New York State Bar Association Brownfields Conference
October 26, 1999, Albany, New York
Linda R. Shaw, Esq.
Knauf Craig Koegel & Shaw, LLP
Rochester, New York
(716) 546-8430
B. Brownfields
vs. Greenfields Due Diligence
Due diligence required for a brownfield site clearly requires different steps and quite often more steps than those required to develop a greenfield site. This is not to say that all brownfield transactions are more complicated than greenfield transactions. A former developer in the Buffalo, New York area frequently reminds a local brownfield panel of experts that developers do not focus on the many steps typically required under the State Environmental Quality Review Act (SEQRA), local zoning laws, and other state and local requirements to develop a greenfield site. For example, installing new infrastructure and utilities through a wetland is a time consuming and common problem encountered during greenfield development. SEQRA, zoning and other local infrastructure requirements are generally not as problematic for a brownfield site, which are typically located in more developed and impacted areas. However, developers tend to be more comfortable handling greenfield development issues during the daily course of their business and do not consider such issues to be barriers to development, despite their associated cost or difficulty.
By
contrast, environmental contamination is perceived as a significant barrier
to property development of any kind. The presence of the contamination
itself is not necessary the barrier, but the number of "unknowns" that
may be associated with the actual presence of such contamination or the
perception of residual contamination even after the site is remediated
effectively creates a development barrier. The "unknowns" include: (1)
the lengthy and cumbersome process to redevelop a brownfield site in conjunction
with State and/or federal agency oversight; (2) need to investigate on-
and off-site contamination in certain circumstances; and (3) lack of liability
relief even after a cleanup is conducted. Unless "location, location, location"
is driving a brownfield transaction, these "unknowns" create barriers that
overcome many brownfield transactions.
C."Time
is of the Essence" For A Successful Site Redevelopment Project
Lack
of time destroys most real estate deals on greenfield or brownfield sites.
In my personal experience working on brownfield redevelopment projects,
time is more important in certain circumstances than money. Of course time
and money are closely related; if a project takes too long, unreasonable
costs may be incurred. However, the traditional length of time to investigate
and remediate the average brownfield site (egs. gasoline stations, light
industrial manufacturing facilities) under legislatively prescribed remediation
programs is barely accomplished within the one to two year time frame typically
associated with an entire redevelopment project. Unless remediation and
redevelopment are accomplished simultaneously, time frames typically associated
with development projects cannot be met on brownfield sites.
Unfortunately,
the New York State Department of Environmental Conservation ("DEC") does
not view economic redevelopment of brownfield sites as one of its goals.
Despite attempts by Governor Pataki and former Governor Cuomo to encourage
redevelopment of such sites through initiatives such as the non-statutory
Voluntary Cleanup Program and 1996 Bond Act Brownfield Restoration Program,
until a new law is passed that establishes an expedited program for the
redevelopment of such properties, brownfield redevelopment projects in
New York remain difficult and time consuming. This
article will focus on the various due diligence requirements necessary
to move a brownfield project forward in an expedited fashion under both
current New York State brownfield programs and future anticipated legislative
programs.
As
noted above in Section I, time is of the essence with most development
projects. Prospective tenants or buyers generally have a schedule with
limited flexibility on either side of their time line in which to handle
newly discovered environmental issues. On the other hand, DEC is generally
more comfortable with the following two scenarios involving contaminated
property: (1) a parcel which experiences a new emergency spill and can
be remediated in an expedited fashion with little investigation; or (2)
a parcel on which long-term historic contamination has been discovered
that is currently unoccupied.
The
emergency spill program has always worked well in New York with one exception.
The two hour spill reporting requirement for a new spill encourages immediate
action and cleanup. Time is not wasted delineating plumes before the bulk
of contamination is removed. However, once a spill site is cleaned up,
it is difficult to obtain a "closure" letter unless a formal post spill
investigation is performed. In other words, former spill sites that were
remediated receive little in the way of a liability release from the State.
DEC may eventually issue a spill closure letter, which do provide lenders
and buyers with some degree of comfort, but do not necessarily demonstrate
that a certain level of cleanup was achieved making the site acceptable
for resale or safe for a particular use. Therefore, the question remains
on former spill sites whether the sites where cleaned up to a particular
level allowing for specific redevelopment.
With
respect to historic contamination sites that are typically unoccupied,
DEC has acknowledged that investigations can take between two to ten years
prior to commencing remediation. In general, no redevelopment project is
pushing the investigation and remediation time line. The site owner and/or
other potentially responsible parties are not in any rush to cleanup a
site that will have little value even after it is remediated. Unless a
real estate transaction is pushing the envelope, the slow remediation process
may indirectly benefit site owners and other responsible parties who can
hold onto their money until DEC forces them to spend it.
Brownfield
redevelopment sites pose a unique problem because either they are being
actively used or if they are inactive, a redevelopment project is planned
for the site that must inevitably push the environmental due diligence
time frame in order to make the transaction work. In addition, brownfield
sites typically do involve historic long-term contamination that may require
an in-depth upfront investigation.
B.
First Challenge: Conduct an Expedited But Thorough Site Investigation
Therefore,
the initial challenge for DEC and the prospective brownfield redeveloper
or the existing and cooperative site owner is to conduct an expedited,
but thorough, site investigation such that any required remediation can
proceed simultaneously with the one to two year redevelopment project.
As discussed in the "Managing Environmental Due Diligence" presentation,
one of the first steps in most commercial/industrial property due diligence
transactions is to conduct a Phase I site investigation, particularly when
the history of a particular site may be environmentally suspect.
1.Phase I Site AssessmentCreates a Perception of Potential Contamination
Lenders
and many others rely on the preliminary conclusions contained in a Phase
I investigation. It is important to understand an industrial standard "ASTM
Phase I site assessment" is only a paper investigation of a site, not a
physically intrusive one. In other words, a consultant is hired for between
$1,000-$3,000 to review historic records, maps, and any other relevant
documentation. In addition, the consultant typically walks around the site
and/or interviews any relevant personnel regarding the history of operations
and ownership of the site. Phase I site assessments do provide extremely
useful information that can be used to determine whether a site is, at
a minimum, like to be a brownfield site.
For
example, a site that was formally a gasoline station, a manufacturing facility,
or a commercial establishment that may have used chemicals, all are good
historical indicators that the site may be a brownfield site with actual
contamination. A Phase I site assessment, which reveals these and other
similar historic uses, generally recommends a Phase II site assessment,
which is a physically intrusive subsurface investigation of the site.
2.Phase II Site InvestigationCreates Initial Data on Site Contamination
Depending
on whether the Phase I investigation reveals the presence of underground
storage tanks, underground storage areas or other above-ground visual indications
of possible subsurface contamination (egs. floor drains, trenches, fill
pipes), different investigation techniques will be employed. There are
new and improved above-ground techniques to locate underground utilities
and tanks, including magnetometer surveys. However, most environmental
investigations involve the drilling of borings to sample soil and permanent
or temporary wells to sample both soil and groundwater. While horizontal
sampling techniques can be employed (particularly to determine the conditions
of soil and/or groundwater under structures), typically vertical drilling
techniques to a variety of depths are used.
The
size of the site generally plays a factor in the number and depth of wells
and borings necessary to conduct a Phase II investigate of a site. In general,
consultants will explain that a minimum of three subsurface sampling locations
are necessary in order to develop a triangular pattern. Triangulation is
necessary to determine groundwater flow direction on and off the property.
Consultants typically do not explain to their clients that a basic Phase
II investigation of a site is not usually acceptable as a complete site
investigation. A complete investigation of a site is generally defined
in New York as the full characterization of the nature and extent of contamination
on and off the site. In other words, if subsurface contamination is found,
any contaminant plumes found in soil or groundwater emanating from the
source area must be identified and delineated.
C.
#1 Brownfield Deal Killer: Off-Site Groundwater Contamination
If
a Phase II or subsequent site investigation reveals a confined on-site
soil only contamination problem that may be associated with an underground
tank or former drum storage area, the brownfield redevelopment project
can continue with some creative lawyering, engineering, and project management.
An on-site groundwater contamination problem is more difficult and expensive
to remediate but very often can be handled if the economics of a remediation
system do not eliminate the feasibility of the transaction. The current
Voluntary Cleanup Program can be used to provide Department oversight and
a liability release at the completion of the cleanup while redevelopment
proceeds. In general, since a brownfield site property price is discounted
as a result of the contamination, purchasers may be willing to incur the
costs of investigating and remediating on-site.
However,
if a Phase II or subsequent site investigation reveal significant off-site
soil, or even worse, groundwater contamination, this will be one of the
most difficult problems confronting the pending brownfield transaction.
If a buyer is interested in purchasing a brownfield site, he or she is
generally not interested in buying costs associated with remediating the
property next door. In addition to the costs mounting with respect to the
initial acquisition brownfield site, they now find themselves in a position
of being potentially responsible for investigating and/or remediating the
adjacent property. Therefore, depending on the nature and extent of the
off-site contamination, a brownfield redevelopment project may or may not
move forward over this issue. It is difficult to comprehend under current
law why any one would voluntarily take on an off-site groundwater investigation
and remediation project on and under adjacent property.
Under
the current New York State Voluntary Cleanup Program and under the petroleum
remedial program, even innocent prospective buyers are often being
required to investigate off-site for petroleum contamination due to the
potential strict liability of the State's Oil Spill Fund for any residual
off-site contamination that is not remediated by the developer. It is currently
unclear if a prospective buyer, who is otherwise non-responsible, would
be required to investigate for off-site hazardous contamination; however,
it appears based on recent Voluntary Cleanup agreements that DEC is making
all parties investigate off-site.
The
present unclear and unfriendly off-site investigation and remediation policies
have had the recent effect of discouraging New York State brownfield redevelopment.
In addition, the DEC's emerging policies, which have begun to mandate off-site
soil and groundwater investigations, even deep bedrock groundwater investigations,
illustrate an interesting policy dichotomy. The State is apparently so
scared of liability exposure, particularly to the Oil Spill Fund, that
it would rather discourage investigation and redevelopment of contaminated
sites by mandating off-site investigations rather than creating a more
reasonable brownfield policy regarding off-site contamination issues.
In
June 1999, Governors Program Bill #91 was drafted by DEC and the Governor's
office. The new legislation was based on a June 2, 1999 report prepared
by the Superfund Working Group. At the same time, a group known as The
Brownfields Coalition, which represents a broad array of stakeholders in
the brownfield redevelopment movement, also developed a legislative package
designed to encouraged brownfield redevelopment. Neither piece of legislation
has been sponsored by any member of the State Assembly or Senate. However,
during the next several months, both the Governor Office and The Brownfields
Coalition shall be seeking sponsors for their respective bills.
Further, the Business Council's Bill A.8470, sponsored by Assemblyman Aubry
(D-Brooklyn)
and certain Assembly bills sponsored by Assemblywoman Destito (R-Rome)
and Assemblyman Brodsky (D-Westchester), may be updated and reintroduced
in the Year 2000 session. Unfortunately, these latter bills have not moved
forward and are viewed as "one-house" bills with little chance of being
adopted.
1.No
Off-Site Investigation/Remediation Obligations for True Volunteers
Both
the Governor's Bill and The Brownfield Coalition Bill ("Coalition Bill")
legislative proposal provides relief to prospective purchasers of brownfield
sites who discover off-site contamination. Under the Governor's Bill, innocent
prospective buyers of brownfield sites do not have the obligation to investigate
or remediate off-site. However, such buyers are required to perform an
off-site exposure risk assessment. The bill does not go into great detail
on the requirements for the risk assessment. Some risk assessment are very
expensive and elaborate. What is important is that the Governor's Bill
recognizes that innocent buyers cannot take on an off-site remediation
project at their own expense.
Under
the Coalition Bill, non-responsible party buyers do have the obligation
to conduct an on-site property boundary investigation to determine if off-site
migration is occurring by assessing the property boundary on-site conditions.
In other words, a buyer is responsible for determining if off-site migration
is occurring from the on-site source. However, non-responsible buyers are
similarly not responsible for off-site investigation or remediation.
Therefore,
both legislative proposals recognize that detailed off-site investigation
and remediation should not be the responsibility of a true voluntary prospective
purchaser. The big difference between the two bills is that the Coalition
Bill makes any necessary off-site cleanup an affirmative obligation of
the State and gives the developer the option of conducting the off-site
cleanup to save time and recoup the money spent while the Governor's Bill
is silent on who is responsible for cleanup of the off-site contamination.
This single legislative improvement to existing New York State law would
have a significant impact toward encouraging brownfield redevelopment.
2.Non-Contributory
Owners Finally Get "Brownie Points" for Cleaning Up Their Own Sites
When
confronted with an environmental problem, clients who owns or have operated
on a brownfield site, most frequently argue how unfair environmental liability
is, particularly when they did not contribute to the contamination on the
site. Environmental liability strikes any current or past owner, operator,
or party that arranged for disposal or transported material to a given
site that is now contaminated. This liability scheme is particularly painful
for owners of property who did not cause or contribute to the contamination
on their site and are now found stuck with the monetary responsibility
for investigating and remediating such contamination.
Owners
of brownfield sites, who did not contribute to the contamination on their
site but are potentially responsible parties (i.e., "non-contributory owners"),
are also given "breaks"and are encouraged to remediate their own sites.
The Governor's Bill does distinguish between persons responsible for the
disposal of hazardous waste or the discharge of petroleum under applicable
principles of statutory or common law liability from persons whose liability
arises solely from ownership and operation of the site subsequent to the
disposal activity and appears to suggest that the latter category of non-contributory
owners do not have to remediate off-site regardless of the extent of off-site
contamination. This is a clearly a benefit to such parties but may create
problems in the future if off-site contamination poses a significant threat
and there are no responsible parties from whom the State could seek indemnification
or contribution.
Under the Coalition Bill, a non-contributory owner/operator is required to investigate an on-site plume that is migrating off-site to determine the nature and extent of the contamination. DEC then evaluates the information and is required to make a determination whether the off-site contamination poses a significant threat or not. If the contamination does not pose a significant threat, the owner is not required to remediate the off-site contamination. The State would be responsible for any necessary off-site remediation. If the contamination does pose a significant threat, then the owner is required to remediate both on- and off- site.
In
sum, if a Phase II investigation reveals a well-defined on-site soil and/or
groundwater contamination problem and the costs of remediation are affordable
given the economics of the redevelopment project, the brownfield project
may move forward under current State programs and policies, albeit at a
snail's pace. However, when off-site issues arise, particularly off-site
groundwater issues, without new ways to overcome the off-site remediation
requirements (such as those being offered in the new legislative proposals),
off-site problems shall continue to seriously interfere with the prospect
of redeveloping most brownfield projects. The State should, at a minimum,
develop a policy which encourages prospective purchasers to acquire brownfield
sites by not requiring off-site investigation and remediation but requiring
the State to pick up this burden where off-site work is warranted.
III.CURRENT
DEFENSES TO LIABILITY ARE OF LIMITED VALUE
In 1986, the Federal Superfund Law was amended to clarify the third party defense in order to distinguish this defense from the innocent purchaser defense. Unfortunately, both defenses, which hinge on the nature of the contractual relationship between the purchaser and the previous owner, are still so narrowly drafted and so strictly interpreted by the courts that very few purchasers have been able take advantage of the defenses. In order to establish the third party defense, a party must show that the release was caused solely by a third party (who cannot be one of the party's employees or agents) in connection with a contractual relationship (i.e. land contract, deed, or other instrument transferring title or possession) existing directly or indirectly with the party, after the disposal or placement of the hazardous substance on, in or at the facility, provided the party establishes by a preponderance of evidence that (1) he exercised due care with respect to the hazardous substance concerned, taking into consideration the characteristics of such hazardous substances, in light of all relevant facts and circumstances, and (2) took precautions against foreseeable acts or omissions of any such third party and the consequences that could foreseeably result from such acts or omissions.
In
order to establish the innocent purchaser defense, a party must show all
of the above plus show that at the time of acquisition, the party 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 at the facility.
To establish that the party had no reason to know, the party must have
undertaken at the time of acquisition 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.
Factors the court may take into account include: the party's specialized
knowledge, purchase price, commonly known property information, obviousness
of contamination and ability to detect contamination.
Due
to the constraints of both defenses, even prospective buyers that have
conducted Phase I and Phase II investigations have still found themselves
unable to utilize the defenses after site acquisition.
Under
New York State's existing remediation program, there are no defenses to
environmental liability for innocent owners. Under the current New York
State Superfund Program, an owner is required to conduct an investigation
and remediation of a site under a consent order or other legal instrument.
In general it is difficult to obtain a liability release even subsequent
to the completion of the remediation. Consent orders have been negotiated
that contain liability releases but they are difficult to obtain.
Under
the State Voluntary Cleanup Program, a contractual liability release is
provided in exchange for a site investigation and/or cleanup. However,
the State continues to add new reopeners to the liability release weakening
its effect. The standard reopeners include: fraud, discovery of new
contamination unknown at the time the agreement was executed, cleanup levels
are no longer sufficiently protected to enable the contemplated use of
the site to proceed, and the agreement is not being implemented to the
satisfaction of the Department. However, the Department has added a new
"off site migration" reopener which, particularly for petroleum sites,
defeats the entire benefit of the liability release.
If
on-site petroleum contamination on a brownfield site is not migrating,
or does not have the potential to migrate off-site and the site is not
located in a ubiquitous contaminated neighborhood, the off-site migration
reopener in a voluntary cleanup agreement is not problematic. For example,
I have personally found this reopener acceptable in an agreement on a 200
acre site where the on-site contamination was in the middle of the property
and there was no potential for off-site migration of a minor contamination
plume. However, on a typical brownfield site in an urban setting where
adjacent properties might also be contaminated with petroleum, this reopener
has the unintended effect of reversing the burden of proof onto the volunteer
to prove that any off-site contamination discovered on an adjacent site
is not coming from their property. If such proof cannot be made, the release
is lost. Under existing law, the off-site property owner would have to
prove that the contamination on their own site is coming from adjacent
properties and not their own.
The
Governor's Bill at first blush appears to improve the liability release
currently provided by the non-statutory Voluntary Cleanup Program since
it does not include the off-site migration reopener described above. Fewer
reopeners (five rather than seven) apply in the event a party conducts
a residential level of cleanup. However, one new reopener so vague and
broad that I believe it has a similar, if not worse, impact than the off-site
migration reopener. The reopener is as follows: "the remedy is not sufficiently
protective of public health or the environment". Given that a voluntary
cleanup agreement is negotiated with the department and implemented under
department oversight (in fact, the department oversight costs are charged
to the volunteers) it is unclear under what circumstances a remediation
project could not be implemented correctly such that the entire liability
release protection provided in the agreement should be waived. According
to a recent speech given by Charles Sullivan on October 7, 1999, this reopener
was placed into the bill in case "DEC makes a mistake". The problem is
that if DEC makes a mistake, the volunteer has to pay the price.
The
Coalition Bill has the most comprehensive and far-reaching liability release.
When the Bill was negotiated, environmental groups and the business community
found themselves in agreement on two key issues: (1) the remediation of
sites should be conducted in a more expedited fashion; and (2) in exchange
for an expedited cleanup, a volunteer should obtain a liability release
that will encourage both the cleanup and redevelopment of the property.
As a result, the liability release provided in the Brownfield Coalition
Bill has fair and narrowly drawn reopeners which do not provide DEC with
broad and unfettered discretion to eliminate the liability release. The
reopeners include:
IV.BROWNFIELD
TRANSACTION RECOMMENDATIONS
The
organizers of this conference listed on the agenda a number of recommendations
to assist a brownfield redevelopment project. These include: (a) focus
on the known operations and historic information of the site, (b) use field
instruments for real time results, (c) use information when considering
development plans to save remediation costs, and (d) stagger development
with remediation. These are all creative means to expedite the brownfield
redevelopment process and utilize the actual project to implement certain
remedial activities or engineering controls and minimize transaction costs.
The following section will analyze each of these recommendations and provide
several others to encourage the redevelopment of brownfield sites.
A.
Focus on known operations and historic information.
Very
often the costs associated with a Phase II investigation are linked to
the type of constituents that may have been utilized by the prior uses
on the site. For example, if a gasoline station was on the site, a consultant
can focus on petroleum related compounds and sampling techniques. However,
if the site has a more complicated history of solvent usage, metals usage,
or other types of contamination, then the numbers and types of sampling
tests and techniques will increase and add to the costs. Therefore, the
site investigation should be focused on those chemicals and compounds utilized
by prior historic operations.
B.
Use field instruments for real time results.
There
are a number of above-ground survey techniques that can be helpful in providing
preliminary information regarding subsurface conditions. For example, there
are a number of aboveground geophysical survey devices, including most
recently a magnetometer instrument, which can be moved across the surface
of ground in order to attempt to locate underground storage tanks, pipelines,
and other subterranean utilities that may contain contamination. Unfortunately,
these devices are not foolproof. Very often when the site is located in
an urban setting anomalies are detected, such as reinforced concrete containing
barbed wire and improper readings may occur which appear to indicate the
presence of an underground storage tank when in fact it is simply underground
metal material. Therefore, recognizing that these techniques are not foolproof,
they do provide good preliminary indicators of the nature of underground
facilities at the site.
Many
Phase II investigations are done using simplified techniques, such as conducting
soil borings and using an Hnu detector, which is a screening device that
provides an indication of solvent and petroleum contamination. Geoprobe
wells, also known as temporary or mini wells, as opposed to permanent stainless
steel wells, are another technique that may be used to cut costs of investigation
and does not result in permanent wells being left at the site.
C.
Use Information to Save Cost & Integrate/Stagger Redevelopment with
Remediation.
A Brownfield project that I have recently worked on and completed successfully saved remediation costs by integrating remediation with the redevelopment of the property. Turning a former industrial auto body shop service garage and new car dealership 100,000 sq. ft. facility into a state of the art retail store, administrative office building, and day care center complex for a not-for-profit organization that had a limited budget, was a challenge in and of itself. Moreover, the one year redevelopment schedule, which included federally mandated deadlines, forced remediation to occur in conjunction with redevelopment. It is important to recognize that implementation of integration remediation and redevelopment is not an easy task. The coordination between the environmental contractors and the general contractors at the site had to be ongoing on a daily basis in order to successfully achieve the end product. For example, the general contractor at one point during the redevelopment project changed their plans and wanted to pour flowable fill to create a subfloor in one of the areas of the former car dealership site. As a result, the remediation contractor had to expedite their schedule by installing the PVC pipe necessary for the final installation of an air sparging soil paper extraction system before the flowable fill was poured. The end result was a successfully integrated remediation/redevelopment project, such that a not-for-profit organization saved significant costs by not having to subsequently tear up flooring to install a remediation system. The lessons learned on this project were that staggering remediation with a redevelopment project clearly saves costs and time but must be done in such a way that all of the contractors and subcontractors meet frequently and discuss beneficial integration techniques.