Characterization, Fate and Transport of Perchlorate and
TCE in a Large Sandy Drinking Water Aquifer
Mike Flack, ENSR International, Camarillo, CA
An
Overview of Perchlorate Cleanup Technologies Applied at
DoD Facilities
Bryan Harre, NFESC, US Navy, Port Hueneme, CA
Selection
of Remedial Technologies for Perchlorate Impacted Sites
Harry Van Den Berg, ENSR International, Camarillo,
CA
Perchlorate:
Groundwater Contamination and its Removal via Ion Exchange
Technology
Peter Ritchey, Calgon Carbon Corporation, Pittsburgh,
PA
Ex-Situ
Treatment of Perchlorate in Groundwater using Biological
Reactor
Dr. Paul Hatzinger, Shaw Environmental, Lawrenceville, NJ
Dr.
A. Paul Togna, William J. Guarini, Sam Frisch, Dave
Enegess, Paul. M. Sutton
A
State's Perspective on Perchlorate
Millie Garcie-Surrette, MA DEP, Lakeville, MA
Carol Rowan West, MA DEP
An
Overview of Perchlorate Cleanup Technologies Applied at
DoD Facilities
Bryan
Harre, NFESC, Port Hueneme, CA
Ammonium
perchlorate is manufactured for use as the oxidizer
component and primary ingredient in solid propellant for
rockets, missiles, fireworks, and some munitions.
Large-scale production began in the United States
in the mid-1940s. Because of its shelf life, it must be
periodically washed out of the country's missile and
rocket inventory and replaced with a fresh supply. Thus,
large volumes of the compound have been disposed of since
the 1940s.
Since
perchlorate was discovered in water supplies in
California, Nevada, and Arizona, much progress has been
made in developing treatment methods capable of removing
perchlorate from water. Over 65 perchlorate treatment
technology projects have been funded. Agencies funding
this research include the American Waterworks Association
Research Foundation, DOD’s Strategic Environmental
Research and Development Program (SERDP), DOD’s
Environmental Security Technology Certification Program (ESTCP),
the National Science Foundation, several universities,
water utilities, and Department of Defense activities.
Most of the attention has been directed at two
technologies: biological treatment and ion exchange.
In
the biological treatment process, microbes destroy
perchlorate by converting the perchlorate ion to oxygen
and chloride. In most cases, nutrients must be added to
sustain the microbes. Results for both in-situ and ex-situ
systems have reduced the perchlorate concentration to the
reporting limit of 4ppb. Barrier walls using biological
treatment have been implemented at full-scale at the Naval
Weapons Industrial Reserve Plant in McGregor, Texas. This
site has also implemented the injection of carbon sources
to form a biobarrier. ESTCP has funded and will be
performing three demonstrations of in-situ bioremediation
over the next two years.
In
ion exchange the perchlorate ion is replaced by chloride,
a chemically similar but nontoxic ion. Ion exchange
processes have been used in homes and businesses for water
softening for decades. Bench, pilot, and full-scale
studies have demonstrated that ion exchange systems can
reliably reduce perchlorate concentrations and are
approved for drinking water use in California. This
presentation will highlight the efforts of the DOD to
develop treatment technologies.
Selection
of Remedial Technologies for Perchlorate Impacted Sites
Harry Van Den Berg, PE, Sr. Program Manager, ENSR
International, 1220
Avenida Acaso, Camarillo,
CA 93012-8727, Tel: 805-388-3775 xt. 299, Fax:
805-388-3577, Email: hvandenberg@ensr.com
Perchlorate salts, such as ammonium, sodium and potassium
perchlorate are widely used as strong oxidizers in various
industries. Dissolution
of perchlorate salts yields the perchlorate anion, which
is highly stable and mobile in surface and groundwater
systems. Although
perchlorate is a powerful oxidizer when used in solid
form, it resists reduction by strong reducing agents when
dissolved in water due to unfavorable reaction kinetics.
Due to its mobility and stability in aqueous
environments, perchlorate can be found at large distances
from its release source.
Ongoing research of the inhibitory effects of
perchlorate on the uptake of iodide by the thyroid gland
combined with improvements in analytical detection methods
since 1997 have prompted the regulatory community to
propose increasingly stringent action levels. The current
action level in California 4 micrograms per liter, and may
possibly be set lower in the future. Several in-situ and
ex-situ treatment technologies have been developed, or are
currently under development that can address perchlorate
in soil and/or groundwater either via biological reduction
or removal via physical-chemical means.
Similar to other contaminants, the applicability,
effectiveness and cost of these technologies are highly
dependent upon site-specific conditions, such as
hydrogeology, geochemistry, depth to groundwater,
perchlorate distribution and the presence of other
contaminants. This
presentation will provide an overview of the criteria
affecting the selection process, descriptions of
established and innovative treatment technologies and
their typical applicability, and a presentation of
relative cost. Design and performance criteria for the technologies that
have achieved some degree of success in field applications
will be discussed. Test
or operational data will be presented for existing
systems, utilizing in-situ and ex-situ bioremediation,
reverse osmosis and selective anion exchange technologies.
Perchlorate:
Water Contamination and its Groundwater Removal via
Ion Exchange Technology
Peter
Ritchey, Calgon Carbon Corporation, P. O. Box 717
Pittsburgh, PA 15230-0717, Tel: 412-787-6859,
Fax: 412-787-4523,
Email: ritchey@calgoncarbon.com
Perchlorate
removal from groundwater via ion exchange has been
commercially accepted by the water treatment industry.
Three main options exist for perchlorate-removal
treatment systems: non-regenerable
fixed bed, regenerable fixed bed, and regenerable moving
bed.
The
non-regenerable fixed bed systems employ a
highly-selective anion exchange resin which continues to
remove perchlorate long after all other anionic species
have reached breakthrough due to the high selectivity of
the resin for perchlorate.
Several types of anionic resin are commercially
available for the type of system ranging from a simple SBA
Type 1 resin to the highly selective bifunctional resins. Calgon Carbon Corporation (CCC) has also modified
commercially-available resin in its CalMedia program to
lower operating costs for perchlorate treatment.
Currently, > 12,000 gpm of groundwater is being
treated with this technology with a 2-3 fold increase
expected in 2003.
The
regenerable moving bed system, CCC’s ISEP technology,
uses a more-easily regenerable acrylic resin with a brine
regeneration. The
ISEP technology has the advantage of maximizing the
performance of the system via reduced regenerate usage, a
reduced resin requirement, and steady-state operation.
Currently, 2,500 gpm of groundwater is treated via
this technology with
> 15,000 gpm of additional capacity expected to
come online in 2003.
The
regenerable fixed-bed systems can utilize two types of
resin. First,
acrylic regenerable resin can be utilized for perchlorate
removal and regenerated with a brine solution.
This option has not been commercialized due to
higher operating costs versus the ISEP system.
Second, a highly perchlorate selective resin such
as the Oak Ridge Bi-Quat resin can be utilized. This resin offers substantially longer run times between
regenerations and can be regenerated with a FeCl3/HCl
solution.
Advantages
and disadvantages between the three types of will be
presented.
Ex-situ
Treatment of Perchlorate in Groundwater using Biological
Reactors
Paul
B. Hatzinger, Ph.D., Shaw Environmental, Inc., Princeton
Research Center, 4100 Quakerbridge Rd., Lawrenceville, NJ
08648, Tel: 609-936-9300, Email: paul.hatzinger@shawgrp.com
Co-Authors:
Dr. A. Paul Togna, William J. Guarini, Sam Frisch, Dave
Enegess, Paul. M. Sutton
Ammonium
perchlorate (NH4ClO4) has been used
for several decades in the United States as an oxidizer in
solid propellants and explosives.
Past disposal practices of perchlorate-containing
fuels and a variety of military testing and training
activities have resulted in measurable perchlorate
contamination in water in at least 18 states, including
California, Massachusetts, Utah, Nevada, Maryland, and
Texas. Current estimates suggest that the drinking water
of as many as 15 million people may be contaminated with
perchlorate. Biological treatment represents the most
promising technology for economical remediation of
perchlorate in water. During the past few years, we
conducted laboratory pilot studies to evaluate the
effectiveness of biological fluidized bed reactors (FBRs)
for removing perchlorate from groundwater at several sites
across the United States. These sites varied widely in
geochemistry and perchlorate concentration. The treatment
of influent perchlorate levels ranging from greater than
400 mg/L to less than 100 mg/L have been evaluated. The
biological removal of co-contaminants, including chlorate,
nitrate, and nitramine explosives has also been examined.
A summary of the results from the pilot FBR studies will
be presented. Based on the data from field pilot studies,
three full-scale FBR systems have been constructed and are
in operation. These FBRs are currently treating more than
5 million gallons of groundwater per day from influent
perchlorate concentrations ranging from 2 to 35 mg/L to
effluent concentrations of less than the method reporting
limit of 4 mg/L. Two
additional full-scale systems are currently being designed
and fabricated for installation in 2004.
In addition, the FBR has recently been approved by
the California Department of Health Services (CDHS) as
part of a treatment system for the production of drinking
water from perchlorate-contaminated groundwater. The
performance and design parameters for full-scale FBR
systems and a comparison of these systems to other
biological reactor types will be presented.
A
State’s Perspective on Perchlorate
Millie
Garcia-Surette, MPH and Carol Rowan West, Massachusetts
Department of Environmental Protection
Ammonium
perchlorate is widely used as a component of propellants
for rockets, missiles, and fireworks.
It was discovered in surface and ground waters in
the United States in the late 1990s, typically around
military operations, defense contracting and manufacturing
facilities. Perchlorate
has been detected in ground water at the Massachusetts
Military Reservation.
In 2002, perchlorate was detected in the water
supply of the abutting town of Bourne.
In one instance, the Massachusetts Department of
Environmental Protection (DEP) has provided bottled water
to a private home impacted by the release.
Currently there are no established drinking water
standards for perchlorate. This presentation will review the ongoing response by the DEP
to the perchlorate release at the reservation.
The Department’s Bureau of Waste Site Cleanup has
been actively overseeing the site investigation and is
reviewing potential remediation strategies.
The Office of Research and Standards is developing
a reference dose based on studies that characterize the
endocrine disrupting effects of perchlorate on pregnant
women, their fetuses, children and individuals suffering
from hypothyroidism.
The reference dose will be based on a conservative
interpretation of animal and human studies in order to
ensure adequate protection of perchlorate-exposed
populations. The
reference dose will be used to establish ground water and
soil clean up standards under the Massachusetts
Contingency Plan for use at hazardous waste sites in
Massachusetts.
Actions taken by the U.S. EPA and other states on
this issue will be discussed, as well as the need to
respond in a timely fashion to perchlorate releases due to
the potentially severe health consequences.
Top
|