title: Do arsenosugars pose a risk to human health? The comparative toxicities of a trivalent and pentavalent arsenosugar.
abstract: Seafood frequently contains high concentrations of arsenic (approximately 10-100 mg/kg dry weight). In marine algae (seaweed), this arsenic occurs predominantly as ribose derivatives known collectively as arsenosugars. Although it is clear that arsenosugars are not acutely toxic, there is a possibility of arsenosugars having slight chronic toxicity. In general, trivalent arsenicals are more toxic than their pentavalent counterparts, so in this work we examine the hypothesis that trivalent arsenosugars might be significantly more toxic than pentavalent arsenosugars in vitro. We compared the in vitro toxicity of (R)-2,3-dihydroxypropyl-5-deoxy-5-dimethylarsinoyl-beta-D-riboside, a pentavalent arsenosugar, to that of its trivalent counterpart, (R)-2,3-dihydroxypropyl-5-deoxy-5-dimethylarsino-beta-D-riboside. The trivalent arsenosugar nicked plasmid DNA, whereas the pentavalent arsenosugar did not. The trivalent arsenosugar was more cytotoxic (IC50 = 200 microM, 48 h exposure) than its pentavalent counterpart (IC50 > 6000 microM, 48 h exposure) in normal human epidermal keratinocytes in vitro as determined via the neutral red uptake assay. However, both the trivalent and the pentavalent arsenosugars were significantly less toxic than MMA(III), DMA(III), and arsenate. Neither the pentavalent arsenosugar nor the trivalent arsenosugar were mutagenic in Salmonella TA104. The trivalent arsenosugar was readily formed by reaction of the pentavalent arsenosugar with thiol compounds, including, cysteine, glutathione, and dithioerythritol. This work suggests that the reduction of pentavalent arsenosugars to trivalent arsenosugars in biology might have environmental consequences, especially because seaweed consumption is a significant environmental source for human exposure to arsenicals.
authors.affiliation: U.S. Environmental Protection Agency, Research Triangle Park, North Carolina 27711, USA.
authors.forename: Paul
authors.initials: P
authors.lastname: Andrewes
authors.forename: David M
authors.initials: DM
authors.lastname: Demarini
authors.forename: Kunihiro
authors.initials: K
authors.lastname: Funasaka
authors.forename: Kathleen
authors.initials: K
authors.lastname: Wallace
authors.forename: Vivian W M
authors.initials: VW
authors.lastname: Lai
authors.forename: Hongsui
authors.initials: H
authors.lastname: Sun
authors.forename: William R
authors.initials: WR
authors.lastname: Cullen
authors.forename: Kirk T
authors.initials: KT
authors.lastname: Kitchin
mesh_terms: D001149:Arsenates / Q000138:chemical synthesis / Q000633:toxicity*; D001151:Arsenic / Q000032:analysis; D018053:Arsenites / Q000138:chemical synthesis / Q000633:toxicity*; D002470:Cell Survival; D002478:Cells, Cultured; D002851:Chromatography, High Pressure Liquid; D005506:Food Contamination / Q000032:analysis; D006801:Humans; D015603:Keratinocytes / Q000187:drug effects; D009005:Monosaccharides / Q000138:chemical synthesis / Q000633:toxicity*; D009152:Mutagenicity Tests; D011634:Public Health; D012266:Ribose / Q000031:analogs & derivatives / Q000138:chemical synthesis; D018570:Risk Assessment; D012624:Seaweed / Q000737:chemistry; D014874:Water Pollutants, Chemical / Q000032:analysis
chemical_list: D001149:Arsenates; D018053:Arsenites; D009005:Monosaccharides; D014874:Water Pollutants, Chemical; C449161:arsenosugar; D012266:Ribose; D001151:Arsenic