Dietary intake estimations of organohalogen contaminants (dioxins, PCB, PBDE and chlorinated pesticides, e.g. DDT) based on Swedish market basket data.

By use of a Swedish Market basket study from 1999, in which foods were sampled from four regions, the dietary intake of persistent organic pollutants (POPs) was assessed. Based on earlier data, six food groups (fish, meat, dairy products, egg, fats/oils, and pastries; comprising 52 food items) were selected for POP analyses. Homogenates from these six groups were subjected to POP analyses and levels presented on dioxins (PCDD/PCDFs), dioxin-like PCBs, PCB-153, summation operatorPCBs, BDE-47, summation operatorPBDEs, DDE, summation operatorDDTs, HCB, summation operatorHCHs, and summation operatorchlordanes, after adjusting non-quantified levels to 1/2 LOQ. For all compounds, the fish homogenate contained the comparatively highest levels, on a fresh weight basis. Intake calculations based on the six food groups showed that summation operatorPCBs and summation operatorDDTs gave per capita intakes of 615 and 523 ng/day, respectively, that the estimated summation operatorPBDE intake was 51 ng/day and that of dioxins and dioxin-like PCBs was 96 pg WHO-TEQ/day. The estimated mean intakes were below (total-TEQ: 1.3 pg/kgbw/day) or well below (summation operatorDDTs: 8.9 ng/kgbw/day) internationally agreed intake limits (total-TEQ: 2 pg/kgbw/day; summation operatorDDTs: 10,000 ng/kgbw/day). A number of uncertainty factors, including analytical limitations due to low POP levels in food, give reason for caution in the use of the presented intake data. However, the intake estimations of dioxins, summation operatorPCBs and summation operatorPBDEs are well in accordance to calculations of POP intakes in Sweden made by alternate methods.

Bioaccumulation of selected PCBs in zebrafish, three-spined stickleback, and arctic char after three different routes of exposure.

The uptake and elimination of 20 structurally diverse tetra- to heptachlorinated biphenyls were studied in zebrafish (Danio rerio), three-spined stickleback (Gasterosteus aculeatus), and Arctic char (Salvelinus alpinus). The polychlorinated biphenyls (PCBs) were administered to the fish through food, intraperitoneal injection of peanut oil, or intraperitoneal implantation of silicone capsules. The retention of the PCBs in fish exposed through their diet was related with the substitution patterns of the compounds. Ortho-substituted congeners with no unsubstituted meta-para positions had high biomagnification potential. PCBs with low biomagnification all had adjacent vicinal hydrogens, indicating that congeners with this feature may have been metabolically eliminated. The retention characteristics of the PCBs in the diet-exposed and the injected zebrafish were similar. The pattern of congeners in Arctic char indicates that they have a lower capacity to metabolize PCBs compared to three-spined sticklebacks and zebrafish. The levels in the fish exposed to the PCBs through a silastic implant were negatively correlated with the hydrophobicity of the congeners. Most probably congener-specific release rates of the PCBs from the implants mask their retention characteristics. It is suggested that food, mimicking the natural intake route, should be used in PCB exposure studies to validate extrapolations to natural situations.

Male goldfish reproductive behaviour and physiology are severely affected by exogenous exposure to 17beta-estradiol.

Mature male goldfish were exposed to different concentrations of the natural hormone 17beta-estradiol (E2). Two methods of exposure were employed, via ingestion at 0, 1, 10 and 100 microg/g food and via the water at 0, 1 and 10 microg/l. The fish were exposed for 24-28 days during the spawning period. The males were then paired with an artificially induced, spawning female and their sexual behaviour was observed during a 15 min period. The physiological status of the fish was also examined with respect to GSI, presence of milt and spawning tubercles and the blood plasma concentration of E2. Despite the relatively short exposure period, exposure to physiological levels of E2 was shown to severely affect the male goldfish reproductive behaviour and physiology. In conclusion, the results from this study and the ability to interpret the effects on this well-studied species, show that the effects of E2, and possibly other estrogenic EDCs, have severe effects at several vital levels of male goldfish reproduction. The results also suggests that the hormone E2 can act as an endocrine disrupting chemical (EDC) in the environment.

Both ovarian fluid and female urine increase sex steroid hormone levels in mature Atlantic salmon (Salmo salar) male parr.

We compared the ability of urine and ovarian fluid from female Atlantic salmon (Salmo salar) to stimulate increase in plasma concentrations of sex steroid hormones in mature conspecific male parr (priming effect of the stimuli). We also tested the hypothesis that prostaglandin F2alpha (PGF2alpha) may act as a priming pheromone in the tested stimulants. Individual males of salmon parr were exposed to female urine, ovarian fluid, urine-ovarian fluid mix, or PGF2alpha. Plasma concentrations of the sex steroids of 17,20beta-dihydroxy-4-pregnen-3-one (17,20beta-P) were higher in males exposed to urine, ovarian fluids, and PGF2alpha compared to control males. PGF2alpha and a mixture of urine and ovarian fluid also gave increased concentrations of 11-ketotestosterone (11-KT). Concentrations of PGF2alpha were higher in ovarian fluids than in urine. A behavior test with mature male parr in a fluviarium showed neither attraction to nor avoidance of 0.1 nM PGF2alpha, but plasma levels of 17,20beta-P were significantly higher in exposed males compared to controls.

Endocrine, gonadal and behavioral responses of male crucian carp to the hormonal pheromone 17 alpha,20 beta-dihydroxy-4-pregnen-3-one.

The olfactory-mediated responses to the sex hormone 17 alpha,20 beta-dihydroxy-4-pregnen-3-one (17 alpha,20 beta-P) were studied in spermiated and regressed male crucian carp (Carassius carassius L.). The position and spontaneous locomotor activity of single male crucian carp were continuously recorded in an artificial stream. 17 alpha,20 beta-P (final concentration 10(-11) M) was supplied to one half and its ethanol carrier to the other half of the test area. Milt volume and gonadotropin (GtH-II) concentration in the plasma were also measured. The smell of 17 alpha,20 beta-P significantly increased both the GtH-II concentration in the plasma and the volume of strippable milt in spermiated crucian carp. Behaviorally, the side of the test area scented with 17 alpha,20 beta-P was significantly avoided by spermiated males. None of the described effects of 17 alpha,20 beta-P on spermiated males were observed for the regressed crucian carp. In view of the lack of response from regressed crucian carp we suggest that the observed avoidance behavior of 17 alpha,20 beta-P by spermiated males is a relevant reaction for spawning male crucian carp. The results are well in accordance with responses obtained in the closely related goldfish and gives strong support that the wild male crucian carp use the 17 alpha,20 beta-P signal from the females to prepare for the coming spawning.

Behavioural and endocrinological responses of mature male goldfish to the sex pheromone 17alpha,20beta-dihydroxy-4-pregnen-3-one in the water

The behavioural response of spermiated male goldfish to the sex pheromone 17alpha,20ss-dihydroxy-4-pregnen-3-one (17alpha,20ss-P) in the ambient water was measured using a computerized video-image analysis system. The position and spontaneous locomotor activity of single spermiated male goldfish were continuously recorded in an artificial stream. 17alpha,20ss-P (final concentration 10(-11) mol l-1) was supplied to one half and its ethanol carrier to the other half of the test area. The results showed that the fish spent significantly less time in water scented with 17alpha,20ss-P than in control water. Moreover, both the spontaneous locomotor activity and the gonadotropin II concentration in the plasma increased significantly because of contact with 17alpha,20ss-P in the ambient water. The swimming speed was unchanged, whether the fish resided in the 17alpha,20ss-P section or in the section without 17alpha,20ss-P added. In view of the complex dual hormone-pheromone system in goldfish, the possibility of an additional function of 17alpha,20ss-P is discussed. Because the release of the pheromone 17alpha,20ss-P occurs before ovulation and the level then drops drastically, we suggest that the avoidance reaction observed allows the sexually mature male to avoid misdirected courting of non-ovulated females and thus to continue its search for an ovulated female.

The effect of Cu (II) on the electro-olfactogram (EOG) of the Atlantic salmon (Salmo salar L) in artificial freshwater of varying inorganic carbon concentrations.

The effect of inorganic copper species was studied by recording the receptor potential, electro-olfactogram (EOG), from the olfactory epithelium of Atlantic salmon (Salmo salar L). In a series of experiments, the olfactory organ was irrigated with aqueous copper solutions with concentrations of the free cupric ion (Cu2+) ranging from 0.2 to 9.7 microM. The diverse copper species were created by varying the amount of bicarbonate (NaHCO3) in artificial freshwater solutions of equal total copper concentrations. In general, these copper solutions induced a slow depolarization of the baseline followed by a hyperpolarization. The amplitudes of these variations in baseline potentials increased with increasing concentrations of Cu2+ ion, i.e., decreasing concentrations of NaHCO3. Stimulating the olfactory epithelium with L-alanine during the copper exposure evoked atypical EOG responses. The amplitudes and form of the EOGs changed drastically with increasing Cu2+ concentrations, with significant correlation between the reduction in EOG amplitudes and the Cu2+ concentration. The results indicate that among the copper species tested the toxic effect is caused mainly by the dissolved Cu2+ ion. The results also suggest that the Cu2+ ion exerts its toxic effects on the transduction mechanisms of the olfactory receptor cells. The different EOG profiles obtained in response to varying Cu2+ concentrations indicate that this ion affects the transduction mechanisms at different stages.