Occupational exposure to chromium(VI) has long been recognized as a carcinogenic factor for the lung and other respiratory tissues (
1,
2). Approximately 360

000 workers in the US and several million worldwide are currently exposed to Cr(VI) in the workplace. Frequent environmental contamination with this metal has raised significant health concerns for several non-industrial populations, particularly for those with drinking water contamination or residing in close proximity to large sites of chromate disposal (
3,
4). However, it has also been argued that detoxification processes should limit cancer risk to the cases of massive occupational exposures (
5). Carcinogenic potential of Cr(VI) is supported by its ability to cause DNA damage and mutations, although its mutagenicity has been found to be modest and typically detected at very toxic doses (
6). Recent epidemiological and risk assessment studies conducted by the EPA have found ~25% lifetime risk of dying of lung cancer under the current permissible exposure limit (PEL) (
7,
8). These findings served as the basis for the OSHA decision in early 2006 to lower the PEL for Cr(VI) by 10-fold (
9). Even under the new standard, a lifetime exposure was estimated to cause 10–45 additional lung cancers per 1000 workers. This strikingly high cancer risk for Cr(VI) exposures experienced by hundreds of thousands of people requires a much better understanding of the mechanisms of high Cr(VI) genotoxicity and adequate approaches to assess it. Weak mutagenicity and the need for relatively high doses for the induction of other genotoxic responses were clearly inconsistent with the very strong carcinogenic potential of Cr(VI).
Cr(VI) is a pro-carcinogen that generates DNA damaging species via its reductive activation in cells by ascorbate (Asc) and small thiols, such as cysteine and glutathione (
10). While the final product of all reduction reactions is always Cr(III), there are very important differences in reduction rates and the nature of intermediate products. Reduction of Cr(VI) by thiols is relatively slow and produces transient Cr(V) and Cr(IV) species, whereas reaction with the two-electron donor Asc is fast and generates Cr(IV) as the main intermediate (
10,
11). Metabolism of Cr(VI) by Asc and thiols also yields different spectra of ternary Cr-DNA adducts (
10). The formation of Cr(V) intermediates have been frequently considered an important indicator of the genotoxic consequences due to its ability to catalyze Fenton-like redox reactions (
12) and, in some ligand environments, to cause direct DNA oxidation (
13,
14). However, there has been some technical bias for studies with Cr(V) because, unlike Cr(IV), several relatively stable Cr(V) complexes could be synthesized allowing examination of their genotoxic and chemical properties. Considering that Asc is a dominant reducer of Cr(VI) in tissues (
15) and does not directly generate Cr(V) at physiological conditions (
16,
17), then one would predict that only a rapid inflow of massive Cr(VI) doses resulting in a severe drop in Asc levels could cause significant Cr(V) production and DNA damage. The causes for increased Cr(V) formation under these conditions would include a shift to thiol-dependent metabolism and increased stability of Cr(IV) intermediates that can generate Cr(V) via secondary reactions (
10). However, the hypothesis on the overriding importance of Cr(V) is not supported by studies on the formation of mutagenic damage
in vitro (
18) and the fact that Cr(VI) is a weak mutagen in mammalian cells (
6) that rely on thiols to reduce Cr(VI) due to scarcity of cellular Asc in the standard tissue cultures (
10,
19).
In this work, we examined the importance of cellular Asc in the manifestation of the genotoxic abilities of Cr(VI). We found that metabolism of Cr(VI) by cellular Asc caused dramatic increases in the formation of chromosomal damage and mutations at the endogenous Hprt gene. Mechanistically, increased DNA breakage was associated with abnormal processing of Cr-DNA damage by the mismatch repair (MMR) machinery of cells entering G2 phase.