Standards and Practices for All Appropriate Inquiries, 66070-66113 [05-21455]
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66070
Federal Register / Vol. 70, No. 210 / Tuesday, November 1, 2005 / Rules and Regulations
of today’s rule, contact Patricia
Overmeyer of EPA’s Office of
Brownfields Cleanup and
Redevelopment at (202) 566–2774 or at
overmeyer.patricia@epa.gov. Mail
inquiries may be directed to the Office
of Brownfields Cleanup and
Redevelopment (5105T), 1200
Pennsylvania Ave. NW., Washington,
DC 20460.
SUPPLEMENTARY INFORMATION:
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 312
[SFUND–2004–0001; FRL–7989–7]
RIN 2050–AF04
Standards and Practices for All
Appropriate Inquiries
Environmental Protection
Agency.
ACTION: Final rule.
AGENCY:
I. General Information
The Environmental Protection
Agency (EPA) today is establishing
federal standards and practices for
conducting all appropriate inquiries as
required under sections 101(35)(B)(ii)
and (iii) of the Comprehensive
Environmental Response,
Compensation, and Liability Act
(CERCLA). Today’s final rule establishes
specific regulatory requirements and
standards for conducting all appropriate
inquiries into the previous ownership
and uses of a property for the purposes
of meeting the all appropriate inquiries
provisions necessary to qualify for
certain landowner liability protections
under CERCLA. The standards and
practices also will be applicable to
persons conducting site characterization
and assessments with the use of grants
awarded under CERCLA section
104(k)(2)(B).
SUMMARY:
This final rule is effective
November 1, 2006.
ADDRESSES: EPA established a docket
for this action under Docket ID No.
SFUND–2004–0001. All documents in
the docket are listed in the EDOCKET
index at https://www.epa.gov/edocket.
Although listed in the index, some
information is not publicly available,
i.e., information labeled Confidential
Business Information (CBI) or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
is not placed on the Internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available either
electronically in EDOCKET or in hard
copy at the EPA Docket Center, EPA
West Building, Room B102, 1301
Constitution Ave., NW., Washington,
DC. This docket facility is open from
8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding Federal holidays. The
telephone number for the Public
Reading Room is (202) 566–1744, and
the telephone number for the OSWER
Docket is (202) 566–0276.
FOR FURTHER INFORMATION CONTACT: For
further information on specific aspects
DATES:
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A. Who Potentially May be Affected by
Today’s Rule?
This regulation may affect most
directly those persons and businesses
purchasing commercial property or any
property that will be used for
commercial or public purposes and who
may, after purchasing the property, seek
to claim protection from CERCLA
liability for releases or threatened
releases of hazardous substances. Under
section101(35)(B) of CERCLA, as
amended by the Small Business
Liability Relief and Brownfields
Revitalization Act (Pub. L. 107–118, 115
stat. 2356, ‘‘the Brownfields
Amendments’’) such persons and
businesses are required to conduct all
appropriate inquiries prior to or on the
date on which the property is acquired.
Prospective landowners who do not
conduct all appropriate inquiries prior
to or on the date of obtaining ownership
of the property may lose their ability to
claim protection from CERCLA liability
as an innocent landowner, bona fide
prospective purchaser, or contiguous
property owner.
In addition, today’s rule will affect
any party who receives a brownfields
grant awarded under CERCLA section
104(k)(2)(B) and uses the grant money to
conduct site characterization or
assessment activities. This includes
state, local and tribal governments that
receive brownfields site assessment
grants for the purpose of conducting site
characterization and assessment
activities. Such parties are required
under CERCLA section 104(k)(2)(B)(ii)
to conduct such activities in compliance
with the standards and practices
established by EPA for the conduct of
all appropriate inquiries. EPA notes that
today’s rule also may affect other parties
who apply for brownfields grants under
the provisions of CERCLA section
104(k), since such parties may have to
qualify as a bona fide prospective
purchaser to ensure compliance with
the statutory prohibitions on the use of
grant funds under Section
104(k)(4)(B)(I). Any party seeking
liability protection as a bona fide
prospective purchaser, including
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eligible brownfields grantees, must
conduct all appropriate inquiries prior
to or on the date of acquiring a property.
The background document,
‘‘Economic Impacts Analysis for the
Proposed All Appropriate Inquiries
Final Regulation’’ and the Addendum to
this document provide a comprehensive
analysis of all potentially impacted
entities. These documents are available
in the docket established for today’s
rule. A summary of potentially affected
businesses is provided in the table
below.
Our aim in the table below is to
provide a guide for readers regarding
entities likely to be directly regulated or
indirectly affected by today’s action.
This action, however, may affect other
entities not listed in the table. To
determine whether you or your business
is regulated or affected by this action,
you should examine the regulatory
language amending CERCLA. This
language is found at the end of this
Federal Register notice. If you have
questions regarding the applicability of
this action to a particular entity, consult
the person listed in the preceding
section entitled FOR FURTHER
INFORMATION CONTACT.
Industry category
Manufacturing .................................
Wholesale Trade ............................
Retail Trade ....................................
Finance and Insurance ...................
Real Estate .....................................
Professional, Scientific and Technical Services ..............................
Accommodation and Food Services
Repair and Maintenance ................
Personal and Laundry Services .....
State, Local and Tribal Government ............................................
NAICS
code
31–33
42
44–45
52
531
541
72
811
812
N/A
B. How Can I Get Copies of This
Document and Other Related
Information?
1. Docket. EPA established an official
public docket for this action under
Docket ID No. SFUND–2004–0001. The
official public docket consists of the
documents specifically referenced in
this action, any public comments
received, and other information related
to today’s action. Although a part of the
official docket, the public docket does
not include Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Documents in the official public docket
are listed in the index list in EPA’s
electronic public docket and comment
system, EDOCKET. Documents may be
available either electronically or in hard
copy. Electronic documents may be
viewed through EDOCKET. Hard copy
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documents may be viewed at the EPA
Docket Center, EPA West, Room B102,
1301 Constitution Avenue, NW.,
Washington, DC. The EPA Docket
Center Public Reading Room is open
from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding Federal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number for the
OSWER Docket is (202) 566–0276.
2. Electronic Access. You may access
this Federal Register document
electronically through the EPA Internet
under the ‘‘Federal Register’’ listings at
https://www.epa.gov/fedrgstr.
An electronic version of the public
docket also is available through EPA’s
electronic public docket and comment
system, EDOCKET. You may use
EDOCKET at https://www.epa.gov/
edocket/ to view public comments,
access the index listing of the contents
of the public docket, and access those
documents in the public docket that are
available electronically. Once in the
system, select ‘‘search,’’ then key in the
appropriate docket identification
number.
Certain types of information will not
be placed in EDOCKET. Information
claimed as CBI and other information
whose disclosure is restricted by statute,
which is not included in the official
public docket, will not be available for
public viewing in EPA’s electronic
public docket. EPA’s policy is that
copyrighted material will not be placed
in EPA’s electronic public docket but
will be available only in printed, paper
form in the official public docket.
Docket materials that are not available
electronically may be viewed at the
docket facility identified above.
Contents of Today’s Rule
I. Statutory Authority
II. Background
A. What is the Intent of Today’s Rule?
B. What is ‘‘All Appropriate Inquiries?’’
C. What were the Previous Standards for
All Appropriate Inquiries?
D. What are the Liability Protections
Established Under the Brownfields
Amendments?
E. What Criteria Did Congress Establish for
the All Appropriate Inquiries Standard?
III. Summary of Comments and Changes
From Proposed Rule to Final Rule
IV. Detailed Description of Today’s Rule
A. What is the Purpose and Scope of the
Rule?
B. To Whom is the Rule Applicable?
C. Does the Final Rule Include Any New
Reporting or Disclosure Obligations?
D. What are the Final Documentation
Requirements?
E. What are the Qualifications for an
Environmental Professional?
F. References
G. What is Included in ‘‘All Appropriate
Inquiries?’’
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H. Who is Responsible for Conducting the
All Appropriate Inquiries?
I. When Must All Appropriate Inquiries be
Conducted?
J. Can a Prospective Landowner Use
Information Collected for Previous
Inquiries Completed for the Same
Property?
K. Can All Appropriate Inquiries be
Conducted by One Party and Transferred
to Another Party?
L. What Are the Objectives and
Performance Factors for the All
Appropriate Inquiries Requirements?
M. What are Institutional Controls?
N. How must Data Gaps Be Addressed in
the Conduct of All Appropriate
Inquiries?
O. Do Small Quantities of Hazardous
Substances That Do Not Pose Threats to
Human Health and the Environment
Have to Be Identified in the Inquiries?
P. What are the Requirements for
Interviewing Past and Present Owners,
Operators, and Occupants?
Q. What are the Requirements for Reviews
of Historical Sources of Information?
R. What are the Requirements for
Searching for Recorded Environmental
Cleanup Liens?
S. What are the Requirements for
Reviewing Federal, State, Tribal, and
Local Government Records?
T. What are the Requirements for Visual
Inspections of the Subject Property and
Adjoining Properties?
U. What are the Requirements for the
Inclusion of Specialized Knowledge or
Experience on the Part of the
‘‘Defendant?’’
V. What are the Requirements for the
Relationship of the Purchase Price to the
Value of the Property, if the Property was
not Contaminated?
W. What are the Requirements for
Commonly Known or Reasonably
Ascertainable Information about the
Property?
X. What are the Requirements for ‘‘the
Degree of Obviousness of the Presence or
Likely Presence of Contamination at the
Property, and the Ability to Detect the
Contamination by Appropriate
Investigation?’’
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination with Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children from Environmental Risks and
Safety Risks
H. Executive Order 13211: Actions that
Significantly Affect Energy Supply,
Distribution or Use
I. National Technology Transfer
Advancement Act
J. Executive Order 12898: Federal Actions
to Address Environmental Justice in
Minority Populations and Low-Income
Populations
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K. Congressional Review Act
I. Statutory Authority
These regulations are promulgated
under the authority of Section
101(35)(B) of the Comprehensive
Environmental Response,
Compensation, and Liability Act of 1980
(42 U.S.C. 9601), as amended, most
importantly by the Small Business
Liability Relief and Brownfields
Revitalization Act.
II. Background
A. What is the Intent of Today’s Rule?
On August 26, 2004, EPA published a
notice of proposed rulemaking outlining
proposed standards and practices for the
conduct of ‘‘all appropriate inquiries.’’
This regulatory action was initiated in
response to legislative amendments to
the Comprehensive Environmental
Response, Compensation, and Liability
Act (CERCLA). On January 11, 2002,
President Bush signed the Small
Business Liability Relief and
Brownfields Revitalization Act (Pub. L.
107–118, 115 Stat. 2356, ‘‘the
Brownfields Amendments’’). The
Brownfields Amendments amend
CERCLA by providing funds to assess
and clean up brownfields sites,
clarifying CERCLA liability provisions
for certain landowners, and providing
funding to enhance state and tribal
cleanup programs. The intent of today’s
rule is to finalize regulations setting
federal standards and practices for the
conduct of all appropriate inquiries, a
key provision of the Brownfields
Amendments. Subtitle B of Title II of
the Brownfields Amendments revises
CERCLA section 101(35), clarifying the
requirements necessary to establish the
innocent landowner defense. In
addition, the Brownfields Amendments
add protections from CERCLA liability
for bona fide prospective purchasers
and contiguous property owners who
meet certain statutory requirements.
Each of the CERCLA liability
provisions for innocent landowners,
bona fide prospective purchasers, and
contiguous property owners, requires
that, among other requirements, persons
claiming the liability protections
conduct all appropriate inquiries into
prior ownership and use of a property
prior to or on the date a person acquires
a property. The law requires EPA to
develop regulations establishing
standards and practices for how to
conduct all appropriate inquiries.
Congress included in the Brownfields
Amendments a list of criteria that the
Agency must address in the regulations
establishing standards and practices for
conducting all appropriate inquiries
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section 101(35)(2)(B)(ii) and (iii). The
Brownfields Amendments also require
that parties receiving a federal
brownfields grant awarded under
CERCLA section 104(k)(2)(B) to conduct
site characterizations and assessments
must conduct these activities in
accordance with the standards and
practices for all appropriate inquiries.
The regulations established today
only address the all appropriate
inquiries provisions of CERCLA sections
101(35)(B)(i)(I) and 101(35)(B)(ii) and
(iii). Today’s rule does not address the
requirements of CERCLA section
101(35)(B)(i)(II) for what constitutes
‘‘reasonable steps.’’
B. What is ‘‘All Appropriate Inquiries?’’
An essential step in real property
transactions may be evaluating a
property for potential environmental
contamination and assessing potential
liability for contamination present at the
property. The process for assessing
properties for the presence or potential
presence of environmental
contamination often is referred to as
‘‘environmental due diligence,’’ or
‘‘environmental site assessment.’’ The
Comprehensive Environmental
Response Compensation and Liability
Act (CERCLA) or Superfund, provides
for a similar, but legally distinct,
process referred to as ‘‘all appropriate
inquiries.’’
Under CERCLA, persons may be held
strictly liable for cleaning up hazardous
substances at properties that they either
currently own or operate or owned or
operated at the time of disposal. Strict
liability in the context of CERCLA
means that a potentially responsible
party may be liable for environmental
contamination based solely on property
ownership and without regard to fault
or negligence.
In 1986, the Superfund Amendments
and Reauthorization Act ( Pub. L. No.
99–499, 100 stat. 1613, ‘‘SARA’’)
amended CERCLA by creating an
‘‘innocent landowner’’ defense to
CERCLA liability. The new section
101(35)(B) of CERCLA provided a
defense to CERCLA liability, for those
persons who could demonstrate, among
other requirements, that they ‘‘did not
know and had no reason to know’’ prior
to purchasing a property that any
hazardous substance that is the subject
of a release or threatened release was
disposed of on, in, or at the property.
Such persons, to demonstrate that they
had ‘‘no reason to know’’ must have
undertaken, prior to, or on the date of
acquisition of the property, ‘‘all
appropriate inquiries’’ into the previous
ownership and uses of the property
consistent with good commercial or
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customary standards and practices. The
2002 Brownfields Amendments added
potential liability protections for
‘‘contiguous property owners’’ and
‘‘bona fide prospective purchasers’’ who
also must demonstrate they conducted
all appropriate inquiries, among other
requirements, to benefit from the
liability protection.
C. What Were the Previous Standards
for All Appropriate Inquiries?
As part of the Brownfields
Amendments to CERCLA, Congress
established interim standards for the
conduct of all appropriate inquiries. The
federal interim standards established by
Congress became effective on January
11, 2002. In the case of properties
purchased after May 31, 1997, the
interim standards include the
procedures of the ASTM Standard
E1527–97 (entitled ‘‘Standard Practice
for Environmental Site Assessments:
Phase 1 Environmental Site Assessment
Process’’). In the case of persons who
purchased property prior to May 31,
1997 and who are seeking to establish
an innocent landowner defense or
qualify as a contiguous property owner,
CERCLA provides that such persons
must establish, among other statutory
requirements, that at the time they
acquired the property, they did not
know and had no reason to know of
releases or threatened releases to the
property. To establish they did not
know and had no reason to know of
releases or threatened releases, persons
who purchased property prior to May
31, 1997 must demonstrate that they
carried out all appropriate inquiries into
the previous ownership and uses of the
property in accordance with generally
accepted good commercial and
customary standards and practices.
In the case of property acquired by a
non-governmental entity or noncommercial entity for residential or
other similar uses, the current interim
standards for all appropriate inquiries
may not be applicable. For those cases,
the Brownfields Amendments to
CERCLA establish that a ‘‘facility
inspection and title search that reveal
no basis for further investigation shall
be considered to satisfy the
requirements’ for all appropriate
inquiries. In addition, such properties
are not within the scope of today’s rule.
The interim standards remain in effect
only until the effective date of today’s
rule which promulgates federal
regulations establishing standards and
practices for conducting all appropriate
inquiries.
On May 9, 2003, EPA published a
final rule (68 FR 24888) clarifying that
for the purposes of achieving the all
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appropriate inquiries standards of
CERCLA section 101(35)(B), and until
the effective date of today’s regulation,
persons who purchase property on or
after May 31, 1997 could use either the
procedures provided in ASTM E1527–
2000, entitled ‘‘Standard Practice for
Environmental Site Assessments: Phase
I Environmental Site Assessment
Process,’’ or the earlier standard cited by
Congress in the Brownfields
Amendments, ASTM E1527–97.
Today’s notice is a final rule and as
such replaces the current interim
standards for all appropriate inquiries
established by Congress in the
Brownfields Amendments and clarified
by EPA in the May 9, 2003 final rule.
Since the Agency is promulgating a final
rule establishing federal regulations
containing the standards and practices
for conducting all appropriate inquiries,
the interim standard will no longer be
the operative standard for conducting
all appropriate inquiries upon
November 1, 2006, the effective date of
today’s rule. Until November 1, 2006,
both the standards and practices
included in today’s final regulation and
the current interim standards
established by Congress for all
appropriate inquiries will be recognized
by EPA as satisfying the statutory
requirements for the conduct of all
appropriate inquiries under section
101(35)(B) of CERCLA.
D. What are the Liability Protections
Established Under the Brownfields
Amendments?
The Brownfields Amendments
provide important liability protections
for landowners who qualify as
contiguous property owners, bona fide
prospective purchasers, or innocent
landowners. To meet the statutory
requirements for any of these landowner
liability protections, a landowner must
meet certain threshold requirements and
satisfy certain continuing obligations.
To qualify as a bona fide prospective
purchaser, contiguous property owner,
or innocent landowner, a person must
perform ‘‘all appropriate inquiries’’ on
or before the date on which the person
acquired the property. Bona fide
prospective purchasers and contiguous
property owners also must demonstrate
that they are not potentially liable or
affiliated with any other person that is
potentially liable for response costs at
the property. In the case of contiguous
property owners, the landowner
claiming to be a contiguous property
owner also must demonstrate that he
did not cause, contribute, or consent to
any release or threatened release of
hazardous substances. To meet the
statutory requirements for a bona fide
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prospective purchaser, a property owner
must have acquired a property
subsequent to any disposal activities
involving hazardous substances at the
property.
Continuing obligations required under
the statute include complying with land
use restrictions and not impeding the
effectiveness or integrity of institutional
controls; taking ‘‘reasonable steps’’ with
respect to hazardous substances
affecting a landowner’s property to
prevent releases; providing cooperation,
assistance and access to EPA, a state, or
other party conducting response actions
or natural resource restoration at the
property; complying with CERCLA
information requests and administrative
subpoenas; and providing legally
required notices. For a more detailed
discussion of these threshold and
continuing requirements please see
EPA, Interim Guidance Regarding
Criteria Landowners Must Meet in
Order to Qualify for Bona Fide
Prospective Purchaser, Contiguous
Property Owner, or Innocent Landowner
Limitations on CERCLA Liability
(Common Elements, 2003). A copy of
this document is available in the docket
for today’s rule.
EPA notes that, as explained below,
persons conducting all appropriate
inquiries in compliance with today’s
final rule are not entitled to the CERCLA
liability protections provided for
innocent landowners, bona fide
prospective purchasers, and contiguous
property owners, unless they also
comply with all of the continuing
obligations established under the
statute. As explained below, compliance
with today’s final rule is only one
requirement necessary for CERCLA
liability protection. We also note that
the requirements of today’s rule apply to
prospective property owners who are
seeking protection from liability under
the federal Superfund Law (CERCLA).
Prospective property owners wishing to
establish protection from, or a defense
to, liability under state superfund or
other related laws must comply with the
all criteria established under state laws,
including any criteria for conducting
site assessments or all appropriate
inquiries established under applicable
state statutes or regulations.
1. Bona Fide Prospective Purchaser
The Brownfields Amendments added
a new bona fide prospective purchaser
provision at CERCLA section 107(r). The
provision provides protection from
CERCLA liability, and limits EPA’s
recourse for unrecovered response costs
to a lien on property for the lesser of the
unrecovered response costs or increase
in fair market value attributable to
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EPA’s response action. To meet the
statutory requirements for a bona fide
prospective purchaser, a person must
meet the requirements set forth in
CERCLA sections 101(40) and 107(r). A
bona fide prospective purchaser must
have bought property after January 11,
2002 (the date of enactment of the
Brownfields Amendments). A bona fide
prospective purchaser may purchase
property with knowledge of
contamination after performing all
appropriate inquiries, provided the
property owner meets or complies with
all of the other statutory requirements
set forth in CERCLA section 101(40).
Conducting all appropriate inquiries
alone does not provide a landowner
with protection against CERCLA
liability. Landowners who want to
qualify as bona fide prospective
purchasers must comply with all of the
statutory requirements. The statutory
requirements include, without
limitation, that the landowner must:
• Have acquired a property after all
disposal of hazardous substances at the
property ceased;
• Provide all legally required notices
with respect to the discovery or release
of any hazardous substances at the
property;
• Exercise appropriate care by taking
reasonable steps to stop continuing
releases, prevent any threatened future
release, and prevent or limit human,
environmental, or natural resources
exposure to any previously released
hazardous substance;
• Provide full cooperation, assistance,
and access to persons that are
authorized to conduct response actions
or natural resource restorations;
• Comply with land use restrictions
established or relied on in connection
with a response action;
• Not impede the effectiveness or
integrity of any institutional controls;
• Comply with any CERCLA request
for information or administrative
subpoena; and
• Not be potentially liable, or
affiliated with any other person who is
potentially liable for response costs for
addressing releases at the property.
Persons claiming to be bona fide
prospective purchasers should keep in
mind that failure to identify an
environmental condition or identify a
release or threatened release of a
hazardous substance on, at, in or to a
property during the conduct of all
appropriate inquiries does not relieve a
landowner from complying with the
other post-acquisition statutory
requirements for obtaining the liability
protections. Landowners must comply
with all the statutory requirements to
obtain the liability protection. For
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example, an inability to identify a
release or threatened release during the
conduct of all appropriate inquiries
does not negate the landowner’s
responsibilities under the statute to take
reasonable steps to stop a release,
prevent a threatened release, and
prevent exposure to any previous
release once any release is identified.
Compliance with the other statutory
requirements for the bona fide
prospective purchaser liability
protection is not contingent upon the
findings of all appropriate inquiries.
2. Contiguous Property Owner
The Brownfields Amendments added
a new contiguous property owner
provision at CERCLA section 107(q).
This provision excludes from the
definition of ‘‘owner’’ or ‘‘operator’’
under CERCLA section 107(a)(1) and (2)
a person who owns property that is
‘‘contiguous to, or otherwise similarly
situated with respect to, and that is or
may be contaminated by a release or
threatened release of a hazardous
substance from’’ property owned by
someone else. To qualify as a
contiguous property owner, a
landowner must have no knowledge or
reason to know of contamination at the
time of acquisition, have conducted all
appropriate inquiries, and meet all of
the criteria set forth in CERCLA section
107(q)(1)(A), which include, without
limitation:
• Not causing, contributing, or
consenting to the release or threatened
release;
• Not being potentially liable nor
affiliated with any other person who is
potentially liable for response costs at
the property;
• Taking reasonable steps to stop
continuing releases, prevent any
threatened release, and prevent or limit
human, environmental, or natural
resource exposure to any hazardous
substances released on or from the
landowner’s property;
• Providing full cooperation,
assistance, and access to persons that
are authorized to conduct response
actions or natural resource restorations;
• Complying with land use
restrictions established or relied on in
connection with a response action;
• Not impeding the effectiveness or
integrity of any institutional controls;
• Complying with any CERCLA
request for information or
administrative subpoena;
• Providing all legally required
notices with respect to discovery or
release of any hazardous substances at
the property.
The contiguous property owner
liability protection ‘‘protects parties that
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are essentially victims of pollution
incidents caused by their neighbor’s
actions.’’ S. Rep. No. 107–2, at 10
(2001). Contiguous property owners
must perform all appropriate inquiries
prior to purchasing property. However,
performing all appropriate inquiries in
accordance with the regulatory
requirements alone is not sufficient to
assert the liability protections afforded
under CERCLA. Property owners must
fully comply with all of the statutory
requirements to be afforded the
contiguous property owner liability
protection. Persons who know, or have
reason to know, that the property is or
could be contaminated at the time of
acquisition of a property cannot qualify
for the liability protection as a
contiguous property owner, but may be
entitled to bona fide prospective
purchaser status.
Persons claiming to be contiguous
property owners should keep in mind
that failure to identify an environmental
condition or identify a release or
threatened release of a hazardous
substance on, at, in or to a property
during the conduct of all appropriate
inquiries, does not relieve a landowner
from complying with the other statutory
requirements for obtaining the
contiguous landowner liability
limitation. Landowners must comply
with all the statutory requirements to
qualify for the liability protections. For
example, an inability to identify a
release or threatened release during the
conduct of all appropriate inquiries
does not negate the landowner’s
responsibilities under the statute to take
reasonable steps to stop the release,
prevent a threatened release, and
prevent exposure to previous releases
once a release is identified. None of the
other statutory requirements for the
contiguous property owner liability
protection is contingent upon the results
of the conduct of all appropriate
inquiries.
3. Innocent Landowner
The Brownfields Amendments also
clarify the innocent landowner defense.
To qualify as an innocent landowner, a
person must conduct all appropriate
inquiries and meet all of the statutory
requirements. The requirements
include, without limitation:
• Having no knowledge or reason to
know that any hazardous substance
which is the subject of a release or
threatened release was disposed of on,
in, or at the facility;
• Providing full cooperation,
assistance and access to persons
authorized to conduct response actions
at the property;
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• Complying with any land use
restrictions and not impeding the
effectiveness or integrity of any
institutional controls;
• Taking reasonable steps to stop
continuing releases, prevent any
threatened release, and prevent or limit
human, environmental, or natural
resource exposure to any previously
released hazardous substances;
To successfully assert an innocent
landowner liability defense, a property
owner must demonstrate compliance
with CERCLA section 107(b)(3) as well.
Such persons must establish, by a
preponderance of the evidence:
• That the release or threat of release
of hazardous substances and the
resulting damages were caused by an act
or omission of a third party with whom
the person does not have employment,
agency, or a contractual relationship;
• The person exercised due care with
respect to the hazardous substance
concerned, taking into consideration the
characteristics of such hazardous
substance, in light of all relevant facts
and circumstances;
• Took precautions against
foreseeable acts or omissions of any
such third party and the consequences
that could foreseeably result from such
acts or omissions.
Like contiguous property owners,
innocent landowners must perform all
appropriate inquiries prior to or on the
date of acquisition of a property and
cannot know, or have reason to know,
of contamination to qualify for this
landowner liability protection. Persons
claiming to be innocent landowners also
should keep in mind that failure to
identify an environmental condition or
identify a release or threatened release
of a hazardous substance on, at, in or to
a property during the conduct of all
appropriate inquiries, does not relieve
or exempt a landowner from complying
with the other statutory requirements
for asserting the innocent landowner
defense. Landowners must comply with
all the statutory requirements to obtain
the defense. For example, an inability to
identify a release or threatened release
during the conduct of all appropriate
inquiries does not negate the
landowner’s responsibilities under the
statute to take reasonable steps to stop
the release, prevent a threatened release,
and prevent exposure to a previous
release. Compliance with the other
statutory requirements for the innocent
landowner defense is not contingent
upon the results of an all appropriate
inquiries investigation.
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E. What Criteria Did Congress Establish
for the All Appropriate Inquiries
Standard?
Congress included in the Brownfields
Amendments a list of criteria that the
Agency must include in the regulations
establishing standards and practices for
conducting all appropriate inquiries. In
addition to providing these criteria in
the statute, Congress instructed EPA to
develop regulations establishing
standards and practices for conducting
all appropriate inquiries in accordance
with generally accepted good
commercial and customary standards
and practices. The criteria are set forth
in CERCLA section 101(35)(2)(B)(iii)
and include:
• The results of an inquiry by an
environmental professional.
• Interviews with past and present
owners, operators, and occupants of the
facility for the purpose of gathering
information regarding the potential for
contamination at the facility.
• Reviews of historical sources, such
as chain of title documents, aerial
photographs, building department
records, and land use records, to
determine previous uses and
occupancies of the real property since
the property was first developed.
• Searches for recorded
environmental cleanup liens against the
facility that are filed under federal,
state, or local law.
• Reviews of federal, state, and local
government records, waste disposal
records, underground storage tank
records, and hazardous waste handling,
generation, treatment, disposal, and
spill records, concerning contamination
at or near the facility.
• Visual inspections of the facility
and of adjoining properties.
• Specialized knowledge or
experience on the part of the defendant.
• The relationship of the purchase
price to the value of the property, if the
property was not contaminated.
• Commonly known or reasonably
ascertainable information about the
property.
• The degree of obviousness of the
presence or likely presence of
contamination at the property, and the
ability to detect the contamination by
appropriate investigation.
III. Summary of Comments and
Changes From Proposed Rule to Final
Rule
EPA received over 400 public
comments in response to the August 26,
2004 proposed rule. Comments were
received from environmental
consultants with experience in
performing site assessments, trade
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associations, state government agencies,
environmental interest groups, and
other public interest associations.
Commenters generally supported the
purpose and goals of the proposed rule.
Many commenters complimented the
Agency on its decision to develop the
proposed rule using the negotiated
rulemaking process. However,
commenters had differing views on
certain aspects of the proposed rule. In
particular, the Agency received widely
differing views on the proposed
definition of ‘‘environmental
professional.’’ Although many
commenters supported the definition as
proposed, other commenters raised
concerns regarding the stringency of the
proposed qualifications. A significant
number of commenters applauded the
proposed definition of an environmental
professional and stated that it may
increase the rigor and caliber of
environmental site investigations.
Commenters who would not qualify as
an environmental professional under
the proposed definition raised concerns
with regard to the specific qualifications
proposed.
EPA received a significant number of
comments regarding the statutory
requirements for qualifying for the
CERCLA liability protections. Several
commenters also raised concerns with
regard to the performance-based
approach to the all appropriate inquiries
investigation included in the proposed
rule. Commenters were concerned that
the proposed performance-based
approach would make it more difficult
to qualify for the CERCLA liability
protections than an approach that
requires strict adherence to prescriptive
data gathering requirements that do not
allow for the application of professional
judgment. However, the vast majority of
commenters who commented on the
performance-based nature of the
proposed rule supported the proposed
approach.
Other commenters raised concerns
with regard to the proposed rule’s
requirements to identify and comment
upon the significance of ‘‘data gaps’’
where the lack of information may affect
the ability of an environmental
professional to render an opinion
regarding conditions at a property that
are indicative of releases or threatened
releases of hazardous substances.
Commenters were concerned that if any
data gaps exist potential contamination
would not be identified, allowing
property owners to escape liability for
contamination. Other commenters
supported the proposed requirement to
identify data gaps, or missing
information, that may affect the
environmental professional’s ability to
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render an opinion regarding the
environmental conditions at a property
and comment on their significance in
this regard and stated that the
requirement would lend credibility to
the inquiry’s final report.
We received many comments on the
proposed provision to compare the
purchase price of a property to the fair
market value of the property (if the
property were not contaminated). One
concern raised is that commenters
believe that the exact market value of a
property is difficult to determine. Some
commenters took exception to the fact
that EPA did not propose that
prospective landowners have to conduct
formal real estate appraisals of the
property to determine fair market value.
Although this provision has been a
statutory requirement for the conduct of
all appropriate inquiries since 1986,
some commenters thought the
requirement should not be included
within the scope of all appropriate
inquiries. Other commenters stated that
the environmental professional should
not be required to undertake the
comparison.
We received some comments on the
results of the economic impact analysis
that was conducted to assess the
potential costs and impacts of the
proposed rule. Many commenters
generally agreed with the Agency’s
conclusion that the average incremental
cost increase associated with the
requirements in the proposed rule over
the current industry standard would be
minimal. However, some commenters
asserted that EPA underestimated the
incremental costs associated with the
proposed rule. Although a few
commenters mentioned particular
activities included as requirements in
the proposed rule that would increase
the burdens and costs associated with
conducting all appropriate inquiries,
most of these commenters did not
provide specific reasons for claimed
cost increases over baseline activities.
Some commenters simply stated that the
proposed requirements would result in
an increase in the price of phase I
environmental site assessments. We
provide a summary of the comments
received on the economic impact
analysis for the proposed rule, our
responses to issues raised by
commenters, and the results of some
additional analyses conducted based on
some of the issues raised, in an
addendum to the economic impact
analysis, which is provided in the
docket for today’s final rule.
In section IV of this preamble, we
discuss the requirements of the final
rule, including a summary of the
provisions included in the August 26,
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66075
2004 proposed rule, the significant
comments raised in response to the
proposed provisions, and a summary of
our rationale for the final rule
requirements. Generally, the final rule
closely resembles the provisions
included in the proposed rule. We
adopted relatively minor changes in
response to public comments. For
example, we received a number of
comments urging EPA to modify the
proposed definition of environmental
professional to allow individuals who
have significant experience in
conducting environmental site
assessments, but do not have a
Baccalaureate degree, to qualify as
environmental professionals. We were
convinced by the arguments presented
in many of these public comments.
Therefore, the definition of an
environmental professional included in
today’s final rule allows individuals
with ten years of relevant full time
experience to qualify as an
environmental professional for the
purpose of overseeing and performing
all appropriate inquiries.
With respect to the proposed
requirements governing the use of
previously-conducted environmental
site assessments for a particular
property, we agreed with commenters
who pointed out the proposed rule was
unclear. In today’s final rule, we modify
the proposed rule language to allow for
the use of information contained in
previously-conducted assessments, even
if the information was collected more
than a year prior to the date on which
the subject property is acquired. The
final rule does require that all aspects of
a site assessment, or all appropriate
inquiries investigation, completed more
than one year prior to the date of
acquisition of the subject property be
updated to reflect current conditions
and current property-specific
information. In the case of all
appropriate inquiries investigations
completed less than one year prior to
the date of acquisition of the subject
property but more than 180 days before
the acquisition date, the final rule
retains the requirements of the proposed
rule that only certain aspects of the all
appropriate inquiries must be updated.
In the case of the requirement to
search for institutional controls that was
included in the proposed requirements
to review federal, state, tribal and local
government records, we agreed with
commenters who pointed out that
searching for institutional controls
associated with properties located
within a half mile of the subject
property is overly burdensome and
without sufficient benefit to the purpose
of the investigation. The final rule
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requires that the search for institutional
controls be confined to the subject
property only.
We adopted one other change in the
final rule, based upon public comments.
In the proposed rule, we delineated
responsibilities for particular aspects of
the all appropriate inquiries
investigation between the
environmental professional and the
prospective landowner of the subject
property (or grantee). We defined the
inquiry of the environmental
professional to include: interviews with
past and present owners, operators and
occupants; reviews of historical sources
of information; reviews of federal state
tribal and local government records;
visual inspections of the facility and
adjoining property; commonly known or
reasonably ascertainable information;
and degree of obviousness of the
presence or likely presence of
contamination at the property and the
ability to detect the contamination by
appropriate investigation. We also
defined ‘‘additional inquiries’’ that must
be conducted by the prospective
landowner or grantee (or an individual
on the prospective landowner’s or
grantee’s behalf). These ‘‘additional
inquiries’’ include: specialized
knowledge or experience of the
prospective landowner (or grantee); the
relationship of the purchase price to the
fair market value of the property, if the
property was not contaminated; and
commonly known or reasonably
ascertainable information. The
requirement to search for environmental
cleanup liens was proposed to be the
responsibility of the prospective
landowner (or grantee), if the search is
not conducted by the environmental
professional. The proposed rule
required the prospective landowner (or
grantee) to provide all information
collected as part of the ‘‘additional
inquiries’’ to the environmental
professional.
The final rule retains the proposed
delineation of responsibilities. However,
based upon the input provided in public
comments, the final rule does not
require the prospective landowner (or
grantee) to provide the information
collected as part of the ‘‘additional
inquiries’’ to the environmental
professional. Although we continue to
believe that the information collected or
held by the prospective landowner (or
grantee) should be provided to the
environmental professional overseeing
the other aspects of the all appropriate
inquiries, we agree with commenters
who asserted that prospective
landowners and grantees should not be
required to provide this information to
the environmental professional.
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Commenters argued that property
owners (and grantees) may want to hold
some information (e.g., the purchase
price of the property) confidential.
CERCLA liability rests with the owner
or operator of a property and not with
an environmental professional hired by
the prospective landowner and who is
not involved with the ownership or
operation of the property. Since it
ultimately is up to the owner or operator
of a property to defend his or herself
against any claims to liability, we agree
with commenters that asserted that the
regulations should not require that
prospective landowners (or grantees)
provide information collected to comply
with the ‘‘additional inquiries’’
provisions to the environmental
professional. Should the required
information not be provided to the
environmental professional, the
environmental professional should
assess the impact that the lack of such
information may have on his or her
ability to render an opinion with regard
to conditions indicative of releases or
threatened releases of hazardous
substances on, at, in or to the property.
If the lack of information does impact
the ability of the environmental
professional to render an opinion with
regard to the environmental conditions
of the property, the environmental
professional should note the missing
information as a data gap in the written
report. We discuss each of the
requirements of the final rule in Section
IV of this preamble.
IV. Detailed Description of Today’s
Rule
A. What Is the Purpose and Scope of the
Rule?
The purpose of today’s rule is to
establish federal standards and practices
for the conduct of all appropriate
inquiries. Such inquiries must be
conducted by persons seeking any of the
landowner liability protections under
CERCLA prior to acquiring a property
(as outlined in Section II.D. of this
preamble). In addition, persons
receiving federal brownfields grants
under the authorities of CERCLA section
104(k)(2)(B) to conduct site
characterizations and assessments must
conduct such activities in compliance
with the all appropriate inquiries
regulations.
In the case of persons claiming one of
the CERCLA landowner liability
protections, the scope of today’s rule
includes the conduct of all appropriate
inquiries for the purpose of identifying
releases and threatened releases of
hazardous substances on, at, in or to the
property that would be the subject of a
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response action for which a liability
protection would be needed and such a
property is owned by the person
asserting protection from liability.
CERCLA liability is limited to releases
and threatened releases of hazardous
substances which cause the incurrence
of response costs. Therefore, in the case
of all appropriate inquiries conducted
for the purpose of qualifying for
protection from CERCLA liability
(CERCLA section 107), the scope of the
inquiries is to identify releases and
threatened releases of hazardous
substances which cause or threaten to
cause the incurrence of response costs.
In the case of persons receiving
Federal brownfields grants to conduct
site characterizations and assessments,
the scope of the all appropriate inquiries
standards and practices may be broader.
The Brownfields Amendments include a
definition of a ‘‘brownfield site’’ that
includes properties contaminated or
potentially contaminated with
substances not included in the
definition of ‘‘hazardous substance’’ in
CERCLA section 101(14). Brownfields
sites include properties contaminated
with (or potentially contaminated with)
hazardous substances, petroleum and
petroleum products, controlled
substances, and pollutants and
contaminants (as defined in CERCLA
section 101(33)). Therefore, in the case
of persons receiving federal brownfields
grant monies to conduct site assessment
and characterization activities at
brownfields sites, the scope of the all
appropriate inquiries may include these
other substances, as outlined in
§ 312.1(c)(2), to ensure that persons
receiving brownfields grants can
appropriately and fully assess the
properties as required. It is not the case
that every recipient of a brownfields
assessment grant has to include within
the scope of the all appropriate inquiries
petroleum and petroleum products,
controlled substances and CERCLA
pollutants and contaminants (as defined
in CERCLA section 101(33)). However,
in those cases where the terms and
conditions of the grant or the
cooperative agreement with the grantee
designate a broader scope to the
investigation (beyond CERCLA
hazardous substances), then the scope of
the all appropriate inquiries should
include the additional substances or
contaminants.
The scope of today’s rule does not
include property purchased by a nongovernmental entity or non-commercial
entity for ‘‘residential use or other
similar uses * * * [where] a facility
inspection and title search * * * reveal
no basis for further investigation.’’ (Pub.
L. 107–118 § 223). CERCLA section
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101(35)(B)(v) states that in those cases,
title search and facility inspection that
reveal no basis for further investigation
shall satisfy the requirements for all
appropriate inquiries.
We note that today’s rule does not
affect the existing CERCLA liability
protections for state and local
governments that acquire ownership to
properties involuntarily in their
functions as sovereigns, pursuant to
CERCLA sections 101(20)(D) and
101(35)(A)(ii). Involuntary acquisition
of properties by state and local
governments fall under those CERCLA
provisions and EPA’s policy guidance
on those provisions, not under the all
appropriate inquiry provisions of
CERCLA section 101(35)(B).
B. To Whom Is the Rule Applicable?
Today’s rule applies to any person
who may seek the landowner liability
protections of CERCLA as an innocent
landowner, contiguous property owner,
or bona fide prospective purchaser. The
statutory requirements to obtain each of
these landowner liability protections
include the conduct of all appropriate
inquiries. In addition, the rule applies to
individuals receiving Federal grant
monies under CERCLA section
104(k)(2)(B) to conduct site
characterization and assessment
activities. Persons receiving such grant
monies must conduct the site
characterization and assessment in
compliance with the all appropriate
inquiries regulatory requirements.
C. Does the Final Rule Include Any New
Reporting or Disclosure Obligations?
The final rule does not include any
new reporting or disclosure obligations.
The rule only applies to those property
owners who may seek the landowner
liability protections provided under
CERCLA for innocent landowners,
contiguous property owners or bona fide
prospective purchasers. The
documentation requirements included
in this rule are primarily intended to
enhance the inquiries by requiring the
environmental professional to record
the results of the inquiries and his or
her conclusions regarding conditions
indicative of releases and threatened
releases on, at, in, or to the property and
to provide a record of the environmental
professional’s inquiry. Today’s rule
contains no new requirements to notify
or submit information to EPA or any
other government entity.
Although today’s rule does not
include any new disclosure
requirements, CERCLA section 103 does
require persons in charge of vessels and
facilities, including on-shore and offshore facilities, to notify the National
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Response Center of any release of a
hazardous substance from the vessel or
facility in a quantity equal to or greater
than a ‘‘reportable quantity,’’ as defined
in CERCLA section 102(b). Today’s rule
includes no changes to this reporting
requirement nor any changes to any
other reporting or disclosure
requirements under federal, tribal, or
state law.
D. What Are the Final Documentation
Requirements?
The proposed rule required that the
environmental professional, on behalf of
the property owner, document the
results of the all appropriate inquiries in
a written report. As explained in the
preamble to the proposed rule, the
property owner could use this report to
document the results of the inquiries.
Such a report can be similar in nature
to the type of report previously
provided under generally accepted
commercial practices. We proposed no
requirements regarding the length,
structure, or specific format of the
written report. In addition, the proposed
rule did not require that a written report
of any kind be submitted to EPA or any
other government agency, or that a
written report be maintained on-site at
the subject property for any length of
time.
Today’s final rule retains the
requirements, as proposed, for
documenting the results of the all
appropriate inquiries investigation
conducted under the supervision or
responsible charge of an environmental
professional. As noted above, the
primary purpose of the documentation
requirement is to enhance the inquiry of
the environmental professional by
requiring that the environmental
professional record the results of the
inquiries and his or her conclusions.
The written report may allow any
person claiming one of the CERCLA
landowner liability protections to offer
documentation in support of his or her
claim that all appropriate inquiries were
conducted in compliance with the
federal regulations.1 The Agency notes
that while today’s final regulation does
not require parties conducting all
appropriate inquiries to retain the
written report or any other
documentation discovered, consulted,
or created in the course of conducting
the inquiries, the retention of such
documentation and records may be
1 Nothing in this regulation or preamble is
intended to suggest that any particular
documentation prepared in conducting all
appropriate inquiries will be admissible in court in
any litigation where a party raises one of the
liability protections, or will in any way alter the
judicial rules of evidence.
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66077
helpful should the property owner need
to assert protection from CERCLA
liability after purchasing a property.
The final rule requires that a written
report documenting the results of the all
appropriate inquiries include an
opinion of an environmental
professional as to whether the all
appropriate inquiries conducted
identified conditions indicative of
releases or threatened releases of
hazardous substances on, at, in or to the
subject property. The rule also requires
that the report identify data gaps in the
information collected that affect the
ability of the environmental
professional to render such an opinion
and that the environmental professional
comment on the significance of the data
gaps.
Several commenters raised issues
with regard to the proposed requirement
that the environmental professional
document and comment on the
significance of data gaps that affect the
ability of the environmental
professional to identify conditions
indicative of releases or threatened
releases of hazardous substances on at,
in, or to the subject property. Some
commenters stated that the need to
identify data gaps will make it difficult
to determine when an all appropriate
inquiries investigation is complete and
therefore the requirement would act as
a disincentive to the development of
potentially contaminated properties.
Other commenters asserted that the fact
that the regulations recognize data gaps
creates a loophole that would result in
property owners claiming to be
protected from CERCLA liability after
conducting an incomplete investigation
that includes significant data gaps.
These commenters raised concerns that
CERCLA liability protection could be
claimed by property owners simply
because they conducted an all
appropriate inquiries investigation, even
in those cases where releases on, at, in,
or to the property were missed during
the investigation. Other commenters
stated their support for the requirements
to document data gaps, as proposed. A
summary of EPA’s response to these
comments and the requirements for
documenting data gaps included in the
final rule is provided below in Section
IV.N.
The final rule, at § 312.21(d), retains
the proposed requirement that the
environmental professional who
conducts or oversees the all appropriate
inquiries sign the written report. There
are two purposes for the requirement to
include a signature in the report. First,
the individual signing the report must
declare, on the signature page, that he
or she meets the definition of an
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environmental professional, as provided
in § 312.10. In addition, the rule
requires that the environmental
professional declare that: [I, We] have
developed and performed the all
appropriate inquiries in conformance
with the standards and practices set
forth in 40 CFR part 312.
Some commenters raised concerns
about whether the proposed rule would
require the environmental professional
to certify the all appropriate inquiries
report and its findings. Today’s final
rule does not require the environmental
professional to ‘‘certify’’ the results of
the all appropriate inquiries when
signing the report. The two statements
or declarations mentioned above and
required to be included in the final
written report documenting the conduct
of all appropriate inquiries are meant to
document that an individual meeting
the qualifications of an environmental
professional was involved in the
conduct of the all appropriate inquiries
and that the activities performed by, or
under the supervision or responsible
charge of, the environmental
professional were performed in
conformance with the regulations.
Reports signed by individuals holding a
Professional Engineer (P.E.) or
Professional Geologist (P.G.) license,
need not include the individual’s
professional seal.
A few commenters requested that EPA
include specific requirements for the
content of a final report in the final rule.
Given that the type and extent of
information available on a particular
property may vary greatly with its size,
type, past uses, and location, and the
type and extent of information
necessary for an environmental
professional to render an opinion
regarding conditions indicative of
releases or threatened releases of
hazardous substances associated with
any property may vary, we decided not
to include in the final rule specific
requirements governing the content of
all reports.
The provisions of the final rule allow
for the property owner (or grantee) and
any environmental professional engaged
in the conduct of all appropriate
inquiries for a specific property to
design and develop the format and
content of a written report that will
meet the prospective landowner’s (or
grantee’s) objectives and information
needs in addition to providing
documentation that all appropriate
inquiries were completed prior to the
acquisition of the property, should the
landowner (or grantee) need to assert
protection from liability after
purchasing a property.
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E. What Are the Qualifications for an
Environmental Professional?
Proposed Rule
In the Brownfields Amendments,
Congress required that all appropriate
inquiries include ‘‘the results of an
inquiry by an environmental
professional’’ (CERCLA section
101(35)(B)(iii)(I)). The proposed rule
included minimal qualifications for
persons managing or overseeing all
appropriate inquiries. The intent of
setting minimum professional
qualifications, is to ensure that all
inquiries are conducted at a high level
of professional ability and ensure the
overall quality of both the inquiries
conducted and the conclusions or
opinions rendered with regard to
conditions indicative of the presence of
a release or threatened release on, at, in,
or to a property, based upon the results
of all inquiries. The proposed rule
required that an environmental
professional conducting or overseeing
all appropriate inquiries possess
sufficient specific education, training,
and experience necessary to exercise
professional judgment to develop
opinions and conclusions regarding the
presence of releases or threatened
releases of hazardous substances to the
surface or subsurface of a property. In
addition, the proposed rule included
minimum qualifications, including
minimum levels of education and
experience, that characterize the type of
professional who is best qualified to
oversee and direct the development of
comprehensive inquiries and provide
the landowner with sound conclusions
and opinions regarding the potential for
releases or threatened releases to be
present at the property. The proposed
rule allowed for individuals not meeting
the proposed definition of an
environmental professional to
contribute to and participate in the all
appropriate inquiries on the condition
that such individuals are conducting
inquiries activities under the
supervision or responsible charge of an
individual that meets the regulatory
definition of an environmental
professional.
The proposed rule required that the
final review of the all appropriate
inquiries and the conclusions that
follow from the inquiries rest with an
individual who qualifies as an
environmental professional, as defined
in proposed section § 312.10 of the
proposed rule. The proposed rule also
required that in signing the report, the
environmental professional must
document that he or she meets the
definition of an ‘‘environmental
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professional’’ included in the
regulations.
The proposed definition first and
foremost required that, to qualify as an
environmental professional, a person
must ‘‘possess sufficient specific
education, training, and experience
necessary to exercise professional
judgment to develop opinions and
conclusions regarding the presence of
releases or threatened releases * * * to
the surface or subsurface of a property,
sufficient to meet the objectives and
performance factors’’ that are provided
in the proposed regulation. The
proposed definition of an environmental
professional included individuals who
possess the following combinations of
education and experience.
• Hold a current Professional
Engineer’s (P.E.) or Professional
Geologist’s (P.G.) license or registration
from a state, tribe, or U.S. territory and
have the equivalent of three (3) years of
full-time relevant experience; or
• Be licensed or certified by the
federal government, a state, tribe, or
U.S. territory to perform environmental
inquiries as defined in § 312.21 and
have the equivalent of three (3) years of
full-time relevant experience; or
• Have a Baccalaureate or higher
degree from an accredited institution of
higher education in a relevant discipline
of engineering, environmental science,
or earth science and the equivalent of
five (5) years of full-time relevant
experience; or
• As of the date of the promulgation
of the final rule, have a Baccalaureate or
higher degree from an accredited
institution of higher education and the
equivalent of ten (10) years of full-time
relevant experience.
Public Comments
We received a significant number of
public comments on the proposed
definition of environmental
professional. Many commenters
supported the definition of
environmental professional as proposed.
However, a significant number of
commenters raised concerns with regard
to the proposed educational
requirements. Commenters pointed out
that the proposed minimum
qualifications for an environmental
professional did not allow for
individuals with many years of relevant
experience in conducting environmental
site assessments to qualify as
environmental professionals, if such
individuals do not have college degrees.
The proposed rule only allowed for
persons with a Baccalaureate degree or
higher in specific disciplines of science
and engineering, and a specific number
of years of experience, to qualify as an
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environmental professional, unless an
individual was otherwise licensed as an
environmental professional by a state,
tribe or the federal government. Some
commenters questioned the Agency’s
reasoning for restricting the degree
requirements to only certain types of
science or engineering. Commenters
requested that EPA provide more
specific definitions of the types of
science and engineering degrees that
would be necessary to qualify as an
environmental professional.
Commenters also asserted that the
proposed ‘‘grandfather clause’’ allowing
for individuals having a Baccalaureate
degree (or higher) and who accumulated
ten years of full time relevant
experience on or before the
promulgation date of the final rule to
qualify as an environmental
professional was too stringent and
provided too small of a window of
opportunity for individuals not
otherwise meeting the proposed
definition of environmental professional
to qualify.
Some commenters stated that the
definition of environmental professional
should not be restricted to those
individuals licensed as P.E.s or P.G.s. A
few commenters stated that a licensed
professional is no more qualified to
perform all appropriate inquiries
investigations than other individuals
with a significant number of years of
experience in conducting such
activities. Other commenters asserted
that only licensed P.E.s and P.G.s are
qualified to supervise all appropriate
inquiries activities.
EPA also received comments from
independent professional certification
organizations and members of these
organizations, including the Academy of
Certified Hazardous Materials Managers,
requesting that their organizations’
certification programs be named in the
regulatory definition of an
environmental professional.
Final Rule
After careful consideration of the
issues raised by commenters regarding
the proposed definition of
environmental professional, we made a
few modifications to the proposed
definition to reduce the potential
burden that the proposed definition may
have placed upon individuals who have
significant experience in conducting
environmental site assessments but do
not meet the proposed educational, or
college degree, requirements. We agree
with those commenters who asserted
that individuals with a significant
number of years of experience in
performing environmental site
assessments, or all appropriate inquiries
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investigations, should qualify as
environmental professionals for the
purpose of conducting all appropriate
inquiries, even in cases where such
individuals do not have a college
degree. Therefore, in the final rule,
persons with ten or more years of fulltime relevant experience in conducting
environmental site assessments and
related activities may qualify as
environmental professionals, without
having received a college degree.
In addition, we agreed with
commenters who pointed out that the
requirement that environmental
professionals hold specific types of
science or engineering degrees was too
limiting. In the final rule, persons with
any science or engineering degree
(regardless of specific discipline in
science or engineering) can qualify as an
environmental professional, if they also
meet the other required qualifications,
including the requirement to have five
(5) years of full-time relevant
experience.
We also agree with commenters who
asserted that the proposed grandfather
clause was too restrictive. As mentioned
above, we agree with commenters who
pointed out that individuals with a
significant number of years of
experience in conducting environmental
site assessments or all appropriate
inquiries investigations should be able
to qualify as environmental
professionals, for the purpose of
carrying out the provisions of today’s
rulemaking. In addition, we agree with
commenters who stated that the ability
for experienced professionals to qualify
as an environmental professional should
not be limited to those who meet the
threshold qualifications on the effective
date of the final rule. Therefore, the
proposed grandfather clause is not
included within the definition of
environmental professional in the final
rule. As explained above, in today’s
final rule, individuals with ten or more
years of full-time relevant experience in
conducting environmental site
assessments and related investigations
will qualify as environmental
professionals for the purposes of this
rulemaking.
The final rule retains the provision
recognizing as environmental
professionals those individuals who are
licensed by any tribal or state
government as a P.E. or P.G., and have
three years of full-time relevant
experience in conducting all
appropriate inquiries. We continue to
contend that such individuals have
sufficient specific education, training,
and experience necessary to exercise
professional judgment to develop
opinions and conclusions regarding
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conditions indicative of releases or
threatened releases on, at, in, or to a
property, including the presence of
releases to the surface or subsurface of
the property, sufficient to meet the
objectives and performance factors
provided in the regulation. The rigor of
the tribal- and state-licensed P.E. and
P.G. certification processes, including
the educational and training
requirements, as well as the
examination requirements, paired with
the requirement to have three years of
relevant professional experience
conducting all appropriate inquiries
will ensure that all appropriate inquiries
are conducted under the supervision or
responsible charge of an individual well
qualified to oversee the collection and
interpretation of site-specific
information and render informed
opinions and conclusions regarding the
environmental conditions at a property,
including opinions and conclusions
regarding conditions indicative of
releases or threatened releases of
hazardous substances and other
contaminants on, at, in, or to the
property. The Agency’s decision to
recognize tribal and state-licensed P.E.s
and P.G.s reflects the fact that tribal
governments and state legislatures hold
such professionals responsible (legally
and ethically) for safeguarding public
safety, public health, and the
environment. To become a P.E. or P.G.
requires that an applicant have a
combination of accredited college
education followed by approved
professional training and experience.
Once a publicly-appointed review board
approves a candidate’s credentials, the
candidate is permitted to take a rigorous
exam. The candidate must pass the
examination to earn a license, and
perform ethically to maintain it. After a
state or tribe grants a license to an
individual, and as a condition of
maintaining the license, many states
require P.E.s and P.G.s to maintain
proficiency by participating in approved
continuing education and professional
development programs. In addition,
tribal and state licensing boards can
investigate complaints of negligence or
incompetence on the part of licensed
professionals, and may impose fines and
other disciplinary actions such as cease
and desist orders or license revocation.
Although the final rule recognizes
tribal and state-licensed P.E. and P.G.s
and other such government licensed
environmental professionals with three
years of experience to be environmental
professionals, the rule does not restrict
the definition of an environmental
professional to these licensed
individuals. The definition of an
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environmental professional also
includes individuals who hold a
Baccalaureate or higher degree from an
accredited institution of higher
education in engineering or science and
have the equivalent of five (5) years of
full-time relevant experience in
conducting environmental site
assessments, or all appropriate
inquiries. In addition, individuals with
ten years of full-time relevant
experience in conducting environmental
site assessments, or all appropriate
inquiries qualify as environmental
professionals for the purpose of
conducting all appropriate inquiries.
Individuals with these qualifications
most likely will possess sufficient
specific education, training, and
experience necessary to exercise
professional judgment to develop
opinions and conclusions regarding
conditions indicative of releases or
threatened releases on, at, in, or to a
property, sufficient to meet the
objectives and performance factors
included in § 312.20(e) and (f).
In addition to the qualifications for
environmental professionals mentioned
above, EPA is retaining the proposed
provision to include within the
definition of an environmental
professional individuals who are
licensed to perform environmental site
assessments or all appropriate inquiries
by the Federal government (e.g., the
Bureau of Indian Affairs) or under a
state or tribal certification program,
provided that these individuals also
have three years of full-time relevant
experience. We contend that individuals
licensed by state and tribal
governments, or by any department or
agency within the federal government,
to perform all appropriate inquiries or
environmental site assessments, should
be allowed to qualify as an
environmental professional under
today’s regulation. State and tribal
agencies may best determine the
qualifications defining individuals who
‘‘possess sufficient specific education,
training, and experience necessary to
exercise professional judgment to
develop opinions and conclusions
regarding conditions indicative of
releases or threatened releases on, at, in,
or to a property, sufficient to meet the
rule’s objectives and performance
factors’’ within any particular state or
tribal jurisdiction.
In response to requests from members
of independent certification
organizations that EPA recognize in the
regulation those organizations whose
certification requirements meet the
environmental professional
qualifications included in the final rule,
we point out that today’s final rule does
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not reference any private party
professional certification standards.
Such an approach would require that
EPA review the certification
requirements of each organization to
determine whether or not each
organization’s certification requirements
meet or exceed the regulatory
qualifications for an environmental
professional. Given that there may be
many such organizations and given that
each organization may review and
change its certification qualifications on
a frequent or periodic basis, we
conclude that such a undertaking is not
practicable. EPA does not have the
necessary resources to review the
procedures of each private certification
organization and review and approve
each organization’s certification
qualifications. Therefore, the final rule
includes within the regulatory
definition of an environmental
professional, general performance-based
standards or qualifications for
determining who may meet the
definition of an environmental
professional for the purposes of
conducting all appropriate inquiries.
These standards include education and
experience qualifications, as
summarized below. The final rule does
not recognize, or reference, any private
organization’s certification program
within the context of the regulatory
language. However, the Agency notes
that any individual with a certification
from a private certification organization
where the organization’s certification
qualifications include the same or more
stringent education and experience
requirements as those included in
today’s final regulation will meet the
definition of an environmental
professional for the purposes of this
regulation.
Based upon the input received from
the public commenters, EPA determined
that the definition of environmental
professional included in today’s final
rule establishes a balance between the
merits of setting a high standard of
excellence for the conduct of all
appropriate inquiries through the
establishment of stringent qualifications
for environmental professionals and the
need to ensure that experienced and
highly competent individuals currently
conducting all appropriate inquiries are
not displaced.
Summary of Final Rule’s Definition of
Environmental Professional
In summary, the definition of
environmental professional included in
today’s final rule includes individuals
who possess the following
qualifications:
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• Hold a current Professional
Engineer’s or Professional Geologist’s
license or registration from a state, tribe,
or U.S. territory and have the equivalent
of three (3) years of full-time relevant
experience; or
• Be licensed or certified by the
federal government, a state, tribe, or
U.S. territory to perform environmental
inquiries as defined in § 312.21 and
have the equivalent of three (3) years of
full-time relevant experience; or
• Have a Baccalaureate or higher
degree from an accredited institution of
higher education in science or
engineering and the equivalent of five
(5) years of full-time relevant
experience; or
• Have the equivalent of ten (10)
years of full-time relevant experience.
The definition of ‘‘relevant
experience’’ is ‘‘participation in the
performance of environmental site
assessments 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
releases or threatened releases * * * to
the subject property.’’
The final rule retains the proposed
requirement that environmental
professionals remain current in their
field by participating in continuing
education or other activities and be able
to demonstrate such efforts.
The final rule also retains the
allowance for individuals not meeting
the definition of an environmental
professional to contribute to and
participate in the all appropriate
inquiries on the condition that such
individuals are conducting inquiries
activities under the supervision or
responsible charge of an individual that
meets the regulatory definition of an
environmental professional. This
provision allows for a team of
individuals working for the same firm or
organization (e.g., individuals working
for the same government agency) to
share the workload for conducting all
appropriate inquiries for a single
property, provided that one member of
the team meets the definition of an
environmental professional and reviews
the results and conclusions of the
inquiries and signs the final report.
The final rule requires that the final
review of the all appropriate inquiries
and the conclusions that follow from the
inquiries rest with an individual who
qualifies as an environmental
professional, as defined in § 312.10. The
final rule also requires that in signing
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the report, the environmental
professional must document that he or
she meets the definition of an
‘‘environmental professional’’ included
in the regulations.
F. References
Proposed Rule
In the proposed rule, the Agency
reserved a reference section and stated
in the preamble that we may include
references to applicable voluntary
consensus standards developed by
standards’ developing organizations that
are not inconsistent with the final
regulatory requirements for all
appropriate inquiries or otherwise
impractical. The Agency requested
comments regarding available
commercially accepted voluntary
consensus standards that may be
applicable to and compliant with the
proposed federal standards for all
appropriate inquiries.
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, section 12(d) (15 U.S.C. 272
note), directs agencies to use technical
standards that are developed or adopted
by voluntary consensus standards
bodies, unless their use 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. When developing the
proposed rule, EPA considered using an
existing voluntary consensus standard
developed by ASTM International as the
federal standard for all appropriate
inquiries. This standard is known as the
ASTM E1527–2000 standard (entitled
‘‘Standard Practice for Environmental
Site Assessments: Phase I
Environmental Site Assessment
Process’’). In the preamble to the
proposed rule, we acknowledged the
prevalent use of the ASTM E1527–2000
standard and the fact that it generally is
recognized as good and customary
commercial practice. However, when
we proposed the federal standards for
all appropriate inquiries, EPA
determined that the ASTM E1527–2000
standard is inconsistent with applicable
law. As a result, EPA chose not to
reference the ASTM E1527–2000
standard because it was inconsistent
with applicable law.
Public Comments
We received relatively few comments
citing available and applicable
voluntary consensus standards for
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conducting all appropriate inquiries.
Several commenters did argue that the
interim standard cited in the statute, the
ASTM E1527–97 Environmental Site
Assessments: Phase I Environmental
Site Assessment Process, or the updated
ASTM E1527–2000, is sufficient to meet
the statutory criteria. A few commenters
stated a preference for the ASTM
E1527–2000 standard over the
requirements included in the proposed
rule. ASTM International is a standards
development organization whose
committees develop voluntary
consensus standards for a variety of
materials, products, systems and
services. ASTM International is the only
standards development organization
that submitted a comment requesting
that the Agency consider its standard,
the ASTM E1527–2000 Standard
Practice for Environmental Site
Assessments: Phase I Environmental
Site Assessment Process, as an
equivalent standard to the federal
regulations.
Final Rule
Since publication of the proposed
rule, ASTM International and its E50
committee, the committee responsible
for the development of the ASTM
E1527–2000 Phase I Environmental Site
Assessment Process, has reviewed and
updated the ‘‘2000’’ version of the
E1527 standard to address EPA’s
concerns regarding the differences
between the ASTM E1527–2000
standard and the criteria established by
Congress in the Brownfields
Amendments to CERCLA. These
activities were conducted within the
normal review and updating process
that ASTM International undertakes for
each standard over a five-year cycle.
In today’s final rule, EPA is
referencing the standards and practices
developed by ASTM International and
known as Standard E1527–05 (entitled
‘‘Standard Practice for Environmental
Site Assessments: Phase I
Environmental Site Assessment
Process’’) and recognizing the E1527–05
standard as consistent with today’s final
rule. The Agency determined that this
voluntary consensus standard is
consistent with today’s final 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 E1527–05 standard to comply
with today’s final rule.
It is the Agency’s intent to allow for
the use of applicable and compliant
voluntary consensus standards when
possible to facilitate implementation of
the final regulations and avoid
disruption to parties using voluntary
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consensus standards that are found to be
fully compliant with the federal
regulations.
G. What Is Included in ‘‘All Appropriate
Inquiries?’’
Proposed Rule
The proposed regulations for
conducting all appropriate inquiries
outlined the standards and practices for
conducting the activities included in
each of the statutory criterion
established by Congress in the
Brownfields Amendments. These
criteria are set forth in CERCLA section
101(35)(B)(iii) and are:
• The results of an inquiry by an
environmental professional (proposed
§ 312.21).
• Interviews with past and present
owners, operators, and occupants of the
facility for the purpose of gathering
information regarding the potential for
contamination at the facility (proposed
§ 312.23).
• Reviews of historical sources, such
as chain of title documents, aerial
photographs, building department
records, and land use records, to
determine previous uses and
occupancies of the real property since
the property was first developed
(proposed § 312.24).
• Searches for recorded
environmental cleanup liens against the
facility that are filed under Federal,
State, or local law (proposed § 312.25).
• Reviews of Federal, State, and local
government records, waste disposal
records, underground storage tank
records, and hazardous waste handling,
generation, treatment, disposal, and
spill records, concerning contamination
at or near the facility (proposed
§ 312.26).
• Visual inspections of the facility
and of adjoining properties (proposed
§ 312.27).
• Specialized knowledge or
experience on the part of the defendant
(proposed § 312.28).
• The relationship of the purchase
price to the value of the property, if the
property was not contaminated
(proposed § 312.29).
• Commonly known or reasonably
ascertainable information about the
property (proposed § 312.30).
• The degree of obviousness of the
presence or likely presence of
contamination at the property, and the
ability to detect the contamination by
appropriate investigation (proposed
§ 312.31).
Public Comments
We received a few comments
addressing the statutory criteria and the
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inclusion of certain particular criteria
within the scope of the proposed rule.
Some commenters requested that EPA
not include in the final rule the criterion
to consider the relationship of the
purchase price of the property to the fair
market value of the property, if the
property is not contaminated. In
addition, a few commenters stated the
final rule should not include within the
scope of the all appropriate inquiries the
specialized knowledge or experience on
the part of the prospective landowner.
The Agency notes that both criteria
that commenters requested be removed
from the scope of the all appropriate
inquiries regulations are criteria
specifically required by Congress to be
included in the regulations. In addition,
both criteria have been part of the all
appropriate inquiries provisions under
the CERCLA innocent landowner
defense since 1986. The proposed rule
included no changes from the previous
statutory provisions.
Final Rule
The final rule retains provisions
addressing each of the statutory criteria
for the conduct of all appropriate
inquiries included in CERCLA section
101(35)(B)(iii).
H. Who Is Responsible for Conducting
the All Appropriate Inquiries?
The Brownfields Amendments to
CERCLA require persons claiming any
of the landowner liability protections to
conduct all appropriate inquiries into
the past uses and ownership of the
subject property. The criteria included
in the Brownfields Amendments for the
regulatory standards for all appropriate
inquiries require that the inquiries
include an inquiry by an environmental
professional. The statute does not
require that all criteria or inquiries be
conducted by an environmental
professional.
Proposed Rule
The proposed rule required that
many, but not all, of the inquiries
activities be conducted by, or under the
supervision or responsible charge of, an
individual meeting the qualifications of
the proposed definition of an
environmental professional. The
proposed rule also provided that several
of the activities included in the
inquiries could be conducted either by
the prospective landowner or grantee,
and not have to be conducted under the
supervision or responsible charge of the
environmental professional. The
proposed rule required that the results
of all activities conducted by the
prospective landowner or grantee, and
not conducted by or under the
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supervision or responsible charge of the
environmental professional, be provided
to the environmental professional to
ensure that such information could be
fully considered when the
environmental professional develops an
opinion, based on the inquiry activities,
as to whether conditions at the property
are indicative of a release or threatened
release of a hazardous substance (or
other contaminant) on, at, in, or to the
property.
The proposed rule allowed for the
following activities to be the
responsibility of, or conducted by, the
prospective landowner or grantee and
not necessarily be conducted by the
environmental professional, provided
the results of such inquiries or activities
are provided to an environmental
professional overseeing the all
appropriate inquiries:
• Searches for environmental cleanup
liens against the subject property that
are filed or recorded under federal,
tribal, state, or local law, as required by
proposed § 312.25.
• Assessments of any specialized
knowledge or experience on the part of
the landowner, as required by § 312.28.
• An assessment of the relationship of
the purchase price to the fair market
value of the subject property, if the
property was not contaminated, as
required by § 312.29.
• An assessment of commonly known
or reasonably ascertainable information
about the subject property, as required
by § 312.30.
The proposed rule required that all
other required inquiries and activities,
beyond those listed above to be
conducted by, or under the supervision
or responsible charge of, an
environmental professional.
Public Comments
Several commenters asserted that the
mandatory nature of the proposed
provision requiring the prospective
landowner to provide information
regarding the four criteria listed above
to the environmental professional is
problematic. Particularly with regard to
the requirement to provide ‘‘specialized
knowledge or experience of the
defendant,’’ commenters pointed out
difficulties in a prospective landowner
being able to document such knowledge
and experience sufficiently. Also, with
regard to the information related to the
‘‘relationship of the purchase price to
the fair market value of the property, if
the property was not contaminated,’’
many commenters pointed out that
prospective landowners may not want
to divulge information regarding the
price paid for a property. Commenters
pointed out that the requirement to
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consider ‘‘commonly known or
reasonably ascertainable information’’
about a property is implicit to all
aspects of the all appropriate inquiries
requirements. In addition, commenters
stated that CERCLA liability lies solely
with the owners and operators of a
vessel or property. A decision on the
part of a prospective landowner to not
furnish an environmental professional
with certain information related to any
of the statutory criteria can only affect
the property owner’s ability to claim a
liability protection provided under the
statute. In addition, the statute does not
mandate that information deemed to be
the responsibility of the prospective
landowner and not part of the ‘‘inquiry
of the environment professional’’ be
provided to the environmental
professional or even be part of the
inquiry of the environmental
professional. Some of the statutory
criteria are inherently the responsibility
of the prospective landowner.
Final Rule
We agree with the commenters who
asserted that the results and information
related to the criteria identified as being
the responsibility of the prospective
landowner should not, as a matter of
law, have to be provided to the
environmental professional. The statute
does not mandate that a prospective
landowner provide all information to an
environmental professional. Given that
the burden of potential CERCLA
liability ultimately falls upon the
property owner or operator, a
prospective landowner’s decision not to
provide the results of an inquiry or
related information to an environmental
professional he or she hired to
undertake other aspects of the all
appropriate inquiries investigation can
only affect the liability of the property
owner. In addition, we believe that the
environmental professional may be able
to develop an opinion with regard to
conditions indicative of releases or
threatened releases on, at, in, or to a
property based upon the results of the
criteria identified to be part of the
‘‘inquiry of an environmental
professional.’’ Any information not
furnished to the environmental
professional by the prospective
landowner that may affect the
environmental professional’s ability to
render such an opinion may be
identified by the environmental
professional as a ‘‘data gap.’’ The
provisions of the final rule (as did the
proposed rule) then require that the
environmental professional comment on
the significance of the data gap or
missing information on his or her ability
to render such an opinion, in light of all
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other information collected and all other
data sources consulted.
As a result of our consideration of the
issues raised by commenters, today’s
final rule modifies the requirements of
§ 312.22 ‘‘additional inquiries’’ by
stating (in paragraph (a)) that ‘‘persons
* * * may provide the information
associated with such inquiries [i.e., the
information for which the prospective
landowner or brownfields grantee is
responsible] to the environmental
professional * * *.’’ The proposed rule
provided that such information ‘‘must
be provided’’ to the environmental
professional. Although we expect that
most prospective landowners and
grantees will furnish available
information or knowledge about a
property to an environmental
professional he or she hired when such
information could assist the
environmental professional in
ascertaining the environmental
conditions at a property, we affirm that
compliance with the statutory criteria
does not require that such information
be disclosed. Ultimately, CERCLA
liability rests with the owner or operator
of a facility or property owner and it is
the information held by the property
owner or operator that may be reviewed
in a court of law when determining an
owner or operator’s liability status,
regardless of whether all information
was disclosed to an environmental
professional during the conduct of all
appropriate inquiries.
prior to taking title to a property. The
proposed rule provided that prospective
landowners could use information
collected as part of previous inquiries
for the same property, if the inquiries
were completed or updated within one
year prior to the date the property is
acquired. The proposed rule required
that certain information collected as
part of a previous all appropriate
inquiries be updated if it was collected
more than 180 days prior to the date a
person purchased the property. In
addition, in the preamble to the
proposed rule, Agency defined the date
of acquisition of a property as the date
on which the prospective landowner
acquires title to the property.
I. When Must All Appropriate Inquiries
Be Conducted?
CERCLA section 101(40)(B)(i), as
amended, requires bona fide prospective
purchasers to conduct all appropriate
inquiries into ‘‘previous ownerships and
uses of the facility.’’ In the case of
contiguous property owners, CERCLA
section 107(q)(1)(A)(viii) requires that a
person claiming to be a contiguous
property owner conduct all appropriate
inquiries ‘‘at the time at which the
person acquired the property.’’ In the
case of innocent landowners, section
101(35)(B)(i)(I) of CERCLA requires that
the property owner conduct all
appropriate inquiries ‘‘on or before the
date on which the defendant acquired
the facility.’’
Final Rule
The Agency continues to believe that
the event that most closely reflects the
Congressional intent of the date on
which the defendant acquired the
property is the date on which a person
received title to the property. As
explained in the preamble to the
proposed rule, the Agency considered
other dates, such as the date a
prospective landowner signs a purchase
or sale agreement. However, it could be
burdensome to require a prospective
landowner to have completed the all
appropriate inquiries prior to having an
agreement with a seller to complete a
sales transaction. In fact, the time period
between the date on which a sales
agreement is signed and the date on
which the title to the property is
actually transferred to the prospective
landowner may be the most convenient
time for the prospective landowner to
obtain access to the property and
undertake the all appropriate inquiries.
In addition, requiring that all
appropriate inquiries be completed on
some date prior to the date of title
transfer could result in requiring
prospective landowners to undertake all
Proposed Rule
Other than to specify that all
appropriate inquiries must be
conducted on or prior to the date a
person acquires a property, the statute is
silent regarding how close to the actual
date of acquisition the inquiries must be
completed. The proposed rule required
that all appropriate inquiries be
conducted or updated within one year
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Public Comments
Commenters generally agreed with the
proposed provision to define the date of
acquisition of a property as the date on
which a person acquires title to the
property. A few commenters stated that
the requirement for an all appropriate
inquiries investigation to be completed
within a year of the date of acquisition
of the property is too stringent and may
not allow sufficient time for some
property transactions to be completed.
Some commenters also asserted that the
proposed requirement to update certain
aspects of the all appropriate inquiries
investigation, if the investigation was
conducted more than 180 days prior to
the date of the acquisition of the
property was too stringent.
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appropriate inquiries so early in the
property acquisition process as to
require the inquiries to be completed
prior to the prospective landowner
making a final decision on whether to
actually acquire the property.
To increase the potential that the
information collected for the all
appropriate inquiries accurately reflects
the proposed objectives and
performance factors, as well as to
increase the potential that opinions and
judgments regarding the environmental
conditions at a property that are
included in an all appropriate inquiries
report are based on current and relevant
information, the Agency is retaining the
proposed provision that all appropriate
inquiries be conducted within one year
prior to the prospective landowner
acquiring the property. Today’s final
rule includes regulatory language at
§ 312.20(a) clarifying that all
appropriate inquiries must be
conducted within one year prior to the
date on which a person acquires a
property.
All appropriate inquiries may include
information collected for previous
inquiries that were conducted or
updated within one year prior to the
acquisition date of the property. In
addition, as explained in more detail
below, the final rule retains the
requirement that several of the
components of the inquiries be updated
within 180 days prior to the date the
property is purchased. Today’s final
rule includes a definition of the ‘‘date of
acquisition,’’ or purchase date, of a
property (i.e., the date the landowner
obtains title to the property).
Although commenters may be correct
in their assertions that some property
transactions may take more than a year
to close, we continue to believe that it
is important for the all appropriate
inquiries investigation to be completed
within one year prior to the date the
property is acquired. We point out that
the final regulation, as did the proposed
regulation, allows for information from
an older investigation to be used in a
current investigation. However, if the
prior all appropriate inquiries
investigation was completed more than
a year prior to the property acquisition
date, all parts of the investigation must
be reviewed and updated for the all
appropriate inquiries to be complete.
We believe that a year is sufficient time
for conditions at a property to change.
In particular, in cases where there is a
release or threatened release at a
property, significant changes to the
environmental conditions of a property
could occur during the course of a year.
In addition, depending upon the uses
and ownership of a property during the
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course of a one-year time period, overall
conditions at a property could change
and new evidence of a release or
threatened release could appear.
Therefore, today’s final rule requires
that all appropriate inquiries completed
for a particular property more than one
year prior to the date of acquisition of
that property, be updated in their
entirety. As summarized below, the
final rule does allow for the use of
information contained in previous
inquiries, even when the inquiries were
completed more than a year prior to the
property acquisition date, as long as all
information was updated within a year
and includes any changes that may have
occurred during the interim.
J. Can a Prospective Landowner Use
Information Collected for Previous
Inquiries Completed for the Same
Property?
Proposed Rule
The proposed rule allowed parties
conducting all appropriate inquiries to
use the results of and information from
previous inquiries completed for the
same property, under certain
conditions. First, the previous inquiries
must have been conducted in
compliance with the proposed rule and
with CERCLA sections 101(35)(B),
101(40)(B) and 107(q)(A)(viii). In
addition, the information in the
previous inquiries must have been
collected or updated within one year
prior to the date of acquisition of the
property. Certain types of information
collected more than 180 days prior to
the current date of acquisition must be
updated for the current all appropriate
inquiries. Also, the information required
under some specific criterion (e.g.,
relationship of purchase price to
property value, specialized knowledge
on part of defendant) must be collected
specifically for the current transaction.
Public Comments
A significant number of commenters
pointed out that the regulatory language
in proposed § 312.20(b)(1) of the
proposed rule precludes the use of
information contained in assessments or
the results of all appropriate inquiries
conducted more than a year prior to the
date of acquisition of a property.
Commenters pointed out that since the
language in the proposed rule stated
that previously collected information
had to have been collected ‘‘in
compliance with the requirements of
* * * 40 CFR Part 312,’’ any
information included in all appropriate
inquiries reports completed prior to the
promulgation of the final rule could not
be used, since compliance with the
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regulation could not be achieved prior
to its publication.
Final Rule
It is not the Agency’s intent to
disallow the use of information
contained in previous inquiries, if the
environmental professional and the
prospective landowner find the
previously collected information to be
accurate and valid. However, EPA
continues to believe that information
collected as part of a prior all
appropriate inquiries investigation for
the same property should be updated to
reflect current environmental conditions
at the property and to include any
specific information or specialized
knowledge held by the prospective
landowner. The regulatory language in
today’s final rule (at § 312.20(c)(1))
allows for the use of information
collected as part of prior all appropriate
inquiries investigation for the same
property provided that the prior
information was collected ‘‘during the
conduct of all appropriate inquiries in
compliance with CERCLA sections
101(35)(B), 101(40)(B) and
107(q)(A)(viii).’’ We have deleted the
proposed language that would have
required the previously conducted
investigation to have been done in
compliance with the final regulation.
This allows for the use of information
collected as part of previous all
appropriate inquiries, as long as the
information was collected in
compliance with the statutory
provisions for all appropriate inquiries.
For property purchased on or after May
31, 1997, therefore, any information
collected as part of an assessment in
compliance with the ASTM E1527–97
standard or the ASTM E1527–2000
standard may be used as part of a
current all appropriate inquiries
investigation. For property purchased
before May 31, 1997, information from
assessments completed and in
compliance with the statutory
provisions at CERCLA section
101(35)(B)(iv)(I) may be used as part of
a current all appropriate inquiries
investigation. However, this prior
information may only be used if
updated in accordance with §§ 312.20(b)
and (c) of today’s rule.
The final rule continues to recognize
that there is value in using previously
collected information when such
information was collected in accordance
with the statutory provisions and good
customary business practices,
particularly when the use of such
previously-collected information will
reduce the need to undertake
duplicative efforts.
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The final rule also retains the
requirement that certain aspects of the
all appropriate inquiries investigation
be updated if the investigation was
completed more than 180 days prior to
the date of acquisition of the property
(or the date on which the prospective
landowner takes title to the property) to
ensure that an all appropriate inquiries
investigation accurately reflects the
current environmental conditions at a
property. To increase the potential that
information collected about the
conditions of a property is accurate, as
well as increase the potential that
opinions and judgments regarding the
environmental conditions at a property
that are included in an all appropriate
inquiries report are based on current
and relevant information, the final rule
requires that many of the components of
the previous inquiries be updated
within 180 days prior to the date of
acquisition of the property. The
components of the all appropriate
inquiries that must be updated within
180 days prior to the date on which the
property is acquired are:
• Interviews with past and present
owners, operators, and occupants
(§ 312.23);
• Searches for recorded
environmental cleanup liens (§ 312.25);
• Reviews of federal, tribal, state, and
local government records (§ 312.26);
• Visual inspections of the facility
and of adjoining properties (§ 312.27);
and
• The declaration by the
environmental professional
(§ 312.21(d)).
Also, the final rule retains the
proposed requirement that in all cases
where a prospective landowner is using
previously collected information, the all
appropriate inquiries for the current
purchase must be updated to include a
summary of any relevant changes to the
conditions of the property and any
specialized knowledge of the
prospective landowner.
In today’s final rule, we continue to
recognize that it is not sufficient to
wholly adopt previously conducted all
appropriate inquiries for the same
property without any review. Certain
aspects of the all appropriate inquiries
investigation are specific to the current
prospective landowner and the current
purchase transaction. Therefore, the
final rule requires that each all
appropriate inquiries investigation
include current information related to:
• Any relevant specialized knowledge
held by the current prospective
landowner and the environmental
professional responsible for overseeing
and signing the all appropriate inquiries
report (i.e., requirements of § 312.28);
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• The relationship of the current
purchase price to the value of the
property, if the property were not
contaminated (i.e., requirements of
§ 312.29); and
• Commonly known or reasonably
ascertainable information about the
property.
prospective landowner and the
environmental professional, and the
relationship of the purchase price to the
value of the property, if it were not
contaminated.
Public Comments
Commenters generally supported the
proposed provision allowing for all
appropriate inquiries investigations
conducted by or for one party to be used
by another party.
K. Can All Appropriate Inquiries Be
Conducted by One Party and
Transferred to Another Party?
Proposed Rule
The proposed rule allowed for all
appropriate inquiries to be conducted
by one party and transferred to another
party, provided that certain conditions
are met. Under certain circumstances,
the prospective landowner, or a grantee,
may use a report of all appropriate
inquiries conducted for the property by
or for another party, including the seller
of the property or another party. For
example, there are situations where the
federal government or a state
government agency may conduct the all
appropriate inquiries on behalf of the
local government for a property being
purchased by a local government, such
as the ‘‘targeted brownfields
assessments’’ conducted on behalf of
local governments by EPA. This
situation also may occur when a state
government covers the cost of the all
appropriate inquiries for a property
owned by a local government or actually
conducts the all appropriate inquiries
itself when the local government does
not have access to appropriate staff or
capital resources. A local government
may conduct all appropriate inquiries
for a third party in its community, such
as a private prospective landowner. In
addition, local redevelopment agencies
may locate a contaminated property,
conduct all appropriate inquiries,
acquire the property, and then sell the
property to a private developer.
The proposed rule allowed for a
person acquiring a property, or a
grantee, to use the results of an all
appropriate inquiries report conducted
by or for another party, if the report
meets the proposed rule’s objectives and
performance factors and the person who
is seeking to use the previouslycollected information or report reviews
all information collected and updates
the contents of the report as required by
§ 312.20(c) and necessary to accurately
reflect current conditions at the
property. In addition, the proposed rule
required that the prospective
landowner, or grantee, update the
inquiries and the report to include any
commonly known and reasonably
ascertainable information, relevant
specialized knowledge held by the
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Final Rule
For the reasons discussed in the
preamble to the proposed rule and
summarized above, the final rule retains
the provision allowing that all
appropriate inquiries investigations may
be conducted by or for one party and
used by another party. In all cases, the
all appropriate inquiries investigation
must be updated to include commonly
known and reasonably ascertainable
information and any relevant
specialized knowledge held by the
prospective landowner and
environmental professional. In addition,
the evaluation of the relationship
between the purchase price and the fair
market value of the property must
reflect the current sale of the property.
In all other aspects of the investigation,
the all appropriate inquiries must be in
compliance with the provisions of the
final regulation.
L. What Are the Objectives and
Performance Factors for the All
Appropriate Inquiries Requirements?
Proposed Rule
As explained in the preamble to the
proposed rule, when developing the
proposed standards, EPA and the
Negotiated Rulemaking Committee
structured the proposal around the
statutory criteria established by
Congress in section 101(35)(B)(iii) of
CERCLA. As development of the
proposed rule progressed, it became
apparent that the purposes and
objectives for the individual criterion
and the types of information that must
be collected to meet the objectives of
each criterion often overlapped. For
example, in developing standards
addressing the criterion requiring a
review of historical information, a
search for recorded environmental
cleanup liens, and a review of
government records, the Committee
concluded that the objectives of each
criterion or activity were similar, which
could lead to the collection of the same
information to fulfill each of the
criterion’s objectives. For example, a
chain of title document is historic
information that may include
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information on environmental cleanup
liens, as well as information on past
owners of the property indicating that
previous owners managed hazardous
substances on the property.
To avoid requiring duplicative efforts,
but to ensure that the proposed
regulations included standards and
practices that result in a comprehensive
assessment of the environmental
conditions at a property, the proposed
all appropriate inquiries standards were
structured around a concise set of
objectives and performance factors. The
proposed objectives and performance
factors applied to the standards
comprehensively. In conducting the
inquiries collectively, the landowner
and the environmental professional
must seek to achieve the objectives and
performance factors and use the
objectives and standards as guidelines
in implementing, in total, all of the
other proposed regulatory standards and
practices.
Public Comments
Commenters overwhelmingly
supported the proposed approach of
structuring the all appropriate inquiries
standards around a definitive set of
performance factors and objectives.
Commenters stated that the
establishment of performance factors
will improve the quality of
environmental site assessments because
the performance factors allow for the
application of professional judgement
and provide flexibility.
A few commenters did not support
the proposed approach of structuring
the regulations around a set of
performance factors and objectives.
These commenters asserted that the
objectives and performance factors
made the regulation too vague and
open-ended. In addition, the
commenters stated that they want the
regulation to be centered around a
‘‘checklist’’ of activities, each of which
should be required to be completed
independently and without
consideration of a comprehensive
performance approach. Commenters
who argued for a checklist approach
said that such an approach would
ensure that the environmental
professional only would have to
undertake a finite list of activities and
it would be easier (in the commenter’s
opinion) for property owners to obtain
liability protection if the list of activities
could be completed without regard to
performance goals or an overall
objective. These commenters also
expressed concern that, if the
regulations are based on performance
factors that the all appropriate inquiries
investigation would not have an
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endpoint at which prospective
landowners could stop looking for
evidence of releases or threatened
releases. The commenters believed that
under a checklist approach liability
protection would be awarded upon
completion of all activities on the
checklist.
Final Rule
We are retaining the proposed
performance factors and objectives in
the final rule. We continue to believe, as
did many commenters, that basing the
regulations on a set of overall
performance factors and specific
objectives lends clarity and flexibility to
the standards. Such an approach also
allows for the application of
professional judgment and expertise to
account for site-specific circumstances.
The primary objective of an all
appropriate inquiries investigation is to
identify conditions indicative of
releases and threatened releases of
hazardous substances on, at, in, or to the
subject property. In the case of
recipients of brownfields grants, the
objective may be expanded to include
petroleum and petroleum products,
pollutants, contaminants, and
controlled substances, depending upon
the scope of the grantee’s cooperative
agreement.
The performance factors are meant to
guide the individual aspects of the
investigation toward meeting both the
statutory criteria for all appropriate
inquiries and the regulatory objectives
of (1) collecting necessary information
about the uses and ownerships of a
property and (2) identifying, through the
collection of this information,
conditions indicative of releases and
threatened releases on, at, in, or to the
subject property. By establishing a
concise set of objectives and setting
some boundaries on the information
collection activities through the
establishment of performance factors,
we believe that the final rule fulfills the
statutory objectives, provides for a
comprehensive assessment of the
environmental conditions at the
property, and avoids the conduct of
duplicative investigations and data
collection efforts.
EPA disagrees with the commenters
who argued that the proposed approach
of establishing overall objectives and
performance factors for the all
appropriate inquiries standards would
result in an approach that is too vague
and open-ended. In fact, by establishing
clear objectives and setting parameters
to the investigation through a set of
performance factors that include
gathering information that is publicly
available, obtainable from its source
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within reasonable time and cost
constraints, and which can practicably
be reviewed, the approach taken in the
final rule provides reasonable goals and
endpoints to the information collection
requirements. The proposed objectives
provide a discrete list of the types of
information that must be collected as
part of the all appropriate inquiries
investigation. In addition, the
performance factors set boundaries
around the efforts that must be taken
and the cost burdens that must be
incurred to obtain the required
information. The fact that the rule is
framed within a primary objective, to
‘‘identify conditions indicative of
releases and threatened releases of
hazardous substances,’’ actually reduces
the open-ended nature of the
investigation and establishes an overall
goal for the inquiries.
Commenters who advocated that a
checklist approach (or an approach not
based upon overall objectives and
performance factors) is superior because
they believe that it would better provide
for a stopping point in the investigation
may have misunderstood the statutory
requirements that must be met to obtain
a defense to CERCLA liability. These
commenters may have incorrectly
assumed that the completion of the all
appropriate inquiries investigation is all
that is required to obtain liability
protection. The conduct of all
appropriate inquiries is only one
requirement for obtaining relief from
CERCLA liability. Prospective
landowners must conduct all
appropriate inquiries prior to acquiring
a property to qualify for a defense to
CERCLA liability as an innocent
landowner, bona fide prospective
purchaser or contiguous landowner.
However, once a property is acquired,
the property owner must comply with
all of the other statutory criteria
necessary to qualify for the liability
protections. In particular, landowners
must undertake ‘‘reasonable steps’’ to
‘‘stop any continuing releases.’’
Therefore, the final rule’s objective of
identifying conditions indicative of
releases and threatened releases of
hazardous substances on, at, in, or to a
property links appropriately with the
statutory criteria requiring the
landowner to address such releases to
qualify for the liability protections.
Conducting the inquiries merely in
compliance with a checklist and
without the purpose of meeting an
overall objective could result in an
inability to recognize the value of
certain types of information or in
chasing down multiple sources of
information that may not have added
value for meeting the overall objective
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of the investigation. A lack of
information or an inability to obtain
information that may affect the ability of
an environmental professional to
determine whether or not there are
conditions indicative of a release or
threatened release of a hazardous
substance (or other contaminant) on, at,
in or to a property can have significant
consequences regarding a prospective
landowner’s ultimate ability to claim
protection from CERCLA liability.
Failure to identify a release during the
conduct of all appropriate inquiries
does not relieve the property owner
from the responsibility to take
reasonable steps and address the
release. Even if the Agency agreed with
the commenters and adopted a
‘‘checklist’’ approach for the regulation,
simply conducting the checklist of
activities and ending the investigation
after each activity is conducted would
not result in protection from CERCLA
liability (as commenters claimed).
The final rule also establishes that in
those cases where certain information
included in the list of regulatory
objectives (§ 312.20(e)) cannot be found
or obtained within the parameters of the
performance factors, such data gaps
must be identified and the significance
of the missing information with regard
to the environmental professional’s
ability to render an opinion on the
presence of conditions indicative of
releases and threatened releases be
documented. Exhaustive and costly
efforts do not have to be made to access
all available sources of data and find
every piece of data and information
about a property. Nor does the rule
require that duplicative information be
sought from multiple sources. The
inquiries and the overall investigation
must be undertaken to meet the data
collection objectives and primarily
determine the environmental conditions
of the property. Structuring the
standards around such objectives will
render the results of the investigation
more valuable to a landowner in his or
her efforts to comply with the post
acquisition continuing obligations for
obtaining the CERCLA liability
protections than an approach framed
around a mere checklist of activities.
In retaining the proposed objectives
and performance factors, the final rule
allows that an all appropriate inquiries
investigation need not address each of
the regulatory criterion in any particular
sequence. In addition, information
relevant to more than one criterion need
not be collected twice, and a single
source of information may satisfy the
requirements of more than one criterion
and more than one objective. However,
the information required to achieve each
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of the objectives and performance
factors must be obtained for the all
appropriate inquiries investigation to be
complete. Although compliance with
the all appropriate inquiries
requirements ultimately will be
determined in court, the final rule
allows the prospective landowner or
grantee and environmental professional
to determine the best process and
sequence for collecting and analyzing
all required information. The sequence
of activities and the sources of
information used to collect any required
information is left to the judgment and
expertise of the environmental
professional, provided that the overall
objectives and the performance factors
established for the final rule are met.
In performing the inquiries, including
but not limited to conducting
interviews, collecting historical data
and government records, and inspecting
the subject property and adjoining
properties, all parties undertaking all
appropriate inquiries must be attentive
to the fact that the primary objectives of
the regulation are to identify the
following types of information about the
subject property:
• Current and past property uses and
occupancies;
• Current and past uses of hazardous
substances;
• Waste management and disposal
activities that could have caused
releases or threatened releases of
hazardous substances;
• Current and past corrective actions
and response activities undertaken to
address past and on-going releases of
hazardous substances;
• Engineering controls;
• Institutional controls; and
• Properties adjoining or located
nearby the subject property that have
environmental conditions that could
have resulted in conditions indicative of
releases or threatened releases of
hazardous substances on, at, in, or to the
subject property.
EPA notes that in the case of
brownfields grantees, the scope of each
of the activities listed above may be
broader if the grant or cooperative
agreement includes within its scope the
assessment of a property for conditions
indicative of releases or threatened
releases of petroleum and petroleum
products, controlled substances, or
other contaminants.
The final performance factors for
achieving the objectives set forth above
are set forth in § 312.20(e) and require
the persons conducting the inquiries to:
(1) Gather the information that is
required for each standard and practice
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that is publicly available, obtainable
from its source within reasonable time
and cost constraints, and which can
practicably be reviewed, and (2) review
and evaluate the thoroughness and
reliability of the information gathered in
complying with each standard and
practice, taking into account
information gathered in the course of
complying with the other standards and
practices of this subpart. In complying
with § 312.20(f)(2), if the environmental
professional or person conducting the
inquiries determines through such
review and evaluation that the
information is either not thorough or not
reliable, then further inquiries should be
made to ensure that the information
gathered is both thorough and reliable.
The performance factors are provided as
guidelines to be followed in conjunction
with the final objectives for the all
appropriate inquiries.
M. What Are Institutional Controls?
The final rule requires the
identification of institutional controls
placed on the subject property. As
defined in § 312.10, institutional
controls are non-engineered
instruments, such as administrative and
legal controls, that among other things,
can help to minimize the potential for
human exposure to contamination, and
protect the integrity of a remedy by
limiting land or resource use. For
example, an institutional control might
prohibit the drilling of a drinking water
well in a contaminated aquifer or
disturbing contaminated soils.
Institutional controls also may be
referred to as land use controls, activity
and use limitations, etc., depending on
the program under which a response
action is conducted or a release is
addressed.
Institutional controls are typically
used whenever contamination precludes
unlimited use and unrestricted exposure
at the property. Thus, institutional
controls may be needed both before and
after completion of the remedial action
or may be employed in place of a
remedial action. Institutional controls
often must remain in place for an
indefinite duration and, therefore,
generally need to survive changes in
property ownership (i.e., run with the
land) to be legally and practically
effective. Some common examples of
institutional controls include zoning
restrictions, building or excavation
permits, well drilling prohibitions,
easements and covenants.
The importance of identifying
institutional controls during all
appropriate inquiries is twofold. First,
institutional controls are usually
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necessary and important components of
a remedy. Failure to abide by an
institutional control may put people at
risk of harmful exposure to hazardous
substances. Second, an owner wishing
to maintain protections from CERCLA
liability as an innocent landowner,
contiguous property owner, or bona fide
prospective purchaser must fulfill
ongoing obligations to: (1) Comply with
any land use restrictions established or
relied on in connection with a response
action and (2) not impede the
effectiveness or integrity of any
institutional control employed in
connection with a response action. For
a more detailed discussion of these
requirements please see EPA, Interim
Guidance Regarding Criteria
Landowners Must Meet in Order to
Qualify for Bona Fide Prospective
Purchaser, Contiguous Property Owner,
or Innocent Landowner Limitations on
CERCLA Liability (Common Elements,
2003).
Those persons conducting all
appropriate inquiries may identify
institutional controls through several of
the standards and practices set forth in
this rule. As noted, implementation of
institutional controls may be
accomplished through the use of several
administrative and legal mechanisms,
such as zoning restrictions, building
permit requirements, easements,
covenants, etc. For example, an
easement implementing an institutional
control might be identified through the
review of chain of title documents
under § 312.24(a). Furthermore,
interviews with past and present
owners, operators, or occupants
pursuant to § 312.23; and reviews of
federal, tribal, state, and local
government records under § 312.26, may
identify an institutional control or refer
a person to the appropriate source to
find an institutional control. For
example, a review of federal Superfund
records, including Records of Decision
and Action Memoranda, as well as other
information contained in the CERCLIS
database, may indicate that zoning was
selected as an institutional control or an
interview with a current operator may
reveal an institutional control as part of
an operating permit.
The final rule requires that all
appropriate inquiries include a search
for institutional controls placed upon
the subject property as part of the
requirements for reviewing federal,
state, tribal, and local government
records. A discussion of these
requirements is provided in section IV.S
below.
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N. How Must Data Gaps Be Addressed
in the Conduct of All Appropriate
Inquiries?
Proposed Rule
The proposed rule required
environmental professionals,
prospective landowners, and
brownfields grant recipients to identify
data gaps that affect their ability to
identify conditions indicative of
releases or threatened releases of
hazardous substances (and, in the case
of grant recipients, pollutants,
contaminants, petroleum and petroleum
products, and controlled substances).
The proposed rule also required these
persons to identify the sources of
information consulted to address, or fill,
the data gaps and then comment upon
the significance of the data gaps with
regard to the ability to identify
conditions indicative of releases or
threatened releases of hazardous
substances on, at, in or to the subject
property. The proposed rule defined a
data gap as a lack of or an inability to
obtain information required by the
standards and practices listed in the
proposed regulation, despite good faith
efforts by the environmental
professional or the prospective
landowner or grant recipient to gather
such information.
Public Comments
Some commenters raised concerns
that the proposed definition of a data
gap may result in difficulties in
determining when an all appropriate
inquiries investigation is complete.
These commenters stated that the need
to identify and comment on the
significance of data gaps may render it
difficult to complete an investigation,
that could potentially affect a property
owner’s ability to claim protection from
CERCLA liability. Other commenters
asserted that because an investigation
could be considered complete despite
the existence of a data gap, a regulatory
loophole exists (in the opinion of the
commenters) that will result in the
property owner’s being able to claim
protection from CERCLA liability even
when the all appropriate inquiries
investigation results in a failure to
identify a release or threatened release
at a property.
Some commenters stated that the
proposed requirement to identify data
gaps, or missing information, that may
affect the environmental professional’s
ability to render an opinion regarding
the environmental conditions at a
property and comment on their
significance in this regard will lend
credibility to the inquiry’s final report.
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Final Rule
We are retaining the proposed
definition of data gap and the proposed
requirements for identifying and
commenting on the significance of data
gaps. For the purposes of today’s final
rule, a ‘‘data gap’’ is a lack of or inability
to obtain information required by the
standards and practices listed in the
regulation, despite good faith efforts by
the environmental professional or the
prospective landowner (or grant
recipient) to gather such information
pursuant to the objectives for all
appropriate inquiries. In today’s final
rule, § 312.20(g) requires environmental
professionals, prospective landowners,
and grant recipients to identify data
gaps that affect their ability to identify
conditions indicative of releases or
threatened releases of hazardous
substances (and in the case of grant
recipients pollutants, contaminants,
petroleum and petroleum products, and
controlled substances). The final rule
requires such persons to identify the
sources of information consulted to
address the data gaps and comment
upon the significance of the data gaps
with regard to the ability to identify
conditions indicative of releases or
threatened releases. Section 312.21(c)(2)
also requires that the inquiries report
include comments regarding the
significance of any data gaps on the
environmental professional’s ability to
provide an opinion as to whether the
inquiries have identified conditions
indicative of releases or threatened
releases.
In response to issues raised by
commenters, we point out that the final
regulation, as did the proposal, requires
that environmental professionals
document and comment on the
significance of only those data gaps that
‘‘affect the ability of the environmental
professional to identify conditions
indicative of releases or threatened
releases of hazardous substances * * *
on, at, in, or to the subject property.’’ If
certain information included within the
objectives and performance factors for
the final rule cannot be found and the
lack of certain information, in light of
all other information that was collected
about the property, has no bearing on
the environmental professional’s ability
to render an opinion regarding the
environmental conditions at the
property, the final rule does not require
the lack of such information to be
documented in the final report. Given
the restriction on the type of data gaps
that must be documented, and given
that the documentation is restricted to
instances where the lack of information
hinders the ability of the environmental
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professional to render an opinion
regarding the environmental conditions
at the property, we disagree with the
commenters who assert that the
requirement is overly burdensome or
will result in the inability to complete
the required investigations.
Commenters who asserted that the
requirement to document data gaps
would result in a ‘‘loophole’’ that would
allow property owners to claim
protection from CERCLA liability after
conducting an incomplete all
appropriate inquiries investigation may
have misunderstood the scope of the
rule and the statutory requirements for
obtaining the liability protections. As
explained in detail in Section II of this
preamble, the conduct of all appropriate
inquiries is only one requirement
necessary for obtaining protection from
CERCLA liability. The mere fact that a
prospective landowner conducted all
appropriate inquiries does not provide
an individual with protection from
CERCLA liability. To qualify as a bona
fide prospective purchaser, innocent
landowner or a contiguous property
owner, a person must, in addition to
conducting all appropriate inquiries
prior to acquiring a property, comply
with all of the other statutory
requirements. These criteria are
summarized in section II.D. of this
preamble. The all appropriate inquiries
investigation may provide a prospective
landowner with necessary information
to comply with the other postacquisition statutory requirements for
obtaining liability protections. The
conduct of an incomplete all
appropriate inquiries investigation, or
the failure to detect a release during the
conduct of all appropriate inquiries,
does not exempt a landowner from his
or her post-acquisition continuing
obligations under other provisions of
the statute. Failure to comply with any
of the statutory requirements may be
problematic in a claim for protection
from liability.
The final rule retains the requirement
to identify data gaps, address them
when possible, and document their
significance. Prospective landowners
may wish to consider the potential
significance of any data gaps, that may
exist after conducting the preacquisition all appropriate inquiries in
assessing their obligations to fulfill the
additional statutory requirements after
purchasing a property.
If a person properly conducts all
appropriate inquiries pursuant to this
rule, including the requirements
concerning data gaps at §§ 312.10,
312.20(g) and 312.21(c)(2), the person
may fulfill the all appropriate inquiries
requirements of CERCLA sections
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107(q), 107(r), and 101(35), even when
there are data gaps in the inquiries.
However, as explained further in this
preamble, fulfilling the all appropriate
inquiries requirements does not, by
itself, provide a person with a
protection from or defense to CERCLA
liability. Failure to identify a release or
threatened release during the conduct of
all appropriate inquiries does not negate
the landowner’s continuing
responsibilities under the statute,
including the requirements to take
reasonable steps to stop the release,
prevent a threatened release, and
prevent exposure to the release or
threatened release once the landowner
has acquired a property. Also, if an
existing institutional control or land use
restriction is not identified during the
conduct of all appropriate inquiries
prior to the acquisition of a property, a
landowner is not exempt from
complying with the institutional control
or land use restriction after acquiring
the property. None of the other statutory
requirements for the liability protections
is satisfied by the results of the all
appropriate inquiries.
We emphasize that the mere fact that
a prospective landowner conducted all
appropriate inquiries does not provide
an individual with a defense to or
limitation from CERCLA liability. To
qualify as a bona fide prospective
purchaser, innocent landowner or a
contiguous property owner, a person
must, in addition to conducting all
appropriate inquiries prior to acquiring
a property, comply with all of the other
statutory requirements. These criteria
are summarized in section II.D. of this
preamble. The all appropriate inquiries
investigation may provide a prospective
landowner with necessary information
to comply with the other postacquisition statutory requirements for
obtaining liability protections. The
failure to detect a release during the
conduct of all appropriate inquiries
does not exempt a landowner from his
or her post-acquisition continuing
obligations under other provisions of
the statute.
Section 312.20(g) of the final rule
points out that one way to address data
gaps may be to conduct sampling and
analysis. The final regulation does not
require that sampling and analysis be
conducted to comply with the all
appropriate inquiries requirements. The
regulation only notes that sampling and
analysis may be conducted, where
appropriate, to obtain information to
address data gaps. The Agency notes
that sampling and analysis may be
valuable in determining the possible
presence and extent of potential
contamination at a property. Such
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information may be valuable for
determining how a landowner may best
fulfill his or her post-acquisition
continuing obligations required under
the statute for obtaining protection from
CERCLA liability.
O. Do Small Quantities of Hazardous
Substances That Do Not Pose Threats to
Human Health and the Environment
Have To Be Identified in the Inquiries?
Proposed Rule
The environmental professional
should identify and evaluate all
evidence of releases or threatened
releases on, at, in or to the subject
property, in accordance with generally
accepted good commercial and
customary standards and practices.
However, the proposed rule provided
that the environmental professional
need not specifically identify, in the
written report prepared pursuant to
§ 312.21(c), extremely small quantities
or amounts of contaminants, so long as
the contaminants generally would not
pose a threat to human health or the
environment.
Public Comments
EPA received no significant comment
on the proposed provision on the
identification of extremely small
quantities of contamination.
Final Rule
The final retains the provision that
the environmental professional need not
specifically identify, in the written
report prepared pursuant to § 312.21(c),
extremely small quantities or amounts
of contaminants, so long as the
contaminants generally would not pose
a threat to human health or the
environment.
P. What Are the Requirements for
Interviewing Past and Present Owners,
Operators, and Occupants?
Proposed Rule
CERCLA section 101(35)(B)(iii)(II)
requires EPA to include in the standards
and practices for all appropriate
inquiries ‘‘interviews with past and
present owners, operators, and
occupants of the facility for the purpose
of gathering information regarding the
potential for contamination at the
facility.’’ The Agency proposed that the
inquiry of the environmental
professional include interviews with the
current owner(s) and occupant(s) of the
subject property. In addition, the
proposed rule required that interviews
be conducted with current and past
facility managers with relevant
knowledge of the property, as well as
past owners, occupants, or operators,
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and employees of current and past
occupants of the property, as necessary,
to meet the proposed objectives and
performance factors. In the case of
abandoned properties, the Agency
proposed that the inquiry of the
environmental professional include
interviewing one or more owners or
occupants of neighboring or nearby
properties to obtain information on
current and past uses of the property
and other information necessary to meet
the objectives and performance factors.
Public Comments
Several commenters asserted that the
requirement to interview current and
past owners and occupants of a property
may be burdensome. Commenters gave
several reasons for asserting that
interviews may be burdensome. Some
commenters said it is difficult to locate
current and past owners and occupants.
Other commenters questioned the
accuracy of any information that would
be provided by a current or past owner
or occupant. One commenter expressed
concern that the requirement to conduct
interviews of current and past owners
and occupants of a property could result
in the environmental professional
divulging information regarding the sale
of the property against the prospective
landowner’s wishes.
In the case of the proposed interview
requirements for abandoned properties,
some commenters opposed the
requirement to interview at least one
owner or occupant of a neighboring
property. Commenters stated that the
proposed requirement was unreasonable
and that it is impractical to attempt to
find and contact neighboring property
owners and occupants. Some
commenters said that neighboring
property owners and occupants can not
be relied upon to provide accurate
information about a property.
Final Rule
The requirements for conducting
interviews of past and present owners,
operators, and occupants of the subject
property are included in § 312.23. The
final rule identifies these interviews as
being within the scope of the inquiry of
the environmental professional.
Therefore, all interviews must be
conducted by the environmental
professional or by someone under the
supervision or responsible charge of the
environmental professional. The intent
is that an individual meeting the
definition of an environmental
professional (§ 312.10) must oversee the
conduct of, or review and approve the
results of, the interviews to ensure the
interviews are conducted in compliance
with the objectives and performance
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factors (§ 312.20). This is to ensure that
the information obtained from the
interviews provides sufficient
information, in conjunction with the
results of all other inquiries, to allow
the environmental professional to
render an opinion with regard to
conditions at the property that may be
indicative of releases or threatened
releases of hazardous substances (and
pollutants, contaminants, petroleum
and petroleum products, and controlled
substances, if applicable).
The final rule requires the
environmental professional’s inquiry to
include interviewing the current owner
and occupant of the subject property. In
addition, the rule provides that the
inquiry of the environmental
professional include interviews of
additional individuals, including
current and past facility managers with
relevant knowledge of the property, past
owners, occupants, or operators of the
subject property, or employees of
current and past occupants of the
subject property, as necessary to meet
the rule’s objectives and in accordance
with the performance factors. A primary
purpose of the interviews portion of the
all appropriate inquiries is to obtain
information regarding the current and
past ownership and uses of the
property, and obtain information
regarding the potential environmental
conditions of the property. The final
rule does not prescribe particular
questions that must be asked during the
interview. The type and content of any
questions asked during interviews will
depend upon the site-specific
conditions and circumstances and the
extent of the environmental
professional’s (or other individual’s
under the supervision or responsible
charge of the environmental
professional) knowledge of the property
prior to conducting the interviews.
Therefore, the final rule does not
include specific questions for the
interviews, but requires that the
interviews be conducted in a manner
that achieves the objectives and
performance factors. Interviews with
current and past owners and occupants
may provide opportunities to collect
information about a property that was
not previously recorded nor well
documented and may provide valuable
perspectives on how to find or interpret
information required to complete other
aspects of the all appropriate inquiries.
Information gathered during the
interview portion of the all appropriate
inquiries may in turn provide valuable
information for the on-site visual
inspection. Persons conducting the
interviews of current and past owners
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and occupants may want to spend some
time during the interviews requesting
information on the locations of
operations or units used to store or
manage hazardous substances on the
property.
In the case of properties where there
may be more than one owner or
occupant, or many owners or occupants,
the final rule requires the inquiry to
include interviews of major occupants
and those occupants that are using,
storing, treating, handling or disposing
(or are likely to have used, stored,
treated, handled or disposed) of
hazardous substances (or pollutants,
contaminants, petroleum and petroleum
products, and controlled substances, as
applicable) on the property. The rule
does not specify the number of owners
and occupants to be interviewed. The
environmental professional must
perform this function in the manner that
best fulfills the objectives and
performance factors for the inquiries in
§ 312.20(e) and (f). Environmental
professionals may use their professional
judgment to determine the specific
occupants to be interviewed and the
total number of occupants to be
interviewed in seeking to comply with
the objectives and performance factors
for the inquiries. Interviews must be
conducted with individuals most likely
to be knowledgeable about the current
and past uses of the property,
particularly with regard to current and
past uses of hazardous substances on
the property.
In response to commenters who
asserted that the proposed interview
requirements are burdensome, we point
out that the statutory criteria in CERCLA
section 101(35)(B)(iii) include
‘‘interviews with past and present
owners, operators, and occupants of the
facility for the purpose of gathering
information regarding the potential for
contamination at the facility.’’ EPA
asserts that it was clearly congressional
intent that the all appropriate inquiries
investigation include the conduct of
interviews with current and past owners
and occupants. We also assert that
current and past owners and occupants
of a property may be excellent sources
of information regarding past and ongoing uses of the property as well as the
types of waste management activities
that were undertaken at the property.
Given that the ASTM E1527 Phase 1
Environmental Site Assessment Process,
the interim standard for the conduct of
all appropriate inquiries, includes
requirements for conducting interviews
with the current owners and occupants
of a property and provides that other
owners and occupants are good
additional sources of information about
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property uses and potential
contamination at a property, we
disagree with commenters who asserted
that the proposed and final
requirements for conducting interviews
will be overly burdensome.
In the case of abandoned properties,
the final rule requires the inquiry of the
environmental professional to include
interviews with one or more owners or
occupants of neighboring or nearby
properties. In the case of abandoned
properties, it most likely will be
difficult to identify or interview current
or past owners and occupants of the
property. Therefore, the final rule
requires that at least one owner or
occupant of a neighboring property be
interviewed to obtain information
regarding past owners or uses of the
property in cases where the subject
property is abandoned and no current
owner is available to be interviewed.
The final rule defines an abandoned
property as a ‘‘property that can be
presumed to be deserted, or an intent to
relinquish possession or control can be
inferred from the general disrepair or
lack of activity thereon such that a
reasonable person could believe that
there was an intent on the part of the
current owner to surrender rights to the
property.’’ As is the case with
interviews conducted with current and
past owners and occupants of the
property, interview questions should be
developed prior to the conduct of the
interviews, and tailored to gather
information to achieve the rule’s
objectives and performance factors. The
final rule contains no specific
requirements with regard to the type or
content of questions that must be asked
during the interviews.
EPA disagrees with commenters who
stated that it will be difficult to locate
and contact neighboring property
owners and occupants. The final rule, as
did the proposed rule, requires that the
environmental professional only locate
and interview one neighboring property
owner or occupant and only in those
cases where no owner or occupant of
the subject property can be identified.
An environmental professional should
be able to locate one owner or occupant
of a neighboring property when
conducting the on-site visual inspection
of the property. If the environmental
professional cannot easily locate an
owner and occupant of a neighboring
property, he or she may enlist the
assistance of local government officials
in identifying a neighboring property
owner or occupant. As is the case with
information ascertained from any
interview, the environmental
professional must apply his or her
judgment when drawing conclusions
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based on the information provided in
interviews with neighboring property
owners and occupants and should
attempt to verify any information
provided by reviewing other available
sources of information.
Q. What Are the Requirements for
Reviews of Historical Sources of
Information?
Proposed Rule
Historical documents and records
may contain information regarding past
ownership and uses of a property that
may be essential to assessing the
potential for environmental conditions
indicative of releases or threatened
releases of hazardous substances to be
present at the property. Historical
documents and records, among others,
may include chain of title documents,
land use records, aerial photographs of
the property, fire insurance maps, and
records held at local historical societies.
The proposed rule required that the
inquiry of the environmental
professional include a review of
historical documents and records for the
subject property that document the
ownership and use of the property for
a period of time as far back in the
history of the property as it can be
shown that the property contained
structures, or from the time the property
was first used for residential,
agricultural, commercial, industrial, or
governmental purposes.
Public Comments
Some commenters raised concerns
regarding the proposed requirements to
review historical records covering ‘‘a
period of time as far back in the history
of the subject property as it can be
shown that the property contained
structures or from the time the property
was first used for residential,
agricultural, commercial, industrial, or
governmental purposes.’’ Commenters
said that the proposed historical scope
of the records search is too extensive.
Some commenters requested that in the
final rule EPA adopt the provisions for
historical records searches provided in
the ASTM E1527–2000 standard.
Several commenters requested that EPA
explicitly require as part of the review
of historical records a review of chain of
title documents. The commenters
asserted that a review of chain of title
documents is the only reliable way to
identify previous owners of a property.
Final Rule
The statutory criteria in the
Brownfields Amendments require that
reviews of historical sources of
information be conducted to ‘‘determine
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previous uses and occupancies of the
real property since the property was
first developed.’’ The final rule requires
(as did the proposed rule) that historical
records on the subject property be
searched for information on the
property covering a time period as far
back in history as there is
documentation that the property
contained structures or was placed into
use of some form. This provision
follows the statutory language. In
addition, the final rule requires that
historical documents and information
be reviewed to obtain necessary
information for meeting the objectives
and performance factors in § 312.20(e)
and (f). If a search of historical sources
of information results in an inability of
the environmental professional to
document previous uses and
occupancies of the property as far back
in history as it can be shown that the
property contained structures or was
placed into use of some form, and such
information is not acquired elsewhere
during the investigation then it must be
documented as a data gap to the
inquiries. The requirements of
§§ 312.20(g) and 312.21(c)(2) are
applicable to all instances in the all
appropriate inquiries that result in data
gaps.
Despite the concerns raised by some
commenters regarding the scope of the
historical records review, we assert that
the scope of the requirements in the
final rule (as did the scope of the
proposed requirements) reflects the
statutory language provided in CERCLA
section 101(35)(B)(iii). The statutory
criterion provide that all appropriate
inquiries include ‘‘reviews of historical
sources * * * to determine previous
uses and occupancies of the real
property since the property was first
developed.’’ We point out that the final
rule does allow the environmental
professional to exercise his or her
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.’’ We believe
that this provides sufficient flexibility to
allow for any circumstances where, due
to the availability of other information
about a property an environmental
professional may conclude that a
comprehensive search of historical
records is not necessary to meet the
objectives and performance factors.
In response to commenters that
requested that EPA adopt the provisions
of the ASTM E1527–2000 standard for
conducting searches of historical
records, we assert that the scope of the
historical records search in today’s final
rule is very similar to the scope of
ASTM E1527 standard. The ASTM
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66091
E1527 standard, at section 7.3.1,
requires that historical sources of
information be searched to identify ‘‘all
obvious uses of the property* * *from
the present, back to the property’s
obvious first developed use, or back to
1940, whichever is earlier.’’ Given that
the language of both the ASTM E1527
standard and the requirements in the
final rule for conducting historical
records searches is very similar, we
conclude that the intent is the same and
the final rule represents no change from
current good customary business
practice. In addition, the final rule
provides for sufficient flexibility both
within the application of the
performance factors to the historical
records search requirements and in
allowing the environmental professional
to apply his or her judgment ‘‘in the
context of the facts available at the time
of the inquiry.’’
The final rule does not require that
any specific type of historic information
be collected. In particular, the rule does
not require that persons obtain a chain
of title document for the property. The
rule allows for the environmental
professional to use professional
judgment when determining what types
of historical documentation may
provide the most useful information
about a property’s ownership, uses, and
potential environmental conditions
when seeking to comply with the
objectives and performance factors for
the inquiries. Although we agree with
commenters that chain of title
documents may serve as an important
source of information regarding past
ownership of a property, it may not be
the only source of this information. To
the extent that chain of title documents
are otherwise obtained for other
purposes during the conduct of a
property sale or transaction, we believe
that these documents can easily be
made available to the environmental
professional by the prospective
landowner. Given that the final rule
requires that historical records be
searched for information on previous
uses and ownership of a property for as
far back in the history of property as can
be shown that the property contained
structures or was first used for
residential, agricultural, commercial,
industrial or governmental purposes, if
chain of title documents are the best and
most easily attainable source of this
information, we assume that such
documents will be obtained and used by
the environmental professional.
Given the wide variety of property
types and locations to which the final
rule could apply, any list of specific
documents could result in undue
burdens on many prospective
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landowners and grantees due to
difficulties in collecting any specific
document for any particular property or
property location. Therefore, the final
requirements for reviewing historical
documents allow the prospective
landowner or grantee and the
environmental professional to use their
judgment, in accordance with generally
accepted good commercial and
customary standards and practices, in
locating the best available sources of
historical information and reviewing
such sources for information necessary
to comply with the rule’s objectives and
performance factors.
As explained in section IV.J of this
preamble, the prospective landowner,
grantee, or environmental professional
may make use of previously collected
information about a property when
conducting all appropriate inquiries.
The collection of historical information
about a property may be a particular
case where previously collected
information may be valuable, as well as
easily accessible. In addition, nothing in
the rule prohibits a person from using
secondary sources (e.g., a previously
conducted title search) when gathering
information about historical ownership
and usage of a property. As explained in
section IV.J, information must be
updated if it was last collected more
than 180 days prior to the date of
acquisition of the property.
R. What Are the Requirements for
Searching for Recorded Environmental
Cleanup Liens?
For purposes of this rule, recorded
environmental cleanup liens are
encumbrances on property for the
recovery of incurred cleanup costs on
the part of a state, tribal or federal
government agency or other third party.
Recorded environmental cleanup liens
often provide an indication that
environmental conditions either
currently exist or previously existed on
a property that may include the release
or threatened release of a hazardous
substance. The existence of an
environmental cleanup lien should be
viewed as an indicator of potential
environmental concerns and as a basis
for further investigation into the
potential existence of on-going or
continued releases or threatened
releases of hazardous substances on, at,
in, or to the subject property.
Proposed Rule
The proposed rule required that
prospective landowners and grantees, or
environmental professionals on their
behalf, search for environmental
cleanup liens that are recorded under
federal, tribal, state, or local law.
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Environmental cleanup liens that are
not recorded by government entities or
agencies are not addressed by the
language of the statute (the statute
speaks only of ‘‘recorded liens’’);
therefore, the proposed rule required
that only a search for recorded
environmental liens be included in the
all appropriate inquiries investigation.
Public Comments
Some commenters asked that EPA
state more clearly that the responsibility
for searching for environmental cleanup
liens rests with the prospective
landowner and not the environmental
professional. A few commenters
requested that the Agency provide some
guidance on where to find recorded
environmental cleanup liens.
Final Rule
EPA is finalizing the proposed
requirements to search for recorded
environmental cleanup liens without
changes. The all appropriate inquiries
investigation must include a search for
recorded environmental cleanup liens.
The final rule allows that the search for
recorded environmental cleanup liens
be performed either by the prospective
landowner or grantee, or through the
inquiry of the environmental
professional. The search for such liens
may not necessarily require the
expertise of an environmental
professional and therefore may be more
efficiently or more cost-effectively
performed by the prospective
landowner or grantee, or his or her
agent. Such liens may be included as
part of the chain of title documents or
may be recorded in some other manner
or format by state or local government
agencies. If such information is
collected by the prospective landowner
or grantee, or other agent who is not
under the supervision or responsible
charge of the environmental
professional, the final rule allows for,
but does not require, the information
that is collected by or on the behalf of
the prospective landowner or grantee to
be provided to the environmental
professional. If the information is
provided to the environmental
professional, he or she can then make
use of such information during the
conduct of the all appropriate inquiries
and when rendering conclusions or
opinions regarding the environmental
conditions of the property. If such
information is not provided to the
environmental professional and the lack
of such information affects the ability of
the environmental professional to
identify conditions indicative of
releases or threatened releases of
hazardous substances on, at, in or to the
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property, the lack of information should
be noted as a data gap (per the
requirements of § 312.21(b)(2)).
Although some commenters requested
that EPA be more explicit in the final
rule in requiring that the search for
recorded environmental cleanup liens
be conducted by the prospective
landowner (or grantee), we believe that
the decision of who conducts the search
may be best left up to the judgment of
the prospective landowner or grantee
and environmental professional. The
final rule provides in § 312.22 that the
search for recorded environmental
cleanup liens can fall outside the
inquiries conducted by the
environmental professional. The search
for recorded environmental cleanup
liens is not included as part of the
requirements governing the results of an
inquiry by an environmental
professional (§ 312.21). Therefore, the
search may be conducted by the
prospective landowner or grantee, his or
her attorney or agent, or the
environmental professional.
We offer one caution about the
conclusion that might be drawn if no
recorded environmental cleanup liens
are found. If EPA is conducting a
cleanup at site at the time it is
transferred or acquired, EPA is able to
record a lien post acquisition. For
example, one type of lien, often referred
to as a windfall lien, has no statute of
limitations and arises at the time EPA
first spends Superfund money. States
and localities may have similar
mechanisms. Therefore, even if a
recorded environmental cleanup lien is
not found during the conduct of the all
appropriate inquiries investigation, one
may be recorded at a later date if EPA
is undertaking a cleanup or response
action at the property.
With regard to commenters who
requested that EPA provide guidance on
where to search for environmental
cleanup liens, we advise that
prospective landowners and grantees to
seek the advice of a local realtor, real
estate attorney, title company, or other
real estate professional. Environmental
cleanup liens may be recorded as part
of the land title records or as part of
other state or local government land or
real estate records. Recorded
environmental cleanup liens may be
recorded in different places, depending
upon the particular state and particular
locality in which the property is
located.
S. What Are the Requirements for
Reviewing Federal, State, Tribal, and
Local Government Records?
Federal, tribal, state and local
government records may contain
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information regarding environmental
conditions at a property. In particular,
government records, or data bases of
such information, may include
information on previously reported
releases of hazardous substances,
pollutants, contaminants, petroleum
and petroleum products and controlled
substances. Government records and
available databases can provide valuable
information on remedial actions and
emergency response activities that may
have been conducted at a particular
property. Government records also may
include information on institutional
controls related to a particular property.
For example, in the case of NPL sites,
EPA Superfund records, including
Action Memoranda and Records of
Decision, may have information on
institutional controls in place at such
properties. Government records also
may include information on activities or
property uses that could cause releases
or threatened releases to be present at a
property.
Proposed Rule
The proposed rule required that
federal, state, tribal and local
government records be searched for
information necessary to achieve the
objectives and performance factors,
including information regarding the use
and occupancy of and the
environmental conditions at the subject
property and conditions of nearby or
adjoining properties that could have a
impact upon the environmental
conditions of the subject property. The
proposed rule included requirements to
search federal, tribal, state, and local
government records for information
indicative of environmental conditions
at the subject property.
The proposed rule also included
requirements to review government
records, or data bases of information
contained in government records, for
information about nearby and adjoining
properties. Reviews of such records may
provide valuable information regarding
the potential impact to the subject
property from hazardous substances and
petroleum contamination migrating
from contiguous or nearby properties.
The proposed rule included required
minimum search distances for
government records searches of nearby
properties.
To account for property-specific and
regionally-specific conditions that can
influence the appropriateness of the
proposed search distances for any given
type of record and property, the
proposed rule allowed the
environmental professional to adjust the
applicable search distances when
searching for information about off-site
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properties by applying professional
judgment. For example, appropriate
search distances for properties located
in rural settings may differ from
appropriate search distances for urban
settings. In addition, ground water flow
direction, depth to ground water, arid
weather conditions, the types of
facilities located on nearby properties,
and other factors may influence the
degree of impact to a property from offsite sources. Therefore, the proposed
rule allowed the environmental
professional to adjust any or all of the
proposed minimum search distances for
any of the record types, based upon
professional judgment and the
consideration of site-specific conditions
or circumstances when seeking to
achieve the proposed objectives and
performance factors for the required
inquiries.
Public Comments
The Agency received a variety of
comments in which commenters
expressed concerns about the
applicability or adequacy of specific
types of government records included in
the proposed rule (e.g., CERCLIS
records, information on RCRA facilities,
ERNS). A few commenters raised
concerns about the availability of tribal
records. Several commenters raised
concerns regarding the availability of
government records on institutional
controls. Commenters also pointed out
that, given the lack of available
databases and other information on
institutional controls, it may be
particularly difficult to search for
institutional controls associated with
adjoining and nearby properties.
Final Rule
We are finalizing the requirements for
reviewing federal, state, tribal, and local
government data bases as proposed,
with one exception. The final rule
requires that government records and
available lists for institutional and
engineering controls be searched only
for information on such controls at the
subject property. All appropriate
inquiries investigations do not have to
include searches for institutional and
engineering controls in place at nearby
and adjoining properties. We made this
change because we agree with
commenters who pointed out that
information on institutional and
engineering controls may be difficult to
find as there are no available national
sources of this information. Only a few
states have available lists of institutional
controls. In addition, the information
that may be inferred from knowledge of
institutional and engineering controls
that are in place at adjoining and nearby
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properties, i.e., that there was a
response action, a remedial action, or
corrective action taken at the site, can be
inferred from information obtained from
other sources (e.g., CERCLIS, RCRIS,
state records of response actions).
It is important that prospective
landowners obtain information on
institutional and engineering controls in
place at the property being acquired. It
also may be important to locate
information on such controls in place at
nearby properties. To obtain the liability
protections afforded under CERCLA
(i.e., innocent landowner, contiguous
property owner, bona fide prospective
purchaser), the statute requires, as part
of the ‘‘continuing obligations,’’ that the
property owner comply with all land
use restrictions and not impede the
effectiveness of institutional controls.
Therefore, it is important that
information on institutional and
engineering controls be obtained by
prospective landowners, even though
information about such controls may
not have been routinely obtained as part
of due diligence practices prior to
today’s final rule (we note that the
current interim standard does include
provisions for searching for ‘‘activity
and use limitations’’).
Routine ‘‘chain of title’’ reports may
not always contain information labeled
as institutional or engineering controls.
However, title companies may include,
as part of the chain of title reports
‘‘restrictions of record on title’’ when
such restrictions are recorded because of
underlying environmental conditions at
a property. Therefore, when requesting
information on ‘‘institutional controls’’
or ‘‘engineering controls’’ about a
property, prospective landowners,
grantees, and environmental
professionals may want to request
information on ‘‘restrictions of record
on title’’ as well, in case any available
information on institutional or
engineering controls is so labeled in the
chain of title records. In addition to
chain of title records, information on
institutional controls and engineering
controls may be recorded in local land
records. Also, some states are beginning
to create registries to track information
on institutional and engineering
controls. Therefore, prospective
landowners and grantees should
consider consulting these other sources
of information in addition to chain of
title records for information on
institutional and engineering controls.
In response to the commenters who
pointed out particular shortcomings
with specific sources of information
(e.g., CERCLIS, RCRIS, ERNS) we point
out that the requirement to review
government records explicitly provides
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that the reviews be conducted in
compliance with the objectives and
performance standards. If a particular
source of information cannot be
accessed within a reasonable time frame
or within reasonable costs, then the
information should be sought from other
sources. In addition, if a particular
source of information will only provide
information that can more easily or
readily be found elsewhere, the
particular source does not have to be
obtained or consulted. If application of
the objectives and performance
standards to the requirement to review
government records results in an
inability to provide necessary
information (or information identified
as necessary in the objectives for the
final rule), then the lack of information
should be documented as a data gap in
the final report. In addition, the
environment professional should
comment on the significance the lack of
any information has on his or her ability
to identify conditions at the property
that are indicative of releases or
threatened releases of hazardous
substances (in compliance with
§ 312.21(c)(2)).
In response to commenters who
pointed out that it may be difficult to
obtain or gain access to tribal
government records, we point out that
such records need only be searched for
and reviewed in those instances where
the subject property is located on or
near tribal-owned lands. In these cases,
it is important to attempt, within the
scope of the rule’s objectives and
performance factors, to review such
records. When such records are not
available, necessary information should
be sought from other sources. When no
information is available and the
objectives and performance factors of
the final rule cannot be met and the
result is a lack of information that may
affect the environmental professional’s
ability to render an opinion regarding
the environmental conditions of a
property, the lack of information must
be documented as a data gap in
compliance with § 312.21(c)(2).
The final rule requires that the
following types of government records
or data bases of government records be
reviewed to obtain information on the
subject property and nearby properties
necessary to meet the rule’s objectives
and performance standards:
1. Government records of reported
releases or threatened releases at the
subject property, including previously
conducted site investigation reports.
2. Government records of activities,
conditions, or incidents likely to cause
or contribute to releases or threatened
releases, including records documenting
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regulatory permits that were issued to
current or previous owners or operators
at the property for waste management
activities and government records that
identify the subject property as the
location of landfills, storage tanks, or as
the location for generating and handling
activities for hazardous substances,
pollutants, contaminants, petroleum
and petroleum products, or controlled
substances.
3. CERCLIS records—EPA’s
Comprehensive Environmental
Response, Compensation, and Liability
Information System (CERCLIS) database
contains general information on sites
across the nation and in the U.S.
territories that have been assessed by
EPA, including sites listed on the
National Priorities List (NPL). CERCLIS
includes information on facility
location, status, contaminants,
institutional controls, and actions taken
at particular sites. CERCLIS also
contains information on sites being
assessed under the Superfund Program,
hazardous waste sites and potential
hazardous waste sites.
4. Government-maintained records of
public risks—the all appropriate
inquiries government records search
should include a search for available
records documenting public health
threats or concerns caused by, or related
to, activities currently or previously
conducted at the site.
5. Emergency Response Notification
System (ERNS) records—ERNS is EPA’s
data base of oil and hazardous substance
spill reports. The data base can be
searched for information on reported
spills of oil and hazardous substances
by state.
6. Government registries, or publicly
available lists of engineering controls,
institutional controls, and land use
restrictions. The all appropriate
inquiries government records search
must include a search for registries or
publicly available lists of recorded
engineering and institutional controls
and recorded land use restrictions. Such
records may be useful in identifying
past releases on, at, in, or to the subject
property or identifying continuing
environmental conditions at the
property.
The final rule requires that
government records be searched to
identify information relative to the
objectives and in accordance with the
performance factors on: (1) Adjoining
and nearby properties for which there
are governmental records of reported
releases or threatened releases (e.g.,
properties currently listed on the
National Priorities List (NPL), properties
subject to corrective action orders under
the Resource Conservation and
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Recovery Act (RCRA), properties with
reported releases from leaking
underground storage tanks); (2)
adjoining and nearby properties
previously identified or regulated by a
government entity due to environmental
conditions at a site (e.g., properties
previously listed on the NPL, former
CERCLIS sites with notices of no further
response actions planned (NFRAP)); and
(3) adjoining and nearby properties that
have government-issued permits to
conduct waste management activities
(e.g., facilities permitted to manage
RCRA hazardous wastes).
In the case of government records
searches for nearby properties, the final
rule includes minimum search distances
(e.g., properties located either within
one mile or one-half mile of the subject
property) for obtaining and reviewing
records or data bases concerning
activities and facilities located on
nearby properties. The search distances
are based upon our best judgment
regarding the potential impacts that
incidents or circumstances at an
adjoining property may have on the
subject property. With the exception of
the required searches for institutional
and engineering controls, the search
distances finalized in today’s rule are
the search distances that were proposed
in the proposed rule. For example,
government records identifying
properties listed on the NPL must be
searched to obtain information on NPL
sites located within one mile of the
subject property. NPL sites located
beyond one mile of a property most
likely will have little or no impact on
the environmental conditions at the
subject property. In the case of two
types of records, records of hazardous
waste handler and generator records and
permits, records of registered storage
tanks, the final requirements specify
that such records only be searched for
information specific to the subject
property and adjoining properties (the
rule contains no requirement to search
for these two types of government
records for other nearby properties). The
final rule requires that available lists of
institutional controls and engineering
controls only be searched for
information on the subject property.
In the case of all the government
records listed above and in the final rule
in § 312.26, the requirements of this
criterion may be met by searching data
bases containing the same government
records mentioned in the list above that
are accessible and available through
government entities or private sources.
The review of actual records is not
necessary, provided that the same
information contained in the
government records and required to
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meet the requirements of this criterion
and achieve the objectives and
performance factors for these
regulations is attainable by searching
available data bases.
The final rule allows the
environmental professional to adjust the
search distances for reviewing
government records of nearby properties
based upon his or her professional
judgment. Environmental professionals
may consider one or more of the
following factors when determining an
alternative appropriate search distance:
• The nature and extent of a release;
• Geologic, hydrogeologic, or
topographic conditions of the subject
property and surrounding environment;
• Land use or development densities;
• The property type;
• Existing or past uses of surrounding
properties;
• Potential migration pathways (e.g.,
groundwater flow direction, prevalent
wind direction); or
• Other relevant factors.
The final rule requires environmental
professionals to document the rationale
for making any modifications to the
required minimum search distances
included in § 312.26 of the regulation.
T. What Are the Requirements for
Visual Inspections of the Subject
Property and Adjoining Properties?
Proposed Rule
The proposed rule required that an
on-site visual inspection of the subject
property be conducted as part of the all
appropriate inquiries investigations,
with one limited exception. The
proposed on-site visual inspection
requirements included requirements to
inspect any facilities and improvements
on the property as well as all areas
where hazardous substances are or may
have been used, stored, treated,
handled, or disposed. In addition, the
proposed rule included requirements to
visually inspect adjoining properties.
The proposal required that inspections
of adjoining properties be conducted
from the property line, public right-ofway, or other vantage point.
The proposed rule included a limited
exception from the requirement to
conduct the visual inspection ‘‘on-site.’’
The proposed exception provided that
in unusual circumstances where an onsite visual inspection cannot be
performed because of physical
limitations, remote and inaccessible
location, or another inability to obtain
access to the property, provided good
faith efforts are taken to obtain such
access and access to the property could
not be obtained, a visual inspection
could be conducted from an off-site
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vantage point (e.g., property-line,
airplane, public right-of-way). To
qualify for the exception from the
requirement to conduct the inspection
on site, the proposed rule required that
the environmental professional
document the good faith efforts
undertaken to gain access to the
property and explain why such efforts
were unsuccessful. The proposed rule
also required that the environmental
professional document what other
sources of information were consulted
to obtain information regarding the
potential environmental conditions at
the property and the significance of the
failure to conduct the inspection on site
on his or her ability to identify
conditions indicative of releases or
threatened releases of hazardous
substances on, at, in, or to the subject
property.
In the preamble to the proposed rule,
EPA recommended that an
environmental professional conduct the
on-site visual inspection.
Public Comments
A few commenters stated that EPA
should not recommend, as we did in the
preamble to the proposed rule, that an
individual meeting the definition of
environmental professional conduct the
on-site visual inspection. These
commenters stated that anyone under
the responsible charge or supervision of
an environmental professional should
be able to conduct the on-site visual
inspection. Commenters stated, that by
recommending in the preamble that the
environmental professional conduct the
on-site visual inspection, the Agency
was effectively requiring an
environmental professional to conduct
the visual inspection. Other commenters
expressed support for the Agency’s
recommendation.
A few other commenters thought the
proposed exception from the
requirement to conduct the visual
inspection on site was ‘‘broad’’ and
‘‘would increase the likelihood of
inspections not being performed and
contamination not being detected.’’
These commenters expressed a concern
that any exception from the requirement
to conduct an on-site visual inspection
could open the door to abuse and result
in properties being transferred without
being inspected. Commenters raised
concerns that owners of uninspected
properties could obtain liability
protection by claiming to have fulfilled
the requirements of all appropriate
inquiries without knowledge of ongoing releases at a property.
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Final Rule
The final rule, at § 312.27, retains the
proposed requirement that a visual onsite inspection be conducted of the
subject property. The final visual on-site
inspection requirements include
requirements to inspect the facilities
and any improvements on the property,
as well as visually inspect areas on the
property where hazardous substances
may currently be or in the past may
have been used, stored, treated,
handled, or disposed of. We continue to
assert that, and commenters agreed, that
every all appropriate inquiries
investigation must include an on-site
visual inspection of the property. The
on-site inspection of a property most
likely will be an excellent source of
information regarding indications of
environmental conditions on a property.
The final rule requires that a visual onsite inspection of the subject property be
conducted in all but a few very limited
cases. In addition, the final rule retains
the proposed requirement that in those
cases where physical limitations restrict
the portions of the property that may be
visually inspected, that the physical
limitations encountered during the
visual on-site inspection (e.g., weather
conditions, physical obstructions) must
be documented.
We note that persons conducting all
appropriate inquiries with monies
provided in a grant awarded under
CERCLA section 104(k)(2)(B) must,
depending on the terms and conditions
of the grant or cooperative agreement,
include within the scope of the on-site
visual inspection an inspection of the
facilities, improvements, and other areas
of the property where pollutants,
contaminants, petroleum and petroleum
products, or controlled substances may
currently be or in the past may have
been used, stored, treated, handled, or
disposed.
The visual on-site inspection of a
property during the conduct of all
appropriate inquiries may be the most
important aspect of the inquiries and
the primary source of information
regarding the environmental conditions
on the property. In all cases, every effort
must be made to conduct an on-site
visual inspection of a property when
conducting all appropriate inquiries.
We understand that a prospective
landowner, grantee, or environmental
professional, in some limited
circumstances, may not be able to obtain
on-site access to a property. Extreme
and prolonged weather conditions and
remote locations can impede access to a
property. A prospective landowner,
grantee or environmental professional
also could be unable to gain on-site
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access to a property if the owner refuses
to provide access to the party, even after
the party exercises all good faith efforts
to gain access to the property (e.g.,
seeking assistance from state
government officials). Such
circumstances may arise in cases where
a local government becomes a last resort
purchaser of a potentially-contaminated
property that has little economic value.
The unique nature of such transactions
may result in a local government facing
an uncooperative or recalcitrant
property owner. Unlike commercial
property transactions between private
parties, where the parties’ economic and
legal liability interests and the ability to
abandon the transaction can work in
favor of the purchasing party’s ability to
gain access to a property prior to
acquisition, property transactions
between a private party and a local
government may not afford the local
government the same leverage, even if it
is in the public interest to attain
ownership of the property. This
situation may occur when the local
government seeks to assess, clean up,
and revitalize an area, but the owner of
the property is unreachable,
unavailable, or otherwise unwilling to
provide access to the property. In such
limited circumstances, the public
benefit attained from a government
entity gaining ownership of a property
may outweigh the need to gain on-site
access to the property prior to the
transfer of ownership.
The final rule requires, in unusual
circumstances, that the prospective
landowner or grantee make good faith
efforts to gain access to the property.
However, the mere refusal of a property
owner to allow the prospective property
owner or grantee to have access to the
property does not constitute an unusual
circumstance, absent the making of good
faith efforts to otherwise gain access.
The final rule, at § 312.10, defines ‘‘good
faith’’ as ‘‘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.’’
In those unusual circumstances where
a prospective landowner, a grantee, or
an environmental professional, after
undertaking good faith efforts, cannot
gain access to a property and therefore
cannot conduct an on-site visual
inspection, the final rule requires that
the property be visually inspected, or
observed, by another method, such as
through the use of aerial photography,
or be inspected, or observed, from the
nearest accessible vantage point, such as
the property line or a public road that
runs through or along the property. In
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addition, the rule requires that the all
appropriate inquiries report include
documentation of efforts undertaken by
the prospective landowner, grantee, or
the environmental professional to obtain
on-site access to the subject property
and include an explanation of why good
faith efforts to gain access to subject
property were unsuccessful. The all
appropriate inquiries report must
include documentation of other sources
of information that were consulted to
obtain information necessary to achieve
the objectives and performance factors.
This documentation should include
comments, from the environmental
professional who signs the report,
regarding any significant limitations on
the ability of the environmental
professional to identify conditions
indicative of releases or threatened
releases on, at, in, or to the subject
property, that may arise due to the
inability of the prospective landowner,
grantee, or environmental professional
to obtain on-site access to the property.
In those limited cases where an onsite visual inspection cannot be
conducted prior to the date a property
is acquired, we remind prospective
landowners that protection from
CERCLA liability depends upon the
prospective landowner complying with
all of the post-acquisition continuing
obligations provided in the statute.
Therefore, to ensure that adequate
information is attained about a property
to ensure that the property owner can
fulfill these obligations, we recommend
that once a property is purchased, the
property owner conduct an on-site
visual inspection of the property once
the property is acquired, if it could not
be conducted prior to acquisition. Such
an inspection may provide important
information necessary for the property
owner to fully comply with the other
statutory provisions, including on-going
obligations, governing the CERCLA
liability protections.
We disagree with the commenters
who argued that the exception from the
requirement to conduct the visual
inspection on-site is ‘‘broad.’’ We point
out that the exception is limited to the
requirement that the visual inspection
be conducted on-site. In all cases where
the exception applies, the visual
inspection must still be conducted from
another vantage point. In addition, the
exception is limited to only those
circumstances where all good faith
efforts are made to gain access the
property. The final rule requires that all
good faith efforts to gain access be
documented and requires that the
environmental professional comment on
the consequences that the inability to
gain access to the property may have on
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his or her ability to render an opinion
on property conditions that may be
indicative of releases or threatened
releases on, at, in, or to the property.
The exception is very limited in scope
and the documentation requirements
should limit the use of the exception as
well as provide the prospective
landowner with useful information for
determining the potential need for
further investigations of the property
after acquisition.
The final rule also requires that the all
appropriate inquiries investigation
include visual inspections of properties
that adjoin the subject property. Visual
inspections of adjoining properties may
provide excellent information on the
potential for the subject property to be
affected by contamination migrating
from adjoining properties. Visual
inspections of adjoining properties may
be conducted from the subject
property’s property line, one or more
public rights-of-way, or other vantage
point (e.g., via aerial photography).
Where practicable, a visual on-site
inspection is recommended and may
provide greater specificity of
information. The visual inspections of
adjoining properties must include
observing areas where hazardous
substances currently may be, or
previously may have been, stored,
treated, handled, or disposed. Visual
inspections of adjoining properties
otherwise also must be conducted to
achieve the objectives and performance
goals for all the appropriate inquiries.
Physical limitations to the visual
inspections of adjoining properties
should be noted.
As explained in the preamble to the
proposed rule, EPA and the Negotiated
Rulemaking Committee considered,
when developing the proposed rule,
requiring that all activities in the all
appropriate inquiries investigation to be
conducted by persons meeting the
proposed definition of an environmental
professional. Requiring that an
environmental professional conduct all
activities could ensure that all data
collection and investigations are
conducted in a manner and to a degree
of specificity that allows the
environmental professional to make best
use of all information in forming
opinions and conclusions regarding the
environmental conditions at a property.
However, after careful review of the
specific activities included in the
statutory criteria and conducting an
assessment of the costs and burdens of
such a requirement, EPA and the
Committee concluded that it is not
necessary for each and every regulatory
requirement to be conducted by an
environmental professional. As outlined
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in section IV.H of this preamble, today’s
final rule, as did the proposed rule,
allows for certain aspects of the
inquiries to be conducted solely by the
prospective landowner or grantee, while
providing that all other aspects be
conducted under the supervision or
responsible charge of the environmental
professional. Among the activities
required to be conducted under the
supervision or responsible charge of an
environmental professional is the onsite visual inspection.
It continues to be EPA’s
recommendation that visual inspections
of the subject property and adjoining
properties be conducted by an
individual who meets the regulatory
definition of an environmental
professional. Although many other
aspects of the all appropriate inquiries
may be conducted sufficiently and
accurately by individuals other than an
environmental professional (e.g., a
research associate or librarian may be
well qualified to search government
records, an attorney may be well
qualified to conduct a search for an
environmental lien), EPA believes that
an environmental professional is best
qualified to conduct a visual inspection
and locate and interpret information
regarding the physical and geological
characteristics of the property as well as
information on the location and
condition of equipment and other
resources located on the property. EPA
recognizes that other individuals who
do not meet the regulatory definition of
an environmental professional,
particularly when these individuals are
conducting such activities under the
supervision or responsible charge of an
environmental professional, may have
the required skills and knowledge to
conduct an adequate on-site visual
inspection. However, EPA believes that
the professional judgment of an
individual meeting the definition of an
environmental professional is important
to ensuring that all circumstances at the
property that are indicative of
environmental conditions and potential
releases or threatened releases are
properly identified and analyzed. An
environmental professional is best
qualified for identifying such situations
and conditions and rendering a
judgment or opinion regarding the
potential existence of conditions
indicative of environmental concerns.
Although some commenters stated
that EPA should not recommend that
the visual inspection be conducted by a
person meeting the definition of
environmental professional, we point
out that other commenters stated their
support for our recommendation and
some even stated that EPA should
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require in the regulation that the
inspection be conducted by an
environmental professional. We remain
convinced that the on-site visual
inspection of the property can be the
single most important source of
information regarding the
environmental conditions of a property
and that an individual meeting the
regulatory definition of environmental
professional is best able to interpret
such observations of a property and
ascertain the probability of conditions
indicative of releases or threatened
releases of hazardous substances being
present at the property. In addition, we
point out that the definition of
environmental professional included in
the final rule is less stringent than the
proposed definition. Therefore,
commenter concerns regarding any
significant cost burdens associated with
the environmental professional
conducting the on-site visual inspection
may be alleviated. We emphasize that
EPA is recommending that the on-site
visual inspection be conducted by an
individual who meets the definition of
environmental professional included in
the final rule; it is not a requirement
that the inspection be conducted by an
environmental professional. The rule
requires only that the inspection be
conducted by an individual who is
under the supervision or responsible
charge of an individual meeting the
definition of environmental
professional. EPA agrees that if the final
rule required that the on-site visual
inspection be conducted by an
individual meeting the definition of an
environmental professional, the
requirement could impose undue
burdens in certain circumstances. In
addition, there may be circumstances
that in the best professional judgment of
an environmental professional, another
person under the responsible charge of
the environmental professional may be
more qualified to conduct the on-site
inspection. To allow for flexibility and
the application of professional judgment
to specific circumstances, EPA
continues to recommend that an
environmental professional conduct the
on-site inspection, but the Agency is not
requiring that the inspection be
conducted by an environmental
professional.
U. What Are the Requirements for the
Inclusion of Specialized Knowledge or
Experience on the Part of the
‘‘Defendant?’’
Because the conduct of all appropriate
inquiries is one element of a legal
defense to CERCLA liability, the statute
refers to the prospective landowner, or
the user of the all appropriate inquiries
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investigation, as the ‘‘defendant.’’ This
ensures that any information or special
knowledge held by the prospective
landowner with regard to a property and
its conditions be included in the preacquisition inquiries and be considered,
along with all information collected
during the conduct of all appropriate
inquiries, when an environmental
professional renders a judgment or
opinion regarding conditions indicative
of environmental conditions indicative
of releases or potential releases of
hazardous substances on, at, in, or to the
subject property. It is recommended that
this information be revealed to the
parties conducting the all appropriate
inquiries so that any specialized
knowledge may be taken into account
during the conduct of the required
aspects of the all appropriate inquiries.
Congress first added the innocent
landowner defense to CERCLA in the
Superfund Amendments and
Reauthorization Act (SARA) of 1986.
The Brownfields Amendments amended
the innocent landowner defense and
added to CERCLA the bona fide
prospective purchaser and the
contiguous property owner liability
protections to CERCLA liability. The
1986 SARA amendments to CERCLA
established that among other elements
necessary for a defendant to
successfully assert the innocent
landowner defense, a defendant must
demonstrate that he or she had, on or
before the date of acquisition of the
property in question, made all
appropriate inquiries into previous
ownership and uses of the property.
Congress directed courts evaluating a
defendant’s showing of all appropriate
inquiries to take into account, among
other things, ‘‘any specialized
knowledge or experience on the part of
the defendant.’’ Nothing in today’s rule
changes the nature or intent of this
requirement as it has existed in the
statute since 1986.
Proposed Rule
The proposed rule retained, as part of
the federal all appropriate inquiries
requirements, the consideration of any
specialized knowledge or experience of
the prospective landowner (or grantee if
the grantee is or will be the property
owner). The proposed rule did not
extend this requirement beyond what
already was required under CERCLA
and established through case law. The
proposed rule required that all
appropriate inquiries include the
consideration of specialized knowledge
held by the prospective landowner or
grantee with regard to the subject
property, the area surrounding the
subject property, the conditions of
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adjoining properties, as well as other
experience relative to the inquiries that
may be applicable to identifying
conditions indicative of releases or
threatened releases at the subject
property. The proposed rule also
required that the results of the inquiries
take into account any specialized
knowledge related to the property,
surrounding areas, and adjoining
properties held by the persons
responsible for undertaking the
inquiries, including any specialized
knowledge on the part of the
environmental professional.
Public Comments
EPA did not receive significant
comment on the proposed requirements
for considering the specialized
knowledge or experience on the part of
the defendant. A few commenters
mentioned that the proposed
requirements would result in the all
appropriate inquiries investigations
having to include interviews with all
previous owners and occupants of the
property. These commenters may have
mistakenly interpreted the proposed
provisions as requiring that the
specialized knowledge of all current
owners and occupants be considered as
part of the all appropriate inquiries
investigation. We clarify that only the
specialized knowledge of the
prospective landowner or grantee, and
the environmental professional
overseeing the conduct of the inquiries
need be considered.
Final Rule
The final rule retains the proposed
provisions governing the consideration
of specialized knowledge or experience
on the part of the prospective
landowner (or grantee) and the
environmental professional conducting
the all appropriate inquiries
investigation on the part of the
prospective landowner or grantee.
As provided in the preamble to the
proposed rule, existing case law related
to the innocent landowner defense
shows that courts appear to have
interpreted the ‘‘specialized knowledge’’
factor to mean that the professional or
personal experience of the defendant
may be taken into account when
analyzing whether the defendant made
all appropriate inquiries. For example,
in Foster v. United States, 922 F. Supp.
642 (D. D.C. 1996), the owner of a
property formerly owned by the General
Services Administration and
contaminated by, among other things,
lead, mercury and PCBs, brought an
action against the United States and
District of Columbia, prior owners or
operators of the site. The plaintiff was
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a principal in Long & Foster companies
and purchased the property through a
general partnership, and received it by
quitclaim deed. The innocent
landowner defense requires a property
owner to demonstrate that when he or
she purchased a property, he or she did
not know and had no reason to know of
contamination at, on, in, or to the
property. The court rejected the
plaintiff’s claim to the innocent
landowner defense based in part on the
plaintiff’s specialized knowledge. The
court found that his specialized
knowledge included his position at
Long & Foster, which did hundreds of
millions of dollars of commercial real
estate transactions, and his position as
a partner in at least 15 commercial real
estate partnerships. The partnership was
involved as an investor in a number of
real estate transactions, some of which
involved industrial or commercial or
mixed-use property. The court ruled
that ‘‘it cannot be said that [the
partnership] is a group
unknowledgeable or inexperienced in
commercial real estate transactions.’’
Foster, 922 F. Supp. at 656.
In American National Bank and Trust
Co. of Chicago v. Harcros Chemicals,
Inc., 1997 WL 281295 (N.D. Ill. 1997),
the plaintiff was a company ‘‘involved
in brownfields development, purchasing
environmentally distressed properties at
a discount, cleaning them up, and
selling them for a profit.’’ American
National Bank,1997 WL 281295 at *4.
As a counter-claim defendant, the
company asserted it was an innocent
landowner and therefore not liable
pursuant to CERCLA. The court found
that among other reasons the defense
failed because the company possessed
specialized knowledge. The court ruled
that the company was an expert
environmental firm and possessed
knowledge that should have alerted it to
the potential problems at the site.
The final rule requires that the
specialized knowledge of prospective
landowners and the persons responsible
for undertaking the all appropriate
inquiries, including grantees, be taken
into account when conducting the all
appropriate inquiries for the purposes of
identifying conditions indicative of
releases or threatened releases at a
property. However, as evidenced by the
case law cited above, the determination
of whether or not the all appropriate
inquiries standard is met with regard to
specialized knowledge (as well as in
regard to all the criteria) remains within
the discretion of the courts.
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V. What Are the Requirements for the
Relationship of the Purchase Price to
the Value of the Property, if the Property
Was Not Contaminated?
Congress included in the statutory
criteria for all appropriate inquiries a
requirement to consider the relationship
of the purchase price of a property to
the value of the property, if the property
was not contaminated. The criteria was
retained in the criteria included in the
Brownfields Amendments from the all
appropriate inquiries provisions of the
innocent landowner defense established
by Congress in the 1986 amendments to
CERCLA.
Proposed Rule
The proposed rule required that the
prospective landowner or grantee
consider whether or not the purchase
price of the property reflects the fair
market value of the property, assuming
that the property is not contaminated.
The proposed rule required that the
prospective landowner or grantee
consider whether any differential
between the purchase price and the
value of the property is due to the
presence of releases or threatened
releases of hazardous substances at the
property. There may be many reasons
that the price paid for a particular
property is not an accurate reflection of
the fair market value. The all
appropriate inquiries investigation need
only include a consideration of whether
a significant difference between the
price paid for a property and the fair
market value of a property, if the
property were not contaminated, is an
indication that the property may be
contaminated.
Public Comments
Many commenters asserted that an
environmental professional should not
be required to consider the relationship
of the purchase price to the value of the
property as part of the all appropriate
inquiries investigation. Concerns raised
by commenters include whether
environmental professionals are
qualified to assess the fair market value
of a property. Some commenters
thought that a requirement that
prospective landowners or
environmental professionals consider
the relationship of the purchase price of
property to the value of the property
could violate federal or state laws
governing property appraisals. Some
commenters argued that the all
appropriate inquiries investigation
should not include the requirement to
consider the relationship of the
purchase price to the value of the
property because the fair market value
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is not always easily ascertainable. Other
commenters requested that the preamble
to the final rule include a
recommendation that an appraisal be
performed to determine a property’s fair
market value. In addition, commenters
requested that in cases where an
appraisal is conducted to determine the
fair market value of a property, the rule
should require that it meet the Uniform
Standards of Professional Appraisal
Practice. Still other commenters
supported including the requirement in
the final rule, but asked the Agency to
require prospective landowners to
obtain a property appraisal conducted
by a trained or certified real estate
appraiser. Some commenters stated that
prospective landowners should not be
required to divulge information on the
price paid for a property to the
environmental professional or other
third party.
Final Rule
The final rule retains the requirement
to consider the relationship of the
purchase price to the fair market value
of the property, if the property were not
contaminated. The requirement is part
of the statutory criteria established by
Congress and has been part of the
statutory provisions governing all
appropriate inquiries, within the
innocent landowner defense, since
1986. Today’s rule does not change the
previously existing provision. As did
the proposed rule, today’s final rule
allows for this criterion to be conducted
by the prospective landowner or the
grantee or undertaken as part of the
inquiry by an environmental
professional. If an environmental
professional is not qualified to consider
the relationship of the purchase price to
the value of the property, the
prospective landowner or grantee may
undertake the task or hire another third
party to make the comparison of price
and fair market value and consider
whether any differential is due to
potential environmental contamination.
If the relationship of the purchase
price to the fair market value of the
property, assuming the property is not
contaminated, is determined by the
prospective landowner or grantee, or
other agent who is not under the
supervision or responsible charge of the
environmental professional, the final
rule allows for, but does not require, the
information that is collected and the
determination made by or on the behalf
of the prospective landowner to be
provided to the environmental
professional. If the information is
provided to the environmental
professional, he or she can then make
use of such information during the
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conduct of the all appropriate inquiries
and when rendering conclusions or
opinions regarding the environmental
conditions of the property. If the
information is not provided to the
environmental professional and the
environmental professional determines
that the lack of such information affects
his or her ability to identify conditions
indicative of releases or threatened
releases of hazardous substances on, at,
in, or to the property, then the
environmental professional should
identify the lack of information as a data
gap and comment on its significance in
the written report for the all appropriate
inquiries investigation.
The rule does not require that a real
estate appraisal be conducted to achieve
compliance with this criterion.
Although some commenters requested
that the final rule require that a formal
appraisal be conducted and we
acknowledge that there may be potential
value in conducting an appraisal, we
determined that a formal appraisal is
not necessary for the prospective
landowner or grantee to make a general
determination of whether the price paid
for a property reflects its fair market
value. In the case of many property
transactions, a formal appraisal may be
conducted for other purposes (e.g., to
establish the value of the property for
the purposes of establishing the
conditions of a mortgage or to provide
information of relevance where a
windfall lien may be filed). In cases
where the results of a formal property
appraisal are available, the appraisal
results may serve as an excellent source
of information on the fair market value
of the property.
In cases where the results of a formal
appraisal are not available, the
determination of fair market value may
be made by comparing the price paid for
a particular property to prices paid for
similar properties located in the same
vicinity as the subject property, or by
consulting a real estate expert familiar
with properties in the general locality
and who may be able to provide a
comparability analysis. The objective is
not to ascertain the exact value of the
property, but to determine whether or
not the purchase price paid for the
property generally is reflective of its fair
market value. Significant differences in
the purchase price and fair market value
of a property should be noted and the
reasons for any differences also should
be noted.
Although some commenters requested
that EPA be more explicit in the final
rule in requiring that the comparison of
the purchase price to the fair market
value of the property be conducted by
the prospective landowner or grantee
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66099
(and not the environmental
professional), we believe that the
decision of who conducts the
comparison may be best left up to the
judgment of the individual prospective
landowner (or grantee) and
environmental professional. The final
rule provides in § 312.22 that the
comparison of the purchase price to the
fair market value of the property, if it
were not contaminated, can fall outside
the inquiries conducted by the
environmental professional. The criteria
to consider the relationship of the
purchase price to the fair market value
of the property, if it was not
contaminated is not included as part of
the requirements governing the ‘‘results
of an inquiry by an environmental
professional’’ (§ 312.21). Therefore, the
requirement may be conducted by the
prospective landowner or grantee, his or
her attorney or agent, or the
environmental professional. Given that
a prospective landowner or grantee can
conduct the comparison of the purchase
price and the fair market value of the
property or hire another agent other
than the environmental professional to
conduct this task, we conclude that
commenter concerns regarding the
prospective landowner (or grantee)
having to divulge the price paid for a
property to the environmental
professional are unfounded.
W. What Are the Requirements for
Commonly Known or Reasonably
Ascertainable Information About the
Property?
Commonly known or reasonably
ascertainable information includes
information about a property that
generally is known to the public within
the community where the property is
located and can be easily sought and
found from individuals familiar with
the property or from easily attainable
public sources of information. As
mentioned above, the Brownfields
Amendments to CERCLA amended the
innocent landowner defense previously
added to CERCLA in 1986. In addition,
the Brownfields Amendments added to
CERCLA the bona fide prospective
purchaser and the contiguous property
owner liability protections. The 1986
amendments to CERCLA established,
that among other elements necessary for
a defendant to successfully assert the
innocent landowner defense, a
defendant must take into account
commonly known or reasonably
ascertainable information about the
property. Congress retained this
criterion as part of the all appropriate
inquiries requirements included in the
Brownfields Amendments. Today’s rule
does not change the nature or intent of
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this requirement as it has existed in the
statute since 1986.
Proposed Rule
The proposed rule required that all
appropriate inquiries include the
collection and consideration of
commonly known information about the
potential environmental conditions at a
property. The proposed rule required
both the prospective landowner or
grantee and the environmental
professional obtain and consider
commonly known or reasonably
ascertainable information during the
conduct of the all appropriate inquiries
investigation. The proposed rule also
provided a list of potential sources of
such information.
Public Comments
A few commenters expressed concern
that the requirement to consider
commonly known or reasonably
ascertainable information about a
property renders the all appropriate
inquiries requirements too vague and
open-ended. Commenters stated that the
requirement is broad and may result in
the need to interview a large number of
people and consult a wide variety of
sources of information. One commenter
expressed a preference that the federal
standards include only a checklist of
specific sources of information that
must be consulted. A few commenters
thought the list of potential sources of
commonly known information included
in the proposed rule was too broad.
Final Rule
The final rule retains the proposed
provisions requiring that prospective
landowners and environmental
professionals consider commonly
known or reasonably ascertainable
information about a property when
conducting all appropriate inquiries.
This information may be ascertained
from the owner or occupant of a
property, members of the local
community, including owners or
occupants of neighboring properties to
the subject property, local or state
government officials, local media
sources, and local libraries and
historical societies. In many cases, this
information may be incidental to other
information collected during the
inquiries, and separate or distinct efforts
to collect the information may not be
necessary. Information about a property,
including its ownership and uses, that
is commonly known or reasonably
ascertainable within the community or
neighborhood in which a property is
located may be valuable to identifying
conditions indicative of releases or
threatened releases at the subject
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property. Such information, if not
collected during the course of collecting
other information necessary to complete
the all appropriate inquiries
investigation, may be obtained by
interviewing community officials and
other residents of the locality. For
example, neighboring property owners
and local community members may
have information regarding
undocumented uses of a property
during periods when the property was
idle or abandoned. Local community
sources may be good (i.e., reasonably
ascertainable) sources of commonly
known information on uses of a
property and activities conducted at a
property, particularly in the case of
abandoned properties.
The collection and use of commonly
known information about a property
may be done in connection with the
collection of all other required
information for the purposes of
achieving the objectives and
performance factors contained in
§ 312.20. Persons undertaking the all
appropriate inquiries may collect
commonly known or reasonably
ascertainable information on the subject
property from a variety of sources,
including sources located in the
community in which the property is
located. The opinion provided by an
environmental professional regarding
the environmental conditions of a
property and included in the all
appropriate inquiries report should be
based upon a balance of all information
collected, including commonly known
or reasonably ascertainable information
about the property. The potential
sources of commonly known or
reasonably ascertainable information
provided in the proposed rule and
retained in the final rule are provided as
suggestions for where such information
may be found and the list provided is
not meant as an exhaustive list of
sources that must be consulted.
Commonly known information may be
collected from other sources and may be
most easily collected during the conduct
of other aspects of the all appropriate
inquiries investigation (e.g., interviews,
reviews of historical sources of
information, reviews of governmental
records). The requirement is not meant
to require exhaustive data collection
efforts, as some commenters asserted.
The intent of the requirement is to
establish that a prospective landowner
or grantee and an environmental
professional conducting all appropriate
inquiries on his or her behalf must make
efforts to collect and consider
information about a property that is
commonly known within the local
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community or that can be reasonably
ascertained.
There is some case law, related to the
innocent landowner defense, that
provides guidance on how a court may
rule with regard to the need to consider
commonly known or reasonably
ascertainable information about the
property. For example, in Wickland Oil
Terminals v. Asarco, Inc., 1988 WL
167247 (N.D. Cal. 1988), the court noted
that Wickland was aware of potential
water quality problems at the subject
property due to large piles of mining
slag stored at the property, even though
Wickland argued that previous owners
withheld such information, because the
information was available from other
sources consulted by Wickland prior to
purchasing the property, including the
Regional Water Quality Control Board
and a consulting firm hired by
Wickland. Such information was
commonly known by local sources and
therefore should have been considered
by Wickland during its conduct of all
appropriate inquiries.
In Hemingway Transport Inc. v. Kahn,
174 FR 148 (Bankr. D. Mass. 1994), the
court ruled against an innocent
landowner claim because it found ‘‘that
had [the defendants] exerted a modicum
of effort they may easily have
discovered information that at a
minimum would have compelled them
to inspect the property further * * * the
[defendants] could have taken a few
significant steps, literally, to minimize
their liability and discover information
about the property * * *’’ The court
noted that one action the defendants
should have taken to collect available
information about the property included
phone calls to city officials to inquire
about conditions at the property.
X. What Are the Requirements for ‘‘The
Degree of Obviousness of the Presence
or Likely Presence of Contamination at
the Property, and the Ability to Detect
the Contamination by Appropriate
Investigation?’’
Proposed Rule
The proposed rule required that the
inquiries conducted by a prospective
landowner (or grantee) and
environmental professional take into
account all the information collected
during the conduct of the all
appropriate inquiries in considering the
degree of obviousness of and ability to
detect the presence of a release or
threatened release of hazardous
substances at, in, on, or to a property.
In addition, the proposed rule required
the environmental professional to
provide an opinion regarding additional
appropriate investigation, if any may be
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necessary in his or her opinion to
determine the environmental conditions
of the property.
Public Comments
A few commenters asserted that the
proposed requirements regarding the
degree of obviousness of the presence or
likely presence of contamination at the
property, and the ability to detect the
contamination by appropriate inquiry
were too open-ended. Also, a few
commenters suggested that the final rule
should include requirements to conduct
sampling and analysis to meet the
‘‘ability to detect contamination by
appropriate investigation’’ portion of the
statutory criteria. However, commenters
overwhelmingly agreed that the
standards for all appropriate inquiries
should not require sampling and
analysis.
Final Rule
The final rule requires that persons
conducting all appropriate inquiries
consider all the information collected
during the conduct of the inquiries in
totality to ascertain the potential
presence of a release or threatened
release at the property. Persons
conducting all appropriate inquiries,
following the collection of all required
information, must assess whether or not
an obvious conclusion may be drawn
that there are conditions indicative of a
release or threatened release of
hazardous substances (or other
pollutants, contaminants, petroleum or
petroleum products, and controlled
substances) on, at, in, or to the property.
In addition, the rule requires parties to
consider whether or not the totality of
information collected prior to acquiring
the property indicates that the parties
should be able to detect a release or
threatened release on, at, in, or to the
property. The final rule also retains the
proposed requirement that the
environmental professional include as
part of the results of his or her inquiry
an opinion regarding additional
appropriate investigation, if any may be
necessary.
We interpret the statutory criterion to
require consideration of information
already obtained during the conduct of
all appropriate inquiries investigation
and not as a requirement to collect
additional information. We do not agree
with commenters who asserted that the
criterion is open-ended. In fact, we see
this criterion as providing direction on
how all of the information collected
while carrying out the other criteria and
regulatory requirements must be viewed
comprehensively. After collecting and
considering all the information required
to comply with the rule’s objectives and
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performance standards, all the
information should be considered in
total to determine whether or not there
are indications of releases or threatened
releases of hazardous substances on, at,
in, or to the property. In addition, the
environmental professional should
provide an opinion regarding whether
or not additional investigation is
necessary to detect potential
contamination at the site, if in his or her
opinion there are conditions indicative
of releases or threatened releases of
hazardous substances.
The previous innocent landowner
defense (added to CERCLA in 1986)
required a court to consider the degree
of obviousness of the presence or likely
presence of contamination at a property,
and the ability of the defendant (i.e., the
landowner) to detect the contamination
by appropriate investigation. Nothing in
today’s rule changes the nature or intent
of this requirement as it has existed in
the statute since 1986.
Case law relevant to this criterion
indicates that defendants may not be
able to claim an innocent landowner
defense if a preponderance of evidence
available to a prospective landowner
prior to acquiring the property indicates
that the defendant should have
concluded that there is a high likelihood
of contamination at the site. In some
cases (e.g., Hemingway Transport Inc. v.
Kahn, 174 F.R. 148 (Bankr. D. Mass.
1994), and Foster v. United States, 922
F. Supp. 642 (D.D.C. 1996), courts have
ruled that if a defendant had done a bit
more visual inspection or further
investigation, based upon information
available to the defendant prior to
acquiring the property, it would have
been obvious that the property was
contaminated. In Foster v. United
States, the court determined that the
innocent landowner defense was not
available based in part on the fact that
the partnership presumed the site was
free of contamination based upon
cursory visual inspections despite
evidence in the record that, at the time
of the sale, the soil was visibly stained
by PCB-contaminated oil. In addition,
although the property was located in a
run-down industrial area, the defendant
did no investigation into the
environmental conditions at the site
prior to acquiring the property.
EPA also notes that in U.S. v.
Domenic Lombardi Realty, Inc., 290 F.
Supp. 2d 198, 211 (D.R.I. 2003), the
court held that the defendant did not
qualify for the innocent landowner
defense. The defendant could not show
he had ‘‘no reason to know’’ of
contamination at the property or that he
had performed all appropriate inquiries
in accordance with ‘‘good commercial
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or customary practices.’’ The court also
found that the defendant had not
performed even a minimal
environmental assessment of the site
despite having learned that the property
had been used as an automobile
scrapyard. The court noted the
distinction between Phase I and Phase
II environmental assessments and
credited the testimony of the United
States’ expert who concluded that,
under the circumstances of this case, the
defendant should have conducted a
Phase II assessment. Id. at 203–04.
With regard to the conduct of
sampling and analysis, today’s final rule
does not require sampling and analysis
as part of the all appropriate inquiries
investigation. However, sampling and
analysis may be valuable in determining
the possible presence and extent of
potential contamination at a property. In
addition, the fact that the all appropriate
inquiry standards do not require
sampling and analysis does not prevent
a court from concluding that, under the
circumstances of a particular case,
sampling and analysis should have been
conducted to meet ‘‘the degree of
obviousness of the presence or likely
presence of contamination at the
property, and the ability to detect the
contamination by appropriate
investigation’’ criterion and obtain
protection from CERCLA liability.
Prospective landowners should keep in
mind that the conduct of all appropriate
inquiries prior to acquiring a property is
only one requirement that he or she
must comply with to assert protection
from CERCLA liability. The statute
requires that persons, after acquiring a
property, comply with continuing
obligations to take reasonable steps to
stop on-going releases at the property,
prevent any threatened future releases,
and prevent or limit any human,
environmental, or natural resource
exposure to any previously released
hazardous substances (these criteria are
summarized in detail in section II.D. of
this preamble). In certain instances,
depending upon site-specific
circumstances and the totality of the
information collected during the all
appropriate inquiries prior to the
property acquisition, it may be
necessary to conduct sampling and
analysis, either pre-or post-acquisition,
to fully understand the conditions at a
property, and fully comply with the
statutory requirements for the CERCLA
liability protections. In addition,
sampling and analysis may help explain
existing data gaps. Prospective
landowners should be mindful of all the
statutory requirements for obtaining the
CERCLA liability protections when
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considering whether or not to conduct
sampling and analysis prior to or after
acquiring a property. Today’s final
regulation does not require that
sampling and analysis be conducted as
part of the all appropriate inquiries
investigation.
V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735), the Agency must determine
whether this regulatory action is
‘‘significant’’ and therefore subject to
formal review by the Office of
Management and Budget (OMB) and to
the requirements of the Executive Order.
The Executive Order defines
‘‘significant regulatory action’’ as one
that is likely to result in a rule that may:
(1) Have an annual effect on the
economy of $100 million or more or
adversely affect in a material way the
economy, a sector of the economy,
productivity, competition, jobs, the
environment, public health or safety, or
state, local, or tribal governments or
communities; (2) create a serious
inconsistency or otherwise interfere
with an action taken or planned by
another agency; (3) materially alter the
budgetary impact of entitlements,
grants, user fees, or loan programs or the
rights and obligations of recipients
thereof; or (4) raise novel legal or policy
issues arising out of legal mandates, the
President’s priorities, or the principles
set forth in the Executive Order.
Pursuant to the terms of Executive
Order 12866, it has been determined
that today’s final rule is a ‘‘significant
regulatory action’’ because this rule
contains novel policy issues, although it
is not economically significant. As such,
this action was submitted to OMB for
review. Changes made in response to
OMB suggestions or recommendations
are documented in the docket for
today’s rule.
To estimate the economic effects of
today’s final rule, we conducted an
evaluation of the potential effects of this
rule on the universe of prospective
landowners who may chose to comply
with the provisions of today’s final rule
to obtain protection from CERCLA
liability for potential releases and
threatened releases of hazardous
substances that may exist at properties
they intend to purchase. The results of
this analysis are included in the
document titled ‘‘Economic Impact
Analysis for the Final All Appropriate
Inquiries Regulation,’’ which is
included in the docket for today’s final
rule. Based upon the results of the
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Economic Impact Analysis (EIA), EPA
has determined that this final rule will
have an annual effect on the economy
of less than $100 million. The
annualized benefits associated with the
final rule have not been monetized but
are identified and summarized in the
EIA for the all appropriate inquiries
rule.2
1. Methodology
The value of any regulatory action is
traditionally measured by the net
change in social welfare that it
generates. The EIA conducted in
support of today’s rule examines both
costs and qualitative benefits in an effort
to assess the overall net change in social
welfare. The primary focus of the EIA
document is on compliance costs and
economic impacts. Below, EPA
summarizes the analytical methodology
and findings for the all appropriate
inquiries rule. The information
presented is derived from the EIA.
The all appropriate inquiries
regulation potentially will apply to most
commercial property transactions. The
requirements will be applicable to any
public or private party, who may
potentially claim protection from
CERCLA liability as an innocent
landowner, a bona fide prospective
purchaser, or a contiguous property
owner. However, the conduct of all
appropriate inquiries, also known as
environmental due diligence or Phase I
Environmental Site Assessment, is not
new to the commercial property market.
Prior to the Brownfields Amendments to
CERCLA, commercial property
transactions often included an
assessment of the environmental
conditions at properties prior to the
closing of any real estate transaction
whereby ownership was transferred for
the purposes of confirming the
conditions at the property or to establish
an innocent landowner defense should
environmental contamination be
discovered after the property was
acquired. The process most prevalently
used for conducting all appropriate
inquiries, or environmental site
assessments, is the process developed
by ASTM International (formerly known
as the American Society for Testing and
Materials) and entitled ‘‘E1527,
Standard Practice for Environmental
Site Assessments: Phase I
Environmental Site Assessment
Process.’’ In addition, some properties,
2 The document titled ‘‘The Economic Impact
Analysis for the Final All Appropriate Inquiries
Regulation’’ includes (1) the EIA conducted for the
proposed rulemaking and (2) the Addendum to the
EIA. The cost estimates presented in the Addendum
are the estimated costs of the final all appropriate
inquiries regulation.
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particularly in cases where the subject
property is assumed not to be
contaminated or was never used for
industrial or commercial purposes, were
assessed using a less rigorous process
developed by ASTM International,
sometimes referred to as a ‘‘transaction
screen’’ and entitled ‘‘E1528, Standard
Practice for Environmental Site
Assessments: Transaction Screen
Process.’’
Our first step in assessing the
economic impacts of the rule was to
establish a baseline to represent the
relevant aspects to the commercial real
estate market in the absence of any
changes in regulations. Because under
existing conditions almost all
commercial property transactions are
accompanied by either an
environmental site assessment (ESA)
conducted in accordance with ASTM
E1527–2000 or a transaction screen as
specified in ASTM E1528, it was
assumed these practices would continue
even in the absence of the all
appropriate inquiries regulation. The
numbers of each type of assessment
were estimated on the basis of industry
data for recent years, with recent growth
rates in transactions assumed to
continue for the 10-year period covered
by the EIA. An adjustment in the
relative numbers of ESAs and
transaction screens was made to account
for the fact that, under the rule, an ESA
will provide more certain protection
from liability. This adjustment was
made by comparing shifts between the
two procedures that occurred when the
Brownfields Amendments established
the ASTM E1527–2000 standard as the
interim standard for all appropriate
inquiries, and thus as one requirement
for qualifying as an innocent landowner,
bona fide prospective purchaser, or
contiguous property owner.
We then considered the requirements
included in the final rule and compared
them to the requirements for
environmental site assessments
conducted under the ASTM E1527–
2000 and ASTM E1528 standards.
When compared to the ASTM E1527–
2000 standard (i.e., the baseline
standard), today’s final rule is expected
to result in a reduced burden for the
conduct of interviews in those cases
where the subject property is
abandoned; increased burden in those
cases where past owners or occupants
need to be interviewed; increased
burden associated with documenting
recorded environmental cleanup liens;
increased burden for documenting the
reasons for the price and fair market
value of a property in those cases where
the purchase price paid for the subject
property is significantly below the fair
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market value of the property; and
increased burden for recording
information about the degree of
obviousness of contamination at a
property.
To estimate the changes in costs
resulting from the rule, we developed a
costing model. This model estimates the
total costs of conducting site
assessments as the product of costs per
assessment, numbers of assessments per
year, and the number of years in the
analysis. The costs per assessment, in
turn, are calculated by dividing each
assessment into individual labor
activities, estimating the labor time
associated with each, and assigning a
per-hour labor cost to each activity on
the basis of the labor category most
appropriate to that activity. Labor times
and categories are assumed to depend
on the size and type of property being
assessed, with the nationwide
distribution of properties based on data
from industry on environmental sites
assessments and brownfield sites.3 The
estimates and assignments of categories
are made based on the experience of
professionals who have been involved
in large numbers of site assessments,
and who are therefore skilled in cost
estimation for the relevant activities.
Other costs, such as reproduction and
the purchase of data, are added to the
labor costs to form the estimates of total
costs per assessment. These total costs,
stratified by size and type of property,
are then multiplied by estimated
numbers of assessments of each size and
type to generate our estimates of total
annual costs. The model was tested by
comparing its results to industry-wide
estimates of average price of conducting
assessments under baseline conditions,
and generally found to agree. The
difference between the estimated cost to
comply with the final rule and the
estimated cost in the baseline
constitutes our estimate of the
incremental regulatory costs.
The EIA provides a qualitative
assessment of the benefits of the all
appropriate inquiries rule. The benefits
discussed are those that may be
attributed to an increased level of
certainty with regard to CERCLA
liability provided to prospective
purchasers of potentially contaminated
properties, including brownfields, who
comply with the provisions of the rule
and the other statutory provisions
associated with the liability protections.
The basic premise for associating certain
benefits to the rule is the expectation
3 The distribution of abandoned properties and
properties with known owners, modeled as a range,
is based on an estimate of vacant lands in urban
areas and an estimate of abandoned Superfund
sites.
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that the level of certainty provided by
the liability protections may result in
increased brownfields property
transactions. However, it is difficult to
predict how many additional
transactions may occur that involve
brownfields properties in direct
response to the increased certainty of
the liability protections. It also is
difficult to obtain data on changes in
behaviors and practices of prospective
landowners in response to the liability
protections. Therefore, EPA made no
attempt to quantify potential benefits or
compare the benefits to estimated
incremental costs.
The Agency believes that increasing
property transactions involving
brownfields and other contaminated
and potentially contaminated properties
and improving information about
environmental conditions at these
properties may provide additional
indirect benefits such as increased
numbers of cleanups, reduced use of
greenfields, potential increases in
property values, and potential increases
in quality of life measures (e.g.,
decreases in urban blight, reductions in
traffic, congestion, and reduced
pollution due to mobile source
emissions). However, as stated above,
the benefits of the rule are considered
only qualitatively, due to the difficulty
of predicting how many additional
brownfields and contaminated property
transactions may occur in response to
the increased certainty of liability
protections provided by the rule, as well
as the difficulty in getting data on
changes in behaviors and practices in
response to the availability of the
liability protections. EPA is confident
that the new liability protections
afforded to prospective landowners, if
they comply with the all appropriate
inquiries provisions, will result in
increased benefits. EPA is not able to
quantify, with any significant level of
confidence, the exact proportion of the
benefits attributed only to the
availability of the liability protections
and the all appropriate inquiries
regulations. For these reasons, the costs
and benefits could not be directly
compared.
2. Summary of Regulatory Costs in
Proposed Rule
For a given property, the costs of
compliance with the all appropriate
inquiries rule relative to the baseline
depend on whether that property would
have been assessed, in absence of the all
appropriate inquiries regulation, with
an ASTM E1527–2000 assessment
process or with the simpler ASTM
E1528 transaction screen. EPA
estimated the average incremental cost
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of the proposed rule relative to
conducting an ASTM E1527–2000 to be
between $41 and $47. For the small
percentage of cases for which a
transaction screen would have been
preferred to the ASTM E1527–2000 in
the baseline, but which would, as a
result of the proposed rule, require an
assessment in compliance with the all
appropriate inquiries rule, the average
incremental cost was estimated to be
between $1,448 and $1,454. We
estimated that approximately 97 percent
of property transactions will bear only
the incremental cost of the rule relative
to the ASTM E1527–2000 process.
Therefore, the weighted average
incremental cost of the proposed rule,
per transaction, was estimated to be
fairly low, between $84 and $89.
3. Public Comments on EIA for
Proposed Rule
EPA received a number of public
comments on the EIA conducted to
assess the potential costs and impacts of
the proposed rule. We summarized the
public comments received related to the
cost and economic impacts in the
document titled ‘‘Addendum to
Economic Impact Analysis for the Final
All Appropriate Inquiries Regulation’’
(Addendum to the EIA). This document
is included in the docket for today’s
final rule. The Addendum to the EIA
also summarizes EPA’s responses to the
comments received that addressed the
estimated costs and economic impacts.
Many commenters generally agreed
with EPA’s conclusion that the average
incremental cost increase per
transaction associated with the
requirements of the proposed rule
would be minimal. Some commenters
mentioned that the EIA conducted for
the proposed rule underestimated the
incremental costs associated with the
proposed rule. However, only a few
commenters provided an explanation as
to why they thought our cost estimates
were low or provided information
regarding which particular activities
would result in an incremental increase
in the activities and costs associated
with conducting an environmental site
assessment, if conducted in compliance
with the requirements of the proposed
rule. Most commenters did not provide
specific reasons for their claims of cost
increases over the ASTM E1527–2000
standard. A few commenters suggested
that the EIA for the proposed rule
underestimated the level of effort
necessary for locating and interviewing
past owners or occupants, with one
commenter providing an estimated level
of effort of one to three hours for this
task.
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4. Estimate of Costs Associated With the
Final Rule
EPA made one revision to the analysis
of cost impacts associated with the
requirements of the proposed and final
rule in response to specific issues raised
by commenters. EPA agrees with the
commenters who asserted that locating
past owners or occupants of a property
may be more time consuming than
locating the current owners or
occupants, as was assumed in the
analysis of costs conducted for the
proposed rule. Locating past owners or
occupants could require as little as one
5-minute phone call (e.g., if the current
owner has the contact information for
the past owner) or it could require
multiple phone calls that could take in
excess of one hour. For the purpose of
estimating the cost under the final rule,
EPA estimates the incremental burden
for locating past owners or occupants to
be, on average, 0.5 hours per interview
regardless of the property type or size.
EPA did not account for this
incremental burden in our analysis of
the costs associated with the proposed
rule. EPA also recognizes that in some
cases the environmental professional
will need to complete the full interview
with the current owner before
determining that it is necessary to
interview a past owner. In other words,
the environmental professional may
need to complete the interview with the
current owner, and then perform a more
focused interview of a past owner to fill
data gaps. EPA estimates that the
incremental burden for interviewing
past owners or occupants will be 0.5
hours for undeveloped and residential
properties, one hour for commercial and
industrial properties (of all sizes except
large industrial), and 1.5 hours for large
industrial properties. Therefore, EPA
estimates that the total incremental level
of effort for locating and interviewing
past property owners or occupants will
range from one hour to two hours
depending on the property type or size.
The additional incremental hour
burden, however, will not be incurred
in the case of every site assessment. EPA
expects that the interview with past
owners or occupants will be conducted
only for properties with a higher than
average owner or occupant turnover
rate. To derive the number of potentially
affected properties, we assume that the
environmental professional will
interview only the current property
owner if the owner was in the
possession of the subject property for
more than two years. We assume that
after two years of owning a property, the
current property owner should have a
reasonably good knowledge of its
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condition. EPA estimates that 19
percent of Phase I ESAs conducted in a
given year are conducted on properties
that were sold at least once in the
previous two years (for a detailed
explanation on the derivation of this
estimate, see the Addendum to the EIA).
Using the assumption that 15 percent of
all properties are abandoned properties
(see Section 5.6.5.2 of EIA) which
would not be affected by the
requirement to interview past owners or
occupants, we revised our original cost
estimate to account for non-abandoned
properties that were sold over the past
two years. Therefore, for the purpose of
our revised cost analysis, we estimate
that 16 percent of properties will require
an additional interview with past
owners or occupants.
Except for the increase in the level of
effort for the interview task for nonabandoned properties, all other
parameters used in modeling our cost
estimates are the same as presented in
the EIA conducted for the proposed
rule. To derive the incremental average
cost per transaction and the total annual
cost of the final rule, we employed the
methodology explained in detailed in
Chapters 7 and 8 of the EIA conducted
for the proposed rule. Based on our
analysis, the cost of a Phase I ESA under
the final regulation will increase, on
average, between $52 and $58. The
estimated average cost for a Phase I ESA
thus will range between $2,185 and
$2,190.4
Using our revised incremental cost
estimate for conducting interviews of
past owners or occupants, we revised
our estimated total annual cost of the
final rule and our incremental total
annual cost estimate. Our revised total
annual cost estimate for all activities
included in the all appropriate inquiries
investigations conducted under the final
rule is between $693.5 and $695.3
million (calculated using a discount rate
of three percent). Our revised estimate
of the incremental total annual cost of
the final rule is between $29.7 million
and $31.4 million. A more detailed
explanation of our revised cost
estimates, including an additional
sensitivity analysis performed in
response to the public comments, is
included in the document titled
‘‘Addendum to the Economic Impact
Analysis for the Final All Appropriate
Inquiries Regulation.’’ This document is
4 We assumed that the environmental
professionals will need to complete the full
interview with the current owner before conducting
an interview with the past owners or occupants. To
the extent that this may not always be the case, the
average incremental cost (and by extension, the
average cost for an AAI Phase I ESA) is
overestimated.
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in the public docket for today’s final
rule.
B. Paperwork Reduction Act
The information collection
requirements contained in this final rule
were submitted for approval to the
Office of Management and Budget under
the Paperwork Reduction Act, 44 U.S.C.
3501 et seq. The information collection
requirements are not enforceable until
OMB approves them. The Information
Collection Request (ICR) document
prepared by EPA has been assigned EPA
ICR Number 2144.02.
Under the PRA, EPA is required to
estimate the notification, reporting and
recordkeeping costs and burdens
associated with the requirements
specified in today’s rule. Today’s rule
will require persons wanting to assert
one of the liability protections under
CERCLA to conduct some activities that
go beyond current customary and usual
business practices (i.e., beyond ASTM
E1527–2000) and therefore will impose
an information collection burden under
the provisions of the Paperwork
Reduction Act. The information
collection activities are associated with
the activities mandated in section 101
(35)(B) of CERCLA for those persons
wanting to claim protection from
CERCLA liability. None of the
information collection burdens
associated with the provisions of today’s
rule include requirements to submit the
collected information to EPA or any
other government agency. Information
collected by persons affected by today’s
rule may be useful to such persons if
their potential liability under CERCLA
for the release or threatened release of
a hazardous substance is challenged in
a court.
The activities associated with today’s
rule that go beyond current customary
and usual business practices include
interviews with neighboring property
owners and/or occupants in those cases
where the subject property is
abandoned, documentation of all
environmental cleanup liens in the
Phase I Environmental Site Assessment
report, discussion of the relationship of
purchase price to value of the property
in the report, and consideration and
discussion of whether additional
environmental investigation is
warranted. Paperwork burdens are
estimated to be 546,179 hours annually,
with a total cost of $29,583,206
annually. The estimated average burden
hours per response is estimated to be
approximately one hour (or 25 hours per
response, assuming a transition from a
transaction screen). The estimated
average cost burden per response is
estimated to be either $67 or $1,479,
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depending on whether, under baseline
conditions, an ASTM E1527–2000
process or a transaction screen (ASTM
E1528) would have been used.
Under the Paperwork Reduction Act,
‘‘burden’’ means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, or disclose
or provide information to or for a
Federal agency. This includes the time
needed to review instructions; develop,
acquire, install, and utilize technology
and systems for the purposes of
collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
An agency may not conduct or
sponsor, and a person is not required to
respond to a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR part 9. This
ICR is approved by OMB, and the
Agency will publish a technical
amendment to 40 CFR part 9 in the
Federal Register to display the OMB
control number for the approved
information collection requirements
contained in this final rule.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act (RFA),
as amended by the Small Business
Regulatory Enforcement Fairness Act of
1996 (SBREFA), 5 U.S.C. 601 et. seq.,
generally requires an agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedure Act or any
other statute, unless the agency certifies
that the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For the purposes of assessing the
impacts of today’s rule on small entities,
small entity is defined as: (1) A small
business that is defined by the Small
Business Administration by category of
business using the North American
Industrial Classification System
(NAICS) and codified 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
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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.
Since all non-residential property
transactions could be affected by today’s
rule, if it is promulgated, large numbers
of small entities could be affected to
some degree. However, we estimate that
the effects, on the whole, will not be
significant for small entities. We
estimate that, for the majority of small
entities, the average incremental cost of
today’s rule relative to conducting an
ASTM E1527–2000 Phase I
Environmental Site Assessment will be
between $52 and $58. When we
annualize the incremental cost of $58
per property transaction over ten years
at a seven percent discount rate, we
estimate that the average annual cost
increase per establishment per property
transaction will be $8. Thus, the cost
impact to small entities is estimated to
not be significant. A more detailed
summary of our analysis of the potential
impacts of today’s rule to small entities
is included in ‘‘Economic Impacts
Analysis of the Final All Appropriate
Inquiries Regulation.’’ This document is
included in the docket for today’s rule.
After considering the economic
impacts of today’s final rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
We estimate that, on average, 266,000
small entities may purchase commercial
real estate in any given year and
therefore could potentially be impacted
by today’s final rule. Though large
numbers of small entities could be
affected to some degree, we estimated
that the effects, on the whole, would not
be significant for small entities. We
estimate that, for the majority of small
entities, the average incremental cost of
today’s rule relative to conducting an
ASTM E1527–2000 will be between $52
and $58. For the small percentage of
cases for which a transaction screen
would have been preferred to the ASTM
E1527–2000 in the baseline, but which
now will require an assessment in
compliance with the rule, the average
incremental cost of conducting an
environmental site assessment will be
between $1,459 and $1,465. When we
annualize the incremental cost per
property transaction over ten years at a
seven percent discount rate, we estimate
that for the majority of small entities the
average annual cost increase per
establishment per property transaction
will be approximately $8. For the small
percentage of entities transitioning from
transaction screens to the all
appropriate inquiries requirements of
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the final rule, the average annual cost
increase per establishment per property
transaction will be $209.5
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
federal agencies to assess the effects of
their regulatory actions on State, local,
and tribal governments and the private
sector. Under section 202 of the UMRA,
EPA must prepare a written statement,
including a cost-benefit analysis, for
proposed and final rules with ‘‘Federal
mandates’’ that may result in
expenditures to State, local, and tribal
governments, in the aggregate, or to the
private sector, of $100 million or more
in any one year. Before promulgating an
EPA rule for which a written statement
is needed, section 205 of the UMRA
generally requires EPA to identify and
consider a reasonable number of
regulatory alternatives and adopt the
least costly, most cost-effective, or least
burdensome alternative that achieves
the objectives of the rule. The
provisions of section 205 do not apply
when they are inconsistent with
applicable law. Moreover, section 205
allows EPA to adopt an alternative other
than the least costly, most cost-effective
or least burdensome alternative if the
Administrator publishes with the final
rule an explanation of why that
alternative was not adopted.
Before EPA establishes any regulatory
requirements that may significantly or
uniquely affect small governments,
including tribal governments, it must
have developed under section 203 of the
UMRA, a small government agency
plan. The plan must provide for
notifying potentially affected small
governments, enabling officials to have
meaningful and timely input in the
development of regulatory proposals
with significant federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
Today’s rule contains no federal
mandates (under the regulatory
provisions of Title II of the UMRA) for
5 For a very small percentage of entities
transitioning from transaction screens to the all
appropriate inquiries requirements, the maximum
increase per establishment per property transaction
is estimated to be approximately $2,845. When we
annualize this incremental cost per property
transaction over ten years at a seven percent
discount rate, we estimate that the maximum
annual cost increase per establishment per property
transaction will be $405. We estimate that
approximately one fifth of one percent of the
properties transitioning from a transaction screen to
a Phase I ESA will have an impact of this
magnitude each year.
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state, local, or tribal governments or the
private sector. The rule imposes no
enforceable duty on any state, local, or
tribal governments. EPA also
determined that today’s rule contains no
regulatory requirements that might
significantly or uniquely affect small
governments. In addition, as discussed
above, the private sector is not expected
to incur costs of $100 million or more
as a result of today’s rule. Therefore,
today’s rule is not subject to the
requirements of Sections 202 and 205 of
UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the states, on the relationship
between the national government and
the states, or on the distribution of
power and responsibilities among the
various levels of government.’’
Today’s rule does not have federalism
implications. It will not have substantial
direct effects on the states, on the
relationship between the national
government and the states, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. No state and
local government bodies will incur
compliance costs as a result of today’s
rulemaking. Therefore, Executive Order
13132 does not apply to this rule.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ Today’s rule does not
have tribal implications, as specified in
Executive Order 13175. Today’s rule
does not significantly or uniquely affect
the communities of Indian tribal
governments, nor would it impose
direct compliance costs on them. Thus,
Executive Order 13175 does not apply
to this rule.
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G. Executive Order 13045: Protection of
Children From Environmental Risks and
Safety Risks
Executive Order 13045, entitled
‘‘Protection of Children from
Environmental Health Risks and Safety
Risks (62 FR 19885, April 23, 1997)
applies to any rule that: (1) Is
determined to be ‘‘economically
significant’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
the Agency must evaluate the
environmental health or safety effects of
the planned rule on children; and
explain why the planned regulation is
preferable to other potentially effective
and reasonably feasible alternatives
considered by the Agency.
Today’s rule is not subject to the
Executive Order because it is not
economically significant as defined in
Executive Order 12866.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution or Use
Today’s final rule is not a ‘‘significant
energy action’’ as defined in Executive
Order 13211, ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355, May 22, 2001) because it is
not likely to have a significantly adverse
effect on the supply, distribution, or use
of energy. Further, we have concluded
that this rule is not likely to have any
adverse energy effects.
I. National Technology Transfer and
Advancement Act
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (‘‘NTTAA’’), Public Law
104–113, section 12(d) (15 U.S.C. 272
note), directs EPA to use voluntary
consensus standards in its regulatory
activities, unless to do so would be
inconsistent with applicable law or
otherwise impractical. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by voluntary consensus
standards bodies. The NTTAA directs
EPA to provide Congress, through OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards. Today’s
rule involves technical standards.
Therefore, the requirements of section
12(d) of the National Technology
Transfer and Advancement Act of 1995
(15 U.S.C. 272) apply.
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Today’s final rule is based upon a
proposed rule that was developed with
the assistance of a regulatory negotiation
committee comprised of various affected
stakeholder groups and modified
slightly, based upon public comments
received in response to the proposed
rule. When developing the proposed
rule, EPA considered using the existing
standard developed by ASTM
International as the federal standard for
all appropriate inquiries. This standard
is known as the ASTM E1527–2000
standard (‘‘Standard Practice for
Environmental Site Assessment: Phase I
Environmental Site Assessment
Process’’). However, when we proposed
the federal standards for all appropriate
inquiries, EPA determined that the
ASTM E1527–2000 standard is
inconsistent with applicable law.
In CERCLA section 101(35)(B),
Congress included ten specific criteria
to be used in promulgating the all
appropriate inquiries rule. The 2000
version of the ASTM Phase I
Environmental Site Assessment Process
does not address all of the required
criteria. For example, the ASTM
International standard does not provide
for interviews of past owners, operators,
and occupants of a facility. The statute,
however, states that the federally
promulgated standard ‘‘shall include
* * * interviews with past and present
owners, operators, and occupants of the
facility for the purpose of gathering
information regarding the potential for
contamination at the facility.’’ CERCLA
section 101(35)(B)(iii)(II). In addition, as
outlined in the preamble to the
proposed rule (69 FR 52541) the ASTM
E1527–2000 standard also does not meet
other statutory requirements. As a
result, use of the ASTM E1527–2000
standard would be inconsistent with
applicable law.
In today’s final rule, EPA is
referencing the updated standards and
practices developed by ASTM
International and known as Standard
E1527–05 (entitled ‘‘Standard Practice
for Environmental Site Assessments:
Phase I Environmental Site Assessment
Process’’). The Agency has determined
that this voluntary consensus standard
is consistent with today’s final 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 E1527–05 standard to comply
with today’s final rule.
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J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898, ‘‘Federal
Actions to Address Environmental
Justice in Minority Populations and
Low-Income Populations’’ (February 11,
1994), is designed to address the
environmental and human health
conditions of minority and low-income
populations. EPA is committed to
addressing environmental justice
concerns and has assumed a leadership
role in environmental justice initiatives
to enhance environmental quality for all
citizens of the United States. The
Agency’s goals are to ensure that no
segment of the population, regardless of
race, color, national origin, income, or
net worth bears disproportionately high
and adverse human health and
environmental impacts as a result of
EPA’s policies, programs, and activities.
Our goal is to ensure that all citizens
live in clean and sustainable
communities. In response to Executive
Order 12898, and to concerns voiced by
many groups outside the Agency, EPA’s
Office of Solid Waste and Emergency
Response (OSWER) formed an
Environmental Justice Task Force to
analyze the array of environmental
justice issues specific to waste programs
and to develop an overall strategy to
identify and address these issues
(OSWER Directive No. 9200.3–17).
EPA’s brownfields program has a
particular emphasis on addressing
concerns specific to environmental
justices communities. Many of the
communities and neighborhoods that
are most significantly impacted by
brownfields are environmental justice
communities. EPA’s brownfields
program targets such communities for
assessment, cleanup, and revitalization.
The brownfields program has a long
history of working with environmental
justice communities and advocates
through our technical assistance and
grant programs. In addition to the
monies awarded to such communities in
the form of assessment and cleanup
grants, the brownfields program also
works with environmental justice
communities through our job training
grants program. The job training grants
provide money to government entities to
facilitate the training of persons living
in or near brownfields communities to
attain skills for conducting site
assessments and cleanups.
Given that environmental justice
communities are significantly impacted
by brownfields, and the federal
standards for all appropriate inquiries
may play a primary role in encouraging
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the assessment and cleanup of
brownfields sites, EPA made it a priority
to obtain input from representatives of
environmental justice interest groups
during the development of today’s
rulemaking. The Negotiated Rulemaking
Committee tasked with developing the
all appropriate inquiries proposed rule
included three representatives from
environmental justice advocacy groups.
Each representative played a significant
role in the negotiations and in the
development of the proposed rule.
Today’s final rule includes no
significant changes to the proposed rule
and in particular, includes no changes
that will significantly or
disproportionately impact
environmental justice communities.
K. Congressional Review Act
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A major rule
cannot take effect until 60 days after it
is published in the Federal Register.
This action is not a ‘‘major rule’’ as
defined by 5 U.S.C. 804(2). This rule
will be effective November 1, 2006.
List of Subjects in 40 CFR Part 312
Environmental protection,
Administrative practice and procedure,
Hazardous substances,
Intergovernmental relations, Reporting
and recordkeeping requirements.
Dated: October 21, 2005.
Stephen L. Johnson,
Administrator.
For reasons set out in the preamble,
title 40, chapter I of the Code of Federal
Regulations is amended by revising part
312 as follows:
I
PART 312—INNOCENT
LANDOWNERS, STANDARDS FOR
CONDUCTING ALL APPROPRIATE
INQUIRIES
Subpart A—Introduction
Sec.
312.1 Purpose, applicability, scope, and
disclosure obligations.
Subpart B—Definitions and References
312.10 Definitions.
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References.
Subpart C—Standards and Practices
312.20 All appropriate inquiries.
312.21 Results of inquiry by an
environmental professional.
312.22 Additional inquiries.
312.23 Interviews with past and present
owners, operators, and occupants.
312.24 Reviews of historical sources of
information.
312.25 Searches for recorded environmental
cleanup liens.
312.26 Reviews of federal, state, tribal and
local government records.
312.27 Visual inspections of the facility and
of adjoining properties.
312.28 Specialized knowledge or
experience on the part of the defendant.
312.29 The relationship of the purchase
price to the value of the property, if the
property was not contaminated.
312.30 Commonly known or reasonably
ascertainable information about the
property.
312.31 The degree of obviousness of the
presence or likely presence of
contamination at the property, and the
ability to detect the contamination by
appropriate investigation.
Authority: Section 101(35)(B) of CERCLA,
as amended, 42 U.S.C. 9601(35)(B).
PART 312—INNOCENT
LANDOWNERS, STANDARDS FOR
CONDUCTING ALL APPROPRIATE
INQUIRIES
Subpart A—Introduction
§ 312.1 Purpose, applicability, scope and
disclosure obligations.
(a) Purpose. The purpose of this
section is to provide standards and
practices for ‘‘all appropriate inquiries’’
for the purposes of CERCLA sections
101(35)(B)(i)(I) and 101(35)(B)(ii) and
(iii).
(b) Applicability. The requirements of
this part are applicable to:
(1) Persons seeking to establish:
(i) The innocent landowner defense
pursuant to CERCLA sections 101(35)
and 107(b)(3);
(ii) The bona fide prospective
purchaser liability protection pursuant
to CERCLA sections 101(40) and 107(r);
(iii) The contiguous property owner
liability protection pursuant to CERCLA
section 107(q); and
(2) persons conducting site
characterization and assessments with
the use of a grant awarded under
CERCLA section 104(k)(2)(B).
(c) Scope. (1) Persons seeking to
establish one of the liability protections
under paragraph (b)(1) of this section
must conduct investigations as required
in this part, including an inquiry by an
environmental professional, as required
under § 312.21, and the additional
inquiries defined in § 312.22, to identify
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conditions indicative of releases or
threatened releases, as defined in
CERCLA section 101(22), of hazardous
substances, as defined in CERCLA
section 101(14).
(2) Persons identified in paragraph
(b)(2) of this section must conduct
investigations required in this part,
including an inquiry by an
environmental professional, as required
under § 312.21, and the additional
inquiries defined in § 312.22, to identify
conditions indicative of releases and
threatened releases of hazardous
substances, as defined in CERCLA
section 101(22), and as applicable per
the terms and conditions of the grant or
cooperative agreement, releases and
threatened releases of:
(i) Pollutants and contaminants, as
defined in CERCLA section 101(33);
(ii) Petroleum or petroleum products
excluded from the definition of
‘‘hazardous substance’’ as defined in
CERCLA section 101(14); and
(iii) Controlled substances, as defined
in 21 U.S.C. 802.
(d) Disclosure obligations. None of the
requirements of this part limits or
expands disclosure obligations under
any federal, state, tribal, or local law,
including the requirements under
CERCLA sections 101(40)(c) and
107(q)(1)(A)(vii) requiring persons,
including environmental professionals,
to provide all legally required notices
with respect to the discovery of releases
of hazardous substances. It is the
obligation of each person, including
environmental professionals,
conducting the inquiry to determine his
or her respective disclosure obligations
under federal, state, tribal, and local law
and to comply with such disclosure
requirements.
Subpart B—Definitions and References
§ 312.10
Definitions.
(a) Terms used in this part and not
defined below, but defined in either
CERCLA or 40 CFR part 300 (the
National Oil and Hazardous Substances
Pollution Contingency Plan) shall have
the definitions provided in CERCLA or
40 CFR part 300.
(b) When used in this part, the
following terms have the meanings
provided as follows:
Abandoned property means: property
that can be presumed to be deserted, or
an intent to relinquish possession or
control can be inferred from the general
disrepair or lack of activity thereon such
that a reasonable person could believe
that there was an intent on the part of
the current owner to surrender rights to
the property.
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Adjoining properties means: any real
property or properties the border of
which is (are) 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 subject 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 the
standards and practices listed in subpart
C of this part despite good faith efforts
by the environmental professional or
persons identified under § 312.1(b), as
appropriate, to gather such information
pursuant to §§ 312.20(e)(1) and
312.20(e)(2).
Date of acquisition or purchase date
means: the date on which a person
acquires title to the property.
Environmental Professional means:
(1) a person who possesses sufficient
specific education, training, and
experience necessary to exercise
professional judgment to develop
opinions and conclusions regarding
conditions indicative of releases or
threatened releases (see § 312.1(c)) on,
at, in, or to a property, sufficient to meet
the objectives and performance factors
in § 312.20(e) and (f).
(2) 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 three (3) years of full-time relevant
experience; or
(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 as defined in § 312.21 and
have the equivalent of three (3) years of
full-time relevant experience; or
(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 five (5) years of full-time
relevant experience; or
(iv) Have the equivalent of ten (10)
years of full-time relevant experience.
(3) An environmental professional
should remain current in his or her field
through participation in continuing
education or other activities.
(4) The definition of environmental
professional provided above does 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
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as part of the inquiry identified in
§ 312.21(b).
(5) A person who does not qualify as
an environmental professional under
the foregoing definition may assist in
the conduct of all appropriate inquiries
in accordance with this part if such
person is under the supervision or
responsible charge of a person meeting
the definition of an environmental
professional provided above when
conducting such activities.
Relevant experience, as used in the
definition of environmental professional
in this section, 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
releases or threatened releases (see
§ 312.1(c)) to the subject property.
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: nonengineered instruments, such as
administrative and/or legal controls,
that help to minimize the potential for
human exposure to contamination and/
or protect the integrity of a remedy.
§ 312.11
References.
The following industry standards may
be used to comply with the
requirements set forth in §§ 312.23
through 312.31:
(a) The procedures of ASTM
International Standard E1527–05
entitled ‘‘Standard Practice for
Environmental Site Assessments: Phase
I Environmental Site Assessment
Process.’’
(b) [Reserved]
Subpart C—Standards and Practices
§ 312.20
All appropriate inquiries.
(a) ‘‘All appropriate inquiries’’
pursuant to CERCLA section 101(35)(B)
must be conducted within one year
prior to the date of acquisition of the
subject property and must include:
(1) An inquiry by an environmental
professional (as defined in § 312.10), as
provided in § 312.21;
(2) The collection of information
pursuant to § 312.22 by persons
identified under § 312.1(b); and
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(3) Searches for recorded
environmental cleanup liens, as
required in § 312.25.
(b) Notwithstanding paragraph (a) of
this section, the following components
of the all appropriate inquiries must be
conducted or updated within 180 days
of and prior to the date of acquisition of
the subject property:
(1) Interviews with past and present
owners, operators, and occupants (see
§ 312.23);
(2) Searches for recorded
environmental cleanup liens (see
§ 312.25);
(3) Reviews of federal, tribal, state,
and local government records (see
§ 312.26);
(4) Visual inspections of the facility
and of adjoining properties (see
§ 312.27); and
(5) The declaration by the
environmental professional (see
§ 312.21(d)).
(c) All appropriate inquiries may
include the results of and information
contained in an inquiry previously
conducted by, or on the behalf of,
persons identified under § 312.1(b) and
who are responsible for the inquiries for
the subject property, provided:
(1) Such information was collected
during the conduct of all appropriate
inquiries in compliance with the
requirements of CERCLA sections
101(35)(B), 101(40)(B) and
107(q)(A)(viii);
(2) Such information was collected or
updated within one year prior to the
date of acquisition of the subject
property;
(3) Notwithstanding paragraph (b)(2)
of this section, the following
components of the inquiries were
conducted or updated within 180 days
of and prior to the date of acquisition of
the subject property:
(i) Interviews with past and present
owners, operators, and occupants (see
§ 312.23);
(ii) Searches for recorded
environmental cleanup liens (see
§ 312.25);
(iii) Reviews of federal, tribal, state,
and local government records (see
§ 312.26);
(iv) Visual inspections of the facility
and of adjoining properties (see
§ 312.27); and
(v) The declaration by the
environmental professional (see
§ 312.21(d)).
(4) Previously collected information is
updated to include relevant changes in
the conditions of the property and
specialized knowledge, as outlined in
§ 312.28, of the persons conducting the
all appropriate inquiries for the subject
property, including persons identified
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in § 312.1(b) and the environmental
professional, defined in § 312.10.
(d) All appropriate inquiries can
include the results of report(s) specified
in § 312.21(c), that have been prepared
by or for other persons, provided that:
(1) The report(s) meets the objectives
and performance factors of this
regulation, as specified in paragraphs (e)
and (f) of this section; and
(2) The person specified in § 312.1(b)
and seeking to use the previously
collected information reviews the
information and conducts the additional
inquiries pursuant to §§ 312.28, 312.29
and 312.30 and the all appropriate
inquiries are updated in paragraph (b)(3)
of this section, as necessary.
(e) Objectives. The standards and
practices set forth in this part for All
Appropriate Inquiries are intended to
result in the identification of conditions
indicative of releases and threatened
releases of hazardous substances on, at,
in, or to the subject property.
(1) In performing the all appropriate
inquiries, as defined in this section and
provided in the standards and practices
set forth this subpart, the persons
identified under § 312.1(b)(1) and the
environmental professional, as defined
in § 312.10, must seek to identify
through the conduct of the standards
and practices set forth in this subpart,
the following types of information about
the subject property:
(i) Current and past property uses and
occupancies;
(ii) Current and past uses of
hazardous substances;
(iii) Waste management and disposal
activities that could have caused
releases or threatened releases of
hazardous substances;
(iv) Current and past corrective
actions and response activities
undertaken to address past and on-going
releases of hazardous substances;
(v) Engineering controls;
(vi) Institutional controls; and
(vii) Properties adjoining or located
nearby the subject property that have
environmental conditions that could
have resulted in conditions indicative of
releases or threatened releases of
hazardous substances to the subject
property.
(2) In the case of persons identified in
§ 312.1(b)(2), the standards and
practices for All Appropriate Inquiries
set forth in this part are intended to
result in the identification of conditions
indicative of releases and threatened
releases of hazardous substances,
pollutants, contaminants, petroleum
and petroleum products, and controlled
substances (as defined in 21 U.S.C. 802)
on, at, in, or to the subject property. In
performing the all appropriate inquiries,
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as defined in this section and provided
in the standards and practices set forth
in this subpart, the persons identified
under § 312.1(b) and the environmental
professional, as defined in § 312.10,
must seek to identify through the
conduct of the standards and practices
set forth in this subpart, the following
types of information about the subject
property:
(i) Current and past property uses and
occupancies;
(ii) Current and past uses of
hazardous substances, pollutants,
contaminants, petroleum and petroleum
products, and controlled substances (as
defined in 21 U.S.C. 802);
(iii) Waste management and disposal
activities;
(iv) Current and past corrective
actions and response activities
undertaken to address past and on-going
releases of hazardous substances
pollutants, contaminants, petroleum
and petroleum products, and controlled
substances (as defined in 21 U.S.C. 802);
(v) Engineering controls;
(vi) Institutional controls; and
(vii) Properties adjoining or located
nearby the subject property that have
environmental conditions that could
have resulted in conditions indicative of
releases or threatened releases of
hazardous substances, pollutants,
contaminants, petroleum and petroleum
products, and controlled substances (as
defined in 21 U.S.C. 802) to the subject
property.
(f) Performance factors. In performing
each of the standards and practices set
forth in this subpart and to meet the
objectives stated in paragraph (e) of this
section, the persons identified under
§ 312.1(b) or the environmental
professional as defined in § 312.10 (as
appropriate to the particular standard
and practice) must seek to:
(1) Gather the information that is
required for each standard and practice
listed in this subpart that is publicly
available, obtainable from its source
within reasonable time and cost
constraints, and which can practicably
be reviewed; 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 subpart.
(g) To the extent there are data gaps
(as defined in § 312.10) in the
information developed as part of the
inquiries in paragraph (e) of this section
that affect the ability of persons
(including the environmental
professional) conducting the all
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appropriate inquiries to identify
conditions indicative of releases or
threatened releases in each area of
inquiry under each standard and
practice such persons should identify
such data gaps, identify the sources of
information consulted to address such
data gaps, and comment upon the
significance of such data gaps with
regard to the ability to identify
conditions indicative of releases or
threatened releases of hazardous
substances [and in the case of persons
identified in § 312.1(b)(2), hazardous
substances, pollutants, contaminants,
petroleum and petroleum products, and
controlled substances (as defined in 21
U.S.C. 802)] on, at, in, or to the subject
property. Sampling and analysis may be
conducted to develop information to
address data gaps.
(h) Releases and threatened releases
identified as part of the all appropriate
inquiries should be noted in the report
of the inquiries. These standards and
practices however are not intended to
require the identification in the written
report prepared pursuant to § 312.21(c)
of quantities or amounts, either
individually or in the aggregate, of
hazardous substances pollutants,
contaminants, petroleum and petroleum
products, and controlled substances (as
defined in 21 U.S.C. 802) that because
of said quantities and amounts,
generally would not pose a threat to
human health or the environment.
§ 312.21 Results of inquiry by an
environmental professional.
(a) Persons identified under § 312.1(b)
must undertake an inquiry, as defined
in paragraph (b) of this section, by an
environmental professional, or
conducted under the supervision or
responsible charge of, an environmental
professional, as defined in § 312.10.
Such inquiry is hereafter referred to as
‘‘the inquiry of the environmental
professional.’’
(b) The inquiry of the environmental
professional must include the
requirements set forth in §§ 312.23
(interviews with past and present
owners * * *), 312.24 (reviews of
historical sources * * *), 312.26
(reviews of government records), 312.27
(visual inspections), 312.30 (commonly
known or reasonably ascertainable
information), and 312.31 (degree of
obviousness of the presence * * * and
the ability to detect the contamination
* * *). In addition, the inquiry should
take into account information provided
to the environmental professional as a
result of the additional inquiries
conducted by persons identified in
§ 312.1(b) and in accordance with the
requirements of § 312.22.
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(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 releases or threatened
releases of hazardous substances [and in
the case of inquiries conducted for
persons identified in § 312.1(b)(2)
conditions indicative of releases and
threatened releases of pollutants,
contaminants, petroleum and petroleum
products, and controlled substances (as
defined in 21 U.S.C. 802)] on, at, in, or
to the subject property;
(2) An identification of data gaps (as
defined in § 312.10) in the information
developed as part of the inquiry that
affect the ability of the environmental
professional to identify conditions
indicative of releases or threatened
releases of hazardous substances [and in
the case of inquiries conducted for
persons identified in § 312.1(b)(2)
conditions indicative of releases and
threatened releases of pollutants,
contaminants, petroleum and petroleum
products, and controlled substances (as
defined in 21 U.S.C. 802)] on, at, in, or
to the subject property and comments
regarding the significance of such data
gaps on the environmental
professional’s ability to provide an
opinion as to whether the inquiry has
identified conditions indicative of
releases or threatened releases on, at, in,
or to the subject property. If there are
data gaps such that the environmental
professional cannot reach an opinion
regarding the identification of
conditions indicative of releases and
threatened releases, such data gaps must
be noted in the environmental
professional’s opinion in paragraph
(c)(1) of this section; and
(3) The qualifications of the
environmental professional(s).
(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 and belief, [I,
we] meet the definition of Environmental
Professional as defined in § 312.10 of this
part.’’
‘‘[I, We] have the specific qualifications
based on education, training, and experience
to assess a property of the nature, history,
and setting of the subject property. [I, We]
have developed and performed the all
appropriate inquiries in conformance with
the standards and practices set forth in 40
CFR Part 312.’’
§ 312.22
Additional inquiries.
(a) Persons identified under § 312.1(b)
must conduct the inquiries listed in
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paragraphs (a)(1) through (a)(4) below
and may provide the information
associated with such inquiries to the
environmental professional responsible
for conducting the activities listed in
§ 312.21:
(1) As required by § 312.25 and if not
otherwise obtained by the
environmental professional,
environmental cleanup liens against the
subject property that are filed or
recorded under federal, tribal, state, or
local law;
(2) As required by § 312.28,
specialized knowledge or experience of
the person identified in § 312.1(b);
(3) As required by § 312.29, the
relationship of the purchase price to the
fair market value of the subject property,
if the property was not contaminated;
and
(4) As required by § 312.30, and if not
otherwise obtained by the
environmental professional, commonly
known or reasonably ascertainable
information about the subject property.
§ 312.23 Interviews with past and present
owners, operators, and occupants.
(a) Interviews with owners, operators,
and occupants of the subject property
must be conducted for the purposes of
achieving the objectives and
performance factors of § 312.20(e) and
(f).
(b) The inquiry of the environmental
professional must include interviewing
the current owner and occupant of the
subject property. If the property has
multiple occupants, the inquiry of the
environmental professional shall
include interviewing major occupants,
as well as those occupants likely to use,
store, treat, handle or dispose of
hazardous substances [and in the case of
inquiries conducted for persons
identified in § 312.1(b)(2) pollutants,
contaminants, petroleum and petroleum
products, and controlled substances (as
defined in 21 U.S.C. 802)], 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 of
§ 312.20(e) and (f), interviewing one or
more of the following persons:
(1) Current and past facility managers
with relevant knowledge of uses and
physical characteristics of the property;
(2) Past owners, occupants, or
operators of the subject property; or
(3) Employees of current and past
occupants of the subject property.
(d) In the case of inquiries conducted
at ‘‘abandoned properties,’’ as defined
in § 312.10, where there is evidence of
potential unauthorized uses of the
subject property or evidence of
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uncontrolled access to the subject
property, the environmental
professional’s inquiry must include
interviewing one or more (as necessary)
owners or occupants of neighboring or
nearby properties from which it appears
possible to have observed uses of, or
releases at, such abandoned properties
for the purpose of gathering information
necessary to achieve the objectives and
performance factors of § 312.20(e) and
(f).
§ 312.24 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 § 312.20(e) and
(f). 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 subject
property as it can be shown that the
property contained structures or from
the time the property was first used for
residential, agricultural, commercial,
industrial, or governmental purposes.
For the purpose of achieving the
objectives and performance factors of
§ 312.20(e) and (f), 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.
§ 312.25 Searches for recorded
environmental cleanup liens.
(a) All appropriate inquiries must
include a search for the existence of
environmental cleanup liens against the
subject property that are filed or
recorded under federal, tribal, state, or
local law.
(b) All information collected
regarding the existence of such
environmental cleanup liens associated
with the subject property by persons to
whom this part is applicable per
§ 312.1(b) and not by an environmental
professional, may be provided to the
environmental professional or retained
by the applicable party.
§ 312.26 Reviews of Federal, State, Tribal,
and local government records.
(a) Federal, tribal, state, and local
government records or data bases of
government records of the subject
property and adjoining properties must
be reviewed for the purposes of
achieving the objectives and
performance factors of § 312.20(e) and
(f).
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(b) With regard to the subject
property, the review of federal, tribal,
and state government records or data
bases of such government records and
local government records and data bases
of such records should include:
(1) Records of reported releases or
threatened releases, including site
investigation reports for the subject
property;
(2) Records of activities, conditions,
or incidents likely to cause or contribute
to releases or threatened releases as
defined in § 312.1(c), 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) 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 subject property.
(c) With regard to nearby or adjoining
properties, the review of federal, tribal,
state, 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 releases
or threatened releases. Such records or
databases containing such records and
the associated distances from the subject
property for which such information
should be searched include the
following:
(i) Records of NPL sites or tribal- and
state-equivalent sites (one mile);
(ii) RCRA facilities 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
brownfields sites (one-half mile);
(iv) Records of leaking underground
storage tanks (one-half mile); and
(2) Properties that previously were
identified or regulated by a government
entity due to environmental concerns at
the property. Such records or databases
containing such records and the
associated distances from the subject
property for which such information
should be searched include the
following:
(i) Records of delisted NPL sites (onehalf mile);
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66111
(ii) Registries or publicly available
lists of engineering controls (one-half
mile); and
(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, tribalpermitted or registered, or statepermitted or registered waste
management activities. Such records or
data bases that may contain such
records include the following:
(i) Records of RCRA small quantity
and large quantity generators (adjoining
properties);
(ii) Records of federally-permitted,
tribal-permitted, or state-permitted (or
registered) landfills and solid waste
management facilities (one-half mile);
and
(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 § 312.20(e) and
(f).
(d) The search distance from the
subject 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 such 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 release;
(2) Geologic, hydrogeologic, or
topographic conditions of the subject
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); or
(7) Other relevant factors.
§ 312.27 Visual inspections of the facility
and of adjoining properties.
(a) For the purpose of achieving the
objectives and performance factors of
§ 312.20(e) and (f), the inquiry of the
environmental professional must
include:
(1) A visual on-site inspection of the
subject property and facilities and
improvements on the subject property,
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including a visual inspection of the
areas where hazardous substances 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 property
line, public rights-of-way, or other
vantage point (e.g., aerial photography),
including a visual inspection of areas
where hazardous substances may be or
may have been stored, treated, handled
or disposed. Physical limitations to the
inspection of adjacent properties must
be noted.
(b) Persons conducting site
characterization and assessments using
a grant awarded under CERCLA section
104(k)(2)(B) must include in the
inquiries referenced in § 312.27(a)
visual inspections of areas where
hazardous substances, and may include,
as applicable per the terms and
conditions of the grant or cooperative
agreement, pollutants and
contaminants, petroleum and petroleum
products, and controlled substances as
defined in 21 U.S.C. 802 may be or may
have been used, stored, treated, handled
or disposed at the subject property and
adjoining properties.
(c) Except as noted in this subsection,
a visual on-site inspection of the subject
property must be conducted. In the
unusual circumstance where an on-site
visual inspection of the subject property
cannot be performed because of
physical limitations, remote and
inaccessible location, or other inability
to obtain access to the property,
provided good faith (as defined in
§ 312.10) efforts have been taken to
obtain such access, an on-site inspection
will not be required. The mere refusal
of a voluntary seller to provide access to
the subject property does not constitute
an unusual circumstance. In such
unusual circumstances, the inquiry of
the environmental professional must
include:
(1) Visually inspecting the subject
property via another method (such as
aerial imagery for large properties), or
visually inspecting the subject property
from the nearest accessible vantage
point (such as the property line or
public road for small properties);
(2) Documentation of efforts
undertaken to obtain access and an
explanation of why such efforts were
unsuccessful; and
(3) Documentation of other sources of
information regarding releases or
threatened releases at the subject
property that were consulted in
accordance with § 312.20(e). Such
documentation should include
comments by the environmental
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professional on the significance of the
failure to conduct a visual on-site
inspection of the subject property with
regard to the ability to identify
conditions indicative of releases or
threatened releases on, at, in, or to the
subject property, if any.
§ 312.28 Specialized knowledge or
experience on the part of the defendant.
(a) Persons to whom this part is
applicable per § 312.1(b) must take into
account, their specialized knowledge of
the subject property, the area
surrounding the subject property, the
conditions of adjoining properties, and
any other experience relevant to the
inquiry, for the purpose of identifying
conditions indicative of releases or
threatened releases at the subject
property, as defined in § 312.1(c).
(b) All appropriate inquiries, as
outlined in § 312.20, are not complete
unless the results of the inquiries take
into account the relevant and applicable
specialized knowledge and experience
of the persons responsible for
undertaking the inquiry (as described in
§ 312.1(b)).
§ 312.29 The relationship of the purchase
price to the value of the property, if the
property was not contaminated.
(a) Persons to whom this part is
applicable per § 312.1(b) must consider
whether the purchase price of the
subject property reasonably reflects the
fair market value of the property, if the
property were not contaminated.
(b) Persons who conclude that the
purchase price of the subject property
does not reasonably reflect the fair
market value of that property, if the
property were not contaminated, must
consider whether or not the differential
in purchase price and fair market value
is due to the presence of releases or
threatened releases of hazardous
substances.
(c) Persons conducting site
characterization and assessments with
the use of a grant awarded under
CERCLA section 104(k)(2)(B) and who
know that the purchase price of the
subject property does not reasonably
reflect the fair market value of that
property, if the property were not
contaminated, must consider whether or
not the differential in purchase price
and fair market value is due to the
presence of releases or threatened
releases of hazardous substances,
pollutants, contaminants, petroleum
and petroleum products, or controlled
substances as defined in 21 U.S.C. 802.
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§ 312.30 Commonly known or reasonably
ascertainable information about the
property.
(a) Throughout the inquiries, persons
to whom this part is applicable per
§ 312.1(b) and environmental
professionals conducting the inquiry
must take into account commonly
known or reasonably ascertainable
information within the local community
about the subject property and consider
such information when seeking to
identify conditions indicative of
releases or threatened releases, as set
forth in § 312.1(c), at the subject
property.
(b) Commonly known information
may include information obtained by
the person to whom this part applies in
§ 312.1(b) or by the environmental
professional about releases or
threatened releases at the subject
property 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 § 312.20(e) and (f), persons to whom
this part is applicable per § 312.1(b) 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 subject property; 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 subject property;
(2) Local and state government
officials who may have knowledge of, or
information related to, the subject
property;
(3) Others with knowledge of the
subject property; and
(4) Other sources of information (e.g.,
newspapers, Web sites, community
organizations, local libraries and
historical societies).
§ 312.31 The degree of obviousness of the
presence or likely presence of
contamination at the property, and the
ability to detect the contamination by
appropriate investigation.
(a) Persons to whom this part is
applicable per § 312.1(b) and
environmental professionals conducting
an inquiry of a property on behalf of
such persons must take into account the
information collected under § 312.23
through 312.30 in considering the
degree of obviousness of the presence of
releases or threatened releases at the
subject property.
(b) Persons to whom this part is
applicable per § 312.1(b) and
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environmental professionals conducting
an inquiry of a property on behalf of
such persons must take into account the
information collected under § 312.23
through 312.30 in considering the
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ability to detect contamination by
appropriate investigation. The inquiry
of the environmental professional
should include an opinion regarding
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additional appropriate investigation, if
any.
[FR Doc. 05–21455 Filed 10–31–05; 8:45 am]
BILLING CODE 6560–50–P
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Agencies
[Federal Register Volume 70, Number 210 (Tuesday, November 1, 2005)]
[Rules and Regulations]
[Pages 66070-66113]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-21455]
[[Page 66069]]
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Part III
Environmental Protection Agency
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40 CFR Part 312
Standards and Practices for All Appropriate Inquiries; Final Rule
Federal Register / Vol. 70, No. 210 / Tuesday, November 1, 2005 /
Rules and Regulations
[[Page 66070]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 312
[SFUND-2004-0001; FRL-7989-7]
RIN 2050-AF04
Standards and Practices for All Appropriate Inquiries
AGENCY: Environmental Protection Agency.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: The Environmental Protection Agency (EPA) today is
establishing federal standards and practices for conducting all
appropriate inquiries as required under sections 101(35)(B)(ii) and
(iii) of the Comprehensive Environmental Response, Compensation, and
Liability Act (CERCLA). Today's final rule establishes specific
regulatory requirements and standards for conducting all appropriate
inquiries into the previous ownership and uses of a property for the
purposes of meeting the all appropriate inquiries provisions necessary
to qualify for certain landowner liability protections under CERCLA.
The standards and practices also will be applicable to persons
conducting site characterization and assessments with the use of grants
awarded under CERCLA section 104(k)(2)(B).
DATES: This final rule is effective November 1, 2006.
ADDRESSES: EPA established a docket for this action under Docket ID No.
SFUND-2004-0001. All documents in the docket are listed in the EDOCKET
index at https://www.epa.gov/edocket. Although listed in the index, some
information is not publicly available, i.e., information labeled
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Certain other material, such as
copyrighted material, is not placed on the Internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available either electronically in EDOCKET or in hard
copy at the EPA Docket Center, EPA West Building, Room B102, 1301
Constitution Ave., NW., Washington, DC. This docket facility is open
from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding Federal
holidays. The telephone number for the Public Reading Room is (202)
566-1744, and the telephone number for the OSWER Docket is (202) 566-
0276.
FOR FURTHER INFORMATION CONTACT: For further information on specific
aspects of today's rule, contact Patricia Overmeyer of EPA's Office of
Brownfields Cleanup and Redevelopment at (202) 566-2774 or at
overmeyer.patricia@epa.gov. Mail inquiries may be directed to the
Office of Brownfields Cleanup and Redevelopment (5105T), 1200
Pennsylvania Ave. NW., Washington, DC 20460.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Who Potentially May be Affected by Today's Rule?
This regulation may affect most directly those persons and
businesses purchasing commercial property or any property that will be
used for commercial or public purposes and who may, after purchasing
the property, seek to claim protection from CERCLA liability for
releases or threatened releases of hazardous substances. Under
section101(35)(B) of CERCLA, as amended by the Small Business Liability
Relief and Brownfields Revitalization Act (Pub. L. 107-118, 115 stat.
2356, ``the Brownfields Amendments'') such persons and businesses are
required to conduct all appropriate inquiries prior to or on the date
on which the property is acquired. Prospective landowners who do not
conduct all appropriate inquiries prior to or on the date of obtaining
ownership of the property may lose their ability to claim protection
from CERCLA liability as an innocent landowner, bona fide prospective
purchaser, or contiguous property owner.
In addition, today's rule will affect any party who receives a
brownfields grant awarded under CERCLA section 104(k)(2)(B) and uses
the grant money to conduct site characterization or assessment
activities. This includes state, local and tribal governments that
receive brownfields site assessment grants for the purpose of
conducting site characterization and assessment activities. Such
parties are required under CERCLA section 104(k)(2)(B)(ii) to conduct
such activities in compliance with the standards and practices
established by EPA for the conduct of all appropriate inquiries. EPA
notes that today's rule also may affect other parties who apply for
brownfields grants under the provisions of CERCLA section 104(k), since
such parties may have to qualify as a bona fide prospective purchaser
to ensure compliance with the statutory prohibitions on the use of
grant funds under Section 104(k)(4)(B)(I). Any party seeking liability
protection as a bona fide prospective purchaser, including eligible
brownfields grantees, must conduct all appropriate inquiries prior to
or on the date of acquiring a property.
The background document, ``Economic Impacts Analysis for the
Proposed All Appropriate Inquiries Final Regulation'' and the Addendum
to this document provide a comprehensive analysis of all potentially
impacted entities. These documents are available in the docket
established for today's rule. A summary of potentially affected
businesses is provided in the table below.
Our aim in the table below is to provide a guide for readers
regarding entities likely to be directly regulated or indirectly
affected by today's action. This action, however, may affect other
entities not listed in the table. To determine whether you or your
business is regulated or affected by this action, you should examine
the regulatory language amending CERCLA. This language is found at the
end of this Federal Register notice. If you have questions regarding
the applicability of this action to a particular entity, consult the
person listed in the preceding section entitled FOR FURTHER INFORMATION
CONTACT.
------------------------------------------------------------------------
NAICS
Industry category code
------------------------------------------------------------------------
Manufacturing................................................. 31-33
Wholesale Trade............................................... 42
Retail Trade.................................................. 44-45
Finance and Insurance......................................... 52
Real Estate................................................... 531
Professional, Scientific and Technical Services............... 541
Accommodation and Food Services............................... 72
Repair and Maintenance........................................ 811
Personal and Laundry Services................................. 812
State, Local and Tribal Government............................ N/A
------------------------------------------------------------------------
B. How Can I Get Copies of This Document and Other Related Information?
1. Docket. EPA established an official public docket for this
action under Docket ID No. SFUND-2004-0001. The official public docket
consists of the documents specifically referenced in this action, any
public comments received, and other information related to today's
action. Although a part of the official docket, the public docket does
not include Confidential Business Information (CBI) or other
information whose disclosure is restricted by statute. Documents in the
official public docket are listed in the index list in EPA's electronic
public docket and comment system, EDOCKET. Documents may be available
either electronically or in hard copy. Electronic documents may be
viewed through EDOCKET. Hard copy
[[Page 66071]]
documents may be viewed at the EPA Docket Center, EPA West, Room B102,
1301 Constitution Avenue, NW., Washington, DC. The EPA Docket Center
Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding Federal holidays. The telephone number for the Public
Reading Room is (202) 566-1744, and the telephone number for the OSWER
Docket is (202) 566-0276.
2. Electronic Access. You may access this Federal Register document
electronically through the EPA Internet under the ``Federal Register''
listings at https://www.epa.gov/fedrgstr.
An electronic version of the public docket also is available
through EPA's electronic public docket and comment system, EDOCKET. You
may use EDOCKET at https://www.epa.gov/edocket/ to view public comments,
access the index listing of the contents of the public docket, and
access those documents in the public docket that are available
electronically. Once in the system, select ``search,'' then key in the
appropriate docket identification number.
Certain types of information will not be placed in EDOCKET.
Information claimed as CBI and other information whose disclosure is
restricted by statute, which is not included in the official public
docket, will not be available for public viewing in EPA's electronic
public docket. EPA's policy is that copyrighted material will not be
placed in EPA's electronic public docket but will be available only in
printed, paper form in the official public docket. Docket materials
that are not available electronically may be viewed at the docket
facility identified above.
Contents of Today's Rule
I. Statutory Authority
II. Background
A. What is the Intent of Today's Rule?
B. What is ``All Appropriate Inquiries?''
C. What were the Previous Standards for All Appropriate
Inquiries?
D. What are the Liability Protections Established Under the
Brownfields Amendments?
E. What Criteria Did Congress Establish for the All Appropriate
Inquiries Standard?
III. Summary of Comments and Changes From Proposed Rule to Final
Rule
IV. Detailed Description of Today's Rule
A. What is the Purpose and Scope of the Rule?
B. To Whom is the Rule Applicable?
C. Does the Final Rule Include Any New Reporting or Disclosure
Obligations?
D. What are the Final Documentation Requirements?
E. What are the Qualifications for an Environmental
Professional?
F. References
G. What is Included in ``All Appropriate Inquiries?''
H. Who is Responsible for Conducting the All Appropriate
Inquiries?
I. When Must All Appropriate Inquiries be Conducted?
J. Can a Prospective Landowner Use Information Collected for
Previous Inquiries Completed for the Same Property?
K. Can All Appropriate Inquiries be Conducted by One Party and
Transferred to Another Party?
L. What Are the Objectives and Performance Factors for the All
Appropriate Inquiries Requirements?
M. What are Institutional Controls?
N. How must Data Gaps Be Addressed in the Conduct of All
Appropriate Inquiries?
O. Do Small Quantities of Hazardous Substances That Do Not Pose
Threats to Human Health and the Environment Have to Be Identified in
the Inquiries?
P. What are the Requirements for Interviewing Past and Present
Owners, Operators, and Occupants?
Q. What are the Requirements for Reviews of Historical Sources
of Information?
R. What are the Requirements for Searching for Recorded
Environmental Cleanup Liens?
S. What are the Requirements for Reviewing Federal, State,
Tribal, and Local Government Records?
T. What are the Requirements for Visual Inspections of the
Subject Property and Adjoining Properties?
U. What are the Requirements for the Inclusion of Specialized
Knowledge or Experience on the Part of the ``Defendant?''
V. What are the Requirements for the Relationship of the
Purchase Price to the Value of the Property, if the Property was not
Contaminated?
W. What are the Requirements for Commonly Known or Reasonably
Ascertainable Information about the Property?
X. What are the Requirements for ``the Degree of Obviousness of
the Presence or Likely Presence of Contamination at the Property,
and the Ability to Detect the Contamination by Appropriate
Investigation?''
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination with
Indian Tribal Governments
G. Executive Order 13045: Protection of Children from
Environmental Risks and Safety Risks
H. Executive Order 13211: Actions that Significantly Affect
Energy Supply, Distribution or Use
I. National Technology Transfer Advancement Act
J. Executive Order 12898: Federal Actions to Address
Environmental Justice in Minority Populations and Low-Income
Populations
K. Congressional Review Act
I. Statutory Authority
These regulations are promulgated under the authority of Section
101(35)(B) of the Comprehensive Environmental Response, Compensation,
and Liability Act of 1980 (42 U.S.C. 9601), as amended, most
importantly by the Small Business Liability Relief and Brownfields
Revitalization Act.
II. Background
A. What is the Intent of Today's Rule?
On August 26, 2004, EPA published a notice of proposed rulemaking
outlining proposed standards and practices for the conduct of ``all
appropriate inquiries.'' This regulatory action was initiated in
response to legislative amendments to the Comprehensive Environmental
Response, Compensation, and Liability Act (CERCLA). On January 11,
2002, President Bush signed the Small Business Liability Relief and
Brownfields Revitalization Act (Pub. L. 107-118, 115 Stat. 2356, ``the
Brownfields Amendments''). The Brownfields Amendments amend CERCLA by
providing funds to assess and clean up brownfields sites, clarifying
CERCLA liability provisions for certain landowners, and providing
funding to enhance state and tribal cleanup programs. The intent of
today's rule is to finalize regulations setting federal standards and
practices for the conduct of all appropriate inquiries, a key provision
of the Brownfields Amendments. Subtitle B of Title II of the
Brownfields Amendments revises CERCLA section 101(35), clarifying the
requirements necessary to establish the innocent landowner defense. In
addition, the Brownfields Amendments add protections from CERCLA
liability for bona fide prospective purchasers and contiguous property
owners who meet certain statutory requirements.
Each of the CERCLA liability provisions for innocent landowners,
bona fide prospective purchasers, and contiguous property owners,
requires that, among other requirements, persons claiming the liability
protections conduct all appropriate inquiries into prior ownership and
use of a property prior to or on the date a person acquires a property.
The law requires EPA to develop regulations establishing standards and
practices for how to conduct all appropriate inquiries. Congress
included in the Brownfields Amendments a list of criteria that the
Agency must address in the regulations establishing standards and
practices for conducting all appropriate inquiries
[[Page 66072]]
section 101(35)(2)(B)(ii) and (iii). The Brownfields Amendments also
require that parties receiving a federal brownfields grant awarded
under CERCLA section 104(k)(2)(B) to conduct site characterizations and
assessments must conduct these activities in accordance with the
standards and practices for all appropriate inquiries.
The regulations established today only address the all appropriate
inquiries provisions of CERCLA sections 101(35)(B)(i)(I) and
101(35)(B)(ii) and (iii). Today's rule does not address the
requirements of CERCLA section 101(35)(B)(i)(II) for what constitutes
``reasonable steps.''
B. What is ``All Appropriate Inquiries?''
An essential step in real property transactions may be evaluating a
property for potential environmental contamination and assessing
potential liability for contamination present at the property. The
process for assessing properties for the presence or potential presence
of environmental contamination often is referred to as ``environmental
due diligence,'' or ``environmental site assessment.'' The
Comprehensive Environmental Response Compensation and Liability Act
(CERCLA) or Superfund, provides for a similar, but legally distinct,
process referred to as ``all appropriate inquiries.''
Under CERCLA, persons may be held strictly liable for cleaning up
hazardous substances at properties that they either currently own or
operate or owned or operated at the time of disposal. Strict liability
in the context of CERCLA means that a potentially responsible party may
be liable for environmental contamination based solely on property
ownership and without regard to fault or negligence.
In 1986, the Superfund Amendments and Reauthorization Act ( Pub. L.
No. 99-499, 100 stat. 1613, ``SARA'') amended CERCLA by creating an
``innocent landowner'' defense to CERCLA liability. The new section
101(35)(B) of CERCLA provided a defense to CERCLA liability, for those
persons who could demonstrate, among other requirements, that they
``did not know and had no reason to know'' prior to purchasing a
property that any hazardous substance that is the subject of a release
or threatened release was disposed of on, in, or at the property. Such
persons, to demonstrate that they had ``no reason to know'' must have
undertaken, prior to, or on the date of acquisition of the property,
``all appropriate inquiries'' into the previous ownership and uses of
the property consistent with good commercial or customary standards and
practices. The 2002 Brownfields Amendments added potential liability
protections for ``contiguous property owners'' and ``bona fide
prospective purchasers'' who also must demonstrate they conducted all
appropriate inquiries, among other requirements, to benefit from the
liability protection.
C. What Were the Previous Standards for All Appropriate Inquiries?
As part of the Brownfields Amendments to CERCLA, Congress
established interim standards for the conduct of all appropriate
inquiries. The federal interim standards established by Congress became
effective on January 11, 2002. In the case of properties purchased
after May 31, 1997, the interim standards include the procedures of the
ASTM Standard E1527-97 (entitled ``Standard Practice for Environmental
Site Assessments: Phase 1 Environmental Site Assessment Process''). In
the case of persons who purchased property prior to May 31, 1997 and
who are seeking to establish an innocent landowner defense or qualify
as a contiguous property owner, CERCLA provides that such persons must
establish, among other statutory requirements, that at the time they
acquired the property, they did not know and had no reason to know of
releases or threatened releases to the property. To establish they did
not know and had no reason to know of releases or threatened releases,
persons who purchased property prior to May 31, 1997 must demonstrate
that they carried out all appropriate inquiries into the previous
ownership and uses of the property in accordance with generally
accepted good commercial and customary standards and practices.
In the case of property acquired by a non-governmental entity or
non-commercial entity for residential or other similar uses, the
current interim standards for all appropriate inquiries may not be
applicable. For those cases, the Brownfields Amendments to CERCLA
establish that a ``facility inspection and title search that reveal no
basis for further investigation shall be considered to satisfy the
requirements' for all appropriate inquiries. In addition, such
properties are not within the scope of today's rule.
The interim standards remain in effect only until the effective
date of today's rule which promulgates federal regulations establishing
standards and practices for conducting all appropriate inquiries.
On May 9, 2003, EPA published a final rule (68 FR 24888) clarifying
that for the purposes of achieving the all appropriate inquiries
standards of CERCLA section 101(35)(B), and until the effective date of
today's regulation, persons who purchase property on or after May 31,
1997 could use either the procedures provided in ASTM E1527-2000,
entitled ``Standard Practice for Environmental Site Assessments: Phase
I Environmental Site Assessment Process,'' or the earlier standard
cited by Congress in the Brownfields Amendments, ASTM E1527-97.
Today's notice is a final rule and as such replaces the current
interim standards for all appropriate inquiries established by Congress
in the Brownfields Amendments and clarified by EPA in the May 9, 2003
final rule. Since the Agency is promulgating a final rule establishing
federal regulations containing the standards and practices for
conducting all appropriate inquiries, the interim standard will no
longer be the operative standard for conducting all appropriate
inquiries upon November 1, 2006, the effective date of today's rule.
Until November 1, 2006, both the standards and practices included in
today's final regulation and the current interim standards established
by Congress for all appropriate inquiries will be recognized by EPA as
satisfying the statutory requirements for the conduct of all
appropriate inquiries under section 101(35)(B) of CERCLA.
D. What are the Liability Protections Established Under the Brownfields
Amendments?
The Brownfields Amendments provide important liability protections
for landowners who qualify as contiguous property owners, bona fide
prospective purchasers, or innocent landowners. To meet the statutory
requirements for any of these landowner liability protections, a
landowner must meet certain threshold requirements and satisfy certain
continuing obligations. To qualify as a bona fide prospective
purchaser, contiguous property owner, or innocent landowner, a person
must perform ``all appropriate inquiries'' on or before the date on
which the person acquired the property. Bona fide prospective
purchasers and contiguous property owners also must demonstrate that
they are not potentially liable or affiliated with any other person
that is potentially liable for response costs at the property. In the
case of contiguous property owners, the landowner claiming to be a
contiguous property owner also must demonstrate that he did not cause,
contribute, or consent to any release or threatened release of
hazardous substances. To meet the statutory requirements for a bona
fide
[[Page 66073]]
prospective purchaser, a property owner must have acquired a property
subsequent to any disposal activities involving hazardous substances at
the property.
Continuing obligations required under the statute include complying
with land use restrictions and not impeding the effectiveness or
integrity of institutional controls; taking ``reasonable steps'' with
respect to hazardous substances affecting a landowner's property to
prevent releases; providing cooperation, assistance and access to EPA,
a state, or other party conducting response actions or natural resource
restoration at the property; complying with CERCLA information requests
and administrative subpoenas; and providing legally required notices.
For a more detailed discussion of these threshold and continuing
requirements please see EPA, Interim Guidance Regarding Criteria
Landowners Must Meet in Order to Qualify for Bona Fide Prospective
Purchaser, Contiguous Property Owner, or Innocent Landowner Limitations
on CERCLA Liability (Common Elements, 2003). A copy of this document is
available in the docket for today's rule.
EPA notes that, as explained below, persons conducting all
appropriate inquiries in compliance with today's final rule are not
entitled to the CERCLA liability protections provided for innocent
landowners, bona fide prospective purchasers, and contiguous property
owners, unless they also comply with all of the continuing obligations
established under the statute. As explained below, compliance with
today's final rule is only one requirement necessary for CERCLA
liability protection. We also note that the requirements of today's
rule apply to prospective property owners who are seeking protection
from liability under the federal Superfund Law (CERCLA). Prospective
property owners wishing to establish protection from, or a defense to,
liability under state superfund or other related laws must comply with
the all criteria established under state laws, including any criteria
for conducting site assessments or all appropriate inquiries
established under applicable state statutes or regulations.
1. Bona Fide Prospective Purchaser
The Brownfields Amendments added a new bona fide prospective
purchaser provision at CERCLA section 107(r). The provision provides
protection from CERCLA liability, and limits EPA's recourse for
unrecovered response costs to a lien on property for the lesser of the
unrecovered response costs or increase in fair market value
attributable to EPA's response action. To meet the statutory
requirements for a bona fide prospective purchaser, a person must meet
the requirements set forth in CERCLA sections 101(40) and 107(r). A
bona fide prospective purchaser must have bought property after January
11, 2002 (the date of enactment of the Brownfields Amendments). A bona
fide prospective purchaser may purchase property with knowledge of
contamination after performing all appropriate inquiries, provided the
property owner meets or complies with all of the other statutory
requirements set forth in CERCLA section 101(40). Conducting all
appropriate inquiries alone does not provide a landowner with
protection against CERCLA liability. Landowners who want to qualify as
bona fide prospective purchasers must comply with all of the statutory
requirements. The statutory requirements include, without limitation,
that the landowner must:
Have acquired a property after all disposal of hazardous
substances at the property ceased;
Provide all legally required notices with respect to the
discovery or release of any hazardous substances at the property;
Exercise appropriate care by taking reasonable steps to
stop continuing releases, prevent any threatened future release, and
prevent or limit human, environmental, or natural resources exposure to
any previously released hazardous substance;
Provide full cooperation, assistance, and access to
persons that are authorized to conduct response actions or natural
resource restorations;
Comply with land use restrictions established or relied on
in connection with a response action;
Not impede the effectiveness or integrity of any
institutional controls;
Comply with any CERCLA request for information or
administrative subpoena; and
Not be potentially liable, or affiliated with any other
person who is potentially liable for response costs for addressing
releases at the property.
Persons claiming to be bona fide prospective purchasers should keep
in mind that failure to identify an environmental condition or identify
a release or threatened release of a hazardous substance on, at, in or
to a property during the conduct of all appropriate inquiries does not
relieve a landowner from complying with the other post-acquisition
statutory requirements for obtaining the liability protections.
Landowners must comply with all the statutory requirements to obtain
the liability protection. For example, an inability to identify a
release or threatened release during the conduct of all appropriate
inquiries does not negate the landowner's responsibilities under the
statute to take reasonable steps to stop a release, prevent a
threatened release, and prevent exposure to any previous release once
any release is identified. Compliance with the other statutory
requirements for the bona fide prospective purchaser liability
protection is not contingent upon the findings of all appropriate
inquiries.
2. Contiguous Property Owner
The Brownfields Amendments added a new contiguous property owner
provision at CERCLA section 107(q). This provision excludes from the
definition of ``owner'' or ``operator'' under CERCLA section 107(a)(1)
and (2) a person who owns property that is ``contiguous to, or
otherwise similarly situated with respect to, and that is or may be
contaminated by a release or threatened release of a hazardous
substance from'' property owned by someone else. To qualify as a
contiguous property owner, a landowner must have no knowledge or reason
to know of contamination at the time of acquisition, have conducted all
appropriate inquiries, and meet all of the criteria set forth in CERCLA
section 107(q)(1)(A), which include, without limitation:
Not causing, contributing, or consenting to the release or
threatened release;
Not being potentially liable nor affiliated with any other
person who is potentially liable for response costs at the property;
Taking reasonable steps to stop continuing releases,
prevent any threatened release, and prevent or limit human,
environmental, or natural resource exposure to any hazardous substances
released on or from the landowner's property;
Providing full cooperation, assistance, and access to
persons that are authorized to conduct response actions or natural
resource restorations;
Complying with land use restrictions established or relied
on in connection with a response action;
Not impeding the effectiveness or integrity of any
institutional controls;
Complying with any CERCLA request for information or
administrative subpoena;
Providing all legally required notices with respect to
discovery or release of any hazardous substances at the property.
The contiguous property owner liability protection ``protects
parties that
[[Page 66074]]
are essentially victims of pollution incidents caused by their
neighbor's actions.'' S. Rep. No. 107-2, at 10 (2001). Contiguous
property owners must perform all appropriate inquiries prior to
purchasing property. However, performing all appropriate inquiries in
accordance with the regulatory requirements alone is not sufficient to
assert the liability protections afforded under CERCLA. Property owners
must fully comply with all of the statutory requirements to be afforded
the contiguous property owner liability protection. Persons who know,
or have reason to know, that the property is or could be contaminated
at the time of acquisition of a property cannot qualify for the
liability protection as a contiguous property owner, but may be
entitled to bona fide prospective purchaser status.
Persons claiming to be contiguous property owners should keep in
mind that failure to identify an environmental condition or identify a
release or threatened release of a hazardous substance on, at, in or to
a property during the conduct of all appropriate inquiries, does not
relieve a landowner from complying with the other statutory
requirements for obtaining the contiguous landowner liability
limitation. Landowners must comply with all the statutory requirements
to qualify for the liability protections. For example, an inability to
identify a release or threatened release during the conduct of all
appropriate inquiries does not negate the landowner's responsibilities
under the statute to take reasonable steps to stop the release, prevent
a threatened release, and prevent exposure to previous releases once a
release is identified. None of the other statutory requirements for the
contiguous property owner liability protection is contingent upon the
results of the conduct of all appropriate inquiries.
3. Innocent Landowner
The Brownfields Amendments also clarify the innocent landowner
defense. To qualify as an innocent landowner, a person must conduct all
appropriate inquiries and meet all of the statutory requirements. The
requirements include, without limitation:
Having no knowledge or reason to know that any hazardous
substance which is the subject of a release or threatened release was
disposed of on, in, or at the facility;
Providing full cooperation, assistance and access to
persons authorized to conduct response actions at the property;
Complying with any land use restrictions and not impeding
the effectiveness or integrity of any institutional controls;
Taking reasonable steps to stop continuing releases,
prevent any threatened release, and prevent or limit human,
environmental, or natural resource exposure to any previously released
hazardous substances;
To successfully assert an innocent landowner liability defense, a
property owner must demonstrate compliance with CERCLA section
107(b)(3) as well. Such persons must establish, by a preponderance of
the evidence:
That the release or threat of release of hazardous
substances and the resulting damages were caused by an act or omission
of a third party with whom the person does not have employment, agency,
or a contractual relationship;
The person exercised due care with respect to the
hazardous substance concerned, taking into consideration the
characteristics of such hazardous substance, in light of all relevant
facts and circumstances;
Took precautions against foreseeable acts or omissions of
any such third party and the consequences that could foreseeably result
from such acts or omissions.
Like contiguous property owners, innocent landowners must perform
all appropriate inquiries prior to or on the date of acquisition of a
property and cannot know, or have reason to know, of contamination to
qualify for this landowner liability protection. Persons claiming to be
innocent landowners also should keep in mind that failure to identify
an environmental condition or identify a release or threatened release
of a hazardous substance on, at, in or to a property during the conduct
of all appropriate inquiries, does not relieve or exempt a landowner
from complying with the other statutory requirements for asserting the
innocent landowner defense. Landowners must comply with all the
statutory requirements to obtain the defense. For example, an inability
to identify a release or threatened release during the conduct of all
appropriate inquiries does not negate the landowner's responsibilities
under the statute to take reasonable steps to stop the release, prevent
a threatened release, and prevent exposure to a previous release.
Compliance with the other statutory requirements for the innocent
landowner defense is not contingent upon the results of an all
appropriate inquiries investigation.
E. What Criteria Did Congress Establish for the All Appropriate
Inquiries Standard?
Congress included in the Brownfields Amendments a list of criteria
that the Agency must include in the regulations establishing standards
and practices for conducting all appropriate inquiries. In addition to
providing these criteria in the statute, Congress instructed EPA to
develop regulations establishing standards and practices for conducting
all appropriate inquiries in accordance with generally accepted good
commercial and customary standards and practices. The criteria are set
forth in CERCLA section 101(35)(2)(B)(iii) and include:
The results of an inquiry by an environmental
professional.
Interviews with past and present owners, operators, and
occupants of the facility for the purpose of gathering information
regarding the potential for contamination at the facility.
Reviews of historical sources, such as chain of title
documents, aerial photographs, building department records, and land
use records, to determine previous uses and occupancies of the real
property since the property was first developed.
Searches for recorded environmental cleanup liens against
the facility that are filed under federal, state, or local law.
Reviews of federal, state, and local government records,
waste disposal records, underground storage tank records, and hazardous
waste handling, generation, treatment, disposal, and spill records,
concerning contamination at or near the facility.
Visual inspections of the facility and of adjoining
properties.
Specialized knowledge or experience on the part of the
defendant.
The relationship of the purchase price to the value of the
property, if the property was not contaminated.
Commonly known or reasonably ascertainable information
about the property.
The degree of obviousness of the presence or likely
presence of contamination at the property, and the ability to detect
the contamination by appropriate investigation.
III. Summary of Comments and Changes From Proposed Rule to Final Rule
EPA received over 400 public comments in response to the August 26,
2004 proposed rule. Comments were received from environmental
consultants with experience in performing site assessments, trade
[[Page 66075]]
associations, state government agencies, environmental interest groups,
and other public interest associations. Commenters generally supported
the purpose and goals of the proposed rule. Many commenters
complimented the Agency on its decision to develop the proposed rule
using the negotiated rulemaking process. However, commenters had
differing views on certain aspects of the proposed rule. In particular,
the Agency received widely differing views on the proposed definition
of ``environmental professional.'' Although many commenters supported
the definition as proposed, other commenters raised concerns regarding
the stringency of the proposed qualifications. A significant number of
commenters applauded the proposed definition of an environmental
professional and stated that it may increase the rigor and caliber of
environmental site investigations. Commenters who would not qualify as
an environmental professional under the proposed definition raised
concerns with regard to the specific qualifications proposed.
EPA received a significant number of comments regarding the
statutory requirements for qualifying for the CERCLA liability
protections. Several commenters also raised concerns with regard to the
performance-based approach to the all appropriate inquiries
investigation included in the proposed rule. Commenters were concerned
that the proposed performance-based approach would make it more
difficult to qualify for the CERCLA liability protections than an
approach that requires strict adherence to prescriptive data gathering
requirements that do not allow for the application of professional
judgment. However, the vast majority of commenters who commented on the
performance-based nature of the proposed rule supported the proposed
approach.
Other commenters raised concerns with regard to the proposed rule's
requirements to identify and comment upon the significance of ``data
gaps'' where the lack of information may affect the ability of an
environmental professional to render an opinion regarding conditions at
a property that are indicative of releases or threatened releases of
hazardous substances. Commenters were concerned that if any data gaps
exist potential contamination would not be identified, allowing
property owners to escape liability for contamination. Other commenters
supported the proposed requirement to identify data gaps, or missing
information, that may affect the environmental professional's ability
to render an opinion regarding the environmental conditions at a
property and comment on their significance in this regard and stated
that the requirement would lend credibility to the inquiry's final
report.
We received many comments on the proposed provision to compare the
purchase price of a property to the fair market value of the property
(if the property were not contaminated). One concern raised is that
commenters believe that the exact market value of a property is
difficult to determine. Some commenters took exception to the fact that
EPA did not propose that prospective landowners have to conduct formal
real estate appraisals of the property to determine fair market value.
Although this provision has been a statutory requirement for the
conduct of all appropriate inquiries since 1986, some commenters
thought the requirement should not be included within the scope of all
appropriate inquiries. Other commenters stated that the environmental
professional should not be required to undertake the comparison.
We received some comments on the results of the economic impact
analysis that was conducted to assess the potential costs and impacts
of the proposed rule. Many commenters generally agreed with the
Agency's conclusion that the average incremental cost increase
associated with the requirements in the proposed rule over the current
industry standard would be minimal. However, some commenters asserted
that EPA underestimated the incremental costs associated with the
proposed rule. Although a few commenters mentioned particular
activities included as requirements in the proposed rule that would
increase the burdens and costs associated with conducting all
appropriate inquiries, most of these commenters did not provide
specific reasons for claimed cost increases over baseline activities.
Some commenters simply stated that the proposed requirements would
result in an increase in the price of phase I environmental site
assessments. We provide a summary of the comments received on the
economic impact analysis for the proposed rule, our responses to issues
raised by commenters, and the results of some additional analyses
conducted based on some of the issues raised, in an addendum to the
economic impact analysis, which is provided in the docket for today's
final rule.
In section IV of this preamble, we discuss the requirements of the
final rule, including a summary of the provisions included in the
August 26, 2004 proposed rule, the significant comments raised in
response to the proposed provisions, and a summary of our rationale for
the final rule requirements. Generally, the final rule closely
resembles the provisions included in the proposed rule. We adopted
relatively minor changes in response to public comments. For example,
we received a number of comments urging EPA to modify the proposed
definition of environmental professional to allow individuals who have
significant experience in conducting environmental site assessments,
but do not have a Baccalaureate degree, to qualify as environmental
professionals. We were convinced by the arguments presented in many of
these public comments. Therefore, the definition of an environmental
professional included in today's final rule allows individuals with ten
years of relevant full time experience to qualify as an environmental
professional for the purpose of overseeing and performing all
appropriate inquiries.
With respect to the proposed requirements governing the use of
previously-conducted environmental site assessments for a particular
property, we agreed with commenters who pointed out the proposed rule
was unclear. In today's final rule, we modify the proposed rule
language to allow for the use of information contained in previously-
conducted assessments, even if the information was collected more than
a year prior to the date on which the subject property is acquired. The
final rule does require that all aspects of a site assessment, or all
appropriate inquiries investigation, completed more than one year prior
to the date of acquisition of the subject property be updated to
reflect current conditions and current property-specific information.
In the case of all appropriate inquiries investigations completed less
than one year prior to the date of acquisition of the subject property
but more than 180 days before the acquisition date, the final rule
retains the requirements of the proposed rule that only certain aspects
of the all appropriate inquiries must be updated.
In the case of the requirement to search for institutional controls
that was included in the proposed requirements to review federal,
state, tribal and local government records, we agreed with commenters
who pointed out that searching for institutional controls associated
with properties located within a half mile of the subject property is
overly burdensome and without sufficient benefit to the purpose of the
investigation. The final rule
[[Page 66076]]
requires that the search for institutional controls be confined to the
subject property only.
We adopted one other change in the final rule, based upon public
comments. In the proposed rule, we delineated responsibilities for
particular aspects of the all appropriate inquiries investigation
between the environmental professional and the prospective landowner of
the subject property (or grantee). We defined the inquiry of the
environmental professional to include: interviews with past and present
owners, operators and occupants; reviews of historical sources of
information; reviews of federal state tribal and local government
records; visual inspections of the facility and adjoining property;
commonly known or reasonably ascertainable information; and degree of
obviousness of the presence or likely presence of contamination at the
property and the ability to detect the contamination by appropriate
investigation. We also defined ``additional inquiries'' that must be
conducted by the prospective landowner or grantee (or an individual on
the prospective landowner's or grantee's behalf). These ``additional
inquiries'' include: specialized knowledge or experience of the
prospective landowner (or grantee); the relationship of the purchase
price to the fair market value of the property, if the property was not
contaminated; and commonly known or reasonably ascertainable
information. The requirement to search for environmental cleanup liens
was proposed to be the responsibility of the prospective landowner (or
grantee), if the search is not conducted by the environmental
professional. The proposed rule required the prospective landowner (or
grantee) to provide all information collected as part of the
``additional inquiries'' to the environmental professional.
The final rule retains the proposed delineation of
responsibilities. However, based upon the input provided in public
comments, the final rule does not require the prospective landowner (or
grantee) to provide the information collected as part of the
``additional inquiries'' to the environmental professional. Although we
continue to believe that the information collected or held by the
prospective landowner (or grantee) should be provided to the
environmental professional overseeing the other aspects of the all
appropriate inquiries, we agree with commenters who asserted that
prospective landowners and grantees should not be required to provide
this information to the environmental professional. Commenters argued
that property owners (and grantees) may want to hold some information
(e.g., the purchase price of the property) confidential. CERCLA
liability rests with the owner or operator of a property and not with
an environmental professional hired by the prospective landowner and
who is not involved with the ownership or operation of the property.
Since it ultimately is up to the owner or operator of a property to
defend his or herself against any claims to liability, we agree with
commenters that asserted that the regulations should not require that
prospective landowners (or grantees) provide information collected to
comply with the ``additional inquiries'' provisions to the
environmental professional. Should the required information not be
provided to the environmental professional, the environmental
professional should assess the impact that the lack of such information
may have on his or her ability to render an opinion with regard to
conditions indicative of releases or threatened releases of hazardous
substances on, at, in or to the property. If the lack of information
does impact the ability of the environmental professional to render an
opinion with regard to the environmental conditions of the property,
the environmental professional should note the missing information as a
data gap in the written report. We discuss each of the requirements of
the final rule in Section IV of this preamble.
IV. Detailed Description of Today's Rule
A. What Is the Purpose and Scope of the Rule?
The purpose of today's rule is to establish federal standards and
practices for the conduct of all appropriate inquiries. Such inquiries
must be conducted by persons seeking any of the landowner liability
protections under CERCLA prior to acquiring a property (as outlined in
Section II.D. of this preamble). In addition, persons receiving federal
brownfields grants under the authorities of CERCLA section 104(k)(2)(B)
to conduct site characterizations and assessments must conduct such
activities in compliance with the all appropriate inquiries
regulations.
In the case of persons claiming one of the CERCLA landowner
liability protections, the scope of today's rule includes the conduct
of all appropriate inquiries for the purpose of identifying releases
and threatened releases of hazardous substances on, at, in or to the
property that would be the subject of a response action for which a
liability protection would be needed and such a property is owned by
the person asserting protection from liability. CERCLA liability is
limited to releases and threatened releases of hazardous substances
which cause the incurrence of response costs. Therefore, in the case of
all appropriate inquiries conducted for the purpose of qualifying for
protection from CERCLA liability (CERCLA section 107), the scope of the
inquiries is to identify releases and threatened releases of hazardous
substances which cause or threaten to cause the incurrence of response
costs.
In the case of persons receiving Federal brownfields grants to
conduct site characterizations and assessments, the scope of the all
appropriate inquiries standards and practices may be broader. The
Brownfields Amendments include a definition of a ``brownfield site''
that includes properties contaminated or potentially contaminated with
substances not included in the definition of ``hazardous substance'' in
CERCLA section 101(14). Brownfields sites include properties
contaminated with (or potentially contaminated with) hazardous
substances, petroleum and petroleum products, controlled substances,
and pollutants and contaminants (as defined in CERCLA section 101(33)).
Therefore, in the case of persons receiving federal brownfields grant
monies to conduct site assessment and characterization activities at
brownfields sites, the scope of the all appropriate inquiries may
include these other substances, as outlined in Sec. 312.1(c)(2), to
ensure that persons receiving brownfields grants can appropriately and
fully assess the properties as required. It is not the case that every
recipient of a brownfields assessment grant has to include within the
scope of the all appropriate inquiries petroleum and petroleum
products, controlled substances and CERCLA pollutants and contaminants
(as defined in CERCLA section 101(33)). However, in those cases where
the terms and conditions of the grant or the cooperative agreement with
the grantee designate a broader scope to the investigation (beyond
CERCLA hazardous substances), then the scope of the all appropriate
inquiries should include the additional substances or contaminants.
The scope of today's rule does not include property purchased by a
non-governmental entity or non-commercial entity for ``residential use
or other similar uses * * * [where] a facility inspection and title
search * * * reveal no basis for further investigation.'' (Pub. L. 107-
118 Sec. 223). CERCLA section
[[Page 66077]]
101(35)(B)(v) states that in those cases, title search and facility
inspection that reveal no basis for further investigation shall satisfy
the requirements for all appropriate inquiries.
We note that today's rule does not affect the existing CERCLA
liability protections for state and local governments that acquire
ownership to properties involuntarily in their functions as sovereigns,
pursuant to CERCLA sections 101(20)(D) and 101(35)(A)(ii). Involuntary
acquisition of properties by state and local governments fall under
those CERCLA provisions and EPA's policy guidance on those provisions,
not under the all appropriate inquiry provisions of CERCLA section
101(35)(B).
B. To Whom Is the Rule Applicable?
Today's rule applies to any person who may seek the landowner
liability protections of CERCLA as an innocent landowner, contiguous
property owner, or bona fide prospective purchaser. The statutory
requirements to obtain each of these landowner liability protections
include the conduct of all appropriate inquiries. In addition, the rule
applies to individuals receiving Federal grant monies under CERCLA
section 104(k)(2)(B) to conduct site characterization and assessment
activities. Persons receiving such grant monies must conduct the site
characterization and assessment in compliance with the all appropriate
inquiries regulatory requirements.
C. Does the Final Rule Include Any New Reporting or Disclosure
Obligations?
The final rule does not include any new reporting or disclosure
obligations. The rule only applies to those property owners who may
seek the landowner liability protections provided under CERCLA for
innocent landowners, contiguous property owners or bona fide
prospective purchasers. The documentation requirements included in this
rule are primarily intended to enhance the inquiries by requiring the
environmental professional to record the results of the inquiries and
his or her conclusions regarding conditions indicative of releases and
threatened releases on, at, in, or to the property and to provide a
record of the environmental professional's inquiry. Today's rule
contains no new requirements to notify or submit information to EPA or
any other government entity.
Although today's rule does not include any new disclosure
requirements, CERCLA section 103 does require persons in charge of
vessels and facilities, including on-shore and off-shore facilities, to
notify the National Response Center of any release of a hazardous
substance from the vessel or facility in a quantity equal to or greater
than a ``reportable quantity,'' as defined in CERCLA section 102(b).
Today's rule includes no changes to this reporting requirement nor any
changes to any other reporting or disclosure requirements under
federal, tribal, or state law.
D. What Are the Final Documentation Requirements?
The proposed rule required that the environmental professional, on
behalf of the property owner, document the results of the all
appropriate inquiries in a written report. As explained in the preamble
to the proposed rule, the property owner could use this report to
document the results of the inquiries. Such a report can be similar in
nature to the type of report previously provided under generally
accepted commercial practices. We proposed no requirements regarding
the length, structure, or specific format of the written report. In
addition, the proposed rule did not require that a written report of
any kind be submitted to EPA or any other government agency, or that a
written report be maintained on-site at the subject property for any
length of time.
Today's final rule retains the requirements, as proposed, for
documenting the results of the all appropriate inquiries investigation
conducted under the supervision or responsible charge of an
environmental professional. As noted above, the primary purpose of the
documentation requirement is to enhance the inquiry of the
environmental professional by requiring that the environmental
professional record the results of the inquiries and his or her
conclusions. The written report may allow any person claiming one of
the CERCLA landowner liability protections to offer documentation in
support of his or her claim that all appropriate inquiries were
conducted in compliance with the federal regulations.\1\ The Agency
notes that while today's final regulation does not require parties
conducting all appropriate inquiries to retain the written report or
any other documentation discovered, consulted, or created in the course
of conducting the inquiries, the retention of such documentation and
records may be helpful should the property owner need to assert
protection from CERCLA liability after purchasing a property.
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\1\ Nothing in this regulation or preamble is intended to
suggest that any particular documentation prepared in conducting all
appropriate inquiries will be admissible in court in any litigation
where a party raises one of the liability protections, or will in
any way alter the judicial rules of evidence.
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The final rule requires that a written report documenting the
results of the all appropriate inquiries include an opinion of an
environmental professional as to whether the all appropriate inquiries
conducted identified conditions indicative of releases or threatened
releases of hazardous substances on, at, in or to the subject property.
The rule also requires that the report identify data gaps in the
information collected that affect the ability of the environmental
professional to render such an opinion and that the environmental
professional comment on the significance of the data gaps.
Several commenters raised issues with regard to the proposed
requirement that the environmental professional document and comment on
the significance of data gaps that affect the ability of the
environmental professional to identify conditions indicative of
releases or threatened releases of hazardous substances on at, in, or
to the subject property. Some commenters stated that the need to
identify data gaps will make it difficult to determine when an all
appropriate inquiries investigation is complete and therefore the
requirement would act as a disincentive to the development of
potentially contaminated properties. Other commenters asserted that the
fact that the regulations recognize data gaps creates a loophole that
would result in property owners claiming to be protected from CERCLA
liability after conducting an incomplete investigation that includes
significant data gaps. These commenters raised concerns that CERCLA
liability protection could be claimed by property owners simply because
they conducted an all appropriate inquiries investigation, even in
those cases where releases on, at, in, or to the property were missed
during the investigation. Other commenters stated their support for the
requirements to document data gaps, as proposed. A summary of EPA's
response to these comments and the requirements for documenting data
gaps included in the final rule is provided below in Section IV.N.
The final rule, at Sec. 312.21(d), retains the proposed
requirement that the environmental professional who conducts or
oversees the all appropriate inquiries sign the written report. There
are two purposes for the requirement to include a signature in the
report. First, the individual signing the report must declare, on the
signature page, that he or she meets the definition of an
[[Page 66078]]
environmental professional, as provided in Sec. 312.10. In addition,
the rule requires that the environmental professional declare that: [I,
We] have developed and performed the all appropriate inquiries in
conformance with the standards and practices set forth in 40 CFR part
312.
Some commenters raised concerns about whether the proposed rule
would require the environmental professional to certify the all
appropriate inquiries report and its findings. Today's final rule does
not require the environmental professional to ``certify'' the results
of the all appropriate inquiries when signing the report. The two
statements or declarations mentioned above and required to be included
in the final written report documenting the conduct of all appropriate
inquiries are meant to document that an individual meeting the
qualifications of an environmental professional was involved in the
conduct of the all appropriate inquiries and that the activities
performed by, or under the supervision or responsible charge of, the
environmental professional were performed in conformance with the
regulations. Reports signed by individuals holding a Professional
Engineer (P.E.) or Professional Geologist (P.G.) license, need not
include the individual's professional seal.
A few commenters requested that EPA include specific requirements
for the content of a final report in the final rule. Given that the
type and extent of information available on a particular property may
vary greatly with its size, type, past uses, and location, and the type
and extent of information necessary for an environmental professional
to render an opinion regarding conditions indicative of releases or
threatened releases of hazardous substances associated with any
property may vary, we decided not to include in the final rule specific
requirements governing the content of all reports.
The provisions of the final rule allow for the property owner (or
grantee) and any environmental professional engaged in the conduct of
all appropriate inquiries for a specific property to design and develop
the format and content of a written report that will meet the
prospective landowner's (or grantee's) objectives and information needs
in addition to providing documentation that all appropriate inquiries
were completed prior to the acquisition of the property, should the
landowner (or grantee) need to assert protection from liability after
purchasing a property.
E. What Are the Qualifications for an Environmental Professional?
Proposed Rule
In the Brownfields Amendments, Congress required that all
appropriate inquiries include ``the results of an inquiry by an
environmental professional'' (CERCLA section 101(35)(B)(iii)(I)). The
proposed rule included minimal qualifications for persons managing or
overseeing all appropriate inquiries. The intent of setting minimum
professional qualifications, is to ensure that all inquiries are
conducted at a high level of professional ability and ensure the
overall quality of both the inquiries conducted and the conclusions or
opinions rendered with regard to conditions indicative of the presence
of a release or threatened release on, at, in, or to a property, based
upon the results of all inquiries. The proposed rule required that an
environmental professional conducting or overseeing all appropriate
inquiries possess sufficient specific education, training, and
experience necessary to exercise professional judgment to develop
opinions and conclusions regarding the presence of releases or
threatened releases of hazardous substances to the surface or
subsurface of a property. In addition, the proposed rule included
minimum qualifications, including minimum levels of education and
experience, that characterize the type of professional who is best
qualified to oversee and direct the development of comprehensive
inquiries and provide the landowner with sound conclusions and opinions
regarding the potential for releases or threatened releases to be
present at the property. The proposed rule allowed for individuals not
meeting the proposed definition of an environmental professional to
contribute to and participate in the all approp