A review of cyanobacteria and cyanotoxins removal/inactivation in drinking water treatment

被引:257
作者
Westrick, Judy A. [1 ]
Szlag, David C. [1 ]
Southwell, Benjamin J. [1 ]
Sinclair, James [2 ]
机构
[1] Lake Super State Univ, Dept Chem & Environm Sci, Sault Ste Marie, MI 49783 USA
[2] US EPA, Off Groundwater & Drinking Water, Cincinnati, OH 45268 USA
关键词
Drinking water treatment; Cyanotoxins; Cyanobacteria; TOXIN MICROCYSTIN-LR; CHLORINE DIOXIDE; CYLINDROSPERMOPSIS-RACIBORSKII; BY-PRODUCTS; REMOVAL; DEGRADATION; OXIDATION; KINETICS; HEPATOTOXINS; SAXITOXINS;
D O I
10.1007/s00216-010-3709-5
中图分类号
Q5 [生物化学];
学科分类号
071010 ; 081704 ;
摘要
This review focuses on the efficiency of different water treatment processes for the removal of cyanotoxins from potable water. Although several investigators have studied full-scale drinking water processes to determine the efficiency of cyanotoxin inactivation, many of the studies were based on ancillary practice. In this context, "ancillary practice" refers to the removal or inactivation of cyanotoxins by standard daily operational procedures and without a contingency operational plan utilizing specific treatment barriers. In this review, "auxiliary practice" refers to the implementation of inactivation/removal treatment barriers or operational changes explicitly designed to minimize risk from toxin-forming algae and their toxins to make potable water. Furthermore, the best drinking water treatment practices are based on extension of the multibarrier approach to remove cyanotoxins from water. Cyanotoxins are considered natural contaminants that occur worldwide and specific classes of cyanotoxins have shown regional prevalence. For example, freshwaters in the Americas often show high concentrations of microcystin, anatoxin-a, and cylindrospermopsin, whereas Australian water sources often show high concentrations of microcystin, cylindrospermopsin, and saxitoxins. Other less frequently reported cyanotoxins include lyngbyatoxin A, debromoaplysiatoxin, and beta-N-methylamino-L-alanine. This review focuses on the commonly used unit processes and treatment trains to reduce the toxicity of four classes of cyanotoxins: the microcystins, cylindrospermopsin, anatoxin-a, and saxitoxins. The goal of this review is to inform the reader of how each unit process participates in a treatment train and how an auxiliary multibarrier approach to water treatment can provide safer water for the consumer.
引用
收藏
页码:1705 / 1714
页数:10
相关论文
共 81 条
[1]   Kinetics of reactions between chlorine and the cyanobacterial toxins microcystins [J].
Acero, JL ;
Rodriguez, E ;
Meriluoto, J .
WATER RESEARCH, 2005, 39 (08) :1628-1638
[2]   Degradation of microcystin-LR toxin by Fenton and photo-Fenton processes [J].
Bandala, ER ;
Martínez, D ;
Martínez, E ;
Dionysiou, DD .
TOXICON, 2004, 43 (07) :829-832
[3]   Uracil moiety is required for toxicity of the cyanobacterial hepatotoxin cylindrospermopsin [J].
Banker, R ;
Carmeli, S ;
Werman, M ;
Teltsch, B ;
Porat, R ;
Sukenik, A .
JOURNAL OF TOXICOLOGY AND ENVIRONMENTAL HEALTH-PART A, 2001, 62 (04) :281-288
[4]  
Börner T, 2005, AQUAT ECOL SER, V3, P25
[5]   Biodegradation of the cyanobacterial toxin microcystin LR in natural water and biologically active slow sand filters [J].
Bourne, DG ;
Blakeley, RL ;
Riddles, P ;
Jones, GJ .
WATER RESEARCH, 2006, 40 (06) :1294-1302
[6]   The mechanisms of potassium permanganate on algae removal [J].
Chen, JJ ;
Yeh, HH .
WATER RESEARCH, 2005, 39 (18) :4420-4428
[7]   Effects of oxidative and physical treatments on inactivation of Cylindrospermopsis raciborskii and removal of cylindrospermopsin [J].
Cheng, Xiaoliang ;
Shi, Honglan ;
Adams, Craig D. ;
Timmons, Terry ;
Ma, Yinfa .
WATER SCIENCE AND TECHNOLOGY, 2009, 60 (03) :689-697
[8]  
CHOI H, 2007, ENVIRON SCI TECHNOL, V41, P6
[9]  
CHOW CWK, 1997, AQUA, V46, P11
[10]   Microbial activity and bacterial community structure during degradation of microcystins [J].
Christoffersen, K ;
Lyck, S ;
Winding, A .
AQUATIC MICROBIAL ECOLOGY, 2002, 27 (02) :125-136