Abstract
Occurrence of Salmonella spp. in captive wild animal species in India is largely unknown. The purpose of this study was to determine the occurrence of different Salmonella serotypes, antimicrobial resistance patterns and genotypic relatedness of recovered isolates. A total of 370 samples including faecal (n = 314), feed and water (n = 26) and caretakers stool swabs (n = 30) were collected from 40 different wild animal species in captivity, their caretakers, feed and water in four zoological gardens and wildlife enclosures in India. Salmonellae were isolated using conventional culture methods and tested for antimicrobial susceptibility with the Kirby–Bauer disc diffusion method. Salmonella isolates were serotyped and genotyping was performed using enterobacterial repetitive intergenic consensus (ERIC) PCR and 16S rRNA sequencing. Animal faecal samples were also subjected to direct PCR assay. Salmonella was detected in 10 of 314 (3.1%) faecal samples by isolation and 18 of 314 (5.7%) samples by direct PCR assay; one of 26 (3.8%) feed and water samples and five of 30 (16.7%) caretakers stool swabs by isolation. Salmonella was more commonly isolated in faecal samples from golden pheasants (25%; 2/8) and leopard (10%; 2/20). Salmonella enterica serotypes of known public health significance including S. Typhimurium (37.5%; 6/14), S. Kentucky (28.5%; 4/14) and S. Enteritidis (14.3%; 2/14) were identified. While the majority of the Salmonella isolates were pan-susceptible to the commonly used antibiotics. Seven (43.7%; 7/16) of the isolates were resistant to at least one antibiotic and one isolate each among them exhibited penta and tetra multidrug-resistant types. Three S. Kentucky serotype were identified in a same golden pheasants cage, two from the birds and one from the feed. This serotype was also isolated from its caretaker. Similarly, one isolate each of S. Typhimurium were recovered from ostrich and its caretaker. These isolates were found to be clonally related suggesting that wildlife may serve as reservoir for infections to humans and vice versa. These results emphasise the transmission of Salmonella among hosts via environmental contamination of feces to workers, visitors and other wildlife.
Key words: Antimicrobial resistance, ERIC-PCR, India, Salmonella enterica, wild animals
Introduction
Salmonella is one of the noteworthy foodborne pathogens worldwide. Salmonella is ubiquitous with wide host range due to its capacity to survive in adverse environments. Most of the studies on public health implications of Salmonella in wildlife have an emphasis on amphibians and reptiles [1, 2]. The role of captive and free-range wildlife mammals and associated caretakers in the epidemiology of Salmonella is a domain that has rarely been investigated. Various serovars of public health significance including serovar Typhimurium and Newport and antimicrobial resistant strains have been reported from turtle, deer, wild birds and water samples [3–5]. Clonally related isolates of different serovars of public health significance in captive wild mammals and associated environments were recently reported in the USA [6]. Very limited studies have reported the same occurrence of Salmonella serovars from humans and wildlife species, supporting that wild animals serve as reservoirs for salmonellosis in humans [7, 8]. Another serious concern in Salmonella is the growing antimicrobial resistance and the dissemination of multidrug-resistant (MDR) strains. Enterobacterial repetitive intergenic consensus (ERIC) fingerprinting is effective than pulsed-field gel electrophoresis (PFGE) and it is useful for subtyping Salmonella serovars, where similar PFGE patterns occur [9]. ERIC-PCR was found effective over many other molecular typing methods [10, 11]. Besides, ERIC-PCR is a simple and cost-effective technique than PFGE. The aim of this study was to determine the occurrence, serovar distribution, antimicrobial susceptibility patterns and genotypic relatedness of Salmonella isolates recovered from faecal samples of captive wildlife, their caretakers, feed and water in India.
Materials and methods
The study was carried out in four zoological gardens and wildlife enclosures, viz., Nainital Zoo, Nainital, Uttarakhand; Kanpur Zoo, Kanpur, Uttar Pradesh; Deer Park, Indian Veterinary Research Institute, Izatnagar, Bareilly, Uttar Pradesh; Post Graduate Research Institute in Animal Sciences, Chennai, Tamilnadu, India. A total of 370 samples comprising 314 fresh faecal samples of apparently healthy captive animals (40 species) (Tables 1–3), 30 stool swabs from animal caretakers and 26 feed and water samples were collected. Briefly, 10 g samples were pre-enriched in 2% buffered peptone water (BPW) (HiMedia, India), at 37 °C for 16–18 h. The broth culture (100 µl) was transferred to 10 ml Tetrathionate Broth (HiMedia) and incubated at 37 °C for 24 h. A loopful of the suspension was streaked onto Hektoen Enteric Agar (HEA) (HiMedia) and incubated at 37 °C for 24 h [12]. Selected presumptive Salmonella colonies were inoculated onto triple sugar iron (TSI) agar (HiMedia) and Christensen's urea slants (HiMedia) and incubated at 37 °C for 24 h. All presumptive Salmonella isolates were submitted to the National Salmonella Centre (ICAR-IVRI, Bareilly, India) for serotyping. Genomic DNA was isolated directly from 314 faecal samples of captive wildlife by QIAamp DNA Stool Mini Kit (Qiagen, Germany). The extracted DNA was subjected to PCR as described by Lin and Tsen, [13]. Pearson's chi-square and Fisher exact test were employed to compare the prevalence of Salmonella spp. among different zoos and various sample groups viz., wild ruminants, wild non-ruminants, wild birds, caretakers, feed and water (SPSS 22.0 version). The differences among various zoos and sample groups were considered significant at P < 0.05. The antimicrobial resistance profiles of Salmonella enterica isolates were tested to a panel of 23 different antibiotics (BD Diagnostics, Sparks, MD, USA) belonging to 10 classes using the Kirby–Bauer disc diffusion method. The antibiotic used were aminoglycosides-streptomycin (S, 10 µg), gentamicin (Gm, 10 µg), kanamycin (K, 30 µg), amikacin (Ak, 30 µg); colistin (Cl, 10 µg); cephalosporins- cefotaxime (Ctx, 30 µg), ceftazidime (Caz, 30 µg), ceftazidime + clavulanic acid (30/10 µg) and cefotaxime + clavulanic acid (30/10 µg); macrolides-erythromycin (E, 15 µg); fluoroquinolones-enrofloxacin (Ex, 10 µg), ciprofloxacin (Cip, 5 µg), ofloxacin (Of, 5 µg); monobactam-aztreonam (Atm, 30 µg); carbapenem antibiotics-imipenem (Ipm, 10 µg), meropenem (Mem, 10 µg), ertapenem (Etp, 10 µg); penicillins-carbenicillin (Cb, 100 µg), amoxicillin with clavulanic acid (Amc, 10 µg), ampicillin (Am, 10 µg); tetracycline (Te, 30 µg); sulphonamides (sulphamethoxazole with trimethoprim (Sxt, 10 µg)) and others-nitrofurantoin (F/M, 100 µg). Isolates showing resistance to three or more classes of antimicrobials were classified as MDR. Multiple antibiotic resistance index (MARI) for each resistance pattern was calculated.
Table 1.
Prevalence of Salmonella spp. in faecal samples collected from captive wild ruminants
| Captive wild ruminants | No. of samples | Isolation (prevalence %) | Direct PCR (prevalence %) | |
|---|---|---|---|---|
| Common name | Scientific name | |||
| Sambar deer | Rusa unicolor | 5 | – | – |
| Himalayan goral | Naemorhedus goral | 8 | – | – |
| Barking deer | Muntiacus muntjak | 5 | – | – |
| Thamin or Eld's deer | Panolia eldii | 10 | – | – |
| Swamp deer or Barasingha | Cervus duvaucelii | 15 | 1 (6.7) | 2 (13.3) |
| Nilgai or bluebull | Boselaphus tragocamelus | 12 | – | – |
| Spotted deer or Chital | Axis axis | 32 | – | – |
| Blackbuck | Antilope cervicapra | 17 | – | – |
| Indian hog deer | Hyelaphus porcinus | 15 | – | – |
| Sika deer or Japanese deer | Cervus nippon | 3 | – | – |
| Chousingha deer | Tetracerus quadricornis | 2 | – | – |
| Himalayan blue sheep | Pseudois nayaur | 2 | – | – |
| Total | 126 | 1 (0.8) | 2 (1.6) | |
Table 2.
Prevalence of Salmonella spp. in faecal samples collected from captive wild non-ruminants
| Captive wild non-ruminants | No. of samples | Isolation (Prevalence%) | Direct PCR (Prevalence %) | |
|---|---|---|---|---|
| Common name | Scientific name | |||
| Leopard | Panthera pardus | 20 | 2 (10) | 3 (15) |
| Bengal tiger (inc. one white) | Panthera tigris tigris | 9 | – | – |
| Hyena (striped) | Hyaena hyaena | 10 | 1 (10) | 1 (10) |
| Tibetian wolf | Canis lupus chanco | 2 | – | – |
| Jackal | Canis aureus | 5 | – | – |
| Himalayan black bear | Ursus thibetanus laniger | 7 | – | 2 (28.6) |
| Sloth bear | Melursus ursinus | 2 | – | – |
| Hippopotamus | Hippopotamus amphibious | 6 | – | – |
| Indian rhinoceros | Rhinoceros unicornis | 3 | – | – |
| Gray langur | Semnopithecus entellus | 5 | 1 (20) | 1 (20) |
| Bonnet macaque | Macaca radiate | 5 | – | – |
| Rhesus macaque | Macaca mulatta | 3 | – | – |
| Japanese macaque | Macaca fuscata | 2 | – | – |
| Palm civet | Paradoxurus hermaphrodites | 3 | – | 1 (33.3) |
| Red panda | Ailurus fulgens | 2 | – | – |
| Leopard cat | Prionailurus bengalensis | 1 | – | – |
| Zebra | Equus quagga | 1 | – | – |
| Total | 86 | 4 (4.6) | 8 (9.3) | |
Table 3.
Prevalence of Salmonella spp. in faecal samples collected from captive wild birds
| Captive wild birds | No. of samples | Isolation (prevalence %) | Direct PCR (prevalence %) | |
|---|---|---|---|---|
| Common name | Scientific name | |||
| Golden pheasant | Chrysolophus pictus | 8 | 2 (25) | 2 (25) |
| Silver pheasant | Lophura nycthemera | 8 | – | – |
| Cockatiel | Nymphicus hollandicus | 6 | – | – |
| Lady Amherst pheasant | Chrysolophus amhersitae | 12 | 1 (8.3) | 1 (8.3) |
| Kalij pheasant | Lophura leucomelanos | 8 | – | – |
| Sun conure | Aratinga solstitialis | 6 | – | – |
| Red jungle fowl | Gallus gallus | 2 | – | – |
| Indian peafowl | Pavo cristatus | 4 | – | – |
| White peafowl | Pavo cristatus mut. Alba | 3 | 1 (33.3) | 1 (33.3) |
| Saras crane | Grus antigone | 5 | – | – |
| Emu | Dromaius novaehollandiae | 5 | – | – |
| Ostrich | Struthio camelus | 35 | 1 (2.8) | 4 (11.4) |
| Total | 102 | 5 (4.9) | 8 (7.8) | |
The ERIC-PCR assay was performed as per Campioni et al. [14]. The oligonucleotide primers described in a previous study was used [15]. The PCR reaction mixture for amplification consisted of 12.5 µl of 2× PCR master mixtures (ThermoFisher Scientific), 1 µl (10 pmol/μl) of each primer (Eurofins, India), 2 µl of DNA template and nuclease-free water to make final volume up to 25 µl. The program used for the ERIC-PCR are as follows: initial denaturation at 94 °C for 7 min followed by 30 cycles each of denaturation at 94 °C for 30 s, annealing at 52 °C for 1 min and extension at 65 °C for 8 min followed by final extension at 65 °C for 10 min. The PCR was performed in a Thermal Cycler (Eppendorf, Germany). The ERIC-PCR reaction was repeated at least twice for each isolate to verify the reproducibility of the assay. The 16S rRNA gene of the recovered isolates was amplified employing primers of a previous study [16] and sequenced by Sanger dideoxy method using commercial sequencing services (Eurofins Ltd., Bangalore, India). The PCR reaction mixture for amplification consisted of 12.5 µl of 2× PCR master mixtures (ThermoFisher Scientific), 1 µl (10 pmol/μl) of each primer (Eurofins, India), 2 µl of DNA template and nuclease-free water to make final volume up to 25 µl. The cycling conditions for PCR consisted of 5 min initial denaturation at 95 °C followed by 35 cycles each of 1 min denaturation at 94 °C, 30 s annealing at 63 °C and 45 s extension at 72 °C and a final extension step of 5 min at 72 °C. The nucleotide sequences were deposited in GenBank using the National Centre for Biotechnology Information (NCBI, Bethesda, MD) Bankit submission tool http://www3.ncbi.nlm.nih.gov.
Results
Salmonella was detected in 10 of 314 (3.1%) wildlife faecal samples by isolation and 18 of 314 (5.7%) by direct PCR assay; one of 26 (3.8%) feed and water samples and five of 30 (16.7%) caretakers stool swabs. Salmonella was more commonly isolated in faecal samples from golden pheasants (25%; 2/8) and leopard (10%; 2/20). The occurrence of Salmonella in different species is presented in Tables 1–3. Out of 10 isolates from wildlife faecal samples 1 isolate (0.8%) was from captive wild ruminants (n = 126), four isolates (4.6%) were from captive wild non-ruminants (n = 86), five isolates (4.9%) were from captive wild birds (n = 102). Prevalence of Salmonella was further analysed as per the sample group and zoo (Tables 4 and 5). Prevalence of Salmonella spp. among different sample group and different zoos were statistically significant (P < 0.05). By serotyping, 6/16 isolates (37.5%) were found to be S. Typhimurium, four isolates (28.5%) were recognised as S. Kentucky, two isolates (14.3%) were identified as S. Enteritidis, two isolates (14.3%) were untypable, and one each isolate (6.2%) were S. Senftenberg and S. Lamberhurst (Table 6).
Table 4.
Distribution of Salmonella spp. among the different sample groups
| Group | No. of samples screened | No. positive (%) |
|---|---|---|
| Captive wild ruminants | 126 | 1 (0.8%) |
| Captive wild non-ruminants | 86 | 4 (4.6%) |
| Captive wild birds | 102 | 5 (4.9%) |
| Care takers | 30 | 5 (16.7%) |
| Food and water | 26 | 1 (3.8%) |
| Total | 370 | 16 (4.3%) |
| Pearson χ2 value | 14.961 | |
| Fishers exact test value | 12.422 | |
| Asymp. Sig (two-sided) P value | 0.005 | |
| Fishers exact test P value | 0.007 | |
Table 5.
Distribution of Salmonella spp. among different zoos/enclosures
| Zoo/Enclosures | No. of samples screened | No. positive (%) |
|---|---|---|
| Nainital zoo | 118 | 10 (8.5%) |
| Kanpur zoo | 167 | 4 (2.4%) |
| IVRI deer park | 41 | 0 |
| PGRIAS ostrich enclosure | 44 | 2 (4.5%) |
| Total | 370 | 16 (4.3%) |
| Pearson χ2 value | 8.273 | |
| Fishers exact test value | 7.158 | |
| Asymp. Sig (two-sided) P value | 0.041 | |
| Fishers exact test P value | 0.036 | |
Table 6.
Characterisation of Salmonella isolated from this study
| Sl. no | Isolate name | Source | Location | Serotype | Resistance profile | MARI | ERIC cluster | GenBank Accession no. |
|---|---|---|---|---|---|---|---|---|
| 1 | NLA1 | Grey langur | Nainital zoo | Enteritidis | F/MSxt | 0.08 | A2 | KT026973.1 |
| 2 | NL5 | Leopard | Nainital zoo | Typhimurium | Pan-susceptible | 0 | B1 | KT026980.1 |
| 3 | NWP1 | White peafowl | Nainital zoo | Senftenberg | Pan-susceptible | 0 | A2 | KT026979.1 |
| 4 | NLAP12 | Lady amherest pheasant | Nainital zoo | Typhimurium | F/M | 0.04 | B1 | KT026982.1 |
| 5 | NGP3 | Golden pheasant | Nainital zoo | Kentucky | Pan-susceptible | 0 | B2 | KT026975.1 |
| 6 | NGP8 | Golden pheasant | Nainital zoo | Kentucky | Pan-susceptible | 0 | B2 | KT026976.1 |
| 7 | NF6 | Feed (leftover from cage) | Nainital zoo | Kentucky | Pan-susceptible | 0 | B2 | KT026974.1 |
| 8 | NCT11 | Care taker | Nainital zoo | Kentucky | Te | 0.04 | B2 | KT026978.1 |
| 9 | NCT8 | Care taker | Nainital zoo | Typhimurium | AmcAmp | 0.08 | B1 | KT026977.1 |
| 10 | NCT9 | Care taker | Nainital zoo | Typhimurium | AmpSxt | 0.08 | B1 | KT026981.1 |
| 11 | KSWD12 | Swamp deer | Kanpur zoo | Lamberhurst | Pan-susceptible | 0 | A2 | KT026985.1 |
| 12 | KHY1 | Hyena | Kanpur zoo | Untypable | Pan-susceptible | 0 | B1 | KT026984.1 |
| 13 | KL2 | Leopard | Kanpur zoo | Untypable | Pan-susceptible | 0 | B1 | KT026986.1 |
| 14 | KCT3 | Caretaker | Kanpur zoo | Enteritidis | CtxCaz | 0.08 | A2 | KT026983.1 |
| 15 | PGRIASO24 | Ostrich | PGRIAS, Chennai | Typhimurium | AtmCbCtxCaz | 0.17 | A1 | KT026988.1 |
| 16 | PGRIASCT1 | Caretaker | PGRIAS, Chennai | Typhimurium | AtmCbCtxCazAmc | 0.21 | A1 | KT026987.1 |
We found antimicrobial resistance among the isolates at varied frequencies. The highest frequency of resistance was found against cefotaxime (3; 18.7%) and ceftazidime (3; 18.7%), followed by carbenicillin (2; 12.5%), aztreonam (2; 12.5%), amoxiclav (2; 12.5%), sulphamethoxazole with trimethoprim (2; 12.5%), nitrofurantoin (2; 12.5%), ampicillin (2; 12.5%) and tetracycline (1; 6.2%). No resistance was found against streptomycin, gentamicin, kanamycin, amikacin, colistin, ceftazidime + clavulanic acid, cefotaxime + clavulanic acid, erythromycin, enrofloxacin, ciprofloxacin, ofloxacin, meropenem, imipenem, ertapenem. The overall multidrug resistance was low (2/16; 12.5%). Seven (7/16; 43.7%) of the isolates were resistant to one antibiotic and one isolate each exhibited penta and tetra resistance MDR with AtmCbCtxCazAmc and AtmCbCtxCaz R-types, respectively. It should be noted that these two isolates belonged to serovar Typhimurium and were recovered from the ostrich and its caretaker. Eight of the isolates (50%) were pan-susceptible to the panel of 23 antimicrobials included in this study. These isolates belonged to Kentucky (n = 3), Typhimurium (n = 1), Senftenberg (n = 1), Lamberhurst (n = 1) and Untypable serovars (n = 2). MARI among the isolates ranged from 0 to 0.21. Resistance patterns and MARI of the Salmonella serovars are shown in Table 6.
The ERIC PCR typing of 16 S. enterica isolates to determine the genetic diversity and phylogenetic relationship among the strains yielded amplified fragments of size ranging from 150 to 2500 bp and were distributed in two clusters (A & B) with two subclusters each with a Simpson's discriminative index of 0.867 (Fig. 1). Six and ten isolates were grouped in clusters A and B, respectively. Four S. Kentucky isolates from two golden pheasants, feed and its caretaker of Nainital zoo grouped into the same subcluster B2 of cluster B. Similarly S. Typhimurium isolates from ostrich and its caretaker of Chennai grouped into same subcluster A1 of cluster A. Two untypable Salmonella isolates from a hyena and leopard of Kanpur zoo grouped with a S. Typhimurium isolate from a leopard of Nainital zoo in a same subcluster B1 of cluster B. Three S. Typhimurium isolates from two caretakers and a lady Amherest pheasant of Nainital zoo grouped in a same subcluster B1 of cluster B. S. Enteritidis from grey langur and S. Senftenberg from white peafowl of Nainital zoo grouped in a subcluster A2 of cluster A. Similarly S. Enteritidis isolated from caretaker of Kanpur zoo grouped with S. Lamberhurst isolated from swamp deer of Kanpur zoo in a subcluster A2 of cluster A. These results coincided with the 16S rRNA gene sequences submitted in GenBank and the accession numbers are indicated in Table 6.
Fig. 1.
Dendrogram representing genetic relationships among Salmonella strains based on ERIC-PCR fingerprints.
Discussion
The present study documents the occurrence of Salmonella among captive wildlife in India for the first time and indicates the importance of captive wildlife as potential sources of human infections through occupational or other direct or indirect contact with wild animals. In this study, the prevalence varied among the host species (Tables 1–3). The number of tested animals is low for several species, because of the lesser exhibits kept in a zoo. This is the first report regarding the prevalence of Salmonella in healthy captive wild animals in India except for few case reports [17–19]. Previous studies from other countries like the USA have shown that free-range wildlife species such as wild pig, deer, opossum, coyote, crow, elk, etc. could be the main source of S. enterica contamination to water, cattle, pre-harvest lettuce and spinach [3]. To the best of our knowledge and based on available literature, isolation of Salmonella from swamp deer, lady Amherst pheasant and white peafowl appears to be for the first time in the world.
In previous studies Salmonella was isolated from grey langur [20], hyena [21], leopard [22], golden pheasants [23] and ostrich [24]. The isolation rate of Salmonella from the feces of all captive wildlife was 3.1% and by direct PCR assay, detection rate was found to be 5.7%. Direct PCR detection of Salmonella from feces has been reported in many previous studies [25–28]. Our results were in accordance with the previous studies where PCR was found more sensitive than the culture methods. Rychlik et al. [29] reported that the sensitivity of the culture method may be lower than that of DNA-based detection assays because of the inability of culture to detect sublethally injured or viable non-culturable cells. The predominant serovars identified in this study were Typhimurium and Kentucky. Both of these serovars were identified earlier from human infections in India [30]. Two Typhimurium strains isolated in this study were MDR with penta and tetra-type resistant patterns suggesting the significance of this serovar in animal and public health. MDR S. Typhimurium which is associated with invasive infections and mortality in humans has previously been reported from human, domestic and wild animals [31, 32]. In our study, majority of the isolates were pan-susceptible, which is found to be in accordance with a previous study on wildlife [6] and is probably linked to less usage of antibiotics in zoos compared with animal farms. It is clear from our study, prevalence of animal faecal carriers are low. The route of Salmonella transmission are multifaceted and our findings suggest that environmental contamination through indirect sources such as infected animal or human faeces and feed could play important roles. Nevertheless direct transmission of Salmonella from captive wildlife to visitors or caretakers is rare. Genotyping of isolates in the current study showed that most of the Salmonella isolates within serovar are clonally related (Fig. 1). Interestingly, clonally related isolates detected in both animals and caretakers suggest the role of wildlife in transmission, even if it is difficult to determine its direction. In addition, the presence of clonally related isolates in different species of captive wild animals from the same zoo shows that the spread could be due to fomites including caretakers, visitors, vehicles, other implements and other animal species, such as rodents and wild birds. Further we suggest intensive longitudinal studies which may also shed light on various risk factors involved. In conclusion, our study suggests that captive wildlife is asymptomatic carriers of Salmonella. The point to be noted is prevalence of shedding in animals was low. The occurrence of Salmonella and different serovars in captive wildlife species and resistance of some isolates are of public health concern. Understanding the epidemiology and transmission pattern of Salmonella between captive wildlife and caretakers could help to prevent and control the introduction and spread of infections among people.
Acknowledgements
We would like to express our gratitude to ICAR for funding the project, Outreach Programme on Zoonoses.
Ethical standards
Not required.
Conflict of interest
None.
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