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Combined Actions and Interactions of Chemicals in Mixtures

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Four <strong>in</strong>hibitors <strong>of</strong> DNA topoisomerases: nalidixic acid, campothec<strong>in</strong>, mamsachr<strong>in</strong>e<br />

<strong>and</strong> etoposide, have been evaluated for genotoxic effects <strong>in</strong> the w<strong>in</strong>g<br />

spot test <strong>of</strong> Drosophila melanogaster. Tested alone only campthothec<strong>in</strong> <strong>and</strong><br />

etoposide was significantly genotoxic <strong>in</strong> this assay. A significant proportion <strong>of</strong> the<br />

total spot <strong>in</strong>duction was due to mitotic recomb<strong>in</strong>ation. On the other h<strong>and</strong>, the cotreatment<br />

<strong>of</strong> each topoisomerase <strong>in</strong>hibitor with the alkylat<strong>in</strong>g agent ethyl<br />

methansulfonate (EMS) <strong>in</strong>dicate that, while nalidix<strong>in</strong> acid, m-amsachr<strong>in</strong>e <strong>and</strong><br />

etoposide show a tendency <strong>of</strong> antagonistic effect, campothec<strong>in</strong> shows an additive<br />

effect, suggest<strong>in</strong>g mechanistic differences between the activity <strong>of</strong> the four<br />

<strong>in</strong>hibitors <strong>of</strong> DNA topoisomerases (Torres et al. 1998).<br />

In some complex mixtures especially s<strong>in</strong>gle class mixtures like PAH conta<strong>in</strong><strong>in</strong>g<br />

mixtures, additive <strong>in</strong>teractions may be assumed. Although both synergistic <strong>and</strong><br />

antagonistic effects have been demonstrated <strong>in</strong> b<strong>in</strong>ary mixtures <strong>of</strong> different PAH<br />

(Hermann 1981, Hughes & Phillips 1990) (se also section on carc<strong>in</strong>ogenesis) l<strong>in</strong>ear<br />

correlation between mutagenicity <strong>in</strong> Salmonella <strong>and</strong> PAH content <strong>in</strong> city air have<br />

been demonstrated at lower PAH concentrations, but at high PAH concentrations<br />

the mutagenicity <strong>in</strong>creased much more than the PAH content (Nielsen et al. 1999).<br />

Booth et al. (1998) demonstrated l<strong>in</strong>ear correlation <strong>of</strong> DNA adducts <strong>in</strong> mouse sk<strong>in</strong><br />

<strong>in</strong> vivo with PAH content <strong>and</strong> mutagenicity <strong>in</strong> Salmonella <strong>in</strong> a range <strong>of</strong> petroleum<br />

products.<br />

7.2.7.1 Toxicok<strong>in</strong>etic <strong>in</strong>teractions<br />

Bioavailability<br />

If a substance is not absorbed or cannot pass biological barriers it will not react<br />

with DNA. Most chemical compounds are absorbed via a passive diffusion-driven<br />

process <strong>and</strong> <strong>in</strong>teraction with such compounds will normally not be expected.<br />

However, some solvents like DMSO are known to facilitate the cellular uptake <strong>of</strong><br />

some chemical compounds. Interaction can be expected when active transport<br />

processes or a specific transporter is <strong>in</strong>volved. An example <strong>of</strong> the latter is the<br />

absorption <strong>of</strong> cobalt. Iron is known to <strong>in</strong>terfere with the absorption <strong>of</strong> cobalt <strong>in</strong> the<br />

gastro<strong>in</strong>test<strong>in</strong>al tract. Iron deficiency <strong>in</strong>creases the absorption <strong>of</strong> cobalt, thus,<br />

simultaneous adm<strong>in</strong>istration <strong>of</strong> ion reduces cobalt absorption (El<strong>in</strong>der & Friberg<br />

1986). Also, am<strong>in</strong>o acids <strong>and</strong> prote<strong>in</strong>s <strong>in</strong> the diet reduce the absorption <strong>of</strong> cobalt,<br />

s<strong>in</strong>ce both am<strong>in</strong>o acids <strong>and</strong> sulfhydryl groups complex with cobalt ions. It has also<br />

been shown that the genotoxic effect <strong>of</strong> cobalt is reduced with addition <strong>of</strong> the<br />

am<strong>in</strong>o acid aden<strong>in</strong>e (B<strong>in</strong>derup 1993, B<strong>in</strong>derup 1999), these antagonistic effect<br />

might be due to a decrease <strong>in</strong> the absorption <strong>of</strong> the cobalt-aden<strong>in</strong>e complex<br />

compared to the cobalt ion.<br />

Biotransformation<br />

Many genotoxic compounds must undergo biotransformation before they can react<br />

with DNA, <strong>and</strong> some observed species differences <strong>in</strong> susceptibility to<br />

mutagens/carc<strong>in</strong>ogens have a metabolic basis. Also <strong>in</strong>dividual susceptibility among<br />

humans can be due to differences <strong>in</strong> metabolism.<br />

Cytochrome P-450 enzymes carry out many <strong>of</strong> the reactions that convert stable<br />

promutagens to electrophilic, reactive agents. Multiple cyt. P-450 isozymes exist<br />

with different substrate specificities or differences <strong>in</strong> their distribution among<br />

organs, species, <strong>and</strong> <strong>in</strong>dividuals. However most chemicals are enzymatically<br />

deactivated <strong>in</strong> the organism, while rather non-polar, lipid-soluble compounds are<br />

converted by phase I enzymes (eg oxidised by cyt. P450) to more polar <strong>and</strong> water<br />

soluble compounds which are more readily excreted. The oxidation product may be<br />

further metabolised by phase II enzymes (e.g., by hydroxylation, sulphuronidation<br />

or glucuronidation). Competition between metabolic activation <strong>and</strong> detoxification<br />

processes can strongly <strong>in</strong>fluence the genotoxic effect <strong>of</strong> complex mixtures, as some<br />

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