26.12.2012 Views

Toxicology of Industrial Compounds

Toxicology of Industrial Compounds

Toxicology of Industrial Compounds

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

230 PEROXISOME PROLIFERATION<br />

intended usage <strong>of</strong> the particular compound. While hypolipidaemic agents<br />

are only administered to a restricted population <strong>of</strong> humans, exposure to<br />

industrial chemicals such as plasticisers is obviously far more widespread.<br />

For example, based on food surveillance surveys the daily human exposure<br />

to DEHA was reported to be 16 and 8.2 mg per person per day in 1987<br />

and 1990, respectively (MAFF 1987, 1990). In another study, where<br />

DEHA intake was assessed by measuring urinary levels <strong>of</strong> the major<br />

metabolite 2-ethylhexanoic acid, a median value <strong>of</strong> 2.7 mg per person per<br />

day was reported (L<strong>of</strong>tus et al., 1994).<br />

Apart from likely human exposure, consideration should be made <strong>of</strong> the<br />

relative potency <strong>of</strong> the particular compound to produce peroxisome<br />

proliferation and liver tumours in rodents. Plasticisers such as DEHP and<br />

DEHA are far less potent than certain therapeutic agents and<br />

experimentally used compounds (Reddy et al., 1986; Barber et al., 1987;<br />

Bentley et al., 1993; Lake and Lewis, 1993). Moreover rodent liver<br />

peroxisome proliferators exhibit clear no effect levels for both peroxisome<br />

proliferation and for tumour formation. For example, in the rat no effect<br />

levels for liver tumour formation have been observed in studies with<br />

several compounds including bezafibrate, cl<strong>of</strong>ibrate, DEHA and DEHP<br />

(Hartig et al., 1982; NTP 1982a, b). In addition, the threshold for tumour<br />

formation in rodents is appreciably greater than the threshold for<br />

peroxisome proliferation (Hartig et al., 1982; Reddy et al., 1986; Bentley<br />

et al., 1993).<br />

Several mechanisms have been proposed to account for why peroxisome<br />

proliferators produce tumours in rodent liver. If these various hypotheses<br />

are combined then a role for increased cell replication in peroxisome<br />

proliferatorinduced hepatocarcinogenesis may be readily identified. For<br />

example, if hepatocytes are transformed by either oxidative stress-induced<br />

damage or by alternative mechanisms, such initiated cells may be promoted<br />

to liver tumours by enhanced cell replication. Certainly peroxisome<br />

proliferators are effective promoters <strong>of</strong> certain populations <strong>of</strong> initiated cells<br />

and recent studies suggest that peroxisome proliferators can influence rates<br />

<strong>of</strong> both cell replication and cell death in particular populations <strong>of</strong><br />

hepatocytes (Grasl-Kraupp et al., 1993; Popp and Cattley, 1993; Marsman<br />

and Popp, 1994).<br />

With respect to species differences, rats and mice are clearly responsive<br />

species, whereas the majority <strong>of</strong> both in vivo and in vitro studies suggest<br />

that primates including man are either essentially refractory or certainly<br />

much less responsive to rodent peroxisome proliferators. However while<br />

effects on peroxisome morphology and marker enzyme activities have been<br />

extensively studied, few investigations have examined species differences in<br />

peroxisome proliferator-induced cell replication and liver tumour<br />

formation. As enhanced cell replication appears to play a role in peroxisome<br />

proliferator-induced hepatocarcinogenesis in rats and mice, it would

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!