doi:10.1016/j.ecoenv.2004.10.015
Copyright © 2004 Elsevier Inc. All rights reserved.
Development of a zebrafish 4-day embryo-larval bioassay to assess toxicity of chemicals
Benoit Fraysse, Raphael Mons and Jeanne Garric
, 
Laboratoire d’Ecotoxicologie, Cemagref, 3 bis quai Chauveau, CP 220, 69336 Lyon Cedex 09, France
Received 23 March 2004;
revised 1 September 2004;
accepted 13 October 2004.
Available online 1 January 2005.
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Abstract
A 4-day embryo-larval zebrafish test, from blastula stage to hatching included, was developed. The observations of embryo developmental were made at different development stages, for which morphological, physiological, and behavioral endpoints were selected and quantified for unexposed and exposed embryos. The sensitivity and the ability of these endpoints to inform about mode of action (MoA) were established in testing three model toxicants with well-known toxic effects (propranolol, malathion, cadmium). Lethal, sublethal (heart rate/edema, spontaneous movements, and hatching rate/time disturbance), and teratogenic effects were detected for all the studied compounds. This bioassay allows characterization of impairments at different biological levels: neuromuscular, physiological, morphological, and behavioral, and brings useful information about the toxic MoA of the chemicals on nontarget organisms. In this sense to answers the chemical industries and international organization (EMEA) requirements for the environmental risk assessment of new chemicals and pharmaceuticals.
Keywords: Zebrafish; Embryotoxicity; Mode of action; Bioassay; Risk assessment
Fig. 1. Zebrafish free larva at 80 hpf (A) and picture analysis performed. Tail length (A); tail curvature (B1, normal morphology; B2, lordosis—arrow head); pericardial area (C). Scale bar: 0.2 mm.
Fig. 2. Frequency (%) of parameters measured on two populations of developing zebrafish embryos laid by two different genitor groups (Group A, top; Group B, bottom). See text for the measurement procedure. The probability of adequacy between observed values (bars) and theoretical distribution (continuous line: Poisson law; dotted line: Normal law) was estimated with Kolmogorov–Smirnov (KS) and χ2 tests. n, number of values; P, probability.
Fig. 3. Normal (A, control) and abnormal development of zebrafish embryos exposed to model toxicants (B, propranolol; C, malathion) for different observation times and different exposure concentrations. C, cyphosis, L, lordosis, POe, pericardial edema, SOe, sac-yolk edema. The dotted line indicates the theoretical straight back axis.
Fig. 4. Major effects of model toxicants on zebrafish embryo development, in relation to exposure concentration. (A) Effect of propranolol on heart rate at 48 hpf (mean±SD). (B) Effect of malathion on frequency of tail deformations (lordosis, cyphosis, and total of impaired embryos). (C) Effect of cadmium on the hatching time (HT50±IC95%); the symbols are the experimental data (control, white square; Cd treated, black circles) and the dotted line is the logarithmic regression. Same letters indicate no statistically different (ANOVA, Tukey's HSD). The asterisks indicate a significant difference between control (χ2). α
0.05.
Table 1.
Overview of the toxic bioassay guidelines based on the early life stage of freshwater fish

The OECD guidelines take into account the OECD members’ related national standards.
a Early life stage terminology (
Baxter, 1988): embryo, stage before hatching, pro-larva; stage between hatching and yolk-sac resorption; larva, stage between yolk-sac resorption and juvenile morphology.
b Time duration for tests with
D. rerio.c In proposal at ISO section TC147/SC5.
Table 2.
Main developmental period of early development of zebrafish and corresponding toxicological endpoints considered
a Defined by
Kimmel et al. (1995).
b Quantified endpoints.
Table 3.
Effects of model toxicants (propranolol, malathion, cadmium) on zebrafish early life stages

The values are the highest tested concentration (μM) without effect on the considered endpoint. —, indicates no-effect at the highest tested concentration (NOEC).
Table 4.
Review of the embryotoxic effects of malathion for fish

T (°C), temperature in Celsius degrees; h/dpf, hours/days postfecundation; EC50, concentration inducing 50% of effect; NOEC, no observable effect concentration; LOEC, lowest observable effect concentration; effect concentration;
, increase;
, decrease.