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Applied and Environmental Microbiology, June 2006, p. 4423-4425, Vol. 72, No. 6
0099-2240/06/$08.00+0 doi:10.1128/AEM.02662-05
Copyright © 2006, American Society for Microbiology. All Rights Reserved.
Prevalence of Chlamydophila psittaci in Fecal Droppings from Feral Pigeons in Amsterdam, The Netherlands
Edou R. Heddema,1*
Sietske ter Sluis,1
Jan A. Buys,2
Christina M. J. E. Vandenbroucke-Grauls,1,3
Joop H. van Wijnen,2 and
Caroline E. Visser1
Department of Medical Microbiology, Academic Medical Center, University of Amsterdam, Amsterdam, The Netherlands,1
Cluster Environment and Public Health, Municipal Health Service, Amsterdam, The Netherlands,2
Department of Medical Microbiology & Infection Control, VU University Medical Center, Amsterdam, The Netherlands3
Received 10 November 2005/
Accepted 18 March 2006

ABSTRACT
In many cities, the feral rock dove is an abundant bird species
that can harbor
Chlamydophila psittaci. We determined the prevalence
and genotype of
C. psittaci in fresh fecal samples from feral
pigeons in Amsterdam, The Netherlands. The prevalence was 7.9%
overall (26/331; 95% confidence interval, 5 to 11). Ten genotyped
PCR-positive samples were all genotype B.

INTRODUCTION
In many European cities, the feral rock dove (
Columbia livia)
is an abundant bird species that often lives in close contact
with humans. It is known that pigeons, like many other bird
species, can harbor
Chlamydophila psittaci. This bacterium is
a pathogen of birds but can cause zoonotic disease (
5). Birds
can shed this bacterium in the environment when they are either
overtly ill or without any symptoms. In birds, the bacterium
can be isolated from feces, the cloacae, and respiratory and
conjunctiva secretions. For this study, we determined the prevalence
of
C. psittaci shedding in feces from feral pigeons in Amsterdam,
The Netherlands, and the genotype of the PCR-positive samples.
C. psittaci in these specimens was detected with a recently
developed real-time PCR (
6).

Setting and sampling.
The city of Amsterdam consists of 14 town councils. Pigeon samples
were obtained from nine locations in eight town councils. These
locations were geographically widely distributed in Amsterdam,
and all were situated in public areas and chosen based on previous
research of assembling locations for feral pigeons in Amsterdam
(
3). At these locations, pigeons were attracted with food, and
their fresh fecal droppings were sampled with sterile cotton
swabs (MW&E, United Kingdom). Since shedding occurs intermittently
and can be activated by stress factors, such as breeding, samples
were taken on 3 February and 8 March 2005, when breeding activity
was low (low-breeding period), and on 2 May 2005, when breeding
was frequent (
12).

DNA extraction and PCR.
The cotton swabs were placed in 1.5-ml tubes in 300 µl
Baker water (Boom B.V. Meppel, The Netherlands) and vortexed
thoroughly. Fifty microliters of each fecal suspension was used
as input for the DNA extraction procedure (
1).
C. psittaci PCR
was performed as previously described (
6). Briefly, this real-time
PCR targets an 82-bp fragment of the
ompA gene of
C. psittaci as well as an internal control plasmid, using primers CpsittF
(5'-CGCTCTCTCCTTACAAGCC-3') and CPsittR (5'-AGCACCTTCCCA CATAGTG-3').
The internal control, which was added to each sample, has the
same primer sites, length, and nucleotide content as the
C. psittaci amplicon but has a shuffled probe binding region. To
prevent false-positive reactions due to amplicon carryover,
we used the uracil
N-glycosylase system and a unidirectional
workflow combined with separation of PCR mix preparation and
DNA extraction from all (post)amplification activities.

Genotyping.
PCR-positive samples were genotyped by
ompA sequence analysis.
The gene was amplified with the primers CPsittGenoFor (5'-GCTACGGGTTCCGCTCT-3';
nucleotides 400 to 416) and CPsittGenoRev (5'-TTTGTTGATYTGAATCGAAGC-3';
nucleotides 1420 to 1441) (nucleotide positions are according
to the
C. psittaci 6BC
ompA gene [GenBank accession no. X56980]),
resulting in a 1,041-bp amplicon. These primers target the conserved
regions of the
ompA gene enclosing the four variable domains.
Genotype PCR was performed in a LightCycler 2.0 instrument (Roche
Diagnostics, Germany). The final reaction mixture (20 µl)
included 8 µl eluate and was essentially the same as that
described previously (
6). The real-time PCR steps were as follows:
50°C for 10 min; 95°C for 10 min; and 45 cycles of 95°C
for 10 s, 62°C for 5 s, 72°C for 50 s, and 30°C
for 30 s. Ten microliters of the PCR product was analyzed by
1% agarose gel electrophoresis. The expected amplicon was excised
from the gel, purified by a simplified guanidinium thiocyanate
extraction procedure (2.5 µl silica; wash cycles with
L2, ethanol, and acetone), and eluted in 15 µl TE buffer
(10 mM Tris-HCl, 1 mM EDTA [pH 8.0]) (
2). To obtain sufficient
product for sequence analysis, reamplification for only 20 cycles
was performed in a GeneAmp 9700 thermocycler (Perkin-Elmer).
The reaction mixture for reamplification (50 µl) included
2 µl of eluate, 5 µl (10
x) PCR II buffer, 5 µg
bovine serum albumin, 0.25 U AmpliTaq Gold, a 0.16 µM
concentration of each primer, and 4.5 mM MgCl
2. The PCR steps
were as follows: 95°C for 10 min; 20 cycles of 95°C
for 1 min, 55°C for 1 min, and 72°C for 2 min; and 72°C
for 10 min. When a single band of approximately 1,041 bp was
obtained by agarose gel electrophoresis, the PCR product was
subjected to sequence analysis (BigDye Terminator sequencing
kit; Applied Biosystems). Overlapping sequences were obtained
with four sequencing primers, including the above-mentioned
genotype primers and two inner primers, CPsittFinner (5'-CGCTCTCTCCTTACAAGCC-3')
and CPsittRinner (5'-GATCTGAATCGAAGCAATTTG-3'). We used the
C. psittaci ORNI (genotype A) strain and a
C. abortus strain
as positive controls. To prevent amplicon carryover, the same
measures as those described for real-time PCR were taken. The
resulting sequences were aligned, and a similarity index based
on the resulting amino acids was calculated for an 894-bp fragment
of the
ompA gene. Similarity (1 distance) was calculated
by using the pairwise distance method generated by MEGA3 (
8).
Reference
ompA genotype sequences A to F (available in the GenBank
database under accession numbers AY762608 to -12 and AF269261)
were included in this analysis (
4).

Results.
In total, 331 fecal samples were obtained, with 160 samples
obtained before and 171 samples obtained during the breeding
period (Table
1). At least 15 samples were collected at each
location. During the low-breeding period, 5% (8/160; 95% confidence
interval [CI], 2% to 10%) of all samples were PCR positive.
Among samples obtained during the breeding period, 10% (18/171;
95% CI, 6% to 16%) were positive, and hence the prevalence of
positive samples during the breeding period was twice that in
the low-breeding period (
P = 0.07 by Fisher's exact test; GraphPad
Software, San Diego, CA). The overall prevalence was 7.9% (26/331;
95% CI, 5% to 11%). All negative samples were truly negative
since all internal controls were amplified correctly, thus excluding
the occurrence of PCR inhibition. It was possible to genotype
10 of the 26 PCR-positive samples. The obtained sequences were
all 100% similar to reference genotype B. Similarities based
on amino acid sequences were 98% (genotype A), 56% (C), 43%
(D), 99% (E), and 51% (F). The positive controls (
C. psittaci ORNI and
C. abortus) were amplified as expected and could subsequently
be sequenced.
View this table:
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TABLE 1. Number of C. psittaci PCR-positive fecal samples in feral pigeons by sampling location in Amsterdam, The Netherlands
|

Discussion.
This study shows that between 5 and 10% of our sample of urban
feral pigeons in Amsterdam shed
C. psittaci in their feces.
Only genotype B was found in these isolates. We were unable
to genotype all PCR-positive samples. For genotyping, a 1,041-bp
fragment had to be amplified; the genotyping PCR was less sensitive
than the optimized diagnostic real-time PCR, which amplifies
a fragment of only 82 bp. Therefore, samples with relatively
low
C. psittaci loads could not be amplified by genotyping PCR.
The major advantage of this study was the use of an internally
controlled real-time PCR assay. PCR is a sensitive and specific
test compared to enzyme-linked immunosorbent assays and tissue
culture assays available for
C. psittaci detection in birds
(
7,
9). Salinas et al. reported one of the largest series on
the prevalence of
C. psittaci in feral pigeons (
10). In their
study,
C. psittaci was found by culture in 18% (7/39; 95% CI,
9% to 33%) of fecal samples, a prevalence that is similar to
our results obtained by PCR. Recently, Tanaka et al. found
C. psittaci in 106 of 463 (22.9%; 95% CI, 19% to 27%) fecal samples
obtained from feral pigeons. However, they did not use exclusively
fresh fecal samples and applied a nested PCR protocol, which
is known to be particularly prone to contamination (
13).
A previous study indicated that in 2001, the pigeon population size in Amsterdam averaged approximately 30,000 (3). Combined with our results, the number of feral pigeons shedding C. psittaci in their feces would be, on average, about 2,400 (95% CI, 1,500 to 3,300). Our isolates were all identical to genotype B. Currently, at least nine genotypes are known. Each genotype is more or less associated with a specific group of birds from which it is most commonly isolated. Geens et al. and Vanrompay et al. also found genotype B to be particularly associated with the pigeon host (4, 14). However, this genotype has been recovered from many bird species, including turkeys, parakeets, and ducks (11, 15). Whether shedding of C. psittaci by feral pigeons in Amsterdam poses a substantial zoonotic risk for humans has to be determined. Besides the zoonotic potential, there is also the risk of infection of domesticated birds, such as pet birds and poultry, which live in closer contact with human beings. Diagnosing C. psittaci infections has been hampered by a lack of sensitive and specific methods. Culture is only performed in some select laboratories, serologic tests do not fully differentiate infections with the various Chlamydia spp., and PCR is not routinely performed. However, PCR can provide a definitive diagnosis of psittacosis. We recommend that psittacosis in humans be diagnosed by detection of the agent by PCR, with or without serologic testing, instead of by serologic testing alone. Subsequent ompA gene sequence analysis can identify the responsible genotype. This approach could lead to a better understanding of the epidemiology of the different genotypes of C. psittaci in infected bird populations and human psittacosis cases and determine the relationship between the two.

Nucleotide sequence accession numbers.
The
ompA sequences of the positive control strains and the genotype
B sequence obtained from the fecal pigeon samples were submitted
to GenBank under accession no. DQ267973, DQ435299, and DQ435300.

ACKNOWLEDGMENTS
Y. Pannekoek, University of Amsterdam, Amsterdam, The Netherlands,
provided the
C. psittaci ORNI strain. D. Vanrompay, Ghent University,
Ghent, Belgium, provided the
C. abortus strain.

FOOTNOTES
* Corresponding author. Mailing address: Department of Medical Microbiology, Room L1-245, P.O. Box 22660, 1100 DD Amsterdam, The Netherlands. Phone: 31 20 5665731. Fax: 31 20 5669745. E-mail:
e.r.heddema{at}amc.uva.nl.


REFERENCES
1 - Boom, R., C. Sol, J. Weel, K. Lettinga, Y. Gerrits, A. van Breda, and P. Wertheim-van Dillen. 2000. Detection and quantitation of human cytomegalovirus DNA in faeces. J. Virol. Methods 84:1-14.[CrossRef][Medline]
2 - Boom, R., C. J. Sol, M. M. Salimans, C. L. Jansen, P. M. Wertheim-Van Dillen, and J. van der Noordaa. 1990. Rapid and simple method for purification of nucleic acids. J. Clin. Microbiol. 28:495-503.[Abstract/Free Full Text]
3 - Buijs, J. A., and J. H. Van Wijnen. 2001. Survey of feral rock doves (Columba livia) in Amsterdam, a bird-human association. Urban Ecosystems 5:235-241.[CrossRef]
4 - Geens, T., A. Desplanques, M. Van Loock, B. M. Bonner, E. F. Kaleta, S. Magnino, A. A. Andersen, K. D. Everett, and D. Vanrompay. 2005. Sequencing of the Chlamydophila psittaci ompA gene reveals a new genotype, E/B, and the need for a rapid discriminatory genotyping method. J. Clin. Microbiol. 43:2456-2461.[Abstract/Free Full Text]
5 - Haag-Wackernagel, D., and H. Moch. 2004. Health hazards posed by feral pigeons. J. Infect. 48:307-313.[CrossRef][Medline]
6 - Heddema, E. R., M. G. H. M. Beld, B. de Wever, A. A. J. Langerak, Y. Pannekoek, and B. Duim. Development of an internally controlled real-time PCR assay for detection of Chlamydophila psittaci in the LightCycler 2.0 system. Clin. Microbiol. Infect., in press.
7 - Hewinson, R. G., P. C. Griffiths, B. J. Bevan, S. E. Kirwan, M. E. Field, M. J. Woodward, and M. Dawson. 1997. Detection of Chlamydia psittaci DNA in avian clinical samples by polymerase chain reaction. Vet. Microbiol. 54:155-166.[CrossRef][Medline]
8 - Kumar, S., K. Tamura, and M. Nei. 2004. MEGA3: integrated software for molecular evolutionary genetics analysis and sequence alignment. Brief. Bioinform. 5:150-163.[Abstract/Free Full Text]
9 - McElnea, C. L., and G. M. Cross. 1999. Methods of detection of Chlamydia psittaci in domesticated and wild birds. Aust. Vet. J. 77:516-521.[Medline]
10 - Salinas, J., M. R. Caro, and F. Cuello. 1993. Antibody prevalence and isolation of Chlamydia psittaci from pigeons (Columba livia). Avian Dis. 37:523-527.[CrossRef][Medline]
11 - Sayada, C., A. A. Andersen, C. Storey, A. Milon, F. Eb, N. Hashimoto, K. Hirai, J. Elion, and E. Denamur. 1995. Usefulness of omp1 restriction mapping for avian Chlamydia psittaci isolate differentiation. Res. Microbiol. 146:155-165.[Medline]
12 - Scientific Committee on Animal Health and Animal Welfare. 2002. Avian chlamydiosis as a zoonotic risk and reduction strategies. [Online.] http://europa.eu.int/comm/food/fs/sc/scah/out73_en.pdf.
13 - Tanaka, C., T. Miyazawa, M. Watarai, and N. Ishiguro. 2005. Bacteriological survey of feces from feral pigeons in Japan. J. Vet. Med. Sci. 67:951-953.[CrossRef][Medline]
14 - Vanrompay, D., A. A. Andersen, R. Ducatelle, and F. Haesebrouck. 1993. Serotyping of European isolates of Chlamydia psittaci from poultry and other birds. J. Clin. Microbiol. 31:134-137.[Abstract/Free Full Text]
15 - Vanrompay, D., P. Butaye, C. Sayada, R. Ducatelle, and F. Haesebrouck. 1997. Characterization of avian Chlamydia psittaci strains using omp1 restriction mapping and serovar-specific monoclonal antibodies. Res. Microbiol. 148:327-333.[Medline]
Applied and Environmental Microbiology, June 2006, p. 4423-4425, Vol. 72, No. 6
0099-2240/06/$08.00+0 doi:10.1128/AEM.02662-05
Copyright © 2006, American Society for Microbiology. All Rights Reserved.
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