Asserting
the Need for Improved
Airborne Chemical Agent
Monitoring Systems at U.S.
Chemical Weapons Stockpile Sites
Compiled by:
Chemical Weapons Working Group
PO Box 467 Berea, KY 40403
phone: (859) 986-7565
fax: (859) 986-2695
web: http://www.cwwg.org
April 2004
Introduction
Millions of U.S. citizens live within harmful range of old stockpiles of
chemical weapons, stored or being destroyed on eight military bases in Utah,
Oregon, Colorado, Kentucky, Alabama, Arkansas, Indiana and Maryland.
The chemical weapons are filled with lethal nerve agents VX and GB, and mustard,
or blistering, agents.
As the weapons are destroyed--whether by incineration or non-incineration
methods--one of the basic means of ensuring the well-being of citizens living
nearby these stockpiles is to monitor for the release of chemical agents as
completely, accurately and quickly as possible.
However, the Army’s current monitoring system is woefully inadequate, particularly
at its incinerator sites, where chemical agent can be released along with
tons of daily gaseous emissions through smokestacks. Chemical agents
can also be released from places other than incinerator smokestacks, including:
ash bins; rooms that are not sealed; and during movement of weapons from storage
igloos to the disposal facility.
This primer will clarify the inadequacies of existing monitoring systems
and the benefits that additional airborne chemical agent monitors offer.
I. Existing chemical agent monitoring systems
The Army relies primarily on two monitoring systems at its chemical weapons
stockpile sites to sample the air for mustard and nerve agents: Agent
Continuous Air Monitoring Systems (ACAMS) and Depot Area Air Monitoring Systems
(DAAMS). Both ACAMS and DAAMS monitors are positioned throughout chemical
weapons disposal facilities, including in the smokestacks of incinerators.
Additionally, DAAMS stations are also positioned outside of the plants, at
the perimeter of depot property.
ACAMS are very sensitive and can detect even trace levels of chemical agents.
ACAMS are connected to an alarm system, which sounds as soon as chemical agent
is detected. DAAMS are not connected to alarm systems. Rather,
DAAMS tubes collect air samples and are used to confirm readings from ACAMS.
Although the sensitivity of the ACAMS is definitely a plus, there are frequent
“false positive” readings. That is, when an ACAMS alarm sounds, it may
be because of chemical agent but it may also have resulted from some other
industrial chemical or interferent. In fact, the Army has said it is
common to have as many as 5000 such alarms every month. Such a high
number of false readings can lead to a “cry wolf” environment in which workers
disregard ACAMS alarms.
Since ACAMS can only be calibrated to monitor one type of chemical agent
at a time, they do not fully identify chemical emissions. For example,
an incident on March 30, 1998 at the Tooele, Utah incinerator resulted in
the release of an unidentified airborne chemical at a very high concentration.
The Army has insisted that the release was not chemical warfare agent, however
they cannot say what it was, or what the environmental or health impacts of
the release may have been.
The effectiveness of DAAMS tubes placed on the outside of chemical weapons
disposal plants is extremely limited. The distance between DAAMS stations
located at depot perimeters is great enough that a plume of chemical agent
could easily be missed. There are no alarms associated with these monitors,
and DAAMS tubes outside of the facilities are collected every 8 - 12 hours.
In February 2004 in Anniston, Alabama, a routine pull of DAAMS air sampling
tubes revealed a reading for VX nerve agent. No ACAMS alarm ever sounded,
and there is no way to know exactly when the detection occurred during the
12 hours prior to their being collected. The Army used all three DAAMS
tube samples to run the same confirmation test, leaving no other sample with
which a more detailed test could be conducted. All three tubes confirmed
VX agent. However, the source and concentrations of the confirmed agent readings
remain a mystery.
The Army does not monitor for toxic compounds such as PCBs, dioxins or heavy
metals except for a limited time during the trial burn phase. The concentrations
of these kinds of toxic emissions during routine incinerator operations is
unknown.
II. Workers at chemical weapons facilities have testified on the limitations
of the Army’s existing monitoring systems, and the failure of the Army to
fix the problems
Over the years, in state and federal court hearings in Utah and Oregon,
Army experts from chemical weapons incinerators have testified as to the
limitations of the ACAMS and DAAMS monitoring systems. Following is
a summary of issues raised by workers in Oregon district court in 2003:
- Chemical agent could be passing through incinerator smokestacks undetected.
This would explain how chemical agent monitors at an Army facility nearby
the Tooele, Utah chemical weapons incinerator repeatedly alarmed for the presence
of chemical agent at times when the incinerator next door was burning weapons;
but ceased to alarm when the incinerator was shut down.
- Chemical agent monitor verification tests done after the Utah incinerator
released chemical agent through the smokestack in May 2000, revealed only
a 40% and 75% confirmation rate.
- Processes for analyzing monitor readings are not accurate, and prone
to mistakes.
- Worker suggestions on how to improve monitoring systems (such as the
ways in which monitor samples are taken, and how monitor probes are used,
and how the systems are maintained) have been chronically ignored by both
the Army and its contractors.
It is important to note that workers who raised these issues internally
and publicly have been harassed, even by the Army’s attorney, right in the
courtroom! On August 13, 2003, under cross examination by Army attorney
Robert Foster, Mr. Tom Cramer, testifying to the inadequate monitoring
systems, was told that if he testified, his “head would be on the chopping
block.” This shows the Army’s willingness to quash those who
challenge the effectiveness of its monitors.
III. By adding advanced chemical agent monitoring systems to existing
monitors, a much-needed layer of protection would be provided to depot workers
and community members
A. What do we mean by improved or advanced chemical agent monitoring
systems?
One such advanced monitoring system, recommended by the National Research
Council, is an infrared monitoring system called the Open-Path Fourier Transform
Infrared (FTIR) Spectrometer. There are numerous companies producing
infrared technology and the CWWG does not endorse any one provider.
B. How does the technology work?
FTIR technology uses an infrared light beam, shot horizontally from an instrument
that looks like a telescope, to monitor the air for pollutants. The
system can be used to simultaneously monitor more than 50 chemicals and pollutants,
including chemical warfare agents. FTIR can be deployed in the open air surrounding
the chemical weapons storage and disposal facilities.
Infrared technology can “fingerprint” airborne gases generated by
chemical weapons incinerators, meaning it can monitor the emissions, and
accurately identify and measure the concentration of the chemicals it identifies.
It is a computer driven system, which means complete information on chemical
readings are available immediately on a computer screen. This information
can be downloaded, saved, and even used as a means to track changes in air
quality.
The technology can work effectively when infrared beams are configured in
a set of concentric grids surrounding the source of air pollutants (be it
an oil refinery, landfill, incinerator, etc.). For a chemical
weapons facility, this would mean having two grids of infrared beams surrounding
the facility, within the depot. Any chemical agent that crosses that
space would be identified in near real-time.
C. What are the advantages of using this technology in addition
to ACAMS and DAAMS?
For use at chemical weapons facilities, infrared technology would fill a
void by providing prompt, accurate detection of chemical agents outside the
facility. The benefits are huge:
- Airborne chemicals can be completely identified. Think of the
construction workers at the Umatilla, Oregon incinerator who in 1999 were
overcome by a chemical plume that has yet to be identified. This type
of system would take the guess work out of chemical identification, and help
predict where a chemical plume may be headed -- on the grounds of the depot
or over the perimeter and into our communities. That is an important
layer of protection for workers and community members.
- Infrared technology can provide continuous “real-time” monitoring,
meaning there is little or no delay in obtaining information about the emissions
in the area.
- Chemical agents can be quantified in “real-time” (around 15 seconds),
thereby providing better response capabilities.
- Workers at the facilities could respond to incidents much more safely
and effectively if they know exactly what chemicals were released and when.
They would not have to wait hours for results from DAAMS.
- Community members and agencies could view monitoring results from
computer terminals in public spaces. That means we don’t have to wait
for the Army or regulators to tell us what is going on at the facility, or
wait too long to find out about a problem.
IV. The National Research Council has for 10 years advised the
Army to use improved monitoring systems
Following are excerpts from a variety of NRC committee reports regarding
monitoring systems at chemical weapons facilities.
A. Review of Monitoring Activities Within the Army Chemical
Stockpile Disposal Program, 1994:
The major finding of the committee is that the monitoring system
currently in use at JACADS should be improved prior to employment at sites
in the continental United States....The Army should initiate a substantial
program to upgrade the monitoring systems for continental U.S. sites....The
Army should undertake whatever instrument development is necessary to ensure
that improved instrumentation is available to the chemical disposal program
is suitably rugged and operational forms....The Army should test and use new
monitoring instrumentation at JACADS before such instrumentation is employed
at Tooele (3-4).
The relatively slow response of the ACAMS means that, in the event of a
sudden release of agent, plant workers and the local population might be
exposed to a concentration of agent above acceptable levels (25).”
The sampling of the DAAMS range from one hour when detecting in the exhaust
stacks, to eight hours when monitoring plant work areas, and twelve hours
at the site perimeter. These times do not include analysis time.
The response time of DAAMS confirmation of ACAMS alarms requires about 15
to 20 minutes for sample tube collection, transportation to the laboratory,
and analysis (27).
Remote sensing or point source sampling, employing infrared spectroscopy
techniques, could be used to provide more rapid agent detection in plant work
areas. The instruments could operate continuously and have a response
time on the order of 10 seconds or less (31).
B. Recommendations for the Disposal of Chemical Agents and Munitions,
1994:
The ACAMS generates frequent false alarms because it cannot
adequately differentiate agent from other commonly encountered organic contaminants....Further,
when an alarm sounds, the retrieval and laboratory analysis of the DAAMS collection
tubes to verify conditions typically require half an hour or more (93).
C. Review of Systemization of TOCDF, 1996:
Both the Stockpile Committee and the Army recognize that new
monitoring technology will be required to reduce the desired response times
to a few seconds, rather than the few minutes possible with staggered ACAMS.
The Army has contracted for the development and demonstration of a Fourier
Transform Infrared (FTIR) multipass absorption technique, which should be
capable of real-time (> 1 second) detection of high agent release levels
(24).
D. Occupational Health and Workplace Monitoring at Chemical
Agent Disposal Facilities, 2001:
Current workplace monitoring systems for chemical agents are
generally adequate for normal operations but may have serious deficiencies
during accidents or departures from nominal operating conditions. Potential
employee exposures as a result of process upsets and/or accidents can be detected
by existing monitoring systems, but not in real time (29).
Advances in monitoring technology could reduce response times
and/or false positive alarm rates....This could reduce the risk of worker
exposure during both disposal and closure operations (29).
The Army should continue to pursue improvements in airborne agent monitoring,
including improved ACAMS technology (for multi-agent monitoring and lower
false alarm rates), and in methods for identifying interferents that cause
false alarms. It should also pursue new analytical techniques that could
lead to real-time agent detection (29).
E. Evaluation of Chemical Events at Army Chemical Agent
Disposal Facilities, 2002:
Relatively frequent false positive ACAMS alarms for airborne
agent and the lack of true real-time (<10 s) monitoring for airborne agent
have long been a concern of [NRC] committees assessing and examining the chemical
demilitarization program. Improvements in the sensitivity, specificity,
and time response of the ACAMS system and the development of an additional
airborne-agent monitoring technology robust at the parts-per-trillion level
have previously been recommended...Although [PMCD] has made some efforts to
develop better agent-monitoring technology, results to date have been disappointing
(52).
Recommendation 6a. To reduce the rate of false positive alarms for
both airborne and condensed-materials agent contamination, [PMCD] and the
relevant [DoD] research and development agencies...should invigorate and coordinate
efforts to develop chemical agent monitors with improved sensitivity, specificity,
and time response (52).
V. Adding advanced chemical agent monitoring systems is cost effective
and can be accomplished quickly without impacting the chemical weapons disposal
schedule
Infrared monitoring systems like FTIR are “off the shelf” technology, meaning
they are already being used widely by the military and in the private sector.
Examples of their use include:
Deployment
Location
Date
Sponsor
Iraq
Iraq
May 96
UNSCOM
Fenceline Monitoring
Aberdeen, MD
Aug 96
U.S. Army
Iraq
Iraq
Nov 96 UNSCOM
Iraq
Iraq
March 97 UNSCOM
Iraq
Iraq
Aug 97
UNSCOM
Iraq
Iraq
Sept 97 UNSCOM
Process Monitoring
Hill AFB, Utah Dec.
98 U.S. Air Force
Chemical Weapons Remediation Louisiana
July 99 U.S.
Corps of Engineers
Chemical Weapons Remediation Memphis
April 00 U.S.
Corps of Engineers
Chemical Weapons Remediation Ogden,
UT
Sept. 00 U.S.
Corps of Engineers
Chemical Weapons Remediation Anniston,
AL May 01
U.S. Corps of Engineers
Chemical Weapons Remediation Spring
Valley, MD June 01
U.S. Corps of Engineers
Chemical Weapons Remediation Anniston,
AL Apr 02
U.S. Corps of Engineers (Gamiles)
As noted in the chart above, the U.S. Army Corps of Engineers uses Op-FTIR
air monitors at remediation sites where buried chemical weapons are being
un-earthed. The system is used to warn workers, and nearby residents
in the event of a release. Releases have been accurately detected and
reported. It should be noted that Op-FTIR air monitoring was used
during the remediation of Pelham Range, at Fort McClellan, Alabama during
the Spring of 2002. As part of routine operation, intrusive work does
not commence unless the Op-FTIR air monitoring system is operational.
This is standard practice for all of the sites operated by the U.S. Army Corps
of Engineers when open-path air monitors are used.
The U.S. Army Soldier Biological and Chemical Command (SBCCOM) has published
a fact sheet on Op-FTIR monitors, which states
FTIR is used to perform air quality studies of industrial sites,
residential communities, landfills, and more. The technology can identify
all compounds present in a cloud of smoke emitted from an industrial plant,
and it can predict how a cloud of smoke will disperse due to wind speed.
This may be helpful as an emergency evacuation monitor to protect public health.
Open-path FTIR technology can also be used to determine air quality conditions
in a neighborhood setting; determine source-specific fenceline fugitive and
stack pollutant emission concentrations from selected industries; identify
compounds emitted from factories as they change processes, batches, or shifts;
study impurities from vehicles in traffic; perform perimeter monitoring around
remediation sites; determine ambient air quality pollutants in a Community
Bases Environmental protection area; and determine the effectiveness of a
water spray curtain on cloud concentrations.
and, “As required, FTIR would be an ideal tool for use by refineries, environmental
agencies, citizen groups, and state and local governments.”
Vendors for these systems estimate that the total cost of deploying infrared
monitoring systems at all chemical weapons disposal facilities could be in
the range of $16 million. That is a proverbial ‘drop in the bucket’
for the chemical weapons program, projected to cost over $25 billion, and
considering the safety benefits gained by facility managers, depot workers
and nearby community members.
Vendors also believe this technology could be deployed at chemical weapons
sites within months after funding is secured. Deploying these systems
does not require the facilities to shut down, so the chemical weapons destruction
schedule would not be impacted.
Works Cited
Chemical Materials Agency, Anniston Chemical Activity. “Monitoring
station detects VX at perimeter of Pelham Range; no emergency involved.”
Press release, March 3, 2004.
CWWG et al. vs. U.S. Department of the Army et al., US District Court District
of Utah. Case No. 2:96-CV-425(TC). Testimony, June 1999.
Fiori, Mario, Assistant Secretary of the Army, Installations and Environment
(former). Personal correspondance, December 2001.
Gamiles, Donald. CWWG et al. vs. U.S. Army et al. US District Court,
District of Columbia. Case No. 1:03CV00645. Affidavit, August 6, 2003.
GASP et al. vs. Oregon Environmental Quality Comission et al., US Circuit
Court, State of Oregon, County of Multnomah. Case No. 0009-09349.
Testimony, August 2003.
National Research Council. Evaluation of Chemical Events at Army
Chemical Agent Disposal Facilities. Washington, D.C.: National Academies
Press, 2002.
- - -. Occupational Health and Workplace Monitoring
at Chemical Agent Disposal Facilities. Washington, D.C.: National
Academies Press, 2001.
- - -. Recommendations for the Disposal of Chemical
Agents and Munitions. Washington, D.C.: National Academies
Press, 1994.
- - -. Review of Monitoring Activities Within the Army
Chemical Stockpile Disposal Program. Washington, D.C.: National
Academies Press, 1994.
- - -. Review of Systemization of TOCDF.
Washington, D.C.: National Academies Press, 1996.
U.S. Army SBCCOM. “Open Path Fourier Transform Infrared Spectrometer.”
Fact sheet, 2002. <http://www.sbccom.apgea.army.mil/RDA/ecbc/pdfs/ftir.pdf>.
- - -. “Monitoring at Chemical Agent Disposal Facilities.”
Fact sheet, 2003.
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