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硝化颗粒的微生物结构及其雌激素降解特性。

Microbial structure of nitrifying granules and their estrogens degradation properties.

作者信息

Wang X H, Ivanov V

机构信息

CH2M Hill Singapore, 150 Beach Road, 34th Gateway West, Singapore.

出版信息

Water Sci Technol. 2009;59(9):1855-62. doi: 10.2166/wst.2009.218.

Abstract

It has been known that endocrine disruption compounds such as natural estrogens estrone, 17beta-estradiol, estriol, and synthetic steroid 17a-ethynylestradiol can be degraded by nitrifying bacteria. The aim of this research was to test biodegradation of estrogens by microbial granules containing nitrifying bacteria. Cultivation of microbial granules was performed in sequencing batch reactor in model wastewater with carbon to nitrogen ratio of 100:30 by weight. After the system reached the steady state, the mean diameter of granules, sludge volume index of granular biomass, and biomass concentration were 0.6 mm, 22 mL g(-1) and 7 g L(-1), respectively. Nitrite was not detected in the effluent, and conversion of the consumed NH4+-N to NO3--N was 93%. Specific NO3--N production rate was 0.12 d(-1) at the constant NH4+- loading late of 0.9 g L d(-1). The presence of ammonium-oxidizing and nitrite-oxidizing bacteria was confirmed by fluorescence in situ hybridization with 16S rRNA-targeted oligonucleotide probes Nsm156 and Nit3. The estrogen biodegradation by the granules was conducted in batch experiments. The complete biodegradation of the mixture of estrone, 17beta-estradiol, estriol, and 17a-ethynylestradiol, 100 microg L(-1) each, by microbial granules was within 60 days. The order of biodegradation for estrogens by microbial granules was as follows: 17beta-estradiol-->estriol-->estrone-->17a-ethynylestradiol. The degradation rate constants of estrogens by microbial granules were 0.19 d(-1), 1.26 d(-1), 0.14 d(-1) and 0.11 d(-1) for estrone, 17beta-estradiol, estriol and 17a-ethynylestradiol, respectively.

摘要

已知内分泌干扰化合物,如天然雌激素雌酮、17β-雌二醇、雌三醇以及合成类固醇17α-乙炔基雌二醇,可被硝化细菌降解。本研究的目的是测试含硝化细菌的微生物颗粒对雌激素的生物降解作用。微生物颗粒的培养在序批式反应器中进行,使用碳氮比为100:30(重量比)的模拟废水。系统达到稳态后,颗粒的平均直径、颗粒生物质的污泥体积指数和生物质浓度分别为0.6毫米、22毫升/克和7克/升。出水未检测到亚硝酸盐,消耗的NH4+-N转化为NO3--N的转化率为93%。在恒定的NH4+负荷后期为0.9克/升·天的情况下,特定NO3--N产生率为0.12天-1。通过与16S rRNA靶向寡核苷酸探针Nsm156和Nit3进行荧光原位杂交,证实了氨氧化细菌和亚硝酸盐氧化细菌的存在。通过分批实验进行颗粒对雌激素的生物降解。微生物颗粒对雌酮、17β-雌二醇、雌三醇和17α-乙炔基雌二醇各100微克/升的混合物的完全生物降解在60天内完成。微生物颗粒对雌激素的生物降解顺序如下:17β-雌二醇>雌三醇>雌酮>17α-乙炔基雌二醇。微生物颗粒对雌酮、17β-雌二醇、雌三醇和17α-乙炔基雌二醇的降解速率常数分别为0.19天-1、1.26天-1、0.14天-1和0.11天-1。

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