Guidelines for Metals and Metalloids in Ambient ... - ARCHIVE: Defra
Guidelines for Metals and Metalloids in Ambient ... - ARCHIVE: Defra
Guidelines for Metals and Metalloids in Ambient ... - ARCHIVE: Defra
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Arsenic<br />
86. Some toxicologists believe that arsenic does not act by direct reaction<br />
with DNA but rather by <strong>in</strong>terfer<strong>in</strong>g with DNA synthesis. Inhibition of<br />
DNA replicative mechanisms <strong>and</strong> effects on repair mechanisms<br />
could expla<strong>in</strong> the chromosomal effects of arsenic <strong>and</strong> synergism with<br />
DNA-reactive chemicals. Other mechanisms <strong>for</strong> the carc<strong>in</strong>ogenicity of<br />
arsenic have, on the basis of experimental evidence, been suggested;<br />
they <strong>in</strong>clude clastogenicity (chromosomal breakage) <strong>and</strong> mutagenicity<br />
(changes <strong>in</strong> the structure of genetic material). No s<strong>in</strong>gle hypothesis has<br />
attracted universal support.<br />
87. Recent studies have also suggested that DMA, a major metabolite of<br />
<strong>in</strong>gested <strong>in</strong>organic arsenic <strong>in</strong> mammals, may <strong>in</strong>itiate carc<strong>in</strong>ogenesis <strong>in</strong><br />
a number of organs (Yamanaka et al., 2004; Wanibuchi et al., 2004).<br />
The methylation of trivalent arsenic has been associated with DNA<br />
damage <strong>and</strong> activation of AP-1 dependent gene transcription<br />
(Styblo et al., 2002). However, it is unclear if these metabolites are<br />
present <strong>in</strong> sufficient quantities or length of time to <strong>in</strong>duce toxicity<br />
(Schoen et al., 2004).<br />
2.3.3.2 Humans<br />
88. Human genotoxic effects, manifest as an <strong>in</strong>crease <strong>in</strong> risk of<br />
chromosomal abnormalities <strong>in</strong> peripheral leucocytes, have been<br />
reported from one population, employed <strong>in</strong> a Swedish copper smelter.<br />
No associated exposure estimates were presented (Beckman et al.,<br />
1977) <strong>and</strong> it not clear that the effects were attributable to arsenic<br />
exposure. Trivalent arsenic may be more genotoxic to human<br />
lymphocytes than pentavalent arsenic (Nordenson et al., 1981).<br />
89. Close attention has been paid to the carc<strong>in</strong>ogenic effects of <strong>in</strong>haled<br />
arsenic <strong>in</strong> the workplace; <strong>and</strong> <strong>in</strong> particular to the risk of lung cancer.<br />
This <strong>in</strong> part may reflect the relative ease with which secondary<br />
(mortality) data can be collected. Workers exposed to arsenic may also<br />
be exposed to other carc<strong>in</strong>ogens such as tobacco smok<strong>in</strong>g or other<br />
workplace tox<strong>in</strong>s. These need to be accounted <strong>for</strong> although this is<br />
commonly not the case <strong>in</strong> published studies.<br />
90. There is some <strong>in</strong><strong>for</strong>mation suggest<strong>in</strong>g that those who lived <strong>in</strong> the<br />
vic<strong>in</strong>ity of smelters had an <strong>in</strong>creased risk of lung cancer (Pershagen,<br />
1985). When taken together with the studies of developmental defects<br />
mentioned below, these <strong>in</strong>dicate a need to control non-occupational<br />
airborne exposures but the available data on exposure levels would not<br />
be helpful <strong>in</strong> st<strong>and</strong>ard sett<strong>in</strong>g.<br />
91. Increased risks of lung cancer attributed to arsenic have been reported<br />
<strong>in</strong> serial studies of the work<strong>for</strong>ces of two US <strong>and</strong> one Swedish smelters<br />
(Enterl<strong>in</strong>e et al., 1995; Lee-Feldste<strong>in</strong>, 1986; Jarup et al., 1989); <strong>and</strong> <strong>in</strong><br />
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