超富营养化Mahakanadarawa和Nachchaduwa水库中微囊藻毒素和柱体精子素的共存

M. Gunawardana, M. M. Wijesooriya, G. Randima, K. Atapaththu, K. Sanjaya, K. Masakorala, S. W. Gamage
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引用次数: 0

摘要

微囊藻毒素(MCs)和圆柱形精子蛋白酶(CYN)是热带淡水中蓝藻产生的最丰富的毒素。2020年9月,研究了斯里兰卡Anuradhapura地区Mahakanadarawa和Nachchaduwa两个多用途水库MC和CYN的空间分布。对每个水库25个采样点的14个水质参数、浮游植物组成、叶绿素- a、MC和CYN浓度进行了三份分析。两个水库均处于富营养化状态。微囊藻为优势蓝藻,Mahakanadarawa为0 ~ 3.75 × 10.3 cells /mL, Nachchaduwa为1 ~ 7 × 10.3 cell/mL。除微囊藻外,未观察到其他可能产生mc的蓝藻。在Mahakanadarawa, MC的检测范围为0.11-1.63µg/L,高于世界卫生组织饮用水允许水平(1.0µg/L)。虽然Nachchaduwa微囊藻细胞密度较高,但其MC浓度较低(0.06 ~ 0.17µg/L)。Nachchaduwa的CYN浓度高于世界卫生组织饮用水允许值(0.7µg/L)。Nachchaduwa为0.20 ~ 1.02µg/L, Mahakanadarawa为0.03 ~ 0.08µg/L。我们没有在两个储层中观察到任何潜在的产cyn的蓝藻。两个水库MC的空间分布格局与微囊藻细胞密度没有关系。虽然水的大部分理化性质表明适合饮用,但高浓度MC和CYN的共存表明它们不适合饮用。因此,本研究强调了在两个水库中对蓝藻毒素进行路由检测的必要性。此外,我们的研究结果为依赖Mahakanadarawa和Nachchaduwa水库饮用、灌溉和渔业的当地社区带来了潜在的健康风险。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Co-occurrence of microcystin and cylindrospermopsin in hypereutrophic Mahakanadarawa and Nachchaduwa reservoirs
Microcystins (MCs) and cylindrospermopsin (CYN) are the most abundant toxins produced by cyanobacteria in tropical freshwaters. We studied the spatial distribution of MC and CYN in two multipurpose reservoirs, Mahakanadarawa and Nachchaduwa in Anuradhapura district in Sri Lanka in September 2020. Fourteen water quality parameters, phytoplankton composition, chlorophyll- a , MC and CYN concentrations were analyzed in triplicate in 25 sampling sites from each reservoir. Both reservoirs were at hypereutrophic status. Microcystis was the dominant cyanobacteria with 0-3.75 x 10 3 cell/mL in Mahakanadarawa and 1-7 x 10 3 cell/mL in Nachchaduwa. Besides Microcystis , no other potential MC-producing cyanobacteria were observed. In Mahakanadarawa, MC was detected in the range of 0.11-1.63 µg/L which was above the WHO permissible level (1.0 µg/L) for drinking water. Although comparatively high Microcystis cell density was present in Nachchaduwa, its MC concentration was low (0.06-0.17 µg/L). The CYN concentration in Nachchaduwa was above the WHO permissible level (0.7 µg/L) for drinking water. It was 0.20-1.02 µg/L in Nachchaduwa and 0.03-0.08 µg/L in Mahakanadarawa. We did not observe any potential CYN-producing cyanobacteria in either of the reservoirs. There was no relationship between the spatial distribution pattern of MC and Microcystis cell density in both reservoirs. Although the majority of physico-chemical properties of water indicated suitability for drinking, co-occurrence of high concentrations of MC and CYN indicated their unsuitability for drinking. Hence, this study highlights the necessity for routing detection of cyanotoxins in both reservoirs. Further, our findings alarm potential health risks for the local community that relies on Mahakanadarawa and Nachchaduwa reservoirs for drinking, irrigation and fisheries.
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