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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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&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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&lt;p&gt;For more about this collection, &lt;a href="/exhibits/speccoll/exhibits/show/alvin-l--young-collection-on-a"&gt;view the Agent Orange Exhibit.&lt;/a&gt;&lt;/p&gt;</text>
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                <text>A Study of Herbicides and Birth Defects in the Republic of Vietnam: An Analysis of Hospital Records</text>
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                    <text>°1041

Item ID Number
Author
Corporate Author

Report/Article TltlB

Clement Associates, Inc., Arlington, Virginia

A

Summary of the Available Scientific Information on
the Human Health Effects of Agent Orange

Journal/Book Title
Year

1983

Month/Day

Ma 3

v

Color
Number of Images
DOSCMptOn Notes

40
Alvin L Youn

9filed this item under the category
"Human Exposure to Phenoxy Herbicides and TCDD";
VA Contract Number: V101(93)P-953, Carl 0. Schultz,
Ph. D., Project Director

Friday, March 30, 2001

Page 1041 of 1070

�A SUMMARY OF THE AVAILABLE SCIENTIFIC INFORMATION
ON THE HUMAN HEALTH EFFECTS OF AGENT ORANGE

Prepared for:
Contracting Officer's Technical Representative:
Barclay M. Shepard, M.D.
Director, Agent Orange Projects Office
Department of Medicine and Surgery
Veterans Administration
810 Vermont Avenue, N.W.
Washington, D.C. 20420

Submitted by:
Clement Associates, Inc.
1515 Wilson Boulevard
Arlington, Virginia' 22209
under
VA Contract Number: V101(93)P-953
Carl O. Schulz, Ph.D., Project Director

May 3, 1983

�What is "Agent Orange"?
"Agent Orange" is a name that has come to be used to describe a particular type of chemical herbicide (a chemical that
k i l l s plants) that was used in m i l i t a r y operations in Vietnam
from 1962 to 1971.

The name came from the orange stripe that

identified the 55-galIon drums in which the herbicide was shipped
and stored.

"Agent Orange" was not a pure chemical compound

like sodium chloride or sucrose.

Instead, the herbicide was

a mixture of chemicals, containing equal quantities of the
two active ingredients:

2,4-D and 2,4,5-T.

2,4-D and 2,4, 5-T

are weed-killing chemicals that enjoyed extensive commercial
and private use in the United States from the 1950s well into
the 1970s.

2,4-D is still used extensively in this country.

Like many industrial chemical mixtures, the "Agent Orange"
that was manufactured during the Vietnam era contained small
quantities of impurities.

These impurities were chemicals

from which 2,4-D and 2,4,5-T had been made and chemicals that
were produced inadvertantly in the manufacturing process.
Some of the impurities were a family of closely related compounds known as polychlorinated dibenzodioxins which, as a
group, have often been called "dioxins."

One of these dioxins,

2,3, 7,8-tetrachlorodibenzo-p-dioxin (TCDD), has been extensively
tested in experimental animals and is believed to be the most
toxic member of the dioxin family.

It is generally accepted

that TCDD is one of the contaminating dioxins in 2,4,5-T.
It is not known to be present in 2,4-D but other dioxins are.

�In the remainder of this report "dioxins" will be used to r e f e r
to mixtures of polychlorinated dibenzodioxins (usually unidentified).

"TCDD" will be used to designate the specific chemical

2 , 3 , 7 , 8-tetrachlorodibenzo-p-dioxin.
Agent Orange was produced by several manufacturers at
f a c i l i t i e s throughout the United States under contract to the
Department of Defense.

The Department provided specifications

as to the composition of the herbicide such that the nature
and amount of the active ingredients were the same regardless
of the m a n u f a c t u r e r .

Although Defense Department specifications

set an upper limit on the total amount of impurities that could
be present in a batch of Agent Orange, it is certain that both
the exact amount and the nature of these impurities varied
from batch-to-batch, from year-to-year, and from manufacturerto-manufacturer.

Furthermore, since no one attached much sig-

nificance to the presence of impurities in Agent Orange until
late in the Vietnam experience, there is very little information
on how the nature and amount of these impurities varied.
Agent Orange was not identical to commercial formulations
of similar herbicides that were and are currently made and
marketed in the United States and these in turn may be slightly
d i f f e r e n t from those made in other countries around the world.
In short, we don't really know precisely what impurities were
present in Agent Orange, and we don't have any way to find
out.

Because there is quite a bit of evidence that the health

effects of these herbicide mixtures depend heavily on the amounts

�and types of impurities present in the mixture, we can accept,
only with reservations, information on health effects obtained
from studies of people exposed to other herbicide preparations
containing 2,4-D and/or 2,4, 5-T.
If we hope to understand the health effects of Agent Orange
with a high degree of certainty, it is essential to identify and
study people who were exposed to Agent Orange.
Who was exposed to Agent Orange?
The only individuals who are known to have been exposed
to Agent Orange are those individuals who were exposed during
its manufacture or as a result of its use in Vietnam.

However,

because Agent Orange was considered to be relatively safe at
the time of its use, there were no systematic studies to determine how much Agent Orange might enter a person's system as
a result of exposure in a manufacturing plant, from spraying
or being sprayed with it, or from entering an area that had
already been sprayed.

Another way of determining exposure is

to depend on people's memory of when and how often they might
have been exposed.

Unfortunately, several different types of

chemicals were manufactured in most of the plants that manufactured Agent Orange, and, several herbicide mixtures other than
Agent Orange, not to mention insecticides and perhaps other
chemicals, were used in Vietnam.

It would be difficult, if

not impossible, for individuals to know when they were exposed to
Agent Orange specifically.

The Air Force did keep records of

where herbicides were sprayed.

By combining this information

�with information about where and when personnel were stationed
in certain areas, the probability of exposure can be estimated.
Also those people who were actually involved in the handling
and application of Agent Orange were doubtlessly exposed to
it, but it is not possible to determine the amount to which
they were exposed.
What do we know about the health effects of Agent Orange?
As one might guess from the information above, we don't
have specific information on the health effects of Agent Orange
itself.

Scientists cannot identify a group of people who were

exposed to known quantities of Agent Orange and who can be
compared to a group of people who were not exposed to Agent
Orange or similar herbicides.

Furthermore, Agent Orange was

not tested in experimental animals at the time of its manufacture and use.
How do we determine the health effects of Agent Orange?
If we cannot study the health effects of Agent Orange
directly, how can we learn what health effects might result
from exposure to this material?

Several approaches are available

and all of them have been followed during the last 10-15 years.
Each of these approaches has limitations that prevent scientists
from reaching definitive conclusions about the adverse human
health effects of Agent Orange.

Nevertheless, if scientists

and health professionals review the entire body of information
that has become available from all these approaches, certain

�patterns emerge.

It is now possible to begin reaching tentative

conclusions about the health effects of Agent Orange.
all of these conclusions are highly uncertain.

Almost

The results

of studies which are currently in progress or planned for the
future will go a long way in removing this uncertainty, but,
for the general reasons described above and for specific reasons
described below, it is quite clear that we will never be 100%
sure of what the health effects of Agent Orange are.
One of the most promising approaches to studying the health
effects of Agent Orange is to evaluate the health of people
who may have been exposed to Agent Orange as a result of the
Vietnam experience and to compare their health with that of
people who were not exposed to herbicides like Agent Orange.
A few such studies have been conducted and several more are
in progress.

Some of the limitations of these studies have

already been mentioned.

We don't have reliable records of

who was exposed so assumptions are made such as "any veteran
who served in Vietnam was exposed to Agent Orange" (Australian
Veterans Health Study) or "any individual who was assigned
to Operation Ranch Hand was heavily exposed to Agent Orange"
(U.S.

Air Force Epidemiology Study).

These assumptions may

lead to the inclusion in the "exposed" group of people who
had very little exposure.

If there are enough of these people

they tend to decrease the ability of scientists to detect any
real health effects that might be present in those who were
actually heavily exposed.

�Another serious limitation is that it is very difficult
to select a group of "unexposed" people to compare with the
"exposed" group.

Ideally, the two groups should be the same

except for their potential exposure to Agent Orange.

This

means that individuals in both groups should not only be the
same in age, weight, and sex (fairly easy to do), but they
should also have similar smoking habits, diets, jobs, lifestyle,
and places of residence (difficult to do).

A real problem

attached to these studies is that because of the widespread
use in the United States of commercial herbicides that are
similar to Agent Orange and because of the presence of dioxins
in other industrial chemicals in the environment, there is
a possibility that some individuals in the "unexposed" group
have been exposed to the ingredients of Agent Orange.
Another problem with studies of people who were exposed
to Agent Orange is that a relatively short period of time has
elapsed since exposure took place.
used in Vietnam in 1962.

Agent Orange was first

Heavy use and potentially heavy expo-

sure did not occur until several years later, so the amount
of time that has elapsed since most veterans were exposed has
been on the order of 10-15 years.

Certain adverse health effects

e.g., cancer, heart disease, and respiratory disease, that
result from exposure to chemicals often take years to develop
after exposure begins.

Increased cancer rates due to smoking

or exposure to toxic chemicals have been shown to reach a peak
some 20 to 30 years after exposure.

Thus, an absence of evidence

�of elevated cancer and heart disease rates in populations exposed
to Agent Orange could indicate that these effects are not caused
by exposure to Agent Orange.

On the other hand, it might be

that they haven't had time to appear in sufficient numbers
to be detected.
The studies of populations who were probably exposed to
Agent Orange as a result of the Vietnam experience have not
provided clear-cut answers to questions about the health effects
of Agent Orange.

This is the result of some of the limitations

described above.

Furthermore, future studies of this type

will not be capable of answering all these questions.

It is

necessary, therefore, to ask the question, "Where else do we
look for these answers?"

One potentially valuable source of

information is studies of human populations who are or were
exposed to commercial herbicidal mixtures that were similar,
but not identical, to Agent Orange.

There are a number of

these studies available, most are of workmen who sprayed herbicides on the job, but some are of populations who lived in
areas where herbicides containing 2,4,5-T and 2,4-D were used.
Most of these studies are subject to the same limitations as
those on the people exposed to Agent Orange.

In all of these

studies, the determination that a person is or is not exposed
is based on that person's memory of past events or, in many
cases, simply on the basis of where the person lived or worked.
Also people may be included in the exposed group who worked
at a job for only a few weeks or who moved into an area recently.

�On the other hand, people may be included in the unexposed
group if they are currently working in jobs or living in areas
where they are not exposed to herbicides but who may have been
exposed to herbicides in some previous job or place of residence,
perhaps without even knowing it.

Either type of error decreases

the ability of scientists to detect possible effects of exposure
to the chemical.
Another potential source of information about the health
effects of Agent Orange is studies of humans who were exposed
to some of the components of Agent Orange.

There are a number

of groups of people throughout the world who were exposed to
dioxins as a result of industrial accidents or unintentional
release of dioxin into the environment.

Several of these groups

have been followed for a number of years and much information
has been gathered.

It is difficult, however, to judge how

relevant these findings are to people exposed to Agent Orange.
The specific dioxins to which these people were exposed were
not identified and they may be somewhat different from those
found in Agent Orange.
One of the most widely publicized incidents in which humans
were exposed to dioxins was the explosion of a chemical reactor
at the ICMESA plant near Milan, Italy in July, 1976.

A cloud

of chemicals containing relatively large quantities of dioxins
blanketed the small town of Seveso immediately downwind of
the plant.

In succeeding weeks many individuals living in

Seveso showed signs of dioxin exposure, the roost prominent

8

�being chloracne, a severe form of acne which appears as blackheads around the eyes and ears and in some cases covers much
of the body.

This group of exposed people provides a potenti-

ally valuable, though unfortunate, resource for the study of
the health effects of dioxin exposure in humans. Unfortunately
much valuable health information that might have been gained
from this incident has already been lost. The reasons illustrate
why studies on human populations are seldom as informative
as people would hope.
At the time of the ICMESA accident, few people understood
what had actually occurred nor did they recognize the potential
human health implications of the event.

No measurements were

taken to ascertain the composition of the chemical cloud that
moved over Seveso.

It wasn't until nearly four weeks after

the accident that the first systematic efforts were begun to
determine the extent of exposure.

In those four weeks much

happened to alter the scene. Chemical residues in plants and
soil had begun to undergo chemical decomposition.

Chemical

deposits moved as a result of wind, rain and human activity.
Exposed humans moved out of the contaminated area and some
unexposed individuals moved in.

People living in relatively

uncontaminated areas ate food grown in more contaminated areas
and children and pets roamed throughout the area enhancing
their chances of encountering "hot spots" of heavy chemical
contamination. When systematic health assessments began to
be performed three months or more after the accident, many

�exposed individuals could not be located.

Many more refused

to participate in the studies and many of those who participated
in early studies balked at returning several months later for
time-consuming and sometimes painful examinations.

It was

even more difficult to identify comparable "unexposed" people
willing to undergo the same tests and examinations in order
to provide data for comparison purposes.

Attempts to compare

the health of Seveso residents after the accident to their
health before were unsuccessful because health-record-keeping
was very poor and incomplete prior to the accident.

For these

reasons all of the many studies of the Seveso population that
have been done in the eight years since the accident have been
incapable of showing all but the most severe and widespread
effects.

It is little wonder that these studies have generally

been inconclusive.

It is unlikely that future studies designed

to study such long-term effects of the accident as cancer and
heritable genetic disease will be sufficiently sensitive to
detect small but important changes in the incidence of these
diseases.
A final potential source of information about the adverse
health effects of Agent Orange is studies in experimental animals.

Extreme care must be taken in interpreting the results

of animal studies because animals may respond quite differently
from humans.

Experimental animals are often quite different

from humans in the way they absorb chemicals, in where those
chemicals are distributed in the body, in the way the chemicals

10

�are broken down or stored in the body, and in the way the chemicals are eliminated.

Also differences in body size, diet,

lifespan, and the physiology of individual organs may cause
animals to respond differently than humans.

For these reasons

scientists are reluctant to base predictions of human health
effects on animal studies unless the chemical has been tested
in several species of experimental animals and there is some
basis for believing that the test animals are similar to humans
in the way they respond to the chemical.
For reasons touched on earlier, Agent Orange was not tested
in experimental animals and, because the quantity and identity
of the impurities in Agent Orange varied, it cannot be exactly
reproduced for studies in experimental animals now or in the
future.

Therefore, it is necessary to rely on the results

of experimental studies of herbicide mixtures similar to Agent
Orange as well as studies of individual components of Agent
Orange such as 2,4-D, 2,4,5-T, and TCDD to serve as the basis
for the prediction of human health effects of Agent Orange.
The remainder of this report summarizes the information
on health effects available as of early 1984 from all the types
of studies described above.

This section is organized by effect

and in each case the entire body of available evidence is evaluated as a whole.

For more detailed information regarding

specific studies the reader is urged to refer to the Review
of Literature on Herbicides, Including Phenoxy Herbicides and
Associated Dioxins, Volumes III and IV published by the VA.

11

�Summary of health effects information
Cancer
Only one systematic study of cancer in individuals exposed
to Agent Orange in Vietnam has been published.

In this study

of Air Force personnel who were engaged in Operation Ranch
Hand (the herbicide spraying operation in Vietnam) there was
an increased incidence of skin cancer in the exposed group
compared to a comparison group of military personnel who were
not exposed to Agent Orange.

The type of skin cancer seen

was a very common form that is known to be associated with
exposure to sunlight.

Further studies need to be done to deter-

mine whether Ranch Hand personnel were more likely to have
been exposed to sunlight than were the members of the comparison
group.

There was also a slightly increased incidence of cancer

of the mouth and throat in the Ranch Hand group, but this excess
is so small that it may be due to chance.
Two other reports are available on cancer in Vietnam veterans but in neither study was there any confirmation of exposure
nor were matched control groups used for comparison.

In one

study based on Vietnam veterans who registered with the VA's
Agent Orange Registry, there were excess incidences of cancer
of the mouth and throat and of lymphoma (cancer of the lymphatic
system) when compared to the U.S. white male population as
a whole.

In the other report, a physician in Atlanta, Georgia

reported three cases of soft-tissue sarcoma (a rare cancer)
among his patients.

All three of these patients had served

in Vietnam but no other information was given about them.

12

�There have been 11 reports of studies of cancer in men
who were employed in jobs that involved the spraying of herbicides similar to Agent Orange.

Eight of these studies were

limited to men who sprayed 2,4-D- or 2,4,5-T-containing herbicides.

In the others, the workers were exposed to agricultural

chemicals in general, including herbicides.

These three studies

are not discussed here because of the uncertainty regarding
exposure.

Two of the eight studies of 2,4-D or 2,4,5-T indicated

that there was an association between exposure and the incidence
of soft-tissue sarcoma.

A third study showed an association

between exposure and lymphoma, and one study showed an association between exposure and stomach cancer.

Another of these

eight reports described 5 cases of lymphoma with cutaneous
( s k i n ) lesions seen in an English hospital.
cases worked with 2,4-D or 2,4,5-T.

Four of the five

The remaining three reports

showed no association between exposure and any form of cancer,
although in one of these there was a slight association with
soft-tissue sarcoma.
Of seven studies on populations that were exposed to dioxins
either in the workplace or from the environment, two showed
excess incidences of cancers.

A study of workers exposed to

dioxin as a result of a reactor explosion in a 2,4,5-T manufacturing plant in Germany in 1953 showed an excess of stomach
cancer.

Another study of the residents of Midland County,

Michigan, where Dow Chemical Company has a large plant, revealed
an increased incidence of soft-tissue sarcoma in women between

13

�1960 and 1980.

This finding is unlikely to be related to dioxin

exposure, however, because the excess cancer was seen only
in women and several of the people with soft-tissue sarcoma
had lived in Midland County only a short-time prior to the
diagnosis of cancer and had little or no connection with the
company.
Three separate reports describe two cases of lymphoma
and three cases of soft-tissue sarcoma in workers who may have
been exposed to dioxin.
no control groups.

These are isolated case reports with

The evidence for dioxin exposure is very

weak in the three soft-tissue sarcoma cases.
None of the studies of cancer in humans exposed to Agent
Orange, related herbicides, or dioxins provides an answer to
the question as to whether Agent Orange might cause cancer in
humans.

However, when all the reports are taken together certain

patterns appear that provide suggestive evidence that exposure
to dioxin-contaminated herbicides may lead to an increased
incidence of cancer.

Thus, seven reports show or suggest a

relationship between such exposure and soft-tissue sarcoma.
Four reports provide such evidence for lymphoma.

Two studies

show an association with stomach cancer and three reports suggest
a possible association with cancer of the mouth, nose, or throat.
The results of animal studies lend strong support to the
hypothesis that dioxins and dioxin-contaminated herbicides
may cause cancer in humans.

Six studies of the potential for

TCDD to cause cancer in animals were positive.

14

TCDD painted

�on the skin of mice caused cancers related to soft-tissue sarcomas.

Four studies in which rats were given TCDD by mouth

were positive resulting in cancer of the liver, mouth and nose,
tongue, adrenals, and thyroid.

In two studies in which TCDD

was given to mice by mouth, liver and thyroid cancers resulted.
Another chlorinated dioxin, hexachlorodibenzo-p-dioxin, caused
cancer of the liver in mice and rats when given by mouth.
Several studies suggest that when TCDD is given to mice with
other cancer-causing chemicals it increases the response to
those cancer-causing chemicals.
No studies of the carcinogenic potential in experimental
animals of Agent Orange or of commercial herbicides similar
to Agent Orange have been published.

A few studies of the

herbicidal ingredients 2,4-D and 2,4,5-T in rats and mice have
been negative (no cancer), but these studies were not adequate
to detect a small increase in cancer in the treated animals.
The current evidence, though far from conclusive, is s u f f i ciently suggestive to j u s t i f y continued surveillance of people
who have been exposed to dioxin and dioxin-contaminated herbicides in order to confirm or r e f u t e the association of increased
cancer incidence with that exposure.

Such surveillance ought

to include cancer of many types, not only soft-tissue sarcoma.
This limited evidence is also sufficient to j u s t i f y limiting
future exposure of humans to dioxins (especially TCDD) and
dioxin-contaminated mixtures.

15

�Reproductive Effects
Two systematic studies of reproductive performance and
outcome among men who may have been exposed to Agent Orange
in Vietnam have been published.

In the first of these the

Australian government sponsored a study to see whether birth
defects were related to service by the father in Vietnam.
No association was seen, although there was a slightly increased
risk of heart defects and Down's syndrome among the children
of Vietnam veterans.

It should also be recognized that most

of the Australian troops who were stationed in Vietnam were
assigned to areas in which there was little, if any, herbicide
spraying and no Australian troops were directly involved in
spraying herbicides.
In the study of Operation Ranch Hand personnel discussed
in the cancer section above, there was an increased incidence
of spontaneous abortion among the wives of officers in the
Ranch Hand group when compared to wives of officers in the
control group.

There were also increases in deaths of newborn

babies and unspecified (minor) birth defects.

There may have

been slight increases in learning disabilities and physical
handicaps among children of Ranch Hand personnel.

The signi-

ficance of these findings is not clear, because most of the
increases are very small, and many of these differences disappear
if the data are analyzed differently.
Two studies have been reported of men who had been exposed
to herbicides similar to Agent Orange.

A study of wives and

children of herbicide sprayers in New Zealand found no increases

16

�in birth defects, stillbirths, or spontaneous abortion compared
to the population of New Zealand as a whole.

There was a very

small increase in the incidence of heart defects, but this
may have been due to chance.

Another study of children born

to the wives of men who sprayed herbicides for the Long Island
Railroad showed no increase in major birth defects but two
minor birth defects, i.e., misshapen feet and tear duct obstruction, were seen in excess.
Several studies have been conducted to ascertain whether
there are increased incidences of spontaneous abortions, stillbirths, or birth defects in areas where there has been heavy
use of herbicides similar to Agent Orange.

In these situations /

there is the potential for exposure of both parents as opposed
to exposure of only the father as in the four studies discussed
above.

One of these general population studies gained a great

deal of publicity in the late 1970s when it was reported that
women living in the vicinity of Alsea, Oregon experienced a
higher rate of spontaneous abortions than did women living in
other regions of Oregon where herbicides were not commonly used.
Careful review of this study by expert scientists has resulted
in a consensus that the results were misinterpreted and that
the study did not show the claimed effect.

More recently,

a study of people living in an area of New Zealand, where there
was frequent use of herbicides containing 2,4,5-T revealed
an increase in the occurrence of club foot in children in the
region.

Other small and perhaps insignificant increases were

17

�seen in heart defects and malformations of the penis.

A study

conducted in Hungary looked at the rate of five major birth
defects in the general population of the country over a five
year period when the use of 2,4,5-T increased greatly in that
country.
seen.

No changes in the rates of these birth defects were

This study is not very reassuring when it is consid-

ered that most people in the general population were probably
not exposed to the herbicide.
Four studies have been conducted of men exposed to dioxin
as a result of working in plants where 2,4,5-T was manufactured.
None of these studies showed a clear-cut effect on reproductive
outcomes.

Two of these studies did show a slight increase in

spontaneous abortions.

Two studies of the population exposed

to dioxin as a result of ICMESA accident at Seveso suggest
that there may have been an increase in birth defects (particularly of the heart) and an increased incidence of spontaneous
abortions in the year following the accident but the reliability
of these studies is questionable for reasons discussed above.
The studies of the reproductive effects of 2,4-D, 2,4,5-T
and TCDD in experimental animals are of limited usefulness
in helping to predict the reproductive effects of Agent Orange
in Vietnam veterans who are, for the most part, male.

In almost

all of the animal studies, the herbicide or dioxin was given
to pregnant females rather than to male animals.

Nevertheless,

in two studies, relatively uncontaminated 2,4,5-T and TCDD
were fed to both male and female rats and reproductive perfor-

18

�mance and outcome were recorded for three successive generations.
These studies showed that both 2,4,5-T and TCDD decreased the
number of live births and the weight of newborn animals, as
well as causing an increase in birth defects of the kidneys.
Furthermore, numerous studies in which TCDD was given to pregnant
females indicate that it is a potent teratogen (an agent that
causes birth defects).

TCDD causes birth defects in rats,

mice, rabbits and monkeys when given by mouth or injection.
It also causes an increase in the number of spontaneous abortions
and smaller newborn animals.
In summary, no single study of reproduction in humans
exposed to Agent Orange conclusively shows an adverse effect.
However, when all of the human studies of populations exposed
to Agent Orange, similar herbicides, or dioxins are considered
together, several of them show or suggest an increase in the
number of spontaneous abortions, heart defects, and "minor"
birth defects.

When this information is considered with the

results of studies in experimental animals, especially studies
of TCDD, it provides a basis for concern among scientists that
adverse reproductive effects may result from exposure to Agent
Orange and other mixtures that may be contaminated with TCDD.
Enzyme Effects
One of the best studied effects of dioxins in experimental
animals is the ability of these compounds, especially TCDD,
to alter the activity of certain enzymes.

Enzymes are proteins

that serve as catalysts in the destruction or formation of

19

�chemicals in the body.

Many enzymes catalyze the formation

or breakdown of just one chemical whereas other enzymes are
capable of acting upon an entire class of chemicals.
It is next to impossible to study the effects of chemicals
on enzyme activities in humans.

Most enzymes are located in

tissues where metabolic activity is greatest, e.g., the liver,
lungs, intestines, brain, and reproductive organs, and these
tissues are the least accessible to study.

Furthermore, there

are large differences among people in their baseline metabolic
activity.

About the only approach available is to look at

the levels of chemicals produced by enzyme reactions that appear
in the blood and/or urine and determine whether they are different in people exposed to a specific compound when compared
to people who are not exposed to that compound.
Only a few studies of enzyme activities have been conducted
in animals given the herbicidal active ingredients 2,4-D and
2,4,5-T.

These studies suggest that these compounds do not

cause major alterations in enzyme activities and some of the
small effects seen may be the result of contamination of these
chemicals with small amounts of dioxin.

A number of studies

of TCDD, on the other hand, have shown that it alters the activity of a number of enzymes in experimental animals.

The most

well-studied effect is to increase the activity of an enzyme
known as aryl hydrocarbon hydroxylase (AHH).

AHH is important

because it makes certain chemicals more soluble in water and,
thus, more likely to be excreted in the urine.

20

Very small

�amounts of TCDD cause large increases in the activity of this
enzyme in rabbits, mice, rats, guinea pigs, hamsters, birds,
fish, and monkeys.

In several studies where living cells were

taken from humans and allowed to grow in a culture medium,
the addition of TCDD to the culture caused an increase in AHH
activity in the cells.
It is interesting that in two studies of human populations exposed to dioxin as a result of industrial accidents
(one at Seveso and one at a 2,4,5-T manufacturing plant in
England), scientists found elevated levels of d-glucaric acid
in the urine of exposed people.

This chemical is believed

to be formed by enzymes that are very closely associated with
AHH.

This finding adds support to the theory that TCDD stimu-

lates AHH activity in humans.
What are the health implications of stimulation of AHH
activity?

This is a difficult question to answer because the

role of AHH is not yet fully understood. Evidence from animal
experiments and some human evidence indicates that some of
the aryl hydrocarbons

that are altered by AHH are cancer-causing.

Some experiments in animals where TCDD was given to animals
several days before the animals were exposed to cancer-causing
aryl hydrocarbons protected the animals against cancer.
TCDD caused an overall health benefit.

Thus,

Unfortunately, the

picture is much more complicated than that, because, if TCDD
is given to animals at the same time as the aryl hydrocarbon
rather than a few days earlier, the TCDD binds to the site

21

�of the AHH enzyme that is responsible for changing the aryl
hydrocarbon and prevents the AHH enzyme from doing its job.
Thus, administration of TCDD with aryl hydrocarbon causes more
cancer than does the aryl hydrocarbon itself.

An additional

complication is that there is evidence that AHH catalyzes other
tranformations and that some of these may convert inactive
chemicals into toxic ones.

In the absence of complete infor-

mation the fact that TCDD stimulates AHH activity must be viewed
as a potentially adverse effect.
Animal studies have also shown that TCDD alters some enzymes
that are involved in the manufacturer of heme.

Heme is the

portion of hemoglobin that binds oxygen so that red blood cells
can carry oxygen from the lung to the rest of body.

Animal

studies indicate that TCDD decreases the activity of an enzyme
known as uroporphyrinogen decarboxylase in the liver.

This

results in a decrease in the amount of heme synthesis and a
build-up of the chemicals from which heme is formed (porphyrins)
in the body.

As the porphyrin level builds up more porphyrins

are excreted in the urine.

A number of animal experiments

have shown that the pattern and amount of porphyrins excreted
in the urine changes after treatment with TCDD.

Two studies

of workmen exposed to dioxin have shown increased urinary excretion of porphyrins.

The Air Force study of personnel involved

in Operation Ranch Hand has also shown that there are more
men with abnormally high porphyrin levels in the exposed group
than in the comparison group although this finding correlates

22

�more strongly with alcohol use than it does with potential
exposure to Agent Orange.
Interference with porphyrin metabolism may result in a
condition known as porphyria cutanea tarda (PCT) in which the
skin blisters and later becomes dry and brittle particularly
upon exposure to sunlight. Workers who were exposed to dioxins
as a result of two industrial accidents developed this condition
and an unconfirmed report described a number of these cases
among residents of the Seveso area.
The available medical evidence indicates that there are
no lasting adverse health effects that result from alterations
in porphyrin metabolism. The body adjusts to manufacture sufficient heme to adequately supply the oxygen-carrying needs of
the body.

PCT is a relatively rare manifestation of changed

heme metabolism and may be caused by genetic factors and other
external factors, such as alcohol consumption, as well as by
dioxin exposure.

Also PCT is reversible and disappears after

exposure to dioxins ends.
Another enzyme activity for which there is indirect evidence
of interference by dioxins is the conversion and storage of
fats.

In many of the studies of workmen exposed to dioxins,

there were increased levels of fat molecules known as triglycerides in the blood, and these increases were detectable for
many years after exposure.

High levels of triglycerides in

the blood are thought to be associated with heart disease.
To date, there is no conclusive evidence of an association

23

�between heart disease and dioxin exposure but heart disease
would not be expected to appear until many years after exposure.
It appears that dioxins, though not the active herbicide
ingredients 2,4-D and 2,4,5-T, have the ability to alter the
functions of a number of enzymes.

At present none of these

alterations have been shown to be associated with any serious
irreversible adverse health effects in humans but any influence
that substantially alters the way the body handles internal
and external chemicals must be viewed with concern.
Effects on the Immune System
Unlike such well-studied and easily defined systems of
the body as the cardiovascular system and the digestive system,
the "immune system" is not easily defined and is currently
the subject of intensive research to better understand its
structure and function.

The immune system is a large array

of processes and mechanisms that serve to defend the body against
foreign chemicals, disease-causing bacteria, viruses, foreign
cells from outside the body, and abnormal cells from within
the body.

Various organs and tissues of the body participate

in these processes.

The lymphatic system, consisting of the

thymus, spleen, peripheral lymph nodes, lymph, blood, and cerebrospinal fluid, is the most important component of the immune
system, but cells essential to certain functions of the immune
system, are present in all the active tissues of the body.
Scientists have only recently begun to understand some
of the functions of the immune system.

24

Because of this lack

�of basic knowledge, it is difficult to assess the impact of
chemicals on the immune system.

One problem is the large number

of ways in which the immune system functions.

A chemical may

alter only a few of a score of general defense processes.
It may be necessary to run a dozen or so different types of
tests to detect these changes.

Only a few of these tests can

be done outside the body so it is especially difficult to study
altered immune function in humans.

Two additional factors

make it difficult to detect altered immune function in humans.
First, there are tremendous variations among people in the
capability of their immune systems.

A simple example of this

is the difference among people in their allergies.

Allergic

reactions are simply one of the many functions of the immune
systems.

Second, most activities of immune function have no

direct external manifestations. We usually cannot assess a
person's immune function by simple physical examination.

Altered

immune function in humans may only be reflected by subtle changes
in indirect indicators, such as increased susceptibility to
infections or increased sensitivity to materials that cause
allergic reactions.

One result of these problems is that it

is unlikely that effects of chemicals on the immune system
will be detected in humans exposed to those chemicals unless
they are looked for very carefully.
There is no evidence that 2,4-D or 2,4,5-T alter the immune
function of animals.

There are no studies of humans exposed

to Agent Orange or similar herbicides that show an adverse

25

�effect on the immune system.

However, no systematic studies

in which such effects were looked for have been reported.
There is considerable evidence, on the other hand, that
TCDD interferes with the functioning of the immune system in
experimental animals. When TCDD is given to experimental animals,
one of the most common effects is a decrease in the size of
the thymus, an organ that is involved in the immune system.
This effect occurs at doses lower than those that cause changes
in the weight or appearance of other organs.

At even lower

doses, TCDD interferes with the capability of the animal to
produce certain types of white blood cells in response to the
presence of foreign materials in the blood stream.

In some

studies, this effect is paralleled by decreased resistance
of animals to infection by bacteria and viruses.

It appears

that sensitivity to the immunosuppressive effects of TCDD is
greatest when the animals are still unborn and the TCDD is
given to pregnant mothers.

Sensitivity decreases in newborns

but sig nificant effects can still be seen in adult animals
treated with TCDD.

In fact, immune suppression is the most

sensitive indicator of TCDD exposure in mice, occurring at
doses below those that cause changes in enzyme activity.

Fur-

thermore, although immune function improves after exposure
ends, it remains relatively depressed for a very long time
in experimental animals.
i

Most studies of humans who have been exposed to dioxins
have not included tests of immune function. A study has been

26

�described of children who lived in the heavily contaminated
area of Seveso.

The results of this study showed that these

children had higher levels of certain immunologically active
components of the blood than did children from uncontaminated
areas.

Also the body produced more white blood cells in response

to certain foreign materials. These results suggest that exposure to dioxins stimulated immune function in these children
rather than depressing it, as in the animal experiments.

This

finding is not inconsistent, however, with experimental findings
that some chemicals which depress immune function at high doses
may actually stimulate immune functions at low doses.
Another study of workers exposed to dioxin as the result
of an industrial accident has been reported to have shown decreased
immune function in the exposed workers ten years after the
accident, but this study has not been published and cannot
be independently reviewed.

Two other studies of workers exposed

to dioxins in industrial settings have shown decreased resistance
to infection among the exposed workers.

These results, taken

together, fall far short of providing convincing evidence that
dioxin exposure can cause impaired immune function in humans.
Nevertheless, the overwhelmingly positive evidence of such
effects in experimental animals provides some basis for concern
that exposure to dioxin may alter immune function in humans.

Chloracne
Chloracne is a skin condition that is known to result
from exposure to a group of structurally similar compounds

27

�whose common feature is several atoms of chlorine bound to
an aromatic hydrocarbon structure.
is TCDD.

One of these compounds

Chloracne, as its name suggests, is a skin condition

that, in most cases, appears to be very similar to the common
acne that affects most teenagers.

It commonly appears several

weeks after exposure to the chemical that causes it.

The first

sign of chloracne may be excessive oiliness of the skin.

This

is accompanied or followed by the appearance of numerous blackheads.

In mild cases these blackheads may by confined to the

area around the eyes extending along the temples to the ears.
In more severe cases blackheads may break out all over the
body.

In many cases the blackheads may be accompanied by pus-

filled cysts and by an increased and/or darker growth of body
hair.

The skin may become thicker and flake or peel.

In severe

cases, the acne may result in opens sores and permanent scars.
The condition fades slowly after exposure.

Minor cases may

disappear altogether, severe cases will persist years after
the exposure.
There can be little doubt that chloracne results from
exposure to dioxins.

In seven situations where workers were

exposed to dioxins as a result of industrial accidents or poor
housekeeping practices many of the workers developed chloracne.
Chloracne was also diagnosed in 187 people, mostly children,
living in the section of Seveso that was most heavily contaminated with TCDD as a result of the ICMESA accident in 1976.

28

�Two laboratory workers who were exposed during the synthesis
of TCDD developed serious cases of chloracne.
There are no authoritative reports in the literature that
document an association between exposure to Agent Orange or
similar herbicides and chloracne.

The Air Force study of Ranch

Hand personnel showed no excess of acne or other skin conditions
in those individuals when compared to unexposed controls.
Most of the epidemiologic studies of occupational groups involved
in the spraying of herbicides like Agent Orange are silent
on whether or not chloracne was present among the workers who
were studied.

A single report on cancer among herbicide sprayers

in Finland indicated that a nationwide effort turned up "a
few cases of possible chloracne".

One of these cases was diag-

nosed as chloracne by a physician specializing in skin disorders.
On the basis of this isolated report&gt; it would appear that
chloracne is not a sensitive indicator of exposure to herbicides
like Agent Orange.
Animal studies are of little use in studying the potential
of Agent Orange to cause chloacne in humans.

The ingredients

2,4-D and 2,4,5-T have not been extensively tested but it appears
that they do not cause chloracne or similar skin conditions
in experimental animals.
differently to TCDD.

Different kinds of animals react

TCDD causes skin conditions very similar

to chloracne when applied to the ears of rabbits and to the
skin of certain types of mice.

Scientists disagree, however,

as to whether these skin effects are identical to human chlor-

29

�acne.

Some types of experimental animals fail to show any

acne-like condition when treated with TCDD.

Only monkeys appear

to develop a condition that is indistinguishable from human
chloracne when they are exposed to TCDD.
One conclusion that is gaining support on the basis of
both animal and human studies is that susceptibility to chloracne may be genetically controlled.

Two individuals equally

exposed to TCDD may respond differently because of differences
in inherited susceptibility.

This would explain why some of

the workers exposed to dioxins in each of the seven industrial
incidents did not have chloracne even though there is no reason
to believe that they were less exposed than workers who did
get chloracne.

Thus, whereas chloracne may be a sensitive

indicator of exposure to dioxins and mixtures containing dioxins
in some people, it may not be in others.

The absence of chlor-

acne is not a reliable basis for concluding that someone was
not exposed.
Neurobehavioral Effects
It has been known for some time that exposure to relatively
large amounts of 2,4-D (one of the herbicides in Agent Orange),
such as might occur when it is being mixed or sprayed, can
cause adverse effects on the nervous systems.

Workmen who

splashed 2,4-D on their skin or who stood for a long time in
2,4-D spray mist developed a variety of symptoms including
loss of feeling or tingling in the hands and feet and tightening
of muscles in the arms and legs.

30

Examination of these workmen

�showed the loss of a reflex leg jerk when tapped below the
knee and an increase in the amount of time that it takes for
nerve impulses to travel from the hands or feet to the spinal
column and back.

Studies in experimental animals give similar

results to those seen in humans.

These studies suggest that

2,4-D interferes with the transmission of messages from the
nerves to the muscles.
nervous system recovers.

If the exposure is not too great the
However, sustained exposure of experi-

mental animals to relatively large quantities of 2,4-D may
cause long-lasting changes in the brain and spinal cord itself.
A few studies of humans and experimental animals exposed
to the other herbicide in Agent Orange, i.e. 2,4,5-T, have
failed to show any nervous system effects such as those caused
by 2,4-D.

There is some evidence, however, that humans exposed

to dioxins as a result of industrial exposures or accidents
may suffer impaired nervous system function.

A wide range of

signs and symptoms have been reported in these people including
pain in the arms and legs, loss of feeling in the hands and
feet, muscular weakness (particulary in the legs), headache,
loss of memory and concentration, sleep disturbances, nervousness, and emotional and psychiatric abnormalities.

Measurement

of the speed that nerve messages are transmitted showed that
this speed was slowed down in two groups of workers who were
probably exposed to dioxins.
There have been very few studies of the effects of TCDD
or other dioxins on the nervous system in animals.

31

It is not

�clear why this knowledge gap exists, but one possible explanation is that the doses of TCDD needed to cause notable signs
of nervous system damage in experimental animals are higher
than those that cause other serious toxic effects.

Therefore,

scientists have tended to concentrate on the other effects.
The issue as to whether nervous system and psychological
effects have been seen in individuals exposed to Agent Orange
as a result of the Vietnam experience is unclear and controversial.

There is little question that Vietnam veterans experience

a high rate of psychological problems with certain symptoms
appearing with great frequency.

These symptoms include nervous-

ness, disturbed sleep, irritability and short temper, depression,
and suicidal thoughts.

Many psychiatrists consider that some

of these comprise a distinct collection of symptoms or a syndrome
known as post-traumatic stress disorder and that this syndrome
is unrelated to any chemical exposure.

The only evidence in

support of this conclusion is that individuals such as prisoners
of war and hostages who have undergone sustained stress display
similar symptoms.

This does not rule out the possibility that

Agent Orange or dioxin exposure might cause or exacerbate the
condition.

Unfortunately, there are almost no systematic studies

of nervous system function or psychological symptoms among
individuals exposed to Agent Orange.

A recent Air Force study

Df Operation Ranch Hand personnel showed no difference between
Xanch Hand personnel and unexposed controls in terms of several
neasurements of nervous system function including the speed

32

�of transmission of messages along nerves.

On the other hand,

when Ranch Hand personnel were evaluated by analyzing

answers

to questions on tests designed to indicate personality traits,
psychiatrists concluded that these individuals were different
from the comparison group and showed tendencies toward traits
defined as "hypochondria, depression, hysteria, and schizophrenia."
Ranch Hand personnel were also said to feel more isolated and
to have a higher degree of nervousness and anxiety, to be more
easily startled, and to experience more psychosomatic illness
than did the comparison group.

These differences were minor

and are difficult to interpret because the diagnoses were subjective.

The methods used in this study would not show whether

the differences between groups were due to post-traumatic stress,
Agent Orange exposure, or both.
That self-perception of psychological

problems is an impor-

tant component of such an analysis was shown in a study of
100 veterans who were asked about their exposure to Agent Orange
and their current mental and emotional well-being.

Their poten-

tial exposure to Agent Orange was independently assessed by
comparing their service records with records of the timing
and location of herbicide spraying missions in Vietnam.

The

frequency and seriousness of psychological and emotional problems
correlated very closely to how much herbicide the veterans
believed they were exposed to whereas the correlation was much
weaker when the comparison was to how much herbicide exposure
the records showed.

�The issue of the effects of Agent Orange on nervous system
and psychological performance is probably the most difficult
health issue to resolve.

There is a great deal of human and

animal evidence that both 2,4-D and TCDD can adversely affect
the nervous system.

All of this evidence suggests that these

effects are the result of short-term high level exposure rather
than the sustained exposure to lesser amounts.

Clearly more

studies are needed, but, because of the uncertainty regarding
the validity of testing methods and the determination of the
extent of exposure, it is unlikely that future studies will
provide definitive results.
Other Toxic Effects
Studies of people exposed to Agent Orange or similar herbicide mixtures have failed to reveal any significant toxic effect
other than those discussed above.
attributed to TCDD, however.

Other effects have been

As was mentioned briefly in the

section on enzyme effects, there is suggestive evidence that
there is a higher incidence of heart attacks among workmen
exposed to dioxins in industrial accidents.

This evidence

is far from conclusive but it is sufficient justification to
continue to observe the health of people exposed to dioxin,
especially since it may take many years after exposure for
adverse effects on the heart to show up.
The most dramatic sign of fatal dioxin poisoning in experimental animals is an apparent loss of appetite which leads
to a general wasting of the body.

34

The animals eventually die

�of a condition that is very similar to starvation.

This effect

is the result of large single doses of TCDD and no similar
effect has been described in humans so it may be of little
relevance to human health.

The mechanism by which TCDD causes

this apparent loss of appetite is unknown and is the objective
of much current research.

Some results suggest that TCDD may

interfere with an appetite regulating system in the brain or
thyroid.

This "appetite regulating system" may have other

less dramatic functions in controlling bodily processes and
these may be of great importance to human health.

There is

much to be learned in this area.
Animal studies have suggested another aspect of the toxicity
of TCDD which may have important implications for human health.
It has become increasingly clear that some animals are relatively
resistant to some of the toxic effects of TCDD compared to
other animals.

Recent research has shown that this difference

in susceptibility is genetically controlled and that mice with
one parent in common can show large differences in susceptibility
to the toxic effects of TCDD.

The effects for which susceptibil-

ity appears to be genetically controlled include the appearance
of birth defects in the offspring of female mice exposed to
TCDD, the increased activity of several enzymes including AHH
and uroporphyrinogen decarboxylase, depression of immune function, chloracne, and the lethal effects of TCDD.

This suggests

that among humans (who are genetically very diverse compared
to experimental animals) there may be a whole range of suscepti-

35

�bility to the toxic effects of TCDD.

This may explain why

many workmen who were exposed to dioxin in industrial accidents
never developed chloracne.

This diversity of susceptibility

is something of a good news/bad news situation.

The good news

is that many humans may be relatively resistant to the adverse
effects of dioxins.

The bad news is that the presence of resist-

ant individuals in a group of people exposed to dioxins who
are being studied for health effects may mask the occurrence
of severe health effects among a relatively few susceptible
individuals within that group.

This will increase the difficulty

of discovering the adverse health effects of dioxins by studying
exposed human populations.
Summary and Conclusions
What can we say about the health effects of Agent Orange?
Based on the evidence that is available at the present time
we can arrive at almost no definitive conclusions.

The limited

evidence available suggests that 2,4-D and 2,4,5-T by themselves
are not highly toxic to humans.

2,4-D appears to be capable

of causing nervous system toxicity but only in situations where
there is very high-level exposure.

2,4,5-T may contribute

to birth defects when pregnant females are exposed.

There

is no evidence that purified 2,4-D or 2,4,5-T cause cancer,
change the activity of enzymes, affect the immune system, or
cause chloracne or PCT in humans.

The evidence is quite good

that the presence of highly toxic dioxin impurities, especially
TCDD, may determine the adverse human health effects of Agent

36

�Orange and similar herbicide mixtures.

There is very little

direct evidence that Agent Orange causes adverse health effects
in humans, but this may be the result of our inabili-ty to identify
groups of people with well-defined exposure and to study them
properly.

The limited evidence available comes from studies

of humans exposed to Agent Orange and similar herbicides, from
studies of humans exposed to dioxins, and from studies of dioxins
in experimental animals.

These studies provide some support

for the possibility, but do not prove that exposure to dioxincontaminated herbicides causes adverse health effects.

These

adverse effects include cancer at several different sites (not
limited to soft-tissue sarcoma), spontaneous abortion, certain
birth defects, altered enzyme activity, altered porphyrin metabolism, and altered (probably depressed) immune function.

Effects

for which the available evidence is very inconclusive but which
should be the object of further study are neurobehavioral effects
(including psychological effects) and heart disease.

Chloracne

does not seem to be of significant importance except in situations where there has been heavy exposure to herbicides heavily
contaminated with dioxins.

Scientists should abandon the posi-

tion that the presence of chloracne is a sensitive indicator
of exposure to dioxin and dioxin contaminated herbicides.
What will future studies tell us about the health effects
of exposure to Agent Orange?

Studies that are planned or in

progress have the potential to reduce a lot of the uncertainty
regarding the health effects of exposure to Agent Orange.

37

�Because of insurmountable problems in determining the exact
amount and nature of exposure and in selecting appropriate
exposed and unexposed groups to study, however, these studies
will never be able to conclusively demonstrate the absence
of a toxic effect. The areas in which future studies can provide
the most information are in the study of delayed effects of
exposure such as cancer and heart disease.
Studies in experimental animals can still be helpful in
elucidating the possible adverse effects of Agent Orange.
Particularly helpful would be studies of the purified components
of Agent Orange separately and in known combinations. Other
important areas of investigation include effects on immune
function and the genetic control of susceptibility to the toxic
effects of dioxin.
In the meantime, exposed individuals can achieve some
degree of reassurance from the fact that despite their inadequacies,
the studies which have been completed to date have revealed
no widespread or major adverse health effects among the people
who were exposed except for possible psychological effects.
There is no evidence that the psychological disturbances seen
in Vietnam veterans are the result of exposure to Agent Orange.
It is unlikely that the adverse health risks associated with
exposure to Agent Orange in Vietnam are nearly as widespread
as the adverse effects from smoking or chronic alcohol use.
For many of the potential health effects, there is little probability that they will first appear years after exposure.

38

�These include reproductive effects, enzyme effects, chloracne,
and neurobehavioral effects.

It is possible that cancer, immune

deficiencies, and heart disease may first appear years after
exposure.

Heart disease can be detected early, and changes

in life style can dramatically alter the risks of this disease.
Furthermore, factors such as smoking, stress, and lack of exercise
are much more likely to play a major role in heart disease,
and possibly cancer, than is exposure to dioxin.

Persons exposed

to Agent Orange should take no exceptional precautions beyond
those that are prudent for everyone, i.e., consume a balanced
diet, exercise regularly, have regular medical check-ups, be
alert for tell-tale signs of cancer, abstain from smoking,
and use alcohol moderately.

39

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