Revising Underground Storage Tank Regulations-Revisions to Existing Requirements and New Requirements for Secondary Containment and Operator Training, 71708-71796 [2011-29293]
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Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 280 and 281
[EPA–HQ–UST–2011–0301; FRL–9485–5]
RIN 2050–AG46
Revising Underground Storage Tank
Regulations—Revisions to Existing
Requirements and New Requirements
for Secondary Containment and
Operator Training
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
EPA is proposing to make
certain revisions to the 1988
underground storage tank (UST)
technical, financial responsibility, and
state program approval regulations.
These changes establish federal
requirements that are similar to key
portions of the Energy Policy Act of
2005; they also update certain 1988 UST
regulations. Proposed changes include:
Adding secondary containment
requirements for new and replaced
tanks and piping; adding operator
training requirements; adding periodic
operation and maintenance
requirements for UST systems;
removing certain deferrals; adding new
release prevention and detection
technologies; updating codes of
practice; making editorial and technical
corrections; and updating state program
approval requirements to incorporate
these new changes. These changes will
likely protect human health and the
environment by increasing the number
of prevented UST releases and quickly
detecting them, if they occur.
DATES: Comments must be received on
or before February 16, 2012. Under the
Paperwork Reduction Act, comments on
the information collection provisions
are best assured of having full effect if
the Office of Management and Budget
(OMB) receives a copy of your
comments on or before December 19,
2011.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
UST–2011–0301, by one of the
following methods:
• https://www.regulations.gov; Follow
the online instructions for submitting
comments.
• Email:
mcdermott.elizabeth@epa.gov.
• Mail: EPA Docket Center (EPA/DC),
Docket ID No. EPA–HQ–UST–2011–
0301, Mail Code 2822T, 1200
Pennsylvania Ave. NW., Washington,
DC 20460. In addition, please mail a
copy of your comments on the
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SUMMARY:
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information collection provisions to the
Office of Information and Regulatory
Affairs, Office of Management and
Budget (OMB), Attn: Desk Officer for
EPA, 725 17th St. NW., Washington, DC
20503.
• Hand Delivery: EPA Docket Center
(EPA/DC), EPA West, Room 3334, 1301
Constitution Ave. NW., Washington, DC
20460. Attention Docket ID No. EPA–
HQ–UST–2011–0301. Such deliveries
are only accepted during the Docket’s
normal hours of operation, and special
arrangements should be made for
deliveries of boxed information.
Instructions: Direct your comments to
Docket ID No. EPA–HQ–UST–2011–
0301. EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or email. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an email comment directly
to EPA without going through https://
www.regulations.gov your email address
will be automatically captured and
included as part of the comment that is
placed in the public docket and made
available on the Internet. If you submit
an electronic comment, EPA
recommends that you include your
name and other contact information in
the body of your comment and with any
disk or CD–ROM you submit. If EPA
cannot read your comment due to
technical difficulties and cannot contact
you for clarification, EPA may not be
able to consider your comment.
Electronic files should avoid the use of
special characters, any form of
encryption, and be free of any defects or
viruses. For additional information
about EPA’s public docket, visit the EPA
Docket Center homepage at https://
www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket
are listed in the https://
www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
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materials are available either
electronically in https://
www.regulations.gov or in hard copy at
the Docket, EPA/DC, EPA West, Room
3334, 1301 Constitution Ave. NW.,
Washington, DC. The Public Reading
Room is open from 8:30 a.m. to
4:30 p.m., Monday through Friday,
excluding legal holidays. The telephone
number for the Public Reading Room is
(202) 566–1744, and the telephone
number for the EPA Docket Center
(EPA/DC) is (202) 566–0276.
FOR FURTHER INFORMATION CONTACT:
Elizabeth McDermott, OSWER/OUST
(5401P), Environmental Protection
Agency, 1200 Pennsylvania Avenue
NW., Washington, DC 20460; telephone
number: (703) 603–7175; email address:
mcdermott.elizabeth@epa.gov.
Table of Contents
I. General Information
Does this action apply to me?
What should I consider as I prepare my
comments for EPA?
II. Authority
III. Background
Why is EPA changing the UST regulations?
What is the history of the UST laws and
regulations?
What is the impact of this proposal?
What was EPA’s process in deciding which
changes to incorporate in the
regulations?
IV. Proposed Revisions to the Requirements
for Owners and Operators of
Underground Storage Tanks
A. Changes To Establish Federal
Requirements for Operator Training and
Secondary Containment
1. Operator Training
2. Secondary Containment
B. Additional Requirements for Operation
and Maintenance
1. Walkthrough Inspections
2. Spill Prevention Equipment Tests
3. Overfill Prevention Equipment Tests
4. Secondary Containment Tests
5. Operation and Maintenance
Requirements for Release Detection
Equipment
C. Addressing Deferrals
1. Emergency Power Generator UST
Systems
2. Airport Hydrant Fuel Distribution
Systems
3. UST Systems With Field-Constructed
Tanks
4. Wastewater Treatment Tank Systems
5. Maintain Deferral for USTs Containing
Radioactive Material and Emergency
Generator UST Systems at Nuclear
Power Generation Facilities Regulated by
the Nuclear Regulatory Commission
D. Other Changes
1. Changes to Overfill Prevention
Equipment Requirements
2. Internal Linings That Fail the Periodic
Lining Inspection and Cannot Be
Repaired
3. Notification Requirements
4. Alternative Fuels and Compatibility
5. Improving Repairs
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6. Phase Out Vapor Monitoring and
Groundwater Monitoring as Release
Detection Methods
7. Interstitial Monitoring Results, Including
Interstitial Alarms, Under Subpart E
E. General Updates
1. Incorporate Newer Technologies
2. Updates to Codes of Practice Listed in
the UST Regulation
3. Updates To Remove Old Upgrade and
Implementation Deadlines
4. Editorial and Technical Corrections
F. Alternative Options EPA Considered
V. Updates to State Program Approval
Requirements
VI. Overview of Estimated Costs and Benefits
VII. Statutory and Executive Orders
A. Executive Order 12866: Regulatory
Planning and Overview and Executive
Order 13563: Improving Regulation and
Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low-Income
Populations
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I. General Information
Does this action apply to me?
In the table below, EPA is providing
a list of potentially affected entities.
However, this proposed action may
affect other entities not listed below.
The Agency’s goal with this section is
to provide a guide for readers to
consider regarding entities that
potentially could be affected by this
action. If you have questions regarding
the applicability of this action to a
particular entity, consult the person
listed in the preceding section titled FOR
FURTHER INFORMATION CONTACT.
SUPPLEMENTARY INFORMATION:
INDUSTRY SECTORS POTENTIALLY AFFECTED BY THE PROPOSED RULE
Industry sector
NAICS code
Retail Motor Fuel Sales .............................................................................................................................................
Commercial (wholesale trade, retail trade, accommodation, and food services) ......................................................
Institutional (hospitals only) ........................................................................................................................................
Manufacturing .............................................................................................................................................................
Transportation (air, water, truck, transit, pipeline, and airport operations) ................................................................
Communications and Utilities (wired telecommunications carriers; and electric power generation, transmission,
and distribution).
Agriculture (crop and animal production) ...................................................................................................................
447.
42, 44–45, 72 (excluding 447).
622.
31–33.
481, 483–486, 48811.
5171, 2211.
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What should I consider as I prepare my
comments for EPA?
1. Submitting CBI. Do not submit this
information to EPA through https://
www.regulations.gov or email. Clearly
mark the part or all of the information
that you claim to be CBI. For CBI
information on a disk or CD–ROM that
you mail to EPA, mark the outside of the
disk or CD–ROM as CBI and then
identify electronically within the disk or
CD–ROM the specific information that
is claimed as CBI. In addition to one
complete version of the comment that
includes information claimed as CBI, a
copy of the comment that does not
contain the information claimed as CBI
must be submitted for inclusion in the
public docket. Information so marked
will not be disclosed except in
accordance with procedures set forth in
40 CFR part 2.
2. Tips for Preparing Your Comments.
When submitting comments, remember
to:
• Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
• Explain why you agree or disagree,
suggest alternatives, and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
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• If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
• Provide specific examples to
illustrate your concerns and suggest
alternatives.
• Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
• Make sure to submit your
comments by the comment period
deadline identified.
II. Authority
EPA is proposing these regulations
under the authority of sections 2002,
9001, 9002, 9003, 9004, 9005, 9006,
9007, and 9009 of the Solid Waste
Disposal Act of 1970, as amended by the
Resource Conservation and Recovery
Act of 1976, as amended [42 U.S.C.
6912, 6991, 6991(a), 6991(b), 6991(c),
6991(d), 6991(e), 6991(f), 6991(h),
6991(i), and 6991(k)].
III. Background
EPA is proposing certain changes to
the 1988 underground storage tank
(UST) regulations in 40 CFR part 280. In
addition, EPA is planning to implement
the delivery prohibition provision of the
Energy Policy Act of 2005 (hereafter
called Energy Policy Act) for EPA-led
inspections, but will address that
independent of today’s proposal.
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111, 112.
Finally, EPA is proposing to revise its
state program approval (SPA)
requirements in 40 CFR part 281 to
incorporate the changes in 40 CFR part
280. While EPA’s proposed changes to
the 1988 UST regulations will improve
environmental protection, we are
sensitive to future costs for UST owners
and operators and, as a result,
minimized required retrofits.
This proposal strengthens the 1988
UST regulation by increasing the
emphasis on properly operating and
maintaining equipment. The 1988 UST
regulation required owners and
operators have spill, overfill, and release
detection equipment in place, but did
not require proper operation and
maintenance for some of that
equipment. For example, EPA required
spill prevention equipment to capture
drips and spills when the delivery hose
is disconnected from the fill pipe but
did not require periodic testing of that
equipment. Today’s proposed revisions
will require that UST equipment is
operated and maintained properly,
which will improve environmental
protection. These changes also
acknowledge improvements in
technology over the last 20 years,
including the ability to detect releases
from deferred UST systems.
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Why is EPA changing the UST
regulations?
EPA is proposing to revise the 1988
UST regulations to:
• Establish federal requirements that
are similar to certain key provisions of
the Energy Policy Act;
• Ensure owners and operators
properly operate and maintain their
UST systems;
• Include updates to current
technology and codes of practices;
• Make technical and editorial
corrections; and
• Update SPA regulation to address
the proposed changes listed above.
In 1988, EPA first promulgated the
UST regulations (40 CFR part 280) to
prevent, detect, and clean up petroleum
releases into the environment. The 1988
UST regulations required new UST
systems to be designed, constructed,
and installed to prevent releases;
existing UST systems had to be
upgraded to prevent releases. In
addition, owners and operators were
required to perform release detection,
demonstrate financial responsibility,
and clean up releases.
The Energy Policy Act amended
Subtitle I of the Solid Waste Disposal
Act (SWDA), the statute that authorized
the UST program. Key Energy Policy
Act provisions (such as secondary
containment and operator training)
apply to all states receiving federal
Subtitle I money under SWDA,
regardless of their state program
approval status, but do not apply in
Indian country (or in states and U.S.
territories that do not meet EPA’s
operator training or secondary
containment grant guidelines). The U.S.
has a unique legal relationship with
federally recognized Indian Tribes. This
government to government relationship
includes recognizing the rights of Tribes
as sovereign governments to selfdetermination and acknowledging the
federal government’s trust responsibility
to Tribes. As a result, EPA directly
implements the UST program in Indian
country.
In order to establish federal UST
requirements that are similar to the UST
secondary containment and operator
training requirements of the Energy
Policy Act, EPA decided to revise the
1988 UST regulations. EPA also decided
to revise the 1988 UST regulations in
order to achieve better release
prevention and compliance results (see
section IV.B. Additional Requirements
for Operation and Maintenance for
additional information). Today’s
proposed revisions also fulfill objectives
in EPA’s UST Tribal Strategy (August
2006), where both EPA and Tribes
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recognized the importance of
requirements that ensure parity in
program implementation among states
and in Indian country. Requiring
secondary containment will reduce
releases to the environment by
containing them within a secondary
area and detecting them before they
reach the environment. Operator
training will educate UST system
operators and help them prevent
releases by complying with the
regulation and performing better
operation and maintenance of their UST
systems.
Since the beginning of the UST
program, preventing petroleum and
hazardous substance releases from UST
systems into the environment has been
one of the primary goals of the program.
Although EPA and our partners have
made significant progress in reducing
the number of new releases,
approximately 7,000 releases are
discovered each year as of FY 2009.1
Lack of proper operation and
maintenance of UST systems is a main
cause of new releases. Information on
sources and causes of releases shows
that releases from tanks are less
common than they once were. However,
releases from piping and spills and
overfills associated with deliveries have
emerged as more common problems. In
addition, releases at the dispenser are
one of the leading sources of releases.
Finally, data show that release detection
equipment is only detecting
approximately 50 percent of releases it
is designed to detect. These problems
are partly due to improper operation
and maintenance (see section IV.B.
Additional Requirements for Operation
and Maintenance for a more detailed
discussion of problems).2 3
EPA relies on two draft causes of
release studies to help support this
proposed rule. Petroleum Releases at
Underground Storage Tank Facilities in
Florida contains release data on 512
releases from new and upgraded tanks
in Florida.4 The second draft study,
Evaluation of Releases from New and
Upgraded Underground Storage Tank
Systems, contains release data on 580
releases from new and upgraded tanks
in 23 states across the Northeast, South,
1 Semi-Annual Report Of UST Performance
Measures, End Of Fiscal Year 2009, https://epa.gov/
oust/cat/camarchv.htm.
2 Petroleum Releases At Underground Storage
Tank Facilities In Florida, Peer Review Draft, U.S.
EPA/OUST, March 2005.
3 Evaluation Of Releases From New And
Upgraded Underground Storage Tanks, Peer Review
Draft, U.S. EPA/OUST, August 2004.
4 Petroleum Releases At Underground Storage
Tank Facilities In Florida, Peer Review Draft, U.S.
EPA/OUST, March 2005.
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and Central parts of the United States.5
Taken together, these draft studies
provide information about 1092 releases
in 24 of the 50 states. The data in the
two studies, when taken as a whole,
generally provide a representative
sampling of releases across the United
States because nearly half of the states
contributed to the studies. Both drafts
were peer reviewed but never finalized
because the passage of Energy Policy
Act of 2005 required a reallocation of
personnel and resources. Even though
these studies were never finalized, the
underlying data and calculations can be
used to support this proposed rule
because that information did not change
as a result of the peer review process.
Many USTs currently in the ground
were upgraded to meet the spill,
overfill, corrosion protection, and
release detection requirements in the
1988 UST regulation. As these USTs
continue to age, it is vital that we
improve UST operation and
maintenance and test components to
ensure they are still working as
intended. Today’s proposed revisions to
the 1988 UST regulation focus on
ensuring equipment is working, rather
than requiring UST owners and
operators to replace or upgrade
equipment already in place. The 1988
UST regulation require owners and
operators to use equipment that could
help prevent releases; today’s proposed
revisions highlight the importance of
operating and maintaining UST
equipment so releases are prevented and
detected early in order to avoid or
minimize potential soil and
groundwater contamination.
EPA is proposing changes to the SPA
regulation (40 CFR part 281) to address
today’s proposed changes to 40 CFR part
280. By doing so, EPA will require states
to generally adopt the 40 CFR part 280
changes proposed today in order to
obtain or retain SPA.
What is the history of the UST laws and
regulations?
In 1984, Congress responded to the
increasing threat to groundwater posed
from leaking USTs by adding Subtitle I
to the Solid Waste Disposal Act
(SWDA). Subtitle I of SWDA required
EPA to develop a comprehensive
regulatory program for USTs storing
petroleum or certain hazardous
substances, ensuring that the
environment and human health are
protected from UST releases. In 1986,
Congress amended Subtitle I of SWDA
and created the Leaking Underground
5 Evaluation Of Releases From New And
Upgraded Underground Storage Tanks, Peer Review
Draft, U.S. EPA/OUST, August 2004.
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Storage Tank Trust Fund to implement
a cleanup program and pay for cleanups
at sites where the owner or operator is
unknown, unwilling, or unable to
respond, or which require emergency
action.
In 1988, EPA promulgated the UST
regulation (40 CFR part 280), which set
minimum standards for new tanks and
required owners and operators of
existing tanks to upgrade, replace, or
close them. In addition, after 1988
owners and operators were required to
report and clean up releases from their
USTs. The 1988 UST regulation set
deadlines for owners and operators to
meet those requirements by December
22, 1998. Owners and operators who
chose to upgrade or replace had to
ensure their UST systems included spill
and overfill prevention equipment and
were protected from corrosion. In
addition, owners and operators were
required to monitor their UST systems
for releases using release detection
(phased in during the 1990s, depending
on when their UST systems were
installed). Finally, owners and operators
were required to have financial
responsibility (phased in through 1998),
which ensured they have financial
resources to pay for cleaning up
releases. EPA has not significantly
changed the UST regulation since 1988.
In 1988, EPA also promulgated a
regulation for state program approval
(40 CFR part 281). Since states are the
primary implementers of the UST
program, EPA established a process
where state programs could operate in
lieu of the federal program if states met
certain requirements and obtained state
program approval from EPA. The state
program approval regulation describes
minimum requirements states must
meet so their programs can be approved
and operate in lieu of the federal
program.
In 2005, the Energy Policy Act further
amended Subtitle I of SWDA. The
Energy Policy Act required states
receiving Subtitle I money from EPA
meet certain requirements. EPA
developed grant guidelines for states
regarding operator training, inspections,
delivery prohibition, secondary
containment, financial responsibility for
manufacturers and installers, public
record, and state compliance reports on
government USTs. The operator training
and secondary containment
requirements are two major pieces of the
Energy Policy Act that currently do not
apply in Indian country, but will apply
when EPA finalizes today’s proposed
regulation.
What is the impact of this proposal?
This proposal will ensure parity in
program implementation among states
and in Indian country. This proposal
will achieve parity by adding certain
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requirements to the federal UST
regulation (that would apply in Indian
country) that are similar to the operator
training and secondary containment
requirements in the Energy Policy Act.
This action will also further strengthen
protection of human health and the
environment from UST releases by
increasing the emphasis on proper
operation and maintenance of release
prevention and detection equipment.
Today’s proposed revisions also reflect
improvements in technology that allow
for the ability to prevent and quickly
detect releases for many tank systems
that are currently deferred. The
regulatory changes proposed today
impose costs to owners and operators of
existing regulated UST systems, owners
and operators of certain deferred USTs,
as well as costs associated with state
review of the regulatory changes. EPA
prepared an analysis of the potential
incremental costs and benefits
associated with this action. This
analysis is contained in the regulatory
impact analysis (RIA) titled Assessment
Of The Potential Costs, Benefits, And
Other Impacts Of The Proposed
Revisions To EPA’s Underground
Storage Tank Regulations, which is
available in the docket for this proposal.
A summary of these impacts is provided
under the Statutory Review section of
this preamble and in the table below.
COSTS AND BENEFITS OF THE PROPOSED RULE
[2008$ millions]
7% Discount rate
Total Annual Compliance Costs ..................................................................................................................
Total Annual Avoided Costs ........................................................................................................................
Net Cost (Savings) to Society .....................................................................................................................
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EPA also prepared a risk assessment
titled Risk Analysis to Support Potential
Revisions to Underground Storage Tank
(UST) Regulations, associated with the
regulatory changes. The risk assessment
examines potential impacts to
groundwater and subsequent chemical
transport, exposure and risk. It is
available for review in the docket for
this proposal.
What was EPA’s process in deciding
which changes to incorporate in the
regulations?
After the Energy Policy Act became
law, EPA recognized a need to revise the
1988 UST regulations. The Energy
Policy Act required additional measures
to protect groundwater (either with
secondary containment or financial
responsibility for manufacturers and
installers) and operator training
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requirements in states receiving federal
Subtitle I money from EPA. However,
no similar requirements would apply in
Indian country until EPA promulgates a
regulation. Both EPA and Tribes are
committed to ensuring program parity
between states and in Indian country,
and today’s proposed regulation, when
final, will achieve this parity.
For over 20 years, the 1988 UST
regulations worked well. However, two
decades of experience implementing the
UST program have shown there are a
number of areas where EPA can
improve the UST program and increase
environmental protection. For example,
updating the regulation to reflect
current technologies and ensuring
release prevention and release detection
equipment are properly operated and
maintained have surfaced as important
regulatory changes.
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3% Discount rate
$210
$300–$740
($530–$90)
$210
$330–$770
($560–$120)
From the start, EPA embraced an
open, inclusive, and transparent process
so all UST stakeholders had an
opportunity to share their ideas and
concerns. EPA recognizes concerns
about costs to owners and operators and
the importance of limiting requirements
for retrofits. In developing this rule, we
reached out to stakeholders involved in
all aspects of the tank program,
provided multiple opportunities for
sharing ideas, and kept stakeholders
informed of progress.
Using information from our extensive
outreach, EPA compiled potential
proposed changes to the 1988 UST
regulations. We added or deleted items
to the list of changes based on data,
analysis, costs and benefits resulting
from the proposed changes, and EPA
discretion. Ultimately, EPA identified
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the items in today’s proposal as most
appropriate.
IV. Proposed Revisions to the
Requirements for Owners and
Operators of Underground Storage
Tanks
The following sections describe EPA’s
proposal, starting with requirements for
operator training and secondary
containment. The next four sections
address changes to the existing
regulation in 40 CFR part 280, organized
by topic: Additional requirements for
operation and maintenance; proposed
approach for currently deferred tanks;
other changes to improve release
prevention and release detection; and
general updates to the 1988 UST
regulation. Finally, there is a section
describing alternative options
considered.
After each proposed regulatory
change, EPA poses some questions to
which readers may wish to respond. In
addition to these specific questions,
readers may provide comments to any
other area of the proposal on which they
wish to comment.
A. Changes To Establish Federal
Requirements for Operator Training and
Secondary Containment
1. Operator Training
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What is EPA proposing?
EPA is proposing to add a new
subpart, subpart J—Operator Training,
to 40 CFR part 280. Through subpart J,
EPA is proposing the following training
requirements for three UST system
operator classes.
New Definitions
EPA is proposing the following new
terms and definitions:
• Class A operator—individual with
primary responsibility for operating and
maintaining an UST system according to
applicable requirements established by
the implementing agency. The Class A
operator typically manages resources
and personnel, such as establishing
work assignments, to achieve and
maintain compliance with regulatory
requirements.
• Class B operator—individual with
day-to-day responsibility for
implementing applicable regulatory
requirements established by the
implementing agency. The Class B
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product and equipment compatibility;
reporting and recordkeeping;
environmental and regulatory
consequences of releases; and training
requirements for Class C operator.
Training for Class B operators may be
general or specific to a Class B
operator’s site.
Æ Class C operator—appropriate
action to take in response to
emergencies (including situations
posing an immediate danger or threat to
the public or environment and that
require immediate action) or alarms
caused by spills or releases from an UST
system. Training for Class C operators
may be general or specific to a Class C
Training Requirements
operator’s site.
• How operators are designated—UST
• Training programs for Class A and
owners and operators must designate
B operators must, at a minimum, teach
individuals for each of the three
and evaluate their knowledge on the
operator classes. UST owners and
purpose, methods, and functions of
operators must designate at least one
items listed in the minimum training
Class A and one Class B operator for
areas above. Training programs for Class
each UST or group of USTs at a facility. C operators must teach and evaluate
UST owners and operators must
their knowledge of the items listed in
designate all of their employees who
the minimum training areas above.
meet the Class C operator definition as
• A training program must meet the
Class C operators.
minimum requirements discussed above
• Who must be trained—This
and evaluate knowledge through a test,
proposed training requirement covers
practical demonstration, or another
all UST systems storing regulated
approach acceptable to the
substances. UST owners and operators
implementing agency. In lieu of a
must ensure designated individuals
training program, all three operator
meet specific training requirements
classes must pass comparable
according to the operator class in which
examinations that assess their
they are designated.
knowledge in the minimum training
• Requirements for operator
areas above.
training—UST owners and operators
• The evaluation component of
must ensure operators in each class
successfully complete training programs training programs and comparable
examinations must be developed and
or comparable examinations that, at a
administered by an independent
minimum, cover these areas:
Æ Class A operator—spill and overfill organization, the implementing agency,
or delegated authority.
prevention; release detection; corrosion
protection; emergency response;
• When designated operators must
product and equipment compatibility;
complete operator training—UST
financial responsibility; notification and owners and operators must ensure all
storage tank registration; temporary and designated Class A, B, and C operators
permanent closure; related reporting
are trained or successfully complete a
and recordkeeping; environmental and
comparable examination according to
regulatory consequences of releases; and criteria and within time frames in the
training requirements for Class B and C
schedule below. Phase in is based on
operators. Training for Class A operators when USTs were installed because
is general on all listed areas.
newer UST systems tend to have fewer
Æ Class B operator—operation and
releases than older UST systems.6
maintenance; spill and overfill
prevention; release detection and
6 Evaluation Of Releases From New And
related reporting; corrosion protection
Upgraded Underground Storage Tanks, Peer Review
and related testing; emergency response; Draft, U.S. EPA/OUST, August 2004.
operator typically implements in the
field aspects of operation, maintenance,
and associated recordkeeping for an
UST system.
• Class C operator—employee
responsible for initially addressing
emergencies presented by a spill or
release from an UST system. The Class
C operator typically controls or
monitors dispensing or sale of regulated
substances.
• Training program—any program
established by the implementing agency
that provides information to and
evaluates the knowledge of a Class A,
Class B, or Class C operator regarding
requirements for UST systems.
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PHASE-IN SCHEDULE FOR OPERATOR TRAINING
Date when operator training or comparable
examination is required
Criteria
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One or more USTs at the facility were installed on or before 12/22/1988 .....................................
No USTs at the facility were installed on or before 12/22/1988 and at least one UST at the facility was installed on or before 12/22/1998.
All USTs at the facility were installed after 12/22/1998 ...................................................................
After the last date in the table above,
UST owners and operators must ensure
designated Class A and B operators are
trained within 30 days of assuming
duties. Designated Class C operators
must be trained before assuming their
duties.
• Retraining—Class A and B
operators of UST systems determined by
the implementing agency to be out of
compliance must complete a training
program or comparable examination in
accordance with requirements in
§ 280.242. At a minimum, training must
cover the area(s) determined to be out of
compliance. Retraining must occur
within 30 days from the date an
implementing agency determines an
UST system is out of compliance.
Retraining is not required if:
Æ Class A and B operators take annual
refresher training which covers all
applicable training requirements for
their operator class; or
Æ The implementing agency, at its
discretion, grants a waiver relinquishing
the Class A and B operators from
meeting the retraining requirement.
• Documentation—UST owners and
operators must maintain documents that
identify all operators by class and
demonstrate that training or retraining,
if necessary, was completed. These
documents must contain:
Æ A list of designated Class A, B, and
C operators for each UST facility—
Include names, operator class trained,
date assumed duties, date completed
initial training, and date of any
retraining. These records must be
maintained for all Class A, B, and C
operators at the facility for the previous
three years.
Æ Proof of training or retraining—A
paper or electronic record that, at a
minimum, includes name of trainee,
date trained, and operator class. In
addition, records from classroom or
field training programs or a comparable
examination, must be signed by the
trainer or examiner and include the
printed name of the trainer or examiner,
company name, address, and phone
number. Records from computer-based
training, at a minimum, must include
the name of the training program and
web address, if Internet-based. Records
of retraining must include those areas
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on which the Class A or B operator was
retrained. Records of training or
retraining must be maintained as long as
the Class A, Class B, and Class C
operators are designated at the facility.
Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing operator training
requirements to ensure that all regulated
UST systems are operated by properly
trained individuals. The operator
training provision of the Energy Policy
Act requires state implementing
agencies, as a condition of receiving
federal Subtitle I money, develop statespecific training requirements for three
classes of UST system operators. EPA
issued grant guidelines that provide
minimum requirements state operator
training programs must include in order
for states to continue receiving federal
Subtitle I money.7 The operator training
grant guidelines apply to most UST
systems in the United States; however,
not all are covered. UST systems not
covered include those in Indian country
where EPA is the primary implementing
agency, and in states and territories that
do not meet the requirements of EPA’s
operator training grant guidelines.
Through today’s proposal, EPA is
closing the gap in coverage and ensuring
all operators are trained according to
their level of responsibility, as
designated as Class A, B, or C.
Sufficiently training UST operators will
increase compliance with regulatory
requirements. In addition, operator
training may decrease UST system
releases by educating Class A, B, and C
operators about their UST system
requirements, and may result in greater
protection of human health and the
environment.
Today’s proposed operator training
regulation for UST owners and
operators is consistent with the
requirements in EPA’s operator training
grant guidelines for states. In both, EPA
establishes minimum operator training
requirements, yet allows flexibility to
tailor training programs for specific
7 Grant Guidelines To States For Implementing
The Operator Training Provision Of The Energy
Policy Act Of 2005: https://www.epa.gov/oust/
fedlaws/optraing.htm.
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One year after effective date of rule.
Two years after effective date of rule.
Three years after effective date of rule.
needs. This means that although there
may be variations among operator
training programs, all Class A, B, and C
operators will be trained to meet
minimum requirements.
Definitions—EPA is proposing
specific definitions of the three operator
classes to distinguish them from the
term operator defined in the 1988 UST
regulation. Only if a Class A, B, or C
operator meets the definition of operator
in the 1988 UST regulation will he or
she then be subject to the same
responsibilities and liabilities as an
operator. EPA’s proposed definitions of
Class A, B, and C operators do not
relieve owners and operators, as defined
in the 1988 UST regulation, from any
legal responsibility. EPA based the
proposed three operator class
definitions on duties each typically
performs at UST facilities.
EPA is proposing a definition for
training program. It is important that
training programs for Class A, B, and C
operators include both sharing
information and evaluating knowledge.
How operators are designated—EPA is
proposing how UST owners and
operators designate the three operator
classes for their facilities. EPA is taking
the position that designating at least one
Class A and B operator at each facility
is sufficient. Class A and B operators
can provide adequate training to Class C
operators, which should ease UST
owners’ and operators’ ability to comply
with this requirement. Because a Class
C operator’s duties typically place him
or her in a position of providing initial
response to an emergency, any UST
owner’s and operator’s employee who
meets the Class C operator definition
must be designated as such and trained
in emergency response.
EPA will allow UST owners and
operators to designate contractors as
their Class A and B operators as long as
they are responsible for all areas
required in the training for the class of
operator designated. UST owners and
operators must maintain documentation
containing individual names of Class A
and B contractors who complete
operator training. It will be easier for
implementing agencies to verify
training, retraining, and refresher
training using individual names rather
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than company names. All Class C
operators must be employees of the UST
system owner and operator.
EPA wants to ensure Class A and B
operator training addresses all
components and encompasses the entire
UST system. If an UST system is out of
compliance and the implementing
agency determines retraining is
required, Class A or B operators must
either be retrained or take annual
refresher training. EPA cautions UST
owners and operators to consider
whether contractors serving as Class A
or B operators can be designated.
Because some contractors specialize in
UST services, they might not be eligible
to be Class A or B operators. For
example, if a contractor is only
responsible for release detection
compliance, that contractor would not
be eligible to be a Class A or B operator
because he or she is not responsible for
all required training areas.
EPA realizes many UST owners and
operators may want to designate one
person at an UST facility as responsible
for all Class A, B, and C operator duties.
EPA will allow one person to serve in
multiple operator classes; however, that
person must be trained for each class
designated.
Who must be trained—When final,
today’s proposal will require training for
designated Class A, B, and C operators
at UST systems regulated under Subtitle
I. This includes UST systems of all
attended and unattended facilities. An
unattended UST facility means a Class
A, B, or C operator may not be present
during times when a facility is
operating. Nonetheless, even at
unattended UST facilities, designated
Class A, B, and C operators must still
meet the operator training requirement.
Requirements for operator training—
EPA based the three operator classes on
duties each typically performs at UST
facilities. Building on that, EPA is
proposing each person designated in an
operator class pass an examination
comparable to the training program, or
meet a specific training program, which
will:
• For Class A operator, teach and
evaluate his or her knowledge to make
informed decisions regarding
compliance and determine whether
appropriate people are fulfilling the
operation, maintenance, and
recordkeeping requirements for UST
systems.
• For Class B operator, teach and
evaluate his or her knowledge and skills
to implement UST regulatory
requirements on typical UST system
components or site-specific equipment
at the UST facility.
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• For Class C operator, teach and
evaluate his or her knowledge to take
appropriate action in response to
emergencies (including situations
posing an immediate danger or threat to
the public or environment and that
require immediate action) or alarms
caused by spills or releases from an UST
system.
For each class of operator, EPA
considered developing specific training
curricula that would prescribe length of
training, areas to cover, and trainer
qualifications. EPA decided that
providing the general criteria
requirements presented in today’s
proposal is the best approach because
they provide flexibility while being
comparable to EPA’s operator training
grant guidelines for states and ensuring
each class of operator is trained.
EPA proposes not to restrict who may
develop and administer the training
component of a training program.
However, to avoid potential conflicts of
interest, EPA proposes to only allow
independent organizations to develop
and administer the evaluation
component training programs and
comparable examinations, as long as
they meet the minimum requirements in
today’s proposal. EPA considers
independent organizations to include a
wide array of program providers who
are not affiliated with the Class A, B, or
C operators they are training. For
example, Class A or B operators can
train other Class A or B operators at the
same UST facility, but they cannot
develop or conduct the evaluation
component of the training program for
those operators. However, as discussed
earlier, Class A or B operators can train
and evaluate Class C operators. In
addition, the implementing agency may
develop and administer a training
program or comparable examination.
Although not specifically listed in the
regulation, EPA will allow a variety of
ways to train operators. These include
classroom, computer-based, hands on,
and any combination of these.
Accepted in lieu of completing a
training program, Class A, B, or C
operators can pass a comparable
examination (for example, via
classroom, Internet, or computer
program) that meets the requirements
for operator training criteria described
in today’s proposal.
When designated operators must
complete operator training—EPA is
proposing that UST owners and
operators ensure all Class A, B, and C
operators successfully complete a
training program or a comparable
examination over three years, based on
UST installation dates. This phased-in
approach will stagger the need for
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operator training and reduce a rush at
the end of the initial three year period.
Since older USTs potentially pose a
greater risk to the environment, EPA
decided Class A, B, and C operators of
those systems should be trained first.
After the initial three year phase-in
period and for consistency with EPA’s
operator training grant guidelines for
states, EPA is proposing new Class A, B,
and C operators be trained as follows:
• Class A and B operators must be
trained within 30 days of assuming
duties. 30 days are sufficient for Class
A and B operators to receive operator
training.
• Class C operators must be trained
before they assume their duties; it is
critical that they are trained
immediately in order to respond to
emergencies.
Retraining—UST system
noncompliance can be an indication
that Class A and B operators are not
doing what is necessary to maintain
compliance. If an UST system is out of
compliance, then generally, Class A and
B operators designated for that UST
system need to be retrained. Retraining
must, at a minimum, cover those areas
determined by the implementing agency
to be out of compliance. Retraining must
be completed within 30 days of the
implementing agency making a final
determination of noncompliance. EPA is
proposing to allow annual refresher
training in lieu of retraining as long as
all training areas required by regulation
are covered. Refresher training must
have been in place at the time the
implementing agency determined the
UST system was out of compliance.
EPA is also proposing to allow
implementing agencies, at their
discretion, to waive the retraining
requirement. EPA recommends that
such a waiver be in writing. In granting
a waiver, EPA expects the implementing
agency to consider factors such as the
severity and areas of noncompliance. In
those instances where UST system
noncompliance violations do not
warrant retraining, EPA encourages
implementing agencies to provide
information to Class A and B operators
so they are able to return their facilities
to compliance. These allowances will
provide greater flexibility for UST
owners and operators to meet the
retraining requirement. This proposal is
consistent with EPA’s retraining
requirement for noncompliance with
significant operational compliance
requirements and an annual refresher
training allowance provided in our
operator training grant guidelines for
states.
EPA considered requiring retraining
when UST facilities change equipment,
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but decided this would be an
unnecessary burden on both the
regulated community and implementing
agencies. If an UST system is out of
compliance because of an equipment
change, EPA is proposing that the
implementing agency require that UST
owners and operators ensure Class A
and B operators are retrained as
proposed above.
Documentation—EPA is proposing
UST owners and operators maintain a
list of Class A, B, and C operators at
each UST facility for the previous three
years. Keeping this list for three years is
adequate because it is consistent with
the inspection frequency provided by
the Energy Policy Act. Owners and
operators must have a list of trained
operators for the past three years each
time they are inspected. In addition,
UST owners and operators must also
document verification of training or
retraining, as appropriate, for each class
of operator. EPA will require basic
information to document Class A, B,
and C operators and confirm they are
appropriately trained. For example,
classroom training must be signed by
the trainer; computer based training
does not require a signature but must
indicate the name of the training.
Records verifying training or retraining
must be maintained as long as the Class
A, B, and C operators are designated at
the facility. This time frame will allow
owners and operators to demonstrate
Class A, B, and C operators are trained
as long as they are designated at the
facility.
What issues related to this change does
EPA request comment or additional
data on?
• Should EPA impose a limit on the
number of USTs or facilities a Class A
or B operator is responsible for? If so,
what should the limit be and why?
• EPA is seeking information about
the number of unattended regulated
UST facilities in the United States. How
many regulated UST facilities are
unattended in the United States?
• EPA is basing the initial period for
meeting the training requirement on the
UST installation date. Should we
consider other criteria? If so, what and
why?
• Is there a need for a phased-in
schedule for operator training? If so, is
EPA’s proposed schedule reasonable?
• Does EPA’s proposal prohibit
training approaches currently available?
If so, which ones and why?
• Should EPA prohibit particular
training approaches? If so, which ones
and why?
• Although operators can access any
available information source to obtain
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necessary knowledge of UST systems, in
order to address potential conflicts of
interest concerns, only independent
organizations are allowed to develop
and administer the evaluation
component of training programs and
comparable examinations. Are there
cases where EPA should consider
exceptions to this proposed
requirement?
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
2. Secondary Containment
What is EPA proposing?
EPA is proposing to add in 40 CFR
part 280 secondary containment and
interstitial monitoring requirements for
new and replaced tanks and piping. In
addition, UST systems must have
under-dispenser containment for new
dispenser systems.
New Definitions
EPA is proposing the following new
terms and definitions:
• Dispenser system—Equipment
located above ground that meters the
amount of regulated substances
transferred to a point of use outside the
UST system, such as a motor vehicle.
This system includes equipment
necessary to connect the dispenser to
the UST system.
• Replaced—
Æ For a tank: To remove a tank and
install another tank.
Æ For piping: To remove 50 percent or
more of piping and install other piping,
excluding connectors, connected to a
single tank. For tanks with multiple
piping runs, this definition applies
independently to each piping run.
• Secondary containment or
secondarily contained—A release
prevention and release detection system
for a tank and/or piping. This system
has an inner and outer barrier with an
interstitial space that is monitored for
leaks.
• Under-dispenser containment
(UDC)—Containment underneath a
dispenser system designed to prevent
dispenser system leaks from reaching
soil or groundwater.
Secondary Containment
EPA is proposing owners and
operators install secondary containment
(including interstitial monitoring) for
new or replaced tanks and piping
installed after the effective date of the
final UST regulation. EPA is not
proposing secondary containment for
the following types of piping:
• Suction piping that meets the
requirements of § 280.41(b)(2)(i) through
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71715
(v), sometimes called safe suction
piping; and
• Piping associated with fieldconstructed tanks and airport hydrant
fuel distribution systems.
EPA is proposing secondarily
contained tanks and piping be:
• Able to contain regulated
substances leaked from the primary
containment until they are detected and
removed;
• Able to prevent release of regulated
substances to the environment at any
time during the operational life of the
UST system; and
• Monitored for a leak at least once
every 30 days using interstitial
monitoring according to § 280.43(g).
In addition to the requirements above,
pressurized piping must have an
automatic line leak detector according
to § 280.44(a).
EPA is proposing to remove the
option in § 280.42 for owners and
operators to use a release detection
method other than interstitial
monitoring for hazardous substance
USTs installed after the effective date of
the final UST regulation.
Under-Dispenser Containment
EPA is proposing owners and
operators install under-dispenser
containment beneath new dispenser
systems at UST systems. EPA will
incorporate this new requirement by
adding a new subsection (f) to § 280.20,
which will require under-dispenser
containment beneath each new
dispenser system at an UST system.
EPA is proposing a dispenser system
be considered new when both the
dispenser system and equipment
needed to connect the dispenser system
to the UST system are installed at an
UST facility. The equipment connecting
the dispenser system to the UST system
includes check valves, shear valves,
unburied risers or flexible connectors,
or other transitional components
beneath the dispenser that connect it to
underground piping. Finally, underdispenser containment must be liquid
tight on its sides, bottom, and at any
penetrations and allow for visual
inspection and access to the
components in the containment system,
or must be continuously monitored for
leaks from the dispenser system.
Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing this change to
prevent regulated substances from
reaching the environment and ensure a
consistent level of environmental
protection for regulated UST systems
across the United States. Data from
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release sites show a higher number of
releases from single-walled tanks and
piping when compared to secondarily
contained systems.8 9 Releases could be
reduced for tanks and piping if they are
secondarily contained.
The Energy Policy Act requires state
implementing agencies, as a condition
of receiving federal Subtitle I money,
implement additional measures to
protect groundwater. Under the law,
state implementing agencies’ choices to
protect groundwater were secondary
containment (including under-dispenser
containment) or financial responsibility
for manufacturers and installers (and
installer certification). 54 of 56 state
implementing agencies chose secondary
containment. The Energy Policy Act did
not specifically require additional
measures to protect groundwater in
Indian country. As the primary
implementer for more than 2,600 UST
systems in Indian country, 10 EPA is
proposing secondary containment for
new and replaced tanks and piping
along with under-dispenser
containment beneath all new dispenser
systems at UST systems. Over the last
seven years, approximately 25 new UST
systems per year were installed in
Indian country.11 The final UST
regulation will bring UST systems in
Indian country to the same level of
environmental protection as those
regulated by states.
The Energy Policy Act requires states
that receive federal Subtitle I money
(and that choose the secondary
containment option) to have secondary
containment and under-dispenser
containment for tanks, piping, and
dispensers only if they are installed or
replaced within 1,000 feet of an existing
community water system or potable
drinking water well.12 However, EPA is
proposing all new and replaced tanks
and piping have secondary containment
and UST systems have under-dispenser
containment beneath all new dispenser
systems for the following reasons:
8 Petroleum Releases At Underground Storage
Tank Facilities In Florida, Peer Review Draft, U.S.
EPA/OUST, March 2005.
9 Evaluation Of Releases From New And
Upgraded Underground Storage Tanks, Peer Review
Draft, U.S. EPA/OUST, August 2004.
10 Semi-Annual Report Of UST Performance
Measures, End Of Fiscal Year 2009, https://epa.gov/
oust/cat/camarchv.htm.
11 E2, Incorporated, memoranda and analyses
submitted under Contract EP–W–05–018, ‘‘U.S.
Environmental Protection Agency. Underground
Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.’’ These
supporting materials can be found in the docket for
the proposed rulemaking.
12 Title XV, subtitle B, Section 1530 of Energy
Policy Act of 2005, 109th Congress Public Law 58,
August 8, 2005.
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• Nearly all new and replaced tanks
and piping are installed within 1,000
feet of an existing community water
system or potable drinking water well.
We assume that any UST listed with a
commercial ownership type (i.e., gas
station) is located within 1,000 feet of
an on-site well or public water line
because nearly all commercially-owned
facilities with USTs require water
utilities in order to operate and all
privately owned facilities (i.e., fleet
fueling for non-marketers) are also
assumed to be in close proximity to
some type of water supply given that
these sites are typically combined with
other functional operations (office,
maintenance, manufacturing, etc.) and
require water for restrooms, water
fountains, shops, etc.;13
• Some state implementing agencies
that require secondary containment only
within 1,000 feet of one of these water
sources have informed EPA that
installations of single-walled tanks or
piping are not occurring; and
• Secondary containment and underdispenser containment will help protect
other sensitive areas, such as designated
source water protection areas, natural
springs, and surface waters.
EPA is not proposing secondary
containment for piping that meets the
requirements of 280.41(b)(2)(i) through
(v), sometimes called safe suction
piping because it is currently not
required to meet release detection
requirements. This type of piping uses
a suction pump to deliver regulated
substances from the UST to the
dispenser. Safe suction piping operates
at less than atmospheric pressure,
slopes back towards the UST so
regulated substances drain to the UST if
suction is lost, and has only one check
valve located close to the suction pump.
As discussed in the 1988 UST
regulation preamble, these
characteristics ensure that little, if any,
regulated substances will be released if
a break occurs in the line.14
EPA is not proposing secondary
containment for piping associated with
field-constructed tanks and airport
hydrant fuel distribution systems. EPA
understands this piping typically is
larger diameter and runs for long
distances, making it difficult to slope
the piping back to an interstitial
monitoring area. In addition, EPA
13 E2, Incorporated, memoranda and analyses
submitted under Contract EP–W–05–018, ‘‘U.S.
Environmental Protection Agency. Underground
Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.’’ These
supporting materials can be found in the docket for
the proposed rulemaking.
14 Preamble to 40 CFR part 280, FR Vol. 53, No.
185, Friday, September 23, 1988, p. 37154.
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understands it is difficult to keep water
out of the interstitial area of these long
piping runs. Since nearly all this piping
is steel, corrosion can occur in the
interstitial area when an electrolyte,
such as water, is in the interstitial area.
This corrosion can significantly shorten
the piping’s life. Corrosion protection
safeguards piping in contact with the
ground, but does not protect the inside
part of piping from corrosion. To
prevent corrosion caused by water in
the interstitial area, owners and
operators would need to add corrosion
protection inside the interstitial area of
piping, which EPA realizes would be
difficult, if not impossible, to do. Given
all of these issues, secondary
containment for these piping runs could
potentially reduce environmental
protection.
EPA is proposing owners and
operators install tank and piping
secondary containment that: will
contain regulated substances leaked
from the primary containment until they
are detected and removed; is able to
prevent the release of regulated
substances to the environment at any
time during the operational life of the
UST system; and is monitored for a leak
at least once every 30 days using
interstitial monitoring. These
requirements are consistent with the
1988 UST regulation for secondarily
contained hazardous substance tanks
(§ 280.42) and are necessary to help
prevent releases to the environment.
The secondary containment
requirement applies to new or replaced
underground tanks and piping regulated
under Subtitle I except those excluded
by regulation at 40 CFR 280.10(b) and
those deferred by regulation at 40 CFR
280.10(c). All petroleum and hazardous
USTs are intended to meet the
secondary containment requirement
with the corresponding use of
interstitial monitoring. EPA’s current
regulation allows variances to the use of
interstitial monitoring as the method of
release detection for hazardous
substance USTs. Since these variances
are no longer an option, EPA is
eliminating this language to avoid
confusion.
EPA is not proposing secondary
containment and/or under-dispenser
containment for UST systems where
installation began on or before the
effective date of the final UST
regulation. Similar to the definition of
existing tank system in the 1988 UST
regulation, EPA considers an
installation to have begun after the
owner or operator has obtained all
federal, state, and local approvals or
permits and:
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• Physical construction or installation
began; or
• The owner or operator entered into
a contractual agreement that cannot be
cancelled or modified without
substantial loss and physical
construction or installation will
commence within a reasonable time
frame.
Requiring retrofits would be a
significant financial burden for owners
and operators. EPA anticipates owners
and operators will replace single-walled
UST systems as they age. When owners
and operators replace singled-walled
UST systems after the effective date of
the final UST regulation, new tanks and
piping will need to be secondarily
contained and new dispensers will have
under-dispenser containment.
To implement secondary containment
and under-dispenser containment, EPA
is proposing to add new terms and
definitions: Dispenser system; replaced;
secondary containment or secondarily
contained; and under-dispenser
containment. EPA defined these terms
so they are no less stringent than the
definitions contained in EPA’s
secondary containment grant guidelines
to state implementing agencies.15
EPA’s secondary containment grant
guidelines provide states with
significant flexibility to define
‘‘replaced’’ as it applies to piping. The
guidelines require that states, at a
minimum, consider replacing piping
when 100 percent of piping, excluding
connectors, connected to a single UST is
removed and other piping is installed.
When deciding how to best define
replaced as it applies to piping, EPA
analyzed state UST regulations for
approximately 40 states that currently
require secondary containment and
interstitial monitoring.16 About 75
percent of these states have
requirements as stringent as, or more
stringent than, the 50 percent threshold
EPA proposes.
In addition, EPA performed a
screening analysis using limited,
readily-available data to determine
when repair cost approached
replacement cost (and at what point
owners and operators were most likely
to replace the entire piping run rather
15 Grant
Guidelines To States For Implementing
The Secondary Containment Provision Of The
Energy Policy Act Of 2005: https://epa.gov/oust/
fedlaws/secondco.htm.
16 E2, Incorporated, memoranda and analyses
submitted under Contract EP–W–05–018, ‘‘U.S.
Environmental Protection Agency. Underground
Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.’’ These
supporting materials can be found in the docket for
the proposed rulemaking.
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than repair it).17 The screening analysis
suggested replacement cost of an entire
piping run became equal to repair cost
when about 60 percent of a piping run
is repaired. Based on this information,
EPA is proposing owners and operators
secondarily contain an entire piping run
when 50 percent or more of a piping run
is replaced. This is consistent with most
state implementing agency decisions
and existing economic incentives. This
will also prevent owners and operators
from leaving small pipe sections in the
ground to avoid this proposed
secondary containment requirement. If
an UST has multiple piping runs, the
secondary containment requirement
will only apply to those where 50
percent or more of piping is replaced.
Currently installed piping runs, and
piping runs where less than 50 percent
of the piping is repaired, will not
require secondary containment.
For pressurized piping, EPA considers
a piping run to be the piping that
connects the submersible turbine pump
(STP) to all of the dispensers fed by that
pump. For example, if a tank has two
STPs, the piping associated with each
STP would be considered separate
piping runs. For suction piping, a
piping run is the piping that runs
between the tank and the suction pump.
Consistent with EPA’s current policy,
if an owner or operator chooses to
reinstall a secondarily contained tank or
piping that was previously installed,
that tank or piping must meet new tank
and piping standards in § 280.20 at the
time of installation.
The Energy Policy Act defined
secondary containment as a release
detection and prevention system that
meets the interstitial monitoring
requirement in § 280.43(g). Based on
this definition, EPA is proposing to
include interstitial monitoring as part of
the secondary containment definition.
Therefore, secondary containment
means having an interstitial space to
monitor and monitoring that space for a
leak. Consistent with the 1988 UST
regulation release detection
requirements, EPA is proposing
interstitial monitoring of new and
replaced secondarily contained tanks
and piping at least once every 30 days.
EPA is proposing owners and
operators install under-dispenser
containment beneath new dispenser
systems at UST systems. Data from
release sites show dispensers are one of
the leading release sources.18 19 Under17 IEc Incorporated, Work Assignment # 1–19,
‘‘Methodology and Calculator for Secondary
Containment for Piping,’’ October 3, 2008.
18 Petroleum Releases At Underground Storage
Tank Facilities In Florida, Peer Review Draft, U.S.
EPA/OUST, March 2005.
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dispenser containment is located
underground and will prevent some
releases by containing small releases
that occur inside and beneath the
dispenser. EPA considers a dispenser
system new when both the dispenser
and equipment needed to connect the
dispenser to an UST system are
installed at an UST facility. EPA is
proposing check valves, shear valves,
unburied risers or flexible connectors,
and other transitional components be
included as equipment that connects a
dispenser to an UST system. This
equipment is located beneath the
dispenser and typically connects
underground piping to a dispenser. If an
owner or operator replaces a dispenser
but uses existing equipment to connect
a dispenser to the UST system, then
under-dispenser containment is not
required.
To contain small releases from the
dispenser, piping, and other equipment,
the under-dispenser containment must
be liquid tight. EPA is proposing underdispenser containment be liquid tight
on its sides, bottom, and at any
penetrations through the containment.
EPA is proposing periodic testing of
under-dispenser containment in the
secondary containment tests section (see
section B–4). In addition, an owner or
operator must have access to and be able
to visually inspect the containment. If
visual inspection and access are not
available, then under-dispenser
containment must be continuously
monitored to ensure containment is
intact and free of liquids. Continuous
monitoring and visual inspections
(required in the proposed walkthrough
inspections discussed in section B–1)
will ensure problems with the underdispenser containment will be detected
before a release to the environment
occurs.
The Energy Policy Act requires underdispenser containment beneath new
motor fuel dispenser systems at UST
systems. However, EPA is aware of a
small number of dispenser systems
which do not dispense motor fuel (for
example, kerosene dispensers). Small
releases can occur at these dispensers in
the same manner as they occur at motor
fuel dispensers.20 21 22 Therefore, EPA is
19 Evaluation Of Releases From New And
Upgraded Underground Storage Tanks, Peer Review
Draft, U.S. EPA/OUST, August 2004.
20 Petroleum Releases At Underground Storage
Tank Facilities In Florida, Peer Review Draft, U.S.
EPA/OUST, March 2005.
21 Evaluation Of Releases From New And
Upgraded Underground Storage Tanks, Peer Review
Draft, U.S. EPA/OUST, August 2004.
22 Frequency And Extent Of Dispenser Releases
At Underground Storage Tank Facilities In South
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proposing owners and operators install
under-dispenser containment beneath
new dispenser systems at UST systems,
irrespective of whether they dispense
motor fuel.
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What issues related to this change does
EPA request comment or additional
data on?
• If you have any of the following
data, please provide the:
Æ Number of UST systems not
installed within 1,000 feet of any
existing community water system or
potable drinking water well.
Æ Number of non-motor fuel
dispensers connected to UST systems in
the United States.
Æ Typical length or percentage of
piping repaired during a typical repair.
Æ Costs, types and frequency of
piping repairs and replacements.
• Are there regulatory incentives that
EPA should consider to encourage
owners and operators to move toward
secondary containment? If yes, what are
those incentives?
• In addition to the three types of
piping identified for exclusion by EPA,
are there other types of piping for which
secondary containment is impractical or
unnecessary? If yes, what are those
types and why is secondary
containment impractical or
unnecessary?
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
B. Additional Requirements for
Operation and Maintenance
The 1988 UST regulation required
owners and operators to install
improved UST system equipment to
detect and prevent releases; however, it
did not require operation and
maintenance for all of that equipment.
Owners and operators need to properly
operate and maintain their UST system
equipment in order to prevent and
quickly detect releases. Therefore, we
propose to add requirements for
periodic spill, overfill, secondary
containment, and release detection
testing along with periodic walkthrough
inspections to prevent and quickly
detect releases.
When a test or inspection occurs,
owners and operators may find
problems with the UST system. When a
test or inspection indicates a problem,
owners and operators must repair the
problem to remain in compliance with
the 1988 UST regulation. Section 280.33
of the 1988 regulation describes repair
requirements for UST systems.
Carolina (EPA–510–R–04–004, September 2004).
https://epa.gov/oust/pubs/dispenser.htm.
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1. Walkthrough Inspections
What is EPA proposing?
In § 280.37, EPA is proposing owners
and operators perform walkthrough
inspections of their UST systems at least
once every 30 days and meet one of
these three options:
• Option 1: Conduct operation and
maintenance walkthrough inspections
that, at a minimum and as appropriate
to the facility, check the following
equipment:
Æ Spill prevention equipment
fi Open and visually check for any
damage;
fi Remove any liquid or debris;
fi Check each fill cap to make sure it
is securely on the fill pipe; and
fi If secondarily contained with
continuous interstitial monitoring,
check for a leak in the interstitial area.
Æ Sumps and dispenser cabinets
fi Open and visually check for any
damage, leaks to the containment area,
or releases to the environment;
fi Remove any liquid (in contained
areas) or debris; and
fi If contained areas are secondarily
contained with continuous interstitial
monitoring, check for a leak in the
interstitial area.
Æ Monitoring/observation wells
fi Check covers to make sure they are
secured.
Æ Cathodic protection
fi Check to make sure impressed
current cathodic protection rectifiers are
on and operating; and
fi Ensure records of three year
cathodic protection testing and 60 day
impressed current system inspections
are reviewed and current.
Æ Release detection
fi Check to make sure the release
detection system is on and operating
with no alarm conditions or other
unusual operating conditions present;
fi Check any devices such as tank
gauge sticks, groundwater bailers, and
hand-held vapor monitoring devices for
operability and serviceability; and
fi Ensure records of release detection
testing are reviewed monthly and
current.
• Option 2—Conduct operation and
maintenance walkthrough inspections
according to a standard code of practice
developed by a nationally recognized
association or independent testing
laboratory that are comparable to the
specific requirements listed above.
• Option 3—Conduct operation and
maintenance walkthrough inspections
developed by the implementing agency
that are comparable to the specific
requirements listed above.
EPA is proposing owners and
operators maintain walkthrough
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inspection records for one year. Each
record must include a listing of each
area checked, whether each area
checked was acceptable or needed to
have some action taken, and a
description of actions taken to correct
an issue.
Why is EPA proposing this change?
What background information is
available about this change?
The 1988 UST regulation focused on
owners and operators installing
improved UST equipment, but did not
require significant equipment operation
and maintenance activities. After more
than 20 years of experience with UST
requirements, EPA finds both using
improved equipment and operating and
maintaining UST equipment are
necessary to protect human health and
the environment. 12 states have adopted
monthly walkthrough inspection
requirements for their UST facilities. Of
those states, only California has been
implementing the requirement long
enough to provide input about the
effectiveness of walkthrough
inspections. California indicates that,
according to UST inspectors and
industry people, the monthly
inspections decreased the number of
violations found, reduced the frequency
and duration of release detection
alarms, prompted better record keeping,
and resulted in overall better operations
at the UST facility.23
As part of operating and maintaining
UST systems, EPA proposes owners and
operators conduct walkthrough
inspections at least once every 30 days.
Periodic walkthrough inspections will
help owners and operators detect
problems earlier, resulting in fewer
releases to the environment and reduced
environmental impacts of releases that
reach the environment.
Walkthrough inspections are designed
to verify proper function or operating
condition of easily accessible UST
system components and ensure required
records are current. These inspections
typically include reviewing records and
checking components to confirm
function or condition. For example,
owners and operators will be required to
review current records and ensure
equipment is operating properly;
containment sumps are free of liquid
and debris; and leaks are not occurring
at dispensers, submersible turbine
pumps, and other areas. EPA used the
Petroleum Equipment Institute’s
Recommended Practice 900,
Recommend Practices for the Inspection
and Maintenance of UST Systems, as a
23 Email from Laura Fisher, California State Water
Resources Control Board, April 30, 2010.
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guide as we developed the proposed
walkthrough inspection requirements.
EPA is proposing allowing owners and
operators to hire a third party to
conduct walkthrough inspections
instead of performing the inspection
themselves.
EPA is proposing three options for
owners and operators to choose from in
conducting walkthrough inspections:
follow the specific requirements
(described below) appropriate to the
UST facility; use a code of practice
developed by a nationally recognized
association or independent testing
laboratory; or follow requirements
developed by the implementing agency.
At a minimum, walkthrough inspections
conducted according to a code of
practice or developed by the
implementing agency need to be
comparable to the following
requirements. The specific requirements
proposed and reasons for their inclusion
in the regulation are:
• For spill prevention equipment—
open each spill prevention area, check
for damage, and remove any liquid or
debris; check the fill cap to make sure
it is securely on the fill pipe; and for
secondarily contained spill prevention
equipment with continuous interstitial
monitoring, check for a leak in the
interstitial area.
Æ Damaged spill prevention
equipment can release regulated
substances into the environment and
liquid or debris can reduce the
equipment’s capacity. Fill caps not
secure on the fill pipe can result in
vapors exiting the tank and can render
overfill prevention inoperable in tanks
that use flow restrictors in the vent line.
Some spill prevention equipment
construction materials may not be
designed to contain regulated
substances for long periods of time. For
spill prevention equipment with two
walls and continuous interstitial area
monitoring, owners and operators need
to check the monitoring device or area
to make sure the interstitial monitoring
is operating properly and does not
indicate a leak in the interstitial area.
• For sumps, including submersible
turbine pump sumps and transition
sumps—open and visually check for
damage, leaks to the containment area,
or releases to the environment; remove
any liquid (in contained sumps) or
debris; and for secondarily contained
sumps with continuous interstitial
monitoring, check for a leak in the
interstitial area.
Æ Drips and other small releases from
damaged components contained by the
sump can result in regulated substances
remaining in the sump. Damaged sumps
can release regulated substances into the
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environment. Liquid or debris can
reduce the capacity of a contained
sump. Some sump construction
materials may not be designed to
contain regulated substances for long
periods of time. For sumps with two
walls and continuous interstitial area
monitoring, owners and operators need
to check the monitoring device or area
to make sure the interstitial monitoring
is operating properly and does not
indicate a leak in the interstitial area.
• For dispenser cabinets—open each
cabinet; visually check for damage,
leaks to the containment area, or
releases to the environment; remove any
liquid (in dispensers with underdispenser containment) or debris; and
for dispenser sumps with continuous
interstitial monitoring, check for a leak
in the interstitial area.
Æ Visual checks for dispensers are
important because the 1988 UST
regulation does not require release
detection for dispensers. Drips and
other small releases from damaged
components in the dispenser cabinet
can result in regulated substances
remaining in the dispenser sump or
being released to the environment.
Damaged under-dispenser containment
(if present) can release regulated
substances into the environment. If
under-dispenser containment is present,
liquid or debris can reduce the capacity
of the containment sump. Some underdispenser containment construction
materials may not be designed to
contain regulated substances for long
periods of time. For dispenser sumps
with two walls and continuous
interstitial area monitoring, owners and
operators need to check the monitoring
device or area to make sure the
interstitial monitoring is operating
properly and does not indicate a leak in
the interstitial area.
• For monitoring or observation
wells—check the covers to make sure
they are secured.
Æ These wells need to be secured to
avoid potential contamination of wells
through the well cover (for example by
surface runoff or accidental fuel
delivery to the well).
• For cathodic protection—check to
make sure impressed current cathodic
protection rectifiers are on and
operating; ensure records of three year
cathodic protection testing and 60 day
impressed current system inspections
are reviewed and up to date.
Æ Impressed current cathodic
protection systems need to be on and
operating to protect underground metal
components of the UST system that
routinely contain regulated substances
from corrosion. In addition, owners and
operators need to retain records of the
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71719
most recent two cathodic protection
tests (required once every three years)
and the most recent three inspections
(required once every 60 days) for
impressed current systems. These
records show that cathodic protection
systems are on and operating properly
to protect UST system components from
corrosion. Owners and operators who
record rectifier readings and compare
those readings to the normal operating
parameters of the rectifier during the 30
day walkthrough inspections will meet
the 60 day impressed current inspection
requirement in § 280.31(c) without
further activity. Failure to operate and
maintain cathodic protection could
mean that metal UST system
components are corroding and could
result in a release to the environment.
• For release detection—check to
make sure the release detection system
is on and operating with no alarm
conditions or other unusual operating
conditions present; check any devices
such as tank gauge sticks, groundwater
bailers, and hand-held vapor monitoring
devices for operability and
serviceability; and ensure records of
release detection testing are reviewed
monthly and up to date.
Æ Release detection equipment needs
to be operable in order to detect releases
when they occur. Owners and operators
must respond to release detection
alarms. Manual release detection
equipment needs to be serviceable and
operational so owners and operators can
perform proper release detection. In
addition, owners and operators need to
ensure they review the most recent
month’s release detection information
and retain the most recent year’s worth
of release detection records. These
records are required for all methods of
release detection, and reviews ensure
UST systems are being checked for a
release at least once every 30 days.
Failure to perform these checks could
mean release detection equipment is not
operating properly and could result in a
release to the environment.
Owners and operators using
continuous interstitial monitoring for
double-walled spill prevention devices,
sumps, or dispenser containment areas
need to check the interstitial monitoring
to make sure it is operating properly and
does not indicate a leak in the
interstitial area. EPA is aware of these
continuous interstitial monitoring
methods: vacuum, pressure, or liquidfilled interstitial area monitoring and
placing sensors in the interstitial area.
For vacuum, pressure, or liquid-filled
interstitial area monitoring using
electronic devices and sensors, owners
and operators will need to check the
electronic device to make sure it is not
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in alarm. For interstitial areas monitored
using vacuum, pressure, or liquid-filled
interstitial area monitoring not using
some type of electronic monitoring,
owners and operators will need to make
sure the vacuum, pressure, or liquid is
maintaining its appropriate level.
Owners and operators who do not check
the interstitial monitoring of spill
prevention devices must perform
periodic spill prevention equipment
testing described in § 280.35(a)(ii) of the
proposed UST regulation. Owners and
operators who do not check the
interstitial monitoring of sumps or
dispenser containment areas and who
use those areas for interstitial
monitoring for their piping must
perform the periodic testing of
secondary containment described
§ 280.36(a)(iii) of the proposed UST
regulation.
EPA is proposing walkthrough
inspections be conducted at least every
30 days. 30 days is a reasonable time
frame because:
• Deliveries occur frequently—often
daily or every few days;
• Dispenser filters are changed every
few weeks or months;
• It is consistent with the 30 day
release detection monitoring
requirement; and
• Current operation and maintenance
industry standards (Petroleum
Equipment Institute Recommended
Practice 900) recommend monthly
checks as one of the periodic inspection
frequencies.
EPA is proposing owners and
operators retain the most recent year’s
worth of records to demonstrate
compliance with the walkthrough
inspection requirement. Owners and
operators will be required to document
they performed each of the required
activities at least once every 30 days.
Keeping one year’s worth of records is
consistent with the current
recordkeeping requirement for release
detection monitoring. EPA is proposing
owners and operators document each
area checked, whether each area
checked was acceptable or needed to
have some action taken, and provide a
description of any actions taken to
correct an issue. This information is
important to assist implementing
agencies in determining proper
operation and maintenance.
What issues related to this change does
EPA request comment or additional
data on?
• Is a 30 day inspection frequency an
appropriate time frame for owners and
operators to conduct walkthrough
inspections?
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• Is it reasonable for owners and
operators to begin conducting
walkthrough inspections immediately
after the final UST regulation becomes
effective?
• Is specialized training required for
individuals completing walkthrough
inspections? If yes, what should EPA
establish as the extent of the training?
• Are there other codes of practice
that should be included for conducting
walkthrough inspections?
• Is requiring owners and operators to
keep the most recent year’s worth of
records sufficient?
• Are the items EPA proposes
checking appropriate? Should EPA add
anything? Are there checks EPA is
proposing that should not be required?
• Should EPA consider not requiring
owners and operators to remove water
from contained sumps when both of the
following conditions exist?
Æ Owners and operators choose to
connect an anode to the metal
components in the sump for corrosion
protection and
Æ The sump is not used for interstitial
monitoring.
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
2. Spill Prevention Equipment Tests
What is EPA proposing?
In § 280.35, EPA is proposing owners
and operators test spill prevention
equipment (such as a catchment basin,
spill bucket, or other spill containment
device) at installation and at least once
every 12 months. This test must ensure
spill prevention equipment is liquid
tight by performing a vacuum, pressure,
or liquid test according to one of the
following:
• Requirements developed by the
manufacturer (Note that owners and
operators may use this option only if the
manufacturer developed spill
prevention equipment test
requirements);
• Code of practice developed by a
nationally recognized association or
independent testing laboratory; or
• Requirements determined by the
implementing agency to be no less
protective of human health and the
environment than the two bulleted
items above.
Exception: EPA is proposing spill
prevention equipment tests not be
required in those situations where spill
prevention equipment has two walls
and the space between the walls is
monitored continuously (interstitial
monitoring) to ensure the integrity of
both the inner and outer wall.
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EPA is proposing owners and
operators maintain the following:
• Records of spill prevention
equipment tests for three years; or
• Documentation showing the spill
prevention equipment has two walls
and is monitored continuously for each
spill prevention device installed at the
facility. Owners and operators must
maintain this documentation for as long
as the spill prevention equipment is
monitored continuously and for three
additional years after continuous
monitoring ends.
EPA is proposing owners and
operators meet this requirement within
one year after the effective date of the
final UST regulation for existing UST
systems and at installation for UST
systems installed after the effective date
of the final regulation.
Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing this change to help
ensure small releases occurring when
the delivery transfer hose is
disconnected from the fill pipe are
contained in the spill prevention
equipment. Owners and operators need
to properly operate and maintain their
spill prevention equipment in order to
prevent releases to the environment. If
a small release occurs at the fill port and
the spill prevention equipment is not
liquid tight, then the release can exit the
spill prevention equipment and reach
the environment. EPA is aware of
various problems with spill prevention
equipment. Examples include damage
due to: Vehicle drive over; ground
movement or freeze/thaw cycles;
inadequate installation practices; and
normal wear and tear. In addition, the
typical life of spill prevention
equipment is about three to seven years,
but the 1988 UST regulation does not
have a replacement requirement.
Today’s proposed periodic spill
prevention equipment test will
minimize problems and ensure spill
prevention equipment will contain
small releases from the delivery hose
when disconnected from the fill pipe.
EPA is proposing not to require
owners and operators of double-walled
spill prevention equipment with
continuous interstitial monitoring to
conduct annual tests because this spill
prevention equipment is continuously
checked for tightness through interstitial
monitoring. EPA is proposing owners
and operators in the monthly
walkthrough inspections visually check
continuous interstitial monitoring
methods that do not alert the owner and
operator with an alarm. Additional
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information on these inspections is
available in section B–1.
EPA is proposing to require vacuum,
pressure, or liquid methods when
testing spill prevention equipment. We
believe these options provide owners
and operators with significant flexibility
for testing this equipment.
EPA is proposing to specifically allow
owners and operators to use
manufacturer’s requirements or a code
of practice developed by a nationally
recognized association or independent
testing laboratory for spill prevention
equipment tests. The manufacturer’s
requirement is an option only when the
manufacturer has developed a testing
requirement. In response to today’s
proposed regulation, EPA anticipates
nationally recognized associations or
independent testing laboratories will
develop codes of practice for spill
prevention equipment tests and
manufacturers will develop testing
requirements. In addition, EPA is
providing implementing agencies
flexibility to allow other methods they
determine to be as protective of human
health and the environment as the
manufacturer’s requirements or a code
of practice. This option allows
alternatives in the event codes of
practice and manufacturer’s testing
requirements are not developed.
EPA is proposing owners and
operators conduct spill prevention
equipment tests at least once every 12
months. We propose this frequency
because spill prevention equipment is
prone to problems that can occur over
the course of a year and frequent tests
will catch problems earlier. In addition,
testing every 12 months is consistent
with other testing requirements, such as
annual automatic line leak detector
testing, in the 1988 regulation.
EPA is proposing owners and
operators maintain spill prevention
equipment test records three years for
each spill containment device at a
facility. These records will enable
implementing agencies to determine
whether owners and operators
conducted annual spill prevention
equipment testing during the three year
inspections required by the Energy
Policy Act. These records will also
demonstrate that owners and operators
tested their spill prevention equipment,
ensuring it will contain small drips and
spills that can occur when the transfer
hose is disconnected from the fill pipe.
In order for double-walled spill
prevention equipment with continuous
interstitial monitoring to be exempt
from spill prevention equipment tests,
owners and operators will need to
maintain documentation showing spill
prevention equipment has two walls
and uses continuous interstitial
monitoring. In addition, EPA is
proposing owners and operators
maintain this documentation for three
years after continuous interstitial
monitoring ends. EPA is proposing
maintaining this documentation so
owners and operators can demonstrate
compliance with the spill prevention
equipment testing requirement.
What issues related to this change does
EPA request comment or additional
data on?
• Is a 12 month frequency an
appropriate time frame for spill
prevention equipment tests? For
example, should EPA consider more
frequent tests in sensitive areas, such as
source water protection areas?
• Are there other acceptable test
methods in addition to vacuum,
pressure, or liquid spill prevention
equipment tests?
• Is the one year time frame proposed
for owners and operators to begin
implementing this requirement
reasonable?
Please provide reasoning or
justification if you disagree with or
71721
propose something different from EPA’s
proposal.
3. Overfill Prevention Equipment Tests
What is EPA proposing?
In § 280.35, EPA is proposing owners
and operators test proper operation of
overfill prevention equipment
(automatic shutoff devices, flow
restrictors, and high level alarms) at
installation and at least once every three
years. The test must ensure overfill
prevention equipment is set to activate
at the appropriate level in the tank (as
specified in § 280.20(c)) and the
equipment will activate when the
regulated substance reaches that height.
EPA is proposing owners and operators
test according to one of the following:
• Requirements developed by the
manufacturer (Note that owners and
operators may use this option only if the
manufacturer developed overfill
prevention equipment test
requirements);
• Code of practice developed by a
nationally recognized association or
independent testing laboratory; or
• Requirements determined by the
implementing agency to be no less
protective of human health and the
environment than the two bulleted
items above.
EPA is proposing owners and
operators maintain records of overfill
prevention equipment tests for three
years for each overfill device installed at
a facility.
For UST systems installed after the
effective date of the final UST
regulation, EPA is proposing owners
and operators meet this requirement at
installation. For UST systems installed
on or before the final UST regulation is
effective, EPA is proposing owners and
operators meet this requirement within
three years and according to the time
frames in the following table:
PHASE-IN SCHEDULE FOR OVERFILL PREVENTION EQUIPMENT TESTS
Criteria
Date by which first test must be conducted
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One or more USTs at the facility were installed on or before 12/22/1988 .....................................
No USTs at the facility were installed on or before 12/22/1988 and at least one UST at the facility was installed on or before 12/22/1998.
All USTs at the facility were installed after 12/22/1998 ...................................................................
Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing this change to help
ensure overfill prevention equipment is
operating properly and will activate
before an UST is overfilled. Owners and
operators need to properly operate and
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maintain their overfill prevention
equipment in order to prevent releases
to the environment. If overfill
prevention equipment is not working
properly, an UST can be overfilled and
release product to the environment. EPA
is aware that USTs are being overfilled
and there are problems with overfill
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One year after effective date of rule.
Two years after effective date of rule.
Three years after effective date of rule.
prevention equipment. Examples
include: Tampering; improper use; and
normal wear and tear. The proposed
periodic overfill prevention equipment
tests will minimize problems and
ensure overfill prevention equipment is
operating properly.
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Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
Overfill prevention test methods
should not overfill the tank to determine
whether overfill prevention equipment
is operating properly. Rather, the
equipment should be tested or inspected
to determine whether it will operate or
activate properly according to
requirements set forth in the UST
regulation. For example, a test or
inspection for an automatic shutoff
device in the fill pipe might include
removing the device and checking it for
the ability to operate and measuring the
position of the device in the tank to
determine whether it will activate at the
correct height.
For overfill prevention equipment
tests, EPA is proposing owners and
operators use manufacturer’s
requirements or a code of practice
developed by a nationally recognized
association or independent testing
laboratory. The manufacturer’s
requirement is an option only when the
manufacturer has developed a testing
requirement. In response to this
proposed regulation, EPA anticipates
nationally recognized associations or
independent testing laboratories will
develop codes of practice for overfill
prevention equipment tests, and
manufacturers will develop testing
requirements. In addition, EPA is
providing implementing agencies
flexibility to allow other methods they
determine to be as protective of human
health and the environment as the
manufacturer’s requirements or a code
of practice. This option allows
alternatives in the event that codes of
practice and manufacturer’s testing
requirements are not developed.
EPA is proposing owners and
operators conduct overfill prevention
equipment tests at least once every three
years. We propose this frequency
because overfill prevention equipment
is less prone to problems than spill
prevention equipment, but still needs
periodic testing. In addition, a three
year time frame is consistent with other
testing requirements, such as cathodic
protection testing and the proposed
three year interstitial integrity testing.
EPA is proposing to stagger
implementation over a three year period
based on the installation date of the
oldest UST at the facility. The proposed
phase-in will require overfill prevention
equipment in older UST systems that
pose a greater risk to the environment to
be tested first. The phase-in approach
will allow overfill prevention
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equipment tests to be spread out and
reduce the risk of a last-minute rush of
owners and operators obtaining overfill
prevention equipment tests at the end of
the initial three-year period.
EPA is proposing owners and
operators maintain overfill prevention
equipment test records for three years
for each overfill device at a facility.
These records will demonstrate to
implementing agencies that the overfill
prevention equipment has been tested,
is set at the appropriate height in the
tank, and will activate when regulated
substances reach that height. EPA is
proposing owners and operators
maintain records for three years to
coincide with the three year inspection
frequency required by the Energy Policy
Act.
What issues related to this change does
EPA request comment or additional
data on?
• Is a three year frequency an
appropriate time frame for overfill
prevention equipment tests? For
example, should EPA consider more
frequent tests in sensitive areas such as
source water protection areas? Should
EPA consider less frequent testing?
• Should EPA consider owners and
operators retain overfill prevention
equipment test records for a different
time frame?
• Is the three year time frame and
phase-in proposed for owners and
operators to begin implementing this
requirement reasonable?
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
4. Secondary Containment Tests
What is EPA proposing?
In § 280.36, EPA is proposing owners
and operators test secondary
containment areas that use interstitial
monitoring at least once every three
years. A secondary containment test
(also called an interstitial integrity test)
is performed in the space between tank
walls, pipe walls, or in a secondary
containment sump area and ensures the
area being tested has integrity and will
contain a leak. Secondary containment
areas include tank and piping
interstitial areas, as well as containment
sumps used as part of the piping
secondary containment and interstitial
monitoring. EPA is proposing owners
and operators test interstitial integrity
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areas using a vacuum, pressure, or
liquid method according to one of the
following:
• Requirements developed by the
manufacturer (Note that owners and
operators may use this option only if the
manufacturer developed interstitial
integrity test requirements);
• Code of practice developed by a
nationally recognized association or
independent testing laboratory; or
• Requirements determined by the
implementing agency to be no less
protective of human health and the
environment than the two bulleted
items above.
Exceptions: EPA is proposing the
following exceptions apply to
interstitial integrity tests:
• Tanks—Owners and operators
using continuous interstitial monitoring
on their tanks will not be required to
perform periodic interstitial integrity
tests.
• Piping—Owners and operators
using vacuum monitoring, pressure
monitoring, or liquid-filled interstitial
space monitoring on their underground
piping will not be required to perform
periodic interstitial integrity tests.
• Containment sumps—Owners and
operators using containment sumps
which have two walls and continuously
monitor the interstitial space between
the walls for releases will not be
required to perform interstitial integrity
tests.
EPA is proposing owners and
operators maintain the following:
• Records of interstitial integrity tests
for three years; or
• Documentation demonstrating that
the tanks, piping, or containment sumps
are not required to have a periodic
interstitial integrity test according to the
exceptions above. Owners and operators
must maintain this documentation for as
long as the tank, piping, or containment
sump uses one of the continuous
methods listed in the exceptions and for
three additional years after continuous
monitoring ends.
For UST systems installed after the
effective date of the final UST
regulation, EPA is proposing owners
and operators meet this requirement at
installation. For UST systems installed
on or before the final UST regulation is
effective, EPA is proposing owners and
operators meet this requirement within
three years and according to the time
frames in the following table:
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Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
71723
PHASE-IN SCHEDULE FOR INTERSTITIAL INTEGRITY TESTS
Criteria
Date by which first test must be conducted
One or more USTs at the facility were installed on or before 12/22/1988 .....................................
No USTs at the facility were installed on or before 12/22/1988 and at least one UST at the facility was installed on or before 12/22/1998.
All USTs at the facility were installed after 12/22/1998 ...................................................................
This proposed requirement only applies
to UST systems using interstitial
monitoring. It does not apply to UST
systems without secondary containment
or those with secondary containment
but not using interstitial monitoring for
release detection.
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
Why is EPA proposing this change?
What background information is
available about this change?
The Energy Policy Act requires states
that receive federal Subtitle I money
implement additional measures to
protect groundwater, either with
secondary containment for new and
replaced tanks and piping or financial
responsibility for manufacturers and
installers. 54 of 56 states have
implemented the secondary
containment option. To ensure
secondary containment is working
properly, the integrity of the interstitial
space needs to be tested. Therefore, EPA
is proposing periodic interstitial
integrity tests of the interstitial space in
secondarily-contained UST systems
which use interstitial monitoring for
release detection. These systems need to
contain a leak until interstitial
monitoring detects the regulated
substance. Currently, EPA has no
requirement for ensuring the integrity of
secondary containment areas.
Since most states implemented the
secondary containment requirements in
the Energy Policy Act for most new and
replaced tanks and piping, new and
replaced UST systems will be
secondarily contained with interstitial
monitoring. This requirement signals a
move from non-secondarily contained
UST systems using methods of release
detection that detect a release only after
regulated substances have reached the
environment to secondary containment
with interstitial monitoring that
identifies a problem before regulated
substances reach the environment.
Interstitial integrity tests will confirm
for owners and operators that secondary
containment will contain a leak until it
is detected and the problem is repaired.
Some interstitial monitoring methods
for tanks, piping, and containment
sumps already continuously ensure the
interstitial area’s integrity. When an
owner or operator uses one of these
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methods, EPA will not require periodic
interstitial integrity tests.
• Tanks—According to EPA’s source
and cause of release information, tanks
are not the leading source of
releases 24 25 In addition, tanks are
nearly always constructed in a factory
under controlled conditions, making it
less likely problems will occur in
interstitial areas after installation. For
these reasons, EPA proposes not to
require owners and operators to conduct
periodic interstitial integrity tests of
tanks using continuous interstitial
monitoring. Methods of continuous
interstitial monitoring for tanks include
liquid filled, vacuum, pressure, and
sensors in the interstitial space.
• Piping—EPA’s source and cause of
release information shows that a
significant number of releases occur
from piping.26 27 In addition, piping and
containment sumps are assembled in
the field during the installation process,
potentially creating increased
opportunities for releases. Therefore,
unless owners and operators use
continuous liquid-filled, vacuum, or
pressure interstitial monitoring for
piping release detection, EPA is
proposing to require periodic interstitial
integrity testing for piping. For example,
owners and operators who choose to use
sensors in containment sumps for
piping interstitial monitoring must also
perform three year interstitial integrity
tests of the piping interstitial space.
• Containment sumps—Similar to
piping, EPA’s source and cause of
release information shows that a
significant number of releases occur in
containment sump areas. EPA is also
aware of issues with the tightness of
containment sumps. Based on this
information, EPA is proposing owners
and operators conduct periodic
interstitial integrity tests of containment
sumps used for piping interstitial
24 Petroleum Releases At Underground Storage
Tank Facilities In Florida, Peer Review Draft, U.S.
EPA/OUST, March 2005.
25 Evaluation Of Releases From New And
Upgraded Underground Storage Tanks, Peer Review
Draft, U.S. EPA/OUST, August 2004.
26 Petroleum Releases At Underground Storage
Tank Facilities In Florida, Peer Review Draft, U.S.
EPA/OUST, March 2005.
27 Evaluation Of Releases From New And
Upgraded Underground Storage Tanks, Peer Review
Draft, U.S. EPA/OUST, August 2004.
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One year after effective date of rule.
Two years after effective date of rule.
Three years after effective date of rule.
monitoring, unless the containment
sump has two walls and the interstitial
space between the walls in the sump is
continuously monitored. For example, if
an owner or operator has a doublewalled containment sump and uses a
sensor, vacuum, pressure, or liquidfilled interstitial area to continuously
monitor the space between the two
walls, then periodic interstitial integrity
tests of that sump are not required
under this proposal. Owners and
operators of double-walled sumps
without continuous interstitial
monitoring must perform three year
interstitial integrity tests.
Continuous interstitial monitoring
means the secondary containment space
is monitored all the time by a method
or device and owners and operators
check the continuous monitoring
method or device for a leak at least once
every 30 days. In addition, owners and
operators must immediately respond to
any alarms they encounter. Methods of
continuous interstitial monitoring
include vacuum, pressure, and liquidfilled interstitial areas along with
sensors and probes located in the
interstitial area.
EPA is proposing owners and
operators conduct interstitial integrity
tests for tanks, piping, and sumps at
least once every three years. EPA is
proposing this frequency because we
believe secondarily contained UST
systems are much less prone to releases
than single-walled UST systems.
However, since owners and operators
are relying on the interstitial space to
detect problems, the interstitial areas
still need periodic tests to ensure proper
operation and maintenance. A three
year time frame is consistent with other
testing requirements, such as cathodic
protection testing and the proposed
overfill prevention equipment testing.
EPA is proposing to stagger
implementation over a three year period
based on the installation date of the
oldest UST at the facility. The proposed
phase-in will require older UST systems
that may pose a greater risk to the
environment to be tested first. The
phase-in approach will allow interstitial
tests to be spread out and reduce the
risk of a last-minute rush of owners and
operators obtaining tests at the end of
the initial three-year period.
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Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
EPA is proposing owners and
operators maintain interstitial integrity
test records for three years for each
regulated tank, pipe, and containment
sump at a facility or maintain
documentation demonstrating periodic
interstitial integrity tests are not
required. Documentation supporting
that periodic interstitial integrity tests
are not required could include: the tank
or piping uses vacuum, pressure, or
liquid-filled interstitial monitoring; the
tank uses continuous interstitial sensors
for interstitial monitoring; or the
containment sump has two walls and
the space between the containment
sump walls is continuously monitored.
In addition, EPA is proposing owners
and operators maintain this
documentation for three years after
continuous interstitial monitoring ends.
EPA is proposing owners and operators
maintain this documentation so they
can demonstrate to implementing
agencies compliance with the interstitial
integrity test requirement. This
documentation coincides with the three
year inspection requirements in the
Energy Policy Act.
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
What issues related to this change does
EPA request comment or additional
data on?
• Is a three year frequency an
appropriate time frame for interstitial
integrity tests? For example, should EPA
consider more frequent tests in sensitive
areas such as source water protection
areas?
• Should EPA consider owners and
operators retain records of interstitial
integrity tests for a different time frame?
• Should EPA consider interstitial
integrity tests for tanks using
continuous interstitial sensors? Should
EPA consider limiting this exclusion to
discriminating sensors?
• Is there a need for a phased-in
schedule to implement this
requirement? Is the three year time
frame and phase-in proposed for owners
and operators to begin implementing
this requirement reasonable?
Please provide reasoning or justification
if you disagree with or propose
something different from EPA’s
proposal.
5. Operation and Maintenance
Requirements for Release Detection
Equipment
What is EPA proposing?
In § 280.40, EPA is proposing UST
owners and operators perform annual
operation and maintenance tests on
electronic and mechanical components
of their release detection equipment to
ensure the equipment is operating
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properly. Owners and operators will be
required to check the following
equipment:
• ATG and other controllers
Æ Test alarm;
Æ Verify system configuration; and
Æ Test battery back-up.
• Probes and sensors
Æ Inspect for residual build-up;
Æ Ensure floats move freely;
Æ Ensure shaft is not damaged;
Æ Ensure cables are free of kinks,
bends, and breaks; and
Æ Test alarm operability and
communication with controller.
• Line leak detector
Æ Simulate leak which determines
capability to detect a leak; and
Æ Inspect leak sensing o-ring.
• Vacuum pumps and pressure gauges
Æ Ensure communication with sensors
and controller.
EPA is proposing owners and operators
meet this requirement according to one
of the following: manufacturer’s
instructions; a code of practice
developed by a nationally recognized
association or independent testing
laboratory; or requirements developed
by the implementing agency.
EPA is proposing owners and
operators maintain records of the annual
operation tests for three years. At a
minimum, records must: list each
component tested; indicate whether
each component met the criteria listed
above or needed to have action taken;
and describe any action taken to correct
an issue.
EPA is proposing owners and
operators begin meeting this
requirement no later than one year after
the effective date of the final UST
regulation.
Why is EPA proposing this change?
What background information is
available about this change?
EPA is concerned about the
performance of release detection
equipment. Inspectors routinely find
release detection equipment installed on
UST systems, but that equipment is not
properly operated and maintained. In
addition, information from an analysis
in Florida indicates, ‘‘Leak detection
successfully detected 26 percent of all
releases. Conversely, leak detection was
specifically identified as failing to
detect 23 percent of releases.’’ The
analysis also says the exact reason for
the leak detection failure could not be
determined. However, the analysis
provided these possible reasons, ‘‘* * *
faulty equipment; improper installation;
operation or maintenance; or
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insufficient performance standards.’’ 28
To increase the effectiveness of release
detection, EPA is targeting operation
and maintenance.
The 1988 UST regulation in
§ 280.40(a)(2) requires that release
detection ‘‘Is installed, calibrated,
operated, and maintained in accordance
with the manufacturer’s instructions,
including routine maintenance and
service checks for operability or running
condition;’’. Most owners and operators
installed the required release detection
equipment, but some owners and
operators are not properly operating and
maintaining their equipment. To
achieve optimal performance from
equipment and meet release detection
requirements, it is important for UST
system owners and operators to both
install the equipment and properly
operate and maintain it. In the 1988
UST regulation, EPA did not provide
specifics on minimum requirements to
ensure adequate operation and
maintenance of release detection
equipment. As a result, operation and
maintenance requirements vary greatly,
even between similar types of
equipment.
Some manufacturers’ requirements do
not adequately address operation and
maintenance. For example, some
manufacturers only recommend
operation and maintenance checks; but
EPA is taking the position that checks
should be mandatory instead of
optional. In addition, similar release
detection components should be tested
in a similar manner, which will increase
the likelihood all release detection
equipment will function at optimal
levels for as long as possible.
California’s in-field analysis of sensors
used for release detection and anecdotal
feedback supports EPA’s belief. 29
EPA is proposing this change to
improve and standardize operation and
maintenance for all release detection
equipment. This proposed change will
provide owners and operators with an
understanding of equipment tests
necessary to ensure equipment is
properly operated and maintained. EPA
is proposing a set of minimum operation
and maintenance criteria owners and
operators must follow for all electronicand mechanical-based release detection
equipment. EPA is also addressing
equipment that is neither electronically
nor mechanically based (for example,
28 Petroleum Releases At Underground Storage
Tank Facilities In Florida, Peer Review Draft, U.S.
EPA/OUST, March 2005.
29 California’s ‘‘Field Evaluation Of Underground
Storage Tank System Leak Detection Sensors,’’
August 2002. https://www.waterboards.ca.gov/
water_issues/programs/ust/leak_prevention/
sensors/index.shtml.
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bailers and measuring sticks used for
activities such as statistical inventory
reconciliation [SIR]) separately under
the walkthrough inspections section
(see section B–1).
EPA based these proposed operation
and maintenance minimum
requirements for release detection on
common requirements and
recommendations by various equipment
manufacturers of similar equipment.
EPA used the National Work Group on
Leak Detection Evaluation’s (NWGLDE)
list of leak detection equipment to
identify commonly used equipment.30
In addition, EPA’s publication,
Operating And Maintaining
Underground Storage Tanks Systems:
Practical Help And Checklists and
Petroleum Equipment Institute’s
Recommended Practices for the
Inspection and Maintenance of UST
Systems (RP 900) also helped establish
proper operation and maintenance
activities.
Regarding our proposal to use a code
of practice developed by a nationally
recognized association or independent
testing laboratory, EPA knows of one
code of practice currently being
developed that may address operability
testing for release detection equipment.
After that code of practice is final, EPA
will review it and decide whether to
include it in the final UST regulation.
EPA is proposing owners and
operators maintain records of annual
operation tests for three years. Results of
tests must include: a list of each
component tested; whether it tested
acceptable or needed action; and a
description of any action taken to
correct an issue. Three years worth of
records are consistent with the three
year inspection cycle, and content of the
records will allow owners and operators
to demonstrate compliance with this
operation and maintenance
requirement.
Finally, EPA is allowing owners and
operators up to one year from the
effective date of the final UST regulation
to meet this requirement. One year is
consistent with the annual test
frequency requirement already in place
for automatic line leak detectors, and
many third-party service providers
nationwide already perform the testing.
What issues related to this change does
EPA request comment or additional
data on?
• Are the proposed minimum
operation and maintenance
30 National Work Group On Leak Detection
Evaluation’s (NWGLDE) List Of Leak Detection
Evaluations For Storage Tank Systems: https://
www.nwglde.org/.
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requirements sufficient to cover release
detection equipment on regulated UST
systems?
• Are there additional performance
tests EPA should consider?
Please provide reasoning or justification
if you disagree with or propose
something different from EPA’s
proposal.
C. Addressing Deferrals
Note about the overlap of UST
regulations and Spill Prevention Control
and Countermeasures (SPCC)
regulations: At the time of the 1988 UST
regulation, facilities with an aggregate
completely buried storage capacity
greater than 42,000 gallons and located
near navigable waters of the U.S. or
adjoining shorelines were subject to
both UST rules and SPCC rules. Since
then, SPCC rules have been amended
and the rule exempts completely buried
storage tanks, as well as connected
underground piping, underground
ancillary equipment, and containment
systems, when subject to the technical
requirements of 40 CFR part 280. In
today’s proposal, EPA proposes to
continue to defer the aboveground
components associated with airport
hydrant systems and USTs with fieldconstructed tanks. Only those deferred
aboveground components will be
subject to SPCC requirements. EPA is
proposing to regulate the underground
components associated with airport
hydrant systems and USTs with fieldconstructed tanks. In addition, EPA is
proposing to regulate wastewater
treatment tank systems and UST
systems that store fuel solely for use by
emergency power generators deferred
under the 1988 regulation. Once the
proposal becomes final, these UST
systems will no longer be subject to
SPCC requirements.
1. Emergency Power Generator UST
Systems
What is EPA proposing?
EPA is proposing to eliminate the
current deferral in § 280.10(d) for UST
systems storing fuel solely for use by
emergency power generators. This
means emergency power generator USTs
will no longer be deferred from release
detection requirements in 40 CFR part
280, subpart D and will be subject to all
UST requirements.
In addition, EPA is proposing that, no
later than 30 days after the effective date
of the final UST regulation, owners of
UST systems storing fuel solely for use
by emergency power generators notify
appropriate implementing agencies that
their systems exist.
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71725
EPA is proposing owners and
operators of UST systems storing fuel
solely for use by emergency power
generators begin meeting these
requirements as follows:
• For systems installed after the
effective date of the final UST
regulation, at the time of installation.
• For systems installed on or before
the effective date of the final UST
regulation, within one year of the
effective date of the final UST
regulation.
Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing to regulate UST
systems storing fuel solely for use by
emergency power generators because
our previous rationale for deferring
release detection no longer applies. To
allow time for developing workable
release detection requirements, EPA in
the 1988 UST regulation deferred
release detection requirements for UST
systems storing fuel solely for use by
emergency power generators. The 1988
UST regulation preamble indicated that
monthly monitoring requirements were
unworkable because these tanks often
were located at unmanned stations in
remote areas and visited infrequently.
EPA always intended for these
systems to meet release detection
requirements when appropriate release
detection methods became available.
Since the 1988 UST regulation, release
detection technologies have matured
greatly. In addition, technology is now
available to perform release detection at
remote sites. Emergency generator tanks
and piping can now be monitored for
releases by the majority of methods
listed in § 280.43. EPA estimates about
30 percent of active UST systems storing
fuel solely for use by emergency power
generators already have release
detection.
Effective remote monitoring methods
for release detection are now available
and used to monitor unmanned UST
systems storing fuel solely for use by
emergency power generators. Numerous
contractors perform remote monitoring
for releases at these unmanned sites.
Remote monitors transmit visual or
audible alarms to a receiving console at
a manned location when there is a
suspected or confirmed release. This
provides owners and operators with
real-time release detection data for
immediate response to suspected or
confirmed releases at sites with
unmanned UST systems storing fuel
solely for use by emergency power
generators.
Emergency power generator UST
systems are located throughout the
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country. EPA’s review of several state
databases revealed these systems are
located at hospitals, universities,
communication utilities, military
installations, and other locations relying
on backup power sources. EPA
estimates UST systems storing fuel
solely for use by emergency power
generators now represent approximately
3 percent of the active tank
population.31
Additionally, 21 states currently
require release detection for emergency
power generator UST systems.
Automatic tank gauging and secondary
containment with interstitial monitoring
are the most common release detection
methods used for tanks associated with
these systems. Line tightness testing,
line leak detectors, or secondary
containment with interstitial monitoring
are the most common release detection
methods used for piping. Note that safe
suction piping does not require release
detection. With technology now
available to detect releases from
emergency power generator UST
systems and because these systems pose
the same risk to human health and the
environment as any other UST system,
EPA is proposing to remove the deferral
from release detection.
EPA is proposing owners and
operators of emergency power generator
UST systems installed on or before the
effective date of the final UST regulation
begin performing release detection
within one year of the effective date of
the final regulation. EPA is taking the
position that one year is reasonable
because these USTs are fully regulated
except for release detection, and some
are already performing release
detection. After the effective date of the
final regulation, all emergency power
generator UST systems must include
release detection when installed.
Notification
To make implementing agencies
aware that emergency power generator
UST systems exist, EPA is proposing
owners of these systems submit a onetime notification to the implementing
agency. Owners must notify within 30
days of the effective date of the final
regulation. This will allow
implementing agencies to include
emergency power generator UST
systems in their inventories.
What issues related to this change does
EPA request comment or additional
data on?
• Is EPA’s estimate of 3 percent for
UST systems storing fuel solely for use
by emergency power generators
accurate?
• Are there technical concerns EPA
should address in requiring release
detection for emergency power
generator UST systems?
• Is EPA’s estimate of 30 percent
installed release detection on UST
systems storing fuel solely for use by
emergency power generators accurate?
• How many UST facilities have 10 or
more emergency power generator UST
systems? Who owns these facilities?
Please provide reasoning or justification
if you disagree with or propose
something different from EPA’s
proposal.
2. Airport Hydrant Fuel Distribution
Systems
What is EPA proposing?
EPA is proposing to regulate currently
deferred airport hydrant fuel
distribution systems (also referred to as
airport hydrant systems). This means
airport hydrant systems will no longer
be deferred from the requirements of 40
CFR part 280, subparts B (UST Systems:
Design, Construction, Installation and
Notification); C (General Operating
Requirements); D (Release Detection); E
(Release Reporting, Investigation, and
Confirmation); G (Out-of-Service UST
Systems and Closure); and H (Financial
Responsibility).
Airport hydrant systems installed on
or before the effective date of the final
UST regulation must begin meeting the
requirements of subparts B (except
§ 280.22) and C within three years of the
effective date of the final UST
regulation, subpart D according to the
schedule in the table below, and
§ 280.22 of subpart B along with
subparts E, G, and H on the effective
date of the final UST regulation. Airport
hydrant systems installed after the
effective date of the final UST regulation
must meet these requirements at the
time of installation. Airport hydrant
systems with aboveground storage tanks
(ASTs) directly connected to the
underground hydrant piping are not
regulated UST systems under 40 CFR
part 280, unless 10 percent or more of
the total capacity of the system,
including underground piping, is
beneath the surface of the ground.
SCHEDULE FOR PHASE IN OF SUBPART D
Component and type of release detection used
Piping using periodic pressurized
bulk line tightness testing.
Time frame
(after [effective date of rule])
Within three years.
Between years three and six
Between years six and seven.
Description of requirement
Conduct one piping tightness test according to the bulk line tightness
testing requirement using the maximum detectable leak rates for
semiannual testing. For bulk piping segments not capable of meeting the 3.0 gallon per hour leak rate, owners and operators may
use a leak rate of up to 6.0 gallons per hour.
Conduct one piping tightness test according to the bulk line tightness
testing requirement using the maximum detectable leak rates for
semiannual testing.
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After year seven.
All other piping and tank release
detection methods.
Begin conducting piping tightness testing according to the bulk line
tightness testing requirement.
Within three years.
Perform release detection according to this subpart.
EPA is proposing to define an airport
hydrant fuel distribution system as an
UST system that is a combination of one
or more tanks directly connected to
underground hydrant piping used to
fuel aircraft. These systems do not have
31 Industrial Economics, Inc., ‘‘Detailed
Assessment of UST Universe by Tank Use and
Industry Sector,’’ Work Assignment 1–15, Task 6,
January 23, 2009.
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a dispenser at the end of the piping run,
but rather a hydrant (fill stand). If an
AST is feeding an intermediary tank or
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tanks, this proposed definition does not
include the AST, but does include all
underground piping entering and
leaving intermediary tanks and the
intermediary tank(s). Intermediary tanks
are those tanks directly connected to the
hydrant piping.
Release Detection—Tanks
EPA is proposing airport hydrant
system tanks installed prior to the
effective date of the final UST regulation
meet these requirements:
• The following tanks must be
monitored using release detection
methods specified in § 280.43.
Æ Shop fabricated tanks.
Æ Field-constructed tanks with a
capacity less than or equal to 50,000
gallons.
• Field-constructed tanks with
capacity greater than 50,000 gallons
must either be monitored using release
detection methods specified in § 280.43
or use one of the alternatives for tanks
listed in section C–3—UST Systems
With Field-Constructed Tanks.
EPA is proposing new or replaced
airport hydrant system tanks installed
after the effective date of the final UST
regulation be secondarily contained and
perform interstitial monitoring
according to § 280.43(g).
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Release Detection—Piping
EPA is proposing airport hydrant
system piping meet these release
detection requirements:
• Piping must be monitored using
release detection methods specified in
§ 280.44; or
• Use one of these alternatives:
Perform a semiannual or annual bulk
line tightness test at or above operating
pressure in accordance with the table
below. Bulk piping segments ≥100,000
gallons not capable of meeting the
maximum 3.0 gallon per hour leak rate
for the semiannual test may be tested at
a leak rate up to 6.0 gallons per hour
according to the schedule in § 280.40(c):
MAXIMUM DETECTABLE LEAK RATE PER TEST SECTION VOLUME
Semiannual test
maximum detectable
leak rate
(gallons per hour)
<50,000 ..........................................................................................................................................
≥50,000 to <75,000 .......................................................................................................................
≥75,000 to <100,000 .....................................................................................................................
≥100,000 ........................................................................................................................................
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Test section volume
(gallons)
1.0
1.5
2.0
3.0
The bulk line tightness test must be
capable of detecting the maximum
detectible leak rate listed in the table
above with a probability of detection of
0.95 and a probability of false alarm of
0.05.
Æ Perform continuous interstitial
monitoring designed to detect a release
from any portion of the underground
piping that routinely contains product
according to § 280.43(g).
Æ Use an automatic line leak detector
that alerts the presence of a leak by
restricting or shutting off flow of
regulated substances through piping or
triggering an audible or visual alarm.
This method may be used only if it can
detect a leak of three gallons per hour
at 10 pounds per square inch line
pressure within one hour or equivalent.
When using this method, also:
–At least every three months, perform
interstitial monitoring, designed to
detect a release from any portion of the
underground piping that routinely
contains product, according to
§ 280.43(g); and
–Conduct an annual leak detector
operation test according to
§ 280.40(a)(3).
Æ The implementing agency may
approve another method if the owner
and operator can demonstrate the
method can detect a release as
effectively as any of the other three
methods. In comparing methods, the
implementing agency shall consider the
size of release the method can detect
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and frequency and reliability of
detection. Owners and operators must
comply with conditions imposed by the
implementing agency.
All recordkeeping requirements in
§ 280.45 apply to these proposed release
detection methods.
Release Prevention
EPA is proposing airport hydrant
systems meet corrosion protection, spill,
and overfill requirements. For corrosion
protection, EPA is proposing airport
hydrant systems meet one of these:
• The new tank and piping standards
described in § 280.20; or
• Airport hydrant systems installed
on or before the effective date of the
final UST regulation can be constructed
of metal and cathodically protected
according to a code of practice
developed by a nationally recognized
association or independent testing
laboratory and meet the following:
Æ Field installed cathodic protection
systems must be: designed by a
corrosion expert; designed to allow for
the determination of current operating
status for impressed current systems;
and operated and maintained in
accordance with § 280.31 or guidelines
established by the implementing
agency; and
Æ Tanks greater than 10 years old
without cathodic protection must be
assessed to ensure they are structurally
sound and free of corrosion holes prior
to adding cathodic protection. The
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Annual test maximum
detectable leak rate
(gallons per hour)
0.5
0.75
1.0
1.5
assessment must be by internal
inspection or another method the
implementing agency determines
adequately assesses the tank for
structural soundness and corrosion
holes.
EPA is proposing airport hydrant
systems installed on or before the
effective date of the final UST regulation
that are not upgraded according to
§ 280.21 within three years of the
effective date of the final UST regulation
be permanently closed according to
§ 280.70. EPA is proposing internal
lining not be allowed for meeting the
corrosion protection upgrade
requirement.
EPA is proposing to exclude new and
replaced piping in airport hydrant
systems from secondary containment
requirements in § 280.20(b).
Notification
EPA is proposing that, no later than
30 days after the effective date of the
final UST regulation, owners of
regulated airport hydrant systems
installed prior to the effective date of
final UST regulation notify appropriate
implementing agencies that their
systems exist.
Financial Responsibility
EPA is proposing airport hydrant
systems no longer be deferred. This
means airport hydrant systems that have
not been permanently closed will be
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subject to financial responsibility
requirements in subpart H.
Deferred Components
Aboveground components of airport
hydrant systems are currently regulated
by SPCC because they are not fully
regulated under the UST regulations.32
EPA is proposing to continue deferring
aboveground tanks associated with
airport hydrant systems that meet the
UST system definition from the
requirements of subparts B, C, D, E, and
G.
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Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing to regulate airport
hydrant systems because a release from
one of these systems may pose a
significant threat to human health and
the environment. In addition,
technology is now available for release
prevention and adequate release
detection monitoring. In some cases
airport hydrant system piping stores
millions of gallons of fuel; airport
hydrant systems handle large volumes
of regulated substances on a daily basis.
Leaks from underground piping and
other appurtenances can contaminate
subsurface soil beneath the airport
apron and runways, groundwater, and
nearby surface water. Even though there
is a small universe of these systems,
mainly owned by the Department of
Defense (DoD), evidence shows a
substantial release can have a major
impact on the environment.
For example, at Pease Air Force Base,
jet fuel was delivered to the runway
apron via an underground fueling
system. Throughout the life of the
system, releases contaminated soils and
groundwater, forming plumes of
regulated substances in the
groundwater.33 A site release study
identified 60 to 70 release points with
varying degrees of severity along the
refueling system line. Free product was
found under the apron when the
systems were closed.34 There are no
available historical records showing the
sources of release or the volumes of
regulated substances released. However,
32 Spill Prevention, Control, And Countermeasure
Rule. https://www.epa.gov/oem/content/spcc/
index.htm.
33 New Hampshire Department of Environmental
Services, Air Resources Division. 2009. Permit
Application Review Summary, Former Pease AFB
Remediation Project, 09–0113. 10 March 2010, see:
https://www2.des.state.nh.us/OneStopPub/Air/
330159094909-0113TypeSummary.pdf.
34 Hilton, Scott. Site Summaries Pease Air Force
Base Newington/Portsmouth. 2008. NH Department
of Environmental Services. 10 March 2010 see:
https://des.nh.gov/organization/divisions/waste/
hwrb/fss/superfund/summaries/pease.htm.
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the presence of soil and groundwater
contamination poses a significant threat
to public health and the environment.
In the 1988 UST regulation, EPA
deferred airport hydrant systems
because release detection and
prevention technologies were not
readily available for these unique
systems. Given current availability of
those technologies, requiring release
prevention equipment and regular
release detection tests are keys to
preventing and quickly identifying
releases before they contaminate the
surrounding environment. Additionally,
16 state UST programs which include
approximately 40 percent of the existing
universe of these UST systems, no
longer defer airport hydrant systems and
now regulate them.
EPA is proposing to define airport
hydrant system in order to clarify which
components of these systems will be
regulated. There is currently some
uncertainty about what an airport
hydrant system is because of the lack of
a federal definition and inconsistencies
between different state definitions.
Today’s proposed definition of airport
hydrant system clarifies which
components will be regulated. Examples
of tank and piping configurations for
airport hydrant systems can be found in
the docket for this proposed
rulemaking.35
EPA is proposing airport hydrant
systems installed on or before the
effective date of the final UST regulation
begin meeting the requirements of
subparts B (except § 280.22) and C
within three years of the effective date
of the final UST regulation, subpart D
according to the phase in schedule in
the table above, and § 280.22 of subpart
B along with subparts E, G, and H on the
effective date of the final UST
regulation. Airport hydrant systems
installed after the effective date of the
final UST regulation must meet all
requirements at installation. Three years
allows owners and operators enough
time to implement the requirements of
subparts B (except § 280.22) and C. EPA
is providing a phase in period for bulk
line tightness testing in subpart D to
allow owners and operators ample time
to upgrade their piping systems and
meet the leak rate criteria. EPA is
proposing to allow owners and
operators for the first six years (two test
periods) to meet a higher threshold of
up to 6.0 gallons per hour for those
piping segments that cannot meet the
more stringent maximum 3.0 gallons per
hour threshold due to technical reasons.
These technical reasons include
35 Example Tank and Piping Configurations for
Airport Hydrant Systems developed by EPA/OUST.
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exceeding capabilities of currently
available pressure-based methods to
achieve the required leak rate. Currently
available methods are capable of testing
larger volume test sections to a leak rate
of 6.0 gallons. The higher threshold of
6.0 gallons per hour provides for use of
existing test methods during the first six
year period. Six years will provide
owners and operators time to upgrade
their piping systems to meet the up to
3.0 gallon per hour threshold for
semiannual testing. Between years six
and seven of the phase in, EPA proposes
to allow owners and operators to
conduct one additional bulk tightness
test that meets the semiannual testing
threshold. Beginning in year seven,
owners and operators must begin
meeting the semiannual and annual
bulk line tightness testing requirements
described earlier in this section. For all
other tank and piping release detection
options, EPA is proposing a three year
phase in because these methods will not
require significant construction or
upgrades for implementation. Finally,
owners and operators can implement
the requirements of § 280.22 of subpart
B along with subparts E, G, and H
beginning on the effective date of the
final UST regulation because upgrades
or special equipment are not needed to
meet the requirements in these subparts.
Release Detection
EPA is proposing release detection for
airport hydrant systems because, unlike
in the 1980s, release detection
technologies are now available. Airport
hydrant systems typically consist of a
series of large diameter shop-fabricated
tanks; although some airport hydrant
systems use field-constructed tanks.
EPA is proposing release detection
requirements for shop-fabricated tanks
and field-constructed tanks in airport
hydrant systems. See section C–3 for
proposed release detection requirements
for UST systems with field-constructed
tanks.
EPA discussed airport hydrant
systems in the 1988 UST regulation
preamble. These systems were very
large, contained great volumes of fuel
(capacities in the millions of gallons),
and consisted of miles of piping that
was typically eight to 24 inches in
diameter. Airport hydrant systems
typically had cathodic protection and
were monitored for releases
periodically. Inventory control was
often used, but the sensitivity of this
technique was limited due to the large
volume airport hydrant systems
typically handled. No single leak test
appeared to be an industry standard.
Between proposing and finalizing the
1988 UST regulation, EPA became
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aware of several airport hydrant system
leaks that harmed the environment.
However, limited information kept EPA
from realizing the extent of airport
hydrant system problems. At the time,
EPA believed release detection was not
feasible for airport hydrant systems. To
allow more time to gather information,
EPA deferred airport hydrant systems in
the 1988 regulation from release
detection requirements in subpart D as
well as subparts B, C, E, G, and H
requirements.
Over the last 20 years, the petroleum
services industry developed release
detection monitoring technologies for
airport hydrant systems. NWGLDE’s list
in Large Diameter Line Leak Detection
Methods (6 Inches Diameter Or
Above) 36 identifies methods capable of
detecting releases from airport hydrant
systems.
EPA contacted several vendors to
determine strengths and limitations of
release detection methods for airport
hydrant systems. EPA also talked with
DoD’s Defense Logistics Agency (DLA)
Energy 37 about their challenges in
addressing release detection
requirements in states, such as
California, which do not defer airport
hydrant systems from release detection.
DLA Energy also monitors airport
hydrant systems in other states, which
provides them with significant
information about airport hydrant
system release detection.
EPA acknowledges airport hydrant
systems vary greatly and most of these
systems cannot meet underground
piping release detection requirements in
the 1988 UST regulation because of
issues such as time to conduct the test
and leak rate thresholds. Nonetheless,
other release detection methods are
currently available to monitor airport
hydrant systems. EPA is not proposing
release detection methods monitor at
the same leak rate or frequency as
pressurized piping systems at retail
service stations. Standard release
detection systems can successfully test
and detect releases on USTs and
pressurized piping at retail service
stations, but cannot achieve the same
accuracy within a reasonable time frame
on underground piping in airport
hydrant systems. The large diameters
and varying pipe lengths in airport
hydrant systems introduce variables that
prohibit accurate monitoring at leak
rates within a reasonable time frame
required in the 1988 UST regulation.
36 National Work Group On Leak Detection
Evaluation’s (NWGLDE) List Of Leak Detection
Evaluations For Storage Tank Systems: https://
www.nwglde.org/.
37 Defense Logistics Agency Energy was formerly
known as Defense Energy Support Center (DESC).
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Compared to typical retail service
stations, airport hydrant systems have
large product volume throughputs. The
1988 UST regulation release detection
test methods are limited by volume. To
produce accurate test results,
underground hydrant system piping
needs to be isolated in appropriately
sized segments. Some airport hydrant
systems have numerous isolation points
with available connections for release
detection equipment; others have up to
one-half mile between underground
piping segments available for accurate
testing. The greater the volume of a
segment, the more time it takes to obtain
a valid result at a given leak rate.
Product temperature fluctuations
present challenges for release detection
testing of airport hydrant system piping.
As temperatures fluctuate, product
expands or contracts, increasing or
decreasing product volume and
pressure. Fluctuating line pressure
during a release detection test can mask
an existing release or falsely indicate
one occurred. To lessen this, an out of
service period when testing large
diameter airport hydrant piping could
range from one to several days after the
last product transfer in order to meet
maximum leak detection rates in the
1988 UST regulation. Removing airport
hydrant systems from service for these
extended periods will greatly impede
their purpose. In contrast, out of service
periods on underground piping at retail
service stations can last up to several
hours after the last product transfer
prior to pressure testing.
Although technology is available, it
would be cost prohibitive and require
significant facility down time for
owners and operators to monitor airport
hydrant systems for releases at the rates
and frequencies required in the 1988
UST regulation.38 As a result, EPA is
proposing several options for owners
and operators to meet the release
detection requirement. These options
provide flexibility for a wide variety of
airport hydrant systems. In those
instances where airport hydrant systems
can meet the release detection methods
in § 280.43 and § 280.44, owners and
operators may use those methods. EPA
is also proposing the following four
alternatives to meet the airport hydrant
system release detection requirement for
piping.
38 See section F of this preamble and Regulatory
Impact Analysis (RIA) for the proposed rule,
available as a separate document in the docket, for
information on the cost differences between
meeting conventional release detection
requirements and the proposed alternative
requirements for airport hydrant systems and UST
systems with field-constructed tanks.
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• Perform semiannual or annual bulk
line testing at or above operating
pressure with a probability of detection
of 0.95 and a probability of false alarm
of 0.05. EPA thinks this will be the most
frequently used method due to cost and
minimal impact on down time for the
piping system. It allows owners and
operators to meet a variable leak rate
based on piping test section volume.
The leak rate ranges from one to three
gallons 39 per hour, depending on
piping volume for semiannual testing
and from 0.5 to 1.5 gallons per hour for
annual testing. EPA is proposing three
gallons per hour as the maximum
threshold because the majority of
available bulk line testing methods are
capable of meeting this leak detection
rate. To effectively detect leaks from the
pressurized piping systems, industry
practice involves performing pressurebased testing at levels above standard
operating pressure. EPA is proposing
requiring a test pressure at or above
operating pressure in consideration of
these bulk piping systems typically
operating at pressures much higher than
conventional gasoline stations. Testing
at 1.5 times operating pressure may not
be practical or safe for these piping
systems. The probabilities of detection
and false alarm are consistent with the
line leak detection requirements in the
1988 UST regulation.
• Use continuous interstitial
monitoring—This monitoring method is
designed to detect a release from any
portion of the underground piping that
routinely contains product; it must
operate in an uninterrupted manner.
EPA considered requiring an automatic
line leak detector in combination with
this alternative method, similar to
conventional pressurized piping
requirements in the 1988 UST
regulation. However, conventional line
leak detectors today cannot properly
operate on bulk pressurized piping in
airport hydrant systems.
• Use an automatic line leak
detector—Conventional pressurized
piping systems operate at a significantly
lower pressure than airport hydrant
systems. In addition, EPA is not aware
of a line leak detector that adequately
detects releases on airport hydrant
systems. Yet because some states
regulate airport hydrant systems and
industry has experience with these
systems, comparable release detection
technology may be developed in the
future. With that in mind, EPA is
39 Owners and operators of bulk piping systems
with test section volumes of 100,000 gallons or
greater, due to technical reasons discussed in this
section, may test their systems at a higher threshold
of up to 6.0 gallons per hour within the six year
phase-in period.
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proposing line leak detectors be capable
of detecting a release rate of three
gallons per hour at 10 pounds per
square inch line pressure within one
hour or equivalent. This is consistent
with the 1988 UST regulation. To detect
a release from any portion of the
underground piping that routinely
contains product, EPA is proposing to
combine this alternative with interstitial
monitoring performed at least once
every three months. This combination
will quickly detect catastrophic releases
while checking for much smaller
problems on a less frequent—every
three month—basis. Owners and
operators will be required to conduct an
annual test of the line leak detector’s
operation according to the final UST
regulation. See section B–5 for more
information on the annual test.
• Approval by the implementing
agency of another method if the owner
and operator can demonstrate that the
method can detect a release as
effectively as any of the methods listed
above—The implementing agency must
consider the size of the release that the
method can detect as well as the
frequency and reliability of detection
when comparing methods. Owners and
operators must comply with any
conditions imposed by the
implementing agency on the method’s
use.
Release Prevention
In § 280.20, EPA is proposing new or
replaced tanks and piping have
secondary containment with interstitial
monitoring. Airport hydrant systems’
piping ranges from eight to 24 inches in
diameter with very long lengths,
sometimes miles. In contrast,
pressurized piping at a typical retail gas
station is two inches in diameter with
relatively short lengths.
EPA discussed with DLA Energy and
industry the feasibility of installing
secondary containment on piping
associated with airport hydrant systems.
These systems, primarily located on
military installations, are complex and
lack similarity. EPA is taking the
position that installing secondary
containment on airport hydrant system
piping may be impracticable.
To detect a leak, secondary
containment must be a liquid tight
barrier designed to hold the leak
between the tank and the barrier. Piping
is sloped in fractions of an inch per foot
of piping run to direct a leak toward the
interstitial monitor. Because airport
hydrant system piping lengths can
typically be thousands of feet, it would
be very difficult to install a system with
enough slope that could adequately
monitor the lowest point of a piping
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run. In addition, variable sized fittings
are needed to join different diameters of
piping, increasing the complexity of
installing secondary containment.
Finally, airport hydrant system piping is
normally constructed of steel.
Condensation can accumulate between
the inner and outer walls, promoting
corrosion of both pipe walls in the
interstitial space and increasing the
likelihood of a release to the
environment.
EPA acknowledges engineering and
design challenges (that is, varying
piping diameter and length, along with
corrosion) that can occur when
providing secondary containment for
piping associated with airport hydrant
systems.40 Therefore, EPA is proposing
not to require this piping meet
secondary containment requirements.
However, EPA is proposing new and
replaced underground tanks associated
with airport hydrant systems meet
secondary containment requirements.
See section A–2 for more information
about proposed secondary containment
requirements for tanks.
As with all other regulated UST
systems, EPA is proposing all airport
hydrant systems meet corrosion
protection requirements. Because
interim prohibition has been in effect
since May 1985, these systems generally
are already equipped with corrosion
protection (that is, constructed of: noncorrodible material; coated and
cathodically protected steel; fiberglass
reinforced plastic; or steel tank clad
with fiberglass reinforced plastic).
EPA is proposing not to allow adding
internal lining as a means of corrosion
protection for tanks in airport hydrant
systems that are not already upgraded.
In the 1988 UST regulation, EPA
allowed internal lining as a corrosion
protection upgrade, but stated in the
preamble that internal lining of steel
tanks was a temporary upgrade to meet
corrosion protection requirements, only
if the lining continued meeting original
design specifications. After 1998, if an
inspected lining did not meet original
design specifications and could not be
repaired according to industry codes, it
no longer met the upgrade requirements
and had to be replaced. In addition,
lining inspections show there are issues
with internal linings.41 Reports of
premature failures due to improper
installation cause additional concerns
about the long-term integrity of the
40 DOD’s
DLA Energy, ‘‘Response to EPA—
Release Detection Point Paper,’’ dated 03/10.
41 LUSTLINE, Bulletin 38, June 2001. https://
www.neiwpcc.org/lustline/.
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lining.42 A study of lined tanks up to12
years old concluded that 44 percent of
tanks’ linings were cracked, discolored,
and flaked from tank walls.43 If internal
lining fails, the chance of a leak into the
environment is greater when there is no
external corrosion protection on the
tank. Because of these concerns, EPA is
proposing internal lining not be an
option for meeting the corrosion
protection requirements for tanks in
airport hydrant systems.
As with all other regulated UST
systems, EPA is proposing airport
hydrant systems meet spill and overfill
requirements to prevent releases to the
environment. After discussion with
industry and DLA Energy, EPA is taking
the position that existing airport
hydrant systems are already equipped
with spill prevention devices that will
adequately prevent spills and overfills.
Airport hydrant systems installed on
or before the effective date of the final
UST regulation that do not meet the
upgrade requirements within three years
after the effective date of the rule must
be permanently closed according to
§ 280.70. EPA is requiring permanent
closure to prevent releases to the
environment from airport hydrant
systems that have not been upgraded.
Notification
To make implementing agencies
aware airport hydrant systems exist,
EPA is proposing owners of these
systems submit a one-time notification
to the implementing agency. Owners
must notify within 30 days of the
effective date of the final regulation.
This will allow implementing agencies
to include airport hydrant systems in
their inventories.
Financial Responsibility
Because EPA is proposing to
eliminate the deferral for airport
hydrant systems, they will no longer be
exempt from financial responsibility
requirements in subpart H. Owners and
operators will be required to comply by
the effective date of the final UST
regulation. The 1988 UST financial
responsibility regulation exempts state
and federal entities. Therefore, federal
and state owners and operators of
airport hydrant systems will not have to
meet the financial responsibility
requirement. Nearly all airport hydrant
systems are owned by the federal
government.
42 Wisconsin Department Of Commerce Web site:
https://www.commerce.state.wi.us/er/pdf/bst/
ProgramLetters_PL/ER-BST-PL-LINING.pdf.
43 LUSTLINE, Bulletin 30, September 1998.
https://www.neiwpcc.org/lustline/.
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Deferred Components
EPA is proposing to continue
deferring aboveground tanks associated
with airport hydrant systems from the
requirements of subparts B, C, D, E, and
G. EPA regulates underground storage
tanks and piping through 40 CFR part
280 and aboveground tanks through 40
CFR part 112 (Oil Pollution Prevention).
Facilities with 1,320 gallons of
aboveground oil storage capacity that
could reasonably be expected to
discharge oil into navigable waters or
adjoining shoreline are subject to the
SPCC regulation, under the authority of
the Clean Water Act (CWA).44 The SPCC
regulation includes requirements for oil
spill prevention, preparedness, and
response to prevent oil discharges to
navigable waters and adjoining
shorelines.45 The SPCC regulation
requires periodic integrity testing and
inspection of bulk storage containers
and periodic integrity testing and leak
testing of valves and piping associated
with containers. The SPCC regulation
also requires regulated facilities prepare
and maintain a written plan that
includes measures to prevent, prepare
for, and respond to oil discharges that
threaten navigable waters and adjoining
shorelines. For these reasons, we believe
the SPCC regulation is the most effective
means of addressing aboveground tanks
associated with airport hydrant systems.
What issues related to this change does
EPA request comment or additional
data on?
• Are the release detection options
and time frames appropriate and
sufficient?
• Is the performance requirement of
three gallons per hour at 10 pounds per
square inch line pressure within one
hour or equivalent proposed for line
leak detectors for bulk piping
appropriate?
• Should EPA consider including
specific requirements for nonpressurized piping tightness testing
methods such as chemical marker
methods? If so, what should those
requirements be?
• Are there other release detection
options EPA should consider?
• In order to address potential
concerns associated with over
pressurizing bulk piping systems, EPA
proposed testing at the system’s
operating pressure instead of above it.
EPA understands there are industry
standards that recommend testing above
operating pressure. Is testing these
systems at operating pressure sufficient?
Please provide specific detail to
accompany your answer.
• Is the definition of airport hydrant
fuel distribution system clear and
appropriate?
• Are you aware of any releases from
airport hydrant systems? If so, what
were the sources, causes, and impacts to
the environment?
• Should EPA consider revising the
date in 280.73 for previously deferred
UST systems? Revision of this date
would mean that these UST systems
closed prior to the effective date of the
final rule would not have to meet
Subpart G unless the implementing
agency directs otherwise based on a
current or potential threat to human
health and the environment. How many
71731
of these UST systems have been closed
since December 22, 1988?
Please provide reasoning or justification
if you disagree with or propose
something different from EPA’s
proposal.
3. UST Systems With Field-Constructed
Tanks
What is EPA proposing?
EPA is proposing to regulate currently
deferred UST systems with fieldconstructed tanks. This means fieldconstructed tanks will no longer be
deferred from the requirements of 40
CFR part 280, subparts B (UST Systems:
Design, Construction, Installation and
Notification), C (General Operating
Requirements), D (Release Detection), E
(Release Reporting, Investigation, and
Confirmation), G (Out-of-Service UST
Systems and Closure), and H (Financial
Responsibility).
UST systems with field-constructed
tanks installed on or before the effective
date of the final UST regulation must
begin meeting the requirements of
subparts B (except § 280.22) and C
within three years of the effective date
of the final UST regulation, subpart D
according to the schedule in the table
below, and § 280.22 of subpart B along
with subparts E, G, and H on the
effective date of the final UST
regulation. UST systems with fieldconstructed tanks installed after the
effective date of the final UST regulation
must meet these requirements at the
time of installation.
SCHEDULE FOR PHASE IN OF SUBPART D
Time frame (after
[effective date of rule ])
Piping using periodic pressurized
bulk line tightness testing.
Within three years.
Between years three and six.
Conduct one piping tightness test according to the bulk line tightness
testing requirement using the maximum detectable leak rates for
semiannual testing. For bulk piping segments not capable of meeting the 3.0 gallon per hour leak rate, owners and operators may
use a leak rate of up to 6.0 gallons per hour.
Between years six and seven.
Conduct one piping tightness test according to the bulk line tightness
testing requirement using the maximum detectable leak rates for
semiannual testing.
After year seven.
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Component and type of release detection used
Begin conducting piping tightness testing according to the bulk line
tightness testing requirement.
Within three years.
Perform release detection according to this subpart.
All other piping and tank release
detection methods.
44 Overview Of Oil Pollution Prevention
Regulations. https://www.epa.gov/oem/content/
lawsregs/opprover.htm.
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Description of
requirement
45 Spill Prevention, Control, And Countermeasure
Rule. https://www.epa.gov/oem/content/spcc/
index.htm.
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Release Detection—Tanks
Release Prevention
EPA is proposing that UST systems
with field-constructed tanks installed
prior to the effective date of the final
UST regulation meet these release
detection requirements:
• Field-constructed tanks with
capacity less than or equal to 50,000
gallons must be monitored using the
release detection methods in § 280.43.
• Field-constructed tanks with a
capacity greater than 50,000 gallons
must either be monitored using release
detection methods in § 280.43 or use
one of these alternatives:
Æ Conduct an annual bulk tank
tightness test that can detect a 0.5 gallon
per hour leak rate;
Æ At least once every 30 days, use an
automatic tank gauging system to
perform release detection, which can
detect a leak rate of one gallon per hour
or less. At least every three years, this
method must be combined with a bulk
tank tightness test that can detect a 0.2
gallon per hour leak rate;
Æ At least once every 30 days, use an
automatic tank gauging system to
perform release detection, which can
detect a leak rate of two gallons per hour
or less. At least every two years, this
method must be combined with a bulk
tank tightness test that can detect a 0.2
gallon per hour leak rate; or
Æ The implementing agency may
approve another method if the owner
and operators can demonstrate the
method can detect a release as
effectively as any of the other three
methods. In comparing methods, the
implementing agency shall consider the
size of release the method can detect
and frequency and reliability of
detection. Owners and operators must
comply with conditions imposed by the
implementing agency.
All bulk tank tightness testing must be
capable of detecting leak rates with a
probability of detection of 0.95 and a
probability of false alarm of 0.05.
All recordkeeping requirements in
§ 280.45 apply to these proposed release
detection methods.
Tanks associated with new or
replaced UST systems with fieldconstructed tanks installed after the
effective date of the final UST regulation
must be secondarily contained and
perform interstitial monitoring
according to § 280.43(g).
EPA is proposing UST systems with
field-constructed tanks meet corrosion
protection, spill, and overfill
requirements. For corrosion protection,
EPA is proposing UST systems with
field-constructed tanks meet one of
these:
• The new tank and piping standards
described in § 280.20; or
• UST systems with field-constructed
tanks installed on or before the effective
date of the final UST regulation can be
constructed of metal and cathodically
protected according to a code of practice
developed by a nationally recognized
association or independent testing
laboratory and meet the following:
Æ Field installed cathodic protection
systems must be: designed by a
corrosion expert; designed to allow for
the determination of current operating
status for impressed current systems;
and operated and maintained in
accordance with § 280.31 or guidelines
established by the implementing
agency; and
Æ Tanks greater than 10 years old
without cathodic protection must be
assessed to ensure they are structurally
sound and free of corrosion holes prior
to adding cathodic protection. The
assessment must be by internal
inspection or another method the
implementing agency determines
adequately assesses the tank for
structural soundness and corrosion
holes.
EPA is proposing UST systems with
field-constructed tanks installed on or
before the effective date of the final UST
regulation that are not upgraded
according to § 280.21 within three years
of the effective date of the final UST
regulation must be permanently closed
according to § 280.70. EPA is proposing
internal lining not be allowed for
meeting the corrosion protection
upgrade requirement.
EPA is proposing to exclude new and
replaced piping of UST systems with
field-constructed tanks from secondary
containment requirements in
§ 280.20(b).
Release Detection—Piping
EPA is proposing underground piping
of UST systems with field-constructed
tanks meet the release detection
requirements for hydrant piping
described in C–2—Airport Hydrant Fuel
Distribution Systems.
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Notification
EPA is proposing that, no later than
30 days after the effective date of the
final UST regulation, owners of
regulated UST systems with fieldconstructed tanks notify appropriate
implementing agencies that their
systems exist.
Financial Responsibility
EPA is proposing UST systems with
field-constructed tanks no longer be
deferred. This means UST systems with
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field-constructed tanks that have not
been permanently closed will be subject
to financial responsibility requirements
in subpart H.
Deferred Components
EPA is proposing to continue
deferring aboveground tanks associated
with UST systems with fieldconstructed tanks from the requirements
of subparts B, C, D, E, and G.
Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing to regulate UST
systems with field-constructed tanks
because they are very large and pose a
substantial threat to human health and
the environment. Typical tank sizes
range from 20,000 gallons to greater
than two million gallons. The total
universe of UST systems with fieldconstructed tanks is small. There are
approximately 239 UST systems with
field-constructed tanks.
Several releases from bulk fieldconstructed tanks have been recorded at
the Craney Island Fuel Terminal in
Portsmouth, VA.46 For example, a 2.1
million gallon field-constructed UST
system that operated from the 1950s to
the mid 1980s released an estimated
300,000 to 500,000 gallons of product
into the environment. Free product was
found within 20 feet of a nearby creek,
and the resulting plume covered more
than five acres. Remediation efforts have
been on-going since 1986. The release
was attributed to tank and/or piping
failures and possibly from a nearby tank
that had a 127,000 gallon overfill in
1986. Another 2.1 million gallon fieldconstructed tank system that operated
from the 1950s until 2000 released an
estimated 175,000 to 250,000 gallons of
jet fuel into the environment. The
release was attributed to piping failures.
The resulting plume covered three acres
and threatened a nearby creek. In both
of these examples, release prevention
and release detection requirements
could have reduced the severity of these
releases and may well have prevented
these releases.
EPA is also proposing this change
because design and construction
standards for UST systems with fieldconstructed tanks are now available. In
the 1988 UST regulation preamble, EPA
indicated tank design and construction
methods for field-constructed tanks
differed from factory-built tanks; we did
not have sufficient time to develop an
appropriate regulation related to design
and construction for those tanks.
Although design standards are now
46 Virginia
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available for aboveground fieldconstructed tanks, EPA is not aware of
standards written according to a
national code of practice developed by
a nationally recognized or independent
testing laboratory. However, military
construction standards, written as
guidance for aboveground and
underground storage tank construction
projects on military installations, are
available.47 EPA considers current
military construction standards
appropriate to sufficiently address fieldconstructed tank design and
construction. Implementing agencies
may use military design and
construction standards to address the
site specific nature of field-constructed
tank systems on military installations.
Note that more stringent standards will
prevail if a field-constructed tank is
installed in a locale with more stringent
design standards. EPA expects owners
and operators to use these existing
standards and specifications for design
and construction of UST systems with
field-constructed tanks.
EPA is proposing UST systems with
field-constructed tanks installed on or
before the effective date of the final UST
regulation begin meeting the
requirements of subparts B (except
§ 280.22) and C within three years of the
effective date of the final UST
regulation, subpart D according to the
phase in schedule in the table above,
and § 280.22 of subpart B along with
subparts E, G, and H on the effective
date of the final UST regulation. UST
systems with field-constructed tanks
installed after the effective date of the
final UST regulation must meet all
requirements at installation. Three years
allows owners and operators enough
time to implement the requirements of
subparts B (except § 280.22) and C. EPA
is providing a phase in period for bulk
line tightness testing in subpart D to
allow owners and operators ample time
to upgrade their piping systems and
meet the leak rate criteria. EPA is
proposing to allow owners and
operators for the first six years (two test
periods) to meet a higher threshold of
up to 6.0 gallons per hour for those
piping segments that cannot meet the
more stringent maximum 3.0 gallons per
hour threshold, due to technical
reasons. These technical reasons
include exceeding capabilities of
47 United Facilities Criteria (UFC) 3–460–01,
‘‘Petroleum Fuel Facilities,’’ prescribes basic
specifications and guidance for designing fueling
systems on military installations. Unless otherwise
noted, the handbook uses nationally recognized
association and institute standards in accordance
with the appropriate service policy. For the
purposes of this preamble, a ‘‘field-constructed
tank’’ is analogous to a ‘‘cut and cover’’ tank.
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currently available pressure-based
methods to achieve the required leak
rate. Currently available methods are
capable of testing larger volume test
sections to a leak rate of 6.0 gallons. The
higher threshold of 6.0 gallons per hour
provides for use of existing test methods
during the first six year period. Six
years will provide owners and operators
time to upgrade their piping systems to
meet the up to 3.0 gallon per hour
threshold for semiannual testing.
Between years six and seven of the
phase in, EPA proposes to allow owners
and operators to conduct one additional
bulk tightness test that meets the
semiannual testing threshold. Beginning
in year seven, owners and operators
must begin meeting the semiannual and
annual bulk line tightness testing
requirements described earlier in this
section. For all other tank and piping
release detection options, EPA is
proposing a three year phase in because
these methods will not require
significant construction or upgrades for
implementation. Finally, owners and
operators can implement the
requirements of § 280.22 of subpart B
along with subparts E, G, and H
beginning on the effective date of the
final UST regulation because upgrades
or special equipment are not needed to
meet the requirements in these subparts.
71733
In the 1988 UST regulation, EPA
deferred UST systems with fieldconstructed tanks in part due to lack of
appropriate release detection methods.
At that time, EPA believed the majority
of release detection methods applied to
factory-built tank systems and did not
adequately work for UST systems with
field-constructed tanks. Over the last 20
years, effective release detection
methods for UST systems with fieldconstructed tanks have evolved.
However, prescribed leak rates for fieldconstructed tanks differ from those in
§ 280.43 of the 1988 UST regulation,
which generally apply to factory-built
tanks. Additionally, 19 state UST
programs, which include approximately
60 percent of the existing universe of
these UST systems, now regulate UST
systems with field-constructed tanks.
NWGLDE’s list in Bulk Underground
Storage Tank Leak Detection Methods
(50,000 Gallons or Greater) 48 identifies
several methods applicable to fieldconstructed tanks. Third party
evaluators verified those release
detection methods achieve a variety of
performance standards. EPA contacted
several vendors and DLA Energy to find
out about their experiences with release
detection methods for field-constructed
tanks in states, such as California,
which require UST systems with fieldconstructed tanks meet release detection
requirements.
EPA recognizes that most release
detection methods for factory-built
tanks are capable of monitoring UST
systems with field-constructed tanks up
to 50,000 gallons. After evaluating
current methods, EPA realized existing
release detection options for tanks in
§ 280.41 of the 1988 UST regulation are
generally not applicable to UST systems
greater than 50,000 gallons because
most methods are limited by tank
capacity. As a result, EPA is proposing
alternative release detection monitoring
methods at different leak rates and
frequencies for UST systems with fieldconstructed tanks greater than 50,000
gallons than for factory-built tanks.
Based on limited data about leaks
from field-constructed tanks, EPA is
proposing two release detection
requirements depending on tank size.
UST systems with field-constructed
tanks up to 50,000 gallons will be
required to meet requirements in
§ 280.41(a). UST systems with fieldconstructed tanks greater than 50,000
gallons will be required either to meet
requirements in § 280.41(a) or use an
alternative release detection method
described below. EPA estimates a subset
of larger size tanks will be able to use
automatic tank gauging systems set to
achieve leak rates in 280.43(d).
NWGLDE’s list identifies numerous
automatic tank gauging systems capable
of detecting leaks on tanks up to
100,000 gallons.49
Owners and operators of UST systems
with field-constructed tanks greater than
50,000 gallons will be allowed to choose
several alternative release detection
methods. They must either perform
annual bulk underground tank tightness
testing that can detect a 0.5 gallon per
hour leak rate or use an automatic tank
gauging system that can detect up to a
two gallon per hour leak rate.
Depending on the automatic tank
gauging system’s leak rate, a bulk
underground tank tightness test at a rate
of 0.2 gallon per hour will be required
at least every two or three years. This
proposed automatic tank gauging
requirement is different from the 1988
release detection requirement for
factory-built tanks. These proposed leak
48 National Work Group on Leak Detection
Evaluation’s (NWGLDE) List of Leak Detection
Evaluations for Storage Tank Systems: https://
www.nwglde.org/.
49 National Work Group on Leak Detection
Evaluation’s (NWGLDE) List of Leak Detection
Evaluations for Storage Tank Systems: https://
www.nwglde.org/.
Release Detection
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rates and time frames for release
detection testing are appropriate
because they will detect releases within
a reasonable time frame given the large
tank sizes and time needed to perform
testing on these tanks.
In addition, implementing agencies
may approve another method of release
detection for UST systems with fieldconstructed tanks if the owner and
operator can demonstrate the method
can detect a release as effectively as any
of the methods listed above. The
implementing agency must consider the
size of release the method can detect as
well as frequency and reliability of
detection when comparing methods.
Owners and operators must comply
with any conditions imposed by the
implementing agency on the method’s
use.
EPA acknowledges the complexities
in performing release detection on tanks
significantly larger than 50,000 gallons.
Perhaps the most critical aspect is
allowing sufficient time for a tank to
reach a state of equilibrium. As tank size
increases, the time for a tank to reach an
equilibrium state increases significantly.
Based on discussions with release
detection vendors, many larger tanks
require multiple inactive days to yield
an accurate test result.
Most UST systems with fieldconstructed tanks are owned by DoD.
Taking these tanks out of service for
multiple days to meet the 1988 release
detection requirement would impede
DoD’s mission, be impractical to
sustain, and result in significant costs.50
Our proposed alternatives for release
detection provide appropriate
environmental protection without
substantially compromising DoD’s
mission. DoD can choose to combine an
automatic tank gauge, at leak rates
achievable by automatic tank gauges on
the market for monthly tank monitoring,
with precision bulk tank tightness
testing. The probabilities of detection
and false alarm EPA proposes for bulk
tank tightness testing are consistent
with the line leak detection
requirements in the 1988 UST
regulation. DoD can also choose to
perform bulk tank tightness testing as a
stand-alone method of release detection.
Staggering the test frequency will allow
DoD to take tanks out of service at
50 See section F of this preamble and Regulatory
Impact Analysis (RIA) for the proposed rule,
available as a separate document in the docket, for
information on the cost differences between
meeting conventional release detection
requirements and the proposed alternative
requirements for airport hydrant systems and UST
systems with field-constructed tanks.
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different intervals without hindering its
mission.
Although current release detection
methods can successfully perform tests
and detect leaks on pressurized piping
at retail service stations, these systems
cannot achieve the same level of
accuracy on large diameter underground
piping of UST systems with fieldconstructed tanks. EPA is proposing
piping of UST systems with fieldconstructed tanks meet the same
requirements proposed for airport
hydrant system piping. See section C–2
for proposed release detection
requirements for airport hydrant system
piping.
Release Prevention
In § 280.20, EPA is proposing new or
replaced tanks and piping have
secondary containment. Secondary
containment poses a much smaller risk
to the environment by providing an
additional measure for containing
released regulated substances in the
interstitial space between the two walls
of the UST system. Secondary
containment must be: Able to contain
regulated substances released from the
UST system until they are detected and
removed; able to prevent the release of
regulated substances to the environment
at any time during the operational life
of the UST system; and checked for
evidence of a leak at least once every 30
days using interstitial monitoring that
meets the requirements of 280.43(g) for
tanks. For UST systems with fieldconstructed tanks, EPA is proposing
only new and replaced tanks meet the
secondary containment requirement.
EPA discussed with DLA Energy and
other vendors the feasibility of installing
secondary containment on piping of
UST systems with field-constructed
tanks. Field-constructed tank system
pipes range from four to 20 inches in
diameter, with lengths normally greater
than 30,000 feet.51 Due to complex
configurations and varying pipe lengths,
we believe installing secondary
containment on piping of UST systems
with field-constructed tanks may be
impractical. It would be difficult to
design a liquid tight barrier that could
accommodate varying diameters of
underground piping. Because leaks
occur at fittings and valves, installing
fittings and valves to join pipes with
various diameters along the piping run
increases the likelihood of a release.
Because field-constructed tank system
pipe lengths are normally significantly
greater than lengths of piping at a
typical retail gasoline station, it would
be very difficult to install a system with
enough sloping that could adequately
monitor the lowest point of a piping
run. Finally, condensation can
accumulate in the interstice between the
inner and outer steel pipe walls,
promoting corrosion of both pipe walls
in the interstitial space and increasing
the likelihood of a release to the
environment.
EPA acknowledges there are
engineering and design challenges (that
is, varying pipe diameter and length,
along with water accumulation in the
interstitial space) when secondarily
containing piping of UST systems with
field-constructed tanks.52 Therefore,
EPA is proposing not to require
secondary containment for piping of
UST systems with field-constructed
tanks. However, EPA is proposing new
and replaced field-constructed tanks
meet secondary containment
requirements. See section A–2 for more
information about the proposed
secondary containment requirements for
tanks.
As with all other regulated UST
systems, EPA is proposing UST systems
with field-constructed tanks meet
corrosion protection requirements.
Because interim prohibition has been in
effect since May 1985, UST systems
with field-constructed tanks generally
are already equipped with corrosion
protection (that is, constructed of: Noncorrodible material; coated and
cathodically protected steel; fiberglass
reinforced plastic; or steel tank clad
with fiberglass reinforced plastic). Fieldconstructed UST systems made of
concrete would meet the corrosion
protection requirement because they are
constructed of a non-corrodible
material.
As with airport hydrant systems, EPA
is proposing not to allow adding an
internal lining as a means of corrosion
protection for UST systems with fieldconstructed tanks that are not already
upgraded. See section C–2 for an
explanation of why EPA is not allowing
these USTs to be upgraded with internal
lining.
As with all other regulated UST
systems, EPA is proposing UST systems
with field-constructed tanks meet spill
and overfill requirements to prevent
releases to the environment. After
discussion with industry and DoD’s
DLA Energy, EPA is taking the position
that existing UST systems with fieldconstructed tanks are already equipped
with spill and overfill prevention
devices that will adequately prevent
spills and overfills.
51 DOD’s DLA Energy, ‘‘Response to EPA—
Release Detection Point Paper,’’ dated 03/10.
52 DOD’s DLA Energy, ‘‘Response to EPA—
Release Detection Point Paper,’’ dated 03/10.
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To make implementing agencies
aware that UST systems with fieldconstructed tanks exist, EPA is
proposing owners of these systems
submit a one-time notification to the
implementing agency. Owners must
notify within 30 days of the effective
date of the final regulation. This will
allow implementing agencies to include
UST systems with field-constructed
tanks in their inventories.
systems with field-constructed tanks
reasonable? If not, please explain why.
• Should EPA consider alternative
options for closing very large UST
systems in place? For example, should
EPA consider requiring removal or
allowing closure in place without filling
the UST?
• Should EPA consider revising the
date in 280.73 for previously deferred
UST systems? Revision of this date
would mean that these UST systems
closed prior to the effective date of the
final rule would not have to meet
Subpart G unless the implementing
agency directs otherwise based on a
current or potential threat to human
health and the environment. How many
of these UST systems have been closed
since December 22, 1988?
Please provide reasoning or justification
if you disagree with or propose
something different from EPA’s
proposal.
Financial Responsibility
4. Wastewater Treatment Tank Systems
Because EPA is proposing to
eliminate the deferral for UST systems
with field-constructed tanks, they will
no longer be exempt from financial
responsibility requirements in subpart
H. Owners and operators will be
required to comply by the effective date
of the final UST regulation. The 1988
UST financial responsibility regulation
exempts state and federal entities.
Therefore, federal and state owners and
operators of UST systems with fieldconstructed tanks will not have to meet
the financial responsibility requirement.
Nearly all UST systems with fieldconstructed tanks are owned by the
federal government.
What is EPA proposing?
UST systems with field-constructed
tanks installed on or before the effective
date of the final UST regulation that do
not meet the upgrade requirements
within three years after the effective
date of the rule must be permanently
closed according to § 280.70. EPA is
requiring permanent closure to prevent
releases to the environment from UST
systems with field-constructed tanks
that have not been upgraded.
Notification
Deferred Components
As with airport hydrant systems, EPA
is proposing to continue deferring the
aboveground tanks associated with UST
systems with field-constructed tanks
from subparts B, C, D, E, and G. See
section C–2 for an explanation of why
EPA proposes to continue deferring
these aboveground components.
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What issues related to this change does
EPA request comment or additional
data on?
• Are the release detection options
and time frames appropriate and
sufficient?
• Are there other release detection
options EPA should consider?
• Are you aware of any releases from
UST systems with field-constructed
tanks? If so, what were the sources,
causes, and impacts to the environment?
• Is the proposed time frame for
implementing the requirements for UST
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EPA is proposing to regulate
wastewater treatment tank systems that
are not part of a wastewater treatment
facility regulated under § 402 or 307(b)
of the CWA.
This means wastewater treatment tank
systems that are currently deferred in
§ 280.10(c)(1) will no longer be deferred
from the requirements of 40 CFR part
280 subparts B (UST Systems: Design,
Construction, Installation and
Notification), C (General Operating
Requirements), D (Release Detection), E
(Release Reporting, Investigation, and
Confirmation), G (Out-of-Service UST
Systems and Closure), and H (Financial
Responsibility). These wastewater
treatment tanks that are currently
deferred in § 280.10(c)(1) will be
referred to as ‘‘wastewater treatment
tanks’’ in the discussion below.
Wastewater treatment tank systems
installed on or before the effective date
of the final UST regulation must begin
meeting the requirements of subparts B
(except § 280.22), C, and D within three
years of the effective date of the final
UST regulation and § 280.22 of subpart
B along with subparts E, G, and H on the
effective date of the final UST
regulation. Wastewater treatment tank
systems installed after the effective date
of the final UST regulation must meet
these requirements at the time of
installation.
Release Detection
EPA is proposing wastewater
treatment tank systems no longer be
deferred from release detection. This
means wastewater treatment tank
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systems must meet the release detection
requirements in 40 CFR part 280,
subpart D.
Release Prevention
EPA is proposing wastewater
treatment tank systems meet corrosion
protection, spill, and overfill
requirements. For corrosion protection,
EPA is proposing wastewater treatment
tank systems meet one of these:
• The new tank and piping standards
described in § 280.20; or
• Wastewater treatment tank systems
installed on or before the effective date
of the final UST regulation can be
constructed of metal and cathodically
protected according to a code of practice
developed by a nationally recognized
association or independent testing
laboratory and meet the following:
Æ Field installed cathodic protection
systems must be: Designed by a
corrosion expert; designed to allow for
the determination of current operating
status for impressed current systems;
and operated and maintained in
accordance with § 280.31 or guidelines
established by the implementing
agency; and
Æ Tanks greater than 10 years old
without cathodic protection must be
assessed to ensure they are structurally
sound and free of corrosion holes prior
to adding cathodic protection. The
assessment must be by internal
inspection or another method the
implementing agency determines
adequately assesses the tank for
structural soundness and corrosion
holes.
EPA is proposing wastewater treatment
tank systems installed on or before the
effective date of the final UST regulation
that are not upgraded according to
§ 280.21 within three years of the
effective date of the final UST regulation
be permanently closed according to
§ 280.70. EPA is proposing internal
lining not be allowed for meeting the
corrosion protection upgrade
requirement.
Notification
EPA is proposing that, no later than
30 days after the effective date of the
final UST regulation, wastewater
treatment tank system owners notify
appropriate implementing agencies that
their systems exist.
Financial Responsibility
EPA is proposing wastewater
treatment tank systems no longer be
deferred. This means wastewater
treatment tank systems that have not
been permanently closed will be subject
to financial responsibility requirements
in subpart H.
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Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing to regulate
wastewater treatment tank systems
(including oil-water separators)
containing regulated substances in 40
CFR part 280 if they are not part of a
wastewater treatment facility regulated
under § 402 or 307(b) of the CWA. In the
1988 UST regulation, EPA deferred
these systems because we were
uncertain about how many of these UST
systems exist and the appropriateness of
some release detection systems for these
systems. EPA still is uncertain about
how many wastewater treatment tank
systems exist. Removing the deferral
will allow us to determine how many
are subject to 40 CFR part 280;. In
addition, release detection methods are
available to detect releases from these
systems. EPA is proposing to regulate
these types of UST systems to protect
human health and the environment
from discharges of regulated substances
contained in these systems. When
wastewater treatment tank systems are
not part of a wastewater treatment
facility regulated under § 402 or 307(b)
of the CWA, they must meet all
requirements in 40 CFR part 280,
including requirements for design,
construction, installation, and
notification; general operating; release
detection; and closure.
To help determine the universe of
wastewater treatment tank systems we
are proposing to regulate, EPA queried
several field experts. They were not
aware of any wastewater treatment tank
systems that are part of a wastewater
treatment facility not regulated under
§ 402 or 307(b) of the CWA. Based on
the experts’ information, all wastewater
treatment tanks, including those at most
publicly-owned treatment works and
many private treatment facilities, are all
part of a wastewater treatment facility
regulated by either § 402 or § 307(b) of
the CWA and, therefore, are excluded
from 40 CFR part 280. As a result, it
appears there are no wastewater
treatment tank systems currently
deferred. However, in the event such
tanks exist, they present the same risks
as other UST systems currently
regulated and need to meet the
requirements in 40 CFR part 280 in
order to protect human health and the
environment.
EPA is proposing that wastewater
treatment tank systems installed on or
before the effective date of the final UST
regulation begin meeting the
requirements in 40 CFR 280 subparts B
(except § 280.22), C, and D within three
years of the effective date of the final
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UST regulation and § 280.22 of subpart
B along with subparts E, G, and H on the
effective date of the final UST
regulation. This includes requirements
for design, construction, and installation
(including spill, overfill, and corrosion
protection); release detection;
notification; operation and
maintenance; recordkeeping; and
closure. In the 1988 UST regulation,
deferred wastewater treatment tank
systems were required to meet the
interim prohibition requirements of
§ 280.11 (that is, corrosion protected,
made of non-corrodible materials, or
otherwise designed and constructed to
prevent releases during the operating
life of the facility due to corrosion or
structural failure). Therefore,
wastewater treatment tank systems are
already equipped with corrosion
protection. Wastewater treatment tank
systems installed after the effective date
of the final UST regulation must meet
all 40 CFR part 280 requirements at
installation. Three years allows owners
and operators enough time to
implement the requirements of subparts
B (except § 280.22), C, and D. EPA also
is taking the position that owners and
operators can implement the
requirements of § 280.22 of subpart B
along with subparts E, G, and H
beginning on the effective date of the
final UST regulation because upgrades
or special equipment are not needed to
meet the requirements in these subparts.
As with airport hydrant systems and
UST systems with field-constructed
tanks, EPA is proposing not to allow
adding an internal lining as a means of
corrosion protection for wastewater
treatment tank systems that are not
already upgraded. See section C–2 for
an explanation of why EPA is not
allowing these USTs to be upgraded
with internal lining.
Wastewater treatment tank systems
installed on or before the effective date
of the final UST regulation that do not
meet the upgrade requirements within
three years after the effective date of the
rule must be permanently closed
according to § 280.70. EPA is requiring
permanent closure to prevent releases to
the environment from wastewater
treatment tank systems that have not
been upgraded.
Notification
EPA is proposing owners submit a
one-time notification to implementing
agencies for wastewater treatment tank
systems not regulated by the CWA.
Owners must notify within 30 days of
the effective date of the final regulation.
EPA is proposing this to ensure
implementing agencies are aware these
systems exist.
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Financial Responsibility
Because wastewater treatment tank
systems will no longer be deferred,
those systems not permanently closed
will need to meet financial
responsibility requirements as described
in 40 CFR part 280, subpart H. Federaland state-owned facilities are exempt
from this requirement. Therefore,
federal and state owners and operators
of wastewater treatment tank systems
will not have to meet this requirement.
What issues related to this change does
EPA request comment or additional
data on?
• EPA is taking the position that there
are no wastewater treatment tank
systems affected by this proposal. Are
you aware of systems that would be
subject to this proposed change? If yes,
please provide information about the
number and location of wastewater
treatment tank systems that would be
regulated. For instance are there units
associated with natural gas drilling that
are not regulated by 402 or 307(b)?
• If there are wastewater tank
systems, is it most appropriate to
regulate, exempt, or continue to defer
these systems? Please explain why.
• Should EPA consider revising the
date in 280.73 for previously deferred
UST systems? Revision of this date
would mean that these UST systems
closed prior to the effective date of the
final rule would not have to meet
Subpart G unless the implementing
agency directs otherwise based on a
current or potential threat to human
health and the environment. How many
of these UST systems have been closed
since December 22, 1988?
Please provide reasoning or justification
if you disagree with or propose
something different from EPA’s
proposal.
5. Maintain Deferral for USTs
Containing Radioactive Material and
Emergency Generator UST Systems at
Nuclear Power Generation Facilities
Regulated by the Nuclear Regulatory
Commission
EPA is not proposing changes to the
1988 UST regulation deferral in
§ 280.10(c)(2) and (3) for USTs
containing radioactive material and for
emergency generator UST systems at
nuclear power generation facilities
regulated by the Nuclear Regulatory
Commission (NRC). Currently, these
types of UST systems are deferred from
most UST requirements but are subject
to requirements for interim prohibition,
release response and corrective action,
and where applicable, lender liability
(40 CFR part 280, subparts A, F, and I,
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respectively). EPA has decided to keep
the deferral in order to retain EPA’s
requirements for cleaning up releases
from these USTs.
EPA compared Department of Energy
(DOE) Orders 53 and NRC requirements
to the 1988 UST regulation. This
assessment revealed DOE and NRC
requirements are comparable to EPA
requirements for new and existing USTs
regarding spill and overfill control
(§ 280.30); operation and maintenance
of corrosion protection (§ 280.31);
compatibility (§ 280.32); and release
detection (40 CFR part 280, subpart D).
However, there is no independent
regulatory authority for DOE and NRC to
remediate releases. With that in mind,
EPA is taking the position that it is
appropriate to maintain the deferral for
these USTs as it currently exists in order
for EPA to continue requiring release
response and corrective action.
D. Other Changes
1. Changes To Overfill Prevention
Equipment Requirements
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
What is EPA proposing?
In § 280.20, EPA is proposing to
eliminate flow restrictors (also called
ball float valves) in vent lines as an
overfill prevention option either when
an UST system is installed or when an
UST system’s overfill prevention
equipment is replaced.
Owners and operators using a vent
line flow restrictor before the final UST
regulation becomes effective may
continue using a flow restrictor to meet
the overfill prevention requirements, as
long as it restricts the flow of regulated
substances into the UST when the
device activates.
Owners and operators may continue
to use flow restrictors not in vent lines
(such as flow restrictors in fill pipes),
automatic shutoff devices, and high
level alarms as overfill prevention for all
UST systems.
Why is EPA proposing this change?
What background information is
available about this change?
Spills and overfills are a common
cause of UST system releases (see
sections B–2 and B–3 for additional
discussion). Through extensive
stakeholder outreach, EPA identified
vent line flow restrictors as a significant
concern for operability and safety. To
reduce the frequency of UST releases
due to operability and to address system
safety and personnel safety concerns,
53 DOE Orders establish management objectives,
identify performance requirements and assign
responsibilities consistent with policy and
regulations. See: https://www.directives.doe.gov/
directives/types-of-directives.
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EPA is proposing to eliminate vent line
flow restrictors for new installations and
replacements.
• Operability—For a vent line flow
restrictor to operate properly, the device
must restrict the flow of regulated
substance into the UST when the flow
restrictor engages. If the tank top is not
liquid or vapor tight, flow into the UST
is not restricted because vapors
continue to escape through these nontight areas. If vapors continue to escape
the UST, there is no pressure buildup in
the vapor area of the tank, resulting in
no reduced flow rate into the UST.
Examples where non-tight tank tops
may result in ineffective flow restrictors
include: Loose tank bungs or other tank
top components; tanks with coaxial
stage I vapor recovery installed; and
tanks with both tank top and remote fill
areas.
• System safety—Vent line flow
restrictors can create safety concerns
when they activate. USTs can become
over pressurized and damaged during a
pressurized delivery. The 2005 version
of the Petroleum Equipment Institute’s
installation standard, RP100,
recommends against using vent
restriction devices because the vent line
flow restrictor pressurizes the UST,
creating a hazardous condition when
the device operates as designed.
• Personnel safety—Delivery
personnel can be sprayed with regulated
substances when they disconnect the
delivery hose from the fill pipe and the
vent line flow restrictor activates.
What issues related to this change does
EPA request comment or additional
data on?
• EPA considered eliminating or
phasing out vent line flow restrictors for
currently installed UST systems, but
finds the cost burden for owners and
operators could be high. Please provide
input and information in support of or
against eliminating or phasing out vent
line flow restrictors.
Please provide reasoning or justification
if you disagree with or propose
something different from EPA’s
proposal.
2. Internal Linings That Fail the
Periodic Lining Inspection and Cannot
Be Repaired
What is EPA proposing?
In § 280.21, EPA is proposing owners
and operators permanently close an
UST that uses internal lining as the sole
method of corrosion protection when
both of these conditions exist:
• A lining inspection determines the
internal lining is no longer performing
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71737
according to original design
specifications; and
• The internal lining cannot be
repaired according to a code of practice
developed by a nationally recognized
association or independent testing
laboratory.
For tanks with both internal lining and
cathodic protection, EPA is proposing to
allow owners and operators continue
operating an UST if it fails the lining
inspection and cannot be repaired if
both of these criteria are met:
• The cathodic protection is operated
and maintained according to § 280.31;
and
• The tank was assessed and found to
be structurally sound and free of
corrosion holes when the cathodic
protection was added to the tank.
Why is EPA proposing this change?
What background information is
available about this change?
About 3 percent of tanks today rely on
internal lining as the sole method of
corrosion protection to meet the 1988
UST regulation.54 Tanks that are
internally lined to meet the 1988 UST
regulation corrosion protection
requirement at § 280.21 are typically
older, bare steel tanks installed before
1986. The 1988 UST regulation
preamble says that internal lining, when
used as the sole method for corrosion
protection, is not regarded as a
permanent upgrade. However, it is
adequate if the lining continues to meet
original design specifications. If the
internal lining no longer meets original
design specifications and cannot be
repaired according to industry codes,
then the lined tank is subject to
unprotected tank requirements and
must be replaced after 1998. However,
the language from the 1988 preamble
was not included in § 280.21(b)(1).
EPA is proposing to revise the
internal lining requirements to match
EPA’s intent of replacing internally
lined tanks that fail a lining inspection
and cannot be repaired according to a
code of practice. EPA is proposing that
a lined tank must be permanently closed
if, when inspected, it cannot be repaired
according to a code of practice.
Owners and operators may continue
using internal lining to meet the
corrosion protection requirement, as
long as:
54 E2, Incorporated, memoranda and analyses
submitted under Contract EP–W–05–018, ‘‘U.S.
Environmental Protection Agency. Underground
Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.’’ These
supporting materials can be found in the docket for
the proposed rulemaking.
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• The internal lining is periodically
inspected according to § 280.21(b)(1)(ii);
and
• The internal lining passes the
inspection or is repaired so it meets
original design specifications according
to a code of practice developed by a
nationally recognized association or
independent testing laboratory.
Consistent with current EPA policy,55
tanks using the combination of cathodic
protection and internal lining for
corrosion protection are not required to
be closed if the internal lining fails and
cannot be repaired as long as:
• The cathodic protection is operated
and maintained according to § 280.31;
and
• The tank was assessed and found to
be structurally sound and free of
corrosion holes when the cathodic
protection was added to the tank.
What issues related to this change does
EPA request comment or additional
data on?
• Should EPA consider requiring
lined tanks be closed when they fail a
lining inspection independent of
whether the lining can be repaired? If
yes, please provide information to
support your answer.
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
3. Notification Requirements
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What is EPA proposing?
EPA is proposing these notification
requirement changes in § 280.22:
• Notify implementing agencies
within 30 days of assuming ownership
of an UST system. A new owner is
required to submit a form which
provides the new owner’s name, mailing
address, physical location of USTs, and
name of previous owner;
• Require owners who bring new UST
systems into service notify
implementing agencies of USTs, rather
than state or local agencies designated
by EPA;
• Merge the paragraph about
minimum information with the
paragraph explaining what forms to use
for notification and delete the minimum
information paragraph;
• Require owners of deferred UST
systems EPA is proposing to require a
one-time notification to implementing
agencies within 30 days of the effective
date of the final UST regulation.
55 EPA UST Technical Compendium Question
and Answer #14: https://epa.gov/oust/compend/
nus.htm.
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EPA is proposing changes to the
‘‘Notification For Underground Storage
Tanks’’ form in Appendix I.
EPA is proposing changes to the form
as a result of today’s proposal, and to
change ‘‘State’’ to ‘‘Implementing
Agency’’ throughout the form.
EPA is proposing a new form titled
‘‘Notification of Ownership Change for
Underground Storage Tanks’’ under
Appendix II.
Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing the new ownership
change notification to more effectively
administer the UST program. EPA
required a one-time notification of
regulated USTs by May 8, 1986,56 and
owners who purchased newly installed
UST systems completed and submitted
notification forms to implementing
agencies. However, EPA did not require
people notify implementing agencies
when acquiring a regulated UST, such
as when purchasing an existing service
station.
Without a requirement to notify when
persons assume ownership of UST
systems, implementing agencies have
difficulty administering the UST
program. Persons can assume ownership
through purchase, inheritance,
acquisition of property, or other means.
EPA estimates on average 10 percent of
retail UST facilities change ownership
in a given year.57 Any communication
or outreach is impaired if implementing
agencies do not know the correct
owners of a large proportion of
regulated USTs. When final, this change
will ensure implementing agencies
know the current ownership of
regulated UST systems.
At least 48 of 56 states and territories
realized this need and instituted some
form of ownership change notification.
EPA is following the example of these
states and will require an ownership
change notification to more effectively
administer the UST program.
EPA is proposing to include a form in
Appendix II titled ‘‘Notification of
Ownership Change for Underground
Storage Tanks.’’ The new form specifies
the information persons need to submit
to the implementing agency after they
become owners of underground storage
tanks. EPA is proposing these owners
provide their name, address, phone
56 Solid
Waste Disposal Act § 9002(a)(1).
57 E2, Incorporated, memoranda and analyses
submitted under Contract EP–W–05–018, ‘‘U.S.
Environmental Protection Agency. Underground
Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.’’ These
supporting materials can be found in the docket for
the proposed rulemaking.
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number, name of the facility, location of
USTs, as well as the name, address, and
phone number of the previous owner.
EPA is also proposing owners who
bring UST systems into service notify
implementing agencies, rather than state
and local agencies identified by EPA.
This change is needed for two reasons.
First, an unintended result of the
existing requirement is owners in Indian
country submitted notification forms to
state or local agencies, not to EPA, even
though EPA is the implementing agency
in Indian country. When final, this
change will greatly assist EPA in
implementing the UST program in these
areas. Second, many of the agency
names and addresses EPA identified in
1988 are no longer accurate. When final,
this change will provide owners with
clarity about where to send notification
forms and better accommodate changes
of implementing agencies.
EPA is proposing to merge the
paragraphs discussing the minimum
information owners and operators need
to submit and the form to be submitted
to implementing agencies. This will
reduce redundancy and ease
understanding of this requirement. As a
result, a separate paragraph explaining
what minimum information to submit
for notification will be unnecessary.
EPA is proposing owners of
previously deferred UST systems notify
implementing agencies within 30 days
of the effective date of the final UST
regulation. EPA is proposing this onetime notification because owners of
previously deferred UST systems
brought into service after May 8, 1986
were not required to notify
implementing agencies. Because EPA is
proposing to regulate previously
deferred UST systems and to ensure
they meet requirements of the final UST
regulation, it is imperative
implementing agencies receive notice
about these UST systems.
Due to EPA’s proposed changes to the
UST regulation, we are proposing
changes to the notification form under
Appendix I. This will make the form
request appropriate information
according to today’s proposal. For
instance, the release detection section of
the 1988 UST regulation form did not
include statistical inventory
reconciliation or bulk tightness testing.
The proposed form includes these
methods.
What issues related to this change does
EPA request comment or additional
data on?
• Is a one-time notification for all
UST owners also necessary to
effectively administer the UST program
in jurisdictions (eight states and
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territories and Indian country) where
implementing agencies do not currently
require ownership change notification?
EPA is posing this question because of
the high rate of UST ownership changes
and resulting likelihood implementing
agencies do not know who owns
numerous UST systems.
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
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4. Alternative Fuels And Compatibility
What is EPA proposing?
EPA is proposing changes to two
definitions in § 280.12 of the 1988 UST
regulation.
• Regulated substance—delete
‘‘* * * derived from crude oil though 58
[sic] processes of separation,
conversion, upgrading, and finishing
* * *’’
• Motor fuel—include explanatory
language that a petroleum or petroleumbased substance is typically used to
operate a motor engine and provide
example products (motor gasoline,
aviation gasoline, No. 1 or No. 2 diesel
fuel, or any blend containing one or
more of these substances, such as motor
gasoline blended with alcohol) meeting
the definition.
In addition, EPA is proposing changes
to the compatibility requirement in
§ 280.32 of the 1988 UST regulation.
These changes explain how owners and
operators storing certain regulated
substances must demonstrate that their
UST systems are compatible with
substances stored. Specifically, EPA is
proposing:
• Owners and operators storing any
regulated substance blended with
greater than 10 percent ethanol or
greater than 20 percent biodiesel, or any
other regulated substance identified by
the implementing agency, must use one
or more of the following methods to
demonstrate UST system compatibility
with these regulated substances:
Æ Certification or listing of UST
system components by a nationally
recognized, independent testing
laboratory for use with the fuel stored;
Æ Equipment or component
manufacturer approval. The
manufacturer’s approval must be in
writing; indicate an affirmative
statement of compatibility; specify the
range of ethanol or biodiesel blends the
component is compatible with; and be
from the equipment or component
manufacturer; or
Æ Another method determined by the
implementing agency to be no less
58 This
is an error in 40 CFR 280; ‘‘though’’
should be ‘‘through.’’
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protective of human health and the
environment than the previously listed
methods.
• Owners and operators must
maintain the following records
(according to § 280.34) for the life of the
equipment or component:
Æ Documentation of compliance with
the above section as applicable; and
Æ Records of all equipment or
components installed or replaced after
the effective date of the final UST
regulation. At a minimum, each record
must include the date of installation or
replacement, manufacturer, and model.
EPA is also proposing to delete these
codes of practice.
• American Petroleum Institute
Publication 1626, ‘‘Storing and
Handling Ethanol and Gasoline-Ethanol
Blends at Distribution Terminals and
Service Stations’’
• American Petroleum Institute
Publication 1627, ‘‘Storage and
Handling of Gasoline-Methanol/
Cosolvent Blends at Distribution
Terminals and Service Stations’’
Why is EPA proposing this change?
What background information is
available about this change?
Regulated Substance and Motor Fuel
Definitions
EPA is proposing a change in the
regulated substance definition to clarify
that petroleum does not need to be
derived from crude oil in order to be
regulated when stored in USTs. The
preamble to the supplement to the
proposal for the original UST regulation
indicates that petroleum products can
be derived from other materials, such as
biomass, plant material, organic waste,
coal, and shale oil.59 Petroleum is
comprised of a complex blend of
hydrocarbons regardless of its source
material; therefore, all petroleum poses
risks to human health and the
environment.
Many people interpreted the 1988
UST regulation definition of regulated
substance as applying to petroleum
USTs only if the petroleum was derived
from crude oil. Over time, this
misinterpretation may become more
problematic as the amount of petroleum
derived from non-crude oil based
products, such as natural gasoline,
increases as a result of requirements in
the Energy Independence and Security
Act of 2007. Today’s regulated
substance clarification will eliminate
uncertainty about the regulatory status
of tanks storing petroleum products
59 ‘‘40 CFR Parts 280 and 281 USTs; Supplement
to Proposed Rule,’’ 52 Federal Register 246 (23
December 1987), pg. 48640.
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derived from sources other than crude
oil.
EPA is proposing a change in the
motor fuel definition to better
accommodate new motor fuels that may
be marketed and stored in the future.
The 1988 UST regulation definition
listed motor fuel products, leading to
confusion as to whether new fuels, such
as petroleum blended with ethanol or
biodiesel, are motor fuels. Today’s
proposal clarifies the motor fuel
definition to explain that it is any fuel
typically used to operate a motor
engine.
Compatibility
EPA understands that the chemical
and physical properties of ethanol and
biodiesel can be more degrading to
certain UST system materials than
petroleum alone. As the use of ethanoland biodiesel-blended fuels increases,
EPA is concerned that not all UST
system components are compatible with
these fuel blends.
Gasoline containing 10 percent or less
ethanol (known as E10) has been used
in parts of the United States for many
years, and UST equipment
manufacturers accommodated the E10
market by producing compatible
equipment. According to the Renewable
Fuels Association, ethanol is blended
into over 90 percent of all gasoline sold
in the country,60 predominantly as E10.
Recently, there has been a movement
toward higher blends of ethanol, due in
part to federal and state laws
encouraging the increased use of
biofuels. While most UST system
equipment and components are
compatible with E10, blends greater
than 10 percent ethanol do not have a
long history of storage and may not be
compatible with certain materials used
in UST systems. According to a 2011
report published by U.S. Department of
Energy’s Oak Ridge National
Laboratory,61 some elastomeric
materials are particularly affected by
intermediate ethanol blends and certain
sealants may not be suitable for any
ethanol-blended fuels. A 2007 report
from Underwriters Laboratories (UL) 62
60 Renewable Fuels Association, ‘‘Building
Bridges to a More Sustainable Future: 2011 Ethanol
Industry Outlook.’’ https://www.ethanolrfa.org/page/
-/2011%20RFA%20Ethanol%20Industry
%20Outlook.pdf?nocdn=1.
61 Oak Ridge National Laboratory, ‘‘Intermediate
Ethanol Blends Infrastructure Materials
Compatibility Study: Elastomers, Metals, and
Sealants’’ (March 2011).
62 Underwriters Laboratories, Inc., ‘‘Underwriters
Laboratories Research Program on Material
Compatibility and Test Protocols for E85
Dispensing Equipment’’ (December 2007). Available
in the UST Docket under Docket ID No. EPA–HQ–
UST–2010–0651.
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evaluated the effect of 85 percent
ethanol and 25 percent ethanol blends
on dispenser components. Results
indicated some materials used in the
manufacture of seals were degraded
more when exposed to the 25 percent
ethanol test fluid than when exposed to
the 85 percent ethanol test fluid. Other
literature suggests ethanol fuel blends
can be more aggressive toward certain
materials than independent fuel
constituents, with maximum polymer
swelling observed at approximately 15
percent ethanol by volume.63 Therefore,
EPA is clarifying the compatibility
requirements for owners and operators
who choose to store regulated
substances containing greater than 10
percent ethanol.
EPA is also clarifying the
compatibility requirements for owners
and operators who choose to store
regulated substances containing greater
than 20 percent biodiesel. Although the
total use of biodiesel is significantly less
than that of ethanol, it has become
increasingly available across the United
States and may also be incompatible
with certain materials used in UST
systems. Pure biodiesel (B100), for
example, has known compatibility
issues with certain materials. According
to the U.S. Department of Energy’s
National Renewable Energy Laboratory
(NREL) Biodiesel Handling and Use
Guide, Fourth Edition,64 ‘‘B100 will
degrade, soften, or seep through some
hoses, gaskets, seals, elastomers, glues,
and plastics with prolonged exposure
* * * Nitrile rubber compounds,
polypropylene, polyvinyl, and Tygon®
materials are particularly vulnerable to
B100.’’
In contrast, the properties of very low
blends of biodiesel (B5 or less) are so
similar to those of petroleum diesel that
ASTM International (ASTM) considers
conventional diesel that contains up to
5 percent biodiesel to meet its
‘‘Standard Specification for Diesel Fuel
Oils’’ 65. For biodiesel blends between 5
and 100 percent, there is very little
compatibility information; however,
NREL’s handling and use guide
concludes that biodiesel blends of B20
or less have less of an effect on materials
and very low blends of biodiesel (for
63 Westbrook, P.A., ‘‘Compatibility and
Permeability of Oxygenated Fuels to Materials in
Underground Storage and Dispensing Equipment’’
(January 1999). Available in the UST Docket under
Docket ID No. EPA–HQ–UST–2010–0651.
64 National Renewable Energy Laboratory,
‘‘Biodiesel Handling and Use Guide, Fourth
Edition.’’ (2009). Available in the UST Docket
under Docket ID No. EPA–HQ–UST–2010–0651.
65 ASTM Standard D975, 2010c ‘‘Standard
Specification for Diesel Fuel Oils,’’ ASTM
International, West Conshohocken, PA, 2010, DOI:
10.1520/D0975–10C, https://www.astm.org.
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example, B5 and B2) ‘‘ * * * have no
noticeable effect on materials
compatibility.’’ 66 In addition, fleet
service sites have stored B20 in USTs
for years, and EPA is not aware of
compatibility-related releases associated
with those USTs storing B20. Therefore,
EPA is proposing to require tank owners
and operators who store greater than 20
percent biodiesel in their UST systems
demonstrate compatibility of UST
equipment by one of the methods
proposed in § 280.32.
To avoid risk of increased releases
due to incompatibility of ethanol or
biodiesel blends with UST system
components, EPA is proposing several
options for owners and operators to
demonstrate that their UST systems are
compatible with regulated substances
containing greater than 10 percent
ethanol or greater than 20 percent
biodiesel. These options provide owners
and operators with flexibility in
demonstrating compatibility, yet still
protect human health and the
environment. In the past, tank owners
typically demonstrated compatibility by
using equipment certified or listed by a
nationally recognized, independent
testing laboratory, such as Underwriters
Laboratories (UL). Many UST
components in the ground today were
manufactured before regulated
substances containing ethanol or
biodiesel existed and are not approved
by nationally recognized, independent
testing laboratories for use with these
fuel blends. Currently, certain tanks and
piping have been tested and are listed
by UL for use with higher-level ethanol
blends. Many other components of the
UST system, such as leak detection
devices, sealants, and containment
sumps, may not be listed by UL or
another nationally recognized,
independent testing laboratory for use
with these blends.
In addition, EPA is not aware of any
nationally recognized, independent
testing laboratory that has performed
testing on UST system components with
biodiesel-blended fuels. Absent
certification or listing from a nationally
recognized, independent testing
laboratory, or other verification that
components may be used with anything
beyond conventional fuels, the
suitability of these components for use
with ethanol or biodiesel blends comes
into question. As a result, EPA is
providing options for demonstrating
compatibility to reduce the risk of
releases due to material incompatibility.
66 National Renewable Energy Laboratory,
‘‘Biodiesel Handling and Use Guide, Fourth
Edition.’’ (2009). Available in the UST Docket
under Docket ID No. EPA–HQ–UST–2010–0651.
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Owners and operators choosing to store
regulated substances blended with
greater than 10 percent ethanol or
greater than 20 percent biodiesel must
demonstrate compatibility of the UST
system before storing those regulated
substances.
EPA is proposing owners and
operators use one of these two methods
for demonstrating compatibility of UST
equipment or components with
regulated substances containing greater
than 10 percent ethanol or greater than
20 percent biodiesel: using equipment
or components that are certified or
listed by a nationally recognized,
independent testing laboratory for use
with the fuel stored; or using equipment
or components approved by the
manufacturer to be compatible with the
fuel stored. In addition, implementing
agencies will have the flexibility to
evaluate and allow other methods, if
they are no less protective of human
health and the environment than those
EPA is proposing today.
For those components tested and
approved by a nationally recognized,
independent testing laboratory, owners
and operators will be able to
demonstrate compatibility solely by
keeping records of these components. In
this instance, the testing laboratory’s
listing, labeling, or approval
demonstrates the equipment or
component’s suitability to be used with
the regulated substance stored, which
means owners and operators will be
able to demonstrate compatibility by
retaining equipment or component
records.
Owners and operators will also be
able to demonstrate compatibility by
obtaining manufacturer’s approval of
components’ compatibility with the
regulated substance to be stored. The
manufacturer’s approval must be in
writing and include an affirmative
statement that the component is
compatible with the fuel blend stored.
To add clarity for tank owners and
operators, the manufacturer’s approval
must also specify the range of fuel
blends for which the component is
compatible. Finally, the manufacturer’s
approval must be issued from the
equipment or component manufacturer,
not another entity (such as the installer
or distributor). A manufacturer’s
approval will enable owners and
operators to demonstrate compatibility
for components not approved for use by
a nationally recognized, independent
testing laboratory. It will also provide
confidence for implementing agencies
that the component is compatible with
the fuel stored.
EPA is proposing an additional option
which would allow implementing
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agencies to approve other methods for
demonstrating compatibility with
regulated substances containing greater
than 10 percent ethanol or greater than
20 percent biodiesel. Implementing
agencies will be able to approve
methods they consider no less
protective of human health and the
environment in addition to the
manufacturer’s approval or the listing,
labeling, or approval by a nationally
recognized, independent testing
laboratory. This will provide owners
and operators with additional flexibility
when new methods to determine UST
system component compatibility are
developed.
Although these methods for
demonstrating compatibility will apply
to UST systems storing regulated
substances containing greater than 10
percent ethanol and greater than 20
percent biodiesel, EPA is proposing to
extend the methods to other regulated
substances identified by implementing
agencies. This will provide
implementing agencies with flexibility
when new regulated substances (for
example, biobutanol) enter the fuel
market and allow implementing
agencies to apply these methods for
determining UST system compatibility
to other regulated substances.
EPA is proposing owners and
operators maintain records for the life of
UST systems, if the UST system stores
regulated substances containing greater
than 10 percent ethanol or greater than
20 percent biodiesel or another
regulated substance identified by
implementing agencies. Owners and
operators will be required to retain
equipment or component records in
order to demonstrate their systems are
compatible with these regulated
substances. Without records of the
equipment or components, owners and
operators will not be allowed to store
regulated substances containing greater
than 10 percent ethanol or greater than
20 percent biodiesel in their UST
systems.
To demonstrate compatibility with
regulated substances stored in UST
systems, owners and operators of new
and replaced equipment or components
must retain records for the life of the
equipment or component. This will
ensure new and replaced equipment
and components are compatible with
the regulated substances stored. As
equipment or components are replaced,
records will be available for all UST
system equipment or components,
making it easier for owners and
operators to demonstrate compatibility
with new regulated substances.
Owners and operators must
demonstrate compatibility for the
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following UST system equipment or
components: Tank or internal tank
lining; piping; line leak detector;
flexible connectors; drop tube; spill and
overfill prevention equipment and
components; submersible turbine pump
equipment and components; sealants
(including pipe dope and thread
sealant); fittings; gaskets; bushings;
couplings; boots; containment sumps
(including submersible turbine sumps
and under dispenser containment);
release detection floats, sensors, and
probes; fill and riser caps; and the
product shear valve. These equipment
or components are a subset of an UST
system, as defined by § 280.12, which,
if incompatible, would lead to a liquid
release to the environment.
EPA is clarifying that the
requirements in this section also apply
to both newly installed equipment or
components and equipment where one
or more components are replaced. For
newly installed equipment comprised of
multiple individual, smaller
components and assembled by the
manufacturer, some manufacturers
provide a compatibility certification for
the equipment as a whole. For example,
a manufacturer may certify the entire
submersible turbine pump as being
compatible. The submersible turbine
pump certification would include all
components (gaskets, sealants, bushings,
etc.) of the equipment assembled by the
manufacturer. Therefore, an owner may
obtain one certification for newly
installed manufacturer-assembled
equipment, as long as the manufacturer
certifies the entire piece of equipment as
compatible. However, over the lifetime
of a typical UST system, equipment is
likely to require maintenance, which
may involve replacing components such
as gaskets, sealants, and bushings. It is
important for tank owners to use
compatible replacement components,
especially since these components are
sometimes constructed of materials that
are not compatible with biofuel blends.
Therefore, components (such as gaskets,
sealants, bushings, etc.) replaced after
the equipment was originally installed
will not be covered by the original
manufacturer’s approval. Owners and
operators will need to obtain
manufacturer’s certification indicating
the replaced component is compatible
with the regulated substance stored in
the UST system.
These proposed changes will protect
human health and the environment
from potential additional releases as a
result of incompatible UST systems.
Also, the changes are not overly
burdensome, nor do they require costly
retrofits. These changes will give
owners and operators flexibility, yet
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provide EPA with confidence that UST
systems will be compatible with new
fuel blends when owners and operators
use one or more of the proposed
methods to determine compatibility.
The additional language also provides
owners and operators with certainty on
what is acceptable in demonstrating
UST system compatibility with the
substances stored.
EPA is also proposing to delete two
codes of practice listed in the 1988 UST
regulation. EPA included codes of
practice to help owners and operators
demonstrate compliance with the
compatibility requirement. EPA is now
proposing methods for determining
compatibility, so referencing codes of
practice is unnecessary.
In August 2010, American Petroleum
Institute (API) published an updated
version of API Recommended Practice
1626. Today’s proposal incorporates
several methods API recommends
owners and operators storing blends of
greater than 10 percent ethanol use to
demonstrate UST system compatibility.
If owners and operators follow API
Recommended Practice 1626, Section 7
requirements, for regulated substances
blended with ethanol, they will meet
today’s proposed § 280.32(b) changes.
What issues related to this change does
EPA request comment or additional
data on?
• How many UST systems currently
store petroleum not derived from crude
oil (such as natural gasoline)?
• Should EPA consider allowing
professional engineers to make
compatibility determinations?
• Are there additional methods for
effectively demonstrating compatibility?
If yes, please provide details.
• Are there other alternatives to
demonstrating compatibility (such as
using secondarily contained USTs) that
tank owners and operators should be
allowed to use, that are no less
protective of human health and the
environment?
• Are the proposed criteria for
manufacturer’s approval reasonable?
• Should EPA consider tiering
methods? For example, if an approval or
listing from a nationally recognized,
independent third party is available,
then the manufacturer approval is not
an option for that component?
• Should EPA waive the
compatibility requirement for UST
systems with secondary containment
and interstitial monitoring? Why or why
not?
• While this proposal requires owners
and operators maintain records to
demonstrate compatibility, we are not
requiring owners and operators transfer
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records to new owners and operators.
Should EPA consider requiring records
transfer?
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
5. Improving Repairs
What is EPA proposing?
EPA is proposing to revise the
definition of repair in § 280.12 to:
• Clarify that all UST system
components, including piping, spill
prevention equipment, overfill
prevention equipment, corrosion
protection equipment, and release
detection equipment are included under
the repairs allowed section of the
regulation, and
• Remove the link that repairs are
only associated with a release from an
UST system by adding to the definition
suspected release and equipment that
has failed to function properly.
For repairs to secondary containment
areas of UST systems, overfill
prevention equipment, and spill
prevention equipment, EPA is
proposing to add tests after a repair to
the repairs allowed section (§ 280.33).
The tests after repair requirements for
these areas are the same as those for
periodic spill and overfill tests
discussed in sections B–2 and B–3. The
tests for interstitial areas after a repair
and periodic interstitial integrity (in
section B–4) are the same, except tanks
with continuous interstitial sensors
must perform a vacuum, pressure, or
liquid test following the repair. These
tests must be conducted within 30 days
of a repair.
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Why is EPA proposing this change?
What background information is
available about this change?
Clarification of UST system
components in the definition of repair—
EPA is proposing to add the following
UST system components to the
definition of repair: Piping; spill
prevention equipment; overfill
prevention equipment; corrosion
protection equipment; and release
detection equipment. By adding these
UST system components, EPA is making
it clear that these specific components
are subject to the repairs allowed
section of the regulation. This means
owners and operators performing
repairs on these UST system
components must follow the repairs
allowed section (§ 280.33). The 1988
UST regulation definition of repair uses
the generic term UST system component
and provides less detail about what an
UST system component is.
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Including repairs not associated with
a confirmed release or suspected release
from the UST system—It is common
practice for owners and operators to fix
UST components that have not caused
a release or suspected release of product
from the UST system. However, the
repair definition in the 1988 UST
regulation does not consider these nonrelease fixes as repairs. EPA is
proposing to modify the repair
definition to include the concept of
repairing equipment that failed to
function properly, delinking a repair
with a release from the UST system.
This proposed change will ensure repair
activities not associated with a release
are conducted properly. For example,
under the 1988 UST regulation, fixing a
cathodic protection system would not
be considered a repair because the UST
component likely has not yet caused a
release of product from the UST system.
In addition, EPA is proposing to include
a suspected release as part of the
definition, so repairs associated with
suspected releases are covered under
the repair definition.
By removing the link between repair
and release, EPA is proposing owners
and operators meet the repairs allowed
section (§ 280.33) when fixing UST
system components that have not
caused a release of product from the
UST system. This means owners and
operators will need to have repairs
performed in accordance with a code of
practice developed by a nationally
recognized association or independent
testing laboratory and test the
equipment after the repair is completed.
Tests after repairs—To ensure
equipment is operating as intended after
a repair, EPA is proposing to require
tests within 30 days of repairing spill,
overfill, and secondary containment
equipment. Except for interstitial
integrity tests in USTs with continuous
interstitial sensors, the tests after repairs
proposal uses periodic tests described in
sections B–2, B–3, and B–4. For USTs
with continuous interstitial sensors,
owners and operators must conduct
vacuum, pressure, or liquid tests to
ensure the secondary containment area
is operating as intended. EPA is
proposing to require tests because
sensors alone cannot immediately
determine whether repairs were
completed properly. Vacuum, pressure,
and liquid tests will be able to ensure
the adequacy of the repair by evaluating
the interstitial area. Tests after repairs
will only apply to those UST
components being repaired and not to
all components at the UST site.
EPA is proposing that tests of spill,
overfill, and interstitial areas after a
repair occur within 30 days of the
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repair. EPA chose 30 days to be
consistent with the time frame for the
tightness testing requirement after
repairing tanks and piping in § 280.33.
What issues related to this change does
EPA request comment or additional
data on?
• Should EPA consider changing the
time frame for conducting an interstitial,
spill, or overfill test from 30 days to
before returning the UST system to
service?
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
6. Phase Out Vapor Monitoring and
Groundwater Monitoring as Release
Detection Methods
What is EPA proposing?
EPA is proposing to phase out vapor
monitoring and groundwater monitoring
as methods of release detection for tanks
and piping in § 280.43.
Owners and operators of UST systems
installed before the effective date of the
final UST regulation will have five years
to comply with another release
detection monitoring method in 40 CFR
280, subpart D.
Why is EPA proposing this change?
What background information is
available about this change?
Although EPA is proposing new and
replaced tanks and piping use
interstitial monitoring (see section A–2),
UST systems installed before the
effective date of the final UST regulation
may continue to use internal or
interstitial release detection methods
listed in subpart D of the 1988 UST
regulation. Automatic tank gauging and
statistical inventory reconciliation are
internal monitoring methods and are
characterized by activities within the
tank or piping to monitor any
discrepancies. Groundwater monitoring
and vapor monitoring are external
monitoring methods and are
characterized by monitoring external
areas (specifically groundwater or soilvapor) that surround an UST system. An
interstitial method monitors the space
between tank or piping walls and
detects a release before it reaches the
environment.
EPA is proposing to phase out the two
external release detection methods—
vapor monitoring and groundwater
monitoring—because these methods
detect releases well after they enter the
environment. In addition, there are
inherent problems with installing and
confirming proper use of these methods.
As methods of release detection, they
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are less protective of the environment
than others. Regulators inspecting UST
systems report common problems they
encounter when inspecting UST
systems using vapor or groundwater
monitoring methods, such as an
insufficient number of wells or wells
improperly located to sufficiently
monitor for potential releases.
Vapor monitoring problems pertain to
confirming whether certain site
conditions exist. In particular,
surrounding soil should be sufficiently
porous to readily allow diffusion into
the excavation area; the ability to
measure vapors should not be affected
by groundwater, rainfall, or soil
moisture; and background
contamination should not interfere with
monitoring methods.
A commonly encountered
groundwater monitoring problem is that
groundwater, at times, can be more than
20 feet from the ground surface, due to
seasonal water table variations.
According to the 1988 UST regulation,
groundwater must never be more than
20 feet from the ground surface and well
slotting must be designed to allow entry
of regulated substances on the water
table into the well under both high and
low groundwater conditions.
Unfortunately, many wells are not
installed appropriately resulting in the
depth of groundwater requirement not
being met.
Many UST facilities do not have site
assessments that confirm whether site
conditions support use of vapor
monitoring and groundwater monitoring
release detection. In instances when site
assessments are available, they are often
not thorough enough to verify whether
regulatory requirements are met.
Without site assessments, regulators are
unable to determine whether site
conditions are met. Reassessing sites to
verify if site conditions support use of
vapor monitoring or groundwater
monitoring is intrusive and costly. Some
UST facilities switch between vapor
monitoring and groundwater
monitoring, depending on seasonal
variations. This practice further
complicates using these methods, such
as whether groundwater rendered the
vapor monitoring inoperable or whether
the wells are designed for both methods.
Even if optimal operating conditions are
met in both of these external methods,
by the time a release is detected,
contamination has already significantly
impacted the environment.
In contrast, internal release detection
methods have an advantage over
external monitoring methods. Internal
methods provide an early warning to
owners and operators because they
indicate unusual operating conditions,
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such as water in the tank or incremental
loss of product. An early warning alerts
owners and operators to take action and
minimize releases to the environment.
EPA estimates approximately 5
percent of all active UST systems are
using vapor monitoring or groundwater
monitoring to comply with release
monitoring requirements.67 Because of
the time it may take for owners and
operators to convert to another method
of release detection, five years will
allow sufficient time for UST system
owners and operators to begin using
another method of release detection.
What issues related to this change does
EPA request comment or additional
data on?
• Is five years for owners and
operators using vapor monitoring and
groundwater monitoring to switch to
another method too short, too long, or
an appropriate length?
• Are there circumstances at existing
facilities that would warrant a subset of
UST systems to use vapor monitoring or
groundwater monitoring beyond the
proposed period of five years. If so,
what are the circumstances?
• Is EPA’s assumption of 5 percent
accurate for the number of active UST
systems using vapor monitoring or
groundwater monitoring to comply with
release detection requirements?
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
7. Interstitial Monitoring Results,
Including Interstitial Alarms, Under
Subpart E
What is EPA proposing?
EPA is proposing clarifications of
UST owners’ and operators’
responsibilities regarding interstitial
monitoring results, including alarms,
under 40 CFR part 280, subpart E.
Specifically, EPA is proposing these
changes:
• Section 280.50(b)—add interstitial
spaces of secondarily contained UST
systems and provide examples of
unusual operating conditions.
• Section 280.50(c)—clarify that an
alarm during release detection
monitoring is subject to the reporting
requirement.
• Section 280.52(a)—require owners
and operators of UST systems with
secondary containment using interstitial
67 E2, Incorporated, memoranda and analyses
submitted under Contract EP–W–05–018, ‘‘U.S.
Environmental Protection Agency. Underground
Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.’’ These
supporting materials can be found in the docket for
the proposed rulemaking.
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monitoring follow integrity test
requirements (proposed in section B–4)
to confirm a suspected release, and
clarify actions UST owners and
operators must take if a test confirms a
leak or indicates a release exists.
Why is EPA proposing this change?
What background information is
available about this change?
The 1988 UST regulation adequately
covers interstitial monitoring.
Nonetheless, EPA is proposing these
changes to reinforce that a leak into an
interstitial space of a secondarily
contained UST system is also a potential
threat to the environment and must be
investigated, addressed, and as
necessary, reported.
In section A–2, EPA is proposing
interstitial monitoring for all new or
replaced tanks and piping. As new
systems are installed, interstitial
monitoring will become more widely
used as a method of release detection.
With this in mind, EPA wants UST
owners and operators to clearly
understand how interstitial monitoring
results, including interstitial alarms
(and alarms associated with other types
of release detection monitoring if
interstitial monitoring is not used), must
be handled.
In the 1988 UST regulation, EPA
intended that product or water in the
interstice, and alarms signifying the
presence of those conditions, are
unusual operating conditions and must
be investigated appropriately. However,
EPA did not indicate how UST owners
and operators were to address
discrepancies with interstitial spaces.
As a result, some UST owners and
operators were uncertain about how best
to respond to interstitial monitoring
results and alarms associated with
interstitial monitoring that indicate a
release may have occurred. This section
provides specific information to
alleviate uncertainty for owners and
operators.
• Add interstitial spaces of
secondarily contained UST systems and
provide examples of unusual operating
conditions
Æ Two unusual operating condition
examples—water in the interstitial
space (presumably from a breach in the
secondary wall) and product in the
interstitial space (presumably from a
breach in the primary wall)—are
important along with other suspected
release conditions listed in the 1988
UST regulation. Water or product in the
interstitial space indicates there is a
problem with the UST system that
needs to be resolved. As a result, EPA
is specifying these conditions as
unusual operating conditions and will
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require UST owners and operators
investigate and address them.
• Clarify that an alarm during release
detection monitoring, which indicates a
potential release or compromise of the
interstitial space, is subject to the
reporting requirement
Æ UST owners and operators must
appropriately address release detection
monitoring alarms. For example,
continuously monitored systems will
trigger an alarm indicating a potential
release or that the interstitial space has
been compromised. UST owners and
operators must appropriately address all
alarms in the same manner. EPA is
adding interstitial monitoring in subpart
E to emphasize its importance because
the proposed secondary containment
requirement for new and replaced
system discussed in section A–2 will
increase the use of interstitial
monitoring. UST owners and operators
will not be required to report alarms
from defective equipment or false
alarms as suspected releases. Also, UST
owners and operators will not have to
report leaks that are contained in the
interstitial space, but they must
investigate and repair the problems.
However, as required in § 280.43(g),
groundwater, soil moisture, or rainfall
must not render the testing or sampling
method inoperative so that a release
could go undetected for more than 30
days. Finally, regulated substance in the
interstitial space poses safety concerns
and can also affect testing and sampling
methods. For safety reasons, owners and
operators must ensure the method of
interstitial monitoring continues to
operate and should always remove any
regulated substance from the interstitial
area.
• Require owners and operators of
UST systems with secondary
containment using interstitial
monitoring follow integrity test
requirements (proposed in section B–4)
to confirm a suspected release and
clarify actions UST owners and
operators must take if a test confirms a
leak or indicates a release exists
Æ Requiring UST owners and
operators to follow integrity test
requirements of the interstitial area will
ensure both inner and outer walls are
checked when investigating a suspected
release. EPA also is taking the position
that it is important to clarify actions
UST owners and operators must take if
a test confirms a leak or indicates a
release exists. If a leak is confirmed,
UST owners and operators must correct
or address the problem. In addition to
options listed in the 1988 UST
regulation, EPA is proposing to include
closure as another option. Nothing in
this proposal changes the requirement
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in subpart F for UST owners and
operators to take corrective action if a
release occurred.
What issues related to this change does
EPA request comment or additional
data on?
EPA did not identify specific issues
for comment.
E. General Updates
1. Incorporate Newer Technologies
What is EPA proposing?
EPA is proposing to include
technologies developed since issuing
the 1988 UST regulation and clarify the
use of those technologies. EPA is
proposing these changes:
• Tanks—revise steel-fiberglassreinforced-plastic composite in
§ 280.20(a)(3) to steel tank clad or
jacketed with a non-corrodible material.
UST owners and operators will be able
to use jacketed tanks to meet EPA’s
proposed requirement for secondary
containment and interstitial monitoring
described in section A–2.
• Piping—revise fiberglass-reinforced
plastic in § 280.20(b)(1) to noncorrodible material. This will allow UST
owners and operators to install other
piping, such as flexible plastic, that
does not corrode.
• Release detection—add two release
detection options: Continuous in-tank
leak detection (CITLD) and statistical
inventory reconciliation (SIR). UST
owners and operators will be able to use
these additional options to meet release
detection requirements in § 280.40, as
long as the methods meet the following:
Æ CITLD—automatic tank gauge
operating on an uninterrupted basis or
operating within a process that allows
the system to gather incremental
measurements to determine the leak
status of the tank at least once every 30
days.
Æ SIR—quantitative analysis with a
calculated leak rate capable of detecting
a 0.2 gallon per hour leak rate within 30
days with a probability of detection of
0.95 and a probability of false alarm of
0.05 is required, based on a threshold
that does not exceed one-half the
minimum leak rate.
EPA is proposing to list three
additional continuous interstitial
monitoring methods in § 280.43(g):
Liquid-filled, pressure, and vacuum
interstitial monitoring. These methods
must be capable of detecting a breach in
both the inner and outer walls of the
tank and piping.
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Why is EPA proposing this change?
What background information is
available about this change?
Since EPA promulgated the 1988 UST
regulation, newer tank, piping, and
release detection technologies have been
developed and are being used. EPA is
proposing this change to acknowledge
newer UST related technologies and
clarify the use of these technologies.
Clad and Jacketed Tanks
The 1988 UST regulation allows these
tank technologies: Coated and
cathodically protected steel; fiberglass
reinforced plastic; steel-fiberglassreinforced-plastic composite; and metal
without additional corrosion protection,
provided that a corrosion expert
determines the site is not corrosive
enough to cause a release from corrosion
during the tank’s life. The 1988
regulation also allows use of other tank
technologies that implementing
agencies determine are no less
protective of human health and the
environment than those listed above.
Additional non-corrodible materials are
now used as claddings for steel tanks,
and they are as effective at preventing
corrosion as technologies in the 1988
regulation. EPA considers a cladding to
be a non-corrosive dielectric material,
bonded to the steel tank with sufficient
durability to prevent corrosion during
the tank’s life. EPA did not include
jacketed tanks in the 1988 regulation,
even though they are no less protective
of human health and the environment
than technologies listed in the
regulation. EPA considers jacketed to be
a non-corrosive dielectric material that:
Is constructed as secondary containment
(jacketed) around a steel tank; has
sufficient durability to prevent
corrosion during the tank’s life; and
prevents a regulated substance released
from the primary steel tank wall from
reaching the environment. EPA
estimates 10 percent of regulated tanks
today are jacketed with a non-corrodible
material and 18 percent are clad with a
non-corrodible material.68
Non-Corrodible Piping
The 1988 UST regulation allows
fiberglass-reinforced plastic piping as a
non-corrodible piping option, as well as
other piping technologies that
implementing agencies determine are no
less protective of human health and the
environment than those in the
68 E2, Incorporated, memoranda and analyses
submitted under Contract EP–W–05–018, ‘‘U.S.
Environmental Protection Agency. Underground
Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.’’ These
supporting materials can be found in the docket for
the proposed rulemaking.
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regulation. Non-corrodible piping not
made of fiberglass-reinforced plastic (in
particular, flexible plastic piping) was
installed beginning in the 1990s and has
evolved over the past 20 years. Flexible
plastic piping is made of various noncorrodible materials, such as
polyethylene and polyurethane. EPA
estimates at least 13 percent of regulated
piping currently installed is made of
non-corrodible materials that are not
fiberglass-reinforced plastic.69 Revising
fiberglass-reinforced piping to noncorrodible piping will allow UST
owners and operators to install other
types of non-corrodible piping, such as
flexible plastic, without requiring
implementing agencies to make a
determination.
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Release Detection Technologies
The 1988 UST regulation allows UST
owners and operators to use other
methods that meet release detection
performance criteria listed at
§ 280.43(h). Although CITLD and SIR
are allowed under § 280.43(h), it is
important to specify both by name.
CITLD
The 1988 UST regulation allows ATG
systems as a recognized method of
release detection. However, it is
generally listed with performance
requirements consistent with the
method being used to perform a static
test. ATG relies on system down time,
absent product delivery or dispensing
activities. In static testing mode, the
ATG system analyzes product level and
determines whether or not a leak is
present during that down time. Yet for
years, UST owners and operators used
ATG systems as a means of continually
monitoring tanks for potential releases.
Continuous in-tank leak detection has
evolved as a reliable means of providing
release detection equivalent to other
methods specified in § 280.41. Within
this category of methods, EPA will also
allow continuous in-tank methods
where the system incrementally gathers
measurements to determine the tank’s
leak status within the 30-day monitoring
period. Today’s proposal formally
recognizes CITLD as a release detection
method in § 280.43(d). Per § 280.41, a
conclusive pass or fail result must be
obtained within the 30-day monitoring
period. All monitoring records must be
maintained according to § 280.45.
Another method of release detection is
69 E2, Incorporated, memoranda and analyses
submitted under Contract EP–W–05–018, ‘‘U.S.
Environmental Protection Agency. Underground
Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.’’ These
supporting materials can be found in the docket for
the proposed rulemaking.
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required in the event of an inconclusive
result. UST owners and operators may
perform an in-tank static test using the
ATG system or another method in
subpart D.
SIR
Today’s proposal adds SIR by name to
the final UST regulation and clarifies its
use. SIR must:
• Report a quantitative result with
calculated leak rate;
• Be capable of detecting a leak rate
of at least 0.2 gallon per hour with a
probability of detection of not less than
0.95 and a probability of false alarm of
no greater than 0.05; and
• Use a threshold that does not
exceed one-half the minimum
detectable leak rate.
A quantitative result with a calculated
leak rate is necessary to effectively
perform release detection using SIR.
Some SIR methods are qualitative based
methods that simply provide a result of
pass or fail without any additional
information for UST owners and
operators to gauge the validity of the
reported results. Based on information
in NWGLDE’s list,70 approximately 15
percent of SIR methods listed are
qualitative-based methods. Many state
UST implementing agencies already
only allow the use of quantitative
methods. Today’s proposal will no
longer allow qualitative SIR as an option
for meeting the release detection
requirement.
Consistent with some of the release
detection methods described in
§ 280.43(h), EPA maintained the
performance standard of 0.2 gallon per
hour with a probability of detection of
0.95 and a probability of false alarm of
0.05. However, we are not requiring the
additional standard of 150 gallons
within a month per § 280.43(h). EPA
included this additional standard in the
1988 UST regulation to primarily
address external methods. EPA added
the standard because it is more difficult
to demonstrate that external methods
meet a small hourly leak rate than a
larger, though equivalent, volume. SIR
is an in-tank monitoring method and the
0.2 gallon per hour standard with a
probability of detection (Pd) of 0.95 and
a probability of false alarm (Pfa) of 0.05
is the applicable standard to use.
SIR must also meet EPA’s established
requirement for probability of detection
and probability of false alarm. In a
normal probability distribution, SIR
data typically analyzed through the
70 National Work Group On Leak Detection
Evaluation’s (NWGLDE) List Of Leak Detection
Evaluations for Storage Tank Systems: https://
www.nwglde.org/.
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calculation of the reportable values of
minimum detectable leak rate (MDL)
and the leak declaration threshold (T)
are related as follows:
• MDL is always greater than T
• Pd = (1–Pfa), then MDL = 2 times
T (i.e., T = 1⁄2 MDL).
Any analysis of data indicating a
threshold value greater than one-half
minimum detectable leak rate should be
appropriately investigated as a
suspected release.
In this proposal, EPA is addressing
the following issues associated with
using SIR:
• SIR is not the same as inventory
control
Æ For years, users, vendors, and
regulators incorrectly linked SIR to the
inventory control method described in
§ 280.43(a). SIR is more sophisticated
than inventory control and not subject
to the same requirement to combine it
with tank tightness testing and limit its
use to 10 years. Note § 280.50(c)(2)
states, ‘‘In the case of inventory control,
a second month of data does not
confirm the initial result.’’ This
language allowed owners and operators
to use a second month of inventory
control data to confirm initial possible
failure results. However, this allowance
does not apply to SIR.
• Results for release detection,
including SIR, are required within the
30-day monitoring period
Æ EPA considered including a
requirement that UST owners and
operators obtain a record of SIR results
within 30 days. However, we believe
this requirement is adequately covered
in 40 CFR part 280, subpart D of the
1988 UST regulation. As § 280.41 states,
‘‘Tanks * * * must be monitored for
releases at least every 30 days using one
of the methods listed in § 280.43(d)
through (h) * * *’’. In today’s proposal,
EPA is adding a subsection to formally
recognize SIR. A definitive result of pass
or fail that identifies the tank’s leak
status is required within the 30-day
monitoring period for all release
detection methods, including SIR.
• Owners and operators must use
another method of release detection if
SIR results are inconclusive results
Æ For years, implementing agencies
have been concerned about inconclusive
results when using SIR for release
detection. In 1993, EPA issued a policy
regarding inconclusive SIR results,71
which says all methods used to meet
release detection requirements in
§ 280.41 must obtain a conclusive result
of pass or fail within the 30-day
71 UST Technical compendium, question and
answer number 21: https://epa.gov/oust/compend/
rd.htm.
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monitoring period. All monitoring
records must be maintained according
to § 280.45. For SIR, this means UST
owners and operators must obtain a
report determining release status within
the 30-day monitoring period. Another
method of release detection is required:
when results are inconclusive; prior to
sufficient data being gathered to
generate an initial report at startup; or
when a report is not available for any
month of monitoring.
• Initial SIR report at startup
Æ SIR methods need to gather data
over a period of time in order to
determine whether the tank is leaking.
In some cases, regulatory agencies have
addressed significant lag times between
when data is collected to when a tank
status determination is available to
owners and operators. NWGLDE’s list of
third-party evaluated methods indicates
the data collection period required for
SIR methods ranges from 15 to 90 days.
However, most methods require
between 23 to 30 days to gather
sufficient measurements that provide an
accurate result. Any method that goes
beyond a 30-day monitoring period is
inconsistent with the established
requirement and does not protect
human health and the environment. It is
imperative that UST owners and
operators determine the status of their
tanks within the established monitoring
period to avoid increased risk of
contamination.
Æ EPA recognizes that a rolling
collection of data may be used to
analyze the leak status of the tank. For
example, data from the previous 30-day
monitoring period may be added to
measurements taken within the current
30-day monitoring period to determine
whether or not the tank is leaking.
However, the majority of data must
come from the current 30-day period
and another method of release detection
must be used to monitor the tank during
this startup period. Subsequent
monitoring continuously rolls data
forward and provides sufficient data in
a timely manner to determine pass or
fail.
Interstitial Monitoring
EPA is proposing to add three
methods of interstitial monitoring—
vacuum, pressure, and liquid-filled
methods—in § 280.43(g)(4). Although
these interstitial methods are covered
under the general description provided
in § 280.43(g), These methods should be
included as distinct interstitial
monitoring options. Each of these
methods must be capable of detecting
breaches in both the inner and outer
walls of secondarily contained tanks
and secondarily contained piping.
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What issues related to this change does
EPA request comment or additional
data on?
• Should EPA require specific
performance standards for vacuum,
pressure, and liquid-filled interstitial
monitoring? If so, what should the
performance standards be and why?
• Are there performance standards for
release detection methods that should
be added or removed?
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
2. Updates to Codes of Practice Listed in
the UST Regulation
What Is EPA Proposing?
EPA is proposing to update the codes
of practice (also called standards or
recommended practices) listed in the
1988 UST regulation to reflect new
codes, changes to code names, and new
nationally recognized associations and
independent testing laboratories. EPA
proposes to update, add, or remove
codes of practice to the following
specific areas of the 1988 UST
regulation:
Section 280.11—Interim Prohibition for
Deferred UST Systems
Updated Codes:
—NACE International Recommended
Practice RP 0285, Corrosion Control of
Underground Storage Tank Systems
by Cathodic Protection
Added Codes:
—NACE International Standard Practice
SP 0169, Control of External
Corrosion on Underground or
Submerged Metallic Piping Systems
—American Petroleum Institute
Recommended Practice 1632,
Cathodic Protection of Underground
Petroleum Storage Tanks and Piping
Systems
—Steel Tank Institute Recommended
Practice R892, Recommended Practice
for Corrosion Protection of
Underground Piping Networks
Associated with Liquid Petroleum
Storage and Dispensing Systems
Section 280.20(a)(1)—Fiberglass Tanks
Updated Codes:
—Underwriters Laboratories Standard
1316, Glass-Fiber-Reinforced Plastic
Underground Storage Tanks for
Petroleum Products, Alcohols, and
Alcohol-Gasoline Mixtures
—Underwriters Laboratories of Canada
S615, Standard for Reinforced Plastic
Underground Tanks for Flammable
and Combustible Liquids
Removed Codes:
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—American Society of Testing and
Materials Standard D4021–86,
Standard Specification for GlassFiber-Reinforced Polyester
Underground Petroleum Storage
Tanks
Section 280.20(a)(2)—Steel Tanks With
Cathodic Protection
Updated Codes:
—Steel Tank Institute Specification stiP3® Specification and Manual for
External Corrosion Protection of
Underground Steel Storage Tanks
—Underwriters Laboratories Standard
1746, Standard for External Corrosion
Protection Systems for Steel
Underground Storage Tanks
—Underwriters Laboratories of Canada
S603, Standard for Steel Underground
Tanks for Flammable and
Combustible Liquids
—Underwriters Laboratories of Canada
S603.1, Standard for External
Corrosion Protection Systems for Steel
Underground Tanks for Flammable
and Combustible Liquids
—Underwriters Laboratories of Canada
S631, Standard for Isolating Bushings
for Steel Underground Tanks
Protected with External Corrosion
Protection Systems
—NACE International Recommended
Practice RP 0285, Corrosion Control of
Underground Storage Systems by
Cathodic Protection
—Underwriters Laboratories Standard
58, Standard for Steel Underground
Tanks for Flammable and
Combustible Liquids
Added Codes:
—Steel Tank Institute Standard F841,
Standard for Dual Wall Underground
Steel Storage Tanks
Section 280.20(a)(3)—Clad or Jacketed
Steel Tanks
Updated Codes:
—Underwriters Laboratories Standard
1746, Standard for External Corrosion
Protection Systems for Steel
Underground Storage Tanks
Added Codes:
—Steel Tank Institute Specification
F894, ACT–100® Specification for
External Corrosion Protection of FRP
Composite Steel USTs
—Steel Tank Institute Specification
F961, ACT–100–U® Specification for
External Corrosion Protection of
Composite Steel Underground Storage
Tanks
—Steel Tank Institute Specification
F922, Steel Tank Institute
Specification for Permatank®
Removed Codes:
—Association for Composite Tanks
ACT–100, Specification for the
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Fabrication of FRP Clad Underground
Storage Tanks
Section 280.20(a)(6)—Secondary
Containment Tanks (New Addition to
the Regulation—See Section A–2)
Added Codes:
—Underwriters Laboratories Standard
58, Standard for Steel Underground
Tanks for Flammable and
Combustible Liquids
—Underwriters Laboratories Standard
1316, Glass-Fiber-Reinforced Plastic
Underground Storage Tanks for
Petroleum Products, Alcohols, and
Alcohol-Gasoline Mixtures
—Underwriters Laboratories Standard
1746, Standard for External Corrosion
Protection Systems for Steel
Underground Storage Tanks
—Steel Tank Institute Standard F841,
Standard for Dual Wall Underground
Steel Storage Tanks
—Steel Tank Institute Specification
F922, Steel Tank Institute
Specification for Permatank®
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Section 280.20(b)(1)—Non-corrodible
Piping
Updated Codes:
—Underwriters Laboratories Standard
971, Standard for Non-Metallic
Underground Piping for Flammable
Liquids
—Underwriters Laboratories of Canada
Standard S660, Standard for NonMetallic Underground Piping for
Flammable Liquids
Removed Codes:
—Underwriters Laboratories Standard
567, Pipe Connectors for Flammable
and Combustible and LP Gas
—Underwriters Laboratories of Canada
Standard CAN 4–S633–M81, Flexible
Underground Hose Connectors
Section 280.20(b)(2)—Steel Piping With
Cathodic Protection
Updated Codes:
—American Petroleum Institute
Recommended Practice 1632,
Cathodic Protection of Underground
Petroleum Storage Tanks and Piping
Systems
—NACE International Standard Practice
SP 0169, Control of External
Corrosion on Underground or
Submerged Metallic Piping Systems
Added Codes:
—Underwriters Laboratories Subject
971A, Outline of Investigation for
Metallic Underground Fuel Pipe
—Steel Tank Institute Recommended
Practice R892, Recommended Practice
for Corrosion Protection of
Underground Piping Networks
Associated with Liquid Petroleum
Storage and Dispensing Systems
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—NACE International Recommended
Practice RP 0285, Corrosion Control of
Underground Storage Systems by
Cathodic Protection
Removed Codes:
—National Fire Protection Association
Standard 30, Flammable and
Combustible Liquids Code
—American Petroleum Institute
Publication 1615, Installation of
Underground Petroleum Storage
Systems
—American Petroleum Institute
Recommended Practice 1631, Interior
Lining and Periodic Inspection of
Underground Storage Tanks
—National Leak Prevention Association
Standard 631, Entry, Cleaning,
Interior Inspection, Repair, and Lining
of Underground Storage Tanks
—Ken Wilcox Associates Recommended
Practice, Recommended Practice for
Inspecting Buried Lined Steel Tanks
Using a Video Camera
Section 280.20(b)(3)—Metal Piping
Without Additional Corrosion
Protection
Removed Codes:
—National Fire Protection Association
Standard 30, Flammable and
Combustible Liquids Code
—National Association of Corrosion
Engineers Standard RP–01–69,
Control of External Corrosion on
Submerged Metallic Piping Systems
Section 280.21(e)—Upgrade
Requirements for Previously Deferred
UST Systems (New Addition to the
Regulation—See Section C)
Added Codes:
—NACE International Recommended
Practice RP 0285, Control of
Underground Storage Tank Systems
by Cathodic Protection
—NACE International Standard Practice
SP 0169, Control of External
Corrosion on Underground or
Submerged Metallic Piping Systems
—National Leak Prevention Association
Standard 631, Entry, Cleaning,
Interior Inspection, Repair, and Lining
of Underground Storage Tanks
—American Society for Testing and
Materials Standard G158, Standard
Guide for Three Methods of Assessing
Buried Steel Tanks
Section 280.20(b)(5)—Secondary
Containment Piping (New Addition to
the Regulation—See Section A–2)
Added Codes:
—Underwriters Laboratories Standard
971, Standard for Non-Metallic
Underground Piping for Flammable
Liquids
—Underwriters Laboratories Subject
971A, Outline of Investigation for
Metallic Underground Fuel Pipe
Section 280.20(d)—Installation
Updated Codes:
—American Petroleum Institute
Publication 1615, Installation of
Underground Petroleum Storage
System
—Petroleum Equipment Institute
Publication RP100, Recommended
Practices for Installation of
Underground Liquid Storage Systems
Added Codes:
—National Fire Protection Association
Standard 30, Flammable and
Combustible Liquids Code
—National Fire Protection Association
Standard 30A, Code for Motor Fuel
Dispensing Facilities and Repair
Garages
Removed Codes:
—American National Standards
Institute Standard B31.3, Petroleum
Refinery Piping
—American National Standards
Institute Standard B31.4, Liquid
Petroleum Transportation Piping
System
Section 280.21—Lining Inspection
Standards (New Addition to the
Regulation—See Section E–3)
Added Codes:
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Section 280.30—Spill and Overfill
Control
Updated Codes:
—National Fire Protection Association
Standard 385, Standard for Tank
Vehicles for Flammable and
Combustible Liquids
—American Petroleum Institute
Recommended Practice 1621, Bulk
Liquid Stock Control at Retail Outlets
Added Codes:
—American Petroleum Institute
Recommended Practice 1007, Loading
and Unloading of MC 306/DOT 406
Cargo Tank Motor Vehicles
Removed Codes:
—National Fire Protection Association
Standard 30, Flammable and
Combustible Liquids Code
Section 280.31—Operation and
Maintenance of Corrosion Protection
Updated Codes:
—NACE International Recommended
Practice RP 0285, Control of
Underground Storage Tank Systems
by Cathodic Protection
Added Codes:
—NACE International Standard Practice
SP 0169, Control of External
Corrosion on Underground or
Submerged Metallic Piping Systems
—NACE International Test Method TM
0101, Measurement Techniques
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Related to Criteria for Cathodic
Protection on Underground or
Submerged Metallic Tank Systems
—NACE International Test Method
TM0497, Measurement Techniques
Related to Criteria for Cathodic
Protection on Underground or
Submerged Metallic Piping Systems
—Steel Tank Institute Recommended
Practice R051, Cathodic Protection
Testing Procedures for sti-P3 USTs
Section 280.32—Compatibility
Removed Codes:
—American Petroleum Institute
Publication 1626, Storing and
Handling Ethanol and GasolineEthanol Blends at Distribution
Terminals and Service Stations
—American Petroleum Institute
Publication 1627, Storage and
Handling of Gasoline-Methanol/
Cosolvent Blends at Distribution
Terminals and Service Stations
Section 280.43(a)—Inventory Control
Updated Codes:
—American Petroleum Institute
Recommended Practice RP 1621, Bulk
Liquid Stock Control at Retail Outlets
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Updated Codes:
—National Fire Protection Association
Standard 30, Flammable and
Combustible Liquids Code
—American Petroleum Institute
Recommended Practice RP 2200,
Repairing Crude Oil, Liquified
Petroleum Gas, and Product Pipelines
—American Petroleum Institute
Recommended Practice RP 1631,
Interior Lining and Periodic
Inspection of Underground Storage
Tanks
—National Leak Prevention Association
Standard 631, Entry, Cleaning,
Interior Inspection, Repair, and Lining
of Underground Storage Tanks
Added Codes:
—National Fire Protection Association
Standard 326, Safeguarding of Tanks
and Containers for Entry, Cleaning, or
Repair
—Steel Tank Institute Recommended
Practice R972, Recommended Practice
for the Addition of Supplemental
Anodes to sti-P3® Tanks
—NACE International Recommended
Practice RP 0285, Control of
Underground Storage Tank Systems
by Cathodic Protection
—Fiberglass Tank and Pipe Institute
Recommended Practice T–95–02,
Remanufacturing of Fiberglass
Reinforced Plastic (FRP) Underground
Storage Tanks
Section 280.36—Secondary
Containment Testing (New Addition to
the Regulation—See Section B–4)
Added Codes:
—Steel Tank Institute Recommended
Practice R012, Recommended Practice
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Section 280.37—Walkthrough
Inspections (New Addition to the
Regulation—See Section B–1)
Added Codes:
—Petroleum Equipment Institute
Recommended Practice RP 900,
Recommended Practices for the
Inspection and Maintenance of UST
Systems
Section 280.33—Repairs
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for Interstitial Tightness Testing of
Existing Underground Double Wall
Steel Tanks
—Fiberglass Tank and Pipe Institute
Protocol, Field Test Protocol for
Testing the Annular Space of Installed
Underground Fiberglass Double and
Triple-Wall Tanks with Dry Annular
Space
Section 280.43(g)—Interstitial
Monitoring
Removed Codes:
—Steel Tank Institute Standard F841,
Standard for Dual Wall Underground
Steel Storage Tanks (moved to new
section 280.20(a)(6))
Section 280.71—Permanent Closure
Updated Codes:
—American Petroleum Institute
Recommended Practice RP 1604,
Closure of Underground Petroleum
Storage Tanks
—American Petroleum Institute
Recommended Practice RP 1631,
Interior Lining and Periodic
Inspection of Underground Storage
Tanks
—The National Institute for
Occupational Safety and Health
Publication 80–106, Criteria for a
Recommended Standard * * *
Working in Confined Space
Added Codes:
—American Petroleum Institute
Recommended Practice 2016,
Guidelines and Procedures for
Entering and Cleaning Petroleum
Storage Tanks
—National Fire Protection Association
Standard 326, Safeguarding of Tanks
and Containers for Entry, Cleaning, or
Repair
Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing this change to
update the codes of practice associated
with regulated UST systems. The 1988
UST regulation relies heavily on codes
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of practice developed by nationally
recognized associations or independent
testing laboratories.
EPA reviewed information on more
than 200 codes of practice from more
than 25 code-making groups that have
been developed or revised since the
1988 regulation.72 As a result of this
review, EPA proposes to add 18 codes
of practice not previously listed in the
1988 regulation, remove or move 12,
and update all codes of practice in the
1988 UST regulation (see the specific
additions, updates, and removals listed
above). EPA is proposing to add the 18
codes of practice that were previously
not listed because they are applicable to
the UST regulation and did not exist
when EPA originally promulgated the
1988 UST regulation. EPA is proposing
to remove or move the 12 codes of
practice in the 1988 UST regulation for
one of the following reasons:
• The code of practice is out of date,
no longer available, was withdrawn, or
rescinded;
• The code of practice did not
provide any information appropriate to
the section of the regulation where it
was referenced;
• The information in the code of
practice did not adequately address the
part of the regulation where it was
referenced; or
• The code of practice is no longer
needed.
For example, the Association for
Composite Tanks ACT–100 tank
standard was listed in § 280.20(a)(3) as
a code of practice for meeting the clad
tank requirement. EPA is removing this
code of practice because both the
association and code of practice no
longer exist.
In several cases, EPA is proposing to
move a code of practice from one
section of the 1988 UST regulation to
another section. For example, EPA is
proposing to move Steel Tank Institute
Standard F841, Standard for Dual Wall
Underground Steel Storage Tanks from
§ 280.43(g)—interstitial monitoring to
§ 280.20(a)(6)—secondary containment
tanks. EPA is proposing this because we
are adding secondary containment
requirements to the performance
standards for new UST systems portion
of this proposed UST regulation.
Note: EPA is aware of at least one code of
practice (Petroleum Equipment Institute
standard for testing of spill, overfill,
interstitial areas, and release detection)
72 E2, Incorporated, memoranda and analyses
submitted under Contract EP–W–05–018, ‘‘U.S.
Environmental Protection Agency. Underground
Storage Tanks/Leaking Underground Storage Tanks
Analytical and Technical Support.’’ These
supporting materials can be found in the docket for
the proposed rulemaking.
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currently being developed that could be
potentially relevant to this proposed UST
regulation. Other standards may be
developed before EPA publishes a final UST
regulation. If so, EPA will consider including
them in the final UST regulation.
What issues related to this change does
EPA request comment or additional
data on?
• Should other codes of practice be
added to or removed from the UST
regulation? If so, please provide EPA
with information about the code and the
specific location in the UST regulation
where the code should be included or
removed.
• The regulations at § 280.20(d)
require that all tanks and piping be
properly installed in accordance with a
code of practice developed by a
nationally recognized association or
independent testing laboratory and in
accordance with manufacturer’s
instructions. Since the installation
codes of practice also address other UST
system components such as spill and
overfill, should EPA consider revising
§ 280.20(d) such that all portions of the
UST system must be installed according
to a code of practice and according to
manufacturer’s instructions?
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
3. Updates to Remove Old Upgrade and
Implementation Deadlines
What is EPA proposing?
EPA is proposing to revise the UST
regulation to remove references to the
1998 deadline and old phase-in
schedules, while continuing to allow
testing of corrosion protection and
release detection. For those deferred
UST systems EPA is proposing to
regulate, we are proposing those
systems be allowed to upgrade with
spill, overfill, and corrosion protection.
EPA is proposing the following specific
revisions:
Revise upgrading of existing UST
systems in the 1988 UST regulation
(§ 280.21).
• Remove the 1998 upgrade deadline
references, but continue to allow:
Æ Testing of internally-lined USTs;
Æ Tanks and piping with cathodic
protection; and
Æ Upgrades of deferred UST systems
EPA is proposing to regulate, including
wastewater treatment tank systems,
airport hydrant systems, UST systems
with field-constructed tanks, and UST
systems that store fuel solely for use by
emergency power generators. See
section C for additional information on
deferred UST systems.
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• Require UST systems not upgraded
with corrosion protection, spill, or
overfill prevention be permanently
closed according to subpart G, unless
the implementing agency determines an
upgrade is appropriate or the UST
system was deferred in the 1988 UST
regulation.
Revise release detection requirements
in the 1988 UST regulation.
• Section 280.40
Æ Remove phase-in schedule for
release detection probabilities;
Æ Remove phase-in schedule for
release detection monitoring;
Æ Remove references to upgrade
deadlines;
Æ Remove references to existing
USTs; and
Æ Address deferred UST systems EPA
is proposing to regulate, add language
about implementing release detection
monitoring for these systems in
§ 280.40(c).
• Section 280.41
Æ Remove inventory control and
annual tightness testing as a regulatory
option;
Æ Remove reference to upgrade
deadlines; and
Æ Make the inventory control and five
year tightness testing language historical
by putting language in this section in
the past tense.
• Section 280.42
Æ Remove 1998 references and
upgrade language for existing hazardous
substance UST systems.
EPA is proposing to remove the
phase-in schedule in § 280.91 of subpart
H to acknowledge that financial
responsibility implementation deadlines
are passed and remove references to
§ 280.91 and the deadlines in § 280.90.
In addition, EPA is proposing to revise
§ 280.91 to reference the phase-in
schedule for deferred UST systems EPA
is proposing to regulate at § 280.10.
Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing these changes to
acknowledge that the 1998 deadline for
upgrading UST systems with release
prevention and the 1990s release
detection and financial responsibility
deadlines passed more than a decade
ago. Owners and operators had more
than two decades to upgrade their UST
systems and meet the 1988 UST
regulation. In addition, all UST facilities
have been inspected at least once and
are required to meet release detection,
release prevention, and financial
responsibility requirements. EPA is
proposing owners and operators of
upgraded UST systems continue
conducting cathodic protection and
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71749
internal lining testing consistent with
how they previously performed these
tests.
For release detection, EPA is
proposing to eliminate the phase-in for
both release detection probabilities and
release detection monitoring. EPA is
proposing to eliminate these two phasein parts because the deadlines for
implementing these requirements have
passed. Owners and operators have been
implementing these requirements for
more than two decades. The last phasein period applied to systems installed
between 1980 and 1988, giving owners
and operators until 1993 to meet the
subpart D requirements. Any new UST
installed after 1993 had to meet release
detection requirements when installed.
To meet the release detection
requirement, § 280.41 allows owners
and operators of USTs less than 10 years
old to use a combination of monthly
inventory control with tank tightness
testing every five years, until the UST
has been installed for 10 years. When
the UST is 10 years old, owners and
operators must use another release
detection method listed in subpart D.
For new and replaced UST systems
installed after the effective date of the
final UST regulation, interstitial
monitoring will be required. The new
interstitial monitoring requirement will
make inventory control and tank
tightness testing obsolete as a release
detection method 10 years after the UST
regulation is finalized.
For hazardous substance UST systems
release detection, EPA is proposing to
remove 1998 deadline and upgrade
references. The 1988 UST regulation in
§ 280.41 required existing UST systems
meet the requirements for petroleum
UST systems until 1998. After 1998, all
new and existing hazardous substance
UST systems must meet requirements
for new hazardous substance UST
systems. Since the 1998 deadline has
passed, these changes will clarify the
hazardous substance UST system
requirements.
For financial responsibility, EPA is
proposing to remove the phase-in dates
in § 280.91. These phase-in dates passed
more than a decade ago and are no
longer needed. In addition, § 280.90(b)
and (e) contain references to § 280.91
and compliance dates that need to be
removed.
UST systems with field constructed
tanks, airport hydrant systems, and
wastewater treatment tank systems may
be upgraded according to § 280.21.
However, EPA is proposing to no longer
allow UST systems regulated under the
1988 UST regulation to be upgraded if
they have never met the upgrade
requirements. Unless the implementing
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agency determines that an UST system
is acceptable to upgrade, non-upgraded
UST systems must be permanently
closed according to the closure
requirements in subpart G. UST systems
that have not been upgraded are older
and have been in the ground for more
than two decades. In addition, metal
USTs and piping without corrosion
protection pose a significant risk to
human health and the environment
because the metal in contact with soil
corrodes. EPA is proposing that
implementing agencies make case-bycase determinations on when to allow
upgrades. EPA does not expect
implementing agencies to allow
continued use of USTs or piping not
upgraded with corrosion protection.
However, some implementing agencies
may decide to allow owners and
operators of UST systems with corrosion
protection, but without spill or overfill
prevention, to add spill or overfill
prevention instead of requiring
permanent closure.
The proposed requirements in
§ 280.21 will allow UST systems EPA is
proposing to no longer defer to be
upgraded. See section C for additional
information on upgrading these UST
systems.
What issues related to this change does
EPA request comment or additional
data on?
• Does removing the deadlines and
making upgrades historical cause any
unintended regulatory consequences?
• Should EPA consider not allowing
the implementing agency the flexibility
of making a determination to allow an
upgrade?
Please provide reasoning or
justification if you disagree with or
propose something different from EPA’s
proposal.
4. Editorial and Technical Corrections
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
What is EPA proposing?
EPA is proposing these editorial
corrections to the 1988 UST regulation:
• Where ‘‘industry codes’’ and ‘‘codes
and standards’’ are used, replace with
‘‘codes of practice’’
• Revise to appropriately use the
terms: part, subpart, section, and
paragraph
• Section 280.10(c)(3)—change ‘‘10
CFR part 50 Appendix A’’ to ‘‘10 CFR
part 50’’
• Section 280.20(a)(2), paragraph (C)
in the note—change ‘‘G03.1’’ to ‘‘603.1’’
• Section 280.21(b)(2)(iii)—change
‘‘by conducting two (2) tightness tests
that meet the requirements of
§ 280.43(c). The first tightness test must
be conducted prior to installing the
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Jkt 226001
cathodic protection system. The second
tightness test must be conducted
between three (3) and six (6) months
following the first operation of the
cathodic protection system; or’’ to ‘‘by
conducting two tightness tests that meet
the requirements of § 280.43(c). The first
tightness test must be conducted prior
to installing the cathodic protection
system. The second tightness test must
be conducted between three and six
months following the first operation of
the cathodic protection system; or’’
• Section 280.20(c)(1)(ii)(C)—change
‘‘operator’’ to ‘‘transfer operator’’
• Section 280.22(a)—change ‘‘Any
owner who brings an underground
storage tank system into use after May
8, 1986, must within 30 days of bringing
such tank into use, submit, in the form
prescribed in Appendix I of this part, a
notice of existence of such tank system
to the state or local agency or
department designated in Appendix II
of this part to receive such notice.’’ to
‘‘After May 8, 1986, an owner must
submit notice of a tank system’s
existence to the implementing agency
within 30 days of bringing the
underground storage tank system into
use. Owners must use the form in
Appendix I of this part.’’
• Section 280.22(g)—change ‘‘The
form provided in Appendix III of this
part may be used to comply with this
requirement.’’ to ‘‘The statement
provided in Appendix III of this part,
when used on shipping tickets and
invoices, may be used to comply with
this requirement.’’
• Section 280.31—change ‘‘for as long
as the UST system is used to store
regulated substances’’ to ‘‘until the UST
system is permanently closed or
undergoes a change-in-service pursuant
to § 280.71.’’
• Section 280.31—change ‘‘steel’’ to
‘‘metal’’
• Section 280.33(c)—change
‘‘fiberglass pipes’’ to ‘‘non-corrodible
pipes’’
• Section 280.33(g)—change ‘‘for the
remaining operating life of the UST
system’’ to ‘‘until the UST system is
permanently closed or undergoes a
change-in-service pursuant to § 280.71.’’
• Section 280.34—change ‘‘Resource
Conservation and Recovery Act’’ to
‘‘Solid Waste Disposal Act’’
• Section 280.34(b)(2)—change cite
from ‘‘280.31’’ to ‘‘280.31(d)’’
• Section 280.40(a)(3)—change
‘‘probability of detection (Pd) of 0.95
and probability of false alarm (Pfa) of
0.05.’’ to ‘‘probability of detection of
0.95 and probability of false alarm of
0.05.’’
• Section 280.41(b)(2)—change
‘‘conduct’’ to ‘‘conducted’’
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• Section 280.42(a)(1)(ii)—change
‘‘released from the tank system’’ to
‘‘leaked from the primary containment’’
• Section 280.42(d)—delete
‘‘jacketing of’’ from ‘‘* * * jacketing of
double-walled pipe)* * *’’
• Section 280.43(b)(4)—change
‘‘leak’’ to ‘‘release’’
• Section 280.43(b)(5)—delete
‘‘manual’’ from ‘‘manual inventory
control’’
• Section 280.52(a)(1)—change
‘‘repair, replace, or upgrade the UST
system’’ to ‘‘repair, replace, upgrade, or
close the UST system’’
• Section 280.52(a)(1)—change
‘‘leak’’ to ‘‘release’’
• Section 280.52(a)(2)—change
‘‘leak’’ to ‘‘release’’
• Section 280.52(a)(3)—change
‘‘leak’’ to ‘‘release’’
• Section 280.92—definition for
provider of financial assurance—change
‘‘§§ 280.95–280.103’’ to ‘‘§§ 280.95–
280.107’’
• Section 280.92, § 280.95(b)(1)(iii),
§ 280.95(c)(5), and § 280.95(d)—change
‘‘Rural Electrification Administration’’
to ‘‘Rural Utilities Service’’
• Section 280.94(a)(1)—change
‘‘§§ 280.95–280.103’’ to ‘‘§§ 280.95–
280.107’’
• Section 280.95(b)(1)(ii)—change
‘‘165.145’’ to ‘‘§ 265.145’’
• Section 280.95(c)(5)(i)—change
‘‘form’’ to ‘‘from’’
• Section 280.95(d)—change ‘‘[insert:
‘‘suddent accidential releases’’ and/or
‘‘nonsudden accidential releases]’’ to
‘‘[insert: ‘‘sudden accidental releases’’ or
‘‘nonsudden accidental releases’’ or
‘‘accidental releases’’]’’
• Section 280.95(d)—change
‘‘Liabilitly’’ to ‘‘Liability’’ under Letter
From Chief Financial Officer
• Section 280.95(d)—change ‘‘lastest’’
to ‘‘latest’’ under Letter From Chief
Financial Officer, Alternative I, Number
11
• Section 280.95(d)—remove ‘‘$’’
symbol for Number 8 under Alternative
II of the Letter From Chief Financial
Officer
• Section 280.95(d)—add ‘‘$’’ symbol
for Numbers 13 and 14 under
Alternative II of the Letter From Chief
Financial Officer
• Section 280.96(b)—change
‘‘§ 280.110(c)’’ to ‘‘§ 280.114(e)’’
• Section 280.96(c), Guarantee
(Recital 3)—change three ‘‘40 CFR
280.108’’ citations to ‘‘40 CFR
§ 280.112’’
• Section 280.96(c), Guarantee
(Recital 3)—change ‘‘accidential’’ to
‘‘accidental’’
• Section 280.96(d)—change
‘‘280.108’’ to ‘‘§ 280.112’’
• Section 280.97(a)—change
‘‘§ 290.93’’ to ‘‘§ 280.93’’
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• Section 280.98(b)—change
‘‘Resource Conservation and Recovery
Act (RCRA)’’ to Solid Waste Disposal
Act’’
• Section 280.98(b), Performance
Bond, paragraph 4,—change ‘‘[* * *
either ‘‘sudden’’ or ‘‘nonsudden’’ or
‘‘sudden and nonsudden’’] accidental
releases arising from’’ to ‘‘either
‘‘sudden accidental releases’’ or
‘‘nonsudden accidental releases’’ or
‘‘accidental releases’’] arising from
* * *’’
• Section 280.98(b)—change two ‘‘40
CFR 280.108’’ citations to ‘‘40 CFR
280.112’’
• Section 280.98(b)—add end
brackets to ‘‘State of Incorporation’’ and
‘‘Liability Limit’’
• Section 280.98(d)—change ‘‘40 CFR
280.108’’ citation to ‘‘40 CFR 280.112’’
• Section 280.99(b)—change
‘‘Resource Conservation and Recovery
Act of 1976’’ to Solid Waste Disposal
Act’’
• Section 280.99(b)—change
‘‘persuant’’ to ‘‘pursuant’’
• Section 280.99(b)—change ‘‘curent’’
to ‘‘current’’
• Section 280.99(c)—change ‘‘40 CFR
280.108’’ citation to ‘‘40 CFR 280.112’’
• Section 280.101(d)—change
‘‘280.107(b)(5)’’ to ‘‘§ 280.111(b)(8)’’
• Section 280.103(b)(1), Trust
Agreement, paragraph 2—change
‘‘standpoint’’ to ‘‘[insert ‘‘standby’’
where trust agreement is standby trust
agreement]’’
• Section 280.103(b)(1), Trust
Agreement, section 4—add opening
quotation mark for ‘‘Third-Party
Liability Claims’’
• Section 280.103(b)(1), Trust
Agreement, section 4—add opening
quotation mark for ‘‘compensating third
parties for bodily injury and property
damage caused by’’
• Section 280.104(b)—change
‘‘Moody’s rating of Aaa, A, A’’ to
‘‘Moody’s rating of Aaa, Aa, A’’
• Section 280.104(b)—change
‘‘refunded issues and’’ to ‘‘refunded
issues, and’’
• Section 280.104(e), Letter From
Chief Financial Officer—change
‘‘[insert: ‘‘sudden accidental releases’’
and/or ‘‘nonsudden accidental
releases’’]’’ to ‘‘[insert: ‘‘sudden
accidental releases’’ or ‘‘nonsudden
accidental releases’’ or ‘‘accidental
releases’’]’’. Note that this change occurs
in two places in the letter.
• Section 280.104(e), Letter From
Chief Financial Officer, last paragraph—
change ‘‘not backed by third-party credit
enhancement or are insured by a
municipal bond insurance company.’’ to
‘‘not backed by third-party credit
enhancement or insured by a municipal
bond insurance company.’’
• Section 280.105(c)—change
‘‘[insert: ‘‘sudden accidental releases’’
and/or ‘‘nonsudden accidental
releases’’]’’ to ‘‘[insert: ‘‘sudden
accidental releases’’ or ‘‘nonsudden
accidental releases’’ or ‘‘accidental
releases’’]’’
• Section 280.105(c)—change 10(a)
and 11(a) under Worksheet for
Municipal Financial Test, Part II from
‘‘Debt Service (from 4d)’’ to ‘‘Debt
Service (from 4c)’’
• Section 280.106(a)(1)—change
‘‘§ 280.104(c)’’ to ‘‘§ 280.104(d) and
§ 280.104(e)’’
• Section 280.106(b)—change
‘‘§ 280.114(c)’’ to ‘‘§ 280.114(e)’’
• Section 280.106(d), under Local
Government Guarantee With Standby
Trust Made by a State, recital 7d—
change ‘‘loaded’’ to ‘‘loaned’’
• Section 280.106(e), under Local
Government Guarantee Without
Standby Trust Made by a State, recital
7d—change ‘‘loaded’’ to ‘‘loaned’’
• Section 280.106(e), under Local
Government Guarantee Without
Standby Trust Made by a Local
Government, recital 8d—change
‘‘loaded’’ to ‘‘loaned’’
• Section 280.107(d)—change
‘‘[insert: ‘‘sudden accidental releases’’
Minimum
duration of
test
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Nominal tank capacity
550 gallons or less .................................................................
551–1,000 gallons (when tank diameter is 64’’) ....................
551–1,000 gallons (when tank diameter is 48’’) ....................
551–1,000 gallons (also requires periodic tank tightness
testing).
1,001–2,000 gallons (also requires periodic tank tightness
testing).
Æ Section 280.41(a)(2)—modify tank
sizes in text so it is consistent with the
table above. ‘‘Tanks with capacity of 550
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36
44
58
36
hours
hours
hours
hours
Weekly standard (one test)
Monthly standard
(four test
average)
................................
................................
................................
................................
10 gallons ..............................
9 gallons ................................
12 gallons ..............................
13 gallons ..............................
5
4
6
7
36 hours ................................
26 gallons ..............................
13 gallons.
gallons or less and tanks with a capacity
of 551 to 1000 gallons that meet the tank
diameter criteria in § 280.43(b) may use
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and/or ‘‘nonsudden accidental
releases’’]’’ to ‘‘[insert: ‘‘sudden
accidental releases’’ or ‘‘nonsudden
accidental releases’’ or ‘‘accidental
releases’’]’’
• Section 280.107(d), third paragraph
under Letter From Chief Financial
Officer—change ‘‘ten’’ to ‘‘five’’
• Section 280.109(b)(3)—change
‘‘§ 280.107(b)’’ to ‘‘§ 280.111(b)’’
• Section 280.111(b)(9)(ii)—change
‘‘§ 280.107(a)(3)’’ to ‘‘§ 280.107(c)’’
• Section 280.111(b)(9)(iii)—change
‘‘§ 280.107(a)(3)’’ to ‘‘§ 280.107(c)’’
• Section 280.111(b)(9)(iii)—change
‘‘§ 280.107(a)(3)(i)’’ to ‘‘§ 280.107(c)(1)’’
• Section 280.111(b)(9)(iii)—change
‘‘§ 280.107(a)(3)(ii)’’ to ‘‘§ 280.107(c)(2)’’
• Section 280.113—change
‘‘properly’’ to ‘‘permanently’’
EPA is proposing these technical
corrections to the 1988 UST regulation:
• Section 280.12—revise exclusion
(d) of the definition of UST to
incorporate a revision in section 9001 of
the SWDA as shown below
‘‘(d) Pipeline facility (including
gathering lines):
(1) Which is regulated under chapter
601 of Title 49, or
(2) Which is an intrastate pipeline
facility regulated under state laws as
provided in chapter 601 of Title 49,
and which is determined by the
Secretary of Transportation to be
connected to a pipeline or to be
operated or intended to be capable of
operating at pipeline pressure or as an
integral part of a pipeline;’’
• Section 280.43(b)(1)—replace ‘‘a
period of at least 36 hours’’ with ‘‘the
minimum duration of test in the table
below’’; this updates current UST
capacity allowances when using manual
tank gauging as a method of release
detection
Æ Section 280.43(b)(4)—replace
existing table with the one below; this
ensures information in the table is
consistent with the change in
§ 280.43(b)(1)
Frm 00045
Fmt 4701
Sfmt 4702
gallons.
gallons.
gallons.
gallons.
manual tank gauging (conducted in
accordance with § 280.43(b))’’; and
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Æ Section 280.43(b)(5)—modify tank
sizes in text so it is consistent with the
table above. ‘‘Tanks of 550 gallons or
less nominal capacity and tanks with a
nominal capacity of 551 to 1000 gallons
that meet the tank diameter criteria in
the table in (b)(4) may use this as the
sole method of release detection. All
other tanks with a nominal capacity of
551 to 2,000 gallons may use the
method in place of manual inventory
control in § 280.43(a). Tanks of greater
than 2,000 gallons nominal capacity
may not use this method to meet the
requirements of this subpart.’’
• Section 280.43—remove the
requirement for inventory control in the
automatic tank gauging release detection
method
• Section 280.92—change the
definition of accidental release from
‘‘release of petroleum from an
underground storage tank’’ to ‘‘release of
petroleum arising from operating an
underground storage tank’’
• Section 280.104(h)—add this
subsection: ‘‘(h) If the local government
owner or operator fails to obtain
alternate assurance within 150 days of
finding that it no longer meets the
requirements of the bond rating test or
within 30 days of notification by the
Director of the implementing agency
that it no longer meets the requirements
of the bond rating test, the owner or
operator must notify the Director of
such failure within 10 days.’’
• Revise Appendix III to read: ‘‘Note.
A federal law (the Solid Waste Disposal
Act, as amended, requires owners of
certain underground storage tanks to
notify implementing agencies of the
existence of their tanks. Notifications
must be made within 30 days of
bringing the tank into use. Consult
EPA’s regulations at 40 CFR 280.22 to
determine if you are affected by this
law.’’
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Why is EPA proposing this change?
What background information is
available about this change?
EPA is proposing to make editorial
and technical corrections to the 1988
UST regulation. Proposed editorial
corrections include: correcting
misspellings; capitalizing words;
removing unused acronyms; using
conventional number formatting; and
appropriately referring to parts,
subparts, sections, and paragraphs. In
addition, EPA is proposing technical
corrections which include updating the
regulation to incorporate statutory
changes that occurred since the 1988
regulation was promulgated and
clarifying long-standing Agency
policies.
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The editorial change to § 280.10(c)(3)
makes the citation to Nuclear Regulatory
Commission regulation more general, in
the event requirements for emergency
generator UST systems at nuclear power
facilities are moved from Appendix A to
some other part of the Nuclear
Regulatory Commission regulation.
The editorial change to § 280.22(a)
makes the language easier to understand
and consistent with the proposed new
paragraphs of § 280.22(b) and
§ 280.22(h).
The editorial change to
§ 280.20(c)(1)(ii)(C) clarifies that the
transfer operator needs to be alerted.
This change makes the language
consistent with § 280.20(c)(1)(ii)(B). The
editorial change to § 280.22(g) clarifies
the content of and how to use Appendix
III of the 1988 UST regulation to meet
the notification requirement.
The editorial changes to § 280.31 will
eliminate any potential confusion with
the temporary closure requirement and
ensure all metal components comply
with this section. Temporary closure
requires owners and operators operate
and maintain corrosion protection even
when the UST system is emptied. The
operation and maintenance of corrosion
section indicates that releases due to
corrosion must be prevented as long as
the UST system is used to store
regulated substances. While EPA has
interpreted that the UST system is used
to store regulated substances even if it
is empty during temporary closure, this
proposed change will clarify this
position. In addition, UST systems have
metal components, other than steel,
protected from corrosion. Changing the
word steel to metal at the beginning of
this section will make it clear that the
operation and maintenance
requirements for corrosion protection
apply to all metal components.
The editorial change to § 280.33(g)
will clarify when the operating life of an
UST system ends. EPA does not define
an operating life; rather, we describe
permanent closure and change-inservice. With this change, EPA is
proposing the operating life of an UST
system ends when an owner or operator
permanently closes the UST system or
the UST system undergoes a change-inservice from regulated to unregulated.
EPA is proposing a technical
correction to revise the definition of
UST as it relates to pipeline facilities.
This revision directly incorporates a
change made to Section 9001 of the
Solid Waste Disposal Act after the 1988
UST regulation was promulgated.
EPA is proposing a technical
correction to clarify that hazardous
substance USTs must be able to contain
regulated substances released from the
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Frm 00046
Fmt 4701
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UST system until the substances are
detected and removed. Based on the
1988 UST regulation definition of
release, the statement implies that a
regulated substance has reached the
environment. Because a regulated
substance should be contained in the
UST system’s secondary containment,
EPA is proposing to change the term
released to leaked, indicating a leak
occurred from the primary containment
but did not reach the environment.
Therefore, secondary containment
would then contain the leak. The
editorial change to § 280.42(d) removes
confusion about whether piping that is
already double-walled also needs to be
jacketed.
EPA is proposing technical
corrections to § 280.43(d) which will
codify long-standing Agency policies for
using manual tank gauging and
automatic tank gauging. These changes
update UST capacity allowances when
using manual tank gauging and remove
the requirement for USTs using
automatic tank gauging to conduct
additional inventory control. Since 1990
and 1989, EPA allowed these deviations
from the 1988 UST regulation through
policy for manual tank gauging and
automatic tank gauging, respectively.
EPA also stated these allowances in our
publications: Manual Tank Gauging For
Small Underground Storage Tanks;
Musts For USTs: A Summary of Federal
Regulations For Underground Storage
Tank Systems; and Straight Talk On
Tanks: Leak Detection Methods For
Petroleum Underground Storage Tanks
And Piping. With regard to manual tank
gauging, note the expanded coverage of
larger tanks is limited in some respects
by the diameter of the tank as noted in
the revised table.
EPA is proposing to add closure as an
option at § 280.52(a)(1) to provide
owners and operators additional
flexibility when suspected and
confirmed releases occur.
EPA is proposing an editorial
correction of ‘‘leak’’ to ‘‘release’’ in
§ 280.43(b)(4) and § 280.52(a)(1), (2),
and (3) because release is defined as
regulated substance reaching the
environment in the 1988 UST
regulation.
EPA is updating references of ‘‘Rural
Electrification Administration’’ (REA) to
‘‘Rural Utilities Services’’ (RUS). Under
the Federal Crop Insurance Reform and
Department of Agriculture
Reorganization Act of 1994, REA
reorganized to RUS.
EPA is proposing to amend the
definition of ‘‘accidental release’’ under
§ 280.92 so it matches the definition
stated in the original preamble for the
financial responsibility requirements
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(53 FR 43334). EPA intended the
definition in the preamble to be
included in the 1988 UST regulation,
but two important words were
inadvertently omitted. By changing this,
EPA is clarifying that owners and
operators are required to have financial
responsibility for releases arising from
operating USTs (including releases due
to filling USTs and releases occurring at
dispensers).
The editorial change to § 280.103(b)(1)
will correct a typographical error [i.e.,
‘‘standpoint’’] and clarify the trust fund
language.
The editorial change to the last
paragraph of the Letter to the Chief
Financial Officer under § 280.104(e)
clarifies that no credit enhancement of
any type is permitted for revenue bonds,
consistent with the preamble to the
1988 UST regulation (58 FR 9033).
The editorial addition of § 280.104(h)
will make requirements for the local
government bond rating test under
§ 280.104 consistent with requirements
of the financial test under § 280.95(g).
EPA included this requirement for
private owners and operators in the
1988 UST regulation but inadvertently
omitted it for local government owners
and operators.
The editorial change to the third
paragraph of the Letter From Chief
Financial Officer under § 280.107(d)
will make the wording of the letter
consistent with the amount of coverage
required in § 280.107(b).
EPA defines and discusses permanent
closure, not proper closure, in the 1988
UST regulation. This clarified that in
§ 280.113, financial responsibility is
required during temporary closure.
The update to Appendix III removes
old dates and clarifies the language in
the statement for shipping tickets and
invoices.
What issues related to this change does
EPA request comment or additional
data on?
• Are there other editorial corrections
(such as typographical errors or
inaccurate references) EPA should
make?
Please provide reasoning or justification
if you disagree with or propose
something different from EPA’s
proposal.
F. Alternative Options EPA Considered
What options did EPA consider?
In developing today’s proposed
regulatory changes (hereafter the
Preferred Option), EPA considered and
evaluated variations of a subset of the
proposed regulatory requirements using
two alternative options (hereafter
Option 1 and Option 2). The table below
highlights differences between our
Preferred Option and Options 1 and 2.
Some of the proposed regulatory
requirements do not vary across the
options (for example, notification of
ownership changes is required in all
three). As a result, proposed regulatory
changes discussed earlier in the
preamble, but not listed here, mean
those changes are in effect in all three
options. Overall, Options 1 and 2
consist of regulatory changes that are
more and less stringent, respectively,
than proposed changes in the Preferred
Option. After reviewing comments, EPA
may use one or more of these options in
whole or in part to establish the final
UST regulation.
COMPARISON OF PREFERRED OPTION AND OPTIONS 1 AND 2
Options
Proposed requirement
1
Walkthrough inspections ...........................................................
Overfill prevention equipment tests ...........................................
Spill prevention equipment tests ...............................................
Monthly ...................................
3 year ......................................
1 year ......................................
Secondary containment tests ....................................................
Elimination of flow restrictors in vent lines for all new tanks
and when overfill devices are replaced.
Operability tests for release detection methods ........................
Change leak rate probabilities from 95/5 to 99/1 (Pd/Pfa) .......
Eliminate groundwater and vapor monitoring as release detection methods.
Remove deferrals for airport hydrant fuel distribution systems
and UST systems with field-constructed tanks.
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Preferred
3 year ......................................
Required .................................
Monthly ...................................
1 year ......................................
Require replacement every 3
years (no testing).
1 year ......................................
Required .................................
Not required.
No change.
1 year ......................................
Not required ............................
5-year phase-out .....................
1 year ......................................
Required .................................
Immediately .............................
3 year.
Not required.
No change.
Regulate under alternative release detection requirements.
Require them to meet same
release detection requirements as conventional
USTs.
Maintain deferrals.
Below we explain Options 1 and 2, as
well as our rationale for each. (Note that
EPA conducted a regulatory impact
analysis (RIA) for all three options. The
results are discussed in the RIA
document titled Assessment Of The
Potential Costs, Benefits, And Other
Impacts Of The Proposed Revisions To
EPA’s Underground Storage Tank
Regulations which is available in the
docket for this proposed regulation.)
What is EPA’s rationale for Option 1?
In Option 1, EPA considered requiring
annual tests of overfill prevention
equipment and interstitial areas. EPA
assessed the costs of conducting annual
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tests for these components and decided
instead to propose overfill prevention
equipment testing and interstitial
integrity testing every three years. This
will reduce the overall compliance cost
burden on owners and operators
without significantly compromising
benefits of these tests. When compared
to other components such as spill
prevention equipment, both interstitial
areas and overfill prevention equipment
are less likely to fail or be damaged.
Overfill prevention equipment is in the
tank; interstitial areas for tanks and
piping are typically buried several feet
underground. Spill prevention
PO 00000
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2
Quarterly.
3 year.
1 year.
equipment encounters frequent human
and climate interaction, making it prone
to frequent damage and failure.
Secondary containment reduces the
likelihood that a release into the
environment will occur because a leak
is contained if a breach of the inner wall
occurs. As a result, less frequent
periodic tests of overfill prevention
equipment and interstitial areas would
adequately ensure the integrity and
functionality of equipment. In addition,
a three year test requirement for these
two components will match the
inspection cycle, allowing inspectors to
ensure tests are completed. Therefore,
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testing overfill prevention equipment
and interstitial areas every three years is
sufficient.
In Option 1, EPA considered
mandatory replacement of spill
prevention equipment every three years,
regardless of the spill prevention
equipment’s condition. As discussed
earlier in the preamble, various sources
indicated spill prevention equipment is
a major source of confirmed releases
and typically has a short lifespan. After
EPA evaluated the cost of requiring spill
prevention equipment replacement
every three years, we determined the
cost burden of this requirement on
owners and operators would be
significant. While developing today’s
proposal, EPA made a conscious effort
to limit removing or replacing existing
UST system equipment (for example,
eliminating the use of ball floats as a
form of overfill prevention in new tanks
instead of requiring removal in existing
tanks) to minimize impacts on owners
and operators, both in terms of reducing
compliance costs and interrupting daily
operations. As a result, EPA instead is
proposing annual tests of spill
prevention equipment. This balances
the benefits of properly functioning spill
prevention equipment with the
potential costs imposed on owners and
operators.
When considering changes to existing
release detection requirements, EPA
evaluated the possibility of modifying
the leak probability of detection (Pd)
from 95 percent to 99 percent and the
leak probability of false alarm (Pfa) from
5 percent to 1 percent. EPA initially
believed increasing the Pd rate for
release detection equipment
performance would be a relatively low
cost action that would significantly
increase identifying potential releases to
the environment. EPA also believed that
decreasing the Pfa rate would be a
relatively low cost means of reducing
the number of nuisance alarms owners
and operators experience. Because they
would have a higher confidence that
alarms identify real problems, owners
and operators would be more likely to
respond. Even though most equipment
in use today is capable of meeting more
stringent probability rates, almost all
release detection devices would require
some modification to achieve these
results. Even a relatively minor software
upgrade could be a significant cost to
owners and operators. In addition,
release detection vendors would need to
perform significant testing and
verification to determine whether their
equipment would meet the new Pd/Pfa
rates. After considering the potential
cost impacts, other proposed
requirements, such as training owners
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and operators and requiring periodic
walkthrough inspections, are sound
alternatives for environmental
protection. Therefore, EPA instead is
proposing periodic operation and
maintenance for existing release
detection equipment to ensure its
proper operation.
EPA is proposing to eliminate
groundwater and vapor monitoring as
permissible methods of release
detection. In Option 1, EPA considered
an immediate ban of these two options
as release detection methods because
inspectors told us these methods are
unsuitable and should be removed as
soon as possible. Approximately 5
percent of UST systems use
groundwater or vapor monitoring for
release detection, which means the
affected population of users is relatively
small. Yet EPA recognizes this would
require retrofitting or replacing existing
equipment. To accommodate owners
and operators and provide them with
sufficient lead time to meet this
requirement, EPA today is proposing a
five year phase out for owners and
operators to select, install, and begin
using another method of release
detection.
In evaluating release detection
methods suitable for UST systems with
field-constructed tanks and airport
hydrant fuel distribution systems, EPA
considered requiring these tanks and
systems comply with the same release
detection requirements conventional
UST systems meet under 40 CFR part
280, subpart D. After assessing costs,
technical feasibility, and potential
impacts to facility operations, EPA
decided to propose a release detection
regulatory structure specific to fieldconstructed tanks and airport hydrant
fuel distribution piping, per § 280.46
and § 280.47, respectively. It is
sometimes impossible for very large
tanks and piping volumes to achieve
thresholds for current release detection
methods. When a threshold is
achievable, the time needed to reach it
is often very long and impractical. The
RIA indicates the total annual costs to
meet conventional release detection
requirements are $153 million, while
total annual costs under the proposed
alternative release detection
requirements are $23 million. As a
result, it is appropriate to propose
release detection methods specific to
these systems. This will effectively
protect the environment by quickly
detecting releases from these tanks and
piping.
What is EPA’s rationale for Option 2?
In comparing costs with benefits of
potential proposed changes, EPA
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weighed different frequencies for
walkthrough inspections and periodic
equipment testing. In Option 2, EPA
assessed quarterly walkthrough
inspections and not requiring interstitial
integrity testing as ways to reduce
potential cost impacts on owners and
operators. While quarterly walkthrough
inspections would reduce costs to
owners and operators, EPA is taking the
position that a period less frequent than
monthly walkthrough inspections
would considerably reduce benefits.
High operator turnover, frequency of
small leaks at dispensers and
submersible turbine sumps, and
frequency of deliveries all contribute to
the need for monthly walkthrough
inspections. With that in mind, EPA
today is proposing monthly
walkthrough inspections so owners and
operators can consistently and routinely
verify proper UST system component
performance. This will ensure problems
are detected before a release occurs or
contaminates the environment.
The 1988 UST regulation does not
require owners and operators to ensure
the integrity of secondarily contained
areas, and EPA considered not requiring
periodic interstitial integrity testing.
Because of the Energy Policy Act
secondary containment requirement for
nearly all new and replaced tanks and
piping, all UST systems will eventually
be secondarily contained (including
interstitial monitoring for release
detection) and we should require
periodic interstitial integrity testing to
ensure leaks into secondary
containment areas will be properly
detected and contained. As described in
Option 1, EPA considered annual
interstitial integrity testing, but decided
to propose a three year testing
requirement, which will lower cost
impacts of this requirement on owners
and operators while retaining the
environmental benefit of testing.
To reduce total compliance costs of
today’s proposal for owners and
operators, EPA considered allowing
continued use of flow restrictors in vent
lines (that is, ball float valves) as an
acceptable form of overfill prevention
equipment. After considering
stakeholders’ concerns, EPA is taking
the position that vent line flow
restrictors present problems for
operability and safety reasons. As
described previously, EPA is proposing
to eliminate ball float valves as overfill
prevention for all new tanks and when
overfill prevention is replaced in
existing tanks.
EPA considered maintaining
groundwater and vapor monitoring as
acceptable forms of release detection in
Option 2. All tanks and piping will
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eventually use secondary containment
with interstitial monitoring as their
release detection method, and as a
result, groundwater and vapor
monitoring will eventually not be used.
Stakeholders raised concerns about
these two release detection methods,
more than other methods. For both
groundwater and vapor monitoring,
releases travel through the environment
to sampling points before releases are
discovered. Other release detection
methods provide more immediate
detection of releases. In addition,
numerous concerns were raised about
frequent misapplications and improper
designs of monitoring wells for these
two methods. Consequently, EPA today
is proposing to phase out groundwater
and vapor monitoring as release
detection methods. This will address
stakeholders’ concerns that UST
systems using these two methods
represent an unacceptable risk to the
environment.
V. Updates to State Program Approval
Requirements
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What is EPA proposing?
EPA is proposing these substantive
changes to the 1988 state program
approval (SPA) regulation (40 CFR part
281) to make it consistent with certain
Energy Policy Act requirements and
certain proposed changes to the 1988
UST technical regulation (40 CFR part
280).
• Section 281.30(a), § 281.33(c)(2),
and § 281.33(d)(3)—require secondary
containment for new or replaced tanks
and piping and under-dispenser
containment for new motor fuel
dispenser systems for UST systems
located within 1,000 feet of a potable
drinking water well or community water
system, unless a state requires
manufacturer and installer financial
responsibility according to § 9003(i)(2)
of the Solid Waste Disposal Act.
• Section 281.30(b)—eliminate flow
restrictors for new or replaced overfill
prevention.
• Section 281.30(c)—add notification
for ownership changes.
• Section 281.31 and § 281.33(b) and
(c)—delete upgrading requirements and
eliminate phase-in schedule; add phasein schedule for previously deferred UST
systems.
• Section 281.32(e) and (f) and
§ 281.33(a)(3)—add periodic testing of
spill and overfill prevention equipment,
secondary containment areas, and
mechanical and electronic components;
and operation and maintenance
walkthrough inspections, as well as
maintaining associated records.
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• Section 281.33(c)—limit use of
monthly inventory control in
combination with tank tightness testing
conducted every five years for the first
10 years after the tank is installed or
upgraded, if the tank was installed prior
to a state receiving SPA.
• Section 281.33(e)—require
hazardous substance USTs to only use
secondary containment with interstitial
monitoring.
• Section 281.34(a)(1)—add
‘‘interstitial space may have been
compromised’’ to suspected releases.
• Section 281.37—eliminate phase-in
requirement for financial responsibility.
• Section 281.39—require operator
training according to § 9010 of the Solid
Waste Disposal Act.
• Section 281.41(a)—require states to
have delivery prohibition in accordance
with § 9012 of the SWDA.
• Section 281.60—add requirement
for the Administrator to initiate
proceedings to withdraw program
approval when an approved program
fails to submit a revised application
within three years of 40 CFR part 281
changes that require a program revision,
which will follow the proceedings
procedures from the 1988 SPA
regulation.
EPA is not proposing to add the
proposed compatibility requirement
changes (see § 280.32) to 40 CFR part
281.
EPA is also proposing these technical
changes to the SPA regulation.
• Section 281.10—change ‘‘subpart’’
to ‘‘part’’.
• Section 281.11(c), § 281.12(b)(2),
§ 281.20(d), § 281.21(a)(2), § 281.23,
§ 281.50(a), and formerly § 281.51—
eliminate interim approval.
• Section 281.12(a)(2)—change
‘‘Indian lands’’ to ‘‘Indian country’’.
• Formerly § 281.32(e)—eliminate
requirement to maintain upgrade
records.
• Formerly § 281.38—eliminate
reserved section for financial
responsibility for USTs containing
hazardous substances.
• Move § 281.39 to § 281.38—Lender
Liability.
• Section 281.51, formerly § 281.52—
add requirement for approved states to
submit a revised application within
three years of 40 CFR part 281 changes
that require a program revision.
• Section 281.61—move § 281.60(b)
to § 281.61(b)(2).
Why is EPA proposing this change?
What background information is
available about this change?
The 1988 SPA regulation in 40 CFR
part 281 sets criteria state UST programs
must meet to receive EPA’s approval to
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operate in lieu of the federal UST
program. The 1988 SPA regulation sets
performance criteria states must meet to
be considered no less stringent than the
1988 UST regulation (hereafter 40 CFR
part 280) and provides requirements for
states to have adequate enforcement. It
also details the components of a SPA
application.
EPA is proposing certain changes to
the 1988 SPA regulation to make it
consistent with today’s proposed
changes to the 1988 UST technical
regulation. By doing so, EPA will
require states to adopt UST technical
regulation changes when final, in order
to obtain or retain SPA. EPA is
proposing to keep the general format of
the 1988 SPA regulation. We are not
proposing to make the SPA regulation as
explicit or prescriptive as the UST
technical regulation. Finally, EPA is
proposing technical corrections and
adding a deadline for state program
revisions whenever EPA makes
substantive changes to the SPA
regulation.
Addressing Energy Policy Act
Requirements and Proposed 40 CFR Part
280 Changes
How SPA Works
EPA’s proposed UST technical
regulation changes and Energy Policy
Act requirements primarily impact the
1988 SPA regulation in 40 CFR part 281,
Subpart C—Criteria for No Less
Stringent. Thirty-six states, plus the
District of Columbia and Puerto Rico,
have state program approval and run
their own underground storage tank
programs in lieu of the federal program.
To ensure these jurisdictions, and any
other states or territories obtaining SPA,
adopt the 40 CFR part 280 changes
when final, EPA must update Subpart C.
To continue providing states with
flexibility and not disrupt current state
programs, EPA is proposing to revise the
SPA regulation to make it consistent
with, but not identical to, the 40 CFR
part 280 changes. Instead, EPA is
proposing changes to the SPA regulation
in a less prescriptive manner than in the
changes in 40 CFR part 280. EPA
decided to continue this successful
approach to implement the UST SPA
program.
The 1988 SPA regulation developed
no less stringent criteria in the form of
objectives.73 EPA is continuing this
format so that, taken as a whole, state
programs will be no less stringent than
the federal requirements, even though
they may deviate slightly from what is
explicitly required in 40 CFR part 280.
73 Federal Register, Vol. 53, No. 185, September
23, 1988, page 37216.
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For example, § 281.30 covers the no less
stringent requirement for new UST
system design, construction, and
installation; it corresponds to § 280.20
of the UST technical regulation, but is
much less explicit about requirements.
According to § 281.30 and to receive
SPA, a state must require all new UST
systems ‘‘* * * [b]e designed,
constructed, and installed in a manner
that will prevent releases for their
operating life due to manufacturing
defects, structural failure, or corrosion
* * *’’. In contrast, § 280.20 is much
more explicit about how tank owners
and operators ensure their tanks and
piping prevent releases. It states what is
required to prevent releases and
provides codes of practice to comply.
Although § 281.30 is less explicit, it
nonetheless ensures owners and
operators in approved states install UST
systems that prevent releases and
provides states flexibility in achieving
that goal.
Proposed Goal Oriented Changes
EPA is proposing these goal oriented
changes to Subpart C—Criteria for No
Less Stringent. By the term ‘‘goal
oriented changes,’’ EPA means changes
in which states have some flexibility as
to how they will meet the goals of the
particular SPA regulation section. They
reflect certain 40 CFR part 280 proposed
changes.
• § 281.30(c)—add notification for
ownership changes.
• § 281.31 and § 281.33(b)—add a
phase-in schedule for upgrading
previously deferred UST systems.
• § 281.32(e) and (f) and
§ 281.33(a)(3)—add periodic testing of
spill and overfill prevention equipment,
secondary containment areas, and
mechanical and electronic components;
and operation and maintenance
walkthrough inspections, as well as
maintaining associated records.
EPA’s proposed ownership change
notification requires anyone who
assumes ownership of an UST system to
notify the implementing agency within
30 days of assuming ownership and
specifies what notification must
include. Our proposed SPA regulation
change in § 281.30(c) is much less
prescriptive and indicates states require
owners and operators to ‘‘* * *
adequately notify the implementing
state agency within a reasonable
timeframe when assuming ownership of
an UST system using a form designated
by the state agency.’’ This provides
states some flexibility in complying,
including allowing them to continue
relying on an annual tank registration
program to meet this requirement. This
is a reasonable way to ensure states
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know who owns USTs in their
jurisdiction. EPA does not have an
annual registration program, so we
specify a timeframe in § 280.22 because
we want to know who owns tanks in
jurisdictions where we are the
implementing agency.
In § 280.21, EPA is proposing that
previously deferred wastewater
treatment tank systems, airport hydrant
fuel distribution systems, and UST
systems with field-constructed tanks
meet specific upgrade requirements.
This is one way of achieving the goal
states need to meet in § 281.31. In
§ 281.31, states will be required to
ensure tanks are upgraded to prevent
releases due to corrosion, spills, and
overfills or be permanently closed.
These more general requirements are
sufficient for a state program to protect
human health and the environment
because they require UST systems to
‘‘* * * prevent releases for their
operating life * * *’’. EPA finds it is
also adequate to upgrade previously
deferred systems to this standard.
Additionally, EPA is proposing
previously deferred UST systems be
upgraded within three years of a state
submitting its SPA application for
approval or revision. In the past, EPA
experienced problems with requiring
states to have a particular requirement
by a certain date in order to receive
SPA. States applying for SPA after a
deadline passed often have difficulty
implementing or obtaining a retroactive
requirement. A retroactive or deadline
leads to complications with little added
benefit.
In today’s proposal, EPA is adding
various operation and maintenance
requirements. In 40 CFR part 280, EPA
is proposing specific frequencies and
procedures for testing spill and overfill
prevention equipment, secondary
containment integrity testing, release
detection equipment testing, and
operation and maintenance walkthrough
inspections. In § 281.32, EPA is
proposing states require these tests in a
manner and frequency that ensures
proper functionality of equipment,
includes proper operation and
maintenance of the UST system, and
prevents releases for the life of the
equipment and UST system. This
approach allows states who have these
requirements, despite different
frequencies or manners, to receive SPA,
as long as their requirements
sufficiently ensure properly functioning
non-releasing UST systems. EPA is also
proposing to update § 281.32(g) by
adding these tests to the recordkeeping
requirements of SPA.
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Proposed Energy Policy Act Changes
In today’s SPA regulation proposal,
EPA is addressing Energy Policy Act
requirements more generally than in
today’s UST technical regulation
proposal, yet they are slightly different
than the goal oriented approach above.
The Energy Policy Act amends the Solid
Waste Disposal Act and requires states
that receive federal Subtitle I money to
adopt operator training requirements,
delivery prohibition, and additional
measures to protect groundwater from
contamination. In the additional
measures to protect groundwater
provision, states must meet either
secondary containment and interstitial
monitoring for new or replaced tanks
and piping within 1,000 feet of a potable
drinking water well or community water
system, or manufacturer and installer
financial responsibility and installer
certification. The secondary
containment requirement includes
under-dispenser containment on any
new motor fuel dispenser system within
1,000 feet of a potable drinking water
well or community water system.
EPA developed guidelines for states to
implement Energy Policy Act
requirements; many states and
territories implemented the Energy
Policy Act requirements according to
these guidelines. In order to establish
similar requirements in Indian country
and in states and territories that do not
adopt Energy Policy Act requirements,
EPA is adding secondary containment
and operator training to today’s 40 CFR
part 280 proposal. In proposing those
requirements, EPA does not want to
supersede programs states developed to
meet Energy Policy Act requirements.
Requiring states to alter newly
implemented provisions would be a
disservice to them, as well as UST
owners and operators. Therefore, EPA is
proposing to address in today’s SPA
regulation proposal the secondary
containment, manufacturer and installer
financial responsibility and installer
certification, delivery prohibition, and
operator training requirements that
appear in the Energy Policy Act. So,
states already meeting these Energy
Policy Act requirements need not
change their programs to receive SPA.
EPA is proposing additional measures
to protect groundwater and operator
training requirements in Subpart C
(§ 281.22(d)(3), § 281.30(a),
§ 281.33(c)(2), and § 281.39). Delivery
prohibition is in Subpart D—Adequate
Enforcement of Compliance
(§ 281.41(a)). Because delivery
prohibition is an enforcement tool, EPA
is proposing to require states have
authority to prohibit deliveries
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according to Energy Policy Act, rather
than make this a no less stringent
requirement.
EPA is not proposing to add delivery
prohibition to 40 CFR part 280 because
delivery prohibition is primarily an
enforcement tool for implementing
agencies; it is not a requirement for
owners and operators. Because the
Energy Policy Act gives EPA clear
delivery prohibition enforcement
authority, we do not need to add
delivery prohibition to the UST
technical regulation. However, the only
way to ensure states have that same
authority is to require states to have
authority to implement delivery
prohibition as a prerequisite for SPA, as
proposed in § 281.41(a).
Proposed Specific Changes
EPA is proposing specific changes
below to Subpart C—Criteria for No Less
Stringent. They reflect proposed 40 CFR
part 280 changes. This specific
approach is the only way for states to
adopt this group of proposed changes.
The goal of these proposed sections
remains intact, yet the specific changes
ensure states adopt the 40 CFR part 280
changes when final, and are able to
receive SPA.
• § 281.30(b)—eliminate flow
restrictors for new or replaced overfill
prevention
• § 281.31—delete upgrading
requirements
• § 281.33(c)—limit use of monthly
inventory control in combination with
tank tightness testing conducted every
five years for the first 10 years after the
tank is installed or upgraded, if the tank
was installed prior to a state receiving
SPA
• § 281.33(e)—require hazardous
substance USTs to only use secondary
containment with interstitial monitoring
• § 281.34(a)(1)—add ‘‘* * *
interstitial space may have been
compromised * * *’’ to suspected
releases
• § 281.37—eliminate phase-in
requirement for financial responsibility
EPA is proposing in § 281.30(b) states
wishing to receive SPA not allow
installation of flow restrictors
(commonly referred to as ball floats) in
vent lines for overfill protection. The
existing goal of § 281.30(b) is for states
to require that UST systems have spill
and overfill prevention equipment. In
the proposed language, EPA maintains
the overall goal to prevent spills and
overfills; however, owners and
operators can no longer install ball
floats to achieve that goal.
The deadlines for upgrades and for
owners and operators to obtain financial
responsibility have passed. As a result,
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EPA is proposing to eliminate these
UST technical regulation deadlines in
the SPA regulation. In § 281.31 and
§ 281.33(b), EPA is removing UST
upgrades, except for previously deferred
USTs. In § 281.37, we are eliminating
the financial responsibility phase-in
schedule. Please note EPA is proposing
states allow upgrades prior to
submitting their approval or revision
applications for SPA, rather than only
until December 22, 1998. EPA is taking
this action due to states’ previous
problems with implementing a
retroactive requirement when applying
for SPA after the upgrade deadline.
In § 281.33(c), EPA is proposing
monthly inventory control in
combination with tank tightness testing
conducted every five years for the first
10 years after a tank is installed or
upgraded, only if a tank was installed
prior to a state receiving SPA. This
reflects a proposed change in 40 CFR
part 280 and avoids another problem in
the 1988 SPA regulation. First, EPA is
proposing to eliminate this method.
Second, EPA is proposing to tie the date
for eliminating this method to a state’s
submission of its SPA application for
approval or revision. As discussed
earlier, EPA is taking the position that
it is better to tie deadlines in the SPA
regulation to states’ submission of SPA
applications, rather than specific dates.
In today’s notice, EPA is proposing
states wishing to receive SPA will no
longer be able to allow installation of
non-secondarily contained hazardous
substance UST systems. This is
consistent with EPA’s proposed change
in § 280.42(e); an equivalent and
specific proposed change to the SPA
regulation is the only way to ensure
states adopt it. For consistency with
proposed changes in the UST technical
regulation and to ensure states wishing
to receive SPA adopt this change, in
§ 281.34(a)(1), EPA is proposing to add
‘‘* * * interstitial space may have been
compromised * * *’’ to suspected
releases conditions.
Proposed UST Technical Regulation
Changes Not Addressed in Proposed
SPA Regulation
EPA is not proposing to address in the
proposed SPA regulation (§ 281.32) the
methods for determining compatibility.
Today’s proposed compatibility
proposal in § 281.32 allows owners and
operators to use any method for
determining compatibility approved by
an implementing agency, as long as the
method is no less protective of human
health and the environment. It is
unnecessary to change the SPA
regulation because the proposed UST
technical regulation in § 281.32 will
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provide states with discretion to ensure
compatibility. Also, the proposed UST
technical regulation change delineates
how owners and operators can
demonstrate they are storing substances
in UST systems made of or lined with
materials that are compatible with the
substances stored. This is more
prescriptive than the general format of
the SPA regulation, and thus is not
appropriate for the SPA regulation.
Addressing SPA Revision Process
EPA is proposing to add a
requirement for approved states to
submit a revised application within
three years of SPA regulation changes
that require a program revision under
§ 281.51. Approved states are required
to revise their programs and submit
revised applications whenever the
federal program changes or EPA’s
Administrator requests a revised
application based on changes to a state’s
program. Given today’s proposed
significant changes, it is necessary to
develop a timeframe which will ensure
approved states meet SPA regulation
changes in a reasonable time.
After discussions with states and
reviews of other EPA programs, EPA is
taking the position that three years is a
reasonable time for approved states to
submit revised applications resulting
from SPA regulation changes. Also, EPA
will work with states to ensure they
meet this three-year deadline. EPA’s
proposed language in § 281.51 is
intended only to require a state program
revision within three years if EPA
makes changes that necessitate state
program changes. For instance, EPA
changes to Subpart C—Criteria for No
Less Stringent would likely require a
state program revision, unless EPA is
only making minor editorial changes.
While most states will be able to meet
the three-year deadline for program
revision, EPA is aware that some states
may need additional time. EPA will
notify states that have not revised their
program within three years. EPA will
ask those states to demonstrate their
level of effort, show progress to date,
and provide dates when they will
achieve major milestones for revising
their programs and submitting a revised
application. EPA will consider these
factors before initiating program
approval withdrawal.
Additional Proposed Changes to SPA
Regulation
EPA is proposing these additional
SPA regulation changes; they are not a
direct result of proposed 40 CFR part
280 changes. Rather, the majority are
corrections to the 1988 SPA regulation.
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• § 281.10—change ‘‘subpart’’ to
‘‘part’’
• § 281.11(c), § 281.12(b)(2), § 281.23,
and formerly § 281.51—eliminate
interim approval
• § 281.12(a)(2)—change ‘‘Indian
lands’’ to ‘‘Indian country’’
• § 281.32(e)—eliminate requirement
to maintain upgrade records
• Formerly § 281.38—eliminate
reserved section for financial
responsibility for USTs containing
hazardous substances
• Move § 281.39 to § 281.38—Lender
Liability
• § 281.61—move § 281.60(b) to
§ 281.61(b)(2)
The SPA regulation incorrectly uses
the term subpart in § 281.10, and
therefore EPA is proposing to correctly
change this to part. EPA has been using
the term Indian country instead of
Indian lands for years. We are proposing
to incorporate this term, which does not
alter the meaning, in the SPA
regulation. EPA is proposing to remove
the reserved financial responsibility for
USTs containing hazardous substances
section (formerly § 281.38); move the
lender liability section from § 281.39 to
§ 281.38; and include the new operator
training section in § 281.39. Because
operator training needs to be in subpart
C, which has no remaining section
numbers, this eliminates the need to
renumber subpart D. Also, the reserved
financial responsibility for hazardous
substances section is unnecessary since
there is no corresponding requirement
in 40 CFR part 280.
EPA is proposing to delete the interim
SPA approval language (in § 281.11(c)
and § 281.51). In more than 20 years of
the UST program, no state has sought
interim approval; it is more beneficial to
receive full approval all at once, rather
than in steps. Also, because 36 states
plus the District of Columbia and Puerto
Rico have SPA, interim SPA approval is
unnecessary at this time.
EPA is proposing to eliminate the
requirement to maintain upgrade
records for the operational life of an
UST facility. This requirement in
§ 281.32(e) of the 1988 SPA regulation
does not exist in 40 CFR part 280. In
addition, EPA is proposing to no longer
allow upgrades.
EPA is also proposing to move
§ 281.60(b) to § 281.61(b). This
paragraph explains the procedure EPA
will follow to withdraw approval. This
paragraph is better suited for § 281.61,
which explains the procedures for
withdrawing approval, as opposed to
§ 281.60, which explains the criteria for
withdrawal.
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What issues related to this change does
EPA request comment or additional
data on?
EPA requests comments on:
• Is three years an appropriate
timeframe for requiring a SPA state to
submit a revised application? Please
provide justification.
• Should EPA address the proposed
procedures for determining
compatibility of § 280.32 into the SPA
regulation?
Please provide reasoning or justification
if you disagree with or propose
something different from EPA’s
proposal.
VI. Overview of Estimated Costs and
Benefits
EPA prepared an analysis of the
potential incremental costs and benefits
associated with this action. This
analysis is contained in the regulatory
impact analysis (RIA) document titled
Assessment of the Potential Costs,
Benefits, and Other Impacts of the
Proposed Revisions to EPA’s
Underground Storage Tank Regulations,
which is available in the docket for this
proposal. RIA estimated regulatory
implementation and compliance costs,
and benefits for three regulatory options
as described above in section V,
subsection F. On an annualized basis,
the estimated regulatory compliance
costs for the three options in today’s
proposed action are $210 million
(Preferred Option), $520 million (Option
1), and $130 million (Option 2).
Separately, this analysis assessed the
potential benefits of the proposed
regulation. As discussed in the RIA, a
substantial portion of the beneficial
impacts associated with the proposed
regulation are avoided cleanup costs as
a result of preventing releases and
reducing the severity of releases.
Today’s action is expected to have
annual cost savings related to avoided
costs of $300–$740 million per year
under the Preferred Option, $310–$770
million per year under Option 1, and
$110–$590 million per year under
Option 2.
We recognize that the estimated
number of avoided releases and releases
reduced in severity is based on expert
judgment. Moreover, the cost savings
estimates reflect cost data from only a
small number of state programs (e.g.,
such as New Hampshire). We solicit
public input on the accuracy of the
expected reduction in releases due to
the proposed requirements provided by
the experts, as well as remediation cost
data for releases of different sizes and
types. Please provide relevant data and
studies on this topic. EPA solicits
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comment on the methodology and
results from the RIA, as well as any data
that the public feels would be useful in
a revised analysis including specifically
cost estimates for remediation and
EPA’s methods for estimating prevented
releases under the proposed rule.
VII. Statutory and Executive Orders
A. Executive Order 12866: Regulatory
Planning and Review and Executive
Order 13563: Improving Regulation and
Regulatory 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
EO 13563 (76 FR 3821, January 21,
2011) and any changes made in
response to OMB recommendations
have been documented in the docket for
this action.
B. Paperwork Reduction Act
The information collection
requirements in this proposed rule have
been submitted for approval to the
Office of Management and Budget
(OMB) under the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. The
Information Collection Request (ICR)
document prepared by EPA has been
assigned EPA ICR number 1360.11.
Today’s proposed regulation contains
mandatory information collection
requirements. The labor burden and
associated costs for these requirements
are estimated in the ICR supporting
statement for today’s proposed action.
The supporting statement identifies and
estimates the burden for each of the
changes to the regulations that include
recordkeeping or reporting
requirements. Proposed changes
include: Adding secondary containment
requirements for new and replaced
tanks and piping; adding operator
training requirements; adding periodic
operation and maintenance
requirements for UST systems;
removing certain deferrals; adding new
release prevention and detection
technologies; and updating state
program approval requirements to
incorporate these new changes.
Based on the same data and cost
calculations applied in the Regulatory
Impact Assessment (RIA) for today’s
action, but using the burden estimations
for ICRs, the ICR supporting statement
estimates an average annual labor hour
burden of 2.3 million hours and $135
million for the proposed regulation. One
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time capital and hourly costs are
included in these estimates based on a
three year annualization period. Burden
is defined at 5 CFR 1320.3(b). The total
universe of respondents for this ICR is
comprised of 223,558 facilities and 56
states and territories.
An agency may not conduct or
sponsor, and a person is not required to
respond to, a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR Part 9.
To comment on the Agency’s need for
this information, the accuracy of the
provided burden estimates, and any
suggested methods for minimizing
respondent burden, EPA has established
a public docket for this rule, which
includes this ICR, under Docket ID
number EPA–HQ–UST–2011–0301.
Submit any comments related to the ICR
to EPA and OMB. See ADDRESSES
section at the beginning of this notice
for where to submit comments to EPA.
Send comments to OMB at the Office of
Information and Regulatory Affairs,
Office of Management and Budget, 725
17th Street NW., Washington, DC 20503,
Attention: Desk Office for EPA. Since
OMB is required to make a decision
concerning the ICR between 30 and 60
days after November 18, 2011, a
comment to OMB is best assured of
having its full effect if OMB receives it
by December 19, 2011. The final rule
will respond to any OMB or public
comments on the information collection
requirements contained in this proposal.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA)
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For purposes of assessing the impacts
of today’s rule on small entities, a small
entity is defined as: (1) A small business
as defined by the Small Business
Administration’s (SBA) regulations at 13
CFR 121.201; (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population of less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise which is independently
owned and operated and is not
dominant in its field.
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After considering the economic
impacts of today’s proposed regulation
on small entities, EPA certifies that this
action will not have a significant
economic impact on a substantial
number of small entities. The small
entities directly regulated by this
proposed rule are small businesses and
small governmental jurisdictions. We
have determined that at most 1 percent
of potentially affected small firms in the
retail motor fuel sector (NAICS 447) will
experience an impact over 1 percent of
revenues but less than 3 percent of
revenues. No small firms have impacts
above 3 percent of revenues. In
addition, we estimate that no small
governmental jurisdictions would be
impacted at 1 percent or 3 percent of
revenues. This certification is based on
the small entities analysis contained in
the RIA for today’s proposal.
Although this proposed regulation
will not have a significant economic
impact on a substantial number of small
entities, EPA nonetheless tried to reduce
the impact of this regulation on the
regulated community in general, which
is primarily comprised of small
businesses. EPA conducted extensive
outreach in order to determine which
changes to make to the 1988 regulations.
EPA worked with representatives of
owners and operators and reached out
specifically to small businesses. In
addition, EPA considered the impacts of
each potential regulatory change and
worked to limit changes that required
retrofits, since changes requiring
retrofits would place a high financial
burden on small businesses. Finally,
EPA maintained numerous options for
compliance in order to provide small
entities with as much flexibility as
possible.
We continue to be interested in the
potential impacts of the proposed rule
on small entities and welcome
comments on issues related to such
impacts.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), 2 U.S.C.
1531–1538, requires Federal agencies,
unless otherwise prohibited by law, to
assess the effects of their regulatory
actions on State, local, and tribal
governments and the private sector.
This rule contains a Federal mandate
that may result in expenditures of $100
million or more for the private sector in
any one year. Accordingly, EPA
prepared under section 202 of the
UMRA a written statement (an appendix
to the RIA), which is summarized
below.
As estimated in the RIA, on an
annualized basis, the total estimated
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regulatory compliance costs for the
three options in today’s proposed action
are $210 million (Preferred Option),
$520 million (Option 1), and $130
million (Option 2). Of this amount,
annualized costs to state/local
governments total $9 million under the
Preferred Option, $19 million under
Option 1, and $6 million under Option
2. These costs consist of estimated
regulatory compliance costs for state/
local governments that currently own or
operate UST systems and annualized
costs of $120,000 for states to
implement the proposed rule. EPA
estimates total annualized costs to
owners and operators of tribally owned
UST systems are $0.7 million under the
Preferred Option. The estimated
annualized cost to the private sector
range is approximately $180 million
under the Preferred Option, $350
million under Option 1, and $120
million under Option 2. While the
proposed regulation may result in
expenditures of $100 million or more
for the private sector, thereby triggering
section 202 of the UMRA, this rule is
not subject to the requirements of
section 204 of UMRA because EPA does
not believe state, local, and tribal
governments will incur aggregate costs
of over $100 million per year.
Consistent with section 205, EPA
identified and considered a reasonable
number of regulatory alternatives.
Today’s proposed regulation identifies a
number of regulatory options, and the
RIA estimates the annual cost across the
three considered options may range
between $130 million and $520 million.
Section 205 of the UMRA requires
federal agencies to select the least costly
or most cost-effective regulatory
alternative unless the Agency publishes
with the final rule an explanation of
why such alternative was not adopted.
As discussed earlier in the preamble, as
part of EPA’s deliberative process for
today’s proposed rule, EPA considered
and evaluated variations of a subset of
the proposed requirements using two
alternative options (Options 1 and 2).
The preferred option provides the
greatest difference between beneficial
impact and costs of any of the options.
The requirements proposed under the
Preferred Option provide for greater
protection of human health and the
environment and better addresses
stakeholder concerns, compared to the
lower cost and proposed requirements
of Option 2.
This rule is not subject to the
requirements of section 203 of UMRA
because it contains no regulatory
requirements that might significantly or
uniquely affect small governments.
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E. Executive Order 13132: Federalism
This action does not have federalism
implications. It will not have substantial
direct effects on the States, on the
relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in EO
13132. Under the proposed rule, total
costs to all affected states and local
governments (including direct
compliance costs, notification costs, and
state program costs) are approximately
$9 million. This is not considered to be
a substantial compliance cost under
federalism requirements. Thus, EO
13132 does not apply to this action.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and State and local governments, EPA
specifically solicits comment on this
proposed action from State and local
officials.
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F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Subject to the Executive Order 13175
(65 FR 67249, November 9, 2000) EPA
may not issue a regulation that has tribal
implications, that imposes substantial
direct compliance costs, and that is not
required by statute, unless the Federal
government provides the funds
necessary to pay the direct compliance
costs incurred by tribal governments, or
EPA consults with tribal officials early
in the process of developing the
proposed regulation and develops a
tribal summary impact statement.
EPA concluded that this action will
have tribal implications to the extent
that tribally-owned entities with UST
systems on Indian country would be
affected. However, it will neither
impose substantial direct compliance
costs on tribal governments, nor
preempt tribal law. Total annualized
costs for tribally-owned UST systems in
Indian country are estimated to be $0.7
million.
EPA consulted with tribal officials
early in the process of developing this
proposed regulation to welcome
meaningful and timely input into its
development. EPA began its
consultation with Tribes on possible
changes to the UST regulation shortly
after the passage of the Energy Policy
Act of 2005. The Energy Policy Act
directed EPA to coordinate with Tribes
to develop and implement an UST
program strategy in Indian country to
supplement the program’s existing
approach. EPA and Tribes worked
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collaboratively to develop a tribal
strategy.
There are certain key provisions of the
Energy Policy Act that apply to states
receiving federal Subtitle I money, but
do not apply in Indian country.
Nonetheless, EPA’s goal is to establish
in Indian country similar federal
requirements to these Energy Policy Act
provisions as an important step in
achieving more consistent program
results in release prevention. Both EPA
and Tribes recognize the importance of
having policies that can help ensure
parity in program implementation
between states and in Indian country.
In addition to our early consultation
with Tribes, EPA also reached out again
to Tribes as we started the official
rulemaking process and throughout the
development of this proposed
regulation. EPA sent letters to leaders of
over 500 Tribes as well as to Tribal
regulatory staff to invite their
participation in the development of the
regulation. EPA heard from both Tribal
officials who work as regulators as well
as representatives of owners and
operators of UST systems in Indian
country. The Tribal regulators raised
concerns about ensuring parity of
environmental protection between states
and Indian country.
EPA finds that today’s proposed
changes to the UST regulation are
needed to ensure parity between UST
systems in states and in Indian country.
This regulation is also needed to ensure
equipment is not just installed but is
working properly to protect the
environment from potential releases.
EPA specifically solicits additional
comment on this proposed action from
Tribal officials.
G. Executive Order 13045: Protection of
Children From Environmental Health
And Safety Risks
This action is not subject to EO 13045
(62 FR 19885, April 23, 1997) because
the Agency does not believe the
environmental health risks or safety
risks addressed by this action present a
disproportionate risk to children. EPA’s
risk assessment for this proposed
rulemaking examines potential impacts
to groundwater and subsequent
chemical transport, exposure and risk.
While the risk assessment did not
specifically measure exposure to
children, the general exposure scenarios
reflect four exposure pathways that have
the most significant potential for human
health impacts. These are: (1) Ingestion
of chemicals in groundwater that have
migrated from the source area to
residential drinking water wells; (2)
inhalation of volatile chemicals when
showering with contaminated
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groundwater; (3) dermal contact with
chemicals while bathing or showering
with contaminated groundwater; and (4)
inhalation of vapors that may migrate
upward from contaminated groundwater
into overlying buildings.
Adults and children can potentially
be exposed through all four exposure
pathways considered. For adults,
inhalation of vapors while showering is
the most significant exposure pathway;
for children, ingestion is the most
significant pathway, because they are
assumed to take baths and are, therefore,
not exposed via shower vapor
inhalation. As a result of the longer
exposure from showering, adults are the
more sensitive receptors for cancer
effects compared to children,
particularly those under five who are
assumed to take more baths and fewer
showers.74
While the screening level risk
assessment is limited in that it only
examines benzene impacts, the
proposed rule would likely reduce other
contaminant exposures to children in a
similar pattern and would not create
significant adverse impacts on
children’s health.
The screening level population
analysis performed to examine EO
12898 shows that children under 18
years and children under five years are
slightly less likely to be found in the
vicinity of UST facilities. This suggests
that the impacts of the proposed rule
will not have a disproportionate impact
on children’s health. Moreover, because
all regulatory options proposed today
would increase regulatory stringency
and reduce the number and size of
releases, EPA does not expect the
proposed regulation to have any
disproportionate adverse impact on
children. The public is invited to submit
comments or identify peer-reviewed
studies and data that assess effects of
early life exposure to petroleum
products.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This action is not a ‘‘significant
energy action’’ as defined in Executive
Order 13211 (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 following summarizes EPA’s
assessment of the energy impacts that
the proposed rulemaking will have on
energy supply, distribution, and use.
74 United States Department of Health and Human
Services, Public Health Service, Agency for Toxic
Substances and Disease Registry, ‘‘Toxicological
Profile for Polycyclic Aromatic Hydrocarbons,’’
August 1995.
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The proposed regulation consists of
additional regulatory requirements that
apply to the owners and operators of
underground storage tanks. To the
extent that the proposed regulation
affects the motor fuel sector, it does so
at the retail motor fuel sales level, rather
than the level of refineries or
distributors, who supply the retail
stations with motor fuel. Therefore, we
do not expect the proposed regulation to
have a significant adverse impact on
energy supply or distribution.
The additional regulatory
requirements contained in the proposed
regulation may increase compliance
costs for owners and operators of retail
motor fuel stations. If owners and
operators of retail motor fuel stations
affected by the proposed regulation can
pass through their increased compliance
costs, energy use may be affected via
higher energy prices caused by the
proposed regulation. However, we do
not expect a significant change in retail
gasoline prices to result from this
proposed regulation for the following
reasons: (1) Economic analyses of retail
fuel prices have revealed that demand
for gasoline is highly sensitive to price
(elastic) within localized geographic
areas. As a result, if one motor fuel
retailer in an area passes through
increases in compliance costs by
increasing gasoline prices, while
another does not, the one with higher
prices is at a competitive disadvantage;
and (2) retail motor fuel stations often
have associated stores and/or services,
such as car washes, repair operations,
and convenience outlets, on which they
can more successfully pass through
increases in compliance costs.
Furthermore, when considered in the
context of total fuel consumption in the
United States, the proposed rule would
represent only a very small fraction of
motor fuel prices even if it was fully
passed through to consumers.
According to the Bureau of
Transportation Statistics, the United
States consumed approximately 171
billion gallons of motor fuel (including
gasoline and diesel) in 2008 at an
average price of $3.27.75 This implies
75 The 2008 prices per gallon for all grades of
retail motor gasoline and No. 2 diesel fuel (all
concentrations of sulfur) were $3.32 and $3.15,
respectively, as reported by the Bureau of
Transportation Statistics in Table 3–8: Sales Price
of Transportation Fuel to End-Users in National
Transportation Statistics 2010 (at https://
www.bts.gov/publications/
national_transportation_statistics/pdf/entire.pdf).
We weight these prices according to prime supplier
sales volumes in 2009 published by the Energy
Information Administration, which summed to
362,798.5 thousands of gallons per day for gasoline
and 132,489.3 thousands of gallons per day for all
grades of diesel fuel (at https://www.eia.gov/dnav/
pet/pet_cons_prim_dcu_nus_a.htm).
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that U.S. consumers spent $558 billion
in 2008 on motor fuel. The overall cost
of the proposed regulation is
approximately $210 million, less than
one-tenth of 1 percent of the amount
spent by end users on motor fuel in
2008. In comparison, an increase of 1
cent in the average price of motor fuel
in 2008 would have increased the total
cost to consumers by approximately
$1.7 billion. Given these circumstances,
the proposed regulations should not
have a measurable impact on retail
motor fuel prices. As a result, EPA does
not expect the proposed regulations to
have a significant adverse impact on
energy prices or use.
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 (15 U.S.C. 272 note) directs
EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
materials specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by voluntary consensus standards
bodies. NTTAA directs EPA to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards.
This proposed regulation involves
technical standards. EPA is proposing to
use voluntary consensus standards,
called codes of practice identified in
section E–2 of the preamble. These
codes of practice meet the objectives of
today’s proposed regulation by
establishing criteria for the design,
construction, and maintenance of
underground storage tanks.
EPA welcomes comments on this
aspect of the proposed regulation and,
specifically, invites the public to
identify potentially applicable voluntary
consensus standards and to explain why
such standards should be used in this
regulation.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898 (59 FR 7629
(Feb. 16, 1994)) establishes federal
executive policy on environmental
justice. Its main provision directs
federal agencies, to the greatest extent
practicable and permitted by law, to
make environmental justice part of their
mission by identifying and addressing,
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71761
as appropriate, disproportionately high
and adverse human health or
environmental effects of their programs,
policies, and activities on minority
populations and low-income
populations in the United States.
To inform us about the socioeconomic
characteristics of communities
potentially affected by the proposed
regulation, EPA conducted a screening
analysis to examine whether there is a
statistically significant disparity
between socioeconomic characteristics
of populations located near UST
facilities and those that are not.76 As
discussed in the RIA, the results
indicate that minority and low-income
populations are slightly more likely to
be located near UST facilities. An
environmental justice analysis would
then require an assessment of whether
there would be disproportionate and
adverse impacts on these populations.
However, because all regulatory options
considered in this proposed regulation
would increase regulatory stringency
and reduce the number and size of
releases, EPA does not anticipate the
proposed regulation to have any
disproportionately high and adverse
human health or environmental effects
on these minority or low-income
communities or any community.
List of Subjects
40 CFR Part 280
Environmental protection,
Administrative practice and procedures,
Confidential business information,
Groundwater, Hazardous materials,
Petroleum, Reporting and recordkeeping
requirements, Underground storage
tanks, Water pollution control, Water
supply.
40 CFR Part 281
Environmental protection,
Administrative practice and procedures,
Hazardous substances, Petroleum, State
program approval, Underground storage
tanks.
Dated: October 25, 2011.
Lisa P. Jackson,
Administrator.
For the reasons stated in the
preamble, Title 40 Chapter I of Code of
Federal Regulations is proposed to be
amended as follows.
76 Note that the affected populations identified in
the screening analysis summarized here are simply
defined by specific demographics surrounding UST
locations. These affected populations are not
necessarily equivalent to communities that others
have specifically identified as ‘‘environmental
justice communities.’’
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PART 280—TECHNICAL STANDARDS
AND CORRECTIVE ACTION
REQUIREMENTS FOR OWNERS AND
OPERATORS OF UNDERGROUND
STORAGE TANKS (UST)
1. The authority citation for part 280
is revised to read as follows:
Authority: 42 U.S.C. 6912, 6991, 6991(a),
6991(b), 6991(c), 6991(d), 6991(e), 6991(f),
6991(g), 6991(h), 6991(i).
2. Revise § 280.10 to read as follows:
§ 280.10
Applicability.
(a) The requirements of this part
apply to all owners and operators of an
UST system as defined in § 280.12
except as otherwise provided in
paragraphs (b) and (c) of this section.
(1) Previously deferred UST systems.
UST systems previously deferred from
subparts B, C, D, E, G and H (airport
hydrant fuel distribution systems, UST
systems with field-constructed tanks,
and wastewater treatment tank systems)
and UST systems previously deferred
from subpart D (UST systems that store
fuel solely for use by emergency power
generators) must begin meeting the
requirements of this part as follows:
(i) UST systems installed on or before
[effective date of rule] must meet the
schedule in the following table.
Subpart or Section
UST systems that store fuel solely for use by
emergency power generators.
D .......................................................................
[1 Year after effective date of rule].
Airport hydrant fuel distribution systems; UST
systems with field-constructed tanks; and
wastewater treatment tank systems.
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Type of UST system
B (except § 280.22) and C ...............................
D .......................................................................
§ 280.22 of subpart B, E, G and H ..................
[3 Years after effective date of rule].
See the phase in schedule in § 280.40(c).
[effective date of rule].
(ii) UST systems installed after
[effective date of rule] must meet all
requirements at installation.
(2) Any UST system listed in
paragraph (c) of this section must meet
the requirements of § 280.11.
(b) The following UST systems are
excluded from the requirements of this
part:
(1) Any UST system holding
hazardous wastes listed or identified
under Subtitle C of the Solid Waste
Disposal Act, or a mixture of such
hazardous waste and other regulated
substances.
(2) Any wastewater treatment tank
system that is part of a wastewater
treatment facility regulated under
Section 402 or 307(b) of the Clean Water
Act.
(3) Equipment or machinery that
contains regulated substances for
operational purposes such as hydraulic
lift tanks and electrical equipment
tanks.
(4) Any UST system whose capacity is
110 gallons or less.
(5) Any UST system that contains a de
minimis concentration of regulated
substances.
(6) Any emergency spill or overflow
containment UST system that is
expeditiously emptied after use.
(c) Deferrals. Subparts B, C, D, E, and
G of this part do not apply to:
(1) Aboveground tanks associated
with:
(i) Airport hydrant fuel distribution
systems; and
(ii) UST systems with fieldconstructed tanks;
(2) Any UST systems containing
radioactive material that are regulated
under the Atomic Energy Act of 1954
(42 USC 2011 and following); and
(3) Any UST system that is part of an
emergency generator system at nuclear
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Effective date
power generation facilities regulated by
the Nuclear Regulatory Commission
under 10 CFR part 50.
3. In § 280.11 revise the Note at the
end of the section to read as follows:
§ 280.11 Interim prohibition for deferred
UST systems.
*
*
*
*
*
Note to paragraphs (a) and (b): The
following codes of practice may be used as
guidance for complying with this section:
(A) NACE International Recommended
Practice RP 0285, ‘‘Corrosion Control of
Underground Storage Systems by Cathodic
Protection’’;
(B) NACE International Standard Practice
SP 0169, ‘‘Control of External Corrosion on
Underground or Submerged Metallic Piping
Systems’’;
(C) American Petroleum Institute
Recommended Practice 1632, ‘‘Cathodic
Protection of Underground Petroleum Storage
Tanks and Piping Systems’’; or
(D) Steel Tank Institute Recommended
Practice R892, ‘‘Recommended Practice for
Corrosion Protection of Underground Piping
Networks Associated with Liquid Petroleum
Storage and Dispensing Systems’’.
4. Section 280.12 is amended as follows:
a. By adding in alphabetical order
definitions for ‘‘Airport hydrant fuel
distribution system,’’ ‘‘Class A
operator,’’ ‘‘Class B operator,’’ ‘‘Class C
operator,’’ ‘‘Dispenser system,’’
‘‘Replaced,’’ ‘‘Secondary containment,’’
‘‘Training program,’’ and ‘‘Underdispenser containment,’’ and
b. By revising the definitions for
‘‘Motor fuel,’’ ‘‘Regulated substance,’’
‘‘Repair,’’ and ‘‘Underground storage
tank.’’
§ 280.12
Definitions.
*
*
*
*
*
Airport hydrant fuel distribution
system means an UST system that is a
combination of one or more tanks
directly connected to underground
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hydrant piping used to fuel aircraft.
These systems do not have a dispenser
at the end of the piping run, but rather
have a hydrant (fill stand). If an
aboveground storage tank (AST) is
feeding an intermediary tank or tanks,
this definition does not include the
AST, but does include all underground
piping entering and leaving the
intermediary tank(s) and the
intermediary tank(s). Intermediary tanks
are those tanks directly connected to the
hydrant piping.
*
*
*
*
*
Class A operator means the individual
who has primary responsibility to
operate and maintain the UST system in
accordance with applicable
requirements and standards established
by the implementing agency. The Class
A operator typically manages resources
and personnel, such as establishing
work assignments, to achieve and
maintain compliance with regulatory
requirements.
Class B operator means the individual
who has day-to-day responsibility for
implementing applicable regulatory
requirements and standards established
by the implementing agency. The Class
B operator typically implements in-field
aspects of operation, maintenance, and
associated recordkeeping for the UST
system.
Class C operator means the employee
responsible for initially addressing
emergencies presented by a spill or
release from an UST system. The Class
C operator typically controls or
monitors the dispensing or sale of
regulated substances.
*
*
*
*
*
Dispenser system means equipment
located aboveground that meters the
amount of regulated substances
transferred to a point of use outside the
UST system, such as a motor vehicle.
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This system includes the equipment
necessary to connect the dispenser to
the underground storage tank system.
*
*
*
*
*
Motor fuel means petroleum or a
petroleum-based substance that is
typically used in the operation of a
motor engine, such as motor gasoline,
aviation gasoline, No. 1 or No. 2 diesel
fuel, or any blend containing one or
more of these substances (for example:
motor gasoline blended with alcohol).
*
*
*
*
*
Regulated substance means
(a) Any substance defined in section
101(14) of the Comprehensive
Environmental Response, Compensation
and Liability Act (CERCLA) of 1980 (but
not including any substance regulated
as a hazardous waste under subtitle C),
and
(b) Petroleum, including crude oil or
any fraction thereof that is liquid at
standard conditions of temperature and
pressure (60 degrees Fahrenheit and
14.7 pounds per square inch absolute).
The term ‘‘regulated substance’’
includes but is not limited to petroleum
and petroleum-based substances
comprised of a complex blend of
hydrocarbons, such as motor fuels, jet
fuels, distillate fuel oils, residual fuel
oils, lubricants, petroleum solvents, and
used oils.
*
*
*
*
*
Repair means to restore a tank, pipe,
spill prevention equipment, overfill
prevention equipment, corrosion
protection equipment, release detection
equipment or other UST system
component that has caused a release or
a suspected release of product from the
UST system or has failed to function
properly.
Replaced means
(a) For a tank—to remove a tank and
install another tank.
(b) For piping—to remove 50 percent
or more of piping and install other
piping, excluding connectors, connected
to a single tank. For tanks with multiple
piping runs, this definition applies
independently to each piping run.
*
*
*
*
*
Secondary containment or
Secondarily contained means a release
prevention and release detection system
for a tank and/or piping. These systems
have an inner and outer barrier with an
interstitial space that is monitored for
leaks.
*
*
*
*
*
Training program means any program
established by the implementing agency
that provides information to and
evaluates the knowledge of a Class A,
Class B, or Class C operator regarding
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requirements and standards for UST
systems.
Under-dispenser containment or UDC
means containment underneath a
dispenser system designed to prevent
dispenser system leaks from reaching
soil or groundwater.
*
*
*
*
*
Underground storage tank or UST
means any one or combination of tanks
(including underground pipes
connected thereto) that is used to
contain an accumulation of regulated
substances, and the volume of which
(including the volume of underground
pipes connected thereto) is 10 percent
or more beneath the surface of the
ground. This term does not include any:
(a) Farm or residential tank of 1,100
gallons or less capacity used for storing
motor fuel for noncommercial purposes;
(b) Tank used for storing heating oil
for consumptive use on the premises
where stored;
(c) Septic tank;
(d) Pipeline facility (including
gathering lines):
(1) Which is regulated under U.S.C.
chapters 601 and 603, or
(2) Which is an intrastate pipeline
facility regulated under state laws as
provided in U.S.C. 49 chapters 601 and
603,and which is determined by the
Secretary of Transportation to be
connected to a pipeline, or to be
operated or intended to be capable of
operating at pipeline pressure, or as an
integral part of a pipeline;
(e) Surface impoundment, pit, pond,
or lagoon;
(f) Storm-water or wastewater
collection system;
(g) Flow-through process tank;
(h) Liquid trap or associated gathering
lines directly related to oil or gas
production and gathering operations; or
(i) Storage tank situated in an
underground area (such as a basement,
cellar, mineworking, drift, shaft, or
tunnel) if the storage tank is situated
upon or above the surface of the floor.
The term underground storage tank or
UST does not include any pipes
connected to any tank which is
described in paragraphs (a) through (i)
of this definition.
*
*
*
*
*
5. Revise Subpart B to read as follows:
71763
Subpart B—UST Systems: Design,
Construction, Installation and
Notification
§ 280.20 Performance standards for new
UST systems.
In order to prevent releases due to
structural failure, corrosion, or spills
and overfills for as long as the UST
system is used to store regulated
substances, all owners and operators of
new UST systems must meet the
following requirements.
(a) Tanks. Each tank must be properly
designed and constructed, and any
portion underground that routinely
contains product must be protected
from corrosion, in accordance with a
code of practice developed by a
nationally recognized association or
independent testing laboratory as
specified in paragraphs (a)(1) through
(a)(5) of this section. In addition, all
new or replaced tanks where
installation began after [effective date of
rule] must be secondarily contained in
accordance with paragraph (a)(6) of this
section:
(1) The tank is constructed of
fiberglass-reinforced plastic; or
Note to paragraph (a)(1): The following
codes of practice may be used to comply with
paragraph (a)(1) of this section:
(A) Underwriters Laboratories Standard
1316, ‘‘Glass-Fiber-Reinforced Plastic
Underground Storage Tanks for Petroleum
Products, Alcohols, and Alcohol-Gasoline
Mixtures’’; or
(B) Underwriter’s Laboratories of Canada
S615, ‘‘Standard for Reinforced Plastic
Underground Tanks for Flammable and
Combustible Liquids’’.
(2) The tank is constructed of steel
and cathodically protected in the
following manner:
(i) The tank is coated with a suitable
dielectric material;
(ii) Field-installed cathodic protection
systems are designed by a corrosion
expert;
(iii) Impressed current systems are
designed to allow determination of
current operating status as required in
§ 280.31(c); and
(iv) Cathodic protection systems are
operated and maintained in accordance
with § 280.31 or according to guidelines
established by the implementing
agency; or
Subpart B—UST Systems: Design,
Construction, Installation and
Notification
Sec.
280.20 Performance standards for new UST
systems.
280.21 Upgrading of existing UST systems.
280.22 Notification requirements.
Note to paragraph (a)(2): The following
codes of practice may be used to comply with
paragraph (a)(2) of this section:
(A) Steel Tank Institute Specification
‘‘sti-P3® Specification and Manual for
External Corrosion Protection of
Underground Steel Storage Tanks’’;
(B) Underwriters Laboratories Standard
1746, ‘‘Standard for External Corrosion
Protection Systems for Steel Underground
Storage Tanks’’;
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(C) Underwriters Laboratories of Canada
S603, ‘‘Standard for Steel Underground
Tanks for Flammable and Combustible
Liquids,’’ and S603.1, ‘‘Standard for External
Corrosion Protection Systems for Steel
Underground Tanks for Flammable and
Combustible Liquids,’’ and S631, ‘‘Standard
for Isolating Bushings for Steel Underground
Tanks Protected with External Corrosion
Protection Systems’’;
(D) Steel Tank Institute Standard F841,
‘‘Standard for Dual Wall Underground Steel
Storage Tanks’’; or
(E) NACE International Recommended
Practice RP 0285, ‘‘Corrosion Control of
Underground Storage Systems by Cathodic
Protection,’’ and Underwriters Laboratories
Standard 58, ‘‘Standard for Steel
Underground Tanks for Flammable and
Combustible Liquids’’.
(3) The tank is constructed of steel
and clad or jacketed with a noncorrodible material; or
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Note to paragraph (a)(3): The following
codes of practice may be used to comply with
paragraph (a)(3) of this section:
(A) Underwriters Laboratories Standard
1746, ‘‘Standard for External Corrosion
Protection Systems for Steel Underground
Storage Tanks’’;
(B) Steel Tank Institute Specification F894,
‘‘ACT–100® Specification for External
Corrosion Protection of FRP Composite Steel
USTs’’;
(C) Steel Tank Institute Specification F961,
‘‘ACT–100–U® Specification for External
Corrosion Protection of Composite Steel
Underground Storage Tanks’’; or
(D) Steel Tank Institute Specification F922,
‘‘Steel Tank Institute Specification for
Permatank®’’.
(4) The tank is constructed of metal
without additional corrosion protection
measures provided that:
(i) The tank is installed at a site that
is determined by a corrosion expert not
to be corrosive enough to cause it to
have a release due to corrosion during
its operating life; and
(ii) Owners and operators maintain
records that demonstrate compliance
with the requirements of paragraph
(a)(4)(i) of this section for the remaining
life of the tank; or
(5) The tank construction and
corrosion protection are determined by
the implementing agency to be designed
to prevent the release or threatened
release of any stored regulated
substance in a manner that is no less
protective of human health and the
environment than paragraphs (a)(1)
through (4) of this section; or
(6) The tank is secondarily contained.
Secondary containment must be
periodically tested in accordance with
§ 280.36. Secondarily contained tanks
must meet the following:
(i) Be able to contain regulated
substances leaked from the primary
containment until they are detected and
removed; and
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(ii) Be able to prevent the release of
regulated substances to the environment
at any time during the operational life
of the UST system.
(iv) Cathodic protection systems are
operated and maintained in accordance
with § 280.31 or guidelines established
by the implementing agency; or
Note to paragraph (a)(6): The following
codes of practice may be used to comply with
paragraph (a)(6) of this section:
(A) Underwriters Laboratories Standard 58,
‘‘Standard for Steel Underground Tanks for
Flammable and Combustible Liquids’’;
(B) Underwriters Laboratories Standard
1316, ‘‘Glass-Fiber-Reinforced Plastic
Underground Storage Tanks for Petroleum
Products, Alcohols, and Alcohol-Gasoline
Mixtures’’;
(C) Underwriters Laboratories Standard
1746, ‘‘Standard for External Corrosion
Protection Systems for Steel Underground
Storage Tanks’’;
(D) Steel Tank Institute Standard F841,
‘‘Standard for Dual Wall Underground Steel
Storage Tanks’’; or
(E) Steel Tank Institute Specification F922,
‘‘Steel Tank Institute Specification for
Permatank®’’.
Note to paragraph (b)(2): The following
codes of practice may be used to comply with
paragraph (b)(2) of this section:
(A) American Petroleum Institute
Recommended Practice 1632, ‘‘Cathodic
Protection of Underground Petroleum Storage
Tanks and Piping Systems’’;
(B) Underwriters Laboratories Subject
971A, ‘‘Outline of Investigation for Metallic
Underground Fuel Pipe’’;
(C) Steel Tank Institute Recommended
Practice R892, ‘‘Recommended Practice for
Corrosion Protection of Underground Piping
Networks Associated with Liquid Petroleum
Storage and Dispensing Systems’’;
(D) NACE International Standard Practice
SP 0169, ‘‘Control of External Corrosion on
Underground or Submerged Metallic Piping
Systems’’; or
(E) NACE International Recommended
Practice RP 0285, ‘‘Corrosion Control of
Underground Storage Systems by Cathodic
Protection’’.
(b) Piping. The piping that routinely
contains regulated substances and is in
contact with the ground must be
properly designed, constructed, and
protected from corrosion in accordance
with a code of practice developed by a
nationally recognized association or
independent testing laboratory as
specified in paragraphs (b)(1) through
(b)(4) of this section. In addition, except
for suction piping that meets the
requirements of 280.41(b)(1)(ii)(A)
through (E) and piping associated with
field-constructed tanks and airport
hydrant fuel distribution systems, all
new or replaced piping where
installation began after [effective date of
rule] must be secondarily contained in
accordance with paragraph (b)(5) of this
section. The entire piping run must be
replaced when 50 percent or more of a
piping run is replaced.
(1) The piping is constructed of a noncorrodible material; or
Note to paragraph (b)(1): The following
codes of practice may be used to comply with
paragraph (b)(1) of this section:
(A) Underwriters Laboratories Standard
971, ‘‘Standard for Non-Metallic
Underground Piping for Flammable Liquids’’;
or
(B) Underwriters Laboratories of Canada
Standard S660, ’’ Standard for Non-Metallic
Underground Piping for Flammable Liquids’’.
(2) The piping is constructed of steel
and cathodically protected in the
following manner:
(i) The piping is coated with a
suitable dielectric material;
(ii) Field-installed cathodic protection
systems are designed by a corrosion
expert;
(iii) Impressed current systems are
designed to allow determination of
current operating status as required in
§ 280.31(c); and
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(3) The piping is constructed of metal
without additional corrosion protection
measures provided that:
(i) The piping is installed at a site that
is determined by a corrosion expert to
not be corrosive enough to cause it to
have a release due to corrosion during
its operating life; and
(ii) Owners and operators maintain
records that demonstrate compliance
with the requirements of paragraph
(b)(3)(i) of this section for the remaining
life of the piping; or
(4) The piping construction and
corrosion protection are determined by
the implementing agency to be designed
to prevent the release or threatened
release of any stored regulated
substance in a manner that is no less
protective of human health and the
environment than the requirements in
paragraphs (b)(1) through (3) of this
section; or
(5) The piping is secondarily
contained. Secondary containment must
be periodically tested in accordance
with § 280.36. Secondarily contained
piping must meet the following:
(i) Be able to contain regulated
substances leaked from the primary
containment until they are detected and
removed; and
(ii) Be able to prevent the release of
regulated substances to the environment
at any time during the operational life
of the UST system.
Note to paragraph (b)(5): The following
codes of practice may be used to comply with
paragraph (b)(5) of this section:
(A) Underwriters Laboratories Standard
971, ‘‘Standard for Non-Metallic
Underground Piping for Flammable Liquids’’;
or
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(B) Underwriters Laboratories Subject
971A, ‘‘Outline of Investigation for Metallic
Underground Fuel Pipe’’.
(c) Spill and overfill prevention
equipment.
(1) Except as provided in paragraphs
(c)(2) and (c)(3) of this section, to
prevent spilling and overfilling
associated with product transfer to the
UST system, owners and operators must
use the following spill and overfill
prevention equipment:
(i) Spill prevention equipment that
will prevent release of product to the
environment when the transfer hose is
detached from the fill pipe (for example,
a spill catchment basin); and
(ii) Overfill prevention equipment
that will:
(A) Automatically shut off flow into
the tank when the tank is no more than
95 percent full; or
(B) Alert the transfer operator when
the tank is no more than 90 percent full
by restricting the flow into the tank or
triggering a high-level alarm; or
(C) Restrict flow 30 minutes prior to
overfilling, alert the transfer operator
with a high level alarm one minute
before overfilling, or automatically shut
off flow into the tank so that none of the
fittings located on top of the tank are
exposed to product due to overfilling.
(2) Owners and operators are not
required to use the spill and overfill
prevention equipment specified in
paragraph (c)(1) of this section if:
(i) Alternative equipment is used that
is determined by the implementing
agency to be no less protective of human
health and the environment than the
equipment specified in paragraph
(c)(1)(i) or (ii) of this section; or
(ii) The UST system is filled by
transfers of no more than 25 gallons at
one time.
(3) Flow restrictors used in vent lines
may not be used to comply with
paragraph (c)(1)(ii) of this section when
overfill prevention is installed or
replaced after [effective date of rule].
(4) Spill and overfill prevention
equipment must be periodically tested
in accordance with § 280.35.
(d) Installation. All tanks and piping
must be properly installed in
accordance with a code of practice
developed by a nationally recognized
association or independent testing
laboratory and in accordance with the
manufacturer’s instructions.
Note to paragraph (d): Tank and piping
system installation practices and procedures
described in the following codes of practice
may be used to comply with the
requirements of paragraph (d) of this section:
(A) American Petroleum Institute
Publication 1615, ‘‘Installation of
Underground Petroleum Storage System’’;
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(B) Petroleum Equipment Institute
Publication RP100, ‘‘Recommended Practices
for Installation of Underground Liquid
Storage Systems’’; or
(C) National Fire Protection Association
Standard 30, ‘‘Flammable and Combustible
Liquids Code’’ and Standard 30A, ‘‘Code for
Motor Fuel Dispensing Facilities and Repair
Garages’’.
(e) Certification of installation. All
owners and operators must ensure that
one or more of the following methods of
certification, testing, or inspection is
used to demonstrate compliance with
paragraph (d) of this section by
providing a certification of compliance
on the UST notification form in
accordance with § 280.22.
(1) The installer has been certified by
the tank and piping manufacturers; or
(2) The installer has been certified or
licensed by the implementing agency; or
(3) The installation has been
inspected and certified by a registered
professional engineer with education
and experience in UST system
installation; or
(4) The installation has been
inspected and approved by the
implementing agency; or
(5) All work listed in the
manufacturer’s installation checklists
has been completed; or
(6) The owner and operator have
complied with another method for
ensuring compliance with paragraph (d)
of this section that is determined by the
implementing agency to be no less
protective of human health and the
environment.
(f) Dispenser Systems. Each UST
system must be equipped with underdispenser containment for any new
dispenser system installed.
(1) A dispenser system is considered
new when both the dispenser and the
equipment needed to connect the
dispenser to the underground storage
tank system are installed at an UST
facility. The equipment necessary to
connect the dispenser to the
underground storage tank system
includes check valves, shear valves,
unburied risers or flexible connectors,
or other transitional components that
are beneath the dispenser and connect
the dispenser to the underground
piping.
(2) Under-dispenser containment
must be liquid-tight on its sides, bottom,
and at any penetrations. Underdispenser containment must allow for
visual inspection and access to the
components in the containment system
or be continuously monitored for leaks
from the dispenser system.
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§ 280.21 Upgrading of existing UST
systems.
In accordance with subpart G of this
part, owners and operators must
permanently close any UST system that
does not meet the new UST system
performance standards in § 280.20 or
has not been upgraded in accordance
with paragraphs (b) through (d) of this
section. This does not apply to
previously deferred UST systems
described in paragraph (e) of this
section and where an upgrade is
determined to be appropriate by the
implementing agency.
(a) Alternatives allowed. All existing
UST systems must comply with one of
the following requirements:
(1) New UST system performance
standards under § 280.20;
(2) The upgrading requirements in
paragraphs (b) through (d) of this
section; or
(3) Closure requirements under
subpart G of this part, including
applicable requirements for corrective
action under subpart F.
(b) Tank upgrading requirements.
Steel tanks must be upgraded to meet
one of the following requirements in
accordance with a code of practice
developed by a nationally recognized
association or independent testing
laboratory:
(1) Interior lining. Tanks upgraded by
internal lining must meet the following:
(i) The lining was installed in
accordance with the requirements of
§ 280.33, and
(ii) Within 10 years after lining, and
every 5 years thereafter, the lined tank
is internally inspected and found to be
structurally sound with the lining still
performing in accordance with original
design specifications. If the internal
lining is no longer performing in
accordance with original design
specifications and cannot be repaired in
accordance with a code of practice
developed by a nationally recognized
association or independent testing
laboratory, then the lined tank must be
permanently closed in accordance with
subpart G of this part.
(2) Cathodic protection. Tanks
upgraded by cathodic protection must
meet the requirements of
§ 280.20(a)(2)(ii), (iii), and (iv) and the
integrity of the tank must have been
ensured using one of the following
methods:
(i) The tank was internally inspected
and assessed to ensure that the tank was
structurally sound and free of corrosion
holes prior to installing the cathodic
protection system; or
(ii) The tank had been installed for
less than 10 years and is monitored
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monthly for releases in accordance with
§ 280.43(d) through (i); or
(iii) The tank had been installed for
less than 10 years and was assessed for
corrosion holes by conducting two
tightness tests that meet the
requirements of § 280.43(c). The first
tightness test must have been conducted
prior to installing the cathodic
protection system. The second tightness
test must have been conducted between
three and six months following the first
operation of the cathodic protection
system; or
(iv) The tank was assessed for
corrosion holes by a method that is
determined by the implementing agency
to prevent releases in a manner that is
no less protective of human health and
the environment than paragraphs
(b)(2)(i) through (iii) of this section.
(3) Internal lining combined with
cathodic protection. Tanks upgraded by
both internal lining and cathodic
protection must meet the following:
(i) The lining was installed in
accordance with the requirements of
§ 280.33; and
(ii) The cathodic protection system
meets the requirements of
§ 280.20(a)(2)(ii), (iii), and (iv).
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
Note to paragraph (b): The following
historical codes of practice were listed as
options for complying with paragraph (b) of
this section:
(A) American Petroleum Institute
Publication 1631, ‘‘Recommended Practice
for the Interior Lining of Existing Steel
Underground Storage Tanks’’;
(B) National Leak Prevention Association
Standard 631, ‘‘Spill Prevention, Minimum
10 Year Life Extension of Existing Steel
Underground Tanks by Lining Without the
Addition of Cathodic Protection’’;
(C) National Association of Corrosion
Engineers Standard RP–02–85, ‘‘Control of
External Corrosion on Metallic Buried,
Partially Buried, or Submerged Liquid
Storage Systems’’; and
(D) American Petroleum Institute
Publication 1632, ‘‘Cathodic Protection of
Underground Petroleum Storage Tanks and
Piping Systems’’.
Note to paragraph (b)(1)(ii): The following
codes of practice may be used to comply with
the periodic lining inspection requirement of
this section:
(A) American Petroleum Institute
Recommended Practice 1631, ‘‘Interior
Lining and Periodic Inspection of
Underground Storage Tanks’’;
(B) National Leak Prevention Association
Standard 631, ‘‘Entry, Cleaning, Interior
Inspection, Repair, and Lining of
Underground Storage Tanks’’; or
(C) Ken Wilcox Associates Recommended
Practice, ‘‘Recommended Practice for
Inspecting Buried Lined Steel Tanks Using a
Video Camera’’.
(c) Piping upgrading requirements.
Metal piping that routinely contains
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regulated substances and is in contact
with the ground must be cathodically
protected in accordance with a code of
practice developed by a nationally
recognized association or independent
testing laboratory and must meet the
requirements of § 280.20(b)(2)(ii), (iii),
and (iv).
Note to paragraph (c): The codes of
practice listed in the note following
§ 280.20(b)(2) may be used to comply with
this requirement.
(d) Spill and overfill prevention
equipment. To prevent spilling and
overfilling associated with product
transfer to the UST system, all existing
UST systems must comply with new
UST system spill and overfill
prevention equipment requirements
specified in § 280.20(c).
(e) Upgrade requirements for
previously deferred UST systems.
Previously deferred wastewater
treatment tank systems, airport hydrant
fuel distribution systems, and UST
systems with field-constructed tanks
where installation commenced on or
before [effective date of rule] must meet
the following requirements according to
the time table in subpart A or be
permanently closed pursuant to subpart
G of this part.
(1) Corrosion protection. UST system
components in contact with the ground
that routinely contain regulated
substances must meet one of the
following:
(i) The new UST system performance
standards for tanks at § 280.20(a) and for
piping at § 280.20(b); or
(ii) Be constructed of metal and
cathodically protected according to a
code of practice developed by a
nationally recognized association or
independent testing laboratory and
meets the following:
(A) Cathodic protection must meet the
requirements of § 280.20(a)(2)(ii), (iii)
and (iv) for tanks, and § 280.20(b)(2)(ii),
(iii), and (iv) for piping.
(B) Tanks greater than 10 years old
without cathodic protection must be
assessed to ensure the tank is
structurally sound and free of corrosion
holes prior to adding cathodic
protection. The assessment must be by
internal inspection or another method
determined by the implementing agency
to adequately assess the tank for
structural soundness and corrosion
holes.
Note to paragraph (e): The following codes
of practice may be used to comply with this
paragraph:
(A) NACE International Recommended
Practice RP 0285, ‘‘Control of Underground
Storage Tank Systems by Cathodic
Protection’’;
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(B) NACE International Standard Practice
SP 0169, ‘‘Control of External Corrosion on
Underground or Submerged Metallic Piping
Systems’’;
(C) National Leak Prevention Association
Standard 631, ‘‘Entry, Cleaning, Interior
Inspection, Repair, and Lining of
Underground Storage Tanks’’; or
(D) American Society for Testing and
Materials Standard G158, ‘‘Standard Guide
for Three Methods of Assessing Buried Steel
Tanks’’.
(2) Spill and overfill prevention
equipment. To prevent spilling and
overfilling associated with product
transfer to the UST system, all
previously deferred UST systems must
comply with new UST system spill and
overfill prevention equipment
requirements specified in § 280.20(c).
§ 280.22
Notification requirements.
(a) After May 8, 1986, an owner must
submit notice of a tank system’s
existence to the implementing agency
within 30 days of bringing the
underground storage tank system into
use. Owners must use the form in
Appendix I of this part.
Note to paragraph (a): Owners and
operators of UST systems that were in the
ground on or after May 8, 1986, unless taken
out of operation on or before January 1, 1974,
were required to notify the designated state
or local agency in accordance with the
Hazardous and Solid Waste Amendments of
1984, Public Law 98–616, on a form
published by EPA on November 8, 1985 (50
FR 46602) unless notice was given pursuant
to section 103(c) of CERCLA. Owners and
operators who have not complied with the
notification requirements may use portions I
through VI of the notification form contained
in Appendix I of this part.
(b) Within 30 days of acquisition, any
person who assumes ownership of a
regulated underground storage tank
system, except as described in
paragraph (a) of this section, must
submit a notice of the ownership change
to the implementing agency, using the
form in Appendix II of this part.
(c) In states where state law,
regulations, or procedures require
owners to use forms that differ from
those set forth in Appendix I and
Appendix II of this part to fulfill the
requirements of this section, the state
forms may be submitted in lieu of the
forms set forth in Appendix I and
Appendix II of this part. If a state
requires that its form be used in lieu of
the form presented in Appendix I and
Appendix II of this part, such form
must, at a minimum, collect the
information prescribed in Appendix I
and Appendix II of this part.
(d) Owners required to submit notices
under paragraph (a) or (b) of this section
must provide notices to the appropriate
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implementing agency for each tank they
own. Owners may provide notice for
several tanks using one notification
form, but owners who own tanks
located at more than one place of
operation must file a separate
notification form for each separate place
of operation.
(e) All owners and operators of new
UST systems must certify in the
notification form compliance with the
following requirements:
(1) Installation of tanks and piping
under § 280.20(e);
(2) Cathodic protection of steel tanks
and piping under § 280.20(a) and (b);
(3) Financial responsibility under
subpart H of this part; and
(4) Release detection under §§ 280.41
and 280.42.
(f) All owners and operators of new
UST systems must ensure that the
installer certifies in the notification
form that the methods used to install the
tanks and piping complies with the
requirements in § 280.20(d).
(g) Beginning October 24, 1988, any
person who sells a tank intended to be
used as an underground storage tank
must notify the purchaser of such tank
of the owner’s notification obligations
under paragraph (a) of this section. The
statement provided in Appendix III of
this part, when used on shipping tickets
and invoices, may be used to comply
with this requirement.
(h) Within 30 days of [Effective date
of rule], all owners of previously
deferred UST systems must submit a
notice of tank system existence to the
implementing agency, using the form in
Appendix I of this part.
6. In § 280.30 revise the Note to read
as follows:
§ 280.30
*
*
Spill and overfill control.
*
*
*
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
Note: The transfer procedures described in
National Fire Protection Association
Standard 385, ‘‘Standard for Tank Vehicles
for Flammable and Combustible Liquids’’ or
American Petroleum Institute Recommended
Practice 1007, ‘‘Loading and Unloading of
MC 306/DOT 406 Cargo Tank Motor
Vehicles’’ may be used to comply with
paragraph (a) of this section. Further
guidance on spill and overfill prevention
appears in American Petroleum Institute
Recommended Practice 1621, ‘‘Bulk Liquid
Stock Control at Retail Outlets’’.
*
*
*
*
*
7. In § 280.31 revise the introductory
text and the Note to read as follows:
§ 280.31 Operation and maintenance of
corrosion protection.
All owners and operators of metal
UST systems with corrosion protection
must comply with the following
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requirements to ensure that releases due
to corrosion are prevented until the UST
system is permanently closed or
undergoes a change-in-service pursuant
to § 280.71:
*
*
*
*
*
Note to paragraph (b): The following codes
of practice may be used to comply with
paragraph (b) of this section:
(A) NACE International Test Method TM
0101, ‘‘Measurement Techniques Related to
Criteria for Cathodic Protection on
Underground or Submerged Metallic Tank
Systems’’;
(B) NACE International Test Method
TM0497, ‘‘Measurement Techniques Related
to Criteria for Cathodic Protection on
Underground or Submerged Metallic Piping
Systems’’;
(C) Steel Tank Institute Recommended
Practice R051, ‘‘Cathodic Protection Testing
Procedures for sti-P3 USTs’’;
(D) NACE International Recommended
Practice RP 0285, ‘‘Control of Underground
Storage Tank Systems by Cathodic
Protection’’; or
(E) NACE International Standard Practice
SP 0169, ‘‘Control of External Corrosion on
Underground or Submerged Metallic Piping
Systems’’.
*
*
*
*
*
8. Amend § 280.32 to revise paragraph
(a) and to add paragraphs (b) and (c) to
read as follows:
§ 280.32
Compatibility.
*
*
*
*
*
(a) Owners and operators must use an
UST system made of or lined with
materials that are compatible with the
substance stored in the UST system.
(b) Owners and operators storing any
regulated substance containing greater
than 10 percent ethanol or greater than
20 percent biodiesel, or any other
regulated substance identified by the
implementing agency, must use one or
more of the following methods to
demonstrate UST system compatibility
with these regulated substances:
(1) Certification or listing of UST
system components by a nationally
recognized, independent testing
laboratory for use with the regulated
substance stored;
(2) Equipment or component
manufacturer approval. The
manufacturer’s approval must be in
writing, indicate an affirmative
statement of compatibility, specify the
range of biofuel blends the component
is compatible with, and be from the
equipment or component manufacturer;
or
(3) Another method determined by
the implementing agency to be no less
protective of human health and the
environment than the methods listed in
paragraphs (b)(1) or (b)(2) of this
section.
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(c) Owners and operators must
maintain the following records (in
accordance with § 280.34) for the life of
the equipment or component:
(1) Documentation of compliance
with paragraph (b) of this section, as
applicable; and
(2) Records of all equipment or
components installed or replaced after
[effective date of rule]. At a minimum,
each record must include the date of
installation or replacement,
manufacturer, and model.
9. Revise § 280.33 to read as follows:
§ 280.33
Repairs allowed.
Owners and operators of UST systems
must ensure that repairs will prevent
releases due to structural failure or
corrosion as long as the UST system is
used to store regulated substances. The
repairs must meet the following
requirements:
(a) Repairs to UST systems must be
properly conducted in accordance with
a code of practice developed by a
nationally recognized association or an
independent testing laboratory.
Note to paragraph (a): The following codes
of practice may be used to comply with
paragraph (a) of this section:
(A) National Fire Protection Association
Standard 30, ‘‘Flammable and Combustible
Liquids Code’’;
(B) American Petroleum Institute
Recommended Practice RP 2200, ‘‘Repairing
Crude Oil, Liquified Petroleum Gas, and
Product Pipelines’’;
(C) American Petroleum Institute
Recommended Practice RP 1631, ‘‘Interior
Lining and Periodic Inspection of
Underground Storage Tanks’’;
(D) National Fire Protection Association
Standard 326, ‘‘Safeguarding of Tanks and
Containers for Entry, Cleaning, or Repair’’;
(E) National Leak Prevention Association
Standard 631, ‘‘Entry, Cleaning, Interior
Inspection, Repair, and Lining of
Underground Storage Tanks’’;
(F) Steel Tank Institute Recommended
Practice R972, ‘‘Recommended Practice for
the Addition of Supplemental Anodes to stiP3® Tanks’’;
(G) NACE International Recommended
Practice RP 0285, ‘‘Control of Underground
Storage Tank Systems by Cathodic
Protection’’; or
(H) Fiberglass Tank and Pipe Institute
Recommended Practice T–95–02,
‘‘Remanufacturing of Fiberglass Reinforced
Plastic (FRP) Underground Storage Tanks’’.
(b) Repairs to fiberglass-reinforced
plastic tanks may be made by the
manufacturer’s authorized
representatives or in accordance with a
code of practice developed by a
nationally recognized association or an
independent testing laboratory.
(c) Metal pipe sections and fittings
that have released product as a result of
corrosion or other damage must be
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replaced. Non-corrodible pipes and
fittings may be repaired in accordance
with the manufacturer’s specifications.
(d) Repaired tanks and piping must be
tightness tested in accordance with
§ 280.43(c) and § 280.44(b) within 30
days following the date of the
completion of the repair except as
provided in paragraphs (d)(1) through
(4), of this section:
(1) The repaired tank is internally
inspected in accordance with a code of
practice developed by a nationally
recognized association or an
independent testing laboratory; or
(2) The repaired portion of the UST
system is monitored monthly for
releases in accordance with a method
specified in § 280.43(d) through (i);
(3) UST systems with secondary
containment must be tested as specified
in § 280.36 within 30 days following the
completion of any repair. Tanks using
interstitial sensors must be tested using
a vacuum, pressure, or liquid method in
accordance with one of the criteria
listed in § 280.36(a)(1)(ii) following any
repair; or
(4) Another test method is used that
is determined by the implementing
agency to be no less protective of human
health and the environment than those
listed above.
(e) Within 6 months following the
repair of any cathodically protected
UST system, the cathodic protection
system must be tested in accordance
with § 280.31(b) and (c) to ensure that
it is operating properly.
(f) Within 30 days following any
repair to spill or overfill prevention
equipment, the repaired spill or overfill
prevention equipment must be tested in
accordance with § 280.35 to ensure it is
operating properly.
(g) UST system owners and operators
must maintain records (in accordance
with § 280.34) of each repair until the
UST system is permanently closed or
undergoes a change-in-service pursuant
to § 280.71.
10. Revise § 280.34 to read as follows:
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§ 280.34
Reporting and recordkeeping.
Owners and operators of UST systems
must cooperate fully with inspections,
monitoring and testing conducted by the
implementing agency, as well as
requests for document submission,
testing, and monitoring by the owner or
operator pursuant to section 9005 of
Subtitle I of the Solid Waste Disposal
Act, as amended.
(a) Reporting. Owners and operators
must submit the following information
to the implementing agency:
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(1) Notification for all UST systems
(§ 280.22), which includes certification
of installation for new UST systems
(§ 280.20(e)) and notification when any
person assumes ownership of an UST
system (§ 280.22(b));
(2) Reports of all releases including
suspected releases (§ 280.50), spills and
overfills (§ 280.53), and confirmed
releases (§ 280.61);
(3) Corrective actions planned or
taken including initial abatement
measures (§ 280.62), initial site
characterization (§ 280.63), free product
removal (§ 280.64), investigation of soil
and ground-water cleanup (§ 280.65),
and corrective action plan (§ 280.66);
and
(4) A notification before permanent
closure or change-in-service (§ 280.71).
(b) Recordkeeping. Owners and
operators must maintain the following
information:
(1) A corrosion expert’s analysis of
site corrosion potential if corrosion
protection equipment is not used
(§ 280.20(a)(4); § 280.20(b)(3)).
(2) Documentation of operation of
corrosion protection equipment
(§ 280.31(d));
(3) Documentation of compatibility
for UST systems (§ 280.32(c));
(4) Records for all UST system
equipment installed or replaced after
[effective date of rule] (§ 280.32(c));
(5) Documentation of UST system
repairs (§ 280.33(g));
(6) Documentation of compliance for
spill and overfill prevention equipment
(§ 280.35(c));
(7) Documentation of compliance for
tanks, piping, and containment sumps
using interstitial monitoring
(§ 280.36(c));
(8) Documentation of periodic
walkthrough inspections (§ 280.37(b));
(9) Recent compliance with release
detection requirements (§ 280.45);
(10) Results of the site investigation
conducted at permanent closure
(§ 280.74); and
(11) Documentation of operator
training (§ 280.245).
(c) Availability and Maintenance of
Records. Owners and operators must
keep the records required either:
(1) At the UST site and immediately
available for inspection by the
implementing agency; or
(2) At a readily available alternative
site and be provided for inspection to
the implementing agency upon request.
(3) In the case of permanent closure
records required under § 280.74, owners
and operators are also provided with the
additional alternative of mailing closure
records to the implementing agency if
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they cannot be kept at the site or an
alternative site as indicated above.
11. Add § 280.35 to Subpart C to read
as follows:
§ 280.35 Periodic testing of spill and
overfill prevention equipment.
(a) Owners and operators of UST
systems with spill and overfill
prevention equipment must meet the
following requirements to ensure the
equipment is operating properly and
will prevent releases to the
environment:
(1) Spill prevention equipment (such
as a catchment basin, spill bucket, or
other spill containment device) must
prevent releases to the environment by
meeting one of the following:
(i) The spill prevention equipment
has two walls and the space between the
walls is monitored continuously to
ensure the integrity of the inner and
outer walls is maintained; or
(ii) The spill prevention equipment is
tested at installation and at least once
every 12 months to ensure the spill
prevention equipment is liquid tight by
using vacuum, pressure, or liquid
testing in accordance with one of the
following criteria:
(A) Requirements developed by the
manufacturer (Note: Owners and
operators may use this option only if the
manufacturer has developed testing
requirements);
(B) Code of practice developed by a
nationally recognized association or
independent testing laboratory; or
(C) Requirements determined by the
implementing agency to be no less
protective of human health and the
environment than the requirements
listed in paragraphs (a)(1)(ii)(A) and (B)
of this section; and
(2) Overfill prevention equipment
must be tested at installation and at
least once every three years. At a
minimum, testing must ensure that
overfill prevention equipment is set to
activate at the correct level specified in
§ 280.20(c) and will activate when
regulated substance reaches that level.
Testing must be conducted in
accordance with one of the criteria in
paragraph (a)(1)(ii) of this section.
(b) Owners and operators must begin
meeting these requirements as follows:
(1) For UST systems in use on or
before [Effective date of rule]:
(i) Not later than [One year after
effective date of rule] for spill
prevention equipment; and
(ii) For overfill prevention equipment,
not later than the phase-in schedule in
the following table:
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PHASE-IN SCHEDULE FOR OVERFILL PREVENTION EQUIPMENT TESTING
Date by which first test must be
conducted
Criteria
One or more USTs at the facility were installed on or before 12/22/1988 .....................................
No USTs at the facility were installed on or before 12/22/1988 and at least one UST at the facility was installed on or before 12/22/1998.
All USTs at the facility were installed after 12/22/1998 ...................................................................
(2) For UST systems brought into use
after [Effective date of rule], these
requirements apply at installation.
(c) Owners and operators must
maintain the following records (in
accordance with § 280.34) for spill and
overfill prevention equipment:
(1) All records of spill prevention
equipment testing and overfill
prevention equipment testing must be
maintained for three years; and
(2) For spill prevention equipment not
tested every 12 months, documentation
showing that the spill prevention
equipment has two walls and is
monitored continuously. Owners and
operators must maintain this
documentation for as long as the spill
prevention equipment is monitored
continuously, and for three additional
years after continuous monitoring ends.
12. Add § 280.36 to Subpart C to read
as follows:
§ 280.36 Periodic testing of secondary
containment.
(a) Owners and operators of UST
systems with secondary containment
using interstitial monitoring must
ensure the integrity of all interstitial
areas (including all containment sumps
used for interstitial monitoring).
(1) Tanks must meet one of the
following:
(i) The interstitial space is
continuously monitored; or
(ii) The interstitial space is not
continuously monitored and the
integrity of the interstitial space is
ensured at least once every three years
by using vacuum, pressure, or liquid
testing in accordance with one of the
following criteria:
(A) Requirements developed by the
manufacturer (Note: Owners and
operators may use this option only if the
manufacturer has developed integrity
testing requirements);
(B) Code of practice developed by a
nationally recognized association or
independent testing laboratory; or
(C) Requirements determined by the
implementing agency to be no less
protective of human health and the
environment than the requirements
listed in paragraphs (a)(1)(ii)(A) and (B)
of this section;
(2) Piping must meet one of the
following:
(i) The interstitial space is
continuously monitored using vacuum,
pressure, or a liquid-filled interstitial
space; or
(ii) The interstitial space is monitored
using an interstitial monitoring method
not listed in paragraph (a)(2)(i) of this
section and the integrity of the
interstitial space is ensured at least once
every three years by using vacuum,
pressure, or liquid testing in accordance
[1 year after effective date of rule].
[2 years after effective date of rule].
[3 years after effective date of rule].
with one of the criteria listed in
paragraph (a)(1)(ii) of this section; and
(3) Containment sumps must meet
one of the following:
(i) The containment sump has two
walls and the space between the walls
is continuously monitored; or
(ii) The containment sump is tested at
least every three years to ensure the
containment sump is liquid tight by
using vacuum, pressure, or liquid
testing in accordance with one of the
criteria listed in paragraph (a)(1)(ii) of
this section.
Note to paragraphs (a)(1)(ii), (a)(2)(ii), and
(a)(3)(ii): The following codes of practice may
be used to comply with paragraphs (a)(1)(ii),
(a)(2)(ii), and (a)(3)(ii) of this section:
(A) Steel Tank Institute Recommended
Practice R012, ‘‘Recommended Practice for
Interstitial Tightness Testing of Existing
Underground Double Wall Steel Tanks’’; or
(B) Fiberglass Tank and Pipe Institute
Protocol, ‘‘Field Test Protocol for Testing the
Annular Space of Installed Underground
Fiberglass Double and Triple-Wall Tanks
with Dry Annular Space’’.
(b) Owners and operators of UST
systems using interstitial monitoring
must begin meeting this requirement as
follows:
(1) For UST systems in use on or
before [Effective date of rule], not later
than the phase-in schedule in the
following table:
PHASE-IN SCHEDULE FOR INTERSTITIAL AREA TESTING
Date by which first test must be
conducted
Criteria
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
One or more USTs at the facility were installed on or before 12/22/1988 .....................................
No USTs at the facility were installed on or before 12/22/1988 and at least one UST at the facility was installed on or before 12/22/1998.
All USTs at the facility were installed after 12/22/1998 ...................................................................
(2) For UST systems brought into use
after [Effective date of rule], these
requirements apply at installation.
(c) Owners and operators must
maintain the following records (in
accordance with § 280.34) for the time
frames indicated for each tank, piping,
and containment sump that uses
interstitial monitoring:
(1) Records of interstitial space testing
must be maintained for three years; or
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(2) As appropriate, records
demonstrating: the tank is using
continuous interstitial monitoring; the
piping is using continuous interstitial
monitoring with vacuum, pressure,
liquid-filled interstitial space; and the
containment sump has two walls and
uses continuous interstitial monitoring.
Owners and operators must maintain
these records for as long as the tank,
piping, or containment sump uses one
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[1 year after effective date of rule].
[2 years after effective date of rule].
[3 years after effective date of rule].
of these continuous methods of
interstitial monitoring, and for three
additional years after continuous
monitoring ends.
13. Add § 280.37 to Subpart C to read
as follows:
§ 280.37 Periodic operation and
maintenance walkthrough inspections.
(a) To properly operate and maintain
UST systems, owners and operators
must meet one of the following:
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(1) Conduct a walkthrough inspection
at least once every 30 days that, at a
minimum and as appropriate to the
facility, checks the following equipment
as specified:
(i) Spill prevention equipment—open
and visually check for any damage;
remove any liquid or debris; check each
fill cap to make sure it is securely on the
fill pipe; and for spill prevention
equipment with continuous interstitial
monitoring, check for a leak in the
interstitial area,
(ii) Sumps—open and visually check
for any damage, leaks to the
containment area, or releases to the
environment; remove any liquid (in
contained sumps) or debris; and for
sumps with continuous interstitial
monitoring, check for a leak in the
interstitial area,
(iii) Dispenser cabinets—open and
visually check for any damage, leaks to
the containment area, or releases to the
environment; remove any liquid (in
dispensers with under-dispenser
containment) or debris; and for underdispenser containment with continuous
interstitial monitoring, check for a leak
in the interstitial area,
(iv) Monitoring/observation wells—
check covers to make sure they are
secured,
(v) Cathodic protection—check to
make sure impressed current cathodic
protection rectifiers are on and
operating; and ensure records of three
year cathodic protection testing and 60
day impressed current system
inspections are reviewed and current,
and
(vi) Release detection systems—check
to make sure the release detection
system is on and operating with no
alarms or other unusual operating
conditions present; check any devices
such as tank gauge sticks, groundwater
bailers, and hand-held vapor monitoring
devices for operability and
serviceability; and ensure records of
release detection testing are reviewed
monthly and current; or
(2) Conduct operation and
maintenance walkthrough inspections at
least once every 30 days according to a
standard code of practice developed by
a nationally recognized association or
independent testing laboratory that are
comparable to (a)(1) of this section; or
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(3) Conduct operation and
maintenance walkthrough inspections
developed by the implementing agency
that are comparable to paragraph (a)(1)
of this section.
(b) Owners and operators must
maintain records (in accordance with
§ 280.34) of operation and maintenance
walkthrough inspections for one year.
The record must include a listing of
each area checked, whether each area
checked was acceptable or needed to
have any action taken, and a description
of any actions taken to correct an issue.
Note to paragraph (a)(2): The following
code of practice may be used to comply with
paragraph (a)(2) of this section:
(A) Petroleum Equipment Institute
Recommended Practice RP 900,
‘‘Recommended Practices for the Inspection
and Maintenance of UST Systems’’.
14. Revise Subpart D to read as
follows:
Subpart D—Release Detection
Sec.
280.40 General requirements for all UST
systems.
280.41 Requirements for petroleum UST
systems.
280.42 Requirements for hazardous
substance UST systems.
280.43 Methods of release detection for
tanks.
280.44 Methods of release detection for
piping.
280.45 Release detection recordkeeping.
280.46 Alternative methods of release
detection for field-constructed tanks.
280.47 Alternative methods of release
detection for bulk piping.
Subpart D—Release Detection
§ 280.40 General requirements for all UST
systems.
(a) Owners and operators of UST
systems must provide a method, or
combination of methods, of release
detection that:
(1) Can detect a release from any
portion of the tank and the connected
underground piping that routinely
contains product;
(2) Is installed and calibrated in
accordance with the manufacturer’s
instructions;
(3) Beginning on [One year after
effective date of rule], is operated and
maintained, and electronic and
mechanical components are tested for
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proper operation, in accordance with
one of the following: Manufacturer’s
instructions; a code of practice
developed by a nationally recognized
association or independent testing
laboratory; or requirements developed
by the implementing agency. A test of
the proper operation must be performed
at least annually and, at a minimum and
as applicable to the facility, cover the
following components and criteria:
(i) Automatic tank gauge and other
controllers: Test alarm; verify system
configuration; test battery backup;
(ii) Probes and sensors: Inspect for
residual buildup, ensure floats move
freely; ensure shaft is not damaged;
ensure cables are free of kinks, bends,
and breaks; test alarm operability and
communication with controller;
(iii) Line leak detector: Test operation
to meet criteria in § 280.44(a) by
simulating a leak; inspect leak sensing
o-ring; and
(iv) Vacuum pumps and pressure
gauges: Ensure proper communication
with sensors and controller.
(4) Meets the performance
requirements in § 280.43, § 280.44,
§ 280.46, or § 280.47, as applicable, with
any performance claims and their
manner of determination described in
writing by the equipment manufacturer
or installer. In addition, the methods
listed in § 280.43(b); § 280.43(c);
§ 280.43(d); § 280.43(h);
§ 280.43(i);§ 280.44(a); § 280.44(b);
§ 280.46; and § 280.47, must be capable
of detecting the leak rate or quantity
specified for that method in the
corresponding section of the rule with a
probability of detection of 0.95 and a
probability of false alarm of 0.05.
(b) When a release detection method
operated in accordance with the
performance standards in § 280.43,
§ 280.44, § 280.46, or § 280.47 indicates
a release may have occurred, owners
and operators must notify the
implementing agency in accordance
with subpart E.
(c) Owners and operators of Airport
hydrant fuel distribution systems, UST
systems with field-constructed tanks,
and wastewater treatment tank systems
must comply with the release detection
requirements of this Subpart according
to the following table:
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SCHEDULE FOR PHASE-IN OF RELEASE DETECTION FOR AIRPORT HYDRANT FUEL DISTRIBUTION SYSTEMS, UST SYSTEMS
WITH FIELD-CONSTRUCTED TANKS, AND WASTEWATER TREATMENT TANK SYSTEMS
Type of UST system
Time frame (after [effective date of rule])
Description of requirement
Bulk piping associated with airport hydrant fuel
distribution systems and field-constructed
tanks using § 280.47(a) for piping release detection.
Within three years ............................................
Between years three and six ...........................
Conduct one bulk piping tightness test according to § 280.47(a) using the maximum
detectable leak rates for semiannual testing. For bulk piping segments not capable
of meeting the up to 3.0 gallon per hour
leak rate, owners and operators may use a
leak rate of up to 6.0 gallons per hour.
Between years six and seven ..........................
Conduct one bulk piping tightness test according to § 280.47(a) using the maximum
detectable leak rates for semiannual testing.
After year seven ...............................................
Conduct bulk piping tightness testing according to § 280.47(a).
Bulk piping associated with airport hydrant fuel
distribution systems and field-constructed
tanks not using § 280.47(a) for piping release
detection.
Within three years ............................................
Perform release detection according to this
subpart.
Underground tanks associated with hydrant fuel
distribution systems and field-constructed
tanks.
Within three years ............................................
Perform release detection according to this
subpart.
Wastewater treatment tank systems ..................
Within three years ............................................
Perform release detection according to this
subpart.
manual tank gauging (conducted in
accordance with § 280.43(b));
(iii) Field-constructed tanks greater
than 50,000 gallons may use the
alternative release detection
requirements in § 280.46; and
(iv) Tanks using § 280.43(e) or
§ 280.43(f) to monitor for releases, must
begin using one of the methods listed in
§ 280.43(d), (g), (h), or (i) not later than
[Five years after effective date of rule].
(2) Tanks installed after [effective date
of rule] must be monitored for releases
at least every 30 days in accordance
with § 280.43(g).
(b) Piping. Underground piping that
routinely contains regulated substances
must be monitored for releases in a
manner that meets one of the following
requirements:
(1) Piping installed on or before
[effective date of rule] must meet one of
the following:
(i) Pressurized piping. Underground
piping that conveys regulated
substances under pressure must:
(A) Be equipped with an automatic
line leak detector conducted in
accordance with § 280.44(a); and
(B) Have an annual line tightness test
conducted in accordance with
§ 280.44(b) or have monthly monitoring
conducted in accordance with
§ 280.44(c).
(ii) Suction piping. Underground
piping that conveys regulated
substances under suction must either
have a line tightness test conducted at
least every 3 years and in accordance
with § 280.44(b), or use a monthly
monitoring method conducted in
accordance with § 280.44(c). No release
detection is required for suction piping
that is designed and constructed to meet
the following standards:
(A) The below-grade piping operates
at less than atmospheric pressure;
(B) The below-grade piping is sloped
so that the contents of the pipe will
drain back into the storage tank if the
suction is released;
(C) Only one check valve is included
in each suction line;
(D) The check valve is located directly
below and as close as practical to the
suction pump; and
(E) A method is provided that allows
compliance with paragraphs (b)(2)(ii)–
(iv) of this section to be readily
determined.
(iii) Bulk piping. Underground piping
associated with airport hydrant fuel
distribution systems and fieldconstructed tanks must meet one of the
following release detection
requirements:
(A) The requirements in paragraphs
(b)(1)(i) or (ii) of this section; or
(B) The alternative release detection
requirements in § 280.47.
(2) Piping installed or replaced after
[effective date of rule] must meet one of
the following:
(i) Pressurized piping must be
monitored for releases at least every 30
(d) Any UST system that cannot apply
a method of release detection that
complies with the requirements of this
subpart must complete the closure
procedures in subpart G. For previously
deferred UST systems described in
subpart A, this requirement applies after
the effective date for subpart D
described in § 280.10(a)(1).
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
§ 280.41 Requirements for petroleum UST
systems.
Owners and operators of petroleum
UST systems must provide release
detection for tanks and piping as
follows:
(a) Tanks. Tanks must be monitored
for releases as follows:
(1) Tanks installed on or before
[effective date of rule] must be
monitored for releases at least every 30
days using one of the methods listed in
§ 280.43(d) through (i) except that:
(i) UST systems that meet the
performance standards in § 280.20 or
§ 280.21, and the monthly inventory
control requirements in § 280.43(a) or
(b), may use tank tightness testing
(conducted in accordance with
§ 280.43(c)) at least every 5 years until
10 years after the tank was installed or
upgraded under § 280.21(b), whichever
is later;
(ii) Tanks with capacity of 550 gallons
or less and tanks with a capacity of 551
to 1,000 gallons that meet the tank
diameter criteria in § 280.43(b) may use
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days in accordance with § 280.43(g) and
be equipped with an automatic line leak
detector in accordance with § 280.44(a).
(ii) Suction piping must be monitored
for releases at least every 30 days in
accordance with § 280.43(g). No release
detection is required for suction piping
that meets paragraphs (b)(1)(ii)(A)
through (E) of this section.
(iii) Underground bulk piping
associated with airport hydrant fuel
distribution systems and fieldconstructed tanks must meet the
requirements in paragraph (b)(1) of this
section.
§ 280.42 Requirements for hazardous
substance UST systems.
Owners and operators of hazardous
substance UST systems must provide
containment that meets the following
requirements and monitor these systems
using § 280.43(g) at least every 30 days:
(a) Secondary containment systems
must be designed, constructed and
installed to:
(1) Contain regulated substances
leaked from the primary containment
until they are detected and removed;
(2) Prevent the release of regulated
substances to the environment at any
time during the operational life of the
UST system; and
(3) Be checked for evidence of a
release at least every 30 days.
Note to paragraph (a): The provisions of 40
CFR 265.193, Containment and Detection of
Releases, may be used to comply with these
requirements for tanks installed on or before
[effective date of rule].
(b) Double-walled tanks must be
designed, constructed, and installed to:
(1) Contain a release from any portion
of the inner tank within the outer wall;
and
(2) Detect the failure of the inner wall.
(c) External liners (including vaults)
must be designed, constructed, and
installed to:
(1) Contain 100 percent of the
capacity of the largest tank within its
boundary;
(2) Prevent the interference of
precipitation or ground-water intrusion
with the ability to contain or detect a
release of regulated substances; and
(3) Surround the tank completely (i.e.,
it is capable of preventing lateral as well
as vertical migration of regulated
substances).
(d) Underground piping must be
equipped with secondary containment
that satisfies the requirements of this
section (e.g., trench liners, doublewalled pipe). In addition, underground
piping that conveys regulated
substances under pressure must be
equipped with an automatic line leak
detector in accordance with § 280.44(a).
(e) For hazardous substance UST
systems installed on or before [Effective
date of rule] other methods of release
detection may be used if owners and
operators:
(1) Demonstrate to the implementing
agency that an alternate method can
detect a release of the stored substance
as effectively as any of the methods
allowed in §§ 280.43(b) through (i) can
detect a release of petroleum;
(2) Provide information to the
implementing agency on effective
corrective action technologies, health
risks, and chemical and physical
properties of the stored substance, and
the characteristics of the UST site; and,
(3) Obtain approval from the
implementing agency to use the
alternate release detection method
before the installation and operation of
the new UST system.
§ 280.43
tanks.
Each method of release detection for
tanks used to meet the requirements of
§ 280.41, except field-constructed tanks
installed on or before [Effective date of
rule] with capacities greater than 50,000
gallons that meet § 280.46, must be
conducted in accordance with the
following:
(a) Inventory control. Product
inventory control (or another test of
equivalent performance) must be
conducted monthly to detect a release of
at least 1.0 percent of flow-through plus
130 gallons on a monthly basis in the
following manner:
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
Nominal tank capacity
Minimum duration of test
550 gallons or less ....................................................
551–1,000 gallons (when tank diameter is 64’’) .......
551–1,000 gallons (when tank diameter is 48’’) .......
551–1,000 gallons (also requires periodic tank tightness testing).
1,001–2,000 gallons (also requires periodic tank
tightness testing).
(5) Tanks of 550 gallons or less
nominal capacity and tanks with a
VerDate Mar<15>2010
22:10 Nov 17, 2011
Jkt 226001
Methods of release detection for
36
44
58
36
hours
hours
hours
hours
Note to paragraph (a): Practices described
in the American Petroleum Institute
Recommended Practice RP 1621, ‘‘Bulk
Liquid Stock Control at Retail Outlets’’ may
be used, where applicable, as guidance in
meeting the requirements of this paragraph.
(b) Manual tank gauging. Manual tank
gauging must meet the following
requirements:
(1) Tank liquid level measurements
are taken at the beginning and ending of
a period of at least 36 hours during
which no liquid is added to or removed
from the tank;
(2) Level measurements are based on
an average of two consecutive stick
readings at both the beginning and
ending of the period;
(3) The equipment used is capable of
measuring the level of product over the
full range of the tank’s height to the
nearest one-eighth of an inch;
(4) A release is suspected and subject
to the requirements of subpart E if the
variation between beginning and ending
measurements exceeds the weekly or
monthly standards in the following
table:
Weekly standard
(one test)
Monthly standard
(four test average)
..........................
..........................
..........................
..........................
10 gallons ........................
9 gallons ..........................
12 gallons ........................
13 gallons ........................
5
4
6
7
36 hours ..........................
26 gallons ........................
13 gallons.
nominal capacity of 551 to 1,000 gallons
that meet the tank diameter criteria in
PO 00000
(1) Inventory volume measurements
for regulated substance inputs,
withdrawals, and the amount still
remaining in the tank are recorded each
operating day;
(2) The equipment used is capable of
measuring the level of product over the
full range of the tank’s height to the
nearest one-eighth of an inch;
(3) The regulated substance inputs are
reconciled with delivery receipts by
measurement of the tank inventory
volume before and after delivery;
(4) Deliveries are made through a drop
tube that extends to within one foot of
the tank bottom;
(5) Product dispensing is metered and
recorded within the local standards for
meter calibration or an accuracy of 6
cubic inches for every 5 gallons of
product withdrawn; and
(6) The measurement of any water
level in the bottom of the tank is made
to the nearest one-eighth of an inch at
least once a month.
Frm 00066
Fmt 4701
Sfmt 4702
gallons.
gallons.
gallons.
gallons.
the table in paragraph (b)(4) of this
section may use this as the sole method
E:\FR\FM\18NOP2.SGM
18NOP2
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Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
of release detection. All other tanks with
a nominal capacity of 551 to 2,000
gallons may use the method in place of
inventory control in § 280.43(a). Tanks
of greater than 2,000 gallons nominal
capacity may not use this method to
meet the requirements of this Subpart.
(c) Tank tightness testing. Tank
tightness testing (or another test of
equivalent performance) must be
capable of detecting a 0.1 gallon per
hour leak rate from any portion of the
tank that routinely contains product
while accounting for the effects of
thermal expansion or contraction of the
product, vapor pockets, tank
deformation, evaporation or
condensation, and the location of the
water table.
(d) Automatic tank gauging.
Equipment for automatic tank gauging
that tests for the loss of product and
conducts inventory control must meet
the following requirements:
(1) The automatic product level
monitor test can detect a 0.2 gallon per
hour leak rate from any portion of the
tank that routinely contains product;
and
(2) The test must be performed with
the system operating in one of the
following modes:
(i) In-tank static testing conducted on
a periodic basis; or
(ii) Continuous in-tank leak detection
operating on an uninterrupted basis or
operating within a process that allows
the system to gather incremental
measurements to determine the leak
status of the tank at least once every 30
days.
(e) Vapor monitoring. Testing or
monitoring for vapors within the soil
gas of the excavation zone must meet
the following requirements:
(1) The materials used as backfill are
sufficiently porous (e.g., gravel, sand,
crushed rock) to readily allow diffusion
of vapors from releases into the
excavation area;
(2) The stored regulated substance, or
a tracer compound placed in the tank
system, is sufficiently volatile (e.g.,
gasoline) to result in a vapor level that
is detectable by the monitoring devices
located in the excavation zone in the
event of a release from the tank;
(3) The measurement of vapors by the
monitoring device is not rendered
inoperative by the ground water,
rainfall, or soil moisture or other known
interferences so that a release could go
undetected for more than 30 days;
(4) The level of background
contamination in the excavation zone
will not interfere with the method used
to detect releases from the tank;
(5) The vapor monitors are designed
and operated to detect any significant
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Jkt 226001
increase in concentration above
background of the regulated substance
stored in the tank system, a component
or components of that substance, or a
tracer compound placed in the tank
system;
(6) In the UST excavation zone, the
site is assessed to ensure compliance
with the requirements in paragraphs
(e)(1) through (4) of this section and to
establish the number and positioning of
monitoring wells that will detect
releases within the excavation zone
from any portion of the tank that
routinely contains product; and
(7) Monitoring wells are clearly
marked and secured to avoid
unauthorized access and tampering.
(f) Ground-water monitoring. Testing
or monitoring for liquids on the ground
water must meet the following
requirements:
(1) The regulated substance stored is
immiscible in water and has a specific
gravity of less than one;
(2) Ground water is never more than
20 feet from the ground surface and the
hydraulic conductivity of the soil(s)
between the UST system and the
monitoring wells or devices is not less
than 0.01 cm/sec (e.g., the soil should
consist of gravels, coarse to medium
sands, coarse silts or other permeable
materials);
(3) The slotted portion of the
monitoring well casing must be
designed to prevent migration of natural
soils or filter pack into the well and to
allow entry of regulated substance on
the water table into the well under both
high and low ground-water conditions;
(4) Monitoring wells shall be sealed
from the ground surface to the top of the
filter pack;
(5) Monitoring wells or devices
intercept the excavation zone or are as
close to it as is technically feasible;
(6) The continuous monitoring
devices or manual methods used can
detect the presence of at least one-eighth
of an inch of free product on top of the
ground water in the monitoring wells;
(7) Within and immediately below the
UST system excavation zone, the site is
assessed to ensure compliance with the
requirements in paragraphs (f)(1)
through (5) of this section and to
establish the number and positioning of
monitoring wells or devices that will
detect releases from any portion of the
tank that routinely contains product;
and
(8) Monitoring wells are clearly
marked and secured to avoid
unauthorized access and tampering.
(g) Interstitial monitoring. Interstitial
monitoring between the UST system
and a secondary barrier immediately
around or beneath it may be used, but
PO 00000
Frm 00067
Fmt 4701
Sfmt 4702
71773
only if the system is designed,
constructed and installed to detect a
leak from any portion of the tank that
routinely contains product and also
meets one of the following
requirements:
(1) For double-walled UST systems,
the sampling or testing method can
detect a release through the inner wall
in any portion of the tank that routinely
contains product;
(2) For UST systems with a secondary
barrier within the excavation zone, the
sampling or testing method used can
detect a release between the UST system
and the secondary barrier;
(i) The secondary barrier around or
beneath the UST system consists of
artificially constructed material that is
sufficiently thick and impermeable (at
least 10¥6 cm/sec for the regulated
substance stored) to direct a release to
the monitoring point and permit its
detection;
(ii) The barrier is compatible with the
regulated substance stored so that a
release from the UST system will not
cause a deterioration of the barrier
allowing a release to pass through
undetected;
(iii) For cathodically protected tanks,
the secondary barrier must be installed
so that it does not interfere with the
proper operation of the cathodic
protection system;
(iv) The ground water, soil moisture,
or rainfall will not render the testing or
sampling method used inoperative so
that a release could go undetected for
more than 30 days;
(v) The site is assessed to ensure that
the secondary barrier is always above
the ground water and not in a 25-year
flood plain, unless the barrier and
monitoring designs are for use under
such conditions; and,
(vi) Monitoring wells are clearly
marked and secured to avoid
unauthorized access and tampering.
(3) For tanks with an internally fitted
liner, an automated device can detect a
release between the inner wall of the
tank and the liner, and the liner is
compatible with the substance stored.
(4) For UST systems using continuous
vacuum, pressure, or liquid-filled
methods of interstitial monitoring, the
method must be capable of detecting a
breach in both the inner and outer walls
of the tank and/or piping.
(h) Statistical inventory
reconciliation. Statistically based testing
or monitoring methods must meet the
following requirements:
(1) Report a quantitative result with a
calculated leak rate;
(2) Be capable of detecting a leak rate
of 0.2 gallon per hour; and
E:\FR\FM\18NOP2.SGM
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Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
(3) Use a threshold that does not
exceed one-half the minimum detectible
leak rate.
(i) Other methods. Any other type of
release detection method, or
combination of methods, can be used if:
(1) It can detect a 0.2 gallon per hour
leak rate or a release of 150 gallons
within a month with a probability of
detection of 0.95 and a probability of
false alarm of 0.05; or
(2) The implementing agency may
approve another method if the owner
and operator can demonstrate that the
method can detect a release as
effectively as any of the methods
allowed in paragraphs (c) through (h) of
this section. In comparing methods, the
implementing agency shall consider the
size of release that the method can
detect and the frequency and reliability
with which it can be detected. If the
method is approved, the owner and
operator must comply with any
conditions imposed by the
implementing agency on its use to
ensure the protection of human health
and the environment.
§ 280.44
piping.
Methods of release detection for
Each method of release detection for
piping used to meet the requirements of
§ 280.41, except bulk piping that meets
§ 280.47, must be conducted in
accordance with the following:
(a) Automatic line leak detectors.
Methods which alert the operator to the
presence of a leak by restricting or
shutting off the flow of regulated
substances through piping or triggering
an audible or visual alarm may be used
only if they detect leaks of 3 gallons per
hour at 10 pounds per square inch line
pressure within 1 hour. An annual test
of the operation of the leak detector
must be conducted in accordance with
§ 280.40(a)(3).
(b) Line tightness testing. A periodic
test of piping may be conducted only if
it can detect a 0.1 gallon per hour leak
rate at one and one-half times the
operating pressure.
(c) Applicable tank methods. Except
as described in § 280.41(a), any of the
methods in § 280.43(e) through (i) may
be used if they are designed to detect a
release from any portion of the
underground piping that routinely
contains regulated substances.
§ 280.45
Release detection recordkeeping.
All UST system owners and operators
must maintain records in accordance
with § 280.34 demonstrating compliance
with all applicable requirements of this
subpart. These records must include the
following:
(a) All written performance claims
pertaining to any release detection
system used, and the manner in which
these claims have been justified or
tested by the equipment manufacturer
or installer, must be maintained for 5
years, or for another reasonable period
of time determined by the implementing
agency, from the date of installation;
(b) The results of any sampling,
testing, or monitoring must be
maintained for at least 1 year, or for
another reasonable period of time
determined by the implementing
agency, except as follows:
(1) The results of annual operation
tests conducted in accordance with
§ 280.40(a)(3) must be maintained for
three years. At a minimum, the results
must list each component tested,
indicate whether each component tested
meets criteria in § 280.40(a)(3) or needs
to have action taken, and describe any
action taken to correct an issue; and
(2) The results of tank tightness
testing or bulk tank tightness testing
conducted in accordance with
§ 280.43(c) or § 280.46 must be retained
until the next test is conducted; and
(c) Written documentation of all
calibration, maintenance, and repair of
release detection equipment
permanently located on-site must be
maintained for at least one year after the
servicing work is completed, or for
another reasonable time period
determined by the implementing
agency. Any schedules of required
calibration and maintenance provided
by the release detection equipment
manufacturer must be retained for 5
years from the date of installation.
§ 280.46 Alternative methods of release
detection for field-constructed tanks.
Owners and operators of fieldconstructed tanks with a capacity
greater than 50,000 gallons may use one
or a combination of the following
alternative methods of release detection:
(a) Conduct an annual bulk tank
tightness test that can detect a 0.5 gallon
per hour leak rate;
(b) Use an automatic tank gauging
system to perform release detection at
least every 30 days that can detect a leak
rate less than or equal to one gallon per
hour. This method must be combined
with a bulk tank tightness test that can
detect a 0.2 gallon per hour leak rate
performed at least every three years;
(c) Use an automatic tank gauging
system to perform release detection at
least every 30 days that can detect a leak
rate less than or equal to two gallons per
hour. This method must be combined
with a bulk tank tightness test that can
detect a 0.2 gallon per hour leak rate
performed at least every two years; or
(d) Another method approved by the
implementing agency if the owner and
operator can demonstrate that the
method can detect a release as
effectively as any of the methods
allowed in paragraphs (a) through (c) of
this section. In comparing methods, the
implementing agency shall consider the
size of release that the method can
detect and the frequency and reliability
of detection. If the method is approved,
the owner and operator must comply
with any conditions imposed by the
implementing agency on its use.
§ 280.47 Alternative methods of release
detection for bulk piping.
Owners and operators of underground
piping associated with airport hydrant
fuel distribution systems and fieldconstructed tanks may use one or a
combination of the following alternative
methods of release detection:
(a) Perform a semiannual or annual
bulk line tightness test at or above
operating pressure in accordance with
the table below. Bulk piping segments
≥100,000 gallons not capable of meeting
the maximum 3.0 gallon per hour leak
rate for the semiannual test may be
tested at a leak rate up to 6.0 gallons per
hour according to the schedule in
§ 280.40(c):
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
MAXIMUM DETECTABLE LEAK RATE PER TEST SECTION VOLUME
Test section volume
(gallons)
Semiannual test
maximum detectable leak rate
(gallons per hour)
<50,000 ......................................................................................................................................................
≥50,000 to <75,000 ...................................................................................................................................
≥75,000 to <100,000 .................................................................................................................................
≥100,000 ....................................................................................................................................................
1.0
1.5
2.0
3.0
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PO 00000
Frm 00068
Fmt 4701
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E:\FR\FM\18NOP2.SGM
18NOP2
Annual test
maximum detectable leak rate
(gallons per hour)
0.5
0.75
1.0
1.5
Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
(b) Perform continuous interstitial
monitoring designed to detect a release
from any portion of the underground
piping that routinely contains product
in accordance with § 280.43(g);
(c) Use an automatic line leak detector
that alerts the operator to the presence
of a leak by restricting or shutting off
flow of regulated substances through
piping or triggering an audible or visual
alarm. This method may be used only if
it can detect a leak of three gallons per
hour at 10 pounds per square inch line
pressure within one hour or equivalent.
When using this method, the following
must also be met:
(1) Perform interstitial monitoring,
designed to detect a release from any
portion of the underground piping that
routinely contains product, in
accordance with § 280.43(g) at least
every three months; and
(2) Conduct an annual test of the
operation of the leak detector in
accordance with § 280.40(a)(3); or
(d) Another method approved by the
implementing agency if the owner and
operator can demonstrate that the
method can detect a release as
effectively as any of the methods
allowed in paragraphs (a) through (c) of
this section. In comparing methods, the
implementing agency shall consider the
size of release that the method can
detect and the frequency and reliability
of detection. If the method is approved,
the owner and operator must comply
with any conditions imposed by the
implementing agency on its use.
15. In § 280.50 revise paragraphs (b)
and (c) to read as follows:
§ 280.50
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
16. In § 280.52 revise paragraph (a) to
read as follows:
guidance for conducting safe closure
procedures at some hazardous substance
tanks.]
§ 280.52 Release investigation and
confirmation steps.
*
*
*
*
*
*
(a) System test. Owners and operators
must conduct tests (according to the
requirements for tightness testing in
§ 280.43(c) and § 280.44(b) or, for UST
systems with secondary containment
and interstitial monitoring, the integrity
testing specified in § 280.36) that
determine whether a leak exists in that
portion of the tank that routinely
contains product, the attached delivery
piping, or a breach of the interstitial
space.
(1) If the system test confirms a leak,
owners and operators must repair,
replace, upgrade, or close the UST
system. In addition, owners and
operators must begin corrective action
in accordance with subpart F if the test
results for the system, tank, or delivery
piping indicate that a release exists.
(2) Further investigation is not
required if the test results for the
system, tank, and delivery piping do not
indicate that a release exists and if
environmental contamination is not the
basis for suspecting a release.
(3) Owners and operators must
conduct a site check as described in
paragraph (b) of this section if the test
results for the system, tank, and delivery
piping do not indicate that a release
exists but environmental contamination
is the basis for suspecting a release.
*
*
*
*
*
17. In § 280.71 revise the Note at the
end of the section to read as follows:
Reporting of suspected releases.
*
*
*
*
*
(b) Unusual operating conditions
observed by owners and operators (such
as the erratic behavior of product
dispensing equipment, the sudden loss
of product from the UST system, an
unexplained presence of water in the
tank, or water or product in the
interstitial space of secondarily
contained systems), unless system
equipment is found to be defective but
not leaking, and is immediately repaired
or replaced.
(c) Monitoring results, including
alarms, from a release detection method
required under § 280.41 and § 280.42
that indicate a release may have
occurred unless:
(1) The monitoring device is found to
be defective, and is immediately
repaired, recalibrated or replaced, and
additional monitoring does not confirm
the initial result; or
(2) In the case of inventory control, a
second month of data does not confirm
the initial result.
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71775
§ 280.71 Permanent closure and changesin-service.
*
*
*
*
*
[Note: The following cleaning and closure
procedures may be used to comply with this
section:
(A) American Petroleum Institute
Recommended Practice RP 1604, ‘‘Closure of
Underground Petroleum Storage Tanks’’;
(B) American Petroleum Institute Standard
2015, ‘‘Requirements for Safe Entry and
Cleaning of Petroleum Storage Tanks’’;
(C) American Petroleum Institute
Recommended Practice 2016, ‘‘Guidelines
and Procedures for Entering and Cleaning
Petroleum Storage Tanks’’;
(D) American Petroleum Institute
Recommended Practice RP 1631, ‘‘Interior
Lining and Periodic Inspection of
Underground Storage Tanks,’’ may be used as
guidance for compliance with this section;
(E) National Fire Protection Association
Standard 326, ‘‘Safeguarding of Tanks and
Containers for Entry, Cleaning, or Repair’’;
and
(F) The National Institute for Occupational
Safety and Health Publication 80–106,
‘‘Criteria for a Recommended Standard * * *
Working in Confined Space’’ may be used as
PO 00000
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*
*
*
*
18. Revise § 280.90 to read as follows:
§ 280.90
Applicability.
(a) This subpart applies to owners and
operators of all petroleum underground
storage tank (UST) systems except as
otherwise provided in this section.
(b) Owners and operators of
petroleum UST systems are subject to
these requirements in accordance with
§ 280.91.
(c) State and Federal government
entities whose debts and liabilities are
the debts and liabilities of a state or the
United States are exempt from the
requirements of this subpart.
(d) The requirements of this subpart
do not apply to owners and operators of
any UST system described in § 280.10
(b), (c)(2) or (c)(3).
(e) If the owner and operator of a
petroleum underground storage tank are
separate persons, only one person is
required to demonstrate financial
responsibility; however, both parties are
liable in event of noncompliance.
19. Revise § 280.91 to read as follows:
§ 280.91
Compliance dates.
Owners of petroleum underground
storage tanks must comply with the
requirements of this subpart. Previously
deferred UST systems must comply
with the requirements of this subpart
according to the schedule in § 280.10.
20. In § 280.92 revise the definitions
‘‘Accidental release,’’ ‘‘Financial
reporting year,’’ and ‘‘Provider of
financial assurance’’ to read as follows:
§ 280.92
Definition of terms.
*
*
*
*
*
Accidental release means any sudden
or nonsudden release of petroleum
arising from operating an underground
storage tank that results in a need for
corrective action and/or compensation
for bodily injury or property damage
neither expected nor intended by the
tank owner or operator.
*
*
*
*
*
Financial reporting year means the
latest consecutive twelve-month period
for which any of the following reports
used to support a financial test is
prepared:
(1) a 10–K report submitted to the
SEC;
(2) an annual report of tangible net
worth submitted to Dun and Bradstreet;
or
(3) annual reports submitted to the
Energy Information Administration or
the Rural Utilities Service.
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‘‘Financial reporting year’’ may thus
comprise a fiscal or a calendar year
period.
*
*
*
*
*
Provider of financial assurance means
an entity that provides financial
assurance to an owner or operator of an
underground storage tank through one
of the mechanisms listed in §§ 280.95–
280.107, including a guarantor, insurer,
risk retention group, surety, issuer of a
letter of credit, issuer of a state-required
mechanism, or a state.
*
*
*
*
*
21. Revise § 280.94 paragraph (a)(1) to
read as follows:
§ 280.94 Allowable mechanisms and
combinations of mechanisms.
(a) * * *
(1) An owner or operator, including a
local government owner or operator,
may use any one or combination of the
mechanisms listed in §§ 280.95 through
280.107 to demonstrate financial
responsibility under this subpart for one
or more underground storage tanks; and
*
*
*
*
*
22. In § 280.95 revise paragraph
s(b)(1)(ii), (b)(4)(i), (c)(5) introductory
text, (c)(5)(i) and (d) to read as follows:
§ 280.95
Financial test of self-insurance.
*
*
*
*
*
(b) * * *
(1) * * *
(ii) The sum of the corrective action
cost estimates, the current closure and
post-closure care cost estimates, and
amount of liability coverage for which a
financial test is used to demonstrate
financial responsibility to EPA under 40
CFR 264.101, 264.143, 264.145, 265.143,
265.145, 264.147, and 265.147 or to a
state implementing agency under a state
program authorized by EPA under 40
CFR part 271; and
(4) * * *
(i) File financial statements annually
with the U.S. Securities and Exchange
Commission, the Energy Information
Administration, or the Rural Utilities
Service; or
*
*
*
*
*
(c) * * *
(5) If the financial statements of the
owner or operator, and/or guarantor, are
not submitted annually to the U.S.
Securities and Exchange Commission,
the Energy Information Administration
or the Rural Utilities Service, the owner
or operator, and/or guarantor, must
obtain a special report by an
independent certified public accountant
stating that:
(i) He has compared the data that the
letter from the chief financial officer
specifies as having been derived from
the latest year-end financial statements
of the owner or operator, and/or
guarantor, with the amounts in such
financial statements; and
*
*
*
*
*
(d) To demonstrate that it meets the
financial test under paragraph (b) or (c)
of this section, the chief financial officer
of the owner or operator, or guarantor,
must sign, within 120 days of the close
of each financial reporting year, as
defined by the twelve-month period for
which financial statements used to
support the financial test are prepared,
a letter worded exactly as follows,
except that the instructions in brackets
are to be replaced by the relevant
information and the brackets deleted:
Letter from Chief Financial Officer
I am the chief financial officer of [insert:
name and address of the owner or operator,
or guarantor]. This letter is in support of the
use of [insert: ‘‘the financial test of selfinsurance,’’ and/or ‘‘guarantee’’] to
demonstrate financial responsibility for
[insert: ‘‘taking corrective action’’ and/or
‘‘compensating third parties for bodily injury
and property damage’’] caused by [insert:
‘‘sudden accidental releases’’ or ‘‘nonsudden
accidental releases’’ or ‘‘accidental releases’’]
in the amount of at least [insert: dollar
amount] per occurrence and [insert: dollar
amount] annual aggregate arising from
operating (an) underground storage tank(s).
Underground storage tanks at the following
facilities are assured by this financial test or
a financial test under an authorized State
program by this [insert: ‘‘owner or operator,’’
and/or ‘‘guarantor’’]: [List for each facility:
the name and address of the facility where
tanks assured by this financial test are
located, and whether tanks are assured by
this financial test or a financial test under a
State program approved under 40 CFR part
281. If separate mechanisms or combinations
of mechanisms are being used to assure any
of the tanks at this facility, list each tank
assured by this financial test or a financial
test under a State program authorized under
40 CFR part 281 by the tank identification
number provided in the notification
submitted pursuant to 40 CFR 280.22 or the
corresponding State requirements.]
A [insert: ‘‘financial test,’’ and/or
‘‘guarantee’’] is also used by this [insert:
‘‘owner or operator,’’ or ‘‘guarantor’’] to
demonstrate evidence of financial
responsibility in the following amounts
under other EPA regulations or state
programs authorized by EPA under 40 CFR
parts 271 and 145:
EPA Regulations
Amount
Closure (§§ 264.143 and 265.143)
Post-Closure Care (§§ 264.145 and
265.145).
Liability Coverage (§§ 264.147 and
265.147).
Corrective Action (§§ 264.101(b)) ..
Plugging
and
Abandonment
(§ 144.63).
Closure ...........................................
Post-Closure Care ..........................
Liability Coverage ...........................
Corrective Action ............................
Plugging and Abandonment ...........
$lll
$lll
Total ........................................
$lll
$lll
$lll
$lll
$lll
$lll
$lll
$lll
$lll
This [insert: ‘‘owner or operator,’’ or
‘‘guarantor’’] has not received an adverse
opinion, a disclaimer of opinion, or a ‘‘going
concern’’ qualification from an independent
auditor on his financial statements for the
latest completed fiscal year.
[Fill in the information for Alternative I if
the criteria of paragraph (b) of § 280.95 are
being used to demonstrate compliance with
the financial test requirements. Fill in the
information for Alternative II if the criteria of
paragraph (c) of § 280.95 are being used to
demonstrate compliance with the financial
test requirements.]
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Alternative I
1. Amount of annual UST aggregate coverage being assured by a financial test, and/or guarantee .........................................................
2. Amount of corrective action, closure and post-closure care costs, liability coverage, and plugging and abandonment costs covered
by a financial test, and/or guarantee.
3. Sum of lines 1 and 2 .................................................................................................................................................................................
4. Total tangible assets .................................................................................................................................................................................
5. Total liabilities [if any of the amount reported on line 3 is included in total liabilities, you may deduct that amount from this line and
add that amount to line 6].
6. Tangible net worth [subtract line 5 from line 4] ........................................................................................................................................
$lll
$lll
$lll
$lll
$lll
$lll
Yes / No
7. Is line 6 at least $10 million? ....................................................................................................................................................................
8. Is line 6 at least 10 times line 3? ..............................................................................................................................................................
9. Have financial statements for the latest fiscal year been filed with the Securities and Exchange Commission?
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10. Have financial statements for the latest fiscal year been filed with the Energy Information Administration?
11. Have financial statements for the latest fiscal year been filed with the Rural Utilities Service?
12. Has financial information been provided to Dun and Bradstreet, and has Dun and Bradstreet provided a financial strength rating of
4A or 5A? [Answer ‘‘Yes’’ only if both criteria have been met.]
71777
lll
lll
lll
Alternative II
1. Amount of annual UST aggregate coverage being assured by a test, and/or guarantee .......................................................................
2. Amount of corrective action, closure and post-closure care costs, liability coverage, and plugging and abandonment costs covered
by a financial test, and/or guarantee.
3. Sum of lines 1 and 2 .................................................................................................................................................................................
4. Total tangible assets .................................................................................................................................................................................
5. Total liabilities [if any of the amount reported on line 3 is included in total liabilities, you may deduct that amount from this line and
add that amount to line 6].
6. Tangible net worth [subtract line 5 from line 4] ........................................................................................................................................
7. Total assets in the U.S. [required only if less than 90 percent of assets are located in the U.S.]
$lll
$lll
$lll
$lll
$lll
$lll
$lll
Yes / No
8. Is line 6 at least $10 million? ....................................................................................................................................................................
9. Is line 6 at least 6 times line 3? ................................................................................................................................................................
10. Are at least 90 percent of assets located in the U.S.? [If ‘‘No,’’ complete line 11.] ..............................................................................
11. Is line 7 at least 6 times line 3? [Fill in either lines 12–15 or lines 16–18:] ...........................................................................................
12. Current assets .........................................................................................................................................................................................
13. Current liabilities ......................................................................................................................................................................................
14. Net working capital [subtract line 13 from line 12] .................................................................................................................................
15. Is line 14 at least 6 times line 3? ............................................................................................................................................................
16. Current bond rating of most recent bond issue ......................................................................................................................................
17. Name of rating service ............................................................................................................................................................................
18. Date of maturity of bond .........................................................................................................................................................................
19. Have financial statements for the latest fiscal year been filed with the SEC, the Energy Information Administration, or the Rural
Utilities Service?
[If ‘‘No,’’ please attach a report from an
independent certified public accountant
certifying that there are no material
differences between the data as reported in
lines 4–18 above and the financial statements
for the latest fiscal year.]
[For both Alternative I and Alternative II
complete the certification with this
statement.]
I hereby certify that the wording of this
letter is identical to the wording specified in
40 CFR part 280.95(d) as such regulations
were constituted on the date shown
immediately below.
[Signature]
[Name]
[Title]
[Date]
*
*
*
*
*
23. In § 280.96 revise paragraphs (b),
(c)(3), and (d) to read as follows:
§ 280.96
Guarantee.
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
*
*
*
*
*
(b) Within 120 days of the close of
each financial reporting year the
guarantor must demonstrate that it
meets the financial test criteria of
§ 280.95 based on year-end financial
statements for the latest completed
financial reporting year by completing
the letter from the chief financial officer
described in § 280.95(d) and must
deliver the letter to the owner or
operator. If the guarantor fails to meet
the requirements of the financial test at
the end of any financial reporting year,
within 120 days of the end of that
financial reporting year the guarantor
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22:10 Nov 17, 2011
Jkt 226001
shall send by certified mail, before
cancellation or nonrenewal of the
guarantee, notice to the owner or
operator. If the Director of the
implementing agency notifies the
guarantor that he no longer meets the
requirements of the financial test of
§ 280.95 (b) or (c) and (d), the guarantor
must notify the owner or operator
within 10 days of receiving such
notification from the Director. In both
cases, the guarantee will terminate no
less than 120 days after the date the
owner or operator receives the
notification, as evidenced by the return
receipt. The owner or operator must
obtain alternative coverage as specified
in § 280.114(e).
(c) * * *
(3) [Insert appropriate phrase: ‘‘On
behalf of our subsidiary’’ (if guarantor is
corporate parent of the owner or
operator); ‘‘On behalf of our affiliate’’ (if
guarantor is a related firm of the owner
or operator); or ‘‘Incident to our
business relationship with’’ (if guarantor
is providing the guarantee as an
incident to a substantial business
relationship with owner or operator)]
[owner or operator], guarantor
guarantees to [implementing agency]
and to any and all third parties that:
In the event that [owner or operator]
fails to provide alternative coverage
within 60 days after receipt of a notice
of cancellation of this guarantee and the
[Director of the implementing agency]
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lll
lll
lll
lll
$lll
$lll
$lll
lll
lll
lll
lll
lll
has determined or suspects that a
release has occurred at an underground
storage tank covered by this guarantee,
the guarantor, upon instructions from
the [Director], shall fund a standby trust
fund in accordance with the provisions
of 40 CFR 280.112, in an amount not to
exceed the coverage limits specified
above.
In the event that the [Director]
determines that [owner or operator] has
failed to perform corrective action for
releases arising out of the operation of
the above-identified tank(s) in
accordance with 40 CFR part 280,
subpart F, the guarantor upon written
instructions from the [Director] shall
fund a standby trust in accordance with
the provisions of 40 CFR 280.112, in an
amount not to exceed the coverage
limits specified above.
If [owner or operator] fails to satisfy
a judgment or award based on a
determination of liability for bodily
injury or property damage to third
parties caused by [‘‘sudden’’ and/or
‘‘nonsudden’’] accidental releases
arising from the operation of the aboveidentified tank(s), or fails to pay an
amount agreed to in settlement of a
claim arising from or alleged to arise
from such injury or damage, the
guarantor, upon written instructions
from the [Director], shall fund a standby
trust in accordance with the provisions
of 40 CFR 280.112 to satisfy such
judgment(s), award(s), or settlement
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Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
accidental releases’’ or ‘‘nonsudden
accidental releases’’ or ‘‘accidental releases’’
‘‘arising from operating the underground
storage Tank’’].
Penal sums of bond:
Per occurrence $ lllllllllllll
Annual aggregate $
lllllllllll
Surety’s bond number: llllllllll
Know All Persons by These Presents, that
we, the Principal and Surety(ies), hereto are
firmly bound to [the implementing agency],
in the above penal sums for the payment of
which we bind ourselves, our heirs,
executors, administrators, successors, and
assigns jointly and severally; provided that,
where the Surety(ies) are corporations acting
as co-sureties, we, the Sureties, bind
ourselves in such sums jointly and severally
only for the purpose of allowing a joint
action or actions against any or all of us, and
for all other purposes each Surety binds
itself, jointly and severally with the
§ 280.97 Insurance and risk retention
Principal, for the payment of such sums only
group coverage.
as is set forth opposite the name of such
(a) An owner or operator may satisfy
Surety, but if no limit of liability is indicated,
the requirements of § 280.93 by
the limit of liability shall be the full amount
obtaining liability insurance that
of the penal sums.
conforms to the requirements of this
Whereas said Principal is required under
section from a qualified insurer or risk
Subtitle I of the Solid Waste Disposal Act, as
retention group. Such insurance may be amended, to provide financial assurance for
[insert: ‘‘taking corrective action’’ and/or
in the form of a separate insurance
‘‘compensating third parties for bodily injury
policy or an endorsement to an existing
and property damage caused by’’ either
insurance policy.
‘‘sudden accidental releases’’ or ‘‘nonsudden
*
*
*
*
*
accidental releases’’ or ‘‘accidental releases’’;
25. In § 280.98 revise paragraphs (b)
if coverage is different for different tanks or
locations, indicate the type of coverage
and (d) to read as follows:
applicable to each tank or location] arising
§ 280.98 Surety bond.
from operating the underground storage tanks
identified above, and
*
*
*
*
*
Whereas said Principal shall establish a
(b) The surety bond must be worded
standby trust fund as is required when a
as follows, except that instructions in
surety bond is used to provide such financial
brackets must be replaced with the
assurance;
relevant information and the brackets
Now, therefore, the conditions of the
deleted:
obligation are such that if the Principal shall
faithfully [‘‘take corrective action, in
Performance Bond
accordance with 40 CFR part 280, subpart F
Date bond executed: lllllllllll and the Director of the state implementing
Period of coverage: llllllllllll agency’s instructions for,’’ and/or
Principal: [legal name and business address
‘‘compensate injured third parties for bodily
of owner or operator]
injury and property damage caused by’’
lllllllllllllllllllll either ‘‘sudden accidental releases’’ or
Type of organization: [insert ‘‘individual,’’
‘‘nonsudden accidental releases’’ or
‘‘joint venture,’’ ‘‘partnership,’’ or
‘‘accidental releases’’] arising from operating
‘‘corporation’’]
the tank(s) indentified above, or if the
lllllllllllllllllllll Principal shall provide alternate financial
State of incorporation (if applicable):
assurance, as specified in 40 CFR part 280,
lllllllllllllllllllll subpart H, within 120 days after the date the
Surety(ies): [name(s) and business
notice of cancellation is received by the
address(es)]
Principal from the Surety(ies), then this
lllllllllllllllllllll obligation shall be null and void; otherwise
Scope of Coverage: [List the number of tanks
it is to remain in full force and effect.
at each facility and the name(s) and
Such obligation does not apply to any of
address(es) of the facility(ies) where the tanks the following:
are located. If more than one instrument is
(a) Any obligation of [insert owner or
used to assure different tanks at any one
operator] under a workers’ compensation,
facility, for each tank covered by this
disability benefits, or unemployment
instrument, list the tank identification
compensation law or other similar law;
number provided in the notification
(b) Bodily injury to an employee of [insert
submitted pursuant to 40 CFR 280.22, or the
owner or operator] arising from, and in the
corresponding state requirement, and the
course of, employment by [insert owner or
name and address of the facility. List the
operator];
coverage guaranteed by the bond: ‘‘taking
(c) Bodily injury or property damage
corrective action’’ and/or ‘‘compensating
arising from the ownership, maintenance,
third parties for bodily injury and property
use, or entrustment to others of any aircraft,
motor vehicle, or watercraft;
damage caused by’’ either ‘‘sudden
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
agreement(s) up to the limits of coverage
specified above.
*
*
*
*
*
(d) An owner or operator who uses a
guarantee to satisfy the requirements of
§ 280.93 must establish a standby trust
fund when the guarantee is obtained.
Under the terms of the guarantee, all
amounts paid by the guarantor under
the guarantee will be deposited directly
into the standby trust fund in
accordance with instructions from the
Director of the implementing agency
under § 280.112. This standby trust fund
must meet the requirements specified in
§ 280.103.
24. In § 280.97 revise paragraph (a) to
read as follows:
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(d) Property damage to any property
owned, rented, loaned to, in the care,
custody, or control of, or occupied by [insert
owner or operator] that is not the direct result
of a release from a petroleum underground
storage tank;
(e) Bodily injury or property damage for
which [insert owner or operator] is obligated
to pay damages by reason of the assumption
of liability in a contract or agreement other
than a contract or agreement entered into to
meet the requirements of 40 CFR 280.93.
The Surety(ies) shall become liable on this
bond obligation only when the Principal has
failed to fulfill the conditions described
above.
Upon notification by [the Director of the
implementing agency] that the Principal has
failed to [‘‘take corrective action, in
accordance with 40 CFR part 280, subpart F
and the Director’s instructions,’’ and/or
‘‘compensate injured third parties’’] as
guaranteed by this bond, the Surety(ies) shall
either perform [‘‘corrective action in
accordance with 40 CFR part 280 and the
Director’s instructions,’’ and/or ‘‘third-party
liability compensation’’] or place funds in an
amount up to the annual aggregate penal sum
into the standby trust fund as directed by [the
Regional Administrator or the Director]
under 40 CFR 280.112.
Upon notification by [the Director] that the
Principal has failed to provide alternate
financial assurance within 60 days after the
date the notice of cancellation is received by
the Principal from the Surety(ies) and that
[the Director] has determined or suspects that
a release has occurred, the Surety(ies) shall
place funds in an amount not exceeding the
annual aggregate penal sum into the standby
trust fund as directed by [the Director] under
40 CFR 280.112.
The Surety(ies) hereby waive(s)
notification of amendments to applicable
laws, statutes, rules, and regulations and
agrees that no such amendment shall in any
way alleviate its (their) obligation on this
bond.
The liability of the Surety(ies) shall not be
discharged by any payment or succession of
payments hereunder, unless and until such
payment or payments shall amount in the
annual aggregate to the penal sum shown on
the face of the bond, but in no event shall the
obligation of the Surety(ies) hereunder
exceed the amount of said annual aggregate
penal sum.
The Surety(ies) may cancel the bond by
sending notice of cancellation by certified
mail to the Principal, provided, however, that
cancellation shall not occur during the 120
days beginning on the date of receipt of the
notice of cancellation by the Principal, as
evidenced by the return receipt.
The Principal may terminate this bond by
sending written notice to the Surety(ies).
In Witness Thereof, the Principal and
Surety(ies) have executed this Bond and have
affixed their seals on the date set forth above.
The persons whose signatures appear
below hereby certify that they are authorized
to execute this surety bond on behalf of the
Principal and Surety(ies) and that the
wording of this surety bond is identical to the
wording specified in 40 CFR 280.98(b) as
such regulations were constituted on the date
this bond was executed.
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Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
Principal
[Signature(s)]
[Names(s)]
[Title(s)]
[Corporate seal]
Corporate Surety(ies)
[Name and address]
[State of Incorporation: lllll]
[Liability limit: $lllll]
[Signature(s)]
[Names(s) and title(s)]
[Corporate seal]
[For every co-surety, provide signature(s),
corporate seal, and other information in the
same manner as for Surety above.]
Bond premium: $lllll
*
*
*
*
*
(d) The owner or operator who uses
a surety bond to satisfy the requirements
of § 280.93 must establish a standby
trust fund when the surety bond is
acquired. Under the terms of the bond,
all amounts paid by the surety under the
bond will be deposited directly into the
standby trust fund in accordance with
instructions from the Director under
§ 280.112. This standby trust fund must
meet the requirements specified in
§ 280.103.
26. In § 280.99 revise paragraphs (b)
and (c) to read as follows:
§ 280.99
Letter of credit.
*
*
*
*
(b) The letter of credit must be
worded as follows, except that
instructions in brackets are to be
replaced with the relevant information
and the brackets deleted:
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*
Irrevocable Standby Letter of Credit
[Name and address of issuing institution]
[Name and address of Director(s) of state
implementing agency(ies)]
Dear Sir or Madam: We hereby establish
our Irrevocable Standby Letter of Credit No.
lllll in your favor, at the request and
for the account of [owner or operator name]
of [address] up to the aggregate amount of [in
words] U.S. dollars ($[insert dollar amount]),
available upon presentation [insert, if more
than one Director of a state implementing
agency is a beneficiary, ‘‘by any one of you’’]
of
(1) your sight draft, bearing reference to
this letter of credit, No. lllll, and
(2) your signed statement reading as
follows: ‘‘I certify that the amount of the draft
is payable pursuant to regulations issued
under authority of Subtitle I of the Solid
Waste Disposal Act, as amended.’’
This letter of credit may be drawn on to
cover [insert: ‘‘taking corrective action’’ and/
or ‘‘compensating third parties for bodily
injury and property damage caused by’’
either ‘‘sudden accidental releases’’ or
‘‘nonsudden accidental releases’’ or
‘‘accidental releases’’] arising from operating
the underground storage tank(s) identified
below in the amount of [in words] $[insert
dollar amount] per occurrence and [in words]
$[insert dollar amount] annual aggregate:
[List the number of tanks at each facility
and the name(s) and address(es) of the
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22:10 Nov 17, 2011
Jkt 226001
facility(ies) where the tanks are located. If
more than one instrument is used to assure
different tanks at any one facility, for each
tank covered by this instrument, list the tank
identification number provided in the
notification submitted pursuant to 40 CFR
280.22, or the corresponding state
requirement, and the name and address of
the facility.]
The letter of credit may not be drawn on
to cover any of the following:
(a) Any obligation of [insert owner or
operator] under a workers’ compensation,
disability benefits, or unemployment
compensation law or other similar law;
(b) Bodily injury to an employee of [insert
owner or operator] arising from, and in the
course of, employment by [insert owner or
operator];
(c) Bodily injury or property damage
arising from the ownership, maintenance,
use, or entrustment to others of any aircraft,
motor vehicle, or watercraft;
(d) Property damage to any property
owned, rented, loaned to, in the care,
custody, or control of, or occupied by [insert
owner or operator] that is not the direct result
of a release from a petroleum underground
storage tank;
(e) Bodily injury or property damage for
which [insert owner or operator] is obligated
to pay damages by reason of the assumption
of liability in a contract or agreement other
than a contract or agreement entered into to
meet the requirements of 40 CFR 280.93.
This letter of credit is effective as of [date]
and shall expire on [date], but such
expiration date shall be automatically
extended for a period of [at least the length
of the original term] on [expiration date] and
on each successive expiration date, unless, at
least 120 days before the current expiration
date, we notify [owner or operator] by
certified mail that we have decided not to
extend this letter of credit beyond the current
expiration date. In the event that [owner or
operator] is so notified, any unused portion
of the credit shall be available upon
presentation of your sight draft for 120 days
after the date of receipt by [owner or
operator], as shown on the signed return
receipt.
Whenever this letter of credit is drawn on
under and in compliance with the terms of
this credit, we shall duly honor such draft
upon presentation to us, and we shall deposit
the amount of the draft directly into the
standby trust fund of [owner or operator] in
accordance with your instructions.
We certify that the wording of this letter of
credit is identical to the wording specified in
40 CFR 280.99(b) as such regulations were
constituted on the date shown immediately
below.
[Signature(s) and title(s) of official(s) of
issuing institution]
[Date]
This credit is subject to [insert ‘‘the most
recent edition of the Uniform Customs and
Practice for Documentary Credits, published
and copyrighted by the International
Chamber of Commerce,’’ or ‘‘the Uniform
Commercial Code’’].
(c) An owner or operator who uses a letter
of credit to satisfy the requirements of
§ 280.93 must also establish a standby trust
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71779
fund when the letter of credit is acquired.
Under the terms of the letter of credit, all
amounts paid pursuant to a draft by the
Director of the implementing agency will be
deposited by the issuing institution directly
into the standby trust fund in accordance
with instructions from the Director under
§ 280.112. This standby trust fund must meet
the requirements specified in § 280.103.
*
*
*
*
*
27. In § 280.101 revise paragraph (d)
to read as follows:
§ 280.101 State fund or other state
assurance.
*
*
*
*
*
(d) The Regional Administrator will
notify the state of his determination
regarding the acceptability of the state’s
fund or other assurance in lieu of
financial mechanisms specified in this
subpart. Within 60 days after the
Regional Administrator notifies a state
that a state fund or other state assurance
is acceptable, the state must provide to
each owner or operator for which it is
assuming financial responsibility a
letter or certificate describing the nature
of the state’s assumption of
responsibility. The letter or certificate
from the state must include, or have
attached to it, the following information:
The facility’s name and address and the
amount of funds for corrective action
and/or for compensating third parties
that is assured by the state. The owner
or operator must maintain this letter or
certificate on file as proof of financial
responsibility in accordance with
§ 280.111(b)(8).
28. In § 280.103 revise paragraph
(b)(1) and the Trust Agreement
introductory text and section 4 to read
as follows:
§ 280.103
Standby trust fund.
*
*
*
*
*
(b)(1) The standby trust agreement, or
trust agreement, must be worded as
follows, except that instructions in
brackets are to be replaced with the
relevant information and the brackets
deleted:
Trust Agreement
Trust agreement, the ‘‘Agreement,’’ entered
into as of [date] by and between [name of the
owner or operator], a [name of state] [insert
‘‘corporation,’’ ‘‘partnership,’’ ‘‘association,’’
or ‘‘proprietorship’’], the ‘‘Grantor,’’ and
[name of corporate trustee], [insert
‘‘Incorporated in the state of lllll’’ or
‘‘a national bank’’], the ‘‘Trustee.’’
Whereas, the United States Environmental
Protection Agency, ‘‘EPA,’’ an agency of the
United States Government, has established
certain regulations applicable to the Grantor,
requiring that an owner or operator of an
underground storage tank shall provide
assurance that funds will be available when
needed for corrective action and third-party
compensation for bodily injury and property
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damage caused by sudden and nonsudden
accidental releases arising from the operation
of the underground storage tank. The
attached Schedule A lists the number of
tanks at each facility and the name(s) and
address(es) of the facility(ies) where the tanks
are located that are covered by the [insert
‘‘standby’’ where trust agreement is standby
trust agreement] trust agreement.
[Whereas, the Grantor has elected to
establish [insert either ‘‘a guarantee,’’ ‘‘surety
bond,’’ or ‘‘letter of credit’’] to provide all or
part of such financial assurance for the
underground storage tanks identified herein
and is required to establish a standby trust
fund able to accept payments from the
instrument (This paragraph is only
applicable to the standby trust agreement.)];
Whereas, the Grantor, acting through its
duly authorized officers, has selected the
Trustee to be the trustee under this
agreement, and the Trustee is willing to act
as trustee;
Now, therefore, the Grantor and the
Trustee agree as follows:
*
*
*
*
*
Section 4. Payment for [‘‘Corrective Action’’
and/or ‘‘Third-Party Liability Claims’’]
The Trustee shall make payments from the
Fund as [the Director of the implementing
agency] shall direct, in writing, to provide for
the payment of the costs of [insert: ‘‘taking
corrective action’’ and/or ‘‘compensating
third parties for bodily injury and property
damage caused by’’ either ‘‘sudden
accidental releases’’ or ‘‘nonsudden
accidental Releases’’ or ‘‘accidental releases’’]
arising from operating the tanks covered by
the financial assurance mechanism identified
in this Agreement.
The Fund may not be drawn upon to cover
any of the following:
(a) Any obligation of [insert owner or
operator] under a workers’ compensation,
disability benefits, or unemployment
compensation law or other similar law;
(b) Bodily injury to an employee of [insert
owner or operator] arising from, and in the
course of employment by [insert owner or
operator];
Issue date
(c) Bodily injury or property damage
arising from the ownership, maintenance,
use, or entrustment to others of any aircraft,
motor vehicle, or watercraft;
(d) Property damage to any property
owned, rented, loaned to, in the care,
custody, or control of, or occupied by [insert
owner or operator] that is not the direct result
of a release from a petroleum underground
storage tank;
(e) Bodily injury or property damage for
which [insert owner or operator] is obligated
to pay damages by reason of the assumption
of liability in a contract or agreement other
than a contract or agreement entered into to
meet the requirements of 40 CFR 280.93.
The Trustee shall reimburse the Grantor, or
other persons as specified by [the Director],
from the Fund for corrective action
expenditures and/or third-party liability
claims in such amounts as [the Director] shall
direct in writing. In addition, the Trustee
shall refund to the Grantor such amounts as
[the Director] specifies in writing. Upon
refund, such funds shall no longer constitute
part of the Fund as defined herein.
*
*
*
*
*
29. Amend § 280.104 as follows:
a. By revising paragraph (b)
b. By revising paragraph (d)
c. By revising paragraph (e)
d. By adding paragraph (h)
§ 280.104
test.
Local government bond rating
*
*
*
*
*
(b) A local government owner or
operator or local government serving as
a guarantor that is not a general-purpose
local government and does not have the
legal authority to issue general
obligation bonds may satisfy the
requirements of § 280.93 by having a
currently outstanding issue or issues of
revenue bonds of $1 million or more,
excluding refunded issues, and by also
having a Moody’s rating of Aaa, Aa, A,
or Baa, or a Standard & Poor’s rating of
AAA, AA, A, or BBB as the lowest
Outstanding
amount
Maturity date
rating for any rated revenue bond issued
by the local government. Where bonds
are rated by both Moody’s and Standard
& Poor’s, the lower rating for each bond
must be used to determine eligibility.
Bonds that are backed by credit
enhancement may not be considered in
determining the amount of applicable
bonds outstanding.
*
*
*
*
*
(d) To demonstrate that it meets the
local government bond rating test, the
chief financial officer of a general
purpose local government owner or
operator and/or guarantor must sign a
letter worded exactly as follows, except
that the instructions in brackets are to
be replaced by the relevant information
and the brackets deleted:
Letter from Chief Financial Officer
I am the chief financial officer of [insert:
name and address of local government owner
or operator, or guarantor]. This letter is in
support of the use of the bond rating test to
demonstrate financial responsibility for
[insert: ‘‘taking corrective action’’ and/or
‘‘compensating third parties for bodily injury
and property damage’’] caused by [insert:
‘‘sudden accidental releases’’ or ‘‘nonsudden
accidental releases’’ or ‘‘accidental releases’’]
in the amount of at least [insert: dollar
amount] per occurrence and [insert: dollar
amount] annual aggregate arising from
operating (an) underground storage tank(s).
Underground storage tanks at the following
facilities are assured by this bond rating test:
[List for each facility: the name and address
of the facility where tanks are assured by the
bond rating test].
The details of the issue date, maturity,
outstanding amount, bond rating, and bond
rating agency of all outstanding bond issues
that are being used by [name of local
government owner or operator, or guarantor]
to demonstrate financial responsibility are as
follows: [complete table]
Bond rating
Rating agency
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
[Moody’s or Standard &
Poor’s]
The total outstanding obligation of [insert
amount], excluding refunded bond issues,
exceeds the minimum amount of $1 million.
All outstanding general obligation bonds
issued by this government that have been
rated by Moody’s or Standard & Poor’s are
rated as at least investment grade (Moody’s
Baa or Standard & Poor’s BBB) based on the
most recent ratings published within the last
12 months. Neither rating service has
provided notification within the last 12
months of downgrading of bond ratings
below investment grade or of withdrawal of
bond rating other than for repayment of
outstanding bond issues.
I hereby certify that the wording of this
letter is identical to the wording specified in
VerDate Mar<15>2010
22:10 Nov 17, 2011
Jkt 226001
40 CFR part 280.104(d) as such regulations
were constituted on the date shown
immediately below.
[Date] llllllllllllllllll
[Signature] lllllllllllllll
[Name] lllllllllllllllll
[Title] lllllllllllllllll
(e) To demonstrate that it meets the
local government bond rating test, the
chief financial officer of local
government owner or operator and/or
guarantor other than a general purpose
government must sign a letter worded
exactly as follows, except that the
instructions in brackets are to be
PO 00000
Frm 00074
Fmt 4701
Sfmt 4702
replaced by the relevant information
and the brackets deleted:
Letter from Chief Financial Officer
I am the chief financial officer of [insert:
name and address of local government owner
or operator, or guarantor]. This letter is in
support of the use of the bond rating test to
demonstrate financial responsibility for
[insert: ‘‘taking corrective action’’ and/or
‘‘compensating third parties for bodily injury
and property damage’’] caused by [insert:
‘‘sudden accidental releases’’ or ‘‘nonsudden
accidental releases’’ or ‘‘accidental releases’’]
in the amount of at least [insert: dollar
amount] per occurrence and [insert: dollar
amount] annual aggregate arising from
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operating (an) underground storage tank(s).
This local government is not organized to
provide general governmental services and
does not have the legal authority under state
law or constitutional provisions to issue
general obligation debt.
Issue date
Underground storage tanks at the following
facilities are assured by this bond rating test:
[List for each facility: the name and address
of the facility where tanks are assured by the
bond rating test].
The details of the issue date, maturity,
outstanding amount, bond rating, and bond
Outstanding
amount
Maturity date
71781
rating agency of all outstanding revenue bond
issues that are being used by [name of local
government owner or operator, or guarantor]
to demonstrate financial responsibility are as
follows: [complete table]
Bond rating
Rating agency
[Moody’s or Standard &
Poor’s]
The total outstanding obligation of [insert
amount], excluding refunded bond issues,
exceeds the minimum amount of $1 million.
All outstanding revenue bonds issued by this
government that have been rated by Moody’s
or Standard & Poor’s are rated as at least
investment grade (Moody’s Baa or Standard
& Poor’s BBB) based on the most recent
ratings published within the last 12 months.
The revenue bonds listed are not backed by
third-party credit enhancement or insured by
a municipal bond insurance company.
Neither rating service has provided
notification within the last 12 months of
downgrading of bond ratings below
investment grade or of withdrawal of bond
rating other than for repayment of
outstanding bond issues.
I hereby certify that the wording of this
letter is identical to the wording specified in
40 CFR part 280.104(e) as such regulations
were constituted on the date shown
immediately below.
[Date] llllllllllllllllll
[Signature] lllllllllllllll
[Name] lllllllllllllllll
[Title] lllllllllllllllll
*
*
*
*
*
(h) If the local government owner or
operator fails to obtain alternate
assurance within 150 days of finding
that it no longer meets the requirements
of the bond rating test or within 30 days
of notification by the Director of the
implementing agency that it no longer
meets the requirements of the bond
rating test, the owner or operator must
notify the Director of such failure within
10 days.
30. In § 280.105 revise paragraph (c)
and the Letter From Chief Financial
Officer to read as follows:
§ 280.105
Local government financial test.
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
*
*
*
*
*
(c) To demonstrate that it meets the
financial test under paragraph (b) of this
section, the chief financial officer of the
local government owner or operator,
must sign, within 120 days of the close
of each financial reporting year, as
defined by the twelve-month period for
which financial statements used to
support the financial test are prepared,
a letter worded exactly as follows,
except that the instructions in brackets
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Jkt 226001
are to be replaced by the relevant
information and the brackets deleted:
Letter From Chief Financial Officer
I am the chief financial officer of [insert:
name and address of the owner or operator].
This letter is in support of the use of the local
government financial test to demonstrate
financial responsibility for [insert: ‘‘taking
corrective action’’ and/or ‘‘compensating
third parties for bodily injury and property
damage’’] caused by [insert: ‘‘sudden
accidental releases’’ or ‘‘nonsudden
accidental releases’’ or ‘‘accidental releases’’]
in the amount of at least [insert: dollar
amount] per occurrence and [insert: dollar
amount] annual aggregate arising from
operating [an] underground storage tank[s].
Underground storage tanks at the following
facilities are assured by this financial test
[List for each facility: the name and address
of the facility where tanks assured by this
financial test are located. If separate
mechanisms or combinations of mechanisms
are being used to assure any of the tanks at
this facility, list each tank assured by this
financial test by the tank identification
number provided in the notification
submitted pursuant to 40 CFR part 280.22 or
the corresponding state requirements.]
This owner or operator has not received an
adverse opinion, or a disclaimer of opinion
from an independent auditor on its financial
statements for the latest completed fiscal
year. Any outstanding issues of general
obligation or revenue bonds, if rated, have a
Moody’s rating of Aaa, Aa, A, or Baa or a
Standard and Poor’s rating of AAA, AA, A,
or BBB; if rated by both firms, the bonds have
a Moody’s rating of Aaa, Aa, A, or Baa and
a Standard and Poor’s rating of AAA, AA, A,
or BBB.
Worksheet for Municipal Financial Test
Part I: Basic Information
1. Total Revenues
a. Revenues (dollars)llllllllll
Value of revenues excludes liquidation of
investments and issuance of debt. Value
includes all general fund operating and nonoperating revenues, as well as all revenues
from all other governmental funds including
enterprise, debt service, capital projects, and
special revenues, but excluding revenues to
funds held in a trust or agency capacity.
b. Subtract interfund transfers
(dollars)llllllllll
c. Total Revenues
(dollars)llllllllll
2. Total Expenditures
PO 00000
Frm 00075
Fmt 4701
Sfmt 4702
a. Expenditures
(dollars)llllllllll
Value consists of the sum of general fund
operating and non-operating expenditures
including interest payments on debt,
payments for retirement of debt principal,
and total expenditures from all other
governmental funds including enterprise,
debt service, capital projects, and special
revenues.
b. Subtract interfund transfers
(dollars)llllllllll
c. Total Expenditures (dollars)
llllllllll
3. Local Revenues
a. Total Revenues (from 1c)
(dollars)llllllllll
b. Subtract total intergovernmental transfers
(dollars)llllllllll
c. Local Revenues
(dollars)llllllllll
4. Debt Service
a. Interest and fiscal charges
(dollars)llllllllll
b. Add debt retirement
(dollars)llllllllll
c. Total Debt Service
(dollars)llllllllll
5. Total Funds
(Dollars)llllllllll
(Sum of amounts held as cash and
investment securities from all funds,
excluding amounts held for employee
retirement funds, agency funds, and trust
funds)
6. Population
(Persons)llllllllll
Part II: Application of Test
7. Total Revenues to Population
a. Total Revenues (from
1c)llllllllll
b. Population (from 6)llllllllll
c. Divide 7a by 7bllllllllll
d. Subtract 417llllllllll
e. Divide by 5,212llllllllll
f. Multiply by 4.095llllllllll
8. Total Expenses to Population
a. Total Expenses (from
2c)llllllllll
b. Population (from 6)llllllllll
c. Divide 8a by 8bllllllllll
d. Subtract 524llllllllll
e. Divide by 5,401llllllllll
f. Multiply by 4.095llllllllll
9. Local Revenues to Total Revenues
a. Local Revenues (from
3c)llllllllll
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18NOP2
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Federal Register / Vol. 76, No. 223 / Friday, November 18, 2011 / Proposed Rules
b. Total Revenues (from
1c)llllllllll
c. Divide 9a by 9bllllllllll
d. Subtract .695llllllllll
e. Divide by .205llllllllll
f. Multiply by 2.840llllllllll
10. Debt Service to Population
a. Debt Service (from
4c)llllllllll
b. Population (from 6)llllllllll
c. Divide 10a by 10bllllllll
d. Subtract 51llllllll
e. Divide by 1,038llllllll
f. Multiply by ¥1.866llllllll
11. Debt Service to Total Revenues
a. Debt Service (from 4c)llllllll
b. Total Revenues (from 1c)llllllll
c. Divide 11a by 11bllllllll
d. Subtract .068llllllll
e. Divide by .259llllllll
f. Multiply by -3.533llllllll
12. Total Revenues to Total Expenses
a. Total Revenues (from 1c)llllllll
b. Total Expenses (from 2c)llllllll
c. Divide 12a by 12bllllllll
d. Subtract .910llllllll
e. Divide by .899llllllll
f. Multiply by 3.458llllllll
13. Funds Balance to Total Revenues
a. Total Funds (from 5)llllllll
b. Total Revenues (from 1c)llllllll
c. Divide 13a by 13bllllllll
d. Subtract .891llllllll
e. Divide by 9.156llllllll
f. Multiply by 3.270llllllll
14. Funds Balance to Total Expenses
a. Total Funds (from 5)llllllll
b. Total Expenses (from 2c)llllllll
c. Divide 14a by 14bllllllll
d. Subtract .866llllllll
e. Divide by 6.409llllllll
f. Multiply by 3.270llllllll
15. Total Funds to
Populationllllllll
a. Total Funds (from 5)llllllll
b. Population (from 6)llllllll
c. Divide 15a by 15bllllllll
d. Subtract 270llllllll
e. Divide by 4,548llllllll
f. Multiply by 1.866llllllll
16. Add 7f + 8f + 9f + 10f + 11f + 12f +
13f + 14f + 15f + 4.937llllllll
I hereby certify that the financial index
shown on line 16 of the worksheet is greater
than zero and that the wording of this letter
is identical to the wording specified in 40
CFR part 280.105(c) as such regulations were
constituted on the date shown immediately
below.
[Date]
[Signature]
[Name]
[Title]
*
*
*
*
*
31. Amend § 280.106 as follows:
a. By revising paragraph (a)(1)
b. By revising paragraph (b)
c. By revising paragraph (d)(7)(d)
d. By revising paragraph (e)(7)(d)
e. By revising paragraph (e)(8)(d)
VerDate Mar<15>2010
22:10 Nov 17, 2011
Jkt 226001
§ 280.106
Local government guarantee.
(a) * * *
(1) Demonstrate that it meets the bond
rating test requirement of § 280.104 and
deliver a copy of the chief financial
officer’s letter as contained in
§ 280.104(d) and § 280.104(e) to the
local government owner or operator; or
*
*
*
*
*
(b) If the local government guarantor
is unable to demonstrate financial
assurance under any of § § 280.104,
280.105, 280.107(a), 280.107(b), or
280.107(c), at the end of the financial
reporting year, the guarantor shall send
by certified mail, before cancellation or
non-renewal of the guarantee, notice to
the owner or operator. The guarantee
will terminate no less than 120 days
after the date the owner or operator
receives the notification, as evidenced
by the return receipt. The owner or
operator must obtain alternative
coverage as specified in § 280.114(e).
*
*
*
*
*
(d) * * *
(7) * * *
(d) Property damage to any property
owned, rented, loaned to, in the care,
custody, or control of, or occupied by
[insert: local government owner or
operator] that is not the direct result of
a release from a petroleum underground
storage tank;
*
*
*
*
*
(e) * * *
(7) * * *
(d) Property damage to any property
owned, rented, loaned to, in the care,
custody, or control of, or occupied by
[insert: local government owner or
operator] that is not the direct result of
a release from a petroleum underground
storage tank;
*
*
*
*
*
(8) * * *
(d) Property damage to any property
owned, rented, loaned to, in the care,
custody, or control of, or occupied by
[insert: local government owner or
operator] that is not the direct result of
a release from a petroleum underground
storage tank;
*
*
*
*
*
32. In § 280.107 revise paragraph (d)
to read as follows:
§ 280.107
Local government fund.
*
*
*
*
*
(d) To demonstrate that it meets the
requirements of the local government
fund, the chief financial officer of the
local government owner or operator
and/or guarantor must sign a letter
worded exactly as follows, except that
the instructions in brackets are to be
replaced by the relevant information
and the brackets deleted:
PO 00000
Frm 00076
Fmt 4701
Sfmt 4702
Letter from Chief Financial Officer
I am the chief financial officer of [insert:
name and address of local government owner
or operator, or guarantor]. This letter is in
support of the use of the local government
fund mechanism to demonstrate financial
responsibility for [insert: ‘‘taking corrective
action’’ and/or ‘‘compensating third parties
for bodily injury and property damage’’]
caused by [insert: ‘‘sudden accidental
releases’’ or ‘‘nonsudden accidental releases’’
or ‘‘accidental releases’’] in the amount of at
least [insert: dollar amount] per occurrence
and [insert: dollar amount] annual aggregate
arising from operating (an) underground
storage tank(s).
Underground storage tanks at the following
facilities are assured by this local government
fund mechanism: [List for each facility: the
name and address of the facility where tanks
are assured by the local government fund].
[Insert: ‘‘The local government fund is
funded for the full amount of coverage
required under § 280.93, or funded for part of
the required amount of coverage and used in
combination with other mechanism(s) that
provide the remaining coverage.’’ or ‘‘The
local government fund is funded for five
times the full amount of coverage required
under § 280.93, or funded for part of the
required amount of coverage and used in
combination with other mechanisms(s) that
provide the remaining coverage,’’ or ‘‘A
payment is made to the fund once every year
for seven years until the fund is fully-funded
and [name of local government owner or
operator] has available bonding authority,
approved through voter referendum, of an
amount equal to the difference between the
required amount of coverage and the amount
held in the dedicated fund’’ or ‘‘A payment
is made to the fund once every year for seven
years until the fund is fully-funded and I
have attached a letter signed by the State
Attorney General stating that (1) the use of
the bonding authority will not increase the
local government’s debt beyond the legal
debt ceilings established by the relevant state
laws and (2) that prior voter approval is not
necessary before use of the bonding
authority’’].
The details of the local government fund
are as follows:
Amount in Fund (market value of fund at
close of last fiscal year):lllll
[If fund balance is incrementally funded as
specified in § 280.107(c), insert:
Amount added to fund in the most recently
completed fiscal year:lllll
Number of years remaining in the pay-in
period: lllll]
A copy of the state constitutional
provision, or local government statute,
charter, ordinance or order dedicating the
fund is attached.
I hereby certify that the wording of this
letter is identical to the wording specified in
40 CFR 280.107(d) as such regulations were
constituted on the date shown immediately
below.
[Date]
[Signature]
[Name]
[Title]
*
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§ 280.109 Cancellation or nonrenewal by a
provider of financial assurance.
operators of UST systems must ensure
they have designated Class A, Class B,
and Class C operators who meet the
requirements of this subpart.
*
§ 280.241
33. In § 280.109 revise paragraph (b)
(3) to read as follows:
*
*
*
*
(b) * * *
(3) The evidence of the financial
assistance mechanism subject to the
termination maintained in accordance
with § 280.111(b).
34. In § 280.111 revise paragraphs
(b)(9)(ii) and (iii) to read as follows:
§ 280.111
Recordkeeping.
*
*
*
*
*
(b) * * *
(9) * * *
(ii) Year-end financial statements for
the most recent completed financial
reporting year showing the amount in
the fund. If the fund is established
under § 280.107(c) using incremental
funding backed by bonding authority,
the financial statements must show the
previous year’s balance, the amount of
funding during the year, and the closing
balance in the fund.
(iii) If the fund is established under
§ 280.107(c) using incremental funding
backed by bonding authority, the owner
or operator must also maintain
documentation of the required bonding
authority, including either the results of
a voter referendum (under
§ 280.107(c)(1)), or attestation by the
State Attorney General as specified
under § 280.107(c)(2).
*
*
*
*
*
35. Revise § 280.113 to read as
follows:
§ 280.113
Release from the requirements.
An owner or operator is no longer
required to maintain financial
responsibility under this subpart for an
underground storage tank after the tank
has been permanently closed or, if
corrective action is required, after
corrective action has been completed
and the tank has been permanently
closed as required by 40 CFR part 280,
subpart G.
36. Add Subpart J to read as follows:
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
Subpart J—Operator Training
Sec.
280.240 General requirement for all UST
systems.
280.241 Designation of operators.
280.242 Requirements for operator training.
280.243 Timing of operator training.
280.244 Retraining.
280.245 Documentation.
Subpart J—Operator Training
§ 280.240
systems.
General requirement for all UST
Not later than [Three years after
effective date of rule], all owners and
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Designation of operators.
UST system owners and operators
must designate:
(a) At least one Class A and one Class
B operator for each UST or group of
USTs at a facility; and
(b) Each individual who meets the
definition of Class C operator at the UST
facility as a Class C operator. Class C
operators must be employees of the UST
system owner and operator.
§ 280.242
training.
Requirements for operator
UST system owners and operators
must ensure Class A, Class B, and Class
C operators meet the requirements of
this section. Any individual designated
for more than one operator class must
successfully complete the required
training program or comparable
examination according to the operator
class in which the individual is
designated.
(a) Class A operators. Each designated
Class A operator must either be trained
in accordance with paragraphs (a)(1)
and (a)(2) of this section or pass a
comparable examination in accordance
with paragraph (e) of this section. Class
A operators must receive training from
an independent trainer.
(1) At a minimum, the training
program for the Class A operator must
provide general knowledge of the
requirements in this paragraph. At a
minimum, the training must teach the
Class A operators, as applicable, on the
purpose, methods, and function of:
(i) Spill and overfill prevention;
(ii) Release detection;
(iii) Corrosion protection;
(iv) Emergency response;
(v) Product and equipment
compatibility;
(vi) Financial responsibility;
(vii) Notification and storage tank
registration;
(viii) Temporary and permanent
closure;
(ix) Related reporting and
recordkeeping;
(x) Environmental and regulatory
consequences of releases; and
(xi) Training requirements for Class B
and Class C operators.
(2) At a minimum, the training
program must evaluate Class A
operators to determine these individuals
have the knowledge and skills to make
informed decisions regarding
compliance and determine whether
appropriate individuals are fulfilling the
operation, maintenance, and
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recordkeeping requirements for UST
systems in accordance with paragraph
(a)(1) of this section.
(b) Class B operators. Each designated
Class B operator must either receive
training in accordance with paragraphs
(b)(1) and (b)(2) of this section or pass
a comparable examination, in
accordance with paragraph (e) of this
section. Class B operators must receive
training from an independent trainer.
(1) At a minimum, the training
program for the Class B operator must
cover either: General requirements that
encompass all regulatory requirements
and typical equipment used at UST
facilities; or site-specific requirements
which address only the regulatory
requirements and equipment specific to
the facility. At a minimum, the training
program for Class B operators must
teach the Class B operator, as
applicable, on the purpose, methods,
and function of:
(i) Operation and maintenance;
(ii) Spill and overfill prevention;
(iii) Release detection and related
reporting;
(iv) Corrosion protection and related
testing;
(v) Emergency response;
(vi) Product and equipment
compatibility;
(vii) Reporting and recordkeeping;
(viii) Environmental and regulatory
consequences of releases; and
(ix) Training requirements for Class C
operator.
(2) At a minimum, the training
program must evaluate Class B operators
to determine these individuals have the
knowledge and skills to implement
applicable UST regulatory requirements
in the field on the components of
typical UST systems or, as applicable,
site-specific equipment used at an UST
facility in accordance with paragraph
(b)(1) of this section.
(c) Class C operators. Each designated
Class C operator must either: Be trained
by a Class A or Class B operator in
accordance with paragraphs (c)(1) and
(c)(2) of this section; complete a training
program in accordance with paragraphs
(c)(1) and (c)(2) of this section; or pass
a comparable examination, in
accordance with paragraph (e) of this
section.
(1) At a minimum, the training
program for the Class C operator must
teach the Class C operators to take
appropriate actions in response to:
(i) Emergencies; and
(ii) Alarms caused by spills or releases
from the UST system.
(2) At a minimum, the training
program must evaluate Class C operators
to determine these individuals have the
knowledge and skills to take appropriate
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action in response to emergencies
(including situations posing an
immediate danger or threat to the public
or to the environment and that require
immediate action) or alarms caused by
spills or releases from an underground
storage tank system.
(d) Training program. Any training
program must meet the minimum
requirements of this section and include
an evaluation through testing, a
practical demonstration, or another
approach acceptable to the
implementing agency. The evaluation
component of the training program must
be developed and administered by an
independent organization or the
implementing agency or delegated
authority.
(e) Comparable Examination. A
comparable examination must, at a
minimum, test the knowledge of the
Class A, Class B, or Class C operators in
accordance with the requirements of
paragraphs (a), (b), (c) of this section, as
applicable. The examination must be
developed and administered by an
independent organization or the
implementing agency or delegated
authority.
§ 280.243
Timing of operator training.
(a) An owner and operator must
ensure that designated Class A, Class B,
and Class C operators meet
requirements in § 280.242 according to
the following schedule:
PHASE-IN SCHEDULE FOR OPERATOR TRAINING
Date when operator training or comparable
examination is required
Criteria
One or more USTs at the facility were installed on or before 12/22/1988 .....................................
No USTs at the facility were installed on or before 12/22/1988 and at least one UST at the facility was installed on or before 12/22/1998.
All USTs at the facility were installed after 12/22/1998 ...................................................................
(b) Class A and Class B operators
designated after the applicable effective
date indicated in the schedule above
must meet requirements in § 280.242
within 30 days of assuming duties.
(c) Class C operators designated after
the applicable effective date indicated
in the schedule above must be trained
before assuming duties of a Class C
operator.
§ 280.244
Retraining.
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Class A and Class B operators of UST
systems determined by the
implementing agency to be out of
compliance must complete a training
program or comparable examination in
accordance with requirements in
§ 280.242. At a minimum, the training
must cover the area(s) determined to be
out of compliance. UST system owners
and operators must ensure Class A and
Class B operators are retrained pursuant
to this section no later than 30 days
from the date the implementing agency
determines the facility is out of
compliance except in one of the
following situations:
(a) Class A and Class B operators take
annual refresher training. Refresher
training for Class A and Class B
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operators must cover all applicable
requirements in § 280.242, or
(b) The implementing agency, at its
discretion, grants a waiver of this
retraining requirement to either the
Class A or Class B operator or both.
§ 280.245
Documentation.
Owners and operators of underground
storage tank systems must maintain a
list of designated Class A, Class B, and
Class C operators and maintain records
verifying that training and retraining, as
applicable, have been completed, in
accordance with § 280.34 as follows:
(a) The list must:
(1) Identify all Class A, Class B, and
Class C operators at the facility over the
last three years; and
(2) Include names, class of operator
trained, date assumed duties, date each
completed initial training, and any
retraining.
(b) Records verifying completion of
training or retraining must be a paper or
electronic record for Class A, Class B,
and Class C operators. The records, at a
minimum, must identify name of
trainee, date trained, and operator
training class completed. Owners and
operators must maintain these records
for as long as Class A, Class B, and Class
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[1 year after effective date of rule].
[2 years after effective date of rule].
[3 years after effective date of rule].
C operators are designated. The
following requirements also apply to the
following types of training:
(1) Records from classroom or field
training programs or a comparable
examination must, at a minimum, be
signed by the trainer or examiner and
list the printed name of the trainer or
examiner and the company name,
address, and phone number;
(2) Records from computer-based
training must, at a minimum, indicate
the name of the training program and
web address, if Internet-based; and
(3) Records of retraining must include
those areas on which the Class A or
Class B operator has been retrained.
37. Appendix III to Part 280 is revised
to read as follows:
Appendix III to Part 280—Statement for
Shipping Tickets and Invoices
Note. A federal law (the Solid Waste
Disposal Act, as amended), requires owners
of certain underground storage tanks to notify
implementing agencies of the existence of
their tanks. Notifications must be made
within 30 days of bringing the tank into use.
Consult EPA’s regulations at 40 CFR 280.22
to determine if you are affected by this law.
BILLING CODE 6560–50–P
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BILLING CODE 6560–50–C
Act of 1976, as amended (42 U.S.C. 6912,
6991(c), (d), (e)).
Subpart A—Purpose, General
Requirements and Scope
PART 281—APPROVAL OF STATE
UNDERGROUND STORAGE TANK
PROGRAMS
38. Revise Part 281 to read as follows:
PART 281—APPROVAL OF STATE
UNDERGROUND STORAGE TANK
PROGRAMS
Subpart A—Purpose, General Requirements
and Scope
Sec.
281.10 Purpose.
281.11 General requirements.
281.12 Scope and definitions.
Subpart B—Components of a Program
Application
Sec.
281.20 Program application.
281.21 Description of state program.
281.22 Procedures for adequate
enforcement.
281.23 Memorandum of agreement.
281.24 Attorney General’s statement.
Subpart C—Criteria for No Less Stringent
Sec.
281.30 New UST system design,
construction, installation, and
notification.
281.31 Upgrading existing UST systems.
281.32 General operating requirements.
281.33 Release detection.
281.34 Release reporting, investigation, and
confirmation.
281.35 Release response and corrective
action.
281.36 Out-of-service UST systems and
closure.
281.37 Financial responsibility for UST
systems containing petroleum.
281.38 Lender liability.
281.39 Operator training.
Subpart D—Adequate Enforcement of
Compliance
Sec.
281.40 Requirements for compliance
program and authority.
281.41 Requirements for enforcement
authority.
281.42 Requirements for public
participation.
281.43 Sharing of information.
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Subpart E—Approval Procedures
Sec.
281.50 Approval procedures for state
programs.
281.51 Revision of approved state
programs.
Subpart F—Withdrawal of Approval of State
Programs
Sec.
281.60 Criteria for withdrawal of approval
of state programs.
281.61 Procedures for withdrawal of
approval of state programs.
Authority: Sections 2002, 9004, 9005, 9006
of the Solid Waste Disposal Act, as amended
by the Resource Conservation and Recovery
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approved program. EPA retains
authority to take enforcement action in
approved states as necessary and will
notify the designated lead state agency
of any such intended action.
§ 281.10
§ 281.12
Purpose.
(a) This part specifies the
requirements that state programs must
meet for approval by the Administrator
under § 9004 of the Solid Waste
Disposal Act, and the procedures EPA
will follow in approving, revising and
withdrawing approval of state programs.
(b) State submissions for program
approval must be in accordance with
the procedures set out in this part.
(c) A state may apply for approval
under this part at any time after the
promulgation of release detection,
prevention, and corrective action
regulations under § 9003 of the Solid
Waste Disposal Act.
(d) Any state program approved by
the Administrator under this part shall
at all times be conducted in accordance
with the requirements of this part.
§ 281.11
General Requirements.
(a) State Program Elements. The
following substantive elements of a state
program must be addressed in a state
application for approval:
(1) Requirements for all existing and
new underground storage tanks:
(i) New UST systems (design,
construction, installation, and
notification);
(ii) Upgrading of existing UST
systems;
(iii) General operating requirements;
(iv) Release detection;
(v) Release reporting, investigation,
and confirmation;
(vi) Out-of-service USTs and closure;
(vii) Release response and corrective
action;
(viii) Financial responsibility for UST
systems containing petroleum; and
(ix) Operator training.
(2) Provisions for adequate
enforcement of compliance with the
above program elements.
(b) Final Approval. The state must
demonstrate that its requirements under
each state program element for existing
and new UST systems are no less
stringent than the corresponding federal
requirements as set forth in subpart C of
this part. The state must also
demonstrate that it has a program that
provides adequate enforcement of
compliance with these requirements.
(c) States with programs approved
under this part are authorized to
administer the state program in lieu of
the federal program and will have
primary enforcement responsibility with
respect to the requirements of the
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Scope and Definitions.
(a) Scope
(1) The Administrator may approve
either partial or complete state
programs. A ‘‘partial’’ state program
regulates either solely UST systems
containing petroleum or solely UST
systems containing hazardous
substances. If a ‘‘partial’’ state program
is approved, EPA will administer the
remaining part of the program. A
‘‘complete’’ state program regulates both
petroleum and hazardous substance
tanks.
(2) EPA will administer the UST
program in Indian country, except
where Congress has clearly expressed an
intention to grant a state authority to
regulate petroleum and hazardous
substance USTs in Indian country. In
either case, this decision will not impair
a state’s ability to obtain program
approval for petroleum and/or
hazardous substances in non-Indian
country in accordance with this part.
(3) Nothing in this subpart precludes
a state from:
(i) Adopting or enforcing
requirements that are more stringent or
more extensive than those required
under this part; or
(ii) Operating a program with a greater
scope of coverage than that required
under this part. Where an approved
state program has a greater scope of
coverage than required by federal law,
the additional coverage is not part of the
federally-approved program.
(b) Definitions
(1) The definitions in part 280 apply
to this entire part.
(2) For the purposes of this part the
term ‘‘final approval’’ means the
approval received by a state program
that meets the requirements in
§ 281.11(b).
Subpart B—Components of a Program
Application
§ 281.20
Program Application.
Any state that seeks to administer a
program under this part must submit an
application containing the following
parts:
(a) A transmittal letter from the
Governor of the state requesting
program approval;
(b) A description in accordance with
§ 281.21 of the state program and
operating procedures;
(c) A demonstration of the state’s
procedures to ensure adequate
enforcement;
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(d) A Memorandum of Agreement
outlining roles and responsibilities of
EPA and the implementing agency;
(e) An Attorney General’s statement in
accordance with § 281.25 certifying to
applicable state authorities; and
(f) Copies of all applicable state
statutes and regulations.
Note to § 281.20: EPA has designed an
optional application form that is available for
use by state applicants.
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§ 281.21
Description of State Program.
A state seeking to administer a
program under this part must submit a
description of the program it proposes
to administer under state law in lieu of
the federal program. The description of
a state’s existing or planned program
must include:
(a) The scope of the state program:
(1) whether the state program
regulates UST systems containing
petroleum or hazardous substances, or
both;
(2) whether the state program is more
stringent or broader in scope than the
federal program, and in what ways; and
(3) whether the state has any existing
authority over Indian lands or has
existing agreements with Indian Tribes
relevant to the regulation of
underground storage tanks.
(b) The organization and structure of
the state and local agencies with
responsibility for administering the
program. The jurisdiction and
responsibilities of all state and local
implementing agencies must be
delineated, appropriate procedures for
coordination set forth, and one state
agency designated as a ‘‘lead agency’’ to
facilitate communications between EPA
and the state.
(c) Staff resources to carry out and
enforce the required state program
elements, both existing and planned,
including the number of employees,
agency where employees are located,
general duties of the employees, and
current limits or restrictions on hiring or
utilization of staff.
(d) An existing state funding
mechanism to meet the estimated costs
of administering and enforcing the
required state program elements, and
any restrictions or limitations upon this
funding.
§ 281.22 Procedures for Adequate
Enforcement.
A state must submit a description of
its compliance monitoring and
enforcement procedures, including
related state administrative or judicial
review procedures.
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§ 281.23
Memorandum of Agreement.
EPA and the approved state will
negotiate a Memorandum of Agreement
(MOA) containing proposed areas of
coordination and shared responsibilities
between the state and EPA and separate
EPA and state roles and responsibilities
in areas including, but not limited to:
Implementation of partial state
programs; enforcement; compliance
monitoring; EPA oversight; and sharing
and reporting of information. At the
time of approval, the MOA must be
signed by the Regional Administrator
and the appropriate official of the state
lead agency.
§ 281.24
Attorney General’s Statement.
(a) A state must submit a written
demonstration from the Attorney
General that the laws and regulations of
the state provide adequate authority to
carry out the program described under
§ 281.21 and to meet other requirements
of this part. This statement may be
signed by independent legal counsel for
the state rather than the Attorney
General, provided that such counsel has
full authority to independently
represent the state Agency in court on
all matters pertaining to the state
program. This statement must include
citations to the specific statutes,
administrative regulations, and where
appropriate, judicial decisions that
demonstrate adequate authority to
regulate and enforce requirements for
UST systems. State statutes and
regulations cited by the state Attorney
General must be fully effective when the
program is approved.
(b) If a state currently has authority
over underground storage tank activities
on Indian country, the statement must
contain an appropriate analysis of the
state’s authority.
Subpart C—Criteria for No Less
Stringent
§ 281.30 New UST System Design,
Construction, Installation, and Notification.
In order to be considered no less
stringent than the corresponding federal
requirements for new UST system
design, construction, installation, and
notification, the state must have
requirements that ensure all new
underground storage tanks, and the
attached piping in contact with the
ground and used to convey the
regulated substance stored in the tank,
conform to the following:
(a) Be designed, constructed, and
installed in a manner that will prevent
releases for their operating life due to
manufacturing defects, structural
failure, or corrosion. Unless the state
requires manufacturer and installer
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financial responsibility and installer
certification in accordance with
§ 9003(i)(2) of the Solid Waste Disposal
Act, then the state must meet the
following:
(1) Tanks and piping replaced or
installed after the state’s submission of
its state program approval or revision
application must use interstitial
monitoring within secondary
containment in accordance with
§ 9003(i)(1) of the Solid Waste Disposal
Act.
(2) Motor fuel dispenser systems
installed and connected to an UST
system after the state’s submission of its
state program approval or revisions
application must be equipped with
under-dispenser containment in
accordance with § 9003(i)(1) of the Solid
Waste Disposal Act.
Note to paragraph (a): Codes of practice
developed by nationally-recognized
organizations and national independent
testing laboratories may be used to
demonstrate that the state program
requirements are no less stringent in this
area.;
(b) Be provided with equipment to prevent
spills and tank overfills when new tanks are
installed or existing tanks are upgraded,
unless the tank does not receive more than
25 gallons at one time. Flow restrictors used
in vent lines are not allowable forms of
overfill prevention when overfill prevention
is installed or replaced after the state applies
for state program approval or revision.
(c) All UST system owners and operators
must notify the implementing state agency of
the existence of any new UST system and
adequately notify the implementing state
agency within a reasonable timeframe when
assuming ownership of an UST system using
a form designated by the state agency.
§ 281.31
Upgrading UST Systems.
In order to be considered no less
stringent than the corresponding federal
upgrading requirements, the state must
have requirements that ensure UST
systems installed prior to the state
applying for state program approval or
revision meet the requirements of
§ 281.30; are upgraded to prevent
releases for their operating life due to
corrosion, and spills, and overfills; or
are permanently closed with the
following exceptions:
(a) Upgrade Requirements for
Previously Deferred UST Systems.
Previously deferred wastewater
treatment tank systems, airport hydrant
fuel distribution systems, and UST
systems with field-constructed tanks
where installation commenced before
the state’s submission of its state
program approval or revision
application must, within three years of
the effective date of this section, as
amended, or prior to the state’s
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submission of its state program approval
or revision application, whichever date
is later, meet the requirements of
§ 281.30 or be permanently closed.
(b) Upgrade Requirements for Other
UST Systems. States may allow UST
systems to be upgraded if the state
determines that the upgrade is
appropriate to prevent releases for the
operating life of the UST system due to
corrosion and spill or overfills.
§ 281.32
General Operating Requirements.
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In order to be considered no less
stringent than the corresponding federal
general operating requirements, the state
must have requirements that ensure all
new and existing UST systems conform
to the following:
(a) Prevent spills and overfills by
ensuring that the space in the tank is
sufficient to receive the volume to be
transferred and that the transfer
operation is monitored constantly;
(b) Where equipped with cathodic
protection, be operated and maintained
by a person with sufficient training and
experience in preventing corrosion, and
in a manner that ensures that no
releases occur during the operating life
of the UST system;
Note to paragraph (b): Codes of practice
developed by nationally-recognized
organizations and national independent
testing laboratories may be used to
demonstrate the state program requirements
are no less stringent.
(c) Be made of or lined with materials that
are compatible with the substance stored;
(d) At the time of upgrade or repair, be
structurally sound and upgraded or repaired
in a manner that will prevent releases due to
structural failure or corrosion during their
operating lives;
(e) Have spill and overfill prevention
equipment periodically tested in a manner
and frequency that ensures its functionality
for the operating life of the equipment and
have the integrity of secondary containment
periodically tested in a manner and
frequency that prevents releases during the
operating life of the UST system, except on
equipment not required to be tested by 40
CFR part 280.
(f) Have operation and maintenance
walkthrough inspections periodically
conducted in a manner and frequency that
ensures proper operation and maintenance
for the operating life of the UST system.
(g) Have records of monitoring, testing,
repairs, and operation and maintenance
walkthrough inspections. These records must
be made readily available when requested by
the implementing agency.
§ 281.33
Release Detection.
In order to be considered no less
stringent than the corresponding federal
requirements for release detection, the
state must have requirements that at a
minimum ensure all UST systems are
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provided with release detection that
conforms to the following:
(a) General Methods. Release
detection requirements for owners and
operators must consist of a method, or
combination of methods, that is:
(1) Capable of detecting a release of
the regulated substance from any
portion of the UST system that routinely
contains regulated substances—as
effectively as any of the methods
allowed under the federal technical
standards—for as long as the UST
system is in operation. In comparing
methods, the implementing agency shall
consider the size of release that the
method can detect and the speed and
reliability with which the release can be
detected.
(2) Designed, installed, calibrated,
operated and maintained so that
releases will be detected in accordance
with the capabilities of the method;
(3) Operated and maintained, and
electronic and mechanical components
are tested periodically, in a manner and
frequency that ensures proper operation
to detect releases for the operating life
of the release detection equipment.
(b) Phase-in of requirements. Release
detection requirements must, at a
minimum, be applied at all UST
systems, except for UST systems
previously deferred under
§ 280.10(a)(1), prior to the state’s
submission of its state program approval
or revision application. Release
detection requirements must, at a
minimum, be scheduled to be applied to
previously deferred UST systems as
follows:
(1) Immediately when a new
previously deferred UST system is
installed, and
(2) For any wastewater treatment tank
system, airport hydrant fuel distribution
system, or UST system with field
constructed tanks installed prior to the
state’s submission of its state program
approval or revision application, within
three years of the effective date of this
section, as amended, or prior to the
state’s submission of its state program
approval or revision application,
whichever date is later.
(3) For any UST system that stores
fuel solely for the use of emergency
power generators that was installed
prior to the state’s submission of its
state program approval or revision
application, within one year of the
effective date of this section, as
amended, or prior to the state’s
submission of its state program approval
or revision application, whichever date
is later.
(c) Requirements for Petroleum Tanks.
All petroleum tanks must meet the
following requirements:
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(1) All petroleum tanks must be
sampled, tested, or checked for releases
at least monthly, except that tanks (that
is, tanks and piping protected from
releases due to corrosion and equipped
with both spill and overfill prevention
devices) installed prior to the state’s
submission of its State Program
Approval or revision application may
temporarily use monthly inventory
control (or its equivalent) in
combination with tightness testing (or
its equivalent) conducted every five
years for the first 10 years after the tank
is installed; and
(2) New or replaced petroleum tanks
must use interstitial monitoring within
secondary containment in accordance
with § 9003(i)(1) of the Solid Waste
Disposal Act except when the state
requires manufacturer and installer
financial responsibility and installer
certification in accordance with
§ 9003(i)(2) of the Solid Waste Disposal
Act.
(d) Requirements for Petroleum
Piping. All underground piping
attached to the tank that routinely
conveys petroleum must conform to the
following:
(1) If the petroleum is conveyed under
greater than atmospheric pressure:
(i) The piping must be equipped with
release detection that detects a release
within an hour by restricting or shutting
off flow or sounding an alarm; and
(ii) The piping must have monthly
monitoring applied or annual tightness
tests conducted.
(2) If suction lines are used:
(i) Tightness tests must be conducted
at least once every 3 years, unless a
monthly method of detection is applied
to this piping; or
(ii) The piping is designed to allow
the contents of the pipe to drain back
into the storage tank if the suction is
released and is also designed to allow
an inspector to immediately determine
the integrity of the piping system.
(3) New or replaced petroleum piping
must use interstitial monitoring within
secondary containment in accordance
with § 9003(i)(1) of the Solid Waste
Disposal Act except when the state
requires evidence of financial
responsibility and certification in
accordance with § 9003(i)(2) of the Solid
Waste Disposal Act.
(e) Requirements for Hazardous
Substance UST Systems. All hazardous
substance UST systems must use
interstitial monitoring within secondary
containment of the tanks and the
attached underground piping that
conveys the regulated substance stored
in the tank. For hazardous substance
UST systems installed prior to the
state’s submission of its state program
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approval or revision application, owners
and operators can use another form of
release detection if the owner and
operator can demonstrate to the state (or
the state otherwise determines) that
another method will detect a release of
the regulated substance as effectively as
other methods allowed under the state
program for petroleum UST systems and
that effective corrective action
technology is available for the
hazardous substance being stored that
can be used to protect human health
and the environment.
§ 281.34 Release Reporting, Investigation
and Confirmation.
In order to be considered no less
stringent than the corresponding federal
requirements for release reporting,
investigation, and confirmation, the
state must have requirements that
ensure all owners and operators
conform with the following:
(a) Promptly investigate all suspected
releases, including:
(1) When unusual operating
conditions, release detection signals and
environmental conditions at the site
suggest a release of regulated substances
may have occurred or the interstitial
space may have been compromised; and
(2) When required by the
implementing agency to determine the
source of a release having an impact in
the surrounding area; and
(b) Promptly report all confirmed
underground releases and any spills and
overfills that are not contained and
cleaned up.
(c) Ensure that all owners and
operators contain and clean up
unreported spills and overfills in a
manner that will protect human health
and the environment.
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
§ 281.35
Action.
Release Response and Corrective
In order to be considered no less
stringent than the corresponding federal
requirements for release response and
corrective action, the state must have
requirements that ensure:
(a) All releases from UST systems are
promptly assessed and further releases
are stopped;
(b) Actions are taken to identify,
contain and mitigate any immediate
health and safety threats that are posed
by a release (such activities include
investigation and initiation of free
product removal, if present);
(c) All releases from UST systems are
investigated to determine if there are
impacts on soil and ground water, and
any nearby surface waters. The extent of
soil and ground-water contamination
must be delineated when a potential
threat to human health and the
environment exists.
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(d) All releases from UST systems are
cleaned up through soil and ground
water remediation and any other steps,
as necessary to protect human health
and the environment;
(e) Adequate information is made
available to the state to demonstrate that
corrective actions are taken in
accordance with the requirements of
paragraphs (a) through (d) of this
section. This information must be
submitted in a timely manner that
demonstrates its technical adequacy to
protect human health and the
environment; and
(f) In accordance with § 280.67, the
state must notify the affected public of
all confirmed releases requiring a plan
for soil and ground water remediation,
and upon request provide or make
available information to inform the
interested public of the nature of the
release and the corrective measures
planned or taken.
§ 281.36 Out-of-Service UST Systems and
Closure.
In order to be considered no less
stringent than the corresponding federal
requirements for temporarily closed
UST systems and permanent closure,
the state must have requirements that
ensure UST systems conform with the
following:
(a) Removal from Service. All new
and existing UST systems temporarily
closed must:
(1) Continue to comply with general
operating requirements, release
reporting and investigation, and release
response and corrective action;
(2) Continue to comply with release
detection requirements if regulated
substances are stored in the tank;
(3) Be closed off to outside access; and
(4) Be permanently closed if the UST
system has not been protected from
corrosion and has not been used in one
year, unless the state approves an
extension after the owner and operator
conducts a site assessment.
(b) Permanent Closure of UST
Systems. All tanks and piping must be
cleaned and permanently closed in a
manner that eliminates the potential for
safety hazards and any future releases.
The owner or operator must notify the
state of permanent UST system closures.
The site must also be assessed to
determine if there are any present or
were past releases, and if so, release
response and corrective action
requirements must be complied with.
(c) All UST systems taken out of
service before the effective date of the
federal regulations must permanently
close in accordance with paragraph (b)
of this section when directed by the
implementing agency.
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§ 281.37 Financial Responsibility for UST
Systems Containing Petroleum.
(a) In order to be considered no less
stringent than the federal requirements
for financial responsibility for UST
systems containing petroleum, the state
requirements for financial responsibility
for petroleum UST systems must ensure
that:
(1) Owners and operators have $1
million per occurrence for corrective
action and third-party claims in a timely
manner to protect human health and the
environment;
(2) Owners and operators not engaged
in petroleum production, refining, and
marketing and who handle a throughput
of 10,000 gallons of petroleum per
month or less have $500,000 per
occurrence for corrective action and
third-party claims in a timely manner to
protect human health and the
environment;
(3) Owners and operators of 1 to 100
petroleum USTs must have an annual
aggregate of $1 million; and
(4) Owners and operators of 101 or
more petroleum USTs must have an
annual aggregate of $2 million.
(b) States may allow the use of a wide
variety of financial assurance
mechanisms to meet this requirement.
Each financial mechanism must meet
the following criteria in order to be no
less stringent than the federal
requirements. The mechanism must: Be
valid and enforceable; be issued by a
provider that is qualified or licensed in
the state; not permit cancellation
without allowing the state to draw
funds; ensure that funds will only and
directly be used for corrective action
and third party liability costs; and
require that the provider notify the
owner or operator of any circumstances
that would impair or suspend coverage.
(c) States must require owners and
operators to maintain records that
demonstrate compliance with the state
financial responsibility requirements,
and these records must be made readily
available when requested by the
implementing agency.
§ 281.38
Lender Liability.
(a) A state program that contains a
security interest exemption will be
considered to be no less stringent than,
and as broad in scope as, the federal
program provided that the state’s
exemption:
(1) Mirrors the security interest
exemption provided for in 40 CFR part
280, subpart I; or
(2) Achieves the same effect as
provided by the following key criteria:
(i) A holder, meaning a person who
maintains indicia of ownership
primarily to protect a security interest in
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a petroleum UST or UST system or
facility or property on which a
petroleum UST or UST system is
located, who does not participate in the
management of the UST or UST system
as defined under § 280.10 of this
chapter, and who does not engage in
petroleum production, refining, and
marketing as defined under § 280.200(b)
of this chapter is not:
(A) An ‘‘owner’’ of a petroleum UST
or UST system or facility or property on
which a petroleum UST or UST system
is located for purposes of compliance
with the requirements of 40 CFR part
280; or
(B) An ‘‘operator’’ of a petroleum UST
or UST system for purposes of
compliance with the requirements of 40
CFR part 280, provided the holder is not
in control of or does not have
responsibility for the daily operation of
the UST or UST system.
(ii) [Reserved]
(b) [Reserved]
each day of violation. If the violation is
continuous, civil penalties shall capable
of being assessed up to $5,000 or more
for each day of violation.
(4) To prohibit the delivery, deposit,
or acceptance of a regulated substance
into an underground storage tank
identified by the state to be ineligible for
such delivery, deposit, or acceptance in
accordance with § 9012 of the Solid
Waste Disposal Act.
(b) The burden of proof and degree of
knowledge or intent required under
state law for establishing violations
under paragraph (a)(3) of this section,
must be no greater than the burden of
proof or degree of knowledge or intent
that EPA must provide when it brings
an action under Subtitle I of the Solid
Waste Disposal Act.
(c) A civil penalty assessed, sought, or
agreed upon by the state enforcement
agency(ies) under paragraph (a)(3) of
this section must be appropriate to the
violation.
§ 281.39
§ 281.42 Requirements for Public
Participation.
Operator Training.
In order to be considered no less
stringent than the corresponding federal
requirements for operator training, the
state must have an operator training
program that meets the minimum
requirements of § 9010 of the Solid
Waste Disposal Act.
Subpart D—Adequate Enforcement of
Compliance
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
§ 281.41 Requirements for Enforcement
Authority.
(a) Any state agency administering a
program must have the authority to
implement the following remedies for
violations of state program
requirements:
(1) To restrain immediately and
effectively any person by order or by
suit in state court from engaging in any
unauthorized activity that is
endangering or causing damage to
public health or the environment;
(2) To sue in courts of competent
jurisdiction to enjoin any threatened or
continuing violation of any program
requirement;
(3) To assess or sue to recover in court
civil penalties as follows:
(i) Civil penalties for failure to notify
or for submitting false information
pursuant to tank notification
requirements must be capable of being
assessed up to $5,000 or more per
violation.
(ii) Civil penalties for failure to
comply with any state requirements or
standards for existing or new tank
systems must be capable of being
assessed for each instance of violation,
up to $5,000 or more for each tank for
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Any state administering a program
must provide for public participation in
the state enforcement process by
providing any one of the following three
options:
(a) Authority that allows intervention
analogous to Federal Rule 24(a)(2), and
assurance by the appropriate state
enforcement agency that it will not
oppose intervention under the state
analogue to Rule 24(a)(2) on the ground
that the applicant’s interest is
adequately represented by the State.
(b) Authority that allows intervention
as of right in any civil action to obtain
the remedies specified in 281.41 by any
citizen having an interest that is or may
be adversely affected; or
(c) Assurance by the appropriate state
agency that:
(1) It will provide notice and
opportunity for public comment on all
proposed settlements of civil
enforcement actions (except where
immediate action is necessary to
adequately protect human health and
the environment);
(2) It will investigate and provide
responses to citizen complaints about
violations; and
(3) It will not oppose citizen
intervention when permissive
intervention is allowed by statute, rule,
or regulation.
§ 281.43
Sharing of Information.
(a) States with approved programs
must furnish EPA, upon request, any
information in state files obtained or
used in the administration of the state
program. This information includes:
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Fmt 4701
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71795
(1) Any information submitted to the
state under a claim of confidentiality.
The state must submit that claim to EPA
when providing such information. Any
information obtained from a state and
subject to a claim of confidentiality will
be treated in accordance with federal
regulations in 40 CFR part 2; and
(2) Any information that is submitted
to the state without a claim of
confidentiality. EPA may make this
information available to the public
without further notice.
(b) EPA must furnish to states with
approved programs, upon request, any
information in EPA files that the state
needs to administer its approved state
program. Such information includes:
(1) Any information that is submitted
to EPA without a claim of
confidentiality; and
(2) Any information submitted to EPA
under a claim of confidentiality, subject
to the conditions in 40 CFR part 2.
Subpart E—Approval Procedures
§ 281.50 Approval Procedures for State
Programs.
(a) The following procedures are
required for all applications, regardless
of whether the application is for a
partial or complete program, as defined
in § 281.12, or final approval in
accordance with § 281.11.
(b) Before submitting an application
to EPA for approval of a state program,
the state must provide an opportunity
for public notice and comment in the
development of its underground storage
tank program.
(c) When EPA receives a state
program application, EPA will examine
the application and notify the state
whether its application is complete, in
accordance with the application
components required in § 281.20. The
180-day statutory review period begins
only after EPA has determined that a
complete application has been received.
(d) The state and EPA may by mutual
agreement extend the review period.
(e) After receipt of a complete
program application, the Administrator
will tentatively determine approval or
disapproval of the state program. EPA
shall issue public notice of the tentative
determination in the Federal Register;
in enough of the largest newspapers in
the state to attract statewide attention;
and to persons on the state agency
mailing list and any other persons who
the agency has reason to believe are
interested. Notice of the tentative
determination must also:
(1) Afford the public 30 days after the
notice to comment on the state’s
application and the Administrator’s
tentative determination; and
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(2) Include a general statement of the
areas of concern, if the Administrator
indicates the state program may not be
approved; and
(3) Note the availability for inspection
by the public of the state program
application; and
(4) Indicate that a public hearing will
be held by EPA no earlier than 30 days
after notice of the tentative
determination unless insufficient public
interest is expressed, at which time the
Regional Administrator may cancel the
public hearing.
(f) Within 180 days of receipt of a
complete state program application, the
Administrator must make a final
determination whether to approve the
state program after review of all public
comments. EPA will give notice of its
determination in the Federal Register
and codify the approved state program.
The notice must include a statement of
the reasons for this determination and a
response to significant comments
received.
§ 281.51 Revision of Approved State
Programs.
mstockstill on DSK4VPTVN1PROD with PROPOSALS2
(a) Either EPA or the approved state
may initiate program revision. Program
revision may be necessary when the
controlling federal or state statutory or
regulatory authority is changed or when
responsibility for the state program is
shifted to a new agency or agencies. The
state must inform EPA of any proposed
modifications to its basic statutory or
regulatory authority or change in
division of responsibility among state
agencies. EPA will determine in each
case whether a revision of the approved
program is required. Approved state
programs must submit a revised
application within three years of any
changes to this part that requires a
program revision.
(b) Whenever the Administrator has
reason to believe that circumstances
have changed with respect to an
approved state program or the federal
program, the Administrator may
request, and the state must provide, a
revised application as prescribed by
EPA.
(c) The Administrator will approve or
disapprove program revisions based on
the requirements of this part and of
Subtitle I pursuant to the procedures
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under this section, or under § 281.50 if
EPA has reason to believe the proposed
revision will receive significant negative
comment from the public.
(1) The Administrator must issue
public notice of planned approval or
disapproval of a state program revision
in the Federal Register; in enough of the
largest newspapers in the state to attract
statewide attention; and by mailing to
persons on the state agency mailing list
and to any other persons who the
agency has reason to believe are
interested. The public notice must
summarize the state program revision,
indicate whether EPA intends to
approve or disapprove the revision, and
provide for an opportunity to comment
for a period of 30 days.
(2) The Administrator’s decision on
the proposed revision becomes effective
60 days after the date of publication in
the Federal Register in accordance with
paragraph (c)(1) of this section, unless
significant negative comment opposing
the proposed revision is received during
the comment period. If significant
negative comment is received, EPA
must notify the state and within 60 days
after the date of publication, publish in
the Federal Register either:
(i) A withdrawal of the immediate
final decision, which will then be
treated as a tentative decision in
accordance with the applicable
procedures of § 281.50(e) and (f); or
(ii) A notice that contains a response
to significant negative comments and
affirms either that the immediate final
decision takes effect or reverses the
decision.
(d) Revised state programs that
receive approval must be codified in the
Federal Register.
Subpart F—Withdrawal of Approval of
State Programs
§ 281.60 Criteria for Withdrawal of
Approval of State Programs.
The Administrator may withdraw
program approval when the Agency
determines that a state no longer has
adequate regulatory or statutory
authority or is not administering and
enforcing an approved program in
accordance with this part. The state
must have adequate capability to
administer and enforce the state
PO 00000
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Sfmt 9990
program. In evaluating whether such
capability exists, the Agency will
consider whether the state is
implementing an adequate enforcement
program by evaluating the quality of
compliance monitoring and
enforcement actions.
§ 281.61 Procedures for Withdrawal of
Approval of State Programs.
(a) The following procedures apply
when a state with an approved program
voluntarily transfers to EPA those
program responsibilities required by
federal law.
(1) The state must give EPA notice of
the proposed transfer, and submit, at
least 90 days before the transfer, a plan
for the orderly transfer of all relevant
program information necessary for EPA
to administer the program.
(2) Within 30 days of receiving the
state’s transfer plan, EPA must evaluate
the plan and identify any additional
information needed by the federal
government for program administration.
(3) At least 30 days before the transfer
is to occur, EPA must publish notice of
the transfer in the Federal Register; in
enough of the largest newspapers in the
state to attract statewide attention; and
to persons on appropriate state mailing
lists.
(b) The following procedures apply
when the Administrator considers
withdrawing approval.
(1) When EPA begins proceedings to
determine whether to withdraw
approval of a state program (either on its
own initiative or in response to a
petition from an interested person),
withdrawal proceedings will be
conducted in accordance with
procedures set out in 40 CFR 271.23(b)
and (c), except for § 271.23(b)(8)(iii) to
the extent that it deviates from
requirements under § 281.60.
(2) If the state fails to take appropriate
action within a reasonable time, not to
exceed 120 days after notice from the
Administrator that the state is not
administering and enforcing its program
in accordance with the requirements of
this part, EPA will withdraw approval
of the state’s program.
[FR Doc. 2011–29293 Filed 11–17–11; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 76, Number 223 (Friday, November 18, 2011)]
[Proposed Rules]
[Pages 71708-71796]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2011-29293]
[[Page 71707]]
Vol. 76
Friday,
No. 223
November 18, 2011
Part III
Environmental Protection Agency
-----------------------------------------------------------------------
40 CFR Parts 280 and 281
Revising Underground Storage Tank Regulations--Revisions to Existing
Requirements and New Requirements for Secondary Containment and
Operator Training; Proposed Rule
Federal Register / Vol. 76 , No. 223 / Friday, November 18, 2011 /
Proposed Rules
[[Page 71708]]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 280 and 281
[EPA-HQ-UST-2011-0301; FRL-9485-5]
RIN 2050-AG46
Revising Underground Storage Tank Regulations--Revisions to
Existing Requirements and New Requirements for Secondary Containment
and Operator Training
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing to make certain revisions to the 1988
underground storage tank (UST) technical, financial responsibility, and
state program approval regulations. These changes establish federal
requirements that are similar to key portions of the Energy Policy Act
of 2005; they also update certain 1988 UST regulations. Proposed
changes include: Adding secondary containment requirements for new and
replaced tanks and piping; adding operator training requirements;
adding periodic operation and maintenance requirements for UST systems;
removing certain deferrals; adding new release prevention and detection
technologies; updating codes of practice; making editorial and
technical corrections; and updating state program approval requirements
to incorporate these new changes. These changes will likely protect
human health and the environment by increasing the number of prevented
UST releases and quickly detecting them, if they occur.
DATES: Comments must be received on or before February 16, 2012. Under
the Paperwork Reduction Act, comments on the information collection
provisions are best assured of having full effect if the Office of
Management and Budget (OMB) receives a copy of your comments on or
before December 19, 2011.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
UST-2011-0301, by one of the following methods:
https://www.regulations.gov; Follow the online instructions
for submitting comments.
Email: mcdermott.elizabeth@epa.gov.
Mail: EPA Docket Center (EPA/DC), Docket ID No. EPA-HQ-
UST-2011-0301, Mail Code 2822T, 1200 Pennsylvania Ave. NW., Washington,
DC 20460. In addition, please mail a copy of your comments on the
information collection provisions to the Office of Information and
Regulatory Affairs, Office of Management and Budget (OMB), Attn: Desk
Officer for EPA, 725 17th St. NW., Washington, DC 20503.
Hand Delivery: EPA Docket Center (EPA/DC), EPA West, Room
3334, 1301 Constitution Ave. NW., Washington, DC 20460. Attention
Docket ID No. EPA-HQ-UST-2011-0301. Such deliveries are only accepted
during the Docket's normal hours of operation, and special arrangements
should be made for deliveries of boxed information.
Instructions: Direct your comments to Docket ID No. EPA-HQ-UST-
2011-0301. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://www.regulations.gov or email. The https://www.regulations.gov Web site
is an ``anonymous access'' system, which means EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an email comment directly to EPA without
going through https://www.regulations.gov your email address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, EPA recommends that you include your name
and other contact information in the body of your comment and with any
disk or CD-ROM you submit. If EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment. Electronic files should avoid
the use of special characters, any form of encryption, and be free of
any defects or viruses. For additional information about EPA's public
docket, visit the EPA Docket Center homepage at https://www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket are listed in the https://www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the Docket, EPA/DC,
EPA West, Room 3334, 1301 Constitution Ave. NW., Washington, DC. The
Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The telephone number for the Public
Reading Room is (202) 566-1744, and the telephone number for the EPA
Docket Center (EPA/DC) is (202) 566-0276.
FOR FURTHER INFORMATION CONTACT: Elizabeth McDermott, OSWER/OUST
(5401P), Environmental Protection Agency, 1200 Pennsylvania Avenue NW.,
Washington, DC 20460; telephone number: (703) 603-7175; email address:
mcdermott.elizabeth@epa.gov.
Table of Contents
I. General Information
Does this action apply to me?
What should I consider as I prepare my comments for EPA?
II. Authority
III. Background
Why is EPA changing the UST regulations?
What is the history of the UST laws and regulations?
What is the impact of this proposal?
What was EPA's process in deciding which changes to incorporate
in the regulations?
IV. Proposed Revisions to the Requirements for Owners and Operators
of Underground Storage Tanks
A. Changes To Establish Federal Requirements for Operator
Training and Secondary Containment
1. Operator Training
2. Secondary Containment
B. Additional Requirements for Operation and Maintenance
1. Walkthrough Inspections
2. Spill Prevention Equipment Tests
3. Overfill Prevention Equipment Tests
4. Secondary Containment Tests
5. Operation and Maintenance Requirements for Release Detection
Equipment
C. Addressing Deferrals
1. Emergency Power Generator UST Systems
2. Airport Hydrant Fuel Distribution Systems
3. UST Systems With Field-Constructed Tanks
4. Wastewater Treatment Tank Systems
5. Maintain Deferral for USTs Containing Radioactive Material
and Emergency Generator UST Systems at Nuclear Power Generation
Facilities Regulated by the Nuclear Regulatory Commission
D. Other Changes
1. Changes to Overfill Prevention Equipment Requirements
2. Internal Linings That Fail the Periodic Lining Inspection and
Cannot Be Repaired
3. Notification Requirements
4. Alternative Fuels and Compatibility
5. Improving Repairs
[[Page 71709]]
6. Phase Out Vapor Monitoring and Groundwater Monitoring as
Release Detection Methods
7. Interstitial Monitoring Results, Including Interstitial
Alarms, Under Subpart E
E. General Updates
1. Incorporate Newer Technologies
2. Updates to Codes of Practice Listed in the UST Regulation
3. Updates To Remove Old Upgrade and Implementation Deadlines
4. Editorial and Technical Corrections
F. Alternative Options EPA Considered
V. Updates to State Program Approval Requirements
VI. Overview of Estimated Costs and Benefits
VII. Statutory and Executive Orders
A. Executive Order 12866: Regulatory Planning and Overview and
Executive Order 13563: Improving Regulation and Regulatory Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low-Income
Populations
SUPPLEMENTARY INFORMATION:
I. General Information
Does this action apply to me?
In the table below, EPA is providing a list of potentially affected
entities. However, this proposed action may affect other entities not
listed below. The Agency's goal with this section is to provide a guide
for readers to consider regarding entities that potentially could be
affected by this action. If you have questions regarding the
applicability of this action to a particular entity, consult the person
listed in the preceding section titled FOR FURTHER INFORMATION CONTACT.
Industry Sectors Potentially Affected by the Proposed Rule
------------------------------------------------------------------------
Industry sector NAICS code
------------------------------------------------------------------------
Retail Motor Fuel Sales......... 447.
Commercial (wholesale trade, 42, 44-45, 72 (excluding 447).
retail trade, accommodation,
and food services).
Institutional (hospitals only).. 622.
Manufacturing................... 31-33.
Transportation (air, water, 481, 483-486, 48811.
truck, transit, pipeline, and
airport operations).
Communications and Utilities 5171, 2211.
(wired telecommunications
carriers; and electric power
generation, transmission, and
distribution).
Agriculture (crop and animal 111, 112.
production).
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What should I consider as I prepare my comments for EPA?
1. Submitting CBI. Do not submit this information to EPA through
https://www.regulations.gov or email. Clearly mark the part or all of
the information that you claim to be CBI. For CBI information on a disk
or CD-ROM that you mail to EPA, mark the outside of the disk or CD-ROM
as CBI and then identify electronically within the disk or CD-ROM the
specific information that is claimed as CBI. In addition to one
complete version of the comment that includes information claimed as
CBI, a copy of the comment that does not contain the information
claimed as CBI must be submitted for inclusion in the public docket.
Information so marked will not be disclosed except in accordance with
procedures set forth in 40 CFR part 2.
2. Tips for Preparing Your Comments. When submitting comments,
remember to:
Identify the rulemaking by docket number and other
identifying information (subject heading, Federal Register date and
page number).
Explain why you agree or disagree, suggest alternatives,
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If you estimate potential costs or burdens, explain how
you arrived at your estimate in sufficient detail to allow for it to be
reproduced.
Provide specific examples to illustrate your concerns and
suggest alternatives.
Explain your views as clearly as possible, avoiding the
use of profanity or personal threats.
Make sure to submit your comments by the comment period
deadline identified.
II. Authority
EPA is proposing these regulations under the authority of sections
2002, 9001, 9002, 9003, 9004, 9005, 9006, 9007, and 9009 of the Solid
Waste Disposal Act of 1970, as amended by the Resource Conservation and
Recovery Act of 1976, as amended [42 U.S.C. 6912, 6991, 6991(a),
6991(b), 6991(c), 6991(d), 6991(e), 6991(f), 6991(h), 6991(i), and
6991(k)].
III. Background
EPA is proposing certain changes to the 1988 underground storage
tank (UST) regulations in 40 CFR part 280. In addition, EPA is planning
to implement the delivery prohibition provision of the Energy Policy
Act of 2005 (hereafter called Energy Policy Act) for EPA-led
inspections, but will address that independent of today's proposal.
Finally, EPA is proposing to revise its state program approval (SPA)
requirements in 40 CFR part 281 to incorporate the changes in 40 CFR
part 280. While EPA's proposed changes to the 1988 UST regulations will
improve environmental protection, we are sensitive to future costs for
UST owners and operators and, as a result, minimized required
retrofits.
This proposal strengthens the 1988 UST regulation by increasing the
emphasis on properly operating and maintaining equipment. The 1988 UST
regulation required owners and operators have spill, overfill, and
release detection equipment in place, but did not require proper
operation and maintenance for some of that equipment. For example, EPA
required spill prevention equipment to capture drips and spills when
the delivery hose is disconnected from the fill pipe but did not
require periodic testing of that equipment. Today's proposed revisions
will require that UST equipment is operated and maintained properly,
which will improve environmental protection. These changes also
acknowledge improvements in technology over the last 20 years,
including the ability to detect releases from deferred UST systems.
[[Page 71710]]
Why is EPA changing the UST regulations?
EPA is proposing to revise the 1988 UST regulations to:
Establish federal requirements that are similar to certain
key provisions of the Energy Policy Act;
Ensure owners and operators properly operate and maintain
their UST systems;
Include updates to current technology and codes of
practices;
Make technical and editorial corrections; and
Update SPA regulation to address the proposed changes
listed above.
In 1988, EPA first promulgated the UST regulations (40 CFR part
280) to prevent, detect, and clean up petroleum releases into the
environment. The 1988 UST regulations required new UST systems to be
designed, constructed, and installed to prevent releases; existing UST
systems had to be upgraded to prevent releases. In addition, owners and
operators were required to perform release detection, demonstrate
financial responsibility, and clean up releases.
The Energy Policy Act amended Subtitle I of the Solid Waste
Disposal Act (SWDA), the statute that authorized the UST program. Key
Energy Policy Act provisions (such as secondary containment and
operator training) apply to all states receiving federal Subtitle I
money under SWDA, regardless of their state program approval status,
but do not apply in Indian country (or in states and U.S. territories
that do not meet EPA's operator training or secondary containment grant
guidelines). The U.S. has a unique legal relationship with federally
recognized Indian Tribes. This government to government relationship
includes recognizing the rights of Tribes as sovereign governments to
self-determination and acknowledging the federal government's trust
responsibility to Tribes. As a result, EPA directly implements the UST
program in Indian country.
In order to establish federal UST requirements that are similar to
the UST secondary containment and operator training requirements of the
Energy Policy Act, EPA decided to revise the 1988 UST regulations. EPA
also decided to revise the 1988 UST regulations in order to achieve
better release prevention and compliance results (see section IV.B.
Additional Requirements for Operation and Maintenance for additional
information). Today's proposed revisions also fulfill objectives in
EPA's UST Tribal Strategy (August 2006), where both EPA and Tribes
recognized the importance of requirements that ensure parity in program
implementation among states and in Indian country. Requiring secondary
containment will reduce releases to the environment by containing them
within a secondary area and detecting them before they reach the
environment. Operator training will educate UST system operators and
help them prevent releases by complying with the regulation and
performing better operation and maintenance of their UST systems.
Since the beginning of the UST program, preventing petroleum and
hazardous substance releases from UST systems into the environment has
been one of the primary goals of the program. Although EPA and our
partners have made significant progress in reducing the number of new
releases, approximately 7,000 releases are discovered each year as of
FY 2009.\1\ Lack of proper operation and maintenance of UST systems is
a main cause of new releases. Information on sources and causes of
releases shows that releases from tanks are less common than they once
were. However, releases from piping and spills and overfills associated
with deliveries have emerged as more common problems. In addition,
releases at the dispenser are one of the leading sources of releases.
Finally, data show that release detection equipment is only detecting
approximately 50 percent of releases it is designed to detect. These
problems are partly due to improper operation and maintenance (see
section IV.B. Additional Requirements for Operation and Maintenance for
a more detailed discussion of problems).2 3
---------------------------------------------------------------------------
\1\ Semi-Annual Report Of UST Performance Measures, End Of
Fiscal Year 2009, https://epa.gov/oust/cat/camarchv.htm.
\2\ Petroleum Releases At Underground Storage Tank Facilities In
Florida, Peer Review Draft, U.S. EPA/OUST, March 2005.
\3\ Evaluation Of Releases From New And Upgraded Underground
Storage Tanks, Peer Review Draft, U.S. EPA/OUST, August 2004.
---------------------------------------------------------------------------
EPA relies on two draft causes of release studies to help support
this proposed rule. Petroleum Releases at Underground Storage Tank
Facilities in Florida contains release data on 512 releases from new
and upgraded tanks in Florida.\4\ The second draft study, Evaluation of
Releases from New and Upgraded Underground Storage Tank Systems,
contains release data on 580 releases from new and upgraded tanks in 23
states across the Northeast, South, and Central parts of the United
States.\5\ Taken together, these draft studies provide information
about 1092 releases in 24 of the 50 states. The data in the two
studies, when taken as a whole, generally provide a representative
sampling of releases across the United States because nearly half of
the states contributed to the studies. Both drafts were peer reviewed
but never finalized because the passage of Energy Policy Act of 2005
required a reallocation of personnel and resources. Even though these
studies were never finalized, the underlying data and calculations can
be used to support this proposed rule because that information did not
change as a result of the peer review process.
---------------------------------------------------------------------------
\4\ Petroleum Releases At Underground Storage Tank Facilities In
Florida, Peer Review Draft, U.S. EPA/OUST, March 2005.
\5\ Evaluation Of Releases From New And Upgraded Underground
Storage Tanks, Peer Review Draft, U.S. EPA/OUST, August 2004.
---------------------------------------------------------------------------
Many USTs currently in the ground were upgraded to meet the spill,
overfill, corrosion protection, and release detection requirements in
the 1988 UST regulation. As these USTs continue to age, it is vital
that we improve UST operation and maintenance and test components to
ensure they are still working as intended. Today's proposed revisions
to the 1988 UST regulation focus on ensuring equipment is working,
rather than requiring UST owners and operators to replace or upgrade
equipment already in place. The 1988 UST regulation require owners and
operators to use equipment that could help prevent releases; today's
proposed revisions highlight the importance of operating and
maintaining UST equipment so releases are prevented and detected early
in order to avoid or minimize potential soil and groundwater
contamination.
EPA is proposing changes to the SPA regulation (40 CFR part 281) to
address today's proposed changes to 40 CFR part 280. By doing so, EPA
will require states to generally adopt the 40 CFR part 280 changes
proposed today in order to obtain or retain SPA.
What is the history of the UST laws and regulations?
In 1984, Congress responded to the increasing threat to groundwater
posed from leaking USTs by adding Subtitle I to the Solid Waste
Disposal Act (SWDA). Subtitle I of SWDA required EPA to develop a
comprehensive regulatory program for USTs storing petroleum or certain
hazardous substances, ensuring that the environment and human health
are protected from UST releases. In 1986, Congress amended Subtitle I
of SWDA and created the Leaking Underground
[[Page 71711]]
Storage Tank Trust Fund to implement a cleanup program and pay for
cleanups at sites where the owner or operator is unknown, unwilling, or
unable to respond, or which require emergency action.
In 1988, EPA promulgated the UST regulation (40 CFR part 280),
which set minimum standards for new tanks and required owners and
operators of existing tanks to upgrade, replace, or close them. In
addition, after 1988 owners and operators were required to report and
clean up releases from their USTs. The 1988 UST regulation set
deadlines for owners and operators to meet those requirements by
December 22, 1998. Owners and operators who chose to upgrade or replace
had to ensure their UST systems included spill and overfill prevention
equipment and were protected from corrosion. In addition, owners and
operators were required to monitor their UST systems for releases using
release detection (phased in during the 1990s, depending on when their
UST systems were installed). Finally, owners and operators were
required to have financial responsibility (phased in through 1998),
which ensured they have financial resources to pay for cleaning up
releases. EPA has not significantly changed the UST regulation since
1988.
In 1988, EPA also promulgated a regulation for state program
approval (40 CFR part 281). Since states are the primary implementers
of the UST program, EPA established a process where state programs
could operate in lieu of the federal program if states met certain
requirements and obtained state program approval from EPA. The state
program approval regulation describes minimum requirements states must
meet so their programs can be approved and operate in lieu of the
federal program.
In 2005, the Energy Policy Act further amended Subtitle I of SWDA.
The Energy Policy Act required states receiving Subtitle I money from
EPA meet certain requirements. EPA developed grant guidelines for
states regarding operator training, inspections, delivery prohibition,
secondary containment, financial responsibility for manufacturers and
installers, public record, and state compliance reports on government
USTs. The operator training and secondary containment requirements are
two major pieces of the Energy Policy Act that currently do not apply
in Indian country, but will apply when EPA finalizes today's proposed
regulation.
What is the impact of this proposal?
This proposal will ensure parity in program implementation among
states and in Indian country. This proposal will achieve parity by
adding certain requirements to the federal UST regulation (that would
apply in Indian country) that are similar to the operator training and
secondary containment requirements in the Energy Policy Act. This
action will also further strengthen protection of human health and the
environment from UST releases by increasing the emphasis on proper
operation and maintenance of release prevention and detection
equipment. Today's proposed revisions also reflect improvements in
technology that allow for the ability to prevent and quickly detect
releases for many tank systems that are currently deferred. The
regulatory changes proposed today impose costs to owners and operators
of existing regulated UST systems, owners and operators of certain
deferred USTs, as well as costs associated with state review of the
regulatory changes. EPA prepared an analysis of the potential
incremental costs and benefits associated with this action. This
analysis is contained in the regulatory impact analysis (RIA) titled
Assessment Of The Potential Costs, Benefits, And Other Impacts Of The
Proposed Revisions To EPA's Underground Storage Tank Regulations, which
is available in the docket for this proposal. A summary of these
impacts is provided under the Statutory Review section of this preamble
and in the table below.
Costs and Benefits of the Proposed Rule
[2008$ millions]
------------------------------------------------------------------------
7% Discount rate 3% Discount rate
------------------------------------------------------------------------
Total Annual Compliance Costs..... $210 $210
Total Annual Avoided Costs........ $300-$740 $330-$770
Net Cost (Savings) to Society..... ($530-$90) ($560-$120)
------------------------------------------------------------------------
EPA also prepared a risk assessment titled Risk Analysis to Support
Potential Revisions to Underground Storage Tank (UST) Regulations,
associated with the regulatory changes. The risk assessment examines
potential impacts to groundwater and subsequent chemical transport,
exposure and risk. It is available for review in the docket for this
proposal.
What was EPA's process in deciding which changes to incorporate in the
regulations?
After the Energy Policy Act became law, EPA recognized a need to
revise the 1988 UST regulations. The Energy Policy Act required
additional measures to protect groundwater (either with secondary
containment or financial responsibility for manufacturers and
installers) and operator training requirements in states receiving
federal Subtitle I money from EPA. However, no similar requirements
would apply in Indian country until EPA promulgates a regulation. Both
EPA and Tribes are committed to ensuring program parity between states
and in Indian country, and today's proposed regulation, when final,
will achieve this parity.
For over 20 years, the 1988 UST regulations worked well. However,
two decades of experience implementing the UST program have shown there
are a number of areas where EPA can improve the UST program and
increase environmental protection. For example, updating the regulation
to reflect current technologies and ensuring release prevention and
release detection equipment are properly operated and maintained have
surfaced as important regulatory changes.
From the start, EPA embraced an open, inclusive, and transparent
process so all UST stakeholders had an opportunity to share their ideas
and concerns. EPA recognizes concerns about costs to owners and
operators and the importance of limiting requirements for retrofits. In
developing this rule, we reached out to stakeholders involved in all
aspects of the tank program, provided multiple opportunities for
sharing ideas, and kept stakeholders informed of progress.
Using information from our extensive outreach, EPA compiled
potential proposed changes to the 1988 UST regulations. We added or
deleted items to the list of changes based on data, analysis, costs and
benefits resulting from the proposed changes, and EPA discretion.
Ultimately, EPA identified
[[Page 71712]]
the items in today's proposal as most appropriate.
IV. Proposed Revisions to the Requirements for Owners and Operators of
Underground Storage Tanks
The following sections describe EPA's proposal, starting with
requirements for operator training and secondary containment. The next
four sections address changes to the existing regulation in 40 CFR part
280, organized by topic: Additional requirements for operation and
maintenance; proposed approach for currently deferred tanks; other
changes to improve release prevention and release detection; and
general updates to the 1988 UST regulation. Finally, there is a section
describing alternative options considered.
After each proposed regulatory change, EPA poses some questions to
which readers may wish to respond. In addition to these specific
questions, readers may provide comments to any other area of the
proposal on which they wish to comment.
A. Changes To Establish Federal Requirements for Operator Training and
Secondary Containment
1. Operator Training
What is EPA proposing?
EPA is proposing to add a new subpart, subpart J--Operator
Training, to 40 CFR part 280. Through subpart J, EPA is proposing the
following training requirements for three UST system operator classes.
New Definitions
EPA is proposing the following new terms and definitions:
Class A operator--individual with primary responsibility
for operating and maintaining an UST system according to applicable
requirements established by the implementing agency. The Class A
operator typically manages resources and personnel, such as
establishing work assignments, to achieve and maintain compliance with
regulatory requirements.
Class B operator--individual with day-to-day
responsibility for implementing applicable regulatory requirements
established by the implementing agency. The Class B operator typically
implements in the field aspects of operation, maintenance, and
associated recordkeeping for an UST system.
Class C operator--employee responsible for initially
addressing emergencies presented by a spill or release from an UST
system. The Class C operator typically controls or monitors dispensing
or sale of regulated substances.
Training program--any program established by the
implementing agency that provides information to and evaluates the
knowledge of a Class A, Class B, or Class C operator regarding
requirements for UST systems.
Training Requirements
How operators are designated--UST owners and operators
must designate individuals for each of the three operator classes. UST
owners and operators must designate at least one Class A and one Class
B operator for each UST or group of USTs at a facility. UST owners and
operators must designate all of their employees who meet the Class C
operator definition as Class C operators.
Who must be trained--This proposed training requirement
covers all UST systems storing regulated substances. UST owners and
operators must ensure designated individuals meet specific training
requirements according to the operator class in which they are
designated.
Requirements for operator training--UST owners and
operators must ensure operators in each class successfully complete
training programs or comparable examinations that, at a minimum, cover
these areas:
[cir] Class A operator--spill and overfill prevention; release
detection; corrosion protection; emergency response; product and
equipment compatibility; financial responsibility; notification and
storage tank registration; temporary and permanent closure; related
reporting and recordkeeping; environmental and regulatory consequences
of releases; and training requirements for Class B and C operators.
Training for Class A operators is general on all listed areas.
[cir] Class B operator--operation and maintenance; spill and
overfill prevention; release detection and related reporting; corrosion
protection and related testing; emergency response; product and
equipment compatibility; reporting and recordkeeping; environmental and
regulatory consequences of releases; and training requirements for
Class C operator. Training for Class B operators may be general or
specific to a Class B operator's site.
[cir] Class C operator--appropriate action to take in response to
emergencies (including situations posing an immediate danger or threat
to the public or environment and that require immediate action) or
alarms caused by spills or releases from an UST system. Training for
Class C operators may be general or specific to a Class C operator's
site.
Training programs for Class A and B operators must, at a
minimum, teach and evaluate their knowledge on the purpose, methods,
and functions of items listed in the minimum training areas above.
Training programs for Class C operators must teach and evaluate their
knowledge of the items listed in the minimum training areas above.
A training program must meet the minimum requirements
discussed above and evaluate knowledge through a test, practical
demonstration, or another approach acceptable to the implementing
agency. In lieu of a training program, all three operator classes must
pass comparable examinations that assess their knowledge in the minimum
training areas above.
The evaluation component of training programs and
comparable examinations must be developed and administered by an
independent organization, the implementing agency, or delegated
authority.
When designated operators must complete operator
training--UST owners and operators must ensure all designated Class A,
B, and C operators are trained or successfully complete a comparable
examination according to criteria and within time frames in the
schedule below. Phase in is based on when USTs were installed because
newer UST systems tend to have fewer releases than older UST
systems.\6\
---------------------------------------------------------------------------
\6\ Evaluation Of Releases From New And Upgraded Underground
Storage Tanks, Peer Review Draft, U.S. EPA/OUST, August 2004.
[[Page 71713]]
Phase-In Schedule for Operator Training
----------------------------------------------------------------------------------------------------------------
Criteria Date when operator training or comparable examination is required
----------------------------------------------------------------------------------------------------------------
One or more USTs at the facility were One year after effective date of rule.
installed on or before 12/22/1988.
No USTs at the facility were installed on Two years after effective date of rule.
or before 12/22/1988 and at least one
UST at the facility was installed on or
before 12/22/1998.
All USTs at the facility were installed Three years after effective date of rule.
after 12/22/1998.
----------------------------------------------------------------------------------------------------------------
After the last date in the table above, UST owners and operators
must ensure designated Class A and B operators are trained within 30
days of assuming duties. Designated Class C operators must be trained
before assuming their duties.
Retraining--Class A and B operators of UST systems
determined by the implementing agency to be out of compliance must
complete a training program or comparable examination in accordance
with requirements in Sec. 280.242. At a minimum, training must cover
the area(s) determined to be out of compliance. Retraining must occur
within 30 days from the date an implementing agency determines an UST
system is out of compliance. Retraining is not required if:
[cir] Class A and B operators take annual refresher training which
covers all applicable training requirements for their operator class;
or
[cir] The implementing agency, at its discretion, grants a waiver
relinquishing the Class A and B operators from meeting the retraining
requirement.
Documentation--UST owners and operators must maintain
documents that identify all operators by class and demonstrate that
training or retraining, if necessary, was completed. These documents
must contain:
[cir] A list of designated Class A, B, and C operators for each UST
facility--Include names, operator class trained, date assumed duties,
date completed initial training, and date of any retraining. These
records must be maintained for all Class A, B, and C operators at the
facility for the previous three years.
[cir] Proof of training or retraining--A paper or electronic record
that, at a minimum, includes name of trainee, date trained, and
operator class. In addition, records from classroom or field training
programs or a comparable examination, must be signed by the trainer or
examiner and include the printed name of the trainer or examiner,
company name, address, and phone number. Records from computer-based
training, at a minimum, must include the name of the training program
and web address, if Internet-based. Records of retraining must include
those areas on which the Class A or B operator was retrained. Records
of training or retraining must be maintained as long as the Class A,
Class B, and Class C operators are designated at the facility.
Why is EPA proposing this change? What background information is
available about this change?
EPA is proposing operator training requirements to ensure that all
regulated UST systems are operated by properly trained individuals. The
operator training provision of the Energy Policy Act requires state
implementing agencies, as a condition of receiving federal Subtitle I
money, develop state-specific training requirements for three classes
of UST system operators. EPA issued grant guidelines that provide
minimum requirements state operator training programs must include in
order for states to continue receiving federal Subtitle I money.\7\ The
operator training grant guidelines apply to most UST systems in the
United States; however, not all are covered. UST systems not covered
include those in Indian country where EPA is the primary implementing
agency, and in states and territories that do not meet the requirements
of EPA's operator training grant guidelines.
---------------------------------------------------------------------------
\7\ Grant Guidelines To States For Implementing The Operator
Training Provision Of The Energy Policy Act Of 2005: https://www.epa.gov/oust/fedlaws/optraing.htm.
---------------------------------------------------------------------------
Through today's proposal, EPA is closing the gap in coverage and
ensuring all operators are trained according to their level of
responsibility, as designated as Class A, B, or C. Sufficiently
training UST operators will increase compliance with regulatory
requirements. In addition, operator training may decrease UST system
releases by educating Class A, B, and C operators about their UST
system requirements, and may result in greater protection of human
health and the environment.
Today's proposed operator training regulation for UST owners and
operators is consistent with the requirements in EPA's operator
training grant guidelines for states. In both, EPA establishes minimum
operator training requirements, yet allows flexibility to tailor
training programs for specific needs. This means that although there
may be variations among operator training programs, all Class A, B, and
C operators will be trained to meet minimum requirements.
Definitions--EPA is proposing specific definitions of the three
operator classes to distinguish them from the term operator defined in
the 1988 UST regulation. Only if a Class A, B, or C operator meets the
definition of operator in the 1988 UST regulation will he or she then
be subject to the same responsibilities and liabilities as an operator.
EPA's proposed definitions of Class A, B, and C operators do not
relieve owners and operators, as defined in the 1988 UST regulation,
from any legal responsibility. EPA based the proposed three operator
class definitions on duties each typically performs at UST facilities.
EPA is proposing a definition for training program. It is important
that training programs for Class A, B, and C operators include both
sharing information and evaluating knowledge.
How operators are designated--EPA is proposing how UST owners and
operators designate the three operator classes for their facilities.
EPA is taking the position that designating at least one Class A and B
operator at each facility is sufficient. Class A and B operators can
provide adequate training to Class C operators, which should ease UST
owners' and operators' ability to comply with this requirement. Because
a Class C operator's duties typically place him or her in a position of
providing initial response to an emergency, any UST owner's and
operator's employee who meets the Class C operator definition must be
designated as such and trained in emergency response.
EPA will allow UST owners and operators to designate contractors as
their Class A and B operators as long as they are responsible for all
areas required in the training for the class of operator designated.
UST owners and operators must maintain documentation containing
individual names of Class A and B contractors who complete operator
training. It will be easier for implementing agencies to verify
training, retraining, and refresher training using individual names
rather
[[Page 71714]]
than company names. All Class C operators must be employees of the UST
system owner and operator.
EPA wants to ensure Class A and B operator training addresses all
components and encompasses the entire UST system. If an UST system is
out of compliance and the implementing agency determines retraining is
required, Class A or B operators must either be retrained or take
annual refresher training. EPA cautions UST owners and operators to
consider whether contractors serving as Class A or B operators can be
designated. Because some contractors specialize in UST services, they
might not be eligible to be Class A or B operators. For example, if a
contractor is only responsible for release detection compliance, that
contractor would not be eligible to be a Class A or B operator because
he or she is not responsible for all required training areas.
EPA realizes many UST owners and operators may want to designate
one person at an UST facility as responsible for all Class A, B, and C
operator duties. EPA will allow one person to serve in multiple
operator classes; however, that person must be trained for each class
designated.
Who must be trained--When final, today's proposal will require
training for designated Class A, B, and C operators at UST systems
regulated under Subtitle I. This includes UST systems of all attended
and unattended facilities. An unattended UST facility means a Class A,
B, or C operator may not be present during times when a facility is
operating. Nonetheless, even at unattended UST facilities, designated
Class A, B, and C operators must still meet the operator training
requirement.
Requirements for operator training--EPA based the three operator
classes on duties each typically performs at UST facilities. Building
on that, EPA is proposing each person designated in an operator class
pass an examination comparable to the training program, or meet a
specific training program, which will:
For Class A operator, teach and evaluate his or her
knowledge to make informed decisions regarding compliance and determine
whether appropriate people are fulfilling the operation, maintenance,
and recordkeeping requirements for UST systems.
For Class B operator, teach and evaluate his or her
knowledge and skills to implement UST regulatory requirements on
typical UST system components or site-specific equipment at the UST
facility.
For Class C operator, teach and evaluate his or her
knowledge to take appropriate action in response to emergencies
(including situations posing an immediate danger or threat to the
public or environment and that require immediate action) or alarms
caused by spills or releases from an UST system.
For each class of operator, EPA considered developing specific
training curricula that would prescribe length of training, areas to
cover, and trainer qualifications. EPA decided that providing the
general criteria requirements presented in today's proposal is the best
approach because they provide flexibility while being comparable to
EPA's operator training grant guidelines for states and ensuring each
class of operator is trained.
EPA proposes not to restrict who may develop and administer the
training component of a training program. However, to avoid potential
conflicts of interest, EPA proposes to only allow independent
organizations to develop and administer the evaluation component
training programs and comparable examinations, as long as they meet the
minimum requirements in today's proposal. EPA considers independent
organizations to include a wide array of program providers who are not
affiliated with the Class A, B, or C operators they are training. For
example, Class A or B operators can train other Class A or B operators
at the same UST facility, but they cannot develop or conduct the
evaluation component of the training program for those operators.
However, as discussed earlier, Class A or B operators can train and
evaluate Class C operators. In addition, the implementing agency may
develop and administer a training program or comparable examination.
Although not specifically listed in the regulation, EPA will allow
a variety of ways to train operators. These include classroom,
computer-based, hands on, and any combination of these.
Accepted in lieu of completing a training program, Class A, B, or C
operators can pass a comparable examination (for example, via
classroom, Internet, or computer program) that meets the requirements
for operator training criteria described in today's proposal.
When designated operators must complete operator training--EPA is
proposing that UST owners and operators ensure all Class A, B, and C
operators successfully complete a training program or a comparable
examination over three years, based on UST installation dates. This
phased-in approach will stagger the need for operator training and
reduce a rush at the end of the initial three year period. Since older
USTs potentially pose a greater risk to the environment, EPA decided
Class A, B, and C operators of those systems should be trained first.
After the initial three year phase-in period and for consistency
with EPA's operator training grant guidelines for states, EPA is
proposing new Class A, B, and C operators be trained as follows:
Class A and B operators must be trained within 30 days of
assuming duties. 30 days are sufficient for Class A and B operators to
receive operator training.
Class C operators must be trained before they assume their
duties; it is critical that they are trained immediately in order to
respond to emergencies.
Retraining--UST system noncompliance can be an indication that
Class A and B operators are not doing what is necessary to maintain
compliance. If an UST system is out of compliance, then generally,
Class A and B operators designated for that UST system need to be
retrained. Retraining must, at a minimum, cover those areas determined
by the implementing agency to be out of compliance. Retraining must be
completed within 30 days of the implementing agency making a final
determination of noncompliance. EPA is proposing to allow annual
refresher training in lieu of retraining as long as all training areas
required by regulation are covered. Refresher training must have been
in place at the time the implementing agency determined the UST system
was out of compliance.
EPA is also proposing to allow implementing agencies, at their
discretion, to waive the retraining requirement. EPA recommends that
such a waiver be in writing. In granting a waiver, EPA expects the
implementing agency to consider factors such as the severity and areas
of noncompliance. In those instances where UST system noncompliance
violations do not warrant retraining, EPA encourages implementing
agencies to provide information to Class A and B operators so they are
able to return their facilities to compliance. These allowances will
provide greater flexibility for UST owners and operators to meet the
retraining requirement. This proposal is consistent with EPA's
retraining requirement for noncompliance with significant operational
compliance requirements and an annual refresher training allowance
provided in our operator training grant guidelines for states.
EPA considered requiring retraining when UST facilities change
equipment,
[[Page 71715]]
but decided this would be an unnecessary burden on both the regulated
community and implementing agencies. If an UST system is out of
compliance because of an equipment change, EPA is proposing that the
implementing agency require that UST owners and operators ensure Class
A and B operators are retrained as proposed above.
Documentation--EPA is proposing UST owners and operators maintain a
list of Class A, B, and C operators at each UST facility for the
previous three years. Keeping this list for three years is adequate
because it is consistent with the inspection frequency provided by the
Energy Policy Act. Owners and operators must have a list of trained
operators for the past three years each time they are inspected. In
addition, UST owners and operators must also document verification of
training or retraining, as appropriate, for each class of operator. EPA
will require basic information to document Class A, B, and C operators
and confirm they are appropriately trained. For example, classroom
training must be signed by the trainer; computer based training does
not require a signature but must indicate the name of the training.
Records verifying training or retraining must be maintained as long as
the Class A, B, and C operators are designated at the facility. This
time frame will allow owners and operators to demonstrate Class A, B,
and C operators are trained as long as they are designated at the
facility.
What issues related to this change does EPA request comment or
additional data on?
Should EPA impose a limit on the number of USTs or
facilities a Class A or B operator is responsible for? If so, what
should the limit be and why?
EPA is seeking information about the number of unattended
regulated UST facilities in the United States. How many regulated UST
facilities are unattended in the United States?
EPA is basing the initial period for meeting the training
requirement on the UST installation date. Should we consider other
criteria? If so, what and why?
Is there a need for a phased-in schedule for operator
training? If so, is EPA's proposed schedule reasonable?
Does EPA's proposal prohibit training approaches currently
available? If so, which ones and why?
Should EPA prohibit particular training approaches? If so,
which ones and why?
Although operators can access any available information
source to obtain necessary knowledge of UST systems, in order to
address potential conflicts of interest concerns, only independent
organizations are allowed to develop and administer the evaluation
component of training programs and comparable examinations. Are there
cases where EPA should consider exceptions to this proposed
requirement?
Please provide reasoning or justification if you disagree with or
propose something different from EPA's proposal.
2. Secondary Containment
What is EPA proposing?
EPA is proposing to add in 40 CFR part 280 secondary containment
and interstitial monitoring requirements for new and replaced tanks and
piping. In addition, UST systems must have under-dispenser containment
for new dispenser systems.
New Definitions
EPA is proposing the following new terms and definitions:
Dispenser system--Equipment located above ground that
meters the amount of regulated substances transferred to a point of use
outside the UST system, such as a motor vehicle. This system includes
equipment necessary to connect the dispenser to the UST system.
Replaced--
[cir] For a tank: To remove a tank and install another tank.
[cir] For piping: To remove 50 percent or more of piping and
install other piping, excluding connectors, connected to a single tank.
For tanks with multiple piping runs, this definition applies
independently to each piping run.
Secondary containment or secondarily contained--A release
prevention and release detection system for a tank and/or piping. This
system has an inner and outer barrier with an interstitial space that
is monitored for leaks.
Under-dispenser containment (UDC)--Containment underneath
a dispenser system designed to prevent dispenser system leaks from
reaching soil or groundwater.
Secondary Containment
EPA is proposing owners and operators install secondary containment
(including interstitial monitoring) for new or replaced tanks and
piping installed after the effective date of the final UST regulation.
EPA is not proposing secondary containment for the following types of
piping:
Suction piping that meets the requirements of Sec.
280.41(b)(2)(i) through (v), sometimes called safe suction piping; and
Piping associated with field-constructed tanks and airport
hydrant fuel distribution systems.
EPA is proposing secondarily contained tanks and piping be:
Able to contain regulated substances leaked from the
primary containment until they are detected and removed;
Able to prevent release of regulated substances to the
environment at any time during the operational life of the UST system;
and
Monitored for a leak at least once every 30 days using
interstitial monitoring according to Sec. 280.43(g).
In addition to the requirements above, pressurized piping must have
an automatic line leak detector according to Sec. 280.44(a).
EPA is proposing to remove the option in Sec. 280.42 for owners
and operators to use a release detection method other than interstitial
monitoring for hazardous substance USTs installed after the effective
date of the final UST regulation.
Under-Dispenser Containment
EPA is proposing owners and operators install under-dispenser
containment beneath new dispenser systems at UST systems. EPA will
incorporate this new requirement by adding a new subsection (f) to
Sec. 280.20, which will require under-dispenser containment beneath
each new dispenser system at an UST system.
EPA is proposing a dispenser system be considered new when both the
dispenser system and equipment needed to connect the dispenser system
to the UST system are installed at an UST facility. The equipment
connecting the dispenser system to the UST system includes check
valves, shear valves, unburied risers or flexible connectors, or other
transitional components beneath the dispenser that connect it to
underground piping. Finally, under-dispenser containment must be liquid
tight on its sides, bottom, and at any penetrations and allow for
visual inspection and access to the components in the containment
system, or must be continuously monitored for leaks from the dispenser
system.
Why is EPA proposing this change? What background information is
available about this change?
EPA is proposing this change to prevent regulated substances from
reaching the environment and ensure a consistent level of environmental
protection for regulated UST systems across the United States. Data
from
[[Page 71716]]
release sites show a higher number of releases from single-walled tanks
and piping when compared to secondarily contained systems.\8 9\
Releases could be reduced for tanks and piping if they are secondarily
contained.
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\8\ Petroleum Releases At Underground Storage Tank Facilities In
Florida, Peer Review Draft, U.S. EPA/OUST, March 2005.
\9\ Evaluation Of Releases From New And Upgraded Underground
Storage Tanks, Peer Review Draft, U.S. EPA/OUST, August 2004.
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The Energy Policy Act requires state implementing agencies, as a
condition of receiving federal Subtitle I money, implement additional
measures to protect groundwater. Under the law, state implementing
agencies' choices to protect groundwater were secondary containment
(including under-dispenser containment) or financial responsibility for
manufacturers and installers (and installer certification). 54 of 56
state implementing agencies chose secondary containment. The Energy
Policy Act did not specifically require additional measures to protect
groundwater in Indian country. As the primary implementer for more than
2,600 UST systems in Indian country, \10\ EPA is proposing secondary
containment for new and replaced tanks and piping along with under-
dispenser containment beneath all new dispenser systems at UST systems.
Over the last seven years, approximately 25 new UST systems per year
were installed in Indian country.\11\ The final UST regulation will
bring UST systems in Indian country to the same level of environmental
protection as those regulated by states.
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\10\ Semi-Annual Report Of UST Performance Measures, End Of
Fiscal Year 2009, https://epa.gov/oust/cat/camarchv.htm.
\11\ E2, Incorporated, memoranda and analyses submitted under
Contract EP-W-05-018, ``U.S. Environmental Protection Agency.
Underground Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.'' These supporting materials can
be found in the docket for the proposed rulemaking.
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The Energy Policy Act requires states that receive federal Subtitle
I money (and that choose the secondary containment option) to have
secondary containment and under-dispenser containment for tanks,
piping, and dispensers only if they are installed or replaced within
1,000 feet of an existing community water system or potable drinking
water well.\12\ However, EPA is proposing all new and replaced tanks
and piping have secondary containment and UST systems have under-
dispenser containment beneath all new dispenser systems for the
following reasons:
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\12\ Title XV, subtitle B, Section 1530 of Energy Policy Act of
2005, 109th Congress Public Law 58, August 8, 2005.
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Nearly all new and replaced tanks and piping are installed
within 1,000 feet of an existing community water system or potable
drinking water well. We assume that any UST listed with a commercial
ownership type (i.e., gas station) is located within 1,000 feet of an
on-site well or public water line because nearly all commercially-owned
facilities with USTs require water utilities in order to operate and
all privately owned facilities (i.e., fleet fueling for non-marketers)
are also assumed to be in close proximity to some type of water supply
given that these sites are typically combined with other functional
operations (office, maintenance, manufacturing, etc.) and require water
for restrooms, water fountains, shops, etc.;\13\
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\13\ E2, Incorporated, memoranda and analyses submitted under
Contract EP-W-05-018, ``U.S. Environmental Protection Agency.
Underground Storage Tanks/Leaking Underground Storage Tanks
Analytical And Technical Support.'' These supporting materials can
be found in the docket for the proposed rulemaking.
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Some state implementing agencies that require secondary
containment only within 1,000 feet of one of these water sources have
informed EPA that installations of single-walled tanks or piping are
not occurring; and
Secondary containment and under-dispenser containment will
help protect other sensitive areas, such as designated source water
protection areas, natural springs, and surface waters.
EPA is not proposing secondary containment for piping that meets
the requirements of 280.41(b)(2)(i) through (v), sometimes called safe
suction piping because it is currently not required to meet release
detection requirements. This type of piping uses a suction pump to
deliver regulated substances from the UST to the dispenser. Safe
suction piping operates at less than atmospheric pressure, slopes back
towards the UST so regulated substances drain to the UST if suction is
lost, and has only one check valve located close to the suction pump.
As discussed in the 1988 UST regulation preamble, these characteristics
ensure that little, if any, regulated substances will be released if a
break occurs in the line.\14\
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\14\ Preamble to 40 CFR part 280, FR Vol. 53, No. 185, Friday,
September 23, 1988, p. 37154.
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EPA is not proposing secondary containment for piping associated
with field-constructed tanks and airport hydrant fuel distribution
systems. EPA understands this piping typically is larger diameter and
runs for long distances, making it difficult to slope the piping back
to an interstitial monitoring area. In addition, EPA understands it is
difficult to keep water out of the interstitial area of these long
piping runs. Since nearly all this piping is steel, corrosion can occur
in the interstitial area when an electrolyte, such as water, is in the
interstitial area. This corrosion can significantly shorten the
piping's life. Corrosion protection safeguards piping in contact with
the ground, but does not protect the inside part of piping from
corrosion. To prevent corrosion caused by water in the interstitial
area, owners and operators would need to add corrosion protection
inside the interstitial area of piping, which EPA realizes would be
difficult, if not impossible, to do. Given all of these issues,
secondary containment for these piping runs could potentially reduce
environmental protection.
EPA is proposing owners and operators install tank and piping
secondary containment that: will contain regulated substances leaked
from the primary containment until they are detected and removed; is
able to prevent the release of regulated substances to the environment
at any time during the operational life of the UST system; and is
monitored for a leak at least once every 30 days using interstitial
monitoring. These requirements are consistent with the 1988 UST
regulation for secondarily contained hazardous substance tanks (Sec.
280.42) and are necessary to help preven