Beversdorf Lucas J, Chaston Sheena D, Miller Todd R, McMahon Katherine D
Department of Civil and Environmental Engineering, University of Wisconsin-Madison, 1415 Engineering Drive, Madison, Wisconsin, 53706, United States of America.
Department of Bacteriology, University of Wisconsin-Madison, 1550 Linden Drive, Madison, Wisconsin, 53706, United States of America.
PLoS One. 2015 May 6;10(5):e0125353. doi: 10.1371/journal.pone.0125353. eCollection 2015.
Cyanobacterial harmful algal blooms (cyanoHABs) are a primary source of water quality degradation in eutrophic lakes. The occurrence of cyanoHABs is ubiquitous and expected to increase with current climate and land use change scenarios. However, it is currently unknown what environmental parameters are important for indicating the presence of cyanoHAB toxins making them difficult to predict or even monitor on time-scales relevant to protecting public health. Using qPCR, we aimed to quantify genes within the microcystin operon (mcy) to determine which cyanobacterial taxa, and what percentage of the total cyanobacterial community, were responsible for microcystin production in four eutrophic lakes. We targeted Microcystis-16S, mcyA, and Microcystis, Planktothrix, and Anabaena-specific mcyE genes. We also measured microcystins and several biological, chemical, and physical parameters--such as temperature, lake stability, nutrients, pigments and cyanobacterial community composition (CCC)--to search for possible correlations to gene copy abundance and MC production. All four lakes contained Microcystis-mcyE genes and high percentages of toxic Microcystis, suggesting Microcystis was the dominant microcystin producer. However, all genes were highly variable temporally, and in few cases, correlated with increased temperature and nutrients as the summer progressed. Interestingly, toxin gene abundances (and biomass indicators) were anti-correlated with microcystin in all lakes except the largest lake, Lake Mendota. Similarly, gene abundance and microcystins differentially correlated to CCC in all lakes. Thus, we conclude that the presence of microcystin genes are not a useful tool for eliciting an ecological role for toxins in the environment, nor are microcystin genes (e.g. DNA) a good indicator of toxins in the environment.
蓝藻有害藻华(cyanoHABs)是富营养化湖泊水质退化的主要来源。cyanoHABs的发生很普遍,并且预计随着当前气候和土地利用变化情景而增加。然而,目前尚不清楚哪些环境参数对于指示cyanoHAB毒素的存在很重要,这使得它们难以在与保护公众健康相关的时间尺度上进行预测甚至监测。我们使用定量聚合酶链反应(qPCR)来量化微囊藻毒素操纵子(mcy)内的基因,以确定在四个富营养化湖泊中哪些蓝藻分类群以及占总蓝藻群落的百分比负责微囊藻毒素的产生。我们靶向微囊藻属16S、mcyA以及微囊藻属、席藻属和鱼腥藻属特异性的mcyE基因。我们还测量了微囊藻毒素以及几个生物学、化学和物理参数,如温度、湖泊稳定性、营养物质、色素和蓝藻群落组成(CCC),以寻找与基因拷贝丰度和微囊藻毒素产生的可能相关性。所有四个湖泊都含有微囊藻属-mcyE基因和高比例的有毒微囊藻属,这表明微囊藻属是主要的微囊藻毒素生产者。然而,所有基因在时间上都高度可变,并且在少数情况下,随着夏季的推进,与温度和营养物质的增加相关。有趣的是,除了最大的门多塔湖外,所有湖泊中的毒素基因丰度(和生物量指标)与微囊藻毒素呈负相关。同样,在所有湖泊中,基因丰度和微囊藻毒素与CCC的相关性也不同。因此,我们得出结论,微囊藻毒素基因的存在不是揭示毒素在环境中的生态作用的有用工具,微囊藻毒素基因(如DNA)也不是环境中毒素的良好指标。