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生物方法去除饮用水中蓝藻毒素的潜力:综述。

Potential of biological approaches for cyanotoxin removal from drinking water: A review.

机构信息

INRS-ETE, Université du Québec, 490, Rue de la Couronne, Québec, Canada G1K 9A9.

INRS-ETE, Université du Québec, 490, Rue de la Couronne, Québec, Canada G1K 9A9; Department of Civil Engineering, Lassonde School of Engineering, York University, North York, Toronto, Ontario, Canada M3J 1P3.

出版信息

Ecotoxicol Environ Saf. 2019 May 15;172:488-503. doi: 10.1016/j.ecoenv.2019.01.066. Epub 2019 Feb 6.

Abstract

Biological treatment of cyanotoxins has gained much importance in recent decades and holds a promise to work in coordination with various physicochemical treatments. In drinking water treatment plants (DWTPs), effective removal of cyanotoxins with reduced toxicity is a primary concern. Commonly used treatments, such as ozonation, chlorination or activated carbon, undergo significant changes in their operating conditions (mainly dosage) to counter the variation in different environmental parameters, such as pH, temperature, and high cyanotoxin concentration. Presence of metal ions, natural organic matter (NOM), and other chemicals demand higher dosage and hence affect the activation energy to efficiently break down the cyanotoxin molecule. Due to these higher dose requirements, the treatment leads to the formation of toxic metabolites at a concentration high enough to break the guideline values. Biological methods of cyanotoxin removal proceed via enzymatic pathway where the protein-encoding genes are often responsible for the compound breakdown into non-toxic metabolites. However, in contrast to the chemical treatment, the biological processes advance at a much slower kinetic rate, predominantly due to a longer onset period (high lag phase). In fact, more than 90% of the studies reported on the biological degradation of the cyanotoxins attribute the biodegradation to the bacterial suspension. This suspended growth limits the mass transfer kinetics due to the presence of metal ions, NOMs and, other oxidizable matter, which further prolongs the lag phase and makes biological process toxic-free, albeit less efficient. In this context, this review attempts to bring out the importance of the attached growth mechanism, in particular, the biofilm-based treatment approaches which can enhance the biodegradation rate.

摘要

近年来,生物处理氰化物受到了极大的重视,并有望与各种物理化学处理协同工作。在饮用水处理厂 (DWTP) 中,有效去除具有降低毒性的氰化物是首要关注的问题。常用的处理方法,如臭氧氧化、氯化或活性炭,其操作条件(主要是剂量)会发生显著变化,以应对不同环境参数(如 pH 值、温度和高浓度氰化物)的变化。金属离子、天然有机物 (NOM) 和其他化学物质的存在需要更高的剂量,因此会影响到有效分解氰化物分子的活化能。由于这些更高的剂量要求,处理会导致在足够高的浓度下形成有毒代谢物,从而打破指导值。去除氰化物的生物方法是通过酶促途径进行的,其中蛋白质编码基因通常负责将化合物分解成无毒代谢物。然而,与化学处理相比,生物过程的动力学速率要慢得多,主要是由于起始期较长(高迟滞期)。事实上,超过 90%的关于氰化物生物降解的研究都归因于细菌悬浮液的生物降解。这种悬浮生长由于存在金属离子、NOM 和其他可氧化物质而限制了质量传递动力学,这进一步延长了迟滞期,使生物过程无毒,尽管效率较低。在这方面,本综述试图强调附着生长机制的重要性,特别是基于生物膜的处理方法,可以提高生物降解速率。

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