An estrogen receptor （ER）/androgen receptor （AR） ligand competitive binding assay （ER/AR-binding assay） and chemical analyses were used to evaluate the endocrine disrupting chemicals （EDCs） behavior of two mun...An estrogen receptor （ER）/androgen receptor （AR） ligand competitive binding assay （ER/AR-binding assay） and chemical analyses were used to evaluate the endocrine disrupting chemicals （EDCs） behavior of two municipal wastewater treatment plants （WWTPs） （K and S）. In the influents, estrone （E 1）, androsterone （A）, androstenedione （AD）, BPA （bisphenol A）, NP （nonylphenol） and daidzein （DZ） were detected in high amounts with subsequent 24 h-average concentrations of 350, 1000, 29, 1300, 3900, and 5700 ng/L in K-WWTP and of 310, 620, 59, 1600, 2600, and 8400 ng/L in S-WWTP. The estrogenic （androgenic） activity as 17β-estradiol （E2） equivalents （EEQ） or testosterone （Te） equivalents （TEQ） was consequently 620 ng E2/L （570 ng Te/L） and 580 ng E2/L （800 ng Te/L） for the two WWTPs. The removal efficiencies of the above mentioned sole target chemicals were 51%-100% for K-WWTP and 55.6%-100% for S-WWTP. The removal efficiencies of EEQ were about 73% for both WWTPs, while the removal efficiencies of TEQ were 62.1% for K-WWTP and 98.4% for S-WWTP. In addition, chemical-derived EEQ were about 1.2%-52.4% of those by ER-binding assay for K-WWTP and the corresponding ratios were 1.3%-83.3% for S-WWTP, while chemical derived TEQ were less than 3% of values measured by the AR-binding assay for both WWTPs.展开更多
文摘An estrogen receptor （ER）/androgen receptor （AR） ligand competitive binding assay （ER/AR-binding assay） and chemical analyses were used to evaluate the endocrine disrupting chemicals （EDCs） behavior of two municipal wastewater treatment plants （WWTPs） （K and S）. In the influents, estrone （E 1）, androsterone （A）, androstenedione （AD）, BPA （bisphenol A）, NP （nonylphenol） and daidzein （DZ） were detected in high amounts with subsequent 24 h-average concentrations of 350, 1000, 29, 1300, 3900, and 5700 ng/L in K-WWTP and of 310, 620, 59, 1600, 2600, and 8400 ng/L in S-WWTP. The estrogenic （androgenic） activity as 17β-estradiol （E2） equivalents （EEQ） or testosterone （Te） equivalents （TEQ） was consequently 620 ng E2/L （570 ng Te/L） and 580 ng E2/L （800 ng Te/L） for the two WWTPs. The removal efficiencies of the above mentioned sole target chemicals were 51%-100% for K-WWTP and 55.6%-100% for S-WWTP. The removal efficiencies of EEQ were about 73% for both WWTPs, while the removal efficiencies of TEQ were 62.1% for K-WWTP and 98.4% for S-WWTP. In addition, chemical-derived EEQ were about 1.2%-52.4% of those by ER-binding assay for K-WWTP and the corresponding ratios were 1.3%-83.3% for S-WWTP, while chemical derived TEQ were less than 3% of values measured by the AR-binding assay for both WWTPs.
