Chatziefthimiou Aspassia D, Metcalf James S, Glover W Broc, Banack Sandra A, Dargham Soha R, Richer Renee A
Weill Cornell Medicine - Qatar, Qatar Foundation, Education City, PO Box 24144, Doha, Qatar.
Institute for Ethnomedicine, PO Box 3464, Jackson, WY 83001, USA.
Toxicon. 2016 May;114:75-84. doi: 10.1016/j.toxicon.2016.02.016. Epub 2016 Feb 24.
Desert environments and drylands experience a drastic scarcity of water resources. To alleviate dependence on freshwater for drinking water needs, countries have invested in infrastructure development of desalination plants. Collectively, the countries of the Arabian Gulf produce 45% of the world's desalinated water, which is stored in dams, mega-reservoirs and secondary house water tanks to secure drinking water beyond daily needs. Improper storage practices of drinking water in impoundments concomitant with increased temperatures and light penetration may promote the growth of cyanobacteria and accumulation of cyanotoxins. To shed light on this previously unexplored research area in desert environments, we examined drinking and irrigation water of urban and rural environments to determine whether cyanobacteria and cyanotoxins are present, and what are the storage and transportation practices as well as the environmental parameters that best predict their presence. Cyanobacteria were present in 80% of the urban and 33% of the rural water impoundments. Neurotoxins BMAA, DAB and anatoxin-a(S) were not detected in any of the water samples, although they have been found to accumulate in the desert soils, which suggests a bioaccumulation potential if they are leached into the aquifer. A toxic BMAA isomer, AEG, was found in 91.7% of rural but none of the urban water samples and correlated with water-truck transportation, light exposure and chloride ions. The hepatotoxic cyanotoxin microcystin-LR was present in the majority of all sampled impoundments, surpassing the WHO provisional guideline of 1 μg/l in 30% of the urban water tanks. Finally, we discuss possible management strategies to improve storage and transportation practices in order to minimize exposure to cyanobacteria and cyanotoxins, and actions to promote sustainable use of limited water resources.
沙漠环境和旱地面临着水资源极度匮乏的问题。为了减少饮用水对淡水的依赖,各国纷纷投资建设海水淡化厂的基础设施。阿拉伯海湾国家合计生产了全球45%的淡化水,这些水被储存在大坝、大型水库和家庭二级水箱中,以确保满足日常需求之外的饮用水供应。蓄水设施中饮用水储存方式不当,再加上温度升高和光线穿透增加,可能会促进蓝藻生长和蓝藻毒素积累。为了深入了解这个此前在沙漠环境中未被探索的研究领域,我们对城乡环境中的饮用水和灌溉用水进行了检测,以确定是否存在蓝藻和蓝藻毒素,以及最佳预测其存在的储存、运输方式和环境参数。80%的城市蓄水设施和33%的农村蓄水设施中存在蓝藻。虽然在沙漠土壤中发现神经毒素β-甲基氨基-L-丙氨酸(BMAA)、二氨基丁酸(DAB)和类毒素-a(S)会积累,但在任何水样中均未检测到它们,这表明如果它们渗入含水层,可能具有生物累积潜力。一种有毒的BMAA异构体,即2-氨基乙磺酸(AEG),在91.7%的农村水样中被发现,但城市水样中均未检测到,且与水车运输、光照和氯离子有关。大多数采样蓄水设施中都存在肝毒性蓝藻毒素微囊藻毒素-LR,30%的城市水箱中的微囊藻毒素-LR含量超过了世界卫生组织1微克/升的临时指导值。最后,我们讨论了可能的管理策略,以改善储存和运输方式,从而尽量减少接触蓝藻和蓝藻毒素,并采取行动促进有限水资源的可持续利用。