Exposure to 17 alpha-ethinylestradiol and bisphenol A--effects on larval moulting and mouthpart structure of Chironomus riparius.

The effects of the endocrine-disrupting chemicals 17alpha-ethinylestradiol (EE) and bisphenol A (BPA) on the development of the aquatic life-cycle stages (eggs to pupa) of Chironomus riparius were investigated. The test species was exposed to sublethal concentrations of EE and BPA (10 ng/L-1mg/L) and effects on larval weight and moulting success were recorded. In addition, three mouthpart structures (mentum, mandibles, and pecten epipharyngis) present on the head capsules of fourth-instar larvae were examined for structural deformities. Moulting was delayed and larval wet weight significantly reduced (P<0.05) at the highest treatment concentration (1mg/L) of both chemicals. No significant effect on either of these parameters was noted in the remaining treatments. However, deformities in the mouthparts of C. riparius were observed at very low exposure concentrations (10 ng/L), although the incidence of deformities was greater in the chironomids exposed to EE than BPA. Effects were mainly associated with the mentum, with statistically significant differences in median deformity score (Kruskal-Wallis P<0.001) recorded for both chemicals. At similar effect concentrations, an increased percentage of exposed animals had deformities of the pecten epipharyngis; however, little evidence of deformity was noted for the mandibles. At high concentrations, where moulting and wet weight were affected, no incidence of mouthpart deformity was noted. The relevance of these results in relation to the identification of an "endocrine-sensitive" endpoint for invertebrates is discussed.

Population responses of the freshwater amphipod Gammarus pulex (L.) to an environmental estrogen, 17alpha-ethinylestradiol.

The effects of the environmental estrogen 17alpha-ethinylestradiol (EE) on mixed populations of 90 individual Gammarus pulex were examined following a 100-d exposure in a flow-through system. Counts of total animal numbers revealed that, in all treatment groups, population size dramatically increased due to recruitment, with neonate and juvenile gammarids the most abundant. At concentrations of 1 and 10 microg/L EE, the recorded mean population sizes of 385 and 411, respectively, were significantly greater (p = 0.018) than the control (169). Mean population sizes in the solvent control (257) and 100 ng/L EE treatment (267) were not significantly different (p > 0.05) from the control. In addition to total counts, detailed image analysis of each individual animal allowed the assessment of length-frequency distributions, adult sex ratio, number of precopula pairs/ovigerous females, and measurement of secondary antenna and gnathopod length (secondary sex characteristics). The sex ratio of adults at 100 ng, 1 microg, and 10 microg/L EE was greater than 2:1 (female:male), and significantly more females (p = 0.008) were recorded at these concentrations compared with the control. The number of male adults, precopula guarding pairs, and ovigerous females did not differ between treatments (p > 0.05). Secondary antennal and gnathopod length in males was consistently greater than in females (p < or = 0.001), but comparison between groups revealed no difference in these parameters.