A novel arsenic containing riboside (arsenosugar) in three species of gastropod
Introduction
High arsenic concentrations in marine organisms were first reported in the early 1900s, and following considerable work over the last 20 years, the chemical structures of many of the marine arsenic compounds are now known (Francesconi and Edmonds, 1997). In marine animals arsenobetaine is by far the major arsenic compound. Tetramethylarsonium ion, arsenocholine, and trimethylarsine oxide are also found in marine animals but they generally occur only as minor compounds (see Fig. 1 for structures of arsenic compounds). The pattern of arsenic compounds in marine algae is quite different from that in animals. In algae, arsenic containing ribosides (arsenosugars) are the major arsenic compounds (Morita and Shibata, 1990), and arsenobetaine, tetramethylarsonium ion, arsenocholine, and trimethylarsine oxide are absent. Most of the arsenosugars identified in algae are dimethylated arsinoyl (Me2AsO-) derivatives of ribosides, chiefly compounds 1–4 (Fig. 1). One trimethylated arsonio (Me3As+-) riboside (arsenosugar 5) has also been reported from algal sources (Shibata and Morita, 1988; Francesconi et al., 1992a). In seawater and marine sediments, arsenic is present mainly as arsenate along with some arsenite and traces of methylarsonic acid and dimethylarsinic acid (Andreae, 1979; Reimer and Thompson, 1988; Santosa et al., 1994). Neither arsenobetaine nor arsenosugars have been detected thus far in seawater or sediments.
Two questions fundamental to our understanding of the cycling of arsenic in marine systems remain unanswered. First, what are the processes whereby inorganic arsenate in seawater is biotransformed by algae into arsenosugars; and, second, what is the origin of arsenobetaine in marine animals. A proposed biogenetic pathway for arsenosugars (Edmonds and Francesconi, 1987) has been supported by identification of key intermediates in marine biota (Francesconi et al., 1992a). The origin of arsenobetaine, however, is more speculative. Although some evidence has been presented for a biogenetic pathway to arsenobetaine beginning with dimethylated arsenosugars (Edmonds et al., 1982), the key intermediate in the proposed pathway, dimethylarsinoylethanol, has not been detected in biota, and the final biotransformation of dimethylarsinoylethanol to arsenobetaine was not observed in laboratory experiments designed to simulate natural marine environments (Francesconi and Edmonds, 1994). An alternative pathway beginning with trimethylated arsenosugars has some experimental support: under anaerobic microbial conditions the arsenosugar 5 was converted in high yield to arsenocholine (Francesconi et al., 1992b); and, in a second experiment, arsenocholine fed to fish was converted to arsenobetaine (Francesconi et al., 1989).
Arsenobetaine clearly plays an important role in the cycling of arsenic in marine systems, and recent results showing the presence of arsenobetaine in terrestrial organisms (Šlejkovec et al., 1997; Geiszinger et al., in press) suggest that its production is more widespread than previously thought. Elucidation of the biogenesis of arsenobetaine might be aided by the identification of naturally occurring arsenic compounds. Consequently, the search for key intermediates in the proposed biogenetic pathways leading to arsenobetaine forms the basis of the work reported here.
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Collection and preparation of gastropod samples
Three species of gastropod (family Muricidae, order Neogastropoda) were examined namely Thais distinguenda Röding, 1798, Thais bitubercularis Lamarck, 1822 and Morula musiva Kiener, 1836. The muricids are carnivorous gastropods feeding on various invertebrates, such as bivalves, gastropods and barnacles (Cernohorsky, 1978). Specimens were hand-collected from rocky shores at Phuket, Thailand in October 1996. A total of six samples was obtained: T. distinguenda from one site (Laem Nga); T.
Total arsenic in the gastropods
Concentrations of total arsenic in the three species of gastropods ranged from 112 to 339 μg As g−1 dry mass (Table 1). These arsenic concentrations fall within the range previously reported for gastropods from Japan (Shiomi et al., 1984), USA (Hall et al., 1978) and Hong Kong (Phillips and Depledge, 1986), but are higher than those generally found in other marine animals (Francesconi and Edmonds, 1997). There is no readily apparent explanation for the high arsenic concentrations in gastropods.
Arsenic compounds in the gastropods
Acknowledgements
We thank Michael Bech for collecting the gastropods and for comments, and Vibeke Eriksen for technical support.
References (28)
- et al.
Accumulation of arsenic in yellow-eye mullet (Aldrichetta forsteri) following oral administration of organoarsenic compounds and arsenate
Sci Total Environ
(1989) - et al.
Arsenic speciation in shrimp and mussels from the Mid-Atlantic hydrothermal vents
Mar Chem
(1997) Arsenic speciation in seawater and interstitial waters: the influence of biological–chemical interactions on the chemistry of a trace element
Limnol Oceanogr
(1979)- Cernohorsky W. Tropical marine Pacific shells. Sydney, Australia: Pacific Publications Pty Ltd.,...
- et al.
Arsenic in the environment
Chem Rev
(1989) - et al.
Transformations of arsenic in the marine environment
Experientia
(1987) - et al.
Dimethyloxarsylethanol from anaerobic decomposition of brown kelp Ecklonia radiata: a likely precursor of arsenobetaine in marine fauna
Experientia
(1982) - et al.
Arsenic compounds in tissues of the leatherback turtle, Dermochelys coriacea
J Mar Biol Assoc UK
(1994) - Francesconi KA, Edmonds JS. Biotransformation of arsenic in the marine environment. In: Nriagu JO, editor. Arsenic in...
- et al.
Arsenic and marine organisms
Adv Inorg Chem
(1997)