Introduction
On January 11,
2002, President Bush signed into law the Small Business
Liability Relief and Brownfields Revitalization Act (the
"Act"). The Act’s passage came after years of Congressional
debate and deadlock over amendments to the Comprehensive
Environmental Response Compensation and Liability Act ("CERCLA"),
commonly referred to as the Superfund law. 42 U.S.C. § 9601
et seq. The Act combined two earlier bills –
the Small Business Liability Protection Act, and the
Brownfields Revitalization and Environmental Restoration
Act. These two bills reflect the dual purpose of the Act -
of providing relief from Superfund liability for small
businesses and certain property owners, and to promote the
revitalization of "brownfields," properties where
redevelopment is hindered by the presence or potential
presence of contamination.
The Act provides
needed, new defenses to CERCLA liability. It generally
prohibits federal enforcement action at contaminated sites
being addressed under State oversight To promote the
revitalization of brownfields, the Act authorizes federal
funding for State brownfields programs, and for grants/loans
for brownfields assessment and remediation. The Act reflects
Congress’ intention that the States play a primary role in
brownfields revitalization.
In Section I
below, we provide an overview of CERCLA liability. In
Section II, we address the clarification the Act provides to
the pre-existing "innocent landowner" defense under CERCLA.
In Section III, we address the new "bona fide prospective
purchaser" defense to CERCLA liability the Act provides for,
and compare that new defense to the "innocent landowner"
defense. In Section IV, we address the other new exemptions
and other relief from CERCLA liability provided through the
Act. In Section V, we address the brownfields revitalization
provisions of the Act.
Overview of
CERCLA Liability.
The risk of
incurring environmental liabilities merely from acquiring
title to contaminated property arises primarily from CERLCA.
42 U.S.C. §§ 9601 et seq. CERCLA was enacted
to address the public health and other threats posed by
sites where hazardous substances have been, or may be,
released into the environment. In addition to establishing
the Superfund - a fund to cover the cost of cleaning up
sites for which no responsible party can be made to pay,
CERCLA gives the federal Environmental Protection Agency
("EPA") broad powers to clean up facilities contaminated by
hazardous substances, either by arranging for the cleanup
itself or ordering a responsible party to do so. 42 U.S.C.
§§ 9604, 9606-07.
A broad range of
chemicals and wastes that are toxic or otherwise harmful to
human health or the environment are included within the
scope of "hazardous substances" governed by CERCLA. 42 U.S.C.
§ 9601(14). Petroleum and other oil products, however, are
excluded from the definition of "hazardous substances."
Id. A release of petroleum or other oil products are
governed by state law. See e.g., North
Carolina Oil Pollution and Hazardous Substances Control Act,
N.C. Gen. Stat. §§ 143-215.75 et
seq.
A "facility"
under CERCLA includes any site or area where a hazardous
substance has been deposited, stored, disposed of, or
placed, or otherwise come to be located. 42 U.S.C.
§ 9601(9).
Section 107 of
CERCLA imposes strict liability for the costs of responding
to a release or material threat of a release of hazardous
substances on a wide range of "potentially responsible
parties" or "PRP’s." In general, anyone who incurs cleanup
costs, whether it is EPA, a State, a PRP or other private
party, can sue PRP’s to recover those costs, or a fair
contribution of those costs. 42 U.S.C. §§ 9607(a), 9613(f).
The PRP’s are:
-
the owner
and operator of the facility;
-
any person
who at the time of disposal of any hazardous substance
owned or operated the facility at which such hazardous
substances were disposed of;
-
Any person
who by contract, agreement, or otherwise arranged for
disposal or treatment, or arranged with a transporter
for transport for disposal or treatment, of hazardous
substances owned or possessed by such person, by any
other party or entity, at any facility owned or operated
by another party and containing such hazardous
substances; and
-
Any person
who accepts or accepted hazardous substances for
transport to disposal or treatment facilities.
42 U.S.C.
§ 9601(a)(1)-(4).
The current
owner and operator of the facility are liable pursuant to
Section 107(a)(1), even if no disposal of hazardous
substances has taken place during their ownership, unless
they qualify for any of defenses discussed below.
The Fourth
Circuit Federal Court of Appeals has broadly interpreted the
term "disposal" as used in Section 107(a)(2) to impose
liability not only for active involvement in the "dumping"
or "placing" of hazardous substances, but for ownership of
the facility at a time that hazardous substances were
"spilling" or "leaking." Nurad, Inc. v. William E. Hooper
& Sons, Inc., 966 F.2d 837, 846 (4th Cir.
1992). Thus, for example, if a tank, pipe or other vessel
that is no longer actively used on the property contains
hazardous substances that continue to leak from the tank,
pipe or vessel, anyone who owned or operated the property
during this passive leaking may qualify as an owner or
operator during time of "disposal." This may be true even if
someone bought the property unaware of the existence of the
underground tank or piping that is the source of this
passive leaking.
Clarification to
the Pre-Existing Innocent Landowner Defense.
Before the Act,
the defenses to CERCLA liability were very limited. Those
were the release of hazardous substances was caused solely
either by an act of God, an act of war, or by a third-party
in certain circumstances. 42 U.S.C. § 9601(b).
The "innocent
landowner" defense is technically just the third-party
defense asserted by a current owner of contaminated
property. Essentially, an innocent landowner is one who
bought the property after the disposal of hazardous
substances took place, did not know or have reason to know
of the prior disposal of hazardous substances after making
"appropriate inquiries" about the property, exercised due
care with respect to the hazardous substances once detected,
and took precautions against foreseeable acts or omissions
of the responsible third party.
To qualify as an
innocent landowner, the current owner of the facility must
show:
-
The release
or threat of a release of a hazardous substance was
caused solely by a third party;
-
The third
party is not an employee or agent of the current owner;
-
The acts or
omissions of the third party did not occur in connection
with a direct or indirect contractual relationship to
the current owner, or if there was a
contractual relationship (e.g., the one who sold the
property to the current owner is a liable party), the
current owner acquired the property after the disposal
of placement of the hazardous substance, and
one or more of the following were true:
-
at the
time the current owner acquired the facility, they
did not know and had no reason to know that any
hazardous substance which is the subject of the
release or threatened release was disposed of, in ,
or at the facility,
-
the
current owner is a government entity which acquired
the facility by escheat, or through any other
involuntary transfer or acquisition, or through the
exercise of eminent domain authority, or
-
the
current owner acquired the facility by inheritance
or bequest; and
The owner
exercised due care with respect to the hazardous
substances, and took precautions against foreseeable
acts or omissions of the third party.
42 U.S.C.
§§ 9607(b), 9601(35)(A) (emphasis added).
To establish
that the property owner "had no reason to know of" a prior
disposal of hazardous substances, Congress indicated in
previous amendments to CERCLA that it must have undertaken,
at the time of acquisition, "all appropriate inquiry
into the previous ownership and uses of the property
consistent with good commercial and customary practices
in an effort to minimize liability." 42 U.S.C.
§ 9601(35)(B)(emphasis added).
Until the Act
was signed into law in 2002, confusion understandably
remained over exactly what level of due diligence
constituted "all appropriate inquiry . . . consistent with
good commercial and customary practices." In the Act,
Congress attempted to address this confusion. First,
Congress indicated that, in the case of property for
residential use or other similar use purchased by a
nongovernmental entity, a facility inspection and title
search that reveal no basis for further investigation is
considered to satisfy the "all appropriate inquiries"
requirement. 42 U.S.C. § 9601(35)(B)(v).
Second, Congress
directed EPA to adopt regulations establishing the standards
and practices for conducting "all appropriate inquiries" by
January 11, 2004. At press time for this paper, EPA had not
yet published proposed regulations on this subject. EPA is
utilizing the "negotiated rulemaking process" in preparing
these new, important regulations, by which representatives
of various interest groups are invited to negotiate the text
of proposed regulations with EPA. A copy of a "Negotiated
Rulemaking Committee (draft) Final Consensus Document" on
these new regulations, dated December 5, 2003, can be
obtained at EPA’s brownfields web page, at www.epa.gov/swerosps/bf/index.html.
In the interim,
however, for any property acquisition that occurred after
May 31, 1997, Congress indicated in the Act that the
procedures of environmental due diligence established by the
American Society for Testing and Materials ("ASTM"),
including, "Standard Practice for Environmental Site
Assessment: Phase 1 Environmental Site Assessment Process,"
satisfy the "all appropriate inquiries" requirement. 42
U.S.C. § 9601(35)(B)(iv)(II)(2002). Congress thereby
utilized commonly-used standards for conducting phase 1
environmental site assessments and transaction screenings as
the interim standard until EPA enacts the anticipated
regulations defining "all appropriate inquiry."
The New Defense
for "Bona Fide Prospective Purchasers," How it Differs from
the Innocent Landowner Defense, and Windfall Liens.
After the Act,
the innocent landowner defense remains available only to the
purchaser of property that did not know and had no reason to
know of a prior release of hazardous substances on the
property. One of the major changes to CERCLA in the Act is
the addition of a defense for one who buys contaminated
property with knowledge of the contamination,
provided certain conditions are met. This is the "bona fide
prospective purchaser" defense ("BFPP"). As stated in an
internal EPA memo:
The BFPP
provisions represent a significant change in CERCLA. For the
first time, a party may purchase property with knowledge of
contamination and not acquire liability under CERCLA as long
as that party meets the BFPP criteria.
See
Memo Re: Bona Fide Prospective Purchasers and the New
Amendments to CERCLA, Breen, Director of Office of Site
Remediation Enforcement, May 31, 2002.
Accordingly,
under the Act, a defense to CERCLA liability is now
available to one who buys property after a release of
hazardous substances occurs there regardless of what the
buyer learns from pre-acquisition due diligence, provided
the buyer upon acquisition meets the conditions expected of
them in assisting with an appropriate response by others to
the release or threatened release. If the buyer conducts
"all appropriate inquiry," and as a result, does not learn
about the prior release, the innocent landowner defense
should be available. If the buyer conducts "all appropriate
inquiry," and as a result, learns of the prior release, the
BFPP defense is available, provided all conditions for that
defense listed below are met.
The relevant
provision in the Act provides that a BFPP, whose potential
liability for a release or threatened release is based
solely on the purchaser being considered to be an owner or
operator of a facility, shall not be liable as long as the
BFPP does not impede the performance of a response action.
42 U.S.C. § 107(r)(1). A "bona fide prospective purchaser"
is a person that:
Acquired
ownership of the facility after the date of enactment of the
Act (signed into law January 11, 2002);
All disposal of
hazardous substances at the facility occurred before the
acquisition;
Made "all
appropriate inquiries" into the previous ownership and uses
of the facility in accordance with generally accepted good
commercial and customary standards and practices . . . .
Provided all
legally required notices with respect to the discovery or
release of any hazardous substances;
Exercised
appropriate care with respect to hazardous substances found
at the facility by taking reasonable steps to stop any
continuing release, to prevent any threatened future
release, and to prevent or limit human, environmental or
natural resource exposure to any previously released
hazardous substance;
Provided full
cooperation, assistance, and access to persons that are
authorized to conduct response actions;
Is in compliance
with any land use restrictions established applied to the
property;
Complied with
any request for information or administrative subpoena;
Is not
potentially liable, or affiliated with any person who is
potentially liable for response costs through any familial
relationship, any contractual, corporate or financial
relationship (other than a contractual, corporate or
financial relationship that is created by the instruments by
which title to the facility is conveyed), or the result of a
reorganization of a business entity that was potentially
liable.
42 U.S.C. §
9601(40).
As with the
pre-existing innocent landowner defense, "all appropriate
inquiries," for all acquisitions occurring after May 31,
1997, means compliance with ASTM procedures on an interim
basis, until EPA publishes its anticipated regulations on
what constitutes "all appropriate inquiries." Id. at
§ 9601(40)(B)(ii).
The BFPP defense
is not absolute, however. The Act provides the United States
with a "windfall lien" that can be collected against a BFPP
to cover unrecovered response costs incurred
by EPA in cases where the response action has resulted in an
increase in the fair market value of the property. Id.
at § 9607(r)(2)-(3). The windfall lien cannot exceed the
increase in market value attributable to the EPA-financed
response action. Id. at § 9607(r)(4). The windfall
lien goes into effect when EPA incurs the response costs,
and remains in effect until it is satisfied or EPA recovers
all of its response costs. Id. at § 9607(r)(4). This
lien is meant to avoid allowing a BFPP to profit from use of
money from the Superfund to finance a response action on
their property that is not recovered by the United States
from the PRPs.
Other New
Exemptions and Other Relief from CERCLA Liability.
The
Contiguous Property Owners’ Exemption.
The Act also
includes a new, conditional exemption from Superfund
liability for owners or operators of contaminated
property that is contiguous to property, owned by
another party, from which hazardous substances have been
released. 42 U.S.C. § 9607(q). This new exemption is
very similar to a prior EPA policy in dealing with
contiguous property owners or operators.
Under this
new defense:
-
A person
that owns real 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, real property
that is not owned by that person shall not be considered
to be an owner or operator of . . . facility under
[Section 107(a)(1)-(2)] solely by reason of the
contamination if [they]:
-
did not
cause, contribute or consent to the release or
threatened release;
-
are not
potentially liable, or affiliated with any person that
is potentially liable, for response costs at a facility
through any direct or indirect familial relationship or
any contractual, corporate, or financial relationship
(other than such a relationship created by a contract
for the sale of goods or services);
-
is not the
result of a reorganization of a business entity that was
potentially liable;
-
take
"reasonable steps" to stop any continuing release, and
prevent or limit human, environmental or natural
resource exposure to any hazardous substance released on
or property owned by that person;
-
comply with
CERCLA requests for information and administrative
subpoenas;
-
provide full
cooperation, assistance and access to persons that are
authorized to conduct response actions or natural
resource restorations at the facility from which there
has been a release or threatened release (including the
cooperation and access necessary for the installation,
integrity, operation, and maintenance of any complete or
partial response action or natural resource restoration
at the facility);
-
comply with
any land use restrictions established or relied on in
connection with the response action at the facility;
-
does not
impede the effectiveness or integrity of any
institutional control employed in connection with a
response action;
-
complies
with any request for information or administrative
subpoena;
-
provides all
legally required notices with respect to the discovery
or release of any hazardous substances at the facility;
-
conducted
"all appropriate inquiry" within the meaning of Section
9601(35)(B) with respect to the property, and did not
know or have reason to know that the property was or
could be contaminated by a release or threatened release
of one or more hazardous substances from other real
property not owned or operated by the person.
Id.
at 9607(q)(i)-(viii).
The burden
is on the contiguous property owner or operator to show
all of these conditions are met, by a preponderance of
the evidence, for this exemption to apply. Id. at
9607(q)(B).
Some
commentators have noted that requiring a contiguous
property owner to take "reasonable steps" to stop any
continuing release, and prevent or limit human,
environmental or natural resource exposure to any
hazardous substance could cause confusion, since there
are no standards for determining what affirmative
"reasonable steps" must be taken to meet this
requirement. The Act does address groundwater
contamination that migrated below contiguous property to
the source of the release. It provides in such
circumstances the "reasonable steps" the contiguous
property owner or operator must take shall not generally
include groundwater investigations or installation of
groundwater remediation systems. Id. at
9607(q)(D).
The Act
provides that any person who does not qualify for this
exemption because they had, or had reason to have,
knowledge that the property was or could be contaminated
by a release from other property, may nevertheless
qualify as a BFPP, if they make the requisite showing.
Id. at 9607(q)(C). As noted, the BFPP defense is
available to a person who, as a result of
pre-acquisition appropriate inquiry, knew or had reason
to know of a release or threatened release. Id.
at 9601(40).
The Act also
allows EPA to issue an assurance that no enforcement
action will be initiated against a contiguous property
owner or operator, and affords them protection against
CERCLA cost recovery or contribution actions. Id.
at 9607(q)(D)(3).
The De
Micromis Exemption.
The Act also
includes a new, conditional exemption for waste
generators or transporters who disposed of only very
small volumes of materials containing hazardous
substances at sites listed on EPA’s National Priorities
List ("NPL"). Id. at 9607(o). The provision
provides that:
-
[Subject
to the exceptions described below], a person shall
not be liable, with respect to costs at a facility
on the [NPL], . . . if liability is based upon
[Sections 9601(a)(3)-(4) – generator or transporter
liability] and the person . . . can demonstrate
that:
-
the
total amount of the material containing
hazardous substances that the person arranged
for disposal or treatment of, arranged with a
transporter for transport for disposal or
treatment of, or accepted for transport for
disposal or treatment, at the facility was less
than 110 gallons or liquid materials or less
than 200 pounds of solid materials (or such
greater or lesser amounts as the [EPA]
Administrator may determine by regulation; and
-
all
or part of the disposal, treatment, or transport
concerned occurred before April 1, 2001.
Id.
at 9607(o)(1).
This exemption
will generally afford liability protection to businesses or
persons who have contributed less than two drums of liquid
waste, or a comparable amount of solid waste.
This new
exemption is conditional, and does not apply if the
President (EPA by delegation) determines that:
-
the
materials containing hazardous substances have
contributed significantly or could contribute
significantly, either individually or in the aggregate,
to the cost of the response action or natural resource
restoration with regard to the facility; or
-
the person
seeking the exemption has failed to comply with a
information request or administrative subpoena, or has
impeded or is impeding, through action or inaction, the
performance of a response action or natural resource
restoration with respect to the facility; or
-
a person has
been convicted of a criminal violation for the conduct
to which the exemption would apply, and that conviction
has not been vitiated.
Id.
at 9607(o)(2). This obviously gives EPA rather broad
authority for finding a particular person cannot avail
themselves of this exemption to CERCLA liability. It remains
to be seen how EPA will exercise its authority under this
"pull back" provision. Notably, there is no judicial review
allowed of EPA decisions to exercise this authority. Id.
at 9607(o)(3).
Regardless, this
new exemption emphasizes the importance for small quantity
waste generators to keep complete manifests and other
records regarding their waste disposal.
The Act also
gives certain liability protections to de micromis waste
generators The plaintiff has the burden of showing the
exemption is inapplicable to the defendants in a cost
contribution suit under CERCLA arising from an NPL site,
except when either EPA, or a State or local government is
the plaintiff. Id. at 9607(o)(4). Further, if the
private plaintiff in such a suit fails to make that showing,
they are liable for the relevant defendant’s costs of
defense, including reasonable attorney’s and expert witness
fees. Id. at 9607(p)(7). This should make plaintiffs
in such suits more diligent in screening who they name as
defendants before the action is brought, and thereby reduce
the scope of defendants in CERCLA contribution suits.
The
Municipal Solid Waste Exemption.
The Act also
creates a new, conditional exemption for certain generators
of "municipal solid waste" that is disposed of at facilities
listed on the NPL. Id. at 9607(p). Subject to certain
exceptions described below, it exempts from waste generator
liability for "municipal solid waste" ("MSW") disposal at
such facilities persons or businesses that can demonstrate
that they are:
-
an owner,
operator or lessee of residential property from which
all of the person’s MSW was generated with respect to
the facility;
-
a business
entity (including a parent, subsidiary or affiliate of
the entity) that, during its three taxable years
preceding the date of its notification of potential
CERCLA liability, employed an average not more than 100
full-time individuals, or the equivalent thereof; and
that is a "small business concern" within the meaning of
the Small Business Act, from which was generated all of
the MSW attributable to the entity with respect to the
facility; or
-
a
tax-exempt, not-for-profit organization, as described in
501(c)(3) of the Internal Revenue Code which, during the
year preceding its receipt of notification of potential
CERCLA liability, employed not more than 100 paid
individuals at the location from which was generated all
of the MSW attributable to the organization with respect
to the facility.
Id.
at 9607(p)(1). Notably, the exemption is not available to
municipalities, that commonly own the relevant landfill.
"Municipal solid
waste" is defined as waste material this is:
-
generated by
a household (including a single or multi-family
residence); and
-
generated by
a commercial, industrial, or institutional entity, to
the extent that the waste material –
-
is essentially the same as waste normally
generated by a household;
-
is collected and disposed of with other
municipal solid waste as part of normal
municipal solid waste collection services;
and
-
contains a relative quantity of hazardous
substances no greater than the relative
quantity of hazardous substances contained
in waste material generated by a typical
single-family household.
Id.
at 9607(p)(4)(A).
Examples
of MSW include:
-
[F]ood
and yard waste, paper, clothing, appliances,
consumer product packaging, disposable diapers,
office supplies, cosmetics, glass and metal food
containers, elementary or secondary school science
laboratory waste, and household hazardous waste.
Id.
at 9607(p)(4)(B).
MSW does
not include:
Id.
at 9607(p)(4)(C).
Like with the de
micromis exemption, however, there is a "pull back"
provision, by which the President (EPA) may nullify the
exempt status of a MSW generator if it makes the
determination, which is not subject to judicial review,
that:
-
the MSW has
contributed significantly or could contribute
significantly, either individually or in the aggregate,
to the cost of a response action or a natural resource
restoration with respect to the facility;
-
the
generator failed to comply with an information request
or administrative subpoena issued pursuant to CERCLA; or
-
the
generator has impeded or is impeding a response action
or natural resource restoration at the NPL facility.
Id.
at 9607(p)(2)-(3).
Another
similarity to the de micromis exemption is certain liability
protection is afforded those who qualify for the MSW
exemption. First, no cost contribution action under CERCLA
can be brought by anyone against the owner, operator or
lessee of residential property that qualifies for the MSW
exemption, except when EPA or a State or local government is
the plaintiff. Id. at 9607(p)(6). Further, regarding
MSW disposed of on or after April 1, 2001, the plaintiff in
a cost contribution suit under CERCLA arising from an NPL
site has the burden of showing the MSW exemption is
inapplicable to the defendants, except when either EPA, or a
State or local government is the plaintiff. Id. at
9607(p)(5)(A). And regarding MSW disposed of before April 1,
2001, that burden rests with the plaintiff in such a
contribution suit, regardless of who the plaintiff is.
Id. at 9607(p)(5)(B).
Alternative Settlements for Parties with Limited
Ability to Pay.
As part of the
effort to relieve small businesses of the financial impact
of CERCLA liability, the Act also amends Section 122(g) of
CERCLA, which regards expedited settlements with de minimis
parties, to authorize expedited, reduced or "inability to
pay" settlements with PRP’s that demonstrate an inability or
limited ability to pay CERCLA response costs. 42 U.S.C. §
9622(g)(7)-(12)(the added provisions). Consistent with prior
EPA policy, the general test for such a settlement is
whether the person or business can pay response costs and
still maintain their basic business operations, considering
their overall financial condition and demonstrable
constraints on their ability to raise revenues. Id.
at 9622(g)(7)(B). As a condition to such a settlement, the
applicant must waive all claims for contribution under
CERCLA, unless the President determines such a waiver to be
unjust. Id. at 9622(g)(8)(A). The President may
decline to offer such a settlement to a PRP if he determines
the PRP has failed to comply with any request for
information or administrative subpoena, or has impeded or is
impeding the performance of a response action with respect
to the relevant facility. Id. at 9622(g)(8)(B).
Every
"inability-to-pay" settlement reached per this provision,
once finalized, must be publicized to all PRP’s who have yet
to settle their liability to the United States with respect
to the relevant facility. Id. at 9622(g)(12).
Brownfields
Revitalization Provisions.
Funding
For Brownfields Assessment, Revolving Loans and
Remediation.
Section
9604 of CERCLA sets forth the authority of EPA in
responding to a release or threatened release of
hazardous substances. The Act contains a new
subsection (k) in Section 9604, which codifies and
expands upon EPA’s brownfields revitalization
program. In the new subsection 9604(k), Congress
provided for three main types of federal brownfield
grants, available to "eligible entities." Those are:
(1) assessment grants, (2) revolving loan fund
grants, and (3) cleanup or remediation grants.
The Act
authorizes $200 million per year for fiscal years
2002 - 2006 for these grants. Id. at
9604(k)(12)(A). $50 million per year (or 25% of the
total amount funded if less than $200 million) is
appropriated for such efforts at
petroleum-contaminated facilities that qualify as
brownfield sites. Id. at 9604(k)(12)(B).
Before
addressing the specifics regarding these different
types of grants, it is important to recognize what
is a "brownfield site" where such funds can be
spent, and who is an "eligible entity" that can
obtain such grants.
A
New Definition of "Brownfield Site" for Funding
Purposes.
The Act contains
the new, following definition of a "brownfield site":
real
property, the expansion, redevelopment, or reuse of
which may be complicated by the presence or
potential presence of a hazardous substance,
pollutant or contaminant.
Id.
at 9601(39)(A). Notwithstanding the exclusion of petroleum
from the definition of "hazardous
substances" in CERCLA, for purposes of brownfields
revitalization funding, the term "brownfield site" expressly
includes sites contaminated by petroleum that:
-
meet the
definition of a "brownfield site" stated above;
-
is
determined by EPA or a State to be of relative low risk,
-
for which
there is no viable responsible party, and will be
assessed and cleaned up by a person who is not
potentially liable for the costs of doing so; and
-
Is not the
subject of a RCRA corrective action order for a
underground storage tank release.
Id.
at 9601(39)(D)(ii)(II). The definition also includes
mine-scarred land. Id. at 9601(39)(D)(ii)(III).
The term "brownfield
site," however, expressly excludes facilities which are:
-
the subject
of planned or ongoing removal action;
-
listed or
proposed for listing on the NPL;
-
the subject
of a CERCLA unilateral administrative order, court
order, administrative order on consent or judicial
consent decree;
-
have valid
permits under the Solid Waste Disposal Act, the Federal
Water Pollution Control Act, the Toxic Substances
Control Act or the Safe Drinking Water Act;
-
subject to
corrective action under the Solid Waste Disposal Act,
for which a corrective action permit or order has been
issued;
-
a land
disposal unit for which closure notification under
subtitle C of the Solid Waste Disposal Act has been
submitted, and closure requirement have been specified;
-
subject to
the jurisdiction, custody or control of a department,
agency or instrumentality of the United States, except
for land held in trust by the United States for an
Indian tribe;
-
where a
release of polychlorinated biphenyls (PCBs) subject to
remediation under the Toxic Substances Control Act has
occurred; and
-
where
assistance for response activity under subtitle I of the
Solid Waste Disposal Act (i.e. the Leaking Underground
Storage Tank Trust Fund) has been given.
Id.
at 9601(39)(B). The Act authorizes the President, however,
to make financial assistance available to many of these
facilities upon a finding that financial assistance will
protect human health and the environment, and either promote
economic development or enable the creation of, preservation
of, or addition to parks, greenways, undeveloped property,
other recreational property, or other property used for
nonprofit purposes. Id. At 9601(39)(C).
Who
Qualifies as an "Eligible Entity" for Funding?
This term
"eligible entity," who can apply for brownfields grants, is
defined to include:
-
a general
purpose unit of local government;
-
a land
clearance authority operating under the supervision and
control of a general purpose unit of local government;
-
a government
entity created by a State legislature;
-
a State
chartered (or state sanctioned) redevelopment agency;
-
a State;
-
an Indian
Tribe (except in Alaska); and
-
an Alaska
Native Regional or Village Corporation.
Id.
at 9604(k)(1). Notably, private entities are not included in
this definition. As noted below, however, funds for a
revolving loan fund can be given to an eligible entity
(e.g., local government), which can then use those funds to
make one or more loans to private parties. Id. at
9604(k)(3)(B)(i).
Brownfield Assessment Grants.
In
the Act, Congress directed EPA to establish a
program to provide grants to inventory,
characterize, assess and conduct planning
related to brownfields sites, and to perform
targeted site assessments. Id. at
9604(k)(2)(A). Such grants may be awarded to an
eligible entity on a community-wide or
site-by-site basis, not to exceed $200,000 for a
particular site (subject to increase of
$350,000). Id. at 9604(k)(4)(A)(i).
Brownfield Revolving Loan Funds.
Congress also
directed the President to establish a program to grant funds
to eligible entities to be used for capitalization of
revolving loan funds. Id. at 9604(k)(3)(A)(i). A
recipient of such a grant can use the funds to assist others
with brownfields remediation, in the form of either:
-
loans to
another eligible entity, or a site owner, developer, or
another person; or
-
one or more
"subgrants" to another eligible entity or other
nonprofit organization to remediate a site owned by the
subgrant recipient.
Id.
at 9604(k)(3)(B).
An eligible
entity receiving revolving loan funding must contribute a
matching share of at least 20% from non-federal sources,
unless EPA determines this requirement would place an undue
hardship on the eligible entity. Id. at 9604(k)(9)(B)(iii).
A grant for
revolving loan funds cannot exceed $1,000,000 per entity per
year, applying certain factors in determining whether to
make any further grants to the same entity. Id. at
9604(k)(4)(A)(ii).
Brownfield Remediation or Cleanup Grants.
The final type
of grant is for:
eligible
entities or nonprofit organizations, where
warranted, to be used directly for remediation of
one or more brownfield sites owned by the entity or
organization receiving the grant, in amounts not to
exceed $200,000 for each site to be remediated.
Id.
at 9604(k)(3)(A)(ii). As with a grant for revolving loan
funds, the recipient of such a grant must contribute a
matching 20%. Id. at 9604(k)(9)(B)(iii). The matching
share can be "paid" by providing labor, materials or
services.
In determining
whether to make such a brownfields remediation grant, EPA
must take into account:
-
the extent
to which a grant will facilitate the creation of,
prevention of, or addition to a park, greenway,
undeveloped property, recreational property, or other
property used for non-profit purposes;
-
the extent
to which a grant will meet the environmental remediation
and redevelopment needs of a low income or small
population community;
-
the extent
to which a grant will facilitate the use or reuse of
existing infrastructure;
-
the benefit
of promoting the long-term availability of funds from a
revolving loan fund for brownfield remediation; and
-
such other
factors considered appropriate.
Id.
at 9604(k)(3)(C).
Prohibitions and Other Conditions for Brownfield
Grants.
No part of any
brownfield grant or loan may be used to pay:
-
any penalty
or fine;
-
a federal
cost-share requirement;
-
an
administrative cost;
-
response
costs at a brownfield site for which the recipient is a
PRP (under Section 9607);
-
a cost of
complying with any federal law.
Id.
at 9604(k)(4)(B).
Each recipient
of a loan or grant under the Act will be required to comply
with the National Contingency Plan ("NCP") in conducting any
assessment and remediation "only to the extent that the
requirement is relevant and appropriate" to this brownfield
revitalization program. Id. at 9604(k)(9)(A).
Compliance with the NCP can add significantly to the costs
of assessment and remediation of contaminated site. Congress
clearly expressed its desire that federal brownfields funds
be maximized by avoiding such costs if possible. It will be
interesting to see the degree to which EPA imposes NCP
requirements, such as community involvement in the
remedy-selection process, in any loan or grant agreements.
Funding
For State Response Programs
One of Congress’
objectives in the Act was to facilitate brownfields
revitalization through State programs. In that vein, in
addition to the grant programs described above, Congress
authorized to be appropriated $50,000,000 for each fiscal
year 2006-2006 for grants to eligible States or Indian
tribes. Id. at 9628(a)(3). States or Indian tribes
may use such grants to:
-
to establish
or enhance their own programs for addressing
contaminated sites;
-
to
capitalize a revolving loan fund for brownfield
remediation under Section 9604(k)(3); or
-
to purchase
insurance or develop a risk sharing pool, an indemnity
pool, or an insurance mechanism to provide financing for
response actions.
Id.
at 9628(a)(1)(B).
To be eligible
for these "response program" grants, States or tribes must
either sign a memorandum of agreement with the EPA, or have
a response program that includes each of the following
elements or is taking reasonable steps to include them:
-
a timely
survey and inventory of brownfield sites in the state;
-
oversight
and enforcement authorities adequate to ensure that
response actions will protect human health and the
environment and be conducted in accordance with
applicable law, and that all necessary response
activities are completed in all response actions;
-
mechanisms
and resources to provide "meaningful" opportunities for
public participation," including public access to
relevant documents, prior notice and opportunity for
public comment, and a mechanism for permitting and
appropriately responding to public requests for site
assessments; and
-
mechanisms
for approvals or clean-up plans and for certification
that response actions at brownfield sites have been
completed.
Id.
at 9628(a). For fiscal year 2004, EPA will consider funding
requests up to $1.5 million per state or tribe under this
program.
Limitations On EPA Enforcement Actions
The Act also
provides that, in cases where a person conducts a response
action at a brownfield site that is in compliance with the
state or tribal response program, the President may not
bring an administrative or judicial enforcement action under
106(a) of CERCLA, or take a judicial action to recover
response costs under Superfund 107(a). Id. at
9628(b)(1)(A). However, there are broad exceptions to that
prohibition. The President may bring administrative or
enforcement action against such persons when:
-
the State
requests that the President provide assistance in the
form of a response action;
-
the EPA
Administrator determines that contamination has migrated
or will migrate across a State line, resulting in the
need for further response action, or the President
determines the contamination has migrated or is likely
to migrate onto federally owned property;
-
after taking
into consideration the response activities already
taken, the EPA Administrator finds that a release or
threatened release may present "an imminent and
substantial endangerment" to public health or welfare or
the environment, and that additional response actions
are likely to be necessary to address, prevent, limit or
mitigate" the release or threatened release; and/or
-
the EPA
administrator, after consultation with the State,
determines that information, that on the earlier of the
date on which cleanup was approved or completed, was not
known by the State, as recorded in documents prepared or
relied on in selecting or conducting the cleanup, has
been discovered regarding the contamination or
conditions at a facility indicating it presents a threat
requiring further remediation.
Id.
at 9628(b)(1)(B).
Before EPA
initiates an enforcement action pursuant to one of these
exceptions, it must, except in emergency situations, give
State officials 48 hours advance notice of the action EPA
intends to take. The State, in turn, must notify EPA, within
48 hours, of any State actions that are planned with regard
to the brownfield site in question. Id. at
9628(b)(1)(D).
One condition to
the prohibition against federal enforcement action at
brownfield sites is it only applies in States that maintain
and update at least every year, and make available to the
public a record of sites (presumably brownfield sites) at
which response actions have been completed in the previous
year, or are planned. Id. at 9628(b)(1)(C). It might
be prudent for anyone conducting remediation under a State
brownfields agreement to ensure the State list complies with
this requirement.
Deferral
of Listing on the NPL
The Act also
directs the President "generally shall" defer final listing
of a brownfields site on the NPL, at the request of a State,
if the President determines that:
-
the State or
another party under an agreement with or order from the
State is conducting a response action at the same site
in compliance with a State program that specifically
governs response actions for protection of public health
and the environment, and that will provide long-term
protection to public health and the environment; or
-
the State is
"actively pursuing" an agreement to perform a response
action at the site with a person whom the State believes
is capable of performing that response action
appropriately.
Id.
at 9605(h)(1).
The President
may decline the request of deferral, to discontinue the
deferral, upon determining that:
-
deferral
would not be appropriate because the State, as an owner
of operator or significant contributor of hazardous
substances at the facility, is a PRP;
-
the criteria
under the NCP for issuance of a health advisory have
been met; or
-
the
conditions for deferral are no longer being met.
Id.
at 9605(h)(4).
Also, if after
one year following a proposal to list a brownfields site on
the NPL, the President determines that the State is not
making reasonable progress towards completing a response
action at that site, the President may then list the site on
the NPL. Id. at 9605(h)(2).
By
Keith H. Johnson,
Poyner & Spruill LLP, (919) 783-1013,
kjohnson@poynerspruill.com and Daniel F. Mclawhorn,
Associate City Attorney, City of Raleigh (919) 890-3060;
dan.mclawhorn@ci.raleigh.nc.us.