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Combined Actions and Interactions of Chemicals in Mixtures

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cells are deficient <strong>in</strong> O 6 alkyl guan<strong>in</strong>e-DNA-alkyl-transferase, but the differences <strong>in</strong><br />

resistance to ethylat<strong>in</strong>g substances may moreover be due to a more efficient<br />

excision repair system <strong>in</strong> human cells (Galloway 1994).<br />

DNA replication<br />

Changes <strong>in</strong> the fidelity <strong>of</strong> the replication <strong>of</strong> DNA are another source to<br />

comb<strong>in</strong>ational effects concern<strong>in</strong>g genotoxic compounds. Errors dur<strong>in</strong>g DNA<br />

replication may, for example, be caused by imbalances <strong>of</strong> the <strong>in</strong>tracellular DNA<br />

precursor pool. In this case, the repair system is unable to function because the<br />

right nucleotides are miss<strong>in</strong>g. Exposure to hydroxyurea <strong>in</strong>hibits the<br />

deoxyribonucleotide reductase thereby giv<strong>in</strong>g imbalance <strong>of</strong> the nucleotide pool. A<br />

dramatic enhancement <strong>of</strong> the mutagenic effect <strong>of</strong> alkylat<strong>in</strong>g agents has, for<br />

example, been observed after co-exposure with hydroxyurea (Walum et al. 1990).<br />

Oxidative damage<br />

In general, metal genotoxicity appears to follow two predom<strong>in</strong>ant modes <strong>of</strong> action,<br />

i.e. <strong>in</strong>teraction with DNA repair processes (described above) <strong>and</strong> <strong>in</strong>duction <strong>of</strong><br />

oxidative damage. Co(II) is known as a transition metal <strong>and</strong> can therefore, after<br />

reaction with cellular H2O2, generate active oxygen species (AOS) <strong>in</strong> a Fenton-like<br />

reaction.<br />

Hard metals (WC-Co) are made <strong>of</strong> a mixture <strong>of</strong> cobalt metal (5-10%) <strong>and</strong> wolframcarbide<br />

particles (WC>80%). Excessive <strong>in</strong>halation <strong>of</strong> WC-Co is associated with the<br />

occurrence <strong>of</strong> different lung diseases <strong>in</strong>clud<strong>in</strong>g an excess <strong>of</strong> lung cancers. In human<br />

peripheral lymphocytes Co powder <strong>and</strong> WC-Co both <strong>in</strong>duced DNA s<strong>in</strong>gle str<strong>and</strong><br />

breaks (ssb) measured by the alkal<strong>in</strong>e COMET <strong>and</strong> alkal<strong>in</strong>e elution assay (Anard et<br />

al. 1997). On the basis <strong>of</strong> equivalent cobalt-WC content, WC-Co produced<br />

significantly more ssb than Co. WC alone did not produce ssb. There is strong<br />

experimental evidence (Lison et al. 1995) that the <strong>in</strong>teractive (geno)toxicity <strong>of</strong><br />

WC-Co is mediated by AOS produced by the association <strong>of</strong> Co <strong>and</strong> WC but not by<br />

Co or WC alone. Anard et al. (1997) showed that 1 M formate, a hydroxyl<br />

scavenger had a protective effect aga<strong>in</strong>st the production <strong>of</strong> ssb by WC-Co particles,<br />

which is consistent with the implication <strong>of</strong> an <strong>in</strong>creased production <strong>of</strong> hydroxyl<br />

radicals when Co is mixed with WC particles.<br />

Di-(ethylhexyl)phthalate) (DEHP) is a plasticizer used <strong>in</strong> the production <strong>of</strong> PVC<br />

plastics products. DEHP is assumed to be a non-genotoxic carc<strong>in</strong>ogen, act<strong>in</strong>g as a<br />

peroxisome proliferator. DEHP is not genotoxic <strong>in</strong> Drosophila melanogaster, on<br />

the other h<strong>and</strong> DEHP enhances the genotoxic effect (acts as a co-mutagen) <strong>of</strong> Nnitrosodimethylam<strong>in</strong>e<br />

(NDMA) <strong>in</strong> this test organism measured as DNA-dsb. It was<br />

assumed that the co-mutagenic effect <strong>of</strong> DEHP was caused by oxygen radicals<br />

generated by DEHP (Kawai 1998).<br />

Cell cycle regulation<br />

Some clastogenic agents, e.g. ionis<strong>in</strong>g radiation <strong>and</strong> various cytostatic drugs such<br />

as bleomyc<strong>in</strong>, are able to <strong>in</strong>duce double str<strong>and</strong> breaks at any time <strong>in</strong> the cell cycle.<br />

When the cells are exposed prior to DNA synthesis phase (S-phase) the aberrations<br />

are <strong>of</strong> chromosome-type. When the cells are exposed after the S-phase, the<br />

aberrations are <strong>of</strong> chromatid-type. Most clastogens, however, are S-phase<br />

dependant. The breaks will manifest as chromatid-type aberrations <strong>in</strong> the<br />

subsequent metaphase. Many cytotoxic chemicals do prolong the cell cycle time.<br />

This is a potential basis for antagonistic effects, s<strong>in</strong>ce the longer the period between<br />

exposure <strong>and</strong> DNA synthesis, the more chance the cell has to repair the damage.<br />

95

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