Arsenate and dimethylarsinic acid in drinking water did not affect DNA damage repair in urinary bladder transitional cells or micronuclei in bone marrow
Abstract:Arsenic is a human skin, lung, and urinary bladder carcinogen, and may act as a cocarcinogen in the skin and urinary bladder. Possible modes of action of arsenic carcinogenesis/cocarcinogenesis include oxidative stress induction and inhibition of DNA damage repair. We investigated the effects of arsenic in drinking water on DNA damage repair in urinary bladder transitional cells and on micronucleus formation in bone marrow. F344 rats were given 100 ppm arsenate [As(V)] or dimethylarsinic acid [DMA(V)] in drink… Show more
“…In addition, MMA(III) and DMA(III) increased the frequency of mutations at the thymidine kinase (TK) locus in LY5178 mouse lymphoma cells but only at highly cytotoxic levels. The positive results in the TK mutation assay can be ascribed either to the fact that this assay detects a wide range of genetic alterations, including chromosomal mutations (Wang et al., 2009 ), and/or to excessive levels of cytotoxicity (OECD, 2015 ). In line with these findings, MMA(III) induced significant increases in mutagenesis at the gpt locus of Chinese hamster G12 cells only at highly cytotoxic concentrations and most mutants exhibited transgene deletions.…”
Section: Assessmentmentioning
confidence: 99%
“…Since 2009, only one additional study was identified related to in vivo clastogenicity of methylated arsenicals. Wang et al (2009) conducted a study to explore whether a 1-week oral exposure of F344 female rats to 100 mg/L of DMA(V) or As(V) in drinking water, followed by a 24-h recovery period, could increase the MN frequency in the bone marrow cells. Neither DMA(V) nor As(V) exposure increased MN frequencies in the bone marrow, and DMA(V) did not increase cyclophosphamide (CP)-induced MN.…”
The European Commission asked EFSA for a risk assessment on small organoarsenic species in food. For monomethylarsonic acid MMA(V), decreased body weight resulting from diarrhoea in rats was identified as the critical endpoint and a BMDL10 of 18.2 mg MMA(V)/kg body weight (bw) per day (equivalent to 9.7 mg As/kg bw per day) was calculated as a reference point (RP). For dimethylarsinic acid DMA(V), increased incidence in urinary bladder tumours in rats was identified as the critical endpoint. A BMDL10 of 1.1 mg DMA(V)/kg bw per day (equivalent to 0.6 mg As/kg bw per day) was calculated as an RP. For other small organoarsenic species, the toxicological data are insufficient to identify critical effects and RPs, and they could not be included in the risk assessment. For both MMA(V) and DMA(V), the toxicological database is incomplete and a margin of exposure (MOE) approach was applied for risk characterisation. The highest chronic dietary exposure to DMA(V) was estimated in ‘Toddlers’, with rice and fish meat as the main contributors across population groups. For MMA(V), the highest chronic dietary exposures were estimated for high consumers of fish meat and processed/preserved fish in ‘Infants’ and ‘Elderly’ age class, respectively. For MMA(V), an MOE of ≥ 500 was identified not to raise a health concern. For MMA(V), all MOEs were well above 500 for average and high consumers and thus do not raise a health concern. For DMA(V), an MOE of 10,000 was identified as of low health concern as it is genotoxic and carcinogenic, although the mechanisms of genotoxicity and its role in carcinogenicity of DMA(V) are not fully elucidated. For DMA(V), MOEs were below 10,000 in many cases across dietary surveys and age groups, in particular for some 95th percentile exposures. The Panel considers that this would raise a health concern.
“…In addition, MMA(III) and DMA(III) increased the frequency of mutations at the thymidine kinase (TK) locus in LY5178 mouse lymphoma cells but only at highly cytotoxic levels. The positive results in the TK mutation assay can be ascribed either to the fact that this assay detects a wide range of genetic alterations, including chromosomal mutations (Wang et al., 2009 ), and/or to excessive levels of cytotoxicity (OECD, 2015 ). In line with these findings, MMA(III) induced significant increases in mutagenesis at the gpt locus of Chinese hamster G12 cells only at highly cytotoxic concentrations and most mutants exhibited transgene deletions.…”
Section: Assessmentmentioning
confidence: 99%
“…Since 2009, only one additional study was identified related to in vivo clastogenicity of methylated arsenicals. Wang et al (2009) conducted a study to explore whether a 1-week oral exposure of F344 female rats to 100 mg/L of DMA(V) or As(V) in drinking water, followed by a 24-h recovery period, could increase the MN frequency in the bone marrow cells. Neither DMA(V) nor As(V) exposure increased MN frequencies in the bone marrow, and DMA(V) did not increase cyclophosphamide (CP)-induced MN.…”
The European Commission asked EFSA for a risk assessment on small organoarsenic species in food. For monomethylarsonic acid MMA(V), decreased body weight resulting from diarrhoea in rats was identified as the critical endpoint and a BMDL10 of 18.2 mg MMA(V)/kg body weight (bw) per day (equivalent to 9.7 mg As/kg bw per day) was calculated as a reference point (RP). For dimethylarsinic acid DMA(V), increased incidence in urinary bladder tumours in rats was identified as the critical endpoint. A BMDL10 of 1.1 mg DMA(V)/kg bw per day (equivalent to 0.6 mg As/kg bw per day) was calculated as an RP. For other small organoarsenic species, the toxicological data are insufficient to identify critical effects and RPs, and they could not be included in the risk assessment. For both MMA(V) and DMA(V), the toxicological database is incomplete and a margin of exposure (MOE) approach was applied for risk characterisation. The highest chronic dietary exposure to DMA(V) was estimated in ‘Toddlers’, with rice and fish meat as the main contributors across population groups. For MMA(V), the highest chronic dietary exposures were estimated for high consumers of fish meat and processed/preserved fish in ‘Infants’ and ‘Elderly’ age class, respectively. For MMA(V), an MOE of ≥ 500 was identified not to raise a health concern. For MMA(V), all MOEs were well above 500 for average and high consumers and thus do not raise a health concern. For DMA(V), an MOE of 10,000 was identified as of low health concern as it is genotoxic and carcinogenic, although the mechanisms of genotoxicity and its role in carcinogenicity of DMA(V) are not fully elucidated. For DMA(V), MOEs were below 10,000 in many cases across dietary surveys and age groups, in particular for some 95th percentile exposures. The Panel considers that this would raise a health concern.
“…Several methods have been reported for use in evaluating potential toxicity of drinking water, such as the Ames test, micronucleus test, and comet assay (Sujbert et al 2006;Wang et al 2009;Zegura et al 2009). The comet assay can be used to investigate chemically or physically induced single-strand breaks in DNA and has been used to evaluate mutagenic activity of surface and drinking water, and the micronucleus test can be used to detect chromosomal damage (Kummrowa et al 2003).…”
End points of reproductive toxicity were investigated in male mice (Mus musculus, ICR) fed Nanjing City tap water for 90 days. There was no significant alteration in body weights between treatment and control mice. In treated mice, flow cytometry analysis of testicular tissue indicated that the relative percentage of the elongated spermatid (HC) decreased significantly (P < 0.05). Also slight increases in the relative percentage of round spermatids (1C) and primary spermatocytes (4C) were noted. The ratios of 4C:2C (diploid germ cells) and 1C:2C increased, and testicular histopathology indicated an expansion of interstitial space and a decreased number and size of Leydig cells in treated mice. The current study suggests that Nanjing City tap water is toxic to the reproductive system of mice and additional study to evaluate its effects on other species, including human beings, would be warranted.
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