Literature DB >> 33224510

Detection of Chlamydiaceae in Swiss wild birds sampled at a bird rehabilitation centre.

Sandro Stalder1, Hanna Marti2, Nicole Borel2, Prisca Mattmann3, Barbara Vogler1, Nina Wolfrum1, Sarah Albini1.   

Abstract

BACKGROUND: Annually, 800-1500 wild birds are admitted to the rehabilitation centre of the Swiss Ornithological Institute, Sempach, Lucerne, Switzerland. The workers of the centre come in close contact with the avian patients and might therefore be exposed to zoonotic agents shed by these birds, such as Chlamydia psittaci.
METHODS: In the present study, 91 choanal, 91 cloacal and 267 faecal swabs from 339 wild birds of 42 species were investigated using a stepwise diagnostic approach.
RESULTS: Chlamydiaceae were detected in 0.9 per cent (0.3-2.6 per cent) of birds (n=3), all of them members of the Columbidae family. The Chlamydiaceae species of two of these birds (one Eurasian collared dove, one fancy pigeon) were identified as C psittaci types B and E by PCR and outer membrane protein A genotyping.
CONCLUSION: The findings of the current study suggest that zoonotic transmission of Chlamydiaceae is very unlikely for songbird and waterfowl species tested herein, while pigeons might pose a risk to workers at rehabilitation centres. © British Veterinary Association 2020. Re-use permitted under CC BY-NC. No commercial re-use. Published by BMJ.

Entities:  

Keywords:  Chlamydia psittaci; Chlamydiaceae; Switzerland; bird rehabilitation centre; wild birds

Year:  2020        PMID: 33224510      PMCID: PMC7662422          DOI: 10.1136/vetreco-2020-000437

Source DB:  PubMed          Journal:  Vet Rec Open        ISSN: 2052-6113


Introduction

The rehabilitation centre of the Swiss Ornithological Institute is located in Sempach, Lucerne, Switzerland. In the last 10 years, between 800 and 1500 birds were admitted for treatment annually. The workers of the rehabilitation centre come in close contact with the birds and their faeces during the time of treatment. Thus, the workers might be exposed to zoonotic agents shed by these birds, such as Chlamydia psittaci. Several Chlamydiaceae species are harboured by wild birds, for example, C abortus, C avium, C pecorum and Candidatus C ibidis.1–7 C psittaci, the causative agent of psittacosis/ornithosis in human and avian chlamydiosis, has been detected in more than 460 avian species.8 The clinical signs in C psittaci-infected birds are variable, depending on age, species and immune status of the host, and the pathogenicity of the causative strain.9 Clinical signs include respiratory, enteric and ocular signs, but asymptomatic infections are common.10 In Switzerland, 46 cases in birds have been reported to the Federal Food Safety and Veterinary Office from 2010 to 2019.11 Transmission from birds to humans occurs through inhalation of feather dust or aerosols from urine, dried faeces, and respiratory and eye secretions.12 Most infected humans remain asymptomatic or have mild symptoms, but in some cases C psittaci causes severe pneumonia. Studies investigating the occurrence of Chlamydiaceae in European wild birds reported infection rates ranging from 2.8 per cent to 14.8 per cent determined using PCR or immunoassay.5 13–18 In Switzerland, two PCR-based studies focusing on pigeons reported infection rates of 8.4 per cent and 16.9 per cent,19 20 and another PCR-based study reported infection rates of 14.3 per cent in pigeons, 0.4 per cent in songbirds and 4.3 per cent in waterfowl.21 The highest infection rates of Chlamydiaceae were observed in Columbiformes and Psittaciformes, where C psittaci is the most frequently detected species.22 23 Passeriformes were only occasionally diagnosed with chlamydiosis.24 25 The current study aims to investigate whether admitted wild birds pose a risk of zoonotic chlamydial infection to workers at a Swiss wild bird rehabilitation centre.

Materials and methods

Samples

Samples were obtained from the wild bird rehabilitation centre of the Swiss Ornithological Institute in Sempach, Lucerne, Switzerland, between April and October 2018 (online supplemental table 1). Around two-thirds of the birds were admitted during the peak season from May to mid-July, the majority of which were juveniles. Submitted avian patients received care depending on their condition, for example, feeding, cleaning, veterinary care, treatment or surgery if necessary. The staff of the rehabilitation centre (six persons, among one veterinarian) come into close contact with the birds while handling them, although manual handling is reduced to the necessary minimum. Juvenile birds are kept in small boxes with household paper or foam pads as substrate. Fledged birds are transferred to cages with foam pads or an outdoor aviary. The boxes and foam pads are cleaned every one to two hours using an industrial dishwasher; cages are cleaned with water and soap—depending on the amount and quality of faeces—daily or twice daily. Disinfection of the cages (Meliseptol rapid, B Braun) is carried out before each reassignment. The outdoor aviaries are cleaned when necessary using a high-pressure cleaner at 60°C while wearing a protective mask and goggles. This study included 339 wild birds representing nine orders and 42 species, as shown in table 1.
Table 1

Species, number of sample types and number of individual birds per total number of birds tested for Chlamydiaceae using real-time PCR in this study

OrderFamilySpecies name (Latin)Species name (English)Number of available and Chlamydiaceae*-positive swab samples per anatomical siteChlamydiaceae-positive birds (%, 95% CI)Mean Ct value, Chlamydiaceae quantitative PCRChlamydia psittaci-positive birds (%)Accession number of ompA study sequence
FaecesChoanaCloaca
AnseriformesAnatidaeAnas platyrhynchosMallard0/260/40/40/29 (0, 0–11.7)n.d.
Cygnus olorMute swan0/00/10/10/1 (0, 0–79.4)n.d.
Mergus merganserCommon merganser0/90/00/00/9 (0, 0–29.9)n.d.
ApodiformesApodidaeApus apusCommon swift0/150/70/70/20 (0, 0–16.1)n.d.
Tachymarptis melbaAlpine swift0/30/00/00/3 (0, 0–56.2)n.d.
CharadriiformesLaridaeLarus michahellisYellow-legged gull0/30/10/10/4 (0, 0–49.0)n.d.
CiconiiformesCiconiidaeCiconia ciconiaWhite stork0/30/20/20/5 (0, 0–43.5)n.d.
ColumbiformesColumbidaeColumba livia domesticaFancy pigeon0/41/11/11/5 (20, 3.6–62.5)Choana: 28.0Cloaca: 29.31/1 (100)MT450277
Columba livia domesticaFeral pigeon0/50/20/20/6 (0, 0–39.0)n.d.
Columba palumbusCommon wood pigeon1/40/10/11/5 (20, 3.6–62.5)Faeces: 37.90/1 (0)
Streptopelia decaoctoEurasian collared dove0/21/21/21/4 (25, 4.6–69.9)Choana: 36.0Cloaca: 16.91/1 (100)MT450278
GruiformesRallidaeCrex crexCorn crake0/10/00/00/1 (0, 0–79.4)n.d.
Fulica atraEurasian coot0/20/10/10/3 (0, 0–56.2)n.d.
PasseriformesAcrocephalidaeAcrocephalus scirpaceusEurasian reed warbler0/00/10/10/1 (0, 0–79.4)n.d.
EmberizidaeEmberiza citrinellaYellowhammer0/10/10/10/1 (0, 0–79.4)n.d.
FringillidaeCarduelis carduelisGoldfinch0/80/10/10/8 (0, 0–32.4)n.d.
Chloris chlorisEuropean greenfinch0/40/40/40/7 (0, 0–35.4)n.d.
Coccothraustes coccothraustesHawfinch0/10/10/10/2 (0, 0–65.8)n.d.
Fringilla coelebsCommon chaffinch0/40/10/10/4 (0, 0–49.0)n.d.
Serinus serinusEuropean serin0/10/00/00/1 (0, 0–79.4)n.d.
HirundinidaeDelichon urbicumCommon house martin0/20/00/00/2 (0, 0–65.8)n.d.
Hirundo rusticaBarn swallow0/40/20/20/6 (0, 0–39.0)n.d.
MotacillidaeMotacilla albaWhite wagtail0/30/00/00/3 (0, 0–56.2)n.d.
MuscicapidaeErithacus rubeculaEuropean robin0/00/10/10/1 (0, 0–79.4)n.d.
Ficedula hypoleucaEuropean pied flycatcher0/10/00/00/1 (0, 0–79.4)n.d.
Muscicapa striataSpotted flycatcher0/30/00/00/3 (0, 0–56.2)n.d.
Phoenicurus ochrurosBlack redstart0/60/20/20/8 (0, 0–32.4)n.d.
ParidaeCyanistes caeruleusEurasian blue tit0/180/70/70/25 (0, 0–13.3)n.d.
Parus majorGreat tit0/150/30/30/18 (0, 0–17.6)n.d.
PasseridaePasser domesticusHouse sparrow0/400/110/110/48 (0, 0–7.4)n.d.
Passer montanusEurasian tree sparrow0/50/10/10/6 (0, 0–39.0)n.d.
SittidaeSitta europaeaEurasian nuthatch0/00/10/10/1 (0, 0–79.4)n.d.
SturnidaeSturnus vulgarisCommon starling0/40/20/20/6 (0, 0–39.0)n.d.
SylviidaeSylvia atricapillaEurasian blackcap0/70/10/10/7 (0, 0–35.4)n.d.
Sylvia borinGarden warbler0/10/00/00/1 (0, 0–79.4)n.d.
TurdidaeTurdus merulaBlackbird0/500/220/210/67 (0, 0–5.4)n.d.
Turdus philomelosSong thrush0/30/30/30/4 (0, 0–49.0)n.d.
Turdus pilarisFieldfare0/20/10/10/3 (0, 0–56.2)n.d.
Turdus viscivorusMistle thrush0/10/00/00/1 (0, 0–79.4)n.d.
PelecaniformesArdeidaeArdea cinereaGrey heron0/00/20/20/2 (0, 0–65.8)n.d.
PiciformesPicidaeDendrocopos majorGreat spotted woodpecker0/30/10/10/3 (0, 0–56.2)n.d.
Picus viridisEuropean green woodpecker0/30/00/10/4 (0, 0–49.0)n.d.
Total1/2672/912/913/339 (0.9, 0.3–2.6)2/3 (66.7)

*All faecal swabs were obtained from living birds after defecation. Both choanal and cloacal swabs were available from 89 deceased birds. From one blackbird only a choanal swab was available. From one Eurasian blue tit a faecal and a choanal swab were available. Only a cloacal swab was obtained from one Eurasian blue tit and one European green woodpecker. All three swab types were obtained from 20 birds that died or were euthanased during treatment due to trauma or disease.

CI, confidence interval; Ct, cycle threshold; n.d., not determined; ompA, outer membrane protein A.

Species, number of sample types and number of individual birds per total number of birds tested for Chlamydiaceae using real-time PCR in this study *All faecal swabs were obtained from living birds after defecation. Both choanal and cloacal swabs were available from 89 deceased birds. From one blackbird only a choanal swab was available. From one Eurasian blue tit a faecal and a choanal swab were available. Only a cloacal swab was obtained from one Eurasian blue tit and one European green woodpecker. All three swab types were obtained from 20 birds that died or were euthanased during treatment due to trauma or disease. CI, confidence interval; Ct, cycle threshold; n.d., not determined; ompA, outer membrane protein A. The age of 316 birds was known, of which 163 were nestlings, 126 juveniles and 27 adults. Dry choanal (n=91) and cloacal swabs (n=91) (FLOQSwabs, COPAN Flock Technologies) were obtained from deceased birds only. Dry faecal swabs (n=267) were taken from living birds after defecation. Samples were stored at −80°C until further processing.

DNA extraction

A commercial kit (Genomic DNA from tissue, NucleoSpin Tissue from Macherey-Nagel) was used to extract the DNA of choanal and cloacal swabs. DNA of the faecal samples was extracted with the Macherey-Nagel NucleoSpin stool kit according to the manufacturer’s instructions. Extracted DNA was stored at −20°C until further use.

Real-time qPCR assays for detection of Chlamydiaceae

First, all samples were tested in duplicates with a 23S rRNA-based Chlamydiaceae family-specific quantitative PCR (qPCR) (111 bp) modified to include an internal positive amplification control (IPC; enhanced green fluorescent protein (eGFP))26–28 on an Applied Biosystems 7500 Real-Time PCR System (Thermo Fisher Scientific). The cycle conditions were 95°C for 20 seconds, followed by 45 cycles of 95°C for three seconds and 60°C for 30 seconds. For every sample, a 25 µl reaction mix was prepared, including 12.5 µl TaqMan Universal PCR MasterMix, 500 nM of the primers ‘CH23S-F’ (5’-CTGAAACCAGTAGCTTATAAGCGGT-3’) and ‘CH23S-R’ (5’-ACCTCGCCGTTTAACTTAACTCC-3’), 200 nM of the probe ‘CH23S-P’ (5’ FAM-CTCATCATGCAAAAGGCACGCCG-TAMRA 3’), and 200 nM each of the primers ‘eGFP-1-F’ (5’-GACCACTACCAGCAGAACAC-3’) and ‘eGFP-10-R’ (5’-CTTGTACAGCTCGTCCATGC-3’), and the probe ‘eGFP-HEX’ (5’-HEX-AGCACCCAGTCCGCCCTGAGCA-BHQ1-3’). A sevenfold dilution series of C abortus DNA with a known number of DNA copies was included in each run as a positive control and standard curve. Molecular grade water was included as a negative control in each run. Samples were interpreted as positive if the mean cycle threshold (Ct value) was less than 38. Samples with higher Ct values or inhibited amplification were retested in duplicate. Samples repeatedly showing a Ct value greater than 38 were considered positive. Samples with inhibited amplification were retested undiluted and tenfold diluted, both in duplicates. Secondly, in samples positive for Chlamydiaceae, a C psittaci-specific qPCR (76 bp) was performed as previously described, modified to include an IPC.29 30 The reaction mix contained 4 µl (<150 ng/µl) sample template, 1 µl eGFP template, 1 x TaqMan Universal PCR MasterMix, 900 nM of the primers ‘CppsOMP1-F’ (5’-CACTATGTGGGAAGGTGCTTCA-3’) and ‘CppsOMP1-R’ (5’-CTGCGCGGATGCTAATGG-3’), 200 nM probe ‘CppsOMP1-S’ (5’-FAM-CGCTACTTGGTGTGAC-TAMRA-3’), 900 nM of the primers ‘eGFP-1-F’ (5’-GACCACTACCAGCAGAACAC-3’) and ‘eGFP-2-R’ (5’-GAACTCCAGCAGGACCATG-3’), and 200 nM probe ‘eGFP-HEX’ (5’-HEX-AGCACCCAGTCCGCCCTGAGCA-BHQ1-3’) in a final volume of 25 µl.

Outer membrane protein A genotyping PCR

Samples that were positive for C psittaci in qPCR were subjected to an outer membrane protein A (ompA) genotyping PCR. Per sample, a reaction mix with a final volume of 50 µl containing 25 µl REDTaq ReadyMix (Merck KGaA), 200 nM of the primers ‘ompA F (CTU)’ (5’-ATGAAAAAACTCTTGAAATCGG-3’) and ‘ompA rev’ (5’-TCCTTAGAATCTGAATTGAGC-3’), and 3 µl sample template with a DNA concentration of 25 ng/µl was prepared.31 Cycling conditions were 10 minutes at 95°C, followed by 35 cycles of 95°C for 30 seconds, 49°C for 30 seconds, 72°C for 60 seconds and a final elongation at 72°C for seven minutes. PCR products were purified using the QIAquick PCR Purification Kit (Qiagen) according to the manufacturer’s instructions. Purified amplicons were Sanger-sequenced by Microsynth. The obtained sequences were assembled and analysed using the Geneious Prime software version 2019.2.3 and compared against the National Center for Biotechnology Information database using the BLASTn tool (https://blast.ncbi.nlm.nih.gov/). All primers and probes used in this study were obtained from Microsynth.

Results

Chlamydiaceae were detected in 0.9 per cent (95 per cent confidence interval: 0.3–2.6 per cent) of the birds (n=3) of three different species, namely in one of five (20 per cent, 3.6–62.5 per cent) fancy pigeons (Columba livia domestica), one of five (20 per cent, 3.6–62.5 per cent) common wood pigeons (Columba palumbus), and one of four (25 per cent, 4.6–69.9 per cent) Eurasian collared doves (Streptopelia decaocto), as shown in table 1. Five individual samples were positive for Chlamydiaceae: both choanal and cloacal swabs from the Eurasian collared dove and fancy pigeon, and a faecal swab from the common wood pigeon. Both choanal and cloacal swabs from the Eurasian collared dove and fancy pigeon were positive for C psittaci by species-specific qPCR. OmpA genotyping classified the organism detected in the cloacal sample of the Eurasian collared dove as C psittaci B. C psittaci detected in the choanal swab of the fancy pigeon belonged to the ompA genotype E. C psittaci was not detected in the Chlamydiaceae-positive faecal swab of the common wood pigeon, and ompA genotyping was not successful due to low copy numbers (table 1). Thus, it was not possible to specify the detected Chlamydiaceae in this sample.

Discussion

The workers at the rehabilitation centre belong to the population at risk for zoonotic diseases transmitted by birds. Among all bird orders, Columbiformes and psittacine birds show the highest Chlamydia prevalence, ranging between 3.4 per cent and 50 per cent.22 23 In this study, three of 20 (15 per cent, 5.2–36.2 per cent) of the Columbiformes were positive for Chlamydiaceae, whereof two were positive for C psittaci. This is in accordance with the findings of other studies performed in Switzerland.20 21 C psittaci genotype B, which was found in one Eurasian collared dove, is the predominant genotype in the European pigeon population.22 32 33 Genotype E, which was found in one fancy pigeon, infects a variety of avian species and is frequently found in pigeons worldwide.34–37 Both genotypes are zoonotic, but human infection is mostly associated with genotype A causing a more severe course of disease.38–40 Chlamydiaceae were not detected in any other bird order included in this study. Partly, the low infection rate might be due to the selection of study samples. The majority of birds (n=246) were tested via faecal swabs only. Testing of faecal swabs has been shown to be a less sensitive method for detection of Chlamydiaceae compared with choanal swabs.41 Furthermore, most birds were nestlings (n=163) or juveniles (n=126), which were previously shown to have lower Chlamydiaceae prevalence than adult birds.18 However, these circumstances reflect the real conditions in the rehabilitation centre during the peak season. The findings in this study are in accordance with those of Zweifel and others,21 reporting low infection rates of non-C psittaci-Chlamydiaceae in songbirds (0.4 per cent) and waterfowl (4.3 per cent). In this study, excretion of Chlamydiaceae under stressful conditions in a bird rehabilitation centre was only present in pigeons. As pigeons mostly harbour C psittaci, they may therefore pose a hazard to workers at rehabilitation centres. In order to minimise the risk of zoonotic chlamydial transmission, protective equipment (eg, gloves, masks) should always be used and appropriate hygiene measures (eg, washing hands) should be adhered to when handling wild birds.42
  39 in total

1.  Prevalence of Chlamydophila psittaci-positive cloacal PCR tests in wild avian casualties in the UK.

Authors:  E Sharples; S J Baines
Journal:  Vet Rec       Date:  2009-01-03       Impact factor: 2.695

2.  Chlamydophila psittaci in free-living Blue-fronted Amazon parrots (Amazona aestiva) and Hyacinth macaws (Anodorhynchus hyacinthinus) in the Pantanal of Mato Grosso do Sul, Brazil.

Authors:  Tânia de Freitas Raso; Gláucia Helena Fernandes Seixas; Neiva Maria Robaldo Guedes; Aramis Augusto Pinto
Journal:  Vet Microbiol       Date:  2006-08-08       Impact factor: 3.293

3.  Prevalence of Chlamydia psittaci in the feral pigeon population of Basel, Switzerland.

Authors:  Ila Geigenfeind; Daisy Vanrompay; Daniel Haag-Wackernagel
Journal:  J Med Microbiol       Date:  2011-09-15       Impact factor: 2.472

Review 4.  Chlamydia psittaci infections: a review with emphasis on avian chlamydiosis.

Authors:  D Vanrompay; R Ducatelle; F Haesebrouck
Journal:  Vet Microbiol       Date:  1995-07       Impact factor: 3.293

5.  More than classical Chlamydia psittaci in urban pigeons.

Authors:  Konrad Sachse; Simone Kuehlewind; Anke Ruettger; Evelyn Schubert; Gernot Rohde
Journal:  Vet Microbiol       Date:  2012-01-08       Impact factor: 3.293

6.  Chlamydia psittaci in Eurasian Collared Doves (Streptopelia decaocto) in Italy.

Authors:  Manuela Donati; Karine Laroucau; Mauro Delogu; Fabien Vorimore; Rachid Aaziz; Eleonora Cremonini; Roberta Biondi; Claudia Cotti; Raffaella Baldelli; Antonietta Di Francesco
Journal:  J Wildl Dis       Date:  2015-01       Impact factor: 1.535

7.  Comparison of pharyngeal, fecal, and cloacal samples for the isolation of Chlamydia psittaci from experimentally infected cockatiels and turkeys.

Authors:  A A Andersen
Journal:  J Vet Diagn Invest       Date:  1996-10       Impact factor: 1.279

8.  Risk factors associated with Chlamydia psittaci infections in psittacine birds and bird handlers.

Authors:  H M N Tolba; R M M Abou Elez; I Elsohaby
Journal:  J Appl Microbiol       Date:  2018-11-23       Impact factor: 3.772

9.  Investigation on the frequency of Chlamydia sp. infections in tits (Paridae).

Authors:  H A Holzinger-Umlauf; R E Marschang; M Gravendyck; E F Kaleta
Journal:  Avian Pathol       Date:  1997       Impact factor: 3.378

10.  Genotyping of Chlamydophila psittaci using a new DNA microarray assay based on sequence analysis of ompA genes.

Authors:  Konrad Sachse; Karine Laroucau; Helmut Hotzel; Evelyn Schubert; Ralf Ehricht; Peter Slickers
Journal:  BMC Microbiol       Date:  2008-04-17       Impact factor: 3.605

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Authors:  Barbara R Vogler; Katrin Zurfluh; Prisca Mattmann; Kira Schmitt; Sarah Albini
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