Electrophoretic determination of estrogen-induced protein in fish exposed to synthetic and naturally occurring chemicals.

In a first step we investigated whether Leuciscus idus, a fish routinely used to assess the quality of surface water in Germany, is suitable to indicate the presence of endocrine-disrupting chemicals. An electrophoretic method was used to determine estrogen-induced protein in fish serum (presumed vitellogenin). This method was tested by exposing juvenile L. idus to 17 alpha-ethinylestradiol, 17 beta-estradiol and estrone. Nominal concentrations of the steroid were compared with concentrations determined analytically by using GC/MS techniques. Under flow-through conditions, 7 days of exposure to 6 ng/l EE2 significantly induced serum vitellogenin in juvenile L. idus. In juvenile rainbow trout (Oncorhynchus mykiss) 4 ng/l EE2 induced significantly elevated levels of serum vitellogenin. In Danio rerio oral application of 40 micrograms 4-nonylphenol/fish per day during a 3-week exposure period caused a major increase of serum vitellogenin. Physiological protein induction could also be measured in Abramis brama, Cyprinus carpio, Oncorhynchus mykiss, Perca fluviatilis, Rutilus rutilus obtained from natural habitats and in Rhodeus sericeus. The minimum amount of blood required for electrophoretic analysis was 1 microliter which should allow monitoring of small sized fish species as well as juvenile fish.

Endocrine disrupters in the aquatic environment.

Possible mechanisms to explain endocrine effects on reproduction and sex differentiation are presented for selected pharmaceuticals, agrochemicals, industrial chemicals and plant sterols which are known to be present in the aquatic environment. Disruptions of the hormonal coordination can be induced by xenobiotics on various levels of the hierachically organised endocrine system of vertebrates. Phthalate plasticisers, for example, may disrupt the pituitary control of gonadal functions; prenatal/larval exposure to synthetic estrogen impairs sex differentiation and neuroendocrine sexual determination of the central nervous system; phenylurea herbicides block the androgen receptor; the biotransformation of weakly estrogenic plant sterol components of paper mill wastewater (e.g. beta-sitosterol) may lead to androgenic compounds. The effect of hypolipidemic drugs on lipid homeostasis (peroxysom proliferation) is transmitted via a receptor protein that seems to be closely related to the endocrine system both functionally as well as phylogenetically; possible interferences with the neuroendocrine control of sex differentiation are also discussed. In invertebrates, tributyltin is known to effect the biosynthesis of steroidal sexual hormones. PCBs are suspected to be competitive inhibitors of the steroid catabolism. In order to identify potential risks caused by chemicals to the reproductive capacities of aquatic animals and to the quality of drinking water, methods should be established to detect endocrine disrupters at the various levels of the endocrine system.

Application of an androgen receptor assay for the characterisation of the androgenic or antiandrogenic activity of various phenylurea herbicides and their derivatives.

The potency of different substances for [3H]dihydrotestosterone ([3H]DHT) displacement from the bovine androgen receptor was tested. The phenylurea herbicide linuron and its derivative 3,4-dichloroaniline (3,4-DCA), which are found in sediments and surface waters, are known to displace bound testosterone from the rat androgen receptor. Because 3,4-DCA is rapidly taken up by fish and metabolised into 3,4-dichloroacetanilide (3,4-DCAc), it was investigated whether the displacement effects are attributable to 3,4-DCA or to 3,4-DCAc. The potency of 3,4-DCAc androgen receptor binding was compared with that of several phenylurea compounds. In a radioreceptor assay with calf uterus cytosol as androgen receptor preparation, the specific binding of [3H]DHT, the endogenous ligand, was completely displaceable by increasing concentrations of 3,4-DCAc. The relative binding affinities (RBA) of the various compounds were about 1/10(4) to 1/10(5) of that of DHT. 3,4-DCAc had the relative highest affinity (1.31 x 10(-4)), followed by linuron, 3,4-dichlorophenylurea, flutamide, 3,4-DCA and diuron with the lowest RBA (2.4 x 10(-5)). Hence the metabolism of xenobiotic compounds has to be considered to estimate potential ecotoxiocological effects. This test not only can be used to screen for androgen- and antiandrogen-like substances in environmentally relevant samples such as surface waters, but might also be applied for drug testing and for residue monitoring.