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Appl Environ Microbiol, May 1998, p. 1743-1749, Vol. 64, No. 5
WATER ECOscience Pty. Ltd., Mount Waverley,
Victoria 3149, Australia
Received 30 December 1997/Accepted 9 March 1998
We recently described a reverse transcription-PCR (RT-PCR) for
detecting low numbers of viable Cryptosporidium parvum
oocysts spiked into clarified environmental water concentrates. We have now modified the assay for direct analysis of primary sample
concentrates with simultaneous detection of viable C. parvum oocysts, Giardia cysts, and a novel type of
internal positive control (IPC). The IPC was designed to assess both
efficiency of mRNA isolation and potential RT-PCR inhibition.
Sensitivity testing showed that low numbers of organisms, in the range
of a single viable cyst and oocyst, could be detected when spiked into
100-µl packed pellet volumes of concentrates from creek and river
water samples. The RT-PCR was compared with an immunofluorescence (IF)
assay by analyzing 29 nonspiked environmental water samples. Sample
volumes of 20 to 1,500 liters were concentrated with a wound fiberglass
cartridge filter. Frequency of detection for viable Giardia
cysts increased from 24% by IF microscopy to 69% by RT-PCR. Viable
C. parvum oocysts were detected only once by RT-PCR (3%)
in contrast to detection of viable Cryptosporidium spp. in
four samples by IF microscopy (14%), suggesting that
Cryptosporidium species other than C. parvum were present in the water. This combination of the large-volume sampling method with RT-PCR represents a significant advance in terms
of protozoan pathogen monitoring and in the wider application of PCR
technology to this field of microbiology.
The ability of Giardia
intestinalis and Cryptosporidium parvum to cause
waterborne disease is well documented (12, 19, 22, 38).
However, analytical methods widely used to detect the presence of these
organisms in water do not provide the quality of data required to
assess health risk and effectively manage this problem (15, 21,
27, 42). Considerable effort is being made worldwide to
improve detection methodologies through the application of techniques
such as flow cytometry (45), laser scanning
(5), immunomagnetic separation (7), and PCR. In particular, PCR is an attractive diagnostic procedure as it is rapid,
sensitive, and pathogen specific. While many PCR methods have been
described for both Giardia and Cryptosporidium
detection (1, 11, 18, 20, 23, 24, 26, 29, 39, 47), this
technology is only slowly emerging as a practical method for pathogen
assessment of water quality. This is largely due to the low numbers of
cysts and oocysts in water and the requirement for significant sample
concentration factors to reduce large sample volumes to the microliter
quantities that are compatible with PCR. Concentration of
microorganisms in water samples, or their nucleic acids, leads to the
coconcentration of substances such as humic acids which can severely
reduce PCR efficiency and reliability (41, 44, 48). One
approach that is becoming widely used to overcome these problems is to
use paramagnetic beads to purify target nucleic acids (14, 25,
39). Magnetic bead technology is a powerful tool for water
microbiology as it is simple to use, does not require expensive
equipment, and can effectively separate and concentrate a range of rare
molecules from inhibitory sample matrices. We have previously reported
the use of this approach to successfully capture heat shock protein
(HSP) mRNA for reverse transcription-PCR (RT-PCR) detection of low
numbers of viable Cryptosporidium parvum oocysts in water
(39).
While sensitive detection methods are important, equal consideration
must be given to sample concentration methodology. Required are
concentration techniques that are compatible with viability detection
systems and suitable for rapid processing of large sample volumes.
Sample volumes for analyses of surface water and drinking water of 100 and The aim of this study was to develop an RT-PCR assay for the
simultaneous detection of viable Giardia and
Cryptosporidium in large-volume water samples. Our approach
was to concentrate cysts and oocysts from water samples with the
Diamond filter (28), then selectively capture mRNA with
oligo(dT)25 magnetic beads, and detect viable organisms by
RT-PCR. An RNA internal control that hybridized to the magnetic beads
was used to monitor the entire detection process from mRNA capture
through RT-PCR for every sample.
Cyst and oocyst stock preparation.
Viable Giardia
intestinalis cysts and C. parvum oocysts used
throughout this study were obtained from several sources. Viable G. intestinalis cysts and C. parvum oocysts,
cultured and harvested from Mongolian gerbils, were purchased
(DyNAgenics, Neosho, Mont.) as crude, partially purified, fecal
suspensions. C. parvum oocysts harvested from an endemically
infected dairy herd were supplied by Peter Cox (AWT Ensight, Sydney,
Australia), and C. parvum oocysts were also obtained from
calf fecal specimens supplied by Michael O'Callaghan (Department of
Primary Industries, Adelaide, South Australia, Australia). Additional
G. intestinalis cysts from human fecal specimens were
supplied by Gribbles Pathology (Melbourne, Australia). All fecal
samples were emulsified in phosphate-buffered saline (PBS),
semipurified by Percoll-sucrose density gradient centrifugation, and
stored at 4°C. The concentrations of cyst and oocyst stocks were
determined in triplicate with a hemocytometer.
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Sensitive and Rapid Detection of Viable
Giardia Cysts and Cryptosporidium parvum Oocysts
in Large-Volume Water Samples with Wound Fiberglass Cartridge
Filters and Reverse Transcription-PCR
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ABSTRACT
Top
Abstract
Introduction
Materials & Methods
Results
Discussion
References
![]()
INTRODUCTION
Top
Abstract
Introduction
Materials & Methods
Results
Discussion
References
1,000 liters, respectively, have been recommended elsewhere
(16), and the most commonly used method for concentration of
Giardia cysts and Cryptosporidium oocysts from
water is the American Society for Testing and Materials yarn-wound
cartridge filter method (16). However, parasite recovery
with this technique is generally poor (10). Vortex flow
filtration, membrane filtration, and capsule filters have been proposed
for concentration of 10-liter volumes in the U.S. Environmental
Protection Agency draft Cryptosporidium method
(6). However, each method is limited to some degree by
either small sample volumes, interference by high sample turbidity, high equipment costs, long processing times, or laboratory-based equipment, necessitating the transportation of water to the laboratory. Chemical flocculation, while an effective procedure (35, 37, 46), may inactivate viable organisms (9) and is
generally restricted to volumes of less than 20 liters. One technique
that offers many advantages is a filtration-elution procedure which uses cheap, negatively charged fiberglass filters in a simple entrapment-backwash elution format (28). High efficiencies
of recovery for Giardia cysts in spiked 20-liter samples
have been reported elsewhere (28).
![]()
MATERIALS AND METHODS
Top
Abstract
Introduction
Materials & Methods
Results
Discussion
References
Water samples.
Volumes of water between 20 and 1,500 liters
were concentrated by a modification of a method described by Payment et
al. (28). This involved filtration through a wound
fiberglass depth cartridge filter with a nominal pore size of 1 µm
(Memtec Limited, Timonium, Md.) and elution with a beef extract eluent
(1.5% beef extract, 0.5% Tween 80, pH 9.75). The flow rate of water
through the filters varied between 4 and 15 liters min
1.
Either samples were filtered on-site and the filter was transported to
the laboratory on ice, or volumes of water were collected in sterile
20-liter plastic containers which were transported to the laboratory
and filtered within 4 h of collection. Additional 500-ml samples
were collected from each site to determine the physicochemical quality
of each sample as described in Standard Methods for the
Examination of Water and Wastewater, 18th ed. (3).
Cysts and oocysts were eluted off the filter within 24 h of sample
collection by backflushing with 1.8 liters of eluent. The eluate was
immediately adjusted to pH 7.2 ± 0.2 with the addition of 1 N
HCl. Backflushings were concentrated by centrifugation at 3,500 × g for 20 min, and the final pellet was resuspended in PBS to
a volume between 3 and 10 ml. Equal volumes of concentrates were
analyzed by both immunofluorescence (IF) microscopy and RT-PCR, but
sample portions for IF-DAPI-PI microscopy first required clarification by Percoll-sucrose density gradient centrifugation (4).
Cysts and oocysts were enumerated, and viability was determined as
described above. Density gradient centrifugation was not required for
RT-PCR analysis of sample concentrates.
Preparation of spiked samples for Diamond filters.
Ten
spiking experiments were performed on 50-liter volumes of tap water
with a turbidity range of 3 to 5 nephelometric turbidity units (NTU).
The water was seeded with 500 to 2,000 cysts and oocysts, which were 8 to 12 weeks old. The seeded samples were filtered (flow rates, 7 to 15 liters min
1) and recovered by backflushing and
centrifugation as described above. Recovered cysts and oocysts were
enumerated, and the percentage of recovery was determined.
Preparation of spiked samples for RT-PCR. Sample concentrates were heated to 60°C for 30 min to inactivate any indigenous viable Giardia cysts or Cryptosporidium oocysts. Fresh dilutions of viable cysts and oocysts were prepared in PBS. The G. intestinalis and C. parvum stocks were approximately 75 and 90% viable, respectively. Fifty-microliter volumes containing approximately 500, 100, 50, 10, 5, and 0 viable cysts and oocysts were inoculated into 100-µl packed pellet volumes (volume of material remaining after centrifugation at 5,000 × g and removal of supernatant) of heat-inactivated sample concentrates or directly into InstaGene (Bio-Rad). Sterile water was inoculated into sample concentrates or InstaGene for negative controls. A 50-µl volume of each dilution was also stained and enumerated as described above to obtain a count of each inoculum.
RNA internal positive control (IPC).
An RNA fragment was
added to each sample at the stage of oocyst and cyst lysis to monitor
the efficiency of both mRNA capture by the magnetic beads and the
subsequent RT and PCR. The RNA IPC was constructed with the use of
modifying primers to amplify a 290-bp sequence of nontarget DNA by PCR
(39). The 5' end of the upstream primer was modified to
contain the T7 phage promoter sequence followed by an additional 6 nucleotides (13, 40). The downstream primer (5' modified
with 15 thymidine bases) was designed to add a 3' tail of 15 adenosine
bases to the IPC. The PCR product was transcribed with the riboprobe T7
in vitro transcription system (Promega). After in vitro transcription,
the DNA was digested with RQ1 DNase (Promega) and the RNA was purified
by phenol-chloroform extraction followed by precipitation with ethanol
(32). The resultant RNA IPC containing a 15-nucleotide-long
polyadenylated tail was resuspended in diethylpyrocarbonate-treated
water (DEPC-H2O), diluted to a concentration of
approximately 5 fg µl
1, and stored in 100-µl aliquots
at
70°C. PCR was performed on the preparation to confirm the
absence of DNA.
Heat shock and mRNA extraction.
Both spiked and nonspiked
Diamond filter concentrates were pelleted by centrifugation at
5,000 × g for 3 min. Pellets containing cysts and
oocysts were resuspended in 200 µl of InstaGene and incubated at
45°C for 20 min to maximize HSP mRNA production. Following heat
shock, 200 µl of lysis-binding buffer (100 mM Tris-HCl [pH 8.0],
500 mM LiCl, 10 mM EDTA [pH 8.0], 1% lithium dodecyl sulfate, 5 mM
dithiothreitol) was added to each sample, and this mixture was then
subjected to freeze-thaw treatment to rupture cysts and oocysts and
release nucleic acids. This involved five cycles of freezing the
samples in liquid nitrogen for 30 s and thawing them at 65°C for
1 min. Extraction and isolation of mRNA were achieved with 40 µg of
oligo(dT)25 magnetic beads (Dynal, Oslo, Norway) per
sample, as previously described (39). Immediately after
freeze-thaw lysis, debris was pelleted by centrifugation at 17,000 × g for 3 min and the supernatant containing the mRNA was
added to prepared beads. At this stage, 2 µl of RNA IPC was added to
assess the ability of the beads to capture the mRNA, ensure that RNases
did not destroy the RNA prior to addition to the RT, and also ensure
that negative results were not due to inhibition of the RT or PCR.
Hybridization was performed with gentle mixing by rolling at 30°C for
30 min, and then the beads were washed once with 400 µl of wash
buffer (10 mM Tris-HCl [pH 8.0], 0.15 M LiCl, 1.0 mM EDTA, 0.1%
lithium dodecyl sulfate) and once with 400 µl of 1× PCR buffer (10 mM Tris-HCl [pH 8.3], 50 mM KCl) with a magnetic concentrator to
retain the beads. The bound mRNA and beads were finally resuspended in
5 µl of DEPC-H2O and added to the RT reaction mixture.
mRNA for use as controls was extracted from approximately
103 G. intestinalis cysts and C. parvum oocysts, resuspended in 100 µl of DEPC-H2O,
stored at
70°C, and used neat or diluted as required.
RNase and DNase treatment of Giardia mRNA. Experiments were performed to confirm that RNA was being specifically isolated from Giardia with the oligo(dT)25 magnetic beads, following the protocol previously described (39).
Inactivation of indigenous Giardia cysts in water concentrates. In order to confirm the viability of Giardia detected in nonspiked water concentrates, concentrates positive for Giardia were treated with either heat or formaldehyde to inactivate the cysts. Heat treatment involved incubation of the water concentrate at 60°C in a water bath for 30 min. Formaldehyde treatment was performed by adding sufficient formaldehyde to the sample concentrate to obtain a final concentration of 10% (vol/vol). After incubation at room temperature for 2 h, the formaldehyde was removed by centrifugation at 5,000 × g for 3 min. The supernatant containing the formaldehyde was discarded, and the pellet was washed once in PBS. Both heat-inactivated and formaldehyde-inactivated concentrates were then concentrated by centrifugation, and the pellets were resuspended in InstaGene and treated as described above within 2 h of treatment.
PCR primers and probes. The sequences and references for all PCR primers and oligonucleotide probes used in this study are presented in Table 1. For Giardia detection, we initially tried the G. intestinalis-specific GHSP1-GHSP2 primer set (1); however, neither a PCR nor an RT-PCR product could be reliably detected with these primers. The Giardia spp. primer set GGL-GGR (23, 24) was subsequently used, as it demonstrated reliable and sensitive Giardia detection. Primers for multiplex PCR (Giardia spp., C. parvum, and IPC) were each modified by the 5' addition of a 20-mer universal primer sequence (UPS; 5'-GCGGTCCCAAAAGGGTCAGT-3') (36).
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RT-PCR. RT-PCR was performed with the GeneAmp RNA PCR kit (Perkin-Elmer); however, Amplitaq Gold DNA polymerase (Perkin-Elmer) was used in place of the Amplitaq DNA polymerase. The captured mRNA was reverse transcribed with oligo(dT)16 primers (Perkin-Elmer). Each RT reaction mixture (30 µl) contained 1× PCR buffer II (10× PCR buffer II contains 500 mM KCl and 100 mM Tris-HCl [pH 8.3]), 5 mM MgCl2, 1 mM deoxynucleoside triphosphates (1 mM [each] dATP, dTTP, dCTP, and dGTP), 1.7 µM oligo(dT)16 primer, 20 U of RNase inhibitor, 50 U of murine leukemia virus reverse transcriptase, and 5 µl of DEPC-H2O containing mRNA-bead complex. RT was performed in an FTS-960 thermal sequencer (Corbett Research, Sydney, Australia) at 42°C for 30 min. Following RT, the samples were heated to 95°C for 5 min to inactivate the reverse transcriptase and were then held at 4°C until aliquots were added to the PCR mixture. A 10-µl aliquot of the RT reaction mixture was added directly to separate PCR mixtures. Each PCR mixture contained 1× PCR buffer II, 2.5 mM MgCl2, 0.5 µM (each) primer, and 1.5 U of Amplitaq Gold DNA polymerase. Amplification was performed in the FTS-960 thermal sequencer with the following protocol: activation of the Amplitaq Gold DNA polymerase at 95°C for 10 min; then 40 cycles of 95°C for 20 s, 60°C for 45 s, and 72°C for 45 s; and a final extension step at 72°C for 5 min. The PCR products were held at 4°C until analyzed. The annealing temperature used for the GHSP primer set was 55°C. PCR products were detected by polyacrylamide gel electrophoresis with silver staining (39).
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RESULTS |
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Detection of Giardia and C. parvum by RT-PCR. Our intention was to develop a multiplex RT-PCR for the simultaneous detection of Giardia spp., C. parvum, and IPC. The primers used for detection of each target were modified by the 5' addition of a 20-mer UPS, making the PCR products 40 bp larger. This modification has been reported to eliminate most of the optimization steps required for multiplex PCR (36). The UPS modification of primers facilitated successful multiplex PCR (Fig. 1); however, the sensitivity of the CHSP1-CHSP4 PCR was decreased 10-fold (data not shown). Optimum detection sensitivity was achieved with one RT step, and aliquots of the resultant cDNA pool were added to two separate PCRs, one for the detection of Giardia and the IPC with the UPS-modified primers and one for the detection of C. parvum with the unmodified CHSP1-CHSP4 primer pair. This represented a compromise between detection sensitivity and ease of use.
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Water sample analyses for Giardia and C. parvum. Wound fiberglass depth filter cartridges (Diamond filters) were used to concentrate Giardia cysts and Cryptosporidium oocysts from water. Ten spiking experiments were conducted in 50-liter volumes of tap water to evaluate the performance of the Diamond filter. These gave recoveries for Giardia cysts and Cryptosporidium oocysts of 45 to 88% (average, 74%) and 43 to 84% (average, 54%), respectively. DAPI-PI staining indicated that the C. parvum oocyst stock was 75 to 79% viable while the viability of oocysts in sample concentrates was 73 to 75%, indicating that there was no loss of viability throughout the concentration process.
To compare the performance of the RT-PCR method with that of IF-DAPI-PI microscopy, 29 water samples were collected with the Diamond filters. Sample volumes concentrated were between 20 and 1,500 liters. Several physicochemical and microbiological water quality parameters were tested for these samples and are shown in Table 3, demonstrating the range of water types that are compatible with this method. Separate volumes of the water concentrates were tested by RT-PCR and IF-DAPI-PI microscopy. mRNA was extracted directly from the water concentrates. However, due to interfering debris in the concentrates, a clarification step was required prior to fluorescent staining and microscopy. Table 4 shows the results of RT-PCR detection of viable Giardia and C. parvum compared to those of Giardia and Cryptosporidium detection by IF-DAPI-PI microscopy. Overall, viable Giardia cysts were detected in 20 (69%) samples by RT-PCR and only 7 (24%) samples by IF-DAPI-PI microscopy. In the river and creek samples alone, the detection of viable Giardia was fourfold higher by RT-PCR than by microscopy. An example of results obtained from analysis of creek samples is given in Fig. 3. Viable Cryptosporidium oocysts were detected in four (14%) samples by IF-DAPI-PI microscopy. However, viable C. parvum oocysts were detected only once by RT-PCR (Table 4). Viable Giardia cysts and C. parvum oocysts were not detected in drinking water samples by either method. Comparable results were obtained by both detection methods for treated sewage samples. Interestingly, while Giardia cysts were present, no C. parvum oocysts were detected in these samples by either assay.
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DISCUSSION |
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We have developed an assay which utilizes RT coupled with two different PCRs for the simultaneous detection of viable Giardia spp. and C. parvum. This is a reliable and economic test which is more sensitive than a widely used IF microscopy procedure. In addition, this method specifically detects the human pathogen C. parvum. We attempted to use the GHSP PCR primers (1) in our assay to detect the human pathogen G. intestinalis, but to date we have found this RT-PCR to be unreliable.
Initially, we designed this test as a multiplex PCR for single-tube detection of C. parvum, Giardia, and IPC, but a 10-fold loss in detection sensitivity was observed for the C. parvum component. During the course of this study, another laboratory reported successful multiplex PCR for G. intestinalis and C. parvum with HSP primers (29). This multiplex was not used in an RT-PCR format, and while detection of cysts and oocysts in environmental water concentrates was possible, the detection limit was not specified. In our study, isolation and purification of mRNA with magnetic beads coupled to a single RT with a two-tube PCR permitted sensitive detection of low numbers of cysts and oocysts from sample concentrates. A brief comparison of two reported C. parvum HSP primer sets (29, 39) showed no difference in detection sensitivity (Fig. 2B and C), despite a reported significant theoretical difference in melting temperatures between CHSP1 and CHSP4 primers (29).
Wound fiberglass cartridge filters (Diamond filters) were used for concentrating sample volumes of up to 420 liters of river and creek water and 1,500 liters of drinking water. These filters have been reported elsewhere for concentration of 1,000 to 2,000 liters of drinking water for Giardia detection (28). Assessment of filter performance with 50-liter spiked samples during this study demonstrated an average recovery of 74 and 54% for Giardia and Cryptosporidium, respectively. In addition, the viability of seeded C. parvum oocysts was not altered during collection and processing of samples. Based on these results, concentration of Giardia and Cryptosporidium with the Diamond filter is an efficient method, convenient for processing large-volume water samples. Furthermore, even when sample turbidity was high (6.5 to 120 NTU), sample volumes up to 420 liters could be easily filtered and positive results could be obtained by RT-PCR for viable Giardia (Table 3; Fig. 3). We are currently evaluating the performance of these filters under high-turbidity conditions as measured by spiking experiments.
Clarification of samples by Percoll-sucrose density gradient centrifugation contributes significantly to losses of Giardia and Cryptosporidium (21), compromising the sensitivity of any subsequent detection method. mRNA capture with oligo(dT)25 beads and detection with RT-PCR overcame these limitations, as sample clarification was not required. In addition, the detection of viable parasites was defined by the presence or absence of the correct RT-PCR product, thus overcoming the difficulties often encountered with microscopy caused by sample debris masking fluorescence, interference from autofluorescing algae, or misinterpretation of vital dye stain patterns caused by sample exposure to chlorine (30, 31, 33, 34). However, one obvious limitation of RT-PCR is that it is not strictly quantitative, although a most probable number format may be used if enumeration is required (43).
This RT-PCR method was able to detect low numbers of Giardia cysts and C. parvum oocysts artificially spiked into river and creek water concentrates with packed pellets of 100 µl. Oligo(dT)25 magnetic beads overcame potential RT-PCR inhibition and proved to be a convenient and efficient mRNA purification system.
An RNA IPC was developed to guard against false-negative results. It was added to all samples analyzed at a very low concentration (10 fg), and the effect each sample had on the efficiency of mRNA capture and RT-PCR could be evaluated by visually comparing the intensities of the IPC RT-PCR products of samples and controls. Equivalent intensities gave confidence that negative results were valid and not due to magnetic bead capture failure, RNA degradation, or inhibition of the RT or PCR.
The test detected only viable organisms since mRNA was selectively recovered from samples and previously RT-PCR-positive samples were rendered negative by heat or formalin treatment, thus demonstrating that amplifiable mRNA was not maintained in cysts treated in either of these ways. Our observation that heat-inactivated cysts did not produce or maintain mRNA is in contrast with that by another investigator, who reported detection of giardin mRNA after heat treatment (23). This discrepancy may be related to experimental differences such as the time between inactivation of cysts and mRNA extraction.
The high sensitivity of the assay was further demonstrated by a comparison of RT-PCR with IF-DAPI-PI microscopy in 29 nonspiked water samples. The RT-PCR was found to be the more sensitive detection method, detecting the presence of viable Giardia in four times as many river and creek samples as did IF-DAPI-PI microscopy. Interestingly, the intensity of the PCR products from these analyses (Fig. 3) suggested viable cyst concentrations greater than 20 cysts per sample concentrate, and yet only one viable cyst was detected in the same concentrate by IF-DAPI-PI microscopy. This suggests possible losses of cysts throughout the density gradient clarification process and nondetection by IF microscopy. Due to the inability of the Cryptosporidium fluorescent antibody to specifically stain C. parvum oocysts, it was not possible to compare the detection of viable C. parvum in 3% of samples by RT-PCR with the detection of viable Cryptosporidium in 14% of samples by microscopy. However, a lack of C. parvum RT-PCR detection sensitivity can be discounted, given the results of spiking experiments. The difference in detection rates suggests that viable Cryptosporidium species other than C. parvum may have been present in those water samples.
To address this possibility, the Cryptosporidium HSP genus primer set recently described (29) was used to analyze 16 water samples. All samples were positive with the correct-size PCR product. However, these primer sequences appear to have cross-reactivity with hsp genes from a range of other organisms which may be expected to occur naturally in water. This genus PCR is therefore likely to be of diagnostic value only in conjunction with Cryptosporidium species-specific probes, such as the CPHSP2475 C. parvum probe (29).
The results presented in this paper demonstrate the effectiveness of using Diamond filter concentration in conjunction with RT-PCR for detection of viable waterborne Giardia and Cryptosporidium. The use of magnetic bead mRNA capture with RT-PCR to directly screen sample concentrates for parasites significantly enhances the quality of pathogen incidence data compared to that with microscopy-based detection. First, low theoretical detection limits, <0.01 cysts or oocysts/liter or better, are conveniently achieved, as large volumes (>100 liters) are easily sampled and analyzed. Secondly, actual detection limits are lower in that RT-PCR is more sensitive than IF microscopy. Thirdly, detection of viable parasites is possible. Other benefits include batch sample processing, objective assessments, and short analysis times. For example, analysis of 15 water sample concentrates takes one operator 6 h by RT-PCR compared with 3 to 4 days by IF microscopy.
More work is now required to standardize PCR-based methods between laboratories and to demonstrate the portability and reliability of this technology for environmental pathogen monitoring.
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ACKNOWLEDGMENTS |
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This work was substantially supported by funding from the Government of Victoria through the Water Bureau, Department of Natural Resources and Environment, and in part by the Urban Water Research Association, Australia.
We also thank Peter Cox and Malcolm Warnecke for critical review of the manuscript and Joanne O'Toole and Kate Hines for advice and expert technical assistance.
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FOOTNOTES |
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* Corresponding author. Mailing address: WATER ECOscience Pty. Ltd., 68 Ricketts Rd., Mount Waverley, Victoria 3149, Australia. Phone: 61 3 9550 1031. Fax: 61 3 9543 7185. E-mail: ckaucner{at}wes.com.au.
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