Previous Article | Next Article 
Appl Environ Microbiol, June 1998, p. 2284-2286, Vol. 64, No. 6
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
Detection of Cyclospora cayetanensis
in Wastewater
Gregory D.
Sturbaum,1
Ynes R.
Ortega,2
Robert H.
Gilman,3,4,5,*
Charles R.
Sterling,2
Lilia
Cabrera,5 and
Donald
A.
Klein1
Department of Microbiology, Colorado State
University, Ft. Collins, Colorado1;
Department of Veterinary Science and Microbiology, University
of Arizona, Tucson, Arizona2;
Department
of International Health, Johns Hopkins University, Baltimore,
Maryland3; and
Departamento de
Patologia, Universidad Peruana Cayetano
Heredia,4 and
Asociacion Benefica
PRISMA,5 Lima, Peru
Received 15 October 1997/Accepted 25 March 1998
 |
ABSTRACT |
Cyclospora cayetanensis causes diarrheal disease
worldwide without a confirmed mode of transmission. Wastewater was
examined for the presence of this organism. Oocysts were detected
microscopically, and their identity was confirmed by molecular
techniques. These findings verify that current techniques can isolate
Cyclospora oocysts and suggest that fecally contaminated
water may act as a vehicle of transmission.
 |
TEXT |
Cyclospora cayetanensis
has emerged as an important cause of acute and chronic gastroenteritis
worldwide (2). The environmentally resistant form of the
organism, an oocyst, is shed in feces and subsequently sporulates to
the infectious form after 7 to 12 days of incubation at ambient
temperature (2, 5, 6). While the mode of transmission has
not been entirely elucidated, C. cayetanensis oocysts have
been detected on vegetables sold in the San Juan of Miraflores
shantytown (Lima, Peru), where cyclosporiasis is endemic
(5a), and consumption of Guatemalan raspberries has been
epidemiologically linked with recent C. cayetanensis
outbreaks in the United States (2). Although highly
suspected, cyclosporiasis via contaminated water has not been confirmed
(2).
This study was conducted from March to June 1997 in the San Juan of
Miraflores shantytown. Eleven water samples were collected from the
primary oxidation lagoon and analyzed for C. cayetanensis by
fluorescent microscopy and PCR specific for C. cayetanensis.
Eight water samples, ranging in volume from 1 to 5 liters, were
collected with the Envirochek capsule (Gelman Sciences, Ann Arbor,
Mich.). Particulate matter was eluted by hand with 100 ml of eluting
solution and concentrated in accordance with the manufacturer's
recommendations (Gelman Sciences). The eluting solution consisted of
1% sodium dodecyl sulfate, 1% Tween 80, NaCl,
KH2PO4, Na2HPO4
· 12H2O, KCl, and Antifoam A (Sigma Chemical Co.).
Elution by hand consisted of horizontal agitation for 10 min, releasing
trapped particles. Suspended particulate matter was decanted into a
250-ml centrifuge bottle and centrifuged at 1,050 × g
for 10 min. Two additional washings were performed, with rotation of
the capsule 90° each time. The centrifuged particulate matter was
added together as a final centrifugate.
Three samples, 378 liters each, were collected with the Hannifin
polypropylene cartridge filter (Commercial Filters Parker Hannifin
Corp., Lebanon, Ind.). These samples were eluted by hand according to
standard procedures (1). The woven filter was sliced to the
core, and the fibers were divided into six equal portions. Fibers were
successively washed in three 1-liter volumes of eluting solution, with
wringing of the fibers between containers. The eluate suspensions were
combined, and a 100-ml aliquot was centrifuged at 1,050 × g for 10 min.
All centrifugates were resuspended in a 2.5% potassium dichromate
solution. A centrifugate between 0.1 and 0.5 ml was mixed with zinc
sulfate (specific gravity, 1.2) for selective centrifugation for 1 min
at 600 × g. Particles with a specific gravity of less than 1.2 were harvested for microscopic examination. Wet mount preparations were scanned at a magnification of ×200 with UV
epifluorescence (excitation filter, 355 to 425 nm; dichroic
beam-splitting mirror, 455 nm; and suppression filter, 470 nm). Objects
that autofluoresed and had the same size and shape as C. cayetanensis oocysts were examined at a magnification of ×1,000
with phase-contrast microscopy for confirmation. All samples were
subjected to a nested PCR protocol amplifying a 294-bp portion of the
18S rDNA segment (7). The PCR protocol included a 50-µl
subsample from a 1-ml concentrated water sample suspension in potassium
dichromate. The subsample was washed four times with 1× PCR buffer by
centrifugation at 14,000 × g for 3 min. The packed
pellet was resuspended in 25 µl of 1× PCR buffer (The 1× PCR buffer
is made originally as a 10× PCR buffer, and from this a 1× buffer was
made by a 1:10 dilution with double-distilled sterile water. The 10×
buffer contains the following components: 500 mM KCl, 100 mM Tris-HCl
[pH 9.0, 25°C], 1% Triton X-100 [Fisher, Petersberg, Pa.], and
15 mM MgCl2.) and 25 µl of 6% resin matrix (Instagene;
Biorad, Hercules, Calif.). The resin matrix removes inhibitors from the
DNA preparation suspension. The suspension was subjected to seven
freeze-thaw cycles of 2 min in a dry ice-ethanol bath followed by 2 min
in a 98°C water bath (4). The suspension was vortexed and
centrifuged at 14,000 × g for 3 min. Twenty-five
microliters of supernatant was transferred to a microcentrifuge tube
for PCR amplification. The PCR assay and primers were as described by
Yoder et al. (7) except that the annealing temperature of
52°C was changed to 50°C and a cytosine replaced an adenosine at
position 14 in CYC3FE. Amplification products were confirmed by
restriction fragment length polymorphisms (RFLP) with one unit of the
restriction endonuclease MnlI (Amersham Life Sciences Inc.,
Arlington Heights, Ill.) (3). The predicted restriction
fragment sizes are 140 bp, 106 bp, and 48 bp for C. cayetanensis and 127 bp, 106 bp, and 62 bp for Eimeria
spp. Microscopically confirmed C. cayetanensis positive
control oocysts were obtained from Universidad Peruana Cayetano
Heredia. C. cayetanensis DNA was liberated by the simple
freeze-thaw technique and purified by phenol-chloroform extraction. The
Eimeria sp. positive control of avian origin was obtained
from Ynes Ortega. Eimeria DNA was obtained by the same
protocol as for Cyclospora spp. and amplified by the nested
PCR assay. Ten microliters was analyzed for amplified product by
electrophoresis in a 1.2% agarose gel stained with ethidium bromide.
Restriction endonuclease digests were analyzed in a 4% MetaPhor
agarose gel (FMC BioProducts, Rockland, Maine) stained with ethidium
bromide.
Unsporulated oocysts were observed (1 oocyst per liter) in four of the
eight samples collected with the Envirochek capsule and in all three
samples collected with the Hannifin filter. On direct examination, 2 of
the 11 samples contained sporulated oocysts (Fig.
1). Following a 2-week incubation period
at ambient temperature, sporulated oocysts were detected in
one additional sample. Amplified product in one
microscopy-positive sample was confirmed as C. cayetanensis
by RFLP fragment digestion (Fig. 2). The
PCR detection limit was determined to be 10 oocysts per inoculated
fecal sample (unpublished results).

View larger version (131K):
[in this window]
[in a new window]
|
FIG. 1.
Photomicrograph of C. cayetanensis in
wastewater by Nomarski interference-contrast microscopy; bar = 5 µm. The arrow indicates an oocyst with two
sporocysts.
|
|

View larger version (93K):
[in this window]
[in a new window]
|
FIG. 2.
C. cayetanensis and Eimeria
amplified products from nested PCR (lanes 2 to 5) and RFLP fragments
from MnlI digestion of those PCR amplified products (lanes 7 to 10). Lanes 1, 6, and 11, molecular size standards; lanes 2 and 7, negative control; lanes 3 and 8, Universidad Peruana Cayetano Heredia
C. cayetanensis positive control; lanes 4 and 9, C. cayetanensis from wastewater; lanes 5 and 10, Eimeria spp. (U of A) positive control. Primers migrated to
point P.
|
|
This is the first report to confirm the detection of oocysts of
C. cayetanensis in wastewater. Contact with C. cayetanensis-contaminated water at some point may be the source of
the oocysts detected on vegetables in Peru and the epidemiological link
with raspberries from Guatemala. Our findings provide evidence that
C. cayetanensis has the potential to be transmitted via
contamination of drinking or irrigation water with wastewater.
 |
ACKNOWLEDGMENTS |
We are indebted to Field Willingham and Carrie Hancock for their
assistance during this study.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
International Health, Johns Hopkins University, 615 N. Wolfe Street, Baltimore, MD 21205. Phone: (410) 614-3959. Fax: (410) 614-6060. E-mail: rgilman{at}jhsph.edu.
 |
REFERENCES |
| 1.
|
American Public Health Association.
1995.
Immunofluorescence method for Giardia and Cryptosporidium spp. (PROPOSED), p. 9-111.
In
Standard methods for the examination of water and wastewater, 19th ed. American Public Health Association, Washington, D.C.
|
| 2.
|
Herwaldt, B. L.,
M.-L. Ackers, and the Cyclospora Working Group.
1997.
An outbreak in 1996 of cyclosporiasis associated with imported raspberries.
N. Engl. J. Med.
336:1548-1556[Abstract/Free Full Text].
|
| 3.
|
Jinneman, K. C.,
J. H. Wetherington,
A. M. Adams,
J. M. Johnson,
B. J. Tenge,
N.-L. Dang, and W. E. Hill.
1996.
In
Differentiation of Cyclospora sp. and Eimeria spp. by using the polymerase chain reaction amplification products and restriction fragment length polymorphisms. Laboratory Information Bulletin No. 4044. U.S.
Food and Drug Administration, Washington, D.C.
|
| 4.
|
Johnson, D. W.,
N. J. Pieniazek,
D. W. Griffin,
L. Misener, and J. B. Rose.
1995.
Development of a PCR protocol for sensitive detection of Cryptosporidium oocysts in water samples.
Appl. Environ. Microbiol.
61:3849-3855[Abstract].
|
| 5.
|
Ortega, Y. R.,
R. H. Gilman, and C. R. Sterling.
1993.
A new coccidian parasite (Apicomplexa: Eimeriidae) from humans.
J. Parasitol.
80:625-629.
|
| 5a.
|
Ortega, Y. R.,
C. R. Roxas,
R. H. Gilman,
N. Miller,
L. Cabrera,
C. Taquiri, and C. Sterling.
1997.
Isolation of Cryptosporidium parvum and Cyclospora cayetanensis from vegetables collected in markets of an endemic region in Peru.
Am. J. Trop. Med. Hyg.
57:683-686.
|
| 6.
|
Ortega, Y. R.,
C. R. Sterling,
R. H. Gilman,
V. A. Cama, and F. Diaz.
1993.
Cyclospora species a new protozoan pathogen of humans.
N. Engl. J. Med.
328:1308-1312[Abstract/Free Full Text].
|
| 7.
|
Yoder, K. E.,
O. Sethabutr, and D. A. Relman.
1996.
PCR-based detection of the intestinal pathogen Cyclospora, p. 169-176.
In
D. H. Persing (ed.), PCR protocols for emerging infectious diseases, a supplement to Diagnostic molecular microbiology: principles and applications. ASM Press, Washington, D.C.
|
Appl Environ Microbiol, June 1998, p. 2284-2286, Vol. 64, No. 6
0099-2240/98/$04.00+0
Copyright © 1998, American Society for Microbiology. All rights reserved.
This article has been cited by other articles:
-
Villena, I., Aubert, D., Gomis, P., Ferte, H., Inglard, J.-C., Denis-Bisiaux, H., Dondon, J.-M., Pisano, E., Ortis, N., Pinon, J.-M.
(2004). Evaluation of a Strategy for Toxoplasma gondii Oocyst Detection in Water. Appl. Environ. Microbiol.
70: 4035-4039
[Abstract]
[Full Text]
-
Shields, J. M., Olson, B. H.
(2003). PCR-Restriction Fragment Length Polymorphism Method for Detection of Cyclospora cayetanensis in Environmental Waters without Microscopic Confirmation. Appl. Environ. Microbiol.
69: 4662-4669
[Abstract]
[Full Text]
-
Orlandi, P. A., Carter, L., Brinker, A. M., da Silva, A. J., Chu, D.-M., Lampel, K. A., Monday, S. R.
(2003). Targeting Single-Nucleotide Polymorphisms in the 18S rRNA Gene To Differentiate Cyclospora Species from Eimeria Species by Multiplex PCR. Appl. Environ. Microbiol.
69: 4806-4813
[Abstract]
[Full Text]
-
Orlandi, P. A., Lampel, K. A.
(2000). Extraction-Free, Filter-Based Template Preparation for Rapid and Sensitive PCR Detection of Pathogenic Parasitic Protozoa. J. Clin. Microbiol.
38: 2271-2277
[Abstract]
[Full Text]