National Research Council Canada, Biotechnology Research Institute, 6100 Royalmount Ave., Montreal, QC H4P 2R2, Canada.
Appl Environ Microbiol. 2010 Aug;76(15):5105-12. doi: 10.1128/AEM.00183-10. Epub 2010 Jun 18.
Toxic cyanobacterial blooms, as well as their increasing global occurrence, pose a serious threat to public health, domestic animals, and livestock. In Missisquoi Bay, Lake Champlain, public health advisories have been issued from 2001 to 2009, and local microcystin concentrations found in the lake water regularly exceeded the Canadian drinking water guideline of 1.5 microg liter(-1). A quantitative PCR (Q-PCR) approach was developed for the detection of blooms formed by microcystin-producing cyanobacteria. Primers were designed for the beta-ketoacyl synthase (mcyD(KS)) and the first dehydratase domain (mcyD(DH)) of the mcyD gene, involved in microcystin synthesis. The Q-PCR method was used to track the toxigenic cyanobacteria in Missisquoi Bay during the summers of 2006 and 2007. Two toxic bloom events were detected in 2006: more than 6.5 x 10(4) copies of the mcyD(KS) gene ml(-1) were detected in August, and an average of 4.0 x 10(4) copies ml(-1) were detected in September, when microcystin concentrations were more than 4 microg liter(-1) and approximately 2 microg liter(-1), respectively. Gene copy numbers and total microcystin concentrations (determined by enzyme-linked immunosorbent assay [ELISA]) were highly correlated in the littoral (r = 0.93, P < 0.001) and the pelagic station (r = 0.87, P < 0.001) in 2006. In contrast to the situation in 2006, a cyanobacterial bloom occurred only in late summer-early fall of 2007, reaching only 3 x 10(2) mcyD(KS) copies ml(-1), while the microcystin concentration was barely detectable. The Q-PCR method allowed the detection of microcystin-producing cyanobacteria when toxins and toxigenic cyanobacterial abundance were still below the limit of detection by high-pressure liquid chromatography (HPLC) and microscopy. Toxin gene copy numbers grew exponentially at a steady rate over a period of 7 weeks. Onshore winds selected for cells with a higher cell quota of microcystin. This technique could be an effective approach for the routine monitoring of the most at-risk water bodies.
有毒蓝藻水华及其在全球范围内的日益增加,对公共健康、家畜和牲畜构成了严重威胁。在尚普兰湖的米西索基湾,从 2001 年到 2009 年发布了公共卫生警报,并且湖中发现的局部微囊藻浓度经常超过加拿大饮用水准则的 1.5 微克/升。开发了一种定量 PCR(Q-PCR)方法来检测由产生微囊藻的蓝藻形成的水华。设计了用于微囊藻合成中涉及的β-酮酰基合酶(mcyD(KS))和第一脱水酶结构域(mcyD(DH))的 mcyD 基因的引物。在 2006 年和 2007 年的夏季,使用 Q-PCR 方法跟踪米西索基湾的产毒蓝藻。在 2006 年检测到两次有毒水华事件:8 月检测到 mcyD(KS)基因的超过 6.5×10(4)个拷贝/ml,9 月检测到平均 4.0×10(4)个拷贝/ml,当时微囊藻浓度超过 4 微克/升和大约 2 微克/升。在 2006 年,沿海站(r = 0.93,P <0.001)和浮游生物站(r = 0.87,P <0.001)中的基因拷贝数和总微囊藻浓度(通过酶联免疫吸附测定[ELISA]确定)高度相关。与 2006 年的情况相反,蓝藻水华仅在 2007 年夏末-初秋发生,达到仅 3×10(2)个 mcyD(KS)拷贝/ml,而微囊藻浓度几乎无法检测到。Q-PCR 方法允许在通过高效液相色谱(HPLC)和显微镜检测到毒素和产毒蓝藻丰度仍低于检测限的情况下检测产毒蓝藻。毒素基因拷贝数在 7 周的时间内以稳定的速率呈指数增长。向岸风选择具有更高微囊藻细胞配额的细胞。该技术可能是对最危险水体进行常规监测的有效方法。