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Joint International Conference on Long-term Experiments ...

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trigger still other resp<strong>on</strong>ses. In this way, the animal may eventually reach some state of<br />

equilibrium but in the presence of a changed biochemical milieu.<br />

If, now, we c<strong>on</strong>tinue treating this animal with the 100 % blocking dose for most of its<br />

natural life span, we can expect this changed biochemical milieu to be reflected in the<br />

patterns of lesi<strong>on</strong>s that are associated with the aging process. Thus, the treated animals will<br />

tend to have a different syndrome of chr<strong>on</strong>ic lesi<strong>on</strong>s than untreated c<strong>on</strong>trols. If the strains of<br />

rat or mouse chosen are pr<strong>on</strong>e to tumor, untreated, then we can expect that this shift in<br />

senile lesi<strong>on</strong>s will involve a shift in neoplastic lesi<strong>on</strong>s.<br />

Suppose we used some other drug, like e calcium channel blocker, or a m<strong>on</strong>oamine<br />

oxidase (MAO) inhibitor, or any other drug at a dose sufficiently high to produce a<br />

sustained biological effect. The same argument holds, that the resulting change in<br />

biochemical milieu will produce a shift in senile lesi<strong>on</strong>s (including tumor patterns).<br />

Suppose, instead of a drug, we use an insecticide, or a dye precursor, or any other agent, but<br />

at a dose sufficiently high ti produce a discernible biological effect (like a 10 % reducti<strong>on</strong> in<br />

weight). The same argument holds.<br />

Thus, we can expect, just from the design of these studies, that the “carcinogenesis”<br />

bioassay will show a treatment-related shift in neoplastic lesi<strong>on</strong>s for every compound tested.<br />

MATERIALS AND METHOD<br />

A. Using Data from the “Carcinogenesis”Bioassay<br />

The standard statistical analyses of the “carcinogenesis” bioassay require that we compare<br />

counts of animals with specific tumor types between treatment groups. As a result, the<br />

unsual NTP study involves formal hypothesis tests comparing tumor incidences for 10-15<br />

tumor types, each comparis<strong>on</strong> involving a test of c<strong>on</strong>trols versus low dose; c<strong>on</strong>trols versus<br />

high dose; two dose-resp<strong>on</strong>se tests, adjusted for early deaths; and n<strong>on</strong>linearity hypothesis<br />

tests per sex per species.<br />

The problem of multiple testing and inflati<strong>on</strong> of the false-positive error rate has had<br />

c<strong>on</strong>siderable discussi<strong>on</strong> in the literature. However, there is another side of the problem, the<br />

false-negative error rate. There are <strong>on</strong>ly 50 animals per treatment, sex, species, and a<br />

statistical test that compares the number of animals with the a given lesi<strong>on</strong> cannot detect a<br />

slight shift in the probability of lesi<strong>on</strong>. For instance, if the background incidence of a<br />

particular tumor is 20 % and if the treatment reduces that to 7%, half of the studies would<br />

show a “significant” difference and half would not. Thus, the failure to show “significant”<br />

differences between treatments and c<strong>on</strong>trols for some of the compounds that have been<br />

tested is no proof that there was no effect. In fact, a rather dramatic increase or reducti<strong>on</strong> in<br />

a particular tumor type could have occurred without producing a “significant” result.<br />

There are ways of strengthening the power of statistical hypothesis tests. One way is to<br />

allow each animal to provide more informati<strong>on</strong>. When we compare the counts of animals<br />

with a specific tumor type, each animal provides <strong>on</strong>ly 0 or a 1, the least amount of<br />

informati<strong>on</strong> available from a single experimental unit. The fact that we look at several<br />

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