Abstract
The fish embryo acute toxicity (FET) test with the zebrafish (Danio rerio) embryo according to OECD TG 236 was originally developed as an alternative test method for acute fish toxicity testing according to, e.g., OECD TG 203. Given the versatility of the protocol, however, the FET test has found application beyond acute toxicity testing as a common tool in environmental hazard and risk assessment. Whereas the standard OECD guideline is restricted to four core endpoints (coagulation as well as lack of somite formation, heartbeat, and tail detachment) for simple, rapid assessment of acute toxicity, further endpoints can easily be integrated into the FET test protocol. This has led to the hypothesis that an extended FET test might allow for the identification of different classes of toxicants via a “fingerprint” of morphological observations. To test this hypothesis, the present study investigated a set of 18 compounds with highly diverse modes of action with respect to acute and sublethal endpoints. Especially at higher concentrations, most observations proved toxicant-unspecific. With decreasing concentrations, however, observations declined in number, but gained in specificity. Specific observations may at best be made at test concentrations ≤ EC10. The existence of a “fingerprint” based on morphological observations in the FET is, therefore, highly unlikely in the range of acute toxicity, but cannot be excluded for experiments at sublethal concentrations.
Highlights
In 2019, the European Union produced 277.8 million tons of hazardous chemicals (Eurostat 2020), and, according to CEFIC (2021) and Statista, the 2018 globalResponsible Editor: Philippe Garrigues chemical revenue amounted to approximately US $ 4100 billion
In order to meet these concerns, in 2003, Germany replaced whole effluent acute fish toxicity (AFT) testing according to OECD TG 203 (OECD 1992, 2019) with the zebrafish (Danio rerio) fish egg test (Bundesgesetzblatt 2005; ISO 2007), and, in 2013, the OECD adopted the fish embryo acute toxicity (FET) test (TG 236; (OECD 2013)) as an alternative method for the AFT test
The present study investigated 18 compounds with highly diverse modes of action with respect to acute and sublethal morphological endpoints in the FET test
Summary
In 2019, the European Union produced 277.8 million tons of hazardous chemicals (Eurostat 2020), and, according to CEFIC (2021) and Statista (https://www.statista.com/), the 2018 globalResponsible Editor: Philippe Garrigues chemical revenue amounted to approximately US $ 4100 billion. Since tests with vertebrates are an integral part of environmental hazard identification and risk assessment of chemicals, Environ Sci Pollut Res plant protection products, pharmaceuticals, biocides, feed additives, and effluents (Scholz et al 2013), this increase in testing requirements has raised increasing concern about animal welfare (Braunbeck et al 2005, 2015; Paparella et al 2020; von Hellfeld et al 2020). In order to meet these concerns, in 2003, Germany replaced whole effluent acute fish toxicity (AFT) testing according to OECD TG 203 (OECD 1992, 2019) with the zebrafish (Danio rerio) fish egg test (Bundesgesetzblatt 2005; ISO 2007), and, in 2013, the OECD adopted the fish embryo acute toxicity (FET) test (TG 236; (OECD 2013)) as an alternative method for the AFT test. According to current EU Animal Welfare Regulation (EU 2010), zebrafish embryos are not regarded protected according to current EU animal welfare legislation (Strähle et al 2012)
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