The EPA (Environmental Protection Agency)
defines a brownfield site as, "A site, or portion thereof, that has actual
or percieved contamination and an active potential for development or reuse."
These sites usually exist in an urban setting and have potential real estate
value or are surrounded by high value properties. There are presently
more than 450,000 brownfield sites in the United States. These sites
are waiting to be returned to some productive use. Many of these
areas accross the country were once used for industrial and commercial
purposes and have since been abandoned; some are contaminated. Because
lenders, investors, and developers may fear the liability issues of these
sites, they are more attracted to developing sites in pristine areas.
This leads to the abandonment of industrial facilities that create safety
and health risks for residents, and the numbers of brownfield sites continues
to increase.
The EPA recently established its Brownfields Technology
Support Center to ensure that decision makers are fully aware of the technologies
available for site assesment and cleanup of brownfield sites. The
EPA encourages the use of innovative, cost-effective technologies to characterize
and clean up contaminated sites.
Phytoremediation, or the cleanup of environmental
contamination using plants, offers an effective solution for the remediation
and reconstruction of these brownfield sites. Some of the phytoremedial
techniques that can be used in such a setting include phytoextraction,
phytovolatilization, phytodegredation, hydraulic control, vegetative caps,
and constructed wetlands. Phytoremediation might also be considered
in conjunction with natural attenuation at a brownfield site.
Phytoremediating brownfield sites may offer some
advantages that either chemical or mechanical treatments don't offer.
Some of these advantages are reduced costs, positive community acceptance,
aesthetic improvements of the site, and the ease of adaptability to redevelopment
plans. Since many brownfield sites contain low concentrations of
contaminants, and over large amounts of surface area, phytoremediation
can be a good alternative to either mechanical or chemical treatments.
Brownfield sites often contain a "collection" of contaminants. Plant
species used in phytoremediation can potentially treat a wide variety of
contaminants or families of contaminants (such as metals, organics, etc.).
Brownfield sites are also often located in an urban setting and phytoremediation
offers a solution through which soil remains in place during treatment
and is usable after treatment.
Although phytoremediation may be a promising way
to treat a brownfield site, there are a few limitations to using this method
of remediation. One of these is the time it can take for a phytoremidial
system to become effective. It often takes several growing seasons
before a phytoremediation setup to become completely effective. This
may prohibit the use of phytoremediation of sites where the time period
for cleanup is limited. Another limiting factor is root depth.
If the contaminant is buried deep within the soil, the roots of the plant
species will not be able to take up the contaminant. If the plants
can successfully uptake the pollutant, then a remediator must be aware
of the dangers involved with the translocation of the contaminant into
plant tissues. If the brownfield site typically attracts wildlife,
this may pose a threat when the animals feed on the phytoremediating plant
species. In techniques such as phytovolitilization, sometimes the
toxin that is released into the air can be more dangerous than its original
form, which can be a threat to both wildlife and humans. One more
limitation of phytoremediation is that it may not work on all types of
contaminants, and in this case another method of cleanup would be required.
Aspects of Plant Life in the
Phytoremediation of Brownfields
Landscape Architecture and
Phytoremediation
References