本powerpoint演示文稿首先简要概述了2007年魁北克的情况:环境部2007-2017年计划；194个湖泊受到蓝藻（CB）的影响（MDDEP，2007年）； 对七家饮用水厂进行了监测，并在原水中检测到了所有蓝藻毒素；和 未检测到蓝耳毒素 植物的净化水。2008年，108个湖泊受CB影响，包括6个水体，5个海滩关闭（MDDEP，2007年）。文献综述揭示了以下情况:与蓝藻（CB）增殖相关的条件；氰基毒素健康风险；蓝藻和蓝藻毒素监测 饮用水处理厂框架（DWTP）；以及传统和新颖的在线检测方法 蓝藻监测。研究目的是:监测生物多样性的时空变化 在加拿大魁北克的两个饮用水处理厂（DWTPs）通过传统和新型在线方法检测蓝藻和蓝藻毒素； 评估常规CB丰度测量方法与新型在线活体PC荧光之间的相关性；并且，用最合适的蓝藻监测参数验证体内PC荧光。研究方法包括两个现场，多探针系统（MPS），MPS协议和抓取取样。结论表明:两个地点的蓝藻丰度和微囊藻毒素浓度都有很高的时空变化；在两种DWTPs中，所有常规监测参数与体内PC荧光和MC-LR浓度之间均存在高度和显著的相关性；并且，在两个监测的DWTPs上验证体内PC荧光最合适的参数是 蓝藻生物量。包括表、图。

This powerpoint presentation begins by providing a brief overview of the situation in Quebec in 2007: Ministry of the Environment's plan 2007-2017; 194 lakes affected by cyanobacteria (CB) (MDDEP,2007); seven potable water plants were monitored and all detected cyanotoxins in raw water; and, no cyanotoxins were detected in treated water of plants. In 2008, 108 lakes were affected by CB including six water bodies, and five beaches were closed (MDDEP,2007). A literature review revealed the following: conditions correlated with cyanobacteria (CB) proliferations; cyanotoxin health risks; cyanobacterial and cyanotoxin monitoring frameworks for drinking water treatment plants (DWTP); and, conventional and novel online methods of cyanobacterial monitoring. Study objectives were to: monitor the spatio-temporal variations of cyanobacteria and cyanotoxins by conventional and novel online methods at two drinking water treatment plants (DWTPs) in Quebec, Canada; evaluate the correlations between conventional methods of measuring CB abundance and novel online in vivo PC fluorescence; and, validate in vivo PC fluorescence with the most appropriate cyanobacterial monitoring parameter. Research methodology included two field sites, multi-probes systems (MPS), MPS protocol, and grab sampling. Conclusions indicate that: there was high spatio-temporal variation in cyanobacterial abundance and microcystin concentration at both sites; at both DWTPs, high and significant correlations were derived between all conventional monitoring parameters and both in vivo PC fluorescence and the concentration of MC-LR; and, the most appropriate parameter to validate in vivo PC fluorescence at the two monitored DWTPs is cyanobacterial biovolume. Includes table, figure.