Philip Morris
Do Rodent Studies Predict Human Cancers?
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- Wildavsky, A.
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- E12
- Document File
- 2502145956/2502146352/Thresholds 4
- Master ID
- 2502146051/6295
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- Ames, B.
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- Crisp, P.F.
- Doll
- Doull, J.
- Ellwein
- Fears
- Freedman
- Gladwell, M.
- Gold, L.
- Gough, M.
- Griesemer, R.A.
- Harris, R.
- Krewski, D.
- Lave, L.
- Levenson, L.
- Markov
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- Peto, R.
- Salzburg
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- Train, R.
- Weibull
- Zeisel
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- Congress
- Division of Toxicological Research + Tes
- Epa, Environmental Protection Agency
- Executive Office of the President
- FDA, Food and Drug Administration
- Food Safety Council
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- Nas, Natl Academy of Sciences
- Natl Inst of Environmental Health
- Natl Public Radio
- Office of Technology Assessment
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Document Images
DO RODENT STUDIES PREDICT HUMAN CANCERS?
by
Aaron Wildavsky
Why does it matter if animal cancer studies are worthwhile or
worthless or someplace in between? The answer to this question is
that regulation of exposure to chemicals, including the intermittent
exposures to trace elements to which the general pubic is subject, are
largely based on interpretations of animal-cancer bioassays. If these
tests are reasonably accurate in predicting the probability, sites, and
severity of human cancers, then regulation of chemicals suspected of
causing cancer (carcinogens) is on firm ground. But if these animal
cancer tests are weak or worse, so that one cannot reasonably predict
human cancers from them, then regulation rests on quicksand. .
Whether or not rodent tests predict human cancers, animal
studies have many other important uses. Research into cancer
mechanisms or problems of the immune system, for instance, may be
furthered by introducing novel genes into small animals, such as
transgenic mice, to discover better how life systems work.1 There is
no doubt that models based on research with animals have increased
our understanding of metastasis, which is so important in the spread
of cancer.2 None of the many invaluable uses of animal cancer tests,
however, tells us whether they can come close enough often enough
to be a valid source of evidence in predicting human cancer.
I

The Right Ouestions
We would like to know how much damage to human
populations is caused by different types and quantities of exposure
to various substances. That estimate requires answering
subquestions about conditions. Routes of exposure may differ in that
some come from breathing, others from eating, still others, like x-
rays, through the skin, from natural sources and medical uses.
Quantities may differ from a little to a lot to immense. Timing differs
from exposure all at once or over periods of time. If a precise
answer to the question of adverse effects cannot be given, we might
be satisfied with knowing that there is a great deal of harm or
moderate or very little or probably none.3
How reliable are these tests? If the tests were repeated on the
same species, would we get nearly the same results? If they were
repeated on different animal species, would we come up with similar
results? If chemicals are carcinogenic in several animal species, it is
more likely that they are carcinogenic to mammals in general,
including human beings, than if they cause cancer in a single species.
It is also important to distinguish rates and sites of cancer by age,
because cancer is largely though not entirely a disease of old age, and
by sex, because men and women are affected differently. Dioxin in
large and continuous doses appears unfriendly to mammals but it is
the dose that matters.

3
Regulatory agencies assume that chemicals carcinogenic at
some dose in any animal are also carcinogenic to human beings. We
want to find out if that assumption is true.
As precisely as possible, we wish to answer Freedman and
Zeisel's question, "Are chemicals that have been shown to be
carcinogenic through experimental animals also carcinogenic to
humans?"4 The reason for their inclusion of the modifier
"experimental animals" has to do with the particular conditions
under which animals are tested_ Therefore they also ask, "Do
experimental animals (rodents, in particular) and humans have
similar susceptibility to the carcinogenic effect of chemicals, or are
rodents incomparably more susceptible than humans?"5
The answer to the first question is "sometimes" rodent cancers
are cancers in humans too, but we do not know when_ The same is
true of one type of rodent to another. The answer to the second
question is "yes, mostly, but not always." If we know that a single
dose LD50 for dioxin ranges from 2500 ug/kg in guinea pigs to 5000
in hamsters, a difference of 2500, does that give us confidence about
rodent to human transfers?
Suppose that we arrive at several different answers: one is
that there is a ten percent probability that a substance causing
cancer in a mouse or rate at a given dose will do the same in a
human being. From one point of view, nine times out of ten the
extrapolation from mouse to man would be wrong. From another
point of view, why take chances with human health if the probability
of getting a cancer is that high? Were we to find, however, that
when we get the answers from the tests we would know within a
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factor of several hundred times to several hundred thousand times
whether rodents predict to humans, that might not be a reasonable
approximation. The question is not only whether we can get an
answer but what kind of answer we will get.
The Process of Animal Cancer Testing
Around 1915 or 1916 scientists learned that they could induce
cancer in animals by treating them with certain chemicals. The
methods of giving animals cancer vary greatly. "Chemicals have
been introduced into experimental animals by every orifice (orally,
nasally, urethrally, vaginally, rectally), by various types of injections
(intramuscular, intraperitoneal, intravenous, subcutaneous), by skin
painting, by surgery, and by other methods.6
Approximately 30 percent of the rodents get some form of
cancer absent exposure to chemicals, though all 30 percent to do not
die of it. This is one reason why a control group is essential. Because
a chemical's effects at high doses may not show up at low doses, it is
necessary to further subdivide the animals into different dose
groups. Given that sex plays an important role in cancer, a further
subdivision is between male and female. Usually there are three
dose groups (0, half or one-tenth the MTD, MTD) and two species.
There are at least twelve groups of animals. By convention and by
statistical necessity, there are usually fifty animals, most often
rodents, in each group.
Though only a few facts about the process of animal cancer
testing have been given, we are already in a position to understand

5
three of its most basic aspects--its short time compared to human
epidemiological studies, its high cost, and its essentially statistical
character. A great advantage of rodent testing is that these animals
live only about two years. Therefore one doesn't have to wait too
long to get results. One can also test any chemical, including new
chemicals, for which epidemiological evidence may not be available.
But the task is not easy or cheap. It is costly to keep these animals
under controlled conditions for up to two years. The painstaking
work of examining animals for tumors requires pathologists. When
each animal dies or, as the too-kindly parlance states, is sacrificed,
several pathologists must carefully examine around forty sites
around and about animal organs and tissues to search for tumors,
some of which are so small they can be discerned only with high-
powered microscopes.
That is why there is a team of pathologists who first work
separately and then meet to resolve differences before their findings
are accepted for further evaluation.7 These pathologists consider,
whether the tumors or other abnormalities are actually induced by
the chemical, an opinion based on what they know about the normal
incidence of tumors and their experience. They ask themselves not
only whether the incidence of tumors is higher but whether they are
of a different size or shape or color or contain any other signs that
might show them to be similar to or different from naturally
occurring lesions.8
In order to understand better whether the proper dose was
administered, the animals have to be weighed to discern whether
they have lost appropriate amounts of weight and examined to see

whether the dose is either so large as to threaten their lives from
causes other than cancer or so small as to make its effects
unnoticeable.
Now we are in a position to understand why rodent-cancer
tests are so expensive. When one multiplies the time these tests
take, roughly three years, times the cost of keeping twelve groups of
animals in controlled conditions, and adds the cost of killing and
dissecting them as well as the cost of preparing and examining forty
slides per animal, and of reconciling differences, the substantial costs
do not appear out of Iine.g
It is possible for a government regulator to conclude that the
tests are inadequate or that the substance being tested is actually a
carcinogen. But it is not possible under the rules to say that the
substance is not, insofar as is known, a carcinogen. Instead, the
closest government scientists are allowed to come is to say that "the
compound has not been shown to be carcinogenic."1o
What, we may ask, is the meaning of classifying a substance as
a suspected carcinogen? It is worth attending closely to Chu and his
colleagues' discussion:
If malignant tumors or a combination of malignant and benign
tumors are produced, then the compound is considered
carcinogenic to the animals. If the significant result is only the
production of benign tumors, then the compound may pose a
potential health hazard and is termed a suspected carcinogen
or a carcinogen, depending on the nature of the benign tumor.
For example, 2,4-dinitrotoluence . . . was considered a

7
suspected carcinogen since it induced only benign tumors
(fibromas of the skin and subcutaneous tissue in male Fischer
344 rats and fibroadenomas of the mammary gland in
females)_ Ideally, a distinction should be made between truly
benign tumors, which never progress to malignancy, and
tumors that are in a benign state according to histopathologic
criteria at the time of diagnosis. Scientific judgments in this
area are limited by inability to predict the biological behavior
of a lesion on the basis of morphological criteria, but it appears
that there are few, if any, truly benign tumors in rodents.1 1
The two sentences are telling. The "it appears" reflects a judgment
that any tumor might turn bad; the "if this were true" suggests that
this assumption lacks credibility. Is it in the interests of public
safety to treat all tumors, however benign in appearance, as if they
might turn malignant, because we do not know they won't? Or is this
"might turn malignant" a way of prejudicing the outcome so the -
chemicals will be found to induce cancers whether they do or don't?
In the EPA's 1976 "Interim Procedures and Guidelines for
Health Assessments of Suspected Carcinogens," EPA Administrator
Russell Train acknowledged that animal tests could not prove that a
chemical would be carcinogenic in people, but that a substance would
be considered a "presumptive cancer risk" if it "causes a statistically
significant excess incidence of benign or malignant tumors in humans
or animals."12 If benign is bad, what could be good?
Calculating Toxicity by the LDSp Test
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In the field of pesticide regulation, lethality is calculated
through the assignment of an LD50, the lethal dose for one-half of
the test animals during the test period_ The relevant number for
aspirin would be 730mg/kg, signifying that 50 percent of the test
animals died when exposed to 730 mg of aspirin per kilogram of
their body weight.13 The larger the LD50, the more of a substance it
takes to produce a toxic effect, the less harmful the chemical.
Among species most commonly used to carry out the LD50 test
are fish, birds, rabbits, mice, and rats, although occasionally monkeys
and dogs are used. Generally, about 60 animals of a particular
species and a specific dosing method are used. The application is
made by inserting a tube down the throat of the animal, by forcing
injection of vapors, or by application to the skin.14 The usual test
lasts about two weeks, during which the animals either die or, at the
end, are killed off. The usual symptoms are bleeding from the mouth
or eyes, convulsions, diarrhea, and what are exquisitely termed .
"unusuat vocalizations." Rather than tolerate early death, according
to the British Toxicological Society, "There is pressure on the
toxicologists to allow the study to continue, even when the animals
are in distress since their premature killing may alter the end-point
of the study, and so possibly affect the classification of the material
being tested."15 Needless to say, animal rights advocates are not
happy with this method. Whether one believes that the LD50 test
involves "a ritual mass execution of animals"16 or that "the main
information they give is an indication of the size of dose required to
commit suicide,"17 or even whether most experts consider "the

9
modern toxicological routine procedure a wasteful endeavor in which
scientific inventiveness and commonsense have been replaced by a
thoughtless completion of standard protocols,"t$ there is ample
scientific doubt about the value of the LD50 test for the purpose of
predicting human effects.19 The basic difficulty is that enormous
differences between different (even from closely related) species are
reported, ranging from 5 to 75 times, which renders findings
suspect_ZO If LD50 tests are useful in providing evidence to save
human life from suffering, there would still have to be a debate over
whether the animal suffering entailed can be justified. If, however,
the observations are too unreliable to be useful, no such question
arises.
Toxicity
The best explanation for laymen I have heard of the difference
with which we have been concerned--between very large and very
small exposures to different kinds of species--comes from reporter
Richard Harris of National Public Radio, together with a number of
cancer researchers and government officials. Their dialogue is
instructive:
Penelope Fenner Crisp (Environmental Protection Agency):
We're coming to discover that there are more differences
between species than we had expected or, frankly, hoped that
existed.

1
Harris: It turns out that a great many chemicals that can cause
cancer in one species don't seem to do anything at all in
another species. Here's an analogy.
(Excerpt from music from a CD)
Harris: The difference between rodents and people can be as
dramatic as the difference between this CD and an LP. You
could drop this CD, get it dusty, even scratch it, and you
wouldn't necessarily hurt it.
(Sound of record being scratched by a stereo needle and music
played from an LP)
Harris: By try the same thing with a record, and you can just
hear the damage. To be sure, some things will damage either a
CD or a record album--say, a hot windowsill. Likewise, John
Doull from the University of Kansas says some chemicals do
cause cancer in all sorts of animals ...
Now nobody's suggesting that these chemicals are harmless,
but in some cases scientists believe that the standards may be
vastly overstating the health risks. Again, this comes down to
a necessary but flawed shortcut the EPA uses to size up a
chemical. Scientists give a huge dose of chemicals to rats and
then estimate the effects of that chemical at lower doses. By
