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                    <text>Item D Number

°1968

Author

Young, Alvin L.

Corporate Author
RBOOrt/APtiClB Title

Lettcr

to J. S. Coombs from Alvin L. Young. January 25,

1984

Journal/Book Title
Year

000

°

Month/Day
Color
Number of knages

3

Young responds to Coombs's letter of January 13, 1984 (also
included in item), discussing Young's support of the
Australian Servicemen's Health Study protocol and his
concern about the commitment of resources. See item 1969
for continuation of this line of correspondence.

Monday. July 30. 2001

Pago 1968 of 1993

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

January 25, 1984

Dear Mr. Coombs:
I have reviewed your letter of January 13, 1984 requesting
my signature on the attached document as affirmation that
the Australian Servicemen's Health Study is "epidemiologically
sound and feasible and that its performance is scientifically
desirable."
I fully appreciate your concern that the protocol is now
finalized and that it is imperative for the study, if approved,
be initiated immediately. My concern is not whether the protocol
is epidemiologically sound (in my opinion it certainly is) nor
whether its performance is scientifically desirable (in my
opinion both of our nations will gain valuable information from
this scientific study), rather my concern is with the word
"feasible." The study is feasible only if the resources are
committed. The commitment of resources to such a study is not
one that should be made lightly. It will involve governmental
priorities and political concerns. As an "outsider" I must
not contribute to those deliberations.
I endorse the scientific validity of the protocol and recognize
the importance of conducting, in a timely manner, health studies
of veterans who served in Vietnam.
Sincerely,

«r.

//'

,

Alvin Lj Y~6ung
Senior Policy Analyst for
Life Sciences

Mr. J. S. Coombs O.C.
G.P.O. Box 4842
Sydney, N.S.W. 2001
Australia

�ROYAL COMMISSION ON THE USE AND
EFFECTS OF CHEMICAL AGENTS ON AUSTRALIAN PERSONNEL
IN VIETNAM
Commissioner: The Hon. Mr Justice Phillip Evatt DSC
Secretary: Mr B.D. Meade

G.P.O. Box 4842
Sydney. N.S.W. 2001
Telephone: (02) 239 6222
13 January, 1984

Dr. Alvin L. Young, Lt. C o l . , U . S . A . F . , PhD,
Senior Policy Analyst for L i f e Sciences,
Executive O f f i c e of the President,
O f f i c e for Science and Technology Policy,
WASHINGTON DC 20500 USA

Dear Al,
Notwithstanding the participation of all members
of the Scientific Advisory Panel in the finalisation of the
protocol our masters require the attached confirmation of
the agreement reached which I included in a letter to the
appropriate Minister. Accordingly I would be obliged if
you would return the attached document as a matter of extreme
urgency.
Kind regards,

J. S. Coombs Q.C.

Attachment.

�The Hon. Mr. Justice Phillip Evatt DSC LLB,
Royal Commissioner,
Royal Commission on the Use and Effects of
Chemical Agents on Australian Personnel
In Vietnam,
G.P.O. Box 4842,
SYDNEY. N.S.W. 2001
Dear Judge,
We the undersigned, members of your Scientific
Advisory Panel, hereby confirm that we took part in a review
and critique of a protocol for Australian Servicemens Health
Study leading to its consolidation into the protocol dated
22 December, 1983.
We confirm our agreement that the study is
epidemiologically sound and feasible and that its performance
is scientifically desirable.
Yours sincerely,

Dr. Bruce Armstrong

Dr. Tony McMichael MB, BS

Dr. John Mathews B. Sc, MB, MD, MRACP,
PhD, FRACP

Dr. D. Riedel, M.Sc, PhD

Dr. Alvin Young

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                    <text>ftemU Number

0197

Author

Young. Alvin L.

°

Executive Office of the President, Office of Science and

RBPOrt/ArtiClB Tlth

Lettor to

6, 1984

Mrs. Pat Bragg from Alvin L. Young. February

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Letter discusses the telephone conversation that Bragg and
Young had the previous week regarding the official visit of Mr.
John Coombs and Dr. John Matthews from the Australian
Royal Commission on the Use and Effects of Chemical
Agents on Australian personnel in Vietnam. The mentioned
attached itinerary is missing. See item 1966 for proposed
itinerary for this visit.

Monday. July 30. 2001

Page 1970 of 1993

�EXECUTIVE OFFICE OF THE PRESIDENT
OFFICE OF SCIENCE AND TECHNOLOGY POLICY
WASHINGTON. D C 20600

February 6, 1984

Dear Mrs./Bragg:
This is to confirm our telephone conversation of last week
informing you of the official visit of Mr. John Coombs and
Dr. John Matthews from the Australian Royal Commission on the
Use and Effects of Chemical Agents on Australian Personnel
in Vietnam (itinerary attached). Dr. Matthews is the principal
investigator of the Australian Serviceman's Health Study and
Mortality Study. The two men will be in Washington for the
release of the Air Force Health Study, February 24, 1984,
and requested that arrangements be made with the Air Force
for them to meet with the Air Force Principal Investigators.
Mr. Coombs and Dr. Matthews have suggested either a late
afternoon or an evening meeting on February 24, or a meeting
on Saturday morning, February 25. Dr. Barclay Shepard,
Veterans Administration, has offered to provide an office for
the meeting. I would appreciate your assistance in coordinating
the meeting between these two scientific teams. If you have
any questions or if I can be of assistance, please contact
me at 395-3125.
Sincerely,

to

Alvin Young"
LT COL USAF, Ph.D
Senior Policy Analyst
for Life Sciences

Mrs. Pat Bragg
HQ USAF/SGI
Boiling, AFB, D.C.

cc:

20332

Dr. Barclay Shepard

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                    <text>Item D Number

01959

Author

Young. Alvm L.

Corporate Author
RBpOPt/ArtiClB Titta Letter to The Honorable Mr. Justice Phillip Evatt from
Alvin L. Young. January 26. 1984

Journal/Book Title
Year

000

°

Month/Day
Color
Number of Images

1

DOSCrutOn NOteS

Young endorses the scientific validity of the Australian
Servicemen's Health Study protocol and recognizes the
importance of conducting this study. See item 1968 for
correspondence leading to this letter.

Monday. July 30. 2001

Page 1969 of 1993

�EXECUTIVE OFFICE OF THE PRESIDENT
Ol F ICE OP SCIFNCF AND TECHNOLOGY I'OL ICY

January 26, 1984

Dear Judge,
I endorse the scientific validity of the protocol
for the Australian Servicemen's Health Study and
recognize the importance of conducting, in a
timely manner, health studies of veterans who
served in Vietnam.
Sincerely,

Alvin L. Young
Senior Policy Analyst
for Life Sciences

The Honorable Mr. Justice Phillip Evatt DSC LLB,
Royal Commissioner,
Royal Commission on the Use and Effects of
Chemical Agents on Autstralian Personnel
In Vietnam,
G.P.O. Box 4842
SYDNEY. N.S.W. 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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01885

Author
Corporate Author
RUpOrt/ArtiClB TltlB Submission to the Scientific Advisory Committee,
Australian Veterans Herbicide Studies, 3rd Meeting to
be held in Sydney 3 &amp; 4th March 1981.

Journal/Book Title
Year

1981

Month/Day

February 26

Color

!

Number of Images

64

Descrlpton Notes

Wednesday, July 18, 2001

Pago 1885 of 1908

�26th February, 1901

SUBMISSION TO THE! SCIENTIFIC ADVISORY COMMITTEE
AUSTRALIAN VETERANS HERBICIDE STUDIES

3rd Meeting to be held in Sydne.y
3 &amp; 4th March 1981

SECTIONS:

1. Pilot Study FJroposa3

. •

2. Progress Report on Exposure Lstiiuatiun
*

3. Revised Plans ?.nd Estimates for ths Study

�SECTION 1

^

:

' " - . : '

• -.

••

PILOT STUDY PROPOSAL

Page
1.

AUSTRALIAN VETERANS HERBICIDE STUDIES

•

.

1

• 1.1 EJackground

1.2 Postulated effects of herbicides
2. AIMS AND OBJECTIVES OF THE PILOT STUDY

7

2.1 General Aims

.2.2 Specific Objectives

'

3. RESEARCH PLAN

'

_

"

-

•

"

A." METHODS OF DATA COLLECTION TO RE TESTED FOR THE FAMILY SURVEY

8
13

A.I Data collection methods to be tested
A. 2 The questionnaire
Zf."3" Data collection by Questionnaire

-

A.A Coding and data entry for Questionnaire
• A.5 Medical history and examination
5. VALIDATION OF fCDICAL DATA

'• •

" . . ' . "

19

5.1 Overviev/
/

5.2

Methodology

5.3 Conditions to ba validated
5.A Service Medical Records
5.5 Non-Service Records
6. COKTIDIKTIALITY AM) PRIVACY ISSUES

'"'

23

6.1 Confidentiality
6.2 Privccy
7.

STATISTICAL AfiALYSIS G;r 1i!F. PILOT STUDY

25

8.

ATrNDJCES

28

'

8.3

SI rue I urc; of tht1 lnte::vicv//C?Jf-&gt;stionr!£iirc

fi.?

Structui-R of •:•'.? t-tjo'.ical Hirtory and Modical Examination of
Adu3ts

B.3 MedJcal Cxor:i.i.n::;.iur-; of Children

�&gt;

• •

-1-

•

.

1. AUSTRALIAN VETLMhS HERDiCIDC STUDIES

I.I Kackground

.

'

.

.

. '

•

In its report of its second meeting he.ld in Sydney 14th
September, 1980 the Scientific Advisory Cormjittcc (SAC) considered a
research protocol which set out the broad long-tern 'strategy proposed by
the investigators from the Commonwealth Institute of Health. The
Committee reported that it "considered these planned investigations to
cover fairly completely the possibilities for epidorniological
investigation in Australia of the effects of herbicide exposure in Vietnam
during the Vietnam war". T!" . Committee identified measurement of exposure
to herbicides and the comparability of Vietnam veterans and a proposed
control group as two key issues which must be clarified before the
scientific viability of the whole study could be assessed. The Committee
also recommended expanded pilot studies to provide the data necessary for
a fully informed choice of the best method within a spectrum ranging from
a mailed self-administered questionnaire (SAQ) to interview and medical
examination of all-veterans and their progeny. It was considered that as
far as possible these preliminary investigations should be incorporated
into a single pilot study to avoid the delays of a sequential approach.
It was noted that there may be advantage to all concerned if the Committee
were to review plans for the pilot study prior to their commencement.
Work is currently proceeding according to a plan drawn up for the
pilot survey. Due to limited resources in personnel end shortage of'time
it has not been possibJe to provide completed documentation for all
aspects of the pilot study. The present submission is a summary which has
been prepared to meet a deadline. Further development, particularly of
data collection instruments, is proceeding rapidly cr.ci more information
could be-nade available to the Conndttee during its meeting, if so desired.
A progress report on exposure estimation .is subr.iittex' in section 2 and
revised plans and estimates for the investigation are submitted in section
3.

�*

• - 2 -

.

.

.

I'2 Posiulolnci effects of herbicides*
The terms of reference as given by the Department of Veterans'
Affairs to the now Commonweal th Institute of Health concerned the possible
effects of contact v/ith or exposure to Agent Orange and subsequent
disabilities in Australian veterans, or in complications of pregnancy in
their spouses and the occurrence of congenital malformations in their
offspring. Although the possible effects of Agent Orange remain the primary
concern of the investigators, the possible effects of exposure to other
herbicides such as Agent Blue (cacog'ylic acid) will also be actively sought
in the investigation.
Agent Orange consisted of a mixture of 2,4-D and 2,4,5,-T. The
latter is contaminated during manufacture with TCOD
(2,3,7,8-tetrachlorodibanzo-para-dioxin). The pharmaco-dynamics and
toxicology of these chemicals has recently been reviewed by the Department of
Health. 2,4-D may be absorbed from the gastrointestinal tract or by
•inhalation. Little absorption occurs directly though the skin. Absorbed
2,4-D is quick] y excreted from the body, mostly in urine as the free acid.
It does not accumulate in the body. There are many reports of consumption of
•sublethal doses of 2,4-D without any apparent ill-effects. However,
occupationally exposed workers have complained of rcn-specific symptoms such
as excessive fatigue, epigastric pains, anorexia (loss of appetite),
occasional upper respiratory tract symptoms and impaired taste sensitivity.
Medical investigation has not implicated 2,4-D as the cause of all symptoms
but did suggest indications of increased incidence of liver disc9.se among
workers with chronic exposure to herbicides. Isolated cases of peripheral
neuropathy and contact dermatitis following exposure to 2,4-D have been
reported.
2,4, 5- T is readily ah; orbed from the gastrointestinal tract after
incjGstion and probably aftcr_ inhalation. Skin absorption, however. is
slight. Like 2,/t-D it is readily excreted and is not stored in the: body.
.Stove rnetaoolism does occur in animz-.ls but the bulk is secreted unchanged in
the urine, "iho oral dose required to produce symptoms in man is probably
three to four grains. Medical exyrcination of workers engaged in the
manufacture of 2,4,5-T has shown increased incidence of chloracne which could
be attributed to the presence of TCDD as an impurity. It should be noteci
that increased incidences of urinary por'phyria, chloracnc and nirrutisrii have
been demonstrated in workers employed in n^nufc.cturing chlorinated phenols
such an Z/ijS-trichlorophonol, the precursor of 2,4,5-T. Again, the
responsible agent could be TCDf), and most reports do not distinguish its
effect from possible: effects cf 7,4,5-T. 2,4,5-T has been shown to csuse
toratogenic effects in animals which cannot be wholly attributed to the;
presence of toxic impurities such r.s TCOE.). Who the v or not 2,4,5-T is
carcinogenic cannot be deduced conclusively from results reported to date.
2,'i,5--T, like 2,4-D, does not- increase mutation rates nor stimulate
mutc'C^nic responses in rats r.nd mice. Jt does, hov/ever, produce chromatic!
a bnorma lilies, j.n vitro in cultured n-jiioi lyriipiujcylos and affect the
cf).ccn.os;o!::«j!S onrj j.eproUuclivG Riec-lianisms of dioui-e si/j hamster bone narrow
cells. It shcvjjd I: -2 r.Jclefl, however; that these effects may IKIVO been due to
cellular toxicity lather than ^etTit.ic ol.tei
Information in tl-.ir; section has been obtoinscl Riciniy from ur,[rjb}is!ii-cl
doc%;.i:writi, preparcci tiy tf-o ii;:parLi".t:nt of Health,

�•-

.

-3-

• . ' TCDD was present in Agent Orange and Agent Purple used by U.S.
military forces in South Vietnam. Kr.av/Jeclge of the toxic effects of TCDD in
man comes mainly from medical assessment of occupation-ally exposed workers
engaged, in the production of chlorinated phenols and their derivates.
Limited data are available from known episodes of exposure of the general
population. Table 1.1 lists known toxic effects attributed to TCDD in
TABLE 1.1 TOXIC EFFECTS OF TCDD IN MAN

Dermatologi ca1; Chloracne
Porphyria cutanea tarda
Hyperpigmentation and hirsutism
Internal:

,
"~

~

Psychifit3.\ic:

Liver damage (mild fibrosis, fatty
changes, haernofuscin deposition and
parenchymai-cell degeneration)
Raised serum hepatic enzyme levels
Disorders of fat metabolism
Disorders of carbohydrate metabolism
Cardiovascular disorders
Urinary tract disorders
Rc'spiratory tract disorders
Pancreatic disorders
Polyneuropathies
Sensory impairments (sight, hearing,
. ' 'smell, taste)
Neurasthenic or depressive syndromes

Source: Horcberger, E. Reggi&amp;ni, Ci. Sarnbreth, 3. and Wipf, U.K.,
^J.CL.J^9.u;Pj_jJyil- ^2» 2273 (1979)
Expos2cJ individuals may develop a variety of medical conditions with
chloracne, n-?LirologicRl and behavioural changes, liver end fat metabolism
disorders end signs of porphyria cutanea t&amp;rda (a disorder of porphyrin
metabolism) arr.ong the most frequently rej.iort»d toxic effects. Reports from
Sweden have shown recently a statistically significant c'ssociation between
human exposure to chlorc;:f;enoxy acids and chj orophcnols end increased
incidence of certain soft, tissue sorccr-iata snci lymphomata.

�Table 1.2 summarises the results of some toxicological experiments
with TCOD in laboratory animals.
TABLE 1.2 TCDD - EXPERIMENTAL TOX1CITY
•A

Dose
LDtjQ for laboratory animals
Systemic lesions (liver, blood,
skin, etc) and clinical chemistry
abnormal findings at chronic
administration
Embryotoxicity, foetotoxicity,
postnatal growth retardation
Reproduction, fertility
Immunodeficiency (atrophy of
lymphoid tissue)
Enzyme induction
Carcinogenicity
Mutagerdcity (?)

(0.6-ll5)ug/kg

0.1 ug/kg
0.25 ug/kg
0.01 ug/kg
0.1 ug/kg
1 ug/kg
0.1 ug/kg
2 ug/ml

(1) Indicative-; values
Note: lug = O.OOlmg
Source: Homberejer,

Regggiani, fi. Sambreth. J. and V/ipf, U.K.,
22, 3273 (1979)

Chronic toxicity of TCDD is most often manifested as hop::tic
necrosis (death of liver cells) and thymic and lymphojd atrophy. The degree
of hepatic involvement appears to be dose and species related. Suprossion of
the thyniu-; and lyrnphoid tissue leads to decreased iraiune responses in mice,
rats and guinea pigs. Acne of increasing severity v/as produced when
AS'Creasing doses of TCOD were applied to 7?abbit's ears. A total close of
0.002 to 6.C03 mo/kg over a nine month period produced severe hstmotoJogical
changes F.rsci death in rhesus monkeys, making these among the most
TCOD-susceptible animals tested.
TCOO is o potent teratogen which causes increased fetal mortality in
animals. It pio^uces cleft palate snd kidney rbnormalities in mice at doses
as low as 0.001 r.ig/ky whilst di?pres»s?ci fetal v/eight t-nd visoral Ic-sions, occur
in rats ot O.CC05&gt; to 0.003 nig/kg. Teratolcigical effects in rhcsuc- rnoniwys
h&amp;vs not bee;i demonstrated. Studies on the corcinorjenic potentifil of TCTJi)
h.r.ve bc.-cn Jess conclusive. The potential r;iutacenicity of 1CDD in hun;ans has
not bjen cttcr^inecl. reeding studies with i-ats tiavc not sh.own iT.utag3n.ic
effucU-. but TCiJi) has b&amp;en 5-.!N.o\vn to induce rnutagrnic changes in so.'i-;-: stjains
of bscterici, in common with many other substances.

�Cacodylic scid

•

.

•

When used as a herbicide cacodylic acid has the potential for
absorption by inhalation and through the skin. No human data arc known to be
available on its dermal absorption and very little is known about human
pulmonary absorption of organic arsenicGls. Ingested seafood arsenic is
apparently absorbed from the gastrointestinal tract. Whilst no data are
available on the distribution of organic arsenic compounds in humans, studies
with forestry workers exposed to cacodylic acid have demonstrated its rapid
urinary clearance form the body.
•
Study of the biotransformation of cacodylic scid in living rats has
shown that it is fairly stable i_n .vivo and is not converted to inorganic
arsenic. Any in vivo transformation of cacodylic acid in other species is
not clear. Little data are available on the chronic toxicity of cacodylic
acid in humans. Toxic effects of these organic arsenicals used as drugs are
mainly manifested in ths central nervous system and include encephalopathy
and optic atrophy. Other less frequent side effect include dermatitis, liver
damage and disturbances of the haemopoetic system. Cacodylic acid has been
considered as a source of intcxication of domestic animals leading to
symptoms similar to those produced by chronic ingestion of inorganic
arsenic. Chronic feeaing of cacodylic acid to rats and beagle dcgs has
produced..no significant effects on body weigh1;, food consumption, organ
weights, urinslysis or haematoionical system.
Organic arsenr'.cals have no known rnutagenic or teratogenic effects in
man or animals and no conclusive evidence cf carcinogenic activity in
laboratory animals is known. N'-j epidemic]ogical investigations r.re known to
have: been conducted on the carcinogenicity of cacodylic acid or other organic
arsenic compounds.
There are only three reported studies of the toxic effects to humans
of cacodylic acid end its salts in the recent literature. The most extensive
documentation of Cc'coclylic acid tox.icity in humans is that of Peoples £t «J_.
(I97i0. Tncse authors reviewed 3/i uncontroIJed cases of occupational
exposure finioogst CaHfornian agricultural workers which occurred bc-twcen
197J5--7?. exposure cccurrod as a result of misuse, accident or equipment
tfH.1function. Basically, cscodylic acid noted as a chemical irritant.
Ir.gsstiun produced nausea, coJic vr;;;iiting and diarrhriee;. Application to ths
fcye prc'Ciuceci ir.jjcj conjunctivitis whilst der.r.al application produced a contact
dermatitis or an alJergic response, The worst ca.se was that of a spray-rig
operator who received particularly heavy exposure by drenching of rhis
cJothing and by splashing of he.rbio.icie so.luLicr, into his mouth. H J was
hospitalised with "paralysis, irregular :rer.pir:-ition, nur-ibner-? anc! f^inti.r^g".
Investigation revealed no orcpn dr.rriare a. ici recovery was spontaneous. F'ull
rt-(,civory \.-)s always pvfrrpt in tfie yth;:r casc-s, anc! blood arsenic levels
al'./ctys rcn:air:r;'d nonr^l. No chronic effects were reported.

�[rir)rQ:inic Arsnnic
Chronic exposure tc rnco'icir.al inorganic arsenics such as Fowlers'
solution produces a characteristic syndrcr.se of tv/perpi client ntion followed by
keratoses and, infrequently, dermal neoplasia. "this distinctive clinical
syndrome has lead to general agreement that srsciiic can cause skin cancer.
There have been numerous reports and several epitieraiclocjical studies of the
incidence of cancer amongst workers occupational! y exposed to arsenic in
nining and metallurgy, in the chemical industry end in agriculture. The
cpidcmiological data are ccnsistcnt with but do not demonstrate a causal
relationship between inorganic arsenic and cancer of the skin and respiratory
tract.
• There is nothing in the recent literature to suggest that cacodylic acid
is degraded to inorganic arsenic _in vivo. Indeed there is ample evidence
that such a process wculd be contrary to the established metabolic fate of
arsenic compounds in r.i£rr.;nals.
Halclicsin (Malelhion)
Maidiosin is an organophosphorus insecticide of moderate mammalian
toxicity. It is rapidly rr;staboliscc! to a variety of products and excreted
laroc-'ly .in the urine. It is not cumulative in body tissues. Sublethai
exposure can cause depression of plasma colincsterasc activity but this
requires a high intake. Spontaneous recovery occurs after cessation of
exposure.
•
"
r*

Other insecticides used in Vietnam include DDT. The chronic toxicity of
DOT to fi.an has been thoroughly .investigated. Massive chronic exposure
produces orJy a mild 3tiniu.lat.ian of tho rnicrosomal enzymes of the .liver.

In this investigation the major postulated effects are those related to
TCi'JD, since- this is the.- potentially ruost toxic contaminant in Agent Orange
which comprised a very higi'i pioportiGn of'herbicide usad in Vietnam.

�42.

'

--

/.'-..••

AIMS AND OBJECTIVES OF THE PILOT STUDY

2.1 General Aims

§

.

-

.

The purpose of the Pilot Study is to assist in planning the mainsurvey. It addresses rnethodcJonical issues related to study design
including the comparability of Vietnam veterans snd the proposed control
group and, methods of data collection. It is not expected to provide
data on the effects of herbicide exposure in Vietnam but is expected to
test methodology and provide a basis for logical decision as to the best
and most acceptable methods 'if the conducting the main survey.
.2.2

The specific objectives of the pilot stuoy are as follows:
2.2.1. Tojrihqs_e t2etween_sever£l methods of data cohloctien.
The choice vail "be maae primarily on the response rate and quality of
data, although the cost and duration of data collection will also be a
consideration.
2.2.2. Cotnparability of Veteran jand Coritro.l Groups
The pilot study will obtain data on comparability additional to that
available a priori from existing records.
2.2.3. TesJ_o/_Prcced_ur8S_ toJ-'e_uspd

As far eis possible the procedures to be used in the family survey will be
.tested during the pilot study. The greatest eipphssis will be on data
collection and analysis related to the specific objectives of the pilot
study.

�3.

RESEARCH PLAN

3.1. Vietnam Veterans nnci Contro^ Grouos
1.
About 40,000 male army personnel served in Vietnam. About 11,000
male personnel served in the Army during the period of the Vietnam War but
were not sent to Vietnam. It has been decided to restrict the study at this
stags to male Arrny personnel for the following reasons:
(a) To avoid the introduction of possible confounding factors. This means
the veteran and control groups should be as homogeneous as possible.
The minimal medical standards of en cry into the three Forces were not the same. The Army had a far larger contingent of National Servicemen
than either the Navy or Air Force and the usual Service experiences
(e.g. diet, living conditions, combat conditions) of members of each
Force were presumably quite different. It was therefore decided to drew
the veteran and control groups from within a single Force.
(b) The possible herbicide effects could be very Final 1. As large as
possible a sample of veterans and controls should be considered so as to
maximise the chances of detecting such effects. The Army was the
largest Force and also contained the highest number of potentially
exposed individuals. It was therefore preferred to the Navy or Air
Force.
(c) There are only a few hundred potentially exposed female Army personnel.
Btcause of marriage and the subsequent change of surname it would be
difficult to contact these individuals. rurVh-.Tii'ore, even if all could
be contacted a few hundred is toe few for the lively detection of the
types of effects to bo. considered ir- the family survey. It was decided
to District the , study, at. least in;u.a!ly; to nisle servicemen.
Australian involvement in Vietnam ceased at the r;nd of 1972. It
was decided that only nale servicemen who enlisted pre-1573 and who served
-in the Army at some period during the Vietr.cm War years would be included in
the study. Of this group those who went to Vietnam will be known as the V
grou.o, those who did not v.-ill be known as the C group.

Before undertaking &amp; statistics! analysis of the possible effect cf
herbicide exposure, it is necessary to compare the V and C groups.
Significant differences bstw&amp;en the group? should IK-. noted and, whsre
possible, corrected for in the final analysis, "So date it hus been possible1
to compare the V and C groups on the basis of ac:a at en] is twin I:, tirns spont
in Avir.y and f,'atiorinl/i&lt;egujar service.-. The two groups jn:e str.ilcliccilly
significantly different (p 0.01) with lecipect to each of these three
variables. Figure 1 illustrates the results.
- The (.'ifferencn in the age at on.liii.ment' dJrlriL-u lions. of the V rind
C groups (fig 3.J (a)) is dun to the-: feet that, although there are none of
the C group in the GL" ':&gt;•'• category, their; o.rc: 417 of the V group in this
category. In the othe/: /i age at f;nl}.:;rnK:nt catec;o?-ios abivjl 85"; fa 12 in the
V cjvoufj and ]55c ;'o t!:e C QLOUO. Tho effects of c-ijo v.v:: '.•.icll--doc:uf'ientf.sd Jn
tha cpide.-niolc-jici-J l::tc.rati.ri?: ?.p.d it i-i'iajld bo j:c«3'jiblc to adjust for thi.:;

�Figure 3.1 (b) shows that, for the V group there is a higher
percentage of Regular servicemen than of National servicemen. Exactly
the opposite is true of the C group. It is not so obvious how one should
adjust for this difference between the groups. This matter needs close
attention. The psychological scores in the entrance medical exam could •
be of assistance in this regard as could further information to be
obtained via the pilot study questionnaires.
Figure 3.1 (c) shows that the V group is different from the C
groups in so far as a much larger proportion of the former remained in
the Army for more than six years (this being the shortest optional sign on period for a Regular serviceman). This difference is probably largely
attributable to the fact that more of the V group were Regular servicemen
making a career of the Army. However other effects could also be
operating and the data to be collected from the pilot study should be
studied closely with regard to this difference.
•The results of the pilot study will be needed before the
question of comparability csn be addressed more fully. This will give
information on other variables such as ethnicity, socio-economic status,
rural/urban living, together with a self-assessment of the reason for not
going to Vietnam. It is planned that Army medical records of the
entrance physical examination will be used to give medical and
psychological status at the time of enlistment.
3.3 fission of the Pilot Study
Twenty three Sydney metrcpolitpn electorates h^vn been
selected. Six hundred individuals are; to be drawn from these
electorates, 300 frcm the V group r.nd 300 from the C group. Three
different interview modes (self-administered (SA), telephone (T) and
face-to face (fF)) are to be assessed. One'hundred individuals; from both
the V and C groups will be interviewed under each method.
Figure 3.2 illustrates the egc at enlistment, length of service
and Rcgulcr/Mc-tional service profiles of the V and C subgroups in the
selector! Sydney electorates. Those should be compared with the
Austrcilia-wjoe profiles illustrates in figure 3.1. It ic clear that, at
leai-t on the basis of these; three variables, the chosen Sydney
electorates are representative of the whole of Australia for V and C
groups.
Since; age at enlistment, length of service end Regular/National
service rtetus have been slicv;n to be important variables, it was decided
to strsi'.ify v&lt;t.sn selecting trie pilot survey sample. To ensure that there
are a i-ufrlcionl nur-.ihsr of individuals in each stratum, some of the ck;t'?!
have b:,an cropped. Subject to the coritrainls in-posed by the overall
numbers ?;v?liable in the ehosc-r, Sydney electorates in each stratum, the:
design tio.s been chosen to be as "balan^d" as possible with respect to
th'j V ar.rj C groups. Table. 3.1 below FI-.CWS the i'.umbers to be. sampled from
each s'-rfiliuTi

�-10-

Mjmber of Veterans and Controls to be selected at random
from each stratum by service status ?.nd time in the Army.

Service

Time in

Status

Army

Vietnam (V)

non-Vietnam (C)

Age at enlistment

Ago at enlistment

LE 20 GT 20

Regular

GT 2 yr.

Army

,

38
38

' 42

National

GT 2 yr.

37

Service

LE 2 yr.

GT 20
43*

42

LE 2 yr.

LE 20

MARGINAL TOTAL

*

40*

16*

25*

14*

2*

37

41

48

89

150

150

150

150

the maximum possible number so far indentified as
resident in the Sydney study area.

�-II --

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.........i_..i_..,. ,,..j ...,.. ..—(...., ...... . . ... .
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Figure 3.1 I'VofiJca by (a) a^o, (l&gt;) RCI-VJCG .'.-.tc.tui- and (c) '}.C:!;£'r.h of
*

service: for Lho total population oT the V and C croups .if. /'.'U-;l.;v.O.:i.f-..

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for vhe

iilj.cn v.o be i--:i;rij)J.od d n the Tilot Si-udy.

of :?cr ice

�V' '•!
*v

'

-

.

•

-5"?-*••&gt;-

4. METHODS OF DATA COLLECTION ID .BE TESTED FOR THE: FAMILY SURVEY
* ! Data Collection Methods to be Tested
•
Four different methods of data collection arc to be tested in the
pilot study giving a total of five different data sets for analysis. They
are:
1.
2.
3.
4.
5.

Self-administered questionnaire
Telephone interview
Face-to-face interview
Telephone interview and medical exaTiination
Face-to-face interview and medical examination.

The saTie questionnaire will be used for methods 1, 2 and 3. Differing
additional instructions, standard probes and explanatory remarks will be
issued for the questionnaire for each of methods 2 and 3. The questionnstire
is dividad- into two- booklets - ons for the male, the other for his wife.
The one questionnaire also serves veterans and controls. The areas
of the questionnaire not applicable to controls are clearly designated.
The mailing initiating the self-administered questionnaire,
telephone interview and face-to-fcce interview will take place on the sense
day. A mailing house v/ill be used for the pilot study as this will b'e
necessary in any type of family survey.
4.1 1. * ™ ' ~~f-admini.—stored Questionnaire
Sel — •--•---•--••-----— - ------ ' — •---"• '-----' "
1

3

The two questionnaires, two postage paid return addressed envelopes and tv.'O
questionnaire cor.ifi-.er it slips will be mailed together with an individually
addressed covering letter. A reminder letter, together with another set of
questionnaires, ccmrnant slips and return envelopes will, be sent ?s-/y_
weeks later to non-responclers. Ten days later, again, continued
non-respbnders will be contacted by telephone reminder call and a door-knrck
reminder will be made about 12 days after that. There will be no deviation
from the self -administered approach. Neither telephonists nor door-knock
interviewers may conduct the' interview.. The door knocker may take delivery
of the questionnaire.
4.1 2. Te_le3hone i
An individually addressed letter will be mailed to each veteran together w:.th
two slips (on which fie and his wife will suggest the lest tirr.ss and telephone
numbers at v.-hic:i they can be contacted) and two postage paid addressed return
envelopes. Telephone interviewing will take place or. t!io re turn slips are
receiver] . ton-resporidfjrs v/ill be contacted by r.,«cns of a printout provided
by Telecom or by consulting telephone directories. Thone v/itl-iout teleph.o;«?s
v/ill be door-knockeci and inter viev.'C-c' f2co-to-i'ace.
v .

4.1 3. ^ ^ A .. J: ° I inter views
"r.cb£.!
Initial contact will be by neans of on iridiv.iiii..all.y yr'drossed Ir.tter
t-xplainicg the stu'Jy r.nci ttiat an ir.tcrvir:v;er will cnll ov uclt'plv.'.no to rnnko
times. To:: thn inter views. Tlss trap, and wife will bo inl.c^-viev.-c;ci at l.ir:-er. find
places convordc.'nt to tier;;.

�'

ft

'

-14-

In all three methods an attempt will be made to get non-responders to
complete' a mini-questionnaire including brief health entails and the reason
for non-response.
4.1 4. TelephonG: interview plus_rcqdical exafnination
On completion of the telephone interview, the interviewer will
offer, to a prs-se3acted sample, the medical examination. Family preference
for location and time will be noted.
4.1 5. race-to-fcicc interview plus medical examination
On completion of the face-to-face interview the interviewer v/ill
offer to a pre-selected sample the medical examination. Again the family
preference for location and time will be noted.
Appointments for the examination will be finalised from the Study
office.
The entire fieldwork period from the mailing date to cut-off is two
calendar months.
4.2

The broad objectives of the questionnaire are:
• . To collect all data that may be relevant. Areas to he covered are
exposure to herbicides, serviceman's medical disorders, familybirth defects, female reproductive histories, possible confounding
factors, comparability of veterans and controls:
. To collect valid data.
' . Upgrade personal details for continued subject surveillance.
. Ease of management and administration.'
-. To facilitate easy entry into computer snd the subsequent editing.
, To collect relevant data to categorise individuals for each
disorder.
. To attract and hold the interest of the subject.
II. 1has been possible to design or,;- ciuostionnairc, which contains the
items c'eivnrtf necessary to achieve these objectives, that cjin successfully be
both self- t'.rid interviev-'er-ac^dnistcrcd. The use of the standard
GuosUomriJrc-! r.lso ailor/s Tor f-xac.-t statisriceil anofiysis of the; quality of
clatti between rr.cthc'Js o.'id rerr.ovos a vc:ri?i/iQ rram the f.swosn'.cnt of resp
rates. ]nc.!ivicinal items have t'C-yn disigrjcci to cr-ver one v? more of the
ncj (.icLti areas:

�^
.
.
..
.
• .
.
.
•
.

. .. -15'
general demographic
socioeconomic
comparabiJity of veterans arid controls
confounding factors
3ong-terrr. surveillance of the veteran
exposure to herbicides
medical status of veteran
reproduction in women
birth defects in children.

•

.
/

''
.

-

;

Available literature and experience suggested that the male subjects
would not adequately answer questions on reproduction in their wives, birth
defects Jn their children nor be able to give the names and addresses of
attending doctors or hospitals. It was, therefore, decided to provide one
questionnaire for the man and a shorter separate questionnaire for his wife
, to provide details of her reproductive history and any birth defects in her •
• children (details of the structure of the questionnaire are appended in 10. 1).
.1
'
The internal design of the questionnaire has considered:
number of questions. On3y those needed to gain necessary
data have been included. No areas of interest are omitted.
Question design. The qj.-estions are simply worried; easily
understood; not open to interpretation; allow for and cover all
possibJe answers to each question.
Length. The questionnaire is of reasonable length with no
unnecessary areas.
The order of questions is logical and tactful.
"fte subject's task is straightforward, simple and ronains
constant for closed questions.
.:,
The instructions and explanations to the subject or interview&amp;r
are adequate and clear, friendly and occur es frequently as
necessary.
*

Coding provisions arc clear and -nccurnte and alJow for spc-edy
operation.
ton-ceded questions provide well-designed space for writinrj
opon--en.cbd answers --.rid the coding plan provides for the ultimate
coding .
Th'-! skip instructions follow one? system only. As both vritco'c-ris
and controls arc using the s?.;*ie questionnaire c.l^ar ciofirsitioM
has been provided whore questions aro not relevant for centre] s.
Coriipr.jTitij lity . Vihei'O possible r.nd i-pproprJat.e the questionnaire
provides for Comparability with othoi relevant studies.

�-16-

•

fS

4.3 Data Jpol lgj2Uon_ f 'or jjuesti onna ire

4.3.1 Interviews
Standard explanations, probes and extra question leads will be
written into the questionnaires used for both telephone and face-to-face
interviews. A questionnaire manual, specific interviewing manual and a
coding manual will be issued.
4.3.2 Interviewers

.

•

• .

The telephone interviewing, face-to-face interviewing, telephone .
reminder and door-knock reminder burden of the pilot study is to be
contracted to an interviewing consultancy. Only firms capable of undertaking
the family survey will be considered. The consultant will bs required to
provide female interviewers of the highest stanoard and experience. Close
field supervision will be mandatory to ensure correct interviewing
techniques, quality control of data and standard approach.
In addition information will be provided by the consultant on
fundamental comparability matters such as time taken for interview, number of
calls (telephone, in person) to achieve interview, rapport, relative costs.
times .of day and week contacts were established, fc'ach respondent, will be
eskod to complete the subject's comment sheet, which was mailed with the
questionnaire, to gain direct information from each subject about his OY: her
feelings about the questionnaire and the study in general. After each
telephone and face-to-face interview the respondent will be asked these
questions also, further feedback about the pilot study, the questionnaire
and the data collection method will be gained in debriefing sessions with
interviewers and their supervisors.
t\ . /! Coding _s_ncj_ Jjs t a J'n tr y for .Ousst Jcnna .Ire
4./S.1 Coo'i ncj
Where the possible range of answsrs to a question can be
anticipated, the question is pre-coded. Whore tables of responses occur, the
coding scheme is prc-plsnnad. Alphabetical punching will be used where
coding :!&amp; impossible and where absolute accuracy of recording is needed e.g.
names a
open
dat
of coded answers is required.

Tha subject will tick pve-codod boxes or y.-rite answers in full.
i-sse cofnpletea1 schso'uics will bs editec1 ard poftcoded by study staff.
-._\c';:"'1: o- f ;:cri_ interv.k:v.|s
The interviewer will automatically code t'Eicf1. reply except Ir.o^c
ing p-jstcudii-g which vail La done in the office.

TMe L;;!fir,t;t".-ip.-iiri; layout iu fJcr-ignc-c! so tint thin can bs rvvia

�Medical
The medical examination is being developed in order to examine 200
families, 100 of whom will be controls and 100 will be veterans. 100 of the
families have been interviewed by telephone end 100 face to face.
The medical examination is planned to be the sama in essentials in
the pilot study as any medical examination that rcay be conducted in the main
survey of families.
/4.5.I. .Objectives

.

The objectives of the medical examination in the pilot study are:
1.

To compare the methods of data collection i.e. to determine if medical
examination contributes to the quality of the data.

2.

To help validate information obtained at interview.

3.

To screen subjects for

• •

•

(i)

Specific conditions - in the past or present, that could be
related to herbicides.

(ii)

Present state of health.

(iii) Indications of chronic disease that may or may not be related to
herbicide effect.
A.

To look for observable birth defects in the offspring of subjects.

4.5.2.
Ths conditions presently regarded by Veterans as related to
herbicide exposuie include:
'. ' i

Skin dir.ecr.r; » paiticu.lfjr.ly chloraene;
Altered Behaviour e.g. violent niaocJ swings;
Neurological sy.T.ptor.is su;h as nj^bnviss ana tingling of extremities;
'Various cjastro-int^stinal disturbances.
, !

Many of these complaints are subjective and difficult to measure. With
this in mind the proposed bodies. 1 t-"xar,iin;-ition v.'ill not be primarily ciir.ea.se
oriented but rather sy::iptu."; oriented.
It v/ill involve a d:-:t.yi.lcd Medical I Li story in order to determine if the
outcomes of interest exist, but in the context of post and present health,
PiTsoriyl, fciin?.Jy jsrd cccupational histories as vzll as a pl'iysi
examination v/ilh specie. I sifiph-ayis on t^rotet to-c?as will bz jncluded.
A series of psyches lo-j.icr. 1 ti'-r.ts j n ccTinion u:;e on.- p3r:nnc:d in an effort
to elucidate the particularly difficult area oT bc'Ivjv.i.otJT.T,! change.

�4.5.3 Facility

'

•

_

It ir&gt; proposed that the medical examinations should take place
at a centrally located public Hospital or other facility.
A team of two physicians, one paediatrician, 2 nurses and a
clerk should be able to handle A families in the examination period which
is estimated to be 3-4 hours.
The location should have laboratory, equipment, waiting room
and interviewing room facilities.
The Medical history and physical examination will be performed
by separate physicians, while psychological tests will be supervised by
nurses.
.
.
.

�" '-19-

•'

. tt
5.
-

5.1

VALIDATION OF MEDICAL. DATA
Overview
^

*

""

•

.'

•

N

'

ff

' Medical record validation is planned to run concurrently with
the checking, editing and coding as well as input cf the data.. It is
• important that the validation and input phases are co-ordinated and that
an even balance of work is maintained. Medical record validation will be
'performed by the medical record administrator (Ms. Keitha Jones)
appointed to the project, with the assistance of a second medical record
administrator.
5.2 Methodology

Upon receipt of information from 600 Pilot Study survey
questionnaires, information will be checked, edited, coded and input by
key punch operators.
Computer lists of all YES responses to medical questions will be
generated, pjovidinr] the subject has completed the section on health care
facility treatment/type of facility/address of facility/approximate date
of treatment.
Listings will be by subject name v/ith groupings by health care
facility to be approached.
Computer validation checklists will be generated for each
subject, containing the following information;
SUBJECT'S NAML7ADDRESS/DOB/CUESTION NUMBER (YES RESPONSE) NAME
OF HEALTH CARE FACILITY.

KsLhodoloyy of validation of Hospital Medical Records will be as
follows:
ed ValjLcintion Format
•. i
1.
2.
3.
4.

Condition investigated
Condition not investigated
Condition investigated but not-validated
Condition investigated/condition confinr.ed and accounted for by
known disease factors
5. Condition investicjatcci/conciitjon confirmed but not accounted for
by known disease factors
Lists of medical records to be viewed vill be; sent to esch hospital
medic.!!, record Fd:n.unstratcr/|-or&gt;pitfil administration with a
photoco-.y of the subject's signed consent to release information.
The subject's oricjinal consent forn will be retained v/iLhi.n the
Her'jicicie Study offices,
Each valiaation checklist v.-iJJ be coded by ths M . R . A . using the
Int.c?.national C3assif.1 cation of Discr.fcas Sth. f\evJ£ion V.'.H.O. r.i&gt; each
conJition is validated.
Viilidator's irdtir-ls nrid clclc of vr«.Ucation wi.ll also to eritcvecj.

.

�-205.3. £onditjonsjto_bc_ va3.iidatcd

\
The following target organs/systems/conditions v.'ill be assigned
specific disease codes, using I.C.D.9 for the purpose of
validation. Broad 1.C.D.9 groupings will be used for preliminary
statistical analysis.
TARGET ORG AN/SYSTjFM/CONDI TION

ICO GROUPING

ICD SPECIFIC COOES

Demiatological
•
Nsoplastic
Hepatic
Haemopoetic
Immunological
(Endocrir e/Me tabol i c/Nu tr i t)
Cardiovascular
Renal
Reproductive - Male
(Incl. Sexual)
- Female
Neurological

680 - 709
140 - 239
570 ~ 573
280 - 289

to be decided

240 - 279
390 - 459
580 - 599

•

600-608 (D.S.M. Ill) (ICO 9-300-316)?
630 - 676 610-629
320 - 389

Medical record validation will also include chocking hospital medical
records for:
Reported deaths of offsprings
)
Reported neoplasms of offsprings

) VETERANS &amp; CONTROL

Reported Birth defects of offspring)
Reported birth defects, reported deaths/reported neoplasms of
offspring will be coded using JCC 9 aftc-.r medical record validation.

�5 /J

-

Service M3d.lcal Records (covering the period of Vietnam Conflict)
Army health services medical records are storeri in Melbourne
(separately from the Central Army Records Office) and vail be viewed
in order to determine:

1.1 Type of medical data available
Number of mecljcal examinations performed
Content of each medical examination
Methods of question batteries/scoring used by the Army medical
personnel
Methods of determining medical status on entry into the army
Determine who will retrieve/select 600 index cards and pre-code the
information
1.2 It is proposed that the statistician and medical record administrator
view and select these records for the Pilot Study
1.3 These records are stored via the last tv/o digits of the Army service
number (6 or 7 digit number depending on type of enlistment).
5.5 N'qn-Service Records
5.5.1 Valicjat1on j.isj_ rig rb so ita 1 Records
5.5.1.1 in all subj ects
Identification sheet/reported final diagnoses
Hospital discharge summary/concurrent final diagnoses - copy retained
by M.R.A.

Operation charts
- Various treatment charts
Physician's notes (past/present history of illness to be validated)
Nurses notes
Consultation charts
.
.
.
Laboratory cherts/biochemistry - Abnormal rerults/x-ray/cat
scans/nuclear nsdicine/special radiolog.i cal procedures
Cancer registration notification and subsequent fornis
.Hospital discharge reports (rases where no discharge summary is
.available)
.,

�5.5.1.2. ^Additional sources for birth j nf onMtion nnd_bir_th_ 9^
Obstetrical charts/delivery charts
Newborn (reported birth defects) charts
5.5.2

.

•

'

-

Validation v/i. tfy General Practi t ipnsr Records

The methodology will be as for hospital medical records, refer
5.2.1 with computer validation checklists, and standard contract letter
(comptuer generated) requesting validation of reported yes responses to
target organ conditions.
The £[U_a.li_ty of_J^ta_obtG.incb_le from G.P. records is at nr_cfinnt;__an
facTor._ l_ b_ ~ r r e " . o n V t x i storage iJs "well as 're IrToval we triads
_
Ij&gt; .alsojjin i'^ino\sTi_facu.or. The R.A.c.G.F. P.b.M.R. system has been
Tritreauced~tC) rJany G.P"" surgeries in N.S.W. and in these cases retrieval
of recent medical information should present no problems.
5.5.3. Vaiidation
- - ' - - - The methodology will be as for Hospital/G.P. records and presents
the sane problems of retrieval systems. Quality of data available is also
an unknown factor.
5. 5. i\ ffiljdjatj.on using cithej^fedicajl ^Record Sources

"...

1. Death certificates
2. Post mortem reports
3. Coroners Court Medicn.1 Records may be used for reported deaths by ir.ScTis
of misadventure. These reports do not appc-;ar to be" sent to hospital
medical record departments as a matter of course.
/u

Health Statistics Bureau

5. Perinatal Statistics Unit Commoriwea.Hh Institute of Health Sydney
University - Or. Paul Lancaster.
;/
6. Maternal and Child Health Division of Health Coniaiicsicm - Dr.
. (GratUn-Smith)
.
• .7. Community Health Centres
D.

Mco'i'oank for 1975 is an unbiased although limited source of JFifonT.^tion
(as a foll--bT'c!&lt; validstion instivr.-.?nt ) . Kocovds are hold hy t!io
Cc:.Y.ionwi?ciJih j&gt;pGrt[:,ant of Health, i\\v.i could possibly be i.;s&lt;;Ci as a
va.Udat j.on fo? refiorte-c! riiar;nosr;i-&gt; 01 as an i ncopendont source of dc:t? on
ouvcer;:2.
This is biing ifivcstignlf-a furth.ev. ~lhs major p/o^le-ri Et
present appears to be retrieve:], of identifying :.rifonaatio;i. .

�6.

CONFIDENTIALITY AND PRIVACY ISSULS

6-1 Confidentiality

'
\

•

'

..

,
•

Much of the information being sought is sensitive and personal, and
some may be relevant should the veteran make a future medical claim. In
order to reduce non-compliance, it is essential that in format ion collected
from subjects should be used only for the purposes of the investigation, and
that this can be absolutely guaranteed. A unique confidential survey number
v/ill be assigned to each subject and only this number wiJl be used to
identify data. A separate f le vail be kept of names, service number and
this confidential survey number.
The investigation should be required to refuse access to individual
data to any other government department or organisation. A means to ensure
this is currently being investigated, one possibility being that members of
the study team should have the status of Census Officers.
• ••

•

6.2 Privacy
Medical record administrators constantly face the problem of
balancing the desire for personal privacy against the need for
public/research information. In many situations a great deal of personal
discretion is used, since legal precedent is practically non-existent..
6.2.1 New Sputl'i V.'n I cs privacy Corr&lt;mij._tce_
The New South Wales Privacy Ccrrmittee was established under the
Privacy Act, 1975 (N.S.W.) as a direct result of Professor W.L. Morrison's
Report cri the Law of privacy (1973). The 13 robbers of the Privacy
Committee have four main functions; namely - Research (to research and
develop a general policy towards privacy), Complaints, Public Education, and
Law Reform.
•^.
6.2.2

Heal th Corr^ission _oj*__ Ngw South Wales

The Health Commission of N.S.W. refers any requests for research
involving difficult confidentiality issues to the N.S.W. Privacy Committee,
and is usually guided by that Commit lee's decision, before allowing the
researcher access to Hospital Medical Records.
i

The Health Cnraiission of New South Wales has also distribute:! a
Circular No. 80/106, issued 31 st March 1900, to all Hospitals and Corwunity
Health Centres.
. . . _ . . J d °f this circular states "No information concern.! no a
patient cff'cTicnr'is to be supplied to another person without the written
consent of the patient or client. This written consent must be preserved in
the case notes". The client must be ]'Nr GRMfD of the purposes of th? lj;-iiy
requci'-lincj hir&gt; confidential information, and must be Icyully capable of
giving conse:-it. This consent must be fjccly given, arid cover what is
required.
Section 8.3 fAfites "Information should not b:.: supplied for ror;'X:?::!i
v/ithout consc;n'L"o"fThe p'sticnl. or conbultal.icn \;i th the.1 eppropriatt; t'ics;;.ii;aj
or rocjicr.n.l r.ut! ;ori ty . Attention is r'j'i'Wii vo lh:; guiciijliivji; for acccrcs vo
dav.n p;:oa;ced by tn&gt;? Privacy Commit toe".

�,-./,
J,^

•. .
6.?..'!&gt;. Action^.bcinn_t_fike_n

": -24-

. -

Letters explaining the aims, recjirerr.ents and Methodology of the
Veterans Herbicide Study will be sent to both the Privacy Convnitteo of
N.S.W. and the Health Commission of M.S.W., and if required, discussions
v/ill be organised between members of the herbicide Study Group and the
Privacy Committee. Prof. L. Davidson v/ill be writing tc the Department of
Veterans' Affairs in Canberra to address the question of confidentiality of
a national level.
At no time will medical records of any kinci be viewed by a member
of the Veterans Herbicide Study without the express informed consent of
Veterans/Controls/Wives etc. Production of the patient's signed consent
will accompany all requests for medical record validation.
Confidentiality and privacy of questionnaires will be maintained at
all times within the offices of the Herbicide Study Group.

�-25-

•
7.

7.1

STATISTICAL ANALYSIS OF TIE PILOT STUDY

Response Rates

.

&gt;

-

Three types of response rates are of interest:
(a) overall response

i.e. v/hethcr any questions answered (? agreement
to participate)
*

C-*) ^I^IJl^Lj^SSD^L i'G&gt; now many ar&gt;d which questions were answered
• • - -1satisfactorily. (This is an aspect of data
quality)
(c) nj3dic_al_examination response i.e. hov/ many of the respondents agree
•. . "
to and attend a medical examination
Ths rates (a) and (c) will be assessed as follows for each of the three
interview modes:
100 -Vietnam veterans (V) and 100 non-Vietnam controls (C)

Stratified random sample of 50 from each of V and C groups
These are the 'selected individuals'

Questionnaire to all 200-&gt;

Response rate (a)

If 'selected individual, responds to questionnaire ascs/tain
willingness to participate in nodical exmsmination

On3y fcir T and FT modes,- ascertain av.tfjr.clance rate
at medical exa'njnation

e.sonso

�tt

'

• -26-

.

•

'

••'

"' '

Sierniatycki* has found that the three interview modes yielded
response rates of
(a)

SA - 70.3%

(b)

T - 73.5%

(c)

»

FF - 84.1%

Similar results are expected in our study and will be presented
as follows:
Interview
Mode

Pecentarje
overall response

Within respondents
% positive response
•' to medical

SA
T

-Within respondents
% attendance at
medical
(estimate only)

KF

The estimate of the % attendance at medical for the SA mode will
be calculated on the basis of the observed mean attendance rate among
those in the T and TF modes who gave a positive response. Only an
estimate is to be calculated for the SA mode because of the time
requirements for the pilot survey. Al] response rates will be calculated
usinrj appropriately weighted values from each stratum.
The rate (b) will be used to identify sensitive areas of the
questionnaire whose wording should be reconsidered and to alert the
statistician to tests whose power may be seriously affected by the
presence of missing values. Power studies will have to be conducted in
the light of the (b) response rates.
All three response rates will be used as estimates of the
figures to b&amp; expected in ths main survey power calculations associated
with the various hypotheses to be tested can then be made using these
estimates.
".

There are two important aspects here:
(a) .the problem of non-response.1 on specific questions should bo'
addressed. This has two obvious implications (i) can the question bs changed so as to increase response rate?
(ii) \vhat is the effect on the power of the tts.ts to lie carried out
), say, estimates of the missing vnlu-is?
( ) 0. Sic;niatycki. A cornporison of n.ail, telephone and home .interview
*
strategics for household feaHh surveys AJi'H 69: 23B-M5, 1^75.

�W

'

•

-27-

'

(b) The problem of bias i.e. false reporting of nodical status. There
are several ways in which one can try to detect this and determine
hew often it occurs in different typos of individuals:
•

(i)

use of medical records librarian to check on diagnosed illnesses

(ii) use Army entrance medical examination data if feasible on some
reported illnesses
(iii) use incidence of medical disorders thought to be unrelated to
herbicide exposure to "flag" over-reporting
(iv) look at correlations between the battery scorer, on the
questionnaire and on the medical. Low correlation could
indicate false reporting and/or an inconsistent form of scoring
in these two modes.
7.3 Comparability

' •.

The issue of comparability of the V and C groups lias several
aspects:
(a)tfs'dicalrecords of the; entrancefcxaniwill be available on all 600
individuals. In addition, agu at enlistment, length of service and
Regular/National service status are already known for each individual.
(b) Additional information will only be available from respondents. It
is there fore necessary to determine whether the respondent (R) c-nd
non-respondent (fW) sections of the V and C subgroups sampled ore
comparable. This will be done via
(i)

entrance medical exa&lt;n records, age of enlistment, length of
service. Rsgu 1 fir/National service status, place of residence

(ii) a mini-questionnaire to Ws. This will ask for education,
occupation and any chronic radical problems in self or family.
• If the R and MR sections of the sample of 600 are comparable on
the. basis of (i) &amp;nd (ii) in both th2 V and C groups, no adjustment is
necessary. If nnt, the differences should bs ascertained and taken into
account when preparing pcv-ver calculations for the main study onci devising
.possible statistical, analyses.
•'
(c) The R sections of tho V and C su!. groups will be compared via
additional inf conation on the questionnaire e.g. nationality,
income, education, occupation, ru::;.. I/urban r;tatus.
(d) Within the: V subgroups of respondents it will also ht&gt; necessary to
compare ttiosr-; v;!ic went, into the; fr'.old with those v.'iio stayed on the
bases.
If it is founri th-:;t groups arc not comparable:, the rli f f crciv.cs
should be ascortn\r-.o.n r.nrl thsir known i :i fu.oL-i in ti-.e areas of intriri-;;!:
siioi .'Id br: su.'J i.o.'i oj.oscOy. Wl^vrevor povr:.bJo. t-n appj-nf)rJolo adjusl'i^nt
sliould be iixjo.-i.o'-it^o in the: CM'irJoir-..

�U

- •

8.

•

-28-

.

APPENDICES

'

'

'

8-1 Structure of
A

•

- MALr QUEST IpKMIRE

(For Pilot Study)

1.. Personnel information.
2.

General information
2.1 Nature of study itself
2.2 Subjects participation
2.2.1. Importance
2.2.2. Voluntary

•

•

.

'.

2.2.3. Confidential
2.3 Contacts for further information.
3.

Instructions.
3.1 How to fill in the questionnaire
3.2 V/hat to do with completed questionnaire
3.2.1. Where; to send it
3.2.2. Date to send it by
3.3 Contacts for help in filling in questionnaire

A. Subject identification
A.I Todays date
A.2 ' Surname
A.3 Given names
"
A.A Address in full
A.5 Mono phone number
A.6 Work phone number
A.7 Confidential survey number

, . - ' . .
•

.
'

5. Demoqraphics
5.1 'Dole of birth
•
5.2 Type of place where lived while growing up
5.3 Years of schooling
5.4 Tertiary qualifications
5.5 Kaeiai origins

.:
'
^

.
•
• ..-.

6. Occupational and Exposure History
6.1 Gencial job history
•
6.1.3. Prior to go: no defence services
6.1.2 V.'hilo in defence services
6.1.3. After leaving defence services
6.2 Job contact with specific chemicals and substanc-es

'

6.4 Details of defence service
6. &lt;';,.!

Da to of enlistr.-.f.int

6.A.2

Ital'e of clisehriiVjt;

6.-'i.3 Status within service
f

- -

t*

\ t-

i

+•

'

'•

'

:'

'

6.5.1 L'Crto'ls of service
6.5.2 Details of cf;i.::iiicul exposures
6.5.2. .1 Sprayifn;, riie!.rlcMls
6.5.2.2 Mixino, carryinrj or locrJirg chi:mi.CQls
6.5.2.3 Clctrniri:; or rqi.'iin'nci equipmsnt used to carry

•

�6.5.2. 4 . In area while it was being sprayed by aircraft
• 6.5.2.3 In area while it was being sprayed from
vehicle, boat or backpack
6.5.2.6 In area where vegetation was dead and dying
6.6 Leisure time exposure to specific chemicals and substances
7. Medical history
7.1 Height
'
'
.
7.2 Weight
'
7.3 Self-rating of heal.h
7.3.1 Physical health
7.3.2 Mental health
7.4 Specific medical conditions requiring validation
7.4.1 Derrnatologic
7.4.2 Neoplastic
' 7.4.3 Hepatic
7.4.4 HaeiTiOpoietic
7.4.5 Immunologic
:

'

•

.

' '

7.4.6 Cardiac
7.4.7 Endocrine conditions
• 7.4.8 Urinary/kidney conditions
" """ 7.4.9 Reproductive
' . 7.4.10 Neurologic
7.4.11 Psychological
8. History of smoking, alcohol and marijuana use
8.1 Sn-oking tii story
8.1.1 Now/ever
8.1.2 Stopped/started
8.1.3 Quantity
8.2. Alcohol Consumption
8.2.1 Now/ever
8.2.2 Stopped/started

'.
.

8.2.3 Quantity

8.3.

Marijuana use
8.3.1 Lver
8.3.2 Quantity

9.

s
Marital history
'
"'
9J Current, marital status
.
9.2 Number of marriages
9.3 Number of relationships lasting more than 6 months

.. '

10. ljj-egrr;incy outcome

10.3 ftecord of all live births

3.0.2 Record of all occasions on which tried for n period of at
least a year to conceive n child but were not ab.le lo c.io so
10.3 Record of all prrcjriTiric.ies not ending in a Live birth
10. /: i'.c-cc-icl of oil children horn with birth defects
10.5 Kf^-erd of nil ci'iildren di£;(jnosea as bejiio cancer

11. f't-STcp'Jons of hijsbindr. or ex-hutbcinds health
13.1 Pliysicr.1 health

�.

••

, - . •

12. Closing statment
12.1

:

*

-30-

. . .

Thanks

12.2 Reminder about what to do with questionnaire
B. FEMALE QUESTIONNAIRE

1. Personnel information2.

3.

General information
2.1 Nature of study itself
2.2 Subjects participation
2.2.1 Importance
2.2.2 Voluntary
*
2.2.3 Confidential
2.3 Contacts for further information

.'

Instructions
3.1 How to fill in the questionnaire
3.2 What to do with completed questionnaire
3.2.1 Where to send it
- 3.2.2 Date to send it by
3.3 Contacts for help in filling in questionnaire

A. Subject identification
4.1 Todays date
A.2 Surname
A. 3 Given n&amp;r;:es
A.i\ Address in. full
A.5 Home phone number
A. 6 Work phono number

.

5. Demoqraphics
5.1 "Date of birth
5.2 Years of schooling
5.3 Tertiary qualifications
5.A Racial origins
6. Occupations! History

6.1 General job history

7. Medical history
7.1 Height
7.2 height
8. History of smoking and alcohol consumption
8.1 Srr.old.ng KLstory
6.1.1 tow/ever
8.1.2 Stoppod/stnrted
8.1.3 Clientity
" .
8.2 Alcohol consumption
8.2.1 Now/ever
8.2.2 Sloppy/started
8.2.3 Qjcntily

�&amp;

'

-31-

9. Marital history
9.1 Current marital status
10. Pregnancy outcome

10.1 Record of all live births including children who have since died
10.2 Record of all occasions on which tried for a period of at least a
year to conceive a child but were r.ut able to do so
10.3 Record of all pregnancies net ending in a live birth
10./i Record of all children born with birth defects
10.5 Record of all children diagnosed as having cancer
11. Perceptions of husbands or ex-husbands health
11.1 Physical health
11.2 Mental health
12. Closing statement'
. "
.- 12.1 Thanks
12.2 Reminder about what to do with questionnaire

�-32•2

'

tniclurc of the M i e r i i a l r l i s ^ o r ^ a P d t e r J i c a l Examination of Adu3 t s

It is proposed to examine 200 subjects and their children.
The time of the medical examination will be approximately 3 to 4
hours.
It is proposed to examine the veterans children at the same time
generally in the company of their mother.
PROGRAMME

The proposed medical examination will be in six parts :Administration, medical history, laboratory data collection, physical
examination, psychological tests, examination of offspring.
SCOPE AND CONTENT OF THE MEDICAL EXAMINATION

•

1. ADMINISTRATION - 10 minutes.

During administration identification details and age etc. will be
collected
2. MEDICAL HISTORY - A5 minutes.
Performed by Physician No. 1.
The system review v/i31 be a standard medical history with more or
less emphasis on outcomes of interest.
3.

LABORATORY DATA - 15 minutes.

Vcne puncture to be performed by a nurse.
Laboratory data to provit!?. haernato.logy and biochemical information.
- Provision to be made for serum storage at -70-' C.
The nurse will also record vital statistics e.g. height, weight and
supervise spirometry.
4.

PHYSICAL. EXAMINATION -• 60 minutes.
Performed by Physician No. 2.

(i)

General examination major systems.

(ii)

Skin examination with photography if necessary.

%

" .

•(iii) tourological examination. •
(iv) [-.'Xcittination of target organs e.g. liver, spleen, 3'yrcph glands
and testes.
5.

PSYDDLCGICAL TESTS -• 60 minutes.

Proposed Psycho] coir;:-:! ttsts are the Corne.l] Index (C.I..) end the
M.innesot'i! ;&gt;j]tiplujs;ic Personality Inventory (f..Mpj).
Two olhc:i indices tl&gt;:&gt;.t may be suitable are K:inn corisidarrd - tho
Onr.t? tv^siJonnaire and the !5ock Octpressic.i :nvc i ritory. A re-run of
the Army's pjycholorjical tests prior to ent:y into i'ho servicos is
being coroicirred.

iics'i tests iiifiy be yr^inisVcrc-'Ci by &lt;; nurse.

�-336.

OFFSPRING

•'

-

' • - . ' .

- examination to be performed by a Paediatrician.
(i)• General physical examination.

(ii) Birth defects.
. 8.3

Medical Examination of Children

'.,

-.

•'
'

..
••

As previously stated it is intended that the children of
veterans be examined by a Paediatrician at the same time as the subjects
are being examined.
Resources are being planned on the basis of examining
approximately 400 children.

..

The medical examination of the children will have as its objectives:
1. An estimate of present state of health.
2. Recording of any observable birth defects
2.. _ _ validation of any reported birth defects or medical conditions.
A provisional list of birth defects has been compiled based en
tht birth defects to be included in a case-control study of the effect of
service in Vietnam to be conducted by the Center for Disease Control,
Atlanta, USA.
A parent of the children will be asked about the listed birth
defects and confirmation will bs sought cither with evidence of surgical
correction or at physical examination.
Where the terminology is general and a positive response is
obtained, specification and confirmation will be obtained via hospital
and doctor nodical records.

�d

.

-34-

6.3.1. List of Birth Defects

.

SPINA BIFIDA AND/OR HYDROCEFKALUS
MICROCEPHALUS
•
NEUROFI6ROMOTOSIS

.

-'

'

'

'

&lt;

'

"'

ANOPHTHALMOS
MICROPHTHALMOS

•

. '

BUPHTHALMOS
CONGENITAL CATARACT

.

. '

COLOBOMA
ANOf/iALY OF TIE EAR - IMPAIRING HEARING
KIART CONDITIONS
CONGENITAL CYSTIC DISEASE OF ANY ORGAN
ANOMALIES OF THE GASTRO INTESTINAL TRACT
CLEFT LIP AND/OR PALATE
HYPGSPADIUS
EPIDSPADIUS

.

' .

ANOMALIES OF THE URINARY TRACT
'

ANOMALIES OF THE FEMALE GENITAL TRACT
CLUB FOOT
REDUCTION DLTOrWITIES OF THE LIMBS
CHONDRODYSTRCHIY
OSTEO GttlESIS IMPERFECT A

HEREDITARY OEDEMA OF THE'LEGS

SPECIFIC ANOMALIES OF HAIR
SPECIFIC ANOMALIES OF NAILS

ANOI-IALIES OF TH: ENDOCRIK:: SYSTEM

;/

SITUS INVERSUS

DOWNS SYNDROME
DI AF'HfViG 1ATIC HH^I A
CONGENITAL NEOPLASf-!

'

-

CYOTOMEGALO VIRUS

-

HERPES SIMPLEX
SYPilYLIS '

'

-

�SECTION 2
DRfiFT

REPORT -:.26/02/81

HERBICIDE EXPOSURE IN VIETNAM

CONSIDERATIONS

JOHN ROGERS

�1.

INTRODUCTION

-

1
t

2. HERBICIDES USED BY US FORCES

1

3. HERBICIDES USED BY AUSTRALIAN FORCES

4

4. NON HERBICIDE EXPOSURE

5

.

5. SUMMARY OF POSSIBLE CHEMICAL EXPOSURES IN VIETNAM

5

6. MODELLING EXPOSURE

6

7. DATA
8.

.

.

.

6

AERIAL SPRAYING

-

a) Spray drift

'

"

8

i) "Deterministic" model.
Conclusions
'

8
10
t

ii) "Statistical" model
Comments
9.

RECOMMENDATIONS

10. REFERENCES
APPENDIX I

11
11

-•

'
'

.7

13

-

- '' -.

14

' .

Comments on Recofiimondations

.

19

i.

APPENDIX II

Additional references required
APPENDIX III

"Statistical" model

20

-

.

23

�Research on 2,4-0, 2,4,5-T and related herbicides began during
World War II, and had at that time a clearly military connotation.
However, herbicides were not used for military purposes in World War
II. The first, small-scale military use of herbicides was in the
1950's in the Malayan "emergency". In tha early 1960's the
possibility of tactical use of herbicides was given considerable
impetus. A number of herbicictas were evaluated, in various
combinations, for their phytoxic effectiveness in South Vietnam.
In South Vietnam, the first military herbicide operations were
carried out in early 1962, and were phased out in 1971. After a
relatively slow buildup from 1962 to 1965, the operations increased
rapidly to a peax in 1967, declined, but only slightly, in 1968 and
1969, and dropped sharply in 1970. According to information from US
Department of Defence, the last herbicide spraying by fixed-wing
aircraft was flown on January 7, 1971. After this, herbicide
operations were limited to spraying around perimeters of the fire
bases, on enemy cache sites, and along land and water communication
routes, and v/ere all carried out by'helicopter or on the ground. The
last helicopter operation under U.S. control was flown on Cctooer 31,
1971.
Herbicides used by US forces
The herbicidal "Agents" used for military purposes in South
Vietnam were identified by cods names referring to the color of bands
painted on the containers of the chemicals. These of interest to thisstudy are the Agents: Orange, White &amp; Blue.
Agent Orange is a 50:50 mixture of the n-butyl esters of 2,4-0
([2,A-ciichloroprTenoxy]acetic acid) and 2,4,5~T
([2,4,5-trichloropnenoxyjacetic acid). Each gallon of Orange
contained t\ ID of 2,4-0 and 4.6 Ib of 2.5,5-T en an acid ectjivalent___ _
basis.3 Orange was tne agent used most extensively in uris Vietnam
war" until its use was terminated on April 15, 1970 because of the
concerns of its possible teratogsnicity and its concaminati.cn with the
highly toxic TCDO (2,J5,7,8-tetrachlorodioerizo-para-dioxin).
/\g_cnt Wnite is a mixture containing 2 Ib of 2,4-0 and'6.54 Ib of
piclordm"(4-amino-3,5,6-trichloropicolinic acid) per gallon on an acid
equivalent basis, (or 4:1 on a molar basis). It is a formulated
product containing 2,4-0 and picloram as the triisopropsnolamine
salts, with tne addition of surfactants and water.

*This introduction is based on material in reference
a

(17).

Acid equivalent is the weight of the acid form of the chemical,
this is used oecause the weights of various ester or amine
formulations vary. Expression in terms of acid equivalents
provides a uniform basis for comparison of different formulations

�Avjgnt Bluj3 was formulated as the sodium salt of cacocJylic acid
(hydroxycrirp.nlnylarsine oxide). It contained a minimum of'21 percent
sodium cacciiylate v/ith additional free cacoclylic .-jcid for a total
dimetnylarsinic acid equivalent of not less tran 26 percent on a
weight basis, or 3.1 Ib of cacodylic acid and about 1.7 Ib arsenic per
gallon, v/ith 5 percent surfactant and 0.5 percent antifoam agent.
All agents were intended for use at a rate of 3 gal./acre (28
litres per hectare), except that in the earlier operations and on rare
occasions thereafter, only half of this dose was used. The homicides
were applied oy US forces fixed-wing aircacft (UC-123), helicopter
(UH-1), from trucks, from river boats, and from backpacks. South
Vietnamese forces may have also oeen involved disseminating the
herbicides Orange, White &amp; Blue by these methods.
Both aircraft types were outfitted with special spraying
equipment, consisting essentially of a container for the herbicide and
a spray boom witn nozzles. The container of tne UC-123 spray system
had a nominal capacity of 1000 gal. -and the plans normally flew at 150
ft. (45 m) with a delivery speed of 130 to 140 knots. The "spray-on"
time of 3 1/2 to 4 minutes permitted approximately 950 gallons of
herbicid-j to be distributed at the rate of 28 litre/hectare over a
path of 14 km length. During the peak of activity (1968--1969)
approximately 30 C-123/UC-124 aircraft were employed. However, r'nany
other squadrons of C-123 aircraft were used routinely throughout South
Vietnam in transport operations (4).
Tne capacity of the UH-1 spray system container was 2GO gal. but
the helicopter could carry only 100 gal. d'js to weight limitations.
Spraying by fixed-wing aircraft accounted for the greater majority of
the nerbicide used in the Vietnam war, at least into the later part of
1970 from which time on helicopter herbicide operations increased and
gradually became predominant, until they became the only aerial means
of heroicide delivery. (17)
The amount of herbicide used by year is listed in table 1 (17) and
the estimates of quantities of herbicide component total usage is
given in table 2 (66). Tne region that received the greatest
concentration of herbicides was the Rung-Sac Special Region south of
Saigon and adjoining Pnouc Tuy province (where tns Australians were
posted). This level is reflected in the quantities used in military
region III which included the Rung-Sat Special Region (taole 3). Trie
correspondence of spray missions in military region III and ins
positions of Australian soldiers has yet to be determined - and the
numbers involved is suoject only to conjecture.

�Tablc 1

Application of^..

War_by Year (17)

1962July 1965

Millions of
Aug-fec
1965
1966 1967 ._ 1968

Orange

NAa

.37

White

NAa

0

Blue

NAa

0

Total'

1.27 '

.37

1.64

3.17

1969 _ _ 1970

Total

2.22

3.25

.57

.0
0

11.22

.53

1.33 .2.13

1.02

.22

.01

5.24

.02

.38

.28

.26

.13

.00

1.12

4.83

4.63

4.53

.97

.01

18.85

2.19

a Not available

TABLE 2. Estimated quantities of herbicicios ijr-.ci TCDD ciiggeminaterj in
_ Soutn Vieinc.:,\ frc.~'. January ic^i2^(^ru^ry_I97i_ (6i)

Chemical

Pounds

2,4-D

55,940,150"

2,4, 5-T

44,232,600
363

F3icloram
Cacodylic Acid
Total of Herbicides

3,041,800
,3,543,710
106,763,260

Tne mean TCOD concentration in Herbicide; Orsngn was estimated at 1.93 ppm.
v•

�TA3L£ !&gt;

y.^Jj?LrbJj:lc^^
.
'
A

:

' ''

Herbicide Expenditure
(gallons)
Orange
White
Blue

Combat Tactical Zones
CTZ I

2,250,000

363,000

. 298,000

CTZ II

2,519,000

729,000

473,000

e 5,309,000

3,719,000

294,000

1,227,000

435; ooo

J#,p_00

5,2/16,000

1,127,000

*

CTZ III
(includes Saigon)
CTZ IV

Subtotals

J,227,00

Grand total

* Source: HERBS tape (65)

Herb,icides

strai ion f orces

Australian troops may have also ooen exposed to herbicides sprayed
for perimeter vegetation control around the Australian camps. The
cnemicals used were on the whole obtained commercially from within
Australia and included GRAXX3XONE (paraquat) REGLCNE (diquat), TOROON 50D
(piclora;n/2,4-D) and HYVAR (oranacil). Tne annual usage in Vietnam -in -the years 1960 to 1971 was of the order of ( )
6:
9,000

liters of diquat

1,600

liters of TORDON 500

4,000

kg bromacil

.•
•'

Cofn.T.encing November 1967 a field investigation was conducted under
scientific supervision to establish the metnodology for disseminating
tnese herbicides. Suossquent to toxic effects b:&gt;ing found in operators -breakdown of mucous membranes, nose oleed-5, ulceration of lips and
conjunctivitis - the use of DM50* was discontinued and strict procedures
for handling were recommended (31).
In addition the Department of Defense "accords a fairly high degree
of probability" that the Australia Task Force procurrcd and used 1,000
gallons of Agent Blue (cacodylic acid) obtained from local sources ( )
6.

*

DM50 is a chemical which accelerates the uptake of herbicide into
plants, and unfortunately has tlu same-effect for hu-r.ans.

�-5-

Non Herbicide Exposures

•

•• .

.•

Further to th3 heroicides diss-^rnnunated by the U.S. forces, the
Australian troops may have co;na in contact with Ma.lati~i:'.on sprayed from
specially prepared C--123 planes or "uug-biras". • The Malathion was
selected for malarial mosquito control on advice frcin the World Health
Organization. Unlike the hsroicidcs which were sprayed in "remote" areas
the Malathion was sprayed "indiscriminately" over
populated areas, "even whole to,-;ns" (A.L. Young, private conuiunication).
These aircraft routinely sprayed insecticide adjacent to military and
civilian installations, as well as in areas where military operations
were in progress or about to commence (4)
Medical treatments are also of interest, in particular
(1) antimalarial drugs including the experimental drug Dapsone which was
used oetween 1969 and 1970and withdrawn after adverse side effects and
(2) innoculations for Plague which too had adverse side effects but
remained in use.
Summary of possible^ j^hj^nica 1 exposures in ^i.".tnam.
Thus the chemicals which are of interest to the Australian Veterans
Herbicide study are:
1. Agents used by U.S. forces
(a) Orange
'(b) White

. .
.

(c) Blue
. (d)

Malathion;

;"•"" .

.. . .

2. "Agents" used by Australian forces
(a)

Grammoxone

,
/

(b) Reglone
(c) llyvar
[(d) Agent Blue]
(e)

Insecticides;

3. Australian Medical Treatments
'"V-

(a) Antimalarials
(b) Plague innor.ulations.

*"
"

i

�•

Modjjllincj exposure

-6-

.

The object of the Veterans l-brbici.de Gtuay is to explore the
causal effects of hcrbicirJe exposure in Vietnam with regard to
possible adverse health outcome in Australian Vietnam Veterans.
The hypothesis that a certain herbicide (or even combinations of
chemicals) could cause the undesirable health effect can only be
demonstrated by being consistent with the current knowledge of the
chemical(s) biological action. Secondly to validate the supposition
a dose-response relationship must bo shown i.e. TTe health effect
should increase with increasing exposure.
Any attempt to determine the 'dose1 or exposure of military
personnel must be predicted on events that occurred at least ten
years ago. Since there was no sampling program associated with the
handing or dissemination of the heroicides in South Vietnam, a .
quantitative determination of exposure in terms of actual dose can
only be suoject to speculation (/'O. • However, it is still possible
to determine "relative" exposure levels.
For tne "Agents" of greatest concern, namely Orange, White and
Blue, it is true to say that exposure did not include all Australian
servicemen. Moreover, within the military population at risk, the
range in magnitude of exposure must have been great. The range is
so great that it is plausible that the possible errors in predicting
this "relative" exposure may be less than the range itself.
Data
To predict exposure levels with certainty it is necessary to
have a minimum of verifiable data available. To demonstrate a
possiole causal or 'legal' connection requires a higher standard of
documented information.
Exposure to Malathion is a case which amplifies this point. No
documented information regarding the "indiscriminate:" spraying of
this substance is available. It may be possible to show
relationship between otner highly correlated confounding factors,
such as corneat duty or season and presumed Mslathion exposure.
.Witnout supplementary documentary evidence it is impossible to
separate the effects of the selection criteria from the exposure.
A correlation between such "Malathion exposure" and health
effects would ue insufficient to prove the causal nature of
exposure. There is no way that such an effect could DC ascribed to
the exposure to Malatnion alone.
To obtain a presumed exposure level for Agents Orange, White and
Blue the follo.vjng sources of data are available:
1. The so called "HERBS" computer tapes which document the
herbicide sprayinfj missions of United States fixed wing
aircraft, [approximately 8CK of total heruioido dissrainated by

�-7-

Unitcd States and South Vietnam forces is documented on these
tapes]. The information on tape includes: Start co-ordinates,
finish co-ordinate, gallons of agent and type of agent. The
spraying from helicopters is omitted - as is record of aerial
spraying before 1965.
2. The Australian army has supplied the locations of approximately
70% of Australian Units [based on commander diary information].
This is the so called "CM)11 data. Vital co-ordinate
information is currently incomplete, but should be able to bs
obtained.
3. A comprehensive survey of all Army personnel in South Vietnam to
be conducted by this study will include questions .to fill in
information gaps i.e. Report possible exposure to helicopter
spray missions; unit postings (which are not included in "CARD"
data); subjective information on exposure to handling
herbicides, spraying from backpacks, trucks and boats, to aerial
spraying and to.areas that were recently sprayed. Questions
allowing the assessment of the internal consistency of the
soJrces of information are to be included.
4. Survey questions will include checks for accidental and
occupational exposure to phenoxy herbicides, arsenicals,
asbestos and other Detrimental environmental agents outside the
potential exposure in Vietnam.
Aerial Sgrayjnc[

'

•

• '

The exposure to the aerial application to these agents may be
separated logically into four areas:
a. Spj?ay_drift and concentrations in "jungle"* from aerial
application. This concerns the fate of spray from the time the
spray leaves the plane until spray particles impact on the
jungle foliage, tree trunks and ground and to the herbicide
distribution within the jungle ecosystem.
•b&lt; J^LF.°_nrO°nt£LOLa!LG. in JunQle 3nc' hence likely sources of
contamination. Addresses .the following areas:
i) volatalisation and revolatalisation
ii) pnotodeconiposition and biodegredation of herbicide
components
•
iii) redistribution of herbicide components within the jungle
environment e.g. after leaf fall
iv) Bioaccumulation

"jungle" is used to indicate all possible tynes of vegetation
such as forest, savanna, mangrove, swamp and cultivated land.

�•

-8t

^ •

.

c. Exposure ^nodes;

i.e. exposure via dermal, alimentary and pulmonary routes
including relative absorption values and likely sources of
contamination via eacli route.
d. Exposure categories
i.e. use current data in the scientific literature to choose a_
priori meaningful exposure level categorisations.
a) Spray drift
There are two models which are proposed for spray drift
calculation. They are not of necessity mutually exclusive and are
as follows:
i) J!te_teiininj.stic^ model of spray fate.
"The generalised model format is for a mass continuity equation
that in principle provides a complete description of the
trajectory and properties of an aerosol or heavy particulate
cloud, from the time of cloud stabilization to the collection by
downwind surfaces. The terms included in the generalised model
must therefore specify the direction and rate of downwind cloud
travel, the alongwind crosswind snd vertical cloud dimensions of
travel time and distance, the distribution of material within
the cloud as a function of time and distance., and loss of
material through gravitational settling, impaction or deposition
on vegetation or other surfaces." (19) Ine model snculd also
provide for the. effects of variations in chemical and physical
properties of the material contained in the spray cloud e.g. the
volatility of components; the mode of release and source
emission time; and in meteorological, micro-meteorological,
terrain and vegetative factors.
Spray "drift" is used interchangab.lv to describe two distinct
processes. Trie first type of "drift" refers to the variation of
the actual flightpath to the "HERDS" data and the second to the
.spreading of the spray cloud due to physical and meteorological
conditions. The former could conceivably be tens of kilometres
while the latter should be 1 kilometre at most.
Although it has been stressed that the pilots were able to lay
spray swaths accurately and that drift "just did not occur"
(A.L. Young private communication), [Herbicide]" mission
commanders stated that drift was a common problem and could
extend frcv.i 1 to ?. kilometers. Ons "Rancn Hand" commander said
in several cases drift could be up to 10 k:n. (These .instances
were mountainous regions usually occupied by enemy forces) (18).
r

To reliably estimate the spray fate requires the following
information.
1) Jl^UyJ__fJ^Y,.:path. The "IERRS" tapes give: the positions of
flighupaLn""cn;ipaj"rits. SJncc all trie 1'jxed wiivj mission

�preparation included aerial reconrmsanoe it :n&lt;ay bs assumed that
the endpoints or at leas'; the startpoint was relinbJy achieved.
However it has been stated that the actual flightpath may have
deviated markedly from a straight line (A.L. Young private
communications) with terrain being a major factor. Furthermore,
if a mission involved clearing jungle along a river bank or
road, the straight line approximation would be grossly in error*.
2) Sp_L?iy_.-PJ:lliy£.icl sizs,_o'iRt.ribution is a critical factor in
determining drift potential "revolatilisat Ion arid particularly
fate within the jungle canopy -- drops smaller than ISQuci would
.pose a problem. If the spray is volatile, i.e. Orange, the
larger droplets can vapouriss to these dimensions, exaggerating
the problem. The droplet size is highly dependent on viscosity,
nozzle geometry, spray system pressure and aircraft speed.
Incomplete data on particle size distribution is included in
Table 4.
.
k

TABLE 4 Spray characteristics of C-12'.5 Modular Internal Spray
Systern_._TflTTs'pray m'aterlai'uhkriov/n'j"
Aircraft speed
Aircraft altitude
Tank volume
Spray time
Particle size: (percentage
by volume)
100J 1.9%
.
100-500U 76.2%
500

130 Knots
150 ft (45 m)
1,000 gal (4,500 1)
3.5-4 min

•

21.995

87% impacted within 1 min
13K drifted or volatilized
Mean particle volume

*

•

0.61ul

The committee on Effects of Herbicides in Vietnam (17) found
several instances where defoliation missions were more than 8km
from the nominated path.

�The problem of volatility would also affect the water soluble
Agents Blue and White which were sprayed in a concentrated
form. Experience in agriculture has shown that it is possible
for the water to vapouriss from spray particles leaving a dust
of the concentrate which impacts with extreme unreliability
(70). The effect varies inversely with droplet size. The water
solubility of these Agents mean that they have a vastly
different environmental fate if it rained within 6 hours of
application.
Il^rpjnme^ejrolp^Y.. The "deposition and/or drift of a spray cloud
is hlgnly dependant on the locajL_ meterological conditions. Such
factor as terrain, jungle surface and tiros of day dictate local
v/ind direction, thermals and inversions which are impressed upon
the larger scale weather patterns. Fortunately jungle provides
micrometerological patterns which are stable over large areas so
reliable predictions are possible given the factors of terrain,
jungle surface, time of day and weather.
A factor which interacts considerably with micro-meteorological
factors to produce drift is aircraft spray height - it must be
stressed that, although highly dedicated, the US pilots were
operating undsr combat conditions, in many cases over difficult
terrain so that the value of 150ft (45m) must be treated as a
nominal altitude only.
Conclusions

.

-

The overwhelming problem yet to be faced is that of the validity
of this model. Agricultural experience (70) has shown the
inadequacies, even disasters, of models of spray behaviour in well
controlled situations. The variety of specialised models available
and the controversy over their validity (0), (9), (19), (70), (71)
illustrates the potential problems.
Furthermore the available models concern the application of
dilute solutions (of ths order of 1 in 100) applied over an even
crop surface by single lignt plane from an altitude of 3 meters
•versus the situation in Vietnam where a concentrated solution was
applied over a rougn jungle surface by a formation of cargo planes,
flying at a nominal 45 meters. The utility of such models to the
Vietnam situation could only be classed as fortuitous.
In addition volatile esters "were requested [and used] in order
to achieve more uniform coverage withj.n_ a forest csnopy"(66). Thus
the volatilisation from puri:ic.U&gt;s~~wiv.hin the sp ay cloud and from
herbicide on leaf surfaces must, be included in any model of spray
fate and/or exposure.
It is obvious that there are many problems to be addressed
before the deterministic mocisl would be a viable preposition.
Validity could only be assessed by a careful re-enactment of the
Vietnamese spraying operations under a variety of operational and
wea tt if r cone1 i ti ons.

�-11ii) Statistical Model
The requirements of the "deterministic" rncdsl for hard data may
not be fulfilled from the distance of time so it is suggested
that a simpler "statistical" model of spray fate be used.
It will be assumed that the planes started from the "HERBS"
startpoint and headed in the direction of the endpoint. The
variance of the probability distribution function of the actual
fligntpath is assumed to increase with increasing distance from
the startpoint. The "actual" endpoint is distributed at a mean
distance of 14 km from the startpoint.
The percolation and vertical distribution of spray within the
jungle is more complex. The "deterministic" model would be of
great benefit in calculating this distribution. The most
satisfactory method would be to assign various fractions of the
spray cloud to the sections of interest in the jungle ecosystem
i.e. soil and lower canopy.
'The spray swath distribution function is derived assuming the
flightpath is known. The major factor affecting variance of
this distribution function being the number of aircraft and the
terrain.
The position of the troops will be treated as a two dimensional
gaussian distribution centered on the "CARD" data co-ordinate.
The variance will include such factors as co-ordinate accuracy
and whether the troops were on patrol.
The time effect is included in a simple exponential model of
herbicide component decay choosing appropriate decay rates from
the scientific literature. The effect of vegetation cover
protection and exposure modes is included as a multiplicative
factor. Considering ths simplifications so far, it is proposed
that a simple cumulative model of exposure be used, giving
relative exposure days as an output. (For the full mathematical
treatment see Appendix III.)
Comments
The relativity of unrelated modes of exposure poses scientific
problems which will take at least 6 man months to treat. References
(!&gt;), (22), (26), (40), (41), (42), (50), (_58) and experience in
Australia with council workers spraying 2,4,5-T coupled with U.S.
Air Force documents (currently requested) concerning calibration and
spray simulation will enaole a reasonable connection to be obtained.
The latter documents will also provide a more accurate basis for
the numerical values proposed in Appendix III.
The work of Isensec (35) tins shown that bioaccumulation
.(1000-6000 x accumulation) of dioxin contained in contaminated silt
is possible by aouatic organisms. Considering the volu.v.s of Agent
Orange (the source of dioxin) which was distributed over the Rung Sat

�-12fishing region it is
dioxir, contamination
highly cpcculntjvs.
health effects it is
significant fraction

highly probable that seafood was a source of
- the relative amounts and significance is
For the purposes of regression analysis on
hoped that this background exposure is' no a
of the total exposure.

�-1J5-

ftecojr[fiy ndnt i otis_

1. Run modified "HOPPS:I program using simple assumptions to
estimate size of exposed group.

2. Maintain liason with Australian and U.S. experts in the fields
of Pesticides.

3. Continue collecting relevant articles from World literature.
.

•

4. Develop models for
(a) Spray drift
(b) Environmental fate of herbicides
(c) Exposure modes
(d) Exposure categories.

5. That the models of drift and environmental fate be tested using
•
simulants to assess likely validity of theoretical predictions
of drift and foliage penetration under conditions similar to
those in South Vietnam.

/
6. The proposed models should be subject to extensive scientific
peer review

�-14-

1.

Comments by Dow Cftem j.cal Company on oresqntati.cn JTttr!&lt;2_by_ D,r. _T.D.
Sterling Royal COTnissiori~ - Herbieldejs~and PesTicicias
1973

2.

Report of ths _ Consul tatlve Council^ onjconqonital abnormalities in j:hs
Yarram District Oept. of Primary Industry" Canberra 1978 ~
Principles and Methods for jevaluat Ing the _tox ic i ty_qf_ chsm icals.
! Environmental Health Criteria' 6 TiHO 1978" " "
"
•

Part

4.

Criteria for Cstsrmlninn,_E_xpjJsu_re_ Leysjs^M-l.i.H taiQL^_rs5nr}? 1_ to^jjloxin
and j-ieraicida drangs during t^e'vTet'nam War TcJra'Yt) USAF "
~

5.

Advisory Committes on Pesticides Further _Rov .lev/ of the Sa.rety For use
In ths U.K. of the Herbicide 2,/t,3,-T "- 1980

6.

Pcstlcidos used in Vistnafn Host 11 i t i e s and t_hg 1 r u se . in
_

Agriculture : Ccnparitivg Study (draff) Environmental Health
' Dept. Health) 1980
7.

Anon Report^ qn^ the Asrial uss(_of_ Phenoxy Horb-lcides Department of Food
and Agricufuffe California 19"78

6.

Bache D . H . , Saye r W . 3 . D . Transport of Aerial Spray, I.__A mode 1 of
Aerial Dispersion Agric. Meterol. 15 pp 257-271 1975

»

9.

Bache D.H., Uk S. Transport of Aeria 1 Soray , n_.___ Igsnsp^or t jvithin a
crop canopy Agric. Meterol. 15 pp"3Vl-377 1975~

10.

Barnes J.M.

11.

Bartleson F.D., Harrison D.D., Morgan J.D. Field Studies of wildlife
exposed to TCDD contaminated .Soils AFATL-TR-75-49 "1975

. _
Assessing Hazards...Fro_m
low doses of toxic subs cancels Br. teci. "Bul." 31 op I95-2CO 1975

*

12.

Baur J.R. , Bovey R.W., McCall H.G. Thermal and Ultraviolet loss of
Herbicides Arch. Environ. Contam. Toxicol 1 p'p 239 -"302 "1973

'13.

Bbhm H.H. , Muller H. Model Studies on the Accumulation^ _p_f ferbicides LJ
Microalgae NaturwissensnaYten 63 p296 1976

14.

Bovey R.W. , Young A.L. The Science of 2, A, 5, -T and Assqciatsd Phenoxy
Herbicides Wiley I960"

15.

Byast T.H., Hance R.J. pj^gr^djrti^njpJL^^
Soils _lncupated_ in tjng Ll^oo^s 'cory_ - 197?

16.

Cocucci S. e al AbDrotinn_jridjrrr.nsJ.oj;a^i_o_n_jDj^_.t^^
^

17.

'*'•* PP;*y2"-'tS4 1979

Committee on the Effects of Herbicides in Vietnam The__E_ffects_gif
l'!?rJi-iP^.es_-ir] A°'^^_/J ' ^ l . . J ~ Summary and Conclusions "National
clL^^l
Academy of Sciences

�-15Comptroller General L!Lj&gt; i_£rcyn_cj__Trc:qps In _Squch Vlelna'n v/ere_in areas
sprayed with Hgrbicide rj'vanrfj' U."5~ iJelTcral /\ccbjntin"g'"orrTce l~979 ""
19.

Cramer H.E., Boyle D.G. llj£jiicnLn£^
particle; behavlcijr - -

20.

Crosby D.G. Conquering thg Monster — T^e_Phgtpohemicaj[_ Past rue tign^of
^l°J!P.cl-i9£iP_5. 1'^itn MaficnafMeeting oT Arr.erican CheinicaT'SoH'ety
1977 "(See Kcport on Aerial use . . . )

21.

Crosby D.G. , Wong A. S.

^

~

"

"

~

' 19/7

22.

Phar M.M., Tandon J.S. , Sircar K. P. ^sorpUon_ejTd_Dccretionjof
2 &gt; A,.'j-TrJ L chlqroo(ienoxy Ac st. ic_ Acid^in Map "Arch ."frit r'PharTikYcody'n . 210
pp 230-255 "1974"

23.

Dodge J.M.

24.

Donaldson T.W., Irvine F.N. 2j_A, 5-T Res iducs in Dlackbsrry_Fj.'iji t
Asian v/sed Science Society Corif. r979"~

25.

Farwell S.O., Robinson E., Powell W.J. , Adams D.F. Survey of airbourns
2, A-D in South Central Wash i ngton J. Air. Pollut. Con cam. '26 pp 22A~-3"i5
1976

26.

Feldman R.J., Haibach H.L. PgLrc^tenpous^onstrabion of ^sornu^Postj.cides
and Herbicides in Man Tox. Appl. Pnarm". 28"pp 125-132" 1974

27.

Gsbefugi I., Baumann R., Korte F. ^^c^j^^sr^^j^cr^j^jj^^
•
jiJCOD) unter simulierten Ur^^^ltbediTp^j'sn Naturiwissehs'ci : ialf"tibn~64 pp
486-487 1977

. 28.

Gehring P.J. e_t al_ The Fatc_qf 2.4,5-T Following Oral Ad.T.inistratiofi to
Man Tox. Appl. Pnarm. 26 p'p 352-"36l 1973 " """"
~
-- --

Trig Phenoxy Hgrblcidss - A Sum:nary

- 1977
7th

29..

Hance R.J. Herbicide pgrsistence and breakdown in soil in the long
term Proc. Assoc. Ap"p"r~Biol.~ -

30.

Hiles R.A. and Bruce R.D. ZjJiLJbL^A^JlL0^
elimination _in the rat: First Trdgfr"6'f'"zc'r~o_ n'fdpv?" CoVtneuT'l'oxicol. 14
pp 599~ 600 " 1976

31.

Holt E.S. (Major)

^Rsoort_of_the spraying oif J tJ rbic_l_des at_ J.st_
ArA.U~.FiVG" RopoiT "2/68 "1963" " " •

32.

Hook J.B., Cardona R. Osborn J.L., Bailie M.D.

The Renal _Hand.li.na of

Cosmst. Toxicol. 14 pp 19-23" "1976"
33.

I ARC Monographs Vol.
I ARC Lyon 1973

2

34.

1ARC Monographs Vol. 15

Some' inorgcinic f.nd £rnono^J.alic_cp;i:f:ioi.ind_s
......
" ..... " .................... ~~ ..... """
Somq_ Fu^^ntsM-fi^JJ^

�-1635.

-I ARC Monographs Vol. 23 Borne Mstals and Metallic Compounds IARC Lyon
1980
"

36.

Isensee A.R. Bioaccumulation of 2,3,7,8 (TCDD) in 'Chlorinated Pnenoxy
Acids and their D~ioxins'~~Ramel (edT~ 19/8

37.

Isensee A.R., Jones G.F.. /V3sprDtioj}^ajid_Tjraj}sj^c_a^gn_o^f Rggt_ and
Foliage^Applied ^^-Dichloroohe^nqi^ 2.71 - bTch j qrod i o'^n^p'-pj:dioxln . and
2,3,7,8 TCDD J. AgrTTood" Cnem. 19 pp f2J.O-f2i4 1971
"

38.

Kimbrough R.D. (eu) Halogenated Biphenyls,, Kaphthalenes, pj.benzgdioxj.ris
and related products Elsevier North" riofland "J980

39.

Kirkwood R.D. Plant target areas and methods of attacking them
Application of Pesticioes 2 Cranfield i960

40.

Aerial

Kolmodin-Hedrnan B, Erne K and Akerblcm M. flielo^/\Dp_lic_ation_ of pj-ienoxy
• •herbicides in Field Worker Exposure during Pesticide Application ~eo
TordoTr 1979

Al.

Lavy T.L. Measuroment of 2? A, 5£T exposure of^forest workers
Forest Produces" A'ssociaton 1978

National

A2.

Leng M.L.
ReaHstic Evaluat3.on of J-brcan Exposure jTrgni^aopj ^-^^j
2,4,5-1 sprays Dow" CneiiTical Co.Tipa"ny " 1973

43.

McNulty W.P. Toxicity 0/2.3,7,8 - Tetrachlorodibsnzo-n-:dioxin for
Rr^S'JS Monkeys: Brief Rdporu Bull. Environ. Contain" l"ox~r8~pp""l08""-109
1977
44. " Nash R.G., E3eall M.L. Fatc_of_Si IVRX,,^!^. ,_ip_ _and ?-12i2jQj TCODJn_a
' mlcroagroecosystem chamosr A3S~PAP AM. Cl-EM "socTl"75 p$T"TsT78
" '
45.

Nash R.G., Bsall M.L. Distribution of Silycx, 2,A,-D and TCDi) toplipd
•• to Turf in _Chafnbers and Field P'fots J.~Agric. cFicm. 28 pp ~5"i4^623 J'980

46.

Office of the President Report_on_ ^Jl^T A report of the panel on
Herbicides of the -President 's'Scie'rice Advisory Committee. C.M. McLeod
Chairman. Office of Science and Technology

47.

Poland A., Glover E. , Kende A,S. SterpqopecJ.fic_,_
.
of 2, ^i 7j 8 - 1 e t r ach 1 o roc! i ben ?. o -r^-c'l J c"x ih_ J5£jj(T&gt;a Qc'M:o\Jal "" " ?." IB 6l
Cnem 2M "pp 4936~494"6 "1976

48.

Poland A., Kende A. ^JJ^.S-leJij'ajphl^orcciibjijn^
cpnt: cmi j r.ant and m J l c u I V P
"f'^'J- TTOG" "35 p

p

~

49.

Poland A., Kendo A.

50.

Ramsey J.C., Lavy T.L. and Bra'jn IV.H.

51.

F^pgiyni G. EstJnintion of thc_l_CDD tpxic_ppU5nt,:lnl in
" ~ ' ~ C c n i L~" S'c,c'.~ ~ioxjf.:ol "[i''t-"i"iii"i7""

"

"

~

"

TlTe_Gc&gt;nct}c_Exprorision_of AHM ActivJ.t'y:_ ryidRnc^
_ j n fYaTrpsZibn'sTv'r:''jn]"c"ii
~
""
"
T.97'7
"........."
E_x_nosurc of For r. s i: " Wo jJke r s_ t.g
' ~ ' " '
"

�-17-

52.

Rose J.Q. ej: al_ The £ate_ pXJ?^
_
_
following single .ar.J"repeatwT Or'al_"Do5es~"to JtiiVT&lt;at~"~Tox. AppTr"f3harm.
'

36 pp"209-226""T976"

53.

Schultz D.P., Harman P.O. Residues of 2./i,-D in Pcr.d Waters, Mud, and
Iis!lJ.2Zl Pest- Mon - J - 9 PP 173-179 1974
~
~"

54.

Simpson G.R. Aerial Spraying - S a f e Use of PesUoidgs on Cotton Crops
Health Commission of N.S".-W. 1979
"
." '
".

55.
•
56.

Sirons G.J., Frank R.F., Dell R.M. PicLojran^Rsjsid^^
Macdonal^^Cjrtj/jr Freejway Right qf Way^ BGl~i EnVir6rr."c"bn'ta"?Tf.~ Tox. 18 pp
526-533 1977"'
Stevens T.S., DiPastiuals L.C., Farmer J.D. Acu^c_IJiha_latJLO^Tcx_i£(y_ooy__
' .1 Herb icicles, .CscocfylTc "Acid and"
.
_
_
Disodiuir. Mathanoarsbnic'^cicl Bull. Environ. ContarnrTox. 2Jrpp'"Jo?i-311

••a—

-

-•

••HI

•• — I

• •

I* .-».•-.&lt;•••-*—..—J»^. . J.. II I

•—

i

.

I

I

1979

57.

Stewart W. A Retrospective Study of Agnnt_0^ange_jnnjj
Vietnam Veterans (Draft)~ US" Veterans7\3sbciation 1979

58.

Tordoir W.F., Van Heemstra (ed) T. Field_ Workgr Expos-jre duri
Pesticide Application Elsevier Nortn Holland 1930

59.

Torstensson N.T.L. Dearedaticn__o_f 2,/t-D nnd MCPA in Soils of low pH
Env. Qual. Safe. (SuppT3" pp" 262-5" 1975

60.

Walsh I..M. et al Occurrence anci Distrihuti^on _of ^.rcenic in__Soils and
Plants EnvirotiT lteaitfrpers.""l? pp 67-71 1977

61.

Ward C.T., Matsumura F. Fate of 2,3,78 (TCDD) in a Model Aquatic
_Envirpnrnent Arch. Environ. Con cam. Tox. "7 p~p 349-357 1978

62.

Wauchope R.D., McWhorter C.G. Arsenic Residues int Sjjyb
Simulated MS_M_A_ Spray Drift Bull. EnvTrdni" " Con tan. "fox.' 17 p"p r65"-167
1977"

63.

V/eakley B.S. How dangerous is sodium cacodylate? J. Micros.
249-251 1977

64.

Woolson L'.A. Rate &lt;^J\rsj?nicn]js_jjiJ}^
Environ. Health Pefs. 19 pp"73~81. 1977

65.

Young A. L. Use of Herbicides in South , Vietnam JLggl^gT^ Educational
Conference on Heruiciae Ora'nya, Silve'r Springs Maryland 1.900

66.

Young A . L . , Calcagni J.A., Thalken C.E., Tremblay J.W. ln;?_J.oxA^
mnn ris&lt; of

67.

Young A.I.., Thalken C.E., Arnold E.L., Cupello 3.M. , Cockerharn L.G.,
S...?j ?.J.i 8"JTCDCO. jLJlJyi\q.J:nxiro[i^cnt j_Sj^™^
~
' " ~ " " "

109 pp

�-1868.

Young A . L . , Wolfs W.M. Cr^r^ia J[o_^_e^ujTj0tinr; ^?P°stjr?_]:c!V(l!-^. 0?&gt;
miHtary_persopnol._to Dipx Jri" ~c:7icl_horb Vb Lc!?. JJrsnif :-j JjuHn'q j'^_ Viecr':o:,i
tfa: ~ Position ^er'l^nluUxf by USlJOO* to L.6 VACC'i2"Cec"~i979

69.

Zepp R.G. , Wolfe N . L . , Baughman fi.L., Gordon J.A. ^hemipnl^ anf[
Riotochsmica 1_ Alts r a t i o _n_f _ 2,A-D Esters in theAc]uatic J

Southeast &amp;Tv."~Res7"Lat3. U.S".

1975

70.

Casimir M., Watt J.W. Ac'rial Snrny Apnl icat.ion _ Agaihist Insects .Pests
AG Bulletin. Department of Agriculture NSW 079"

71.

Cran field Institute of Technology College of Aeronautics. Aerial
Application of Pesticides. Vol. I-II, Short Course, 1900.

�-19-

2. (a) Mr James Watt, Research &amp; Development Officer (Gayer
Australia), 666-9041
- field trials/aerial spraying .(mathematical
models/literature)
(b) Mr Jack Snelson, Pesticides Co-ordinato.v for Commonwealth
Department of Primary Industry (062) 72-3933
- most complete source of world literature concerning
pesticides available in Australia
tc

(c) Mr Brad brett, Australian Veterinary Chemical Association
(AVCA), Uth Floor, 60 York Street (290-0700)
- good source of literature
- excellent contacts in private and public sectors
(d) Or
-

"Dick" Albanez
statistics
theoretical models of spray drift
exposure (of Ranch Hand personnel).

3. (a) Jack Snelson is an excellent source
(b) C.I.H. library is most helpful in obtaining material once
the reference is found
(c) Commonwealth Health library, Canberra has access to the
Dialog database which includes Chemical Abstracts and
Science Citation Tndgx_. Tne latter is line" most" useful
source for D-) obtaining complete list of "material
published by a given author in given years (ii) obtaining
complete list of all books/articles which cite a given work.
Relevant authors are:
Alan Poland
D.G. Crosby
G. Rcggiani
H.E. Cramer

-

enzyme induction
heroicide degredation
Seveso/dioxin long term effects.
Spray drift

(d) The Medlars/Mcdline database has already been searched and
printouts are filed. (This database is limited because it
excludes articles without a direct medical context.)
(e) Obtain as much in formation as possible concerning American
experiences with thsir surveys via Dick Albanez and Bill
Wolfe - especially information much Al Young may have,
and the report by Steven Mocks dealing with the herbicide
spray mission simulations cone in Florida by USAF.

�-20-

References yet to he obtained
..

^

Anonymous , 197/4 . D JJinoci tion_ o_f _n.ranga_ torJiici dc_oy _ino.inoration .
Final Environ^2nlarjvtaIe;nenE'r "OepartmenF'of the Air Fo'rce,
Washington, D.C. 737 p.
Bethel, J.S., Turnbull, K.J., Briggs, D. and Florcs, J. , 1975.
l^iJay^r^o£_yie^nain fore5_ts_. American Forests,
: 26-30, 36-61."

Brown , • 3 . W . , 1 962 . Vegetation?*.! spray tests in Jpu.tlTj/jjBtna^. U.S.
Army Chemical Corps [Biological Laboratories, Fort Oe'trick,
Frederick, Maryland. 11? p. Available from the Defense
Documentation Center, Defense Logistics Agency, Cameron Station,
Alexandria, Virginia, DOC Number PD 476961.
Carrier, J.M., 1974. Jh?_J^^yjl'lJ^il^hJcid^_jn^^nG and
Mickey's Informants in South Vietnam. The Effects of" Herbicides
Ln South Vietnam. Part B. Working Papers. National Academy of
Science, Washington, D.C. 15 p.
Coates, 3.H. , Sharpe, L.M. and Pollack, H. , 1962. The present
sJ^tH %_° L.9.nILr DAc.aJL Jlci?i.E2LL-9.!L.v.L195i.? t L9n__i n__r els tic n 60 _m i 1 it a ry
nseds'. Tecnnical Mo'tes 62-68. """Institute ToT Dsfen'ss Analyses', "
Departmsnt of Defense, Wasnington, D.C. 30 p.
Craig, D.A. , 1975. i-MJLtJJ?JLkApA^
Historical
Report. San Antonio Air LcglstTcs Center, Oirectcfate of Energy
Management, Kelly AFB, Texas. 58 p.
Darrow, R.A., 1973. fpLi.?3G_(^na_ract^r|^ics__
c u ;
^
Sci. Soc. Am. "Aostrf 66, pp. 29-30.

Wsed
-.

Darrow, R.A. , Irish, K.R. and Minarik, C.E., 1969. H?rbicidss_ Used
Technical Report SAOQ-TR-69-11078.
^
Directorate of Air Force Aerospace Fuels, Kelly AFB, Texas.
60 p.
.
•' /

Darrow, R.A., Truchclut, G.B. and Bartlett, C.M. , 1966. OCON1JS
defoliation test: program. Technical Report 79. Crops
DeparLTnenYJ"7~BioIc"gicar"Sciences Laboratory, U.S. Army
Biological Center, Fort Patrick, Frederick, Maryland. 216 p.
_
Basj3_G3G;ji:own, N:;_w~Brunsw jck,_ Canada. ' TechnicarTi'e.'iiorandum "
141. "D^paftmenT oP"Li&gt;2 ~Ar&gt;,y~, "FortDstrick, Frederick, Maryland.

Demaree, K.D. and Creager, R.A., J968.
~

Fee, D.C. , Hughss, B.M., Taylor, M.L., Tiernan, T.O. and Hill, C.E.,
1975. Analy,l^C3l__MGJ^hod_ql_ony__fqr .Hj_rj)i£idQ__Ora:Tgo. Vol. I .
I
DeterrMin'ation of UiTgin o"i"u5AV" 'i'toc'ks ~ locnnical Report
ARL-75--0110. Aerospace Research Laboratories, Wright-Patterson
AFB, Ohio. 30 p.

�-21Grover R.J. Relative Volocj t ies of ester &amp;_arninc t
,2,4-D KccdTSci . "24 f 26-28""

^
™

Grover R.3. , Maybank J. and Yoshida K. 1972 Droplet and vapour d r i f t
from uu ty 1 e s ce rjr.nd d irne thy_l am incjva 1 tn o f ~2 , 4-0 Weed" Sci 20:
320-324
Harrigan, E.T., 1970. Calibration Test of tha UC-12:5:&lt;/A/A63Y-1 Snray_
Sy_s_tenni. Technical Repoi7Lr"ATJTC-lTf-7~u"J6. Arnia'TidhC'Developir.en'if
and Test Center, Eglin AFB, Florida. 160 p.
Hughes, B.M., Fee, D.C. , Taylor, M . L . , Tiernan, T.O., Hill, C.F. and
Wu, R.L.C. , 1975. Analytical Msthodplogy^^ for jj^rplcirJe^
"
"

Vol. I. Determination oi" Giemical Co.T.positicn". technical"
Report A.RL-75--0110. Aerospace Research Laboratories,
Wright-Patterson AFB, Ohio. 357 p.

Hurt t , W . and Darrow , R . A . , 1968 . Biolpgical_ ef Feet iveness o F_Stul 1
§i£LuAlJDl^.^f!SS.' Technical Kepoft"ArATL-TR"68-l22". "Mr
Force" ArfnamdhV Laboratory, Eglin AFB, Florida. 31 p.
Irish, K.R. , Darrow, R.A. snd Minarik, C.E., 1969. Inrormation
tnanunl
- . - ion ontroI in SoutheGs t Asia . Mic I . Pubi ic .
33. Department of the Army, Fort De trick, Frederick, Maryland.
71 p.

Kearney, P.C. , V.'oolson, E.A. , Isensee &amp; Hslling, C.S., 1973.
JeJ,rGc!^jr£dJjDj2!^^
Dpccn u_am i nn t ion . Environ. Health Perspect. Exp. fssue No. 5,
pp". "273-277.
Klein, R.E. and Harrigan, E.T., 1969. Comparison/Test of Defoliants.
Technical Report ADTC-TR-69-30, Vol. I. " Armament "Development and
Test Center, Eglin AFB, Florida. 356 p.
McConnell, A.F. , 1970. Mission: RANCH HAND. Air University
Review, 21 ( ) 89-94.
2:
Newton , , M . , 1 975 . E£i\^oj]^_s£t aj_imoact_ _q f _ " A ^ D . . .
reforestation _tests JJ2J!'c-Ll;££r!Jrlrc^O' 'A'eed Sci. Soc. ATI.,
'Ao'sTrT' 1 Vi7"52 p.
Tschi rley , F . H. , 1 968 . Response __p_f _t.r onicQ_l _,and_ .SMbj: r£p_ij^a l__woody_
£la_nts_J;o crie."Tncal t"reat-;.iqnts. ~ t«searcn Report D^-f3-67.
AgricukuFaTTtoseafcn Service's, U.S. Department of Agriculture,
Washington, D.C. 197 p.

Westing, A.H., 1976. ^3ogi£al_j:cn_s£gjo^
Jtndcjchina War. SlbckhoJiri InterniVtTonai Peace Research
InstituceT"""Alrngrist and Wiksel Interr.ation, Stockholm, Sweden.
119 p.

�-22-

Statistical model

To be "tabled at meeting.

�SECTION 3

• . Revised Pjjins and Estimates for the Study
During January 1931, three sets of plans for the study were
prepared in conjunction with Professor MacLennan, Dr. Byth and Ms. Rose.
These plans (copies of which are attached) addressed the Investigation
Programme at three levels:
Overall Strategic Plan
1 Year Plan (1981)
Plan for the Pilot Survey (to June 1981)
Since these plans were prepared, more detailed ones have been
compiled in each of the main disciplinary areas of the study. We are
currently monitoring progress agajnst these plans on a weekly basis.
We look forward to the opportunity to give a presentation of the
current plan and on progress.

�IXSTITU-TE: OF HEALTH

PROJECT PLAN

193T

I Apii!

RESEARCH PROGRAMME:
ASPECT OF INVESTIGATION

1932

Oc'ob*

July

January

"Ajsr.t Orange* Scientific In
J Year Mcsf'cr Plon
1933

j October

! April

Jonuory.

April

July

October

January

Maintain nomot and oddf*ii««

3a*a «n mortality and iMiotui of v«i«funt oid control*

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RESEARCH PROGRAMME:

PROJECT PLAN

ts:vj =!S:YY or svc^er

"Agent Oror-ijc" Scientific lnv«tiso^on

ASPECT OF MVESTICATiOSi

Master Plan for 1981

1981

Jc-iJory

February

April

McrcS

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July-

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Sentcrfibor

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November

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�</text>
                  </elementText>
                </elementTextContainer>
              </element>
            </elementContainer>
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      </file>
    </fileContainer>
    <collection collectionId="30">
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            <element elementId="50">
              <name>Title</name>
              <description>A name given to the resource</description>
              <elementTextContainer>
                <elementText elementTextId="4687">
                  <text>Alvin L. Young Collection on Agent Orange</text>
                </elementText>
              </elementTextContainer>
            </element>
            <element elementId="41">
              <name>Description</name>
              <description>An account of the resource</description>
              <elementTextContainer>
                <elementText elementTextId="49809">
                  <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>
                </elementText>
              </elementTextContainer>
            </element>
          </elementContainer>
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      </elementSetContainer>
    </collection>
    <itemType itemTypeId="1">
      <name>Text</name>
      <description>A resource consisting primarily of words for reading. Examples include books, letters, dissertations, poems, newspapers, articles, archives of mailing lists. Note that facsimiles or images of texts are still of the genre Text.</description>
      <elementContainer>
        <element elementId="52">
          <name>Box</name>
          <description>The box containing the original item.</description>
          <elementTextContainer>
            <elementText elementTextId="19367">
              <text>070</text>
            </elementText>
          </elementTextContainer>
        </element>
        <element elementId="53">
          <name>Folder</name>
          <description>The folder containing the original item.</description>
          <elementTextContainer>
            <elementText elementTextId="19368">
              <text>1885</text>
            </elementText>
          </elementTextContainer>
        </element>
        <element elementId="54">
          <name>Series</name>
          <description>The series number of the original item.</description>
          <elementTextContainer>
            <elementText elementTextId="19371">
              <text>Series III Subseries IV</text>
            </elementText>
          </elementTextContainer>
        </element>
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        <description>The Dublin Core metadata element set is common to all Omeka records, including items, files, and collections. For more information see, http://dublincore.org/documents/dces/.</description>
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          <element elementId="40">
            <name>Date</name>
            <description>A point or period of time associated with an event in the lifecycle of the resource</description>
            <elementTextContainer>
              <elementText elementTextId="19369">
                <text>February 26 1981</text>
              </elementText>
            </elementTextContainer>
          </element>
          <element elementId="50">
            <name>Title</name>
            <description>A name given to the resource</description>
            <elementTextContainer>
              <elementText elementTextId="19370">
                <text>Submission to the Scientific Advisory Committee, Australian Veterans Herbicide Studies, 3rd Meeting to be held in Sydney 3 &amp; 4th March 1981.</text>
              </elementText>
            </elementTextContainer>
          </element>
          <element elementId="49">
            <name>Subject</name>
            <description>The topic of the resource</description>
            <elementTextContainer>
              <elementText elementTextId="19372">
                <text>AVHS</text>
              </elementText>
              <elementText elementTextId="19373">
                <text>study protocol</text>
              </elementText>
            </elementTextContainer>
          </element>
        </elementContainer>
      </elementSet>
    </elementSetContainer>
    <tagContainer>
      <tag tagId="1">
        <name>ao_seriesIII</name>
      </tag>
    </tagContainer>
  </item>
</itemContainer>
