Johnson Andrew, Tanaka Hiroaki, Okayasu Yuji, Suzuki Yutaka
Centre for Ecology and Hydrology Wallingford, Wallingford, Oxfordshire, OX10 8BB, UK.
Environ Sci. 2007;14(6):319-29.
Both the UK and Japan are densely populated islands with relatively short rivers. Therefore, both countries are likely to be highly exposed to contaminants emanating from their human populations. This review considered how effective the different sewage treatment facilities of the two countries are at removing steroid estrogens from the effluent. The methods of estrogen analysis in sewage effluent, the number and importance of different sewage treatment types, and their apparent effectiveness at removing estrogens were all considered. In both countries, the activated sludge treatment was dominant in terms of people served and water discharged. The analytical techniques used by those studying estrogen concentrations in effluents in both countries were broadly similar. Activated sludge plant (ASP) effluent in the UK typically contained around 2 ng/L estradiol (E2) and 8 ng/L estrone (E1), while Japanese ASPs typically reported E2 as below detection, and 10 ng/L E1 in their effluents. When estrogenic bioassays were used in Japan, they typically record an estrogenic potency of 10 ng/L E2 equivalents. Even taking into account ethinylestradiol (EE2) (not found in Japanese effluents), the overall estrogenicity of British sewage effluents would appear to be the same as that of Japanese sewage effluents (around 10 ng/L E2 equivalents). This suggests that the ASPs serving the large urban communities in Japan and the UK would have effluent of similar estrogenic potencies. Less information is available about the more numerous biological (trickling) filter plants (BFP) in the UK and oxygen ditches (OD) in Japan which tend to serve smaller, more rural communities. The available data would suggest that the BFPs are significantly less efficient than the ODs at removing E1. This would suggest that in similar circumstances, British headwaters (where this sewage treatment plant (STP) type is often found) might be more at risk from endocrine disruption than their Japanese counterparts. Overall, the apparently higher incidence of endocrine disruption in British wild fish than in Japanese wild fish cannot be attributed to differences in the efficiency of their respective STPs.
英国和日本都是人口密集的岛屿国家,河流相对较短。因此,两国都可能高度暴露于来自其人口的污染物中。本综述探讨了两国不同的污水处理设施在去除污水中类固醇雌激素方面的效果如何。研究了污水中雌激素的分析方法、不同污水处理类型的数量和重要性,以及它们在去除雌激素方面的明显效果。在两国,活性污泥处理在服务人口和排放水量方面都占主导地位。两国研究污水中雌激素浓度的人员所使用的分析技术大致相似。英国活性污泥厂(ASP)的出水通常含有约2纳克/升的雌二醇(E2)和8纳克/升的雌酮(E1),而日本活性污泥厂的出水通常报告E2低于检测限,E1为10纳克/升。在日本使用雌激素生物测定法时,它们通常记录的雌激素效价为10纳克/升E2当量。即使考虑到乙炔雌二醇(EE2)(在日本污水中未发现),英国污水的总体雌激素活性似乎与日本污水相同(约10纳克/升E2当量)。这表明,服务于日本和英国大型城市社区的活性污泥厂的出水具有相似的雌激素活性。关于英国数量更多的生物(滴滤)滤池厂(BFP)和日本的氧化沟(OD)的信息较少,这些设施往往服务于规模较小、更偏远的社区。现有数据表明,生物滤池厂在去除E1方面的效率明显低于氧化沟。这表明,在类似情况下,英国上游水域(这种污水处理厂(STP)类型经常出现)可能比日本上游水域面临更大的内分泌干扰风险。总体而言,英国野生鱼类中内分泌干扰的发生率明显高于日本野生鱼类,这不能归因于各自污水处理厂效率的差异。