Development of Magnetic Particle Concentrator for Cryptosporidium and Giardia Pathogens Capture in Shellfish Palsiri Srirungruang1*, Pimchanok Witayaudom1, Narongsak Boonkhao2, Pranee Inprakhon3, Warawoot Thowladda 4, Kittipong Harncharoen1, Mayuna Srisuphanunt1# 1 Programe of Studies, Faculty of Public Health, Mahidol University, Bangkok 10400, Thailand 2 Institute of Medical and Public Health Technology, Nonthaburi 11150, Thailand 3 Faculty of Science, Mahidol University, Bangkok 10400, Thailand 4 Faculty of Science, King Mongkut’s Institute of Technology Ladkrabang, Bangkok 10520, Thailand *Palsiri.pal@hotmail.com, #Mayunaph@yahoo.com Abstract Cryptospordium and Giardia pathogens are the significant protozoan parasites cause diarrhea in humans worldwide via drinking water and food. The detection of both parasites requires special methods and laboratory equipments, due to the small size and frequently low number of their oo(cysts) in water and food. Thailand posts recently a trade deficit as such equipments imports. The aim of the study is to develop domestic Magnetic Particle Concentrator (MPC) for Cryptospordium and Giardia oo(cysts) detection in shellfish. The developed thai MPC was validated by the recovery efficiency of the oo(cysts) detection in seeding water samples to compare with the imported MPC. The efficiency comparison of thai MPC and imported MPC for oo(cysts) recovery detection was no significant difference (p < 0.05). Total of 100 oysters, economical shellfish, were collected from local markets in Bangkok and its surroundings. All samples were homogenized and Cryptosporidium and Giardia (oo)cysts were enumerated using a combined Immunomagnetic Separation and Immunofluorescence antibody method. Cryptosporidium oocysts and Giardia cysts were found in 9 % and 8 %, respectively. The results indicated that thai MPC was developed with low cost and instead use of imported products with no difference quality. The presence of Cryptosporidium and Giardia in the oysters provide in epidemiological study and a situation of sanitary risk with determining the safety of shellfish for human consumption. Keywords: Cryptosporidium, Giardia, Magnetic Particle Concentrator (MPC), shellfish Introduction Cryptosporidium and Giardia are the important protozoan parasites found commonly in water and food and cause diarrhea in humans worldwide. Infections by either Cryptosporidium oocysts or Giardia cysts are upon transmission by drinking water and food with a low infectious dose (1 and 2) and fatalities can occur in widespread outbreaks where the children and elderly or immunosuppressed are infected ,due to no effective drug treatment or vaccine available at present (3). Moreover, numerous waterborne outbreaks of cryptosporidiosis and giardiasis have been documented (4 - 11). Oocysts and cysts are often excreted in large quantities with the feces of infected animals and humans and remain infective for months in environmental waters and are highly resistant to chemical disinfectants (12). There has been several disease outbreak evidences from these waterborne protozoa in different from other countries in the United States and European regions (13). In Thailand, cryptosporidiosis has been reported in HIV infected patients with the prevalence rate between 2.5% and 25% (14 - 19) and few reported in water and food contamination (18, 20 and 21). Although parasitic water and food-borne disease is a significant public health problem, water and food are rarely tested for parasite contamination. This may be due to the small size and frequently low number of Cryptosporidium oocysts and Giardia cysts in naturally contaminated water and food, and lack of the promising method to determine the enteric parasites in water and foods. The detection of these parasites is difficult and requires special methods and also efficient laboratory equipments. Most of the equipments in the country are imported and it is also lopsided for Thailand. No previous data is available describing the detection equipments of these parasitic enteropathogens in water and food in Thailand. The aims of the study is the development of domestic Magnetic Particle Concentrator (MPC), one of the laboratory equipments, by using local materials for the detection of Cryptospordium and Giardia oo(cysts) in shellfish. Methodology Magnetic Particle Concentrator Development The description and specification data of imported MPC were studied and used as the prototype model for the development of the domestic MPC by using local materials in Thailand. Efficiency Comparison between thai-MPC and imported MPC The comparison of the efficacy between imported MPC and thai MPC was evaluated and validated for the recovery levels of Cryptosporidium and Giardia oo(cysts) detection in 6 different concentrations of seeding water samples. For the seeding experiment, Cryptosporidium and Giardia oo(cysts) were diluted with PBS buffer for the initial concentration as 400,300,200,100,50,25 oocysts/l and 300, 200, 100,50,25,10 cysts/l , respectively and spiked 1 ml each of these concentration into the seeding water samples with brought up to 10 ml with sterile water and subjected to IMS, using the Dynal Dynabeads® anti-Cryptosporidium kit and the Aureon anti-Giardia IMS kit (ImmTech, Inc. New Windsor, MD), according to the manufacturer's instructions. The oo(cysts) in seeded water samples were evaluated for the efficiency of thai MPC compared to the imported MPC. Samples collection and preparation A total of 100 raw oyster samples were collected from different local markets in Bangkok and its surroundings, including Tai market, Marketing Organization for farmers, Yin Charoen market, Prannok market and Huai Khwang market. All samples were kept cool at 4°C in an insulated container with ice for immediate transportation to the laboratory and processed within 24 hours. Each sample consisted of the whole meat from 10 oysters was pooled and kept separately. An aliquot of each individual sample was stored before the constitution of the pool for further Cryptosporidium and Giardia species identification. The pooled samples were homogenized in PBS (0.04 M, pH 7.2) using a stomacher or a Moulinex blender machine. The resulting homogenates of each pool were then passed through a sieve (mesh size 45 and 150 μm), subjected to lipid extraction with PBS/diethyl ether (2:1, v/v), and concentrated by centrifugation at 1,250 × g, for 5 min, at 4 °C. The sediments from each pool were examined for the presence of Cryptosporidium and Giardia (oo)cysts. Isolation, Concentration and Purification of (oo)cysts by IMS To recover Cryptospordium and Giardia oo(cysts) from the homogenate pellets, each 10-ml sample was processed by IMS according to the manufacturer's instructions (Dynabeads anti-Cryptosporidium ;Dynal and anti-Giardia kit; Aureon). Briefly, 100 μl of antiCryptosporidium and anti-Giardia beads were added to a 10-ml homogenate sample obtained after shellfish preparation. The sample was then processed according to the recommendations of the manufacturer, using thai MPC equipment for IMS processing. After dissociation from magnetic beads, (oo) cysts were transferred to a new microcentrifuge tube and treated with 5 μl of 1 N NaOH to neutralize the pH. The resultant suspension for screening was clean and approximately 50 μl total volume. This resulted final sample was divided into two portions, and one portion was examined by the immunofluorescent assay (IFA) to detect Cryptosporidium oocysts and Giardia cysts. Detection and identification of Cryptosporidium and Giardia (oo)cysts by IFA A direct immunofluorescence antibodies (IFA) assay was applied to detect Cryptosporidium and Giardia oo(cysts) in the sediments obtained. Samples were placed on glass microscope slides. Slides were fixed with methanol and air dried, oo(cysts) were enumerated by IFA using a commercially available test kit (MeriFluor Cryptosporidium/Giardia; Sanofi Diagnostics Pasteur, France) per the manufacturer's instructions. The oo(cysts) were identified under an FITC filter using fluorescence microscopy (OLYMPUS, Model BX 51), according to the criteria proposed by Graczyk et al. (22), i.e. brilliant green fluorescence, correct shape and size of the FITC-labelled objects with clearly visible oocyst wall. Statistical data analysis Statistical analyses were performed on logarithmically transformed data of Cryptosporidium oocysts and Giardia cysts numbers and then process using Pearson correlation analysis. Values of P < 0.05 were considered statistically significant. All the analyses were performed using SPSS for Windows software (version 11.5) software. Results The thai MPC was successfully developed by using local materials for Cryptosporidium and Giardia detection in shellfish samples. The detection limit in seeding water samples for Cryptosporidium and Giardia at the initial inoculum were 50 oocysts/l and 25 cysts/l, respectively. The efficacy of imported MPC and thai MPC for Cryptosporidium and Giardia oo(cysts) detection in oysters was no significant difference (p < 0.05),as shown in Figure 1. The detection of Cryptosporidium and Giardia oo(cysts) in total of 100 raw oysters were found in 9 % and 8 %, respectively. (Table 1). Figure 1. Efficiency comparison of imported MPC and thai MPC for Cryptosporidium and Giardia oo(cysts) detection. Table 1. Prevalence of Cryptosporidium and Giardia oo(cysts) in raw oyster samples. Location Sampling (raw oysters) No of positive No. samples Cryptosporidium Giardia local markets in Bangkok and surrounding -Tai market 25 3 3 - Marketing Organization for farmers 25 1 1 -Yin Charoen market 20 1 1 - Prannok market 15 2 2 - Huai Khwang market 15 2 1 100 9 8 Total Discussion and Conclusion Cryptosporidium and Giardia present public health challenges due to their low infective dose, ease of dispersal and persistence in the environment, difficulty to reliably isolate and detect, small (oo)cyst size that may bypass common water treatments and relative resistance to disinfection (23 and 24). Both parasites may be transmitted by direct fecal–oral route (and thus by direct contact with infected animals or humans) or by ingestion of food or water contaminated with (oo)cysts (25). Agricultural practices including manure storage and manure application to arable land, discharge of contaminated water, pasturing of livestock near water sources and disposal of fecally contaminated waste from abattoirs and wastewater treatment facilities may result in contamination of the environment with large numbers of (oo)cysts (26 and 27). With (oo)cysts circulating in environmental water supplies, and waterborne outbreaks documented in developed countries throughout the world, attention has been drawn to transmission potential of parasites in contaminated shellfish to consumers. Through improved detection methods, studies continue to confirm the presence of these parasites in livestock and contaminated water sources. Although studies examining shellfish for these zoonotic protozoa are limited, literature available on bioaccumulation and retention of (oo)cysts in shellfish highlights the need to examine the efficacy of current sanitation and depuration protocols to prevent the public from acquiring cryptosporidiosis and/or giardiasis from the consumption of contaminated shellfish. The Thai market in 2010 is valued medical devices and laboratory equipment at US$795 million. Moreover, the Ministry of Commerce showed the top ten imported goods in 2012, scientific instruments was imported continuously and ranked number 6 at more than a billion baht deficit (28). Even though the market is vibrant, it is also lopsided. Two-thirds of medical devices in the country are imported, with products from the United States accounting for 29% of inbound shipments, according to figures from the Thai Medical Device Technology Industry Association (ThaiMed). In fact, Thailand needs to import about 10 billion baht in medical devices annually to meet local demand. Although the country has a substantial number of manufacturers, currently these tend to concentrate on a relatively small number of product categories. Progress is being achieved, however, toward upgrading local production of medical devices to reduce imports. Imports of diagnostic or laboratory reagents or equipments hit 3.63 billion baht and exports were just 186.3 million baht in the 10 months. Thus, this study was successfully developed the domestic Magnetic Particle Concentrator (MPC) ,one of these laboratory equipments , which is promising use to replace the imported product with no different quality, but lower cost and reduce the trade balance. Thailand, as a leader in Asia, plays a vital role in many regional and international organizations dedicated to promoting the advancement of medical devices in the area. Therefore, signifcant investment opportunity exists in this medical sector, especially for artificial blood vessels, disposable diagnostic test kits, respiratory systems, rehabilitation equipment, orthopedic and implant devices, and neurosurgical devices and accessories. Thailand also takes part in groups such as the Asian Harmonization Working Party and the ASEAN Consultative Committee on Standards and Quality. Both of these strive to achieve conformity in medical device regulations and upgrade professional training in the region. Bivalve shellfish (mussels, oysters, clams, and cockles) are economically important sea food that are harvested commercially and preferentially consumed raw. As shellfish filter large volumes of water that trap suspended particles from water and many commercial species thrive in coastal marine environments where nutrient levels are high, but these areas may be contaminated with sewage and livestock effluent (29 and 30). Shellfish filter ~ 20– 100 L of seawater in 24 h (depending on species) and can accumulate very high (oo)cyst loads in their digestive gland, intestinal tract and gills (30 and 31) and can concentrate pathogenic organisms, which may act as potential vehicles of transmission to the consumer. In contaminated water, the concentration of (oo)cysts significantly increases the potential risk of infection to humans upon consumption of raw or undercooked shellfish (32 and 34). However, few cases of cryptosporidiosis and giardiasis have been positively linked to eating shellfish and this creates doubt regarding the significance of consuming protozoancontaminated shellfish as a public health concern (32). As many species of shellfish are eaten raw or lightly cooked, there is potential for consumers to ingest pathogens if they are not excreted or inactivated by the shellfish (30). Oysters and clams may present a higher risk of seafood-borne disease as they are normally eaten whole (including gills and intestinal tract) and raw or very lightly cooked (35). Cryptosporidium oocysts and Giardia cysts have been identified in shellfish from different regions of the world, many of which were marketable product destined for human consumption (36 - 41). Several studies record the presence of protozoa in water and shellfish, however these reports are disconnected because the majority of research has been conducted in different geographical locations or during different time periods and on different bivalve species (42). Evaluation of treated downstream water samples and neighbouring harvested shellfish (Ruditapes decussates and Mytilus galloprovincialis) in a geographically closed environment in Southern Italy found Giardia in 16/21 wastewater and 7/21 downstream water samples, and Cryptosporidium in 5/21 and 8/21 wastewater and downstream water samples, respectively (42). Surprisingly, IFA and molecular testing were negative for both protozoa in shellfish and various physical, ecological, and climatic conditions were suggested to account for the lack of contamination in shellfish. In Thailand, Cryptosporidium was found in 8.3% and 15.6% of market shellfish from Bangkok and Samut Prakan, respectively. The variance was attributed to differences in physical, ecological, and anthropogenic conditions including different contamination levels of the water sources (41). In future studies water samples should be collected at the same time as shellfish in order to correlate parasite levels in water with shellfish contamination. Further, serial sampling of a location over time is needed to understand the dynamics between shellfish contamination and their ability to naturally clear the parasites. Nevertheless, this study was carried out to investigate the presence of Cryptosporidium and Giardia protozoan parasites in oysters, the economically important shellfish and the most destined for consumption in Thailand. Cryptosporidium oocysts and Giardia cysts were detected in local markets of Thailand and its surroundings with 9 % and 8% of all oysters examined was positive. This is probably an underestimation of the true fraction of oysters contaminated with these parasites, compared with the previous reports. In addition, Fayer et al. (2002 and 2004) observed that only 50% of gill washings seeded with 500 Cryptosporidium oocysts tested positive with an immunofluorescence assay, indicating a low sensitivity of this detection method. These differences in positive samples from the different locations may be caused by physical, ecological and anthropogenic conditions. This could relay to different contamination levels of marine water by Cryptosporidium and Giardia (oo)cysts and consequently to contamination of harvested shellfish populations. Isolation of Cryptosporidium oocysts from naturally contaminated shellfish is technologically complex, and large variability exists regarding methods used to process shellfish samples for the presence of protozoan parasites. Several methods are available (32 and 43 - 48) but few data are available on recovery efficiencies of the various methods, their specificity or sensitivity, and no generally accepted gold standard method is currently available (30 and 32). Variation in recovery efficiencies exists among similar methods (12– 70%) and depends on mollusc species as well as between tissues examined (33, 47, 49 and 50-51). A recently developed processing method utilizing whole shellfish tissues from which protozoa (oo)cysts are isolated using immunomagnetic separation (IMS) and enumerated by IFA has achieved the highest recovery efficiencies to date, 70–80% for both Cryptosporidium and Giardia (30). Enumeration by IFA following IMS is the standard method of evaluation in water described in the USEPA-1623 method and has been used for processing shellfish samples, although underestimation in lightly contaminated oysters using this method has been estimated to be 50% (52 and 53). Purification of (oo)cysts by IMS also has contradictory results. IMS has been integrated into the detection of Cryptosporidium and Giardia in shellfish similar to the USEPA test descriptions for water sample concentrates (30, 39 and 54), but some researchers have found that the mucoid quality of various shellfish tissues compromises IMS function and others have discontinued use of the method (40 and 47). Furthermore, IMS is expensive (48), each test costing at least US$ 90. This cost makes routine large-scale monitoring efforts cost prohibitive. To counteract cost, most studies employing IMS either used a smaller sample size or pooled samples to facilitate processing of larger quantities of shellfish, both of which can compromise detection (39 and 47). In future research should be studied by using molecular methods for the detection of Cryptosporidium and Giardia in shellfish and drinking water supplies, which will be better understanding the transmission of these water and food-borne diseases. However, with or without IMS, shellfish samples are now commonly analyzed by both IFA and PCR. As there are discrepancies in both methods (e.g. IFA can stain empty oocyst walls and depends on the skill of the slide reader whereas PCR can appear negative due to a lack of sensitivity or positive due to presence of DNA from degraded cells), using a combination of techniques that rely on different substrates (e.g. proteins or DNA) can increase the likelihood of detection (32, 50 and 53). Some studies have identified positive water, fecal, or homogenized shellfish samples by IFA, and have then performed complementary PCR analysis for final confirmation and genotyping (32, 49 and 55). This study gave the efficient thai MPC equipment with low cost and instead use of imported products with no difference quality. 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M., Tabares E., Lopez-Rodas V. and Costas E. Detection of infectious Cryptosporidium parvum oocysts in mussels (Mytilus galloprovincialis) and cockles (Cerastoderma edule). Applied and Environmental Microbiology 2000; 66: 1866–1870. Acknowledgements : This work was supported by the Thailand Research Fund under the TRF MAG project and partial supported by E for L Co.Ltd. We would like to thank the local network authorities for effort to facilitate data and sample collection and the Faculty of Public Health, Mahidol University for institutional research support facilities.