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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Pesticides <strong>and</strong> cancer<br />
96<br />
<str<strong>on</strong>g>the</str<strong>on</strong>g> so-called re-entry time. During <str<strong>on</strong>g>the</str<strong>on</strong>g> work, <str<strong>on</strong>g>the</str<strong>on</strong>g> amount of pesticides<br />
<strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> area of leaves touched by <str<strong>on</strong>g>the</str<strong>on</strong>g> nurseryman during a working day<br />
are of critical importance. Important factors include <str<strong>on</strong>g>the</str<strong>on</strong>g> length of <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
working day <strong>and</strong> <str<strong>on</strong>g>the</str<strong>on</strong>g> substance’s degradati<strong>on</strong>, evaporati<strong>on</strong> <strong>and</strong><br />
transferability <str<strong>on</strong>g>from</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> treated plant surfaces to <str<strong>on</strong>g>the</str<strong>on</strong>g> nurseryman.<br />
There are very few studies of greenhouse workers’ exposure to pesticides<br />
that can be used as models for exposure. Kirknel et al. (1997) menti<strong>on</strong> a<br />
few German <strong>and</strong> some Dutch studies in this area. The result of <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
Danish studies accords with those of <str<strong>on</strong>g>the</str<strong>on</strong>g> German <strong>and</strong> Dutch studies. The<br />
Danish studies must be regarded as representative of a broad secti<strong>on</strong> of<br />
work functi<strong>on</strong>s in pot-plant nurseries in that <str<strong>on</strong>g>the</str<strong>on</strong>g>y include not <strong>on</strong>ly work<br />
directly with plants but also moving of work-benches <strong>and</strong> packing of<br />
plants. Dutch studies in tall crops in greenhouses, such as tomatoes <strong>and</strong><br />
cucumbers, fall within <str<strong>on</strong>g>the</str<strong>on</strong>g> result of <str<strong>on</strong>g>the</str<strong>on</strong>g> Danish model. The result of <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
Danish model is expressed as <str<strong>on</strong>g>the</str<strong>on</strong>g> 90-percentile, i.e. <str<strong>on</strong>g>the</str<strong>on</strong>g> highest exposure<br />
that 90% of a group of nurserymen can be exposed to. This cut-off point<br />
is generally regarded as high, with good safety. The Danish studies do<br />
not include <str<strong>on</strong>g>the</str<strong>on</strong>g> spraying of pesticides. Most spraying of pesticides in<br />
greenhouses is d<strong>on</strong>e automatically, with little risk of exposure. However,<br />
<str<strong>on</strong>g>the</str<strong>on</strong>g>re is some limited spraying in Danish greenhouses with a h<strong>and</strong>-held<br />
spray gun, where <str<strong>on</strong>g>the</str<strong>on</strong>g> exposure is c<strong>on</strong>sidered to be relatively high.<br />
Measurements of this work functi<strong>on</strong> are being studied in <str<strong>on</strong>g>the</str<strong>on</strong>g> UK<br />
(pers<strong>on</strong>al informati<strong>on</strong>, Erik Kirknel).<br />
Kirknel et al. (1997) have developed a model for <str<strong>on</strong>g>the</str<strong>on</strong>g> exposure to <strong>and</strong><br />
absorpti<strong>on</strong> of pesticides <strong>on</strong> re-entry into greenhouses. The daily potential<br />
exposure can here reach approx. 100 milligrammes of pesticide per<br />
working day, but typically lies in <str<strong>on</strong>g>the</str<strong>on</strong>g> interval 1-60 milligrammes in a<br />
working day of 6 hours with c<strong>on</strong>tact with <str<strong>on</strong>g>the</str<strong>on</strong>g> treated plants <strong>on</strong>e day after<br />
<str<strong>on</strong>g>the</str<strong>on</strong>g> pesticide treatment. The most critical variable is <str<strong>on</strong>g>the</str<strong>on</strong>g> rate at which <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
pesticide disappears <str<strong>on</strong>g>from</str<strong>on</strong>g> <str<strong>on</strong>g>the</str<strong>on</strong>g> plant’s surface. In <str<strong>on</strong>g>the</str<strong>on</strong>g> exposure model,<br />
account is also taken of <str<strong>on</strong>g>the</str<strong>on</strong>g> amount of pesticide that can penetrate <str<strong>on</strong>g>the</str<strong>on</strong>g><br />
skin. It is <strong>on</strong>ly <str<strong>on</strong>g>the</str<strong>on</strong>g> amount that penetrates <str<strong>on</strong>g>the</str<strong>on</strong>g> skin that causes possible<br />
<strong>health</strong> effects. The amount is normally less than <str<strong>on</strong>g>the</str<strong>on</strong>g> amount that l<strong>and</strong>s <strong>on</strong><br />
<str<strong>on</strong>g>the</str<strong>on</strong>g> skin.<br />
6.1.4 Risk of cancer<br />
Human data <strong>on</strong> exposure to pesticides <strong>and</strong> cancer are mainly based <strong>on</strong><br />
occupati<strong>on</strong>al exposure in farming, forestry <strong>and</strong> horticulture <strong>and</strong> am<strong>on</strong>g<br />
workers employed in <str<strong>on</strong>g>the</str<strong>on</strong>g> producti<strong>on</strong> of pesticides. Reviews of <str<strong>on</strong>g>the</str<strong>on</strong>g>se<br />
studies have not revealed a significant rise in <str<strong>on</strong>g>the</str<strong>on</strong>g> total mortality <str<strong>on</strong>g>from</str<strong>on</strong>g><br />
cancer am<strong>on</strong>g pers<strong>on</strong>s occupati<strong>on</strong>ally exposed to pesticides (Dich et al.<br />
1997; Mar<strong>on</strong>i, Fait 1993; Blair, Zahm 1991). Fur<str<strong>on</strong>g>the</str<strong>on</strong>g>rmore, <str<strong>on</strong>g>the</str<strong>on</strong>g> total<br />
mortality was found to be lower am<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g>se groups of pers<strong>on</strong>s exposed<br />
to pesticides than am<strong>on</strong>g <str<strong>on</strong>g>the</str<strong>on</strong>g> general populati<strong>on</strong>. This has usually been<br />
ascribed to a “<strong>health</strong>y worker effect” <strong>and</strong>, in <str<strong>on</strong>g>the</str<strong>on</strong>g> case of people employed<br />
in farming, to a <strong>health</strong>ier lifestyle am<strong>on</strong>g farming families. However,<br />
farmers, in particular, seem to have a higher occurrence of some types of<br />
cancer, including n<strong>on</strong>-Hodgkin’s lymphoma, Hodgkin’s disease, multiple<br />
myeloma, leukaemia, soft-tissue sarcoma <strong>and</strong> cerebral cancer, skin<br />
cancer, lip cancer, stomach cancer <strong>and</strong> prostate cancer (Dich et al. 1997;<br />
Blair, Zahm 1995: Blair et al. 1992). Most epidemiological studies of<br />
cancer <strong>and</strong> pesticides have dealt with pesticides as a whole <strong>and</strong> are short