Abstract
Solar radiation reduces Cryptosporidium infectivity. Biofilms grown from stream microbial assemblages inoculated with oocysts were exposed to solar radiation. The infectivity of oocysts attached at the biofilm surface and oocysts suspended in water was about half that of oocysts attached at the base of a 32-μm biofilm.
TEXT
Cryptosporidium parvum is a public health concern, infecting thousands of individuals as a result of contaminated water (2, 3, 13, 32). Traditional water treatment targeting Cryptosporidium is difficult (28). Artificial UV radiation has irreversible effects on oocyst infectivity (5, 8, 11, 12, 16, 23, 33) but can be cost-prohibitive, so the use of natural solar radiation to inactivate oocysts is worth investigating. Solar radiation (UV and non-UV wavelengths) has been shown through cell culture infectivity to effectively disinfect C. parvum (6).
Biofilms retain pathogens at high densities, with the potential for release to the water, and protect oocysts from environmental conditions (9, 18, 24, 28, 30, 31); biofilm cells are more resistant to biocides and environmental conditions than planktonic cells of the same species (1, 10, 14, 17, 19, 31).
Oocysts (i) attached to the biofilm surface, (ii) attached at depth in the biofilm, and (iii) attached to a biofilm resuspended in water were exposed to solar radiation to test the hypothesis that biofilms provide protection for oocysts against exposure to solar radiation.
Biofilms and creek water were collected from Monocacy Creek (Bethlehem, PA) (30, 31). Biofilms were scraped from rocks, filtered through 6-μm filter paper, and centrifuged, and the pelleted biofilm cells were resuspended in filter-sterilized creek water (0.22-μm-pore-size filter). Cell concentration was determined by DAPI (4′,6-diamidino-2-phenylindole) staining (19). Aliquots of 5 × 106 cells in sterile creek water with 30% glycerol were frozen (−80°C) until used to inoculate flow chambers.
Single-channel flow chambers (24 mm by 8 mm by 4 mm [length by width by height]) with glass coverslips (Stovall Life Science, Inc., Greensboro, NC) were inoculated with 5 ×106 biofilm cells for 24 h before flow of sterile creek water was started. A 12-channel peristaltic pump (IPC pump; Ismatec, Glattbrugg, Switzerland) maintained constant laminar flow (0.17 ml/min) (4).
Biofilms were grown for 3 days with 2.5 × 106 C. parvum oocysts (Iowa isolate; Waterborne, Inc., New Orleans, LA) seeded into the sterile creek water influent (8.3 × 105 oocysts/liter). Biofilm thickness was measured using a scanning confocal microscope (Zeiss LSM 510 META laser scanning microscope).
Three experiments (Table 1) were performed using four treatments: (i) oocysts attached at the top of a biofilm (the sun-exposed surface), (ii) oocysts attached at the bottom of a 30-μm biofilm (with the biofilm between the oocysts and the sun), (iii) biofilm-associated oocysts scraped from the flow chamber and resuspended in creek water (simulating oocysts that detach from biofilm), and (iv) oocysts in sterile creek water. All experiments included light and dark controls: light controls consisted of oocysts in creek water exposed to sunlight, and dark controls were wrapped in aluminum foil to block sunlight. The three experiments were exposed to solar radiation for 90, 50, and 60 min, respectively. The experimental duration was determined by the total solar radiation (Table 1), which varied as a result of weather and season conditions and was monitored in real time using a calibrated solar radiometer (PUV-500; Biospherical Instruments, Inc., San Diego, CA).
Table 1.
Experiment | Date | Dose (kJ/m2) |
No. of 320-nm exposure daysa | |||
---|---|---|---|---|---|---|
305 nm | 320 nm | 340 nm | 380 nm | |||
A: Oocysts on top and bottom of biofilm | July 9 | 0.7 | 4.0 | 8.6 | 10.4 | 0.37 |
B: Biofilm-associated oocysts resuspended in creek water | July 15 | 0.5 | 3.1 | 6.6 | 8.3 | 0.28 |
C: Oocysts on top and bottom of biofilm and resuspended biofilm-associated oocysts | August 25 | 0.3 | 2.5 | 5.5 | 6.9 | 0.23 |
A value of 10.9 kJ/m2 represents one 320-nm exposure day or the amount of solar UV at 320 nm received during 1 day of full sunlight (no clouds) at the water surface during summer solstice and average ozone conditions at 41°N latitude (7).
Experiments were performed on a rooftop with no shadows. Temperature was maintained at 2 to 5°C using a water bath, ice bath, and recirculating pump, monitored with iButton temperature sensors (Dallas Semiconductor, Dallas, TX).
Because previous work demonstrated that oocysts attach and remain at the biofilm surface under these flow conditions (30), flow chambers were placed face up for experiments exposing oocysts at the top of the biofilm to direct solar radiation. For treatments with oocysts at the bottom of the biofilm, flow chambers were placed upside down, allowing the solar radiation to pass through the biofilm before reaching the oocysts. For treatments with biofilm-associated oocysts, biofilms were scraped from the flow chamber and resuspended in creek water. This suspension was injected back into the flow chamber for solar exposure. Oocysts with no biofilm association were tested by suspending oocysts in sterile creek water injected into the flow chamber.
After exposure, biofilms were resuspended in sterile creek water, and oocysts were purified by immunomagnetic separation (IMS) using the Virusys IMS kit (Virusys Co., Sykesville, MD) according to the manufacturer's protocol (oocysts were dissociated from beads using 0.05 M HCl).
Oocyst infectivity was determined using in vitro cell culture infection of human ileocecal adenocarcinoma (HCT-8) cells grown in eight-well chamber slides (22, 27). Oocysts were pretreated with 10% sodium hypochlorite, and oocyst concentration was determined by hemocytometry. For each treatment (performed in duplicate), six wells on each chamber slide were infected with 200 oocysts and two wells were left uninfected to monitor the cell monolayer. The infectivity of the oocyst stock (stored at 4°C in the dark) was also determined. Infected chamber slides were incubated (37°C, 5% CO2, 48 h) and stained with Sporo-Glo antibody (Waterborne, Inc., New Orleans, LA) according to the manufacturer's protocol. Infection foci were counted using a Nikon epifluorescence microscope (Nikon, Inc., Melville, NY), and the percentage of infective oocysts was calculated by dividing the number of infection foci by 200 (number of oocysts inoculated into each well).
Transmittance through flow chambers containing (i) creek water, (ii) intact biofilm, and (iii) biofilm scraped from the flow chamber and resuspended in water was measured in the lab using custom spectrophotometer components (USB200 diode array UV-VIS spectrometer [Ocean Optics, Inc., Dunedin, FL] and 50-mm reflectance integrating sphere illuminated with an Ocean Optics PX-2 xenon strobe lamp emitting 250 to 850 nm [Avantes, Inc., Broomfield, CO]). Attenuation by the flow chamber with deionized water was not significant (19% at 320 nm) compared to biofilm attenuation and was used as 100% relative transmittance.
Independent t tests were used to determine if a significant difference existed between oocyst infectivity in all treatments using the Analyze-it add-in (Analyze-it Software, Ltd., Leeds, England) for Microsoft Excel.
Sun-exposed oocysts were less infectious than oocysts in the dark (P < 0.01) (Fig. 1). These data support the observations of others that solar radiation reduces oocyst infectivity (6, 11, 15); however, approximately 20% of the oocysts exposed to the highest levels of solar radiation remained infectious and a potential public health threat.
Total solar exposure for each experiment was converted to 320-nm exposure days using a value of 10.9 kJ/m2, the amount of solar UV at 320 nm received during a day of full sunlight during summer solstice and average ozone conditions at 41°N latitude (7). Despite various lengths of exposure time (90, 50, and 60 min for the July 9, July 15, and August 25 experiments, respectively), sky conditions resulted in all three experiments having similar solar exposure (0.37, 0.28, and 0.23 exposure days, respectively) (Table 1), and these exposures were comparable to those in previous experiments (6) (0.33 to 0.38 exposure days), in which infectivity was reduced to 0 to 6% of the stock infectivity (compared to 16 to 20% in these experiments). Differences in infectivity reductions may result from the greater attenuation of radiation by the glass-covered flow chambers used here compared to the quartz dishes used previously (6), variation in oocyst lots (26), and overnight oocyst storage before infectivity processing (6).
The infectivity of oocysts attached at the top of the biofilm (n = 4 individual flow chambers) was significantly less than the infectivity of oocysts on the bottom of the biofilm (n = 4 individual flow chambers) (P < 0.01) (Fig. 1), suggesting that the biofilm provides a protective barrier for oocysts against solar radiation. Others found that shortwave radiation did not reach the bottom of a biofilm, allowing UV-sensitive organisms to survive (20). This conclusion is supported by optical transmittance data that showed that solar radiation was attenuated by the biofilm: less than one percent of the shortwave radiation (less than 300 nm) passed through a biofilm (23 to 40 μm), while up to 82% of longer-wavelength radiation, shown to significantly reduce infectivity (6), was able to pass through the biofilm (Fig. 2). These data suggest that oocysts at depth in a biofilm may be impacted more by longwave radiation as opposed to the shortwave UV radiation commonly used for disinfection.
The ability of the biofilm to absorb UV wavelengths may be a result of microbial production of sunscreen-like compounds as a response to strong solar radiation (20, 25). The biofilm culture used in these experiments was collected in the summer, when production of these compounds should be highest, if present. However, no difference was observed in the transmittance data from biofilms collected in different seasons or other sites with various sunlight exposure (data not shown), suggesting that either these compounds are present in all the sampled biofilms in equal quantities, which is unlikely because of the various environmental conditions under which they were collected, or that the inherent structure of the biofilm prevents the penetration of shortwave radiation.
Although biofilms may provide a protective barrier for oocysts against solar radiation, environmental oocysts are likely to be found suspended in the water column attached to fecal debris or biofilm material from a previous association. Oocysts may remain associated with biofilm material in suspension, providing similar protection to the oocyst as being embedded at depth within the biofilm (Fig. 1). The infectivity of biofilm-associated oocysts resuspended in creek water (n = 6 individual flow chambers) was not significantly different than that of oocysts at the bottom of a biofilm (n = 4 individual flow chambers) (P = 0.19) (Fig. 1). Oocysts have been shown to be protected from environmental conditions following storage in fecal material, a result of mucopolysaccharides inserted into the oocyst wall (21). Biofilm material may similarly embed in the oocyst wall and protect the oocyst from solar radiation through solar radiation absorption.
In the environment, oocysts are likely found attached to biofilm or fecal material from previous association. As shown by these experiments, associations with biofilm material reduce the impacts of detrimental solar radiation.
ACKNOWLEDGMENT
This research was funded by National Science Foundation CAREER award (no. 0545687) to K. L. Jellison.
Footnotes
Published ahead of print 30 March 2012
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