Subchronic organismal toxicity, cytotoxicity, genotoxicity, and feeding response of pacific oyster ( Crassostrea gigas) to lindane (γ‐HCH) exposure under experimental conditions

Abstract This study evaluated organismal toxicity, cytotoxicity, and genotoxicity and the filtration rate in response to different concentrations of subchronic lindane (gamma‐hexachlorocyclohexane [γ‐HCH]), exposure (12 d) in adult Pacific oysters Crassostrea gigas. Oysters were exposed in vivo in l...

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Bibliographic Details
Published in:Environmental Toxicology and Chemistry
Main Authors: Anguiano, Gerardo, Llera‐Herrera, Raul, Rojas, Emilio, Vazquez‐Boucard, Celia
Format: Article in Journal/Newspaper
Language:English
Published: Wiley 2007
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Online Access:http://dx.doi.org/10.1897/06-377r3.1
https://api.wiley.com/onlinelibrary/tdm/v1/articles/10.1897%2F06-377R3.1
https://setac.onlinelibrary.wiley.com/doi/pdf/10.1897/06-377R3.1
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Summary:Abstract This study evaluated organismal toxicity, cytotoxicity, and genotoxicity and the filtration rate in response to different concentrations of subchronic lindane (gamma‐hexachlorocyclohexane [γ‐HCH]), exposure (12 d) in adult Pacific oysters Crassostrea gigas. Oysters were exposed in vivo in laboratory aquaria to 10 different concentrations (0.0–10.0 mg/L) of γ‐HCH. The median lethal concentration (LC50) after 12 d was calculated as 2.22 mg/L. Cytotoxic effects were observed in hemocytes, where the mean cell viability was significantly decreased at 1.0 mg/L of γ‐HCH after 12 d. Genotoxicity of γ‐HCH measured by single cell gel electrophoresis assay, in hemocytes was evident at 0.7 mg/L of γ‐HCH after 12 d. After 4 h of exposure to γ‐HCH, filtration rates were reduced compared with controls to 65.8 and 38.2% at concentrations of 0.3 and 0.7 mg/L, respectively, and after 11 d of exposure, filtration rates were reduced to 60.4 and 30.9% at concentrations of 0.1 mg/L and higher. These results show the subchronic effects of γ‐HCH at different concentrations and effect sensitivities are categorized as filtration rate < genotoxicity < cytotoxicity < mortality. The relevance of integral toxicity evaluation, considering different endpoints from molecular, cellular, and individual levels is discussed.