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气提式三重循环生物膜反应器处理制药废水中的甾体雌激素 被引量:3

The Treatment of Estrogen Pharmaceutical Wastewater by Triplet Loop Airlift Biofilm Reactor
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摘要 为验证气提式三重循环生物膜反应器处理甾体雌激素的效能,建立了一套SPE/HPLC/MS/MS分析方法,对反应器进、出水中的甾体雌激素——甾酮(E1),17β-雌二醇(E2),雌三醇(E3)以及17α-乙炔基雌二醇(EE2)进行检测.该方法的加标回收率为88%~103%,精密度为4%~9%.该方法对E1,E2,E3和EE2的进水定量限(LOQ)分别为0.7,0.8,0.9和0.5ng/L;对出水的定量限分别为2.0,1.0,2.0和1.0ng/L.CODCr和氨氮容积负荷最高为7.5和1.6kg/(m^3·d),出水依然能够保持稳定.进水pH稳定在9.0~10.5,而反应器的pH一直稳定在9.0以下,体系对pH变化造成的冲击比较适应.同时,反应器内形成了稳定的NO2^- -N积累,CODCr和氨氮的去除率分别达到了70%和73%. An analytical method performed by solid-phase extraction (SPE) system with high pressure liquid chromatography and tandem mass spectrometry (HPLC/MS/MS) was developed for validating the efficiency of the triplet loop airlift biofilm reactor (TLABR). The steroid estrogens, including estrone (E1), 17β-estradiol (E2), estriol (E3) and 17α-ethynylestradiol (EE2), of influent and effluent of the bioreactor were determined by this method. The average recoveries ranged from 88% to 103% and the precision of the method ranged from 4% to 9%. The limit of quantification (LOQ) was determined at 0.7 ng/L for E1, 0.8 ng/L for E2, 0.9 ng/L for E3, and 0.5 ng/L for EE2 in influent, and 1.0 ng/L for E2 and EE2, and 2.0 ng/L for E1 and E3 in effluent. The effluent could still remain stable, when the influent volume load of CODer and NH3-N reached as high as 7.5 and 1.6 kg/(m^3·d) respectively. The influent pH was generally kept at 9.0 - 10.5, and the pH within the reactor remained stable at below 9.0. Therefore, the system could adapt to the impact of pH. Also, stable accumulation of NO2^- -N was formed in the reactor, and the removal rates of CODer and ammonia reached 70% and 73% , respectively.
出处 《环境科学研究》 EI CAS CSCD 北大核心 2006年第4期56-60,共5页 Research of Environmental Sciences
基金 北京市自然科学基金资助项目(8042007)
关键词 气提式三重循环生物膜反应器 SPE/HPLC/MS/MSW分析方法 甾体雌激素 短程硝化 triplet loop airlift biofilm reactor SPE/HPLC/MS/MS analytical method estrogen shortcut nitrification
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  • 1贾立敏,给水排水,1998年,24卷,6期
  • 2贝雷,油脂化学与工艺学,1989年
  • 3Tong Seongkhim,Einviron Toxicol Chem,1999年,18卷,2424页
  • 4Tong Zhou,Environ Toxicol Chem,1999年,18卷,2817页
  • 5Kelce W R,Abstract SOT Annual meeting,1995年,254页
  • 6Ternes T A, Stumpf M, Mueller J,et al. Behaviour and occurrence of estrogens in municipal sewage treatment plants - Ⅰ. Investigations in Germany, Canada and Brazil[ J ]. Sci Total Environ, 1999a,225: 81 - 90.
  • 7Tabata A, Kashiwa S, Ohnishi Y, et al. Estrogenic influence of estradiol- 17β,p- nonylphenol and bisphenol A on Japanese Medaka (Oryzias iatipes) at detected environmental concentrations [ J ]. Water Sci Technol, 2001,43(2) :109 - 116.
  • 8Kuch H M, Ballschmitter K. Determination of endocrinedisrupting phenolic compounds and estrogens in surface and drinking water by HRGC-(NCI) -MS in the picogram per liter range [ J ]. Environ Sci Technol, 2001,35 ( 15 ):3201 - 3206.
  • 9Larsson D G J, Adolfsson-Erici M, Parkkonen J, et al.Ethinyloestradiol-anundesired fish contraceptive? [ J ].Aquat Toxicol, 1999,45 ( 2 - 3 ) :91 - 97.
  • 10Colucci M S, Topp E. Persistence of estrogenic hormones in agricultural soils: Ⅱ. 17α-Ethynylestradiol [ J ]. J Environ Qual,2001,30 (6) :2077 - 2080.

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