functions in subparts E or
F, in accordance with 271.10, the State
program must include requirements
respecting international shipments
equivalent to those at subparts E and F.
States are also not authorized to
administer the Federal government’s
functions in subpart H, but in this case,
States are not required to adopt those
provisions. However, EPA would
encourage States to incorporate all the
import and export related requirements
into their regulations for the
convenience of the regulated
community and for completeness,
particularly where a State has already
incorporated 40 CFR part 262, subparts
E, F and H, the import manifest
submittal requirements in 264.71(a)(3)
and 265.71(a)(3), or the domestic
management provisions for SLABs in 40
CFR part 266, subpart G. If or when a
State chooses to adopt these import/
export provisions, when final, care
should be taken not to replace Federal
or international references with State
terms. Moreover, if finalized, the
provisions of today’s notice would take
effect in all States upon the effective
date of the final rule.
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VI. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order (EO) 12866
(58 FR 51735, October 4, 1993), this
action is a ‘‘significant regulatory
action.’’ This action may raise novel
legal or policy issues [3(f)(4)] arising out
of legal mandates, although it is not
economically significant. Accordingly,
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EPA submitted this action to the Office
of Management and Budget (OMB) for
review under EO 12866. Any changes
made in response to OMB’s
recommendations have been
documented in the docket for this
action.
This rule, as proposed, is projected to
result in a net increase in costs to
certain importers, exporters, and
transporters of affected hazardous
wastes. Increased costs are also
projected for the federal government.
The total net cost of this proposal is
estimated to be $919,000 during the first
year following rule implementation.
Exporters are projected to account for
approximately 68 percent of this total.
Benefits of this action include the U.S.
meeting its legal obligations to
implement the Amended 2001 OECD
Decision, increased regulatory
efficiency, reduced risks associated with
the treatment and disposal of hazardous
wastes, and improved data collection.
The total net cost estimate for this
proposal is significantly below the $100
million threshold 18 established under
part 3(f)(1) of the Order. Thus, this
proposal is not considered to be an
economically significant action.
However, in an effort to comply with
the spirit of the Order, we have
prepared an economic assessment 19 in
support of this proposed rule. The
RCRA docket established for today’s
rulemaking maintains a copy of this
document for public review. Interested
persons are encouraged to read and
comment on this document.
B. Paperwork Reduction Act
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 2308.01.
The proposal requires that the
affected sources submit the following:
• Under the proposed OECD
revisions: U.S. recovery facilities will
have to submit a certificate of recovery
to the foreign exporter, and to the
competent authority of the country of
export and EPA, as soon as possible, but
no later than thirty (30) days after the
completion of recovery and no later
than one (1) calendar year following
18 This $100 million threshold applies to both
costs, and cost savings.
19 Cost Assessment for the Proposed Rule on
Exports and Imports of Hazardous Waste Destined
for Recovery Among OECD Countries and Exports
of Spent Lead-Acid Batteries from the U.S. (Cost
Assessment).
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receipt of waste; U.S. facilities that
exchange or accumulate the waste
shipments (e.g., R12/R13 facilities)
before final recovery at another facility
(e.g., R1–R11 facilities) will have to
prepare and provide a certificate of
recovery for R12/R13 recovery
operations, and provide and maintain a
copy of the certificate of recovery for the
subsequent R1–R11 recovery operations;
U.S. recovery facilities that cannot
complete the intended recovery and
must re-export or otherwise return the
hazardous waste shipment will have to
submit new notification documents and
comply with the associated Amber
control procedures; and U.S. exporters
will have to keep records of the
additional certifications of recovery and
any R12/R13 certifications they receive
from recovery facilities in other OECD
countries.
• Under the proposed SLAB
revisions: SLAB exporters will have to:
Comply with the full subpart H
requirements if going to countries listed
in § 262.58(a)(1) (e.g., submitting
notices, originating a movement
document for each shipment, keeping
records of all confirmations of receipt
and recovery they receive, submitting
exception reports and annual reports,
and recordkeeping); and comply with
portions of the subpart E requirements
if going elsewhere (e.g., submitting
notices, providing a copy of EPA’s
Acknowledgement of Consent for each
shipment, submitting annual reports
and recordkeeping).
• Under the proposed import
documentation revisions: U.S. receiving
facilities will have to submit to EPA
copies of documentation confirming
EPA’s consent to the import each time
they submit to EPA a copy of the RCRA
hazardous waste manifest for each
hazardous waste import shipment
within thirty (30) days of shipment
delivery.
All affected sources will have to
retain records of this paperwork for a
period of three years, which is
consistent with the RCRA hazardous
waste requirements of §§ 262.53, 262.56,
262.57, 262.83, 262.87, 264.71 and
265.71. The collection of the requested
information is mandatory, as it is
needed by EPA as a part of its overall
compliance and enforcement program
for the protection of human health and
the environment.
The estimated annual public reporting
burden for the new paperwork
requirements in the proposed rule is
approximately 4.62 hours/year per
respondent under the proposed OECD
revisions; 20.73 hours/year per
respondent under the proposed SLAB
revisions; and 9.15 hours/year per
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respondent under the proposed import
consent documentation. The annual
public recordkeeping burden is
estimated to average 10.20 hours/year
per respondent under the proposed
OECD revisions, and 0.25 hours/year
per respondent under the proposed
SLAB revisions. The total annual public
burden is estimated to be 15,077 hours
and $840,500 during the first year of
implementation, and 9,024 hours and
$389,600 after the first year. The capital
and start-up plus total operation and
maintenance costs are expected to be
negligible. Burden is defined at 5 CFR
1320.3(b).
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, EPA has established
a public docket for this rule, which
includes this ICR, under Docket ID
number EPA–HQ–RCRA–2005–0018.
Submit any comments related to the ICR
to EPA and OMB. See ADDRESSES
section at the beginning of this notice
for where to submit comments 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 Office for EPA.
Since OMB is required to make a
decision concerning the ICR between 30
and 60 days after October 6, 2008, a
comment to OMB is best assured of
having its full effect if OMB receives it
by November 5, 2008. 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)
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 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
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CFR 121.201; (2) a small governmental
jurisdiction that is a 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-for-profit
enterprise which is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of today’s proposed rule on
small entities, I certify that this action
will not have a significant economic
impact on a substantial number of small
entities. 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. The primary purpose of the
regulatory flexibility analyses is to
identify and address regulatory
alternatives ‘‘which minimize any
significant economic impact of the 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.
We have determined that a substantial
number of potentially affected small
businesses (importers, exporters, and
transporters) will not experience
significant negative economic impacts.
For the purpose of our impact analyses,
small business is defined either by the
number of employees or by the dollar
amount of sales. The level at which a
business is considered small is
determined for each North American
Industrial Classification System
(NAICS) code by the Small Business
Administration. No small governmental
jurisdiction or small not-for-profit
organizations are expected to be affected
by this action, as proposed.
While a significant number of
exporters may be small businesses, the
results of our analysis indicate that the
cost to individual small entities in each
potentially affected sector (as identified
by NAICS codes) is likely to be
insignificant. Our analysis specifically
examined the potentially impacted
small companies with fewer than 20
employees. The average annual gross
sales of these companies were found to
range from $0.4 million to $4.1 million,
depending upon NAICS sector. The
annual compliance costs for these
companies, as a percentage of average
annual gross sales, was found to range
from 0.01 percent to 0.08 percent.
The reader is encouraged to review
our regulatory flexibility screening
analysis prepared in support of this
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determination. This analysis is
incorporated into the Cost Assessment,
which is available in the docket
established for this 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.
D. Unfunded Mandates Reform Act of
1995
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.
This proposal contains no Federal
mandates (under the regulatory
provisions of Title II of the UMRA) for
State, local, or tribal governments, or the
private sector, in large part because the
UMRA does not apply to rules that are
necessary for the national security or the
ratification or implementation of
international treaty obligations (e.g., the
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Amended 2001 OECD Decision). In any
event, EPA has determined that this
rule, as proposed, does not contain a
Federal mandate that may result in
expenditures of $100 million or more
for State, local, and tribal governments,
in the aggregate, or the private sector in
any one year. The total cost impacts of
this proposed action are estimated to be
$919,000 during the first year, and
approximately $468,000 per year
thereafter.
Finally, EPA has determined that this
rule contains no regulatory
requirements that might significantly or
uniquely affect small governments.
Small governments are not affected by
this action, as proposed.
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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
rule does not have Federalism
implications because the State and local
governments do not administer the
export and import requirements under
RCRA. Thus, Executive Order 13132
does not apply to this rule.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and State and local governments, EPA
specifically solicits comment on this
proposed rule from State and local
officials.
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
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regulatory policies that have tribal
implications.’’ This proposed rule does
not have tribal implications, as specified
in Executive Order 13175. No Tribal
governments are known to own or
operate businesses that may be affected
by this proposal. Thus, Executive Order
13175 does not apply to this proposed
rule. EPA specifically solicits additional
comment on our determination under
this Order and on this proposed rule
from tribal officials.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
Executive Order 13045, entitled
‘‘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
preferable to other potentially effective
and reasonably feasible alternatives
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
residing in the United States.
H. Executive Order 13211: Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use
This proposed rule is not a
‘‘significant energy action’’ as defined in
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355 (May
22, 2001)) because it is not likely to
have a significant adverse effect on the
supply, distribution, or use of energy.
This rule, as proposed, will not
seriously disrupt energy supply,
distribution patterns, prices, imports or
exports. In fact, this proposed rule is
designed to improve regulatory
efficiency and improve information
collection, in part by implementing
technical corrections and clarifications
to the existing regulations.
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I. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, 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 rulemaking does not
involve technical standards. Therefore,
EPA is not considering the use of any
voluntary consensus standards.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order (EO) 12898 (59 FR
7629 (Feb. 16, 1994)) establishes federal
executive policy on environmental
justice. Its main provision directs
federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
EPA has determined that this
proposed rule will not have
disproportionately high and/or adverse
human health or environmental effects
on minority or low-income populations
because it does not directly affect the
level of protection provided to human
health or the environment. This
proposal is designed to improve
regulatory efficiency and improve
information collection, in part by
implementing technical corrections and
clarifications to the existing regulations.
List of Subjects
40 CFR Part 262
Environmental protection, Exports,
Hazardous materials transportation,
Hazardous waste, Imports, International
organizations, Labeling, Packaging and
containers, Recycling, Reporting and
recordkeeping requirements.
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40 CFR Part 264
Environmental protection, Hazardous
waste, Imports, Packaging and
containers, Reporting and recordkeeping
requirements.
40 CFR Part 265
Environmental protection, Hazardous
waste, Imports, Packaging and
containers, Reporting and recordkeeping
requirements.
40 CFR Part 266
Environmental protection, Exports,
Spent Lead-Acid Batteries, Recycling,
Waste treatment and disposal.
40 CFR Part 271
Environmental protection,
Administrative practice and procedure,
Hazardous materials transportation,
Hazardous waste, Intergovernmental
relations, Penalties, Reporting and
recordkeeping requirements.
Dated: September 19, 2008.
Stephen L. Johnson,
Administrator.
For the reasons stated in the
preamble, title 40, chapter 1 of the Code
of Federal Regulations is proposed to be
amended as follows.
PART 262—STANDARDS APPLICABLE
TO GENERATORS OF HAZARDOUS
WASTE
1. The authority citation for part 262
continues to read as follows:
Authority: 42 U.S.C. 6906, 6912, 6922–
6925, 6937, and 6938.
2. 262.55 is amended by revising the
introductory text to read as follows:
§ 262.55
Exception reports.
In lieu of the requirements of
§ 262.42, a primary exporter must file an
exception report with the Office of
Enforcement and Compliance
Assurance, Office of Federal Activities,
International Compliance Assurance
Division (2254A), Environmental
Protection Agency, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460, if
any of the following occurs:
*
*
*
*
*
3. Section 262.58 is revised to read as
follows:
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§ 262.58
International agreements.
(a) Any person who exports or
imports hazardous waste subject to the
Federal manifest requirements of part
262, or subject to the universal waste
management standards of 40 CFR part
273, or subject to State requirements
analogous to 40 CFR part 273, or exports
spent lead-acid batteries subject to the
spent lead-acid battery management
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standards of 40 CFR part 266, subpart G
or subject to State requirements
analogous to 40 CFR part 266, subpart
G, to or from designated Member
countries of the Organization for
Economic Cooperation and
Development (OECD) as defined in
paragraph (a)(1) of this section for
purposes of recovery is subject to
subpart H of this part. The requirements
of subparts E and F of this part do not
apply to such exports and imports.
(1) For the purposes of subpart H, the
designated OECD Member countries
consist of Australia, Austria, Belgium,
the Czech Republic, Denmark, Finland,
France, Germany, Greece, Hungary,
Iceland, Ireland, Italy, Japan,
Luxembourg, the Netherlands, New
Zealand, Norway, Poland, Portugal, the
Slovak Republic, South Korea, Spain,
Sweden, Switzerland, Turkey, the
United Kingdom, and the United States.
(2) For the purposes of subpart H of
this part, Canada and Mexico are
considered OECD Member countries
only for the purpose of transit.
(b) Any person who exports
hazardous waste to or imports
hazardous waste from: A designated
OECD Member country for purposes
other than recovery (e.g., incineration,
disposal), Mexico (for any purpose), or
Canada (for any purpose) remains
subject to the requirements of subparts
E and F of this part, and is not subject
to the requirements of subpart H of this
part.
4. Section 262.60(e) is revised to read
as follows:
*
*
*
*
*
(e) The importer must provide the
transporter with an additional copy of
the manifest and documentation
confirming EPA’s consent to the import
of hazardous waste to be submitted by
the receiving facility to U.S. EPA in
accordance with § 264.71(a)(3) and
§ 265.71(a)(3) of this chapter.
5. Subpart H is revised to read as
follows:
Subpart H—Transboundary Movements of
Hazardous Waste for Recovery Within the
OECD
Sec.
262.80 Applicability.
262.81 Definitions.
262.82 General conditions.
262.83 Notification and consent.
262.84 Movement document.
262.85 Contracts.
262.86 Provisions relating to recognized
traders.
262.87 Reporting and recordkeeping.
262.88 Pre-approval for U.S. recovery
facilities [Reserved].
262.89 OECD waste lists.
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Subpart H—Transboundary
Movements of Hazardous Waste for
Recovery Within the OECD
§ 262.80
Applicability.
(a) The requirements of this subpart
apply to imports and exports of wastes
that are considered hazardous under
U.S. national procedures and are
destined for recovery operations in the
countries listed in § 262.58(a)(1). A
waste is considered hazardous under
U.S. national procedures if it meets the
Federal definition of hazardous waste in
40 CFR 261.3 and it is subject to either
the Federal manifesting requirements at
40 CFR part 262, subpart B, to the
universal waste management standards
of 40 CFR part 273 or to State
requirements analogous to 40 CFR part
273, or for exports only, if the waste is
subject to 40 CFR part 266, subpart G or
to State requirements analogous to 40
CFR part 266, subpart G.
(b) Any person (exporter, importer, or
recovery facility operator) who mixes
two or more wastes (including
hazardous and non-hazardous wastes)
or otherwise subjects two or more
wastes (including hazardous and nonhazardous wastes) to physical or
chemical transformation operations, and
thereby creates a new hazardous waste,
becomes a generator and assumes all
subsequent generator duties under
RCRA and any exporter duties, if
applicable, under this subpart.
§ 262.81
Definitions.
The following definitions apply to
this subpart.
(a) Competent authority means the
regulatory authority or authorities of
concerned countries having jurisdiction
over transboundary movements of
wastes destined for recovery operations.
(b) Countries concerned means the
OECD Member countries of export or
import and any OECD Member
countries of transit.
(c) Country of export means any
designated OECD Member country
listed in § 262.58(a)(1) from which a
transboundary movement of hazardous
wastes is planned to be initiated or is
initiated.
(d) Country of import means any
designated OECD Member country
listed in § 262.58(a)(1) to which a
transboundary movement of hazardous
wastes is planned or takes place for the
purpose of submitting the wastes to
recovery operations therein.
(e) Country of transit means any
designated OECD Member country
listed in § 262.58(a)(1) and (a)(2) other
than the country of export or country of
import across which a transboundary
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movement of hazardous wastes is
planned or takes place.
(f) Exporter means the person under
the jurisdiction of the country of export
who has, or will have at the time the
planned transboundary movement
commences, possession or other forms
of legal control of the wastes and who
proposes transboundary movement of
the hazardous wastes for the ultimate
purpose of submitting them to recovery
operations. When the United States
(U.S.) is the country of export, exporter
is interpreted to mean a person
domiciled in the United States.
(g) Importer means the person to
whom possession or other form of legal
control of the waste is assigned at the
time the waste is received in the country
of import.
(h) OECD area means all land or
marine areas under the national
jurisdiction of any OECD Member
country listed in § 262.58. When the
regulations refer to shipments to or from
an OECD Member country, this means
OECD area.
(i) OECD means the Organization for
Economic Cooperation and
Development.
(j) OECD Decision means the OECD
‘‘Decision of the Council C(2001)107/
FINAL, Concerning the Control of
Transboundary Movements of Wastes
Destined for Recovery Operations, as
Amended by C(2004)20.’’
(k) Recognized trader means a person
who, with appropriate authorization of
countries concerned, acts in the role of
principal to purchase and subsequently
sell wastes; this person has legal control
of such wastes from time of purchase to
time of sale; such a person may act to
arrange and facilitate transboundary
movements of wastes destined for
recovery operations.
(l) Recovery facility means a facility
which, under applicable domestic law,
is operating or is authorized to operate
in the country of import to receive
wastes and to perform recovery
operations on them.
(m) Recovery operations means
activities leading to resource recovery,
recycling, reclamation, direct re-use or
alternative uses, which include:
R1 Use as a fuel (other than in direct
incineration) or other means to
generate energy
R2 Solvent reclamation/regeneration
R3 Recycling/reclamation of organic
substances which are not used as
solvents
R4 Recycling/reclamation of metals
and metal compounds
R5 Recycling/reclamation of other
inorganic materials
R6 Regeneration of acids or bases
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R7
Recovery of components used for
pollution abatement
R8 Recovery of components used from
catalysts
R9 Used oil re-refining or other reuses
of previously used oil
R10 Land treatment resulting in
benefit to agriculture or ecological
improvement
R11 Uses of residual materials
obtained from any of the operations
numbered R1–R10
R12 Exchange of wastes for
submission to any of the operations
numbered R1–R11
R13 Accumulation of material
intended for any operation
numbered R1–R12
(n) Transboundary movement means
any movement of wastes from an area
under the national jurisdiction of one
OECD Member country to an area under
the national jurisdiction of another
OECD Member country.
§ 262.82
General conditions.
(a) Scope. The level of control for
exports and imports of waste is
indicated by assignment of the waste to
either a list of wastes subject to the
Green control procedures or a list of
wastes subject to the Amber control
procedures and by the national
procedures of the United States, as
defined in § 262.80(a). The two lists
correspond to Appendices 3 and 4,
respectively, of the OECD Decision and
have been incorporated by reference in
§ 262.89(d).
(1) Listed wastes subject to the Green
control procedures.
(i) Green wastes that are not
considered hazardous under U.S.
national procedures as defined in
§ 262.80(a) are subject to existing
controls normally applied to
commercial transactions.
(ii) Green wastes that are considered
hazardous under U.S. national
procedures as defined in § 262.80(a) are
subject to the Amber control procedures
set forth in this subpart.
(2) Listed wastes subject to the Amber
control procedures.
(i) Amber wastes that are considered
hazardous under U.S. national
procedures as defined in § 262.80(a) are
subject to the Amber control procedures
set forth in this subpart.
(ii) Amber wastes that are considered
hazardous under U.S. national
procedures as defined in § 262.80(a), are
subject to the Amber control procedures
in the United States, even if they are
imported to or exported from a
designated OECD Member country
listed in § 262.58(a)(1) that does not
consider the waste to be hazardous. In
such an event, the responsibilities of the
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Amber control procedures shift as
provided:
(A) For U.S. exports, the United States
shall issue an acknowledgement of
receipt and assume other
responsibilities of the competent
authority of the country of import.
(B) For U.S. imports, the U.S. recovery
facility/importer and the United States
shall assume the obligations associated
with the Amber control procedures that
normally apply to the exporter and
country of export, respectively.
(iii) Amber wastes that are not
considered hazardous under U.S.
national procedures as defined in
§ 262.80(a), but are considered
hazardous by an OECD Member country
are subject to the Amber control
procedures in the OECD Member
country that considers the waste
hazardous. All responsibilities of the
U.S. importer/exporter shift to the
importer/exporter of the OECD Member
country that considers the waste
hazardous unless the parties make other
arrangements through contracts.
Note to paragraph (a)(2): Some wastes
subject to the Amber control procedures are
not listed or otherwise identified as
hazardous under RCRA, and therefore are not
subject to the Amber control procedures of
this subpart. Regardless of the status of the
waste under RCRA, however, other Federal
environmental statutes (e.g., the Toxic
Substances Control Act) restrict certain waste
imports or exports. Such restrictions
continue to apply with regard to this subpart.
(3) Procedures for mixtures of wastes.
(i) A Green waste that is mixed with
one or more other Green wastes such
that the resulting mixture is not
considered hazardous under U.S.
national procedures as defined in
§ 262.80(a) shall be subject to the Green
control procedures, provided the
composition of this mixture does not
impair its environmentally sound
recovery.
Note to paragraph (a)(3)(i): The regulated
community should note that some OECD
Member countries may require, by domestic
law, that mixtures of different Green wastes
be subject to the Amber control procedures.
(ii) A Green waste that is mixed with
one or more Amber wastes, in any
amount, de minimis or otherwise, or a
mixture of two or more Amber wastes,
such that the resulting waste mixture is
considered hazardous under U.S.
national procedures as defined in
§ 262.80(a) are subject to the Amber
control procedures, provided the
composition of this mixture does not
impair its environmentally sound
recovery.
Note to paragraph (a)(3)(ii): The regulated
community should note that some OECD
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Member countries may require, by domestic
law, that a mixture of a Green waste and
more than a de minimis amount of an Amber
waste or a mixture of two or more Amber
wastes be subject to the Amber control
procedures.
(4) Wastes not yet assigned to an
OECD waste list are eligible for
transboundary movements, as follows:
(i) If such wastes are considered
hazardous under U.S. national
procedures as defined in § 262.80(a),
such wastes are subject to the Amber
control procedures.
(ii) If such wastes are not considered
hazardous under U.S. national
procedures as defined in § 262.80(a),
such wastes are subject to the Green
control procedures.
(b) General conditions applicable to
transboundary movements of hazardous
waste: (1) The waste must be destined
for recovery operations at a facility that,
under applicable domestic law, is
operating or is authorized to operate in
the importing country;
(2) The transboundary movement
must be in compliance with applicable
international transport agreements; and
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Note to paragraph (b)(2): These
international agreements include, but are not
limited to, the Chicago Convention (1944),
ADR (1957), ADNR (1970), MARPOL
Convention (1973/1978), SOLAS Convention
(1974), IMDG Code (1985), COTIF (1985), and
RID (1985).
(3) Any transit of waste through a
non-OECD Member country must be
conducted in compliance with all
applicable international and national
laws and regulations.
(c) Provisions relating to re-export for
recovery to a third country: (1) Reexport of wastes subject to the Amber
control procedures from the United
States, as the country of import, to a
third country listed in § 262.58(a)(1)
may occur only after an exporter in the
United States provides notification to
and obtains consent from the competent
authorities in the third country, the
original country of export, and new
transit countries. The notification must
comply with the notice and consent
procedures in § 262.83 for all countries
concerned and the original country of
export. The competent authorities of the
original country of export, as well as the
competent authorities of all other
countries concerned have thirty (30)
days to object to the proposed
movement.
(i) The thirty (30) day period begins
once the competent authorities of both
the initial country of export and new
country of import issue
Acknowledgements of Receipt of the
notification.
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(ii) The transboundary movement may
commence if no objection has been
lodged after the thirty (30) day period
has passed or immediately after written
consent is received from all relevant
OECD importing and transit countries.
(2) In the case of re-export of Amber
wastes to a country other than those
listed in § 262.58(a)(1), notification to
and consent of the competent
authorities of the original OECD
Member country of export and any
OECD Member countries of transit is
required as specified in paragraph (c)(1)
of this section, in addition to
compliance with all international
agreements and arrangements to which
the first importing OECD Member
country is a party and all applicable
regulatory requirements for exports from
the first country of import.
(d) Duty to return or re-export wastes
subject to the Amber control procedures.
When a transboundary movement of
wastes subject to the Amber control
procedures cannot be completed in
accordance with the terms of the
contract or the consent(s) and
alternative arrangements cannot be
made to recover the waste in an
environmentally sound manner in the
country of import, the waste must be
returned to the country of export or reexported to a third country. The
provisions of paragraph (c) of this
section apply to any shipments to be reexported to a third country. The
following provisions apply to shipments
to be returned to the country of export
as appropriate:
(1) Return from the United States to
the country of export: The U.S. importer
must inform EPA at the specified
address in § 262.83(b)(1)(i) of the need
to return the shipment. EPA will then
inform the competent authorities of the
countries of export and transit, citing
the reason(s) for returning the waste.
The U.S. importer must complete the
return within ninety (90) days from the
time EPA informs the country of export
of the need to return the waste, unless
informed in writing by EPA of another
timeframe agreed to by the concerned
Member countries. If the return
shipment will cross any new transit
country, the return shipment may only
occur after EPA provides notification to
and obtains consent from the competent
authority of the new country of transit,
and provides a copy of that consent to
the U.S. importer.
(2) Return from the country of import
to the United States: The U.S. exporter
must provide for the return of the
hazardous waste shipment within
ninety (90) days from the time the
country of import informs EPA of the
need to return the waste or such other
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58409
period of time as the concerned Member
countries agree. The U.S. exporter must
submit an exception report to EPA in
accordance with § 262.87(b).
(e) Duty to return wastes subject to the
Amber control procedures from a
country of transit. When a
transboundary movement of wastes
subject to the Amber control procedures
does not comply with the requirements
of the notification and movement
documents or otherwise constitutes
illegal shipment, and if alternative
arrangements cannot be made to recover
these wastes in an environmentally
sound manner, the waste must be
returned to the country of export. The
following provisions apply as
appropriate:
(1) Return from the United States (as
country of transit) to the country of
export: The U.S. transporter must
inform EPA at the specified address in
§ 262.83(b)(1)(i) of the need to return the
shipment. EPA will then inform the
competent authority of the country of
export, citing the reason(s) for returning
the waste. The U.S. transporter must
complete the return within ninety (90)
days from the time EPA informs the
country of export of the need to return
the waste, unless informed in writing by
EPA of another timeframe agreed to by
the concerned Member countries.
(2) Return from the country of transit
to the United States (as country of
export): The U.S. exporter must provide
for the return of the hazardous waste
shipment within ninety (90) days from
the time the competent authority of the
country of transit informs EPA of the
need to return the waste or such other
period of time as the concerned Member
countries agree. The U.S. exporter must
submit an exception report to EPA in
accordance with § 262.87(b).
(f) Requirements for wastes destined
for and received by R12 and R13
facilities. The transboundary movement
of wastes destined for R12 and R13
operations must comply with all Amber
control procedures for notification and
consent as set forth in § 262.83 and for
the movement document as set forth in
§ 262.84. Additional responsibilities of
R12/R13 facilities include:
(1) Indicating in the notification
document the foreseen recovery facility
or facilities where the subsequent R1–
R11 recovery operation takes place or
may take place.
(2) Within three (3) days of the receipt
of the wastes by the R12/R13 recovery
facility or facilities, the facility(ies) shall
return a signed copy of the movement
document to the exporter and to the
competent authorities of the countries of
export and import. The facility(ies) shall
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retain the original of the movement
document for three (3) years.
(3) As soon as possible, but no later
than thirty (30) days after the
completion of the R12/R13 recovery
operation and no later than one (1)
calendar year following the receipt of
the waste, the R12 or R13 facility(ies)
shall send a certificate of recovery to the
foreign exporter and to the competent
authority of the country of export and to
the Office of Enforcement and
Compliance Assurance, Office of
Federal Activities, International
Compliance Assurance Division
(2254A), Environmental Protection
Agency, 1200 Pennsylvania Avenue,
NW., Washington, DC 20460, by mail,
e-mail without digital signature
followed by mail, or fax followed by
mail.
(4) When an R12/R13 recovery facility
delivers wastes for recovery to an R1–
R11 recovery facility located in the
country of import, it shall obtain as soon
as possible, but no later than one (1)
calendar year following delivery of the
waste, a certification from the R1–R11
facility that recovery of the wastes at
that facility has been completed. The
R12/R13 facility must promptly transmit
the applicable certification to the
competent authorities of the countries of
import and export, identifying the
transboundary movements to which the
certification pertain.
(5) When an R12/R13 recovery facility
delivers wastes for recovery to an R1–
R11 recovery facility located:
(i) in the initial country of export,
Amber control procedures apply,
including a new notification;
(ii) in a third country other than the
initial country of export, Amber control
procedures apply, with the additional
provision that the competent authority
of the initial country of export shall also
be notified of the transboundary
movement.
(g) Laboratory analysis exemption.
The transboundary movement of an
Amber waste is exempt from the Amber
control procedures if it is in certain
quantities and destined for laboratory
analysis to assess its physical or
chemical characteristics, or to determine
its suitability for recovery operations.
The quantity of such waste shall be
determined by the minimum quantity
reasonably needed to perform the
analysis in each particular case
adequately, but in no case exceed
twenty-five kilograms (25 kg). Waste
destined for laboratory analysis must
still be appropriately packaged and
labeled.
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Jkt 217001
§ 262.83
Notification and consent.
(a) Applicability. Consent must be
obtained from the competent authorities
of the relevant OECD countries of
import and transit prior to exporting
hazardous waste destined for recovery
operations subject to this subpart.
Hazardous wastes subject to the Amber
control procedures are subject to the
requirements of paragraph (b) of this
section; and wastes not identified on
any list are subject to the requirements
of paragraph (c) of this section.
(b) Amber wastes. Exports of
hazardous wastes from the United States
as described in § 262.80(a) that are
subject to the Amber control procedures
are prohibited unless the notification
and consent requirements of paragraph
(b)(1) or paragraph (b)(2) of this section
are met.
(1) Transactions requiring specific
consent:
(i) Notification. At least forty-five (45)
days prior to commencement of each
transboundary movement, the exporter
must provide written notification in
English of the proposed transboundary
movement to the Office of Enforcement
and Compliance Assurance, Office of
Federal Activities, International
Compliance Assurance Division
(2254A), Environmental Protection
Agency, 1200 Pennsylvania Avenue,
NW., Washington, DC 20460, with the
words ‘‘Attention: OECD Export
Notification’’ prominently displayed on
the envelope. This notification must
include all of the information identified
in paragraph (d) of this section. In cases
where wastes having similar physical
and chemical characteristics, the same
United Nations classification, the same
RCRA waste codes, and are to be sent
periodically to the same recovery
facility by the same exporter, the
exporter may submit one general
notification of intent to export these
wastes in multiple shipments during a
period of up to one (1) year. Even when
a general notification is used for
multiple shipments, each shipment still
must be accompanied by its own
movement document pursuant to
§ 262.84.
(ii) Tacit consent. If no objection has
been lodged by any concerned country
(i.e., exporting, importing, or transit) to
a notification provided pursuant to
paragraph (b)(1)(i) of this section within
thirty (30) days after the date of issuance
of the Acknowledgement of Receipt of
notification by the competent authority
of the country of import, the
transboundary movement may
commence. Tacit consent expires one
(1) calendar year after the close of the
thirty (30) day period; renotification and
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renewal of all consents is required for
exports after that date.
(iii) Written consent. If the competent
authorities of all the relevant OECD
importing and transit countries provide
written consent in a period less than
thirty (30) days, the transboundary
movement may commence immediately
after all necessary consents are received.
Written consent expires for each
relevant OECD importing and transit
country one (1) calendar year after the
date of that country’s consent unless
otherwise specified; renotification and
renewal of each expired consent is
required for exports after that date.
(2) Transboundary movements to
facilities pre-approved by the competent
authorities of the importing countries to
accept specific wastes for recovery:
(i) Notification. The exporter must
provide EPA a notification that contains
all the information identified in
paragraph (d) of this section in English,
at least ten (10) days in advance of
commencing shipment to a preapproved facility. The notification must
indicate that the recovery facility is preapproved, and may apply to a single
specific shipment or to multiple
shipments as described in paragraph
(b)(1)(i) of this section. This information
must be sent to the Office of
Enforcement and Compliance
Assurance, Office of Federal Activities,
International Compliance Assurance
Division (2254A), Environmental
Protection Agency, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460,
with the words ‘‘OECD Export
Notification—Pre-approved Facility’’
prominently displayed on the envelope.
General notifications that cover multiple
shipments as described in paragraph
(b)(1)(i) of this section may cover a
period of up to three (3) years. Even
when a general notification is used for
multiple shipments, each shipment still
must be accompanied by its own
movement document pursuant to
§ 262.84.
(ii) Exports to pre-approved facilities
may take place after the elapse of seven
(7) working days from the issuance of an
Acknowledgement of Receipt of the
notification by the competent authority
of the country of import unless the
exporter has received information
indicating that the competent authority
of any concerned country objects to the
shipment.
(c) Wastes not covered in Appendices
3 and 4 of the OECD Decision. Wastes
destined for recovery operations, that
have not been assigned to Appendices 3
or 4 of the OECD Decision, but which
are considered hazardous under U.S.
national procedures as defined in
§ 262.80(a), are subject to the
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notification and consent requirements
established for the Amber control
procedures in accordance with
paragraph (b) of this section. Wastes
destined for recovery operations, that
have not been assigned to Appendices 3
or 4 of the OECD Decision, and are not
considered hazardous under U.S.
national procedures as defined by
§ 262.80(a) are subject to the Green
control procedures.
(d) Notifications submitted under this
section must include the information
specified in paragraphs (d)(1) through
(d)(14) of this section:
(1) Serial number or other accepted
identifier of the notification document;
(2) Exporter name and EPA
identification number (if applicable),
address, telephone and fax numbers,
and e-mail address;
(3) Importing recovery facility name,
address, telephone and fax numbers, email address, and technologies
employed;
(4) Importer name (if not the owner or
operator of the recovery facility),
address, telephone and fax numbers,
and e-mail address; whether the
importer will engage in waste exchange
or storage, meeting the definition of R12
or R13 recovery operations in
§ 262.81(m), prior to delivering the
waste to the final recovery facility and
identification of recovery operations to
be employed at the final recovery
facility;
(5) Intended transporter(s) and/or
their agent(s); address, telephone, fax,
and e-mail address;
(6) Country of export and relevant
competent authority, and point of
departure;
(7) Countries of transit and relevant
competent authorities and points of
entry and departure;
(8) Country of import and relevant
competent authority, and point of entry;
(9) Statement of whether the
notification is a single notification or a
general notification. If general, include
period of validity requested;
(10) Date(s) foreseen for
commencement of transboundary
movement(s);
(11) Means of transport envisaged;
(12) Designation of waste type(s) from
the appropriate list (Part I or II of
Appendix 3 or 4) of the OECD Decision,
description(s) of each waste type,
estimated total quantity of each, RCRA
waste code, and the United Nations
number for each waste type;
(13) Specification of the recovery
operation(s) according to § 262.81(m).
(14) Certification/Declaration signed
by the exporter that states:
I certify that the above information is
complete and correct to the best of my
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18:15 Oct 03, 2008
Jkt 217001
knowledge. I also certify that legallyenforceable written contractual
obligations have been entered into, and
that any applicable insurance or other
financial guarantees are or shall be in
force covering the transboundary
movement.
Name: lllllllllllllll
Signature: lllllllllllll
Date: llllllllllllllll
Note to Paragraph (d)(14): The United
States does not currently require financial
assurance for these waste shipments.
However, U.S. exporters may be asked by
other governments to provide and certify to
such assurance as a condition of obtaining
consent to a proposed movement.
(e) Certificate of Recovery. As soon as
possible, but no later than thirty (30)
days after the completion of recovery
and no later than one (1) calendar year
following receipt of the waste, the U.S.
recovery facility shall send a certificate
of recovery to the exporter and to the
competent authorities of the countries of
export and import by mail, e-mail
without a digital signature followed by
mail, or fax followed by mail.
§ 262.84
Movement document.
(a) All U.S. parties subject to the
contract provisions of § 262.85 must
ensure that a movement document
meeting the conditions of paragraph (b)
of this section accompanies each
transboundary movement of wastes
subject to the Amber control procedures
from the initiation of the shipment until
it reaches the final recovery facility,
including cases in which the waste is
stored and/or sorted by the importer
prior to shipment to the final recovery
facility, except as provided in
paragraphs (a)(1) and (2) of this section.
(1) For shipments of hazardous waste
within the United States solely by water
(bulk shipments only), the generator
must forward the movement document
with the manifest to the last water (bulk
shipment) transporter to handle the
waste in the United States if exported by
water (in accordance with the manifest
routing procedures at § 262.23(c)).
(2) For rail shipments of hazardous
waste within the United States which
originate at the site of generation, the
generator must forward the movement
document with the manifest (in
accordance with the routing procedures
for the manifest in § 262.23(d)) to the
next non-rail transporter, if any, or the
last rail transporter to handle the waste
in the United States if exported by rail.
(b) The movement document must
include all information required under
§ 262.83 (for notification), as well as the
following paragraphs (b)(1) through
(b)(7) of this section:
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(1) Date movement commenced;
(2) Name (if not exporter), address,
telephone and fax numbers, and e-mail
of primary exporter;
(3) Company name and EPA ID
number of all transporters;
(4) Identification (license, registered
name or registration number) of means
of transport, including types of
packaging envisaged;
(5) Any special precautions to be
taken by transporter(s);
(6) Certification/declaration signed by
the exporter that no objection to the
shipment has been lodged as follows:
I certify that the above information is
complete and correct to the best of my
knowledge. I also certify that legallyenforceable written contractual
obligations have been entered into, that
any applicable insurance or other
financial guarantees are or shall be in
force covering the transboundary
movement, and that:
1. All necessary consents have been
received; OR
2. The shipment is directed to a
recovery facility within the OECD area
and no objection has been received from
any of the countries concerned within
the thirty (30) day tacit consent period;
OR
3. The shipment is directed to a
recovery facility pre-authorized for that
type of waste within the OECD area;
such an authorization has not been
revoked, and no objection has been
received from any of the countries
concerned.
(Delete sentences that are not
applicable)
Name: lllllllllllllll
Signature: lllllllllllll
Date: llllllllllllllll
(7) Appropriate signatures for each
custody transfer (e.g., transporter,
importer, and owner or operator of the
recovery facility).
(c) Exporters also must comply with
the special manifest requirements of 40
CFR 262.54(a), (b), (c), (e), and (i) and
importers must comply with the import
requirements of 40 CFR part 262,
subpart F.
(d) Each U.S. person that has physical
custody of the waste from the time the
movement commences until it arrives at
the recovery facility must sign the
movement document (e.g., transporter,
importer, and owner or operator of the
recovery facility).
(e) Within three (3) working days of
the receipt of imports subject to this
subpart, the owner or operator of the
U.S. recovery facility must send signed
copies of the movement document to
the exporter, to the Office of
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Enforcement and Compliance
Assurance, Office of Federal Activities,
International Compliance Assurance
Division (2254A), Environmental
Protection Agency, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460,
and to the competent authorities of the
countries of export and transit. If the
concerned U.S. recovery facility is a
R12/R13 recovery facility under
§ 262.81(m), the facility shall retain the
original of the movement document for
three (3) years.
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§ 262.85
Contracts.
(a) Transboundary movements of
hazardous wastes subject to the Amber
control procedures are prohibited unless
they occur under the terms of a valid
written contract, chain of contracts, or
equivalent arrangements (when the
movement occurs between parties
controlled by the same corporate or
legal entity). Such contracts or
equivalent arrangements must be
executed by the exporter and the owner
or operator of the recovery facility, and
must specify responsibilities for each.
Contracts or equivalent arrangements
are valid for the purposes of this section
only if persons assuming obligations
under the contracts or equivalent
arrangements have appropriate legal
status to conduct the operations
specified in the contract or equivalent
arrangements.
(b) Contracts or equivalent
arrangements must specify the name
and EPA ID number, where available, of
paragraph (b)(1) through (b)(4) of this
section:
(1) The generator of each type of
waste;
(2) Each person who will have
physical custody of the wastes;
(3) Each person who will have legal
control of the wastes; and
(4) The recovery facility.
(c) Contracts or equivalent
arrangements must specify which party
to the contract will assume
responsibility for alternate management
of the wastes if their disposition cannot
be carried out as described in the
notification of intent to export. In such
cases, contracts must specify that:
(1) The person having actual
possession or physical control over the
wastes will immediately inform the
exporter and the competent authorities
of countries of export and import and,
if the wastes are located in a country of
transit, the competent authorities of that
country; and
(2) The person specified in the
contract will assume responsibility for
the adequate management of the wastes
in compliance with applicable laws and
regulations including, if necessary,
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arranging the return of wastes and, as
the case may be, shall provide the
notification for re-export.
(d) Contracts must specify that the
importer will provide the notification
required in § 262.82(c) prior to the reexport of controlled wastes to a third
country.
(e) Contracts or equivalent
arrangements must include provisions
for financial guarantees, if required by
the competent authorities of any
concerned country, in accordance with
applicable national or international law
requirements.
Note to Paragraph (e): Financial guarantees
so required are intended to provide for
alternate recycling, disposal or other means
of sound management of the wastes in cases
where arrangements for the shipment and the
recovery operations cannot be carried out as
foreseen. The United States does not require
such financial guarantees at this time;
however, some OECD Member countries do.
It is the responsibility of the exporter to
ascertain and comply with such
requirements; in some cases, transporters or
importers may refuse to enter into the
necessary contracts absent specific references
or certifications to financial guarantees.
(f) Contracts or equivalent
arrangements must contain provisions
requiring each contracting party to
comply with all applicable requirements
of this subpart.
(g) Upon request by EPA, U.S.
exporters, importers, or recovery
facilities must submit to EPA copies of
contracts, chain of contracts, or
equivalent arrangements (when the
movement occurs between parties
controlled by the same corporate or
legal entity). Information contained in
the contracts or equivalent arrangements
for which a claim of confidentiality is
asserted in accordance with 40 CFR
2.203(b) will be treated as confidential
and will be disclosed by EPA only as
provided in 40 CFR 260.2.
Note to Paragraph (g): Although the United
States does not require routine submission of
contracts at this time, the OECD Decision
allows Member countries to impose such
requirements. When other OECD Member
countries require submission of partial or
complete copies of the contract as a
condition to granting consent to proposed
movements, EPA will request the required
information; absent submission of such
information, some OECD Member countries
may deny consent for the proposed
movement.
§ 262.86
traders.
Provisions relating to recognized
(a) A recognized trader who takes
physical custody of a waste and
conducts recovery operations (including
storage prior to recovery) is acting as the
owner or operator of a recovery facility
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and must be so authorized in
accordance with all applicable Federal
laws.
(b) A recognized trader acting as an
exporter or importer for transboundary
shipments of waste must comply with
all the requirements of this subpart
associated with being an exporter or
importer.
§ 262.87
Reporting and recordkeeping.
(a) Annual reports. For all waste
movements subject to this subpart,
persons (e.g., exporters, recognized
traders) who meet the definition of
primary exporter in § 262.51 or who
initiate the movement documentation
under § 262.84 shall file an annual
report with the Office of Enforcement
and Compliance Assurance, Office of
Federal Activities, International
Compliance Assurance Division
(2254A), Environmental Protection
Agency, 1200 Pennsylvania Avenue,
NW., Washington, DC 20460, no later
than March 1 of each year summarizing
the types, quantities, frequency, and
ultimate destination of all such
hazardous waste exported during the
previous calendar year. (If the primary
exporter or the person who initiates the
movement documentation under
§ 262.84 is required to file an annual
report for waste exports that are not
covered under this subpart, he may
include all export information in one
report provided the following
information on exports of waste
destined for recovery within the
designated OECD Member countries is
contained in a separate section.) Such
reports shall include all of the following
paragraphs (a)(1) through (a)(6) of this
section specified as follows:
(1) The EPA identification number,
name, and mailing and site address of
the exporter filing the report;
(2) The calendar year covered by the
report;
(3) The name and site address of each
final recovery facility;
(4) By final recovery facility, for each
hazardous waste exported, a description
of the hazardous waste, the EPA
hazardous waste number (from 40 CFR
part 261, subpart C or D), designation of
waste type(s) and applicable waste
code(s) from the appropriate OECD
waste list (Appendices 3 or 4 of the
OECD Decision), DOT hazard class, the
name and U.S. EPA identification
number (where applicable) for each
transporter used, the total amount of
hazardous waste shipped pursuant to
this subpart, and number of shipments
pursuant to each notification;
(5) In even numbered years, for each
hazardous waste exported, except for
hazardous waste produced by exporters
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of greater than 100kg but less than
1000kg in a calendar month, and except
for hazardous waste for which
information was already provided
pursuant to § 262.41:
(i) A description of the efforts
undertaken during the year to reduce
the volume and toxicity of the waste
generated; and
(ii) A description of the changes in
volume and toxicity of the waste
actually achieved during the year in
comparison to previous years to the
extent such information is available for
years prior to 1984; and
(6) A certification signed by the
person acting as primary exporter or
initiator of the movement
documentation under § 262.84 that
states:
I certify under penalty of law that I
have personally examined and am
familiar with the information submitted
in this and all attached documents, and
that based on my inquiry of those
individuals immediately responsible for
obtaining the information, I believe that
the submitted information is true,
accurate, and complete. I am aware that
there are significant penalties for
submitting false information including
the possibility of fine and
imprisonment.
(b) Exception reports. Any person
who meets the definition of primary
exporter in § 262.51 or who initiates the
movement documentation under
§ 262.84 must file an exception report in
lieu of the requirements of § 262.42 (if
applicable) with the Office of
Enforcement and Compliance
Assurance, Office of Federal Activities,
International Compliance Assurance
Division (2254A), Environmental
Protection Agency, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460, if
any of the following occurs:
(1) He has not received a copy of the
RCRA hazardous waste manifest (if
applicable) signed by the transporter
identifying the point of departure of the
waste from the United States, within
forty-five (45) days from the date it was
accepted by the initial transporter;
(2) Within ninety (90) days from the
date the waste was accepted by the
initial transporter, the exporter has not
received written confirmation from the
recovery facility that the hazardous
waste was received;
(3) The waste is returned to the
United States.
(c) Recordkeeping. (1) Persons who
meet the definition of primary exporter
in § 262.51 or who initiate the
movement documentation under
§ 262.84 shall keep the following
records paragraphs (c)(1)(i) through
(c)(1)(iv) of this section:
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(i) A copy of each notification of
intent to export and all written consents
obtained from the competent authorities
of countries concerned for a period of at
least three (3) years from the date the
hazardous waste was accepted by the
initial transporter;
(ii) A copy of each annual report for
a period of at least three (3) years from
the due date of the report;
(iii) A copy of any exception reports
and a copy of each confirmation of
delivery (i.e., movement
documentation) sent by the recovery
facility to the exporter for at least three
(3) years from the date the hazardous
waste was accepted by the initial
transporter or received by the recovery
facility, whichever is applicable; and
(iv) A copy of each confirmation of
recovery sent by the recovery facility to
the exporter for at least three (3) years
from the date that the recovery facility
completed processing the waste
shipment.
(2) The periods of retention referred to
in this section are extended
automatically during the course of any
unresolved enforcement action
regarding the regulated activity or as
requested by the Administrator.
§ 262.88 Pre-approval for U.S. recovery
facilities [Reserved]
§ 262.89
OECD waste lists.
(a) General. For the purposes of this
subpart, a waste is considered
hazardous under U.S. national
procedures, and hence subject to this
subpart, if the waste:
(1) Meets the Federal definition of
hazardous waste in 40 CFR 261.3; and
(2) Is subject to either the Federal
RCRA manifesting requirements at 40
CFR part 262, subpart B, to the universal
waste management standards of 40 CFR
part 273, to State requirements
analogous to 40 CFR part 273, to the
export requirements in the spent leadacid battery management standards of
40 CFR part 266, subpart G, or to State
requirements analogous to the export
requirements in 40 CFR part 266,
subpart G.
(b) If a waste is hazardous under
paragraph (a) of this section, it is subject
to the Amber control procedures,
regardless of whether it appears in
Appendix 4 of the OECD Decision.
(c) The appropriate control
procedures for hazardous wastes and
hazardous waste mixtures are addressed
in § 262.82.
(d) The OECD waste lists, entitled
‘‘List of Wastes Subject to the Green
Control Procedure’’ and ‘‘List of Wastes
Subject to the Amber Control
Procedure,’’ are set forth in Appendix 3
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58413
and Appendix 4, respectively, of the
OECD Decision. These lists are
incorporated by reference. These
incorporations by reference were
approved by the Director of the Federal
Register in accordance with 5 U.S.C.
552(a) and 1 CFR part 51 on [date of
approval for incorporation by reference].
These materials are incorporated as they
exist on the date of the approval and a
notice of any change in these materials
will be published in the Federal
Register. The materials are available for
inspection at: the U.S. Environmental
Protection Agency, Docket Center Public
Reading Room, EPA West, Room 3334,
1301 Constitution Avenue, NW.,
Washington, DC 20004 (Docket # EPA–
HQ–RCRA–2005–0018) or at the
National Archives and Records
Administration (NARA), and may be
obtained from the Organization for
Economic Cooperation and
Development, Environment Directorate,
´
2 rue Andre Pascal, F–75775 Paris
Cedex 16, France. For information on
the availability of this material at
NARA, call 202–741–6030, or go to:
https://www.archives.gov/federalregister/cfr/ibr-locations.html.
PART 264—STANDARDS FOR
OWNERS AND OPERATORS OF
HAZARDOUS WASTE TREATMENT,
STORAGE, AND DISPOSAL
FACILITIES
6. The authority citation for part 264
continues to read as follows:
Authority: 42 U.S.C. 6905, 6912(a), 6924,
and 6925.
7. Section 264.12(a)(2) is revised to
read as follows:
§ 264.12
Required notices.
(a)(1) * * *
(2) The owner or operator of a
recovery facility that has arranged to
receive hazardous waste subject to 40
CFR part 262, subpart H must provide
a copy of the movement document
bearing all required signatures to the
foreign exporter; to the Office of
Enforcement and Compliance
Assurance, Office of Federal Activities,
International Compliance Assurance
Division (2254A), Environmental
Protection Agency, 1200 Pennsylvania
Avenue. NW., Washington, DC 20460;
and to the competent authorities of all
other countries concerned within three
(3) working days of receipt of the
shipment. The original of the signed
movement document must be
maintained at the facility for at least
three (3) years. In addition, such owner
or operator shall, as soon as possible,
but no later than thirty (30) days after
the completion of recovery and no later
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than one (1) calendar year following the
receipt of the hazardous waste, send a
certificate of recovery to the foreign
exporter and to the competent authority
of the country of export and to EPA’s
Office of Enforcement and Compliance
Assurance at the above address by mail,
e-mail without a digital signature
followed by mail, or fax followed by
mail.
*
*
*
*
*
8. Section 264.71(a)(3) is revised to
read as follows:
§ 264.71
Use of manifest system.
(a)(1) * * *
(3) If a facility receives hazardous
waste imported from a foreign source,
the receiving facility must mail a copy
of the manifest and documentation
confirming EPA’s consent to the import
of hazardous waste to the following
address within thirty (30) days of
delivery: Office of Enforcement and
Compliance Assurance, Office of
Federal Activities, International
Compliance Assurance Division
(2254A), Environmental Protection
Agency, 1200 Pennsylvania Avenue,
NW., Washington, DC 20460.
*
*
*
*
*
PART 265—INTERIM STATUS
STANDARDS FOR OWNERS AND
OPERATORS OF HAZARDOUS WASTE
TREATMENT, STORAGE, AND
DISPOSAL FACILITIES
9. The authority citation for part 265
continues to read as follows:
Authority: 42 U.S.C. 6905, 6906, 6912,
6922, 6923, 6924, 6925, 6935, 6936, and
6937.
10. Section 265.12(a)(2) is revised to
read as follows:
followed by mail, or fax followed by
mail.
*
*
*
*
*
11. Section 265.71(a)(3) is revised to
read as follows:
§ 265.12
§ 265.71
Required notices.
(a)(1) * * *
(2) The owner or operator of a
recovery facility that has arranged to
receive hazardous waste subject to 40
CFR part 262, subpart H must provide
a copy of the movement document
bearing all required signatures to the
foreign exporter; to the Office of
Enforcement and Compliance
Assurance, Office of Federal Activities,
International Compliance Assurance
Division (2254A), Environmental
Protection Agency, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460;
and to the competent authorities of all
other countries concerned within three
(3) working days of receipt of the
shipment. The original of the signed
movement document must be
maintained at the facility for at least
three (3) years. In addition, such owner
or operator shall, as soon as possible,
but no later than thirty (30) days after
the completion of recovery and no later
than one (1) calendar year following the
receipt of the hazardous waste, send a
certificate of recovery to the foreign
exporter and to the competent authority
of the country of export and to EPA’s
Office of Enforcement and Compliance
Assurance at the above address by mail,
e-mail without a digital signature
Use of manifest system.
(a)(1) * * *
(3) If a facility receives hazardous
waste imported from a foreign source,
the receiving facility must mail a copy
of the manifest and documentation
confirming EPA’s consent to the import
of hazardous waste to the following
address within thirty (30) days of
delivery: Office of Enforcement and
Compliance Assurance, Office of
Federal Activities, International
Compliance Assurance Division
(2254A), Environmental Protection
Agency, 1200 Pennsylvania Avenue,
NW., Washington, DC 20460
*
*
*
*
*
PART 266—STANDARDS FOR THE
MANAGEMENT OF SPECIFIC
HAZARDOUS WASTES AND SPECIFIC
TYPES OF HAZARDOUS WASTE
MANAGEMENT FACILITIES
12. The authority citation for part 266
is revised to read as follows:
Authority: 42 U.S.C. 1006, 2002(a), 3001–
3009, 3014, 3017, 6905, 6906, 6912, 6921,
6922, 6924–6927, 6934, and 6937.
13. In § 266.80(a) the table is revised
to read as follows:
§ 266.80
Applicability and requirements.
(a) * * *
And if you * * *
Then you * * *
And you * * *
(1) Will be reclaimed through regeneration (such as by electrolyte replacement).
.......................................................
Generate, collect, and/or transport
these batteries.
(3) Will be reclaimed other than
through regeneration.
Store these batteries but you
aren’t the reclaimer.
(4) Will be reclaimed other than
through regeneration.
Store these batteries before you
reclaim them.
(5) Will be reclaimed other than
through regeneration.
Don’t store these batteries before
you reclaim them.
Are exempt from 40 CFR parts
262 (except for § 262.11), 263,
264, 265, 266, 268, 270, 124 of
this chapter, and the notification
requirements at section 3010 of
RCRA.
Are exempt from 40 CFR parts
262 (except for § 262.11), 263,
264, 265, 266, 270, 124 of this
chapter, and the notification requirements at section 3010 of
RCRA.
Are exempt from 40 CFR parts
262 (except for § 262.11), 263,
264, 265, 266, 270, 124 of this
chapter, and the notification requirements at section 3010 of
RCRA.
Must comply with 40 CFR
266.80(b) and as appropriate
other regulatory provisions described in 266.80(b).
Are exempt from 40 CFR parts
262 (except for § 262.11), 263,
264, 265, 266, 270, 124 of this
chapter, and the notification requirements at section 3010 of
RCRA.
Are subject to 40 CFR parts 261
and § 262.11 of this chapter.
(2) Will be reclaimed other than
through regeneration.
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Are subject to 40 CFR parts 261
and § 262.11, and applicable
provisions under part 268.
Are subject to 40 CFR parts 261,
§ 262.11, and applicable provisions under part 268.
Are subject to 40 CFR parts 261,
§ 262.11, and applicable provisions under part 268.
Are subject to 40 CFR parts 261,
§ 262.11, and applicable provisions under part 268.
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58415
If your batteries * * *
And if you * * *
Then you * * *
And you * * *
(6) Will be reclaimed through regeneration or any other means.
Export these batteries for reclamation in a foreign country.
Are exempt from 40 CFR parts
263, 264, 265, 266, 268, 270,
124 of this chapter, and the notification requirements at section 3010 of RCRA. You are
also exempt from part 262, except for 262.11, and except for
the applicable requirements in
either:.
(1) 40 CFR part 262 subpart H; or
(2) 262.53 ‘‘Notification of Intent
to Export, 262.56(a)(1) through
(4), (6), and (b) ‘‘Annual Reports,’’ and 262.57 ‘‘Recordkeeping’’.
(7) Will be reclaimed through regeneration or any other means.
Transport these batteries in the
U.S. to export them for reclamation in a foreign country.
Are exempt from 40 CFR parts
263, 264, 265, 266, 268, 270,
124 of this chapter, and the notification requirements at section 3010 of RCRA.
Are subject to 40 CFR part 261
and § 262.11, and either must
comply with 40 CFR part 262,
subpart H (if shipping to one of
the OECD countries specified in
40 CFR 262.58(a)(1)), or must:
(a) Comply with the requirements
applicable to a primary exporter
in 40 CFR 262.53, 262.56(a)(1)
through (4), (6), and (b) and
262.57; and
(b) Export these batteries only
upon consent of the receiving
country and in conformance
with the EPA Acknowledgement
of Consent as defined in subpart E of part 262 of this chapter; and
(c) Provide a copy of the EPA Acknowledgment of Consent for
the shipment to the transporter
transporting the shipment for
export.
Must comply with applicable requirements in 40 CFR part 262,
subpart H (if shipping to one of
the OECD countries specified in
40 CFR 262.58(a)(1)), or must
comply with the following:
(a) You may not accept a shipment if you know the shipment
does not conform to the EPA
Acknowledgment of Consent;
(b) You must ensure that a copy
of the EPA Acknowledgment of
Consent accompanies the shipment; and
(c) You must ensure that the shipment is delivered to the facility
designated by the person initiating the shipment.
*
*
*
*
Authority: 42 U.S.C. 6905, 6912(a), and
6926.
*
PART 271—REQUIREMENTS FOR
AUTHORIZATION OF STATE
HAZARDOUS WASTE PROGRAMS
14. The authority citation for part 271
continues to read as follows:
15. Section 271.1(j) is amended by
adding the following entries to Table 1
and Table 2 in chronological order by
date of publication in the Federal
Register, to read as follows:
§ 271.1
*
Purpose and scope.
*
*
*
*
(j) * * *
TABLE 1—REGULATIONS IMPLEMENTING THE HAZARDOUS AND SOLID WASTE AMENDMENTS OF 1984
Promulgation date
Title of regulation
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*
*
[Insert date of publication of final
rule in the Federal Register
(FR)].
*
*
*
VerDate Aug<31>2005
*
Federal Register reference
Effective date
*
*
*
Exports of hazardous waste ......... [Insert FR page numbers] .............
*
*
[Insert date of X months from date
of publication of final rule].
*
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TABLE 2—SELF-IMPLEMENTING PROVISIONS OF THE HAZARDOUS AND SOLID WASTE AMENDMENTS OF 1984
Effective date
Self-implementing provision
RCRA citation
*
*
*
*
[Insert date X days after of publication of Exports of hazardous waste ...................
final rule in the Federal Register (FR)].
*
*
*
*
*
3017(a)
Federal Register reference
*
*
[Insert Federal Register reference for
publication of final rule].
*
[FR Doc. E8–22536 Filed 10–3–08; 8:45 am]
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Agencies
[Federal Register Volume 73, Number 194 (Monday, October 6, 2008)]
[Proposed Rules]
[Pages 58388-58416]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-22536]
[[Page 58387]]
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Part V
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Parts 262, 264, et al.
Revisions to: The Requirements for Transboundary Shipments of Wastes
Between OECD Countries, the Requirements for Export Shipments of Spent
Lead-Acid Batteries, the Requirements on Submitting Exception Reports
for Export Shipments of Hazardous Wastes, and the Requirements for
Imports of Hazardous Wastes; Proposed Rule
Federal Register / Vol. 73, No. 194 / Monday, October 6, 2008 /
Proposed Rules
[[Page 58388]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 262, 264, 265, 266, and 271
[EPA-HQ-RCRA-2005-0018; FRL-8720-3]
RIN 2050-AE93
Revisions to: The Requirements for Transboundary Shipments of
Wastes Between OECD Countries, the Requirements for Export Shipments of
Spent Lead-Acid Batteries, the Requirements on Submitting Exception
Reports for Export Shipments of Hazardous Wastes, and the Requirements
for Imports of Hazardous Wastes
AGENCY: Environmental Protection Agency.
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: This rule proposes to amend certain existing regulations
promulgated under the hazardous waste provisions of the Resource
Conservation and Recovery Act (RCRA) regarding the export and import of
hazardous wastes from and into the United States. Specifically, we are
proposing to modify: The requirements to implement the OECD framework
concerning the transboundary movement of hazardous waste among
countries belonging to the Organization for Economic Cooperation and
Development (OECD), including reducing the number of control levels,
exempting qualifying shipments sent for laboratory analyses from
certain paperwork requirements, requiring recovery facilities to submit
a certificate of recovery, adding provisions for the return or re-
export of wastes subject to the Amber control procedures, and
clarifying certain existing provisions that were identified as
potentially ambiguous to the regulated community; the regulations
regarding the management of spent lead-acid batteries being reclaimed
to require appropriate notice and consent for those batteries intended
for reclamation in a foreign country; the exception reporting
requirements for hazardous waste exports to specify that all exception
reports submitted to EPA be sent to the Office of Enforcement and
Compliance Assurance's Office of Federal Activities in Washington, DC
rather than to the Administrator; and the hazardous waste import
requirements such that U.S. importers would give the initial
transporter a copy of the EPA-provided documentation confirming EPA's
consent to the import when they provide the RCRA hazardous waste
manifest, and that the documentation would be submitted by the U.S.
receiving facility to EPA along with the RCRA hazardous waste manifest
within thirty days of import shipment delivery. Finally, separate from
this proposed rule, EPA is publishing in https://www.epa.gov/epawaste/
hazard/international/oecd-slab-rule.htm a draft guidance document on
how U.S. receiving facilities may request EPA to identify them as pre-
approved facilities to receive hazardous waste from OECD Member
countries.
DATES: Comments must be received on or before December 5, 2008. Under
the Paperwork Reduction Act, comments on the information collection
provisions must be received by OMB on or before November 5, 2008.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
RCRA-2005-0018, by one of the following methods:
https://www.regulations.gov: Follow the on-line
instructions for submitting comments.
E-mail: rcra-docket@epa.gov, Attention Docket No. EPA-HQ-
RCRA-2005-0018.
Fax: (202) 566-9744, Attention Docket No. EPA-HQ-RCRA-
2005-0018.
Mail: RCRA Docket No. EPA-HQ-RCRA-2005-0018, Environmental
Protection Agency, Mail Code: 2822T, 1200 Pennsylvania Avenue, NW.,
Washington, DC 20460. Please include a total of 2 copies. 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
St. NW., Washington, DC 20503.
Hand Delivery: RCRA Docket No. EPA-HQ-RCRA-2005-0018, EPA
West Building, Room 3334, 1301 Constitution Ave., NW., Washington DC
20004. 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-
2005-0018. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://
www.regulations.gov or 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.
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 RCRA Docket, EPA/
DC, EPA West, Room 3334, 1301 Constitution Avenue, NW., Washington, DC.
The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal holidays. The telephone number for the
Public Reading Room is (202) 566-1744 and the telephone number for the
RCRA Docket is (202) 566-0270.
FOR FURTHER INFORMATION CONTACT: Laura Coughlan, Hazardous Waste
Identification Division, Office of Solid Waste (5304P), Environmental
Protection Agency, 1200 Pennsylvania Avenue, NW., Washington, DC 20460;
telephone number: (703) 308-0005; fax number: (703) 308-0514; e-mail:
coughlan.laura@epa.gov.
SUPPLEMENTARY INFORMATION: The information presented in this preamble
is organized as follows:
I. General Information
A. List of Acronyms Used in This Proposed Rule
B. What are the statutory authorities for this proposed rule?
C. Does this proposed rule apply to me?
D. What is the purpose of this proposed rule?
[[Page 58389]]
II. Background
A. OECD Revisions
B. SLAB Revisions
C. Exception Report Revisions for Exports Under Subparts E and H
of 40 CFR Part 262
D. Import Revisions
III. Summary of This Proposed Rule and Changes
A. Changes to 40 CFR Part 262, Subpart E
B. Changes to 40 CFR 262.60(e), Subpart F
C. Changes to 40 CFR Part 262, Subpart H
D. Changes to 40 CFR 264.12(a)(2) and 40 CFR 265.12(a)(2)
E. Changes to 40 CFR 264.71(a)(3) and 40 CFR 265.71(a)(3)
F. Changes to 40 CFR 266.80(a)
G. Changes to 40 CFR 271.1
IV. Costs and Benefits of the Proposed Rule
A. Introduction
B. Analytical Scope
C. Cost Impacts
D. Benefits
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
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act of 1995
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 Risks and Safety Risks
H. Executive Order 13211: Actions Concerning Regulations that
Significantly Affect Energy Supply, Distribution, or Use
I. National Technology Transfer Advancement Act
J. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
I. General Information
A. List of Acronyms Used in This Proposed Rule
------------------------------------------------------------------------
Acronym Meaning
------------------------------------------------------------------------
BCI............................... Battery Council International
CBI............................... Confidential Business Information
CERCLA............................ Comprehensive Environmental
Response, Compensation, and
Liability Act
CFR............................... Code of Federal Regulations
EPA............................... U.S. Environmental Protection Agency
FR................................ Federal Register
HSWA.............................. Hazardous and Solid Waste Amendments
LAB............................... Lead-Acid Battery
NAICS............................. North American Industrial
Classification System
NTTAA............................. National Technology Transfer and
Advancement Act
NAFTA............................. North American Free Trade Agreement
OECD.............................. Organization for Economic
Cooperation and Development
OMB............................... Office of Management and Budget
OSWER............................. Office of Solid Waste and Emergency
Response
RCRA.............................. Resource Conservation and Recovery
Act
RFA............................... Regulatory Flexibility Act
SIC............................... Standard Industrial Classification
SLAB.............................. Spent Lead-Acid Battery
SBREFA............................ Small Business Regulatory
Enforcement Fairness Act
TRI............................... Toxics Release Inventory
UMRA.............................. Unfunded Mandates Reform Act
------------------------------------------------------------------------
B. What are the statutory authorities for this proposed rule?
The authority to propose this rule is found in sections 1006, 1007,
2002(a), 3001-3010, 3013-3015, and 3017 of the Solid Waste Disposal
Act, as amended by the Resource Conservation and Recovery Act (RCRA),
and as amended by the Hazardous and Solid Waste Amendments, 42 U.S.C.
6905, 6906, 6912, 6921-6930, 6934-6936, and 6938.
C. Does this proposed rule apply to me?
1. OECD Revisions
The OECD revisions in this proposed rule affect all persons who
export or import hazardous waste, export or import universal waste, or
export spent lead-acid batteries (SLABs) destined for recovery
operations in countries belonging to the Organization for Economic
Cooperation and Development (OECD), except for Mexico and Canada. Any
transboundary movement of hazardous wastes between the United States
and either Mexico or Canada will continue to be regulated by their
respective bilateral agreements and applicable regulations. Potentially
affected entities may include, but are not limited to:
------------------------------------------------------------------------
Industry sector NAICS SIC
------------------------------------------------------------------------
Utilities..................................... 221100 4939
Petroleum and Coal Products Manufacturing..... 324 29
Chemical Manufacturing........................ 325100 28
Primary Metal Manufacturing................... 331 33
Fabricated Metal Product Manufacturing........ 332 34
Machinery Manufacturing....................... 333 35
Computer and Electronic Product Manufacturing. 334110 357
Electrical Equipment, Appliance, and Component 335 36
Manufacturing................................
Transportation Equipment Manufacturing........ 336 37
Miscellaneous Manufacturing................... 339900 39
Scrap and Waste Materials..................... 423930 5093
Materials Recovery Facilities................. 562920 4953
------------------------------------------------------------------------
2. SLAB Revisions
The SLAB revisions in this proposed rule affect all persons who
export SLABs for reclamation in any foreign country. Potentially
affected entities may include, but are not limited to:
------------------------------------------------------------------------
Industry sector NAICS SIC
------------------------------------------------------------------------
Hazardous Waste Collectors.................... 562112 4212
Recyclable Material Hauling, Long-Distance.... 484230 4213
Batteries, automotive, merchant wholesalers... 423120 5013
Lead-acid storage batteries, manufacturing.... 335911 3691
Automotive Parts, Accessories, and Tire Stores 441310 5013
Tire Dealers.................................. 441320 5014
All other General Merchandise Stores.......... 452990 5399
New Car Dealers............................... 441110 5511
[[Page 58390]]
Recyclable Material Wholesaler................ 423930 5093
Other Waste Collection........................ 562119 4212
Recyclable Material Collection Services, Solid 562111 4212
Waste Collection.............................
Marinas....................................... 713930 4493
General Freight Trucking, Long-Distance, TL... 484121 4213
General Freight Trucking, Long-Distance, LTL.. 484122 4213
Specialized Freight Trucking.................. 484200 4213
Freight Carriers (except air couriers), Air 481112 4512
Scheduled....................................
Freight Charter Services, Air................. 481212 4522
Freight Railways, Line-Haul................... 482111 4011
Freight Transportation, Deep Sea, to and from 483113 4424
Domestic Ports...............................
Freight Transportation, Deep Sea, to or from 483111 4412
Foreign Ports................................
------------------------------------------------------------------------
3. Exception Report Revisions for Exports Under Subparts E and H of 40
CFR Part 262
The exception report change to 40 CFR part 262, subpart E and
subpart H of this proposed rule affect all persons who export hazardous
waste, universal waste, or SLABs to any foreign country. Potentially
affected entities may include, but are not limited to:
------------------------------------------------------------------------
Industry sector NAICS SIC
------------------------------------------------------------------------
Utilities..................................... 221100 4939
Petroleum and Coal Products Manufacturing..... 324 29
Chemical Manufacturing........................ 325100 28
Primary Metal Manufacturing................... 331 33
Fabricated Metal Product Manufacturing........ 332 34
Machinery Manufacturing....................... 333 35
Computer and Electronic Product Manufacturing. 334110 357
Electrical Equipment, Appliance, and Component 335 36
Manufacturing................................
Transportation Equipment Manufacturing........ 336 37
Miscellaneous Manufacturing................... 339 39
Scrap and Waste Materials..................... 423930 5093
------------------------------------------------------------------------
4. Import Revisions
The import revisions in this proposed rule affect all persons
importing hazardous waste from a foreign country that must comply with
40 CFR part 262, subpart F, and all facilities receiving imported
hazardous waste from a foreign country that must comply with either
264.71(a)(3) or 265.71(a)(3). This includes those hazardous waste
import shipments originating in OECD countries, as well as in non-OECD
countries. Potentially affected entities may include, but are not
limited to:
------------------------------------------------------------------------
Industry sector NAICS SIC
------------------------------------------------------------------------
Hazardous Waste Collectors.................... 562112 4212
Recyclable Material Hauling, Long-Distance.... 484230 4213
Recyclable Material Wholesaler................ 423930 5093
Other Waste Collection........................ 562119 4212
Recyclable Material Collection Services, Solid 562111 4212
Waste Collection.............................
General Freight Trucking, Long-Distance, TL... 484121 4213
Scrap and Waste Materials..................... 423930 5093
Materials Recovery Facilities................. 562920 4953
------------------------------------------------------------------------
The lists of potentially affected entities in the above tables may
not be exhaustive. The Agency's aim is to provide a guide for readers
regarding those entities that potentially could be affected by this
action. However, this action may affect other entities not listed in
these tables. If you have questions regarding the applicability of this
proposed rule to a particular entity, consult the person listed in the
preceding section entitled FOR FURTHER INFORMATION CONTACT.
D. What is the purpose of this proposed rule?
1. OECD Revisions
This proposed rule is intended to implement the OECD's ``Decision
of the Council C(2001)107/FINAL, Concerning the Control of
Transboundary Movements of Wastes Destined for Recovery Operations, as
amended by C(2004)20'' (hereinafter referred to as the Amended 2001
OECD Decision), which amended the OECD Decision (1992) on the same
subject. The purpose of these revisions was to encourage consistency
and harmonization between the OECD and the Basel Convention,\1\ which
in turn, promotes economic
[[Page 58391]]
efficiency and the recovery of waste in an environmentally sound
manner.
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\1\ The Basel Convention on the Control of Transboundary
Movements of Hazardous Wastes and their Disposal is a comprehensive
global environmental agreement on hazardous and other wastes. The
Convention has 170 Member countries, also known as Parties, and aims
to protect human health and the environment against the adverse
effects resulting from the generation, management, transboundary
movements and disposal of hazardous and other wastes. More
information on the Basel Convention may be found at https://
www.basel.int.
---------------------------------------------------------------------------
The Amended 2001 OECD Decision was supported by the United States
and imposes legally binding commitments on the United States pursuant
to Articles 5(a) and 6 of the OECD Convention. By consenting to the
Decision, the United States Government has agreed to promulgate
regulations necessary to ensure that the United States can uphold the
agreement.
Further, this proposed rule clarifies certain regulations to
articulate more explicitly EPA's original intent in those regulations
and to eliminate any confusion on the part of the regulated community.
2. SLAB Revisions
EPA also proposes to amend the RCRA hazardous waste regulations for
SLABs specified in 40 CFR part 266, subpart G by requiring notification
and consent for the export of SLABs in order to ensure that SLABs are
sent to reclamation facilities in countries that can manage them in an
environmentally sound manner. The notification and consent requirements
are intended to: (1) Reduce potential risk to human health and the
environment, including potential risk from the transboundary movement
of pollution from other countries to the U.S., and (2) harmonize the
notice and consent procedures with international practice (see II.B.4)
and with the RCRA universal waste regulations for the export of SLABs,
resulting in a more uniform practice for notification and consent for
SLABs.
Notification of potential exports of hazardous waste destined for
recovery in another country is a key component of multilateral
environmental systems for appropriate governmental oversight to ensure
proper management of the waste. The notification mechanism allows for
all concerned countries (i.e., exporting, importing, and transit) to
determine whether the hazardous waste can be handled safely based on
the requirements of their waste management systems. Specifically, the
importing country has the opportunity to confirm that the particular
facility that is designated to receive the waste is qualified to manage
it in a safe and environmentally sound manner, and has all appropriate
approvals, permits, or licenses. Furthermore, the notice and consent
process is the fundamental tool that is employed in transboundary waste
arrangements to provide business certainty for legitimate trade.
Risks to human health and the environment derived from improper
SLAB recycling techniques are of major concern internationally. The
Basel Convention has developed two guidance documents 2 3 to
assist governments, transporters, and recyclers to achieve
environmentally sound management of SLABs. Indeed, the Basel Convention
considers transboundary movement of SLABs to be ``illegal traffic'' if
it occurs without prior notification. Similar guidance was developed by
the Commission for Environmental Cooperation \4\ (CEC) for use by North
American countries to promote sound management of SLABs.\5\ A 1996 OECD
Ministerial Declaration on risk reduction from lead called on Member
countries to take domestic and international action to reduce human
exposure to lead from a variety of sources.\6\ Further, the Report of
the Special Rapporteur of the U.N. Commission on Human Rights \7\
expressed concerns that ``the United States system does not impose
export regulations on SLABs destined for recycling,'' and suggests that
``the recycling of lead-acid batteries is one of the greatest potential
sources of risk, especially for exposed workers in the informal sector
in many developing countries.''
---------------------------------------------------------------------------
\2\ Basel Convention Training Manual: National Management Plans
for Used Lead Acid Batteries, SBC No. 2004/5, 2004.
\3\ Technical Guidelines for the Environmentally Sound
Management of Waste Lead-acid Batteries, SBC No. 2003/9, 2003.
\4\ The Commission for Environmental Cooperation is an
international organization created by Canada, Mexico and the United
States under the North American Agreement on Environmental
Cooperation (NAAEC). The CEC was established to address regional
environmental concerns, help prevent potential trade and
environmental conflicts, and to promote the effective enforcement of
environmental law. The Agreement complements the environmental
provisions of the North American Free Trade Agreement (NAFTA).
\5\ Practices and Options for Environmentally Sound Management
of Spent Lead-acid Batteries within North America, Commission for
Environmental Cooperation, December 2007.
\6\ The Global Pursuit of the Sound Management of Chemicals, The
World Bank, February 2004.
\7\ Adverse effects of the illicit movement and dumping of toxic
and dangerous products and wastes on the enjoyment of human rights,
U.N. Commission on Human Rights, Economic and Social Council, E/
CN.4/2003/56/Add.1, 10 January 2003, p. 17.
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For economic and efficiency reasons, some highly industrialized
countries may ship their SLABs to less industrialized countries for
SLAB breaking, draining, component separation, slag generation and lead
refining. Human health and environmental risk issues can arise when
these recycling processes are performed with insufficient human health
or environmental safety controls. The results could include: (1)
Significant increases in elevated blood lead levels in facility workers
and their families; (2) increases in uncontrolled releases of lead-
laden slag to soil, surface water and ground water sources; and (3)
lead air-emissions from lead smelting without the proper air-emissions
controls.
EPA would like to focus on the use of preventative measures to
decrease the proportionate risks to human health and the global
environment. There are inherent human health and environmental hazards
associated with a significant amount of SLABs being exported across
borders without the knowledge and consent of receiving countries and/or
SLABs being exported to countries with substandard smelting
infrastructures. Amending the current RCRA hazardous waste regulations
to include the notification and consent requirements would help ensure
that SLABs are exported to countries with the capacity to handle them
in an environmentally sound manner and to aid countries with tracking
the movements and life-cycle management of SLABs inside their borders.
EPA believes that the notification and consent approach is an effective
way of preventing the export of SLABs to countries and to facilities
that do not have the capability of safely managing the SLABs by
providing the receiving country with the necessary information about
the proposed shipment and requiring its consent before the export can
proceed. In addition, by providing the receiving country with this
information, they can monitor and track the export and the facility's
management of the SLABs for safe management. The purpose of the
notification and consent requirements for SLABs destined for
reclamation in this proposed rule is consistent with the purpose of the
notification and consent requirements in RCRA section 3017. Congress,
in enacting section 3017, considered it important to require
notification and consent for exports of hazardous wastes. The
legislative history for section 3017 indicates that Congress felt that
prior notification of an export to the receiving country would allow
that country to make an informed decision as to whether it would accept
the waste and, if so, how it would safely manage that waste. Congress
noted that problems, such as harm to human health and the environment
arise when wastes are sent to countries that do not want to receive
them, or lack sufficient information to manage them properly.
EPA believes that the potential reduction in risk to human health
and the environment with this proposed modification will outweigh the
incremental increase in burden to SLAB exporters. Moreover, because the
[[Page 58392]]
notification and consent requirements are intended to ensure that the
receiving country has the necessary advance knowledge of a proposed
shipment of SLABs to a facility in that country, the country can
properly consent (or object) to this shipment based on its knowledge of
the capabilities of the particular facility and its ability to manage
the batteries in a safe and environmentally sound manner.
3. Exception Report Revisions for Exports Under Subparts E and H of 40
CFR Part 262
EPA proposes to amend the exception reporting requirements in 40
CFR part 262, subparts E and H, to specify that all exception reports
be submitted to the Office of Enforcement and Compliance Assurance's
Office of Federal Activities in Washington, DC rather than to the
Administrator.\8\ The Agency proposes this change because it believes
that a more specific address should assist in proper delivery of the
exception report to the appropriate EPA office. The more general
requirement in the existing regulation to send this report to the
``Administrator'' may have not provided sufficiently specific
instruction for those exporters trying to notify EPA of returned
shipments, which could reduce EPA's ability to provide oversight on
such exports. Directing that all exception reports submitted to EPA
pursuant to the requirements in 40 CFR part 262, subparts E and H, be
sent to a specific address should ensure better oversight of (1) return
shipments into the U.S. and (2) compliance with the exception report
requirements without additional regulatory burden.
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\8\ The Office of Enforcement and Compliance Assurance is the
office within EPA that implements the notice and consent scheme for
hazardous waste transboundary shipments.
---------------------------------------------------------------------------
4. Import Revisions
Finally, EPA proposes to amend the import requirements specified in
40 CFR part 262, subpart F. This change would require that the U.S.
importer provide the transporter with a copy of documentation provided
by EPA, confirming EPA's consent to the hazardous waste import under a
specific notice. This documentation would then accompany each RCRA
hazardous waste manifested import shipment and be submitted by the
receiving facility in the U.S. to EPA along with the RCRA hazardous
waste manifest in accordance with Sec. Sec. 264.71(a)(3) and
265.71(a)(3). While EPA currently requires that receiving facilities in
the U.S. submit a copy of the hazardous waste manifest to EPA to
document individual import shipments, it has been difficult for EPA to
match an individual manifest for a hazardous waste import shipment with
the related notice of intent to export from a foreign country for which
EPA has provided consent. One major reason for this difficulty is
because a given destination facility in the U.S. could be receiving the
same hazardous waste from the same foreign exporter under more than one
notice. Adding this requirement will enable EPA to better match the
individual import shipments against the related notice from the foreign
exporting country for which EPA has provided consent, and facilitate
our oversight of such imports.
II. Background
A. OECD Revisions
1. What is the OECD?
The OECD is an international organization established in 1960 to
assist Member countries in achieving sustainable economic growth,
employment, and an increased standard of living, while simultaneously
ensuring the protection of human health and the environment. OECD
Member countries are concerned with a host of international socio-
economic and political issues, including environmental issues. To
address these issues, the OECD Council may negotiate Council Decisions,
which are international agreements that create binding commitments on
the United States under the terms of the OECD Convention, unless
otherwise provided in the Articles of the 1960 Convention. One such
Council Decision addresses the transboundary movement of waste, which
is the subject of this proposed rule. There are currently thirty OECD
Member countries: Australia, Austria, Belgium, Canada, the Czech
Republic, Denmark, Finland, France, Germany, Greece, Hungary, Iceland,
Ireland, Italy, Japan, Luxembourg, Mexico, the Netherlands, New
Zealand, Norway, Poland, Portugal, the Slovak Republic, South Korea,
Spain, Sweden, Switzerland, Turkey, the United Kingdom, and the United
States. The OECD country Web site for each Member country may be found
at https://www.oecd.org/infobycountry/.
2. What OECD Decision formed the basis for the existing regulations in
40 CFR part 262, subpart H?
On March 30, 1992, the OECD Council adopted the ``Decision of the
Council C(92)39/FINAL Concerning the Control of Transfrontier Movements
of Wastes Destined for Recovery'' (hereinafter referred to as the 1992
Decision), which applied to the transboundary movements of wastes
destined for recovery operations between OECD Member countries. The
1992 Decision provided a framework for OECD Member countries to control
the transboundary movement of recoverable wastes in an environmentally
sound and economically efficient manner.
3. Why did EPA establish the existing regulations in 40 CFR part 262,
subpart H?
Due to the legally binding nature of the 1992 Decision, the United
States, as an OECD Member country, was required to implement the terms
of the decision in accordance with Articles 5(a) and 6 of the OECD
Convention. (A copy of the OECD Convention is included in the docket to
this proposed rule.) In order to implement the specific provisions of
the 1992 Decision, EPA published a final rule in the Federal Register
entitled, ``Imports and Exports of Hazardous Waste: Implementation of
OECD Council Decision C(92)39 Concerning the Control of Transfrontier
Movements of Wastes Destined for Recovery Operations'' (61 FR 16289,
April 12, 1996)(hereafter referred to as EPA's OECD rule). These
regulations appear primarily in 40 CFR part 262, subpart H.
4. What OECD Decisions form the basis of the revisions in this proposed
rule?
On June 14, 2001, the OECD Council amended the 1992 Decision by
passing ``Revision of Decision C(92)30/FINAL on the Control of
Transboundary Movement of Wastes Destined for Recovery Operations''
(hereafter referred to as the 2001 OECD Decision). The goal of the 2001
OECD Decision was to harmonize the procedures and requirements of the
OECD with those of the Basel Convention and to eliminate duplicative
activities between the two international organizations as much as
practical. These changes include significant revisions to the original
established framework (such as reducing the levels of control from a
three-tiered system to a two-tiered system), while also adding entirely
new provisions (for example, the new certificate of recovery
requirement). Subsequent to the 2001 OECD Decision, an addendum,
C(2001)107/ADD1 (hereafter referred to as the 2001 OECD Addendum),
which consists of revised versions of the notification and movement
documents and the instructions to complete them, was adopted by the
OECD Council on February 28, 2002. The addendum was incorporated into
the 2001 OECD Decision as section C of Appendix 8, and the combined
version was issued in
[[Page 58393]]
May 2002 as C(2001)107/FINAL. Finally, on March 30, 2004, the OECD
Council adopted C(2004)20 (hereafter referred to as the 2004 OECD
Amendment), which updated the OECD waste lists, entitled ``Appendix 3:
List of Wastes Subject to the Green Control Procedure'' (hereafter
referred to as the Green list) and ``Appendix 4: List of Wastes Subject
to the Amber Control Procedure'' (hereafter referred to as the Amber
List). To the extent possible, the Green and Amber Lists were revised
based on the amendments made to Annexes II, VIII, and IX of the Basel
Convention in November 2003. The OECD Council decisions are
collectively referred to as the Amended 2001 OECD Decision.
5. How does EPA propose to revise the existing regulations to implement
the latest OECD Decisions?
This rule proposes to amend EPA's OECD rule to reflect the
procedural and substantive amendments in the 2001 OECD Decision, the
applicable changes to the new notification and movement documents
presented in the 2001 OECD Addendum, and the changes to the OECD waste
lists as presented in the 2004 OECD Amendment, collectively referred to
as the Amended 2001 OECD Decision. This proposed rule also seeks to
clarify certain existing regulatory provisions that have been
identified as potentially ambiguous to the regulated community.
As noted previously, OECD Council Decisions are international
agreements that create binding commitments on the United States, unless
otherwise provided in the Articles to the 1960 Convention. Therefore,
by consenting to the Amended 2001 OECD Decision, the United States
Government has agreed to establish legal measures necessary to ensure
that the United States can uphold the agreement. EPA believes that RCRA
contains adequate authority to promulgate the requirements of the
Amended 2001 OECD Decision.
It is important to recognize that the OECD Decision allows a Member
country to determine if a waste on an OECD list is hazardous based on
its ``national procedures.'' EPA has determined that a waste is
hazardous under U.S. ``national procedures''--and therefore subject to
the OECD provisions of Subpart H--if the waste meets the following
requirements under RCRA: (a) Meets the Federal definition of hazardous
waste in 40 CFR 261.3; and (b) is subject to either the Federal
hazardous waste manifesting requirements in 40 CFR 262, or to the
universal waste management standards of 40 CFR part 273, or to State
requirements analogous to Part 273. This determination was set forth in
Sec. 262.89(a), and additional discussion on how this provision
impacts transboundary movements of wastes subject to RCRA exemptions,
exclusions and recycling provisions can be found in the April 12, 1996,
preamble to the original OECD rule (61 FR 16290-16316).
6. How does EPA propose to implement future OECD revisions?
(a) Changes to OECD Member Country List
Qualified countries may be invited to accede to the OECD Convention
as new Members. The OECD Convention defines qualified countries as
those that have demonstrated the basic values shared by all Members: An
open market economy, democratic pluralism, and respect for human
rights. Any decision to invite a new country to become a Member of the
OECD must be unanimous, although abstentions may be allowed. Thus, no
new Member may be admitted over the objection of the United States (or
any other Member).
In order to accommodate changes in OECD membership as quickly as
possible, EPA intends to publish in the Federal Register any future
amendments to the list of OECD Member countries set forth in Sec.
262.58(a)(1), as the OECD adds new Member countries or otherwise amends
its list in the future. EPA intends to publish notices of these future
amendments to Sec. 262.58(a)(1) as a final rule without prior notice
and opportunity for comment. EPA believes that the Agency would be able
to make a ``good cause'' finding under the Administrative Procedure Act
(APA) (5 U.S.C. 553(b)(3)(B)) to make these future amendments without
prior notice and comment. EPA believes notice and an opportunity for
comment on future amendments to Sec. 262.58(a)(1) to reflect the
updates to the OECD list of Member countries would be unnecessary,
because the United States, as an OECD Member country, is legally
obligated to implement OECD Decisions with respect to all OECD Member
countries.
(b) Changes to OECD Waste List
The OECD waste list is incorporated by reference and cited in Sec.
262.89(d). If the OECD amends its waste list in the future by decision
of the OECD Council (with the concurrence of the United States), EPA
intends to publish notices of these amendments in the Federal Register
as a final rule without prior notice and an opportunity for comment.
EPA believes that the Agency would be able to make a ``good cause''
finding under the Administrative Procedure Act (APA) (5 U.S.C.
553(b)(3)(B)) to make these future amendments without prior notice and
comment because the purpose of Sec. 262.89(d) is solely
informational--to provide an up-to-date reference of the OECD list.
Public comment on such updates is unnecessary, as EPA would have no
discretion to modify the OECD list. As discussed above, U.S. national
procedures, rather than the OECD list, ultimately determine the
applicability of Subpart H, recognizing that the OECD list will be
relevant for exports to other OECD members.
B. SLAB Revisions
1. What are SLABs?
Lead-acid batteries are secondary, wet cell batteries that contain
liquid and can be recharged for many uses. They are the most widely
used rechargeable batteries in the world and are mainly used as
starting, lighting, and ignition (SLI) power batteries found in
automobiles and other vehicles. A rechargeable SLAB is spent if it no
longer performs effectively and cannot be recharged. Battery failure is
most commonly attributed to water loss and grid corrosion during normal
use. SLABs are considered both solid and hazardous wastes under
Subtitle C of RCRA, because they are classified as spent materials that
exhibit the toxicity characteristic for lead, and the corrosivity
characteristic for the sulfuric acid electrolyte in the battery.
Lead-acid batteries are typically composed of an outside plastic
casing and six inner cells containing lead strips and positive and
negative lead terminals. Each cell is made up of two lead frameworks,
the positive plate being lead dioxide and the negative plate being
spongy lead (a metallic lead in a high-surface-area porous structure).
Each cell is filled with sulfuric acid as the electrolyte. When the
battery is in use, the spongy lead, sulphuric acid, and lead dioxide
react to produce an electrical current. Both electrodes are converted
to lead sulfate, a process which is reversed during recharge.
2. How are SLABs currently managed?
Currently, SLABs are either reclaimed for their lead value or
disposed of. The Battery Council International (BCI) reported a 99.2
percent domestic SLAB reclamation rate for the years 1999-2003, making
lead-acid batteries one of the most recycled consumer products. When a
SLAB is collected, it is sent to a reclaimer where the SLABs are
cracked through various means, such as
[[Page 58394]]
a hammermill in order to separate out the lead, battery casing, plate
separators, and sulfuric acid components into recycling streams and
disposal streams. Specifically, the lead plates, lead oxide paste and
other lead parts are cleaned and then melted together in smelting
furnaces to produce lead ingots along with residual lead dross and
slag. The residual lead dross and slag may be reclaimed further or
disposed of in a landfill. Used sulphuric acid can be (1) Sent for acid
regeneration, where the acid is cleaned for re-use as electrolyte in
the battery manufacturing process, (2) neutralized and released into a
public sewer system once it meets Clean Water Act standards, or (3)
converted into sodium sulfate, an odorless white powder that's used in
laundry detergent, glass and textile manufacturing. If it is a plastic-
cased battery, the plastic is either cleaned and recycled as new
battery casings or disposed of at a landfill. If the battery casing is
made of rubber or other materials, it can be used as a fuel at the
smelter. Other materials from batteries are either recycled or disposed
of in a landfill.
Lead is a highly toxic heavy metal naturally occurring in the
environment. For this reason, proper management of lead and lead-
containing products is essential to the protection of human health and
the environment. In the U.S., the Occupational Safety and Health
Administration (OSHA) has developed standards to address and minimize
workplace exposure to lead (29 CFR Sec. 1910.1025). These standards
establish permissible exposure limits; exposure monitoring, respiratory
protection and safety procedures; and proper warning and sign-age
requirements for facilities processing lead. Proper ventilation,
training and safety procedures also are necessary. In less developed
countries, these precautions may be overlooked, leading to dangerous
conditions. (See ``A Study of the Lead-Acid Battery Industry and Spent
Lead-Acid Battery Exports,'' June 2003, a copy of which is included in
the RCRA docket established for this proposed rule.)
Recent data show that the primary factors influencing decisions to
export SLABs from the United States include the price of scrap lead,
worldwide supply and demand for lead, and the relative price of virgin
lead compared to the price of scrap lead. BCI estimates that in 1995,
approximately 1,078,674 tons of recoverable lead was available from
batteries consumed domestically. BCI also reports that, based on
Department of Commerce data, approximately 104,614 tons of battery
scrap lead were exported in 1995. In contrast, approximately 269,171
metric tons of SLABs were exported in 2006 based on more recent data
from the International Trade Commission, Environment Canada, and
Secretaria de Medio Ambiente y Recursos Naturales (SEMARNAT). Such a
large increase in exports may be in large part due to recent increases
in the domestic and international price of lead.
According to the annual ``Mineral Commodity Summaries'' published
by the U.S. Geological Survey (USGS), the average price of lead for
North American producers increased by 77% from 43.7 cents/pound in 1999
to 77.8 cents/pound in 2006. The average price as reported on the
London Metal Exchange increased by 154% during those same years from
22.8 cents/pound to 58.0 cents/pound. In addition, while export
shipments destined for locations in many countries are subject to
duties or tariffs on any exported SLABs, Canadian and Mexican importers
are allowed, under the conditions of the North American Free Trade
Agreement (NAFTA), to import SLABs without the usual surcharge. Indeed,
data show that Canada and Mexico are the major destination countries to
which U.S. SLABs have been exported in recent years. For example, in
2006 U.S. SLAB exports to Mexico and Canada were estimated to be
199,000 metric tons and 66,000 metric tons, respectively (based on data
from Mexican and Canadian government sources). Comparing this
information to data from the U.S. International Trade Commission, it is
estimated that only 1.8% of SLAB exports are destined for countries
other than Mexico or Canada. (See the EPA Cost Assessment \9\ prepared
in support of this proposed action.)
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\9\ Cost Assessment for the Proposed Rule on Exports and Imports
of Hazardous Waste Destined for Recovery Among OECD Countries and
Exports of Spent Lead-Acid Batteries from the U.S.
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3. How are SLABs currently regulated in the United States?
Under the current Federal hazardous waste regulations established
pursuant to RCRA, SLABs are hazardous wastes if the batteries exhibit
one or more of the characteristics of hazardous waste provided in 40
CFR 261, subpart C (e.g., corrosivity (D001), or toxicity for lead
(D008)). SLABs typically exhibit the toxicity characteristic for lead
and, therefore, are defined as hazardous wastes.
(a) SLABs Sent for Disposal Within the United States
If a generator disposes, rather than reclaims, SLABs, the SLABs
would need to be managed in compliance with the Subtitle C hazardous
waste management regulations, which could include the part 273
universal waste rules. However, in all instances, SLABs that are
disposed of must be managed at a RCRA Subtitle C disposal facility and
are subject to the Land Disposal Restriction requirements of 40 CFR
part 268.
The universal waste regulations, promulgated on May 11, 1995, were
created to provide a streamlined set of management regulations
governing the collection and management of certain widely generated
hazardous wastes, such as spent batteries. For the purposes of the
universal waste regulations, the definition of ``battery'' includes
SLABs. While SLABs managed as universal waste may be drained of
sulphuric acid, the battery casings must be intact. SLABs that have
partially or wholly crushed casings cannot be managed as universal
waste.
A universal waste handler is required to ensure that the SLABs do
not spill or leak and that they are stored in a structurally sound
container. In addition, depending upon the amount of SLABs that are
accumulated, a battery handler may be required to track shipments of
the SLABs sent off-site for reclamation or other management. Universal
waste handlers are not allowed to treat their waste; however, they can
conduct certain activities (e.g., sorting, regeneration \10\, etc.)
provided the battery casings remain intact.
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\10\ Regeneration under 40 CFR part 266, subpart G, includes
only replacing drained electrolyte fluids and replacing ``bad''
battery cells. (See 48 FR at 14496.)
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Other general provisions to which all universal waste handlers are
subject include labeling/marking, accumulation time limits, employee
training, and response to releases of hazardous waste. Off-site
shipments of universal wastes do not require a hazardous waste
manifest, provided they are sent to another universal waste handler or
a specified destination facility, and are shipped by an authorized
universal waste transporter.
(b) SLABs Sent for Reclamation Within the United States
When reclaimed, SLABs are exempt from most of the RCRA Subtitle C
hazardous waste regulations, but are subject to the regulations in part
266, subpart G. (See 40 CFR Sec. 261.6(a)(2)(iv).) Alternatively, they
can also be managed as a universal waste and subject to the universal
waste regulations in 40 CFR part 273. Thus, generators that send SLABs
off-site for reclamation may choose to manage their SLABs either as a
universal waste, in accordance with
[[Page 58395]]
the management standards in 40 CFR part 273, or in accordance with the
management standards in 40 CFR part 266, subpart G.
Under the provisions of 40 CFR part 266, subpart G, persons who
generate, collect, transport, or store SLABs for direct regeneration or
reclamation are exempt from the bulk of the RCRA hazardous waste
regulations (40 CFR parts 262 through 266, 270, 124 and the EPA
notification and identification number requirements). However, 40 CFR
part 266, subpart G imposes certain requirements on reclaimers of SLABs
who do not store prior to reclamation, and on facilities that store
SLABs destined for reclamation, but do not conduct any reclamation. In
addition, owners or operators of facilities that both store and reclaim
SLABs are required to comply with the EPA notification and
identification number requirements and all applicable hazardous waste
management facility provisions in parts 264/265, 270, and 124, and are
subject to 40 CFR parts 261, Sec. 262.11, and applicable provisions
under part 268.
4. What international agreements apply to the export of SLABs?
There are two major international agreements that expressly address
the export of SLABs: (1) The Basel Convention on the Control of
Transboundary Movements of Hazardous Wastes and Their Disposal (Basel
Convention); and (2) the Amended 2001 OECD Decision (see II.A.4 for
more information). This proposal would harmonize the EPA SLAB export
requirements with both of these international agreements.
As noted in footnote 1, the Basel Convention is a multilateral
international agreement governing the transboundary movements of
hazardous wastes. Among other things, the Basel Convention includes a
requirement for notice and written consent for transboundary movements
of hazardous waste between trading countries. SLABs are covered under
the Basel Convention as a hazardous waste and are thus subject to the
notice and consent requirements of the Basel Convention. The United
States is a signatory to the Convention, but has not yet ratified it
and is therefore not legally bound to its requirements.
The Amended 2001 OECD Decision regulates the transboundary
movements of hazardous wastes (e.g. wastes subject to Amber control
procedures) destined for recovery within OECD Member countries. The
Amended 2001 OECD Decision lists SLABs, whether whole or crushed, as
subject to the Amber control procedures.
Currently, under the RCRA hazardous waste regulations, SLABs can be
managed either in accordance with the special regulations under 40 CFR
part 266, subpart G or in accordance with the universal waste
regulations, as discussed above. Under part 266, subpart G, SLABs that
are destined for reclamation are currently exempt from the RCRA export
requirements in 40 CFR part 262, subpart E and subpart H (including the
notice and consent requirements).
On the other hand, under the universal waste regulations, exporters
of SLABs for reclamation are subject to the export requirements in 40
CFR part 273 (including the notice and consent requirements) or, if the
SLABs will be exported to an OECD Member country for recovery, the
export requirements (including notice and consent) in 40 CFR part 262,
subpart H, apply. In addition, even in situations where U.S. exporters
are not subject to the notice and consent requirements, U.S. exporters
may still be required to notify the importing OECD Member country of
their intention to export batteries, pursuant to contracts with foreign
consignees. This is because SLABs, identified by the Amended 2001 OECD
Decision as wastes subject to Amber control procedures, are generally
considered to be hazardous waste under the national procedures of the
importing Member countries.
5. How does EPA propose to revise the SLAB regulations under 40 CFR
part 266, subpart G?
EPA proposes to amend the SLAB regulations under 40 CFR part 266,
subpart G, to require that exporters and transporters handling SLABs
destined for reclamation in a foreign country to comply with the same
requirements specified in the universal waste regulations under 40 CFR
part 273. Specifically, an exporter who sends the SLABs to a foreign
destination other than to those OECD countries specified in 40 CFR
262.58(a)(1) would have to:
(a) Comply with the requirements applicable to a primary exporter
in 40 CFR 262.53, 262.56(a) (1) through (4), (6), 262.56(b) and 262.57;
(b) export such SLABs only upon consent of the receiving country and in
conformance with the EPA Acknowledgement of Consent as defined in
subpart E of 40 CFR part 262 of this chapter; and (c) provide a copy of
the EPA Acknowledgment of Consent for the shipment to the transporter
transporting the shipment for export. In addition, a transporter
transporting a shipment of SLABs to a foreign destination other than to
those OECD countries specified in 40 CFR 262.58(a)(1) would not be able
to accept a shipment if the transporter knew the shipment does not
conform to the EPA Acknowledgment of Consent, and would have to ensure
that: (a) a copy of the EPA Acknowledgment of Consent accompanies the
SLAB export shipment; and (b) the shipment is delivered to the facility
designated by the person initiating the SLAB export shipment.
For SLABs destined for reclamation in OECD countries specified in
40 CFR 262.58(a)(1), exporters and transporters would be subject to the
requirements of 40 CFR part 262, subpart H, the requirements governing
hazardous waste shipments to OECD countries.
C. Exception Report Revisions for Exports Under Subparts E and H of 40
CFR Part 262
EPA proposes to replace ``EPA Administrator'' with ``the Office of
Enforcement and Compliance Assurance, Office of Federal Activities,
International Compliance Assurance Division (2254A), Environmental
Protection Agency, 1200 Pennsylvania Avenue, NW., Washington, DC
20460'' in both Sec. 262.55 and in Sec. 262.87(b).
By providing a specific address for the submission of all exception
reports required by 40 CFR part 262, subparts E and H, EPA can ensure
better oversight of (1) return shipments to the U.S. and (2) compliance
with the exception reporting requirements without any additional
regulatory burden for U.S. exporters. In this proposed rule, EPA is
making very clear that submission of these export exception reports
must be to the same specific EPA address that receives all export
notifications and export annual reports, and with no substitution for
comparable State agencies. States that are interested in receiving a
parallel copy of the exception report will still be able to require the
submission of a copy to their State Director in addition to sending it
to the above federal address.
D. Import Revisions
EPA proposes to amend the import requirements specified in Sec.
262.60(e) to require that the U.S. importer provide the transporter
with a copy of the documentation confirming EPA's consent to the
hazardous waste import, specified under a notice submitted by the
competent authority of the country of export. This documentation must
accompany each RCRA hazardous waste shipment and be submitted by the
U.S. receiving facility to EPA along with the RCRA hazardous waste
manifest as
[[Page 58396]]
required under Sec. Sec. 264.71(a)(3) and 265.71(a)(3).
While EPA currently requires that U.S. receiving facilities submit
a copy of the hazardous waste manifest to EPA to document individual
hazardous waste import shipments, it has proved difficult to match
individual hazardous waste import shipments against a given approved
notice of intent to export from a foreign country. In part, this is
because a given destination facility in the United States could be
receiving the same hazardous waste from the same foreign exporter under
more than one approved notice. Adding this requirement will enable EPA
to match the submitted RCRA hazardous waste manifests for individual
import shipments against the approved import notice that typically
covers the twelve months of imports. Being able to do so will enable
EPA to determine when any import shipments claiming coverage under that
specific notice would or would not be in accordance with the terms of
the approved notice, thus improving our oversight of such imports.
EPA currently responds to specific notices of intent to export
hazardous waste from a foreign country into the United States with
either a written response (e.g., written consent or objection) or a
tacit consent. Tacit consents are allowable for imports subject to
EPA's OECD regulations, as specified in 40 CFR part 262, subpart H. For
such imports, the exporting country may assume tacit consent to the
proposed shipments by EPA if no written response from EPA has been
received by the exporting country thirty working days from the date EPA
sends the exporting country a letter acknowledging receipt of the
notice. Because EPA's consents are currently either tacit or sent in
writing only to the competent authority of the exporting country, EPA
will need to provide or otherwise make available to U.S. importers
documentation confirming the Agency's consent. EPA is considering and
soliciting comments on what would provide adequate documentation of the
Agency's written or tacit consent to a specific notice, and how best to
provide that information to U.S. importers.
III. Summary of This Proposed Rule and Changes
A. Changes to 40 CFR Part 262, Subpart E
This proposed rule amends the exception reporting requirements in
Sec. 262.55 to specify that all exception reports be submitted to the
Office of Enforcement and Compliance Assurance's Office of Federal
Activities in Washington, DC, rather than to the Administrator. In
addition, the proposal also updates Sec. 262.58(a) to reflect that
export shipments of SLABs being managed under 40 CFR part 266, subpart
G that are destined for recovery in one of the OECD Member countries
listed in Sec. 262.58(a)(1) are subject to the requirements of subpart
H. Finally, the proposal adds language in Sec. 262.58(b) of subpart E
to clarify that hazardous waste exports subject to subpart E and
hazardous waste imports subject to subpart F are not subject to subpart
H in order to reduce confusion for U.S. exporters and importers.
B. Changes to 40 CFR 262.60(e), Subpart F
This proposed rule includes the requirement that a U.S. importer
provide the transporter a copy of the documentation confirming EPA's
consent to the import of hazardous waste when the importer provides the
transporter with an additional copy of the manifest.
C. Changes to 40 CFR Part 262, Subpart H
All but the last three changes listed below are necessary to
conform to the revisions in the Amended 2001 OECD Decision. These
changes range from substantive revisions and amendments to changes in
terminology to simple editorial changes. Collectively, these changes
serve to implement the Amended 2001 OECD Decision, as well as clarify
certain sections that were previously ambiguous to the regulated
community. Changes to 40 CFR part 262, subpart H include:
1. Changes in Terminology
In the Amended 2001 OECD Decision, the OECD Council updated several
terms and definitions used in the 1992 Decision. EPA believes that
these changes do not result in substantive changes to the intent of the
requirements, but merely bring them in line with current terminology
used in practice and in other international agreements. To limit any
unnecessary confusion between the U.S. regulations and those of other
OECD Member countries and to promote consistency with the Amended 2001
OECD Decision, this proposed rule adopts these changes in terminology.
Thus, EPA proposes to change the following terminology:
(a) ``Transfrontier'' to ``transboundary'';
(b) ``Tracking document'' to ``movement document'';
(c) ``Amber-list controls'' to ``Amber control procedures'';
(d) ``Notifier'' to ``exporter''; and
(e) ``Consignee'' to ``importer.'' \11\
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\11\ The change from ``consignee'' to ``importer'' is only being
made in 40 CFR part 262 subpart H, and does not affect the use of
consignee in 40 CFR part 262 subpart E.
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2. The Number of Different Levels of Control Is Reduced From Three
(Green, Amber, and Red) to Two (Green and Amber) and the Waste Lists
Have Been Updated
The 2001 OECD Decision replaced the OECD three-tier waste list
(Green, Amber, Red) system with a two-tiered system (Green and Amber)
to conform to the Basel Convention waste lists more closely. Further,
the revised OECD waste lists, as provided by the 2004 OECD Amendment,
better correspond to those of the Basel Convention. Accordingly, we are
proposing to make these same conforming changes to EPA's OECD rule.
Wastes subject to the Green control procedures are those wastes
listed in Parts I and II of Appendix 3 to the Amended 2001 OECD
Decision. Part I contains wastes listed in Annex IX of the Basel
Convention, to which the OECD has made and noted adjustments, as
appropriat