Brownfields to Green: A Proposal for Redevelopment of Brownfields Property for Natural Resource Value

Date01 October 2016
AuthorTara Disy Allden, David Goldman, Frank L. Hearne, and Bill Spinner
10-2016 NEWS & ANALYSIS 46 ELR 10855
Brownf‌ields to Green: A Proposal
for Redevelopment of Brownf‌ields
Property for Natural Resource Value
by Tara Disy Allden, David Goldman, Frank L. Hearne, and Bill Spinner
Tara Disy Allden is an Attorney/Environmental Scientist with Kimley-Horn in Columbia, South Carolina. David Goldman
is a Professional Geologist with Kimley-Horn in Jacksonville, Florida. Frank Hearne is an attorney with Mechanik Nuccio
Hearne & Wester, P.A., in Tampa, Florida. Bill Spinner is a Professional Geologist with Kimley-Horn in Tampa, Florida.
There a re many sites in the United States that are
blighted or undeveloped because of actual or per-
ceived environmental contamination. Often, these
sites are “orphans,” without existing owners having the
wherewithal to undertake responsibility for environmen-
tal remediation. Federal and state laws developed since the
1980s placed strict responsibility for remediation costs on
many types of parties associated with such sites, includ-
ing subsequent owners with no involvement in t he acts
that caused the contamination.1 Consequently, even where
such sites would otherwise be attractive for redevelopment,
the fea r of becoming responsible for expensive and time-
consuming remediation limited the willingness of buy-
ers, investors, lenders, and end-users of such property to
become involved.
As explained more fully below, recent legislation has
provided some mechanisms for incentives to under-
take control of certain types of sites and to accomplish
cleanup and redevelopment. One such approach consists of
“browneld” programs designed to facilitate remediation
of environmental issues and to encourage redevelopment
of t he properties. Federal a nd state browneld programs
provide incentives through a variety of grants, tax incen-
tives, liability protections, partial payment or reimburse-
ment of site-rehabilitation costs, and other methods. e
U.S. Environmental Protection Agency (EPA) estimates
that there are over 450,000 such sites in the country.2 is
is probably an underestimate.
1. Comprehensive Environmental Response, Compensation, and Liability
Act (CERCLA) 42 U.S.C. §§9601-9675, ELR S. CERCLA §§101-405
(among other things, CERLCA imposed cleanup liability on a broad range
of parties with very limited defenses).
2. U.S. EPA, Browneld Overview and Denition, http://www.epa.gov/brown-
elds/browneld-overview-and-denition (last updated Aug. 3, 2016).
Many browneld properties include areas of altered
aquatic ecosystems, such as wetlands and streams, or may
be located in the midst of important wetland or upland
habitat areas for protected plant and animal species. Of
course, during site-rehabilitation eorts, the protection
and restoration of such areas must be taken into account
and properly permitted, including federal, state, and local
approvals. For example, the removal of contaminated sedi-
ments in stream beds or adjacent wetlands is often a part of
site rehabilitation.3
Often, brownelds incentives are provided in con-
nection with redevelopment of the browneld site into a
variety of land uses, including commercial, retail, oce,
residential, a nd other end uses. We think, however, that
when the remediation of contaminated property is under-
taken in areas where natural resource components could
exist, signicant economic and ecological potential may be
available through the development of wetland mitigation
or conservation banks.4 Such banks would provide not only
additional environmental benets, but also an alternative
protable use for the remediated sites that could potentially
bring a new type of developer to the browneld program.
e policy goals of browneld redevelopment are con-
sistent with those of mitigation banking in that under
both programs. the environmentally impacted property is
reused in an eective manner that is benecial to the envi-
ronment, the economy, and society. is Comment pro-
vides some practical thoughts and discussion as to how the
two programs ca n be used together to maximize state and
3. Federal approval for remedial excavations in jurisdictional areas in some
cases may be simplied by the application of Nationwide Permits (NWPs),
including NWP 38, which applies to certain limited remediation projects,
as described in 33 C.F.R. §330 (2008). Many states have similar simplied
approvals for site rehabilitation of a certain scope; see, e.g., F. A.
C r. 62-330.635 (2013) (larger projects will require the full range of
dredge and ll permitting procedures and approvals).
4. e idea could apply to the development of mitigation banks for oset of
impacts involving a variety of habitats. For purposes of this discussion, we
will focus on aquatic resource mitigation banks.

   


Copyright © 2016 Environmental Law Institute®, Washington, DC. Reprinted with permission from ELR®, http://www.eli.org, 1-800-433-5120.

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