[Federal Register: January 14, 2008 (Volume 73, Number 9)]
[Rules and Regulations]
[Page 2146-2156]
From the Federal Register Online via GPO Access [wais.access.gpo.gov]
[DOCID:fr14ja08-3]
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DEPARTMENT OF HOMELAND SECURITY
Coast Guard
33 CFR Part 137
[Docket No. USCG-2006-25708]
RIN 1625-AB09
Landowner Defenses to Liability Under the Oil Pollution Act of
1990: Standards and Practices for Conducting All Appropriate Inquiries
AGENCY: Coast Guard, DHS.
ACTION: Final rule.
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SUMMARY: The Coast Guard is establishing standards and practices
concerning the ``all appropriate inquiries'' element of a defense to
liability of an owner or operator of a facility that is the source of a
discharge or substantial threat of discharge of oil into the navigable
waters or adjoining shorelines or the exclusive economic zone. To be
entitled to the defense, those persons must show, among other elements
not addressed in this rulemaking, that, before acquiring the real
property on which the facility is located, they had made all
appropriate inquiries into its previous ownership and uses to determine
the presence or likely presence of oil. This rule is consistent with a
final rule on this subject published by the Environmental Protection
Agency.
DATES: This final rule is effective February 13, 2008.
ADDRESSES: Comments and material received from the public, as well as
documents mentioned in this preamble as being available in the docket,
are part of docket USCG-2006-25708 and are available for inspection or
copying at the Docket Management Facility (M-30), U.S. Department of
Transportation, West Building Ground Floor, Room W12-140, 1200 New
Jersey Avenue, SE., Washington, DC 20590, between 9 a.m. and 5 p.m.,
Monday through Friday, except Federal holidays. You may also find this
docket on the Internet at http://www.regulations.gov.
FOR FURTHER INFORMATION CONTACT: If you have questions on this rule,
call Benjamin White, National Pollution Funds Center, Coast Guard,
telephone 202-493-6863. If you have questions on viewing the docket,
call Renee V. Wright, Program Manager, Docket Operations, telephone
202-366-9826.
SUPPLEMENTARY INFORMATION:
Regulatory History
On June 12, 2007, we published a notice of proposed rulemaking
(NPRM) entitled ``Landowner Defenses to Liability Under the Oil
Pollution Act of 1990: Standards and Practices for Conducting All
Appropriate Inquiries'' in the Federal Register (72 FR 32232). We
received no comments on the proposed rule. No public meeting was
requested and none was held. The Coast Guard is, therefore, adopting
the NPRM as published and without change as a final rule.
Background and Purpose
In general, under the Oil Pollution Act of 1990 (33 U.S.C. 2701, et
seq.) (OPA 90), an owner or operator of a facility that is the source
of a discharge, or a substantial threat of discharge, of oil into the
navigable waters or adjoining shorelines or the exclusive economic zone
is liable for damages and removal costs resulting from the discharge or
threat. See 33 U.S.C. 2702(a). Under OPA 90, that person is known as a
``responsible party.'' See 33 U.S.C. 2701(32).
The Coast Guard and Maritime Transportation Act of 2004 (Pub. L.
108-293) (the 2004 Act) amended OPA 90, at 33 U.S.C. 2703(d)(4), by
creating an ``innocent landowner'' defense to liability for those
persons who could demonstrate, among other requirements, that before
acquiring the real property on which the facility is located, they did
not know, and had no reason to know that oil that is the subject of the
discharge or substantial threat of discharge was located on, in, or at
the facility. See 33 U.S.C. 2703(d)(2)(A). This is done by establishing
that, before it acquired the real property on which the facility is
located, it carried out ``all appropriate inquiries'' into its previous
ownership and uses according to ``generally accepted good commercial
and customary standards and practices.'' See 33 U.S.C.
2703(d)(4)(A)(i). The Coast Guard is required to establish, by
regulation, the standards and practices for carrying out all
appropriate inquiries (33 U.S.C. 2703(d)(4)(B)), which is the subject
of this rulemaking.
This rulemaking applies to persons planning to acquire real
property on which a facility, as defined under 33 U.S.C. 2701(9), is
located who choose to take steps necessary to protect themselves from
liability should unknown oil that is the subject of a discharge or
substantial threat of discharge be found at the facility after they
acquire it. We call these persons ``landowners'' or ``owners'' in this
preamble. Should prospective landowners opt for this protection, they
may find that they have already complied with this rule if they have
complied with ASTM International (ASTM) E 1527-05, ``Standard Practice
for Environmental Site Assessments: Phase I Environmental Site
Assessment Process.'' The industry standard ASTM E 1527-05, is
consistent with this rule and is compliant with the statutory criteria
for all appropriate inquiries. Persons conducting all appropriate
inquiries may use the procedures included in the ASTM E 1527-05
standard to comply with this rule. For more information on the ASTM
standard, see the ``ASTM Standard E 1527-05'' section in this preamble.
Note that this rule addresses only one of several elements that
must be complied with in order to avail oneself of this protection. The
element addressed in this rule is called the ``all-appropriate-
inquiries'' element found in 33 U.S.C. 2703(d)(4).
Scope of the Rule
Congress included in the 2004 Act a list of criteria that the Coast
Guard must address in their regulations for establishing standards and
practices for conducting all appropriate inquiries. The criteria may be
found in 33 U.S.C. 2703(d)(4)(C). This rulemaking is limited only to
providing those standards and practices relative to the ``all
appropriate inquiries'' element.
[[Page 2147]]
This rulemaking does not address the other requirements in 33 U.S.C.
2703 which also must be met to qualify for the innocent-landowner
defense.
The rule would not apply to real property purchased by a non-
governmental entity or non-commercial entity for residential use or
other similar uses where an inspection and a title search of the
facility and the real property on which the facility is located reveal
no basis for further investigation. In those cases, 33 U.S.C.
2703(d)(4)(E) states that the inspection and title search satisfy the
requirements for all appropriate inquiries.
Also, the rule would not affect the existing OPA 90 liability
protections for State and local governments that acquire a facility
involuntarily in their functions as sovereigns under 33 U.S.C.
2701(26)(B)(i) and 33 U.S.C. 2703(d)(2)(B). Involuntary acquisition of
facilities by State and local governments do not fall under the all-
appropriate-inquiries provision of 33 U.S.C. 2703(d)(4).
Consultation With Other Agencies
Under 33 U.S.C. 2703(d)(4)(B), we are required to consult with the
Environmental Protection Agency (EPA) to develop regulations
establishing standards and practices for conducting ``all appropriate
inquiries.'' On November 1, 2005, EPA published a final rule in the
Federal Register (70 FR 66070) establishing standards and practices for
conducting all appropriate inquiries as required by sections
101(35)(B)(ii) and (iii) of the Comprehensive Environmental Response,
Compensation and Liability Act (CERCLA) (42 U.S.C. 9601, et seq.) found
at 42 U.S.C. 9601(35)(B)(ii) and (iii). CERCLA's liability provision
applies to releases or threatened releases of ``hazardous substances'',
which is defined to exclude most forms of oil. These regulations are
located in 40 CFR part 312. EPA used a negotiated rulemaking process to
develop their standards and practices for conducting all appropriate
inquiries under CERCLA. EPA's Negotiated Rulemaking Committee included
interested parties from environmental interest groups; the
environmental justice community; federal, state, tribal, and local
governments; real estate developers, bankers and lenders; and,
environmental professionals.
The all-appropriate-inquiries provisions of OPA 90 and CERCLA are
similar in many respects, but not identical. The CERCLA provision has a
broader scope than the OPA provision. It addresses certain liability
defense provisions that are unique to CERCLA, involving persons who may
not be affected by this rule, such as contiguous property owners and
bona fide prospective purchasers. While differences between OPA 90 and
CERCLA have required certain differences between the Coast Guard's
final rule and EPA's final rule, we have coordinated with EPA to ensure
that the two rules have been rendered as consistent as possible within
statutory constraints. Maintaining consistency between the two rules
helps standardize practices within the Federal Government.
ASTM Standard E 1527-05
ASTM International (ASTM) E 1527-05, ``Standard Practice for
Environmental Site Assessments: Phase I Environmental Site Assessment
Process,'' is the current voluntary industry standard that defines good
commercial and customary practice in the United States for conducting
an environmental site assessment of a parcel of commercial real estate
with respect to oil under OPA 90 and hazardous substances under CERCLA.
The 2004 Act, at 33 U.S.C. 2703 (d)(4)(D)(ii), refers to ASTM E 1527-
97, which is no longer available from ASTM and has been replaced by
ASTM E 1527-05. Both the EPA and the Coast Guard agree that the new
ASTM E 1527-05 is the active industry standard and is consistent with
Congressional intent. Persons conducting all appropriate inquiries are
permitted to use the procedures included in the ASTM E 1527-05 standard
to comply with this rule, but use of the ASTM is not mandatory.
Regulatory Evaluation
Executive Order 12866
This rule is not a ``significant regulatory action'' under section
3(f) of Executive Order 12866, Regulatory Planning and Review, and does
not require an assessment of potential costs and benefits under section
6(a)(3) of that Order. The Office of Management and Budget has not
reviewed it under that Order.
A final Regulatory Evaluation follows:
Compliance with this rule is required only for those persons
engaging in a commercial real estate transaction who choose to take
steps necessary to protect themselves from liability should unknown oil
that is the subject of a discharge or substantial threat of discharge
be found at the facility after they acquire it.
The following analysis of the economic impacts associated with this
rule relies heavily upon the data collected and the assumptions made in
the Environmental Impact Analysis of EPA's final rule, ``Economic
Impact Analysis for the Final All Appropriate Inquiries Regulation,''
Docket ID No. SFUND-2004-0001 found at http://www.regulations.gov/fdmspublic/component/main
or at EPA Docket Center, EPA West Building,
Room B102, 1301 Constitution Avenue, NW., Washington, DC. EPA surveyed
all publicly available literature on environmental assessments of sites
to determine what standard industry was customarily using. These
assessments correspond to the all appropriate inquiries provision being
addressed in this rulemaking and are commonly known as Phase I
environmental site assessments (Phase I ESAs). EPA determined that the
2000 edition of ASTM E 1527 (i.e., ASTM E 1527-00) would be their
regulatory baseline. This baseline represented the ``no action''
scenario to which all regulatory alternatives were compared and their
economic impacts were measured. ASTM E 1527-00 would have been applied
by industry absent EPA's regulation, because this voluntary industry
standard represented ``generally accepted good commercial and customary
practices.'' This assumption was confirmed by the members of EPA's
Negotiated Rulemaking Committee (See the ``Consultation with Other
Agencies'' section of this preamble.). To further validate their
assumption, EPA received no public comments on this aspect of its
Economic Impact Analysis. In addition, ASTM International states that
ASTM E 1527-97 (the edition referred to in the 2004 Act) is no longer
available because, when a new version of a standard is released,
previous versions of the standard are no longer the active industry
standard. The Coast Guard, after independently contacting ASTM
International, concurs that the ASTM E 1527-00 standard more accurately
reflects the current market conditions than the E 1527-97 standard
referenced in OPA 90 as the acceptable interim standard (33 U.S.C.
2703(d)(4)(D)(ii)). The Coast Guard therefore uses the ASTM E 1527-00
standard as its regulatory baseline for its analysis of the economic
impacts associated with this rule.
Historically, Phase I ESAs have been used towards providing
liability protection to individuals under CERCLA. A recent survey
conducted by Environmental Data Resources, Inc. (EDR) indicates that
approximately 55 percent of all Phase I ESAs are driven exclusively by
a need for the landowner
[[Page 2148]]
to qualify for protection from CERCLA liability. The remaining 45
percent are driven by a desire to assess other business environmental
risk concerns (i.e., asbestos, lead-based paint, oil, etc.).
As previously discussed in the ``Consultation with Other Agencies''
section of this preamble, this rule is consistent with EPA's final
rule. The scope of EPA's rulemaking however is much larger than this
rule. As such, the economic impacts of this rule are a subset of the
impacts estimated by EPA's rulemaking. This reduction in economic
impact results primarily from the lower number of Phase I ESAs expected
to be conducted annually under this rule compared to EPA's final rule.
As was the case with EPA's rulemaking, this rule is expected to
result in the following economic impacts:
(1) A reduced burden for the conduct of interviews in those cases
where the facility and the real property on which the facility is
located is abandoned. The new requirement requires only that
neighboring property owners and occupants be interviewed and not the
current owners and occupants of the abandoned property. This burden
would range from no change to a decrease of 0.5 hour per Phase I ESA
depending on the type and size of the facility and the real property on
which the facility is located.
(2) An increased burden in those cases where past owners or
occupants of the facility and the real property on which the facility
is located need to be interviewed. This would involve the additional
effort required to locate and interview past owners and occupants. This
increased burden would range from 1 hour to 2 hours per Phase I ESA
depending on the type and size of the facility and the real property on
which the facility is located.
(3) An increased burden associated with documenting recorded
environmental cleanup liens. This increased burden would involve
additional time spent in preparing the Phase I ESA report. This
increased burden would range from an additional 0.5 hour to 1 hour per
Phase I ESA depending on the size and type of the facility and the real
property on which the facility is located.
(4) An increased burden for documenting the reasons for the price
and fair market value of a facility and the real property on which the
facility is located in those cases where the purchase price paid is
significantly below its fair market value. This increased burden would
involve interviews with local government officials and increased time
spent in preparing the Phase I ESA report. This increased burden would
reflect an additional 0.5 hour per Phase I ESA for all sizes and types
of facilities and the real properties on which the facilities are
located.
(5) An increased burden for recording information about the degree
of obviousness of the presence or likely presence of oil at a facility
and the real property on which the facility is located. This increased
burden would involve additional time spent in preparing the Phase I
Environmental report. This increased burden would range from 0.5 hour
to 1 hour per Phase I ESA depending on the type and size of the
facility and the real property on which the facility is located.
Using a weighted labor rate of $51.20/hour applied to the
activities (as outlined above) required as a result of their regulation
(as they vary from those required in their regulatory baseline), EPA
determined that there would be an incremental cost ranging from $52 to
$58 per Phase I ESA (the low end estimate assumes that 15 percent of
properties are abandoned, while the high end estimate assumes that 28
percent of properties are abandoned). Our analysis simplifies this
range as an average incremental cost of $55 per Phase I ESA.
A. Analysis Calculations and Results
Using data from EPA's final rule and extrapolated for the period
from 2007 to 2016, there would be an average of 332,038 Phase I ESAs
conducted annually. As previously mentioned, the incremental cost of
conducting a Phase I ESA to comply with EPA's rulemaking above and
beyond what was required under ASTM E 1527-00 as calculated by EPA's
rulemaking would be approximately $55 per ESA.
B. Estimated Annual Number of OPA 90-Related Phase I ESAs
This analysis is severely limited by the lack of data available
which would allow the number of Phase I ESAs conducted applicable to
this rule to be segregated from the total population of Phase I ESAs
conducted.
In order to put an upward bound on the costs associated with this
rule, this analysis first describes the absolute upper bound scenario
(i.e., that all commercial real estate transactions not exclusively
conducted for CERCLA liability protection requiring a Phase I ESA would
be impacted by this rule). Next the Coast Guard developed a more likely
scenario that takes into account that Phase I ESAs for certain
commercial real estate transactions are outside the scope of this rule.
We acknowledge that, of all of the commercial real estate transactions
that occur annually, a likely small percentage would involve--
1. A facility and the real property on which the facility is
located where a discharge or substantial threat of discharge of oil may
impact the navigable waters or exclusive economic zone of the United
States; and
2. A Phase I ESA that was conducted for establishment of the
innocent landowner liability protection provision under OPA 90 and not
to assess environmental risk concerns not related to oil (e.g., lead-
based paint contamination, asbestos, CERCLA hazardous substances,
etc.).
C. Upper Bound Cost Scenario
The estimated incremental cost of this scenario, where all future
Phase I ESAs not conducted specifically for CERCLA liability protection
(i.e., 45 percent as per the results of EDR's survey mentioned above)
are impacted by this rule, would be approximately $8.2 million per
year.
Cost calculation 1--Estimated Annual Number of Coast Guard related
Phase I ESAs
332,038 Phase I ESAs x 0.45 = 149,417 Phase I ESAs
Estimated Annual Cost of Coast Guard related Phase I ESAs
149,417 Phase I ESAs x $55/ESA = $8,217,935 per year.
D. Most Likely Cost Scenario
To more accurately reflect the scope of this rule, certain
commercial real estate transactions involving a Phase I ESA from EPA's
analysis would have to be removed from this analysis. Those include
transactions where a discharge or substantial threat of discharge of
oil from a facility and the real property on which the facility is
located would not have the possibility of impacting the navigable
waters or exclusive economic zone of the United States and transactions
which are conducted for substances other than oil. Absent the data to
make more than an approximation, we assumed that five percent of the
total number of Phase I ESAs may realistically reflect the number of
Phase I ESAs within the scope of this rule. Under this assumption, the
estimated cost associated with this rule would be significantly
reduced. The estimated incremental cost under this scenario is
approximately $913,110 per year.
Cost Calculation 2--Estimated Annual Number of Coast Guard related
Phase I ESAs.
[[Page 2149]]
332,038 Phase I ESAs x 0.05 = 16,602 Phase I ESAs.
Estimated Annual Cost of Coast Guard related Phase I ESAs:
16,602 Phase I ESAs x $55/ESA = $913,110 per year.
ASTM International has since updated their ASTM E 1527 standard.
Their new standard is ASTM E 1527-05. Both EPA and Coast Guard
recognize that this new standard is consistent with their rulemakings
on the subject. See the Federal Register (70 FR 66081). Because the new
standard is consistent with the EPA final rule, which went into effect
on November 1, 2006, and provides documentation for both hazardous
substances and oil, it is likely that all prudent prospective
commercial landowners will be using the more rigorous ASTM standard for
their real estate transactions well before our rule becomes effective.
Thus, the possible economic impact attributed to this rule might be
reduced to a negligible value. The Coast Guard further notes that there
have been no instances to date where a responsible party has attempted
to use the interim innocent-landowner defense to liability provision
under OPA 90.
EPA qualitatively assessed the benefits for their final rule. Of
these benefits, only one is applicable to our rule due to our much
smaller regulatory scope, namely the increased level of certainty with
regard to OPA 90 liability provided to prospective owners of facilities
and the real properties on which they are located with potential oil
discharges. The Coast Guard, as was the case with EPA's analysis, is
not able to quantify, with any significant level of confidence, the
exact proportion of benefits associated with the rule. For these
reasons, the costs and benefits can not be directly compared. However,
because complying with this rule is required only for those persons who
choose to take steps necessary to protect themselves from liability
should unknown oil that is the subject of a discharge or substantial
threat of discharge be found at the facility after they acquire it, it
can be assumed that persons would only do so if the potential benefits
to them associated with this protection from liability outweigh their
costs of compliance.
Small Entities
Under the Regulatory Flexibility Act (5 U.S.C. 601-612), we have
considered whether this rule would have a significant economic impact
on a substantial number of small entities. The term ``small entities''
comprises small businesses, not-for-profit organizations that are
independently owned and operated and are not dominant in their fields,
and governmental jurisdictions with populations of less than 50,000.
As previously stated in the regulatory evaluation section above,
compliance with this rule is only required for those entities,
regardless of their operations, involved in a real estate transaction
who choose to take steps necessary to protect themselves from liability
should unknown oil that is the subject of a discharge or substantial
threat of discharge be found at the facility after they acquire it.
Therefore, it assumed that entities across all industries, as defined
by the North American Industry Classification System (NAICS), could
potentially be affected.
The Regulatory Flexibility Act and the Small Business Regulatory
Enforcement Fairness Act of 1996 require Federal agencies to measure
the regulatory impacts of the rule to determine whether there will be a
significant economic impact on a substantial number of small entities.
Entities, however, may operate at multiple physical locations. For
example, most family-owned restaurants operate at a single location,
while chain restaurants have multiple locations. Thus, the annual
number of transactions per entity, and therefore the demand for Phase I
ESAs, is a function of the number of establishments an entity owns.
According to 2001 U.S. Census data, the distribution of
establishments by entity size of the regulated community is as follows:
Less than 100 employees: 81%
100 to 499 employees: 5%
500 to 1,499 employees: 2%
1,500 employees or more: 12%
According to EPA's Office of Policy, Economics, and Innovations and
EPA's National Center for Environmental Economics, it is a common
practice when a proposed regulation has the potential of affecting all
industries to consider all entities with less than 500 employees as
small. According to 2001 U.S. Census data, when small entities are
defined as entities with less than 500 employees, small entities own 86
percent of all establishments. Using EPA's assumption that small
entities are equally likely to engage in commercial real estate
transactions as large ones, we estimate that 86 percent of all
commercial real estate transactions completed annually involve small
entities. Applying this 86 percent to the ``Most Likely Cost Scenario''
and the ``Upper Bound Cost Scenario'' (See ``Regulatory Evaluation'' in
this preamble.) provides a range in the number of potential
transactions occurring annually of between 14,278 and 128,499.
Based on 2001 Census Bureau data, the average annual revenue per
employee for an entity is approximately $24,000. Therefore, even for a
small entity receiving the minimum average annual revenue of $24,000
that makes one transaction a year (a very conservative assumption), the
annual cost impact of $55 would represent only 0.23 percent of annual
revenues.
Therefore, the Coast Guard certifies under 5 U.S.C. 605(b) that
this final rule will not have a significant economic impact on a
substantial number of small entities.
Assistance for Small Entities
Under section 213(a) of the Small Business Regulatory Enforcement
Fairness Act of 1996 (Pub. L. 104-121), we offered to assist small
entities in understanding this rule so they could better evaluate its
effects on them and participate in the rulemaking. The Coast Guard
received no requests for assistance from small entities concerning this
rulemaking and provided none. Small businesses may send comments on the
actions of Federal employees who enforce, or otherwise determine
compliance with, Federal regulations to the Small Business and
Agriculture Regulatory Enforcement Ombudsman and the Regional Small
Business Regulatory Fairness Boards. The Ombudsman evaluates these
actions annually and rates each agency's responsiveness to small
business. If you wish to comment on actions by employees of the Coast
Guard, call 1-888-REG-FAIR (1-888-734-3247).
Collection of Information
This rule calls for a new collection of information under the
Paperwork Reduction Act of 1995 (44 U.S.C. 3501-3520).
Title: Landowner Defenses to Liability under the Oil Pollution Act
of 1990: Standards and Practices for Conducting All Appropriate
Inquiries.
Summary of the Collection of Information: For landowners choosing
to avail themselves of the innocent-landowner defense, they or their
environmental professionals must conduct all the appropriate inquiries
specified in the rule. Depending upon the particular case, this may
involve interviews, research, and reports.
Need for Information: This rule is needed to assist prospective
landowners in establishing the innocent-landowner defense.
Proposed Use of Information: The information could be used by
persons if
[[Page 2150]]
their liability under OPA 90 for the discharge or substantial threat of
discharge of oil were challenged in a court.
Description of the Respondents: The respondents include anyone
engaging in a commercial real estate transaction that may desire to
assert an innocent landowner defense to liability under OPA 90.
Number of Respondents: We estimate that there would be 16,602
respondents. This is based on an estimate made in the ``Regulatory
Evaluation'' section of this preamble.
Frequency of Response: 1 hour per response.
Burden of Response: $67 per response.
Estimate of Total Annual Burden: 16,602 respondents x 1 hour per
response x $67 per response = $1,112,334
As required by 44 U.S.C. 3507(d), we submitted a copy of this rule
to the Office of Management and Budget (OMB) for its review of the
collection of information. OMB has approved the collection effective
February 13, 2008. The collection will be added to 33 CFR part 137. The
corresponding approval number is OMB Control Number 1625-0111, which
expires on February 13, 2011.
You are not required to respond to a collection of information
unless it displays a currently valid OMB control number.
Federalism
A rule has implications for federalism under Executive Order 13132,
Federalism, if it has a substantial direct effect on State or local
governments and would either preempt State law or impose a substantial
direct cost of compliance on them. We have analyzed this rule under
that Order and have determined that it does not have implications for
federalism.
Unfunded Mandates Reform Act
The Unfunded Mandates Reform Act of 1995 (2 U.S.C. 1531-1538)
requires Federal agencies to assess the effects of their discretionary
regulatory actions. In particular, the Act addresses actions that may
result in the expenditure by a State, local, or tribal government, in
the aggregate, or by the private sector of $100,000,000 or more in any
one year. Though this rule would not result in such an expenditure, we
do discuss the effects of this rule elsewhere in this preamble.
Taking of Private Property
This rule would not effect a taking of private property or
otherwise have taking implications under Executive Order 12630,
Governmental Actions and Interference with Constitutionally Protected
Property Rights.
Civil Justice Reform
This rule meets applicable standards in sections 3(a) and 3(b)(2)
of Executive Order 12988, Civil Justice Reform, to minimize litigation,
eliminate ambiguity, and reduce burden.
Protection of Children
We have analyzed this rule under Executive Order 13045, Protection
of Children from Environmental Health Risks and Safety Risks. This rule
is not an economically significant rule and does not create an
environmental risk to health or risk to safety that may
disproportionately affect children.
Indian Tribal Governments
This rule does not have tribal implications under Executive Order
13175, Consultation and Coordination with Indian Tribal Governments,
because it does not have a substantial direct effect on one or more
Indian tribes, on the relationship between the Federal Government and
Indian tribes, or on the distribution of power and responsibilities
between the Federal Government and Indian tribes.
Energy Effects
We have analyzed this rule under Executive Order 13211, Actions
Concerning Regulations That Significantly Affect Energy Supply,
Distribution, or Use. We have determined that it is not a ``significant
energy action'' under that order because it is not a ``significant
regulatory action'' under Executive Order 12866 and is not likely to
have a significant adverse effect on the supply, distribution, or use
of energy. The Administrator of the Office of Information and
Regulatory Affairs has not designated it as a significant energy
action. Therefore, it does not require a Statement of Energy Effects
under Executive Order 13211.
Technical Standards
The National Technology Transfer and Advancement Act (NTTAA) (15
U.S.C. 272 note) directs agencies to use voluntary consensus standards
in their regulatory activities unless the agency provides Congress,
through the Office of Management and Budget, with an explanation of why
using these standards would be inconsistent with applicable law or
otherwise impractical. Voluntary consensus standards are technical
standards (e.g., specifications of materials, performance, design, or
operation; test methods; sampling procedures; and related management
systems practices) that are developed or adopted by voluntary consensus
standards bodies.
This rule uses the following voluntary consensus standard: ASTM E
1527-05, ``Standard Practice for Environmental Site Assessments: Phase
I Environmental Site Assessment Process.'' The section that references
this standard and the location where this standard is available is
listed in Sec. 137.15. Persons conducting all appropriate inquiries
may use the procedures included in the ASTM E 1527-05 standard to
comply with this rule.
Environment
We have analyzed this rule under Commandant Instruction M16475.lD,
which guides the Coast Guard in complying with the National
Environmental Policy Act of 1969 (NEPA) (42 U.S.C. 4321-4370f), and
have concluded that there are no factors in this case that would limit
the use of a categorical exclusion under section 2.B.2 of the
Instruction. Therefore, this rule is categorically excluded, under
figure 2-1, paragraph (34)(a), of the Instruction, from further
environmental documentation. This rule concerns inquiries into the
previous ownership and uses of facilities and the real property on
which they are located, before they are acquired, to determine the
presence or likely presence of oil. It has no effect on the
environment.
A final ``Environmental Analysis Check List'' and a final
``Categorical Exclusion Determination'' are available in the docket
where indicated under ADDRESSES.
List of Subjects in 33 CFR Part 137
Environmental protection, Administrative practice and procedure,
Petroleum, Intergovernmental relations, Reporting and recordkeeping
requirements.
Words of Issuance and Regulatory Text
0
For the reasons set out in the preamble, the Coast Guard adds 33 CFR
part 137 to read as follows:
PART 137--OIL SPILL LIABILITY: STANDARDS FOR CONDUCTING ALL
APPROPRIATE INQUIRIES UNDER THE INNOCENT LAND-OWNER DEFENSE
Subpart A--Introduction
Sec.
137.1 Purpose and applicability.
137.5 Disclosure obligations.
137.10 How are terms used in this part defined?
[[Page 2151]]
137.15 References: Where can I get a copy of the publication
mentioned in this part?
Subpart B--Standards and Practices
137.18 Duties of persons specified in Sec. 137.1(a).
137.20 May voluntary industry standards be used to comply with this
regulation?
137.25 Qualifications of the environmental professional.
137.30 Objectives and performance factors.
137.33 General all appropriate inquiries requirements.
137.35 Inquiries by an environmental professional.
137.40 Additional inquiries.
137.45 Interviews with past and present owners, operators, and
occupants.
137.50 Reviews of historical sources of information.
137.55 Searches for recorded environmental cleanup liens.
137.60 Reviews of Federal, State, tribal and local government
records.
137.65 Visual inspections of the facility, the real property on
which the facility is located, and adjoining properties.
137.70 Specialized knowledge or experience on the part of persons
specified in Sec. 137.1(a).
137.75 The relationship of the purchase price to the value of the
facility and the real property on which the facility is located, if
oil was not at the facility or on the real property.
137.80 Commonly known or reasonably ascertainable information about
the facility and the real property on which the facility is located.
137.85 The degree of obviousness of the presence or likely presence
of oil at the facility and the real property on which the facility
is located and the ability to detect the oil by appropriate
investigation.
Authority: 33 U.S.C. 2703(d)(4); Department of Homeland Security
Delegation No. 14000.
Subpart A--Introduction
Sec. 137.1 Purpose and applicability.
(a) In general under the Oil Pollution Act of 1990 (33 U.S.C. 2701,
et seq.), an owner or operator of a facility (as defined in Sec.
137.10) that is the source of a discharge, or a substantial threat of
discharge, of oil into the navigable waters or adjoining shorelines or
the exclusive economic zone is liable for damages and removal costs
resulting from the discharge or threat. However, if that person can
demonstrate, among other criteria not addressed in this part, that they
did not know and had no reason to know at the time of their acquisition
of the real property on which the facility is located that oil was
located on, in, or at the facility, the person may be eligible for the
innocent landowner defense to liability under 33 U.S.C. 2703(d)(4). One
element of the defense is that the person made all appropriate
inquiries into the nature of the real property on which the facility is
located before acquiring it. The purpose of this part is to prescribe
standards and practices for making those inquiries.
(b) Under 33 U.S.C. 2703(d)(4)(E), this part does not apply to real
property purchased by a non-governmental entity or non-commercial
entity for residential use or other similar uses where a property
inspection and a title search reveal no basis for further
investigation. In those cases, the property inspection and title search
satisfy the requirements of this part.
(c) This part does not affect the existing OPA 90 liability
protections for State and local governments that acquire a property
involuntarily in their functions as sovereigns under 33 U.S.C.
2703(d)(2)(B). Involuntary acquisition of properties by State and local
governments fall under the provisions of 33 U.S.C. 2703(d)(2)(B), not
under the all-appropriate-inquiries provision of 33 U.S.C. 2703(d)(4)
and this part.
Sec. 137.5 Disclosure obligations.
(a) Under 33 U.S.C. 2703(c)(1), persons specified in Sec.
137.1(a), including environmental professionals, must report the
incident as required by law if they know or have reason to know of the
incident.
(b) This part does not limit or expand disclosure obligations under
any Federal, State, tribal, or local law. It is the obligation of each
person, including environmental professionals, conducting inquiries to
determine his or her respective disclosure obligations under Federal,
State, tribal, and local law and to comply with them.
Sec. 137.10 How are terms used in this part defined?
(a) The following terms have the same definitions as in 33 U.S.C.
2701: damages; discharge; incident; liable or liability; oil; owner or
operator; and removal costs.
(b) As used in this part--
Abandoned property means a property that, because of its general
disrepair or lack of activity, a reasonable person could believe that
there is an intent on the part of the current owners to surrender their
rights to the property.
Adjoining property means real property the border of which is
shared in part or in whole with that of the subject property or that
would be shared in part or in whole with that of the property but for a
street, road, or other public thoroughfare separating the properties.
Data gap means a lack of, or inability to, obtain information
required by subpart B of this part despite good faith efforts by the
environmental professional or persons specified in Sec. 137.1(a), as
appropriate, to gather the information under Sec. 137.33.
Environmental professional means an individual who meets the
requirements of Sec. 137.25.
Facility means any structure, group of structures, equipment, or
device (other than a vessel) which is used for one or more of the
following purposes: exploring for, drilling for, producing, storing,
handling, transferring, processing, or transporting oil. This term
includes any motor vehicle, rolling stock, or pipeline used for one or
more of these purposes.
Good faith means the absence of any intention to seek an unfair
advantage or to defraud another party; an honest and sincere intention
to fulfill one's obligations in the conduct or transaction concerned.
Institutional controls means non-engineered instruments, such as
administrative and/or legal controls, that help to minimize the
potential for human exposure to oil discharge and/or protect the
integrity of a removal action.
Relevant experience means participation in the performance of all-
appropriate-inquiries investigations, environmental site assessments,
or other site investigations that may include environmental analyses,
investigations, and remediation which involve the understanding of
surface and subsurface environmental conditions and the processes used
to evaluate these conditions and for which professional judgment was
used to develop opinions regarding conditions indicative of the
presence or likely presence of oil at the facility and the real
property on which the facility is located.
Sec. 137.15 References: Where can I get a copy of the publication
mentioned in this part?
Section 137.20 of this part refers to ASTM E 1527-05, Standard
Practice for Environmental Site Assessments: Phase I Environmental Site
Assessment Process. That document is available from ASTM International,
100 Barr Harbor Drive, P.O. Box C700, West Conshohocken, PA 19428-2959.
It is also available for inspection at the Coast Guard National
Pollution Funds Center, 4200 Wilson Boulevard, Suite 1013, Arlington,
VA 22203-1804.
Subpart B--Standards and Practices
Sec. 137.18 Duties of persons specified in Sec. 137.1(a).
In order to make all appropriate inquiries, persons seeking to
establish the liability protection under Sec. 137.1(a)
[[Page 2152]]
must conduct the inquiries and investigations as required in this part
and ensure that the inquiries and investigations required to be made by
environmental professionals are made.
Sec. 137.20 May industry standards be used to comply with this
regulation?
The industry standards in ASTM E 1527-05, (Referenced in Sec.
137.15) may be used to comply with the requirements set forth in
Sec. Sec. 137.45 through 137.85 of this part. Use of ASTM E 1527-05
for this purpose is optional and not mandatory.
Sec. 137.25 Qualifications of the environmental professional.
(a) An environmental professional is an individual who possesses
sufficient specific education, training, and experience necessary to
exercise professional judgment to develop opinions and conclusions
regarding conditions indicative of the presence or likely presence of
oil at a facility and the real property on which the facility is
located sufficient to meet the objectives and performance factors in
Sec. 137.30(a) and (b).
(1) Such a person must--
(i) Hold a current Professional Engineer's or Professional
Geologist's license or registration from a State, tribe, or U.S.
territory (or the Commonwealth of Puerto Rico) and have the equivalent
of 3 years of full-time relevant experience;
(ii) Be licensed or certified by the Federal government, a State,
tribe, or U.S. territory (or the Commonwealth of Puerto Rico) to
perform environmental inquiries under Sec. 137.35 and have the
equivalent of 3 years of full-time relevant experience;
(iii) Have a Baccalaureate or higher degree from an accredited
institution of higher education in a discipline of engineering or
science and the equivalent of 5 years of full-time relevant experience;
or
(iv) Have the equivalent of 10 years of full-time relevant
experience.
(2) An environmental professional should remain current in his or
her field through participation in continuing education or other
activities.
(3) The requirements for an environmental professional in this
section do not preempt State professional licensing or registration
requirements, such as those for a professional geologist, engineer, or
site-remediation professional. Before commencing work, a person should
determine the applicability of State professional licensing or
registration laws to the activities to be undertaken as part of an
inquiry under Sec. 137.35(b).
(4) A person who does not qualify as an environmental professional
under this section may assist in the conduct of all appropriate
inquiries according to this part if the person is under the supervision
or responsible charge of an environmental professional meeting the
requirements of this section when conducting the inquiries.
Sec. 137.30 Objectives and performance factors.
(a) Objectives. This part is intended to result in the
identification of conditions indicative of the presence or likely
presence of oil at the facility and the real property on which the
facility is located. In order to meet the objectives of this
regulation, persons specified in Sec. 137.1(a) and the environmental
professional must seek to identify, through the conduct of the
standards and practices in this subpart, the following types of
information about the facility and the real property on which the
facility is located:
(1) Current and past uses and occupancies of the facility and the
real property on which the facility is located.
(2) Current and past uses of oil.
(3) Waste management and disposal activities that indicate presence
or likely presence of oil.
(4) Current and past corrective actions and response activities
that indicate presence or likely presence of oil.
(5) Engineering controls.
(6) Institutional controls, such as zoning restrictions, building
permits, and easements.
(7) Properties adjoining or located nearby the facility and the
real property on which the facility is located that have environmental
conditions that could have resulted in conditions indicative of the
presence or likely presence of oil at the facility and the real
property on which the facility is located.
(b) Performance factors. In order to meet this part and to meet the
objectives stated in paragraph (a) of this section, the persons
specified in Sec. 137.1(a) or the environmental professional (as
appropriate to the particular standard and practice) must--
(1) Gather the information that is required for each standard and
practice listed in this subpart that is publicly available, is
obtainable from its source within a reasonable time and cost, and can
be reviewed practicably; and
(2) Review and evaluate the thoroughness and reliability of the
information gathered in complying with each standard and practice
listed in this subpart taking into account information gathered in the
course of complying with the other standards and practices of this
part.
Sec. 137.33 General all appropriate inquiries requirements.
(a) All appropriate inquiries must be conducted within 1 year
before the date of acquisition of the real property on which the
facility is located, as evidenced by the date of receipt of the
documentation transferring title to, or possession of, the real
property and must include:
(1) An inquiry by an environmental professional, as provided in
Sec. 137.35.
(2) The collection of information under Sec. 137.40 by persons
specified in Sec. 137.1(a).
(b) The following components of the all appropriate inquiries must
be conducted or updated within 180 days before the date of acquisition
of the real property on which the facility is located:
(1) Interviews with past and present owners, operators, and
occupants. See Sec. 137.45.
(2) Searches for recorded environmental cleanup liens. See Sec.
137.55.
(3) Reviews of Federal, State, tribal, and local government
records. See Sec. 137.60.
(4) Visual inspections of the facility, the real property on which
the facility is located, and adjoining properties. See Sec. 137.65.
(5) The declaration by the environmental professional. See Sec.
137.35(d).
(c) All appropriate inquiries may include the results of and
information contained in an inquiry previously conducted by, or on
behalf of, persons specified in Sec. 137.1(a) who are responsible for
the inquiries for the facility and the real property on which the
facility is located if--
(1) The information was collected during the conduct of an all-
appropriate-inquiries investigation under this part.
(2) The information was collected or updated within 1 year before
the date of acquisition of the real property on which the facility is
located.
(3) The following components of the inquiries were conducted or
updated within 180 days before the date of acquisition of the real
property on which the facility is located:
(i) Interviews with past and present owners, operators, and
occupants. See Sec. 137.45.
(ii) Searches for recorded environmental cleanup liens. See Sec.
137.55.
(iii) Reviews of Federal, State, tribal, and local government
records. See Sec. 137.60.
[[Page 2153]]
(iv) Visual inspections of the facility, the real property on which
the facility is located, and the adjoining properties. See Sec.
137.65.
(v) The declaration by the environmental professional. See Sec.
137.35(d).
(4) Previously collected information is updated by including
relevant changes in the conditions of the facility and the real
property on which the facility is located and specialized knowledge, as
outlined in Sec. 137.70, of the persons conducting the all appropriate
inquiries for the facility and the real property on which the facility
is located, including persons specified in Sec. 137.1(a) and the
environmental professional.
(d) All appropriate inquiries may include the results of an
environmental professional's report under Sec. 137.35(c) that have
been prepared by or for other persons if--
(1) The reports meet the objectives and performance factors in
Sec. 137.30(a) and (b); and
(2) The person specified in Sec. 137.1(a) reviews the information
and conducts the additional inquiries under Sec. Sec. 137.70, 137.75,
and 137.80 and updates the inquiries requiring an update under
paragraph (b) of this section.
(e) To the extent there are data gaps that affect the ability of
persons specified in Sec. 137.1(a) and environmental professionals to
identify conditions indicative of the presence or likely presence of
oil, the gaps must be identified in the report under Sec.
137.35(c)(2). In addition, the sources of information consulted to
address data gaps should be identified and the significance of the gaps
noted. Sampling and analysis may be conducted to develop information to
address data gaps.
(f) Any conditions indicative of the presence or likely presence of
oil identified as part of the all-appropriate-inquiries investigation
should be noted in the report.
Sec. 137.35 Inquiries by an environmental professional.
(a) Inquiries by an environmental professional must be conducted
either by the environmental professional or by a person under the
supervision or responsible charge of an environmental professional.
(b) The inquiry of the environmental professional must include the
requirements in Sec. Sec. 137.45 (interviews with past and present
owners), 137.50 (reviews of historical sources), 137.60 (reviews of
government records), 137.65 (visual inspections), 137.80 (commonly
known or reasonably ascertainable information) and 137.85 (degree of
obviousness of the presence or likely presence of oil). In addition,
the inquiry should take into account information provided to the
environmental professional by the person specified in Sec. 137.1(a)
conducting the additional inquiries under Sec. 137.40.
(c) The results of the inquiry by an environmental professional
must be documented in a written report that, at a minimum, includes the
following:
(1) An opinion as to whether the inquiry has identified conditions
indicative of the presence or likely presence of oil at the facility
and the real property on which the facility is located.
(2) An identification of data gaps in the information developed as
part of the inquiry that affect the ability of the environmental
professional to identify conditions indicative of the presence or
likely presence of oil at the facility and the real property on which
the facility is located. The report must also indicate whether the gaps
prevented the environmental professional from reaching an opinion
regarding the identification of conditions indicative of the presence
or likely presence of oil.
(3) The qualifications of the environmental professional.
(4) An opinion regarding whether additional appropriate
investigation is necessary.
(d) The environmental professional must place the following
statements in the written document identified in paragraph (c) of this
section and sign the document: ``[I, We] declare that, to the best of
[my, our] professional knowledge, [I, we] meet the requirements under
33 CFR 137.25 for an environmental professional.'' and ``[I, We] have
the specific qualifications based on education, training, and
experience to assess the nature, history, and setting of a facility and
the real property on which it is located. [I, We] have developed and
conducted all appropriate inquiries according to the standards and
practices in 33 CFR part 137.''
Sec. 137.40 Additional inquiries.
(a) Persons specified in Sec. 137.1(a) must conduct inquiries in
addition to those conducted by the environmental professional under
Sec. 137.35 and may provide the information associated with these
additional inquiries to the environmental professional responsible for
conducting the activities listed in Sec. 137.35--
(1) As required by Sec. 137.55 and if not otherwise obtained by
the environmental professional, environmental cleanup liens against the
facility and the real property on which it is located that are filed or
recorded under Federal, State, tribal, or local law.
(2) As required by Sec. 137.70, specialized knowledge or
experience of the person specified in Sec. 137.1(a).
(3) As required by Sec. 137.75, the relationship of the purchase
price to the fair market value of the facility and the real property on
which the facility is located if the oil was not at the facility and
the real property on which it is located.
(4) As required by Sec. 137.80 and if not otherwise obtained by
the environmental professional, commonly known or reasonably
ascertainable information about the facility and the real property on
which it is located.
(b) [Reserved]
Sec. 137.45 Interviews with past and present owners, operators, and
occupants.
(a) Interviews with owners, operators, and occupants of the
facility and the real property on which the facility is located must be
conducted for the purposes of achieving the objectives and performance
factors of Sec. 137.30(a) and (b).
(b) The inquiry of the environmental professional must include
interviewing the current owner and occupant of the facility and the
real property on which the facility is located. If the facility and the
real property on which the facility is located has multiple occupants,
the inquiry of the environmental professional must include interviewing
major occupants, as well as those occupants likely to use, store,
treat, handle or dispose of oil or those who have likely done so in the
past.
(c) The inquiry of the environmental professional also must
include, to the extent necessary to achieve the objectives and
performance factors in Sec. 137.30(a) and (b), interviewing one or
more of the following persons:
(1) Current and past facility and real property managers with
relevant knowledge of uses and physical characteristics of the facility
and the real property on which the facility is located.
(2) Past owners, occupants, or operators of the facility and the
real property on which the facility is located.
(3) Employees of current and past occupants of the facility and the
real property on which the facility is located.
(d) In the case of inquiries conducted at abandoned properties
where there is evidence of potential unauthorized uses or evidence of
uncontrolled access, the environmental professional's inquiry must
include an interview of at least
[[Page 2154]]
one owner or occupant of a neighboring property from which it appears
possible that the owner or occupant of the neighboring property could
have observed use or other presence or likely presence of oil.
Sec. 137.50 Reviews of historical sources of information.
(a) Historical documents and records must be reviewed for the
purposes of achieving the objectives and performance factors of Sec.
137.30(a) and (b). Historical documents and records may include, but
are not limited to, aerial photographs, fire insurance maps, building
department records, chain of title documents, and land use records.
(b) Historical documents and records reviewed must cover a period
of time as far back in the history of the real property to when the
first structure was built or when it was first used for residential,
agricultural, commercial, industrial, or governmental purposes. The
environmental professional may exercise professional judgment in
context of the facts available at the time of the inquiry as to how far
back in time it is necessary to search historical records.
Sec. 137.55 Searches for recorded environmental cleanup liens.
(a) All appropriate inquiries must include a search for the
existence of environmental cleanup liens against the facility and the
real property on which the facility is located that are filed or
recorded under Federal, State, tribal, or local law.
(b) All information collected by persons specified in Sec.
137.1(a) rather than an environmental professional regarding the
existence of environmental cleanup liens associated with the facility
and the real property on which the facility is located may be provided
to the environmental professional or retained by the applicable party.
Sec. 137.60 Reviews of Federal, State, tribal, and local government
records.
(a) Federal, State, tribal, and local government records or
databases of government records of the facility, the real property on
which the facility is located, and adjoining properties must be
reviewed for the purposes of achieving the objectives and performance
factors of Sec. 137.30(a) and (b).
(b) With regard to the facility and the property on which the
facility is located, the review of Federal, State, and tribal
government records or databases of the government records and local
government records and databases of the records should include--
(1) Records of reported oil discharges present, including site
investigation reports for the facility and the real property on which
the facility is located;
(2) Records of activities, conditions, or incidents likely to cause
or contribute to discharges or substantial threat of discharges of oil,
including landfill and other disposal unit location records and
permits, storage tank records and permits, hazardous waste handler and
generator records and permits, Federal, tribal and State government
listings of sites identified as priority cleanup sites, and spill
reporting records;
(3) Comprehensive Environmental Response, Compensation, and
Liability Information System (CERCLIS) records;
(4) Public health records;
(5) Emergency Response Notification System records;
(6) Registries or publicly available lists of engineering controls;
and
(7) Registries or publicly available lists of institutional
controls, including environmental land use restrictions, applicable to
the facility and the real property on which the facility is located.
(c) With regard to nearby or adjoining properties, the review of
Federal, State, tribal, and local government records or databases of
government records should include the identification of the following:
(1) Properties for which there are government records of reported
discharges or substantial threat of discharges of oil. Such records or
databases containing such records and the associated distances from the
facility and the real property on which the facility is located for
which such information should be searched include the following:
(i) Records of National Priorities List (NPL) sites or tribal- and
State-equivalent sites (one mile).
(ii) Resource Conservation and Recovery Act (RCRA) properties
subject to corrective action (one mile).
(iii) Records of Federally-registered, or State-permitted or -
registered, hazardous waste sites identified for investigation or
remediation, such as sites enrolled in State and tribal voluntary
cleanup programs and tribal- and State-listed brownfield sites (one-
half mile).
(iv) Records of leaking underground storage tanks (one-half mile).
(2) Properties that previously were identified or regulated by a
government entity due to environmental concerns at the facility and the
real property on which the facility is located. The records or
databases containing the records and the associated distances from the
facility and the real property on which the facility is located for
which the information should be searched include the following:
(i) Records of delisted NPL sites (one-half mile).
(ii) Registries or publicly available lists of engineering controls
(one-half mile).
(iii) Records of former CERCLIS sites with no further remedial
action notices (one-half mile).
(3) Properties for which there are records of Federally-permitted,
State-permitted or -registered, or tribal-permitted or -registered
waste management activities. The records or databases that may contain
the records include the following:
(i) Records of RCRA small quantity and large quantity generators
(adjoining properties).
(ii) Records of Federally-permitted, State-permitted or -
registered, or tribal-permitted landfills and solid waste management
facilities (one-half mile).
(iii) Records of registered storage tanks (adjoining property).
(4) A review of additional government records with regard to sites
identified under paragraphs (c)(1) through (c)(3) of this section may
be necessary in the judgment of the environmental professional for the
purpose of achieving the objectives and performance factors of
Sec. Sec. 137.30(a) and (b).
(d) The search distance from the real property boundary for
reviewing government records or databases of government records listed
in paragraph (c) of this section may be modified based upon the
professional judgment of the environmental professional. The rationale
for the modifications must be documented by the environmental
professional. The environmental professional may consider one or more
of the following factors in determining an alternate appropriate search
distance--
(1) The nature and extent of a discharge.
(2) Geologic, hydrogeologic, or topographic conditions of the
property and surrounding environment.
(3) Land use or development densities.
(4) The property type.
(5) Existing or past uses of surrounding properties.
(6) Potential migration pathways (e.g., groundwater flow direction,
prevalent wind direction).
(7) Other relevant factors.
[[Page 2155]]
Sec. 137.65 Visual inspections of the facility, real property on
which the facility is located, and adjoining properties.
(a) For the purpose of achieving the objectives and performance
factors of Sec. 137.30(a) and (b), the inquiry of the environmental
professional must include the following:
(1) A visual on-site inspection of the facility and the real
property on which the facility is located, and the improvements at the
facility and real property, including a visual inspection of the areas
where oil may be or may have been used, stored, treated, handled, or
disposed. Physical limitations to the visual inspection must be noted.
(2) A visual inspection of adjoining properties, from the subject
real property line, public rights-of-way, or other vantage point (e.g.,
aerial photography), including a visual inspection of areas where oil
may be or may have been stored, treated, handled or disposed. A visual
on-site inspection is recommended, though not required. Physical
limitations to the inspection of adjacent properties must be noted.
(b) Except as in paragraph (c) of this section, a visual on-site
inspection of the facility and the real property on which the facility
is located must be conducted.
(c) An on-site inspection is not required if an on-site visual
inspection of the facility and the real property on which the facility
is located cannot be performed because of physical limitations, remote
and inaccessible location, or other inability to obtain access to the
facility and the real property on which the facility is located after
good faith efforts have been taken to obtain access. The mere refusal
of a voluntary seller to provide access to the facility and the real
property on which the facility is located is not justification for not
conducting an on-site inspection. The inquiry of the environmental
professional must include--
(1) Visually inspecting the facility and the real property on which
the facility is located using another method, such as aerial imagery
for large properties, or visually inspecting the facility and the real
property on which the facility is located from the nearest accessible
vantage point, such as the property line or public road for small
properties;
(2) Documenting the efforts undertaken to obtain access and an
explanation of why such efforts were unsuccessful; and
(3) Documenting other sources of information regarding the presence
or likely presence of oil at the facility and the real property on
which the facility is located that were consulted according to Sec.
137.30(a). The documentation should include comments, if any, by the
environmental professional on the significance of the failure to
conduct a visual on-site inspection of the facility and the real
property on which the facility is located with regard to the ability to
identify conditions indicative of the presence or likely presence of
oil at the facility and the real property.
Sec. 137.70 Specialized knowledge or experience on the part of
persons specified in Sec. 137.1(a).
(a) For the purpose of identifying conditions indicative of the
presence or likely presence of oil at the facility and the real
property on which the facility is located, persons specified in Sec.
137.1(a) must take into account their own specialized knowledge of the
facility and the real property on which the facility is located, the
area surrounding the facility and the real property on which the
facility is located, and the conditions of adjoining properties and
their experience relevant to the inquiry.
(b) The results of all appropriate inquiries under Sec. 137.33
must take into account the relevant and applicable specialized
knowledge and experience of the persons specified in Sec. 137.1(a)
responsible for undertaking the inquiry.
Sec. 137.75 The relationship of the purchase price to the value of
the facility and the real property on which the facility is located, if
oil was not at the facility or on the real property.
(a) Persons specified in Sec. 137.1(a) must consider whether the
purchase price of the facility and the real property on which the
facility is located reasonably reflects the fair market value of the
facility and real property if oil was not present or likely present.
(b) If the persons conclude that the purchase price does not
reasonably reflect the fair market value of that facility and real
property if oil was not at the facility and the real property, they
must consider whether or not the differential in purchase price and
fair market value is due to the presence or likely presence of oil.
Sec. 137.80 Commonly known or reasonably ascertainable information
about the facility and the real property on which the facility is
located.
(a) Throughout the inquiries, persons specified in Sec. 137.1(a)
and environmental professionals conducting the inquiry must take into
account commonly known or reasonably ascertainable information within
the local community about the facility and the real property on which
the facility is located and consider that information when seeking to
identify conditions indicative of the presence or likely presence of
oil at the facility and the real property.
(b) Commonly known information may include information obtained by
the person specified in Sec. 137.1(a) or by the environmental
professional about the presence or likely presence of oil at the
facility and the real property on which the facility is located that is
incidental to the information obtained during the inquiry of the
environmental professional.
(c) To the extent necessary to achieve the objectives and
performance factors of Sec. 137.30(a) and (b), the person specified in
Sec. 137.1(a) and the environmental professional must gather
information from varied sources whose input either individually or
taken together may provide commonly known or reasonably ascertainable
information about the facility and the real property on which the
facility is located; the environmental professional may refer to one or
more of the following sources of information:
(1) Current owners or occupants of neighboring properties or
properties adjacent to the facility and the real property on which the
facility is located.
(2) Local and state government officials who may have knowledge of,
or information related to, the facility and the real property on which
the facility is located.
(3) Others with knowledge of the facility and the real property on
which the facility is located.
(4) Other sources of information, such as newspapers, Web sites,
community organizations, local libraries, and historical societies.
Sec. 137.85 The degree of obviousness of the presence or likely
presence of oil at the facility and the real property on which the
facility is located and the ability to detect the oil by appropriate
investigation.
(a) Persons specified in Sec. 137.1(a) and environmental
professionals conducting an inquiry of a facility and the real property
on which it is located on their behalf must take into account the
information collected under Sec. Sec. 137.45 through 137.80 in
considering the degree of obviousness of the presence or likely
presence of oil at the facility and the real property on which the
facility is located.
(b) Persons specified in Sec. 137.1(a) and environmental
professionals conducting an inquiry of a facility and the property on
which the facility is located on their behalf must take into account
the information collected under Sec. Sec. 137.45 through 137.80 in
considering the
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ability to detect the presence or likely presence of oil by appropriate
investigation. The report of the environmental professional should
include an opinion under Sec. 137.35(c)(4) regarding whether
additional appropriate investigation is necessary.
Dated: January 7, 2008.
William Grawe,
Acting Director, National Pollution Funds Center, United States Coast
Guard.
[FR Doc. E8-329 Filed 1-11-08; 8:45 am]
BILLING CODE 4910-15-P