、周海东1, 王晓琳2, 高密军2, 黄 霞1(1.清华大学环境科学与工程系环境模拟与污染控制国家重点联合实验室,北京100084;2.北京科技大学土木与环境工程学院,北京100083) : 以三种酚类化合物(4-OP、4-n-NP、BPA)、五种雌激素(E1、E2、E3、17α-E2、EE2)为目标物,对其在北京市三个污水处理厂进、出水中的浓度及工艺流程中的分布、迁移进行了研究。结果表明,污水处理厂出水中浓度最高的物质是BPA、EE2,分别为(56~140)、(78~115)ng/L。BPA和天然雌激素(17α-E2除外)主要被生物降解去除,而对EE2的去除主要发生在初级处理过程,去除率约为63%。两种烷基酚在污水处理厂并不能被有效去除。与欧美国家、日本等相比,北京市污水处理厂进、出水中的内分泌干扰物浓度偏高,尤其是出水中的雌激素浓度较高,具有一定的环境风险。 : 城市污水; 内分泌干扰物; 分布; 雌激素:X703 :C :1000-4602(2009)23-0075-04 :(20721140019)DistributionofEndocrineDisruptingCompoundsinWastewaterTreatmentPlantsofBeijingZHOUHai-dong1, WANGXiao-lin2, GAOMi-jun2, HUANGXia1(1.StateKeyLaboratoryofEnvironmentalSimulationandPollutionControl,DepartmentofEnvironmentalScienceandEngineering,TsinghuaUniversity,Beijing100084,China;2.SchoolofCivilandEnvironmentalEngineering,UniversityofScienceandTechnologyBeijing,Beijing100083,China) Abstract: Theeightkindsofselectedendocrinedisruptingcompounds(EDCs)composedofthreephenoliccompoundsandfiveestrogenswereinvestigatedinthreewastewatertreatmentplants(WWTPs)ofBeijing.TheseEDCsinclude4-octylphenol(4-OP),4-n-nonylphenol(4-n-NP),bisphenolA(BPA),estrone(E1),estradiol(E2),estriol(E3),17α-estradiol(17α-E2)and17α-ethinylestradi-ol(EE2).BPAandEE2areonthetoplistofselectedEDCsintheeffluentwithconcentrationsof56to140ng/Land78to115ng/L,respectively.BPAandnaturalestrogens(except17α-E2)areremovedmainlybybiologicaltreatmentwhiletheremovalofEE2takesplacemainlyinprimarytreatmentwiththeremovalrateofabout63%.Besides,theprocessesofWWTPsstudiedcannotremovethetwoalkylphe-nols(4-OPand4-n-NP)efficiently.ComparedwiththoseofWWTPsinUSA,EuropeandJapan,EDCsconcentrationsintheinfluentandeffluentofWWTPsstudied,especiallyeffluentestrogens,arehigher,whichshowsanenvironmentalrisk. Keywords: municipalsewage; endocrinedisruptingcompounds(EDCs); distribution; es-trogen·75·第25卷 第23期2009年12月 中国给水排水CHINAWATERWASTEWATER Vol.25No.23Dec.2009 (EDCs),,、、、、[1]。EDCs,(APnEO)、[(OP),(NP)]、A(BPA)[(E1)、(E2)、(E3)(EE2)]。EDCs。[2、3],EDCs,ng/L~μg/L。EDCs,EDCs、。,,(4-OP、4-n-NP、BPA)(E1、E2、E3、17α-E2、EE2),、,。1 试验部分1.1 A40×104m3/d,,A2/O,A2/O,,107km2,、、。B100×104m3/d,、、,A/O。C20×104m3/d,,62%,38%,。1.2 ,,。A:(QH1)、(QH2)、(QH3)、(QH4)、(QH5)、(QH6)。B:(GB1)、(GB2)、(GB3)、(GB4)、(GB5)、(GB6)。C:(JX1)、(JX2)、(JX3)、(JX4)、(JX5)、(JX6)、(JX7)。,2.5~4.0L,,H2SO4pH3.0,4℃。48h。1.3 EDCs1.3.1 98%,,-18℃。、、(MTBE)HPLC,,。1.3.2 1L,。10mL/(7∶3),。50μL100μLBSTFA,70℃60min,、100μL,GC/MS。VF-5(30m×0.25mmI.D.×0.25μm)。GC:1μL,250℃;:100℃1min,10℃/min200℃,15℃/min260℃,3℃/min300℃2min。MS:280℃,250℃,EI,TICSIM。0.3~13.8ng/L,0.9~46.1ng/L,65.9%~105.2%。2 结果与讨论2.1 、EDCsEDCs,AEDCs2843.0ng/L,573.7ng/L,79.8%;BEDCs3222.3ng/L,936.9ng/L,70.9%;CEDCs2083.4ng/L,83.2ng/L,96.0%。·76·第25卷 第23期 中国给水排水 。C,,;B,,17α-E2,。,E1E3,[4]。E1A,B,C,B253.8ng/L,67.3%;A181.2ng/L,80.1%;A、BEDCs,E1,EDCs30%。BPAB,1416.7ng/L,600ng/L,,90%。,,B,4-n-NP14.6%,4-OP10%;,40%。[5~7],、EDCs,,。2.2 EDCsEDCs1。1 EDCsTab.1 DistributionofEDCsalongthreeBeijingWWTPsng·L-14-OP4-n-NPBPAE117α-E2E2E3EE2AQH1159.9101.3699.9911.590.9131.0505.5243.1QH2165.486.2800.4747.285.7104.6448.282.6QH3132.471.9120.7403.977.9145.9173.871.3QH4102.359.4129.1223.560.9172.287.379.9QH5108.572.1107.2138.8098.118.264.9QH695.751.760.6181.249.447.7087.4BGB1114.468.71416.7775.4119.687.5464.4175.6GB2135.662.51965.6753.079.478.9441.7122.3GB3101.464.91588.7749.769.569.1250.981.7GB4118.959.8679.8209.9300.988.9194.1119.0GB591.658.6234.1171.5173.854.971.270.1GB6103.758.7138.4253.8144.264.361.3112.4CJX138.543.9806.3132.022.431.7134.9873.8JX250.656.7917.6114.112.621.9119.2127.5JX336.744.4787.1114.015.830.0133.5163.1JX421.735.8383.726.19.715.449.526.1JX512.220.8203.410.23.86.327.344.4JX614.315.5127.110.91.32.59.263.0JX710.815.556.91.200077.9 ,10%,35%,,,。,,4-OP,3%~35%,APnEO。B,4-n-NP、4-OP,。B,AC,AP[8]。1,,4-OP、4-n-NP20%,A、CEDCs。C4-n-NP、4-OP,。BPA,,A、B。,BPA90%,,BPA·77·周海东,等:北京污水厂进、出水中内分泌干扰物的分布第25卷 第23期,。,E183.2%,11.6%,71.6%,。E395.3%,19.5%,75.8%;E262.3%,15.5%,46.8%。A、CE388%,E270%,E2E3。B,E2E3,,。1,E2,E2、,E2E2,E2,,E2,E2,,E2。17α-E2C,A,B,,,,。EE2,63%,,67%,,,,EE2。3 结论,(4-OP、4-n-NP、BPA)(E1、E2、E3、17α-E2、EE2),2083~3300ng/L,83~950ng/L,70%。BPA、E1、E3、EE2,BPA、EE2。BPA(17α-E2),BPA、E1E390%、83%95%,E262%。EE2,63%。。、,、EDCs,,。致谢:日本京都大学工学研究科的津野洋教授和坂本昌则先生为本研究的EDCs分析提供了一定的技术帮助。:[1] KavlockRJ.OverviewofendocrinedisruptorresearchactivityintheUnitedStates[J].Chemosphere,1999,39(8):1227-1236.[2] SarmahAK,NorthcottGL,LeuschFDL,etal.Asur-veyofendocrinedisruptingchemicals(EDCs)inmunici-palsewageandanimalwasteeffluentsintheWaikatore-gionofNewZealand[J].SciTotalEnviron,2006,355(1-3):135-144.[3] AndersenH,SiegristH,Halling-SorensenB,etal.Fateofestrogensinamunicipalsewagetreatmentplant[J].En-vironSciTechnol,2003,37(18):4021-4026.[4] YingGG,KookanaRS,RuYJ.Occurrenceandfateofhormonesteroidsintheenvironment[J].EnvironInt,2002,28(6):545-551.[5] NakadaN,TanishimaT,ShinoharaH,etal.Pharmaceuti-calchemicalsandendocrinedisruptersinmunicipalwastewaterinTokyoandtheirremovalduringactivatedsludgetreatment[J].WaterRes,2006,40(17):3297-3303.[6] La