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Applied and Environmental Microbiology, May 2000, p. 2267-2268, Vol. 66, No. 5
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
Use of Integrated Cell Culture-PCR To Evaluate the
Effectiveness of Poliovirus Inactivation by Chlorine
Felisa
Blackmer,
Kelly A.
Reynolds,*
Charles P.
Gerba, and
Ian L.
Pepper
Department of Soil, Water and Environmental
Science, The University of Arizona, Tucson, Arizona 85721
Received 5 January 1999/Accepted 1 February 2000
 |
ABSTRACT |
Current standards, based on cell culture assay, indicate that
poliovirus is inactivated by 0.5 mg of free chlorine per liter after 2 min; however, integrated cell culture-PCR detected viruses for up to 8 min of exposure to the same chlorine concentration, requiring 10 min
for complete inactivation. Thus, the contact time for chlorine
disinfection of poliovirus is up to five times greater than previously thought.
 |
TEXT |
The standard method of enterovirus
assay and detection involves the use of animal cell culture. The
presence of virus is indicated by the destruction of cells, referred to
as the cytopathogenic effect (CPE), and requires from 3 to >14 days
(8). Often secondary passage of the environmental samples
onto a fresh monolayer of cells is necessary before CPE is produced,
but secondary passage is not routinely conducted (3, 10).
Integrated cell culture-PCR (ICC-PCR) combines the speed and
sensitivity of PCR with a cultural viability assay to form a molecular
detection method capable of isolating low levels of infectious virus
(8). This study determined the efficacy of ICC-PCR to
evaluate the chlorine contact time necessary to ensure that all target
viruses were inactivated.
Poliovirus type 1 (strain Lsc-2ab) was grown in buffalo green monkey
kidney (BGM) cells (passages 135 to 195) at 37°C until CPE occurred.
Poliovirus was isolated by freeze-thawing and centrifugation as
previously described (8). The titers of virus stocks were determined at 2.3 × 107 PFU/ml using conventional
plaque assay methodology (4). All glassware was exposed to
>5% sodium hypochlorite overnight, rinsed with high-performance
liquid chromatography (HPLC) grade water, and exposed to UV light for
at least 1 h to eliminate chlorine demand. Virus stock and sodium
hypochlorite were added to 50 ml of chlorine demand-free HPLC grade
water for a final concentration of 2.3 × 102 PFU/ml
and 0.5 mg/liter, respectively. Chlorine levels were measured at room
temperature and pH 5.5 using a spectrophotometer (model 2000; Hach,
Loveland, Colo.). Three replicate studies indicated that chlorine
concentrations remained constant for longer than the duration of the
experiments,
10 min.
BGM continuous cell culture flasks (25 cm2) were incubated
with 1 ml of sample at 37°C for time intervals of 0, 1, 2, 3, 4, and
14 days before freezing at
80°C for PCR analysis. For conventional cell culture assays, flasks were incubated up to 14 days and observed daily for CPE. Secondary BGM assays were performed with lysate from the
first passage, but the flasks were not frozen until CPE, or another
2-week incubation, occurred. Prior to PCR analysis, samples were
centrifuged (model 5415C; Sorvall, Newtown, Conn.) for 15 min at
735 × g and
5°C to remove cellular debris.
Target sequences were reverse transcribed as previously described
(8). Cell culture lysate template (5 µl) was added to reverse transcription reagents and extracted by heat (5 min at 98°C),
followed by a single cycle of 24°C for 10 min, 44°C for 60 min,
99°C for 5 min, and 5°C for 5 min. For cDNA amplification, 1.5 µl
of 25 mM MgCl2, 3.5 µl of 10× buffer II (Perkin-Elmer
Cetus Corporation, Norwalk, Conn.), 0.25 µl of upstream primer at 50 pmol/reaction mixture, 0.25 µl of downstream primer (2) at 50 pmol/reaction mixture, 28.75 µl of HPLC grade water, and 0.25 µl
of AmpliTaq Gold Polymerase (Perkin-Elmer Cetus Corporation) were added
per 50-µl reaction mixture. Samples were amplified by single PCR as
follows: (i) 95°C for 5 min; (ii) 25 cycles, with 1 cycle consisting
of 99°C for 1 min, 60°C for 45 s, and 72°C for 1 min; and
(iii) a single 10-min extension step at 72°C. For seminested PCR, 5 µl of the single PCR mixture volume was added to 50-µl reaction
mixtures of fresh reagents with the upstream external primer and a
downstream primer internal to the sequence amplified in single PCR
(7). Amplification conditions were identical to those used
in single PCR for an additional 20 cycles.
PCR products (15 µl) were mixed with 3 µl of Ficoll loading buffer
(20% Ficoll, 1% sodium dodecyl sulfate, 0.25% bromophenol blue, and
0.1 M EDTA [pH 8.0]) and subjected to 1.5% low-electroendosmosis agarose gel electrophoresis at 100 V for 1.75 h (Fisher
Scientific, Fair Lawn, N.J.). The gel was stained with SyberGold for 45 min and evaluated with an AlphaImager 2000 (Alpha Innotech Corporation, San Leandro, Calif.) for the presence of PCR and seminested PCR product
bands at 195- and 106-bp locations, respectively. Positive seminested
PCR products were prepared for dye termination sequencing (University
of Arizona's Laboratory of Molecular Systematics and Evolution
sequencing facility) using a QIAquick-Gel Extraction Kit per the
manufacturer's suggestions (QIAGEN, Inc., Valencia, Calif.).
Previous studies indicate that poliovirus inactivation with free
chlorine occurs after 2 min of exposure to 0.5 mg/liter, yielding a
required Ct value (concentration of
disinfectant × time of exposure) of 1.0 (1, 5). Using
first-passage cell culture as the method for detection of infectious
virus, the results of this study agree with previous studies (Table
1). However, ICC-PCR provided a more
rapid and effective detection method, since analysis of cell culture
lysate from first-passage samples demonstrated that infectious
poliovirus was still present even after 6 min of exposure to 0.5 mg of
free chlorine per liter. A second passage in continuous cell culture
confirmed that not only was poliovirus present but it was also
cytopathogenic. Furthermore, ICC-PCR-positive results required only 2 days of incubation in cell culture versus up to 14 or more days with
conventional cell culture. Ultimately, both methodologies yielded the
same result, but cell culture alone required a second assay to
accurately establish necessary contact time. At 8 min of exposure to
0.5 mg of free chlorine per liter, most samples were completely
disinfected, as determined by two passages in cell culture and ICC-PCR
analysis. Clearly, 8 min was close to the threshold value for complete
disinfection, since a second passage in cell culture showed that only
two of the six replicates harbored infectious poliovirus. ICC-PCR
results from the second-passage lysates confirmed these results. Only after 10 min of exposure to 0.5 mg of free chlorine per liter was the
poliovirus totally inactivated in all samples, yielding a required
Ct value of 5.0. DNA sequencing analysis of the
PCR product indicated that the observed virus was poliovirus type 1 (data not shown).
View this table:
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TABLE 1.
Evaluation of ICC-PCR and cell culture (CPE) to detect
poliovirus inactivation by free chlorine (0.5 mg/liter)a
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|
In conclusion, ICC-PCR provides a more sensitive and rapid method for
detection of infectious poliovirus following chlorine disinfection
compared to conventional cell culture. This new application of ICC-PCR
proved to be more effective at determining the potency of chlorine
disinfection, minimizing the chance for false-negative results with
single-passage cell culture alone. The results of this study suggest
that previous research to determine the resistance of viruses to
chlorine may have underestimated the resistance of at least poliovirus
populations, as previous studies involved only direct cell culture
assay of the virus with no secondary passage and no detection via
ICC-PCR (3, 10). This has serious implications since the
determination of inactivation rates of waterborne virus is crucial to
the drinking water industry. The amount of chlorine that must be
applied is determined by the contact time required to inactivate a
given percentage of a pathogen. The results of this study suggest that
current contact values could be in error of up to 400%
(Ct values of 1 versus 5) (1, 11) and
that a reevaluation of the contact time necessary for the true
disinfection of all infectious viruses present may be needed. This
could help to explain why infectious viruses have been detected in
drinking water after receiving what was believed to be adequate
disinfection (6, 9). Additional studies are needed to
determine the exact mechanism of resistance and if other types of
enteric viruses or disinfectants present similar phenomena.
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ACKNOWLEDGMENTS |
This work was supported by grant 292-95 from AWWARF.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Soil, Water and Environmental Science, University of Arizona, 429 Shantz Building 38, Tucson, AZ 85721. Phone: (520) 419-2051. Fax: (520) 621-1647. E-mail: reynolds{at}u.arizona.edu.
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Applied and Environmental Microbiology, May 2000, p. 2267-2268, Vol. 66, No. 5
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
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