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                    <text>Item 10 Number

°1489

Author

Calcagni, John

Corporate Author

United States Air Force Occupational and Environmental

ROpOrt/ArtlOlO TltlO Summary Flyer to Alert Physicians to the Current
Herbicide Orange Debate

Journal/Book Title
Year

000

°

Month/Day
Color
Number of Images

[1

2

Descriptor Notes

Tuesday, May 15, 2001

Page 1489 of 1514

�Summary Flyer to Alert Physicians to the Current Herbicide Orange Debate
As a result of recent television and newspaper publicity on Herbicide
Orange, Air Force physicians may be asked by their patients to respond to
statements made by the media and to investigate symptoms described in the media
publicity. The programs and articles resulted from a number of claims filed by
veterans with the Veterans Administration alleging that present physical disorders are related to exposure to Herbicide Orange.

The following information

is intended to aid the physician 1n managing an active duty patient should the
individual present questions or allege symptoms.
Herbicide Orange (frequently referred to by the media as Agent Orange)
was an equal mixture' of two herbicides; 2, 4, 5~Trichlorophenoxyacetic acid
(2, 4, 5~T) and 2, 4~Dic.hlorophenoxyacetic acid (2, 4-0}. They have been used
worldwide in agriculture since 1947.

Human health hazards associated with

the use of these herbicides have been minimal and primarily related to selfingestion or gross misuse. Herbicide Orange was used extensively in Southeast
Asia from 1962 to 1969 to defoliate jungle vegetation and deprive the enemy of
a refuge.

In most instances, military personnel did not enter treated areas

until 4-6 weeks after treatment, thus greatly minimizing their chance of contracting or inhaling the herbicide. Air Force personnel most likely to have
been exposed were those involved in actual dedrumming and spraying operations.
A contaminant in the mixture was a substance called 2, 3, 7, 8Tetrachlorodibenzo-p-diox1n (TCOD, Dioxin). This highly toxic contaminant
was present in parts per million amounts in most batches of the herbicide.
Symptoms described by the media have been documented only in industrial

�accidents or gross overexposure. Immediate symptoms such as headache, eye
and skin irritation are the result of the herbicide per se and not dioxin (TCDD).
These symptons clear upon removal from exposure.

Central and peripheral

neuropathy, along with skeletal muscle damage have been described in very
high exposure to 2, 4-D alone. Other symptoms are believed to be related to
the dioxin (TCDD). Included are an acneiform rash with hyperpigmentation,
muscular pain, hepatotoxicity, nephrotoxicity, porphyria cutanea tarda,
hirsut.ism, peripheral neuropathy, hyperlipidemia and constitutional symptoms
such as anorexia, fatigue, lassitude, mental depression, and loss of libido.
There is no substantiated evidence for carcinogencity, teratogenicity,
mutagenicity or fetotoxicity in man.
It is emphasized, however, that in all cases displaying the symptoms
mentioned above, the estimated doses of TCDD received were much greater than
would be expected in personnel routinely working with Herbicide Orange. With
the exception of a few persistent cases of acne, there is no evidence for sustained illness except where permanent organ damage had occurred.

Furthermore,

there is no documentation of the development of adverse effects more than a frw
months after expsoure had ceased.
Personnel describing any of the above symptoms should be reassured that
it is unlikely that their present symptoms are related to Herbicide
Orange. They should be thoroughly evaluated to identify the etiology of the
symptoms and treated accordingly.
Further information, if needed, may be obtained by contacting Lt Col John
Calcagni, USAF, MC, at the USAF Occupational and Environmental Health Laboratory,
Brooks AFB, Texas. AUTOVON 240-2001, Commercial 512, 536-2001.

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&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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                  <text>&lt;p style="margin-top: -1em; line-height: 1.2em;"&gt;The Alvin L. Young Collection on Agent Orange comprises 120 linear feet and spans the late 1800s to 2005; however, the bulk of the coverage is from the 1960s to the 1980s and there are many undated items. The collection was donated to Special Collections of the National Agricultural Library in 1985 by Dr. Alvin L. Young (1942- ). Dr. Young developed the collection as he conducted extensive research on the military defoliant Agent Orange. The collection is in good condition and includes letters, memoranda, books, reports, press releases, journal and newspaper clippings, field logs and notebooks, newsletters, maps, booklets and pamphlets, photographs, memorabilia, and audiotapes of an interview with Dr. Young.&lt;/p&gt;&#13;
&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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              <text>1896</text>
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                <text>Shannon, Peter</text>
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                <text>Letter: to Barclay Shepard from Peter Shannon, 24 July 1981.</text>
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                    <text>Item ID Number

01336

Author

Smith, Pamela W.

Corporate Author

Science Policy Research Division, Library of Congress,

Report/Article TitlO Agent Orange: Veterans' Complaints Concerning
Exposure to Herbicides in South Vietnam, Issue Brief
Number IB80040

Journal/Book Title
Year

1982

Month/Day

APHI 20

Color

n

Number of Images
DeSOriptOU Notes

21

Date

originated: 09/06/79, Date Updated: 04/20/82.
Includes a table of military projects involving agents
orange, purple, pink, or green, with dates and
descriptions of projects. Also includes a table of the
signs, symptoms, and disorders reported after
occupational exposure to TCP, 2,4,5-T or TCDD. Item
gives an overview of background and policy analysis,
health effects, perseonnel exposure, veterans'
problems, Department of Defense efforts, health
studies, the Interagency Work Group and Agent Orange
Working Group, Congressional action, and legislation
and hearings

Thursday, May 03, 2001

Page 1336 of 1403

�AGENT ORANGE:

VETERANS' COMPLAINTS CONCERNING EXPOSURE
TO HERBICIDES IN SOUTH VIETNAM
ISSUE BRIEF NUMBER IB80040

AUTHOR:
Pamela W. Smith
Science Policy Research Division

THE LIBRARY OF CONGRESS
CONGRESSIONAL RESEARCH SERVICE
MAJOR ISSUES SYSTEM

DATE ORIGINATED 09/06/79
DATE UPDATED 04/20/82

FOR ADDITIONAL INFORMATION CALL 287-5700
0426

�CRS- 1

IB80040

UPDATE-04/20/82

ISSUE DEFINITION
From 1962 to 1971, the United States Air Force
(USAF) sprayed various
herbicide mixtures (chemicals that kill plants) in South Vietnam.
The
purpose of the spraying was to defoliate jungle growth to deprive the
Communist forces of ground cover, and to destroy enemy crops to restrict food
supplies. The most extensively used of these herbicide mixtures was known as
Agent Orange, a 50:50 mix of two common herbicides called 2,4,5-T and 2,4-D
(2,4,5-trichlorophenoxyacetic' acid and 2,4-dichlorophenoxyacetic acid).
A
third chemical present in the mixture in small amounts was TCDD, an
inevitable by-product of the manufacture of 2,4,5-T. This chemical, called
tetrachlorodibenzo-para-dioxin or simply "dioxin," is highly toxic
to
laboratory animals when administered in its pure form.
Acute
(short-term)
toxicity values in humans have not been established, although Gosselin et
al., in the 1976 edition of Clinical Toxicology of Commercial Products, puts
TCDD in a class of chemicals for which the "probable lethal dose" for humans
would be less than 5 mg/kg, or about 7 drops for a 150 Ib (70 kg) person.
CRS has been unable to locate any report of a human death from exposure to
pure TCDD.
The human health effect that has been most consistently
documented following exposure to small amounts of TCDD as a contaminant in
other compounds is a skin condition known as chloracne. There is other, less
consistent, evidence of damage to the liver and the nervous system in humans.
Extensive testing on laboratory animals has been done to determine possible
long-term effects of exposure to TCDD.
It can induce cancer in some strains
of rats and mice (carcinogenicity) , cause fetal death in several
species
(fetotoxicity)
and
birth
defects
in
developing
mouse
fetuses
(teratogenicity), but has been found not to cause genetic changes in
mammalian cells (mutagenicity). The American Medical Association's Council
on Scientific Affairs concluded that "there is no scientific evidence that
2,4-D, 2,4,5-T or TCDD has caused reproductive difficulties or hazards in the
human. "
Congressional interest was triggered by receipt of reports from Vietnam
veterans who believed they had been harmed by exposure to herbicides,
particularly Agent Orange. The 96th Congress held numerous hearings on the
use of herbicides in South Vietnam, and various initiatives to deal with the
problem were introduced. P.L. 96-151 was enacted to direct the Veterans
Administration (VA) to conduct an epidemiological study on Vietnam veterans
to determine whether there may be adverse human health effects
associated
with exposure to phenoxy herbicides and/or dioxin.
This study and other
studies planned will help elicit answers to the scientific questions posed by
the Veterans Administration in determining whether or not the veterans'
medical problems, allegedly due to exposure to Agent Orange and
associated
herbicides used in Vietnam, are compensable. Following recommendations made
by the Interagency Work Group on Phenoxy Herbicides
(now the Agent Orange
Working Group), legislation was introduced in the 97th Congress to expand the
scope of the VA's epidemiological study of the health effects of Agent Orange
to include other factors related to military
service in Vietnam.
The
legislation also allows veterans with medically certifiable conditions that
might possibly have been caused by exposure to Agent Orange to receive
medical care in VA facilities.
The bill (H.R. 3499) was considered by the
House and Senate in June 1981, put into final form in October, and signed by
the President Nov. 3, 1981.
Its title is the Veterans' Health Care,
Training, and -Small Business Loan Act of 1981 (P.L. 97-72).

�CRS- 2

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UPDATE-04/20/82

BACKGROUND AND POLICY ANALYSIS
History
During the summer of 1969,
the first reports of human birth defects
allegedly attributed to Agent Orange appeared in Vietnamese newspapers.
Based on these allegations and the results of a study sponsored by the
National Cancer Institute that showed that
2,4,5-T contaminated
with TCDD
caused birth defects in laboratory animals, the USAF stopped spraying 2,4,5-T
in South Vietnam by early 1971.
Although the Department of Defense maintains that only a limited number of
U.S. military personnel can be positively identified as having been exposed
to 2,4,5-T in South Vietnam (i.e., crews of aircraft that were used to spray
herbicides), it is theoretically possible that large numbers of both military
personnel (from the United States, South Vietnam, North Vietnam, Australia,
and New Zealand) and civilians (especially South Vietnamese peasants)
were
exposed to 2,4,5-T through the USAF spraying program. A growing number of
U.S. veterans who served in South Vietnam have begun to attribute the cause
of various chronic ailments which they are now experiencing
(especially
nervous disorders, cancers, and birth defects in their offspring) to exposure
to 2,4,5-T in South Vietnam, and many have filed claims with the VA for
compensation. The VA has not yet awarded compensation to veterans for any
claims related to 2,4,5-T exposure because of the lack of valid human data to
prove a cause and effect relationship between exposure to 2,4,5-T and/or TCDD
and specific health effects (except for chloracne).
TCDD Contamination
The industrial production "of 2,4,5-T always
results in some
TCDD
contamination although TCDD levels can be reduced to about 0.01
parts per
million (ppm) with current technology. Because it was not widely
recognized
until the late 1960s that 2,4,5-T could contain hazardous
amounts of TCDD,
manufacturers did not start reducing the level of TCDD in 2,4,5-T until the
USAF was already winding down its herbicide spraying program.
The average
TCDD levels in the 2,4,5-T - containing
herbicide mixtures used in South
Vietnam were approximately
2 ppm in Agent Orange
(which accounted for
approximately 96% of the 2,4,5-T used in South Vietnam), approximately
32.8
ppm in Agent Purple, and 65.6 ppm in Agents Pink and Green
(Agents Purple,
Pink, and Green contained the remaining 2,4,5-T used in South Vietnam).
The
herbicides procured by the USAF were code named after the colored band that
was placed around each 55 gallon drum in order to identify the contents.
/

Health Effects —

Animal Data

Although TCDD is well established as one of the most toxic chemicals known
for acute (short-term) effects, there is no consensus in the
scientific
community over the -Chronic (long-term) effects on humans of exposure to low
levels of TCDD (such as those levels found in the herbicides used in South
Vietnam) .
Statistically

significant

animal

experiments

have

demonstrated

that

�CRS- 3

IB80040

UPDATE-04/20/82

2,4,5-T containing low levels of TCDD and/or TCDD alone have caused various
tumors in mice and rats. A recently-released National Toxicology Program
bioassay of TCDD confirms these earlier reports that TCDD is carcinogenic in
some laboratory animals. Thymic atrophy (without a corresponding loss in
immune function) and severe weight loss have been observed in many species
after TCDD exposure. In some species, acute exposure to TCDD can cause liver
damage. Birth defects such as cleft palate and kidney abnormalities have
been reported in baby mice when the mothers were exposed during pregnancy. A
National Toxicology Program animal study of male reproductive effects of
exposure to TCDD, however, has failed to reveal a statistically
significant
increase in reproductive abnormalities
in TCDD-exposed animals or birth
defects in the TCDD-exposed male animals' offspring. Although there is some
experimental evidence that TCDD may cause mutations (changes in the cell's
genetic material that may produce birth defects in as-yet-unconceived
offspring), these experiments have been few, they have been done mainly on
non-mammalian species or in vitro (in test tubes), and they have basically
been inconclusive.
Some investigators feel that humans are less sensitive than animals to the
toxic effects of TCDD. There is wide variation of" responses to TCDD among
different species, and the mechanisms of its toxicity and metabolism are not
understood. More work needs to be done to clarify whether human exposure to
TCDD can produce the same health effects with the same potency as those
observed in animal studies.
Health Effects. -- Human.TData.
If a cause and effect relationship is to be scientifically
established
between human exposure to a chemical and chronic health effects, a study
which meets the following minimum criteria must be conducted to prove that
such a relationship exists: a group of people (the "study group") must be
identified that has already been exposed to the chemical under study (it
would help to know the level of exposure); this study group must be large
enough to detect chronic effects with statistical significance
(to find an
effect that occurred in 1 out of 100 people, one would need to examine at
least 100 people); a control group must be found that ideally would differ
from the study group only by never having been exposed to the chemical under
study (thus, any differences in chronic health effects between the study and
control groups could be attributed only to exposure to the chemical under
study); and, due to the long latency period for many chronic effects, the
study and control groups must be followed for as many years after exposure as
it takes for the chronic effects to show up
(i.e., in
carcinogenicity
studies, subjects must be followed for a minimum of 10 to 20 years after
exposure to the suspect carcinogen). These exacting criteria are not met by
most of the studies that have explored the relationship
between human
exposure to TCDD and/or 2,4,5,-T and subsequent health effects.
Only for
chloracne has such a cause and effect relationship been well established.
Workers who have been exposed to TCDD and/or
2,4,5-T in industrial
explosions or who have had other occupational exposure are frequently found
to have a skin condition known as chloracne — which resembles normal acne
except that it is caused by chemical exposure.
Chloracne can appear from
weeks to months after initial exposure and while mild cases (blackheads)
may
clear in a matter of months, severe cases (inflammatory lesions and
scars)
may last up to 30 years after exposure has ceased.
While the severity of
chloracne is not thought to correlate precisely with the intensity or
duration of exposure to TCDD and/or
2,4,5-T, chloracne is associated
so

�CRS- 4

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UPDATE-04/2'0/82

closely with exposure that some scientists argue that patients who have not
exhibited chloracne are unlikely to have suffered other toxic effects of TCDD
and/or 2,4,5-T exposure.
Studies of these exposed workers have also indicated a variety of other
health problems. For example, the United States Air Force Technical Report
on the Toxicology, Environmental Fate, and Human Risk of Herbicide Orange and
its associated Dioxin (1978) listed a number of symptoms, signs, or disorders
that had been reported after occupational exposure to TCP
(trichlorophenol,
2,4,5-T's precursor), 2,4,5-T, or TCDD
(see Appendix).
As noted, these
studies, which reported symptoms associated with human exposure to dioxin,
were not conducted in such a way as to prove a cause-and-effect relationship
between exposure to TCDD and/or 2,4,5-T and any of these effects, but they
may be indicative of such a relationship.
Several of the above studies have focused on investigating
cancer
rates
among exposed workers. These studies do not show a clear
cause/effect
relationship between carcinogenicity associated with exposure to TCDD
and/or
2,4,5-T because very few exposed workers (with the exception
of those in
Nitro, West Virginia) have been followed for more than ten years (the latency
period for most cancers being 15 to 40 years after exposure) and the results
have been equivocal.
However, they support a continuing suspicion and
indicate a need for further study.
When the scientific
panel of the
Interagency Work Group on Phenoxy Herbicides reviewed five research papers by
European scientists, it concluded that despite the studies' limitations, they
do "show a correlation between exposure to phenoxy acid herbicides and an
increased risk of some forms of cancer." A soft-tissue "sarcoma study has
been proposed that will be conducted jointly by the Armed Forces Institute of
Pathology and the National Cancer Institute.
Studies that have been conducted in non-industrial settings have not been
able to prove a cause and effect relationship between exposure to TCDD and/or
2,4,5-T and specific health effects. The National Academy of Sciences
(NAS)
was directed by Congress P.L. 91-441, sec. 506 (c) to conduct a study on the
effects of herbicides in South Vietnam, including health effects.
This NAS
study, as well as at least three other similar studies that were conducted in
South Vietnam during the early 1970s, were unable to find adequate data upon
which to reach any conclusions concerning a causal effect between exposure to
herbicides and any health effects, including birth defects.
An explosion in a Hoffman-LaRoche chemical plant in Seveso, Italy in July
1976 caused thousands of people to be exposed to varying doses of TCDD as a
toxic cloud drifted across the Italian countryside in a cone-shaped pattern
about a mile long and half a mile wide. Some 5400 people lived in the two
zones most directly affected, with an additional
40,000 people
potentially
exposed. Animals began to die 2 to 3 days after the incident with over 1,100
animals killed by direct exposure to TCDD. Over 700 people were
evacuated
from their homes. Chloracne was reported in 187 people, mostly children, and
it tended to heal rapidly. Long-term human health effects of exposure to
TCDD at Seveso are still being studied.
Preliminary
findings reported in
1979 by Hoffman-LaRoche revealed that Seveso residents had suffered liver
damage but that there was no permanent breakdown
in liver function.
They
also reported that rates of spontaneous abortions, fetal malformations,
congenital defects, chromosome aberrations, reactions to infectious
disease,
and morbidity and mortality were not affected by TCDD exposure. As reported
by the American Medical Association's Council on Scientific
Affairs,
"The
most recent progress report on the long-term epidemiologic survey of the
residents of the Seveso area emphasizes the preliminary
nature of their

�. .

CRS- 5

IB80040

UPDATE-04/20/82

findings and reiterates the conclusions of prior investigators.
Except for
the skin, no organs or body functions were impaired.
No derangement of
gestation, no fetal lethality and loss, no gross malformations-, no growth
retardation at term and no cytogenetic abnormalities have yet occurred."
Health effects of domestic use of 2,4,5-T have been
kept
under
surveillance by various Government agencies for some years.
In April
1970,
the Departments of Agriculture, Interior, and Health, Education and Welfare
jointly announced the suspension of certain uses of 2,4,5-T following studies
indicating that it was a teratogen.
On Apr. 21, 1978,
the Environmental
Protection Agency (EPA) issued a Rebuttable Presumption Against
Registration
(RPAR) on 2,4,5-T, finding that the herbicide had exceeded certain
risk
criteria and inviting comments from interested parties. The RPAR was based
on toxicological data from animal
studies showing a correlation between
2,4,5-T exposure and cancer and birth defects. One of the comments received
was from Alsea, Oregon, claiming
that there was a high incidence of
miscarriage among area women following spraying of the local forests with
2,4,5-T. EPA investigated this claim and reported its conclusion that the
incidence of spontaneous abortion over a 6-year period in Alsea was higher
than the rates in two other regions of Oregon that had lower rates of 2,4,5-T
usage. Based on the combination of evidence from the animal studies and the
Alsea study, EPA announced the emergency suspension of the domestic use of
2,4,5-T on forests, pastures, and rights-of-way on Feb. 28, 1979.
The Alsea
study has been criticized on methodological grounds by various groups, and
its results are rejected by a number of writers.
EPA hearings
on
cancellation of 2,4,5-T began in June 1979.
On Mar. 24, 1981,
EPA and Dow
Chemical requested a recess in the hearing to discuss the possiblity of
negotiating a settlement.
The recess has been
extended
while
the
negotiations continue.
Herbicide Spraying in Vietnam
Approximately 107 million pounds of herbicides were aerially disseminated
on 6 million acres of South Vietnam (an area about the size of Connecticut)
from January 1962 to February 1971.
Approximately 276,000 gallons of Agents
Green, Pink, and Purple were sprayed in South Vietnam prior to 1965 when they
were replaced by Agent Orange. Approximately 11 million
gallo.ns of Agent
Orange were then sprayed in South Vietnam — making it the most widely used
herbicide of the war. Ninety percent of Agent Orange was sprayed on 2.9
million acres of inland forests and mangrove forests for defoliation, 8% was
sprayed on enemy crops for crop destruction, and the remaining 2% was sprayed
around base perimeters, cache sites, waterways, and communications lines.
The Air Force continued to operate its herbicide spraying program in South
Vietnam until the late 1960s when the National Cancer
Institute
released
results of an animal bioassay that showed 2,4,5-T to be teratogenic
and/or
fetotoxic in rodents, and newspapers in South Vietnam started reporting
health problems among the rural populations who had been exposed to such
herbicides. The Air Force first restricted the use of Agent Orange to areas
remote from populations
in October of 1969,
then stopped all airplane
spraying of Agent Orange in early 1970 and all helicopter spraying of Agent
Orange by 1971.
All remaining herbicide stocks were gathered and stored at
either Gulfport, Mississippi or Johnston Island in the Pacific until they
were incinerated at sea in 1977.
The following
table outlines
major military projects involving
handling of Agents Orange, Purple, Pink, or Green in South Vietnam.

the

�CRS-6

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UPDATE-04/2'0/82

MILITARY PROJECTS INVOLVING AGENTS ORANGE, PURPLE, PINK, OR GREEN
PROJECT

DATES

DESCRIPTION

AGILE

1960-68

Selection of herbicides., and development
and evaluation of defoliation techniques.

RANCH HAND

1962-71

Aerial spraying of herbicides in South
Vietnam.

Various USAF
Projects

1962-70

'Development and testing of aerial spray
equipment.

PACER IVY

1971

Air Force
Logistics
Command Project

1972-77

PACER HO

1977

Redrumming and movement of surplus
herbicide from South Vietnam to
Johnston Island.
Maintenance of herbicide inventory
and research on options for disposal.
Dedrumming of herbicide inventory and
at-sea incineration of Agent Orange.

Each of these projects involved some human exposure to the herbicide
2,4,5-T and its contaminant, TCDD. The difficulty lies in
determining who may have been exposed and at what level.

�CRS-7

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UPDATE-04/20/82

Personnel Exposed
The early trials that were conducted in South Vietnam to improve aircraft
spray systems (1960 to early 1962) were conducted by USAF personnel assigned
to the Special Aerial Spray Flight Division, Langley AFB, Va. (USAF personnel
engaged in the herbicide program did not receive permanent change of station
assignments to South Vietnam until 1964 -- thus making it more difficult to
track personnel who may have been exposed to herbicides). During late
1962
and early 1963, the Crops Division at Fort Detrick and the USAF Armament
Laboratory at Eglin Air Force Base, Florida were involved in efforts to
provide improvements in spray system components in support of Operation RANCH
HAND.
Most of the personnel involved in the actual handling of herbicide drums
were Vietnamese.
However, a USAF flight mechanic or crew chief was
responsible for ensuring that the aircraft were properly loaded and that the
spray systems were functional. Each herbicide aircrew consisted of a pilot
and a copilot (both usually
officers) and a flight mechanic/spray unit
operator (usually enlisted). The aircrews were frequently joined by South
Vietnamese and U.S. observers. As noted in a USAF report, "within the
aircraft, it was not uncommon to have herbicide leakage from around the
numerous hose connections joining the spray tank and pumps with the wing and
aft spray booms. In hot weather, the odor of herbicide within the aircraft
was decidedly noticeable."
The USAF has data on 6,542 herbicide spraying missions that took place
between August 1965 and February 1971 on its "HERBS" computer tape.
These
data were compiled on a mission-by-mission basis from reports and files in
various commands and offices in South Vietnam and the United States.
The
HERBS tape contains the following data for each mission:
date; mission
number; location; province and UTM coordinates; type of herbicide (basically,
Agents Orange, White, or Blue); quantity of herbicide; area covered; purpose
of mission (defoliation, crop destruction, etc.); and type of aircraft (plane
or helicopter). The NAS used the HERBS tape in its evaluation of the effects
of herbicides on South Vietnam. After evaluating the HERBS data, the NAS
concluded that the HERBS tape accounted for approximately 86% of all
herbicide operations in South Vietnam and that "despite certain
recognized
deficiencies," the HERBS tape is "a reliable source for an assessment of the
major part of the herbicide operation in South Vietnam" and "is the best and
in fact the only available comprehensive computation of the major part of the
herbicide operations conducted in the Vietnam war."
When the DOD suspended all use of 2,4,5-T in South Vietnam, the USAF was
left with an inventory of 2.22 million gallons of unused Agent Orange
(1.37
million gallons which had been shipped to South Vietnam and 0.85
million
gallons which were waiting to be shipped at the Naval Construction Battalion
Center at Gulfport, Mississippi). In April 1972, the 1.37 million gallons of
Agent Orange were moved from South Vietnam to Johnston Island in the Pacific
Ocean for storage. The total amount of TCDD in the remaining Agent Orange
stock was approximately 44.1
pounds.
Problems began to arise in both
locations as drums reportedly began to leak and the USAF expressed concern
over further leakage problems that could occur if a tornado hit the
Mississippi site or if a typhoon hit the Pacific site.
After exploring a
number of options, the USAF decided to dispose of the Agent Orange by burning
it at high temperatures at sea on the Dutch incinerator
ship named the
"Vulcanus." The Agent Orange was drained from the drums at each site and

�CRS- 8

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UPDATE-04/20/82

transferred to the Vulcanus. The empty drums were then rinsed with diesel
fuel and crushed. The rinse fluid was combined with the Agent Orange for
incineration at sea. A total of 15,480 drums of Agent Orange were processed
at the Mississippi site between May 24, 1977, and June 10, 1977, by
approximately 110 USAF officers/technicians from the five Air Logistics
Centers of the Air Force Logistics Command (located at Kelly AFB Texas;
Hill
AFB, Utah; Warner Robbins AFB, Georgia; Tinker AFB, Oklahoma; and McCellan
AFB, California). A total of 24,795 drums of Agent Orange were processed at
the Johnston Island site between July 27, 1977,
and Aug. 23,
1977.
Approximately 100 civilian employees hired by a contractor
performed the
dedrumming process. At both the Johnston Island and Mississippi
sites,
workers were provided with daily changes of work clothes and some with
protective clothing. The Agent Orange was incinerated at sea in the period
from July to September 1977.
Results of industrial hygiene studies conducted
at the time of the disposal operation by the U.S. Air Force
(Gulfport)
and
the Battelle Memorial Institute
(Johnston
Island) revealed no immediate
adverse health effects among the personnel involved in the operation.
Department of Defense, Efforts
The USAF has stated that it can now identify 1,264
servicemen who were
directly exposed to Agent Orange as they handled herbicide., containers and
flew spraying missions in South Vietnam.
The Air Force has initiated a
health effects study of Air Force personnel involved in operation
"Ranch
Hand," who sprayed Agent Orange in Vietnam. The Department of Defense
(DOD)
believes that these individuals had at least 1000
ti-mes more exposure .to
Agent Orange than the average ground troops. The epidemiological study will
try to determine whether a causal relationship
can be established
between
exposure to the 2,4-D/2,4,5-T mixture and long-term health effects. Although
the study was originally scheduled to begin in October 1979, peer review of
its protocols forced delays.
The University of Texas School
of Public
Health, the U.S. Air Force Scientific Advisory Board and the Armed Forces
Epidemiological Board reviewed the
study
protocols
and
recommended
modifications. Then the Air Force asked the National
Academy of Sciences
(NAS) to review the protocols.
On May 6, 1980,
the NAS
announced
recommendations that the scope and duration of the study be expanded to
increase the likelihood of obtaining definitive data.
NAS also expressed
concern about the public perception of credibility
and impartiality
of a
study conducted internally by the Air Force. The Interagency Work Group's
Scientific Panel, however, has recommended that the study, as designed by the
Air Force, be conducted because, despite its limitations,
it provides "a
focus as to the type of health effects that may possibly
occur in other
(ground troop) personnel."
The Ranch Hand study is proceeding in several phases and will continue for
20 years.
The first phase consists
of a detailed
medical
history
questionnaire, which has been administered to the Ranch Handers in their
homes by trained interviewers from Louis Harris and Associates.
A carefully
matched control group, selected from military records held by the Air Force,
has also been interviewed.
The first data from the questionnaire
should be
available by mid-summer 1982.
Also underway is the second phase of the
study, a 3-day series of physical examinations, including a battery of
psychological tests, which will be given to both the study group and the
controls. The contractor for this phase is Kelsey-Seabold of Houston.
The
exams are scheduled to be completed by September 1982,
with
preliminary
findings available 2 to 3 months later. Follow-up exams will be conducted at
1, 3, 5, 10, and 20 years. A mortality analysis on the Ranch Hand group is

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in progress at the Air Force School of Aerospace Medicine, with data
anticipated around August 1982, and a mortality tracking program will be
continued throughout the study. Information on the health status of the
veterans, as shown by the questionnaires and the physical examinations, will
provide data for a morbidity analysis.
Many of the veterans who have filed claims with the VA for compensation
for health effects caused by exposure to TCDD in South Vietnam did not hold
jobs that caused direct exposure to 2,4,5-T. They claim that their exposure
occurred indirectly either by being sprayed with overhead planes
(although
substances other than herbicides were also sprayed from planes) or by being
exposed to 2,4,5-T in the environment.
According to the DOD, military
personnel did not usually enter areas sprayed with Agent Orange until 4 to 6
weeks after treatment.
However, a recent General
Accounting
Office
investigation concluded that a large number of Marines in the I Corps section
of Vietnam from 1966-1969 were in, or close to, areas sprayed with Agent
Orange on both the day of spraying and within 4 weeks afterward.
Some Army
units were also close to Agent Orange spraying.
The Department of Defense has recently made progress in identifying ground
troops that may have been exposed to Agent Orange. Two Army and one Marine
battalion - 31st Engineer Battalion, 2050 troops; 1st Squadron, 9th Calvary
(Air Mobil), 2300 troops and 3rd Battalion, 1st Marines, have been identified
as being in areas of Agent Orange operations.
Exact numbers, locations, and
identities of individuals who may have been sprayed are impossible to
determine.
Veterans' Problems and Veterans^ .Administration E_f_fO'rts
The first reports of veterans' concerns over health effects of exposure to
2,4,5-T began to appear in late 1977 and early 1978, following media coverage
of several veterans' claims.
Veterans have associated a number of illnesses
with exposure to 2,4,5-T, including skin conditions, fatague, nervousness,
numbness in extremities, vision and/or hearing impairments, birth d'efects in
offspring, reduced libido, miscarriages, impotency, respiratory problems,
gastro-intestinal tract disturbances, and various cancers, as well as a
variety of other illnesses.
As of Apr. 1, 1982, the VA had received 13064 claims for damage reportedly
related to in-service exposure to herbicides? 2986 claims have been made due
only to exposure to the herbicides and not for any specific condition; 10078
claims have been filed for specific conditions related to herbicide exposure,
but 3469 of these have not had the diagnosis con-firmed by medical
authority.
Of the 6609 claims with a confirmed diagnosis, 923 (13.7%) have been allowed
for reasons other than Agent Orange exposures and 5686
(86.3%) have been
denied. Approximately 93% or 858 of the total 923 claims allowed were for
service-connected skin conditions, and the remaining 7% or 65 claims were
allowed for cancer, psychiatric and neurological
conditions, and various
other miscellaneous disabilities. The 5686 claims denied fall into the
following categories (many claims have more than one claimed diagnosis): 3055
for various skin conditions; 2335 for nervousness, headache, or fatigue; 886
for paralysis
or numbness; 751 for gastro-intestinal
or genito-urinary
conditions; 399 for various malignancies; 356 for impaired sexual activity;
394 for eye, ear, nose, and throat conditions; 274 for lung conditions; 227
for cardiovascular conditions; and 137 for miscellaneous conditions. The VA
has not awarded compensation for the claims of chronic illnesses
related to
Agent Orange exposure because of the lack of valid human data to prove a

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cause and effect relationship between exposure to a 2,4,5-T/2,4-D mixture
and/or TCDD and specific chronic health effects. Previously, the difficulty
of determining which veterans' were or were not exposed to Agent Orange was
also a factor in denying compensation, but more recently the VA has conceded
exposure for all veterans who were in Vietnam.
The VA is maintaining a registry of all Vietnam veterans who have come to
VA hospitals and health care facilities expressing concern about possible
herbicide-related health problems. Each such veteran, whether experiencing
any health problems or not, is given a physical examination; currently, some
2700-2800 exams are being conducted each month. Data from all the exams is
being computerized into a central Agent Orange Registry in addition to the
individual records being maintained at the local VA facilities.
As of Mar.
25, 1982, 81,670 veterans had received the initial exam, and about 61,000 of
the records had been coded into the computer. Information from the registry
is being analyzed to determine if the veterans have an increased rate of any
particular diseases.
Thus far, nothing unusual or unexpected has turned up.
Treatment of any health problems uncovered by the exams is handled under
normal VA procedures regarding service-connection, ability to pay for medical
care, etc., with the exception that special guidelines have been issued for
the handling of conditions possibly related to Agent orange.
In the Federal
Register of Dec. 2, 1981,
pursuant to Public Law 97-72, the VA issued
guidelines for use by its physicians to "assist them in making determinations
in individual cases as to whether a disability
may have been caused" by
exposure to Agent Orange. Even though treatment may be given for some
conditions, the VA specified that "In accordance with congressional intent, a
determination to furnish care under this authority does not establish that
the condition for which medical care is provided is service-connected" for
purposes of compensation or vocational rehabilitation eligibility.
Three additional VA activities on Agent Orange include participation
in
the tissue registry, the Chloracne Task Force, and investigations into TCDD
residues in body fat tissue of veterans. When VA facilities perform surgery
or autopsies on Vietnam veterans, tissue samples are taken and sent to the
Armed Forces Institute of Pathology where a special tissue registry is being
maintained. Examination of approximately 800 specimens has so far shown no
significant clustering of tumors or other particular
disease features. The
Chloracne Task Force was established in response to a congressional request
to sift out those cases of skin conditions that either resemble or are truly
Chloracne. Those veterans whose medical records show a definite possibility
of Chloracne will be invited to come to non-VA clinics for re-examination
by
dermatologists who have an expert knowledge of the disease.
The VA has
conducted a study to determine if TCDD can be detected in the body fat
tissues of Vietnam veterans at any higher levels than in veterans who were
not in Vietnam. Dioxin in body fat is measured in parts per trillion, levels
which are at the technological limits of available
detection methods.
The
test requires surgical removal of tissue from the abdomen and chemical
analysis of the sample on
gas
chromatography/high
resolution
mass
spectrometry instruments. The results of the study were inconclusive, and
the VA has decided that the reliability of the procedure is not sufficient to
warran-t its use in attempting to verify dioxin exposure.
An additional
problem is that dioxin contamination
is so ubiquitous (from domestic
herbicide use and from its formation in municipal incinerators) that it may
likely be found in everyone's fat tissue.
As mandated in P.L. 96-151, the Veterans' Affairs Amendments, the VA is
currently preparing to perform an epidemiological study of Vietnam veterans
exposed to Agent Orange. Although the study's protocol has been developed

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UPDATE-04/20/82

and validated by an independent group, the VA will perform the testing and
collect the data, with oversight by a non-VA
scientific
committee.
Procurement of an independent contractor for the study's protocol was delayed
for 14 months by a protest filed by the National Veterans Law Center
(NVLC) .
The NVLC alleged that not only was the .VA violating procurement law, but also
the study as currently contemplated did not comply with the requirements of
P.L. 96-151. On Feb. 2, 1981, the General Accounting Office concluded its
investigation and denied the NVLC protest. On May 5, 1981, the VA announced
the awarding of a contract to the University of California at Los Angeles
(UCLA) School of Public Health for the design of the epidemiological study.
UCLA submitted its first draft of the protocol to the VA in August 1981;
it
was peer-reviewed by the VA Advisory Committee on Health-Related
Effects of
Herbicides, by the Office of Technology Assessment, and by the Science
Panel
of the Agent Orange Working Group. All the review groups judged the draft
protocol to be inadequate and not in compliance with the contract. UCLA has
since modified the protocol, expanding on problem areas and incorporating the
suggestions of the review groups; its final submission to the VA is due April
29, 1982.
As with the Ranch Hand study, this epidemiological study will have
two main parts:
a questionnaire on health status and
medical
and
occupational history, and a physical exam with laboratory workup. The study
group will be 18,000 veterans, divided into 3 cohorts of 6000 each.
Two of
the cohorts will have had Vietnam service, and will be distinguished as
having a high or a low likelihood of herbicide exposure.
The third cohort
will be veterans with non-Vietnam military service.
Inclusion of the third
group will generate data about the health effects of Vietnam service in
addition to the information expected about herbicide-related health
effects.
The study will commence with a pilot project to field test its procedures.and
the questionnaire.
P.L. 96-151 also mandated the VA to conduct a comprehensive review and
scientific analysis of the worldwide literature on Agent Orange and other
phenoxy herbicides. JRB Associates prepared the review under contract, and
the VA published the 2-volume study in October 1981.
The VA is now preparing
to contract for an update to the literature review, to reflect new reports
and data -that have appeared.
The Interagency Work Group on Phenoxy Herbicides and Contaminants,
established in December 1979,
recommended that the Centers for Disease
Control (CDC) perform a case-control study to see if there is an increased
incidence of specific malformations in children of Vietnam veterans.
The
population to be studied is a group of 7500 children who have birth defects
and who are registered in CDC's Birth Defects Program (in operation since the
late 1960s). Information on the families of these children, gained by
extensive interviews and questionnaires, will be compared with that for 300
normal controls. The data will be analyzed to see what risk factors in the
parents' lives, including military service in Vietnam, may be related to
increased incidence of malformations in their children.
CDC has completed a
pilot study on a representative sample of the two groups to test the
questionnaire and the procedures for finding the families.
The main study
will be started in late April 1982, and a preliminary report on the issue of
Vietnam service is expected in the fall of 1983.
Detailed analysis of the
data on all risk factors will take several years to complete.
On Sept. 22, 1980, the Work Group held its first public meeting to discuss
problems and proposals related to exposure to herbicides. On Jan. 19,
1981,
the Secretary of Health and Human Services established the "Advisory
Committee on Special Studies Relating to the Possible Long-Term Health
Effects of Phenoxy Herbicides and Contaminants" to advise the Secretary and

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UPDATE-0'4/20/82

the Chair of the Interagency Work Group on Herbicides concerning the Advisory
Committee's oversight of the conduct of the Ranch Hand Study being conducted
by the Air Force. In its seventh report to the White House, the Work Group's
Scientific Panel concluded that:
While it is difficult to accept logically that a
single causative factor -- Herbicide Orange -- could be
responsible for such a diverse set of health effects as
alleged by Vietnam veteran claims to the VA , there is no
definitive evidence that permits selective exclusion of
some of these illnesses. Further, it is possible that
some of these health effects are occurring as a consequence
of Vietnam^ service but not due to exposure to Herbicide
Orange. The Science Panel is not aware of any data that
suggest a modification of its previous recommendation that
the •focus of a study of Vietnam veterans should be
broadened to consider Vietnam service as the exposure
factor rather than focus solely on Herbicide Orange
exposure.... The Science Panel is in receipt of data
which indicate that there is at best a remote chance of
accurate identification of specific ground troops who were
exposed to Herbicide Orange.... The Panel is therefore of
the opinion that design of a scientifically valid Herbicide
Orange study of ground troops may not be possible. If
the focus of a study of Vietnam veterans is broadened to
consider Vietnam service as the exposure factor, a study
of ground troops is necessary and a scientifically valid
study can be designed.
On July 17, 1981,
the Interagency Work Group was renamed and its
membership expanded. Now called the Agent Orange Working Group, it is part
of the Cabinet Council on Human Resources.
The Department of Health and
Human Services is the lead agency.
Because the VA currently recognizes only chloracne as a human health
effect that can be proven to be caused by exposure to 2,4,5-T, veterans may
have difficulty being compensated for even those effects for which there is
strong animal evidence (i.e., cancer and birth defects caused in utero which
are those birth defects that cannot be caused by the father and require the
mother and fetus to be exposed during the actual pregnancy).
Veterans who
claim compensation for health effects which are not supported by strong
animal data (i.e., mutations -- which could cause genetic defects in the
father's sperm that would affect children conceived after exposure) may have
an even tougher case to argue.
The veteran's question then becomes: How much evidence is required to
prove the right to compensation?
On whom does the burden of proof lie
(the
veteran or the VA)? .If more evidence is needed, who will generate it? And
finally, what constitutes fair treatment of veterans while the necessary data
are being gathered?
Congressional Action of the 96th Congress
The 96th Congress responded to the problems of establishing
a cause and
effect relationship between veterans' exposure to herbicides in South Vietnam
and the various health problems they are now experiencing by holding hearings
and enacting legislation.

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The Subcommittee on Oversight and Investigations, of the House Committee on
Interstate and Foreign Commerce held hearings on June 24 and 25, 1979,
to
hear testimony from veterans who allegedly have been affected by herbicide
exposure and from the Veterans Administration regarding its efforts to
unequivocally determine the relationship between herbicide exposure and
health effects. The Subcommittee on Medical Benefits and Facilities of the
House Committee on Veterans' Affairs held two sets of hearings on the hazards
associated with TCDD, veterans' complaints of health effects associated
with
Agent Orange exposure, and Veterans Administration's efforts to resolve the
Agent Orange problem.
The Senate Veterans' Affairs Committee also held hearings to
Agent Orange problem.

examine

the

As a step to gain access to records to locate veterans who may have been
exposed to herbicides in-service,
Title V of H.R.
2282, the Veterans'
Disability Compensation and Survivors' Benefits Amendments of 1979,
requires
the Director of the National Institute for Occupational
Safety and Health,
upon request by the VA (or other appropriate agency) to request the current
mailing address from the Internal Revenue Service of persons whom the VA
certifies may have been exposed to occupational
hazards.
H.R.
2282 was
passed in lieu of its companion bill, S. 689, and became Public Law 96-128 on
Nov. 28, 1979.
Title III of H.R. 3892, the Veterans' Affairs amendments, directs the
Veterans Administration to conduct an epidemiological study of the long-term
health effects on individuals from exposure to dioxins in Vietnam, upon the
Office of Technology Assessment's
(OTA) approval of its protocol.
Its
companion bill, S. 1039, was incorporated in H.R. 3892 as an amendment, and
the measure was enacted by Congress and signed by the President on Dec. 20,
1979 (P.L. 96-151) .
If enacted, S. 2096 would have directed the Secretary
of Health,
Education, and Welfare (now, Health and Human Services)
to undertake an
epidemiological study to determine the long-term adverse human health effects
associated with exposure to dioxins produced during the manufacture of
phenoxy herbicides. This bill proposed to investigate the long-term health
effects of exposure to dioxins, in general, not just to Agent Orange.
As
similarly incorporated in H.R. 3892, S. 2096 would have required that the
study's protocol be approved by the Congressional Office of Technology
Assessment. This bill was presented to the President on Dec. 21, 1979,
and
vetoed by him on Jan. 2, 1980.
President Carter vetoed the bill because the
White House counsel believed that such a procedure violated the separation of
power between the legislative branch and the executive branch.
He did not
feel that the Department of Health and Human Services' study protocol
should
be subject to approval by a congressional agency.
Title X of H.R. 5288, the Veterans' Rehabilitation Program and Veterans'
Educational Assistance Program would have directed the Secretary
of Health
and Human Services to conduct a study of veterans and other groups exposed to
the herbicide known as "Agent Orange" to determine if there may be adverse
health effects associated with such exposure. Like H.R. 3892 (P.L.
96-151)
and S. 2096, the bill called for OTA approval of the study's protocol.
The
bill also would have required the Secretary of Health and Human Services to
coordinate its efforts with other studies in the Federal Government.
During
the debate on S. 1188,
its companion bill, the
Disabled
Veterans'
Rehabilitation Act, the Senate adopted an amendment offered by Senator

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UPDATE-04/20/82

Cranston to expand the study on health effects of exposure to Agent Orange to
include other factors related to service in Vietnam. The Senate also adopted
an amendment offered by Senator
Heinz requiring the VA to promulgate
regulations regarding guidelines to resolve veterans' disability claims based
on exposure to Agent Orange.
The ' amendments were striken by the House
because they were considered to be "non-germane" to the primary focus of the
bill.
S. 1872 (the Vietnam Veterans' Act); H.R.
6050 (the Vietnam Veterans'
Act); H.R. 6377 (the Vietnam Era Veterans Agent Orange Act); each would have
established a presumption of service-connected disability for health
effects
in Vietnam veterans (and birth defects in their children) exposed to Agent
Orange. H.R. 8238 (Independent Agent Orange Study) would have directed the
Veterans Administrator to request the National Academy of Sciences to conduct
a study on veterans exposed to Agent Orange.
H.R. 8300 would have expanded
the scope of the Agent Orange study currently being coordinated by the VA and
would have established deadlines for promulgating regulations related to
Agent Orange exposure claims. These bills received no action.
LEGISLATION
P.L. 97-72, H.R. 3499
Veterans' Health Care, Training and Small Business Loan Act of
1981.
Amends title 38, U.S. Code, to extend the Vietnam-era veterans'
readjustment
counseling program, to provide medical care for Vietnam veterans exposed to
herbicide defoliants (including Agent Orange), to recover the cost of certain
health care provided by the VA, and authorizes the VA to expand the scope of
its epidemiological study on the health effects of Agent Orange, and other
purposes. Introduced May 7, 1981;
referred to Committee on Veterans'
Affairs. Committee consideration and mark-up session held May 12.
Reported
to House (amended) by Committee on Veterans' Affairs (H.Rept. 97-79) May 19.
Passed House (amended) June 2, 1981.
Received in the Senate June 3.
Senate
struck all after the Enacting Clause and substituted the language of S. 921,
June 16. Passed Senate in lieu of S. 921 with amendments, June 16,
1981.
House concurred in Senate amendments with amendments Oct.
2, 1981.
Senate
agreed to House amendments Oct. 16, 1981.
Signed into law Nov. 3, 1981.
H.R.

523

(Roe)

Amends Title 38, U.S. Code, to waive the 1-year limitation on claims for
compensation from the Veterans Administration for disabilities
and diseases
incurred in or aggravated by military service in the case of claims by
veterans who served in Southeast Asia during the Vietnam era for compensation
for disabilities resulting from exposure to the phenoxy herbicides known as
Agent Orange or other phenoxy herbicides.
Introduced Jan. 5, 1981;
referred
to Committee on Veterans' Affairs.
H.R. 1173

(Montgomery, by request)

Amends section 307 of P.L. 96-151, by assigning
the responsibility
of
designating a protocol for, and conducting an epidemiological
study of,
veterans who were exposed to Agent Orange, to an independent
scientific
agency. Introduced Jan. 22, 1981;
referred to Committee on Veterans'
Affairs.
H.R. 1962

(Oilman)

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Amends the Veterans Health Programs Extension and Improvement Act of
1979
to require the Veterans Administration and the National Academy of Sciences
to enter into an agreement under which the Academy will
conduct an
epidemiological study of veterans exposed to Agent Orange.
Introduced Feb.
19, 1981; referred to Committee on Veterans' Affairs.
H.R. 2157

(Mottl)

Expands the scope of a study required to be conducted by the Administrator
of Veterans' Affairs concerning the effect on humans of exposure to the
chemical known as Agent Orange.
Introduced Feb. 25, 1981:
referred to
Committee on Veterans' Affairs.
VA requested Executive comment Mar. 2, 1981.
Referred to Subcommittee on Hospitals and Health Care Apr. 28. Hearings held
Apr. 30. Subcommittee consideration and mark-up session held.
Clean
bill
forwarded to full committee.
H.R. 2297

(Downey)

Amends Title 38, United States Code, to waive the 1-year limitation
on
claims for compensation from the Veterans Administration for disabilities and
disease incurred in or aggravated by military service in the case of claims
by veterans who served in Southeast Asia
during the Vietnam era for
compensation for disabilities
resulting from exposure to the
phenoxy
herbicides known as "Agent Orange" or other phenoxy herbicides.
Introduced
Mar. 4, 1981; referred to Committee on Veterans' Affairs.
H.R. 2493

(Daschle)

Amends Title 38, United States Code, to provide a presumption of service
connection for the occurrence of certain
diseases in veterans who were
exposed to herbicides in Southeast Asia during the Vietnam era.
Introduced
Mar. 12, 1981; referred to Committee on Veterans' Affairs.
H.R. 2953 (Daschle)
Entitles veterans exposed to Agent Orange
during the Vietnam era to
specified medical benefits.
Extends the period during which veterans of such
era may initially request psychological
readjustment counseling.
Extends
specified educational assistance without delimiting periods for vocational
training for specified veterans determined to be in need of such
assistance.
Introduced Apr. 1, 1981;
referred to Committee on Veterans' Affairs.
Referred to Subcommittee on Hospitals and Health Care Apr. 28. Hearings held
Apr. 28. Subcommittee consideration and mark-up session held Apr. 30, 1981.
H.R. 3163

(Railsback)

Requires the Secretary of Health and Human Services to arrange for an
independent epidemiological
study of persons
exposed to Agent Orange.
Introduced Apr. 8, 1981;
referred to Committee on Energy and Commerce.
Referred to Subcommittee on Health and the Environment Apr. 9, 1981.
S. 636 (Cranston et al.)
Entitles the United States to recover the costs of certain
medical
care
and services furnished to a veteran for a non-service-connected
disability
when disability is covered by another form of insurance
or compensation.
Permits the expansion of the scope of the epidemiological
and literature

�CRS- 16

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UPDATE-04/20/82

study of the long term adverse health effects of exposure to Agent Orange
during the Vietnamese conflict to include the effects of other factors.
Introduced Mar. 5, 1981; referred to Committee on Veterans' Affairs.
S. 689 (Heinz)

Amends section 307 of the Veterans Health Programs Extension
and
Improvement Act of 1979 to require the promulgation of regulations containing
guidelines for resolving claims for veterans benefits based on exposure, to
Agent Orange, and for other purposes. Introduced Mar. 12, 1981; referred to
Committee on Veterans' Affairs.
Hearings held Apr. 30, 1981.
S. 921

(Simpson)

Extends the authority of the Administrator
of Veterans' Affairs to
contract for hospital care or medical services in Puerto Rico and the Virgin
Islands without reference to patient loads or incidence of provision of
medical services for veterans treated by the Veterans' Administration in the
contiguous 48 States. Introduced "Apr. 8, 1981;
referred to Committee on
Veterans' Affairs.
Reported with amendment May 15, 1981
(S.Rept.
97-89);
H.R. 3499 passed in lieu (see P.L. 97-72 above) June 16, 1981.
S. 1345 &lt;Heinz)
Authorizes the Administrator of the Veterans' Administration to provide
hospital or nursing home care to a veteran for treatment of a condition
associated with exposure to Agent Orange during service in Vietnam.
Extends
the Vietnam-era veterans' readjustment counseling program.
Directs the
Administrator to expand the scope of the epidemiological study of long term
adverse health effects of other factors involved in such service. Introduced
June 8, 1981; referred to Committee on Veterans' Affairs.
S. 1953

(Specter)

Amends title 38, United States Code to provide a presumption of service
connection for the occurrence of certain diseases
in veterans who were
exposed to phenoxy herbicides while serving in Southeast Asia during the
Vietnam era.
Introduced Dec. 15, 1981; referred to Committee on Veterans
Affairs.
HEARINGS
U.S.

Congress.
House. Committee on Interstate and Foreign
Commerce. Subcommittee on Oversight and Investigations.
Agent Orange: exposure of Vietnam veterans.
Hearing, 96th Congress,
2d session. Sept. 25, 1980.
249 p.
Involuntary exposure to Agent Orange and other toxic
spraying. Hearings, 96th Congress,
1st session. June 26 and 27, 1979.
256 p.

U.S.

Congress. House. Committee on Veterans' Affairs. Ad Hoc
Subcommittee.
Status of Vietnam veterans in the Bay area.
Hearing, 96th Congress, 2d session. Apr. 10, 1980.
64 p.

U.S.

Congress.
House. Committee on Veterans' Affairs.
Subcommittee on Hospitals and Health Care.

�%

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Legislation to improve medical programs administered by
the Veterans Administration (H.R. 2157, H.R. 2953, and H.R. 2999).
Hearings, 97th Congress, 1st session. Apr. 28, 1981.
54 p.
U.S.

Congress. House. Committee on Veterans' Affairs.
.Subcommittee on Medical Facilities and Benefits. Herbicide
"Agent Orange". Hearing, 95th Congress, 2d session. Oct. 11,
1978.
62 p.
Oversight hearing to receive testimony on Agent Orange.
Hearing, 96th Congress, 2d session. Feb. 25, 1980.
121 p.

----- Oversight hearing to receive testimony on Agent Orange.
Hearing, 96th Congress, 2d session. July 22, 1980.
459 p.
--—•- Scientific community report on Agent Orange. Hearing, 96th
Congress, 2d session. Sept. 16, 1980.
145 p.
U.S.

Congress. House. Committee on Veterans' Affairs.
Subcommittee on Oversight and Investigations. Current
status of Agent Orange studies. Hearing, 97th
Congress, 1st session. May 6, 1981.
385 p.

U.S.

Congress.
Senate.
Committee on Veterans' Affairs. Agent
Orange update and appendix: Agent Orange activities (part II).
Hearing, 96th Congress, 2d session. Sept. 10, 1980.
1368 p.
Oversight on issues related to Agent Orange and other
herbicides. Hearing, 97th Congress, 1st session. Nov. 18,
1981.
(not yet printed)
• VA health resources and program extensions and appendix:
Agent Orange activities.
Hearing, 96th Congress, 1st session,
on S. 741 and S. 196.
Apr. 10,. 1979.
462 p.
• Veterans' Programs Extension and Improvement Act of 1981.
Hearing, 97th Congress, 1st session, on S. 26 (titles
II and III, only), S. 380, S. 458, S. 636, S. 689, S. 872, S. 914,
S. 921, and related bills. Apr. 30, 1981.
685 p.
• Vietnam veterans' readjustment. Hearings, 96th Congress, 2d
session.
Feb. 21, Mar. 4, and May 21, 1980.
Part 2.
595-2082 p.

ADDITIONAL REFERENCE SOURCES
American Medical Association.
Council on Scientific
Affairs.
Health effects of "Agent Orange" and
dioxin contaminants (Executive Summary).
1981.
6 p.
Behrens, Richard, et al. Comments from CAST (Council on
Agricultural Science and Technology): Dioxin.
1978,
9 p.
Bucfc, Craig. The Death of a nation.
Aug. 28, 1978:
49-50, 52-55.

New west, v. 3,

�CRS-18

IB80040

UPDATE-04/20/82

Cookson, Clive. "Emergency" ban on 2,4,5-T herbicide
in U.S. Nature, v. 278, Mar. 8, 1979:
10'8-110.
Davis, Donald E. et al. Comments from CAST (Council
on Agricultural Science and Technology): Agent
orange. 1978.
5 p.
Galston, Arthur W. Herbicides: a mixed blessing.
v. 29, February 1979:
85-90.

Bioscience,

International Agency for Research on Cancer.
IARC monographs on
the evaluation of the carcinogenic risk of chemicals to
man: 2,5,5-T, vol. 15, August 1977.
JRB Associates.
Review of literature on herbicides,
including phenoxy herbicides and associated
dioxins. Washington, Veterans Administration,
1981.
2v.
Laporte, Joan-Ramon. Multinationals and health: reflections on
the Seveso catastrophe.
International journal of health
services, v. 8, no. 4, 1978:
619-632.
National Research Council. The effects of herbicides in South
Vietnam: Part A. Summary and conclusions. Washington,
National Academy of Sciences, 1974.
AD-774-749.
398 p.
Peterson, Jeannie. Seveso:
1978:
232-239.

the event.

Ambio, v. 7, no. 5-6,

Reggiani, G. Localized contamination with TCDD - Seveso, Missouri, and
other areas. In: Halogenated biphenyls, terphenyls,
naphthalenes, dibenzodioxins and related products, ed. Renate
D. Kimbrough. Amsterdam, New York, Oxford, Elsevier/North-Holland
Biomedical Press, 1980.
Severe, Richard. Seveso: lessons from an escape.
June 17, 1978:
101-102, 104-106, 108.
U.S.

Economist, v. 2.67,

General Accounting Office. Health effects of exposure to
herbicide orange in South Vietnam should be resolved,
Apr. 6, 1979.
CED-79-22.
U.S. ground troops in South Vietnam were in areas sprayed
with herbicide orange. Nov. 16, 1979.
FPCD-80-23.

Young, Alvin et al. The toxicology, environmental fate and human
risk of herbicide orange and its associated dioxin. The
Surgeon General, U.S. Air Force, Washington, D.C.
October 1978.
Walsh, John. Seveso: the questions persist where dioxin created a
wasteland. Science, v. 197, Sept. 9, 1977:
1064-1067.
Whiteside, Thomas.

Defoliation.

New York, Ballantine,

•- The pendulum and the toxic cloud.

New Haven, Yale

1970.

�, ..

k

CRS-19

IB80040

University Press, 1979.
Zimmerman, David R. Agent Orange: Vietnam's lingering
poison. American health, v. 1, no. 1, Mar./Apr.
1982: 68-72.

UPDATE-04/20/82

�Signs, Symptoms, and Disorders Reported After Occupational Exposure to TCP, 2,4,5-T or TCDD
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due to the overlap to studies by Jirasek et al. and Pazderova et al.
SOURCE:

Young, Alvin et al. The Toxicology, Environmental Fate, and Human Risk of Herbicide
Orange and Its Associated Dioxin, p. VI-14. (Numbers in parentheses identify sources
in Young's bibliography.)

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&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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01435

Author

Young, Alvin L.

Corporate Author
RODOrt/ArtlOlO TltlO Social Controversy and the Dioxln Question

Journal/Book Title

Year

1Q85

Month/Day

September

Color

°

Number of Images

9

DeSCTlptOn Notes

Accepted for publication in Chemosphere 1986

Tuesday, May 15, 2001

Page 1435 of 1514

�SOCIAL CONTROVERSY AND THE DIOXIN QUESTION
A. L. YOUNG
Office of Science and Technology Policy
Executive Office of the President
Washington, D.C. 20506, U.S.A.
ABSTRACT
The dioxin controversy conforms to a model useful for analyzing
"quality of life issues."
Examination of scientific versus social,
political, and legal issues reveals an extensive scientific data base for
„ studying the dioxin controversy.
It is apparent that the factors that
presently drive this controversy are not based on scientific truth. The
dominant role playe'd by the media in keeping the dioxin controversy before
the public is discussed.
INTRODUCTION
Health concerns involving dioxin, especially the 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), date from 1969 - 1970 and its contamination of Agent
Orange, the military defoliant used in the Vietnam Conflict. Current interest
1970

is merely an extension and popularization of issues first publicized in
and again in 1974.

A large volume of toxicological data o« 2,4,5,-

trichlorophenoxyacetic acid (2,4,5-T) and 2,4-dichlorophenoxyacetic acid
(2,4-D), the two herbicides in Agent Orange, were available during the final
years of US involvement in Vietnam, but woefully inadequate toxicological
and enviror.mental data on TCDD precluded resolution of the issues. - Although
scientists

recognized

TCDD was

deforming) in laboratory animals,

acutely

toxic and teratogenic

(birth

no studies were available on the effects

of chronic long-term low-level exposures in lower mammalian'species.

Fur-

thermore, numerous occupational exposures to TCDD were reported during the
industrial production of trichlorophenol, but epidemiologic studies were not
available despite documented exposures as early as 1949.

Presentation to the 5th International Symposium on Dibenzo-p-dioxins and
Dibenzofurans, Beyreuth, FRG, September 1985. Accepted for publication
in CHEMOSPHERE 1986.

�Thus in an attempt to resolve the present controversy, scientists had
to assess the long-term effects of exposure to TCDD either on the basis of
existing

data available from health studies of industrial

from studies of Vietnam veterans exposed to Agent Orange.

populations or
Of course, one

major assumption must be that US military personnel reporting health effects
were probably exposed to Agent Orange and, hence, to TCDD. But, regardless
of any reported health effects, a valid study must include examination

of

all facets of the controversy.
This requirement poses a dilemma because objective analysis depends on
established criteria, but there are simply no models available for analyzing
environmental health issues.

In the absence of such models, examination of

environmental crises involving other chemicals can provide a useful parallel
for

analyzing

contamination
involved

the dioxin controversy.

For

example,

environmental

or "poisoning" episodes during the decade of the

similar chemicals, such as chlorinated

insecticides

seventies
(chlordane,

DDT, andmirex), polychlorinated biphenyls (PCBs), and polybrominated biphenyls (PBBs).

And, during the last few years, the Love Canal episode has

received extensive publicity. Analysis of these episodes, including reports
on PCBs by Hammond (5) and Culhane (3), reports on PBBs by Budd et al. (1),
and Ember's

(5) assessment of the Love Canal episode, reveals that these
v
share common characteristics. Apparently, the public perceives

episodes

highly publicized environmental poisoning

episodes as threats to the

"quality of life," and, as a result of this perception, the episodes lead to
a number of predictable events (see Table 1).
NATURE OF CONTROVERSIES
A

controversy

involving environmental contamination commonly begins

with an episodic event. a specific instance of poisoning that arouses public
and scientific concern.
animals, but

Such an event usually begins with contamination of

its impact rapidly expands to include humans who may have

inadvertently been exposed to the chemical.

Frequently, improper use or

disposal of the chemical precipitates the event (e.g., the PBB episo.de, 1).
Generally, only a few people or livestock are actually exposed to, or
contaminated by, the chemical. This small population, however, is an inadequate sample for establishing cause and effect relationships. "Nevertheless,
concerned individuals respond to the event with lists of observed biological
effects

in animals

and adverse physical

symptoms

in humans.

In most

instances, lay persons (including news reporters), local physicians, or
biologists

compile these lists, and they ultimately become indicators of

�Table 1. Events and Characteristics of Environmental Poisoning Episodes That Define
"Quality of Life" Controversies
Event/Characteristic

Brief Description

Episodic Event

An environmental incident involving poisoning
of man and/or livestock

Inadequate Sample Size

Episodic events involve exposure of small populations of people and/or livestock

Inadequate Scientific Data

Reported symptoms and adverse health effects
are inconsistent with scientific data.

Intense Media Response

Sensational reporting of the episodic event

Inadequate Government Response

The initial failure of government agencies to
respond to public concerns

Special Interest Groups

A group of citizens joined by a common concern
to manipulate public and political attitudes
toward an episodic event or chemical

Initiation of Lawsuits

The threat of legal action in the absence of a
satisfactory resolution of an episodic event

Advisory Groups

At the request of a lead agency, e.g., a state
department of health, qualified representatives from all interested parties join in an
advisory committee to coordinate research
studies, review results, and offer recommendations for resolution of issues

Unsatisfactory Resolution

There are no satisfactory methods for appropriate resolution of "quality of life" controversies.

Congressionally-Mandated Action

Political action groups demand and obtain congressional action, usually in the form of mandated health studies.

�adverse effects to people who feel that they or their animals have been
"potentially" exposed to the chemical. Invariably, these lists are not consistent with accepted scientific data because the media and the public
either confuse or misunderstand the concepts of dose, exposure, and chronic
and acute effects.

As a result, the public concludes that the scientific

data are inadequate. and, in some instances (e.g., the Love Canal episode,
(5), it may express an intense emotional reaction to the scientific data if
it suspects that "contrary" data are wrong or even dishonest.
Of course, the episodic event is "news," and, as such, it always
attracts the local news media.
tains many
providing

Initial coverage of the event usually con-

inaccuracies and reflects a highly emotional orientation.

In

the coverage, the media compare the list of symptoms of a given

episodic event to symptoms from other similar events in the past or in some
other community.

The intensity and duration of coverage depend on the

magnitude or nature of the episode and on the number of people or animals
exposed to "environmental poisoning."

The media response is further charac-

terized by articles in major newspapers or on the evening news, and these
articles are usually followed by other articles containing

"sensational"

stories in popular magazines (e.g., Time, Reader's Digest, Family Circle,
••Playboy,

and Penthouse).

Culmination

of the intense and frequently

inaccurate campaign is marked by television documentaries usually prepared
to highlight significant events or chemicals. For example, "A Plague on Our
Children" was televised nationwide on 2 October 1979 by the Public Broadcasting System in its "NOVA" series and focused on PCBs, TCDD, 2,4,5-T, and
the Love Canal.

The Council for Agricultural Science and Technology (CAST,

2) reviewed this documentary and concluded:
The program was overloaded with interviews with
emotional laymen whose uneducated opinions about
health hazards related to chemicals would be expected
to induce a similar emotional response in the viewer.
Following
local,
responses

the episodic event and intense media coverage, numerous

state, and federal agencies provide immediate but definitive
to the stories. Personnel in these agencies are rarely knowl-

edgeable about the chemicals or the incidents,

but, after cursory reviews

of available information and telephone calls to local scientists, physicians, or other "experts," they release tentative responses to implied or
direct charges of official ineptitude. Frequently, the media and the public
view these efforts as inadequate government behavior and label the concerned
agency as "unresponsive."

�In concluding that the government is unresponsive, concerned citizens
form special interest groups and usually solicit the services of their own
"experts.*

Media coverage and inquiries to elected government officials

prompt public hearings on the episodic event, the tragedies suffered by the
•victims," and reports by the scientific community and government officials.
The

impact of special interest groups on public attitudes and the behavior

of government officials has been described by Ember ( )
5.

For example, the

Love Canal Homeowners Association, a special interest group, launched a
separate

epidemiologic study of the Love Canal "at risk" population and

subsequently used

data derived from the study to elicit responses " from a

number of federal agencies and even a US district court.
Failure to resolve the controversy or to compensate the victims of the
episodic event soon leads to lawsuits against the company responsible for
the event, for production of the chemical, or for both activities. The real
purpose of the lawsuits is to verify the concern of the individuals.

Since

the complex nature of the issues precludes their immediate appearance on
court dockets, lawsuits are always pending.
Many government agencies,

special interest groups, academic and

"research institutions, and concerned citizens become involved in various
facets of the chemical episode.
so many

To minimize the confusion associated with

"players," the lead government agency, usually a state health

department, appoints an advisory group to insure maximum collection

and

review of all relevant data. The composition of this group must reflect the
credentials of "qualified" people representing major players and various
government agencies
advisory

involved in the episode.

One major function of the

group is to offer recommendations that will assist the lead agency

in resolving the issues.
With the possible exception of bans on some of the chlorinated insecticides, the government

and the scientific community have satisfactorily

resolved very few episodes stemming from environmental poisoning. -But, even
tn the ban on DDT, dispassionate scientific data took second place to
emotional concerns in the legal resolution of the issue ( ) These contro4.
versies generally remain unresolved because there simply is no satisfactory
mechanism for treating opposing points of view in complex "quality of life"
issues.

The result has been an increasing public

fear of artificial

chemicals in the environment and lack of confidence in the ability or willingness of government and science to resolve problems related to their use

�or disposal.

Thus, unsatisfactory resolution Is still another unique char-

acteristic of controversies stemming from environmental poisoning episodes.
When it is perceived by the public and special interest groups that the
resolution of a specific controversy is not probable, or cannot be done in a
timely manner,
action.

This

the final recourse is to solicit congresstonally-mandated
action may take the form of a mandated

additional health studies, or presumptive compensation.

scientific

review,

In any case, it is

an expression by the political system that is intended to reflect concern
for the victims of the episodic event.
DISCUSSION
Obviously, the characteristics that distinguish environmental poisoning
episodes from other environmental issues are a combination of scientific,
social, political, and legal factors.
preponderance

If a controversy is based on a

of scientific concerns and these concerns cannot be resolved

to the satisfaction of the media and the public, then one can
conclude that scientific issues drive the controversy.

reasonably

In this instance,

reasonable answers to key scientific questions should lead to satisfactory
resolution of the controversy.

On the other hand, sufficient

scientific

data may permit definitive answers to questions related to public health,
but they may not resolve the initial controversy.

In such instances, one

must conclude that social, political, or legal issues drive the controversy. Obviously, all key scientific questions can never be answered to the
complete satisfaction of all parties, and the same is true for social,
political,

and legal concerns.

Thus,

short-term studies involving

relatively small expenditures of resources might be feasible to enhance the
existing scientific data base.

On the other hand, a reasonably complete

data base for making decisions in the present or immediate future may not
justify

long-term studies (years) requiring major outlays of dollars and

manpower.
The ten characteristics discussed in the above model apply in varying
degrees to all controversies based on environmental

poisoning -episodes.

Like other controversies, the dioxin controversy can be examined in the
framework

of this model.

The analysis begins with an evaluation of the

episodic event and traces its evolution to a full-blown controversy.
difficult

It is

to identify a specific episodic event for dioxin, although the

horse arena deaths in Missouri in 1972 and the Seveso, Italy, Dioxin Episode
of 1976

aroused the public's awareness of dioxin.

Nevertheless, it is

probable that dioxin-contaminated Agent Orange used in South Vietnam repre-

�sents the' major episodic event, especially as it relates to the

intense

publicity given to dioxin, Agent Orange, and the Vietnam veteran in March

1978.
Table 2 describes the dioxin controversy as applied to the criteria for
assessing environmental health issues.

Public and private perceptions

of

controversial issues are manifested as fear of the unknown, such as the risk
associated with a poisonous chemical in the environment.
not

always

react

threatened harm.

The public

does

to that fear in proportion to the seriousness of the
This is particularly true of "quality of life" issues in

which determination of risk involves value choices.

Positions taken by the

media and the courts may be independent of scientific consensus regarding
the actual risk.

The media response to this issue deserves some additional

examples.
INTENSE MEDIA CAMPAIGN
Station WBBM, a television affiliate of the Columbia
System

Broadcasting

in Chicago, Illinois, aired a special report in March 1978.on the

subject, "Agent Orange: Vietnam's Deadly Fog." This film reviewed a number
of past environmental episodes

allegedly involving 2,4,5,-T and TCDD.

JCurtis (7), the WBBM reporter, compared symptoms described by some Vietnam
*•
veterans
in the Chicago area with the symptoms identified in past
"poisoning" episodes. Veterans shown in the film claimed that they had been
sprayed with Agent Orange during combat operations in South Vietnam.

Kurtis

concluded his documentary with these statements:
Officially the Veterans Administration is denying
the claims of poisoning by Agent Orange. Their
scientists simply feel there isn't any evidence to
link defoliation with human problems. But after
researching this report and listening to the recommendations of the leading dioxin scientists in the
country, we feel there is a need for immediate
testing of all Vietnam veterans who handled Agent
Orange or went into sprayed areas. Not only for
the sake of those who have told us of their
symptoms but for the countless others whose lives
and whose children's lives could be blighted by the
dioxin poison in Agent Orange.
Wade

(8) recently reviewed many of these articles and wrote that the

"whole passel" of apprehensions "may have nothing to do with Agent Orange in
scientific

fact, but is grounded in other problems affecting

the Vietnam

veteran population and has been launched into celebrity by a self-generating
series of press and television stories." He observed further:
In favor of the latter hypothesis, it nay be noted
that the first large batch of veterans' complaints
about Agent Orange emerged in 1978 from Chicago
shortly after the showing there of a television

�Table 2. The Dioxin Controversy as Applied to the Criteria for Assessing Environmental
Health Issues
Event/Characteristic

Brief Description

Episodic Event

The use of Dioxin (TCDD) contaminated Agent Orange,
1965-1970, in the Vietnam Conflict

Inadequate Sample Size

No satisfactory Exposure Index has been developed for
Epidemiologic
"studies". Industry populations
exposed to TCDD small.

Inadequate Scientific Data

Little or no data available on the toxicity of TCDD
(e.g., teratogenesis or carcinogenesis) at the time
of Agent Orange use in Vietnam.

Intense Media Response

Most intense media coverage began in March 1978 with
WBBM broadcast of "Agent Orange: Vietnams Deadly
Fog."

Inadequate Government Response

Department of Defense and Veterans Administration did
not respond to the Veterans' concerns over Agent
Orange and dioxin until 1978. Initial response
limited to establishment of the Agent Orange Registry.

Special Interest Groups
**

Vietnam Veterans have not only lobbied the traditional veterans organizations (e.g., American
Legion) but have also founded Vietnam Veterans of
America and Agent Orange International. These two
latter groups have Agent Orange as major issue.

Initiation of Lawsuits

Following more than 5 years of legal maneuvering, an
out-of-court settlement for $180 million occurred
in 1984 between 7 chemical companies (all had been
producers of Agent Orange) and Vietnam veterans as
a class.

Advisory Groups

The Veterans Administration and many individual
states chartered Advisory Groups to provide guidance for the establishment of programs. In 1981,
the Federal government formed the 12-Agency Agent
Orange Working Group.

Unsatisfactory Resolution

Despite the success of the above litigation action,
veterans have been unsuccessful in obtaining compensation for dioxin exposure from the Federal
government.

Congressionally-Mandated Action

In December 1979, Public Law 96-151 required the
conduct of epidemiologic studies of Vietnam
veterans. In November 1981, Public Law 97-72 authorized the Veterans Administration -to provide
eligible veterans medical care and treatment for
illness possibly related to Agent. Orange/Dioxin
exposure.
In October 1984, Public Law 98-542 was
enacted that required VA to.compensate veterans or
their survivors for disabilities or death related
by sound scientific and medical evidence to dioxin
exposure.

�documentary about the herbicide's possible effects
on health. The idea spread like wildfire among
veterans' groups; here at last was a tangible cause
for all their discontents.
Each claim filed
generated more newspaper stories which generated
further claims, until the present fervid atmosphere
had been created.
CONCLUSION
Neither the government nor the scientific community has resolved the
numerous environmental, medical, and political issues surrounding the dioxin
controversy.

Unfortunately,

Federal Agency positions on the

hazards

associated with dioxin are either not well defined or not uniformly
accepted, thus perpetuating the controversy.
continue

The scientific community must

to conduct valid research on pertinent environmental and health-

related issues to provide a reliable basis for appropriate decision making.
REFERENCES
1.

Budd, M.L., N.S. Hayner, H.E.B. Humphrey, J.R. Isbister, H. Price,
M.S. Reizen, G. van Amburg, and K.R. Wilcox, Jr. 1978. Polybrominated biphenyl exposure - Michigan. Morb. Mort. 27(14):115-116,
121.

2.

CAST.
1979. A plague on our children. Council for Agricultural
Science and Technology, Report No. 81. 17p. Headquarters Office:
Department of Agronomy, Iowa State University, Ames, 10. 50010.

3.

Culhane, J. 1980. PCBs: The poison that won't go away. Reader's
Digest 117(704):112-116.

4.

Devlin, R.M.
8(4):322-325.

5.

Ember L.R. 1980.
Uncertain science pushes Love Canal solutions
to political, legal arenas. Chem. Eng. News 58(32):22-29.

6.

Hammond, A.L. 1972.
Chemical pollution:
phenyls. Science 175:156-157.

7.

Kurtis, B. 1978.
"Agent Orange: Vietnam's Deadly Fog". Transcript of a television documentary aired 12 March 1978, WBBM-TV,
Chicago, IL. 30pp.

8.

Wade, N. 1980.

1974.

DDT: A renaissance?

Environ. Sci. Technol.

Polychlorinated bi-

Mythopoiesis. Protest TIBS, June 1980, p". VIII.

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manuscript is a draft version of a chapter or section
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Associated Dioxin: Assessment of a Controversy.
Young, A. L. and G. M. Reggiani, eds. New York:
Elsevier, 1988. This book is available in the NAL
collection, call no.: RA1242 T44 A3. This item gives a
good overview of the Agent Orange Controversy and
the political issues around it.

Tuesday, May 15, 2001

Page 1493 of 1514

�CHAPTER 1
"AGENT ORANGE AT THE CROSSROADS OF SCIENCE AND SOCIAL CONCERNS"

INTRODUCTION
A. L. Young and G. Reggiani

For almost two decades, the United States has been involved in
controversy over its tactical use of herbicides in Southeast
Asia during the Vietnam Conflict. The controversy centered first
on the actual employment of herbicides in South Vietnam, then on
the safe disposal of surplus herbicide following the Conflict,
and lastly whether herbicides were responsible for health problems
reported among Vietnam veterans.
The use of chemicals (herbicides) to control vegetation has been
one of the most controversial subjects arising from the Vietnam
Conflict. The United States Air Force applied most of these
herbicides in jungle areas to clear vegetation from the perimeters
of military bases and camps, along lines of communication, and in
enemy staging areas. The objective was to provide defoliated zones
that would reduce ambushes and disrupt enemy tactics. The most
commonly used "defoliant" was "Agent Orange", a mixture of two
commercial herbicides widely employed for a number of years in
brush control programs throughout the United States and other
countries.
During a five-year period from 1965 to 1970, the United States
Air Force applied more than 42 million liters of Agent Orange in
South Vietnam, and some 2.5 million military personnel from the

�- 2-

United States, Australia, New Zealand, and South Korea served
one-year tours during the same period. Beginning in 1978, many
veterans of that era have reported medical problems that they
believed stemmed from exposure to Agent Orange during their military assignements. Their complaints have ranged from tingling
in the extremities to rare forms of cancer. Some veterans had
fathered children with birth defects. But overwhelming scientific data on the toxicology of chemical components in Agent Orange
do not substantiate these claims.
Nevertheless, the news media has given intense sympathetic coverage to the veterans and their medical complaints. In the meantime,
the governments of the United States and Australia have mobilized
the massive resources of their federal agencies to conduct multimillion dollar, long-term studies of military personnel allegedly
exposed to herbicides in South Vietnam from 1962 to 1970. The
issue is whether actual or perceived health problems stem from
herbicide exposure or whether other factors drive the controversy.
Two key questions must be considered in reviewing present concerns
over Agent Orange. First, why did the Agent Orange issue surface
10 years after it was used in Vietnam? Second, what criteria can
be used to insure an objective analysis of such a complex, controversial, and politically sensitive subject? One answer to the first
question may be that presumed health effects from exposure to the
herbicide did not appear, or at least, were not diagnosed among
Vietnam veterans until late in the 1970's. Another possible answer
is that the general public and Congress only lately recognized the
concerns of Vietnam veterans, and Agent Orange is only a vehicle
to focus those concerns. Certainly, the acrimony and bitterness
over involvement in Vietnam drove most Americans to repress memories
of that war. As a result, they have tended either to ignore veterans
of the Vietnam era or to relegate to a lesser status than veterans
of other wars. Certainly the longing for respectability of Vietnam

�- 3 -

veterans have coincided with increasing American and world-wide
interest in health and environmental issues. Thus, the controversy surrounding Agent Orange has surfaced primarily because
it involves the veterans and herbicides, both of which have
been the center of controversy since they were employed in
Vietnam.
Much of the controversy concerning Agent Orange is attributable
to concern over its toxic dioxin contaminant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). A large volume of toxicological data on
2,4,5-trichlorophenoxyacetic acid (2,4,5-T) and 2,4-dichlorophenoxyacetic acid (2,4-D), the two herbicides in Agent Orange,
were available during the final years of United States involvment
in Vietnam, but woefully inadequate toxicological and environmental
data on TCDD precluded resolution of the issues. Although scientists
recognized that TCDD was acutely toxic and teratogenic (birth
deforming) in laboratory animals, no studies were available on
the effects of chronic longterm, low-level exposure in lower mammalian species. Furthermore, numerous occupational exposures to
TCDD were reported during the industrial production of trichlorophenol, but. human epiderniologic studies were not available despite
documented exposure as early as 1949.
To further complicate the Agent Orange controversy, during the
1970s a number of major chemical episodes occurred that fueled
the issues. In July 1976, the Seveso Accident occurred wherein
a small Italian community became contaminated with TCDD as a
consequence of an accidental release of reactor products from
the synthesis of trichlorophenol. The following years, the controversy surrounding the Love Canal made front page news throughout
the United States and Europe. This was subsequently followed by
the evacuation of Times Beach, Missouri, as a result of the dioxin
contamination from the improper disposition of chemical wastes.

�- 4-

All of these episodes, conbined with the regulatory response of
the United States Federal Agencies resulted in further commitment
of national and state resources to adress the human and environmental impact of dipxin and the phenoxy herbicides.
The scientific resolution of the Agent Orange controversy presumable rests with the results of human epidemiologic studies
assessing the long-term effects of exposure to TCDD and whether
the veterans' complaints are consistent with the data. Of course,
one major as sumption would necessarly be that military personnel
reporting health effects were, in fact, exposed to Agent Orange
and, hence, to TCDD during their tours in Vietnam. Regardless
of any reported health effects, a valid study must include examination of all facets of the controversy.
This requirement poses a dilemma in any attempt to answer the
second question because objective analysis depends on such an
examination, but there are simply no models available for analyzing
environmental health issues.
In a subsequent chapter of this book, Young, proposes that the
examination of environmental crises involving other chemicals
can provide a useful parallel for analyzing the Agent Orange controversy. Accordingly, he suggests that there are a series of
events that describe the nature of "quality of life" controversies
and that these are predictable events. Hence, the chapters and
topics of this book are intended to elucidate such characteristics
as adequacy of the scientific data and assessement of the political,
social and legal issues of the Agent Orange Controversy. It is
appropriate that we adress these components of the controversy
at this time because much, if not most, of the information necessary to make informed judgements is now available. In addition,
certain actions of the courts in the United States, Italy, and
Australia, have taken action that have a significant impact on
the final outcome of the controversy.

�- 5-

On May 9, 1985 the district court for the Eastern District of New
York rendered the final judgement on the largest class action
lawsuit in American legal history, i.e., the Agent Orange product liability litigation.
The central issue of the case was "the ability of the plaintiffs
to demonstrate the necessary causal connection between the exposure of the veterans to Agent Orange and the subsequent development of a variety of ailments".
In the final judgement it was concluded that the incidence provided
by the plaintiffs "lacks sufficient probative force, except in the
case of chloracne, to permit a finding of general causality".
On July 31st, 1985 the Australian Royal Commission on the use and
effects of chemical agents on Autralian personnel in Vietnam,
presented its final report of inquiry to the Governor General.
The report concluded that neither Agent Orange nor the chemical
agents used to defoliate battle zones in Vietnam have any causal
connection with the ailments of the Australian Vietnam veterans.
At about the same time (May 1985) the Court of Appeal of Milan,
Italy, revised the first judgement on the defendants in the Seveso
case largely accepting their claims and the International Steering
Committee for the study of the effects on health of the Seveso
accident concluded its work stating that "nearly 8 years after the
accident in Seveso it has become obvious that besides chloracne
in a very small group of children, no adverse health effects
related to the chemical produced by the accident have been oberwed".
These events prompted us to ask the question whether the outcome
of the judiciary assessements of the Agent Orange issues and the
conclusions of the International Advisory Committee steering the
health surveys of the Seveso population exposed to dioxin could be
taken as a landmark also for the other aspects of the same issue,
i.e., the medical and scientific, the social and political issues
associated with it.

�- 6-

We thought may be the time had arrived for trying to come to a
conclusion of a controversy which has been at the center of concern of million of people and of the governments of several
nations of the western world, beside having affected and changed
the course of our personal life for more than 10 years.
Hence we readily accepted and greatly appreciated the offer of
the Toxicology Forum to present an assessement of the controversial issues related to Agent Orange and Dioxin in the light of
our present knowledge at the Summer Meeting in Aspen, July 1985
and at the Winter Meeting in Washington in February 1986.
We are aware of the difficulties of the task which we have set
for us. In our quest of truth we have approached the issue of the
Agent Orange controversy and its association with Dioxin with
hunrilty, conscious of the impact it has on human lives. However
we tried to remain faithful 1 to the rules of the scientific tradition of research that requires unequivocal proof of cause and
effect relationship in its experimental models. In the choice of
the contributors we have looked not only for professional competence but also for qualities such as reason, logic and objectivity.
We trust that all of us as well as the selected audience of the
Toxicology Forum which discussed the presentations have been
accurate and unbiased.
The future will tell whether in fact the conclusions of the New
York district court and of the Royal Commission of Inquiry mark
the end of the Agent Orange controversy. It is our fervent hope
for all concerned that this will be the case.
However already now we would like to acknowledge the help, advice,
and support we have received from so many scientists and scholars.
Without their suggestions, their sympathy, their goodwill and competence we would not have been, able to put togheter an adequate
account of the Agent Orange controversy.

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&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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This manuscript is a draft version of a chapter or section
from the following book: Agent Orange and its
Associated Dioxin: Assessment of a Controversy.
Young, A. L. and G. M. Reggiani, eds. New York:
Elsevier, 1988. This book is available in the NAL
collection, call no.: RA1242 T44 A3.

Tuesday, May 15, 2001

Page 1502 of 1514

�CHAPTER 15

"AGENT ORANGE IS JUST TOO POTENT A DEMON TO BE EXORCISED
BY SCIENTIFIC FACT: IT MUST BE PROPITIATED."
CONCLUSIONS AND IMPLICATIONS FOR THE FUTURE
A. L. YOUNG AND G. REGGIANI

As noted in the introductory chapter, it is OUT premise
that the Agent Orange Controversy involves more than just
the examination and interpretation of scientific data. Indeed, it is clearly a "quality of life" issue, an issue
full of human emotion, drama and tragedy. The scientific
issues are complex, but careful health surveillance programs
and epidemiological studies provide us with an understanding
of the human toxicologic issues. It is, however, beyond the
scientist to assess the human impact of having participated
in a confusing and frightening war more than a decade ago in
a tropical environment thousands of miles from home.
Many hands have worked at producing, developing, and
taking to a resolution the controversy which surrounds Agent
Orange. There is a never-ending list of books, articles,
newsree.ls, television broadcasts, scientific papers and
reports that have dealt with this fascinating and, at the
same time, frustrating topic, fascinating because it has
challenged the most skilled, and educated minds to understand
and disentangle the riddle of an extremely experimental toxicity of a chemical which seems to be hardly toxic for man,
and frustrating because the perception of its risk for mankind
has always been fraught with so many emotional, and psychological,
social, and political aspects which have made it almost
impossible to come to a definition of risk and therefore to a
resolution which would be satisfactory for all involved.

15: 1

�The perception and the level of acceptance of this risk
have changed continuously during the past twenty years and
are still a matter of dispute.
In this book we have made an attempt to take the
matter from the very moment when Agent Orange was first
produced and used in tactical military programs in the 1960's
to the events which in 1985 crowned the twenty years of the
controversy about its use and the consequences caused, or
allegedly related to its use. Each chapter has offered a
piece of the whole picture, starting with Agent Orange's
use in Vietnam for military purposes, through the identification of the dioxin contaminant, followed then by the
first reaction to the contaminant's subsequent involvement
in other episodes. From a localized and rather illogical
source the issue has spread wider and wider and has finally
involved, the best resources, time, work, skill, facilities,
and experience of the whole nation.
The dominant role played by the media in the controversy
began in the late 1960's and early 1970's and was characterized
by exploitation of all unfavorable news about the Vietnam war.
The use of Agent. Orange and other herbicides was a ready
target for adverse coverage by the press. Unfortunately,
attempts by the media to exploit unfavorable news adversely
affected American attitudes toward Vietnam veterans. Ten
years after Agent Orange was used in Vietnam, the media
continued to criticize, exaggerate, and emotionalize the
use of herbicides in jungle warfare, but, in this instance,
they played, reverse roles by casting Vietnam veterans in
the image of victims.
Emotional role playing by the national news media has
had tragic consequences for the American and Australian people
in a number of ways. It has undermined national unity and

15: 2

�morale by promoting unfounded fears of a cancer epidemic, of
increases in the number of children born with defects, and
misguided ideas of a "risk-free" society. The loss of perspective in this issue has led to irresponsible and unwarranted action, e.g., prohibition or restriction of the use
of herbicides in agriculture. But, perhaps the most serious
consequence of the intense media campaign has been its
negative impact on. the Vietnam veterans, many of whom have
been led to believe that Agent Orange and dioxin adversely
affected their health and the lives of their children. The
emotional impact of this fear campaign on the veteran and
his family has been severe.
The chapter on the state of our knowledge of the animal
toxicology limits itself to only a minimal part of the huge
amount of work which has been carried out in the best toxicology centers and. laboratories of this nation and of many
other nations, too. It tolls us that many aspects of the
mechanism through which the contaminant of Agent Orange,
dioxin, affects the organism are still unknown or not yet
understood. If many questions have been answered, many
others still puzzle our minds, and we do not know where and
what to look at for filling the gaps.
The chapter on epidemiology makes once again clear to
all of us how limited are our possibilities to find the
evidence of an effect on human health when we cannot fix
ourselves the dose at. which a man has been exposed to the
chemical as well as the time, duration and conditions of
the exposure. Furthermore, it points out once again the
difficulties in assessing whether a baseline condition of
the human pathology (cancer, birth defects, abortions,
infertility) has been modified if the effect does not
significantly change the basic incidence and frequency of
that, pathology. It tells us also how long it takes to

15: 3

�plan, organize, carry out and evaluate epidemiological
studies. It tells us finally that ten epidemiological
studies and five health control studies are still under
way and that it will be many more years before we can
know their outcome.
Science, therefore, has still not provided the final
answer for bringing to closure the Agent Orange controversy.
Even so, the answers which have been made available up to
this moment have provided to other forces of society the
means to move on and make some very important decisions.
The political and judiciary institutions of this and other
countries have decided which health damages possibly related,
to exposure to Agent Orange can entitle the Vietnam veterans
to compensation and have judged that the producers of Agent
Orange have no legal liability for its use in the Vietnam
War.
The role of the judiciary, e.g., the Australian Royal
Commission of Inquiry, has been of outstanding importance
for the scientific world in connection with the case of soft
tissue sarcoma and its association with dioxin which was
raised by several Swedish reports beginning in 1979. This
association is fixed in the minds of many, including Congress,
and clearly all scientists examining the dioxin problem and
the episode of exposure to dioxin have had to account for this
rare type of tumor, which in the United States has a death
rate of 0.07 per cent. The judiciary, with its cross-examination procedure and direct confrontation of the ways and methods
used by the authors for the assessment of their cases, took
the function of the "science courts" of ancient notion.
The additional evidence obtained directly from the scientists
who found the association showed that many of their published
statements were exaggerated or not supportable, that in their

15: 4

�assessments there were many opportunities for bias which
had been ignored, and that these biases have been introduced
in the collection of their data. The Royal Commission showed
that their conclusion could not stand a logical and objective
examination and had to be rejected. Moreover, it clearly
showed that there are criteria that one can apply in closing
off a scientific issue, i.e., the issue of the association
of soft tissue sarcoma with dioxin.
In the opinion of one expert in cancer epidemiology
known the world over, Sir Richard Doll, which was submitted
to the Judge of the Australian Royal Commission in December,
1985, "the work of these authors should no longer be cited
as scientific evidence."
To complete the picture we have added for the reader
the stories of four episodes of dioxin exposure, each one
adding to the whole picture by reporting different conditions of and different approaches to the same issue.
Agent Orange is indeed at the crossroads of science
and social concern. Resolution of the controversy must
come through a process that separates factual, scientific
elements from social and political considerations. Once the
scientific aspect is clearly defined, the issues can be
partially assessed in the legal arena, but eventually they
are seen as critical differences in value systems that too
frequently place scientists, government officials, and
individual citizens in adversary relations. In a free,
democratic society, the public must eventually understand
the truth and make the final decisions on issues relating to
the quality of life. Thus, the key for us has been to help
provide a basis for decision making.
15: 5

�It. remains for us to express our opinion on the dispute
that has offered too many contrasting and ever-changing
aspects. First of all, did the controversy have any scientific,
technical, political, or social reason to become, nationally
and internationally, a most remarkable subject of concern
during the last twenty-five years? This, we believe, is a
moot question which nobody can decide. It has been, and
to a certain extent still is, a part of our life which has
to be accepted and respected both for itself arid for the
contrasts and emotions, honest work and efforts which it
has enticed in this arid in other nations. It could be argued
that, with the state of our present information, the meaning
of the Agent Orange controversy has been exaggerated and that
dioxin today can be considered a matter of questionable
importance, It could also be argued, consequently, that
further investments in terms of manpower, facilities, time,
and money to obtain a deeper and wider knowledge of the risks
and hazards posed by dioxin are not justified anymore because
they would not take us to a better understanding of the problem or that the advantage obtained would be minimal and not
proportioned to the efforts required.
It should be said at this point that one must distinguish
between the Agent, Orange and the dioxin issues. While it is
true that no more studies are required beyond those already
running on Agent Orange-exposed Army and Air Force personnel,
this does not apply to dioxin. If the Agent Orange controversy
on one side has been settled in Congress and the courtrooms,
the dioxin controversy is still very much alive and a source
of great concern to the public. By dioxin controversy we
mean, that today we know that the dioxin which was the contaminant of Agent Orange, as well as all other dioxins belonging
to the same chemical class, are a part of our environment.

15: 6

�Sizable amounts of these dioxins and of TCDD, as well, occur
as a fallout of combustion elements and are part of a bioaccumulation process in the fish of the Great Lakes region,
and elsewhere, and are therefore part of our food. We are
not. aware of any acute effect on the health of populations
exposed to the dioxins either in the U.S. or in any other
parts of the world. What we do know is that dioxins are a
part of the group of chemicals which we are absorbing one
way or the other in our bodies and that this is not an
acute, occasional, accidental, or occupational kind of
exposure, but a protracted, chronic exposure to quantities
which are certainly minimal but for which the effects on
our physiological functions and on our organs cannot be excluded and of which practically nothing is known.
It is therefore understandable that public concern
and concern of the scientific and political institutions
has focused on the potential implications of the dioxins for
our health. The issue, therefore, is not the Agent Orange
controversy but the broader issues of how to assess risks
and estimate the hazards to people caused by the chemical which
has given such a dimension to the Agent Orange controversy,
namely, the 2 , 3,7,8--tetrachlorodibenzo-p-dioxin (TCDD).
Historians are not part of the process of risk assessment, Their function is to relate events accurately, without
dramatizing certain facts and underestimating others. Historians must collect and put events in a certain perspective
to provide the student of the past with the witnesses and the
information which should help him in his judgment and equip
him with the available tools for his task and profession. This
is what this book is about. And if it accomplishes what it
was meant to do, our labor has been well spent.

15: 7

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°2104

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Young', Alvin L.

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Report/Article HtlB Letter: From Alvin L. Young to Justice Phillip Evatt
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Personnel in Vietnam

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Augustas
D

1

See ltem 1444 for Gou

9n's article as referred to in the letter
and Items 2078 to 2086 for the Final Report

Tuesday, August 21, 2001

Page 2104 of 2109

�EXECUTIVE OFFICE OF THE PRESIDENT
OFFICE OF SCIENCE AND TECHNOLOGY POLICY
WASHINGTON, D.C. 20506

August 28, 1987

Dear Justice Evatt:
I wish to call your attention to a recent article published
in the National Academy of Sciences' Journal ISSUES IN
SCIENCE AND TECHNOLOGY. The article, titled "Environmental
Epidemiology: Separating Politics and Sciences", was
authored by Dr. Michael Gough, a former Senior Associate
with the Congressional Office of Technology Assessment. In
his article (copy attached, pg. 27) Dr. Gough noted, in
discussing the concerns of the United States Congress for
the Vietnam veteran via a mandated epidemiologic study, that
the origins of the Agent Orange study were obviously
political and social. Hence, he stated: "I believe it is
poor policy to conduct science for purely political reasons.
The better response is to deal with the social and
scientific problems separately". The key, Gough concludes,
is to know when science cannot provide the answer and when a
political decision must be made instead.
In reflecting back to the Final Report of your "Royal
Commission on the Use and Effects of Chemical Agents on
Australian Personnel in Vietnam", it is apparent that you
recognized the limits to which Agent Orange was a science
problem. Indeed, I believe you correctly concluded that
Agent Orange was but a symptom of a larger problem--our
society's inability to deal compassionately with the Vietnam
veteran. I hope your Commission's Report has led the way to
settling the difficult issues of re-adjustment by both the
Vietnam Veteran and the Australian Public.
I wish to again express my appreciation for the
opportunities we have had, in both Australia and the United
States, to meet and express our joint concerns for the
courageous men who served our countries during the Vietnam
Conflict.
Sincerely,

Alvin L. Young,
Senior Policy Analyst
for Life Sciences
The Honorable Justice Phillip Evatt
Royal Commissioner
c/o Selborne Chambers
174 Phillip Street
Sydney 2000, Australia

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ooiss

Author
Corporate Author
Press

Release: Secretary Schweiker's "New" Data Turns Out to Be "Old" Data,
September 24, 1981

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Year
Month/Day

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DBSCriptOR Notes

Press release about an announcement made by G.V. (Sonny) Montgomery,
Chairman, U.S. House of Representatives Committee on Veterans' Affairs regarding
a press conference given by Secretary Schweiker of the Department of Health and
Human Services.

Friday, January 05, 2001

Page 188 of 194

�FOR IMMEDIATE RELEASE

CONTACT:

Ralph Casteel
225-915i

SECRETARY SCHVEIKER'S "NEW" DATA TURNS -OUT TO BE "OLD" DATA

The Chairman of the Veterans' Affairs Committee of the U. S. House
of Representatives, G. V. (Sonny) Montgomery (D-Miss.). announced this
morning that Secretary Schweiker of the Department of Health and Human
Services has needlessly caused undue alarm and concern by his press
conference yesterday on supposedly new data that had been brought to
his attention pertaining to "aerial dumping of herbicides" on American
troops in Vietnam.
The "new data" had been made public more than a year ago —
September 16, 1980 — by Department of the Air Force witnesses before
the Subcommittee on Medical Facilities and Benefits of the House Committee
on Veterans' Affairs.

The record of this hearing was published.

A representative of the Secretary of the Department of Health and
Human Services served as Chairman of an Interagency Work Group appointed
to study the adverse effects of phenoxy herbicides, including Agent
Orange, In humans and was a witness at the same hearing in which this
"new data" was announced.
Chairman Montgomery said, "I regret that Secretary Schweiker did
not check with his staff concerning the disclosure of this information
at our Committee hearing last year.

It serves no useful purpose to

hold press conferences such as that held yesterday by the Secretary.
Such procedures at the highest level of government obviously cause
much emotional upheaval for Vietnam veterans and their families and
for my colleagues and others who are doing everything possible to
determine whether there are long-term health effects due to exposure
to Agent Orange and other herbicides used in Vietnam."

�Montgomery said, "I intend to take this matter up with Secretary
Schueiker personally, and I hope he will begin to work with the Congress,
the Veterans Administration ai;d others in a concerted effort to resolve
these problems rather than going off on his own with press announcements
that serve no useful purpose.

I will ask him to join all of us in the

Congress who are working diligently to resolve this complex issue and
to join in supporting congressional initiatives contained in H. R. 3499
that will provide health, education and employment benefits for all
Vietnam veterans.
results."

September 24, 1981

Working together will hopefully bring about positive

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