Arsenobetaine is a significant arsenical constituent of the red Antarctic alga Phyllophora antarctica

Environmental context. Although arsenic occurs in marine animals at high concentrations, the pathways by which it is biotransformed and accumulated remain largely unknown. The observation that some species of algae can contain significant concentrations of arsenobetaine, a major marine arsenic species, is relevant to explanations of the source of this compound to marine animals and its transport through the marine food web. Abstract. Significant amounts of arsenobetaine (up to 0.80 μg As g–1 dry mass, representing 17% of the extractable arsenic) were found in the extracts of all four samples of the red alga Phyllophora antarctica collected from two sites in Antarctica (Terra Nova Bay and Cape Evans). The assignment was made with high performance liquid chromatography–inductively coupled plasma mass spectrometry (HPLC-ICPMS) based on exact cochromatography with a standard compound with two chromatographic systems (cation-exchange and ion-pairing reversed-phase), each run under two sets of mobile phase conditions. Particular care was taken during sample preparation to ensure that the arsenobetaine was of algal origin and did not result from epiphytes associated with the alga. Another red alga, Iridaea cordata, collected from Terra Nova Bay, did not contain detectable concentrations of arsenobetaine. For both algal species, the majority of the extractable arsenic was present as arsenosugars. Confirmation that marine algae can contain significant amounts of arsenobetaine allows a simpler explanation for the widespread occurrence of this arsenical in marine animals.

[1]  L. Radke,et al.  Fitzroy River Basin, Queensland, Australia. III. Identification of sediment sources in the coastal zone , 2008 .

[2]  S. Foster,et al.  Arsenic and selected elements in inter‐tidal and estuarine marine algae, south‐east coast, NSW, Australia , 2007 .

[3]  P. Smichowski,et al.  Investigation of arsenic speciation in algae of the Antarctic region by HPLC-ICP-MS and HPLC-ESI-Ion Trap MS , 2006 .

[4]  K. Francesconi,et al.  Synthetic routes for naturally-occurring arsenic-containing ribosides , 2006 .

[5]  I. Ipolyi,et al.  Arsenosugars and other arsenic compounds in littoral zone algae from the Adriatic Sea. , 2006, Chemosphere.

[6]  K. Francesconi Current Perspectives in Arsenic Environmental and Biological Research , 2005 .

[7]  S. Pergantis,et al.  First report on the detection and quantification of arsenobetaine in extracts of marine algae using HPLC-ES-MS/MS. , 2005, The Analyst.

[8]  Kevin A Francesconi,et al.  Determination of arsenic species: a critical review of methods and applications, 2000-2003. , 2004, The Analyst.

[9]  K. Francesconi,et al.  Arsenic Compounds in the Environment , 2001 .

[10]  W. Goessler,et al.  Characterization of an algal extract by HPLC-ICP-MS and LC-electrospray MS for use in arsenosugar speciation studies , 2000 .

[11]  W. Goessler,et al.  Uptake of arsenate, trimethylarsine oxide, and arsenobetaine by the shrimp Crangon crangon , 1998 .

[12]  J. Edmonds,et al.  Arsenic and Marine Organisms , 1996 .

[13]  B. Skelton,et al.  Arsenic-containing ribosides from the brown alga Sargassum lacerifolium: X-ray molecular structure of 2-amino-3-[5′-deoxy-5′-(dimethylarsinoyl)ribosyloxy]propane-1-sulphonic acid , 1991 .

[14]  J. Edmonds,et al.  Accumulation of arsenic in yelloweye mullet (Aldrichetta forsteri) following oral administration of organoarsenic compounds and arsenate. , 1989, The Science of the total environment.

[15]  K. Fuwa,et al.  Determination of arsenic compounds in biological samples by liquid chromatography with inductively coupled argon plasma-atomic emission spectrometric detection , 1981 .