Abstract

Arsenic (As) can be transferred along the food chain, while little is known about the toxic effects of dietborne As on marine copepods. In this study, we investigated the short-term and long-term effects of waterborne and dietborne As exposure on the bioaccumulation and biotransformation, as well as developmental toxicity of Tigriopus japonicus. Under acute As exposure, As bioaccumulation increased and reached a plateau with increasing exposure concentration. Moreover, As accumulation at dietborne exposure was 4.3 and 5.7 times greater than that at control group for AsIII and AsⅤ, respectively. At chronic As exposure, As accumulation increased continuously with exposure time, with a 2.8-day extension of development time and a 45% reduction in 10-d fecundity under dietborne exposure compared to control, whereas 2.3-day extension of development time and a 20% reduction in 10-d fecundity were observed under waterborne exposure. Among As species, inorganic As had the highest concentrations, but the proportion of inorganic As decreased from 89% to 63% during 4 to 21 d of exposure, suggesting the conversion of inorganic As to organic As. The organic As was dominated by arsenobetaine (AsB, 13-25%), followed by monomethylarsenic (MMA, 8-25%). These results suggest that dietborne exposure has more pronounced toxic effects on T. japonicus, but the toxicity of As could be reduced through biotransformation under chronic exposure. Therefore, the arsenic species should be considered when assessing As toxicity. Environmental ImplicationArsenic contamination is common in coastal areas. Arsenic can be transferred along the food chain, but the toxicity and biotransformation effects of dietborne As on marine copepods, a predominant group of marine zooplankton, are unclear. This study showed dietborne exposure is the major pathway of As accumulation in chronic exposure. Arsenic inhibited the development and reproduction of the copepod Tigriopus japonicus. But T. japonicus can transform inorganic As to non-toxic arsenobetaine (AsB) through biotransformation to reduce the toxicity of As. The results of this study are of great significance for understanding the ecotoxicological effects of As on marine ecosystems.

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