1. bookVolume 69 (2020): Issue 1 (March 2020)
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2544-4646
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04 Mar 1952
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access type Open Access

Low Occurrence of Acinetobacter baumannii in Gulls and Songbirds

Published Online: 12 Mar 2020
Volume & Issue: Volume 69 (2020) - Issue 1 (March 2020)
Page range: 85 - 90
Received: 05 Dec 2019
Accepted: 11 Feb 2020
Journal Details
License
Format
Journal
eISSN
2544-4646
First Published
04 Mar 1952
Publication timeframe
4 times per year
Languages
English
Abstract

Acinetobacter baumannii is a worldwide occurring nosocomial pathogen, the natural habitats of which remain to be defined. Recently, white stork nestlings have been described as a recurring source of A. baumannii. Here, we challenged the hypothesis of a general preference of A. baumannii for avian hosts. Taking advantage of campaigns to ring free-living birds, we collected cloacal swab samples from 741 black-headed gulls (Chroicocephalus ridibundus) in Poland, tracheal and cloacal swabs from 285 songbirds in Poland as well as tracheal swabs from 25 songbirds in Slovenia and screened those for the growth of A. baumannii on CHROMagar™ Acinetobacter. Of the 1,051 samples collected only two yielded A. baumannii isolates. Each carried one variant of the bla OXA-51-like gene, i.e. OXA-71 and OXA-208, which have been described previously in clinical isolates of A. baumannii. In conclusion, our data do not support a general preference of A. baumannii for avian hosts.

Keywords

Introduction

Acinetobacter baumannii is a Gram-negative bacterium, which causes nosocomial infections worldwide. Due to its remarkable capability to develop multidrug resistance, we are running out of treatment options in many parts of the world (Murray et al. 2015). The World Health Organization (WHO), therefore, ranked carbapenem-resistant A. baumannii on the top of a priority list of antibiotic-resistant bacteria for the treatment of which new antibiotics are urgently needed (Tacconelli et al. 2018).

The natural reservoirs of A. baumannii are poorly defined. Many members of the genus Acinetobacter have ubiquitously spread bacteria found in soil, water, and other environmental sites (Afshinnekoo et al. 2015; Al Atrouni et al. 2016) but also as part of the human microbiome (Fyhrquist et al. 2014). A. baumannii has been isolated from different environmental sites and various animals (Eveillard et al. 2013; Rafei et al. 2015; Kittinger et al. 2017; Furlan et al. 2018). DNA-based studies suggest the rates of colonization of human head and body lice of up to around 50%, depending on the population (Kempf et al. 2012). However, an isolate from lice studied in detail was found to be phylogenetically distinct from clinical isolates and exhibited low virulence (Vallenet et al. 2008; Antunes et al. 2011). In a recent study, A. baumannii was isolated from white stork (Ciconia ciconia) nestlings in Poland at an average rate of 25% (Wilharm et al. 2017). Moreover, genome-based analyses revealed a multitude of distinct lineages and identified the relationship of some stork isolates to clinical strains. Given that A. baumannii was also isolated from poultry livestock, hatcheries, and meat (Martin and Jackel 2011; Lupo et al. 2014; Wilharm et al. 2017), we speculated about a general preference of A. baumannii for avian hosts. To challenge this hypothesis, we performed a culture-based screening of different free-living birds, the results of which are presented here.

Experimental
Materials and Methods

Capture and sampling of songbirds in Poland. In total, 285 wild bird individuals were captured in mist nets during their spring and autumn migration 2016 in the Dąbkowice area (West Pomeranian province; Fig. 1). Ornithologists from the Bird Migration Research Station (Gdańsk, Poland) conduct a scientific study about birds’ migration through the Polish Baltic coast under the name “Operation Baltic” every year, in spring and autumn. All captured birds are ringed, measured and assessed by inspection. Thanks to cooperation with ornithologists from the Operation Baltic, we could collect cloacal and tracheal swabs from 145 bird individuals between April 10 and 16 on spring migration, and from 140 individuals between October 9 and 12 on autumn migration. We collected cloacal and tracheal swabs from all captured birds except those not approved by ornithologists based on the assessment of their general condition. Swab samples were immediately taken from birds after their examination, transferred to Amies transport medium (COPAN 110C, Hain Lifescience, Germany), and stored at 4°C until further analysis (sample processing within seven days). The Bird Migration Research Station was granted legal permission for collection by the General Directorate for Environmental Protection (DZP-WG.6401.03.36.2015. kk and DZP-WG.6401.03.98.2016.km) and by the Maritime Office (OW-A-510/87/17/ds).

Fig. 1.

Map of Poland illustrating the sampling places. White square: bird migration research station at Bukowo. White dots: localization of sampled black-headed gull colonies.

Capture and sampling of gull adult birds and nestlings in Poland. Altogether, 741 black-headed gulls (Chroicocephalus ridibundus) from 16 breeding colonies in Poland were captured in 2017 and 2018 (Fig. 1). The number of breeding pairs in individual colonies varied between 100 and 3,000. All individuals were captured between 25 April and 15 June, while brooding or feeding nestlings. Cloacal swabs were collected from 187 individuals in 2017 and 554 individuals in 2018. Adult birds were older than two years and nestlings were between 7 and 21 days old. Ornithological nets, which were set directly on nests were used to capture black-headed gulls. This procedure did not result in any loss of eggs or nestlings. Legal permissions were granted by the General Directorate for Environmental Protection (DZP-WG.6401.03.97.2017.jro and DZP-WG.6401.03.2.2018.jro) and the Ministry of the Environment (DLP-VIII-6713-21/29762/14/RN). Authority permission ID numbers are as follows: P. Indykiewicz – 116/2017 and 120/2018; M. Ledwoń – 194/2017 and 201/2018; P. Minias – 228/2017 and 235/2018, and J. Nowakowski – 245/2017 and 252/2018.

Capture and sampling of birds in Slovenia. The ringing campaign in the framework of EURING took place in Maribor and surroundings between September 18 and December 10, 2013, as previously described (Škraban et al. 2017).

Isolation and identification of A. baumannii . Swab samples were taken from the choana and rectum, respectively, using the COPAN Amies agar gel medium transport swabs (COPAN 110C, Hain Lifescience, Germany) and stored at 4°C until further analysis. CHRO-Magar™ Acinetobacter (CHROMagar, France) agar plates were prepared as described by the manufacturer without the use of the CHROMagar™ MDR supplement. Swab samples were spread on these agar plates and incubated for 24 hours at 37°C. Reddish colonies tentatively identified as A. baumannii were subjected to colony PCR to detect the bla OXA-51-like β-lactamase gene intrinsic to A. baumannii (Turton et al. 2006) and for species identification using partial rpoB sequencing (Nemec et al. 2009). To this end, a loop-full of each colony to test was resuspended in 50 μl of sterile water. Then, the suspension was incubated at 95°C for 5 minutes and centrifuged for 1 minute at 10,000 g, and 1 μl of the supernatant was taken as a DNA template for every 10 μl of PCR reaction. Full sequencing of the amplified bla OXA-51-like gene was accomplished as described (Zander et al. 2012) applying modified Sanger sequencing with BigDye v3.1 and ABI 3500dx genetic analyzer. Partial rpoB sequences of 861 base pairs in length obtained by the modified Sanger sequencing as above were subjected to nucleotide BLAST analysis for taxonomic classification. Finally, isolates with rpoB sequence identity above 98% to the type strain of A. baumannii in combination with the determination of the bla OXA-51-like gene were considered to belong to the species A. baumannii.

Antimicrobial susceptibility testing. Antimicrobial susceptibilities of A. baumannii isolates were investigated by Etest (bioMérieux, Nuertingen, Germany) and by the automated system VITEK 2 (card AST-N248; bioMérieux) with interpretation according to the recommendations of the European Committee on Antimicrobial Susceptibility Testing (EUCAST v10.0).

Results

In the course of a previously published study on the cultivable microbiota from the choana of free-living birds captured in Slovenia between September and December 2013 (Škraban et al. 2017), 25 choana samples were screened for the presence of A. baumannii as previously established for studies on white stork nestlings (Wilharm et al. 2017). None of the samples yielded A. baumannii isolates.

Of the 145 and 140 songbirds captured along the Baltic Sea during spring and autumn, respectively, in 2016, the European robin Erithacus rubecula was the dominating species (n = 210), followed by blackbird Turdus merula (n = 37), and blackcap Sylvia atricapilla (n = 11) (Table I). Choana and cloacal swabs were all found to be negative for A. baumannii.

The number and age of individuals from the songbird species sampled in 2016.

Bird Species na April 2016 nb October 2016 nc
Age Age
im. ad. L im. ad. L
Turdus merula   37     6     1     0     0     7   18   11     1     0   30
Erithacus rubecula 210   94   13     0     1 108   79   23     0     0 102
Sylvia atricapilla   11     7     3     0     0   10     1     0     0     0     1
Emberiza schoeniclus     1     1     0     0     0     1     0     0     0     0     0
Fringilla coelebs     1     1     0     0     0     1     0     0     0     0     0
Cyanistes caeruleus     7     6     0     0     0     6     1     0     0     0     1
Parus major     3     2     0     0     0     2     0     1     0     0     1
Phoenicurus phoenicurus     1     1     0     0     0     1     0     0     0     0     0
Parus spp.     1     0     0     1     0     1     0     0     0     0     0
Emberiza citrinella     2     0     2     0     0     2     0     0     0     0     0
Dendrocopos major     2     1     1     0     0     2     0     0     0     0     0
Phylloscopus trochilus     6     0     0     1     0     1     3     2     0     0     5
Turdus philomelos     3     2     1     0     0     3     0     0     0     0     0
Total 285 121   21     2     1 145 102   37     1     0 140

The cloacal swabs sampled from black-headed gulls in 2017 (n = 187) were all negative for A. baumannii. Among the individuals sampled cloacally in 2018 (n = 554), two were positive for A. baumannii (from breeding colonies Koronowo and Przykona, respectively) (Table II). Sequencing of the bla OXA-51-like gene intrinsic to A. baumannii revealed that the two isolates carried the OXA-71 and OXA-208 variant, respectively, of the class D β-lactamase OXA-51 family. Both isolates were susceptible to meropenem, imipenem colistin, tigecycline, gentamicin, tobramycin, amikacin, ciprofloxacin, and sulfamethoxazole-trimethoprim. Natural intrinsic resistance to chloramphenicol, penicillins (piperacillin, ampicillin), and cephalosporins (cefotaxime, cefoxitin) was observed for both isolates. In addition, eight isolates of the species Acinetobacter pittii were obtained from gull adults (breeding colonies Koronowo and Jankowo).

The number of black-headed gulls (adult birds and nestlings) sampled in 2017 and 2018.

Colony X Coordinate Y Coordinate No. BP No. BS 2017 No. BS 2018 Total
Koronowo 53.3341667 17.965 657 53 70 123
Bydgoszcz – Stary Port 53.1211111 18.09361111 185 16 16
Bydgoszcz – Przemysłowa 53.1186111 18.10527778 170 50 46 96
Skoki Duże 52.6063889 19.78916667 4500–5500 70 70
Jankowo 52.7827778 18.08416667 451 68 57 125
Kościeszki 52.5733333 18.33111111 354 56 56
Borów 52.1202778 19.56 100 21 21
Jeziorsko 51.7372222 18.64916667 100 15 15
Przykona 52.0055556 18.65777778 3000 33 33
Wola Rogozińska 51.9713889 19.455 3000 18 18
Zlaków Kościelny 52.1969444 19.78916667 300 16 16
Jezioro Ryńskie 53.9194444 21.50861111 1900–2500 30 30
Sętal 53.9036111 20.48222222 425–450 30 30
Jezioro Nielbark 53.3613889 19.52777778 3000 30 30
Zbiornik Poraj 50.6411111 19.2313888 1060 22 22
Łężczok 50.1436111 18.2797222 360 21 21
Stawy Zawadka 49.9644444 19.1163888 460 19 19
Total 187 554 741
Discussion

Acinetobacter baumannii has been isolated sporadically from different avian sources in the past (Ahmed et al. 2007; Muller et al. 2010; Zordan et al. 2011; Kempf et al. 2012; Rafei et al. 2015; Klotz et al. 2018). Additional studies providing evidence for the presence of A. baumannii in bird samples include a study on the rectal carriage of Gram-negative bacteria among 89 seabirds in rehabilitation centres in the USA. In this study, A. baumannii was isolated from 10% of birds, including gulls (Steele et al. 2005). However, the taxonomic classification of bacteria in that study was solely based on phenotypic traits, without the DNA-based corroboration. Even higher isolation rates of more than 30% were recently reported from 48 wild birds’ fecal samples collected in Nigeria (Dahiru and Enabulele 2015). Again, we cannot be certain about the taxonomic claim regarding these isolates due to the lack of genetic evidence. A DNA-based study on 73 pigeon droppings revealed the presence of A. baumannii in 5% of the samples from France and Algeria (Morakchi et al. 2017). Moreover, isolation of A. baumannii was reported from poultry hatcheries (Martin and Jackel 2011; Wilharm et al. 2017), poultry meat (Lupo et al. 2014; Carvalheira et al. 2017), and poultry livestock (Lupo et al. 2014). It has recently been demonstrated that 661 white stork nestlings studied in different regions of Poland over a period of four years were colonized at an average rate of 25% (Wilharm et al. 2017). However, systematic studies for the presence of A. baumannii are not available for other free-living birds leaving open the question of whether birds, in general, are favourable hosts for A. baumannii.

Here, for the first time, a large and diverse set of altogether 1,051 free-living birds was selectively screened for the presence of A. baumannii in cloacal samples (overall 1,026 samples) and tracheal samples (overall 310 samples), using the protocol established for studies on white stork nestlings (Wilharm et al. 2017). The extremely low prevalence of 0.3% in black-headed gulls and non-detection in 310 songbirds compared to 25% prevalence in white stork nestlings strongly argues against a general preference of A. baumannii for avian hosts. In line with this conclusion, no A. baumannii was isolated in a study on the aerobic cloacal and pharyngeal bacteria of 167 free-living birds in Germany (Stenkat et al. 2014). However, our study is limited by the opportunistic sampling design, affecting the species range, further causing potential biases due to specific behaviour and seasonality.

The two A. baumannii strains isolated from gulls were susceptible to clinically relevant antibiotics and exhibited only natural resistance to some penicillins, cephalosporins, and chloramphenicol. This is in full agreement with the resistance profiles previously described for the isolates from white stork nestlings (Wilharm et al. 2017). In conclusion, there is no evidence that these strains faced significant anthropogenic selection pressure in the past suggesting that the strains were acquired from natural habitats.

In summary, the data presented here indicate that there is no general association of A. baumannii with wild birds. Given the obvious risk of poultry livestock to serve as a vector for spreading of A. baumannii (Martin and Jackel 2011; Lupo et al. 2014; Wilharm et al. 2017), it is important to study poultry livestock as well as wild populations of chicken, geese, ducks, turkeys and related species globally to assess the risk potential associated with these populations and to complete our ecological understanding of pathogenic Acinetobacter species.

Fig. 1.

Map of Poland illustrating the sampling places. White square: bird migration research station at Bukowo. White dots: localization of sampled black-headed gull colonies.
Map of Poland illustrating the sampling places. White square: bird migration research station at Bukowo. White dots: localization of sampled black-headed gull colonies.

The number and age of individuals from the songbird species sampled in 2016.

Bird Species na April 2016 nb October 2016 nc
Age Age
im. ad. L im. ad. L
Turdus merula   37     6     1     0     0     7   18   11     1     0   30
Erithacus rubecula 210   94   13     0     1 108   79   23     0     0 102
Sylvia atricapilla   11     7     3     0     0   10     1     0     0     0     1
Emberiza schoeniclus     1     1     0     0     0     1     0     0     0     0     0
Fringilla coelebs     1     1     0     0     0     1     0     0     0     0     0
Cyanistes caeruleus     7     6     0     0     0     6     1     0     0     0     1
Parus major     3     2     0     0     0     2     0     1     0     0     1
Phoenicurus phoenicurus     1     1     0     0     0     1     0     0     0     0     0
Parus spp.     1     0     0     1     0     1     0     0     0     0     0
Emberiza citrinella     2     0     2     0     0     2     0     0     0     0     0
Dendrocopos major     2     1     1     0     0     2     0     0     0     0     0
Phylloscopus trochilus     6     0     0     1     0     1     3     2     0     0     5
Turdus philomelos     3     2     1     0     0     3     0     0     0     0     0
Total 285 121   21     2     1 145 102   37     1     0 140

The number of black-headed gulls (adult birds and nestlings) sampled in 2017 and 2018.

Colony X Coordinate Y Coordinate No. BP No. BS 2017 No. BS 2018 Total
Koronowo 53.3341667 17.965 657 53 70 123
Bydgoszcz – Stary Port 53.1211111 18.09361111 185 16 16
Bydgoszcz – Przemysłowa 53.1186111 18.10527778 170 50 46 96
Skoki Duże 52.6063889 19.78916667 4500–5500 70 70
Jankowo 52.7827778 18.08416667 451 68 57 125
Kościeszki 52.5733333 18.33111111 354 56 56
Borów 52.1202778 19.56 100 21 21
Jeziorsko 51.7372222 18.64916667 100 15 15
Przykona 52.0055556 18.65777778 3000 33 33
Wola Rogozińska 51.9713889 19.455 3000 18 18
Zlaków Kościelny 52.1969444 19.78916667 300 16 16
Jezioro Ryńskie 53.9194444 21.50861111 1900–2500 30 30
Sętal 53.9036111 20.48222222 425–450 30 30
Jezioro Nielbark 53.3613889 19.52777778 3000 30 30
Zbiornik Poraj 50.6411111 19.2313888 1060 22 22
Łężczok 50.1436111 18.2797222 360 21 21
Stawy Zawadka 49.9644444 19.1163888 460 19 19
Total 187 554 741

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