RTDF
The Remediation Technologies
Development Forum
Major Accomplishments (1992-2006)
The RTDF's
Mission
The purpose of the RTDF
is to identify what gov-
ernment and industry
can do together to devel-
op and improve the envi-
ronmental technologies
needed to address their
mutual cleanup prob-
lems in the safest, most
cost-effective manner.
The RTDF fosters public-
and private-sector part-
nerships to undertake
the research, develop-
ment, demonstration,
and evaluation efforts
needed to achieve com-
mon cleanup goals.
EPA 542-F-06-005
^"he U.S. Environmental Protection
Agency (EPA) established the
Remediation Technologies
Development Forum (RTDF) in 1992 to
enhance the development and applica-
tion of innovative hazardous waste char-
acterization and treatment technologies.
One of the RTDF's defining features is
that it fosters collaboration between the
public and private sectors. Eight self-
managed RTDF Action Teams have
formed over the years. Each has brought
together representatives from govern-
ment, industry, and academia who wish
to further develop and promote a specific
technology or address a specific environ-
mental problem area. Action Team mem-
bers provide the knowledge and the
resources (both in terms of monetary
contributions and in-kind services) that
are needed to conduct laboratory and
field demonstrations and to develop
reports, guidance documents, and train-
ing products related to their teams'topic
of interest. The purpose of this factsheet
is to highlight the RTDF Action Teams'
major accomplishments. Additional
details about each team's activities and
access to their technical reports and
other products are available through
.
The Bioremediation Consortium
Founded in 1993, the Bioremediation
Consortium promotes the development
of cost-effective in situ bioremediation
technologies that degrade chlorinated
solvents. Toward that end, the
Consortium has been actively testing
bioremedial approaches since 1995. For
example, the Consortium conducted
Phase I and Phase II demonstration proj-
ects to examine the efficacy of natural
attenuation, co-metabolic bioventing,
and accelerated anaerobic biodegrada-
tion at field sites located at Dover Air
Force Base in Delaware, Kelly Air Force
Base in Texas, Hill Air Force Base in Utah,
and the Bell Aerospace/Textron site in
New York. These demonstration projects,
all of which provide supporting evidence
of bioremediation's efficacy, have been
described in peer-reviewed publications
and technical presentations. In 2004, the
Consortium initiated Phase III of its
research activities when it joined forces
with a multinational team to launch the
In Situ Source Area Bioremediation proj-
ect (see
for details). This project, which is being
conducted in the United Kingdom and is
scheduled to be completed in 2008, is
designed to examine the efficacy of
accelerated anaerobic bioremediation as
an alternative treatment for source areas
contaminated with dense non-aqueous
phase liquids (DNAPLs). In addition to
field work, the Consortium is involved
with communications activities. For
example, the Consortium has partnered
with the Interstate Technology and
Regulatory Council (ITRC) to provide
training on bioremedial technologies,
and the industrial members of the
Consortium have collaborated with ITRC
and the Western Governors'Association
to publish a manual on the principles and
practices of natural attenuation.
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The Lasagna™ Partnership was formed in 1994 and it
completed its work in 1999. The Partnership—consist-
ing of Monsanto, DuPont, General Electric, EPA, the U.S.
Department of Energy (DOE), and others—developed a
technology that reduces contaminants like
trichloroethene (TCE) in deep clay formation soil in a
manner that is faster, less costly, and more effective
than traditional remedial approaches. This technology,
referred to as the Lasagna™ process, uses an electric
current to drive contaminants through a series of pla-
nar treatment zones of activated carbon and iron fil-
ings. The Partnership tested the technology in two
phases at DOE's Paducah Gaseous Diffusion Plant
(PGDP). The Phase I test showed that the technology
was capable of removing over 99 percent of TCE from a
test plot, and the Phase II test showed that the technol-
ogy could treat large quantities of DNAPL. Given the
success of these field studies, the technology earned
regulatory acceptance and was selected as a remedial
solution for a large contaminated cell at the PGDP site.
In addition, the Lasagna process won an "R&D 100"
Award from R&D Magazine in 1999. Licenses for use of
the technology are available through Monsanto, which
holds the patent.
The IINERT Soil-Metals Action Team was established in
1995 to develop, test, and gain regulatory acceptance
for soil remediation technologies that inactivate haz-
ardous metals in the field. The Action Team's crowning
achievement is the work that it performed at a lead-
contaminated site in Joplin, Missouri. At that site, the
Action Team hoped to show that applying reactive
materials to the soil would convert lead into a less toxic
form, reduce the contaminant's solubility and bioavail-
ability, and render it less toxic to humans and the envi-
ronment. To test their hypothesis, Team members
applied phosphorus to several test plots in 1997 and
collected samples from these plots (as well as from
control plots) over several years. They used various
methods to evaluate the impact of the treatments,
including analyzing soil and plant samples, performing
x-ray absorption fine-structure spectroscopy, and con-
ducting animal-dosing studies with immature pigs and
weaning rats. Interim results were presented in the
January 2004 edition of Environmental Science and
Technology. In summary, the results suggest that
adding phosphorus to lead-contaminated soil in the
field does indeed immobilize the contaminant and
reduce its bioavailability, a finding that supports the
idea that IINERT technologies have the potential to be
a viable and cost-effective alternative to traditional soil
cleanup methods.
I)
PRBs are in situ treatment zones of reactive materials
that degrade or immobilize contaminants as ground
water passes through them. The PRB Action Team
formed in 1995 to accelerate the development and reg-
ulatory acceptance of PRB technologies. Early in its
existence, the Action Team helped design a field study
for a zero-valent iron (ZVI) PRB at the Dover Air Force
Base and helped conduct research and a technology
evaluation for a PRB installed near Elizabeth City, North
Carolina. The Action Team also helped coordinate a tri-
agency research project (involving EPA, DOE, and the
Department of Defense) that involved evaluating the
long-term performance of PRBs at eight different sites
across the United States over a 4-year period. The
results from that study have fostered further develop-
ment of PRBs around the world. Stepping into the com-
munication arena, the Action Team has developed
reports that summarize the status of PRB technologies
and created a PRB site-profile database that is routinely
utilized by consultants, regulators, and others. The
database, which is available at , provides information
on more than 60 installed PRBs—more than half of
which represent full-scale applications. The Action
Team has also partnered with ITRC to develop guid-
ance documents and PRB training classes. As part of
that effort, on-site PRB training was delivered to all 10
EPA regional offices and several state environmental
offices between 1997 and 1999.
For the first 8 years of the PRB Action Team's existence,
the group focused on ZVI PRBs that remediate the dis-
solved phase of chlorinated solvent plumes. Starting in
2003, however, the Action Team expanded its scope to
encompass broader applications, such as using
microscale or nanoscale iron as a remedial agent, treat-
ing source zones, and using PRBs to address a broader
suite of contaminants. Currently, the Action Team is
participating in a field project at the Marine Base at
Parris Island, South Carolina. This project—a collabora-
tive effort involving EPA, GeoSyntec Consultants, the
National Aeronautics and Space Administration, and
the U.S. Navy—is designed to examine whether
nanoscale iron (delivered as an emulsion) can treat a
chlorinated-solvent source zone at a drycleaning site.
The Action Team's future goals will be discussed at an
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upcoming meeting, which is scheduled to take place in
Charleston, South Carolina, on October 11-12, 2006.
The Phytoremediation Action Team formed in 1997 to
promote the development and the regulatory accept-
ance of remedial processes that rely on plants. The fol-
lowing three subgroups have formed within the Action
Team:
• The Total (TPH) in
convened to evaluate whether vegetation
enhances the degradation of aged petroleum hydro-
carbons in soil. Subgroup members developed a
standardized test protocol, which called for the
installation of three types of vegetative treatments,
and applied the protocol at 13 field sites. Data col-
lected from 11 of the 13 sites have been analyzed,
and a final report is anticipated in 2006. The follow-
ing are offered as preliminary conclusions: (1) the
plants grew well in petroleum-impacted soils; (2) the
plants enhanced hydrocarbon degradation at two
sites; (3) the remedial impacts were more pro-
nounced at sites that had not previously experienced
extensive biodegradation or weathering; and (4) phy-
toremediation might be a viable treatment alterna-
tive to consider at sites where cost savings are need-
ed, a long treatment time is acceptable, and risk can
be effectively managed through vegetation.
• The Cower
formed to examine whether alter-
native covers (including vegetative covers) are viable
substitutes for more costly conventional landfill cov-
ers. Toward that end, the subgroup established
instrumented landfill cover research stations at 12
sites across the nation to test the performance of
alternative covers against conventional covers. Data
were collected at each of the demonstration sites for
up to 5 years. Based on the results, some site owners
chose to implement full-scale alternative covers, a
decision that is projected to save millions in installa-
tion and operation and maintenance costs. The sub-
group's results will be published in 2006. The report
will provide a large body of data on design, construc-
tion, and monitoring of landfill cover systems, and it
will advance the scientific, engineering, and regulato-
ry community's understanding of how and why land-
fill cover systems work or fail across a range of cli-
mates, designs, and soil conditions. The report will
also challenge some long-held assumptions about
the performance of conventional landfill covers.
The released a
paper entitled Evaluation of Phytoremediation for
Management of Chlorinated Solvents in Soil and
Groundwater in January 2005. The paper identifies a
variety of phytoremediation applications that can be
used to control, transform, or manage chlorinated
volatile organic compounds in soil and ground water.
It also provides insight on how to determine whether
phytoremediation is a viable option and how to
design and monitor pilot- and full-scale projects. See
for a
copy of the paper.
The Sediments Remediation Action Team formed in
1996 to address contaminated sediments—a medium
that is often difficult to assess and remediate, typically
impacted by more than one contaminant, and com-
monly associated with high remedial costs. When the
Action Team formed, members set out to promote the
development of cost-effective on-site sediments reme-
diation technologies. Over the years, the Action Team's
focus expanded to address assessment technologies
and frameworks for evaluating and managing contami-
nated sediments sites. Serving in a consulting capacity,
the Action Team has provided input on two Anacostia
River field projects: one designed to evaluate the effica-
cy of innovative capping methods and another to eval-
uate tools that identify potential areas of ground-water
impingement into surface water. In addition, a subset
of RTDF Action Team members developed a "weight-of-
evidence" approach to evaluate monitored natural
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recovery at contaminated sediments sites, a project
that culminated in the publication of five papers (see
).
Furthermore, in an effort to elevate the dialogue
about sediments-related issues, the Action Team held
several workshops between September 2000 and
February 2004 that addressed in situ treatment tech-
nologies, ground-water/surface-water interactions,
rapid assessment techniques, and beneficial reuse of
dredged materials. The workshops provided a valu-
able forum for presenting and discussing advances
in contaminated sediment risk management and
they facilitated the formation of funded research
collaborations.
mation about innovative NAPL characterization and
remediation methods and has produced a document
(entitled A Decision-Making Framework for Cleanup of
Sites Impacted with Light Non-Aqueous Phase Liquids
[LNAPL]) that presents a consensus-based approach to
LNAPL management. Alliance members have also
developed a 4-hour training program that provides
basic information about the way that LNAPLs behave
in the subsurface (see www.rtdf.org/public/napl/train-
ing).This training has been presented at numerous
locations across the country and delivered as an
Internet seminar on two occasions. The Alliance has
also published cost and performance case stuides for
two LNAPL-contaminated sites.
The NAPL Cleanup Alliance, which formed in 2001, is
comprised of individuals who share an interest in
evaluating remediation technologies and manage-
ment approaches for large-scale NAPL-contaminated
sites. Since its inception, the Alliance has shared infor-
The In Situ Flushing Action Team formed in 1997 and
disbanded in 1999. Within that timeframe, this group
held three meetings and succeeded in bringing
together experts from a variety of organizations who
were interested in furthering the development of in
situ flushing technologies.
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