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P-nitrophenol biodegradation by aerobic microbial granules.

机构信息

Biofouling and Biofilm Processes Section, Water and Steam Chemistry Division, Bhabha Atomic Research Centre, Kalpakkam 603102, Tamil Nadu, India.

出版信息

Appl Biochem Biotechnol. 2012 Jul;167(6):1569-77. doi: 10.1007/s12010-012-9594-y. Epub 2012 Feb 21.

Abstract

Mixed microbial consortia in the form of aerobic microbial granules (AMG) capable of xenobiotic degradation can be developed from activated sludge or by adaptation of microbial granules pre-grown on labile carbon sources. Both of these approaches were investigated for the cultivation of AMG capable of p-nitrophenol (PNP) biodegradation. Attempts to cultivate AMG from activated sludge using PNP as the sole carbon source were not successful due to poor microbial growth and washout of the inoculated activated sludge. As part of the second approach, parallel sequencing batch reactors (SBRs) were inoculated with pre-grown AMG and operated by feeding both acetate and PNP together (RA), PNP alone (RB) or acetate alone (RC). Acetate/PNP mineralization and nitrification were monitored in the three SBRs. PNP biodegradation was quickly established in both RA and RB. PNP removal rates were found to be 47 and 55 mg g VSS(-1) h(-1) in RA and RB, respectively. PNP biodegradation during the SBR cycle consisted of distinct lag, exponential and deceleration phases. However, with higher concentrations of PNP (>50 mg l(-1)), disintegration of granules was observed in RA and RB. When PNP was the sole carbon source, it inhibited the development of aerobic granules from activated sludge and caused disintegration of pre-cultivated aerobic granules. When PNP was the co-substrate along with acetate, the structural and functional integrity (including nitrification) of the granular sludge was maintained. This report highlights the importance of a labile co-substrate for maintaining the physical and functional integrity of granular sludge, when used for toxic waste degradation.

摘要

能够降解异生物质的好氧微生物颗粒(AMG)的混合微生物群落可以从活性污泥中开发,也可以通过适应预先在易生物降解碳源上生长的微生物颗粒来开发。这两种方法都被用于培养能够降解对硝基苯酚(PNP)的 AMG。由于微生物生长不良和接种的活性污泥被冲洗掉,尝试使用 PNP 作为唯一碳源从活性污泥中培养 AMG 没有成功。作为第二种方法的一部分,平行序批式反应器(SBR)用预先生长的 AMG 接种,并通过同时进料乙酸盐和 PNP(RA)、单独进料 PNP(RB)或单独进料乙酸盐(RC)进行操作。在三个 SBR 中监测乙酸盐/PNP 的矿化和硝化作用。在 RA 和 RB 中,PNP 生物降解迅速建立。在 RA 和 RB 中,PNP 的去除率分别为 47 和 55 mg g VSS(-1) h(-1)。在 SBR 周期中,PNP 生物降解由明显的迟滞、指数和减速阶段组成。然而,当 PNP 浓度较高(>50 mg l(-1))时,在 RA 和 RB 中观察到颗粒的崩解。当 PNP 是唯一的碳源时,它抑制了活性污泥中好氧颗粒的发育,并导致预先培养的好氧颗粒崩解。当 PNP 与乙酸盐作为共底物时,颗粒污泥的结构和功能完整性(包括硝化作用)得以维持。本报告强调了在使用有毒废物降解时,易生物降解共底物对于维持颗粒污泥的物理和功能完整性的重要性。

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