Published February 2018 | Version v1
Journal article

Modification and quantification of in vivo EROD live-imaging with zebrafish (Danio rerio) embryos to detect both induction and inhibition of CYP1A

  • 1. Aquatic Ecology and Toxicology Group, Center for Organismal Studies (COS), University of Heidelberg, Im Neuenheimer Feld 504, D-69120 Heidelberg (Germany)
  • 2. Department of Ecosystem Analysis, Institute for Environmental Research, ABBt - Aachen Biology and Biotechnology, RWTH Aachen University, Worringerweg 1, 52074 Aachen (Germany)

Description

Highlights: • Chlorpyrifos is a strong CYP1A inhibitor in zebrafish embryos. • Aroclor 1254 inhibits CYP1A catalytic activity in zebrafish embryos in a specific time-dependent manner. • CYP1A inhibition could also be detected after 3 h short-term exposure of zebrafish embryos to chlorpyrifos. • The lack of CYP1A inhibition after 3 h exposure of zebrafish embryos to Aroclor 1254 demonstrates toxicokinetic mechanisms. • In vivo EROD assay visualizes CYP1A induction/inhibition and allows densitometric quantification and statistical assessment. The visualization of specific activation of the aryl hydrocarbon receptor (AhR) directly in the zebrafish embryo (Danio rerio) via live-imaging is a reliable tool to investigate the presence of dioxin-like substances in environmental samples. The co-existence of inducers and inhibitors of cytochrome P450-dependent monooxygenases (CYP1A) is typical of complex environmental mixtures and requires modifications of the in vivo EROD assay: For this end, zebrafish embryos were used to evaluate the EROD-modifying potentials of common single-compound exposures as well as binary mixtures with the PAH-type Ah-receptor agonist β-naphthoflavone. For chemical testing, chlorpyrifos and Aroclor 1254 were selected; β-naphthoflavone served as maximum EROD induction control. Chlorpyrifos (≤ EC10) could be documented to be a strong CYP1A inhibitor causing characteristic edema-related toxicity. Aroclor 1254 resulted in inhibition of CYP1A catalytic activity in a concentration- and specific time-dependent manner. Next to a fast CYP1A induction, CYP1A inhibition could also be detected after 3 h short-term exposure of zebrafish embryos to chlorpyrifos. This communication also describes techniques for the quantification of fluorescence signals via densitometry as a basis for subsequent statistical assessment. The co-exposure approach with zebrafish embryos accounts for the nature of potential interaction between CYP1A inducers and inhibitors and thus pays tribute to the complexity of environmental mixtures. The co-exposure EROD live-imaging assay thus facilitates a better understanding of mixture effects and allows a better assessment and interpretation of (embryo) toxic potentials.

Availability note (English)

Available from http://dx.doi.org/10.1016/j.scitotenv.2017.09.257

Additional details

Identifiers

DOI
10.1016/j.scitotenv.2017.09.257;
PII
S0048969717326098;

Publishing Information

Journal Title
Science of the Total Environment
Journal Volume
615
Journal Page Range
p. 330-347
ISSN
0048-9697
CODEN
STENDL

Optional Information

Copyright
Copyright (c) 2017 Published by Elsevier B.V.