Cellular reduction of carcinogenic Cr(VI) generates a wide assortment of small DNA modifications resulting from the crosslinking activity of Cr(III) (
1,
2) and the oxidizing properties of intermediate Cr species and other reactive byproducts (
3,
4). Cr(VI) is also known to induce bulky DNA-protein crosslinks (DPC) in various cells in culture and in vivo (
5–
7). Methodological improvements in DPC measurements and positive results from several human studies pointed to the potential utility of these lesions as biomarkers of exposure to toxic Cr compounds (
8). Elevated levels of DPC have been found in peripheral blood lymphocytes among welders (
9,
10), chrome platers (
11,
12) and leather tanners (
13). Lymphocytic DPC have shown a good correlation with the levels of Cr in red blood cells (
11), which is a biomarker of internal dose of Cr(VI) (
14,
15). Higher levels of lymphocytic DPC have also been found in populations residing in areas with environmental Cr contamination (
11,
16). The main advantage of DPC measurements over determinations of total Cr in biological samples, including erythrocytes, is that they assess the presence of elevated genetic damage. DPC levels in human lymphocytes are not significantly affected by age, weight or smoking status (
17), which permits the use of this biomarker for the detection of Cr-associated genetic damage in relatively small groups of exposed individuals (
18). In addition to human biomonitoring, DPC measurements have been used for the assessment of genetic damage in several aquatic species exposed to waterborne Cr(VI) (
19,
20).
Although the biological significance of DPC in general is poorly understood, these bulky lesions have long been assumed to be genotoxic. A likely impediment of DNA replication by Cr-induced DPC has been suggested to lead to gross genetic rearrangements (
9), mutations (
8) or S-phase specific DNA double-strand breaks (
21). Some chemical forms of DPC were indeed tested mutagenic (
22,
23) but others were not (
24). Puga and co-workers (
25) have recently provided experimental evidence that DPC play a major role in the well-established phenomenon of inhibition of inducible gene expression in Cr(VI)-treated cells (
26–
28). They found that Cr(VI) suppressed the aryl hydrocarbon receptor-mediated gene expression by benzo[α]pyrene via DNA crosslinking of the repressory HDAC1-DNMT1 complexes, which blocked their release from the promoters of the inducible genes and prevented chromatin remodeling and RNA polymerase II recruitment. Thus, in addition to their potential role in genotoxic effects of Cr(VI), DPC can also play an important role in the toxicological effects of mixed exposures, particularly for agents that require gene induction for their activation, efficient detoxification or repair of cell injury.
Broader utilization of DPC as a biomarker, particularly for environmentally exposed populations, is hampered by the inability of current analytical approaches to differentiate between Cr(VI)-induced and other forms of DPC. The basis of this problem largely lies in the poorly understood mechanisms of intermolecular crosslinking by Cr(VI), which makes it difficult to devise more specific methodologies. Better defined crosslinking mechanisms would also make it easier to interpret the effects of altered cellular physiology or coexposure conditions on the DPC formation and the associated toxicological effects. In principle, Cr(VI) can induce DPC either via Cr(III)-mediated crosslinking reactions or oxidative mechanisms. The latter can involve either crosslinking by the initial oxidative lesions on DNA (
29,
30) and proteins (
31) or via reactive products of lipid peroxidation, such as malondialdehyde (
32). Formation of advanced products of guanine oxidation by Cr(VI) (
4) is one of the potential routes to protein crosslinking via oxidative mechanisms. Studies in CHO cells showed that about 50% of Cr(VI)-induced DPC were sensitive to disruption by EDTA (
33), which was indicative of a major role of Cr(III) in DNA-protein crosslinking. However, experimentally very similar work using human MOLT4 lymphoma cells detected only a very small effect of EDTA (
7), which has been interpreted as evidence for oxidative linkages in DPC formation. The crosslinking ability of Cr(III) aqua complexes under neutral pH has also been questioned experimentally (
34), although results of this and some other similar in vitro studies could have been adversely impacted by the use of Tris buffer (
1).
In this work, we conducted detailed mechanistic studies of DPC formation by carcinogenic Cr(VI) and the final product of its reduction, Cr(III). The uncertainty about the role of Cr(III) in DPC production was addressed using a more efficient chelation procedure. The process of DNA-protein crosslinking was dependent on Cr(III), but the sequence of reactions leading to the intermolecular conjugation was different than that established for small reducer-Cr(III)-DNA crosslinks (
35,
36).