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基于Förster 共振能量转移(FRET)的免疫分析检测饮用水中的微囊藻毒素-LR。

A Förster Resonance Energy Transfer (FRET)-Based Immune Assay for the Detection of Microcystin-LR in Drinking Water.

机构信息

Istituto di Scienze dell'Alimentazione, CNR, URT-Napoli, 80100 Napoli, Italy.

Istituto di Scienze dell'Alimentazione, CNR, 83100 Avellino, Italy.

出版信息

Sensors (Basel). 2024 May 17;24(10):3204. doi: 10.3390/s24103204.

DOI:10.3390/s24103204
PMID:38794058
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC11487384/
Abstract

is the term used to describe an abnormal and rapid growth of cyanobacteria in aquatic ecosystems such as lakes, rivers, and oceans as a consequence of anthropic factors, ecosystem degradation, or climate change. Cyanobacteria belonging to the genera , , , and produce and release toxins called microcystins (MCs) into the water. MCs can have severe effects on human and animal health following their ingestion and inhalation. The MC structure is composed of a constant region (composed of five amino acid residues) and a variable region (composed of two amino acid residues). When the MC variable region is composed of arginine and leucine, it is named MC-LR. The most-common methods used to detect the presence of MC-LR in water are chromatographic-based methods (HPLC, LC/MS, GC/MS) and immunological-based methods (ELISA). In this work, we developed a new competitive Förster resonance energy transfer (FRET) assay to detect the presence of traces of MC-LR in water. Monoclonal antibody anti-MC-LR and MC-LR conjugated with bovine serum albumin (BSA) were labeled with the near-infrared fluorophores CF568 and CF647, respectively. Steady-state fluorescence measurements were performed to investigate the energy transfer process between anti-MC-LR 568 and MC-LR BSA 647 upon their interaction. Since the presence of unlabeled MC-LR competes with the labeled one, a lower efficiency of FRET process can be observed in the presence of an increasing amount of unlabeled MC-LR. The limit of detection (LoD) of the FRET assay is found to be 0.245 nM (0.245 µg/L). This value is lower than the provisional limit established by the World Health Organization (WHO) for quantifying the presence of MC-LR in drinking water.

摘要

水华是由于人为因素、生态系统退化或气候变化等因素导致蓝藻在湖泊、河流和海洋等水生生态系统中异常快速生长的术语。属于 、 、 和 属的蓝藻会产生并将毒素(称为微囊藻毒素,MCs)释放到水中。MCs 在被摄入和吸入后会对人类和动物健康产生严重影响。MC 的结构由一个恒定区(由五个氨基酸残基组成)和一个可变区(由两个氨基酸残基组成)组成。当 MC 可变区由精氨酸和亮氨酸组成时,它被命名为 MC-LR。目前用于检测水中 MC-LR 存在的最常见方法是基于色谱的方法(HPLC、LC/MS、GC/MS)和基于免疫的方法(ELISA)。在这项工作中,我们开发了一种新的竞争Förster 共振能量转移(FRET)测定法来检测水中痕量 MC-LR 的存在。抗 MC-LR 单克隆抗体和与牛血清白蛋白(BSA)偶联的 MC-LR 分别用近红外荧光染料 CF568 和 CF647 标记。进行稳态荧光测量以研究抗 MC-LR 568 和 MC-LR BSA 647 相互作用时的能量转移过程。由于未标记的 MC-LR 的存在会与标记的 MC-LR 竞争,因此在存在越来越多的未标记的 MC-LR 时,可以观察到 FRET 过程的效率降低。FRET 测定的检测限(LoD)被发现为 0.245 nM(0.245 µg/L)。该值低于世界卫生组织(WHO)为定量饮用水中 MC-LR 存在而建立的暂定限值。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/4c2e57abac0f/sensors-24-03204-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/47b3fdde2d99/sensors-24-03204-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/cb94afedaa9f/sensors-24-03204-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/064ecd920325/sensors-24-03204-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/999b6ac3bb6b/sensors-24-03204-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/4c2e57abac0f/sensors-24-03204-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/47b3fdde2d99/sensors-24-03204-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/cb94afedaa9f/sensors-24-03204-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/064ecd920325/sensors-24-03204-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/999b6ac3bb6b/sensors-24-03204-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/393c/11487384/4c2e57abac0f/sensors-24-03204-g005.jpg

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