4.7 Article

The fish early-life stage sublethal toxicity syndrome - A high-dose baseline toxicity response

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ENVIRONMENTAL POLLUTION
卷 291, 期 -, 页码 -

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ELSEVIER SCI LTD
DOI: 10.1016/j.envpol.2021.118201

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Fish early-life stage; Sublethal toxicity syndrome; Baseline toxicity; Mechanism of action; Teratogens

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TxSnFELS is a common sublethal toxicity syndrome observed in ELS fish, characterized by reduced heart rate, edemas, and morphological abnormalities. This syndrome is mainly seen at high exposure concentrations and is considered a baseline, non-specific toxicity response, but can also occur at low doses through specific action.
A large number of toxicity studies report abnormalities in early life-stage (ELS) fish that are described here as a sublethal toxicity syndrome (TxSnFELS) and generally include a reduced heart rate, edemas (yolk sac and cardiac), and a variety of morphological abnormalities. The TxSnFELS is very common and not diagnostic for any chemical or class of chemicals. This sublethal toxicity syndrome is mostly observed at high exposure concentrations and appears to be a baseline, non-specific toxicity response; however, it can also occur at low doses by specific action. Toxicity metrics for this syndrome generally occur at concentrations just below those causing mortality and have been reported for a large number of diverse chemicals. Predictions based on tissue concentrations or quantitative-structure activity relationship (QSAR) models support the designation of baseline toxicity for many of the tested chemicals, which is confirmed by observed values. Given the sheer number of disparate chemicals causing the TxSnFELS and correlation with QSAR derived partitioning; the only logical conclusion for these high-dose responses is baseline toxicity by nonspecific action and not a lock and key type receptor response. It is important to recognize that many chemicals can act both as baseline toxicants and specific acting toxicants likely via receptor interaction and it is not possible to predict those threshold doses from baseline toxicity. We should search out these specific low-dose responses for ecological risk assessment and not rely on high-concentration toxicity responses to guide environmental protection. The goal for toxicity assessment should not be to characterize toxic responses at baseline toxicity concentrations, but to evaluate chemicals for their most toxic potential. Additional aspects of this review evaluated the fish ELS teratogenic responses in relation to mammalian oral LD50s and explored potential key events responsible for baseline toxicity.

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