Song Haihong, Coggins Liah X, Reichwaldt Elke S, Ghadouani Anas
Aquatic Ecology and Ecosystem Studies, School of Civil, Environmental and Mining Engineering, the University of Western Australia, 35 Stirling Highway, M015, Crawley, WA 6009, Australia.
Toxins (Basel). 2015 Mar 18;7(3):900-18. doi: 10.3390/toxins7030900.
Microcystins are toxins produced by cyanobacteria. They occur in aquatic systems across the world and their occurrence is expected to increase in frequency and magnitude. As microcystins are hazardous to humans and animals, it is essential to understand their fate in aquatic systems in order to control health risks. While the occurrence of microcystins in sediments has been widely reported, the factors influencing their occurrence, variability, and spatial distribution are not yet well understood. Especially in shallow lakes, which often develop large cyanobacterial blooms, the spatial variability of toxins in the sediments is a complex interplay between the spatial distribution of toxin producing cyanobacteria, local biological, physical and chemical processes, and the re-distribution of toxins in sediments through wind mixing. In this study, microcystin occurrence in lake sediment, and their relationship with biological and physicochemical variables were investigated in a shallow, eutrophic lake over five months. We found no significant difference in cyanobacterial biomass, temperature, pH, and salinity between the surface water and the water directly overlying the sediment (hereafter 'overlying water'), indicating that the water column was well mixed. Microcystins were detected in all sediment samples, with concentrations ranging from 0.06 to 0.78 µg equivalent microcystin-LR/g sediments (dry mass). Microcystin concentration and cyanobacterial biomass in the sediment was different between sites in three out of five months, indicating that the spatial distribution was a complex interaction between local and mixing processes. A combination of total microcystins in the water, depth integrated cyanobacterial biomass in the water, cyanobacterial biomass in the sediment, and pH explained only 21.1% of the spatial variability of microcystins in the sediments. A more in-depth analysis that included variables representative of processes on smaller vertical or local scales, such as cyanobacterial biomass in the different layers and the two fractions of microcystins, increased the explained variability to 51.7%. This highlights that even in a well-mixed lake, local processes are important drivers of toxin variability. The present study emphasises the role of the interaction between water and sediments in the distribution of microcystins in aquatic systems as an important pathway which deserves further consideration.
微囊藻毒素是蓝藻产生的毒素。它们存在于世界各地的水生系统中,而且预计其出现的频率和规模将会增加。由于微囊藻毒素对人类和动物有害,为了控制健康风险,了解它们在水生系统中的归宿至关重要。虽然沉积物中微囊藻毒素的存在已被广泛报道,但影响其存在、变异性和空间分布的因素尚未得到充分了解。特别是在经常出现大量蓝藻水华的浅水湖泊中,沉积物中毒素的空间变异性是产毒蓝藻的空间分布、当地生物、物理和化学过程以及通过风混合导致沉积物中毒素重新分布之间的复杂相互作用。在本研究中,在一个浅水富营养湖泊中,对五个月内湖泊沉积物中微囊藻毒素的存在情况及其与生物和理化变量的关系进行了调查。我们发现地表水与直接覆盖沉积物的水(以下简称“上覆水”)之间的蓝藻生物量、温度、pH值和盐度没有显著差异,这表明水柱混合良好。在所有沉积物样本中均检测到微囊藻毒素,浓度范围为0.06至0.78微克等效微囊藻毒素-LR/克沉积物(干质量)。在五个月中的三个月里,沉积物中微囊藻毒素浓度和蓝藻生物量在不同地点有所不同,这表明空间分布是局部和混合过程之间的复杂相互作用。水中总微囊藻毒素、水体深度积分蓝藻生物量、沉积物中蓝藻生物量和pH值的组合仅解释了沉积物中微囊藻毒素空间变异性的21.1%。一项更深入的分析,包括代表较小垂直或局部尺度过程的变量,如不同层中的蓝藻生物量和微囊藻毒素的两个组分,将解释的变异性提高到了51.7%。这突出表明,即使在混合良好的湖泊中,局部过程也是毒素变异性的重要驱动因素。本研究强调了水与沉积物之间的相互作用在水生系统中微囊藻毒素分布中的作用,这是一条值得进一步考虑的重要途径。