Abstract
Investigations conducted on feral African Sacred Ibises ( Threskiornis aethiopicus ) in western France led to the isolation of a strain with chlamydial genetic determinants. Ultrastructural analysis, comparative sequence analysis of the 16S rRNA gene, ompA, and of a concatenate of 31 highly conserved genes, as well as determination of the whole genome sequence confirmed the relatedness of the new isolate to members of the Chlamydiaceae, while, at the same time demonstrating a unique position outside the currently recognized species of this family. We propose to name this new chlamydial species Chlamydia ibidis .
Introduction
As they are relatively easily kept in captivity, African Sacred Ibises have been introduced into many zoological parks around the world. In the 1990s, some of these birds escaped from a zoological park in Brittany (western France), where they had been allowed to fly unrestrained. Subsequently, a feral population established itself and disseminated along the wetlands of the French Atlantic coast. The feral population steadily increased to more than 5,000 birds in 2006 [1]. Major concerns on its possible impact on biodiversity arose from the birds’ predatory behaviour and ecological niche, as well as their potential role as a reservoir for the transmission of pathogens [2].
Avian chlamydiosis has been shown to occur in more than 465 avian species, including domestic, companion and wild birds [3]. Chlamydia psittaci is the most prominent chlamydial agent encountered in Aves. The family Chlamydiaceae currently comprises one genus Chlamydia and eight other species: trachomatis, suis, muridarum, pneumoniae, abortus, caviae, felis, and pecorum [4].
Laboratory diagnosis of chlamydial infections has undergone a remarkable methodological evolution in the past two decades [5]. Notably, multiple PCR-based detection methods that allow rapid detection of all species of the family Chlamydiaceae have been developed. Based on these methods, new and hitherto non-classified chlamydial agents have been recently described [6-12].
In accordance with international conventions, the French authorities have allowed culling operations since 2007 in order to reduce the population of this invasive bird. As ibises were repeatedly observed to feed on open-air duck breeding premises [13], where avian chlamydiosis is highly prevalent [14-16], investigations were therefore conducted on ibises shot during official culling operations.
Here, we report the results of a study conducted on ibises shot during the official culling operations carried out in western France in 2009 and 2010.
Materials and Methods
Samples
The Sacred Ibis is a feral species (origin: zoos) in Western and Southern France. It is considered in France and Europe of concern because of its invasive capacity (see www.europe-aliens.org). France has taken regulations for its destruction, by means of annual County Regulation Acts, that authorize destruction, with details on the protocol and laboratories authorized for analysis. The operations of destruction are ongoing since 2008. From March 2009 to July 2010, the 70 feral birds used in this study were shot by governmental environmental police agents (ONCFS), with precaution not to harm or scare other protected species, as their habitats are protected wetlands. These 70 birds were members of a group that was repeatedly observed to visit duck breeding premises, wetlands, landfills and ruminant manure. Animals that were not dead after being shot were put down by vertebral dislocation. Sample collection was done on dead animals only. For this study, the protocol of destruction was not submitted to an ethical committee, but the regulations were taken after discussion with local stakeholders and wildlife protection non-governmental organizations, in conformity with French, European and International laws and treaties. The transfer of duplicate cloacal swabs from these birds to the research laboratories where this study was performed was authorized by way of administrative decrees (Prefecture du Morbihan, "arrets" dated 23 February 2009 and 09 July 2010). The first swab was stored dry, to be subjected to DNA extraction, while the second swab was stored in SPG storage buffer [17] at 80°C, later to be used for inoculation of chicken eggs. Key data are summarized in Table 1 .
Table 1. Examination of samples from feral Sacred Ibis populations in 2009 and 2010.
ID | Date of capture |
23S-rtPCR Chlamydiaceae
|
incA-rtPCR C. psittaci | Cell culture isolation | ||
---|---|---|---|---|---|---|
No. of +ve samples | mean Ct | No. of +ve samples | ||||
09-0370 | 10/03/2009 | 0/21 | - | - | - | |
09-0468 | 30/03/2009 | 1/15 | 30.78 | 0/1 | 0/1 | |
10-1398 | 01/07/2010 | 7/34 | 34.93 | 1/7 | 3/7 | |
Total | 8/70 | 1/8 | 3/8 |
Direct detection of Chlamydiaceae DNA from avian samples
The dry panel of cloacal swabs was subjected to DNA extraction using a QIAamp DNA Mini Kit, following the buccal swab protocol (Qiagen, Courtaboeuf, France). DNA was eluted with 150 µl of AE buffer and stored at -20°C before analysis.
A Chlamydiaceae-specific real-time PCR targeting the 23S rRNA gene was used in this study [18]. The protocol includes primers Ch23S-F (5'-CTGAAACCAGTAGCTTATAAGCGGT-3'), Ch23S-R (5'-ACCTCGCCGTTTAACTTAACTCC-3'), and probe Ch23S-p (FAM-5’-CTCATCATGCAAAAGGCACGCCG-3’-TAMRA). Each reaction mix contained 2 µl sample DNA template, 10 µl of Universal Master mix 2X (Applied Biosystems), 0.5 µl of each primer (25 µM) and 2 µl of the probe (1 µM), and 5 µl deionized water. The temperature-time profile was 95°C 10 min, 50 cycles of 95°C 15 s, 60°C 60 s. An internal, positive control was included in each sample to test for the presence of PCR inhibitors (Exogenous internal positive control, TaqMan, Life technologies).
Inoculation of embryonated chicken eggs
For culture, suspensions of cloacal swabs stored in storage buffer at -80°C were thawed, transferred into sterile Eppendorf tubes and centrifuged at 10,000 rpm for 5 min. Supernatants were transferred into a new sterile tube. Antibiotic solution containing 1 mg/ml of vancomycin, 1 mg/ml of streptomycin, 1 mg/ml of kanamycin and 1000 units/ml of nystatin was added to the supernatant and to the resuspended pellet, which were then incubated at 37°C for 2 h before inoculation.
Yolk sacs of 7 day-old embryonated eggs were inoculated with 0.2 ml per egg, and 5 eggs per sample. For each set of inoculations, 3 eggs were inoculated with C. psittaci Loth as a positive control, and 3 other eggs were kept separately as non-infected controls. Eggs were incubated at 38°C and observed daily. Vitellus membranes were collected, then analysed using either a MIF test, i.e. a direct immunofluorescence assay ( Chlamydia direct IF, BioMérieux, Marcy l’Etoile, France) for samples collected in 2009, or Chlamydiaceae-specific real-time PCR for samples collected in 2010.
DNA-based characterization
C. psittaci-specific real-time PCR
The incA-based real-time PCR assay specific for C. psittaci was conducted as previously described [19].
Amplifications for DNA sequencing
Primers used for the partial amplification of ompA and 16S rRNA genes are listed in Table S1 . PCR was performed in a total volume of 50 µl containing 4 µl DNA template, 5 µl 10X PCR reaction buffer, 2 U Hot start Taq DNA polymerase (Qiagen, Courtaboeuf, France), 400 µM of each deoxynucleotide triphosphate, and 0.5 µM of each flanking primer.
DNA sequencing
PCR-amplified segments of ompA and the 16S rRNA gene were purified using the QIAquick PCR Purification Kit (Qiagen, Courtaboeuf, France). DNA sequencing was performed at MWG Biotech France (Roissy, France).
Nucleotide sequences have been deposited under GenBank nos. HQ662953 (10-1398/28), HQ662954 (10-1398/11), HQ662955 (10-1398/6) for the 16S rRNA gene, and nos. HQ662949 (10-1398/28), HQ662950 (08-1274_Flock21), HQ662951 (10-1398/11), HQ662952 (10-1398/6) for ompA.
ompA and 16S rRNA gene sequence analysis
ompA and 16S rRNA gene sequences determined in this study were combined in an alignment with previously published sequences that were relevant for phylogenetic and epidemiological considerations. Sequence data were analyzed using the Bionumerics software package version 4.6 (Applied-Maths, Saint-Martens-Latem, Belgium) as a character dataset. Cluster analysis was conducted using the categorical parameter and the UPGMA coefficient.
Genome sequence analysis
Parallel pyrosequencing of the 10-1398/6 isolate was performed using a 454 Genome Sequencer FLX instrument with GS FLX Titanium series reagents. 449,422 sequence reads were obtained (mean length=342,9 bp; median length= 97,0 bp; total bases=154,112,763 bp). De novo assembly yielded a draft genome of 20 contigs. Four contigs mapped and were ordered to reference strain C. psittaci 6BC, in order to generate a pseudomolecule spanning 1,146,174 bp. The draft genome was annotated using the University of Maryland Institute for Genome Sciences annotation engine (http://ae.igs.umaryland.edu/cgi/index.cgi). Using this annotated draft sequence, the concatenated sequences of 31 conserved genes (dnaG, frr, infC, nusA, pgk, pyrG, rplA, rplB, rplC, rplD, rplE, rplF, rplK, rplL, rplM, rplN, rplP, rplS, rplT, rpmA, rpoB, rpsB, rpsC, rpsE, rpsI, rpsJ, rpsK, rpsM, rpsS, smpB, and tsf) [20] were assembled and compared with the corresponding gene sequences from all other members of the Chlamydiaceae family. Predicted genes were compared by BLAST against the complete set of genes from other chlamydial genomes using an E-value cutoff of 10−5. Synteny and BLAST Score Ratio (BSR) analyses were performed as previously described [21]. Whole nucleotide sequence of 10-1398/6 has been deposited under GenBank no APJW00000000 (Bioproject PRJNA188464).
Electron microscopy
Vero cells were infected with a homogenate from vitellus membranes previously infected with isolate 10-1398/6. Infected cells were harvested at 48 hours post-infection. After washing, cells were fixed in 2% paraformaldehyde and 2.5% glutaraldehyde, scrapped off the culture plate and enrobed in agarose. Agarose containing infected cells was trimmed into ~1mm3 cubes, post-fixed with 1% osmium tetroxide, washed and en bloc stained with 1% uranyl acetate in water. Specimens were then washed and dehydrated using 30%, 50%, 70%, 90% and 100% ethanol in series, 10 minutes each. This was followed by two more 100% ethanol washes and infiltration with increasing concentrations of Spurr resin (Electron Microscopy Sciences, PA). After two exchanges of pure resin, specimens were embedded in Spurr resin and polymerized at 60°C overnight. Silver colored ultrathin (~70nm) sections were cut and collected using a Leica UC6 ultramicrotome (Leica Microsystems, Inc., Bannockburn, IL), counterstained with uranyl acetate and lead, and examined in a transmission electron microscope (Tecnai T12, FEI) operated at 80 kV. Digital images were acquired using an AMT bottom mount CCD camera and AMT600 software (Advanced Microscopy Techniques, MA).
Results
Detection and isolation of chlamydiae from the African Sacred Ibis, Threskiornis aethiopicus
In the present work, examination of cloacal swabs collected from 70 birds using Chlamydiaceae-specific real-time PCR demonstrated that 11% (8/70) of the apparently healthy birds had chlamydiae in their digestive tract (Table 1 ). When re-tested with a C. psittaci incA-specific real-time PCR, only one of the 8 positive Ibis samples remained positive: sample 10-1398/28. The Ct values indicated different levels of excretion among individual birds, three of which qualified as high excreters (Ct < 30), i.e. 09-468/3, 10-1398/6, 10-1398/28.
Duplicates of the Chlamydiaceae PCR-positive dry swabs, which had been stored in SPG medium, were inoculated into embryonated chicken eggs. Chlamydiae were successfully cultured from 3 samples: 10-1398/6, 10-1398/11 and 10-1398/28 (Table 1 ). Isolation was unsuccessful from sample 09-468/3, although it had a high Ct value.
Molecular characterization of the T . aethiopicus chlamydial isolates
The 16S rRNA and ompA gene sequences were obtained to establish the identity of the 3 chlamydial isolates and to indicate their taxonomic position. The 16S rRNA gene sequences of isolates 10-1398/6 and 10-1398/11 were identical. Alignment with representative sequences of all Chlamydia spp. established the position of these isolates within the family Chlamydiaceae, but outside the existing species (Figure 1 ). Sequence similarity measurements listed in Table S2 confirmed the distinct genetic position of these two isolates. However, the 16S rRNA gene sequence of isolate 10-1398/28 was highly homologous to that of the C. psittaci reference strain 6BC (99.85% similarity) (Table S2 ).
BLAST analysis of the ompA sequences confirmed that isolate 10-1398/28 is closely related to C. psittaci strain GD (genotype C) whereas the 10-1398/6 and 10-1398/11 isolates displayed lower similarity to ompA of other Chlamydia spp. (up to 76% versus C. felis and C. psittaci). This further suggested that these two isolates held a phylogenetic position outside the established chlamydial species. The ompA-based dendrogram in Figure S1 confirms that these two isolates form a separate cluster.
Ultrastructural analysis of inclusions generated upon infection with isolate 10-1398/6
Vero cells infected with isolate 10-1398/6 displayed inclusions at different stages of development similar in ultrastructure to inclusions generated upon infection with C. psittaci [22]. Figure 2 displays two typical inclusions observed at 48 hours post-infection. In the less mature, densely packed inclusion shown in Figure 2A , developmental forms corresponding to elementary bodies (EBs) and reticulate bodies (RBs) were observed in similar numbers. EBs were typically spherical with a dense nucleoid, clear periplasm and thickened cell wall as their C. psittaci counterparts [22]. However, some EBs of isolate 10-1398/6 appeared somewhat larger in diameter than C. psittaci EBs (350-400 nm vs. 300-350 nm [22]). Moreover, the condensed nucleoid appeared lobar or folded (as a “wallet”) in many EBs of isolate 10-1398/6, a distinguishing feature that was not observed in micrographs of C. psittaci EBs prepared under the same conditions (not shown). RBs of isolate 10-1398/6 were larger, typically pleiomorphic, with a cell wall that appeared thinner by TEM than that of EBs, and had a loosely distributed, somewhat granular cytoplasm lacking a condensed nucleoid. In the few inclusions that we observed at this developmental stage, most RBs were associated with or near the inclusion membrane, consistent with the proposed contact-dependent model of chlamydial development [23]. Intermediate bodies that display a smaller condensed nucleoid and a partially cleared cytoplasm were also apparent in small numbers. The more mature inclusion of isolate 10-1398/6 shown in Figure 2B was significantly less packed and contained mostly EBs. Both inclusions also displayed evidence of fusion with cytolosic host vesicles and contained apparent RB ghosts and many smaller vesicles. Finally, the more actively replicating inclusion shown in Figure 2A was selectively associated with mitochondria, particularly in areas of the inclusion membrane that are associated with RBs on the inclusion side. Although this is consistent with the reported preferred association of the C. psittaci inclusion with mitochondria [24], observation of a larger number of inclusions at this developmental stage would be required to establish statistical significance.
Phylogenetic characterization of a new Chlamydia species from T . aethiopicus : Chlamydia ibidis
To further confirm the unique taxonomic position of isolates 10-1398/6 and 10-1398/11, genomic DNA from isolate 10-1398/6 was subjected to whole genome sequencing, assembly and annotation. The draft genome scaffold of the 10-1398/6 isolate consists of a single circular chromosome of 1,146,174 bp, encoding 1,057 predicted coding sequences (%GC content= 38.5%; average gene length= 970 bp; percent coding= 88.5%). 31 highly conserved genes were selected from the draft annotated assembly and aligned against the matching genes from all other members of the Chlamydiaceae family using Amphora, as described elsewhere [20]. Figure 3 displays a maximum-likelihood dendrogram based on these alignments that supports the distinctness of 10-1398/6 from these 9 established chlamydial species. Genome synteny analysis shows that the 10-1398/6 genome is similar to C. psittaci but with several regions of rearrangement (Figure 4 ). BSR analysis of the 10-1398/6 genome compared to six C. psittaci genomes (including 3 avian and 3 mammalian isolates) shows that 231/1057 of the 10-1398/6 genes are unique to that genome and not shared with the other C. psittaci isolates (Table 2 ). Many of these unique genes are found in clusters around the chromosome (Figure 5 ). Comparison of the 10-1398/6 plasticity zone relative to several C. psittaci genomes further highlights the divergence of the 10-1398/6 isolate from C. psittaci, as well as the relationship to the plasticity zone of other members of the old genus Chlamydophila (Figure 6 ).
Table 2. Breakdown of predicted protein orthologs between Chlamydia psittaci isolates and 10-1398/6 based on BSR analysis.
# of orthologs |
|||||
---|---|---|---|---|---|
Species | Host | Core (>0.5) | Variable (<0.5 and >0.4) | Unique (<0.4) | Total |
Chlamydia psittaci 6BC | Bird | 736 | 257 | 13 | 1006 |
Chlamydia psittaci RD1 | Bird | 735 | 215 | 3 | 953 |
Chlamydia psittaci 01DC11 | Pig | 738 | 240 | 0 | 978 |
Chlamydia psittaci 02DC15 | Cattle | 740 | 238 | 1 | 979 |
Chlamydia psittaci 08DC60 | Human | 738 | 240 | 0 | 978 |
Chlamydia psittaci C19/98 | Sheep | 739 | 239 | 0 | 978 |
10-1398/6 | Bird | 802 | 23 | 231 | 1057 |
Discussion
Although the importance of C. psittaci as the causative agent of avian chlamydiosis in psittacine birds and domestic fowl has been known for decades [25], several studies provide recent evidence of the occurrence of other chlamydial species in birds, such as C . abortus [26,27], C . suis and C. muridarum [28] as well as C . pecorum and C. trachomatis [12]. Additionally, new and hitherto non-classified chlamydial agents were recently described in chickens [6,16,29], pigeons [11,12], and sea gulls [10].
Avian chlamydiosis due to C. psittaci is a major concern in the French duck industry where human cases of psittacosis are regularly reported. The means of contamination and dissemination of the infection in duck flocks are poorly understood. As Ibises were repeatedly observed to feed on open-air duck breeding premises [13], investigations were conducted in order to assess the occurrence of chlamydiae in these birds. Examination of cloacal swabs collected from wild Ibises showed that 11% had excreted bacteria belonging to the family Chlamydiaceae (Table 1 ). When re-tested with a C. psittaci-specific real-time PCR, only one of the 8 positive Ibis specimens was positive: specimen 10-1398/28. Successful cultivation of 3 isolates (10-1398/6, 10-1398/11 and 10-1398/28) in chicken eggs allowed for a more complete examination.
Isolate 10-1398/28 was genotyped as C. psittaci by real-time PCR and by 16S rRNA gene sequencing. BLAST analysis of the ompA sequence revealed high homology with ompA of genotype C of C. psittaci. This genotype is commonly associated with waterfowl [30]. Although the dataset presented in this study is small, our results suggest a low prevalence of C. psittaci in the Ibis population, such that it probably does not represent a significant reservoir of the pathogen, nor a high risk for the contact duck flocks. Moreover, the detection of C. psittaci genotype C in one of the specimens suggests that the pathogen may have been transmitted to the Ibis from ducks, where it is relatively abundant.
Interestingly, the analysis of the 16S rRNA gene sequence of the two other Ibis isolates (10-1398/6 and 10-1398/11) suggested that they are members of the family Chlamydiaceae, as the 16S rRNA gene sequence homology family-level cut-off values stand at 90% [31], but suggested also that they correspond to a new and hitherto non-classified chlamydial species. Indeed, the 16S rRNA gene sequence homology between the two atypical isolates and C. psittaci or C . abortus was lower than that between C . abortus and C. psittaci (respectively 97.4% and 97.2% versus 99.6%) (Table S2 ). Phylogenetic analysis of 31 concatenated housekeeping genes from the annotated draft genome of the 10-1398/6 isolate further supports this distinct position (Figure 3 ). Genome synteny analysis shows that the 10-1398/6 genome is very similar to that of C. psittaci but with several regions of rearrangement, and BSR analysis of the 10-1398/6 genome compared with other representative C. psittaci genomes revealed that 20% of the 10-1398/6 genes are unique to that genome and not shared with other C. psittaci isolates. This is unusual in the otherwise highly conserved Chlamydiaceae [32]. Analysis of the plasticity zone, a region of genetic divergence amongst the Chlamydiaceae, revealed a unique organization for 10-1398/6. Thus, we propose that 10-1398/6 and the highly similar 10-1398/11 correspond to a new member species of the Chlamydiaceae, with the proposed name Chlamydia ibidis . Studies of isolate 10-1398/6 by transmission electron microscopy confirmed this assessment. Typical membrane-bound inclusions were observed that contained EBs, RBs and intermediate developmental forms typical of the Chlamydiaceae. A unique distinguishing feature was the apparent lobar structure of the condensed nucleoid in EBs.
The question of the origin of C . ibidis in the Sacred Ibis colony of western France looms large. Two possibilities should be considered. First this new species may correspond to a strain that is endogenous to the local avian population yet has escaped detection to this day, perhaps because of not being sought after actively in the past or with the appropriate probes (most detection attempts usually target C. psittaci-specific genes or antigens). This may also be because this strain is relatively innocuous in avian species, including domesticated birds, or because it is not associated with symptomatic zoonotic infection as are its C. psittaci counterparts. Another tantalizing possibility is that the C . ibidis isolate is native – and perhaps specific - to Ibis birds and that it was brought over with these birds from African countries where native Ibises are prevalent. These various possibilities are now being explored.
Follow-up studies are needed in order to assess potential seasonal changes in the prevalence of Chlamydia among the Ibis population. Although a small data set, the number of infected birds seems to be higher in July 2010 than in March 2009. It is unclear whether this reflects accidental or seasonal changes. Seasonal fluctuation has been reported for pigeons [33,34,12]. Further studies are also needed to fully characterise the virulence properties of C . ibidis , to identify the geographical origin of the infection and its range, and to address the critical question of the health risk to humans or other animals, including poultry and avian wildlife. In the absence of this important information, individuals handling Sacred Ibises should assume that the zoonotic risk is similar to that of C. psittaci, and take appropriate precautionary measures.
Description of Chlamydia ibidis sp. nov.
Chlamydia ibidis (ibidis. L. fem. gen. pl. ibidis, of the Ibis, because this bird is the only host currently known). The strains of this species occur in the Ibis and possibly also in other birds. The agent can be recovered from cloacal swabs and faeces. So far, no evidence of a pathogenic potential has emerged. Like all other species of the Chlamydiaceae, C . ibidis strains can be grown in cell culture and in embryonated chicken eggs. The morphology as revealed by electron microscopy harbors the typical features of Chlamydia spp., i.e. intracellular vacuolar inclusions contain electron-dense elementary bodies of less than 1 µm diameter and the slightly larger and more electron-lucent reticulate bodies. Identification of bacteria of this new species can be obtained based on its 16S rDNA and ompA gene sequences. The type strain is 10-1398/6T.
Supporting Information
Acknowledgments
Sampling of Sacred Ibises was performed collaboratively with different partners (ONIRIS, INRA, ONCFS, National Museum of Natural History) in the context of a project to study biosafety issues linked to the Sacred Ibis in western France upon request from the French Ministry of the Environment. Special thanks are owed to Jennifer Bazus, Denis Lacourpaille and to technicians of ONCFS who conducted the official culling operations and were very helpful with the sampling in the field. We are also grateful to Jean Euzeby for his precious advice.
Funding Statement
Patrik Bavoil was supported by NIH U19 AI084044. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
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