Modification to EPA Method 1623 to address a unique seasonal matrix effect encountered in some U.S. source waters.

U.S. Environmental Protection Agency (EPA) Method 1623 is designed to detect and determine concentrations of Cryptosporidium oocysts and Giardia cysts in water through concentration, immuno-magnetic separation (IMS), and immuno-fluorescence assay with microscopic examination. A seasonal interference with the method was observed in some municipal source waters collected from reservoirs and as reported to Shaw Environmental, Inc. in the summers of 2005, 2006, and 2007. This interference, which was not confined to a single region of the nation, caused clumping of the IMS beads during the acid dissociation of the IMS procedure in Method 1623. This effect lowered method recoveries for both Cryptosporidium and Giardia; however, the effect was more pronounced for Giardia. A heat dissociation technique (Ware et al., (2003) J. Microbiol. Methods 55, 575-583) was shown to be a viable option for samples which demonstrate the clumping matrix effect and improved Giardia recoveries in partially clumped samples. The heat dissociation application holds promise for fully clumped samples and warrants further investigation.

A modified EPA Method 1623 that uses tangential flow hollow-fiber ultrafiltration and heat dissociation steps to detect waterborne Cryptosporidium and Giardia spp.

Cryptosporidium and Giardia species are two of the most prevalent protozoa that cause waterborne diarrheal disease outbreaks worldwide. To better characterize the prevalence of these pathogens, EPA Method 1623 was developed and used to monitor levels of these organisms in US drinking water supplies (12). The method has three main parts; the first is the sample concentration in which at least 10 L of raw surface water is filtered. The organisms and trapped debris are then eluted from the filter and centrifuged to further concentrate the sample. The second part of the method uses an immunomagnetic separation procedure where the concentrated water sample is applied to immunomagnetic beads that specifically bind to the Cryptosporidium oocysts and Giardia cysts allowing for specific removal of the parasites from the concentrated debris. These (oo)cysts are then detached from the magnetic beads by an acid dissociation procedure. The final part of the method is the immunofluorescence staining and enumeration where (oo)cysts are applied to a slide, stained, and enumerated by microscopy. Method 1623 has four listed sample concentration systems to capture Cryptosporidium oocysts and Giardia cysts in water: Envirochek filters (Pall Corporation, Ann Arbor, MI), Envirochek HV filters (Pall Corporation), Filta-Max filters (IDEXX, Westbrook, MA), or Continuous Flow Centrifugation (Haemonetics, Braintree, MA). However, Cryptosporidium and Giardia (oo)cyst recoveries have varied greatly depending on the source water matrix and filters used(1,14). A new tangential flow hollow-fiber ultrafiltration (HFUF) system has recently been shown to be more efficient and more robust at recovering Cryptosporidium oocysts and Giardia cysts from various water matrices; moreover, it is less expensive than other capsule filter options and can concentrate multiple pathogens simultaneously(1-3,5-8,10,11). In addition, previous studies by Hill and colleagues demonstrated that the HFUF significantly improved Cryptosporidium oocysts recoveries when directly compared with the Envirochek HV filters(4). Additional modifications to the current methods have also been reported to improve method performance. Replacing the acid dissociation procedure with heat dissociation was shown to be more effective at separating Cryptosporidium from the magnetic beads in some matrices(9,13) . This protocol describes a modified Method 1623 that uses the new HFUF filtration system with the heat dissociation step. The use of HFUF with this modified Method is a less expensive alternative to current EPA Method 1623 filtration options and provides more flexibility by allowing the concentration of multiple organisms.

Using quantitative reverse transcriptase PCR and cell culture plaque assays to determine resistance of Toxoplasma gondii oocysts to chemical sanitizers.

Toxoplasma gondii oocysts are highly resistant to many chemical sanitizers. Methods used to determine oocyst infectivity have relied primarily on mouse, chicken, and feline bioassays. Although considered gold standards, they only provide a qualitative assessment of oocyst viability. In this study, two alternative approaches were developed to quantitate viable T. gondii oocysts following treatment with several common sanitizers. The first is a quantitative reverse transcriptase real-time PCR (RT-qPCR) assay targeting the ACT1 and SporoSAG genes to enumerate viable T. gondii oocysts. RT-qPCR C(T) values between Wescodyne(R), acidified ethanol, or heat treated oocysts were not significantly different as compared with untreated controls. By contrast, treatment with formalin or Clorox(R) resulted in a 2-log(10) reduction in C(T) values. An in vitro T. gondii oocyst plaque assay (TOP-assay) was also developed to measure oocyst viability. This assay used a combination of bead milling and bile digestion, followed by culturing the excysted sporozoites in a confluent fibroblast cell monolayer. Results showed that no significant reduction in sporozoite viability was detected in acidified ethanol or Wescodyne(R) treated oocysts while at least a 2-log(10) reduction in plaques formed was observed with Clorox(R) treated oocysts. Moreover, formalin or heat treatment of oocysts resulted in at least a 5-log(10) reduction in plaques formed. This study demonstrates that an mRNA-based PCR viability assay targeting the ACT1 or SporoSAG genes is a relatively rapid technique compared to in vitro and in vivo assays. In addition, the TOP-assay proved very effective and sensitive at quantifying oocyst viability when compared with animal bioassays.