Report from the Sub-comittee on the environment and health
Report from the Sub-comittee on the environment and health
Report from the Sub-comittee on the environment and health
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Relati<strong>on</strong>ship between<br />
pesticides <strong>and</strong> cancer not<br />
documented<br />
Horm<strong>on</strong>al toxicity<br />
Developmental toxicity<br />
though <str<strong>on</strong>g>the</str<strong>on</strong>g> exposure to DDT was c<strong>on</strong>siderably greater (Krieger et al.<br />
1994). A third major American study was unable to establish any<br />
relati<strong>on</strong>ship between <str<strong>on</strong>g>the</str<strong>on</strong>g> blood c<strong>on</strong>tent of organochlorine compounds <strong>and</strong><br />
<str<strong>on</strong>g>the</str<strong>on</strong>g> risk of breast cancer. However, <str<strong>on</strong>g>the</str<strong>on</strong>g> follow-up period was short, <strong>and</strong><br />
problems with c<strong>on</strong>founder correcti<strong>on</strong> resulted in statistical weakness<br />
(Hunter et al. 1997). Lastly, a recently published Danish study showed a<br />
statistically significant dose-related correlati<strong>on</strong> between <str<strong>on</strong>g>the</str<strong>on</strong>g> blood<br />
c<strong>on</strong>tent of dieldrin <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> risk of breast cancer (Høyer et al. 1998). The<br />
o<str<strong>on</strong>g>the</str<strong>on</strong>g>r relati<strong>on</strong>ships between risk of cancer <strong>and</strong> blood c<strong>on</strong>tent of betahexachlorocyclohexane,<br />
DDT <strong>and</strong> PCB were not statistically significant.<br />
As <str<strong>on</strong>g>the</str<strong>on</strong>g> results of <str<strong>on</strong>g>the</str<strong>on</strong>g> above-menti<strong>on</strong>ed epidemiological studies indicate,<br />
<str<strong>on</strong>g>the</str<strong>on</strong>g>re are data that show that exposure to organochlorine compounds can<br />
be c<strong>on</strong>nected with an increased risk of breast cancer, although without<br />
sufficient, clear grounds to deduce <str<strong>on</strong>g>the</str<strong>on</strong>g> significance for <str<strong>on</strong>g>the</str<strong>on</strong>g> general<br />
populati<strong>on</strong>. A scientific panel appointed by <str<strong>on</strong>g>the</str<strong>on</strong>g> Nati<strong>on</strong>al Cancer Institute<br />
of Canada came to a similar c<strong>on</strong>clusi<strong>on</strong> in a review of studies of mainly<br />
occupati<strong>on</strong>al exposure <strong>and</strong> risk of cancer (Ritter 1997). The panel<br />
c<strong>on</strong>cluded that <str<strong>on</strong>g>the</str<strong>on</strong>g>re was insufficient scientific evidence that pesticides<br />
c<strong>on</strong>tributed significantly to total cancer mortality.<br />
It is well documented that a number of persistent chemicals can affect <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
endocrine system by affecting <str<strong>on</strong>g>the</str<strong>on</strong>g> horm<strong>on</strong>es in <str<strong>on</strong>g>the</str<strong>on</strong>g> body that are<br />
resp<strong>on</strong>sible for maintaining homeostasis <strong>and</strong> regulating <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
developmental processes (Gray, Ostby 1998; Kavlock et al. 1996; Tils<strong>on</strong>,<br />
Kavlock 1997; Porter et al. 1993). Endocrine disruptors have been<br />
broadly defined as exogenous substances that disrupt producti<strong>on</strong>, release,<br />
transport, metabolism, sorpti<strong>on</strong>, acti<strong>on</strong> or eliminati<strong>on</strong> of <str<strong>on</strong>g>the</str<strong>on</strong>g> body’s<br />
natural horm<strong>on</strong>es (Kavlock et al. 1996; Tils<strong>on</strong>, Kavlock 1997). Some of<br />
<str<strong>on</strong>g>the</str<strong>on</strong>g>se substances can induce <str<strong>on</strong>g>the</str<strong>on</strong>g> cytochromal P450 systems in <str<strong>on</strong>g>the</str<strong>on</strong>g> liver.<br />
This can affect <str<strong>on</strong>g>the</str<strong>on</strong>g> metabolism of steroid horm<strong>on</strong>es (including sex<br />
horm<strong>on</strong>es) <strong>and</strong> thyroid horm<strong>on</strong>es, whereby sec<strong>on</strong>dary effects can be<br />
induced in horm<strong>on</strong>e-dependent organs.<br />
However, too little is known about endocrine disruptors, <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
designati<strong>on</strong> has in some cases been used where <str<strong>on</strong>g>the</str<strong>on</strong>g> biological<br />
relati<strong>on</strong>ship is far <str<strong>on</strong>g>from</str<strong>on</strong>g> clarified. The suspici<strong>on</strong> about <str<strong>on</strong>g>the</str<strong>on</strong>g> very persistent<br />
substances DDT, DDE <strong>and</strong> PCB is warranted in view of <str<strong>on</strong>g>the</str<strong>on</strong>g> effects <str<strong>on</strong>g>the</str<strong>on</strong>g>se<br />
substances have <strong>on</strong> wild animals (e.g. seals, otters <strong>and</strong> alligators). For <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
endocrine disruptors, too, <str<strong>on</strong>g>the</str<strong>on</strong>g>re are problems in extrapolating <str<strong>on</strong>g>from</str<strong>on</strong>g><br />
studies of test animals with relatively high exposures to <str<strong>on</strong>g>the</str<strong>on</strong>g> relatively low<br />
exposures that occur in <str<strong>on</strong>g>the</str<strong>on</strong>g> envir<strong>on</strong>ment <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> very small amounts that<br />
humans are exposed to. These endocrine disrupti<strong>on</strong>s cannot be<br />
dem<strong>on</strong>strated in present test systems, but work is going <strong>on</strong> under OECD<br />
to improve <str<strong>on</strong>g>the</str<strong>on</strong>g> test programme for new chemicals, so that animal tests<br />
are better able to document such effects.<br />
Developmental effects are effects that occur in <str<strong>on</strong>g>the</str<strong>on</strong>g> individual during<br />
development as a result of exposure prior to c<strong>on</strong>cepti<strong>on</strong>, in <str<strong>on</strong>g>the</str<strong>on</strong>g> foetal<br />
existence or postnatally until <str<strong>on</strong>g>the</str<strong>on</strong>g> individual is fully developed. The result<br />
of <str<strong>on</strong>g>the</str<strong>on</strong>g> developmental disturbances can be death, structural abnormalities,<br />
inhibited growth or functi<strong>on</strong>al disturbances. However, it is often difficult<br />
to determine whe<str<strong>on</strong>g>the</str<strong>on</strong>g>r miscarriage or stillbirth is due to reproductive or<br />
developmental effects.<br />
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