1. Introduction
Well before the discovery of antibiotics and their development to treat infectious diseases, antimicrobial resistance had naturally developed due to the presence of environmental microorganisms, which are able to synthetize natural antibiotics [
1]. However, during the past several decades, the selection and spread of multidrug-resistant bacteria have been accelerated by the extensive and frequently inappropriate use of antibiotics in human medicine, veterinary care, and agriculture [
2,
3,
4,
5].
The most effective means of combating bacterial infections is represented by antibiotics. Presently, The World Health Organization (WHO) has recognized antimicrobial resistance (AMR) as one of the top ten emerging risks of the twenty-first century, making it one of the greatest threats to global public health [
2]. Furthermore, the “One Health” (OH) research has acknowledged the link between humans, animals, and the environment, emphasizing how AMR affects all three groups collectively [
6,
7].
Although most wildlife species inhabit environments distant from human activity, certain species, such as the red fox, have successfully adapted to peri-urban and urban areas, where they coexist with humans and domestic animals. Unlike livestock or companion animals, wildlife is generally not subjected to direct antimicrobial selection pressure through therapeutic use, except in rare circumstances. Consequently, the detection of antimicrobial-resistant bacteria in wildlife is largely attributed to indirect exposure pathways, including interactions with humans and domestic animals and environmental contamination by anthropogenic waste [
7,
8,
9,
10,
11].
In this context, an increasing number of studies recognize wildlife as an important reservoir of antimicrobial-resistant (AMR) zoonotic pathogens. Both phenotypic and genotypic resistance have been documented in bacterial species of major clinical relevance, such as
Escherichia coli,
Salmonella spp., methicillin-resistant
Staphylococcus aureus (MRSA),
Listeria spp., and
Enterococcus spp., within wild animal populations, indicating that antimicrobial resistance is no longer confined to human and domestic animal environments [
9,
12,
13,
14]. Despite substantial advances in AMR surveillance in humans and livestock, comparable data from wildlife species remain limited, underscoring a significant knowledge gap [
15,
16].
The red fox (
Vulpes vulpes), the most widely distributed species of wild canid in Europe, represents a particularly suitable model for addressing this gap [
3]. With its diverse diet and extensive mobility, it constitutes a significant ecological vector capable of acquiring and transmitting antimicrobial-resistant (AMR) bacteria across habitats. Evidence shows that foxes can acquire AMR bacteria and antibiotic residues from contaminated soil, food, and waste in human-dominated environments, establishing a bidirectional flow of resistance [
1,
17]. Their growing proximity to rural and urban areas increases the likelihood of direct and indirect contact with humans and domestic animals. Consequently, the red fox has been proposed as a sentinel species highly effective for monitoring the dissemination of AMR bacteria in wildlife ecosystems. This is supported by studies which report the fox’s capacity to carry significant bacterial pathogens. For foodborne agents like
Salmonella spp.,
Listeria monocytogenes, and Shiga toxin-producing
E. coli (STEC), foxes primarily serve as environmental sentinels, indicating ecosystem contamination. However, for antimicrobial-resistant bacteria critical in healthcare settings, such as Extended-Spectrum Beta-Lactamase (ESBL)-producing
E. coli, MRSA, and vancomycin-resistant
Enterococcus faecium (VRE), foxes can act as active vehicles for dissemination [
4,
7,
15,
18,
19,
20,
21].
Although adult red foxes often maintain relatively stable home ranges, their adaptability and occasional extra-territorial movements, particularly during dispersal, enable interactions between anthropogenic and natural habitats, which may facilitate the dissemination and persistence of bacteria, including antimicrobial-resistant strains, across ecosystem boundaries. In order to fully comprehend the complex relationship between environmental, animal, and human health, and to develop resulting strategies to control further contamination, it is mandatory for us to place these findings into the One Health concept [
15,
22,
23,
24,
25].
In this context, acquiring new data regarding the fight against one of the most important global threats has become essential for both human and veterinary medicine, as antimicrobial resistance is a persistently expanding issue.
In this context, the aim of the study was to examine populations of red fox in western Romania, in order to evaluate the levels of phenotypic antimicrobial resistance in multiple species of Gram-negative and Gram-positive bacteria, based on samples isolated from the oral cavities and rectums of Vulpes vulpes individuals of different ages and sex, hunted from multiple hunting grounds.
3. Discussion
The present study investigated phenotypic AMR in bacterial isolates obtained between 2022 and 2024 from red foxes (n = 108) across sixteen hunting grounds in western Romania. Samples were collected post mortem from animals that had died due to hunting-related gunshot wounds [
28,
29]. The aim was to evaluate the role of red foxes as potential sentinels for monitoring AMR dynamics in ecosystems shaped by interactions between humans, domestic animals, and wildlife.
The red fox (
Vulpes vulpes) has been increasingly recognized as a valuable One Health sentinel for AMR surveillance because of its wide geographic distribution, opportunistic feeding habits, and adaptability to both rural and urban environments [
30]. By exploiting diverse food sources, foxes are regularly exposed to microbial reservoirs such as small mammals and birds, as well as to anthropogenic contamination originating from human activity, agriculture, and pharmaceutical waste [
31,
32]. This ecological positioning at the interface of natural and human-modified habitats makes them particularly suitable for tracking the circulation of AMR across wildlife, domestic animals, and humans [
33,
34,
35,
36].
Interpretation of antimicrobial resistance prevalence was based on resistant (R) isolates only, with “Susceptible, Increased Exposure” (I) categories treated as susceptible, in accordance with current EUCAST definitions. This approach avoids overestimation of resistance at the population level, which is particularly relevant in wildlife surveillance studies, in which antimicrobial exposure is indirect.
Out of the 137 strains, a subset of isolates initially tested by Kirby–Bauer Disk-Diffusion was selected for Vitek 2 analysis. This subset included isolates initially classified as MDR, i.e., those resistant to at least two antibiotic classes, as well as isolates representing species for which limited data exist in the wildlife studies (e.g., Proteus spp., Shigella sonnei).
The comparison between disk diffusion (DD) and the Vitek 2 system revealed an overall high level of agreement for antimicrobial susceptibility testing in both Gram-negative and Gram-positive isolates, supporting the reliability of DD as a routine screening method. For Gram-negative bacteria, the absence of statistically significant differences for most antibiotics suggests a strong concordance between the two methods, which is consistent with previous reports showing good categorical agreement between disk diffusion and MIC-based automated systems for many drug–organism combinations [
37,
38]. The significant discordance observed for third-generation cephalosporins, however, highlights a known limitation of disk diffusion, as beta-lactam antibiotics, particularly cephalosporins, are more prone to methodological discrepancies due to borderline MIC values and complex resistance mechanisms such as ESBL production [
37,
39]. This finding underscores the importance of confirmatory MIC-based testing when resistance to critical antibiotic classes is suspected.
For Gram-positive isolates, complete concordance between DD and Vitek 2 across all tested antibiotics further supports the robustness of disk diffusion for these organisms. Although oxacillin and cefoxitin showed relatively higher discordance, the lack of statistical significance suggests that these differences were limited and unlikely to affect overall clinical interpretation. The perfect agreement observed for chloramphenicol reinforces the consistency of susceptibility categorization for antibiotics with well-defined breakpoints. Taken together, these results align with works in the existing literature indicating that while disk diffusion generally provides results comparable to MIC-based methods, discrepancies may arise for specific antibiotics or resistance phenotypes, emphasizing the complementary role of automated systems in antimicrobial resistance surveillance and clinical decision-making [
37].
Although no statistically significant association was observed between area of isolation and antimicrobial susceptibility for either Gram-positive or Gram-negative isolates, descriptive differences in resistance frequencies were evident between peri-urban and peri-rural settings. These trends, such as higher resistance to aminoglycosides and cefoxitin among peri-urban Gram-negative isolates and increased resistance to several antibiotics (cefoxitin, cefalexin, imipenem, and ciprofloxacin) among peri-rural Gram-positive strains, may reflect local antibiotic usage practices or environmental exposures that were not sufficient to produce statistically detectable differences [
32]. Additionally, the lack of consistent differences between peri-urban and peri-rural isolates could indicate shared environmental exposures. Given that the investigated hunting grounds are connected by common river systems and water sources, such connectivity may contribute to similarities in bacterial communities and resistance profiles [
32,
40]; however, this interpretation remains speculative in the absence of environmental sampling.
Both peri-urban and peri-rural hunting grounds, which are more anthropogenically influenced (e.g., Buziaș, Moșnița, Oloșag, Boldur, Sacoșul Mare, Nădrag, Surduc, Făget, Traian Vuia, and Margina), harbored bacteria with a broader diversity of antimicrobial resistance (AMR) phenotypes and a higher frequency of multidrug resistance (MDR). In these locations, Escherichia coli isolates commonly displayed resistance to beta-lactams, including third-generation cephalosporins such as ceftazidime, as well as to aminoglycosides, and, in certain groups, carbapenems (imipenem). Fluoroquinolone resistance was also sporadically detected. Methicillin-resistant staphylococci were also identified in samples from the same hunting grounds. By contrast, isolates from forest-dominated areas with limited human or agricultural pressure (e.g., Silvaș, Zeicani, and Crocna-Zimbru) generally retained high susceptibility to chloramphenicol, nitrofurantoin, and trimethoprim–sulfamethoxazole.
Additionally, the lack of consistent differences between peri-urban and peri-rural isolates may reflect shared environmental exposures, as the investigated hunting grounds are connected by common river systems and water sources, which could contribute to a homogenization of bacterial communities and antimicrobial resistance determinants [
30,
37].
Comparable trends have been reported in other European countries. Studies from Denmark, Poland, Norway, the United Kingdom, and Portugal demonstrated that foxes living near rural settlements or livestock facilities carried higher AMR rates and frequent MDR profiles, including methicillin-resistant staphylococci and
E. coli resistant to beta-lactams (e.g., cefotaxime, ampicillin) and tetracycline, whereas isolates from remote forested habitats remained largely susceptible [
7,
11,
23,
41,
42,
43]. Together, these findings support the hypothesis that red foxes act as ecological bridges facilitating the transfer and maintenance of antimicrobial resistance between anthropogenically influenced environments and natural ecosystems [
44,
45].
Within the Romanian dataset, Gram-negative bacteria expressed a higher overall resistance to ceftazidime, followed by amikacin, ciprofloxacin, amoxicillin, gentamicin, ampicillin, and imipenem, with particularly elevated resistance observed in
E. coli and
Salmonella isolates. Resistance in
E. coli was frequent for ceftazidime (up to 67%), ciprofloxacin (up to 56%), imipenem (up to 44%), tetracycline (up to 33%), gentamicin (up to 40%), and ampicillin (up to 56%), whereas trimethoprim–sulfamethoxazole, nitrofurantoin, and chloramphenicol remained mostly effective (67–100%). Similar high-risk profiles have been documented in Poland, Portugal, Ireland and Norway, where foxes carried extended-spectrum beta-lactamase (ESBL)-producing
E. coli [
7,
41,
42,
43,
46,
47].
At the species level,
E. coli isolates showed consistently elevated resistance to ceftazidime, with resistance rates ranging from approximately 40–50% in peri-rural hunting grounds to up to 50% in peri-urban areas, while susceptibility to trimethoprim–sulfamethoxazole and nitrofurantoin remained uniformly high (89–100%) across all sites. Furthermore, in the peri-rural Nădrag and Surduc hunting grounds,
E. coli isolates displayed the highest resistance levels recorded in this study, with resistance rates of 67% to ceftazidime and amoxicillin, 56% to ampicillin and ciprofloxacin, and 44% to cephalexin, imipenem, and amikacin. The Surduc area encompasses an artificial lake that supports recreational activities, seasonal tourism, and the presence of campgrounds, vacation homes, and rental properties, with direct discharge of untreated wastewater into the lake, all of which may contribute to elevated anthropogenic pressure on the local environment. Although no environmental samples were analyzed and no direct assessment of water contamination was performed, previous studies have shown that waste waters, and even natural waters, can act as reservoirs for antimicrobial-resistant bacteria [
7,
48,
49,
50]. This contrasting resistance–susceptibility pattern has been frequently reported in wildlife-associated
E. coli and reflects phenotypic adaptation to beta-lactam selective pressure, without implying confirmed ESBL production in the absence of molecular evidence. In
Proteus spp. from red foxes, multidrug-resistant profiles were observed. However, resistance to imipenem, tetracycline, and nitrofurantoin reflects intrinsic species traits and was excluded from the calculations. Importantly, several isolates showed additional acquired resistance, highlighting the epidemiological role of foxes as carriers of resistant
Proteus species. This is significant as
Proteus can act as a genetic hub in the gut microbiome, transferring resistance genes via mobile elements to other enterobacteria, thereby amplifying and maintaining a reservoir of AMR within wildlife populations and the environments they traverse [
7,
42,
51,
52,
53]. Although less frequent,
Shigella sonnei and
Salmonella enterica isolates revealed localized resistance patterns. Among the
S. sonnei strains from Oloșag, Boldur, and Sacoșul Mare, all isolates were resistant to tetracycline, while partial resistance was observed for cefoxitin and imipenem.
S. enterica isolates remained susceptible to cephalexin, despite resistance to several other beta-lactams, aminoglycosides, and tetracycline. Similar observations in other European studies suggested that these localized resistance patterns could reflect environmental contamination pressures rather than species-wide adaptations [
7,
42,
47].
The staphylococcal isolates comprising the Gram-positive group exhibited an overall favorable antimicrobial susceptibility profile, with chloramphenicol and amikacin remaining highly effective, followed by cephalosporins and imipenem. In contrast, resistance was predominantly observed against beta-lactams (penicillin, oxacillin), tetracycline, clindamycin, and selected aminoglycosides. Methicillin resistance was identified in
S. aureus, S. pseudintermedius and
S. sciuri, paralleling findings from the United Kingdom, Ireland, and Poland, where coagulase-negative staphylococci (
S. aureus, S. sciuri,
S. equorum,
S. capitis) from foxes frequently contained the
mecA gene, with prevalence reaching 89% [
3,
54].
At the species level,
Staphylococcus aureus exhibited the most consistent and elevated resistance among Gram-positive isolates, particularly to tetracycline (75%), gentamicin (62.5%), benzylpenicillin (50%), clindamycin (50%), and trimethoprim–sulfamethoxazole (50%), while resistance to ciprofloxacin and imipenem remained lower (25%), and susceptibility to amikacin and chloramphenicol was largely preserved. In contrast, other staphylococcal species demonstrated more heterogeneous and often narrower resistance profiles.
S. xylosus and
S. vitulinus frequently remained fully susceptible or resistant to only a limited number of antibiotics, whereas
S. sciuri,
S. lentus, and
S. pseudintermedius showed broader resistance patterns, most commonly involving beta-lactams, tetracycline, and clindamycin. Notably, resistance to oxacillin and benzylpenicillin was recurrent across multiple non-aureus species, while susceptibility to chloramphenicol and amikacin was consistently maintained. This species-dependent variability highlights the ecological complexity of staphylococcal resistance in wild red foxes and suggests that, alongside
S. aureus, coagulase-negative staphylococci may serve as important reservoirs of selectively maintained resistance traits in wildlife-associated bacterial communities [
3,
20,
54,
55]. Notably, the highest resistance levels among Gram-positive isolates were recorded in the Nădrag and Surduc hunting grounds, where resistance was observed for clindamycin (83%), ciprofloxacin, tetracycline, and oxacillin (each 66.7%), despite complete susceptibility to chloramphenicol and amikacin. Similar to the Gram-negative findings, the Surduc area is characterized by increased human activity linked to recreational use, which may contribute to elevated environmental selective pressure. Although no environmental matrices were analyzed and causal inference cannot be established, previous studies have identified anthropogenically influenced waters as potential reservoirs for resistant staphylococci [
7,
48,
49,
50].
Methicillin resistance (MR) in staphylococcal isolates was assessed using the MIC values obtained via the Vitek 2 system. This approach was chosen due to the diversity of species studied and the greater accuracy of MIC in detecting methicillin resistance, in accordance with standard guidelines [
26].
Methicillin-resistant staphylococci (MRS) were more frequently detected in foxes from peri-rural areas (9/16; 56.3%) than from peri-urban areas (3/11; 27.3%). Notably, three methicillin-resistant
Staphylococcus aureus (MRSA) isolates were identified exclusively in peri-rural hunting grounds, underscoring the public health relevance of these findings, as MRSA remains one of the most important zoonotic and community-associated antimicrobial-resistant pathogens worldwide [
56,
57]. The higher prevalence of methicillin-resistant staphylococci observed in foxes from peri-rural areas compared with peri-urban environments may reflect differences in ecological exposure to antimicrobial resistance reservoirs [
58,
59]. Peri-rural habitats are closely associated with livestock farming, where the therapeutic and metaphylactic use of antimicrobials, particularly beta-lactams, exerts selective pressure favoring methicillin-resistant strains [
60]. Livestock-associated staphylococci, including both MRSA and methicillin-resistant coagulase-negative staphylococci, can disseminate into the environment through manure, slurry application, and contaminated soils and water sources [
61]. Foxes inhabiting these areas frequently interact with the wildlife–livestock interface through predation, scavenging of animal remains, and contact with farm environments, increasing their likelihood of acquiring resistant bacteria [
62]. In addition, rural ecosystems may promote the persistence and horizontal transfer of resistance determinants such as
mecA and
mecC via mobile genetic elements, supported by high bacterial diversity and environmental co-localization. Notably,
mecC-positive staphylococci have been repeatedly associated with ruminants and wildlife species in rural settings, suggesting that peri-rural environments may act as important reservoirs for these lineages [
63]. In contrast, other studies pointed out that peri-urban foxes are more likely exposed to human-associated staphylococci, where environmental dissemination of resistant strains may be more limited, due to regulated waste management systems. Differences in diet and foraging behavior between peri-rural and peri-urban foxes may further contribute to the observed patterns [
3,
20].
In addition to MRSA, methicillin resistance was observed in other staphylococcal species with known veterinary and opportunistic human relevance.
Staphylococcus pseudintermedius, a common pathogen in dogs and cats and a leading cause of skin and soft tissue infections, was detected among fox isolates, raising concerns regarding potential bidirectional transmission between wildlife and domestic animals, particularly in peri-urban and peri-rural interfaces where spatial overlap is likely [
55,
58]. Furthermore,
Staphylococcus sciuri and other coagulase-negative staphylococci (CoNS), although often regarded as commensals, are increasingly implicated in infections in immunocompromised individuals and in patients with implanted medical devices [
20]. The presence of methicillin resistance in these species provides an early warning signal of the presence of resistance at interfaces where humans, domestic animals, and wildlife converge, rather than evidence of active transmission pathways. This concern is reinforced by molecular evidence from the scientific literature, demonstrating that
mecA and
mecC genes detected in wildlife-associated staphylococci are identical or closely related to those circulating in human and veterinary clinical settings [
57]. Overall, these findings reinforce a One Health perspective in which peri-rural wildlife, particularly red foxes, function as effective sentinels for the occurrence of antimicrobial resistance in environments influenced by human activity. Due to their ecological adaptability, occasional extra-territorial movements, and frequent use of landscapes at the interface of anthropogenic and natural habitats, red foxes are well positioned to reflect resistance pressures driven by agricultural and human activities [
3,
20].
Comparable observations and results have been reported in other European countries, including Ireland, Poland, and Norway, where methicillin-resistant
S. pseudintermedius and CoNS were recovered from foxes in proximity to human settlements and livestock. In the United Kingdom, an investigation of 38 foxes revealed methicillin-resistant
S. sciuri (35%),
S. equorum (27%), and
S. capitis (22%), with the
mecA gene detected in 89% of isolates and broad beta-lactam resistance in 27% [
3,
45]. Although prevalence in wildlife is generally lower than in domestic animals, these findings collectively emphasize that foxes can harbor clinically significant staphylococci, reinforcing the need for integrated surveillance that encompasses wildlife, companion animals, and humans [
64].
Despite the fact that a slightly higher prevalence of multidrug-resistant (MDR) strains was observed in peri-urban compared with peri-rural settings, this difference was not statistically significant, indicating that geographic origin alone did not substantially influence MDR distribution in the study population. This suggests that the emergence of MDR is likely driven by factors other than spatial location, such as shared selective pressures or the intrinsic bacterial characteristics present in each environment [
58]. At the organism level, peri-urban isolates showed higher MDR proportions, with 23.3% of
Escherichia coli and both
Salmonella enterica isolates classified as MDR, compared with peri-rural settings, in which 14.6% of
E. coli isolates and a single
Proteus vulgaris isolate were MDR. Notably, the higher proportion of MDR among Gram-positive isolates points to a biological influence on resistance, suggesting that Gram-positive bacteria may play a larger role in the overall prevalence of multidrug resistance, regardless of location [
60]. As an observation, isolates from peri-rural, forest rich areas, such as Silvaș/Zeicani and Crocna-Zimbru, displayed no MDR isolates, with
E. coli found to be largely susceptible and staphylococci showing no evidence of methicillin resistance.
Previous studies in Europe have reported associations between human population density and MDR prevalence. In Norway, high MDR rates occurred in areas of intermediate-to-high human density, particularly in
E. coli resistant to cefotaxime, ampicillin, and tetracycline [
41]. In other research works, it has been noticed that foxes from peri-urban areas or livestock-associated landscapes carried frequently MDR
Enterobacteriaceae and staphylococci, whereas those from remote forest habitats primarily yielded susceptible strains [
7,
42,
43]. In Denmark, carbapenem- or colistin-resistant
E. coli were detected in 387 of 528 fox samples, with higher prevalence in regions more densely populated by humans [
11]. Taken together, these findings suggest that MDR clustering in red foxes may be influenced by anthropogenic pressures and that patterns documented in Romania are consistent with broader European trends [
32,
64].
In addition to the overall AMR and MDR patterns observed, methicillin-resistant staphylococci (MRS) represent a clinically relevant finding within the red fox populations studied. Staphylococci are important because of their role as common pathogens in companion animals and opportunistic agents in humans [
36]. The identification of cefoxitin-positive isolates in foxes therefore provides a useful perspective for understanding the potential links between wildlife, domestic animals, and clinical settings. MRS were detected among free-living red foxes originating from both, peri-urban and peri-rural hunting grounds, with
S. aureus,
S. pseudintermedius and
S. sciuri representing the main cefoxitin-positive species.
The findings of this study can be understood within a One Health framework, emphasizing the interconnectedness of human, animal, and environmental health, and highlighting how antimicrobial resistance (AMR) exemplifies this interdependence [
65]. The red fox, with its global distribution, ecological adaptability, and broad diet, has been increasingly recognized as a sentinel species for monitoring environmental pressures, including contaminants, emerging resistance, and zoonotic threats [
23,
32]. Our results demonstrate that red foxes can act as effective sentinels for antimicrobial resistance at the interface of wildlife, domestic animals, and humans. By reflecting resistance patterns associated with human-modified environments, foxes provide valuable insight into the occurrence of methicillin-resistant staphylococci and multidrug-resistant Gram-negative bacteria beyond that determined in clinical and agricultural settings. Incorporating this species into integrated surveillance frameworks could enhance early detection of emerging resistance patterns and inform strategies to protect public and animal health.
A major strength of this study lies in the combined use of two complementary phenotypic antimicrobial susceptibility testing methods, namely, disk diffusion (DD) and the Vitek 2 automated system. The high level of agreement observed between DD and Vitek 2 results for both Gram-negative and Gram-positive isolates supports the reliability of disk diffusion as a routine screening tool for antimicrobial resistance. This is particularly relevant in settings where access to automated systems such as Vitek 2 may be limited. Unlike automated platforms, disk diffusion allows greater flexibility in antibiotic selection and is not restricted to predefined testing panels, enabling the evaluation of a broader range of antimicrobials and enhancing the interpretative depth of resistance profiling. While Vitek 2 provides standardized minimum inhibitory concentration (MIC) values and remains a valuable method in clinical and research contexts, its narrower antibiotic coverage in this study (11 agents for Gram-negative and 14 for Gram-positive isolates) resulted in resistance data that was less comprehensive, as previously noted in other investigations [
21,
66]. Another important strength of this work is its contribution to the limited literature on antimicrobial resistance in Romanian wildlife, a field that remains underrepresented, particularly in Eastern Europe. By incorporating a comparative analysis between peri-urban and peri-rural environments, this study provides a nuanced dataset that enhances understanding of resistance patterns across differing ecological interfaces. Such data are essential for framing antimicrobial resistance within a One Health context, where interactions between wildlife, human activity, and environmental pressures play a critical role in resistance emergence and dissemination.
This study has several limitations that should be acknowledged. First, sampling was restricted to a single geographic area, encompassing three counties in western Romania, which may constrain the extrapolation of the findings to other regions of the country with different ecological or anthropogenic pressures. Second, although the study provided an in-depth characterization of phenotypic antimicrobial resistance patterns, molecular analyses of resistance determinants and clonal lineages were not performed. The inclusion of genotypic data would have enabled a more detailed understanding of the underlying resistance mechanisms and potential transmission pathways, particularly for clinically relevant determinants such as carbapenemase-encoding genes or methicillin resistance genes in Staphylococcus aureus. In this context, molecular confirmation could also have clarified the interpretation of isolates classified as susceptible with increased exposure by identifying cryptic resistance genes. Third, only a subset of isolates was examined using the Vitek 2 system due to practical constraints, which may introduce selection bias. Nevertheless, the sample size was sufficient for the statistical analyses performed and does not compromise the validity of the comparison of methods. This strategy was adopted due to practical and financial constraints and is now explicitly acknowledged as a limitation. Lastly, the absence of environmental sampling (e.g., soil and water) represents an additional limitation, as integrating such data would have provided a more comprehensive assessment of antimicrobial resistance across the animal–human–environment interface within a One Health framework.
These findings highlight the complexities of antimicrobial resistance in wildlife and point to key priorities for future research, including genetic analysis of resistance, tracing the sources of such resistance, and combining multiple testing methods to obtain a more complete understanding of resistance in the environment. Within this framework, the red fox appears as an important sentinel animal for monitoring antimicrobial-resistant bacteria in environments affected by anthropogenic activity. Integrated One Health initiatives informed by such surveillance may aid in the creation of evidence-based actions and preventative measures to reduce hazards to human, animal, and environmental health. Finally, continuous attention to animal sentinels may be critical for anticipating and resolving developing concerns at the human–environment interface.