Oil Pollution Prevention; Spill Prevention, Control, and Countermeasure Plan Requirements-Amendments, 77266-77293 [E6-21509]
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Federal Register / Vol. 71, No. 247 / Tuesday, December 26, 2006 / Rules and Regulations
paragraph (a)(1)(iii) of this section shall
be the following:
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I Par. 10. Section 1.964–1T is amended
by revising the first sentence of
paragraph (c)(2) and the last sentence of
paragraph (c)(5)(i) to read as follows:
§ 1.964–1T Determination of the earnings
and profits of a foreign corporation
(temporary).
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(c) * * *
(2) * * * For the first taxable year of
a foreign corporation beginning after
April 25, 2006, in which such foreign
corporation first qualifies as a controlled
foreign corporation (as defined in
section 957 or 953) or a noncontrolled
section 902 corporation (as defined in
section 904(d)(2)(E)), any method of
accounting or taxable year allowable
under this section may be adopted, and
any election allowable under this
section may be made, by such foreign
corporation or on its behalf
notwithstanding that, in previous years,
its books or financial statements were
prepared on a different basis, and
notwithstanding that such election is
required by the Internal Revenue Code
or regulations to be made in a prior
taxable year. * * *
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(5) * * * (i) * * * In the event that
the United States shareholders of the
controlled foreign corporation do not, in
the aggregate, own (within the meaning
of section 958(a)) more than 50 percent
of the total combined voting power of
all classes of the stock of such foreign
corporation entitled to vote, the
controlling United States shareholders
of the controlled foreign corporation
shall be all those United States
shareholders who own (within the
meaning of section 958(a)) stock of such
corporation.
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Cynthia Grigsby,
Senior Federal Register Liaison Officer,
Publications and Regulations Branch, Legal
Processing Division, Associate Chief Counsel
(Procedure and Administration).
[FR Doc. E6–22024 Filed 12–22–06; 8:45 am]
BILLING CODE 4830–01–P
ENVIRONMENTAL PROTECTION
AGENCY
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40 CFR Part 80
Regulation of Fuels and Fuel Additives
CFR Correction
In Title 40 of the Code of Federal
Regulations, parts 72 to 80, revised as of
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July 1, 2006, on page 695, § 80.75 is
corrected by reinstating paragraphs
(a)(2)(ix) and (a)(2)(x) to read as follows:
§ 80.75
Reporting requirements.
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(a) * * *
(2) * * *
(ix) In the case of butane blended with
reformulated gasoline or RBOB under
§ 80.82:
(A) Identification of the butane batch
as complying with the provisions of
§ 80.82;
(B) Identification of the butane batch
as commercial or non-commercial grade
butane;
(C) The batch number of the butane;
(D) The date of production of the
gasoline produced using the butane
batch;
(E) The volume of the butane batch;
(F) The properties of the butane batch
specified by the butane supplier, or the
properties specified in § 80.82(c) or (d),
as appropriate;
(G) The volume of the gasoline batch
subsequent to the butane blending; and
(x) In the case of any imported GTAB,
identification of the gasoline as GTAB.
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[FR Doc. 06–55532 Filed 12–22–06; 8:45 am]
BILLING CODE 1505–01–D
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 112
[EPA–HQ–OPA–2005–0001; FRL–8258–3]
RIN 2050–AG23
Oil Pollution Prevention; Spill
Prevention, Control, and
Countermeasure Plan Requirements—
Amendments
Environmental Protection
Agency.
ACTION: Final rule.
AGENCY:
SUMMARY: The Environmental Protection
Agency (EPA or the Agency) is
amending the Spill Prevention, Control,
and Countermeasure (SPCC) Plan
requirements by: first, providing the
option for owners and operators of
facilities that store 10,000 gallons of oil
or less and meet other qualifying criteria
to self-certify their SPCC Plans in lieu
of review and certification by a
Professional Engineer; second,
providing an alternative to the general
secondary containment requirement
without requiring a determination of
impracticability for facilities that have
particular types of oil-filled equipment;
third, defining and exempting particular
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vehicle fuel tanks and other on-board
bulk oil storage containers used for
motive power; and fourth, exempting
mobile refuelers from the sized
secondary containment requirements for
bulk storage containers. The Agency
also is removing and reserving the SPCC
requirements for animal fats and
vegetable oils that are specific to
onshore oil production facilities,
onshore oil drilling and workover
facilities, and offshore oil drilling,
production, or workover facilities.
Finally, the Agency is extending the
SPCC compliance dates for farms. These
changes significantly reduce the burden
imposed on the regulated community
for complying with the SPCC
requirements, while maintaining
protection of human health and the
environment. In a separate document in
this Federal Register, the Agency is
proposing to extend the compliance
dates for all facilities.
DATES: This final rule is effective
February 26, 2007.
ADDRESSES: The public docket for this
final rule, Docket ID No. EPA–HQ–
OPA–2005–0001, contains the
information related to this rulemaking,
including the response to comment
document. All documents in the docket
are listed in the https://
www.regulations.gov index. Although
listed in the index, some information
may not be publicly available, e.g.,
Confidential Business Information or
other information the disclosure of
which 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 EPA Docket, EPA/DC, EPA West,
Room B102, 1301 Constitution Ave.,
NW., Washington, DC. The Public
Reading Room is open from 8:30 a.m. to
4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone
number of the Public Reading Room is
202–566–1744, and the telephone
number to make an appointment to view
the docket is 202–566–0276. The EPA
Docket Center suffered damage due to
flooding during the last week of June
2006. The Docket Center is continuing
to operate. However, during the
cleanup, there will be temporary
changes to Docket Center telephone
numbers, addresses, and hours of
operation for people who wish to visit
the Public Reading Room to view
documents. Consult EPA’s Federal
Register notice at 71 FR 38147 (July 5,
2006) or the EPA Web site at https://
www.epa.gov/epahome/dockets.htm for
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current information on docket status,
locations and telephone numbers.
FOR FURTHER INFORMATION CONTACT:
For
general information, contact the
Superfund, TRI, EPCRA, RMP and Oil
Information Center at 800–424–9346 or
TDD 800–553–7672 (hearing impaired).
In the Washington, DC metropolitan
area, call 703–412–9810 or TDD 703–
412–3323. For more detailed
information on specific aspects of this
rule, contact Vanessa E. Rodriguez at
202–564–7913
(rodriguez.vanessa@epa.gov), or Mark
W. Howard at 202–564–1964
(howard.markw@epa.gov), U.S.
Environmental Protection Agency, 1200
Pennsylvania Avenue, NW.,
Washington, DC 20460–0002, Mail Code
5104A.
SUPPLEMENTARY INFORMATION:
The
contents of this preamble are:
I. General Information
II. Entities Potentially Affected by This Rule
III. Statutory Authority and Delegation of
Authority
IV. Background
V. Today’s Action
A. Qualified Facilities
1. Overview of the Qualified Facilities
Proposal
2. Summary of This Final Rule for
Qualified Facilities
3. Eligibility Criteria
a. Total Facility Oil Storage Capacity
Threshold
b. Reportable Discharge History
4. Requirements for Qualified Facilities
a. Self-Certification of Plan and Plan
Amendment
b. Elements of Self-Certification and Plan
Amendments for Owners and Operators
of Qualified Facilities
c. Environmental Equivalence and
Impracticability Determinations
B. Qualified Oil-Filled Operational
Equipment
1. Oil-Filled Operational Equipment
Definition
2. Oil-Filled Manufacturing Equipment
3. Eligibility Criteria
a. Reportable Discharge History
b. Consideration of Alternative
Qualification Criteria
4. Requirements for Qualified Oil-Filled
Operational Equipment in Lieu of
Secondary Containment
a. Contingency Plans and Written
Commitment of Manpower, Equipment
and Materials
b. Inspections or Monitoring Program
c. Alternative Options Considered
5. Qualified Oil-Filled Operational
Equipment and Qualified Facilities
Overlap
C. Motive Power
1. Definition of Motive Power
2. Exemption
D. Mobile Refuelers
1. Definition of Mobile Refueler
2. Amended Requirements
E. Animal Fats and Vegetable Oils
F. Extension of Compliance Dates for
Farms
1. Eligibility Criteria
2. Compliance Date Extension for Farms
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
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 &
Safety Risks
H. Executive Order 13211—Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Congressional Review Act
I. General Information
The Environmental Protection Agency
(EPA or the Agency) is amending the
Spill Prevention, Control, and
Countermeasure (SPCC) Plan
requirements of the Oil Pollution
Prevention regulation at 40 CFR part
112 to streamline the regulatory
requirements for owners and operators
of a subset of facilities by: (1) Providing
an option to allow the owners or
operators of facilities with an oil storage
capacity of 10,000 gallons or less and
who meet other qualifying criteria to
self-certify their SPCC Plans in lieu of
review and certification by a
Professional Engineer; (2) allowing
owners and operators of facilities that
have particular types of oil-filled
operational equipment to use an oil spill
contingency plan along with an
inspection or monitoring program as an
alternative to secondary containment for
qualified equipment without requiring a
determination of impracticability; (3)
providing an exemption for newly
defined ‘‘motive power containers’’; and
(4) exempting mobile refuelers from the
specifically sized secondary
containment requirements for bulk
storage containers. In addition, the
Agency is removing and reserving
certain SPCC requirements for animal
fats and vegetable oils; and is extending
the compliance dates for farms. The
purpose of this rulemaking is to provide
streamlined, alternative approaches for
compliance with oil spill prevention
requirements for these entities, and to
improve net welfare by reducing the
costs of regulation and improving
compliance, resulting in greater
environmental protection.
II. Entities Potentially Affected by This
Rule
Industry sector
NAICS code
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Oil Production ..................................................................................................................................................................
Farms ...............................................................................................................................................................................
Electric Utility Plants ........................................................................................................................................................
Petroleum Refining and Related Industries .....................................................................................................................
Chemical Manufacturing ..................................................................................................................................................
Food Manufacturing .........................................................................................................................................................
Manufacturing facilities using and storing animal fats and vegetable oils (AFVO) ........................................................
Metal Manufacturing ........................................................................................................................................................
Other Manufacturing ........................................................................................................................................................
Real Estate Rental and Leasing ......................................................................................................................................
Retail Trade .....................................................................................................................................................................
Contract Construction ......................................................................................................................................................
Wholesale Trade ..............................................................................................................................................................
Other Commercial ............................................................................................................................................................
Transportation ..................................................................................................................................................................
Arts Entertainment & Recreation .....................................................................................................................................
Other Services (Except Public Administration) ...............................................................................................................
Petroleum Bulk Stations and Terminals ..........................................................................................................................
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111, 112
2211
324
325
311, 312
311, 325
331, 332
31–33
531–533
441–446, 448,
451–454
23
42
492, 541, 551,
561–562
481–488
711–713
811–813
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Federal Register / Vol. 71, No. 247 / Tuesday, December 26, 2006 / Rules and Regulations
Industry sector
NAICS code
Education .........................................................................................................................................................................
Hospitals & Other Health Care ........................................................................................................................................
Accommodation and Food Services ................................................................................................................................
Fuel Oil Dealers ...............................................................................................................................................................
Gasoline stations .............................................................................................................................................................
Information Finance and Insurance .................................................................................................................................
Mining ..............................................................................................................................................................................
Warehousing and Storage ...............................................................................................................................................
Religious Organizations ...................................................................................................................................................
Military Installations .........................................................................................................................................................
Pipelines ..........................................................................................................................................................................
Government .....................................................................................................................................................................
The list of potentially affected entities
in the above table 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 this table. If you have questions
regarding the applicability of this action
to a particular entity, consult the person
listed in the preceding section entitled
FOR FURTHER INFORMATION CONTACT.
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III. Statutory Authority and Delegation
of Authority
Section 311(j)(1)(C) of the Clean Water
Act (CWA or the Act), 33 U.S.C.
1321(j)(1)(C), requires the President to
issue regulations establishing
procedures, methods, equipment, and
other requirements to prevent
discharges of oil from vessels and
facilities and to contain such discharges.
The President delegated the authority to
regulate non-transportation-related
onshore facilities to EPA in Executive
Order 11548 (35 FR 11677, July 22,
1970), which has been replaced by
Executive Order 12777 (56 FR 54757,
October 22, 1991). A Memorandum of
Understanding (MOU) between the U.S.
Department of Transportation (DOT)
and EPA (36 FR 24080, November 24,
1971) established the definitions of
transportation-related and nontransportation-related facilities. A MOU
among EPA, the U.S. Department of the
Interior (DOI), and DOT, effective
February 3, 1994, has re-delegated the
responsibility to regulate certain
offshore facilities from DOI to EPA.
IV. Background
On July 17, 2002, EPA published a
final rule amending the SPCC rule,
formally known as the Oil Pollution
Prevention regulation (40 CFR part 112),
promulgated under the authority of
section 311(j) of the CWA. (The SPCC
rule was originally promulgated on
December 11, 1973 (38 FR 34164).) This
rule included revised requirements for
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SPCC Plans and for Facility Response
Plans (FRPs). It also included new
subparts outlining the requirements for
various classes of oil; revised the
applicability of the regulation; amended
the requirements for completing SPCC
Plans; and made other modifications (67
FR 47042). The revised rule became
effective on August 16, 2002. After
publication of this rule, several
members of the regulated community
filed legal challenges to certain aspects
of the rule. Most of the issues raised in
the litigation have been settled,
following which EPA published
clarifications in the Federal Register to
several aspects of the revised rule (69
FR 29728, May 25, 2004).1 In addition,
concerns were raised about the
implementability of certain aspects of
the 2002 rule.
EPA has extended the dates for
compliance with the 2002 rule by
extending the dates for amending and
implementing revised SPCC Plans in 40
CFR 112.3(a), (b), and (c), most recently
by notice dated February 17, 2006 (71
FR 8462). Please see the Federal
Register notice for further discussion on
the compliance extensions. EPA took
the most recent action in order to allow
time to finalize the revisions in today’s
final rule and to provide the regulated
community time to review and
understand the material presented in
the SPCC Guidance for Regional
Inspectors, which was made available in
December of 2005. The Agency also was
concerned that the effects of the
September 2005 hurricanes on many
industry sectors might adversely impact
their ability to meet the compliance
dates if no extension was provided.
October 31, 2007 is the current
deadline for amending and
implementing revised SPCC Plans for
1 American Petroleum Institute v. Leavitt, No.
1:102CV02247 PLF and consolidated cases (D.D.C.
filed Nov. 14, 2002). The remaining issue to be
decided concerns the definition of ‘‘navigable
waters’’ in § 112.2.
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621, 622
721, 722
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4471
51, 52
212
493
813110
928110
4861, 48691
92
facilities (including mobile facilities)
that were in operation on or before
August 16, 2002. Facilities that came
into operation after August 16, 2002 also
must prepare and implement an SPCC
Plan on or before October 31, 2007. As
discussed in Section V.F of this
preamble, today’s final rule provides an
additional extension of the compliance
date for farms. Today’s rule, which is
effective February 26, 2007, does not
modify the compliance dates for owners
and operators of facilities other than
farms. Elsewhere in today’s Federal
Register, EPA is proposing to extend the
compliance dates for owners and
operators of facilities until July 1, 2009
based on further SPCC regulatory
revisions that EPA is considering, and
that it expects to propose in 2007.
On September 20, 2004, EPA
published two Notices of Data
Availability (NODAs). The first NODA
solicited comments on submissions to
EPA that suggested more focused
requirements for owners and operators
of facilities subject to the SPCC rule that
handle oil below a certain threshold
amount, referred to as ‘‘certain
facilities’’ (69 FR 56182). Streamlined
approaches for owners and operators of
facilities with oil capacities below a
certain threshold were discussed in the
NODA-related documents. The second
NODA solicited comments on whether
alternate regulatory requirements would
be appropriate for owners and operators
of facilities with oil-filled and process
equipment (69 FR 56184). EPA has
reviewed the public comments and data
submitted in response to the NODAs in
developing today’s final rule.
Additionally, on December 2, 2005,
EPA issued the SPCC Guidance for
Regional Inspectors. This guidance
document is intended to assist regional
inspectors in reviewing implementation
of the SPCC rule at a regulated facility.
The guidance document is designed to
facilitate an understanding of the rule’s
applicability, to help clarify the role of
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the inspector in the review and
evaluation of a facility owner or
operator’s compliance with the
performance-based SPCC requirements,
and to provide a consistent national
policy on several SPCC-related issues.
The guidance is available to owners and
operators of facilities that may be
subject to the requirements of the SPCC
rule and to the general public on the
Agency’s Web site at https://
www.epa.gov/oilspill. This guidance
document is a living document and will
be revised, as necessary, to reflect any
relevant future regulatory amendments,
including today’s action.
Based on the comments received on
the NODAs, as well as other information
received, EPA proposed to amend the
SPCC rule to address a number of issues
raised, including those pertaining to
qualified facilities, qualified oil-filled
operational equipment, motive power
containers, airport mobile refuelers,
animal fats and vegetable oils, and the
compliance date for farms. (See 70 FR
73524, December 12, 2005.) EPA
discusses each of these issues in Section
V of this preamble. The preamble
generally discusses the comments
received on the proposal, EPA’s
response, and any modifications made
to the proposal. For a more detailed
discussion of the comments received
and EPA’s response, see ‘‘Summary and
Response to Comments,’’ which is
included in the docket for today’s final
rule.
The scope of today’s final rule was
intended to address only certain
targeted areas of the SPCC requirements,
and a number of issues and concerns
raised by the regulated community. As
highlighted in the EPA Regulatory
Agenda and the 2005 OMB report on
‘‘Regulatory Reform of the U.S.
Manufacturing Sector,’’ EPA is
considering further amendments to
address other areas where regulatory
reform may be appropriate. For these
additional areas, the Agency expects to
issue a proposed rule in 2007. Areas
where regulatory reform may be
appropriate include, and are not limited
to, oil and natural gas exploration and
production, farms, and Tier I facilities.
EPA, in conjunction with DOE, has been
conducting an energy impact analysis of
the SPCC requirements, and, to the
extent that the analysis is available, will
consider it to inform the Agency’s 2007
rulemaking.
Because it is highly unlikely that the
Agency will be able to promulgate such
regulatory amendments before the
current October 31, 2007 compliance
date for SPCC becomes effective, EPA
believes it is appropriate to provide an
extension of the compliance date. Such
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an extension has been proposed
elsewhere in today’s Federal Register.
The Agency is not in a position, at
this time, to indicate all the areas for
possible regulatory reform that may be
addressed as part of the 2007 SPCC
proposal. Nevertheless, the Agency
recognizes that owners and operators of
facilities need time to determine which
changes may be made to the rules that
may impact the requirements they are
subject to in order to determine when
they need to comply with the new
requirements.
This approach would allow those
potentially affected in the regulated
community an opportunity to make
changes to their facilities and to their
SPCC Plans necessary to comply with
the revised requirements, rather than
with the existing requirements.
Regarding modifications of the SPCC
regulations, EPA is proposing in a
separate notice in today’s Federal
Register to extend the deadlines for
compliance to July 1, 2009.
V. Today’s Action
A. Qualified Facilities
1. Overview of the Qualified Facilities
Proposal
On December 12, 2005 (70 FR 73524),
EPA proposed to amend the SPCC rule
to provide an option to allow the owner
or operator of a facility that meets the
qualifying criteria (hereafter referred to
as a ‘‘qualified facility’’) to self-certify
the facility’s SPCC Plan in lieu of review
and certification by a licensed
Professional Engineer (PE). EPA
proposed to amend § 112.3 to describe
the SPCC eligibility criteria that a
regulated facility must meet in order to
be considered a qualified facility.
As proposed, the eligibility criteria for
a qualified facility would be a facility
subject to the SPCC rule that (1) has an
aggregate oil storage capacity of 10,000
gallons or less; and (2) had no
discharges as described in § 112.1(b)
during the ten years prior to selfcertification. Self-certified Plans could
not include ‘‘environmentally
equivalent’’ alternatives to required Plan
elements as provided in § 112.7(a)(2) or
contingency planning in lieu of
secondary containment as provided in
§ 112.7(d) on the basis of
‘‘impracticability.’’ However, the
proposal included specified
‘‘environmentally equivalent’’ measures
with respect to security and integrity
testing that would be available to
facility owners and operators that
choose to self-certify. Self-certification
would be optional for owners and
operators of facilities meeting the
eligibility criteria, so that those owners
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and operators of qualified facilities that
found the existing rules more costeffective in achieving compliance with
the SPCC requirements, would continue
to have the option of complying with
the streamlined approach or could
choose to comply with the existing
SPCC requirements (including the PE
certification) to take advantage of the
flexibility offered by PE-certified
impracticability determinations and
environmentally equivalent measures.
In general, the Agency agrees with the
commenters who supported the
qualified facilities proposal for selfcertification and believe that this
revision will relieve regulatory burden
on small oil storage facilities. As one
commenter noted, self-certification
should result in greater compliance
rates across the board. Therefore,
today’s rule finalizes the proposed
provision with a few modifications.
As described in the preamble to the
proposed rule, EPA also considered, but
did not propose, a multi-tiered structure
option based on an analysis prepared for
the U.S. Small Business
Administration’s (SBA) Office of
Advocacy that included a tiered system
for facilities that have total oil storage
capacities between 1,321 and 5,000
gallons, between 5,001 and 10,000
gallons, and greater than 10,000 gallons.
Under this option, Tier I facilities (1,321
to 5,000 gallons oil storage capacity)
would not need a written SPCC Plan
(and therefore no PE certification), but
would adhere to all other SPCC
requirements. Tier II facilities (5,001 to
10,000 gallons oil storage capacity)
would be required to have a written
SPCC Plan, but no PE certification
requirement. Tier III facilities (greater
than 10,000 gallons oil storage capacity)
would be required to have a written
SPCC Plan, certified by a PE. A
significant number of commenters on
the proposed rule supported a multitiered approach.
The Agency continues to believe that
a facility owner or operator cannot
effectively implement an oil spill
prevention program, or any other
program (business or otherwise),
without documentation of that
program’s action items. As a matter of
practice, it would be extremely difficult
for a facility owner or operator to be
able to follow the regulatory
requirements and to comply with all the
recordkeeping components without the
documentation that is the Plan itself.
The Plan also serves as an important
communication and training tool for
both management and oil-handling
personnel at the facility. The sole action
of having to document compliance with
all of the requirements can assist in
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uncovering flaws in the program’s
implementation, and may serve as a tool
to correct them. Additionally, the
documentation of compliance with the
rule’s requirements in a written Plan
serves as a facility-specific oil spill
response and prevention planning
exercise which is designed to improve
oil spill prevention. Nevertheless, the
Agency understands the concerns,
particularly of owners and operators of
facilities with a smaller oil storage
capacity and likely more limited
resources, of the potential effort needed
to develop a complicated Plan. Thus,
the Agency has been exploring the
possibility of developing a further
simplified Plan for facilities that handle
between 1,320 and 5,000 gallons of oil.
However, because the Agency is
considering removing or changing some
of the regulatory requirements and
developing a standardized form/
checklist for ease of implementation, the
Agency chose not to finalize this option
without taking further comment.
Therefore, although EPA is not adopting
a multi-tiered approach in today’s final
rule, the Agency intends to propose a
simplified approach for facilities that
handle between 1,320 and 5,000 gallons
of oil within the near future. In that
proposal, the Agency expects to discuss
the implementation of the SPCC rule for
these facilities.
The preamble to the proposed rule
also described an approach whereby the
Agency would require owners and
operators of qualified facilities to make
a one-time notification to EPA if they
have been in operation or subject to the
SPCC requirements for a period less
than ten years from the time of Plan
certification, and therefore could not
show a ten-year clean spill history as a
qualifier. The comments generally
opposed a notification requirement,
arguing that it would impose additional
burden with no clear benefit for the
regulated community. EPA is not
adopting this one-time notification
requirement, because the Agency does
not believe it would offer any further
environmental protection. The
additional burden of a notification
requirement was not considered
necessary and would be contrary to the
intent of today’s rule.
2. Summary of This Final Rule for
Qualified Facilities
Today’s rule finalizes the proposed
option with modifications to the
reportable discharge history criterion
and to the self-certification limitations
for qualified facilities. The final rule
also places the alternative selfcertification provisions in § 112.6, rather
than in § 112.3(g) as proposed. A facility
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owner or operator may qualify to
prepare a Plan that meets the alternative
requirements in § 112.6 of today’s final
rule, in lieu of a Plan prepared in
accordance with the general
requirements contained in § 112.7 and
the applicable requirements in subparts
B and C of the rule. Finally, today’s
action allows a qualified facility owner
or operator to use environmentally
equivalent measures or an
impracticability determination provided
they are certified by a PE.
To qualify for this option, a facility
must meet the following eligibility
criteria: the facility had no single
discharge as described in § 112.1(b)
exceeding 1,000 U.S. gallons or no two
discharges as described in § 112.1(b)
each exceeding 42 U.S. gallons within
any twelve month period in the three
years prior to the SPCC Plan
certification date, or since becoming
subject to 40 CFR part 112 if the facility
has been in operation for less than three
years, and the facility has 10,000 gallons
or less in aggregate aboveground oil
storage capacity. Discharges as
described in § 112.1(b) that are the
result of natural disasters, acts of war,
or terrorism will not disqualify a facility
owner or operator from using the selfcertification option.
An owner or operator of a qualified
facility may prepare, self-certify and
implement an SPCC Plan that complies
with all of the applicable requirements
of the rule in accordance with § 112.6 of
today’s final rule. No PE certification is
required for qualified facilities’ Plans. A
qualified facility owner or operator also
may choose to prepare a Plan in
accordance with the general Plan
requirements in § 112.7 and applicable
requirements in subparts B and C,
including having the Plan certified by a
Professional Engineer as required under
§ 112.3(d). The qualified facility
approach in today’s final rule is
optional; owners or operators of
facilities that qualify may choose not to
exercise this option.
In proposing this option for facilities
handling smaller amounts of oil, the
Agency sought to focus on those smaller
operations that may be concerned about
the impact of utilizing a PE on their
limited budget. Some of the current
noncompliance with the SPCC
regulation may be attributed to those
concerns. The Agency believes that
providing a simpler, less costly option
for owners and operators of these
smaller, less complex facilities will
improve the overall compliance for the
SPCC regulation, ultimately resulting in
greater environmental protection.
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3. Eligibility Criteria
a. Total Facility Oil Storage Capacity
Threshold
EPA proposed to limit the maximum
aggregate oil storage capacity at a
qualified facility to 10,000 gallons or
less. EPA considered many different
factors before selecting this maximum
storage capacity. As explained in the
preamble to the proposal (70 FR 73529),
EPA has established 10,000 gallons as a
threshold in several other rules relating
to oil discharges. The National Oil and
Hazardous Substances Pollution
Contingency Plan size classes define an
oil discharge to inland waters exceeding
10,000 gallons as a major discharge. An
oil discharge of 10,000 gallons or more
to waters of the U.S. and adjoining
shorelines that could reasonably be
expected to cause substantial harm to
the environment also is one of the
factors used in identifying facilities
whose owners and operators must
prepare and submit a Facility Response
Plan (see 40 CFR 112.20(f)(1)(D). A
number of State regulations also
differentiate regulatory requirements
based on a facility’s total storage
capacity, with some States specifying a
10,000-gallon threshold (e.g., Maryland,
Minnesota, Oregon, New York,
Wisconsin). Finally, 10,000 gallons is a
common storage container size.
More commenters supported than
opposed the proposed threshold
eligibility criterion of total oil storage
capacity of 10,000 gallons or less, while
others offered alternative thresholds.
Many commenters supported the idea of
establishing tiers for qualified facilities.
(As noted earlier, the Agency intends to
propose a more streamlined approach
for owners and operators of facilities
with a total oil storage capacity of 5,000
gallons or less.) Many supporters
believed that the proposed 10,000gallon threshold would reduce the
financial burden on owners and
operators of small facilities. Among
commenters that opposed the threshold,
at least one stated that the proposed
10,000-gallon threshold did not provide
enough regulatory relief to owners and
operators of small facilities, but others
noted that smaller storage sizes do not
necessarily correlate with lower spill
risk.
Facilities handling smaller amounts of
oil are typically simpler in layout and
operation. Most facilities with an oil
storage capacity of 10,000 gallons or less
are in industrial sectors that are endconsumers of oil (i.e. farms, real estate,
rental and leasing, retail trade,
construction [see the Regulatory Impact
Analysis for this action, found in the
docket for today’s final rule]). These
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facilities are commonly not in an oil
production or distribution business and
tend to use oil on-site for heating
purposes, or to fuel emergency power
generators or heavy machinery. The
configuration of the oil-related
equipment tends to be relatively
standard and simple. Oil is commonly
stored in a few bulk storage containers
which are often bought off-the-shelf
from a tank manufacturer or installer
(e.g., standard UL–142 tanks) and
connected with few short lengths of
piping in a standard configuration that
changes relatively little from one facility
to another.
Additionally, these facilities typically
do not have significant transfers of oil
because they do not further distribute
the oil. A survey conducted by EPA of
oil storage facilities (1995 SPCC Survey
of Oil Storage Facilities) found that the
larger the storage capacity at a facility,
the greater the likelihood of larger spills,
more spills, and more cleanup costs
annually. Our regression analyses of the
1995 survey data (see ‘‘Analysis of the
Relationship between Facility
Characteristics and Oil Spill Risk,’’
found in today’s docket) confirmed
similar linkages for facilities with a
greater number of tanks and larger
annual throughput. These analyses were
performed because storage capacity,
number of tanks, and throughput were
identified as important individual
factors in explaining the total annual
spill volume, number of spills, and
cleanup costs. Thus, these factors were
used together in a multivariate
regression model to ensure that these
three variables continue to be
statistically significant variables when
assessing whether there is potential bias
(i.e., an overstatement of the importance
of the variable in explaining the
variation in the dependent variable).
After performing these analyses, storage
capacity and number of tanks were
found to be statistically significant in
relation to all three measures of spill
risk (i.e., total number, volume, and
cleanup costs of oil spills). The Agency
believes simple oil storage
configuration, in conjunction with the
smaller quantities of oil handled at
qualified facilities, makes selfcertification an appropriate alternative.
Therefore, the Agency has decided to
maintain the maximum aggregate oil
storage capacity for qualified facilities at
10,000 gallons as proposed.
The development of streamlined
requirements for owners and operators
of those facilities with a smaller size or
storage volume is not new; industry
standards, engineering codes and
practices, State regulations, local fire
codes and local ordinances often
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recognize the differences between sizes
and complexity of their target facilities
and/or equipment and as a result
incorporate simplified requirements.
The Agency believes that today’s action
provides an alternative compliance
option for owners and operators of
facilities handling smaller amounts of
oil that will ultimately result in
increased environmental protection by
making it easier and less burdensome to
comply.
EPA recognizes that an oil discharge
of less than 10,000 gallons can be
harmful (see 40 CFR part 110, where the
Agency defines what constitutes a
discharge of oil in quantities that may
be harmful). Nevertheless, EPA believes
that it is reasonable to allow owners and
operators of facilities with a capacity of
no more than 10,000 gallons the option
to prepare and implement SPCC Plans
without the involvement of a PE (except
in those cases where environmental
equivalence or an impracticability
determination is requested by an owner
or operator and that the owner or
operator chooses to have a PE certify
part or all of the facility SPCC Plan).
Therefore, the Agency is adopting in
today’s rule a threshold capacity of
10,000 gallons as a criterion for those
facilities that are qualified for selfcertification.
Some commenters argued that the
10,000-gallon threshold would still
preclude owners and operators of
smaller facilities from taking advantage
of the self-certification alternative. For
example, a facility with two 5,000gallon storage containers and a few totes
just exceeds the 10,000-gallon
threshold. Commenters argued that
these kinds of facilities have low
volumes of oil and simple operations,
and that perhaps a slightly higher
threshold would be more appropriate.
The Agency recognizes that regardless
of the threshold quantity selected, there
are likely to be facilities just above that
threshold that will be excluded. To the
extent that facility owners or operators
want to take advantage of the
streamlined approach, they always have
the option of reducing the storage
capacity of oil at their facility by either
removing containers from the facility
inventory, or permanently closing
containers in accordance with § 112.2.
Other commenters suggested higher
threshold quantities, generally based
upon the quantities of oil used or stored
in their particular industry sector. EPA
does not agree that this provides a
rational basis for raising the threshold
limit for qualified facilities. Higher
thresholds would potentially allow
owners and operators of facilities (in
some cases unmanned) with more
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complex operations or more complex oil
system configurations, designs and
layouts, and with the potential for an
increased number of transfers, the
option of foregoing the services of a PE.
Thus, self-certification for owners and
operators of more complex facilities
would not be commensurate with their
potential spill risks.
By limiting the self-certification
option to owners and operators of
facilities with a maximum aggregate oil
storage capacity of 10,000 gallons, the
Agency believes that an owner or
operator of a qualified facility should be
able to self-certify compliance the
facility’s SPCC Plan, and that offering
this simpler and streamlined alternative
will result in greater environmental
protection by improving compliance
with the SPCC rule. Owners and
operators of facilities handling smaller
amounts of oil would still be required
to comply with the SPCC requirements
and to prevent and prepare to respond
to oil discharges to navigable waters and
adjoining shorelines, but they would be
able to do so in a less costly manner. We
believe this alternative certification
provision will prove to be an incentive
for compliance.
b. Reportable Discharge History
Clean Water Act section 311(b)(3)
prohibits ‘‘the discharge of oil * * *
into or upon the navigable waters of the
United States, the adjoining shorelines,
or into or upon the waters of the
contiguous zone’’ or in connection with
specified activities in waters ‘‘in such
quantities as may be harmful * * *.’’
Section 311(b)(4) requires regulations to
define the quantities of oil, ‘‘the
discharge of which may be harmful to
the public health or welfare or the
environment of the United States,
* * *.’’ 33 U.S.C. 1321(b)(3), (4). In part
110, EPA defines a ‘‘discharge of oil in
such quantities that may be harmful’’ as
a discharge of oil that violates
applicable water quality standards; a
discharge of oil that causes a film or
sheen upon the surface of the water or
on adjoining shorelines; or a discharge
of oil that causes a sludge or emulsion
to be deposited beneath the surface of
the water or adjoining shorelines (40
CFR 110.3). The Agency refers to such
discharges as reportable discharges or as
‘‘a discharge as described in § 112.1(b)’’
of the rule. Any person in charge of a
facility must report any such discharge
of oil to waters of the United States,
adjoining shorelines, the contiguous
zone or in connection with specified
activities in waters from the facility to
the National Response Center (NRC) at
1–800–424–8802 immediately. While
EPA recognizes that past discharge
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history does not necessarily translate
into a predictor of future performance,
the Agency believes that discharge
history is a reasonable indicator of a
facility owner or operator’s ability to
develop an SPCC Plan for his smaller oil
storage capacity facility without the
involvement of a PE.
EPA proposed that a qualified facility
subject to the SPCC requirements must
have no reportable oil discharges as
described in § 112.1(b) during the ten
years prior to self-certification or since
becoming subject to the SPCC
requirements, whichever time period is
less. The Agency proposed using a
facility’s reportable discharge history as
a reasonable indicator of the effective
implementation of an SPCC Plan based
on an established record of good oil
spill prevention. The reportable
discharge history criterion was intended
to limit the option of self-certification to
owners and operators of those facilities
that had demonstrated an effective
implementation of spill prevention
measures in the past.
The commenters who supported the
proposed reportable discharge
requirement agree that it is important
for a facility to have a clean spill
history. However, a significant number
of commenters argued against the
proposed reportable discharge history
criterion as an appropriate criterion, and
that the small storage capacity alone
should be sufficient to allow selfcertification. One reason is that some
reportable discharges are not the facility
owner or operator’s fault, but caused by
outside sources. For example, a number
of commenters pointed to the recent
hurricanes in the Gulf Coast states that
led to oil discharges that were not
within the control of the facility owner
or operator. A further reason is that
facilities that have a clean discharge
history might not always remain spillfree. As for the proposed ten-year
period, one commenter stated that
facility owners and operators are only
required to keep records for SPCC Plans
for three years; most owners and
operators keep them for five years.
Another commenter stated that a
discharge history of ten years would
almost be impossible to prove. Another
commenter believed that the
qualification for a qualified facility
should not be based on the ten-year
discharge history, but should be based
on the discharge history under the
current operator. A few commenters
believed that risk of discharge should
determine self-certification.
Additionally, many commenters
recommended alternative discharge
history timeframes in place of the tenyear timeframe EPA proposed. Half of
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the commenters believed that three
years should be the time frame for the
reportable discharge history since the
SPCC record-keeping requirement for
facility owners and operators is three
years. Two commenters mentioned that
if a discharge occurs and the Regional
Administrator (RA) responds, and after
review of the SPCC Plan the RA does
not require an amendment in the Plan,
then the discharge should not count
against the facility owner or operator
when determining its compliance with
a spill-history criterion.
After consideration of the comments
received, EPA is finalizing the
reportable discharge criterion for
qualified facilities but for three years,
rather than ten years. The Agency agrees
with commenters that a ten-year spill
history is unreasonable, particularly
since the facility owner or operator is
only required to keep records for three
years. In addition, EPA is modifying the
types of discharges that must be
considered for this criterion. The final
rule provides that for the three years
prior to the SPCC Plan certification date,
or since becoming subject to 40 CFR
part 112 if the facility has been in
operation for less than three years, the
owner or operator of a facility must
certify that the facility has (1) had no
single discharge as described in
§ 112.1(b) exceeding 1,000 U.S. gallons
or (2) had no two discharges as
described in § 112.1(b) each exceeding
42 U.S. gallons within any twelve
month period. When determining spill
history, the gallon amount specified in
the criterion (either 1,000 or 42) refers
to the amount of oil that actually
reaches waters of the United States,
adjoining shorelines, the contiguous
zone or in connection with specified
activities in waters and not the total
amount of oil spilled. For example, a
facility only experiencing one discharge
over the past ten years in which 1,500
gallons of oil discharged onto the
ground but only 20 gallons reached
waters of the United States (causing a
sheen and reportable to the NRC) would
meet the reportable discharge history
criterion. However, a facility having
1,500 gallon discharge to waters of the
United States would not meet the
reportable discharge history criterion.
In the preamble to the proposed rule,
EPA requested comment on how
extreme events such as natural disasters,
acts of war or terrorism, sabotage or
other calamities might potentially affect
the discharge history criterion for
qualified facilities. Many commenters
stated that it would not be appropriate
to include these events in the discharge
history criterion. The Agency agrees that
those reportable discharges caused by
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external factors beyond the control of
the facility owner or operator such as
natural disasters, acts of war, or
terrorism should not disqualify owners
and operators of otherwise qualified
facilities from taking advantage of the
self-certification option. Therefore, we
have excluded those events from
consideration in the reportable
discharge criterion in today’s final rule.
The Agency did not include sabotage/
vandalism in the final list of reportable
discharge history extreme events
because these are not necessarily
beyond the control or planning ability of
the facility owner or operator. Only
those discharges as described in
§ 112.1(b) that are the result of natural
disasters, acts of war, or terrorism will
not disqualify any owner or operator of
an otherwise qualified facility from
using the self-certification option.
The discharge criterion finalized in
today’s rule is similar to the provision
in § 112.4(a) for discharges that must be
reported to the EPA Regional
Administrator (RA). A discharge that
must be reported to the RA pursuant to
§ 112.4(a) may result from improper
Plan implementation, rather than from a
deficiency in the Plan itself, which
would likely not cause the RA to require
the facility owner or operator to amend
its Plan. Therefore, the EPA does not
agree with the commenters that
suggested excluding those discharges as
described in § 112.1(b) from the
eligibility criterion that have been
investigated by the RA with no
subsequent requirement for a Plan
amendment.
The determination of eligibility based
on reportable discharge history is made
at the time the SPCC Plan is certified—
i.e., when the SPCC Plan is amended to
comply with the SPCC rule revisions in
today’s final rule and those promulgated
in July 2002. Once the compliance date
extension ends, Plans must be amended,
certified and implemented. Any
discharges to navigable waters and
adjoining shorelines that occur from a
qualified facility after the SPCC Plan has
been certified do not impact the
eligibility of an owner or operator of the
qualified facility to take advantage of
the self-certification option. The facility
does not lose eligibility status as a result
of a discharge as described in § 112.1(b),
unless the RA requires an amendment to
the SPCC Plan in accordance with
§ 112.4(d) and specifically requires PEcertification. If an owner or operator
cannot certify that the facility meets the
eligibility criterion at the initial date of
Plan certification, but can later
demonstrate a clean spill history of
three years, as well as compliance with
any remedial actions required by the RA
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following a spill, then a technical
amendment to the Plan can be selfcertified and the Plan can be revised to
allow for qualified status.
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4. Requirements for Qualified Facilities
In today’s rule, the Agency is creating
a new section, § 112.6, with
requirements specific for qualified
facilities whose owners and operators
choose to self-certify their Plans.
Owners and operators of qualified
facilities with an aggregate aboveground
oil storage capacity of 10,000 gallons of
oil or less may choose to comply with
the requirements in § 112.6 by
completing and implementing a selfcertified SPCC Plan. A qualified
facility’s Plan, whether certified by a PE
or self-certified, must comply with all of
the applicable requirements of § 112.7
and subparts B and C of the rule. We
note, however, that a facility’s SPCC
Plan does not need to conform to any
particular format. There is flexibility
with respect to how a facility owner or
operator chooses to maintain the
documentation comprising the facility’s
Plan, just as there is flexibility with
respect to how the owner or operator
chooses to carry out the elements of the
Plan.
a. Self-Certification of Plan and Plan
Amendment
The commenters who supported selfcertification for owners and operators of
qualified facilities believed that it
would relieve burden on the owners and
operators. The commenters who
opposed self-certification did so for four
main reasons. First, some commenters
believe that the preparation of the SPCC
Plan requires scientific, engineering,
and professional judgment skills that are
unique to engineers. Second, some
commenters believe owners and
operators of small facilities often cannot
afford the cost of responding to a spill,
and it is important that the SPCC Plan
is prepared carefully and thoroughly by
a PE. Third, some commenters believe
that not having a PE involved would
adversely affect public health, safety,
and welfare. Fourth, some commenters
believe that the proposal would allow
non-engineers to perform a function that
is only allowed by engineers under the
National Council of Examiners for
Engineering and Surveying, a Model
Law adopted by the majority of States.
The self-certification option is
designed for owners and operators of
those facilities that store smaller
amounts of oil. These smaller amounts
of oil generally translate to facilities
with simpler, pre-engineered
installations, such as restaurants, office
buildings, family farms, automotive
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repair shops, and rural electrical
substations. EPA believes that a
differentiated option for users of smaller
amounts of oil has merit as other official
bodies, such as standards setting
organizations have provided
differentiations in their standards for
smaller users of oil. For example, the
National Fire Protection Association
(NFPA) provides differentiated
requirements based on type of facility
and size of tanks. Specifically, NFPA 30
(Flammable and Combustible Liquids
Code, 2000 Edition) applies to tanks that
exceed 3,000 liters (793 gallons) and
does not apply to facilities storing
flammable and combustible liquids as
covered by NFPA 395, Standard for the
Storage of Flammable and Combustible
Liquids at Farms and Isolated Sites. The
Agency believes that the relative
simplicity of operations at facilities
using smaller amounts of oil has served
as a basis for other official bodies to
develop requirements that are simpler
in scope.
To this end, the Agency is amending
the certification language so that it
clearly states that the owner or operator
of the facility is the certifying official for
those who choose the option to selfcertify the Plan for qualified facilities.
The Agency also intends to develop
materials to assist these owners or
operators in developing SPCC Plans. It
should also be remembered that while
owners and operators of these facilities
may choose not to have their SPCC
Plans certified by a PE, they will still be
required to comply with all of the SPCC
requirements and to develop and
implement a spill prevention program
in accordance with good engineering
practices, and they may do so by
following regulatory guidance, industry
recommended practices and standard
design and operation protocols. Finally,
to the extent that a State has adopted a
law, such as one based on the National
Council of Examiners for Engineering
and Surveying, that requires that a PE to
perform certain functions, including
certifying Plans, nothing in today’s rule
affects whether a facility owner or
operator would be required to utilize a
PE to meet the state or local
requirements since today’s rule does not
pre-empt any State or local
requirements.
The Agency believes providing the
added flexibility of self-certification for
the smaller oil handlers/simpler
operations will yield an increase in
overall compliance for this segment of
the regulated community, which will
result in improved compliance with the
rule and as a result, improve overall
spill prevention and environmental
protection. However, owners or
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operators of some qualified facilities
with complicated operations may
nonetheless find that having a PEcertified Plan offers a more costeffective method of achieving
compliance than the proposed option.
Therefore, a qualified facility owner or
operator could choose to follow the
existing SPCC requirements (including
the PE certification).
The Agency also proposed and is
finalizing today that an owner or
operator of a qualified facility may selfcertify technical amendments to the
Plan, including modification of site
diagrams, and that owners and operators
of facilities with PE-certified Plans that
qualify for self-certification can choose
to self-certify future technical
amendments rather than hire a PE to
certify the technical amendment.
Owners and operators of facilities that
are not eligible to self-certify are
required to have a PE certify such
modifications. In all cases, any technical
amendment in an SPCC Plan must be
certified in writing. As described in the
preamble to the proposed rule, the
Agency notes that under the existing
SPCC regulations, the RA, after
reviewing the facility’s Plan, has the
authority in § 112.4 to require an owner
or operator of a facility that has had a
discharge as described in § 112.1(b) or
that poses an imminent danger of a
discharge as described in § 112.1(b), to
amend its SPCC Plan, including
requiring PE certification in accordance
with § 112.3(d).
b. Elements of Self-Certification and
Plan Amendments for Owners and
Operators of Qualified Facilities
The finalized requirements for owners
and operators of qualified facilities are
similar to those in the proposed
qualified facilities option in the
proposed rule. An owner or operator of
a qualified facility may choose to
comply with the requirements in § 112.6
by completing and implementing a selfcertified SPCC Plan in lieu of having a
PE certified Plan. The SPCC Plan must
comply with all of the applicable
requirements of § 112.7 and subparts B
and C of the rule.
Owners and operators that choose to
self-certify their Plans must certify that
they are familiar with the requirements
of the SPCC rule; they have visited and
examined the facility; the Plan has been
prepared in accordance with accepted
and sound industry practices and
standards; procedures for required
inspections and testing have been
established; the Plan is being fully
implemented; the facility meets the
qualification criteria set forth under
§ 112.3(g); the Plan does not include any
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environmental equivalence measures as
described in § 112.7(a)(2) or
determinations of impracticability
under § 112.7(d) unless each alternative
method and/or determination has been
reviewed and certified by a PE in
accordance with § 112.6(d); and the Plan
and the individual(s) responsible for
implementing the Plan have the full
approval of management and the facility
owner or operator has committed the
necessary resources to fully implement
the Plan.
The qualified facility self-certification
approach is optional. Under today’s
final rule, an owner or operator of a
qualified facility may choose to prepare
and implement a PE-certified SPCC Plan
to comply with the requirements under
40 CFR part 112.
c. Environmental Equivalence and
Impracticability Determinations
Under § 112.7, all facility owners and
operators have the flexibility to deviate
from specific rule provisions if the Plan
states the reason for nonconformance
and if equivalent environmental
protection is provided by some other
means of spill prevention, control, or
countermeasure. These
‘‘environmentally equivalent’’ measures
must be described in the SPCC Plan,
including how the equivalent
environmental protection will be
achieved based on good engineering
practice. Allowance for
‘‘environmentally equivalent’’’
deviations is provided in § 112.7(a)(2),
and the deviations are available only for
the specific requirements listed in
§ 112.7(a)(2), such as fencing and other
security measures, evaluation of the
potential for catastrophic tank failure
due to brittle fracture, integrity testing,
and overfill prevention. Environmental
equivalence is not available for
secondary containment or the
administrative or recordkeeping
requirements of the SPCC rule. As part
of the SPCC Plan, any environmentally
equivalent measures are required to be
certified by a PE and the owner or
operator, and the PE is required to
consider industry standards in the
development of the Plan. Thus, when a
PE certifies a Plan that includes any
environmentally equivalent protection
measure, the PE is certifying that these
alternative measures are consistent with
relevant industry standards.
The SPCC rule also provides
flexibility for owners or operators who
determine that the general secondary
containment requirements in § 112.7(c)
or any of the applicable additional
requirements for secondary containment
in subparts B and C are impracticable.
Where impracticability is demonstrated,
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§ 112.7(d) allows facility owners and
operators the flexibility to instead
develop a contingency plan and comply
with additional requirements. The SPCC
Plan must explain why secondary
containment measures are not
practicable. Section 112.7(d) requires
that, when containment for bulk storage
containers is deemed impracticable, the
owner or operator must conduct both
periodic integrity testing of the
containers and periodic integrity and
leak testing of the valves and piping.
The owner or operator also must
provide an oil spill contingency plan
that follows the provisions of 40 CFR
part 109 (Criteria for State, Local and
Regional Oil Removal Contingency
Plans), and a written commitment of
manpower, equipment, and materials
required to expeditiously control and
remove any quantity of oil discharged
that may be harmful as described in 40
CFR part 110. A PE must certify any
determinations that secondary
containment is impracticable, as well as
the additional measures implemented in
lieu of secondary containment.
Because of the expertise that a PE has
in evaluating whether particular
measures provide equivalent
environmental protection and in
knowing how to effectively implement
such measures, EPA believes that the
flexibility in these performance-based
provisions is best suited to SPCC Plans
that are reviewed and certified by a PE.
The same expertise is necessary in
determining whether the required
secondary containment is impracticable.
EPA proposed that when a Plan is
self-certified, the owner or operator
would not be able to use
environmentally equivalent measures or
to make impracticability determinations
with respect to secondary containment.
Instead, EPA proposed specific
alternative measures for compliance
with security and integrity testing
requirements at qualified facilities that
self-certify. The commenters who
supported this approach indicated that
it added a safety factor into the selfcertification. Most commenters opposed
this approach because impracticability
determinations and environmental
equivalence were originally created to
relieve burden, and owners and
operators of small facilities still need
the flexibility these mechanisms
provide. Some commenters believed
that the agricultural industry would be
negatively affected because the
environmental equivalence and
impracticability provisions are an
important element to reduce the burden
on owners and operators of these
facilities due to topography and
operations. As for the proposed specific
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alternative to environmentally
equivalent measures for security, one
commenter supported this proposal.
With respect to integrity testing, the
Agency proposed to allow self-certifying
owners and operators of qualified
facilities to perform integrity testing by
relying on industry standards for the
integrity testing requirements as an
alternative to the existing bulk storage
containing integrity testing
requirements. All but one commenter
supported the proposal. One commenter
supported it, but also wanted visual
inspection of individual shop-fabricated
tanks up to 10,000 gallons. Another
commenter agreed, but believed that the
expense of the Steel Tank Institute’s
(STI) Tank Inspection Standard, SP001
(July 2005), was high and the STI
standard and accompanying checklists
are not applicable to small facilities. A
hybrid approach also was suggested
whereby owners and operators of
qualified facilities would be allowed to
use the self-certification option, and, in
the event that an environmental
equivalency or impracticability
determination is needed, the owner or
operator must consult a PE for just that
aspect of their program, rather than
requiring a full PE review and approval
of the entire Plan.
The Agency continues to believe that
the flexibility afforded by the
environmental equivalence or
impracticability determinations should
be available only to owners and
operators of facilities having those
elements reviewed and certified by a PE.
At the same time, the Agency recognizes
that by restricting these options for
owners and operators of qualified
facilities, the alternative of selfcertification may not be as attractive for
some owners or operators because they
will lose the added flexibility of further
tailoring the SPCC requirements to their
facility’s characteristics. The Agency
agrees with commenters that under the
proposed rule, there would likely be
certain circumstances where, because of
cost considerations, a facility owner or
operator would not choose to self-certify
because it would be more cost effective
for a PE to prepare an SPCC Plan that
utilizes environmentally equivalent
measures or impracticability
determinations.
In today’s final rule, the Agency
therefore is adopting a hybrid approach.
This approach finalizes the alternatives
for addressing security measures and
integrity testing and also allows owners
or operators of self-certified facilities to
include environmentally equivalent
measures with respect to requirements
other than facility security and integrity
testing, as well as to make
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impracticability determinations,
provided they have a PE certify these
environmentally equivalent measures or
impracticability determinations.
Because qualified facilities typically
have less complex operations and
petroleum system configurations and
storage capacities than other facilities
subject to SPCC requirements, EPA
believes that the alternative
requirements for facility security and
bulk storage container integrity testing
finalized today are appropriate for selfcertification. However, today’s rule does
not preclude a qualified facility from
choosing to have a PE certify the
integrity testing and/or security
measures in the facility’s Plan as
environmentally equivalent measures.
For example, where there are no
industry standards to guide integrity
testing at a qualified facility, the
alternative integrity testing option in
§ 112.6(c)(4)(ii) is not available.
However, the facility owner/operator is
allowed to have a PE certify an integrity
testing protocol in the Plan that is
environmentally equivalent to the
applicable requirements in subpart B or
C. The Agency believes that this
‘‘hybrid’’ approach will further expand
the flexibility offered by the selfcertification compliance option to
owners and operators of qualified
facilities without compromising proper
environmental protection.
Similarly, EPA is adopting a hybrid
approach to certification of technical
amendments to a qualified facility’s
SPCC Plan in § 112.5. PE-certified
sections of a qualified facility’s
‘‘hybrid’’ SPCC Plan require PE
certification of any technical
amendments to that portion of the Plan.
Technical amendments to the non-PE
certified sections of a qualified facility’s
‘‘hybrid’’ Plan can be certified by the
owner or operator.
B. Qualified Oil-Filled Operational
Equipment
The definition of bulk storage
container in § 112.2 specifically
excludes oil-filled electrical, operating,
and manufacturing equipment (‘‘oilfilled equipment’’). Therefore, oil-filled
equipment is not subject to the bulk
storage container requirements in
§§ 112.8(c), 112.9(c), and 112.12(c).
However, oil-filled equipment must
meet the general requirements of
§ 112.7, including the general secondary
containment requirements of § 112.7(c).
The general secondary containment
requirements are intended to address
the most likely oil discharge from oilfilled equipment. Although oil-filled
equipment differs from bulk storage
containers in several ways, the oil
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storage capacity of oil-filled equipment
still counts towards the aggregate oil
storage capacity of the facility.
EPA proposed to amend the SPCC
rule to provide a definition of oil-filled
operational equipment and an optional
alternative to the general secondary
containment requirements for oil-filled
operational equipment at a facility that
meets the qualifying criterion (hereafter
referred to as ‘‘qualified oil-filled
operational equipment’’). These
amendments are being finalized in
today’s rule. The rule allows owners
and operators of facilities with eligible
oil-filled operational equipment as
defined in § 112.2 the option to prepare
an oil spill contingency plan and a
written commitment of manpower,
equipment, and materials to
expeditiously control and remove any
oil discharged that may be harmful
without having to make an individual
impracticability determination as
required in § 112.7(d). If an owner or
operator takes this option, he or she is
also required to establish and document
an inspection or monitoring program for
this qualified oil-filled operational
equipment to detect equipment failure
and/or a discharge in lieu of providing
secondary containment.
New provisions in § 112.7(k) define
the criterion that facilities must meet in
order to be considered eligible for the
‘‘qualified oil-filled operational
equipment’’ option. Eligibility of a
facility with oil-filled operational
equipment is determined by considering
the reportable discharge history from
only oil-filled operational equipment at
the facility; the Agency is adopting the
same reportable discharge history
criterion that it adopted for qualified
facilities, as discussed in Section
V.A.3.b above. That is, the qualified oilfilled operational equipment criterion
specifically requires that the facility did
not discharge more than 1,000 U.S.
gallons in a single discharge as
described in § 112.1(b) or discharge
more than 42 U.S. gallons in each of two
discharges as described in § 112.1(b)
within twelve months, from any oilfilled operational equipment in the
three years prior to the SPCC Plan
certification date, or since becoming
subject to 40 CFR part 112 if the facility
has been in operation for less than three
years.
As proposed, the final rule provides
an alternative means of SPCC
compliance for this equipment;
therefore, an owner or operator could
choose to comply with the existing
SPCC requirements to provide general
secondary containment for each piece of
qualified oil-filled operational
equipment in accordance with
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§ 112.7(c), if desired. For example, oilfilled operational equipment at
electrical substations is often
surrounded by a gravel bed, which
serves as a passive fire quench system
and support for the facility grounding
network that can restrict the movement
of oil in the event of a release. Gravel
beds, if designed to prevent a discharge
as described in § 112.1(b) (i.e., drainage
systems that do not serve as a conduit
to surface waters) may meet the general
secondary containment requirements of
§ 112.7(c). EPA further notes that oilfilled operational equipment located
within buildings with limited drainage
and which prevent a discharge as
described in § 112.1(b), may already
meet the requirements for general
secondary containment of § 112.7(c).
In some situations, permanent
containment structures, such as dikes,
may not be feasible (i.e., for certain
electrical equipment). Section 112.7(c)
allows for the use of certain types of
active containment measures
(countermeasures or spill response
capability), which prevent a discharge
to navigable waters or adjoining
shorelines. Active containment
measures are those that require
deployment or other specific action by
the owner or operator. These measures
may be deployed either before an
activity involving the handling of oil
starts, or in reaction to a discharge so
long as the active measure is designed
to prevent an oil spill from reaching
navigable waters or adjoining
shorelines. Thus, a method of detecting
a discharge is of great importance to
effectively implement the use of active
containment measures. If an owner or
operator provides secondary
containment for oil-filled operational
equipment by the use of active
measures, a contingency plan for this
equipment is not necessary. Ultimately,
the decision whether to use the optional
approach to secondary containment for
qualified oil-filled equipment must be
made by the owner or operator.
1. Oil-Filled Operational Equipment
Definition
EPA proposed to define ‘‘oil-filled
operational equipment’’ as ‘‘equipment
which includes an oil storage container
(or multiple containers) in which the oil
is present solely to support the function
of the apparatus or the device. Oil-Filled
operational equipment is not considered
a bulk storage container, and does not
include oil-filled manufacturing
equipment (flow-through process).’’
Many of the commenters supported this
definition and therefore, we are
finalizing this definition in today’s rule
and including examples in the
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definition to provide additional clarity.
Examples of oil-filled operational
equipment include, but are not limited
to, hydraulic systems, lubricating
systems (i.e., those for pumps,
compressors and other rotating
equipment, including pumpjack
lubrication systems), gear boxes,
machining coolant systems, heat
transfer systems, transformers, circuit
breakers, electrical switches, and other
systems containing oil solely to enable
the operation of the device. When
piping is intrinsic to the oil-filled
operational equipment in a closed loop
system, i.e., inherent to the equipment
and used solely to facilitate operation of
the device, (e.g., for lubrication) then
EPA will consider the piping to be a
component of the oil-filled operational
equipment. However, piping not
intrinsic to the operational equipment
(i.e., flowlines, transfer piping or piping
associated with a process) will not be
considered to be part of the oil-filled
operational equipment.
The Agency received comments that
included alternatives to the definition
proposed. Specifically, commenters
suggested that the word ‘‘storage’’ be
removed from the definition of ‘‘oilfilled operational equipment.’’ The
Agency disagrees with the suggestion to
remove the word ‘‘storage’’ from the
definition because oil-filled operational
equipment includes oil inherent to the
device which is stored prior to and
during use for the operation of the
equipment and when the oil-filled
operational equipment is in standby.
Some commenters asked that EPA
identify generators (‘‘gensets’’) as oilfilled operational equipment. EPA’s
position is that gensets are a
combination of oil-filled operational
equipment and a bulk oil storage
container, and the oil that is consumed
to generate electricity is not inherent to
the device. (The bulk storage container
on a genset often requires the transfer of
oil.) Therefore, although gensets
incorporate oil-filled operational
equipment, such as the lubrication oil
system, gensets, as a whole unit, do not
meet the definition of oil-filled
operational equipment in today’s final
rule. In situations where it is
impracticable to provide appropriate
secondary containment for gensets (for
either the bulk storage containers or oilfilled operational equipment of the
genset), a PE can make a determination
of impracticability in accordance with
§ 112.7(d) and develop a contingency
plan following the provisions of 40 CFR
part 109 and provide a written
commitment of manpower, equipment
and materials to expeditiously control
and remove any quantity of oil
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discharged that may be harmful. See
Chapter 4 of the SPCC Guidance for
Regional Inspectors for further
explanation regarding when sized
secondary containment is required for
mobile or portable containers that are in
a stationary, unattended mode.
Several commenters argued that by
combining oil-filled electrical with
other operational equipment, EPA
diluted the strong case for
differentiation of oil-filled operational
equipment. Commenters also suggested
that EPA redefine electrical equipment
to include not only circuit breakers,
transformers, and electrical switches,
but also hydraulic systems, lubricating
systems, gear boxes, machining coolant
systems, heat transfer systems, etc. In
July 2002, when EPA clarified that oilfilled electrical, operating, and
manufacturing equipment are not bulk
storage containers, the Agency agreed to
continue to evaluate whether the
general secondary containment
requirements found in § 112.7(c) should
be modified for small electrical and
other types of equipment which use oil
for operating purposes. Today’s
definition of oil-filled operational
equipment describes the function of
both electrical equipment, as well as
other types of operating equipment
(hydraulic systems, lubricating systems,
etc.)
Oil-filled electrical and operating
equipment share common
characteristics. They both typically have
minimal oil throughput because such
equipment does not require frequent
transfers of oil. Further, the oil
contained in oil-filled operational
equipment, such as cooling or
lubricating oil, is intrinsic to the
operation of the device and facilitates
the function of the equipment. Utilities
have strong economic incentives to
prevent power outages, to discover and
respond to an outage, and to correct the
conditions that produced the outage as
quickly as possible. Other industry
sectors also have strong incentives to
prevent discharges to avoid disruption
in business and costs of a cleanup. The
Agency believes it is appropriate to
allow the same alternative means of
compliance with the general secondary
containment requirements of § 112.7(c)
for oil-filled operational equipment at
all facilities. In addition, oil-filled
operational equipment often is subject
to routine maintenance and inspections
to ensure proper operation. Therefore,
the Agency believes it is appropriate to
allow the same alternative means of
compliance with general secondary
containment requirements to apply to
both oil-filled electrical and operational
equipment. We have included both
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types of equipment into the definition of
oil-filled operational equipment.
2. Oil-Filled Manufacturing Equipment
The Agency is not finalizing a
definition of oil-filled manufacturing
equipment because we did not propose
and seek comment on a definition.
Additionally, the Agency does not agree
with commenters that the alternative
option to general secondary
containment should also apply to oilfilled manufacturing equipment. Oilfilled manufacturing equipment is
inherently more complicated than oilfilled operational equipment because it
typically involves a flow-through
process and is commonly
interconnected through piping. For
example, oil-filled manufacturing
equipment may receive a continuous
supply of oil, in contrast to the static
capacity of other, non-flow-through oilfilled equipment. Examples of oil-filled
manufacturing equipment include, but
are not limited to, process vessels,
conveyances such as piping associated
with a process, and equipment used in
the alteration, processing or refining of
crude oil and other non-petroleum oils,
including animal fats and vegetable oils.
The final rule does not change any
requirements for oil-filled
manufacturing equipment. Oil-filled
manufacturing equipment remains
subject to the general SPCC
requirements under § 112.7, including a
demonstration of impracticability under
§ 112.7(d) if the SPCC Plan does not
provide for general secondary
containment as required by § 112.7(c).
The oil storage containers associated
with the storage of raw products or
finished oil products are bulk oil storage
containers and are not considered oilfilled manufacturing equipment or oilfilled operational equipment. Oil-filled
manufacturing equipment is distinct
from bulk storage containers in its
purpose and is described in the SPCC
Guidance for Regional Inspectors. Oilfilled manufacturing equipment stores
oil only as an ancillary element of
performing a mechanical or chemical
operation to create or modify an
intermediate or finished product. Some
more specific examples of oil-filled
manufacturing equipment may include
reaction vessels, fermentors, high
pressure vessels, mixing tanks, dryers,
heat exchangers and distillation
columns. Under the SPCC rule, flowthrough process vessels are generally
considered oil-filled manufacturing
equipment since they are not intended
to store oil. EPA expects the owner or
operator and the certifying PE to
delineate bulk storage containers from
the oil-filled manufacturing equipment
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in the facility’s SPCC Plan (i.e., on the
facility’s diagram and in discussion of
compliance with inspection
requirements of the rule). Additionally,
although oil-filled manufacturing
equipment is not a bulk storage
container and is therefore not subject to
the frequent visual inspection
requirement for bulk storage containers
under § 112.8(c)(6), EPA believes that it
is good engineering practice to have
some form of visual inspection or
monitoring for oil-filled manufacturing
equipment in order to prevent
discharges as described in § 112.1(b).
Furthermore, it is a challenge to comply
with several of the SPCC provisions (for
example, requirements for security
under § 112.7(g)) and to address
countermeasures for discharge
discovery under § 112.7(a)(3)(iv))
without some form of inspection or
monitoring program.
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3. Eligibility Criteria
a. Reportable Discharge History
Part 110 defines a discharge of oil in
such quantities that may be harmful to
the public health, welfare, or the
environment of the United States as a
discharge of oil that violates applicable
water quality standards; a discharge of
oil that causes a film or sheen upon the
surface of the water or on adjoining
shorelines; or a discharge of oil that
causes a sludge or emulsion to be
deposited beneath the surface of the
water or adjoining shorelines (40 CFR
110.3). The Agency refers to such
discharges as reportable discharges or as
‘‘a discharge as described in § 112.1(b)’’
of the rule. Any person in charge of a
facility must report any such discharge
of oil from the facility to the National
Response Center (NRC) at 1–800–424–
8802 immediately. While EPA
recognizes that past release history does
not necessarily translate into a predictor
of future performance, the Agency
believes that discharge history is a
reasonable indicator of a facility owner
or operator’s ability to develop an SPCC
Plan for the facility without the
involvement of a PE.
Under the proposal, the alternative
compliance approach for general
secondary containment for oil-filled
operational equipment would not be
allowed to be implemented at the
facility unless the owner or operator had
no reportable discharge from any oilfilled operational equipment in the ten
years prior to the SPCC Plan
certification date, or since becoming
subject to 40 CFR part 112 if the facility
had been in operation for less than ten
years. This criterion was based on a
proposal submitted by the Utility Solid
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Waste Activities Group (USWAG), as
described in the documents
supplementing the September 20, 2004
Notice of Data Availability (NODA) at
69 FR 56184.
Many commenters agreed with the
proposed eligibility requirement.
However, several comments requested
that the qualifier be dropped and the
type of equipment be the only qualifier.
These commenters argued that
reportable discharge history was not a
suitable criterion for a number of
reasons, including: (1) It is arbitrary and
capricious—eligibility should be
rationally related to equipment or
equivalent facility performance; (2) it is
not effective to identify bad actors who
do not report discharges; (3) it is
unreasonable for crude oil and natural
gas production facilities, so no
requirements should apply; and (4) it
does not take into consideration the
volume of oil or location of equipment
in assessing risk. Other commenters
suggested considering the criterion for
submitting reports to EPA under § 112.4
to be the eligibility criterion for oilfilled operational equipment. Another
commenter requested EPA clarify that
the discharge is from regulated
equipment, i.e., equipment that is
greater than 55 gallons.
Although EPA recognizes that past
discharge history does not necessarily
predict future performance, the Agency
believes that discharge history can be
used as a surrogate measure for a facility
owner or operator’s ability to
appropriately manage its oil. Hence, as
with ‘‘qualified facilities,’’ EPA is using
this discharge history criterion to
identify a facility owner or operator’s
ability to effectively implement its SPCC
Plan and prevent discharges in
quantities that may be harmful. In
establishing a good oil spill prevention
history for its oil-filled operational
equipment, a facility then qualifies for
the oil spill contingency plan option in
lieu of secondary containment. Because
the Agency believes it is appropriate to
extend this approach to all oil-filled
operational equipment, regardless of the
oil storage capacity of the equipment,
the spill history criterion is critical to
establish an appropriate balance
between environmental protection and
streamlined requirements by identifying
those facilities whose owners or
operators have demonstrated good spill
prevention practices in the past.
EPA does not agree that this is
unreasonable for crude oil and natural
gas production facilities because the
reportable discharge criterion is
applicable only to the oil-filled
operational equipment at the facility
and is not affected by other discharges
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that may have occurred from the facility
from other types of oil storage
containers. One commenter pointed out
that discharges from compressors,
pumpjacks, and similar equipment are
extremely rare and unlikely to reach
navigable waters and adjoining
shorelines.
Many commenters suggested an
alternate reportable discharge history
period of five years. One commenter
suggested three years and another
suggested either two or five years. A few
commenters suggested the time period
should be five years with a § 112.4 spill
notification trigger.
In response to comments received on
the proposed rule, EPA has reduced the
discharge history period from ten years
to three years, which is consistent with
the recordkeeping requirements in
§ 112.7(e). In addition, rather than
including all discharges reportable to
the National Response Center, the
Agency is specifying amounts of more
than 1,000 U.S. gallons in a single
discharge as described in § 112.1(b) or
more than 42 U.S. gallons in two
discharges as described in § 112.1(b)
within a twelve month period during
the three-year timeframe, or since
becoming subject to 40 CFR part 112 if
the facility has been in operation for less
than three years, only from oil-filled
operational equipment at the facility.
This criterion does not include oil
discharges as described in § 112.1(b)
that are the result of natural disasters,
acts of war, or terrorism. The approach
is similar to the discharges that are
reportable to the Regional Administrator
under § 112.4(a), with the exception that
the criterion finalized today applies
only to discharges from oil-filled
operational equipment and not all oil
containers at a facility as in the case of
§ 112.4(a). When determining spill
history, the gallon amount specified in
the criterion (either 1,000 or 42) refers
to the amount of oil that actually
reaches waters of the United States,
adjoining shorelines, the contiguous
zone or in connection with specified
activities in waters and not the total
amount of oil spilled. For example, a
facility only experiencing one discharge
over the past ten years in which 1,500
gallons of oil discharged onto the
ground but only 20 gallons reached
waters of the United States (causing a
sheen and reportable to the NRC) would
meet the Reportable Discharge History
criterion. However, a facility having
1,500-gallon discharge to waters of the
United States would not meet the
Reportable Discharge History criterion.
The determination of eligibility based
on reportable discharge history is made
at the time the SPCC Plan is certified.
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That is, when the SPCC Plan is
amended to comply with the SPCC rule
revisions in today’s final rule and those
promulgated in July 2002. Once the
current compliance date extension ends,
Plans must be amended, certified and
implemented. Any discharges to
navigable waters and adjoining
shorelines that occur from oil-filled
operational equipment at the facility
after the SPCC Plan has been certified
do not impact the eligibility of qualified
oil-filled operational equipment at the
facility. The facility does not lose
eligibility status as a result of a
discharge as described in § 112.1(b),
unless the RA requires an amendment to
the SPCC Plan in accordance with
§ 112.4(d) and specifically requires
secondary containment for oil-filled
operational equipment. If an owner or
operator cannot certify that the oil-filled
operational equipment meets the
eligibility criterion at the initial date of
Plan certification, but can later
demonstrate a clean spill history of
three years, then a technical amendment
to the Plan can be certified and the Plan
can be revised to allow for qualified
status for oil-filled operational
equipment.
In the preamble to the proposed rule,
EPA requested comment on how
extreme events such as natural disasters
and acts of war, terrorism , sabotage, or
other calamities might potentially affect
the discharge history criterion for
qualified facilities. Many commenters
agreed (and no commenters disagreed)
that EPA should account for extreme
events such as natural disasters, acts of
war or terrorism, etc. in granting
eligibility status. The Agency agrees that
reportable discharges caused by external
factors beyond the control of the facility
owner or operator such as natural
disasters, acts of war, or terrorism
should not disqualify a facility from
eligibility for the qualified oil-filled
equipment provision. Therefore we have
excluded those events from
consideration in the reportable
discharge eligibility criterion in today’s
final rule. The Agency has excluded
sabotage/vandalism from the final list of
extreme events not to be considered in
the reportable discharge history because
these are not necessarily beyond the
control or planning ability of the facility
owner or operator.
b. Consideration of Alternative
Qualification Criteria
One commenter suggested that the
inspection and monitoring program be
the only qualifier for a facility owner or
operator to take advantage of this
option. Other suggestions would allow
eligibility to be based on the type of
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equipment and a commitment or duty to
properly maintain that equipment such
as the duty in 40 CFR 122.41(e) to
maintain wastewater treatment
equipment. In this case, facility owners
or operators would lose eligibility based
on their performance or SPCC
inspection results (i.e. failure to
maintain oil-filled electrical
equipment). The Agency is not
finalizing these alternatives as part of
the eligibility criteria because we
believe it is in the owner or operator’s
best interest to properly maintain
equipment at the facility and a
commitment to the Agency to maintain
equipment is not necessary.
The Agency believes that inspections
and monitoring are part of an effective
spill prevention program and it is more
appropriate to include these prevention
practices as a component of the
alternative option for compliance with
general secondary containment
requirements for oil-filled operational
equipment. To include these spill
prevention practices as a basis for
qualification raises questions on the
length of time and scope of the
inspection and monitoring program
necessary to be in place at the facility
in order to demonstrate qualification.
Additionally, the SPCC regulations
already provide EPA the authority to
require SPCC Plan amendments under
§ 112.4 so it is not necessary to include
an automatic loss of eligibility based on
facility performance or SPCC inspection
results. Section 112.4(a) requires an
owner or operator of a facility that has
discharged more than 1,000 U.S. gallons
of oil in a single discharge as described
in § 112.1(b) or that has discharged more
than 42 U.S. gallons of oil in each of two
discharges as described in § 112.1(b)
within any twelve month period, to
submit information to the EPA RA
within 60 days of the date of the
discharge. As per § 112.4(d), the RA may
require the facility owner or operator to
amend the SPCC Plan in order to
prevent and contain discharges,
including a requirement that a facility
owner or operator provide secondary
containment for qualified oil-filled
operational equipment. The time frame
for this review and amendment process
is described in § 112.4. The facility
owner or operator may choose to appeal
the RA’s decision to require a Plan
amendment under § 112.4. In addition,
a discharge of oil ‘‘in such quantities as
may be harmful’’ as defined in 40 CFR
110.3 that does not trigger the reporting
requirements of § 112.4(a) must still be
reported to the National Response
Center. Criminal action can be taken
against an owner or operator of a facility
if discharges are willfully not reported.
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EPA also receives copies of the NRC
reports and has the authority under
§ 112.1(f) to require a facility owner or
operator to prepare and implement an
SPCC Plan or any applicable part of a
Plan.
Owners and operators of facilities
with qualified oil-filled operational
equipment that choose the alternative to
secondary containment and that
subsequently have a discharge would
not automatically lose eligibility for
today’s optional approach. Owners or
operators of facilities that discharge oil
in quantities that may be harmful from
oil-filled operational equipment should
re-evaluate the effectiveness of the SPCC
Plan (specifically the contingency plan,
written commitment of resources, and
inspections/monitoring alternative
discussed in today’s final rule) and
determine the need for secondary
containment measures in lieu of
contingency planning. Additionally, the
Regional Administrator may determine
that a facility owner or operator is no
longer eligible to have a contingency
plan in lieu of secondary containment
without making an impracticability
determination, and such owners or
operators may be required to amend
their Plans to provide secondary
containment for their oil-filled
operational equipment.
4. Requirements for Qualified Oil-Filled
Operational Equipment In Lieu of
Secondary Containment
a. Contingency Plans and a Written
Commitment of Manpower, Equipment,
and Materials
As described in the preamble to the
proposed rule, EPA believes that
secondary containment often may be
impracticable for oil-filled operational
equipment because of inherent design
and safety considerations, as well as site
configuration. The oil associated with
oil-filled operational equipment remains
inside the equipment and transfers do
not occur regularly; for oil-filled
electrical equipment (i.e., transformers)
transfers typically occur infrequently, if
at all. The complexity of the equipment
and the nature of the use of this
equipment does not lend itself to
traditional bulk storage containment
methods and thus flexibility is
appropriate in this area and may
improve compliance with oil pollution
prevention measures. EPA proposed
amendments to § 112.7 to give owners
and operators of facilities with qualified
oil-filled operational equipment the
option of implementing an inspection
and monitoring program, developing an
oil spill contingency plan and providing
a written commitment of resources
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required to expeditiously control and
remove any quantity of oil discharged
that may be harmful, in lieu of
secondary containment for this
equipment, without having to make an
impracticability determination for each
piece of oil-filled operational
equipment. The inspection and/or
monitoring program, contingency plan
and written commitment of resources
would be included in the facility SPCC
Plan. Commenters generally supported
this proposal and the provision is being
finalized in § 112.7(k) as proposed.
A number of commenters were
unclear regarding the intent of an oil
spill contingency plan. For example, a
common industry interpretation of an
‘‘oil spill contingency plan’’ covers
anticipated responses to oil spills both
on land, as well as spills that reach
navigable waters. Some commenters
suggested that the contingency plan be
in lieu of an SPCC Plan entirely. Others
suggested that it is an administrative
burden to identify downstream water
users and the majority of commenters
suggested that it is inappropriate to
consider large discharges to water since
the goal should be to prevent oil from
getting to navigable waters in the first
place. Several commenters suggested
that implementation of a contingency
plan in accordance with the
requirements of 40 CFR part 109 was
inappropriate because the purpose of
the contingency plan should be to
prevent a discharge to navigable waters
and adjoining shorelines.
Commenters suggested that the oil
spill contingency plan should instead
contain four major elements: hazard
identification, vulnerability analysis,
risk assessment and response actions.
Many of the commenters that suggested
simplifying the contingency planning
option to allow for hazard
identification, vulnerability analysis,
risk assessment, and response actions
may already be in compliance with the
general secondary containment
requirements of the SPCC rule by
utilizing active secondary containment
measures.
We do not believe that a contingency
plan, by itself, is sufficient to substitute
for an SPCC Plan. The purpose of the
SPCC Plan is to prevent discharges of oil
from reaching navigable waters and
adjoining shorelines and includes a
combination of procedures, measures
and equipment to achieve that goal, e.g.,
procedures for inspections and
personnel training, equipment to
prevent and control discharges of oil
and security measures. Conversely, a
contingency plan is a detailed oil spill
response and removal plan that
addresses controlling, containing, and
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recovering an oil discharge in quantities
that may be harmful to navigable waters
or adjoining shorelines. Contingency
plans have a dual purpose. The first
purpose is to outline the response
capability or countermeasures to limit
the quantity of a discharge from
reaching navigable waters or adjoining
shorelines (if possible). The second is to
address the facility owner or operator’s
effective preparation for a response to a
discharge of oil that has already reached
navigable waters or adjoining
shorelines. A contingency plan should
include the ability to expeditiously
control and remove any quantity of oil
discharged that may be harmful.
The elements of the contingency plan
are outlined in § 109.5, and include:
definition of the authorities,
responsibilities, and duties of all
persons, organizations, or agencies that
are to be involved or could be involved
in planning or directing oil removal
operations; establishment of notification
procedures for the purpose of early
detection and timely notification of an
oil discharge; provisions to ensure that
full resource capability is known and
can be committed during an oil
discharge situation; provisions for welldefined and specific actions to be taken
after discovery and notification of an oil
discharge; and specific and well-defined
procedures to facilitate recovery of
damages and enforcement measures as
provided for by state and local statutes
and ordinances.
An owner or operator of a facility
with oil-filled operational equipment
that has submitted a Facility Response
Plan (FRP) to EPA in accordance with
§ 112.20 would not need to also develop
a contingency plan in accordance with
40 CFR part 109 for the oil-filled
operational equipment because an FRP
is more comprehensive than a
contingency plan. Additionally, the
contingency planning requirement can
be met either by a whole new plan or
by ensuring that the elements called for
in 40 CFR part 109 and the
accompanying written commitment of
manpower, equipment and materials are
integrated into the SPCC Plan or another
plan already in place at the facility
(provided that a section crossreferencing the location of requirements
listed in 40 CFR part 109 and the
equivalent requirements in the other
response plan is included).
For a contingency plan to satisfy the
requirements listed in § 112.7(k) of
today’s final rule, a facility owner or
operator must be able to implement the
contingency plan. Activation of the
contingency plan depends on the
capability of the owner or operator of
the facility to quickly detect a discharge.
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Therefore, as part of an evaluation of the
adequacy of a contingency plan to
satisfy the requirements of § 112.7(k),
EPA will consider the time it takes
facility personnel to detect and mitigate
a discharge as described in § 112.1(b).
Inspections or monitoring are
particularly important to detect an oil
discharge when there is no secondary
containment in place. Therefore, EPA
proposed and is finalizing the provision
to require owners and operators of
facilities with qualified oil-filled
operational equipment that choose to
develop and implement contingency
plans to also develop and implement an
inspection or monitoring program, as
further discussed in this section of the
preamble. Because the qualified oilfilled operational equipment approach
is optional, an owner or operator of a
facility with such equipment may
choose to provide general secondary
containment in accordance with
§ 112.7(c) for this oil-filled operational
equipment, if desired. Ultimately, this is
the decision of the owner or operator of
the facility.
The comments received suggest there
is a misunderstanding concerning the
general secondary containment
requirements of § 112.7(c). General
secondary containment under § 112.7(c)
should be designed to address the most
likely discharge from the primary
containment system, i.e., appropriate
containment and/or diversionary
structures or equipment must be
designed to prevent a discharge as
described in § 112.1(b). Secondary
containment may be either passive
measures or active measures
(countermeasures or land-based spill
response capability) since both are
designed to prevent a discharge from
reaching navigable waters or adjoining
shorelines.
Passive measures are permanent
installations (such as dikes or berms)
and do not require deployment or action
by the owner or operator. However,
permanent (passive) containment
structures, such as dikes, may not
always be feasible for certain oil-filled
operational equipment (i.e., electrical
transformers, capacitors, switches). The
owner or operator of an SPCC-regulated
facility may instead use the flexibility of
active containment measures to comply
with the general secondary containment
requirements for oil-filled operational
equipment.
Active containment measures are
those that require deployment or other
specific action by the owner or operator
of a facility. These active measures may
be deployed either before an activity
involving the handling of oil starts, or
in reaction to a discharge, so long as the
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active measure is designed and can
reasonably be implemented to prevent
an oil spill from reaching navigable
waters or adjoining shorelines. The
efficacy of active secondary
containment measures to prevent
discharges depends on their technical
effectiveness (i.e., mode of operation,
absorption rate), placement and
quantity, and timely deployment prior
to, or following a discharge. A method
of detecting a discharge is therefore of
great importance to effectively
implement the use of active
containment measures. These active
measures must be implemented
effectively and in a timely manner to
prevent oil from reaching navigable
waters and adjoining shorelines, as
required by § 112.7(a)(3)(iii) and (c).
Many commenters indicated that the
40 CFR part 109 plan is designed for
local governments and therefore
inappropriate for facilities. Some
commenters suggested using
environmental equivalence to tailor a 40
CFR part 109 plan or allow flexibility
for facility owners and operators to
comply only with applicable
requirements. Other commenters
suggested the use of generic and multifacility plans. Some commenters
suggested expanding the training
requirements to apply to more than just
the oil-handling personnel at the
facility. Commenters also indicated that
it is onerous to list each piece of
equipment in a Plan, and that it is
burdensome to keep the Plan up-to-date
to account for mobile equipment.
Environmental equivalence is
available to allow for alternative means
of fulfilling the same function as the
specific provision listed in § 112.7(a)(2).
Because the contingency plan elements
in part 109 do not contain specific
requirements as to how those elements
are fulfilled, there is no need to provide
for environmentally equivalent means of
fulfilling those requirements, Thus, the
Agency believes that there is already
sufficient flexibility in the criteria for an
oil spill contingency plan in 40 CFR
part 109. Moreover, since the purpose of
the plan is to prepare for response to a
discharge of oil that has reached
navigable waters or adjoining
shorelines, each of the elements of a
contingency plan listed in 40 CFR part
109 are appropriate. Although the
elements of a contingency plan listed in
40 CFR part 109 were originally
developed to outline procedures for
local and regional oil removal
contingency plans, these elements can
be adapted for SPCC regulated facilities.
A sample contingency plan adapted to
the needs of an SPCC-regulated facility
following the provisions of 40 CFR part
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109 is included in Appendix F of the
SPCC Guidance for Regional Inspectors
which is available on the EPA Web site
at https://www.epa.gov/oilspill. The
guidance document also provides more
information on active and passive
secondary containment measures.
Other commenters suggested the use
of generic and multi-facility SPCC
Plans. In July 2002, the Agency stated
that a multi-facility SPCC Plan may be
appropriate for operating equipment
(oil-filled operational equipment) (see
67 FR 47042, 47080.) This type of SPCC
Plan is intended for electrical utility
transmission systems, electrical cable
systems, and similar facilities whose
owners and operators might aggregate
equipment located in diverse areas into
one Plan. Multi-facility Plans would
include all elements required for
individual SPCC Plans. Site-specific
information would be required for all
equipment included in each Plan.
However, the site-specific information
might be maintained in a separate
location, such as a central office, or an
electronic database, as long as such
information was immediately accessible
to responders and inspectors. If you
keep the information in an electronic
database, you must also keep a paper or
other backup that is immediately
accessible for emergency response
purposes, or for EPA inspectors, in case
the computer is not functioning. It is not
clear what the commenters meant by a
generic Plan, however, the Agency
believes that any Plan developed must
be in accordance with the requirements
of 40 CFR part 112.
Commenters recommended that
training at a facility be expanded
beyond the personnel involved in oil
handling, with one commenter
suggesting that training include any
individuals who could reasonably be
expected to implement any component
of the contingency plan; they also
suggested rule language for such an
approach. The Agency agrees that any
employee who is required to implement
any component of an oil spill
contingency plan may be considered
‘‘oil-handling personnel’’ and require
training in accordance with § 112.7(f).
This would consist of training in the
operation and maintenance of
equipment to prevent discharges;
discharge procedure protocols;
applicable pollution control laws, rules
and regulations; general facility
operations; and the contents of the
facility SPCC Plan (including the
contingency plan). Contractors involved
in oil handling activities at the facility
should also have appropriate oil spill
response training.
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Additionally, commenters indicated
that it is onerous to list each piece of
equipment in an SPCC Plan, and that it
is burdensome to keep the Plan up-todate to account for mobile equipment.
The Agency agrees that it may be
burdensome to frequently update an
SPCC Plan for mobile equipment.
However, we believe there is sufficient
flexibility in the SPCC rule to address
this concern. For example, EPA has
stated that if you store mobile
containers in a certain area, you must
mark that area on the diagram. You may
mark the contents of each container
either on the diagram of the facility, or
on a separate sheet or log if those
contents change on a frequent basis.
More information on the flexibility of
the SPCC rule for mobile/portable
containers is available in the SPCC
Guidance for Regional Inspectors
available on the EPA Web site at https://
www.epa.gov/oilspill.
b. Inspections or Monitoring Program
The majority of commenters
supported the proposal to include an
inspection and monitoring program. A
facility owner or operator must be able
to quickly detect a discharge from oilfilled operational equipment in order for
a contingency plan to be effective.
Therefore, the Agency is including a
requirement for an inspection and
monitoring program in today’s rule.
Facility owners or operators who wish
to take advantage of this alternative are
required to develop an appropriate set
of procedures for inspections or a
monitoring program for qualified oilfilled operational equipment. For
facility owners and operators that rely
on contingency planning in lieu of
secondary containment for qualified oilfilled operational equipment, the
discovery of a discharge by inspection
or monitoring is of paramount
importance for effective and timely
implementation of the contingency
plan. An inspection or a monitoring
program ensures that facility personnel
are alerted quickly of equipment failures
and/or discharges. A written description
of the inspection or monitoring program
is required to be included in the SPCC
Plan. Under the requirement in
§ 112.7(e), the owner or operator is
required to keep a record of inspections
and tests, signed by the appropriate
supervisor or inspector, for a period of
three years.
Although oil-filled operational
equipment is not a bulk storage
container and is therefore not subject to
the frequent visual inspection
requirement for bulk storage containers
under § 112.8(c)(6), EPA believes that it
is good engineering practice to have
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some form of visual inspection or
monitoring for oil-filled operational
equipment in order to prevent
discharges as described in § 112.1(b).
Therefore, in lieu of secondary
containment, the proposal included the
requirement for a facility owner or
operator to establish and document an
inspection or monitoring program, in
addition to the preparation of a
contingency plan and a written
commitment of manpower, equipment,
and materials to expeditiously control
and remove discharged oil. One
commenter suggested requiring only
inspection and monitoring for oil-filled
operational equipment up to 5,000gallon capacity and no other written
Plan. The Agency continues to believe
that a written SPCC Plan is essential to
document the prevention procedures
and countermeasures employed at the
facility and is necessary for effective
implementation of an SPCC program, or
any other program (business or
otherwise). As a matter of practice, it
would be extremely difficult for a
facility owner or operator to be able to
follow the regulatory requirements and
to comply with all the recordkeeping
components without the documentation
that is the Plan itself. The Plan also
serves as an important communication
tool for both management and operators
at the facility. The sole action of having
to document all of the requirements can
assist in uncovering flaws in the
program implementation, and may serve
as a tool to correct them. The Plan is
also used to communicate these
procedures and measures to employees.
Additionally, the documentation of
compliance with the rule’s requirements
in a written Plan serves as a facility
specific oil spill response and
prevention planning exercise which is
designed to improve oil spill
prevention.
c. Alternative Options Considered
Many commenters believed, and
supported the Agency’s proposal to not
include, a capacity threshold qualifier.
There was also significant support for
the USWAG multi-tiered option for
electrical equipment, with some
commenters suggesting that the Agency
differentiate between electrical and
other oil-filled operational equipment
and then adopt the USWAG proposal
providing an exemption for most small
equipment. Other commenters
specifically commended EPA for not
including a volume threshold for
applicability of relief based on lack of
data to suggest that large oil-filled
equipment have greater potential for
discharge over small oil-filled
equipment. However, these commenters
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indicated that small equipment should
be exempt because of lack of spill data.
Multiple commenters requested
exemption or deferral requirements in
the same manner as proposed for farms.
Others requested suspension of the
requirements.
The Agency agrees with commenters
that no threshold qualifier is necessary
to allow for an alternative means of
compliance with secondary
containment requirements for oil-filled
operational equipment. The alternative
measure is appropriate based on the
type of equipment, i.e., the oil is
intrinsic to the operational equipment
and present solely to support the
apparatus and there is minimal oil
throughput because such equipment
does not require frequent transfers of
oil. The Agency did not finalize the
multi-tiered approach for electrical
equipment to allow for an exemption for
smaller pieces of oil-filled operational
equipment because we believe there is
still a reasonable potential for
discharges from oil-filled operational
equipment with an oil storage capacity
of 1,320 gallons or less, thus coverage by
some type of SPCC Plan is warranted.
An exemption of these smaller pieces of
oil-filled operational equipment could
in some cases allow for large amounts
of aggregate capacity that would not be
counted for SPCC or FRP purposes, and
would therefore be unregulated, posing
a threat to the environment. However, in
the July 17, 2002 Federal Register
notice, EPA stated ‘‘We believe that it is
not necessary to apply SPCC or FRP
rules requiring measures like secondary
containment, inspections, or integrity
testing, to containers smaller than 55
gallons storing oil because a discharge
from these containers generally poses a
smaller risk to the environment.’’ (67 FR
47066). Oil-filled operational equipment
with a capacity of less than 55 gallons
is not subject to the rule.
Oil-filled electrical and operating
equipment share common
characteristics. They both typically have
minimal oil throughput because such
equipment does not require frequent
transfers of oil. Further, the oil
contained in oil-filled operational
equipment, such as cooling or
lubricating oil, is intrinsic to the
operation of the device and facilitates
the function of the equipment. Should
oil-filled electrical equipment fail,
utilities responsible for such equipment
have strong economic incentives to
prevent power outages, to discover and
respond to an outage, and to correct the
conditions that produced the outage as
quickly as possible to prevent an oil
discharge. Similarly, when other critical
oil-filled operating equipment fails, the
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industry sectors responsible for such
equipment also have strong incentives
to respond and address failures to avoid
disruption in business and costs of a
cleanup. In addition, oil-filled
operational equipment often is subject
to routine maintenance and inspections
to ensure proper operation. Therefore,
the Agency is not promulgating different
requirements, but believes it is
appropriate to offer the same alternative
means of compliance with the general
secondary containment requirements of
§ 112.7(c) to both oil-filled electrical and
operational equipment. Both types of
equipment are addressed in the
definition of oil-filled operational
equipment.
The Agency has decided not to
provide an indefinite extension or
suspension for owners and operators of
facilities with oil-filled operational
equipment. The regulated community,
particularly owners and operators of
electrical facilities, identified secondary
containment for oil-filled operational
equipment as one of its major cost
concerns. Today’s rule addresses that
concern and offers an alternative means
of compliance for oil-filled operational
equipment, while maintaining
protection of human health and the
environment.
5. Qualified Oil-Filled Operational
Equipment and Qualified Facilities
Overlap
Some facilities will meet the criteria
for qualified facilities and have
qualified oil-filled operational
equipment on-site. Owners and
operators of such facilities are able to
benefit from both of the alternative
compliance approaches finalized in
today’s rule. The owner or operator can
choose to develop an oil spill
contingency plan, a written
commitment of manpower, equipment
and materials and an inspection or
monitoring program as an alternative to
secondary containment for qualified oilfilled operational equipment. Since no
impracticability determination is
necessary for qualified oil-filled
operational equipment, the owner or
operator can self-certify his/her SPCC
Plan and is not required to have a PE
develop and certify the contingency
plan for the qualified oil-filled
operational equipment. The
responsibility of preparing a
contingency plan and identifying the
necessary equipment, materials and
manpower to implement the
contingency plan would fall on the
owner or operator of the qualified
facility.
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C. Motive Power
In the proposed rule, EPA addressed
specific types of motor vehicles
(including aircraft, buses, sport utility
vehicles, small construction vehicles,
cherry pickers, self-propelled cranes,
self-propelled aviation ground service
equipment vehicles, self-propelled
forestry, agricultural, construction, and
excavation vehicles and locomotives)
that contain oil in capacities greater
than or equal to 55 gallons solely for the
purpose of providing fuel for
propulsion, or solely to facilitate the
operation of the vehicle, such as
lubrication of moving parts or operation
of onboard hydraulic equipment. Such
oil storage containers are technically
subject to the SPCC rule, including the
requirement for secondary containment
and other SPCC requirements. This
means that heavy equipment dealers,
commercial truck dealers, or certain
parking lots may be subject to the SPCC
requirements (including bulk storage
secondary containment, inspection, and
overfill protection) solely because of the
presence of motive power containers.
EPA never intended to regulate these
motive power containers or facilities
where these vehicles might be located
and who are not otherwise subject to the
SPCC requirements because of the
impracticability of application of the
SPCC requirements to such vehicles.
These individually provide their own
means of propulsion from location to
location within or between facilities.
The management, record keeping, and
compliance with the spill prevention
requirements associated with motive
power containers would be difficult due
to their movement throughout and
between facilities. For example, a truck
with a large fuel tank and associated
large capacity hydraulic units that
moves throughout a facility and
between facilities would require
tracking and containment under the
SPCC requirements. This is
impracticable because such vehicles are
not stationary or located in a specific
operational area, as is the case with
mobile non-vehicular mobile/portable
containers that are placed in specific oil
handling or operational areas. Motor
vehicles with a storage tank capacity of
55 gallons or greater, such as a number
of semi-rigs delivering materials to an
otherwise regulated SPCC facility that
enter and leave a facility on a routine
basis would provide a significant
challenge for compliance with the SPCC
requirements. Finally, these containers
are either ‘‘end use’’ fuel tanks or oilfilled operational equipment in which
transfers from the container are rare
unlike other mobile portable containers.
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To correct this unintended application
of the SPCC rule, EPA proposed to
exempt motive power containers from
the SPCC requirements. Commenters
generally favored this proposal and
agreed that subjecting motive power
containers to SPCC requirements would
be impracticable. In today’s action, EPA
is clarifying its position on motive
power containers associated with selfpropelled motor vehicles by finalizing
the proposed definition and exemption.
The Agency believes that the general
protection and the spill response and
planning activities in place at an
otherwise regulated SPCC facility will
address any discharges associated with
these motive power containers.
For those facilities whose capacity is
comprised solely of motive power
containers, today’s action may result in
the facility no longer being subject to
the SPCC requirements. However, for
owners and operators of these facilities,
EPA maintains the authority, under
311(j)(1)(C) of the CWA, to impose
requirements to prevent oil discharges
from motive power containers. EPA
believes that owners and operators of
these facilities will continue to act
prudently to prevent discharges from
motive power containers from reaching
navigable waters and owners and
operators of non-transportation-related
facilities that fail to do so can be
required by the EPA Regional
Administrator (RA) to develop an SPCC
Plan. The RA has the option under
§ 112.1(f) to require owners and
operators of facilities, including those
with motive power containers, to
prepare and implement an SPCC Plan or
any applicable part, if a determination
is made that it is necessary to prevent
a discharge of oil into waters of the
United States. EPA will continue to
encourage owners and operators of
facilities that are no longer regulated
under the SPCC rule, as a result of
today’s action, to provide prevention,
planning and response measures to
prevent oil discharges from motive
power containers.
1. Definition of Motive Power
One commenter generally supported
the definition as proposed. Several other
commenters opposed the proposed
definition and additional comments
were submitted with alternate
definitions of motive power containers.
Those who opposed the definition
indicated that it will not effectuate its
purpose, simply because the gas tank,
for example, is not used solely to power
the movement of a motor vehicle. Other
reasons for opposition note that the
definition may not be broad enough,
and it should be modified to clarify the
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scope of ‘‘motor vehicle.’’ The definition
may not cover all motive power
configurations, and it may not cover
ground service equipment, including
ground service equipment in the airport
industry sector.
Recommendations included
expanding the definition to include
other mobile equipment like forestry
and mining equipment. Other
commenters indicated that the scope of
the definition should be modified to
clarify that a motor vehicle includes not
just automobiles and trucks, but all
types of motor vehicles including
cranes, cherry pickers, or production
drill rigs at mining sites and equipment
that may be stationary for a temporary
duration. Commenters also suggested
that the definition be revised to cover
various motive power configurations.
EPA agrees with the commenters that
the scope of the definition should be
clarified to include motor vehicle bulk
storage containers that serve a nonoperational purpose in addition to the
propulsion of the motor vehicle (for
example, a bulk storage container that
supplies fuel to an engine which
provides the propulsion for that motor
vehicle, as well as its auxiliary units
and functions (i.e., heaters, air
conditioning units, and electrical power
generation, etc.). As noted by
commenters, the term ‘‘solely’’ in the
definition of motive power containers
limits the inclusion of motor power fuel
tanks that serve one of the nonoperational functions listed above in
addition to providing fuel for
propulsion of the motor vehicle. In
response to this comment, EPA has
removed the word ‘‘solely’’ and
replaced it with the word ‘‘primarily.’’
The definition of motive power
containers only applies to motor
vehicles where the primary purpose of
the bulk storage container is to supply
fuel to power the movement of the
vehicle and, secondly, power other
equipment on board the vehicle, so long
as no further distribution (transfers) of
oil occurs from the container as in the
case with some mobile refuelers.
EPA agrees with the commenters that
additional clarification is needed to
describe the type of motor vehicles
covered under the definition of motive
power containers. Only motor vehicles
which provide their own means of
propulsion fall within the scope of this
definition for the purposes of 40 CFR
part 112. For example, aircraft, cherry
pickers, self-propelled cranes, selfpropelled aviation ground service
equipment vehicles, self-propelled
heavy (forestry, agricultural, mining,
excavation and construction) vehicles
and locomotives, all of which
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individually provide their own means of
propulsion from location to location
within a facility or between facilities,
are considered motor vehicles for the
purposes of this definition and 40 CFR
part 112. However, towed aviation
ground service equipment, non-selfpropelled construction/cargo cranes,
non-self-propelled (forestry,
agricultural, mining, excavation or
construction) equipment, diesel
powered generators, fire pumps, and
compressors are examples of oil-filled
equipment and bulk storage containers
not considered motor vehicles for the
purposes of this definition because they
do not provide their own means of
propulsion. The exemption was based
on the impracticability of application of
SPCC requirements to motor vehicles
and their unique self-propelled
capability of movement within and
between facilities, typically without
restriction.
2. Exemption
This final rule amendment exempts
motive power containers, as defined
above, from SPCC rule applicability by
adding a new paragraph (7) under the
general applicability section, § 112.1(d).
Furthermore, the capacity of these
storage containers are not counted
toward facility oil storage capacity
under § 112.1(d)(2). The RA has the
option under § 112.1(f), however, to
require owners and operators of
facilities, including those with motive
power containers, to prepare and
implement an SPCC Plan or any
applicable part, if a determination is
made that it is necessary in order to
prevent a discharge of oil into waters of
the United States, or adjoining
shorelines.
EPA notes that although this
amendment provides an exemption
from the SPCC requirements for the fuel
tanks and ancillary onboard oil-filled
operational equipment of motor
vehicles, the oil transfer activities
occurring within an SPCC-covered
facility continue to be regulated. An
example of such an activity would be
the transfer of oil from an on-site tank
via a dispenser to a motive power
container. This transfer activity is
subject to the general secondary
containment requirements of § 112.7(c).
An onboard bulk storage container
that supplies oil for the movement of a
vehicle or operation of onboard
equipment, and at the same time, is
used for the distribution or storage of
this oil, is not eligible for this
exemption. For example, a mobile
refueler that has an onboard bulk
storage container used to distribute fuel
to other vehicles on a site may also draw
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its engine fuel (for propulsion) from that
bulk container. However, such bulk
storage containers (on a mobile refueler,
as defined in today’s rule under 112.2)
are exempt from the sized secondary
containment requirements in
§§ 112.8(c)(2) and (11) and 112.12(c)(2)
and (11), as applicable (see Section D
below).
EPA is also not extending the
exemption for motive power containers
to oil drilling and workover equipment,
including rigs. The Agency believes that
because of the unique nature of oil
drilling and workover rig operations and
the large amounts and high flow rates of
oil associated with these activities, it
would not be appropriate or
environmentally sound to exempt them
from the SPCC requirements, and thus
they remain subject to 40 CFR part 112.
Although drilling and workover rigs are
not exempt, other types of motive power
containers located at drilling or
workover facilities (i.e., trucks,
automobiles, bulldozers, seismic
exploration vehicles, or other earthmoving equipment) are exempted. The
Agency believes that the general
protection and the spill response and
planning activities provided at an
otherwise regulated SPCC facility will
help the facility owner or operator to
address any spills associated with these
motive power containers. However, the
specific provisions (such as blowout
prevention), which are present in the
rule for drilling or workover rigs, need
to be preserved to maintain an adequate
level of environmental protection for
these unique activities. Therefore, an
exemption for drilling and workover
equipment, including rigs, is
inappropriate.
Some commenters, representing the
aviation, forestry, mining, recycling, and
construction industries, requested that
stationary cranes, gensets, and other
non-self-propelled operational and
towed ground service equipment be
included in the exemption. The Agency
believes that where these kinds of nonself-propelled, stationary or towed
equipment operate in pre-determined
oil handling areas, an SPCC Plan can
reasonably address oil spill prevention
measures under § 112.8(c)(2) and (11).
For example, the Agency understands
that towed ground service equipment at
an airport is typically located at
terminal gates for use when aircraft are
parked at the gates. This equipment
typically is staged and operated in an
area that includes other oil storage
containers such as airport mobile
refuelers (see Section D below). As such,
the identified oil spill prevention
approach that addresses potential spills
from an airport mobile refueler at the
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gate should also address potential spills
from nearby ground service equipment
used by airline personnel at the same
gate. Thus, the exemption does not
include non-self-propelled stationary or
towed equipment, such as towed ground
service equipment or any type of
gensets, but only motor vehicles that
can provide propulsion to another
location. See Chapter 4 of the SPCC
Guidance for Regional Inspectors for
further explanation regarding when
sized secondary containment is required
for mobile or portable containers that
are in a stationary, unattended mode.
D. Mobile Refuelers
EPA proposed to amend the SPCC
rule to define an airport mobile refueler
as a vehicle with an onboard bulk
storage container designed or used
solely to store and transport fuel for
transfer into or from aircraft and ground
service equipment (such as belt loaders,
tractors, luggage transport vehicles,
deicing equipment, and lifts) at airports.
Airport mobile refuelers have onboard
bulk storage containers that are used
solely to transport and transfer fuel and
are subject to the SPCC rule because
they are containers used to store oil
prior to further distribution and use. As
such, they are subject to all applicable
SPCC rule provisions, including the
sized secondary containment provisions
of §§ 112.8(c)(2) (applicable to all bulk
storage containers) and 112.8(c)(11)
(applicable more specifically to mobile/
portable bulk storage containers). These
provisions require a secondary means of
containment, such as a dike or
catchment basin, sufficient to contain
the capacity of the largest single
compartment or container with
sufficient freeboard to contain
precipitation.
As described in the preamble to EPA’s
proposed rule, members of the aviation
sector have expressed concern that
requiring sized secondary containment
for airport mobile refuelers is not
practicable for safety and security
reasons. They argued that requiring
refuelers to park in specifically sized
secondary containment areas located
within an Airport Operations Area
(AOA) could create a safety and security
hazard because it entails grouping the
vehicles or placing impediments in the
AOA. In response to these concerns,
EPA proposed to exempt airport mobile
refuelers from the specifically sized
secondary containment requirements for
bulk storage containers in § 112.8(c)(2)
and (11), while preserving
environmental protection (especially for
fuel transfers associated with airport
mobile refuelers), afforded by the spill
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prevention provisions outlined in
§ 112.7(c).
Members of the aviation sector were
generally supportive of the proposal.
Commenters generally supported the
proposed exemption of airport mobile
refuelers from certain provisions of the
SPCC regulations and noted that general
secondary containment is already
practiced at airports. Commenters stated
that requiring secondary containment
around airport mobile refuelers, while
they are stationary or idle creates
serious safety and security risks. One
commenter did have reservations about
certain provisions of the rule still
governing airport mobile refuelers,
specifically the provisions of § 112.8(c)
and the general secondary containment
requirements of § 112.7(c). A
Professional Engineering firm opposed
the exemption of airport mobile
refuelers from certain provisions of the
SPCC regulation. The commenter
asserted that the argument regarding the
accident potential for not excluding
airport fuel transporters is highly
questionable, since airport fuel spills are
well documented.
The Agency agrees with the
commenter that fuel spills at airports are
well documented, and that potential
spills from airport mobile refuelers need
to be addressed in the facility’s SPCC
Plan. Nevertheless, the Agency agrees
with those commenters that argued that
the sized secondary containment
requirement did present safety and
security concerns and therefore, we are
finalizing the proposal to exclude
mobile refuelers as defined in today’s
rule in § 112.2 from the specifically
sized secondary containment
requirements for bulk storage containers
in §§ 112.8(c)(2) and (11) and
112.12(c)(2) and (11). General secondary
containment still applies for mobile
refuelers at non-transportation-related
facilities, unless permanently closed as
defined in § 112.2.
Although the Agency did not propose
to extend this exclusion to other mobile
refuelers that may operate within the
confines of a non-transportation facility,
we requested comment as to whether
the proposed exclusion should be more
broadly applied to other types of mobile
refuelers. Commenters responded that
the proposed exclusion for airport
mobile refuelers from the sized
secondary containment requirements
should be extended to mobile refuelers
at industrial sites, construction sites,
chemical complexes (i.e., refineries),
mining sites, seaport terminals, and tank
truck home bases. Several commenters
indicated that the same rationale
discussed in the proposed rule preamble
supporting this exclusion applies to
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owners and operators of industrial
facilities as well. Specifically, one
commenter stated that: (1) Requiring
sized secondary containment for
industrial mobile refuelers is not
practicable and distracts from safety and
security monitoring by providing a
blind spot and hiding location behind
the containment unit; (2) requiring
refuelers to park in specially designated
secondary containment areas located
within an industrial or chemical facility
operating area will create safety and
security hazards by grouping the
vehicles or placing impediments in the
operations area; and (3) requiring
mobile refuelers to return to
containment areas located within the
industrial facilities tank farm between
refueling operations will increase the
risk of accidents (and therefore
accidental oil discharge), as the vehicles
would travel with increased frequency
through the busy industrial operating
areas. Another commenter also
indicated that the clarification should
extend to rail cars, since rail cars are
less mobile then airport mobile refuelers
and additional rail car movements in
congested rail yards exposes these
vehicles to many of the hazards
identified for airport mobile refuelers.
The Agency agrees with commenters
that the exclusion provided for airport
mobile refuelers should be extended to
mobile refuelers at other types of
facilities. The Agency agrees that
providing sized secondary containment
for vehicles that move frequently within
a non-transportation-related facility to
perform refueling operations can raise
safety and security concerns, so the
exclusion from complying with the
sized secondary containment
requirements provided for airport
mobile refuelers is being extended to
mobile refuelers that are vehicles with
an onboard bulk storage container used
to store and transport oil for transfer
into or from other vehicles, ground
service equipment or another oil storage
container.
Furthermore, the Agency continues to
believe that other mobile/portable bulk
storage tanks that are being towed by
vehicles or otherwise moved to or from
a designated area typically cannot be
provided with sized secondary
containment as per §§ 112.8(c)(2) and
(11) and 112.12(c)(2) and (11), as
applicable, during that movement or
relocation. However, when these
mobile/portable bulk storage containers
(except mobile refuelers) are placed in
a designated area of a site (e.g., a
construction site) whereby a dike or
catchment basin sufficient to contain
the capacity of the largest single
compartment or container with
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sufficient freeboard to contain
precipitation can be installed, sized
secondary containment requirements
would apply. In the same vein, the
Agency believes that rail cars cannot be
provided with sized secondary
containment when entering, moving
within, or exiting the confines of a
facility. Conversely, when they are
situated in defined locations at an
otherwise regulated facility, sized
secondary containment, such as a
catchment basin, could be provided. See
Chapter 4 of the SPCC Guidance for
Regional Inspectors for further
explanation regarding when sized
secondary containment is required for
mobile or portable containers that are in
a stationary, unattended mode.
1. Definition of Mobile Refueler
EPA is amending the SPCC rule to
exempt mobile refuelers from the
requirements of §§ 112.8(c)(2) and (11)
and 112.12(c)(2) and (11). In today’s
final rule, EPA defines a mobile refueler
as ‘‘a bulk storage container, onboard a
vehicle or towed, that is designed or
used solely to store and transport fuel
for transfer into or from an aircraft,
motor vehicle, locomotive, vessel,
ground service equipment, or other oil
storage container.’’ The definition is
intended to describe vehicles of various
sizes equipped with a bulk storage
container such as a cargo tank or tank
truck that is used to fuel or defuel
aircraft, motor vehicles, locomotives,
tanks, vessels or other oil storage
containers. The definition is also
intended to describe tank full trailers
and tank semi-trailers including those at
airports that are used to fuel or defuel
aircraft. The definition does not include
other mobile or portable oil storage
containers that are not involved in
fueling activities. When these other
mobile or portable containers are in a
stationary, unattended mode and not
under the direct oversight or control of
facility personnel, the requirements of
§§ 112.8(c)(2) and (11) and 112.12(c)(2)
and (11) apply. (See Chapter 4 of the
SPCC Guidance for Regional
Inspectors.) In addition, the Agency
intends the secondary containment
exemption to apply to vehicles used for
refueling, and not vehicles used
primarily for the bulk storage of oil in
a stationary location, in place of
stationary oil storage containers.
A commenter from the aviation sector
supported EPA’s proposed definition
and encouraged the inclusion of fuel
transfers into or from ground service
equipment. Two commenters from the
chemical manufacturing sector stated
that the definition that was proposed is
too broad and unlawfully extends EPA’s
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jurisdiction. The MOU between DOT
and EPA establishes non-transportation
facilities to include ‘‘highway vehicles
and railroad cars which are used for the
transport of oil exclusively within the
confines of a non-transportation-related
facility and which are not intended to
transport oil in interstate or intrastate
commerce.’’ EPA understands that
mobile refuelers that operate solely
within the confines of an airport, or
other type of facility that is subject to
SPCC regulations would be covered by
the definition of mobile refuelers at
§ 112.2. Thus, a mobile refueler that
operates solely on airport property, or
some other type of facility would be
subject to § 112.7(c) during all periods
of operation. Conversely, for a mobile
refueler that operates on highways (i.e.,
intended to transport oil in interstate or
intrastate commerce) in addition to an
airport, or other type of facility, then
only the period of actual transfer
operations at a non-transportation
facility would be subject to the general
secondary containment requirements of
§ 112.7(c), unless the transfer occurs at
a loading/unloading rack, whereby the
rack and vehicle are subject to the
requirements at § 112.7(h).
Similarly, another commenter
suggested applying the existing
requirements for portable fueling facility
requirements of § 112.3(c) to mobile
refuelers when in a fixed, nontransportation mode. Specific
requirements for mobile facilities
should be developed as a separate
subpart through rulemaking. The
Agency disagrees that a separate
rulemaking be initiated for mobile
refuelers. We believe that the
modification being promulgated today
provides the owner or operator with
considerable flexibility to identify the
appropriate spill prevention measures
under § 112.7(c) applicable to the
mobile refueler operation operating
solely at a non-transportation facility.
Furthermore, we disagree that § 112.3(c)
needs to be modified to apply to this
type of mobile refueler that enters a
non-transportation facility as this
provision already addresses a portable
fueling facility operating in a fixed, nontransportation-related mode. For either
type of mobile refueler, § 112.7(c)
applies.
2. Amended Requirements
This amendment revises §§ 112.8(c)(2)
and (11) and 112.12(c)(2) and (11) to
specifically exempt mobile refuelers, as
defined above, from these provisions.
As noted above, the Agency is
expanding the proposed exemption
from the sized secondary containment
requirements to apply to any person that
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operates a mobile refueler. Since mobile
refuelers are mobile or portable bulk
storage containers, the other provisions
of §§ 112.8(c) and 112.12(c) still apply.
Secondary containment systems
sufficient to contain the capacity of the
largest single compartment or container
with sufficient freeboard to contain
precipitation are no longer required. A
commenter representing small business
expressed concerns about the security,
safety and logistical concerns for the
proposed amendment for airport mobile
refuelers. The commenter recommended
that EPA further revise the SPCC
requirements so that general secondary
containment applies only when airport
mobile refuelers are transferring fuel.
The Agency disagrees that the
amendment should be limited to
transfer operations only, as another
commenter asserts that mobile refuelers
can experience leaks and spills (e.g.,
vehicular accidents, line leaks, or other
equipment/container failure). Thus, we
believe that the general secondary
containment provisions at § 112.7(c)
should apply to all mobile refueler
operations.
Per § 112.7(c), appropriate
containment and/or diversionary
structures or equipment must be
designed to prevent a discharge as
described in § 112.1(b). The Agency
believes general secondary containment
should be designed to address the most
likely discharge from the primary
containment system (i.e., the storage
container). Section 112.7(c) allows for
the use of certain types of active
containment measures
(countermeasures or spill response
capability) which prevent a discharge to
navigable waters or adjoining
shorelines. One aviation commenter
indicated that the availability of ‘‘active
measures’’ is necessary to make the
general secondary containment
provision workable in an airport setting.
To clarify, EPA believes that active
containment measures are those that
require deployment or other specific
action by the owner or operator. These
measures may be deployed either before
an activity involving the handling of oil
starts, or in reaction to a discharge, so
long as the active measure is designed
and can reasonably be implemented to
prevent an oil spill from reaching
navigable waters or adjoining
shorelines. Passive measures are
permanent installations and do not
require deployment or action by the
owner or operator. The efficacy of active
containment measures to prevent a
discharge depends on their technical
effectiveness (i.e., mode of operation,
absorption rate), placement and
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quantity, and timely deployment prior
to, or following a discharge. For
discharges that occur only during
manned activities, such as those
occurring during transfers, an active
measure (i.e., sock, mat, other portable
barrier, or land-based response
capability) may be appropriate,
provided that the measure is capable of
containing the oil discharge volume and
rate, and is timely and properly
constructed/deployed. The Agency also
believes that these active measures may
be appropriately applied to other
situations (i.e., when the refueler is not
engaged in transfer operations or
moving around the facility).
In summary, EPA believes that the
general provisions for secondary
containment address the most likely
spill scenarios associated with this
equipment (i.e., during oil transfers into
or from the mobile refuelers). Section
112.7(c) does not prescribe a size for a
secondary containment structure, but
does require appropriate containment
and/or diversionary structures or
equipment to prevent a discharge as
described in § 112.1(b) including the use
of active measures. This final rule
would maintain environmental
protection, while still allowing the
necessary flexibility for compliance
with the general secondary containment
requirements of the rule for mobile
refuelers at airports or other types of
facilities.
E. Animal Fats and Vegetable Oils
The Agency proposed to amend
Subpart C of part 112 by removing
§ 112.13 (requirements for onshore oil
production facilities), § 112.14
(requirements for onshore oil drilling
and workover facilities), and § 112.15
(requirements for offshore oil drilling,
production, or workover facilities) and
by reserving these sections of Subpart C
of the regulation because they are not
appropriate for animal fats and
vegetable oils. Commenters generally
supported this proposal and therefore,
the Agency has amended the final rule
to remove these provisions. In addition,
the Agency also requested comment on
whether different requirements were
appropriate for animal fats and
vegetable oils from the requirements for
petroleum and other oils. Some
commenters provided suggestions for
differentiating animal fats and vegetable
oils from other classes of oils in the
SPCC rule. The Agency is continuing to
examine these issues to determine the
appropriateness of amendments to the
regulatory scheme to differentiate the
SPCC requirements for animal fats and
vegetable oils from the requirements for
petroleum and other oils and plans to
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address this issue in a future
rulemaking.
As a point of clarification, EPA also
removed the phrase ‘‘for onshore
facilities (excluding production
facilities)’’ from the title of § 112.12
Spill Prevention, Control, and
Countermeasure Plan requirements.
Section 112.2 of the rule defines
production facility to mean ‘‘all
structures (including, but not limited to,
wells, platforms, or storage facilities),
piping (including, but not limited to
flowlines or gathering lines), or
equipment (including, but not limited to
workover equipment, separation
equipment, or auxiliary nontransportation-related equipment) used
in the production, extraction, recovery,
lifting, stabilization, separation or
treating of oil, or associated storage or
measurement, and located in a single
geographical oil or gas field operated by
a single operator.’’ The exclusion of
production facilities from § 112.12 was
originally intended to differentiate
requirements based on facility type and
§ 112.13 applied to onshore production
facilities. Since this final rule removes
the inapplicable requirements for
animal fats and vegetable oils, it is no
longer necessary to differentiate onshore
oil production facilities from other
facilities in § 112.12.
As an editorial change, EPA revised
the provisions in § 112.7(a)(2) and
112.7(d) to eliminate reference to the
inapplicable provisions in §§ 112.13 and
112.14, because these sections have
been removed.
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F. Extension of Compliance Dates for
Farm
While determining if the agriculture
sector warrants specific consideration
under the SPCC rule, EPA proposed to
extend the compliance dates for
preparing or amending and
implementing SPCC Plans for farms that
have a total storage capacity of 10,000
gallons of oil or less either indefinitely
or until the Agency publishes a final
rule in the Federal Register establishing
a new compliance date. This final rule
provides an extension for all farms as
defined in this notice until the Agency
promulgates a rule specifically
addressing how farms should be
regulated under the SPCC rules.
1. Eligibility Criteria
Most commenters, primarily from the
agricultural sector, generally supported
EPA’s proposed extension of
compliance for farms with a storage
capacity of 10,000 gallons of oil or less.
Several commenters who supported the
extension suggested modifications to the
extension as proposed, such as
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expanding the extension to all farms.
Supporters argued the proposal reduces
unnecessary regulatory burden on the
agricultural community, while the
Agency determines if this sector
warrants specific consideration under
the SPCC rule. Others argued that the
sector is already regulated by state and
local agencies for pollution-related
activities on farms. Support for the
argument that the physical layout of a
farm makes this sector unique within
the universe of SPCC-regulated facilities
was also offered. Comments also were
offered in opposition to the extension
and potential exemptions from SPCC
requirements for farms. Commenters
argued that farms may endanger the
environment, farmers, and their
neighbors and expressed concern that
farms are often close to surface waters.
Commenters opposing the extension
also argued that farms should have been
in compliance with the original SPCC
rule and that current technology makes
compliance relatively inexpensive and
easy.
In finalizing the compliance extension
for farms, EPA is adopting the definition
of ‘‘farm,’’ as proposed, for purposes of
part 112 and the extension in the final
rule. EPA defines ‘‘farm,’’ in part, by
adapting the definition used by the
National Agricultural Statistics Service
(NASS) in its Census of Agriculture.
NASS defines a farm as any place from
which $1,000 or more of agricultural
products were produced and sold, or
normally would have been sold, during
the census year. Operations receiving
$1,000 or more in Federal government
payments are counted as farms, even if
they have no sales and otherwise lack
the potential to have $1,000 or more in
sales.
EPA also considered the definition it
uses to exempt farm tanks under the
Underground Storage Tank (UST)
regulations at 40 CFR part 280. As
defined in 40 CFR 280.12, a farm tank
is a tank located on a tract of land
devoted to the production of crops or
raising of animals, including fish. The
preamble to the UST rule explains that
the term ‘‘farm’’ includes fish
hatcheries, rangeland, and nurseries
with growing operations, but does not
include laboratories where animals are
raised, land used to grow timber, and
pesticide aviation operations. This term
also does not include retail stores or
garden centers where the product of
nursery farms is marketed, but not
produced, nor does the Agency interpret
the term ‘‘farm’’ to include golf courses
or other places dedicated primarily to
recreational, aesthetic, or other nonagricultural activities. (See 53 FR 37082,
37117, September 23, 1988.) EPA
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utilized elements of the UST definition
of farm, in combination with the Census
definition, in developing the proposal
and final rule. By combining elements
of both of these approaches, the Agency
believes the definition more specifically
targets the intended universe for the
extension.
Several commenters provided general
remarks on definitions of facility, farm,
farming facility, farming operation, and/
or agribusiness for purposes of the SPCC
rule; some proposed alternate
definitions of farm. One suggested
alternative was to use the definition of
eligible agricultural businesses used in
the ‘‘Agricultural Business Security Tax
Credit Act of 2005’’ (S. 052). Most
broadly, the term ‘‘eligible agricultural
business’’ means any person in the trade
or business of: selling agricultural
products, including specified
agricultural chemicals, at retail
predominantly to farmers and ranchers,
or manufacturing, formulating,
distributing, or aerially applying
specified agricultural chemicals. The
Agency disagrees with expanding the
definition as suggested because we
believe it would apply to businesses
that are distinctly different from farms,
e.g., oil marketing and distribution to
farmers, that do not present the same
unique issues that farms raise. In fact,
these agribusinesses are more like
industrial or manufacturing operations
and thus, it would be inappropriate to
include these businesses within the
compliance extension. Several
commenters suggested that the farm
definition specify that operations
comprised of non-contiguous or nonadjacent agricultural lands would not be
considered a single ‘‘farm facility’’ for
purposes of fuel tank storage capacity
regardless of whether such parcels of
land are under common ownership or
control. They also suggested that the
Agency allow for aggregate tank storage
capacity to be determined separately for
each field or parcel of such agricultural
lands. The definition of facility as
provided in § 112.2 currently provides
the flexibility for the owner or operator
of a farm to determine the scope of his
or her facility as recommended by the
commenters. However, the Agency will
further explore these questions in a
future rulemaking addressing farms.
The Agency is also expanding the
extension to owners and operators of all
facilities that meet the definition of farm
finalized in today’s rule, which was
supported by many of the commenters.
This action allows the Agency to study
the universe and determine whether the
current requirements are appropriate for
farms. The Agency is expanding this
extension because, upon further
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assessment, we believe it is premature
for the Agency to determine that the
current SPCC requirements are
appropriate for farms with oil storage
capacities greater than 10,000 gallons
before we undertake our study of the
universe of farms.
2. Compliance Date Extension for Farms
With today’s action, EPA extends the
compliance dates for the owner or
operator of a farm, as defined in § 112.2,
to prepare or amend and implement the
farm’s SPCC Plan until the effective date
of a rule addressing whether to provide
differentiated requirements for farms.
The Agency will announce the new
compliance date in the Federal Register.
The Agency will be conducting
additional information collection and
analysis to determine if differentiated
SPCC requirements may be appropriate
for farms. The Agency will be working
with USDA to collect data that would
more accurately characterize oil
handling at these facilities, thereby
allowing the Agency to focus on
priorities where substantial
environmental improvements can be
obtained.
Some commenters argued that EPA
should provide a suspension of
requirements rather than an extension of
the compliance date. We believe that
providing a compliance extension in the
same manner as previous compliance
extensions that have been granted is
appropriate. We are not aware that the
farming community has had concerns
with the previous compliance
extensions that have been granted. In
addition, we would have concerns about
the impact that such an action may have
as some number of farms handle
significant quantities of oil and it would
not be appropriate to issue a blanket
suspension of all spill prevention
requirements for owners and operators
of these facilities. By extending the
compliance date, the Agency is allowing
for burden relief, while it makes a
determination of whether the
agriculture sector warrants specific
consideration under the SPCC rule.
Regardless of whether the Agency
ultimately determines that differentiated
requirements for farms are warranted,
we will publish a notice in the Federal
Register proposing new compliance
dates for farms.
VI. Statutory and Executive Order
Reviews
A. Executive Order 12866—Regulatory
Planning and Review
Under section 3(f)(1) of Executive
Order (EO) 12866 (58 FR 51735, October
4, 1993), this action is an ‘‘economically
significant regulatory action’’ because it
is likely to have an annual effect on the
economy of $100 million or more.
Accordingly, EPA submitted this action
to the Office of Management and Budget
(OMB) for review under EO 12866 and
any changes made in response to OMB
recommendations have been
documented in the docket for this
action.
In addition, EPA prepared an analysis
of the potential costs and benefits
associated with this action. This
analysis is contained in the ‘‘Regulatory
Impact Analysis for the Final Revisions
to the Oil Pollution Prevention
Regulations’’ (October 2006). A copy of
the analysis is available in the docket
for this action and the analysis is briefly
summarized here.
The regulatory impact analysis
developed in support of today’s action
compares the compliance costs for
owners and operators of facilities
affected by the 2006 amendments to the
costs owners and operators would face
under the SPCC rule as amended in
2002 with respect to the four major
components of the final rule: (1)
Qualified facilities with 10,000 gallons
77287
or less of storage capacity; (2) facilities
with certain types of oil-filled
operational equipment; (3) facilities
with motive power containers; and (4)
facilities with mobile refuelers.
For each of these components, the
benefits consist of reductions in costs
accruing from reductions in compliance
costs. The main steps used to estimate
the compliance cost impacts of the
SPCC final Rule are as follows:
• Develop the baseline universe of
SPCC-regulated facilities;
• Estimate the number of facilities
affected by the final rule amendments;
• Estimate changes in compliance
cost elements resulting from the final
rule;
• Estimate total compliance cost
savings to owners and operators of
potentially affected facilities; and
• Annualize compliance cost savings
over a ten-year period, 2008 through
2017, and discount the estimates using
3 and 7 percent discount rates.
Based on these procedures, EPA
estimated the average annual number of
potentially affected facilities and the
annual compliance cost savings
associated with each of the four major
components of the final rule, as can be
seen in Exhibit 1. EPA assumes cost
minimization behavior applies to all
owners and operators of facilities that
qualify for reduced regulatory
requirements, whereby all those affected
will seek burden relief. These estimates
are not necessarily additive, given that
they do not account for interactions
among the various components of the
final rule. Exhibit 1 presents one
compliance cost savings scenario for
each rule component, whereby all
qualified facilities, 50 percent of
qualified oil-filled operational
equipment, 10 percent of motive power
containers, and 50 percent of mobile
refuelers are affected.
EXHIBIT 1.—COMPLIANCE COST SAVINGS ASSOCIATED WITH THIS FINAL ACTION
Projected average annual
number of affected facilities
Estimated annual compliance
cost savings
($2005 in millions)
Major components of the final rule
Existing
Qualified Facilities ........................................................................................
Qualified Oil-filled Equipment ......................................................................
Motive Power Containers ............................................................................
Mobile Refuelers ..........................................................................................
337,000
10
28,500
10
New
Discounted 3%
Discounted 7%
$37.9
53.1
1.07
34.4
$37.7
52.8
1.07
34.2
7,260
5,040
516
2,940
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1 The number of existing facilities with qualified oil-filled operational equipment and mobile refuelers is zero because EPA assumed that existing SPCC-regulated facilities would already have secondary containment or a determination of the impracticability of secondary containment in
accordance with § 112.7(d).
EPA also prepared an Alternative
Baseline that describes the estimated
changes in cost savings resulting from
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the 2006 SPCC final rule assuming
partial (50 percent) compliance. For this
alternative analysis, EPA assumed 50
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percent compliance with both the 2002
and 2006 rules. The Agency anticipates
the compliance rate under the 2006 final
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rule to be at the same level as it would
have been under the 2002 rule, or
higher.
B. Paperwork Reduction Act
The information collection
requirements for the final rule were
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
0328.13.
EPA does not collect the information
required by the SPCC rule on a routine
basis. SPCC Plans ordinarily need not be
submitted to EPA, but must generally be
maintained at the facility. Preparation,
implementation, and maintenance of an
SPCC Plan by the facility owner or
operator helps prevent oil discharges,
and mitigates the environmental damage
caused by such discharges. Therefore,
the primary user of the data is the
facility personnel. While EPA may, from
time to time, request information under
these regulations, such requests are not
routine.
Although facility personnel are the
primary data user, EPA also uses the
data in certain situations. EPA reviews
SPCC Plans: (1) When it requests a
facility owner or operator to submit
required information in the event of
certain discharges of oil or to evaluate
an extension request; and, (2) as part of
EPA’s inspection program. State and
local governments also use the data,
which are not necessarily available
elsewhere and can greatly assist local
emergency preparedness efforts.
Preparation of the information for
affected facilities is required under
section 311(j)(1) of the Act as
implemented by 40 CFR part 112.
EPA estimates that in the absence of
this rulemaking, approximately 580,000
facilities would be subject to the SPCC
rule in 2006 and have SPCC Plans. In
addition, EPA estimates that
approximately 17,500 new facilities
would become subject to SPCC
requirements annually. In the absence of
this final rulemaking, EPA projects that
the average annual public reporting and
recordkeeping burden for this
information collection would be
2,695,329 hours.
Under today’s rulemaking, owners
and operators of qualified facilities no
longer need a licensed Professional
Engineer to certify their Plans. Facilities
that store oil solely in motive power
containers are no longer regulated,
while owners and operators of facilities
with oil storage in addition to motive
power containers may incur lower
compliance costs. Today’s rule also
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allows greater use of contingency plans
and written commitment of manpower,
equipment, and resources without
requiring an impracticability
determination when combined with an
inspection or monitoring program as an
alternative to secondary containment for
qualified oil-filled operational
equipment. It also allows mobile
refuelers at airports and facilities within
other industries, to fall under a facility’s
general secondary containment
requirements, rather than require
specifically sized secondary
containment.
Under today’s rule, an estimated
434,000 regulated facilities would
annually be subject to the SPCC
information collection requirements of
this rule during the information
collection period. This figure excludes
farms, to reflect the final compliance
extension. Under this rule, the
estimated annual average burden over
the next three-year ICR period would be
approximately 2,191,069 hours,
resulting in a 19 percent average
reduction. The estimated average annual
public reporting for owners and
operators of individual facilities already
regulated under the SPCC rule would
range between 3.3 and 7.1 hours, while
the burden for owners and operators of
newly regulated facilities would range
between 40.1 and 70.1 hours as a result
of this final action. The net annualized
capital and start-up costs for the SPCC
information collection portion of the
rule would average $1.4 million and net
annualized operation and maintenance
(O&M) costs are estimated to be $34.3
million for owners and operators of all
of these facilities combined.
Burden means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, or disclose
or provide information to or for a
Federal agency. This includes the time
needed to review instructions; develop,
acquire, install, and utilize technology
and systems for the purposes of
collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
An agency may not conduct or
sponsor, and a person is not required to
respond to a collection of information
unless it displays a currently valid OMB
control number. The OMB control
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numbers for EPA’s regulations in 40
CFR are listed in 40 CFR part 9.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act
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 final rule on small entities,
small entity is defined as: (1) a small
business as defined in the SBA’s
regulations at 13 CFR 121.201—the SBA
defines small businesses by category of
business using North American Industry
Classification System (NAICS) codes,
and in the case of farms and production
facilities, which constitute a large
percentage of the facilities affected by
this final rule, generally defines small
businesses as having less than $500,000
in revenues or 500 employees,
respectively; (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 that is independently owned
and operated and is not dominant in its
field.
After considering the economic
impacts of today’s final rule on small
entities, I certify that this action would
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, since the primary purpose of
the regulatory flexibility analyses is to
identify and address regulatory
alternatives ‘‘which minimize any
significant economic impact of the final
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.
This rule reduces regulatory burden
on owners and operators of qualified
facilities and facilities with qualified
oil-filled operational equipment.
Owners and operators of qualified
facilities no longer need a licensed
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Professional Engineer to certify their
Plans. Facilities that store oil solely in
motive power containers are no longer
regulated, while owners and operators
of facilities with oil storage in addition
to motive power containers may incur
lower compliance costs. Today’s rule
also allows greater use of contingency
plans and a written commitment of
manpower, equipment, and materials
without requiring an impracticability
determination as an alternative to
secondary containment for qualified oilfilled operational equipment when
combined with an established and
documented inspection or monitoring
program. It also allows mobile refuelers
no matter the industry to fall under a
facility’s general secondary containment
requirements rather than require
specifically sized secondary
containment. The Agency has therefore
concluded that today’s rule relieves
regulatory burden for small entities.
Overall, EPA estimates that today’s
rule will reduce annual compliance
costs by roughly $38 million for owners
and operators of qualified facilities, $53
million for owners and operators of
facilities with qualified oil-filled
equipment, $1 million for owners and
operators of facilities with motive power
containers, and $34 million for owners
and operators of facilities with mobile
refuelers. Total costs were annualized
over a 10-year period using both 3 and
7 percent discount rates assuming all
qualified facilities, 50 percent of
qualified oil-filled operational
equipment, 10 percent of motive power
containers, and 50 percent of mobile
refuelers are affected under this
scenario. EPA derived these savings by
estimating the number of facilities
affected by each provision in the final
rule; identifying the specific behavioral
changes (e.g., choosing to self-certify an
SPCC Plan rather than using a licensed
PE) that may occur; estimating the unit
costs of compliance measures under the
baseline and regulatory scenarios; and
applying the change in unit costs to the
projected number of affected facilities.
We have therefore concluded that
today’s final rule will relieve regulatory
burden for all affected small entities.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, local,
and tribal governments and the private
sector. Under section 202 of UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
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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 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-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
UMRA a small government agency plan.
The plan must provide for notifying
potentially affected small governments,
enabling officials of affected small
governments to have meaningful and
timely input in the development of EPA
regulatory proposals with significant
Federal intergovernmental mandates,
and informing, educating, and advising
small governments on compliance with
the regulatory requirements. EPA has
determined that this final rule does not
contain a Federal mandate that may
result in expenditures of $100 million or
more for State, local, and tribal
governments, in the aggregate, or the
private sector in any one year. Today’s
final rule would reduce compliance
costs on owners and operators of
affected facilities by as much as $126
million annually, although EPA
acknowledges this estimate is derived
from analyses of each of the four major
components of the final rule and are not
necessarily additive, given that they do
not account for interactions among the
various components. Thus, today’s rule
is not subject to the requirements of
sections 202 and 205 of the UMRA.
EPA has determined that this rule
contains no regulatory requirements that
might significantly or uniquely affect
small governments. As explained above,
the effect of final rule would be to
reduce burden and costs for owners and
operators of qualified regulated
facilities, including certain small
governments that are subject to the rule.
E. Executive Order 13132—Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
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77289
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 final rule does not have
federalism implications. It would 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. Under CWA
section 311(o), States may impose
additional requirements, including more
stringent requirements, relating to the
prevention of oil discharges to navigable
waters. EPA encourages States to
supplement the Federal SPCC program
and recognizes that some States have
more stringent requirements. 56 FR
54612 (October 22, 1991). This final rule
would not preempt State law or
regulations. Thus, Executive Order
13132 does not apply to this final rule.
F. Executive Order 13175—Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ This final rule does not
have tribal implications, as specified in
Executive Order 13175. Today’s rule
would not significantly or uniquely
affect communities of Indian trial
governments. Thus, Executive Order
13175 does not apply to this rule.
G. Executive Order 13045—Protection of
Children From Environmental Health &
Safety Risks
Executive Order 13045, ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997), applies to any rule that:
(1) Is determined to be ‘‘economically
significant’’ as defined under Executive
Order 12866; and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
the Agency must evaluate the
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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. EPA
interprets Executive Order 13045 as
applying only to those regulatory
actions that are based on health or safety
risks, such that the analysis required
under section 5–501 of the Order has
the potential to influence the regulation.
This final rule is not subject to
Executive Order 13045 because the
Agency does not have reason to believe
the environmental health or safety risks
addressed by this action present a
disproportionate risk to children.
H. Executive Order 13211—Actions
That Significantly Affect Energy Supply,
Distribution, or Use
This rule is not a ‘‘significant energy
action’’ as defined in Executive Order
13211, ‘‘Actions Concerning Regulations
that Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355, May
22, 2001) because it is not likely to have
a significant adverse effect on the
supply, distribution, or use of energy.
The overall effect of the rule is to
decrease the regulatory burden on
facility owners or operators subject to its
provisions.
jlentini on PROD1PC65 with RULES
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, section 12(d) (15 U.S.C. 272
note) directs EPA to use voluntary
consensus standards in its regulatory
activities unless to do so would be
inconsistent with applicable law or
otherwise impractical. Voluntary
consensus standards are technical
standards such as 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 rule does not involve technical
standards. Therefore, EPA did not
consider the use of any voluntary
consensus standards.
J. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
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submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A major rule
cannot take effect until 60 days after it
is published in the Federal Register.
This action is a ‘‘major rule’’ as defined
by 5 U.S.C. 804(2) because it will likely
result in an annual effect on the
economy of $100 million or more. This
rule will be effective February 26, 2007.
List of Subjects in 40 CFR Part 112
Environmental protection, Airports,
Animal fats and vegetable oils, Farms,
Fire prevention, Flammable materials,
Materials handling and storage, Oil
pollution, Oil spill response, Penalties,
Petroleum, Reporting and recordkeeping
requirements, Tanks, Water pollution
control, Water resources.
Dated: December 12, 2006.
Stephen L. Johnson,
Administrator.
For the reasons stated in the preamble,
the Environmental Protection Agency
amends 40 CFR part 112 as follows:
I
PART 112—OIL POLLUTION
PREVENTION
1. The authority citation for part 112
continues to read as follows:
I
Authority: 33 U.S.C. 1251 et seq.; 33 U.S.C.
2720; and E.O. 12777 (October 18, 1991), 3
CFR, 1991 Comp., p. 351.
Subpart A—[Amended]
2. Amend § 112.1 by revising
paragraph (d)(2)(ii) and adding
paragraph (d)(7) to read as follows:
I
§ 112.1
General applicability.
*
*
*
*
*
(d) * * *
(2) * * *
(ii) The aggregate aboveground storage
capacity of the facility is 1,320 gallons
or less of oil. For the purposes of this
exemption, only containers with a
capacity of 55 gallons or greater are
counted. The aggregate aboveground
storage capacity of a facility excludes
the capacity of a container that is
‘‘permanently closed,’’ and the capacity
of a ‘‘motive power container’’ as
defined in § 112.2.
*
*
*
*
*
(7) Any ‘‘motive power container,’’ as
defined in § 112.2. The transfer of fuel
or other oil into a motive power
container at an otherwise regulated
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facility is not eligible for this
exemption.
*
*
*
*
*
I 3. Amend § 112.2 by adding
definitions for ‘‘Farm,’’ ‘‘Mobile
refueler,’’ ‘‘Motive power container,’’
and ‘‘Oil-filled operational equipment’’
in alphabetical order to read as follows:
§ 112.2
Definitions.
*
*
*
*
*
Farm means a facility on a tract of
land devoted to the production of crops
or raising of animals, including fish,
which produced and sold, or normally
would have produced and sold, $1,000
or more of agricultural products during
a year.
*
*
*
*
*
Mobile refueler means a bulk storage
container onboard a vehicle or towed,
that is designed or used solely to store
and transport fuel for transfer into or
from an aircraft, motor vehicle,
locomotive, vessel, ground service
equipment, or other oil storage
container.
Motive power container means any
onboard bulk storage container used
primarily to power the movement of a
motor vehicle, or ancillary onboard oilfilled operational equipment. An
onboard bulk storage container which is
used to store or transfer oil for further
distribution is not a motive power
container. The definition of motive
power container does not include oil
drilling or workover equipment,
including rigs.
*
*
*
*
*
Oil-filled operational equipment
means equipment that includes an oil
storage container (or multiple
containers) in which the oil is present
solely to support the function of the
apparatus or the device. Oil-filled
operational equipment is not considered
a bulk storage container, and does not
include oil-filled manufacturing
equipment (flow-through process).
Examples of oil-filled operational
equipment include, but are not limited
to, hydraulic systems, lubricating
systems (e.g., those for pumps,
compressors and other rotating
equipment, including pumpjack
lubrication systems), gear boxes,
machining coolant systems, heat
transfer systems, transformers, circuit
breakers, electrical switches, and other
systems containing oil solely to enable
the operation of the device.
I 4. Amend § 112.3 as follows:
I a. By redesignating paragraph (a) as
paragraph (a)(1).
I b. By adding paragraph (a)(2).
I c. By redesignating paragraph (b) as
paragraph (b)(1).
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Federal Register / Vol. 71, No. 247 / Tuesday, December 26, 2006 / Rules and Regulations
§ 112.6 Qualified Facility Plan
Requirements.
d. By adding paragraph (b)(2).
e. By revising paragraph (d)
introductory text.
I f. By adding paragraph (g).
I
I
§ 112.3 Requirement to prepare and
implement a Spill Prevention, Control, and
Countermeasure Plan.
*
*
*
*
*
(a)(1) * * *
(2) If your onshore facility is a farm
as defined in § 112.2, the compliance
date described in paragraph (a)(1) of this
section is delayed until the effective
date of a rule establishing SPCC
requirements specifically for farms or
otherwise establishes dates by which
farms must comply with the provisions
of this part.
(b)(1) * * *
(2) If your onshore facility meets the
definition of farm in § 112.2, the
compliance date described in paragraph
(b)(1) of this section is delayed until the
effective date of a rule establishing
SPCC requirements specifically for
farms or otherwise establishes dates by
which farms must comply with the
provisions of this part.
*
*
*
*
*
(d) Except as provided in § 112.6, a
licensed Professional Engineer must
review and certify a Plan for it to be
effective to satisfy the requirements of
this part.
*
*
*
*
*
(g) Qualified Facilities. The owner or
operator of a qualified facility as defined
in this subparagraph may self-certify his
or her facility’s Plan, as provided in
§ 112.6. A qualified facility is one that:
(1) Has an aggregate aboveground
storage capacity of 10,000 gallons or
less; and
(2) Has had no single discharge as
described in § 112.1(b) exceeding 1,000
U.S. gallons or no two discharges as
described in § 112.1(b) each exceeding
42 U.S. gallons within any twelve
month period in the three years prior to
the SPCC Plan self-certification date, or
since becoming subject to this part if the
facility has been in operation for less
than three years (other than discharges
as described in § 112.1(b) that are the
result of natural disasters, acts of war,
or terrorism).
I 5. Amend § 112.5 by revising
paragraph (c) to read as follows:
§ 112.5 Amendment of Spill Prevention,
Control, and Countermeasure Plan by
owners or operators.
jlentini on PROD1PC65 with RULES
*
*
*
*
*
(c) Except as provided in § 112.6, have
a Professional Engineer certify any
technical amendments to your Plan in
accordance with § 112.3(d).
I 6. Add § 112.6 to read as follows:
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16:12 Dec 22, 2006
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(a) Preparation and Self-certification
of Plan. If you are the owner or operator
of a facility that meets the qualified
facility qualification criteria in
§ 112.3(g), you may choose to self-certify
your Plan. You must certify in the Plan
that:
(1) You are familiar with the
requirements of this part;
(2) You have visited and examined
the facility;
(3) The Plan has been prepared in
accordance with accepted and sound
industry practices and standards, and
with the requirements of this part;
(4) Procedures for required
inspections and testing have been
established;
(5) The Plan is being fully
implemented;
(6) The facility meets the qualification
criteria set forth under § 112.3(g);
(7) The Plan does not deviate from
any requirement of this part as allowed
by §§ 112.7(a)(2) and 112.7(d), except as
provided in paragraph (c) of this
section; and
(8) The Plan and individual(s)
responsible for implementing the Plan
have the full approval of management
and the facility owner or operator has
committed the necessary resources to
fully implement the Plan.
(b) Self-certification of Technical
Amendments. If you self-certify your
Plan pursuant to paragraph (a) of this
section, you must certify any technical
amendments to your Plan in accordance
with paragraph (a) of this section when
there is a change in the facility design,
construction, operation, or maintenance
that affects its potential for a discharge
as described in § 112.1(b) except:
(1) If a Professional Engineer certified
a portion of your Plan in accordance
with paragraph (d) of this section, and
the technical amendment affects this
portion of the Plan, you must have the
amended provisions of your Plan
certified by a Professional Engineer in
accordance with § 112.6(d)(2).
(2) If the change is such that the
facility no longer meets the qualifying
criteria in § 112.3(g) because it exceeds
10,000 gallons in aggregate aboveground
storage capacity, you must prepare a
Plan in accordance with the general
Plan requirements in § 112.7 and the
applicable requirements in subparts B
and C, including having the Plan
certified by a Professional Engineer as
required under § 112.3(d).
(c) Applicable Requirements. Except
as provided in this subparagraph, your
self-certified SPCC Plan must comply
with § 112.7 and the applicable
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77291
requirements in subparts B and C of this
part:
(1) Environmental Equivalence. Your
Plan may not include alternate methods
which provide environmental
equivalence pursuant to § 112.7(a)(2),
unless each alternate method has been
reviewed and certified in writing by a
Professional Engineer, as provided in
paragraph (d) of this section.
(2) Impracticability. Your Plan may
not include any determinations that
secondary containment is impracticable
and provisions in lieu of secondary
containment pursuant to § 112.7(d),
unless each such determination and
alternative provision has been reviewed
and certified in writing by a
Professional Engineer, as provided in
paragraph (d) of this section.
(3) Security (excluding oil production
facilities). You must either:
(i) Comply with the requirements
under § 112.7(g); or
(ii) Describe in your Plan how you
secure and control access to the oil
handling, processing and storage areas;
secure master flow and drain valves;
prevent unauthorized access to starter
controls on oil pumps; secure out-ofservice and loading/unloading
connections of oil pipelines; address the
appropriateness of security lighting to
both prevent acts of vandalism and
assist in the discovery of oil discharges.
(4) Bulk Storage Container
Inspections. You must either:
(i) Comply with the requirements
under § 112.8(c)(6) or § 112.12(c)(6), as
applicable; or
(ii) Test/inspect each aboveground
container for integrity on a regular
schedule and whenever material repairs
are made. You must determine, in
accordance with industry standards, the
appropriate qualifications for personnel
performing tests and inspections, the
frequency and type of testing and
inspections which take into account
container size, configuration, and design
(such as containers that are: shop built,
skid-mounted, elevated, equipped with
a liner, double walled, or partially
buried). Examples of these integrity tests
include, but are not limited to: visual
inspection, hydrostatic testing,
radiographic testing, ultrasonic testing,
acoustic emissions testing, or other
systems of non-destructive testing. You
must keep comparison records and you
must also inspect the container’s
supports and foundations. In addition,
you must frequently inspect the outside
of the container for signs of
deterioration, discharges, or
accumulation of oil inside diked areas.
Records of inspections and tests kept
under usual and customary business
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Federal Register / Vol. 71, No. 247 / Tuesday, December 26, 2006 / Rules and Regulations
jlentini on PROD1PC65 with RULES
practices satisfy the recordkeeping
requirements of this paragraph.
(d) Professional Engineer Certification
of Portions of a Qualified Facility’s Selfcertified Plan. As described in
paragraph (c) of this section, the facility
owner or operator may not self-certify
alternative measures allowed under
§ 112.7(a)(2) or (d), that are included in
the facility’s Plan. Such measures must
be reviewed and certified, in writing, by
a licensed Professional Engineer as
follows:
(1) For each alternative measure
allowed under § 112.7(a)(2), the Plan
must be accompanied by a written
statement by a Professional Engineer
that states the reason for
nonconformance and describes the
alternative method and how it provides
equivalent environmental protection in
accordance with § 112.7(a)(2). For each
determination of impracticability of
secondary containment pursuant to
§ 112.7(d), the Plan must clearly explain
why secondary containment measures
are not practicable at this facility and
provide the alternative measures
required in § 112.7(d) in lieu of
secondary containment.
(2) By certifying each measure
allowed under § 112.7(a)(2) and (d), the
Professional Engineer attests:
(i) That he is familiar with the
requirements of this part;
(ii) That he or his agent has visited
and examined the facility; and
(iii) That the alternative method of
environmental equivalence in
accordance with § 112.7(a)(2) or the
determination of impracticability and
alternative measures in accordance with
§ 112.7(d) is consistent with good
engineering practice, including
consideration of applicable industry
standards, and with the requirements of
this part.
(3) The review and certification by the
Professional Engineer under this
paragraph is limited to the alternative
method which achieves equivalent
environmental protection pursuant to
§ 112.7(a)(2) or to the impracticability
determination and measures in lieu of
secondary containment pursuant to
§ 112.7(d).
I 7. Amend § 112.7 as follows:
I a. By revising paragraph (a)(2).
I b. By revising paragraph (c)
introductory text.
I c. By revising paragraph (d)
introductory text.
I d. By adding paragraph (k).
§ 112.7 General requirements for Spill
Prevention, Control, and Countermeasure
Plans.
*
*
*
(a) * * *
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*
*
16:12 Dec 22, 2006
Jkt 211001
(2) Comply with all applicable
requirements listed in this part. Except
as provided in § 112.6, your Plan may
deviate from the requirements in
paragraphs (g), (h)(2) and (3), and (i) of
this section and the requirements in
subparts B and C of this part, except the
secondary containment requirements in
paragraphs (c) and (h)(1) of this section,
and §§ 112.8(c)(2), 112.8(c)(11),
112.9(c)(2), 112.10(c), 112.12(c)(2), and
112.12(c)(11), where applicable to a
specific facility, if you provide
equivalent environmental protection by
some other means of spill prevention,
control, or countermeasure. Where your
Plan does not conform to the applicable
requirements in paragraphs (g), (h)(2)
and (3), and (i) of this section, or the
requirements of subparts B and C of this
part, except the secondary containment
requirements in paragraph (c) and (h)(1)
of this section, and §§ 112.8(c)(2),
112.8(c)(11), 112.9(c)(2), 112.10(c),
112.12(c)(2), and 112.12(c)(11), you
must state the reasons for
nonconformance in your Plan and
describe in detail alternate methods and
how you will achieve equivalent
environmental protection. If the
Regional Administrator determines that
the measures described in your Plan do
not provide equivalent environmental
protection, he may require that you
amend your Plan, following the
procedures in § 112.4(d) and (e).
*
*
*
*
*
(c) Provide appropriate containment
and/or diversionary structures or
equipment to prevent a discharge as
described in § 112.1(b), except as
provided in paragraph (k) of this section
for qualified oil-filled operational
equipment. The entire containment
system, including walls and floor, must
be capable of containing oil and must be
constructed so that any discharge from
a primary containment system, such as
a tank or pipe, will not escape the
containment system before cleanup
occurs. At a minimum, you must use
one of the following prevention systems
or its equivalent:
*
*
*
*
*
(d) Provided your Plan is certified by
a licensed Professional Engineer under
§ 112.3(d), or, in the case of a qualified
facility that meets the criteria in
§ 112.3(g), the relevant sections of your
Plan are certified by a licensed
Professional Engineer under § 112.6(d),
if you determine that the installation of
any of the structures or pieces of
equipment listed in paragraphs (c) and
(h)(1) of this section, and §§ 112.8(c)(2),
112.8(c)(11), 112.9(c)(2), 112.10(c),
112.12(c)(2), and 112.12(c)(11) to
prevent a discharge as described in
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Fmt 4700
Sfmt 4700
§ 112.1(b) from any onshore or offshore
facility is not practicable, you must
clearly explain in your Plan why such
measures are not practicable; for bulk
storage containers, conduct both
periodic integrity testing of the
containers and periodic integrity and
leak testing of the valves and piping;
and, unless you have submitted a
response plan under § 112.20, provide
in your Plan the following:
*
*
*
*
*
(k) Qualified Oil-filled Operational
Equipment. The owner or operator of a
facility with oil-filled operational
equipment that meets the qualification
criteria in paragraph (k)(1) of this subsection may choose to implement for
this qualified oil-filled operational
equipment the alternate requirements as
described in paragraph (k)(2) of this subsection in lieu of general secondary
containment required in paragraph (c) of
this section.
(1) Qualification Criteria—Reportable
Discharge History: The owner or
operator of a facility that has had no
single discharge as described in
§ 112.1(b) from any oil-filled operational
equipment exceeding 1,000 U.S. gallons
or no two discharges as described in
§ 112.1(b) from any oil-filled operational
equipment each exceeding 42 U.S.
gallons within any twelve month period
in the three years prior to the SPCC Plan
certification date, or since becoming
subject to this part if the facility has
been in operation for less than three
years (other than oil discharges as
described in § 112.1(b) that are the
result of natural disasters, acts of war or
terrorism); and
(2) Alternative Requirements to
General Secondary Containment. If
secondary containment is not provided
for qualified oil-filled operational
equipment pursuant to paragraph (c) of
this section, the owner or operator of a
facility with qualified oil-filled
operational equipment must:
(i) Establish and document the facility
procedures for inspections or a
monitoring program to detect equipment
failure and/or a discharge; and
(ii) Unless you have submitted a
response plan under § 112.20, provide
in your Plan the following:
(A) An oil spill contingency plan
following the provisions of part 109 of
this chapter.
(B) A written commitment of
manpower, equipment, and materials
required to expeditiously control and
remove any quantity of oil discharged
that may be harmful.
E:\FR\FM\26DER1.SGM
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Federal Register / Vol. 71, No. 247 / Tuesday, December 26, 2006 / Rules and Regulations
Subpart B—[Amended]
8. Amend § 112.8 by revising
paragraphs (c)(2) and (c)(11) to read as
follows:
I
§ 112.8 Spill Prevention, Control, and
Countermeasure Plan requirements for
onshore facilities (excluding production
facilities).
*
*
*
*
*
(c) * * *
(2) Construct all bulk storage tank
installations (except mobile refuelers) so
that you provide a secondary means of
containment for the entire capacity of
the largest single container and
sufficient freeboard to contain
precipitation. You must ensure that
diked areas are sufficiently impervious
to contain discharged oil. Dikes,
containment curbs, and pits are
commonly employed for this purpose.
You may also use an alternative system
consisting of a drainage trench
enclosure that must be arranged so that
any discharge will terminate and be
safely confined in a facility catchment
basin or holding pond.
*
*
*
*
*
(11) Position or locate mobile or
portable oil storage containers to
prevent a discharge as described in
§ 112.1(b). Except for mobile refuelers,
you must furnish a secondary means of
containment, such as a dike or
catchment basin, sufficient to contain
the capacity of the largest single
compartment or container with
sufficient freeboard to contain
precipitation.
*
*
*
*
*
Subpart C—[Amended]
9. Amend § 112.12 by revising the
section heading and by revising
paragraphs (c)(2) and (c)(11) to read as
follows:
I
§ 112.12 Spill Prevention, Control, and
Countermeasure Plan requirements.
jlentini on PROD1PC65 with RULES
*
*
*
*
*
(c) * * *
(2) Construct all bulk storage tank
installations (except mobile refuelers) so
that you provide a secondary means of
containment for the entire capacity of
the largest single container and
sufficient freeboard to contain
precipitation. You must ensure that
diked areas are sufficiently impervious
to contain discharged oil. Dikes,
containment curbs, and pits are
commonly employed for this purpose.
You may also use an alternative system
consisting of a drainage trench
enclosure that must be arranged so that
any discharge will terminate and be
VerDate Aug<31>2005
16:12 Dec 22, 2006
Jkt 211001
safely confined in a facility catchment
basin or holding pond.
*
*
*
*
*
(11) Position or locate mobile or
portable oil storage containers to
prevent a discharge as described in
§ 112.1(b). Except for mobile refuelers,
you must furnish a secondary means of
containment, such as a dike or
catchment basin, sufficient to contain
the capacity of the largest single
compartment or container with
sufficient freeboard to contain
precipitation.
§ 112.13
I
§ 112.14
I
[Removed and Reserved]
11. Remove and reserve § 112.14.
§ 112.15
I
[Removed and Reserved]
10. Remove and reserve § 112.13.
[Removed and Reserved]
12. Remove and reserve § 112.15.
[FR Doc. E6–21509 Filed 12–22–06; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF TRANSPORTATION
Federal Railroad Administration
49 CFR Part 209
[FRA–2006–24512]
RIN 2130–AB70
Revisions to Civil and Criminal
Penalties; Penalty Guidelines
Federal Railroad
Administration (FRA), Department of
Transportation (DOT).
ACTION: Final rule.
AGENCY:
SUMMARY: In this final rule, the Federal
Railroad Administration is revising its
regulations to reflect revisions to the
penalty provisions in the Hazardous
Materials Transportation Safety and
Security Reauthorization Act of 2005
(Title VII of the Safe, Accountable,
Flexible, Efficient Transportation Equity
Act: A Legacy for Users), enacted on
August 10, 2005. We are also revising
baseline assessments for several
categories of violations, including those
related to training and security plans, in
our Civil Penalty Assessment
Guidelines. We publish our Guidelines
in order to provide the regulated
community and the general public with
information on the hazardous materials
civil penalty assessment process for
violations related to the transportation
of hazardous materials by rail.
DATES: Effective Date: This final rule is
effective December 26, 2006.
FOR FURTHER INFORMATION CONTACT:
Roberta Stewart, Trial Attorney, Office
PO 00000
Frm 00049
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77293
of Chief Counsel, RCC–12, Mail Stop 10,
FRA, 1120 Vermont Ave., NW.,
Washington, DC 20590 (telephone 202–
493–6027).
SUPPLEMENTARY INFORMATION:
I. Civil and Criminal Penalties
On August 10, 2005, the President
signed the Safe, Accountable, Flexible,
Efficient Transportation Equity Act: A
Legacy for Users (SAFETEA–LU), Public
Law 109–59, 119 Stat. 1144. Title VII of
SAFETEA–LU—the Hazardous
Materials Transportation Safety and
Security Reauthorization Act of 2005—
revises the maximum and minimum
civil penalties, and the maximum
criminal penalty, for violations of
Federal hazardous materials
transportation law (Federal hazmat law;
49 U.S.C. 5101 et seq.) or a regulation,
order, special permit, or approval issued
under Federal hazmat law (including 49
CFR subtitle B, chapter I, subchapters A
and C). The Federal Railroad
Administration (FRA) is revising
references in our regulations to the
maximum and minimum civil penalties,
and the maximum criminal penalties, to
reflect the following statutory changes:
—The maximum civil penalty was
increased from $32,500 to $50,000 for
a knowing violation, and to $100,000
if the violation results in death,
serious illness or severe injury to any
person, or substantial destruction of
property.
—The minimum civil penalty has
reverted from $275 to $250, except
that a minimum civil penalty of $450
applies to a violation related to
training.
—Criminal penalties now apply to both
reckless and willful violations of
Federal hazardous material
transportation law or a regulation,
order, special permit, or approval
issued thereunder. The criminal
penalties also apply to a knowing
violation of the prohibition in 49
U.S.C. 5104(b) against tampering with
a marking, label, placard, or
description on a shipping document.
—The maximum criminal penalty of
five years’ imprisonment and a fine in
accordance with Title 18 of the
United States Code ($250,000 for an
individual, $500,000 for a
corporation) was retained, except that
the maximum amount of
imprisonment has been increased to
10 years in any case in which the
violation involves the release of a
hazardous material that results in
death or bodily injury to a person.
II. Revisions to Civil Penalty Guidelines
FRA’s hazardous material
transportation enforcement civil penalty
E:\FR\FM\26DER1.SGM
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Agencies
[Federal Register Volume 71, Number 247 (Tuesday, December 26, 2006)]
[Rules and Regulations]
[Pages 77266-77293]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E6-21509]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 112
[EPA-HQ-OPA-2005-0001; FRL-8258-3]
RIN 2050-AG23
Oil Pollution Prevention; Spill Prevention, Control, and
Countermeasure Plan Requirements--Amendments
AGENCY: Environmental Protection Agency.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA or the Agency) is
amending the Spill Prevention, Control, and Countermeasure (SPCC) Plan
requirements by: first, providing the option for owners and operators
of facilities that store 10,000 gallons of oil or less and meet other
qualifying criteria to self-certify their SPCC Plans in lieu of review
and certification by a Professional Engineer; second, providing an
alternative to the general secondary containment requirement without
requiring a determination of impracticability for facilities that have
particular types of oil-filled equipment; third, defining and exempting
particular vehicle fuel tanks and other on-board bulk oil storage
containers used for motive power; and fourth, exempting mobile
refuelers from the sized secondary containment requirements for bulk
storage containers. The Agency also is removing and reserving the SPCC
requirements for animal fats and vegetable oils that are specific to
onshore oil production facilities, onshore oil drilling and workover
facilities, and offshore oil drilling, production, or workover
facilities. Finally, the Agency is extending the SPCC compliance dates
for farms. These changes significantly reduce the burden imposed on the
regulated community for complying with the SPCC requirements, while
maintaining protection of human health and the environment. In a
separate document in this Federal Register, the Agency is proposing to
extend the compliance dates for all facilities.
DATES: This final rule is effective February 26, 2007.
ADDRESSES: The public docket for this final rule, Docket ID No. EPA-HQ-
OPA-2005-0001, contains the information related to this rulemaking,
including the response to comment document. All documents in the docket
are listed in the https://www.regulations.gov index. Although listed in
the index, some information may not be publicly available, e.g.,
Confidential Business Information or other information the disclosure
of which 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 EPA Docket, EPA/
DC, EPA West, Room B102, 1301 Constitution Ave., NW., Washington, DC.
The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal holidays. The telephone number of the
Public Reading Room is 202-566-1744, and the telephone number to make
an appointment to view the docket is 202-566-0276. The EPA Docket
Center suffered damage due to flooding during the last week of June
2006. The Docket Center is continuing to operate. However, during the
cleanup, there will be temporary changes to Docket Center telephone
numbers, addresses, and hours of operation for people who wish to visit
the Public Reading Room to view documents. Consult EPA's Federal
Register notice at 71 FR 38147 (July 5, 2006) or the EPA Web site at
https://www.epa.gov/epahome/dockets.htm for
[[Page 77267]]
current information on docket status, locations and telephone numbers.
FOR FURTHER INFORMATION CONTACT: For general information, contact the
Superfund, TRI, EPCRA, RMP and Oil Information Center at 800-424-9346
or TDD 800-553-7672 (hearing impaired). In the Washington, DC
metropolitan area, call 703-412-9810 or TDD 703-412-3323. For more
detailed information on specific aspects of this rule, contact Vanessa
E. Rodriguez at 202-564-7913 (rodriguez.vanessa@epa.gov), or Mark W.
Howard at 202-564-1964 (howard.markw@epa.gov), U.S. Environmental
Protection Agency, 1200 Pennsylvania Avenue, NW., Washington, DC 20460-
0002, Mail Code 5104A.
SUPPLEMENTARY INFORMATION: The contents of this preamble are:
I. General Information
II. Entities Potentially Affected by This Rule
III. Statutory Authority and Delegation of Authority
IV. Background
V. Today's Action
A. Qualified Facilities
1. Overview of the Qualified Facilities Proposal
2. Summary of This Final Rule for Qualified Facilities
3. Eligibility Criteria
a. Total Facility Oil Storage Capacity Threshold
b. Reportable Discharge History
4. Requirements for Qualified Facilities
a. Self-Certification of Plan and Plan Amendment
b. Elements of Self-Certification and Plan Amendments for Owners
and Operators of Qualified Facilities
c. Environmental Equivalence and Impracticability Determinations
B. Qualified Oil-Filled Operational Equipment
1. Oil-Filled Operational Equipment Definition
2. Oil-Filled Manufacturing Equipment
3. Eligibility Criteria
a. Reportable Discharge History
b. Consideration of Alternative Qualification Criteria
4. Requirements for Qualified Oil-Filled Operational Equipment
in Lieu of Secondary Containment
a. Contingency Plans and Written Commitment of Manpower,
Equipment and Materials
b. Inspections or Monitoring Program
c. Alternative Options Considered
5. Qualified Oil-Filled Operational Equipment and Qualified
Facilities Overlap
C. Motive Power
1. Definition of Motive Power
2. Exemption
D. Mobile Refuelers
1. Definition of Mobile Refueler
2. Amended Requirements
E. Animal Fats and Vegetable Oils
F. Extension of Compliance Dates for Farms
1. Eligibility Criteria
2. Compliance Date Extension for Farms
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
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 & Safety Risks
H. Executive Order 13211--Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Congressional Review Act
I. General Information
The Environmental Protection Agency (EPA or the Agency) is amending
the Spill Prevention, Control, and Countermeasure (SPCC) Plan
requirements of the Oil Pollution Prevention regulation at 40 CFR part
112 to streamline the regulatory requirements for owners and operators
of a subset of facilities by: (1) Providing an option to allow the
owners or operators of facilities with an oil storage capacity of
10,000 gallons or less and who meet other qualifying criteria to self-
certify their SPCC Plans in lieu of review and certification by a
Professional Engineer; (2) allowing owners and operators of facilities
that have particular types of oil-filled operational equipment to use
an oil spill contingency plan along with an inspection or monitoring
program as an alternative to secondary containment for qualified
equipment without requiring a determination of impracticability; (3)
providing an exemption for newly defined ``motive power containers'';
and (4) exempting mobile refuelers from the specifically sized
secondary containment requirements for bulk storage containers. In
addition, the Agency is removing and reserving certain SPCC
requirements for animal fats and vegetable oils; and is extending the
compliance dates for farms. The purpose of this rulemaking is to
provide streamlined, alternative approaches for compliance with oil
spill prevention requirements for these entities, and to improve net
welfare by reducing the costs of regulation and improving compliance,
resulting in greater environmental protection.
II. Entities Potentially Affected by This Rule
------------------------------------------------------------------------
Industry sector NAICS code
------------------------------------------------------------------------
Oil Production............................... 211111
Farms........................................ 111, 112
Electric Utility Plants...................... 2211
Petroleum Refining and Related Industries.... 324
Chemical Manufacturing....................... 325
Food Manufacturing........................... 311, 312
Manufacturing facilities using and storing 311, 325
animal fats and vegetable oils (AFVO).......
Metal Manufacturing.......................... 331, 332
Other Manufacturing.......................... 31-33
Real Estate Rental and Leasing............... 531-533
Retail Trade................................. 441-446, 448,
451-454
Contract Construction........................ 23
Wholesale Trade.............................. 42
Other Commercial............................. 492, 541, 551,
561-562
Transportation............................... 481-488
Arts Entertainment & Recreation.............. 711-713
Other Services (Except Public Administration) 811-813
Petroleum Bulk Stations and Terminals........ 4247
[[Page 77268]]
Education.................................... 61
Hospitals & Other Health Care................ 621, 622
Accommodation and Food Services.............. 721, 722
Fuel Oil Dealers............................. 45431
Gasoline stations............................ 4471
Information Finance and Insurance............ 51, 52
Mining....................................... 212
Warehousing and Storage...................... 493
Religious Organizations...................... 813110
Military Installations....................... 928110
Pipelines.................................... 4861, 48691
Government................................... 92
------------------------------------------------------------------------
The list of potentially affected entities in the above table 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
this table. If you have questions regarding the applicability of this
action to a particular entity, consult the person listed in the
preceding section entitled FOR FURTHER INFORMATION CONTACT.
III. Statutory Authority and Delegation of Authority
Section 311(j)(1)(C) of the Clean Water Act (CWA or the Act), 33
U.S.C. 1321(j)(1)(C), requires the President to issue regulations
establishing procedures, methods, equipment, and other requirements to
prevent discharges of oil from vessels and facilities and to contain
such discharges. The President delegated the authority to regulate non-
transportation-related onshore facilities to EPA in Executive Order
11548 (35 FR 11677, July 22, 1970), which has been replaced by
Executive Order 12777 (56 FR 54757, October 22, 1991). A Memorandum of
Understanding (MOU) between the U.S. Department of Transportation (DOT)
and EPA (36 FR 24080, November 24, 1971) established the definitions of
transportation-related and non-transportation-related facilities. A MOU
among EPA, the U.S. Department of the Interior (DOI), and DOT,
effective February 3, 1994, has re-delegated the responsibility to
regulate certain offshore facilities from DOI to EPA.
IV. Background
On July 17, 2002, EPA published a final rule amending the SPCC
rule, formally known as the Oil Pollution Prevention regulation (40 CFR
part 112), promulgated under the authority of section 311(j) of the
CWA. (The SPCC rule was originally promulgated on December 11, 1973 (38
FR 34164).) This rule included revised requirements for SPCC Plans and
for Facility Response Plans (FRPs). It also included new subparts
outlining the requirements for various classes of oil; revised the
applicability of the regulation; amended the requirements for
completing SPCC Plans; and made other modifications (67 FR 47042). The
revised rule became effective on August 16, 2002. After publication of
this rule, several members of the regulated community filed legal
challenges to certain aspects of the rule. Most of the issues raised in
the litigation have been settled, following which EPA published
clarifications in the Federal Register to several aspects of the
revised rule (69 FR 29728, May 25, 2004).\1\ In addition, concerns were
raised about the implementability of certain aspects of the 2002 rule.
---------------------------------------------------------------------------
\1\ American Petroleum Institute v. Leavitt, No. 1:102CV02247
PLF and consolidated cases (D.D.C. filed Nov. 14, 2002). The
remaining issue to be decided concerns the definition of ``navigable
waters'' in Sec. 112.2.
---------------------------------------------------------------------------
EPA has extended the dates for compliance with the 2002 rule by
extending the dates for amending and implementing revised SPCC Plans in
40 CFR 112.3(a), (b), and (c), most recently by notice dated February
17, 2006 (71 FR 8462). Please see the Federal Register notice for
further discussion on the compliance extensions. EPA took the most
recent action in order to allow time to finalize the revisions in
today's final rule and to provide the regulated community time to
review and understand the material presented in the SPCC Guidance for
Regional Inspectors, which was made available in December of 2005. The
Agency also was concerned that the effects of the September 2005
hurricanes on many industry sectors might adversely impact their
ability to meet the compliance dates if no extension was provided.
October 31, 2007 is the current deadline for amending and
implementing revised SPCC Plans for facilities (including mobile
facilities) that were in operation on or before August 16, 2002.
Facilities that came into operation after August 16, 2002 also must
prepare and implement an SPCC Plan on or before October 31, 2007. As
discussed in Section V.F of this preamble, today's final rule provides
an additional extension of the compliance date for farms. Today's rule,
which is effective February 26, 2007, does not modify the compliance
dates for owners and operators of facilities other than farms.
Elsewhere in today's Federal Register, EPA is proposing to extend the
compliance dates for owners and operators of facilities until July 1,
2009 based on further SPCC regulatory revisions that EPA is
considering, and that it expects to propose in 2007.
On September 20, 2004, EPA published two Notices of Data
Availability (NODAs). The first NODA solicited comments on submissions
to EPA that suggested more focused requirements for owners and
operators of facilities subject to the SPCC rule that handle oil below
a certain threshold amount, referred to as ``certain facilities'' (69
FR 56182). Streamlined approaches for owners and operators of
facilities with oil capacities below a certain threshold were discussed
in the NODA-related documents. The second NODA solicited comments on
whether alternate regulatory requirements would be appropriate for
owners and operators of facilities with oil-filled and process
equipment (69 FR 56184). EPA has reviewed the public comments and data
submitted in response to the NODAs in developing today's final rule.
Additionally, on December 2, 2005, EPA issued the SPCC Guidance for
Regional Inspectors. This guidance document is intended to assist
regional inspectors in reviewing implementation of the SPCC rule at a
regulated facility. The guidance document is designed to facilitate an
understanding of the rule's applicability, to help clarify the role of
[[Page 77269]]
the inspector in the review and evaluation of a facility owner or
operator's compliance with the performance-based SPCC requirements, and
to provide a consistent national policy on several SPCC-related issues.
The guidance is available to owners and operators of facilities that
may be subject to the requirements of the SPCC rule and to the general
public on the Agency's Web site at https://www.epa.gov/oilspill. This
guidance document is a living document and will be revised, as
necessary, to reflect any relevant future regulatory amendments,
including today's action.
Based on the comments received on the NODAs, as well as other
information received, EPA proposed to amend the SPCC rule to address a
number of issues raised, including those pertaining to qualified
facilities, qualified oil-filled operational equipment, motive power
containers, airport mobile refuelers, animal fats and vegetable oils,
and the compliance date for farms. (See 70 FR 73524, December 12,
2005.) EPA discusses each of these issues in Section V of this
preamble. The preamble generally discusses the comments received on the
proposal, EPA's response, and any modifications made to the proposal.
For a more detailed discussion of the comments received and EPA's
response, see ``Summary and Response to Comments,'' which is included
in the docket for today's final rule.
The scope of today's final rule was intended to address only
certain targeted areas of the SPCC requirements, and a number of issues
and concerns raised by the regulated community. As highlighted in the
EPA Regulatory Agenda and the 2005 OMB report on ``Regulatory Reform of
the U.S. Manufacturing Sector,'' EPA is considering further amendments
to address other areas where regulatory reform may be appropriate. For
these additional areas, the Agency expects to issue a proposed rule in
2007. Areas where regulatory reform may be appropriate include, and are
not limited to, oil and natural gas exploration and production, farms,
and Tier I facilities. EPA, in conjunction with DOE, has been
conducting an energy impact analysis of the SPCC requirements, and, to
the extent that the analysis is available, will consider it to inform
the Agency's 2007 rulemaking.
Because it is highly unlikely that the Agency will be able to
promulgate such regulatory amendments before the current October 31,
2007 compliance date for SPCC becomes effective, EPA believes it is
appropriate to provide an extension of the compliance date. Such an
extension has been proposed elsewhere in today's Federal Register.
The Agency is not in a position, at this time, to indicate all the
areas for possible regulatory reform that may be addressed as part of
the 2007 SPCC proposal. Nevertheless, the Agency recognizes that owners
and operators of facilities need time to determine which changes may be
made to the rules that may impact the requirements they are subject to
in order to determine when they need to comply with the new
requirements.
This approach would allow those potentially affected in the
regulated community an opportunity to make changes to their facilities
and to their SPCC Plans necessary to comply with the revised
requirements, rather than with the existing requirements. Regarding
modifications of the SPCC regulations, EPA is proposing in a separate
notice in today's Federal Register to extend the deadlines for
compliance to July 1, 2009.
V. Today's Action
A. Qualified Facilities
1. Overview of the Qualified Facilities Proposal
On December 12, 2005 (70 FR 73524), EPA proposed to amend the SPCC
rule to provide an option to allow the owner or operator of a facility
that meets the qualifying criteria (hereafter referred to as a
``qualified facility'') to self-certify the facility's SPCC Plan in
lieu of review and certification by a licensed Professional Engineer
(PE). EPA proposed to amend Sec. 112.3 to describe the SPCC
eligibility criteria that a regulated facility must meet in order to be
considered a qualified facility.
As proposed, the eligibility criteria for a qualified facility
would be a facility subject to the SPCC rule that (1) has an aggregate
oil storage capacity of 10,000 gallons or less; and (2) had no
discharges as described in Sec. 112.1(b) during the ten years prior to
self-certification. Self-certified Plans could not include
``environmentally equivalent'' alternatives to required Plan elements
as provided in Sec. 112.7(a)(2) or contingency planning in lieu of
secondary containment as provided in Sec. 112.7(d) on the basis of
``impracticability.'' However, the proposal included specified
``environmentally equivalent'' measures with respect to security and
integrity testing that would be available to facility owners and
operators that choose to self-certify. Self-certification would be
optional for owners and operators of facilities meeting the eligibility
criteria, so that those owners and operators of qualified facilities
that found the existing rules more cost-effective in achieving
compliance with the SPCC requirements, would continue to have the
option of complying with the streamlined approach or could choose to
comply with the existing SPCC requirements (including the PE
certification) to take advantage of the flexibility offered by PE-
certified impracticability determinations and environmentally
equivalent measures.
In general, the Agency agrees with the commenters who supported the
qualified facilities proposal for self-certification and believe that
this revision will relieve regulatory burden on small oil storage
facilities. As one commenter noted, self-certification should result in
greater compliance rates across the board. Therefore, today's rule
finalizes the proposed provision with a few modifications.
As described in the preamble to the proposed rule, EPA also
considered, but did not propose, a multi-tiered structure option based
on an analysis prepared for the U.S. Small Business Administration's
(SBA) Office of Advocacy that included a tiered system for facilities
that have total oil storage capacities between 1,321 and 5,000 gallons,
between 5,001 and 10,000 gallons, and greater than 10,000 gallons.
Under this option, Tier I facilities (1,321 to 5,000 gallons oil
storage capacity) would not need a written SPCC Plan (and therefore no
PE certification), but would adhere to all other SPCC requirements.
Tier II facilities (5,001 to 10,000 gallons oil storage capacity) would
be required to have a written SPCC Plan, but no PE certification
requirement. Tier III facilities (greater than 10,000 gallons oil
storage capacity) would be required to have a written SPCC Plan,
certified by a PE. A significant number of commenters on the proposed
rule supported a multi-tiered approach.
The Agency continues to believe that a facility owner or operator
cannot effectively implement an oil spill prevention program, or any
other program (business or otherwise), without documentation of that
program's action items. As a matter of practice, it would be extremely
difficult for a facility owner or operator to be able to follow the
regulatory requirements and to comply with all the recordkeeping
components without the documentation that is the Plan itself. The Plan
also serves as an important communication and training tool for both
management and oil-handling personnel at the facility. The sole action
of having to document compliance with all of the requirements can
assist in
[[Page 77270]]
uncovering flaws in the program's implementation, and may serve as a
tool to correct them. Additionally, the documentation of compliance
with the rule's requirements in a written Plan serves as a facility-
specific oil spill response and prevention planning exercise which is
designed to improve oil spill prevention. Nevertheless, the Agency
understands the concerns, particularly of owners and operators of
facilities with a smaller oil storage capacity and likely more limited
resources, of the potential effort needed to develop a complicated
Plan. Thus, the Agency has been exploring the possibility of developing
a further simplified Plan for facilities that handle between 1,320 and
5,000 gallons of oil. However, because the Agency is considering
removing or changing some of the regulatory requirements and developing
a standardized form/checklist for ease of implementation, the Agency
chose not to finalize this option without taking further comment.
Therefore, although EPA is not adopting a multi-tiered approach in
today's final rule, the Agency intends to propose a simplified approach
for facilities that handle between 1,320 and 5,000 gallons of oil
within the near future. In that proposal, the Agency expects to discuss
the implementation of the SPCC rule for these facilities.
The preamble to the proposed rule also described an approach
whereby the Agency would require owners and operators of qualified
facilities to make a one-time notification to EPA if they have been in
operation or subject to the SPCC requirements for a period less than
ten years from the time of Plan certification, and therefore could not
show a ten-year clean spill history as a qualifier. The comments
generally opposed a notification requirement, arguing that it would
impose additional burden with no clear benefit for the regulated
community. EPA is not adopting this one-time notification requirement,
because the Agency does not believe it would offer any further
environmental protection. The additional burden of a notification
requirement was not considered necessary and would be contrary to the
intent of today's rule.
2. Summary of This Final Rule for Qualified Facilities
Today's rule finalizes the proposed option with modifications to
the reportable discharge history criterion and to the self-
certification limitations for qualified facilities. The final rule also
places the alternative self-certification provisions in Sec. 112.6,
rather than in Sec. 112.3(g) as proposed. A facility owner or operator
may qualify to prepare a Plan that meets the alternative requirements
in Sec. 112.6 of today's final rule, in lieu of a Plan prepared in
accordance with the general requirements contained in Sec. 112.7 and
the applicable requirements in subparts B and C of the rule. Finally,
today's action allows a qualified facility owner or operator to use
environmentally equivalent measures or an impracticability
determination provided they are certified by a PE.
To qualify for this option, a facility must meet the following
eligibility criteria: the facility had no single discharge as described
in Sec. 112.1(b) exceeding 1,000 U.S. gallons or no two discharges as
described in Sec. 112.1(b) each exceeding 42 U.S. gallons within any
twelve month period in the three years prior to the SPCC Plan
certification date, or since becoming subject to 40 CFR part 112 if the
facility has been in operation for less than three years, and the
facility has 10,000 gallons or less in aggregate aboveground oil
storage capacity. Discharges as described in Sec. 112.1(b) that are
the result of natural disasters, acts of war, or terrorism will not
disqualify a facility owner or operator from using the self-
certification option.
An owner or operator of a qualified facility may prepare, self-
certify and implement an SPCC Plan that complies with all of the
applicable requirements of the rule in accordance with Sec. 112.6 of
today's final rule. No PE certification is required for qualified
facilities' Plans. A qualified facility owner or operator also may
choose to prepare a Plan in accordance with the general Plan
requirements in Sec. 112.7 and applicable requirements in subparts B
and C, including having the Plan certified by a Professional Engineer
as required under Sec. 112.3(d). The qualified facility approach in
today's final rule is optional; owners or operators of facilities that
qualify may choose not to exercise this option.
In proposing this option for facilities handling smaller amounts of
oil, the Agency sought to focus on those smaller operations that may be
concerned about the impact of utilizing a PE on their limited budget.
Some of the current noncompliance with the SPCC regulation may be
attributed to those concerns. The Agency believes that providing a
simpler, less costly option for owners and operators of these smaller,
less complex facilities will improve the overall compliance for the
SPCC regulation, ultimately resulting in greater environmental
protection.
3. Eligibility Criteria
a. Total Facility Oil Storage Capacity Threshold
EPA proposed to limit the maximum aggregate oil storage capacity at
a qualified facility to 10,000 gallons or less. EPA considered many
different factors before selecting this maximum storage capacity. As
explained in the preamble to the proposal (70 FR 73529), EPA has
established 10,000 gallons as a threshold in several other rules
relating to oil discharges. The National Oil and Hazardous Substances
Pollution Contingency Plan size classes define an oil discharge to
inland waters exceeding 10,000 gallons as a major discharge. An oil
discharge of 10,000 gallons or more to waters of the U.S. and adjoining
shorelines that could reasonably be expected to cause substantial harm
to the environment also is one of the factors used in identifying
facilities whose owners and operators must prepare and submit a
Facility Response Plan (see 40 CFR 112.20(f)(1)(D). A number of State
regulations also differentiate regulatory requirements based on a
facility's total storage capacity, with some States specifying a
10,000-gallon threshold (e.g., Maryland, Minnesota, Oregon, New York,
Wisconsin). Finally, 10,000 gallons is a common storage container size.
More commenters supported than opposed the proposed threshold
eligibility criterion of total oil storage capacity of 10,000 gallons
or less, while others offered alternative thresholds. Many commenters
supported the idea of establishing tiers for qualified facilities. (As
noted earlier, the Agency intends to propose a more streamlined
approach for owners and operators of facilities with a total oil
storage capacity of 5,000 gallons or less.) Many supporters believed
that the proposed 10,000-gallon threshold would reduce the financial
burden on owners and operators of small facilities. Among commenters
that opposed the threshold, at least one stated that the proposed
10,000-gallon threshold did not provide enough regulatory relief to
owners and operators of small facilities, but others noted that smaller
storage sizes do not necessarily correlate with lower spill risk.
Facilities handling smaller amounts of oil are typically simpler in
layout and operation. Most facilities with an oil storage capacity of
10,000 gallons or less are in industrial sectors that are end-consumers
of oil (i.e. farms, real estate, rental and leasing, retail trade,
construction [see the Regulatory Impact Analysis for this action, found
in the docket for today's final rule]). These
[[Page 77271]]
facilities are commonly not in an oil production or distribution
business and tend to use oil on-site for heating purposes, or to fuel
emergency power generators or heavy machinery. The configuration of the
oil-related equipment tends to be relatively standard and simple. Oil
is commonly stored in a few bulk storage containers which are often
bought off-the-shelf from a tank manufacturer or installer (e.g.,
standard UL-142 tanks) and connected with few short lengths of piping
in a standard configuration that changes relatively little from one
facility to another.
Additionally, these facilities typically do not have significant
transfers of oil because they do not further distribute the oil. A
survey conducted by EPA of oil storage facilities (1995 SPCC Survey of
Oil Storage Facilities) found that the larger the storage capacity at a
facility, the greater the likelihood of larger spills, more spills, and
more cleanup costs annually. Our regression analyses of the 1995 survey
data (see ``Analysis of the Relationship between Facility
Characteristics and Oil Spill Risk,'' found in today's docket)
confirmed similar linkages for facilities with a greater number of
tanks and larger annual throughput. These analyses were performed
because storage capacity, number of tanks, and throughput were
identified as important individual factors in explaining the total
annual spill volume, number of spills, and cleanup costs. Thus, these
factors were used together in a multivariate regression model to ensure
that these three variables continue to be statistically significant
variables when assessing whether there is potential bias (i.e., an
overstatement of the importance of the variable in explaining the
variation in the dependent variable). After performing these analyses,
storage capacity and number of tanks were found to be statistically
significant in relation to all three measures of spill risk (i.e.,
total number, volume, and cleanup costs of oil spills). The Agency
believes simple oil storage configuration, in conjunction with the
smaller quantities of oil handled at qualified facilities, makes self-
certification an appropriate alternative. Therefore, the Agency has
decided to maintain the maximum aggregate oil storage capacity for
qualified facilities at 10,000 gallons as proposed.
The development of streamlined requirements for owners and
operators of those facilities with a smaller size or storage volume is
not new; industry standards, engineering codes and practices, State
regulations, local fire codes and local ordinances often recognize the
differences between sizes and complexity of their target facilities
and/or equipment and as a result incorporate simplified requirements.
The Agency believes that today's action provides an alternative
compliance option for owners and operators of facilities handling
smaller amounts of oil that will ultimately result in increased
environmental protection by making it easier and less burdensome to
comply.
EPA recognizes that an oil discharge of less than 10,000 gallons
can be harmful (see 40 CFR part 110, where the Agency defines what
constitutes a discharge of oil in quantities that may be harmful).
Nevertheless, EPA believes that it is reasonable to allow owners and
operators of facilities with a capacity of no more than 10,000 gallons
the option to prepare and implement SPCC Plans without the involvement
of a PE (except in those cases where environmental equivalence or an
impracticability determination is requested by an owner or operator and
that the owner or operator chooses to have a PE certify part or all of
the facility SPCC Plan). Therefore, the Agency is adopting in today's
rule a threshold capacity of 10,000 gallons as a criterion for those
facilities that are qualified for self-certification.
Some commenters argued that the 10,000-gallon threshold would still
preclude owners and operators of smaller facilities from taking
advantage of the self-certification alternative. For example, a
facility with two 5,000-gallon storage containers and a few totes just
exceeds the 10,000-gallon threshold. Commenters argued that these kinds
of facilities have low volumes of oil and simple operations, and that
perhaps a slightly higher threshold would be more appropriate. The
Agency recognizes that regardless of the threshold quantity selected,
there are likely to be facilities just above that threshold that will
be excluded. To the extent that facility owners or operators want to
take advantage of the streamlined approach, they always have the option
of reducing the storage capacity of oil at their facility by either
removing containers from the facility inventory, or permanently closing
containers in accordance with Sec. 112.2.
Other commenters suggested higher threshold quantities, generally
based upon the quantities of oil used or stored in their particular
industry sector. EPA does not agree that this provides a rational basis
for raising the threshold limit for qualified facilities. Higher
thresholds would potentially allow owners and operators of facilities
(in some cases unmanned) with more complex operations or more complex
oil system configurations, designs and layouts, and with the potential
for an increased number of transfers, the option of foregoing the
services of a PE. Thus, self-certification for owners and operators of
more complex facilities would not be commensurate with their potential
spill risks.
By limiting the self-certification option to owners and operators
of facilities with a maximum aggregate oil storage capacity of 10,000
gallons, the Agency believes that an owner or operator of a qualified
facility should be able to self-certify compliance the facility's SPCC
Plan, and that offering this simpler and streamlined alternative will
result in greater environmental protection by improving compliance with
the SPCC rule. Owners and operators of facilities handling smaller
amounts of oil would still be required to comply with the SPCC
requirements and to prevent and prepare to respond to oil discharges to
navigable waters and adjoining shorelines, but they would be able to do
so in a less costly manner. We believe this alternative certification
provision will prove to be an incentive for compliance.
b. Reportable Discharge History
Clean Water Act section 311(b)(3) prohibits ``the discharge of oil
* * * into or upon the navigable waters of the United States, the
adjoining shorelines, or into or upon the waters of the contiguous
zone'' or in connection with specified activities in waters ``in such
quantities as may be harmful * * *.'' Section 311(b)(4) requires
regulations to define the quantities of oil, ``the discharge of which
may be harmful to the public health or welfare or the environment of
the United States, * * *.'' 33 U.S.C. 1321(b)(3), (4). In part 110, EPA
defines a ``discharge of oil in such quantities that may be harmful''
as a discharge of oil that violates applicable water quality standards;
a discharge of oil that causes a film or sheen upon the surface of the
water or on adjoining shorelines; or a discharge of oil that causes a
sludge or emulsion to be deposited beneath the surface of the water or
adjoining shorelines (40 CFR 110.3). The Agency refers to such
discharges as reportable discharges or as ``a discharge as described in
Sec. 112.1(b)'' of the rule. Any person in charge of a facility must
report any such discharge of oil to waters of the United States,
adjoining shorelines, the contiguous zone or in connection with
specified activities in waters from the facility to the National
Response Center (NRC) at 1-800-424-8802 immediately. While EPA
recognizes that past discharge
[[Page 77272]]
history does not necessarily translate into a predictor of future
performance, the Agency believes that discharge history is a reasonable
indicator of a facility owner or operator's ability to develop an SPCC
Plan for his smaller oil storage capacity facility without the
involvement of a PE.
EPA proposed that a qualified facility subject to the SPCC
requirements must have no reportable oil discharges as described in
Sec. 112.1(b) during the ten years prior to self-certification or
since becoming subject to the SPCC requirements, whichever time period
is less. The Agency proposed using a facility's reportable discharge
history as a reasonable indicator of the effective implementation of an
SPCC Plan based on an established record of good oil spill prevention.
The reportable discharge history criterion was intended to limit the
option of self-certification to owners and operators of those
facilities that had demonstrated an effective implementation of spill
prevention measures in the past.
The commenters who supported the proposed reportable discharge
requirement agree that it is important for a facility to have a clean
spill history. However, a significant number of commenters argued
against the proposed reportable discharge history criterion as an
appropriate criterion, and that the small storage capacity alone should
be sufficient to allow self-certification. One reason is that some
reportable discharges are not the facility owner or operator's fault,
but caused by outside sources. For example, a number of commenters
pointed to the recent hurricanes in the Gulf Coast states that led to
oil discharges that were not within the control of the facility owner
or operator. A further reason is that facilities that have a clean
discharge history might not always remain spill-free. As for the
proposed ten-year period, one commenter stated that facility owners and
operators are only required to keep records for SPCC Plans for three
years; most owners and operators keep them for five years. Another
commenter stated that a discharge history of ten years would almost be
impossible to prove. Another commenter believed that the qualification
for a qualified facility should not be based on the ten-year discharge
history, but should be based on the discharge history under the current
operator. A few commenters believed that risk of discharge should
determine self-certification. Additionally, many commenters recommended
alternative discharge history timeframes in place of the ten-year
timeframe EPA proposed. Half of the commenters believed that three
years should be the time frame for the reportable discharge history
since the SPCC record-keeping requirement for facility owners and
operators is three years. Two commenters mentioned that if a discharge
occurs and the Regional Administrator (RA) responds, and after review
of the SPCC Plan the RA does not require an amendment in the Plan, then
the discharge should not count against the facility owner or operator
when determining its compliance with a spill-history criterion.
After consideration of the comments received, EPA is finalizing the
reportable discharge criterion for qualified facilities but for three
years, rather than ten years. The Agency agrees with commenters that a
ten-year spill history is unreasonable, particularly since the facility
owner or operator is only required to keep records for three years. In
addition, EPA is modifying the types of discharges that must be
considered for this criterion. The final rule provides that for the
three years prior to the SPCC Plan certification date, or since
becoming subject to 40 CFR part 112 if the facility has been in
operation for less than three years, the owner or operator of a
facility must certify that the facility has (1) had no single discharge
as described in Sec. 112.1(b) exceeding 1,000 U.S. gallons or (2) had
no two discharges as described in Sec. 112.1(b) each exceeding 42 U.S.
gallons within any twelve month period. When determining spill history,
the gallon amount specified in the criterion (either 1,000 or 42)
refers to the amount of oil that actually reaches waters of the United
States, adjoining shorelines, the contiguous zone or in connection with
specified activities in waters and not the total amount of oil spilled.
For example, a facility only experiencing one discharge over the past
ten years in which 1,500 gallons of oil discharged onto the ground but
only 20 gallons reached waters of the United States (causing a sheen
and reportable to the NRC) would meet the reportable discharge history
criterion. However, a facility having 1,500 gallon discharge to waters
of the United States would not meet the reportable discharge history
criterion.
In the preamble to the proposed rule, EPA requested comment on how
extreme events such as natural disasters, acts of war or terrorism,
sabotage or other calamities might potentially affect the discharge
history criterion for qualified facilities. Many commenters stated that
it would not be appropriate to include these events in the discharge
history criterion. The Agency agrees that those reportable discharges
caused by external factors beyond the control of the facility owner or
operator such as natural disasters, acts of war, or terrorism should
not disqualify owners and operators of otherwise qualified facilities
from taking advantage of the self-certification option. Therefore, we
have excluded those events from consideration in the reportable
discharge criterion in today's final rule. The Agency did not include
sabotage/vandalism in the final list of reportable discharge history
extreme events because these are not necessarily beyond the control or
planning ability of the facility owner or operator. Only those
discharges as described in Sec. 112.1(b) that are the result of
natural disasters, acts of war, or terrorism will not disqualify any
owner or operator of an otherwise qualified facility from using the
self-certification option.
The discharge criterion finalized in today's rule is similar to the
provision in Sec. 112.4(a) for discharges that must be reported to the
EPA Regional Administrator (RA). A discharge that must be reported to
the RA pursuant to Sec. 112.4(a) may result from improper Plan
implementation, rather than from a deficiency in the Plan itself, which
would likely not cause the RA to require the facility owner or operator
to amend its Plan. Therefore, the EPA does not agree with the
commenters that suggested excluding those discharges as described in
Sec. 112.1(b) from the eligibility criterion that have been
investigated by the RA with no subsequent requirement for a Plan
amendment.
The determination of eligibility based on reportable discharge
history is made at the time the SPCC Plan is certified--i.e., when the
SPCC Plan is amended to comply with the SPCC rule revisions in today's
final rule and those promulgated in July 2002. Once the compliance date
extension ends, Plans must be amended, certified and implemented. Any
discharges to navigable waters and adjoining shorelines that occur from
a qualified facility after the SPCC Plan has been certified do not
impact the eligibility of an owner or operator of the qualified
facility to take advantage of the self-certification option. The
facility does not lose eligibility status as a result of a discharge as
described in Sec. 112.1(b), unless the RA requires an amendment to the
SPCC Plan in accordance with Sec. 112.4(d) and specifically requires
PE-certification. If an owner or operator cannot certify that the
facility meets the eligibility criterion at the initial date of Plan
certification, but can later demonstrate a clean spill history of three
years, as well as compliance with any remedial actions required by the
RA
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following a spill, then a technical amendment to the Plan can be self-
certified and the Plan can be revised to allow for qualified status.
4. Requirements for Qualified Facilities
In today's rule, the Agency is creating a new section, Sec. 112.6,
with requirements specific for qualified facilities whose owners and
operators choose to self-certify their Plans. Owners and operators of
qualified facilities with an aggregate aboveground oil storage capacity
of 10,000 gallons of oil or less may choose to comply with the
requirements in Sec. 112.6 by completing and implementing a self-
certified SPCC Plan. A qualified facility's Plan, whether certified by
a PE or self-certified, must comply with all of the applicable
requirements of Sec. 112.7 and subparts B and C of the rule. We note,
however, that a facility's SPCC Plan does not need to conform to any
particular format. There is flexibility with respect to how a facility
owner or operator chooses to maintain the documentation comprising the
facility's Plan, just as there is flexibility with respect to how the
owner or operator chooses to carry out the elements of the Plan.
a. Self-Certification of Plan and Plan Amendment
The commenters who supported self-certification for owners and
operators of qualified facilities believed that it would relieve burden
on the owners and operators. The commenters who opposed self-
certification did so for four main reasons. First, some commenters
believe that the preparation of the SPCC Plan requires scientific,
engineering, and professional judgment skills that are unique to
engineers. Second, some commenters believe owners and operators of
small facilities often cannot afford the cost of responding to a spill,
and it is important that the SPCC Plan is prepared carefully and
thoroughly by a PE. Third, some commenters believe that not having a PE
involved would adversely affect public health, safety, and welfare.
Fourth, some commenters believe that the proposal would allow non-
engineers to perform a function that is only allowed by engineers under
the National Council of Examiners for Engineering and Surveying, a
Model Law adopted by the majority of States.
The self-certification option is designed for owners and operators
of those facilities that store smaller amounts of oil. These smaller
amounts of oil generally translate to facilities with simpler, pre-
engineered installations, such as restaurants, office buildings, family
farms, automotive repair shops, and rural electrical substations. EPA
believes that a differentiated option for users of smaller amounts of
oil has merit as other official bodies, such as standards setting
organizations have provided differentiations in their standards for
smaller users of oil. For example, the National Fire Protection
Association (NFPA) provides differentiated requirements based on type
of facility and size of tanks. Specifically, NFPA 30 (Flammable and
Combustible Liquids Code, 2000 Edition) applies to tanks that exceed
3,000 liters (793 gallons) and does not apply to facilities storing
flammable and combustible liquids as covered by NFPA 395, Standard for
the Storage of Flammable and Combustible Liquids at Farms and Isolated
Sites. The Agency believes that the relative simplicity of operations
at facilities using smaller amounts of oil has served as a basis for
other official bodies to develop requirements that are simpler in
scope.
To this end, the Agency is amending the certification language so
that it clearly states that the owner or operator of the facility is
the certifying official for those who choose the option to self-certify
the Plan for qualified facilities. The Agency also intends to develop
materials to assist these owners or operators in developing SPCC Plans.
It should also be remembered that while owners and operators of these
facilities may choose not to have their SPCC Plans certified by a PE,
they will still be required to comply with all of the SPCC requirements
and to develop and implement a spill prevention program in accordance
with good engineering practices, and they may do so by following
regulatory guidance, industry recommended practices and standard design
and operation protocols. Finally, to the extent that a State has
adopted a law, such as one based on the National Council of Examiners
for Engineering and Surveying, that requires that a PE to perform
certain functions, including certifying Plans, nothing in today's rule
affects whether a facility owner or operator would be required to
utilize a PE to meet the state or local requirements since today's rule
does not pre-empt any State or local requirements.
The Agency believes providing the added flexibility of self-
certification for the smaller oil handlers/simpler operations will
yield an increase in overall compliance for this segment of the
regulated community, which will result in improved compliance with the
rule and as a result, improve overall spill prevention and
environmental protection. However, owners or operators of some
qualified facilities with complicated operations may nonetheless find
that having a PE-certified Plan offers a more cost-effective method of
achieving compliance than the proposed option. Therefore, a qualified
facility owner or operator could choose to follow the existing SPCC
requirements (including the PE certification).
The Agency also proposed and is finalizing today that an owner or
operator of a qualified facility may self-certify technical amendments
to the Plan, including modification of site diagrams, and that owners
and operators of facilities with PE-certified Plans that qualify for
self-certification can choose to self-certify future technical
amendments rather than hire a PE to certify the technical amendment.
Owners and operators of facilities that are not eligible to self-
certify are required to have a PE certify such modifications. In all
cases, any technical amendment in an SPCC Plan must be certified in
writing. As described in the preamble to the proposed rule, the Agency
notes that under the existing SPCC regulations, the RA, after reviewing
the facility's Plan, has the authority in Sec. 112.4 to require an
owner or operator of a facility that has had a discharge as described
in Sec. 112.1(b) or that poses an imminent danger of a discharge as
described in Sec. 112.1(b), to amend its SPCC Plan, including
requiring PE certification in accordance with Sec. 112.3(d).
b. Elements of Self-Certification and Plan Amendments for Owners and
Operators of Qualified Facilities
The finalized requirements for owners and operators of qualified
facilities are similar to those in the proposed qualified facilities
option in the proposed rule. An owner or operator of a qualified
facility may choose to comply with the requirements in Sec. 112.6 by
completing and implementing a self-certified SPCC Plan in lieu of
having a PE certified Plan. The SPCC Plan must comply with all of the
applicable requirements of Sec. 112.7 and subparts B and C of the
rule.
Owners and operators that choose to self-certify their Plans must
certify that they are familiar with the requirements of the SPCC rule;
they have visited and examined the facility; the Plan has been prepared
in accordance with accepted and sound industry practices and standards;
procedures for required inspections and testing have been established;
the Plan is being fully implemented; the facility meets the
qualification criteria set forth under Sec. 112.3(g); the Plan does
not include any
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environmental equivalence measures as described in Sec. 112.7(a)(2) or
determinations of impracticability under Sec. 112.7(d) unless each
alternative method and/or determination has been reviewed and certified
by a PE in accordance with Sec. 112.6(d); and the Plan and the
individual(s) responsible for implementing the Plan have the full
approval of management and the facility owner or operator has committed
the necessary resources to fully implement the Plan.
The qualified facility self-certification approach is optional.
Under today's final rule, an owner or operator of a qualified facility
may choose to prepare and implement a PE-certified SPCC Plan to comply
with the requirements under 40 CFR part 112.
c. Environmental Equivalence and Impracticability Determinations
Under Sec. 112.7, all facility owners and operators have the
flexibility to deviate from specific rule provisions if the Plan states
the reason for nonconformance and if equivalent environmental
protection is provided by some other means of spill prevention,
control, or countermeasure. These ``environmentally equivalent''
measures must be described in the SPCC Plan, including how the
equivalent environmental protection will be achieved based on good
engineering practice. Allowance for ``environmentally equivalent'''
deviations is provided in Sec. 112.7(a)(2), and the deviations are
available only for the specific requirements listed in Sec.
112.7(a)(2), such as fencing and other security measures, evaluation of
the potential for catastrophic tank failure due to brittle fracture,
integrity testing, and overfill prevention. Environmental equivalence
is not available for secondary containment or the administrative or
recordkeeping requirements of the SPCC rule. As part of the SPCC Plan,
any environmentally equivalent measures are required to be certified by
a PE and the owner or operator, and the PE is required to consider
industry standards in the development of the Plan. Thus, when a PE
certifies a Plan that includes any environmentally equivalent
protection measure, the PE is certifying that these alternative
measures are consistent with relevant industry standards.
The SPCC rule also provides flexibility for owners or operators who
determine that the general secondary containment requirements in Sec.
112.7(c) or any of the applicable additional requirements for secondary
containment in subparts B and C are impracticable. Where
impracticability is demonstrated, Sec. 112.7(d) allows facility owners
and operators the flexibility to instead develop a contingency plan and
comply with additional requirements. The SPCC Plan must explain why
secondary containment measures are not practicable. Section 112.7(d)
requires that, when containment for bulk storage containers is deemed
impracticable, the owner or operator must conduct both periodic
integrity testing of the containers and periodic integrity and leak
testing of the valves and piping. The owner or operator also must
provide an oil spill contingency plan that follows the provisions of 40
CFR part 109 (Criteria for State, Local and Regional Oil Removal
Contingency Plans), and a written commitment of manpower, equipment,
and materials required to expeditiously control and remove any quantity
of oil discharged that may be harmful as described in 40 CFR part 110.
A PE must certify any determinations that secondary containment is
impracticable, as well as the additional measures implemented in lieu
of secondary containment.
Because of the expertise that a PE has in evaluating whether
particular measures provide equivalent environmental protection and in
knowing how to effectively implement such measures, EPA believes that
the flexibility in these performance-based provisions is best suited to
SPCC Plans that are reviewed and certified by a PE. The same expertise
is necessary in determining whether the required secondary containment
is impracticable.
EPA proposed that when a Plan is self-certified, the owner or
operator would not be able to use environmentally equivalent measures
or to make impracticability determinations with respect to secondary
containment. Instead, EPA proposed specific alternative measures for
compliance with security and integrity testing requirements at
qualified facilities that self-certify. The commenters who supported
this approach indicated that it added a safety factor into the self-
certification. Most commenters opposed this approach because
impracticability determinations and environmental equivalence were
originally created to relieve burden, and owners and operators of small
facilities still need the flexibility these mechanisms provide. Some
commenters believed that the agricultural industry would be negatively
affected because the environmental equivalence and impracticability
provisions are an important element to reduce the burden on owners and
operators of these facilities due to topography and operations. As for
the proposed specific alternative to environmentally equivalent
measures for security, one commenter supported this proposal.
With respect to integrity testing, the Agency proposed to allow
self-certifying owners and operators of qualified facilities to perform
integrity testing by relying on industry standards for the integrity
testing requirements as an alternative to the existing bulk storage
containing integrity testing requirements. All but one commenter
supported the proposal. One commenter supported it, but also wanted
visual inspection of individual shop-fabricated tanks up to 10,000
gallons. Another commenter agreed, but believed that the expense of the
Steel Tank Institute's (STI) Tank Inspection Standard, SP001 (July
2005), was high and the STI standard and accompanying checklists are
not applicable to small facilities. A hybrid approach also was
suggested whereby owners and operators of qualified facilities would be
allowed to use the self-certification option, and, in the event that an
environmental equivalency or impracticability determination is needed,
the owner or operator must consult a PE for just that aspect of their
program, rather than requiring a full PE review and approval of the
entire Plan.
The Agency continues to believe that the flexibility afforded by
the environmental equivalence or impracticability determinations should
be available only to owners and operators of facilities having those
elements reviewed and certified by a PE. At the same time, the Agency
recognizes that by restricting these options for owners and operators
of qualified facilities, the alternative of self-certification may not
be as attractive for some owners or operators because they will lose
the added flexibility of further tailoring the SPCC requirements to
their facility's characteristics. The Agency agrees with commenters
that under the proposed rule, there would likely be certain
circumstances where, because of cost considerations, a facility owner
or operator would not choose to self-certify because it would be more
cost effective for a PE to prepare an SPCC Plan that utilizes
environmentally equivalent measures or impracticability determinations.
In today's final rule, the Agency therefore is adopting a hybrid
approach. This approach finalizes the alternatives for addressing
security measures and integrity testing and also allows owners or
operators of self-certified facilities to include environmentally
equivalent measures with respect to requirements other than facility
security and integrity testing, as well as to make
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impracticability determinations, provided they have a PE certify these
environmentally equivalent measures or impracticability determinations.
Because qualified facilities typically have less complex operations and
petroleum system configurations and storage capacities than other
facilities subject to SPCC requirements, EPA believes that the
alternative requirements for facility security and bulk storage
container integrity testing finalized today are appropriate for self-
certification. However, today's rule does not preclude a qualified
facility from choosing to have a PE certify the integrity testing and/
or security measures in the facility's Plan as environmentally
equivalent measures. For example, where there are no industry standards
to guide integrity testing at a qualified facility, the alternative
integrity testing option in Sec. 112.6(c)(4)(ii) is not available.
However, the facility owner/operator is allowed to have a PE certify an
integrity testing protocol in the Plan that is environmentally
equivalent to the applicable requirements in subpart B or C. The Agency
believes that this ``hybrid'' approach will further expand the
flexibility offered by the self-certification compliance option to
owners and operators of qualified facilities without compromising
proper environmental protection.
Similarly, EPA is adopting a hybrid approach to certification of
technical amendments to a qualified facility's SPCC Plan in Sec.
112.5. PE-certified sections of a qualified facility's ``hybrid'' SPCC
Plan require PE certification of any technical amendments to that
portion of the Plan. Technical amendments to the non-PE certified
sections of a qualified facility's ``hybrid'' Plan can be certified by
the owner or operator.
B. Qualified Oil-Filled Operation