Endocrine-disrupting effect of the ultraviolet filter benzophenone-3 in zebrafish, Danio rerio.

The chemical ultraviolet (UV) filter benzophenone-3 (BP-3) is suspected to be an endocrine disruptor based on results from in vitro and in vivo testing. However, studies including endpoints of endocrine adversity are lacking. The present study investigated the potential endocrine-disrupting effects of BP-3 in zebrafish (Danio rerio) in the Fish Sexual Development Test (Organisation for Economic Co-operation and Development TG 234) and a 12-d adult male zebrafish study. In TG 234, exposure from 0 d to 60 d posthatch caused a monotone dose-dependent skewing of the phenotypic sex ratio toward fewer males and more female zebrafish (no observed effect concentration [NOEC]: 191 µg/L, lowest observed effect concentration [LOEC]: 388 µg/L). Besides, gonad maturation was affected in both female fish (NOEC 191 µg/L, LOEC 388 µg/L) and male fish (NOEC 388 µg/L, LOEC 470 µg/L). Exposure to BP-3 did not affect the vitellogenin concentration in TG 234. After 12 d exposure of adult male zebrafish, a slight yet significant increase in the vitellogenin concentration was observed at 268 µg/L but not at 63 µg/L and 437 µg/L BP-3. Skewing of the sex ratio is a marker of an endocrine-mediated mechanism as well as a marker of adversity, and therefore the conclusion of the present study is that BP-3 is an endocrine-disrupting chemical in accordance with the World Health Organization's definition.

Comparison of zebrafish (Danio rerio) and fathead minnow (Pimephales promelas) as test species in the Fish Sexual Development Test (FSDT).

Results are presented from a validation (with 5 laboratories) of the Fish Sexual Development Test (FSDT) developed to detect endocrine disrupters (EDs) and included in the OECD (Organisation for Economic Co-operation and Development) working program. The aromatase-inhibiting fungicide prochloraz was tested in zebrafish (Danio rerio) and fathead minnow (Pimephales promelas). The fish were exposed during sexual differentiation and development from 0 to 60 days post hatch (dph). After exposure, the vitellogenin (VTG) concentrations were quantified in head/tail homogenate and the sex ratio was determined (defined as female, male, intersex or undifferentiated). NOEC/LOEC and EC(x) designs were compared to optimize the test approach. Results show that both species are highly sensitive to prochloraz during sexual development. They respond by skewing of the sex ratio towards male phenotype and by a VTG decline in females. The NOEC/LOEC approach is preferred because sex ratio is difficult to analyze with a regression model. The mean NOEC/LOEC for prochloraz on the sex ratio was 43.3/134 µg/L and 101/293 µg/L for zebrafish and fathead minnow, respectively. The mean NOEC/LOEC on the decline in female VTG concentration was 65/110 µg/L and ~30/68 µg/L respectively. In conclusion, zebrafish and fathead minnow are suitable species in the FSDT and their sexual differentiation is equally labile to EDs.

Effects of the fungicide prochloraz on the sexual development of zebrafish (Danio rerio).

Some chemicals have the potential to adversely affect sexual development through multiple endocrine actions. Prochloraz is an imidazole fungicide that displays diverse mechanisms of action, including inhibition of aromatase activity, inhibition of androgen synthesis, and antagonism of the androgen receptor. The objective of this study was to assess the effects of prochloraz on the sexual development of zebrafish (Danio rerio) in the Fish Sexual Development Test (FSDT) proposed as an OECD test guideline for detection of endocrine disruptors. Zebrafish were exposed to prochloraz (0, 16, 64 or 202 microg/L) for 60 days from 24 h post fertilization. Fish exposed to 202 microg/L prochloraz showed an increased proportion of males. Furthermore, the incidence of intersex and the stages of the gonads were altered in the treated fish compared to the control fish. A significant vitellogenin decrease was observed in both female and male zebrafish at an exposure concentration of 202 microg/L prochloraz. However, in the male fish, significantly increased vitellogenin concentrations were observed in the groups exposed to 16 or 64 microg/L prochloraz. This study serves as a part of the validation of the FSDT and indicates that the FSDT is suitable in detecting compounds with multiple endocrine actions. This is of importance in the assessment of the potential risk of existing and new chemicals.

Detection of endocrine disrupters: evaluation of a Fish Sexual Development Test (FSDT).

Managed by the Organisation for Economic Co-operation and Development (OECD), a comprehensive work is carried out in numerous laboratories to develop test guidelines for the detection of endocrine disrupting chemicals in humans, and various animal species. Development of tests to detect chemicals with endocrine disrupting properties in fish is a part of that work. A Fish Sexual Development Test (FSDT) (an extension of the existing OECD TG 210, fish early life stage toxicity test), proposed as an international test guideline for the detection of endocrine disrupting chemicals, was evaluated by water exposure of juvenile zebrafish to the three natural estrogens: estrone, 17beta-estradiol, and estriol and the synthetic androgen trenbolone (trenbolone acetate). As endpoints, vitellogenin induction and histological changes including changes in sex ratios were investigated. The sex ratio was significantly altered towards females from 49 ng/l estrone, 54 ng/l 17beta-estradiol and 22 microg/l estriol, respectively. An all male population was observed from exposure to 9.7 ng/l trenbolone and above. Significant vitellogenin induction in whole body homogenate was measured after exposure to 14 ng/l estrone, 54 ng/l 17beta-estradiol and 0.6 mug/l estriol, respectively. Significant vitellogenin reduction was measured after exposure to 193 ng/l trenbolone or higher. The present results provide strong evidence that the FSDT is a sensitive test toward estrogenic and especially androgenic exposure and the validation of the FSDT as an OECD test guideline should continue.

Gonad development and vitellogenin production in zebrafish (Danio rerio) exposed to ethinylestradiol and methyltestosterone.

In a partial life-cycle test, the impact of 17alpha-ethinylestradiol (EE2) and 17alpha-methyltestosterone (MT) on juvenile zebrafish was evaluated by use of vitellogenin measurements and gonadal development. Exposure to EE2 (1-25 ng/l) resulted in a dose-dependent increase in vitellogenin production starting at 2 ng/l. Significant changes in sex ratios in female direction were detected at 1 ng/l, with complete sex reversal taking place after exposure to 2 ng/l. No intersex fish were observed after exposure to EE2. Exposure to MT resulted in decreased vitellogenin concentrations. Complete sex reversal was detected in all MT concentrations used (26-1000 ng/l). A large proportion of intersex fish was observed after exposure to 1000 ng MT/l. The period of gonadal sex reversal in non-exposed zebrafish was also studied. The main morphological features of the transformation of ovaries into testis were observed 4-5 weeks after hatching.

Effects of exposure to 17alpha-ethinylestradiol during early development on sexual differentiation and induction of vitellogenin in zebrafish (Danio rerio).

To determine the critical stage of zebrafish development where exposure to xenoestrogens can affect sex ratio and vitellogenin induction, zebrafish (Danio rerio) were exposed to 17alpha-ethinylestradiol (actual concentration 15.4+/-1.4 ng EE2/l) during early development: from fertilisation to hatch; hatch to 10 days post hatch (dph); 10-20 dph; 20-30 dph; 20-40 dph; 20-60 dph; fertilisation to 25 dph; or hatch to 60 dph. Vitellogenin was measured in whole body homogenate 30 dph by ELISA and sex ratio was determined 60 dph by histological examination of the gonads. All exposure periods significantly induced vitellogenin synthesis and affected the sex differentiation leading to development of ovo-testis or complete feminisation of the exposed fish depending on exposure period. Complete sex reversal was obtained in groups exposed from 20 to 60 dph and hatch to 60 dph. The half-life for degradation of vitellogenin was calculated. Juvenile zebrafish were exposed to 15.4+/-1.4 ng EE2/l (actual concentration) from fertilisation to 25 dph and transferred to clean water, after which weekly measurements of vitellogenin concentration in whole body homogenate were performed until day 46 post hatch. The half-life of vitellogenin was 2.4 days.