Department of Chemical and Environmental Engineering, University of Arizona, 1133 James E. Rogers Way, Tucson, AZ 85721, USA.
Environ Int. 2013 Sep;59:303-27. doi: 10.1016/j.envint.2013.06.013. Epub 2013 Jul 24.
Cyanobacteria are ubiquitous microorganisms considered as important contributors to the formation of Earth's atmosphere and nitrogen fixation. However, they are also frequently associated with toxic blooms. Indeed, the wide range of hepatotoxins, neurotoxins and dermatotoxins synthesized by these bacteria is a growing environmental and public health concern. This paper provides a state of the art on the occurrence and management of harmful cyanobacterial blooms in surface and drinking water, including economic impacts and research needs. Cyanobacterial blooms usually occur according to a combination of environmental factors e.g., nutrient concentration, water temperature, light intensity, salinity, water movement, stagnation and residence time, as well as several other variables. These environmental variables, in turn, have promoted the evolution and biosynthesis of strain-specific, gene-controlled metabolites (cyanotoxins) that are often harmful to aquatic and terrestrial life, including humans. Cyanotoxins are primarily produced intracellularly during the exponential growth phase. Release of toxins into water can occur during cell death or senescence but can also be due to evolutionary-derived or environmentally-mediated circumstances such as allelopathy or relatively sudden nutrient limitation. Consequently, when cyanobacterial blooms occur in drinking water resources, treatment has to remove both cyanobacteria (avoiding cell lysis and subsequent toxin release) and aqueous cyanotoxins previously released. Cells are usually removed with limited lysis by physical processes such as clarification or membrane filtration. However, aqueous toxins are usually removed by both physical retention, through adsorption on activated carbon or reverse osmosis, and chemical oxidation, through ozonation or chlorination. While the efficient oxidation of the more common cyanotoxins (microcystin, cylindrospermopsin, anatoxin and saxitoxin) has been extensively reported, the chemical and toxicological characterization of their by-products requires further investigation. In addition, future research should also investigate the removal of poorly considered cyanotoxins (β-methylamino-alanine, lyngbyatoxin or aplysiatoxin) as well as the economic impact of blooms.
蓝藻是普遍存在的微生物,被认为是地球大气形成和固氮的重要贡献者。然而,它们也经常与有毒水华有关。事实上,这些细菌合成的广泛范围的肝毒素、神经毒素和皮肤毒素是一个日益严重的环境和公共卫生问题。本文提供了有关地表水和饮用水中有害蓝藻水华的发生和管理的最新技术状况,包括经济影响和研究需求。蓝藻水华通常是根据环境因素的组合发生的,例如营养浓度、水温、光照强度、盐度、水的流动、停滞和停留时间,以及其他几个变量。这些环境变量反过来又促进了特定菌株、基因控制的代谢物(蓝藻毒素)的进化和生物合成,这些代谢物通常对水生和陆地生命,包括人类,都有害。蓝藻毒素主要在指数生长阶段在细胞内产生。毒素释放到水中可能发生在细胞死亡或衰老期间,但也可能由于进化衍生或环境介导的情况,如化感作用或相对突然的营养限制。因此,当蓝藻水华发生在饮用水资源中时,处理必须去除蓝藻(避免细胞裂解和随后的毒素释放)和以前释放的水中蓝藻毒素。细胞通常通过澄清或膜过滤等物理过程去除,同时保持有限的裂解。然而,水相毒素通常通过物理保留(通过活性炭吸附或反渗透)和化学氧化(通过臭氧化或氯化)去除。虽然已广泛报道了更常见的蓝藻毒素(微囊藻毒素、节旋藻毒素、anatoxin 和 saxitoxin)的有效氧化,但需要进一步研究其副产物的化学和毒理学特征。此外,未来的研究还应研究去除考虑不周的蓝藻毒素(β-甲基氨基-丙氨酸、lyngbyatoxin 或 aplysiatoxin)以及水华的经济影响。