DCU Water Institute, National Centre for Sensor Research (NCSR), School of Chemical Sciences, Dublin City University, Dublin, Ireland.
DCU Water Institute, National Centre for Sensor Research (NCSR), School of Chemical Sciences, Dublin City University, Dublin, Ireland.
Anal Chim Acta. 2017 Apr 29;964:178-186. doi: 10.1016/j.aca.2017.02.035. Epub 2017 Mar 6.
To achieve active management of bathing areas and to reduce risk associated with the presence of fecal pollution, tests capable of rapid on-site assessment of microbiological water quality are required. A protocol for the recovery and detection of fecal pollution indicator bacteria, E. coli, using β-glucuronidase (GUS) activity was developed. The developed protocol involves two main steps: sample preparation and GUS activity measurement. In the sample preparation step, syringe filters were used with a dual purpose, for the recovery and pre-concentration of E. coli from the water matrix and as μL reactors for bacteria lysis and GUS extraction. Subsequently, GUS activity was measured using a continuous fluorometric method developed previously. The optimum GUS recovery conditions for the sample preparation step were found to be 100 μL PELB (supplemented with 1 mg mL lysozyme and 20 mM DTT) at 37 °C for 30 min. The protocol was evaluated on environmental samples (fresh and seawater) against an establish GUS assay method (Coliplage). GUS activities corresponding to samples containing as low as 26 MPN E. coli 100 mL were detected for the seawater sample and as low as 110 MPN E. coli 100 mL for the freshwater samples. By comparison with the Coliplage method, this protocol offered an improvement in the measured GUS activities of 3.1 fold for freshwater samples and 4.1 fold for seawater samples. Furthermore, the protocol developed here, has a time-to-result of 75 min, and successfully addresses the requirement for tests capable of rapid assessment of microbiological water quality.
为了实现浴场的主动管理并降低与粪便污染相关的风险,需要能够快速现场评估微生物水质的测试方法。本研究开发了一种使用β-葡萄糖醛酸酶(GUS)活性来检测粪便污染指示菌大肠杆菌的方法。该方法主要包括两个步骤:样品制备和 GUS 活性测量。在样品制备步骤中,使用了注射器过滤器,其具有双重目的,可从水基质中回收和浓缩大肠杆菌,并作为用于细菌裂解和 GUS 提取的μL 反应器。随后,使用先前开发的连续荧光法测量 GUS 活性。对于样品制备步骤,GUS 最佳回收条件为 37°C 下 100μL PELB(补充 1mg/mL 溶菌酶和 20mM DTT)孵育 30min。该方法在环境样品(淡水和海水)中进行了评估,并与已建立的 GUS 测定方法(Coliplage)进行了比较。对于海水样品,可检测到 GUS 活性对应于低至 26 MPN E. coli 100mL 的浓度,对于淡水样品,可检测到低至 110 MPN E. coli 100mL 的浓度。与 Coliplage 方法相比,该方法可将淡水样品的 GUS 活性提高 3.1 倍,将海水样品的 GUS 活性提高 4.1 倍。此外,该方法的检测时间为 75min,成功满足了快速评估微生物水质的测试要求。