Seasonal Retention and Release of Cryptosporidium parvum Oocysts by Environmental Biofilms in the Laboratory

Cryptosporidium is a genus of waterborne protozoan parasites that causes significant gastrointestinal disease in humans. These parasites can accumulate in environmental biofilms and be subsequently released to contaminate water supplies. Natural microbial assemblages were collected each season from an eastern Pennsylvania stream and used to grow biofilms in laboratory microcosms in which influx, efflux, and biofilm retention were determined from daily oocyst counts. For each seasonal biofilm, oocysts attached to the biofilm quickly during oocyst dosing. Upon termination of oocyst dosing, the percentage of oocysts retained within the biofilm decreased to a new steady state within 5 days. Seasonal differences in biofilm retention of oocysts were observed. The spring biofilm retained the greatest percentage of oocysts, followed (in decreasing order) by the winter, summer, and fall biofilms. There was no statistically significant correlation between the percentage of oocysts attached to the biofilm and (i) any measured stream water quality parameter (including temperature, pH, conductivity, and dissolved organic carbon concentration) or (ii) experimental temperature. Seasonal differences in oocyst retention persisted when biofilms were tested with stream water from a different season. These data suggest that seasonal variation in the microbial community and resulting biofilm architecture may be more important to oocyst transport in this stream site than water quality. The biofilm attachment and detachment dynamics of C. parvum oocysts have implications for public health, and the drinking water industry should recognize that the potential exists for pathogen-free water to become contaminated during the distribution process as a result of biofilm dynamics.Cryptosporidium is a genus of waterborne protozoan parasites that cause a gastrointestinal disease in humans (cryptosporidiosis) that can be prolonged and life-threatening for people with compromised immune systems. Recent advances in medical treatment for cryptosporidiosis exist but are not entirely effective for immunocompromised patients (1). In addition, conventional water treatment does not effectively target Cryptosporidium oocysts because the oocysts'' small size (4 to 8 μm) limits the ability of filters to remove them and, more importantly, oocysts are resistant to chlorine (25). Therefore, environmental control of Cryptosporidium is important to protect public health. To determine the risk of human exposure and infection, the fate and transport of Cryptosporidium oocysts in the environment, including biofilms, should be examined.Within the past two decades, biofilms have been recognized as ubiquitous habitats found on most surfaces exposed to water (20, 24). Environmental biofilms can rapidly accumulate pathogens at densities much higher than water column densities, and the potential for gradual or sudden pathogen loss from the biofilm exists long after entrapment (8, 22). Biofilm sloughing events are commonplace, occurring when a biofilm detaches from the substrate to be resuspended as large particles in the water column, and may result in the release of pathogen reservoirs from the biofilm into the water column (8).Biofilms have been identified as a possible contamination source for drinking water supplies, which may lead to infections for which the source cannot be identified (7, 9). An example of the impact of biofilm sloughing events on human health is seen in the cryptosporidiosis outbreak that occurred in Lancashire County, England, in March 2000 (10). After the outbreak, the oocyst source was identified as cattle feces from adjacent farmland that contaminated the drinking water after abnormally heavy rainfall. The water source was subsequently changed to two upland impounding reservoirs containing filtered surface water. However, oocysts persisted in the water distribution system for 19 days, with large peaks associated with major water main disturbance events, including the initial flushing of the system and a burst in the main supply pipe. This persistence of oocysts in the water supply was attributed to the release of oocysts trapped in biofilms on the interior surface of the distribution pipes and may have contributed to additional infections.Several studies have examined pathogen transport dynamics in biofilms using glass or latex beads of various sizes as surrogates for pathogens (5, 8, 16, 17). A few studies examined the attachment of C. parvum oocysts to biofilms but did not use natural microbial assemblages to make the biofilms (3, 23) or quantify how many oocysts attached or sloughed (9, 22). Rogers and Keevil (22) showed that oocysts attached to a biofilm composed of a natural microbial assemblage collected from a reservoir at a concentration of 1,400 oocysts/cm² after the addition of 10⁸ oocysts in 10 ml of sterile water. Dai and Hozalski (3) and Searcy et al. (23) used pure culture biofilms to demonstrate oocyst attachment; however, only Searcy et al. (23) accounted for sloughing, although no oocyst release from the biofilm was seen during the course of their experiments. Helmi et al. (9) noted attachment and detachment of oocysts from a natural biofilm but did not include a quantitative analysis to account for all oocysts in the flow system over time. None of these studies examined pathogen attachment seasonally over the course of a year. Seasonal changes in temperature, precipitation, and water quality (including nutrient availability) may have significant impacts on the microbial composition and functional structure of a biofilm (14). These changes include structural changes in the biofilm thickness and morphology, as well as changes in the water composition and suspended matter. In addition, seasonal changes in stream flow dynamics may alter biofilm composition and morphology, as well as oocyst attachment and release patterns.This study provides novel information about C. parvum oocyst attachment to biofilms grown in the laboratory from natural microbial assemblages collected seasonally (i.e., in January, April, July, and October) from Monocacy Creek in Bethlehem, PA. Previous work (26) showed that (i) a significant fraction of C. parvum oocysts adhered to the surface of experimental biofilms during a 3-day oocyst dosing period, (ii) a portion of the adhered oocysts immediately released from the biofilm, and (iii) a portion of the oocysts remained attached to the biofilm for a period of days after termination of oocyst dosing. Here, we test the hypotheses that (i) oocyst retention by biofilms varies seasonally and (ii) seasonal changes in water quality influence oocyst retention.     

Capture and retention of Cryptosporidium parvum oocysts by Pseudomonas aeruginosa biofilms

The association of Cryptosporidium oocysts with biofilm communities can influence the propagation of this pathogen through both environmental systems and water treatment systems. We observed the capture and retention of C. parvum oocysts in Pseudomonas aeruginosa biofilms using laboratory flow cells. Biofilms were developed in two different growth media using two different strains of P. aeruginosa, a wild-type strain (PAO1) and a strain that overproduces the exopolysaccharide alginate (PDO300). Confocal laser-scanning microscopy was used in conjunction with image analysis to assess the structure of the biofilms prior to introducing oocysts into the flow cells. More oocysts were captured by the biofilm-coated surfaces than the abiotic glass surface in both media. There was no significant difference in capture across the two strains of P. aeruginosa biofilm, but the fraction of oocysts captured was positively related to biofilm roughness and surface-area-to-volume ratio. Once captured, oocysts were retained in the biofilm for more than 24 h and were not released after a 40-fold increase in the system flow rate. We believe the capture and retention of oocysts by biofilm communities can impact the environmental transmission of C. parvum, and this interaction should be taken into consideration when predicting the migration of pathogens in the environment.     

Capture and Retention of Cryptosporidium parvum Oocysts by Pseudomonas aeruginosa Biofilms

The association of Cryptosporidium oocysts with biofilm communities can influence the propagation of this pathogen through both environmental systems and water treatment systems. We observed the capture and retention of C. parvum oocysts in Pseudomonas aeruginosa biofilms using laboratory flow cells. Biofilms were developed in two different growth media using two different strains of P. aeruginosa, a wild-type strain (PAO1) and a strain that overproduces the exopolysaccharide alginate (PDO300). Confocal laser-scanning microscopy was used in conjunction with image analysis to assess the structure of the biofilms prior to introducing oocysts into the flow cells. More oocysts were captured by the biofilm-coated surfaces than the abiotic glass surface in both media. There was no significant difference in capture across the two strains of P. aeruginosa biofilm, but the fraction of oocysts captured was positively related to biofilm roughness and surface-area-to-volume ratio. Once captured, oocysts were retained in the biofilm for more than 24 h and were not released after a 40-fold increase in the system flow rate. We believe the capture and retention of oocysts by biofilm communities can impact the environmental transmission of C. parvum, and this interaction should be taken into consideration when predicting the migration of pathogens in the environment.     

Reproductive patterns and secondary production of <Emphasis Type="Italic">Gammaropsis japonicus</Emphasis> (Crustacea,Amphipoda) on the seagrass <Emphasis Type="Italic">Zostera marina</Emphasis> of Korea

It is essential to know the nutrient limitation status of biofilms to understand how they may buffer uptake and export of nutrients from polluted watersheds. We tested the effects of nutrient additions on biofilm biomass (chlorophyll a, ash free dry mass (AFDM), and autotrophic index (AI, AFDM/chl a)) and metabolism via nutrient-diffusing substrate bioassays (control, nitrogen (N), phosphorus (P), and N + P treatments) at 11 sites in the Upper Snake River basin (southeast Idaho, USA) that differed in the magnitude and extent of human-caused impacts. Water temperature, turbidity, and dissolved inorganic N concentrations all changed seasonally at the study sites, while turbidity and dissolved inorganic N and P also varied with impact level. Chl a and AI on control treatments suggested that the most heavily impacted sites supported more autotrophic biofilms than less-impacted sites, and that across all sites biofilms were more heterotrophic in autumn than in summer. Nutrient stimulation or suppression of biofilm biomass was observed for chl a in 59% of the experiments and for AFDM in 33%, and the most frequent response noted across all study sites was N limitation. P suppression of chl a was observed only at the most-impacted sites, while AFDM was never suppressed by nutrients. When nutrient additions did have significant effects on metabolism, they were driven by differences in biomass rather than by changes in metabolic rates. Our study demonstrated that biofilms in southeast Idaho rivers were primarily limited by N, but nutrient limitation was more frequent at sites with good water quality than at those with poor water quality. Additionally, heterotrophic and autotrophic biofilm components may respond differently to nutrient enrichment, and nutrient limitation of biofilm biomass should not be considered a surrogate for metabolism in these rivers. Handling editor: D. Ryder     

Near real-time detection of Cryptosporidium parvum oocyst by IgM-functionalized piezoelectric-excited millimeter-sized cantilever biosensor

Piezoelectric-excited millimeter-sized cantilever (PEMC) biosensors were fabricated and functionalized with immunoglobulin M (IgM) for the detection of Cryptosporidium parvum oocyst in a flow configuration at 1 mL/min. The detection of 100, 1000, and 10,000 oocysts/mL was achieved with a positive sensor response in less than 1 min. Bovine serum albumin (BSA) was used as a blocking agent in each experiment and was shown to eliminate non-specific binding. The sensor's resonance frequency response correlates with C. parvum oocyst concentration logarithmically. The oocyst attachment rate was found to increase by an order of magnitude in increasing concentration from 100 to 10,000 oocysts/mL. The significance of these results is that IgM-functionalized PEMC sensors are highly selective and sensitive to C. parvum oocyst and therefore, have the potential to accurately identify and quantify C. parvum oocyst in drinking water.     

Retention and Release of Cryptosporidium parvum Oocysts by Experimental Biofilms Composed of a Natural Stream Microbial Community

Cryptosporidium parvum oocysts accumulate on biofilm surfaces. The percentage of oocysts attached to biofilms remained nearly constant while oocysts were supplied to the system but decreased to a new steady-state level once oocysts were removed from the feed. More oocysts attached to summer biofilm cultures than winter biofilm cultures.Cryptosporidium causes a potentially life-threatening gastrointestinal disease. Because conventional water treatment may not effectively target Cryptosporidium, source water monitoring and protection are important to avoid infection outbreaks.Biofilms can accumulate pathogens at densities that are much higher than water column densities, with the potential for pathogen release long after entrapment (5, 13, 15, 19). Biofilms have been identified as a drinking water contamination source (7), causing infections for which the source cannot be identified (4, 6).Several previous studies examined pathogen transport in biofilms using Cryptosporidium parvum oocysts (2, 6, 15, 16) or beads as pathogen surrogates (3, 5, 11, 12). The former studies did not use natural microbial assemblages (2, 16) or quantify oocyst attachment or sloughing (6, 15). The current study provides novel information about C. parvum oocyst attachment to environmental biofilms, including a mass balance analysis to identify the daily number of oocysts that (i) remained in the flowing water or were sloughed from the biofilm and (ii) were attached to the biofilm. We imaged biofilms using scanning confocal laser microscopy, as used in other studies (9, 17, 20, 21), to identify spatial patterns of oocyst attachment.Biofilms were scraped from rocks found in Monocacy Creek (Bethlehem, PA) into 1 liter of creek water in January 2007 (winter biofilm culture) and July 2008 (summer biofilm culture). The biofilm suspension was vacuum filtered through a 6-μm cellulose filter. The filtrate was centrifuged (1,754 × g for 15 min), and the resulting biofilm pellet was resuspended in 1 ml of raw creek water. The cell concentration was quantified by DAPI (4′,6-diamidino-2-phenylindole) staining (14). Cells were split into aliquots (5 × 10⁶ cells each) and stored at −80°C in cryovials containing 30% glycerol.Single-channel flow chambers (length by width by height, 24 mm by 8 mm by 4 mm) with glass coverslips (Stovall Life Science, Inc., Greensboro, NC) were inoculated with 5 × 10⁶ biofilm cells for 24 h before the flow was started. Filter-sterilized creek water was used as the flow medium. A 12-channel peristaltic pump (Ismatec, Glattbrugg, Switzerland) maintained a constant flow of 0.2 mm/s (1).For biofilm imaging, the following two setups were used: (i) 1 × 10⁴ C. parvum oocysts (Iowa isolate; Waterborne, Inc., New Orleans, LA) (all oocysts were used within 3 weeks of shedding) in the influent each day for 3 days and (ii) 3 × 10⁴ C. parvum oocysts added to the influent for the last 24 h of a 3-day flow experiment. Biofilms were imaged with a Zeiss LSM 510 META laser scanning microscope, using an argon laser (458-nm, 477-nm, 488-nm, and 514-nm excitation wavelengths) and a HeNe1 laser (543-nm excitation wavelength). Biofilms were fixed with methanol, blocked using a 1:10 dilution of fetal bovine serum, and stained with 20 μM SYTO 9 (Invitrogen, Molecular Probes, Eugene, OR) (16). C. parvum oocysts in the biofilm were stained with a Cy3-conjugated monoclonal antibody solution specific for Cryptosporidium (Waterborne, Inc.) (16).For the mass balance analysis, C. parvum oocysts (1 × 10⁴ per day for 3 days) were added to 500 ml constantly stirred influent water to keep oocysts in suspension. Influent water was replaced each day. Experiments to quantify sloughing included 2 or 5 additional days with oocyst-free feed water, for a total of 5 or 8 days. Biofilms used for the 3- and 5-day experiments were grown with the winter biofilm culture; biofilms used for the 8-day experiments were grown with the summer biofilm culture.After each 24-hour period, the remaining influent and effluent waters were processed by membrane filtration (MF) and immunomagnetic separation (IMS) to recover the oocysts. On the last day of each experiment, biofilms were scraped from the flow chambers, resuspended in sterile creek water, and also processed by MF and IMS. MF was performed according to the method of Oda et al. (10), using the 3-μm filter only. IMS was performed on the filtrate using the Aureon IMS kit (ImmTech, Inc., New Windsor, MD), and oocysts were dissociated from the magnetic beads with 0.05 M HCl. IMS products were counted by hemocytometry and corrected for MF and IMS processing losses. An average IMS recovery of 65% ± 4.2% standard error (SE) (determined by four trials using 1 × 10⁴ oocysts in deionized water) was used. MF recoveries were consistent within each day but varied between days. Therefore, an MF recovery control was performed each day using 1 × 10⁴ oocysts in 1 liter deionized water to obtain a daily MF correction factor.The mass balance analysis demonstrated that these methods were effective for tracking oocysts throughout the flow system for the experiment''s duration, accounting for all the oocysts within 8% (Table ​(Table1).1). In a control flow chamber with no biofilm growth (i.e., a clean glass surface), oocyst loss within the system was 1% or less, indicating that very few oocysts attached to any abiotic surface within the flow system. Laboratory biofilms composed of natural microbial assemblages were successfully created, although grazing impacts that would affect biofilm dynamics in the environment were eliminated. The thicknesses of laboratory biofilms (average thickness, 39.6 μm; SD, 4.7 μm; n = 16) were not statistically different (P of 0.17 by independent t test) than those of natural biofilms in Monocacy Creek (average thickness, 35.8 μm; SD, 10.2 μm; n = 36).

TABLE 1.

Mass balance analysis of biofilms grown for 3, 5, and 8 days, with 3-day oocyst dosing^a

Association of Cryptosporidium parvum with suspended particles: impact on oocyst sedimentation

The association of Cryptosporidium parvum oocysts with suspended particles can alter the oocysts' effective physical properties and influence their transport in aquatic systems. To assess this behavior, C. parvum oocysts were mixed with various suspended sediments under a variety of water chemical conditions, and the resulting settling of the oocysts was observed. Direct microscopic observations showed that oocysts attached to suspended sediments. Settling column and batch experiments demonstrated that oocysts are removed from suspension at a much higher rate when associated with sediments. The rate of oocyst sedimentation depended primarily on the type of sediment with which the oocysts were mixed. Changes in background water conditions had a relatively small impact on the extent of oocyst-particle association and the resulting oocyst deposition. We believe that the ubiquitous association of C. parvum oocysts with suspended particles enhances the sedimentation of oocysts in natural waters and that this interaction should generally be considered when predicting the migration of pathogens in the environment.     

Influence of surface characteristics on the stability of Cryptosporidium parvum oocysts

Microelectrophoresis is a common technique for probing the surface chemistry of the Cryptosporidium parvum oocyst. Results of previous studies of the electrophoretic mobility of C. parvum oocysts in which microelectrophoresis was used are incongruent. In this work we demonstrated that capillary electrophoresis may also be used to probe the surface characteristics of C. parvum oocysts, and we related the surface chemistry of C. parvum oocysts to their stability in water. Capillary electrophoresis results indicated that oocysts which were washed in a phosphate buffer solution had neutrally charged surfaces. Inactivation of oocysts with formalin did not influence their electrophoretic mobility, while oocyst populations that were washed in distilled water consisted of cells with both neutral and negative surface charges. These results indicate that washing oocysts in low-ionic-strength distilled water can impart a negative charge to a fraction of the oocysts in the sample. Rapid coagulation experiments indicated that oocysts did not aggregate in a 0.5 M NaCl solution; oocyst stability in the salt solution may have been the result of Lewis acid-base forces, steric stabilization, or some other factor. The presence of sucrose and Percoll could not be readily identified on the surface of C. parvum oocysts by attenuated total reflectance-Fourier transform infrared spectroscopy, suggesting that these purification reagents may not be responsible for the stability of the uncharged oocysts. These findings imply that precipitate enmeshment may be the optimal mechanism of coagulation for removal of oocysts in water treatment systems. The results of this work may help elucidate the causes of variation in oocyst surface characteristics, may ultimately lead to improved removal efficiencies in full-scale water treatment systems, and may improve fate and transport predictions for oocysts in natural systems.     

Detection of Cryptosporidium in water by using polypropylene cartridge filters

Members of the genus Cryptosporidium are protozoan parasites that cause gastroenteritis in humans and animals and appear to be spread largely by the fecal-oral route. A method was developed for the concentration and detection of Cryptosporidium oocysts in water to assess their occurrence in the environment and potential for waterborne disease transmission. This method was developed by using spun polypropylene cartridge filters. Optimal conditions for concentration, filter elution, filter porosity, and detection were determined. Fluoresceinated monoclonal antibodies were used for oocyst detection. Experiments also were conducted to study the effect of flow rate, low oocyst numbers, and the addition of detergents on recovery and retention of oocysts. The method that was developed was sensitive enough to detect oocysts at levels of less than 1 per liter. Using this method, we isolated Cryptosporidium oocysts from secondarily treated sewage.     

Detection of Cryptosporidium in water by using polypropylene cartridge filters.

Members of the genus Cryptosporidium are protozoan parasites that cause gastroenteritis in humans and animals and appear to be spread largely by the fecal-oral route. A method was developed for the concentration and detection of Cryptosporidium oocysts in water to assess their occurrence in the environment and potential for waterborne disease transmission. This method was developed by using spun polypropylene cartridge filters. Optimal conditions for concentration, filter elution, filter porosity, and detection were determined. Fluoresceinated monoclonal antibodies were used for oocyst detection. Experiments also were conducted to study the effect of flow rate, low oocyst numbers, and the addition of detergents on recovery and retention of oocysts. The method that was developed was sensitive enough to detect oocysts at levels of less than 1 per liter. Using this method, we isolated Cryptosporidium oocysts from secondarily treated sewage.     

Association of Cryptosporidium parvum with Suspended Particles: Impact on Oocyst Sedimentation

The association of Cryptosporidium parvum oocysts with suspended particles can alter the oocysts' effective physical properties and influence their transport in aquatic systems. To assess this behavior, C. parvum oocysts were mixed with various suspended sediments under a variety of water chemical conditions, and the resulting settling of the oocysts was observed. Direct microscopic observations showed that oocysts attached to suspended sediments. Settling column and batch experiments demonstrated that oocysts are removed from suspension at a much higher rate when associated with sediments. The rate of oocyst sedimentation depended primarily on the type of sediment with which the oocysts were mixed. Changes in background water conditions had a relatively small impact on the extent of oocyst-particle association and the resulting oocyst deposition. We believe that the ubiquitous association of C. parvum oocysts with suspended particles enhances the sedimentation of oocysts in natural waters and that this interaction should generally be considered when predicting the migration of pathogens in the environment.     

Environmental temperature controls Cryptosporidium oocyst metabolic rate and associated retention of infectivity

Cryptosporidium is a significant cause of water-borne enteric disease throughout the world and represents a challenge to the water industry and a threat to public health. In this study we report the use of a cell culture-TaqMan PCR assay to measure oocyst inactivation rates in reagent-grade and environmental waters over a range of temperatures. While oocysts incubated at 4 degrees C and 15 degrees C remained infective over the 12-week holding period, we observed a 4 log(10) reduction in infectivity for both 20 and 25 degrees C incubation treatments at 12 and 8 weeks, respectively, for all water types examined, a faster rate of inactivation for oocysts than previously reported. This temperature-dependent inactivation was further investigated using a simple and rapid ATP assay described herein. Time course experiments performed in reagent-grade water at incubation temperatures of 4, 15, 20, 25, 30, and 37 degrees C identified a close relationship between oocyst infectivity and oocyst ATP content, demonstrating that temperature inactivation at higher temperatures is a function of increased oocyst metabolic activity. While water quality did not affect oocyst inactivation, biological antagonism appears to be a key factor affecting oocyst removal from environmental waters. Both the cell culture-TaqMan PCR assay and the ATP assay provide a sensitive and quantitative method for the determination of environmental oocyst inactivation, providing an alternative to the more costly and time-consuming mouse infection assay. The findings presented here relating temperature to oocyst inactivation provide valuable information for determining the relative risks associated with Cryptosporidium oocysts in water.     

Influence of Surface Characteristics on the Stability of Cryptosporidium parvum Oocysts

Microelectrophoresis is a common technique for probing the surface chemistry of the Cryptosporidium parvum oocyst. Results of previous studies of the electrophoretic mobility of C. parvum oocysts in which microelectrophoresis was used are incongruent. In this work we demonstrated that capillary electrophoresis may also be used to probe the surface characteristics of C. parvum oocysts, and we related the surface chemistry of C. parvum oocysts to their stability in water. Capillary electrophoresis results indicated that oocysts which were washed in a phosphate buffer solution had neutrally charged surfaces. Inactivation of oocysts with formalin did not influence their electrophoretic mobility, while oocyst populations that were washed in distilled water consisted of cells with both neutral and negative surface charges. These results indicate that washing oocysts in low-ionic-strength distilled water can impart a negative charge to a fraction of the oocysts in the sample. Rapid coagulation experiments indicated that oocysts did not aggregate in a 0.5 M NaCl solution; oocyst stability in the salt solution may have been the result of Lewis acid-base forces, steric stabilization, or some other factor. The presence of sucrose and Percoll could not be readily identified on the surface of C. parvum oocysts by attenuated total reflectance-Fourier transform infrared spectroscopy, suggesting that these purification reagents may not be responsible for the stability of the uncharged oocysts. These findings imply that precipitate enmeshment may be the optimal mechanism of coagulation for removal of oocysts in water treatment systems. The results of this work may help elucidate the causes of variation in oocyst surface characteristics, may ultimately lead to improved removal efficiencies in full-scale water treatment systems, and may improve fate and transport predictions for oocysts in natural systems.     

Viability and infectivity of Cryptosporidium parvum oocysts are retained upon intestinal passage through a refractory avian host.

Six Cryptosporidium-free Peking ducks (Anas platyrhynchos) were each orally inoculated with 2.0 x 10(6) Cryptosporidium parvum oocysts infectious to neonatal BALB/c mice. Histological examination of the stomachs jejunums, ilea, ceca, cloacae, larynges, tracheae, and lungs of the ducks euthanized on day 7 postinoculation (p.i.) revealed no life-cycle stages of C. parvum. However, inoculum-derived oocysts extracted from duck feces established severe infection in eight neonatal BALB/c mice (inoculum dose, 2.5 x 10(5) per mouse). On the basis of acid-fast stained direct wet smears, 73% of the oocysts in duck feces were intact (27% were oocyst shells), and their morphological features conformed to those of viable and infectious oocysts of the original inoculum. The fluorescence scores of the inoculated oocysts, obtained by use of the MERIFLUOR test, were identical to those obtained for the feces-recovered oocysts (the majority were 3+ to 4+). The dynamics of oocyst shedding showed that the birds released a significantly higher number of intact oocysts than the oocyst shells (P < 0.01). The number of intact oocysts shed (87%) during the first 2 days p.i. was significantly higher than the number shed during the remaining 5 days p.i. (P < 0.01) and significantly decreased from day 1 to day 2 p.i. (P < 0.01). The number of oocyst shells shed during 7 days p.i. did not vary significantly (P > 0.05). The retention of infectivity of C. parvum oocysts after intestinal passage through an aquatic bird has serious epidemiological and epizootiological implications. Waterfowl may serve as mechanical vectors for the waterborne oocysts and may enhance contamination of surface waters with C. parvum. As the concentration of Cryptosporidium oocysts in source waters is attributable to watershed management practices, the watershed protection program should consider waterfowl as a potential factor enhancing contamination of the source water with C. parvum.     

Effects of time and watershed characteristics on the concentration of Cryptosporidium oocysts in river water.

Water samples were collected from four locations on two rivers in Washington State and analyzed by membrane filtration-immunofluorescence assay to establish Cryptosporidium oocyst concentrations. Sampling locations were selected to evaluate effects of watershed character, from pristine mountain to downstream agricultural, on oocyst concentrations. Samples were collected at six biweekly intervals from late June to early September, with two additional sets of five samples taken on separate days (one set taken at bihourly intervals and one set taken simultaneously). Cryptosporidium oocysts were found in 34 of 35 samples at concentrations ranging from about 0.2 to 65 oocysts per liter. Oocyst concentrations were highest early in the sampling period, when they were influenced by postrainfall runoff, and decreased through the summer months. Oocyst concentrations found in ten samples collected on two days (5 samples per day) showed no short-term variations. Oocyst concentrations and oocyst production per square mile (ca. 2.6 km2) of watershed found in water draining a controlled public water supply watershed were the lowest observed. The concentrations and production rates for drainage from an adjacent, comparable, but uncontrolled watershed were nearly 10 times higher. The concentration and production rates of the downstream area influenced by dairy farming were nearly 10 times higher than rates at the upstream stations. The data showed clearly that oocyst concentrations were consistently observed above the detection limit of the analytical method, about 0.1 oocysts per liter; that oocyst concentrations were continuous as opposed to intermittent; and that watershed character and management affected surface water oocyst concentrations significantly.     

Effects of time and watershed characteristics on the concentration of Cryptosporidium oocysts in river water.

Water samples were collected from four locations on two rivers in Washington State and analyzed by membrane filtration-immunofluorescence assay to establish Cryptosporidium oocyst concentrations. Sampling locations were selected to evaluate effects of watershed character, from pristine mountain to downstream agricultural, on oocyst concentrations. Samples were collected at six biweekly intervals from late June to early September, with two additional sets of five samples taken on separate days (one set taken at bihourly intervals and one set taken simultaneously). Cryptosporidium oocysts were found in 34 of 35 samples at concentrations ranging from about 0.2 to 65 oocysts per liter. Oocyst concentrations were highest early in the sampling period, when they were influenced by postrainfall runoff, and decreased through the summer months. Oocyst concentrations found in ten samples collected on two days (5 samples per day) showed no short-term variations. Oocyst concentrations and oocyst production per square mile (ca. 2.6 km2) of watershed found in water draining a controlled public water supply watershed were the lowest observed. The concentrations and production rates for drainage from an adjacent, comparable, but uncontrolled watershed were nearly 10 times higher. The concentration and production rates of the downstream area influenced by dairy farming were nearly 10 times higher than rates at the upstream stations. The data showed clearly that oocyst concentrations were consistently observed above the detection limit of the analytical method, about 0.1 oocysts per liter; that oocyst concentrations were continuous as opposed to intermittent; and that watershed character and management affected surface water oocyst concentrations significantly.     

Aging of Cryptosporidium parvum oocysts in river water and their susceptibility to disinfection by chlorine and monochloramine.

Cryptosporidium parvum oocysts were aged in waters from both the St. Lawrence River and the Ottawa River. In situ survival experiments were carried out by incubating the oocysts in either dialysis cassettes or microtubes floated into an overflow tank. A significant portion of the oocysts survived in the test waters for several weeks. Oocyst survival in the St. Lawrence River was better in membrane-filtered (0.2 microm-pore diameter) water than in unfiltered water, suggesting that biological antagonism may play a role in the environmental fate of the parasite. Oocysts aged in river waters under in situ conditions and control oocysts kept refrigerated in synthetic water (100 ppm as CaCO3); pH 7.0) were subjected to the same disinfection protocol. Aged oocysts were at least as resistant as, if not more resistant than, the control oocysts to disinfection. This indicates that the oocysts surviving in the water environment may be just as difficult to inactivate by potable water disinfection as freshly shed oocysts. Therefore, water treatment should not be based on the assumption that environmental oocysts may be more easily inactivated than freshly shed oocysts. First-order kinetics die-off rates varied from one river to another (from 0.013 to 0.039 log(10).day(-1)) and from one experiment to another with water from the same river collected at different times. Calculation of the die-off rates based on either in vitro excystation or in vitro excystation in combination with total counts (overall die-off rates) showed that the assessment of oocyst viability by microscopic methods must account for the total oocyst loss observed during long-term inactivation assays of river waters.     

Development of patent infection in immunosuppressed C57Bl/6 mice with a single Cryptosporidium meleagridis oocyst

The ability of Cryptosporidium meleagridis to produce patent infection was studied in adult C57BL/6 mice that were immunosuppressed with dexamethasone phosphate provided in the drinking water at a dosage of 16 microg/ml. Four days after the onset of immunosuppression, mice were orally challenged with 1, 3, 10, or 1,000 C. meleagridis TU1867 oocysts per mouse. The mice were monitored daily for 18 days postinoculation for oocyst shedding. Five of 10 mice given a single oocyst, 4 of 5 mice given 3 oocysts, and all 9 mice given either 10 or 1,000 oocysts became infected and began shedding oocysts 5-7 days after challenge and continued to shed oocysts until the end of the experiment on day 18 postchallenge. Approximately 10(7) oocysts per mouse per day were excreted, regardless of the challenge dose. Neither the noninfected, immunosuppressed nor the inoculated, nonimmunosuppressed control mice shed oocysts. The excreted oocysts were confirmed to be those of C. meleagridis by polymerase chain reaction-restriction fragment length polymorphism analysis. We show that C. meleagridis, originally classified as an avian pathogen but recently found in humans with cryptosporidiosis, can produce patent infection in mice infected with a single oocyst. Moreover, we demonstrate that the immunosuppressed C57BL/6 adult mouse is an ideal host for the propagation of clonal populations of C. meleagridis isolates for laboratory studies.     

Detection of infectious Cryptosporidium parvum oocysts in surface and filter backwash water samples by immunomagnetic separation and integrated cell culture-PCR.

A new strategy for the detection of infectious Cryptosporidium parvum oocysts in water samples, which combines immunomagnetic separation (IMS) for recovery of oocysts with in vitro cell culturing and PCR (CC-PCR), was field tested with a total of 122 raw source water samples and 121 filter backwash water grab samples obtained from 25 sites in the United States. In addition, samples were processed by Percoll-sucrose flotation and oocysts were detected by an immunofluorescence assay (IFA) as a baseline method. Samples of different water quality were seeded with viable C. parvum to evaluate oocyst recovery efficiencies and the performance of the CC-PCR protocol. Mean method oocyst recoveries, including concentration of seeded 10-liter samples, from raw water were 26.1% for IMS and 16.6% for flotation, while recoveries from seeded filter backwash water were 9.1 and 5.8%, respectively. There was full agreement between IFA oocyst counts of IMS-purified seeded samples and CC-PCR results. In natural samples, CC-PCR detected infectious C. parvum in 4.9% (6) of the raw water samples and 7.4% (9) of the filter backwash water samples, while IFA detected oocysts in 13.1% (16) of the raw water samples and 5.8% (7) of the filter backwash water samples. All CC-PCR products were confirmed by cloning and DNA sequence analysis and were greater than 98% homologous to the C. parvum KSU-1 hsp70 gene product. DNA sequence analysis also revealed reproducible nucleotide substitutions among the hsp70 fragments, suggesting that several different strains of infectious C. parvum were detected.     

Development of pure culture biofilms of P. putida on solid supports

Pseudomonas putida biofilms were developed on and biofilm accumulation rate data were obtained for the following two classes of support materials: charged surfaces and noncharged hydrophobic and hydrophilic surfaces. The effects of surface roughness and porosity on the rate of microbial attachment were also examined.Materials bearing a net positive or negative surface charge supported the greatest biofilm accumulation and the highest biofilm accumulation rate. Uncharged hydrophobic materials achieved the next greatest biofilm accumulation, averaging approximately 50% of the total biomass which was accumulated on the charged surface materials after 16 days. Uncharged hydrophilic materials supported very little biofilm development. In general, biofilm accumulation increased with decreased surface roughness. The effect of pore size on biofilm accumulation was not conclusive.The biofilm accumulation kinetics showed an exponential accumulation rate for the charged surfaces and an approximately linear accumulation rate for the hydrophobic materials. This difference in accumulation kinetics is consistent with proposed differences in the physicochemical mechanism governing attachment to these two types of surface materials.