INTRODUCTION
Antimicrobial resistance (AMR) is a major global threat to public health and animal agriculture (
1,
2). Ongoing misuse and overprescription of antibiotics creates selective pressure for AMR-encoding genes (ARGs) that impact the prevention and treatment of infections in both humans and domestic animals. Of further concern is the growing evidence that residual antibiotics and resistant bacteria may spread from clinical and agricultural settings into natural ecosystems, creating reservoirs of ARGs that could undergo horizontal gene transfer into novel opportunistic pathogens (
3–6). Indeed, clinically relevant antibiotic-resistant bacteria have been identified in a wide range of natural habitats and wild animal species, including those at the human-agriculture-environment interface (for examples, see references
5 and
7 to 10). However, there are still large gaps in our understanding of the potential role natural ecosystems play in the emergence, maintenance, and dispersal of ARGs. We also know relatively little about what forces shape observed patterns of AMR in wild animal populations (
3,
11–13), yet this information is critical for determining if intervention is required and subsequently how control strategies could be implemented (
12).
Understanding ARG dissemination in wild animals requires knowledge, in part, of commensal bacterial transmission. Commensal bacteria in the host gastrointestinal (GI) tract can acquire and transfer ARGs with relative ease, and resistant bacterial clones are often used as indicators of AMR prevalence in GI bacterial populations (
14–16). Recent work with humans and other animals suggests that these GI bacteria can spread between hosts via interactions, such as physical contact or shared environmental resources (
17,
18). Thus, individuals with direct or indirect associations may share specific bacterial strains (
19–21) or have more similar microbial communities (
22–24).
By extension, physical contact or common environments may similarly promote the spread of antibiotic-resistant bacteria among human and animal hosts. Indeed, there is growing evidence that shared use of environmental resources may facilitate the transmission of resistant bacteria between domestic animals, human populations, environmental reservoirs, and wildlife (
25–27). Within populations, however, there are still unanswered questions regarding the relative importance of AMR “spillover” events from humans or domestic animals compared to independent circulation of resistant bacteria within wild animals. Specifically, are repeated spillovers required to sustain AMR in a wild animal population or, after the initial introduction of an ARG from an anthropogenic source, does interhost transmission within the wild population contribute to AMR maintenance and dispersal? Research on within-species ARG transmission is still rare and primarily limited to studies with livestock (
28,
29) and humans (
30,
31). Comparable studies in wildlife systems would be of significant value for understanding the transmission dynamics of ARGs within natural ecosystems and in the absence of antibiotic use.
In this study, we used wild giraffe (
Giraffa camelopardalis) to investigate the drivers shaping population-level patterns of antibiotic-resistant
Escherichia coli. Giraffe sociality is characterized by fission-fusion social organization, where social group membership changes daily or even hourly as animals move through their environment (
32–35). Variation in patterns of direct or indirect association could influence how antibiotic-resistant bacteria are spread through the population. Commensal
E. coli is commonly found in the GI tracts of a wide range of animals and is disseminated via host contact with fecally contaminated environmental resources or direct host-to-host contact (
36–39). Further, both commensal and pathogenic
E. coli organisms are thought to be particularly important contributors to the global spread of antimicrobial resistance genes via mobile genetic elements (MGEs) (
40,
41). Prior research in the same giraffe population found that social contact networks predicted
E. coli sharing between individuals; giraffe that were more strongly connected in the co-occurrence network were more likely to harbor the same
E. coli strains than giraffe rarely observed together (
21). As a follow-up to this work, we investigated whether giraffe contact networks similarly predict patterns of antibiotic-resistant
E. coli among individuals. First, we identified which host characteristics, including metrics of both host social and spatial connectivity, influence the likelihood of a giraffe harboring resistant
E. coli. We then tested whether giraffe contact networks could promote the dissemination of ARGs between individuals. If social or spatial contact networks predict patterns of observed ARGs within the giraffe population, this would suggest that social associations may facilitate the circulation of resistant bacteria within wildlife populations. Taken together, these results advance our understanding of ARG transmission dynamics, including the forces responsible for the distribution of AMR in natural ecosystems.
DISCUSSION
To date, considerable research has focused on ARG dissemination between natural ecosystems and humans or domestic animals (for examples, see references
27 and
44 to 46). However, less attention has been paid to understanding whether ARGs circulate independently within wild animal populations after an introductory anthropogenic spillover event (but see references
27 and
47). In this study, we investigated the potential drivers shaping patterns of antimicrobial-resistant
E. coli within a population of wild giraffe. While we did find clinically resistant
E. coli in this population, social network analyses provided little evidence for the spread of acquired ARGs via interhost associations. Instead, the presence of AMR in this population may be primarily driven by repeated spillover of resistant bacteria from anthropogenic sources or related to other potential selection pressures for ARGs.
Giraffe home ranges overlap extensively with herds of domestic cattle, and all animals within OPC share common water sources that may act as environmental reservoirs of ARGs and hotspots of transmission from cattle to wild animals. While our current results alone cannot establish whether the resistant
E. coli organisms were directly transmitted from the local cattle population, a number of our findings do provide more general evidence that AMR in this giraffe population was primarily derived from anthropogenic sources. First, 9 of the 10
E. coli isolates we sequenced carried at least one acquired ARG, and all of these ARGs have been previously identified in
E. coli from both humans and domestic cattle in East Africa (
48–52). Further, prior research on AMR at human-livestock-wildlife interfaces suggests that the presence of these ARGs in wild animals is closely associated with anthropogenic land usage (
27,
47,
53–55). Second, although the dominant B1 phylogroup of our sequenced isolates is typical for
E. coli in both domestic and wild herbivorous animals (
36,
56), two other isolates belonged to phylogroups A and B2, the dominant phylogroups of human populations (
36,
57). Both isolates also had MLST sequence types (ST1433 and ST95) previously isolated from humans and frequently associated with extraintestinal diseases, including urinary tract and bloodstream infections (
58,
59). Third, we found that four of our sequenced isolates carried the class 1 integron-integrase gene,
intI1. This MGE-associated gene plays a major role in the global spread of ARGs and is thought to be a reliable genetic marker of anthropogenic pollution (
60,
61). Taken together, these results suggest that giraffe AMR is, in large part, derived from anthropogenic sources. However, the specific local sources of AMR—whether cattle or another unknown source—are yet to be determined.
The genetic characterization of our resistant isolates also provides evidence for both the horizontal transfer of ARGs between bacterial strains and the clonal spread of ARG-carrying
E. coli. On the one hand, we observed multiple instances where isolates with distinct genetic backgrounds harbored the same ARGs in similar genetic contexts. For example, scaffold group 5, which carried the
sul2-
strAB gene cluster, was found in three isolates with three different MLST sequence types. While we could not identify any MGEs associated with this scaffold group, prior studies found that the
sul2-
strAB gene cluster is part of a cassette and typically found on plasmids in a wide range of Gram-negative bacteria, including
E. coli (
62,
63). On the other hand, the ST1670 genomic subtype found in three different giraffe shared matching ARGs that were carried by the same four scaffold groups, which suggests that they may have descended from the same recent ancestor. This is in contrast to prior research on a sympatric population of cattle and wild buffalo in southern Africa that found the spread of ARGs was primarily independent of
E. coli strain sharing between individuals (
27). Together, our findings regarding both horizontal gene transfer and clonal transmission of ARGs suggest that both mechanisms play a role in the maintenance of AMR in this wild animal population and highlight the potential complexity of ARG spread.
The overall low prevalence of AMR identified in this population suggests that spillover from local humans and livestock may be a relatively rare occurrence or that there are simply low reservoirs of resistance to be shared between populations. This is somewhat surprising given reports of high antimicrobial use and AMR in both humans and livestock in Kenya (
64–68) and high prevalence of resistant bacteria observed in previous studies of East African wildlife (
8,
9,
69). In part, this variability in AMR prevalence between studies may be explained by differences in dietary niche between host species. Specifically, the type and location of food consumed may affect the level of exposure to residual antibiotics and resistant bacteria. For example, carnivores typically exhibit the highest AMR risk, possibly due to trophic accumulation of ARGs through the food chain, while herbivores have the lowest risk (
3,
8,
70). Giraffe exposure to AMR may be particularly low because their diet primarily consists of leaves from trees and shrubs, areas where antibiotic contamination and resistant bacteria associated with the host GI tract are less likely to exist.
Alternatively, the low AMR prevalence in this study compared to findings for other African wildlife may simply be an unintended consequence of our sampling design. The GI tract typically harbors a single dominant strain of
E. coli that constitutes more than half of the total isolated colonies (
71,
72). Since many AMR mutations or plasmids can reduce fitness in the absence of antibiotic selection pressures, resistant strains may be outcompeted by nonresistant strains with higher fitness (
73,
74). Thus, finding dominant strains with AMR phenotypes may be relatively rare in wild animals where selection for AMR is low (
27). Genotyping of
E. coli used in this study identified, on average, only 1.7 unique subtypes per giraffe (
21). Consequently, the majority of susceptibility testing was probably conducted on the dominant
E. coli strains, where resistance may have been present but rare. A sampling design that includes susceptibility testing of both dominant and subdominant isolates might have revealed higher levels of AMR within the giraffe population. For example, work with wild African buffalo found AMR in only one dominant
E. coli strain but identified resistance in many subdominant isolates (
27). Similar findings have also been reported for both livestock (
75) and humans (
76,
77). Assessment of these rare, subdominant strains could be more effectively achieved either by initially culturing fecal samples in the presence of antibiotics or through metagenomic sequencing approaches.
AMR prevalence may also be low if the antibiotics we selected were not representative of AMR selection pressures in humans, livestock, and wildlife within the study area. However, it is worth noting that the two antibiotics most frequently used to treat cattle and wildlife (amoxicillin and oxytetracycline; G. Omondi, unpublished data) were also the two most common AMR phenotypes we identified in the giraffe population. Other antibiotics with higher rates of improper usage, such as those obtained over the counter by nonprofessionals near OPC, would be worth including in susceptibility testing for future surveys of AMR in this area (
68).
Despite the relatively low prevalence of giraffe AMR, regression model results indicated that there was a compelling relationship between AMR risk and individual-level measures of social connectedness. In particular, individuals with fewer social links to other giraffe were more likely to harbor resistant
E. coli. However, it is unclear whether this relationship reflects a real effect of social connectivity on AMR or whether it captures variation in another host characteristic not accounted for in our data set. The latter explanation seems more likely given that socially mediated transmission should result in giraffe with higher social degree experiencing higher AMR risk. Indeed, at the network level, neither social nor spatial contact networks explained the observed pattern of AMR-positive giraffe. Instead, we observed strong age-related patterns of AMR, with the highest AMR risk occurring in giraffe younger than 3 months. During the first few months of life, and particularly during the first 2 weeks, calves are kept relatively isolated from other giraffe and consequently have few social associations and small home ranges (
78,
79). Thus, our observed relationship between social and spatial connectedness and AMR risk may simply reflect these early months when associations are less frequent and AMR is high. Future work disentangling age-related social and ranging behaviors from other aspects of social and spatial association will provide a more complete picture of the host traits that predispose certain groups to acquire, maintain, and spread ARGs.
The high likelihood of identifying resistant
E. coli in neonate giraffe compared to other age classes suggests that age may be an important predictor of AMR risk in giraffe. In young giraffe, exposure to residual antibiotics is presumably low, particularly while neonates are exclusively nursing. Therefore, the high prevalence of AMR in neonates compared to other age classes is unlikely to be caused by differential selection pressures related to antibiotic exposure. Instead, our results suggest that resistant
E. coli strains may have a selective advantage over susceptible strains within the neonate GI tract. Some ARGs may be genetically linked to advantageous genes that enhance the fitness of resistant strains, such as encoding mechanisms of colonization, adhesion, or reproduction (
80,
81). For example, the milk diet of giraffe neonates could create a niche for bacterial strains that carry genes for enhanced acquisition or utilization of milk-associated nutrients and antimicrobial resistance (
82,
83). As neonate feeding behavior shifts from nursing to extensive browsing between 2 and 4 months of age (
78,
79), the selective advantage of these strains would be lost and the abundance of resistant bacteria would subsequently decrease (
84). Indeed, our observation that AMR prevalence was higher in neonates (0 to 3 months) than in other giraffe age classes provides support for this hypothesis, but further culture and genome-based work would be required to identify the underlying mechanism(s) responsible for the apparent age-related differences in AMR. It is also worth noting that similar age-related distributions of AMR have also been observed in both humans and domestic animals (for examples, see references
85 to 88)—even in the absence of antibiotic selection pressures (
82)—but the mechanisms underlying these patterns remain largely unknown.
Overall, our results indicate that the presence of AMR in this wild giraffe population is primarily due to dissemination of resistant E. coli strains and/or ARGs from local anthropogenic sources and not independent circulation of ARGs among giraffe. However, our finding that AMR risk differs between giraffe age classes suggests that ARG spread is not a completely random process and that the persistence of resistant strains may be dependent on host traits and competition dynamics of the gut microbial community. To date, the potential hazards of wild animal reservoirs of acquired ARGs have yet to be determined. Yet the mere presence of clinically resistant E. coli in natural ecosystems warrants concern and investigation into the potential consequences for both humans and domestic animals. Future AMR research should therefore include studies of wildlife and environmental reservoirs, with a focus on the role that natural ecosystems may play in the emergence, maintenance, and global spread of AMR.