Angus Scott V, Kwon Hyuck-Jin, Yoon Jeong-Yeol
Department of Agricultural and Biosystems Engineering, The University of Arizona, Tucson, Arizona 85721-0038, USA.
J Environ Monit. 2012 Dec;14(12):3295-304. doi: 10.1039/c2em30700f. Epub 2012 Nov 14.
Cryptosporidium spp. is an obligate, parasitic protozoan that is difficult to detect and causes diarrhea in healthy adults while potentially causing death in the immunocompromised and children. Its treatment options are few and treat the symptoms, not the actual parasite. Current methods of detection are inefficient and rely too heavily upon laboratory sample preparations and technician skill, including differential staining, negative staining, and immunofluorescence methods [especially U.S. Environmental Protection Agency (EPA) Method 1623]. These assays can take from hours to days and require a laboratory environment. In this work, we demonstrated the microbead immunoagglutination assay combined with Mie scatter detection in a microfluidic device to provide a field-deployable and near-real-time alternative to the laboratory-based method (especially EPA Method 1623). Two main challenges were the relatively big diameter of Cryptosporidium oocysts (5-6 μm) and the contaminants in field water samples that negatively affected the immunoagglutination and its scatter detection. We used 4 min sonication to liberate Cryptosporidium oocyst wall proteins (COWP), which was previously used to inactivate Cryptosporidium oocysts. As for the contaminants, we optimized the microbead diameter (920 nm) and the wavelength of incident light (375 nm) to find the angle of scatter detection (45°) where the Mie scatter from immunoagglutinated microbeads was maximum and the background scatter from contaminants was minimum. This enabled the sub-single-oocyst-level detection despite the fact that only a very small volume of water sample (15 μL) was introduced to the microfluidic biosensor. When combined with filtration/concentration, this method is able to detect ≤1 oocyst per large volume of water, comparable to or potentially better than the EPA method 1623, while effectively reducing the time and labor necessary for staining and microscopic analysis. For faster, near-real-time assays, filtration/concentration may not be used, where the detection limit was 1-10 oocysts per mL with the total assay time of 10 min including the 4 min sonication time. The linear range of assay was over 5 orders of magnitude. The final device was compact and had the potential to be used in field situations, and required less technical expertise and/or training compared to the other methods.
隐孢子虫属是一种专性寄生原生动物,难以检测,可导致健康成年人腹泻,而在免疫功能低下者和儿童中可能导致死亡。其治疗选择有限,只能缓解症状,而非针对实际的寄生虫。目前的检测方法效率低下,过于依赖实验室样品制备和技术人员技能,包括鉴别染色、负染色和免疫荧光方法[特别是美国环境保护局(EPA)方法1623]。这些检测可能需要数小时至数天时间,且需要实验室环境。在这项工作中,我们展示了在微流控装置中结合米氏散射检测的微珠免疫凝集测定法,以提供一种可现场部署且近乎实时的方法,替代基于实验室的方法(特别是EPA方法1623)。两个主要挑战是隐孢子虫卵囊相对较大的直径(5 - 6μm)以及野外水样中的污染物,这些污染物会对免疫凝集及其散射检测产生负面影响。我们使用4分钟超声处理来释放隐孢子虫卵囊壁蛋白(COWP),该蛋白此前用于使隐孢子虫卵囊失活。对于污染物,我们优化了微珠直径(920nm)和入射光波长(375nm),以找到散射检测角度(45°),在该角度下免疫凝集微珠的米氏散射最大,而污染物的背景散射最小。尽管仅向微流控生物传感器引入了非常少量的水样(15μL),但这仍实现了亚单卵囊水平的检测。当与过滤/浓缩相结合时,该方法能够检测每大量水样中≤1个卵囊,与EPA方法1623相当或可能更好,同时有效减少了染色和显微镜分析所需的时间和人力。对于更快的近乎实时检测,可不使用过滤/浓缩,此时检测限为每毫升1 - 10个卵囊,总检测时间为10分钟,包括4分钟超声处理时间。测定的线性范围超过5个数量级。最终的装置紧凑,有可能用于现场情况,并且与其他方法相比需要更少的技术专业知识和/或培训。