Daily Development forTuesday, January 15, 2002
By: Patrick A. Randolph,
Jr.
Elmer F. Pierson Professor of Law
UMKC School of Law
Of Counsel: Blackwell Sanders Peper Martin
Kansas City, Missouri
prandolph@cctr.umkc.edu
I am setting forth here excerpts from DIRTer Larry Schnapf's
excellent summary in his environmental newsletter of the salient elements of
the new CERCLA amendments that just passed the Congress, known as the
"Brownfields Amendments" but in some cases going beyond the
brownfieds problem. In a separate
posting, I'll provide other excerpts from the newsletter, but the two parts of
this DD contain those elements that I think are likely to have the greatest
interest:
First, there is a discussion of the revisions of the statute
relating to the "good faith purchaser" defense - largely good news
for real estate investors. Second,
there is a discussion of the revisions of the statute dealing with owners of
properties adjacent to polluted sites that suffer from migration. Also good news. (At least I read it that way.)
Title II of the Small Business Liability Relief and
Brownfields Revitalization Act legislation is called the Brownfields
Revitalization and Environmental Restoration Act (the "Brownfield
Amendments").
This title clarifies and establishes new defenses to CERCLA
liability and contains a number of incentives that are designed to promote the
reuse and development of brownfield sites.
Part I:
Changes to Innocent Purchaser's Defense
The CERCLA third-party defense provides that a person may
not be liable under CERCLA if it can establish by a preponderance of evidence
that the release was SOLELY to the acts or omissions of a third party who was
not an agent or employee of the defendant, the defendant did not have a direct
or indirect contractual relationship with the third party, the defendant
exercised due care in dealing with the hazardous substances and the defendant
took precautions against foreseeable acts or omissions of any third party and
the foreseeable consequences of those acts or omissions. This defense has generally been unavailable
to purchasers or occupiers of contaminated property or anyone in the chain of
title because of the requirement that the person asserting the defense cannot
be in contractual relationship with the third party (usually a prior landowner
or tenant) who caused the release.
As a result, Congress enacted the "innocent purchaser's
defense". To take advantage of
this affirmative defense, an owner must establish that it did not know and had
no reason to know that any hazardous substances were disposed of at the
facility. To establish that it had no reason to know of the contamination, a
defendant must demonstrate that it took "all appropriate inquiry into the
previous ownership and uses of the property consistent with good commercial or
customary practice in an effort to minimize liability." In determining
whether there was an "appropriate inquiry," CERCLA requires that any
specialized knowledge or experience of the innocent owner must be taken into
account as well as the relationship of the purchase price to the contaminated
property and whether the presence of contamination was obvious or could be
detected by an appropriate site inspection.
Prior to the enactment of the Brownfield Amendments, an
innocent purchaser also had to comply with the due care and precautionary
requirements of the third party defense in addition to having no reason to know
that there had been a release of hazardous substances at the property. The
Brownfield Amendments add the following obligations that an owner purchaser
must perform to preserve its status as an innocent purchaser: First, the person
must provide full cooperation, assistance, and access to persons that are
authorized to conduct response actions or natural resource restoration at the
property. Second, the person is also
obligated to comply with any land use restrictions established or relied on in
connection with the response action at a vessel or facility and must not impede
the effectiveness or integrity of any institutional control employed at the
vessel or facility in connection with a response action. Finally, the BFP must
provide access that is necessary to allow persons authorized to conduct
response actions at the facility install, operate, maintain or otherwise ensure
the integrity of land use controls that may be a part of a response action.
New Due Diligence Standards
One of the criticisms of CERCLA had been that it did not
create standards for what constituted an "appropriate inquiry." The
Brownfield Amendments establish interim standards for satisfying this
requirement.
EPA is directed to promulgate permanent standards by January
11, 2004. For commercial property purchased before May 31, 1997, the Brownfield
Amendments provide that courts shall take the following factors into account
when determining if a defendant conducted an appropriate inquiry. These factors
are essentially those set forth in the CERCLA innocent purchaser's defense
prior to the Brownfield Amendments:
(1) Any specialized knowledge or experience on the part of
the defendant; ú
(2) The relationship of the purchase price to the value of
the property, if the property was not contaminated; ú
(3) Commonly known or reasonably ascertainable information
about the property; ú
(4) The obviousness of the presence or likely presence of
contamination at the property; and
(5) The ability of the defendant to detect the contamination
by appropriate inspection.
For property purchased on or after May 31, 1997 and until
EPA promulgates its due diligence standards, owners or tenants may satisfy the
appropriate inquiry requirement by performing a Phase I environmental site
assessment in accordance with the American Society for Testing and Materials "E1527
Standard Practice for Environmental Site Assessment: Phase 1 Environmental Site
Assessment Process.
As part of this interim standard, the purchaser must also
exercise "appropriate care" with respect to hazardous substances
found at the facility by taking reasonable steps to stop any continuing
release, prevent any threatened future release, and prevent or limit human,
environmental, or natural resource exposure to any previously released
hazardous substance.
For residential property or other similar use at the time of
purchase by a nongovernmental or noncommercial entity, the a person may qualify
as a BFP by conducting a site inspection and title search that reveal no basis
for further investigation.
In promulgating permanent due diligence standards, EPA is
required to include the following criteria in its standard.
(1) The results of
an inquiry by an environmental professional.
(2) 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.
(3) 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.
(4) Searches for recorded environmental cleanup liens against
the facility that are filed under federal, state or local law.
(6) Reviews of federal, state and local government records,
including waste disposal records, underground storage tank records, and
hazardous waste handling and spill records concerning contamination at or near
the facility.
(7) Visual inspections of the facility and of adjoining
properties.
(8) Specialized knowledge or experience on the part of the
defendant.
(9) The relationship of the purchase price to the value of
the property in an uncontaminated state.
(10) Commonly known or reasonably ascertainable information
about the property, and ú 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.
The Bona Fide Prospective Purchaser Defense
Perhaps the principal drawback of the CERCLA innocent
purchaser defense has been that for a landowner to successfully assert the
defense, it had to establish that it had no reason to know that the property
was contaminated. Since the problem with brownfields is the existence or
suspicion of contamination, the defense was largely unavailable to prospective
developers or tenants of brownfield sites.
To eliminate this obstacle to redevelopment of brownfields,
section 222 of the Brownfield Amendments created a new Bona Fide Prospective
Purchaser ("BFP") defense. This new defense provides that a purchaser
who falls within the definition of a BFP would not be liable as an owner or
operator of a site merely based on its status as an owner or operator of a site
if it does not impede the performance of a response action or natural resource
restoration.
The new BFP defense allows landowners or tenants who
knowingly acquire or lease contaminated property after January 11, 2002 to
avoid CERCLA liability if they can establish by a preponderance a number of
conditions. The BFP defense is not
limited to property that qualifies as a brownfield site but also extends to NPL
sites. To qualify for the BFP Defense, a person must satisfy the following:
(1) All disposal of hazardous substances at the facility
occurred before it acquired the facility.
(2) The person must satisfy the innocent purchaser standards
for "appropriate inquiry" (see above) ú (3) The person must comply
with all reporting requirements and other required notices regarding the
discovery or release of any hazardous substances at the facility.
(4) The person takes "appropriate care" by taking
by taking reasonable steps to stop any continuing release, prevent any
threatened future release; and prevent or limit human, environmental, or
natural resource exposure to any previously released hazardous substance.
(5) The person provides full cooperation, assistance, and
access to persons that are authorized to conduct response actions or natural
resource restoration at the property.
(6) The person is also obligated to comply with any land use
restrictions established or relied on in connection with the response action at
a vessel or facility and must not impede the effectiveness or integrity of any
institutional control employed at the vessel or facility in connection with a
response action.
In addition, the BFP must provides access that is necessary
to allow persons authorized to conduct response actions at the facility
install, operate, maintain or otherwise ensure the integrity of land use
controls that may be a part of a response action. The person must comply with
any request for information or administrative subpoena issued by EPA under its
CERCLA authority. Finally, the person must establish that it is not a PRP or
affiliated with any other PRP for the property through (i) any direct or indirect
familial relationship, or any contractual, corporate, or financial relationship
other than one arising out of conveying title of the facility, or a contract
for the sale of goods or services, or (ii) the result of a reorganization of a
business entity that was a PRP.
Reporter's Comment:
At this point in time, it is unclear if EPA will continue the
Prospective Purchaser Agreement ("PPA") program. It is possible that
EPA may continue to enter into PPAs for purchasers who do not qualify for the
statutory defense owners (e.g., did not conduct due diligence) yet are willing
to provide consideration in exchange for the PPA.
Part Two:
Clarification of the Liability of Owners of Property
Contiguous to Contaminated Sites
In 1995, EPA published its "Policy Toward Owners of
Property With Contaminated Aquifers" to encourage the reuse of
contaminated sites. Under this policy, EPA said it would not hold owners of
property liable when groundwater beneath their site has been contaminated from
an off-site source if the owner did not contribute to the release of the
hazardous substances, was not in a contractual relationship with the person
responsible for the release and there is not an alternative basis for imposing
CERCLA liability on the owner.
The Brownfield Amendments add a new section 107(q) to CERCLA
entitled "Contiguous Properties" that essentially codified this
policy. The new section provides that a
person owning property that is contiguous to or otherwise similarly situated to
a contaminated site and that is or may be contaminated by a release or
threatened release of a hazardous substance from that contaminated site shall
not be considered to be a CERCLA owner or operator solely by reason of the
contamination if it can satisfy the following conditions by a preponderance of
the evidence:
(1) The person did not cause, contribute, or consent to the release or threatened release; ú The person it is not a PRP or affiliated with any other PRP for the property through (i) any direct or indirect familial relationship, or 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 financed or by a contract for the sale of goods or services), or (ii) the result of a reorganization of a business entity that was a PRP.
(2) The person takes reasonable steps to stop any continuing release, prevent any threatened future release; and prevent or limit human, environmental, or natural resource exposure to any hazardous substance released on or from property owned by that person;
(3) The person provides full cooperation, assistance, and access to persons that are authorized to conduct response actions or natural resource restoration at the property;
(4) The person is also obligated to comply with any land use restrictions established or relied on in connection with the response action at a vessel or facility and must not impede the effectiveness or integrity of any institutional control employed at the vessel or facility in connection with a response action. In addition, the BFP must provides access that is necessary to allow persons authorized to conduct response actions at the facility install, operate, maintain or otherwise ensure the integrity of land use controls that may be a part of a response action.
(5) The person must comply with all reporting requirements and other required notices regarding the discovery or release of any hazardous substances at the facility; ú
(6) The person must comply with any request for information or administrative subpoena issued by EPA under its CERCLA authority; and ú
(7)
The person must have conducted an appropriate inquiry at the
time the person acquired title to the property and did not know or have no
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.
Reporter's Comment 1: Unlike the BFP defense, this defense
does not refer to the interim due diligence standards that were added to the
innocent purchaser's defense. Presumably, this is a drafting oversight and that
the same inquiry standards will apply to the contiguous property owner defense.
A property owner who does not qualify for the contiguous property defense
because the person had, or had reason to have know of the contamination may
still be able to qualify for the BFP defense.
A person qualifying as an owner of a contiguous property
owner that has been impacted by a plume of contamination migrating beneath the
site from the contaminated property shall not be required to conduct ground
water investigations or to install ground water remediation systems unless it
would otherwise be required to conduct such activity under the EPA 1995 policy.
Status as an owner of a contiguous property will not preclude that person from
asserting any defense to liability that may be available to the person under
any other law nor does it impose liability that is not otherwise imposed by
section 107(a).
For persons who qualify as an owner of a contiguous
property, the new legislation authorizes EPA to issue assurance that no
enforcement action will be initiated under CERCLA and to provide protection
against claims for contribution or cost recovery.
Reporter's Comment 2: For each of these defenses, a party
must exercise "appropriate care" regarding the contamination at the
site. This means that a BFP, innocent purchaser or contiguous property owner
may still have to incur response costs at a contaminated site even though it
may not be liable as a CERCLA owner or operator. However, it would appear that
these actions would more resemble removal actions and not the full-fledged
remedial action.
Brownfield Funding Program In addition to providing
liability relief to purchasers of contaminated property who qualify as bona
fide purchasers, this law established a statutory brownfield funding program. The
law increases the funding for assessment and cleanup of brownfield sites from
approximately $96 million to $250 million a year for fiscal years 2002 through
2006. Of this amount, $150 million will be allocated to localities, states and
tribes to support site assessment and cleanup. Another $50 million will be used
to establish and enhance state and tribal cleanup programs. Finally, $50
million will be available to clean up sites contaminated with petroleum.
However, if Congress does not appropriate the authorized amount, 25% of the
total funds appropriated by Congress in any one year shall be used to
characterize, assess and remediate petroleum-contaminated sites. It is likely
that this program will replace the current administrative brownfield funding program
that EPA has been using since 1996. However, BCRLF grants that were awarded
before the date of enactment of the law could be used section may be used in
accordance with the criteria established by the law. Eligible Brownfield Sites
To be eligible for funding, the property must fall within the new CERCLA
definition of a "brownfield site". The term refers to real property
where the expansion, redevelopment, or reuse may be complicated by the presence
or potential presence of a hazardous substance, pollutant, or contaminant. The definition of a brownfield site
excludes property that is:
ú Subject to a planned or ongoing removal action under CERCLA; ú Listed or proposed for inclusion on the National Priorities List ("NPL"); ú Subject to a unilateral administrative order, a court order, an administrative order on consent or judicial consent decree; ú Under a permit issued pursuant to RCRA, the CWA, TSCA or the SDWA; ú Subject to corrective action under RCRA section 3004(u) or 3008(h), and a corrective action permit or order has been issued or modified to require the implementation of corrective measures; ú Undergoing RCRA closure for a land disposal unit, a closure notification for a land disposal unit has been submitted or where closure requirements have been specified in a closure plan or permit; ú There has been a release of polychlorinated biphenyls ("PCBs") on a portion of the property that is subject to remediation under TSCA; ú 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; or ú A response action at the site has received financial assistance from the federal Leaking Underground Storage Tank Trust Fund.
EPA is authorized to provide financial assistance to sites
that are statutorily excluded from the definition of a brownfield site if EPA
determines on a site-by-site basis 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. One of the difficulties with the administrative brownfield program
had been that sites contaminated with oil were not eligible for funding because
petroleum was excluded from the CERCLA definition of hazardous substances. The
Brownfield Amendments fill this gap by allowing petroleum-contaminated sites to
be eligible for brownfield financial assistance if they meet certain
conditions. The site must either fall within the definition of a brownfield
site or be administratively included within that definition, EPA or a state
must determined that the site poses a relatively low risk compared with other
petroleum-contaminated sites in the state, there is no viable responsible party
to assess, investigate, or cleanup a site, and the site is not subject to a
corrective action order. In addition
to petroleum-contaminated sites, mine-scarred land and property contaminated
with controlled substances under the Controlled Substances Act land may also be eligible for funding. Sites that qualify as a brownfield site are
not precluded from qualifying for assistance under any other provision of
Federal law.
Entities Eligible for Brownfield Grants The Brownfield
Amendments add a new section 128 to CERCLA that creates a class of entities who
may receive grants to inventory, characterize and remediate brownfield sites.
Eligible entities include the following:
ú A general purpose unit of local government; ú A land clearance authority or other quasi-governmental entity that operates under the supervision and control of or as an agent of a general purpose unit of local government; ú A government entity created by a State legislature; ú A regional council or group of general purpose units of local government; ú A redevelopment agency that is chartered or otherwise sanctioned by a State; ú A State; or ú An Indian Tribe.
Qualifying as eligible entity under CERCLA section 128 will not affect any the liability of that entity or the EPA's response authority under CERCLA (including the petroleum exclusion), RCRA, the CWA, TSCA and the SDWA.
Uses of Brownfield Funds Under the administrative brownfield
program established by EPA, parties interested in remediation brownfield sites
could only obtain loans through the BCRLF. The legislative history for the
Brownfield Amendments recognized that brownfield sites redeveloped for
recreational property, open space or other non-economic uses would not generate
sufficient revenue streams to repay the BCRLF and that it was difficult to
obtain private financing for these properties. In addition, the legislative
history acknowledged that disadvantaged communities might lack the resources to
repay BCRLF awards. As a result, new CERCLA section 128 directs EPA to
establish a program to provide grants to inventory, characterize, assess, and
conduct planning related to brownfield sites under paragraph, and to perform
targeted site assessments at brownfield sites.
Site assessments performed using funds authorized by section 128 must be conducted in accordance with the ASTM E1527 standard for Phase I Environmental Site Assessments until EPA promulgates standards for what constitutes an appropriate inquiry.
The new brownfield grants may be issued to eligible entities to capitalize their own revolving loan programs. The eligible entities shall, in turn, shall use the grant funds to provide assistance for the remediation of brownfield sites in the form of 1 or more loans to an eligible entity, a site owner, a site developer, or another person selected by the eligible entity. The grants may be awarded to an eligible entity on a community-wide or site-by-site basis. The grants shall not exceed $200,000 per site though EPA may waive the $200,000 limitation and permit an eligible entity to receive a grant of up to $350,000 for a brownfield site, depending on the anticipated level of contamination, size, or status of ownership of the site. Eligible entities may not receive more than $1 million. However, EPA is authorized to award additional grants to an eligible entity in subsequent years after the year the initial grant is made. In evaluating whether to provide an additional grant to an eligible entity, EPA must take the following factors into account: ú The number of sites and number of communities that are addressed by the revolving loan fund; ú The demand for funding by eligible entities that have not previously received a grant under this section; ú The demonstrated ability of the eligible entity to use the revolving loan fund to enhance remediation and provide funds on a continuing basis; and ú Other similar factors the Administrator considers appropriate to carry out this section. In addition, EPA has the authority to provide direct grants of up to $200,000 to eligible entities or non-profit organizations to remediate one or more brownfield sites owned by the eligible entity or non-profit organization. In determining whether to make direct remediation grants, EPA is required to take the following factors into account:
ú The extent to which a grant will facilitate the creation
of, preservation of, or addition to a park, a greenway, undeveloped property,
recreational property, or other property used for nonprofit purposes; ú The
extent to which a grant will meet the needs of a community that has an
inability to draw on other sources of funding for environmental remediation and
subsequent redevelopment of the area in which a brownfield site is located
because of the small population or low income of the community; ú The extent to
which a grant will facilitate the use or reuse of existing infrastructure; ú
The benefit of promoting the long-term availability of funds from a revolving loan
fund for brownfield remediation; and ú Other similar factors EPA considers
appropriate to consider for the purposes of this section. Local governments may
use up to 10% of a brownfield grant to develop and implement a brownfields
program that may include monitoring the health of populations exposed to one or
more hazardous substances from a brownfield site, and monitoring and enforcement of any institutional controls at a
brownfield site.
Section 128 also authorizes recipients of a brownfield grant or loan to use a portion of the funds to pay for premiums to purchase environmental insurance premiums, develop a risk sharing pool, an indemnity pool, or insurance mechanism to provide financing for response actions under a State response program.
Another drawback of the current administrative brownfield program was that the response actions had to comply with the national contingency plan ("NCP"). To simply the application process and expedite funding of response actions, section 128 provides that applicants will not have to comply with the NCP. However, if EPA determines that a particular NCP requirement is relevant and appropriate (e.g., public participation), the agency may include this requirement as a condition of the application process. The brownfield funds are intended as seed money to leverage other financial resources. As a result, the Brownfield Amendments allow eligible entity to use brownfield grant funds in conjunction with other sources of money so long as the funds are used to characterize, assess or remediate the brownfield site. Eligible entities must pay a matching share which may be in the form of a contribution of labor, material, or services of at least 20% from non-Federal sources of funding unless EPA determines that the matching share would place an undue hardship on the eligible entity. EPA is also authorized to issue grants to eligible entities or nonprofit organizations to provide, training, research, and technical assistance to individuals and organizations to facilitate the inventory of brownfield sites, site assessments, remediation of brownfield sites, community involvement, or site preparation. If EPA determines that a grant or loan recipient has violated or is in violation of a condition of the grant, loan, or applicable Federal law, EPA may terminate the grant or loan, require the person to repay any funds received; and seek any other legal remedies available to the Administrator.
To be eligible for the $50 million for establishing or
supporting state cleanup programs, a state must have either executed a
Memorandum of Agreement ("MOA") with EPA or established a response
program with the following minimum elements: ú Timely survey and inventory of
brownfield sites in the State; ú Oversight and enforcement authorities or other
mechanisms, and resources that are adequate to ensure that a response action
will protect human health and the environment; be conducted in accordance with
applicable Federal and State law; ú Oversight and enforcement authorities or
other mechanisms, and resources that are adequate to ensure that if a person
conducting the response action fails to complete the necessary response
activities, including operation and maintenance or long-term monitoring
activities, the necessary response activities are completed; ú Mechanisms and
resources to provide meaningful opportunities for public participation; ú
Mechanisms for approval of a cleanup plan, and a requirement for verification
by and certification or similar documentation from the State, an Indian tribe, or
a licensed site professional to the person conducting a response action
indicating that the response is complete. Section 128 provides that any
brownfield grant or loan under this section may not be used to pay a penalty or
fine, a federal cost-share requirement, administrative or oversight costs, a
response cost at a brownfield site where the recipient of the grant or loan is
a PRP or costs to comply with environmental except the cost of compliance with
applicable cleanup laws. Brownfield Grant Application Process The Brownfield
Amendments direct EPA to review grant applications from eligible entities at
least once a year. EPA must also establish a ranking system for evaluating
applications. Grants are to be awarded to the eligible entities that EPA
determines have the highest rankings under the following ranking criteria: ú
The extent a grant will stimulate the availability of other funds for
environmental assessment or remediation, and subsequent reuse of an area where
1 or more brownfield sites are located; ú The potential of the proposed project
or the development plan for an area where 1 or more brownfield sites are
located to stimulate economic development of the area on completion of the
cleanup; ú The extent a grant would address or facilitate the identification
and reduction of threats to human health and the environment, including threats
in areas in which there is a greater-than-normal incidence of diseases or
conditions that may be associated with
exposure to hazardous substances, pollutants, or contaminants; ú The extent a
grant would facilitate the use or reuse of existing infrastructure; ú The
extent a grant would facilitate the creation, preservation, or addition to a
park, greenway, undeveloped property, recreational property, or other property
used for nonprofit purposes; ú The extent a grant would meet the needs of a
community that has an inability to draw on other sources of funding for
environmental remediation and subsequent redevelopment because of the small population
or low income of the community; ú The extent to which the applicant is eligible
for funding from other sources; ú The extent a grant will further the fair
distribution of funding between urban and non-urban areas; ú The extent a grant
provides for involvement of the local community in decisions relating to
cleanup and future use of a brownfield site; and ú The extent a grant would
address or facilitate the identification and reduction of threats to the health
or welfare of children, pregnant women, minority or low-income communities, or
other sensitive populations. Eligible entities may submit applications through
the EPA regional offices using forms to be developed by he agency. EPA must publish guidance to
assist eligible entities in applying for grants and coordinate with other
federal agencies to help make eligible entities aware of other available
Federal resources.
Successful applicants will be required to enter into
agreements that will require the recipient to:
ú Comply with all applicable federal and state laws, ú
Ensure that the cleanup protects human health and the environment, ú Use the
grant or loan exclusively to characterize, assess or remediate brownfield
sites; and ú Comply with other terms and conditions as the Administrator
determines to be necessary to carry out this section. Federal Enforcement Bar
At Sites Remediated Under State Brownfield Programs Over 45 states have enacted
brownfield or voluntary cleanup programs that use risk-based cleanups.
Purchasers of brownfield sites and their lenders have been concerned that EPA
might determine that the site was not adequately remediated. This fear of
federal enforcement is probably more theoretical than real since brownfield
sites are not as seriously contaminated as NPL sites and are therefore usually
not on the federal enforcement radar screen. However, to address these
concerns, approximately a dozen states have entered into a memorandum or
agreement where EPA has agreed not to require additional cleanup except under
certain circumstances.
The Brownfield Amendments added a new section 129 to CERCLA that establishes minimum standards for state response programs standards and the circumstances where EPA may bring enforcement actions at sites remediated under a state response program.
Section 129 provides that where a response action has been completed at an "eligible response site" in accordance with a state program specifically governing response actions for the protection of public health and the environment, EPA may not use its authority under CERCLA sections 106 to compel a cleanup or 107 to recover response costs unless the following circumstances are present. ú The State requests EPA assistance in the performance of a response action; ú EPA determines that contamination has migrated or will migrate across a state line, resulting in the need for further response action to protect human health or the environment; ú EPA determines that contamination has migrated or is likely to migrate onto property subject to the jurisdiction, custody, or control of a department, agency, or instrumentality of the United States and may impact the authorized purposes of the Federal property; ú EPA determines after taking into consideration the response activities already taken 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 mitigate the release or threatened release; or ú EPA determines after consulting with a state that new information that was not known by the state when the response action was approved or completed has been discovered that indicates further remediation is necessary to protect public health or welfare or the environment. Consultation with the State shall not limit the ability of the Administrator to make this determination Under new section 129, an "eligible response site" includes sites that fall within the definition of a brownfield site and those sites that EPA determines are eligible for brownfield financial assistance on a case-by-case basis.
Sites specifically excluded from this definition are NPL
sites and those sites where EPA has conducted or is conducting a preliminary
assessment and site inspection, and where EPA determines after consulting with
the state that the preliminary score of the site makes it eligible for
inclusion on the NPL. However, if EPA determines not to take any further
action, the property may be classified as an eligible response site. In addition, sites that pose a threat to a
sole-source drinking water aquifer or a sensitive ecosystem may not be
considered an "eligible response site.
Congress did not provide for any extensive standards for
state response programs in order for the federal enforcement bar to apply at
eligible response sites. The only state program requirement is that the state
maintain an inventory of sites where response actions have been completed in
the previous year and that are planned in the upcoming year. The inventory must
be updated at least annually and be made available to the public. Each site
should be identified by name and location. The inventory must indicate if a
site will be remediated unrestricted use or if institutional controls will be
used. The specific land use controls that will be used must also be identified
in inventory.
If EPA decides to take a response action at an eligible response site, the agency must notify the state of the proposed action at least 48 hours before taking the action. The state has 48 hours to notify EPA if the eligible response site is or has been subject to a cleanup conducted under a state program or if the state is planning to abate the release or threatened release, identify the actions that are planned. If the state fails to respond within the 48-hour period, EPA may take immediate action. However, if EPA determines that more than one of the exceptions to its enforcement bar applies, the agency may take immediate action after notifying the state. NPL Deferral Of Brownfield Sites The Brownfield Amendments add a new section to CERCLA section 105 authorizing EPA to create the NPL. The legislation provides that EPA shall defer final listing of an eligible response site on the NPL if requested by a state when EPA determines that: ú The state or another party under an agreement or order from the state is conducting a response action at the eligible response site in compliance with a state response program that will be protective of human health and the environment, and provide long-term protection of human health and the environment; or ú The state is actively pursuing an agreement to perform a response action at the site with a person that the state has reason to believe is capable of conducting a response action.
If EPA determines after the last day of the 1-year period
from the date when the eligible response site was proposed to be placed on the
NPL that the state or other party is not making reasonable progress toward
completing the response action, EPA may place the eligible response site on the
NPL. However, EPA could defer the
listing for an additional six months if EPA determines deferring the listing
would be appropriate based on the complexity of the site, substantial progress
has been made in negotiations and other appropriate factors that EPA may
identify. EPA may decline to defer, or elect to discontinue a deferral of a
listing of an eligible response site if it determines that the deferral would
not be appropriate because the state is as an owner, operator or a significant
contributor of hazardous substances to the facility. EPA may also decline or
discontinue deferral if the agency determines the NCP criteria for issuance of
a health advisory have been met or the other conditions for deferral are no
longer being met.
Small Business Liability Protection Act Title I of the
legislation provides liability relief for certain categories of PRPs at CERCLA
sites. These statutory changes essentially codify administrative reforms that
EPA has adopted since 1995. De Micromis PRP Exemption The law adds a new de
micromis PRP exemption to section 107 of CERCLA. This exemption apples to generators or transporters who arranged
for the disposal or transporting of less than 110 gallons of liquid waste or
200 pounds of solid waste before April 1, 2001. In any contribution action, plaintiffs will have the burden of
establishing that these conditions do not apply.
However, the exemption will not apply if EPA determines that the hazardous substances generated or transported by the de micromis PRP contributed significantly or could contribute significantly to the cost of the response action or natural resource damages, if the person has failed to respond to an information request or otherwise is impeding a response action, or the person has been convicted of a criminal violation for the conduct to which the exemption would apply. EPA's decision to withdraw the de micromis exemption will not be subject to judicial review. Municipal Solid Waste Exemption The Brownfield Amendments also add a new exemption for certain generators of municipal solid waste ("MSW") that generated the MSW prior to April 1, 2001. The exemption does not apply to transporters of municipalities that own or operate a MSW landfill.
The exemption defines MSW as waste material generated by a household
(including a single or multifamily residence) and commercial, industrial, or
institutional entity that is essentially the same as waste normally generated
by a household. The waste must be collected and disposed with other MSW as part
of normal MSW collection services and contain a relative quantity of hazardous
substances similar to that contained in waste generated by a typical
single-family household. The
definition of MSW contains a non-exclusive list of exempt MSW including food
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. Waste
materials that are not eligible for the MSW exemption include combustion ash
generated by resource recovery facilities or municipal incinerators, or waste
material from manufacturing or processing operations (including pollution
control operations) that is not essentially the same as waste normally
generated by households.
The MSW exemption applies to an owner, operator, or lessee of residential property that generated municipal solid waste. Also exempt are businesses generating MSW if they employed 100 or fewer workers during the three taxable years preceding receipt of a PRP notice and qualify as a small business concern under the Small Business Act. Finally, the MSW exemption also applies to 501(c)(3) non-profit organizations that employed fewer than 100 paid individuals during the taxable year preceding the PRP notice at the location that generated all of the MSW attributable to the organization. In any contribution action, plaintiffs will have the burden of establishing that these conditions do not apply. Plaintiffs who are unable to establish that the exemption does not apply will be liable to the defendant for all reasonable costs of defending the action, including all reasonable attorney's fees and expert witness fees. However, the MSW exemption will not apply if EPA determines that the hazardous substances generated or transported by the PRP contributed significantly or could contribute significantly to the cost of the response action or natural resource damages, if the person has failed to respond to an information request or otherwise is impeding a response action, or the person has been convicted of a criminal violation for the conduct to which the exemption would apply. EPA's decision to withdraw the municipal solid waste exemption will not be subject to judicial review. Ability to Pay Settlements The Brownfield Amendments also codify the EPA Policy On Ability to Pay Determinations. Under new section 122(g)(7), a PRP that can demonstrate an inability or a limited ability to pay response costs may enter into an expedited settlement to resolve its CERCLA liability. When considering a limited ability to pay settlement, EPA is to take into account the ability of the person to pay response costs and still maintain its basic business operations, including consideration of the overall financial condition of the person and demonstrable constraints on the ability of the person to raise revenues. A PRP requesting a limited ability to pay settlement must promptly provide EPA with all relevant information needed to determine the ability of the person to pay response costs. EPA may decline to offer a limited ability to pay settlement if EPA determines that the PRP has failed to comply with any request for access or information, an administrative subpoena issued by EPA, or has impeded or is impeding the performance of a response action at the facility. If EPA determines that the PRP is unable to pay its total settlement amount at the time of settlement, EPA shall consider alternative payment methods as may be necessary or appropriate.
If EPA determines the PRP is not eligible for limited ability to pay settlement, EPA must notify the PRP as soon as practicable after receipt of sufficient information to make a determination and provide the reasons for the declining to enter into such a settlement. After a limited to pay settlement becomes final, EPA must promptly notify PRPs who have not resolved their liability for the facility of the settlement. As a condition of the settlement, the PRP will be required waive all of the claims (including contribution claims) that the party may have against other PRPs unless EPA determines that requiring a waiver would be unjust. A PRP that enters into a settlement shall not be relieved of the responsibility to provide any information or access requested in accordance with the limited ability to pay settlement or a CERCLA section 104(e) request for information. EPA's decision to enter or refuse to enter into a limited ability to pay will not be subject to judicial review. Effect On Concluded Actions The legislation shall not apply to or in any way affect any settlement lodged in or judgment issued by a United States District Court, or any administrative settlement or order entered into or issued by the United States or any State before the date of the enactment of this Act.
Readers are urged to respond, comment, and
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Items in the Daily Development section
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mtabor@staff.abanet.org
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