Abstract
Based on a large-scale bibliometric dataset, domestic dogs (Canis lupus familiaris) emerge as the most frequently cited host species in the context of zoonoses, being mentioned in at least 10% of publications for nearly a quarter of the pathogens recognized as zoonotic to humans. This review examines the contributions of pet and stray dogs to various zoonotic transmission pathways, highlighting some mismatches between research focus and actual epidemiological risks. Among zoonotic agents associated with dogs, helminths are disproportionately represented in the literature compared to bacteria and viruses. Pet and stray dogs exhibit distinct zoonotic risks due to differences in exposure patterns and human interactions. Stray dogs are frequently involved in environmentally transmitted diseases, particularly soil- and water-borne parasites, due to uncontrolled defecation and opportunistic behavior. Conversely, pet dogs pose greater risks for direct transmission, particularly via bites, close contact infections, and antimicrobial-resistant bacteria. From a public health perspective, integrating dogs into One Health surveillance frameworks is crucial. Routine genomic monitoring of stray dogs could allow early detection of emerging zoonoses, while large-scale deworming programs, improved sanitation infrastructures, and responsible pet management would mitigate both environmental and direct transmission risks. Vector-borne zoonoses require differentiated control measures, including antiparasitic treatments for tick- and flea-borne infections and environmental interventions for mosquito- and sandfly-borne pathogens. This review focuses on pet and stray dogs only, due to the lack of consistent definitions and data availability for other canine categories. Future research should refine ecological and behavioral studies and dog–host interaction analyses to better quantify the zoonotic risks associated with each dog ecotype and guide targeted intervention strategies. This approach enables a more precise zoonotic risk stratification and contributes to effective disease prevention at the human–animal–environment interface.
Keywords: bibliometric analysis, canine ecotypes, one health, transmission pathways, zoonotic pathogens
1. Introduction
Zoonotic diseases, which arise from the close relationship humans have established with surrounding animal species, represent one of the primary threats to global public health [1, 2]. Domestic animals play a key role in the transmission dynamics of these zoonoses due to their abundance and global distribution. The likelihood of pathogen exchange with wild and environmental reservoirs is enhanced through domesticated species, which have central positions in interspecies transmission networks [3]. Thus, they facilitate the gradual adaptation of infectious agents to a wide range of hosts, including humans, acting as intermediaries in the spread of numerous emerging zoonotic diseases [4–8]. This is particularly true for domestic carnivores, which share 90% of their pathogens with other hosts [9]. Canis lupus familiaris harbors the greatest diversity of zoonotic infectious agents among all animal species [10]. In this sense, canine populations generally do not constitute an independent reservoir, in which pathogens can persist in the long term: rather, they are part of a broader maintenance complex [11]. As one of the animals interacting most closely with humans within multi-species maintenance communities, the domestic dog is often a major source of zoonotic infections [12, 13].
Beyond the global abundance of canine populations, the primary reason behind the high potential of dogs for transmitting zoonotic pathogens is the intimate and long-lasting relationship they maintain with humans for thousands of years [14]. As a result of this long-term co-evolution, canine pathogens have gradually adapted to humans [10, 15]. This constant proximity across diverse socio-ecological contexts has created multiple interfaces between dogs and humans [16], providing pathogens with privileged access to various zoonotic transmission pathways through a wide range of direct or indirect interactions. Dog bites, for instance, are a common source of bacterial infections [17, 18], in addition to being responsible for almost all cases of human rabies [19]. “Man's best friend” also play a significant role in the epidemiology of brucellosis [20, 21], leptospirosis [22, 23], and Q fever [24, 25], all diseases transmitted through close contact with the bodily fluids of infected animals. Moreover, dogs are recognized as maintenance hosts for numerous (re)emerging zoonotic vector-borne diseases [26, 27], including ehrlichiosis [28, 29], dirofilariasis [30, 31], and leishmaniasis [32, 33]. Finally, canine populations contribute to the spread of a wide variety of environmentally transmitted parasitic infections [34], most of which being categorized as Neglected Tropical Diseases by the World Health Organization [35], such as cystic echinococcosis [36, 37], foodborne trematodiases [38, 39], and soil-transmitted helminthiasis [40, 41]. The diversity of contamination mechanisms associated with dogs therefore highlights the numerous potential pathways through which canine populations can contribute to the emergence of zoonoses.
Although canine populations are not always able to sustain all these pathogens in the long-term, they can still serve as intermediate link for zoonotic infection, acting as epidemiological bridges [42]. By connecting the maintenance complex to the target host, dogs could then facilitate the spread of infectious agents from wildlife to human populations [43]. Far from being an homogeneous entity, the global dog population encompasses a wide range of socio-ecological profiles and lifestyles, each characterized by specific behaviors, habitat preferences, and interactions with humans and other animal species [38, 43–45], thereby influencing disease transmission mechanisms in varied ways. Excluding wild feral dogs, the spectrum of domestic dogs ranges from 'stray dog' (i.e., dogs roaming freely and exposed to wild or commensal fauna without access to a consistent food source or appropriate veterinary care) to 'pet dog' (i.e., dogs living within human households under controlled conditions regarding their displacements, nutrition, and hygiene), with intermediate profiles in terms of management, such as free-roaming owned dogs or dogs kept in shelters or kennels [46–49]. The zoonotic transmission possibilities at either end of the canine ecotypic spectrum are thus likely to vary in both frequency and transmission mode. For instance, pet dogs may be especially more prone to transmit pathogens directly to their owners through close contacts [50], whereas the free defecation of stray dogs in the environment is believed to facilitate the completion of the life cycle of parasites that can be transmitted to humans via foodborne pathways [51]. Given the diversity and complexity of transmission patterns involving dogs, assessing the overall public health impact attributable to C. lupus familiaris appears neither realistic nor appropriate. It would nonetheless be conceivable and relevant to break down the continuous gradient of canine ecotypes to estimate their respective contributions to zoonotic transmission pathways.
In this context, associating socio-ecological profiles of dogs with specific zoonotic risks may support the development of effective prevention strategies. Several studies have thus recommended differentiated management of canine populations by focusing on key individuals to reduce their respective roles in zoonotic cycles [45]. For instance, targeted rabies vaccination in Africa and Asia has significantly reduced the number of human cases, particularly in urban areas where stray dogs play a predominant role in rabies transmission [52, 53]. Equipping companion dogs with insecticide-impregnated deltamethrin collars has led to a notable reduction in human visceral leishmaniasis in rural areas of Brazil [54, 55]. Screening and culling programs for infected dogs in commercial breeding kennels, combined with strict biosecurity measures, have helped to limit zoonotic infections by Brucella canis [20, 56]. Similarly to these studies, identifying specific transmission pathways of canine pathogens will enable the implementation of targeted health control measures. The aim of this review is therefore to address the diversity of mechanisms by which infectious agents can spread from dogs, focusing on the zoonotic potential of each specific dog ecotype. By synthesizing the available information from the scientific literature, this study seeks to identify overarching trends in public health risks associated with dogs and provide general recommendations for preventing the emergence of zoonoses through the canine epidemiological bridge.
2. Materials and Methods
We first compiled a structured list of zoonotic pathogens potentially transmissible by dogs worldwide. Although taxonomic inconsistencies and evolving classifications complicate this task, the resulting inventory captures a broad and representative set of infectious agents relevant to canine-mediated transmission. For each pathogen, we assessed the zoonotic potential and the degree of canine involvement based on available evidence. This step provided an initial framework for understanding transmission dynamics and identifying areas where the epidemiological role of dogs is poorly documented.
To account for potential bias linked to uneven research attention, we conducted a large-scale lexical analysis of a bibliographic database, using the pathogen as the analytical unit. Pigs were included in this analysis as a reference host species, given their established role in zoonotic transmission, their status as livestock animals—epidemiologically and symbolically distinct from dogs—and their position as the second most frequently cited mammalian species in relation to zoonotic transmissions. This approach offers a standardized, quantitative means of comparing the representation of dogs across various zoonotic cycles.
While bibliometric patterns do not constitute empirical proof of transmission, they reveal how scientific discourse reflects—or overlooks—canine involvement in zoonoses. To refine interpretation, we triangulated these results with targeted literature reviews from specialized sources. This integrative method provides a multi-layered perspective on the zoonotic role of dogs, highlighting imbalances in research coverage and supporting the identification of context-specific priorities for surveillance and disease control.
2.1. Representative List of Zoonotic Pathogens Transmitted by Dogs
To assess the role of the canine species in various zoonotic transmission pathways, we seek to accurately characterize the contamination mechanisms specific to each pathogen linked to dogs. A list of 335 known zoonotic pathogens, classified by taxonomic groups, was then compiled based on various sources, including Taylor et al. [57], Acha et al. [58], Polack et al. [59], Bauerfeind et al. [60], Rahman et al. [1], the MSD Veterinary Manual [61], and the Centers for Disease Control and Prevention [62]. From these references, key information was extracted for each listed infectious agent regarding the public health impact (low, moderate, high, or priority), the primary source of human exposure (animal, environment, food, or vector) and the main zoonotic transmission pathway (accidental ingestion of plants or insects, consumption of animal products, inoculation via bites or scratches, physical or close contact, transmission by ectoparasites, transmission by flying arthropod vectors, consumption of fish or seafood, inhalation, transmission through contact with soil, waterborne transmission, or unsanitary conditions route).
Additional bibliographic searches were then conducted using the Google Scholar database to highlight recognized or strongly suspected transmission cases originating from dogs. If the ability of C. lupus familiaris to transmit the infectious agent to humans was confirmed, the next step would be to estimate, through targeted bibliographic research, whether dogs primarily act as the primary source of zoonotic infection (main transmission host), as a secondary source (frequently implicated host), as an occasional source (a few confirmed cases), or as a potential source (competence demonstrated only in laboratory settings). Eco-epidemiological studies specifically exploring the roles of different types of dogs in the transmission of certain listed pathogens have also been referenced in Supporting Information 1: Table S1, where all the bibliographic information compiled with the corresponding sources is presented. To further investigate the diversity of pathogens transmitted to humans by dogs and the factors that determine this canine competency, χ2 tests were performed to identify potential significant associations. Adjusted standardized residuals were calculated to assess the extent to which the proportion of zoonotic pathogens transmitted by dogs differed by transmission pathways (Supporting Information 2), taxonomic groups and health impact. Data processing, statistical analyses, and graphical representations were performed using R software (version 4.3.1), using the “dplyr,” “tidyr,” “ggplot2,” and “gt” packages (Zoonotic list analysis code available in the Supporting Information 2).
2.2. Bibliometric Analysis to Assess the Pathogen/Dog Association
To evaluate numerically the overall zoonotic involvement of C. lupus familiaris based on the scientific literature, we aim to determine the extent to which canine ecotypes are associated with each listed pathogen at the scale of a bibliographic database. A bibliometric analysis was then conducted on a macroscopic scale using the Web of Science (WoS) Core Collection database as of November 15, 2024. First, we compared the number of results from a search for “dog(s)” in relation to “zoonotic transmission” to different queries searching for other host species or reservoirs of zoonotic importance (number of results for each query compiled in Figure 1). For each of these 335 zoonotic infectious agents on the list, the number of English-language Articles or Reviews mentioning the scientific name of the pathogen (or its abbreviation with the genus shortened) in their topics (TS = titles, keywords, or abstracts) was recorded in column “Total” in Supporting Information 1: Table S1. Among these publications, those that also mentioned the words “dog(s)” and “pig(s)” were counted in the “With_dogs” and “With_pigs” columns, and those that cited the words “pet(s)” and “stray,” in addition to “dog(s),” were counted in the “With_pet_dogs” and “With_stray_dogs” columns, respectively. The searches conducted using terms referring to shelter or free-roaming dogs did not yield enough results to be accounted for. The queries entered in the Web of Science database are available in Supporting Information 1: Table S1. Example to complete the “With_pet_dogs” column: TS = (Microsporum_canis AND dog∗ AND pet∗) AND (LA = English) AND (DT = (Article OR Review)). The factors “Dog's part” ( = “with_dogs”/“total”), “Pig's part” ( = “with_pigs”/“total”), “DogPig's part” ( = log (“with_dogs” + 1) – log (“with_pigs” + 1)), and “Dog's partition” ( = log (“with_stray_dogs” + 1) – log (“with_pet_dogs” + 1)) were then calculated to classify pathogens based on their association with dogs (or pigs). Table 1 includes only pathogens mentioned in more than 100 publications (Total > 100) for which the dog is considered competent (or suspected to be). For the full list of documented zoonotic pathogens, missing information—including WOS queries, number of publications, reservoirs, geographical context, and canine competence—as well as the corresponding bibliographic sources, is available in the full version of Supporting Information 1: Table S1.
Figure 1.

Number of publications provided per query in the Web of Science database.
Table 1.
List of zoonotic pathogens transmissible by dogs.
| Pathogen | Taxo group | Health impact | Exposure source | Pathway | Dog's part | Dog's partition | Zoonotic source potential |
|---|---|---|---|---|---|---|---|
| Helicobacter canis | Bacteria | Low | Animals | Close contact | 0.882 | 0.252 | Primary source |
| Trichuris vulpis | Nematoda | Low | Environment | Unsanitary conditions | 0.827 | −0.049 | Primary source |
| Ehrlichia canis | Rickettsial | Moderate | Vectors | Ectoparasit vector | 0.824 | −0.116 | Primary source |
| Capnocytophaga canimorsus | Bacteria | Moderate | Animals | Bites inoculation | 0.715 | −1.230 | Primary source |
| Staphylococcus pseudintermedius MR | Bacteria | Moderate | Animals | Bites inoculation | 0.714 | −1.209 | Primary source |
| Brucella canis | Bacteria | Moderate | Animals | Close contact | 0.710 | −0.280 | Primary source |
| Dipylidium caninum | Cestoda | Low | Vectors | Accidental ingestion | 0.709 | 0.314 | Primary source |
| Uncinaria stenocephala | Nematoda | Moderate | Environment | Soil transmitted | 0.685 | −0.239 | Primary source |
| Bartonella vinsonii berkhoffii | Bacteria | Low | Vectors | Bites inoculation | 0.673 | −0.025 | Primary source |
| Anaplasma platys | Rickettsial | Low | Vectors | Ectoparasit vector | 0.665 | 0.088 | Primary source |
| Dirofilaria repens | Nematoda | Moderate | Vectors | Flying vector | 0.629 | −0.342 | Primary source |
| Dirofilaria immitis | Nematoda | Moderate | Vectors | Flying vector | 0.622 | −0.248 | Primary source |
| Thelazia callipaeda | Nematoda | Low | Vectors | Flying vector | 0.607 | −0.885 | Primary source |
| Ancylostoma braziliense | Nematoda | Moderate | Environment | Soil transmitted | 0.583 | 0.301 | Primary source |
| Cryptosporidium canis | Protozoa | Moderate | Environment | Unsanitary conditions | 0.582 | −0.368 | Primary source |
| Streptococcus canis | Bacteria | Low | Animals | Bites inoculation | 0.551 | −1.362 | Primary source |
| Ehrlichia ewingii | Rickettsial | Moderate | Vectors | Ectoparasit vector | 0.548 | −0.477 | Primary source |
| Ancylostoma caninum | Nematoda | Moderate | Environment | Soil transmitted | 0.508 | −0.054 | Primary source |
| Toxocara cati | Nematoda | High | Environment | Unsanitary conditions | 0.491 | 0.136 | Occasional source |
| Eucoleus aerophilus | Nematoda | Low | Environment | Unsanitary conditions | 0.482 | −0.436 | Primary source |
| Toxocara canis | Nematoda | High | Environment | Unsanitary conditions | 0.423 | −0.104 | Primary source |
| Chlamydia felis | Bacteria | Low | Animals | Close contact | 0.403 | −0.357 | Potential source |
| Heterobilharzia americana | Trematoda | Moderate | Environment | Soil transmitted | 0.381 | 0.000 | Primary source |
| Leishmania infantum | Protozoa | Priority | Vectors | Flying vector | 0.380 | −0.249 | Primary source |
| Leptospira interrogans Canicola | Bacteria | High | Environment | Close contact | 0.362 | 0.120 | Primary source |
| Rickettsia felis | Rickettsial | Moderate | Vectors | Ectoparasit vector | 0.342 | −0.368 | Secondary source |
| Dracunculus medinensis | Nematoda | High | Environment | Waterborne | 0.333 | 0.301 | Secondary source |
| Ancylostoma ceylanicum | Nematoda | Moderate | Environment | Soil transmitted | 0.323 | −0.058 | Primary source |
| Staphylococcus intermedius MR | Bacteria | High | Animals | Close contact | 0.319 | −1.498 | Primary source |
| Neospora caninum | Protozoa | Low | Food | Animal product | 0.311 | 0.183 | Primary source |
| Campylobacter upsaliensis | Bacteria | Moderate | Food | Animal product | 0.308 | −0.881 | Primary source |
| Taenia multiceps | Cestoda | Moderate | Food | Animal product | 0.302 | 0.058 | Primary source |
| Linguatula serrata | Nematoda | Moderate | Food | Animal product | 0.287 | 0.067 | Primary source |
| Anaplasma phagocytophilum | Rickettsial | Moderate | Vectors | Ectoparasit vector | 0.236 | 0.171 | Secondary source |
| Rickettsia rickettsii | Rickettsial | High | Vectors | Ectoparasit vector | 0.235 | −0.512 | Secondary source |
| Leptospira interrogans Icterohaemorrhagiae | Bacteria | Priority | Environment | Waterborne | 0.234 | 0.131 | Secondary source |
| Angiostrongylus spp. | Nematoda | Moderate | Food | Accidental ingestion | 0.227 | −0.559 | Potential source |
| Ehrlichia chaffeensis | Rickettsial | Moderate | Vectors | Ectoparasit vector | 0.226 | −0.109 | Secondary source |
| Mesocestoides spp. | Cestoda | Low | Food | Animal product | 0.220 | 0.084 | Primary source |
| Echinococcus granulosus (sl) | Cestoda | Priority | Food | Animal product | 0.215 | 0.223 | Secondary source |
| Sarcocystis spp. | Protozoa | Low | Food | Animal product | 0.202 | −0.301 | Potential source |
| Leishmania chagasi | Protozoa | Priority | Vectors | Flying vector | 0.189 | 0.176 | Secondary source |
| Malassezia spp. | Fungi | Low | Animals | Close contact | 0.180 | −0.632 | Secondary source |
| Leptospira interrogans Copenhageni | Bacteria | Priority | Environment | Waterborne | 0.173 | 0.255 | Secondary source |
| Bartonella henselae | Bacteria | Moderate | Vectors | Bites inoculation | 0.172 | −0.180 | Secondary source |
| Spirometra spp. | Cestoda | Moderate | Food | Fish consumption | 0.157 | 0.030 | Secondary source |
| Microsporum canis | Fungi | Moderate | Animals | Close contact | 0.142 | −0.745 | Primary source |
| Rabies virus | Virus | Priority | Animals | Bites inoculation | 0.140 | 0.019 | Primary source |
| Bartonella spp. | Bacteria | Moderate | Vectors | Ectoparasit vector | 0.139 | −0.186 | Occasional source |
| Corynebacterium ulcerans | Bacteria | Low | Animals | Close contact | 0.138 | −0.903 | Secondary source |
| Bordetella bronchiseptica | Bacteria | Low | Animals | Inhalation | 0.132 | −1.176 | Secondary source |
| Trichinella nativa | Nematoda | Moderate | Food | Animal product | 0.123 | 0.477 | Occasional source |
| Dibothriocephalus latus | Cestoda | Moderate | Food | Fish consumption | 0.122 | 0.222 | Secondary source |
| Echinococcus multilocularis | Cestoda | Priority | Food | Animal product | 0.120 | −0.167 | Secondary source |
| Canine Influenza | Virus | Low | Animals | Inhalation | 0.112 | −0.769 | Primary source |
| Trichinella britovi | Nematoda | High | Food | Animal product | 0.109 | 0.477 | Potential source |
| Anaplasma ovis | Rickettsial | Low | Vectors | Ectoparasit vector | 0.105 | −0.125 | Potential source |
| Metagonimus spp. | Trematoda | Moderate | Food | Fish consumption | 0.100 | 0.000 | Secondary source |
| Baylisascaris spp. | Nematoda | Moderate | Environment | Unsanitary conditions | 0.097 | −0.653 | Occasional source |
| Necator americanus | Nematoda | High | Environment | Soil transmitted | 0.094 | −0.921 | Potential source |
| Brugia pahangi | Nematoda | Low | Vectors | Flying vector | 0.089 | 0.477 | Secondary source |
| Macracanthorhynchus spp. | Acanthocephala | Low | Food | Animal product | 0.085 | 0.222 | Potential source |
| Calodium hepaticum | Nematoda | Low | Environment | Unsanitary conditions | 0.083 | −0.176 | Occasional source |
| Rickettsia typhi | Rickettsial | Moderate | Vectors | Ectoparasit vector | 0.081 | −0.368 | Potential source |
| Borrelia burgdorferi (sl) | Bacteria | Priority | Vectors | Ectoparasit vector | 0.077 | −0.377 | Secondary source |
| Alaria spp. | Trematoda | Low | Food | Fish consumption | 0.073 | −0.439 | Secondary source |
| Paragonimus spp. | Trematoda | High | Food | Fish consumption | 0.072 | 0.000 | Secondary source |
| Opistorchis spp. | Trematoda | High | Food | Fish consumption | 0.070 | 0.301 | Secondary source |
| Rickettsia spp. | Rickettsial | Moderate | Vectors | Ectoparasit vector | 0.069 | −0.164 | Secondary source |
| Leishmania braziliensis | Protozoa | Priority | Vectors | Flying vector | 0.069 | 0.000 | Secondary source |
| Giardia duodenalis | Protozoa | Priority | Environment | Waterborne | 0.067 | −0.289 | Secondary source |
| Rickettsia conorii | Rickettsial | Moderate | Vectors | Ectoparasit vector | 0.065 | −0.146 | Secondary source |
| Barmah Forest virus | Virus | Low | Vectors | Flying vector | 0.065 | −0.602 | Secondary source |
| Taenia crassiceps | Cestoda | Low | Food | Animal product | 0.065 | −0.398 | Secondary source |
| Toxoplasma gondii | Protozoa | Priority | Food | Animal product | 0.064 | −0.072 | Occasional source |
| Strongyloides stercoralis | Nematoda | High | Environment | Soil transmitted | 0.063 | −0.234 | Secondary source |
| Cryptosporidium spp. | Protozoa | Moderate | Environment | Unsanitary conditions | 0.060 | −0.301 | Occasional source |
| Brucella suis | Bacteria | Moderate | Animals | Close contact | 0.060 | −0.176 | Occasional source |
| Haplorchis spp. | Trematoda | Moderate | Food | Fish consumption | 0.058 | 0.000 | Secondary source |
| Gnathostoma spinigerum | Nematoda | High | Food | Fish consumption | 0.057 | 0.301 | Secondary source |
| Pasteurella multocida | Bacteria | Moderate | Animals | Bites inoculation | 0.056 | −0.993 | Secondary source |
| Gnathostoma spp. | Nematoda | High | Food | Fish consumption | 0.056 | 0.301 | Potential source |
| Streptococcus equi zooepidemicus | Bacteria | Moderate | Animals | Close contact | 0.055 | −0.477 | Occasional source |
| Leishmania mexicana, tropica | Protozoa | Priority | Vectors | Flying vector | 0.054 | −0.092 | Secondary source |
| Yersinia pestis | Bacteria | Priority | Vectors | Ectoparasit vector | 0.053 | −0.845 | Secondary source |
| Borrelia garinii | Bacteria | Priority | Vectors | Ectoparasit vector | 0.049 | −0.602 | Occasional source |
| Tick-borne relapsing fever Borrelia | Bacteria | Moderate | Vectors | Ectoparasit vector | 0.045 | −0.903 | Occasional source |
| Sporothrix brasiliensis | Fungi | High | Animals | Bites inoculation | 0.040 | 0.000 | Occasional source |
| Trichophyton mentagrophytes | Fungi | Moderate | Animals | Close contact | 0.040 | −0.517 | Secondary source |
| Louping-ill virus | Virus | Low | Vectors | Ectoparasit vector | 0.040 | −0.301 | Potential source |
| Coxiella burnetii | Rickettsial | Priority | Animals | Inhalation | 0.038 | −0.412 | Occasional source |
| Blastocystis spp. | Protozoa | Low | Environment | Unsanitary conditions | 0.038 | −0.103 | Occasional source |
| Sporothrix schenckii | Fungi | Moderate | Animals | Soil transmitted | 0.034 | −0.602 | Occasional source |
| Hymenolepis nana | Cestoda | Moderate | Food | Accidental ingestion | 0.034 | 0.000 | Occasional source |
| Schistosoma mekongi | Trematoda | High | Environment | Waterborne | 0.033 | 0.000 | Occasional source |
| Omsk hemorrhagic fever virus | Virus | High | Vectors | Ectoparasit vector | 0.033 | 0.000 | Potential source |
| Angiostrongylus costaricensis | Nematoda | Moderate | Food | Accidental ingestion | 0.032 | −0.477 | Occasional source |
| Trypanosoma cruzi | Protozoa | Priority | Vectors | Ectoparasit vector | 0.031 | −0.336 | Secondary source |
| Tick-borne encephalitis virus | Virus | Priority | Vectors | Ectoparasit vector | 0.029 | −0.903 | Occasional source |
| Balantidium coli | Protozoa | Low | Environment | Unsanitary conditions | 0.029 | 0.000 | Occasional source |
| Microsporum spp. | Fungi | Low | Animals | Close contact | 0.028 | −0.368 | Secondary source |
| Cryptocotyle lingua | Trematoda | Low | Food | Fish consumption | 0.028 | 0.000 | Occasional source |
| Centrocestus spp. | Trematoda | Low | Food | Fish consumption | 0.028 | 0.000 | Occasional source |
| Opistorchis viverrini | Trematoda | High | Food | Fish consumption | 0.027 | 0.000 | Secondary source |
| Campylobacter coli | Bacteria | Moderate | Food | Animal product | 0.027 | −0.632 | Secondary source |
| Erysipelothrix rhusiopathiae | Bacteria | Moderate | Animals | Close contact | 0.026 | −0.477 | Potential source |
| Francisella tularensis | Bacteria | Priority | Animals | Bites inoculation | 0.025 | −0.954 | Occasional source |
| Streptobacillus moniliformis | Bacteria | Low | Animals | Bites inoculation | 0.024 | −0.477 | Secondary source |
| Clostridium perfringens | Bacteria | High | Food | Animal product | 0.024 | −1.161 | Occasional source |
| Ascaris lumbricoides | Nematoda | High | Environment | Unsanitary conditions | 0.023 | −0.505 | Occasional source |
| EEE virus | Virus | Priority | Vectors | Flying vector | 0.023 | 0.000 | Potential source |
| Powassan virus | Virus | Moderate | Vectors | Ectoparasit vector | 0.022 | 0.000 | Potential source |
| Brucella abortus | Bacteria | Priority | Animals | Animal product | 0.021 | −0.125 | Occasional source |
| Trichinella spiralis | Nematoda | High | Food | Animal product | 0.021 | 0.477 | Occasional source |
| Brucella melitensis | Bacteria | Priority | Animals | Animal product | 0.021 | −0.079 | Occasional source |
| Taenia solium | Cestoda | Priority | Food | Animal product | 0.021 | 0.000 | Occasional source |
| Arcobacter spp. | Bacteria | Moderate | Food | Animal product | 0.020 | −0.813 | Occasional source |
| Cryptosporidium parvum | Protozoa | Priority | Environment | Unsanitary conditions | 0.019 | −0.477 | Occasional source |
| Trichophyton spp. | Fungi | Moderate | Animals | Close contact | 0.017 | −0.477 | Occasional source |
| Campylobacter jejuni | Bacteria | Priority | Food | Animal product | 0.017 | −0.897 | Secondary source |
| Leishmania donovani donovani | Protozoa | Priority | Vectors | Flying vector | 0.016 | −0.380 | Potential source |
| Mycoplasma spp. | Bacteria | Low | Animals | Close contact | 0.014 | −0.253 | Occasional source |
| Moniliformis moniliformis | Acanthocephala | Low | Food | Accidental ingestion | 0.014 | −0.176 | Potential source |
| Clostridioides difficile | Bacteria | High | Environment | Unsanitary conditions | 0.013 | −1.447 | Occasional source |
| Acanthocephalus spp. | Acanthocephala | Low | Food | Fish consumption | 0.013 | 0.058 | Potential source |
| Schistosoma japonicum | Trematoda | High | Environment | Waterborne | 0.013 | 0.000 | Occasional source |
| Murray Valley encephalitis virus | Virus | Moderate | Vectors | Flying vector | 0.012 | 0.000 | Occasional source |
| West Nile virus | Virus | Priority | Vectors | Flying vector | 0.012 | −0.681 | Potential source |
| Clonorchis sinensis | Trematoda | High | Food | Fish consumption | 0.011 | −0.125 | Occasional source |
| Echinostoma spp. | Trematoda | Moderate | Food | Fish consumption | 0.011 | 0.176 | Occasional source |
| Ross River virus | Virus | Moderate | Vectors | Flying vector | 0.010 | 0.000 | Potential source |
| Campylobacter fetus | Bacteria | Low | Food | Animal product | 0.010 | −0.301 | Potential source |
| Entamoeba histolytica | Protozoa | High | Environment | Unsanitary conditions | 0.009 | −0.192 | Occasional source |
| Yersinia enterocolitica | Bacteria | Moderate | Food | Animal product | 0.009 | −1.041 | Occasional source |
| Japanese encephalitis virus | Virus | Priority | Vectors | Flying vector | 0.007 | −0.176 | Potential source |
| Schistosome cercariae | Trematoda | Moderate | Environment | Waterborne | 0.007 | 0.000 | Occasional source |
| Yersinia pseudotuberculosis | Bacteria | Moderate | Food | Animal product | 0.007 | −0.602 | Potential source |
| Salmonella bongori | Bacteria | Moderate | Food | Animal product | 0.007 | 0.000 | Potential source |
| Rotavirus | Virus | High | Environment | Unsanitary conditions | 0.007 | −0.301 | Potential source |
| Mycobacterium bovis | Bacteria | Priority | Animals | Animal product | 0.007 | −0.845 | Occasional source |
| Staphylococcus aureus MR | Bacteria | Priority | Animals | Close contact | 0.006 | −1.439 | Secondary source |
| Hantavirus | Virus | Priority | Environment | Inhalation | 0.006 | −0.301 | Potential source |
| Hepatitis E virus | Virus | High | Food | Animal product | 0.006 | −0.410 | Occasional source |
| Escherichia coli | Bacteria | Priority | Environment | Unsanitary conditions | 0.006 | −1.010 | Secondary source |
| Rift Valley fever virus | Virus | Priority | Vectors | Flying vector | 0.005 | −0.602 | Occasional source |
| Pseudomonas aeruginosa | Bacteria | Moderate | Animals | Close contact | 0.005 | −0.916 | Secondary source |
| Schistosoma mansoni | Trematoda | High | Environment | Waterborne | 0.005 | 0.000 | Potential source |
| Mycobacterium ulcerans | Bacteria | Moderate | Environment | Soil transmitted | 0.004 | 0.000 | Potential source |
| Salmonella enterica | Bacteria | Priority | Food | Animal product | 0.004 | −0.778 | Secondary source |
| Pneumocystis jirovecii | Fungi | High | Animals | Inhalation | 0.004 | −0.301 | Potential source |
| Salmonella typhimurium | Bacteria | High | Food | Animal product | 0.004 | −1.190 | Potential source |
| Listeria monocytogenes | Bacteria | Priority | Food | Animal product | 0.004 | −0.970 | Potential source |
| Bacillus anthracis | Bacteria | Priority | Environment | Soil transmitted | 0.004 | −0.301 | Potential source |
| Candida spp. | Fungi | High | Animals | Close contact | 0.003 | −0.699 | Potential source |
| Vibrio cholerae | Bacteria | High | Environment | Unsanitary conditions | 0.002 | 0.000 | Potential source |
| Lassa virus | Virus | Priority | Animals | Close contact | 0.002 | 0.000 | Potential source |
| Aeromonas hydrophila | Bacteria | Moderate | Environment | Waterborne | 0.001 | 0.000 | Potential source |
| Burkholderia pseudomallei | Bacteria | Priority | Environment | Soil transmitted | 0.001 | −0.301 | Potential source |
| Burkholderia mallei | Bacteria | Priority | Animals | Close contact | 0.000 | 0.000 | Potential source |
A first logistic binomial regression model was selected to evaluate the effects of pathogens' “taxonomic groups”, “transmission pathways” and “health impact” on the probability of mentioning dogs in scientific publications, considering articles “with dogs” as the number of successes out of a “total” number of trials. As a potential epidemiological bridge host frequently involved in zoonotic transmissions [63], the pig was then selected as a reference control species to compare the overall involvement of the dog in the transmission of recognized pathogens to humans. A second logistic binomial regression model was then used to examine the effect of the same explanatory variables on the probability of citing “dog(s)” (coded as success) compared to “pig(s)” (coded as failure). This choice was further supported by bibliometric data, as pigs were the second most frequently cited mammalian species in the Web of Science database in the context of zoonotic transmission. The models including the interaction, selected using Akaike's Information Criterion (AIC), have a residual deviance of 47,403 and 21,316, respectively (with 245 and 229° of freedom) versus a null deviance of 137,487 (Model 1) and 61,623 (Model 2), indicating a substantial fit to the data. For these two statistical models, only the 310 pathogens cited in at least 50 publications were retained to minimize biases caused by small sample sizes. Additionally, 16 extra pathogens, for which dogs and pigs were cited in fewer than 5 articles in total, were excluded from Model 2.
Finally, a third logistic binomial regression model was used to examine the effect of the same explanatory variables on the probability of citing stray dogs (as a success) compared to pet dogs (as a failure). This time, only the 141 pathogens mentioned in at least 5 publications, citing either “pet dogs” and/or “stray dogs,” were retained for this last model, which fitted the data accurately after AIC minimum selection (Model 3 residual deviance of 403 with 85 df against 1406 initially). Using the “dplyr,” “emmeans”, “gt,” and “ggplot2” packages, model summary tables and predicted probability plots were created on R software (version 4.3.1) for the three models (Bibliometric analysis code and Model summaries available in the Supporting Information 2). To perform a cross-validation of bibliographic and bibliometric data, a Spearman correlation test was conducted to assess the relationship between the ordinal variable “Canine zoonotic potential” and the “Dog's part” index, whose distribution is shown in Figure 2.
Figure 2.

Distribution of “Dog's part” mean by zoonotic potential of dogs.
3. Results
3.1. Representative List of Zoonotic Pathogens Transmitted by Dogs
Literature searches revealed 152 pathogens that C. lupus familiaris is able to transmit to humans, representing almost half of the zoonotic agents listed in our study. Dogs play the role of primary host for human transmission for 44 of them, while they may act as a secondary zoonotic source for 60 pathogens and are occasionally involved in the transmission of the remaining 48. To our knowledge, no documented cases of zoonotic transmission by dogs have been reported under natural conditions for the remaining 185 listed pathogens, although 117 of them appear capable of infecting dogs. Among these, dogs may pose a potential zoonotic risk for an additional 46 pathogens, as canine competence remains neither confirmed nor ruled out due to conflicting sources or studies demonstrating transmission potential only under laboratory conditions. Figures 3 and 4 show the proportion of zoonotic pathogens transmitted by dogs across the list, by taxonomic groups and by routes of transmission, respectively.
Figure 3.

Number of zoonotic pathogens by taxonomic groups.
Figure 4.

Number of zoonotic pathogens by transmission pathways.
Figure 3 highlights some taxonomic groups with a higher proportion of zoonotic pathogens transmitted by dogs than others (χ2p-value = 2.558e–04), particularly helminths (adjusted χ2 residuals = 1.98). Conversely, the proportion of viruses for which dogs are competent hosts is significantly lower than expected (adjusted χ2 residuals = −2.82). Figure 4 shows that the proportion of zoonotic pathogens transmitted by dogs varies according to the mode of transmission of infectious agents (χ2p-value = 1.156e–06). Dogs are particularly competent for most pathogens transmitted through food consumption (especially fish or seafood: adjusted χ2 residuals = 1.99), whereas they are generally not competent for those transmitted through direct contact with animals, except in the case of bite inoculations (adjusted χ2 residuals = 1.28). See details of the results of χ2 test by zoonotic potential of dogs in the Supporting Information 2 (χ2 statistic = 97.4; df = 40; p-value = 1.098e–06).
3.2. Bibliometric Analysis to Assess the Pathogen/Dog Association
Figure 1 presents the number of publications citing domesticated host species, major wild reservoirs, and arthropod vectors. It shows that dogs are the most cited animal compartment in the context of zoonotic transmissions, in more than one in seven publications, ahead of pigs, cattle and cats. Pigs, reported at levels comparable to those of dogs, will later be used as a control for comparison with livestock species.
The bibliometric analysis conducted on the WoS Core Collection database measured the proportion of publications mentioning the term “dog” for each of the listed pathogens, thereby identifying the zoonotic agents most associated with C. lupus familiaris in the scientific literature. At the top of the ranked list, as shown in Table 1, are Helicobacter canis, Trichuris vulpis, Ehrlichia canis, Capnocytophaga canimorsus, Staphylococcus pseudintermedius, B. canis, Dipylidium caninum, Uncinaria stenocephala, Bartonella vinsonii berkhoffii, and Anaplasma platys. In addition to this top 10, dogs are mentioned in at least one out of every two publications (Dog's Part Index > 0.5) for 15 other pathogens, compared to only three pathogens for pigs. Among the pathogens cited in at least 50 publications, 77 had a Dog's Part Index exceeding 0.1, whereas pigs were mentioned in more than one in 10 articles for only 42 listed pathogens. Comparatively, the dog index is twice as high as the pig index when averaged across all listed zoonotic pathogens (mean Dog's part = 0.105; mean Pig's part = 0.053). Most pathogens listed have more mentions of pigs than dogs (DogPig_part's > 0 for 139 zoonotic agents compared to 165). However, dogs are cited at least 10 times more than pigs for 56 pathogens, while pigs are cited 10 times more than dogs for half as many (DogPig_part's < 1 for 24 pathogens). Compared to pigs, these results suggest that dogs hold a relatively important place in the epidemiological dynamics of the pathogens they are associated with.
As a cross-validation of the classification established in the previous section, the Spearman's correlation test indicates a very significant positive relationship between “Dogs part” index and Zoonotic potential of dogs (p-value < 2.2 × 10⁻16; rho = 0.668). Thus, we observe in Figure 2 that pathogens for which dogs serve as the primary source of zoonotic infections have a relatively high Dog's part mean of 0.495, although the index exhibits considerable variability (standard deviation (sd) = 0.222). This value progressively decreases depending on the role of dogs in pathogen transmission: 0.117 when dogs act as secondary transmission hosts (sd = 0.105), 0.056 for pathogens that dogs occasionally transmit to humans (sd = 0.089), 0.044 for potential but unconfirmed zoonotic sources (sd = 0.076), and finally, 0.022 for pathogens that dogs do not transmit to humans (sd = 0.031).
Binomial logistic regression Models 1 and 2 demonstrated a significant effect (p-value < 2.2 × 10⁻16) of taxonomic groups, transmission routes, health impact, and their interactions, on the probability of mentioning dogs, respectively, on total publications or compared to pigs. Dogs were three times more likely to be cited in publications referencing pathogens with low (p=0.059) or moderate (p=0.043) public health impacts than in those concerning pathogens of high (p=0.015) or priority (p=0.016) importance. It is worth noting that this trend is not as pronounced for pigs, even though Model 2 does not indicate significant differences between the two host species in terms of probabilities. Additionally, rickettsial organisms, cestodes, and nematodes were frequently associated with dogs in the scientific literature, exhibiting significantly higher predicted probabilities of mentions (p=0.183, p=0.124, and p=0.098, respectively in Model 1) compared to other pathogen groups, notably viruses (p=0.011) or bacteria (p=0.019). Comparatively, rickettsial species, protozoa, and helminths are more likely to be cited alongside dogs than pigs (p > 0.5 in Model 2).
The results of the Model 1 indicate that pathogens transmitted through bites (p=0.150), via ectoparasites (p=0.084) or contact with soil (p=0.078), are associated with the highest frequencies of dog mentions (Figure and summary in Supporting Information 2). Moreover, Model 2 shows that dogs are significantly more frequently cited than pigs (p > 0.5) for these three transmission modes, as well as for fish or seafood consumption, flying vector borne and accidental ingestion (Figure 5). Conversely, pathogens transmitted through inhalation (p=0.009 in Model 1) and close contact (p=0.0015 in Model 1), as well as those associated with animal products and poor hygiene, are more frequently linked to pigs (p < 0.5 in Model 2, Figure 5). This suggests that dogs are less commonly cited in these contexts than livestock species. On a broader scale, the frequency of dog citations varies significantly depending on the exposure source considered. Dogs are most frequently mentioned in cases of vector-borne transmission (p=0.042 [0.028; 0.062]), followed by foodborne transmission (p=0.033 [0.027; 0.041]), environmental transmission (p=0.027 [0.018; 0.038]), and finally, direct transmission (p=0.021 [0.017; 0.025]). Model 2 indeed indicates that only vectorial exposure is more strongly associated with dogs than with pigs (p=0.744), whereas environmental and animal exposure sources are primarily linked to pigs (p < 0.5), as can be seen in Figure 5, which compares the “dog” and “pig” citations by transmission pathways.
Figure 5.

Probability of citing “dogs” against “pigs” by transmission pathways.
In a second step, by comparing the number of publications citing the terms “stray dogs” and “pet dogs,” we aim to assess the extent to which each zoonotic pathogen is associated with one or the other canine lifestyle in the scientific literature. The 10 infectious agents with the highest Dog's Partition Index, and thus most frequently associated with stray dogs compared to pet dogs, are as follows: Heterophyes spp., Dioctophyme renale, Toxascaris leonina, D. caninum, Ancylostoma braziliense, Leptospira interrogans Copenhageni, H. canis, Echinococcus granulosus, Dibothriocephalus latus, and Macracanthorhynchus spp. Conversely, the 10 pathogens most frequently associated with pet dogs compared to stray dogs are: Staphylococcus intermedius, Clostridioides difficile, Staphylococcus aureus, Streptococcus canis, C. canimorsus, S. pseudintermedius, Salmonella typhimurium, Bordetella bronchiseptica, Clostridium perfringens, and Yersinia enterocolitica.
The results of the binomial logistic regression Model 3 assessing the probability of citing “stray dogs” compared to “pet dogs” in publications mentioning pathogens transmitted by dogs are summarized in the Supporting Information 2 across different taxonomic groups, health impacts, and transmission pathways. The deviance analysis indicated significant contributions of the three factors, especially Pathway and Taxonomic group, and their interaction (p-value < 2.2 × 10−16). Zoonoses caused by cestodes (p=0.557), trematodes (p=0.465), nematodes (p=0.428), rickettsiae (p=0409), and protozoa (p=0347) appear to be more frequently associated with stray dogs in the literature, whereas bacteria (p=0.175), fungi (p=0.127), and viruses (p=0.005) are significantly linked to companion dogs. Additionally, no significant differences were found in the predicted probabilities across different levels of public health impact, although companion dogs appear to be associated with more concerning pathogens than stray dogs.
Furthermore, when pathogens are grouped by exposure source, diseases related to direct exposure to “Animals” are significantly less frequently cited in the context of stray dogs compared to other type of exposure (p=0.156 [0.119; 0.202]). Specifically, pathogens transmitted through direct interactions with animals, such as inhalation (p=0.089), close contact (p=0.053) or bite inoculation (p=0.204), demonstrated significantly lower predicted probabilities at the 95% confidence level and were therefore more frequently associated with pet dogs (Figure 6). Conversely, publications reporting pathogens transmitted through fish consumption showed the highest predicted probability of mentioning stray dogs compared to pet dogs (p=0.533), followed by water contamination (p=0.512) and soil-borne pathogens (p=0.464).
Figure 6.

Probability of citing “stray dogs” against “pet dogs” by transmission pathways.
4. Discussion
4.1. Functional Roles, Host Status, and Scientific Representations of Dogs in Zoonotic Transmission
This review highlights the epidemiological significance of C. lupus familiaris as the most frequently cited host species in the context of animal-to-human transmission. This prominence is primarily explained by the species' ecological versatility and ubiquity in domestic environments, where dogs are involved in a wide range of interspecific transmission pathways [43, 63]. In accordance with Morand et al. [10], the proportion of infectious agents shared between dogs and humans is likely the highest in the animal kingdom, largely reflecting the long evolutionary history shared by both species. Despite this apparent centrality, 20% of documented zoonotic pathogens have never been detected in dogs. Moreover, they often act as zoonotic dead-end hosts for nearly half of the listed pathogens, with little or no confirmed human transmission. Nevertheless, our bibliographic analysis indicates that dogs still play a significant role in the infectious dynamics of more than a 100 zoonotic agents, even when they are not essential to pathogen persistence. Indeed, their role in pathogen maintenance clearly extends beyond the 20 zoonotic agents for which they are identified as primary reservoirs.
Even when they do not serve as core maintenance hosts, dogs can facilitate the circulation of numerous generalist pathogens within multi-host communities. Through their interactions with humans, wildlife, and other domestic animals, they contribute to the formation of maintenance complexes, as described by Haydon et al. [11]. In such systems, dogs often act as relay hosts, spatial vectors, or mechanical carriers, rather than as reservoirs per se. Their pivotal function as an intermediary compartment bridging sylvatic and domestic transmission cycles thus appears to be crucial [64–66]. This intermediary role aligns with the definition of “bridge hosts” proposed by Caron et al. [42], which describes species that sustain continuous epidemiological connections between maintenance reservoirs and final hosts—namely humans. The high density, ecological diversity, and social connectivity of dog populations contribute to this bridging function, enabling sustained spillover potential across ecological and social boundaries.
While lexical counts do not allow for precise estimation of the infectious burden attributable to dogs, bibliometric analysis provides a valuable framework to explore how different transmission pathways are associated with canine populations in the scientific literature. This approach allows for a synthesis of the representations attached to the zoonotic role of dogs and offers interpretative tools to anticipate potential emergence risks. Moreover, it facilitates interspecies comparisons of zoonotic potential, supporting the prioritization of health threats based on their perceived weight and visibility. The comparative analysis between pets and livestock, for instance, lays the groundwork for a functional typology of host species—one based not only on biological traits and lifestyles but also on the scientific representations that shape surveillance strategies. Despite a similar publication volume on zoonotic agents when compared to pigs or cattle, dogs appear to be associated with a broader spectrum of pathogens and transmission mechanisms, suggesting a particularly extensive involvement in infectious dynamics. This overrepresentation is especially marked for certain taxonomic groups, such as cestodes, nematodes, and rickettsiae, and for specific transmission routes. While dogs are often implicated in vector-borne, environmental, and bite-related zoonoses, livestock—primarily represented by pigs—tend to be more frequently involved in foodborne, hygiene-related, and close-contact transmissions, reflecting the exposure contexts typical of farming systems.
4.2. Canine Ecotypes and Their Epidemiological Roles in Zoonotic Transmission
The global dog population displays considerable ecological heterogeneity, with individuals variably connected to both pathogen maintenance complexes and human populations, depending on their lifestyle and level of integration [44, 45]. This diversity is rarely reflected in review studies, which often rely on simplified classifications. For methodological consistency, our analysis focused on the two most frequently cited terms in the corpus: pet dog and stray dog, used as proxies for the two ends of the ecotypic gradient. Other categories commonly employed in field studies—such as free-roaming, community, owned, or unrestrained—were too inconsistently cited to support robust comparisons. This limited lexical scope reveals a pronounced polarization in scientific representations of zoonotic risk. Pathogens associated with environmental or parasitic transmission are more frequently linked to stray dogs, often portrayed as diffuse sources of contamination outside human control structures. In contrast, pet dogs are more commonly associated with bacterial infections transmitted through close contact, such as bites or licking. These distinctions help shape contrasting epidemiological profiles: stray dogs are perceived as external, unregulated threats, while pet dogs are seen as intimate companions, potentially facilitating pathogen adaptation within household environments.
Ecological evidence supports this dichotomy. Stray dogs, due to frequent exposure to contaminated environments and the lack of routine veterinary care, are prone to accumulating and disseminating resilient pathogens through their interactions with multi-host systems [51, 67]. Conversely, companion dogs, although generally less exposed to environmental reservoirs, remain deeply embedded in human social spaces. Their proximity to humans creates repeated opportunities for direct transmission and may promote the gradual adaptation of pathogens to human hosts [14, 68, 69]. As the final interface before human infection, the role of pet dogs as potential zoonotic amplifiers should not be underestimated. These findings highlight the importance of integrating ecotype-specific characteristics into zoonotic risk assessment. From a public health perspective, tailored interventions are needed to address the distinct functions of each ecotype within transmission networks. Stray dogs could be prioritized in deworming campaigns aimed at reducing environmental parasitic loads, while in contexts of viral emergence, restrictions on close human–pet interactions may be necessary. More broadly, acknowledging the functional diversity of dogs is essential to developing health management strategies within an ecosystemic framework.
Bibliometric analyses remain heavily dependent on the explicit use of keywords such as dog, stray, and pet, which may reflect editorial conventions rather than precise epidemiological distinctions. The lack of standardized terminology for intermediate profiles makes them difficult to identify automatically and restricts analysis to a binary model. While such lexical simplification is operationally useful, it hampers the classification of ecotypes and limits the ability to accurately represent the complexity of canine populations in real-world contexts, particularly in rural and peri-urban settings, where ownership, mobility, and control are often ambiguous. Despite being underrepresented in the literature, intermediate canine profiles such as free-roaming owned dogs likely play a key epidemiological role. These dogs are omnipresent across rural, peri-urban, and urban environments and often maintain interactions with both confined pets and unregulated stray populations. Acting as epidemiological connectors, they may facilitate the movement of pathogens across ecological and social boundaries [38, 44, 70, 71]. As such, interconnected and sympatric canine subpopulations could contribute to each stage of the species barrier crossing [72], progressively bringing wildlife-origin pathogens closer to human settlements [38, 43] and amplifying the risk of spillover.
4.3. Fecal Contamination and Environmental Transmission
Dogs frequently serve as definitive hosts for a wide diversity of helminth species, shedding infective stages (e.g., eggs or larvae) into the environment [51, 59], where they can persist for extended periods and further infect humans through soil, water, or food contamination [34, 73]. These parasites have prolonged life cycles and exceptional environmental resilience. This allows them to persist in human habitats, facilitates continuous transmission, even in the absence of direct host-to-host contact [74]. For instance, Toxocara canis, Trichuris vulpis, and several Ancylostomatidae—nematode species highly specialized for canine hosts—can survive in the soil for months to years, creating long-lasting sources of exposure [75, 76].
Moreover, stray dogs are more frequently mentioned in the literature for environmentally transmitted helminths, which supports their role in maintaining resistant parasites through open defecation in domestic habitats, public spaces and cultivated agricultural areas [77–81]. The risks of contamination of water sources, other domestic animals and crops, then appear to be particularly high. Beyond passive fecal–oral transmission, stray dog populations actively contribute to the completion of heteroxenous parasitic cycles through their predatory and opportunistic behavior towards intermediate hosts (e.g., aquatic prey, rodents, and livestock carcasses) [38]. The spread of pathogens such as Echinococcus spp. and Fish-borne Zoonotic Trematodes [82–84] is therefore facilitated. In the absence of deworming treatments, roaming dogs, which are more frequently exposed to contaminated environments, could then serve as key local reservoirs, supporting the transmission of neglected tropical diseases by significantly increasing the parasitic load in favorable wetland ecosystems [51, 67, 85].
To mitigate the role of stray and free-roaming dogs in the persistence and transmission of environmental parasites, targeted control strategies must be implemented. Large-scale deworming campaigns should be prioritized for these high-risk canine populations to reduce the environmental burden of helminths and limit parasite dissemination [86]. Improving sanitation infrastructures, including proper waste disposal and the management of dog feces in urban and peri-urban areas, appears to be essential to curbing soil and water contamination [78, 87]. Finally, community awareness programs can encourage responsible pet ownership by promoting movement control and appropriate veterinary monitoring and avoiding abandonment [88, 89].
4.4. Direct Exposure to Animals and Close Contact Transmission
Our bibliographic research indicates that dogs are highly competent hosts for most zoonotic pathogens transmitted via bites or scratches. Dogs indeed play a major epidemiological role in the transmission of rabies [90], as well as in numerous bacterial superinfections resulting from bite wounds (Capnocytophaga spp., Staphylococcus spp., Pasteurella spp., and Streptococcus spp.) [17, 18]. As a result, they are frequently mentioned in scientific publications focusing on these biological agents, particularly in comparison with domesticated artiodactyls, such as pigs, cattle, and small ruminants.
However, the overall epidemiological involvement of dogs in other forms of direct animal-to-human transmission seems limited. Apart from a few canine-adapted bacteria with which they have co-evolved, such as H. canis, B. canis, and Corynebacterium auriscanis, dogs rarely act as efficient vectors for airborne or close-contact zoonotic infections. This explains their overall weak association with viruses (and, to a lesser extent, bacteria, and fungi) in the scientific literature, in accordance with the data presented by Olival et al. [91] and Han et al. [92]. Indeed, pathogens with low environmental persistence generally rely on frequent host-to-host interactions for transmission [93, 94]. For this reason, their favored hosts are species that form dense populations in the wild, such as bats [95], or those raised in large numbers in intensive farming systems [96]—two conditions that typically do not apply to canine populations. While dogs remain competent hosts for many of these pathogens, they are less frequently implicated in epidemiological cycles requiring high infectious pressure for zoonotic transmission. In contexts of poor hygiene conditions or contamination of animal products, the role of dogs appears secondary to that of the livestock species, as represented by pigs in our study. This is particularly the case for bacteria with broad host spectra (e.g., Salmonella spp., Clostridium spp., Campylobacter spp., EHEC, and antibiotic-resistant strains), whose transmission is primarily facilitated in high-density farming environments [97]. Comparative studies should thus refine species-specific intervention strategies according to the associated risks, such as deworming programs for dogs and biosecurity measures for zoonotic bacteria in livestock farming.
Viruses and bacteria are also significantly less frequently reported in association with stray dogs, whereas companion dogs appear more often in publications related to airborne pathogens, close contact infections, and bites. Enclosed settings and the intimate pet/owner interactions could then promote prolonged and repeated exposure to animals, facilitating the sustained spread of directly communicable pathogens [98–100]. In contrast, while stray dogs may harbor many zoonotic pathogens, they interact less frequently and closely with humans, which reduces direct transmission risks [51]. This pattern supports the broader observation that zoonotic diseases requiring direct contact are more prevalent in domestic environments where livestock and pets represent an increased risk. Meanwhile, stray animals are more frequently associated with environmentally mediated infections due to their higher exposure to persistent sources of contamination.
In high-risk settings, health awareness programs contribute to educating pet owners on bite prevention and wound management [101]. In order to mitigate the risks of canine-origin zoonotic transmission through direct contact, routine veterinary monitoring of companion animals must be put in place, including regular health check-ups [68, 69]. A rational management of antimicrobials administered to dogs will also help preventing the development of antibiotic-resistant bacterial strains [102]. In kennels and shelters, strict hygiene protocols, including disinfection, isolation of symptomatic animals, proper ventilation, and routine veterinary care, are essential to limiting pathogen transmission and ensuring animal health [103].
4.5. Vector-Borne Transmission Pathways
Although dogs appear to transmit only a small proportion of all vector-borne pathogens, they are frequently cited in the scientific literature [27, 104, 105], suggesting a high degree of host specificity for many of these zoonotic agents. This specialization imply that dogs often play a crucial role in the vector-borne transmission cycles in which they are involved, especially for rickettsia species that are well adapted to their main host (e.g., Anaplasma platys or E. canis) [29, 106]. This is indeed particularly true for pathogens transmitted by ticks or fleas, as dogs are significantly less frequently associated with pathogens carried by flying blood-feeding insects. This distinction likely reflects the feeding preferences and ecological niches of different arthropod vectors [107, 108]. Although canine populations contribute to the maintenance of pathogens transmitted by mosquitoes, sandflies, and other biting flies, these vectors generally transmit infections to humans without direct involvement of dogs, as observed with Brugia spp. [109] and Leishmania spp. [110]. Indeed, flying insects opportunistically feed on various mammals, a pattern confirmed by comparisons with pigs, where both species serve at equivalent levels.
No significant differences are also observed at a finer scale between canine ecotypes regarding flying vector-borne pathogens. In contrast, transmission via fleas and ticks appears to be particularly specific to dogs compared to pigs, with pets cited more often than stray dogs in transmission cycles involving ectoparasites. Although this last distinction is not statistically significant, it suggests that companion dogs may play an essential role in transporting and sustaining infected vectors within human households [111, 112]. To mitigate vector-borne zoonotic risks associated with companion dogs, regular antiparasitic treatments, including acaricides and insecticidal collars, are crucial, particularly in endemic areas, to curb the proliferation of ticks and fleas within human settings [113, 114].
Although bibliometric analyses generally align with the actual zoonotic potential of dogs across transmission pathways, their involvement in ectoparasite-borne infections may be somewhat overrepresented relative to their confirmed biological competence. This trend could reflect a persistent symbolic association between dogs and external parasites such as fleas and ticks, shaped by their frequent infestation and reinforced in both scientific and public discourse. In the literature, dogs are on average cited more frequently in connection with tick- and flea-borne zoonoses than with other pathogen groups, despite being competent hosts for only a limited subset of these agents. By cross-referencing bibliometric data with empirical assessments of host competence, this integrative approach makes it possible to identify potential overestimations and gaps in current biological knowledge. It also helps to reveal how sociogeographic representations and taxonomic proximity may influence the visibility of certain host–pathogen associations, highlighting the importance of a critical perspective when interpreting bibliometric signals.
4.6. Evaluation and Relevance of the Bibliometric Approach
Our review demonstrates the value of bibliometric methods in identifying broad epidemiological patterns and host involvement in zoonotic transmission [115, 116]. The publication counts presented in this study primarily reflect the scientific discourse more than confirmed host–pathogen associations. However, targeted literature searches on the role of dogs in the transmission of each pathogen to humans have supported the validity of the results. The strong correlation between the “Dog”s part' index and the degree of zoonotic involvement attributed to dogs (Figure 2) suggests that bibliometric indicators closely mirror the epidemiological patterns described in specialized literature. When paired with a critical assessment of host competence, this dual-review approach helps to identify research gaps with clear implications for public health. Cross-referencing bibliometric data with empirical evidence reveals mismatches between scientific attention and actual epidemiological relevance. In some cases, dogs appear overrepresented in the literature without confirmed zoonotic competence—as illustrated by Toxocara cati or Bartonella henselae, which are primarily associated with cats but occasionally co-cited with dogs. Conversely, well-established associations between dogs and certain pathogens may be underrepresented in publication databases, such as for Ancylostoma ceylanicum or Microsporum canis, where additional transmission cycles exist despite a clearly documented canine role.
These discrepancies underscore the limitations of bibliometric approaches and the importance of integrating eco-epidemiological expertise to avoid interpretative biases. Despite these limitations, bibliometric tools remain valuable for analyzing how host species are represented in the scientific literature. They support the identification of dominant transmission pathways and help anticipate potential emergence risks. Integrating machine learning techniques, such as co-occurrence pattern detection or AI-based text mining, could improve the resolution of host–pathogen association mapping across large bibliographic datasets [117–119]. These tools may help identify overlooked associations or novel risks and refine our understanding of the direct and indirect roles dogs may play in disease transmission cycles. Although lexical counts cannot precisely quantify the infectious burden attributable to dogs, they provide a useful framework for classifying transmission pathways based on host association frequency. This method enables interspecies comparisons and helps prioritize health risks according to both ecological significance and visibility in scientific discourse.
5. Conclusion
This study provides a comprehensive assessment of the zoonotic role of C. lupus familiaris, revealing the diverse transmission pathways through which dogs contribute to disease emergence. By combining a structured pathogen inventory, bibliometric analysis, and epidemiological review, our study identifies key transmission dynamics, underscores research gaps, and informs targeted public health interventions. Our findings demonstrate that canine involvement in pathogen transmission to humans varies significantly depending on the transmission pathways and the socio-ecological contexts in which dogs evolve. They can act as primary, secondary, or occasional transmission hosts for nearly half of the recognized zoonotic agents. Among these pathogens, a great diversity of nematodes, cestodes, and rickettsiae stands out in our study, these taxonomic groups being more frequently associated with dogs in the literature than bacteria and viruses. These significant differences between taxa can be largely explained by the ecological characteristics of pathogens, as dogs are more frequently mentioned in relation to soil-contact transmission, tick, or flea-borne pathways, and bite inoculations.
To mitigate the zoonotic risks associated with different canine ecotypes, targeted public health interventions must be adapted to their specific epidemiological roles. Stray dogs, due to their exposure to wildlife reservoirs and contaminated environments, contribute significantly to the persistence of environmentally transmitted parasites [51, 120] and may act as entry points for emerging pathogens [43, 64]. Integrating them into genomic surveillance networks could enhance early detection of zoonotic threats, particularly in high-risk transmission zones such as squares and urban parks [121–123], livestock farming areas [124, 125], and wetland ecosystems [126]. To control their impact on public health, large-scale deworming campaigns should be implemented [86, 127], alongside waste management and sanitation improvements to reduce fecal–oral transmission and limit soil and water contamination [76, 128]. Conversely, companion dogs, while generally benefiting from better veterinary care, pose higher risks for direct-contact transmission of zoonotic pathogens through bites [129] and close contact [98]. Their prolonged and repeated interactions with humans in enclosed settings favor the transmission of directly communicable pathogens within households [18]. Routine veterinary monitoring of pets, including antimicrobial-resistant bacteria surveillance, and responsible pet ownership practices are essential to reduce these risks [68, 69, 130]. Moreover, their close cohabitation with their owners makes them ideal epidemiological sentinels [131–133]—targeted serological surveillance of pet dogs could provide valuable insights into human exposure risks and help detect pathogens with a high potential for zoonotic spillover, including viruses [50]. By tailoring health strategies to different canine ecotypes, zoonotic risks can be effectively controlled, reducing the global burden of dog-mediated zoonoses.
More broadly, the findings of this review indicate that the figure of the “zoonotic dog” constructed in scientific literature aligns most closely with the profile of stray dogs, suggesting a dominant perception of dogs as exogenous threats. This polarization of representations is not without consequence: it structures societal relationships with different categories of dogs, influences perceived dangerousness, and justifies often asymmetrical management policies. Yet, this binary vision—though operationally convenient—tends to obscure intermediate profiles whose epidemiological contributions may be equally significant. It also reflects deep-rooted cognitive and cultural biases that steer surveillance and public health efforts toward certain types of dogs at the expense of a more nuanced, context-sensitive understanding of zoonotic risks. These results thus call for a deconstruction of the homogeneous image of “the Dog” as a zoonotic host. They call for a recontextualization of ecotypic representations within their specific social, territorial, and biological settings, in order to refine prevention strategies and better capture the complexity of the canine epidemiological interface.
This review introduces the concept of a canine epidemiological gateway, emphasizing the role of dogs in facilitating the transmission of environmental pathogens to humans. Each dog ecotype—defined by its lifestyle, mobility, social integration, and access to veterinary care—contributes differently to the emergence and spread of zoonotic agents. A refined classification of these ecotypes, incorporating key behavioral and ecological traits, would improve our ability to identify their specific roles in pathogen transmission [46, 47, 134]. To support this effort, scientific publications should adopt a precise and consistent terminology that allows for clearer attribution of dog categories to distinct zoonotic pathways. A better understanding of these ecotype-specific dynamics is essential for improving zoonotic risk assessments and guiding targeted disease control strategies. For example, free-roaming owned dogs may serve as key epidemiological links between wild and domestic settings [135]. Their high mobility increases their exposure to contaminated environments, while regular human contact enhances their potential as direct transmission vectors [85]. These characteristics make them potential facilitators of pathogen adaptation and dissemination across multispecies networks, underscoring the need for further investigation [136].
Advancing this framework requires a combination of modeling and field-based approaches. Spatial models should be strengthened to identify geographic hotspots where dogs contribute to pathogen spillover [137–139], while GPS tracking can help quantify contact patterns between dogs, wildlife, livestock, and humans, thus informing intervention strategies [140, 141]. In parallel, behavioral and socioeconomic studies are needed to examine how hygiene practices, access to veterinary care, and human–dog relationships influence zoonotic transmission risks. Coupling these empirical approaches with bibliometric data could enhance the predictive value of literature-based tools and support more targeted health measures [142–144]. This integrated strategy helps bridge the gap between large-scale bibliometric evidence and operational zoonotic risk assessment. It supports the development of ecotype-specific interventions that reflect the diversity of epidemiological roles across dog populations. A coordinated, evidence-based approach—combining surveillance, prevention, and targeted responses—is critical to reduce the global burden of dog-mediated zoonoses. To this end, canine populations should be systematically included in One Health biosurveillance frameworks, leveraging their epidemiological significance to improve outbreak detection, prevent disease emergence, and inform control strategies at the human–animal–environment interface.
Data Availability Statement
All data used in this study are publicly available through the Web of Science Core Collection bibliographic database (Clarivate). The list of publications included in the bibliometric analysis is compiled and referenced in Table 1 of the manuscript.
Conflicts of Interest
The authors declare no conflicts of interest.
Funding
Thibaut Langlois and Michel de Garine-Wichatitsky were supported by a research grant from the French National Research Agency (ANR-19-ASIE-0002, Project SEA-dog-SEA), and Thibaut Langlois, employed by the University of Montpellier, was supported by dP GREASE network (Gestion des Risques Emergents en Asie du Sud-Est) coordinated by the CIRAD/Kasetsart University (https://www.grease-network.org). Sylvie Hurtrez-Boussès is employed by University of Montpellier, and part of this work has been also supported by CNRS and IRD.
Supporting Information
Additional supporting information can be found online in the Supporting Information section.
Table S1: List of zoonotic pathogens.
χ2 adjusted standardized residuals. Probability graph of citing “dogs” and “pigs” on the total by transmission pathways. Summary, Results, Analysis of deviance, and Predicted probabilities of Model 1. Summary, Results, Analysis of deviance, and Predicted probabilities of Model 2. Summary, Results, Analysis of deviance, and Predicted probabilities of Model 3. Zoonotic pathogens list analysis code. Bibliometric analysis code.
References
- 1.Rahman M. T., Sobur M. A., Islam M. S., et al. Zoonotic Diseases: Etiology, Impact, and Control. Microorganisms . 2020;8(9) doi: 10.3390/microorganisms8091405.1405 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 2.Di Bari C., Venkateswaran N., Fastl C., et al. The Global Burden of Neglected Zoonotic Diseases: Current State of Evidence. One Health . 2023;17 doi: 10.1016/j.onehlt.2023.100595.100595 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3.Johnson C. K., Hitchens P. L., Pandit P. S., et al. Global Shifts in Mammalian Population Trends Reveal Key Predictors of Virus Spillover Risk. Proceedings of the Royal Society B: Biological Sciences . 2020;287(1924) doi: 10.1098/rspb.2019.2736.20192736 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 4.Chomel B. B. Emerging and Re-Emerging Zoonoses of Dogs and Cats. Animals . 2014;4(3):434–445. doi: 10.3390/ani4030434. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 5.Jacob J., Lorber B., Schlossberg D. Diseases Transmitted by Man’s Best Friend: The Dog. Microbiology Spectrum . 2015;3(4) doi: 10.1128/microbiolspec.IOL5-0002-2015.IOL5-0002-2015 [DOI] [PubMed] [Google Scholar]
- 6.Jose T., Joseph A. Domestic Animals and Zoonosis: A Review. Pharma Innovation . 2020;9(8S):27–29. [Google Scholar]
- 7.Whitfield Y., Smith A. Household Pets and Zoonoses. Environmental Health Review . 2014;57(2):41–49. doi: 10.5864/d2014-021. [DOI] [Google Scholar]
- 8.Tomori O., Oluwayelu D. O. Domestic Animals as Potential Reservoirs of Zoonotic Viral Diseases. Annual Review of Animal Biosciences . 2023;11(1):33–55. doi: 10.1146/annurev-animal-062922-060125. [DOI] [PubMed] [Google Scholar]
- 9.Cleaveland S., Laurenson M. K., Taylor L. H. Diseases of Humans and Their Domestic Mammals: Pathogen Characteristics, Host Range and the Risk of Emergence. Philosophical Transactions of the Royal Society of London. Series B: Biological Sciences . 2001;356(1411):991–999. doi: 10.1098/rstb.2001.0889. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Morand S., McIntyre K. M., Baylis M. Domesticated Animals and Human Infectious Diseases of Zoonotic Origins: Domestication Time Matters. Infection, Genetics and Evolution . 2014;24:76–81. doi: 10.1016/j.meegid.2014.02.013. [DOI] [PubMed] [Google Scholar]
- 11.Haydon D. T., Cleaveland S., Taylor L. H., Laurenson M. K. Identifying Reservoirs of Infection: A Conceptual and Practical Challenge. Emerging Infectious Diseases . 2002;8(12):1468–1473. doi: 10.3201/eid0812.010317. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 12.Macpherson C. Dogs, Zoonoses and Human Health: A Global Perspective. CABI . 2012 [Google Scholar]
- 13.Bryce C. M. Dogs as Pets and Pests: Global Patterns of Canine Abundance, Activity, and Health. Integrative and Comparative Biology . 2021;61(1):154–165. doi: 10.1093/icb/icab046. [DOI] [PubMed] [Google Scholar]
- 14.Overgaauw P. A. M., Vinke C. M., van Hagen M. A. E., Lipman L. J. A. A One Health Perspective on the Human–Companion Animal Relationship With Emphasis on Zoonotic Aspects. International Journal of Environmental Research and Public Health . 2020;17(11) doi: 10.3390/ijerph17113789.3789 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Pearce-Duvet J. M. C. The Origin of Human Pathogens: Evaluating the Role of Agriculture and Domestic Animals in the Evolution of Human Disease. Biological Reviews . 2006;81(3):369–382. doi: 10.1017/S1464793106007020. [DOI] [PubMed] [Google Scholar]
- 16.Cunningham-Smith P., Emery K. Dogs and People: Exploring the Human-Dog Connection. Journal of Ethnobiology . 2020;40(4):409–413. doi: 10.2993/0278-0771-40.4.409. [DOI] [Google Scholar]
- 17.Abrahamian F. M., Goldstein E. J. C. Microbiology of Animal Bite Wound Infections. Clinical Microbiology Reviews . 2011;24(2):231–246. doi: 10.1128/CMR.00041-10. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Ghasemzadeh I., Namazi S. H. Review of Bacterial and Viral Zoonotic Infections Transmitted by Dogs. Journal of Medicine and Life . 2015;c(4):1–5. [PMC free article] [PubMed] [Google Scholar]
- 19.Hampson K., Coudeville L., Lembo T., et al. Estimating the Global Burden of Endemic Canine Rabies. PLOS Neglected Tropical Diseases . 2015;9(4) doi: 10.1371/journal.pntd.0003709.e0003709 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Hensel M. E., Negron M., Arenas-Gamboa A. M. Brucellosis in Dogs and Public Health Risk. Emerging Infectious Diseases . 2018;24(8):1401–1406. doi: 10.3201/eid2408.171171. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21.Santos R. L., Souza T. D., Mol J. P. S., Eckstein C., Paíxão T. A. Canine Brucellosis: An Update. Frontiers in Veterinary Science . 2021;8 doi: 10.3389/fvets.2021.594291.594291 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.Rojas P., Monahan A. M., Schuller S., Miller I. S., Markey B. K., Nally J. E. Detection and Quantification of Leptospires in Urine of Dogs: A Maintenance Host for the Zoonotic Disease Leptospirosis. European Journal of Clinical Microbiology & Infectious Diseases . 2010;29(10):1305–1309. doi: 10.1007/s10096-010-0991-2. [DOI] [PubMed] [Google Scholar]
- 23.Altheimer K., Jongwattanapisan P., Luengyosluechakul S., et al. Leptospira Infection and Shedding in Dogs in Thailand. BMC Veterinary Research . 2020;16(1) doi: 10.1186/s12917-020-2230-0.89 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 24.Celina S. S., Cerný J. D. Coxiella Burnetii in Ticks, Livestock, Pets and Wildlife: A Mini-Review. Frontiers in Veterinary Science . 2022;9 doi: 10.3389/fvets.2022.1068129.1068129 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Ferrara G., Flores-Ramirez G., Palkovicova K., et al. Serological and Molecular Survey of Q Fever in the Dog Population of the Campania Region, Southern Italy. Acta Tropica . 2024;257 doi: 10.1016/j.actatropica.2024.107299.107299 [DOI] [PubMed] [Google Scholar]
- 26.Nguyen V.-L., Dantas-Torres F., Otranto D. Canine and Feline Vector-Borne Diseases of Zoonotic Concern in Southeast Asia. Current Research in Parasitology & Vector-Borne Diseases . 2021;1 doi: 10.1016/j.crpvbd.2020.100001.100001 [DOI] [Google Scholar]
- 27.de Macedo L. O., Bezerra-Santos M. A., Filho C. R. C. U., et al. Vector-Borne Pathogens of Zoonotic Concern in Dogs From a Quilombola Community in Northeastern Brazil. Parasitology Research . 2022;121(11):3305–3311. doi: 10.1007/s00436-022-07661-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Marshet B., Dessie D. A Review on Canine Ehrlichiosis and Its Zoonotic Implications. International Journal of Veterinary Sciences and Animal Husbandry . 2020;5(3):36–42. [Google Scholar]
- 29.Aziz M. U., Hussain S., Song B., Ghauri H. N., Zeb J., Sparagano O. A. Ehrlichiosis in Dogs: A Comprehensive Review About the Pathogen and Its Vectors With Emphasis on South and East Asian Countries. Veterinary Sciences . 2023;10(1) doi: 10.3390/vetsci10010021.21 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 30.Anvari D., Narouei E., Daryani A., et al. The Global Status of Dirofilaria Immitis in Dogs: A Systematic Review and Meta-Analysis Based on Published Articles. Research in Veterinary Science . 2020;131:104–116. doi: 10.1016/j.rvsc.2020.04.002. [DOI] [PubMed] [Google Scholar]
- 31.Atapattu U., Koehler A. V., Huggins L. G., Wiethoelter A., Traub R. J., Colella V. Dogs are Reservoir Hosts of the Zoonotic Dirofilaria sp. ‘Hongkongensis’ and Potentially of Brugia sp. Sri Lanka Genotype in Sri Lanka. One Health . 2023;17 doi: 10.1016/j.onehlt.2023.100625.100625 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32.Hassan M’awia M., Osman O. F., El-Raba’a F. M. A., Schallig H. D. F. H., Elnaiem D.-E. A. Role of the Domestic Dog as a Reservoir Host of Leishmania Donovani in Eastern Sudan. Parasites & Vectors . 2009;2(1) doi: 10.1186/1756-3305-2-26.26 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 33.Vilas-Boas D. F., Nakasone E. K. N., Gonçalves A. A. M., et al. Global Distribution of Canine Visceral Leishmaniasis and the Role of the Dog in the Epidemiology of the Disease. Pathogens . 2024;13(6) doi: 10.3390/pathogens13060455.455 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.Pal M., Tolawak D. A Comprehensive Review on Major Zoonotic Parasites From Dogs and Cats. International Journal of Medical Parasitology and Epidemiology Sciences . 2023;4(1):3–11. doi: 10.34172/ijmpes.2023.02. [DOI] [Google Scholar]
- 35.World Health Organization. Global Report on Neglected Tropical Diseases 2024 . World Health Organization; 2024. [Google Scholar]
- 36.Toews E., Musiani M., Checkley S., Visscher D., Massolo A. A Global Assessment of Echinococcus Multilocularis Infections in Domestic Dogs: Proposing a Framework to Overcome Past Methodological Heterogeneity. International Journal for Parasitology . 2021;51(5):379–392. doi: 10.1016/j.ijpara.2020.10.008. [DOI] [PubMed] [Google Scholar]
- 37.Alvi M. A., Alsayeqh A. F. Food-Borne Zoonotic Echinococcosis: A Review With Special Focus on Epidemiology. Frontiers in Veterinary Science . 2022;9 doi: 10.3389/fvets.2022.1072730.1072730 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 38.Roldan J. A. M., Otranto D. Zoonotic Parasites Associated With Predation by Dogs and Cats. Parasites & Vectors . 2023;16(1) doi: 10.1186/s13071-023-05670-y.55 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39.Hung N., Madsen H., Fried B. Global Status of Fish-Borne Zoonotic Trematodiasis in Humans. Acta Parasitologica . 2013;58(3):231–258. doi: 10.2478/s11686-013-0155-5. [DOI] [PubMed] [Google Scholar]
- 40.Traub R. J., Zendejas-Heredia P. A., Massetti L., Colella V. Zoonotic Hookworms of Dogs and Cats – Lessons From the Past to Inform Current Knowledge and Future Directions of Research. International Journal for Parasitology . 2021;51(13-14):1233–1241. doi: 10.1016/j.ijpara.2021.10.005. [DOI] [PubMed] [Google Scholar]
- 41.Tenorio J. C. B., Tabios I. K. B., Inpankaew T., et al. Ancylostoma Ceylanicum and Other Zoonotic Canine Hookworms: Neglected Public and Animal Health Risks in the Asia-Pacific Region. Animal Diseases . 2024;4(1) doi: 10.1186/s44149-024-00117-y.11 [DOI] [Google Scholar]
- 42.Caron A., Cappelle J., Cumming G. S., de Garine-Wichatitsky M., Gaidet N. Bridge Hosts, A Missing Link for Disease Ecology in Multi-Host Systems. Veterinary Research . 2015;46(1) doi: 10.1186/s13567-015-0217-9.83 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 43.Gamble A., Olarte-Castillo X. A., Whittaker G. R. Backyard Zoonoses: The Roles of Companion Animals and Peri-Domestic Wildlife. Science Translational Medicine . 2023;15(718) doi: 10.1126/scitranslmed.adj0037.eadj0037 [DOI] [PubMed] [Google Scholar]
- 44.Hughes J., Macdonald D. W. A Review of the Interactions Between Free-Roaming Domestic Dogs and Wildlife. Biological Conservation . 2013;157:341–351. doi: 10.1016/j.biocon.2012.07.005. [DOI] [Google Scholar]
- 45.Smith L. M., Hartmann S., Munteanu A. M., Villa P. D., Quinnell R. J., Collins L. M. The Effectiveness of Dog Population Management: A Systematic Review. Animals . 2019;9(12) doi: 10.3390/ani9121020.1020 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 46.Dorji T., Tenzin T., Rinzin K., Phimpraphai W., De Garine-Wichatitsky M. Community Perceptions of Free-Roaming Dogs and Management Practices in Villages at the Periphery of a Protected Area in Bhutan. Chiang Mai University Journal of Natural Sciences . 2020;19(2):293–313. doi: 10.12982/CMUJNS.2020.00020. [DOI] [Google Scholar]
- 47.Dorji T., Tenzin T., Rinzin K., Mahat H., Phimpraphai W., de Garine-Wichatitsky M. A Preliminary Survey of Pet Dogs Roaming Behaviour in the Periphery of Protected Area in Bhutan: A Case Study in Haa District. Bhutan Journal of Natural Resources and Development . 2022;9(2):13–26. doi: 10.17102/cnr.2022.76. [DOI] [Google Scholar]
- 48.Jensen P. The Behavioural Biology of Dogs . CABI; 2007. [Google Scholar]
- 49.Slater M. R., Di Nardo A., Pediconi O., et al. Free-Roaming Dogs and Cats in Central Italy: Public Perceptions of the Problem. Preventive Veterinary Medicine . 2008;84(1-2):27–47. doi: 10.1016/j.prevetmed.2007.10.002. [DOI] [PubMed] [Google Scholar]
- 50.Robertson I. D., Irwin P. J., Lymbery A. J., Thompson R. C. A. The Role of Companion Animals in the Emergence of Parasitic Zoonoses. International Journal for Parasitology . 2000;30(12-13):1369–1377. doi: 10.1016/S0020-7519(00)00134-X. [DOI] [PubMed] [Google Scholar]
- 51.Otranto D., Dantas-Torres F., Mihalca A. D., Traub R. J., Lappin M., Baneth G. Zoonotic Parasites of Sheltered and Stray Dogs in the Era of the Global Economic and Political Crisis. Trends in Parasitology . 2017;33(10):813–825. doi: 10.1016/j.pt.2017.05.013. [DOI] [PubMed] [Google Scholar]
- 52.Lembo T., Hampson K., Kaare M. T., et al. The Feasibility of Canine Rabies Elimination in Africa: Dispelling Doubts With Data. PLoS Neglected Tropical Diseases . 2010;4(2) doi: 10.1371/journal.pntd.0000626.e626 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 53.Cleaveland S., Kaare M., Tiringa P., Mlengeya T., Barrat J. A Dog Rabies Vaccination Campaign in Rural Africa: Impact on the Incidence of Dog Rabies and Human Dog-Bite Injuries. Vaccine . 2003;21(17-18):1965–1973. doi: 10.1016/S0264-410X(02)00778-8. [DOI] [PubMed] [Google Scholar]
- 54.Otranto D., Dantas-Torres F. The Prevention of Canine Leishmaniasis and Its Impact on Public Health. Trends in Parasitology . 2013;29(7):339–345. doi: 10.1016/j.pt.2013.05.003. [DOI] [PubMed] [Google Scholar]
- 55.Alves E. B., Figueiredo F. B., Rocha M. F., Castro M. C., Werneck G. L. Effectiveness of Insecticide-Impregnated Collars for the Control of Canine Visceral Leishmaniasis. Preventive Veterinary Medicine . 2020;182 doi: 10.1016/j.prevetmed.2020.105104.105104 [DOI] [PubMed] [Google Scholar]
- 56.Djokic V., Freddi L., de Massis F., et al. The Emergence of Brucella canis as a Public Health Threat in Europe: What We Know and What We Need to Learn. Emerging Microbes & Infections . 2023;12(2) doi: 10.1080/22221751.2023.2249126.2249126 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 57.Taylor L. H., Latham S. M., Woolhouse M. E. Risk Factors for Human Disease Emergence. Philosophical Transactions of the Royal Society of London. Series B: Biological Sciences . 2001;356(1411):983–989. doi: 10.1098/rstb.2001.0888. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 58.Acha P. N., Szyfres B., Acha P. N. Zoonoses and Communicable Diseases Common to Man and Animals . Washington, DC: Pan American Health Organization; 2001. [Google Scholar]
- 59.Polack B., Boulouis H.-J., Guillot J., Chermette R. Les Zoonoses (Tableaux Synthétiques: Animaux Réservoirs de Pathogènes et Modes de Transmission) Revue Francophone des Laboratoires . 2015;2015(477):67–79. doi: 10.1016/S1773-035X(15)30318-X. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Bauerfeind R., Von Graevenitz A., Kimmig P., et al. Zoonoses: Infectious Diseases Transmissible Between Animals and Humans . Washington, DC, USA: ASM Press; 2015. [DOI] [Google Scholar]
- 61.Zoonotic Diseases - Public Health. MSD Veterinary Manual. https://www.msdvetmanual.com/public-health/zoonoses/zoonotic-diseases, (accessed 2025-03-04)
- 62.CDC. Facts About Diseases that Can Spread Between Animals and People. Healthy Pets, Healthy People. (accessed 2025-03-04) https://www.cdc.gov/healthy-pets/diseases/index.html.
- 63.Desvars-Larrive A., Vogl A. E., Puspitarani G. A., Yang L., Joachim A., Käsbohrer A. A One Health Framework for Exploring Zoonotic Interactions Demonstrated through a Case Study. Nature Communications . 2024;15(1) doi: 10.1038/s41467-024-49967-7.5650 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 64.Ellwanger J. H., Chies J. A. B. The Triad, Dogs, Conservation and Zoonotic Diseases, – An Old and Still Neglected Problem in Brazil. Perspectives in Ecology and Conservation . 2019;17(3):157–161. doi: 10.1016/j.pecon.2019.06.003. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 65.Hernández F. A., Manqui J., Mejías C., Acosta-Jamett G. Domestic Dogs and Wild Foxes Interactions in a Wildlife-Domestic Interface of North-Central Chile: Implications for Multi-Host Pathogen Transmission. Frontiers in Veterinary Science . 2021;8 doi: 10.3389/fvets.2021.631788.631788 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 66.Durães-Oliveira J., Palma-Marques J., Moreno C., et al. Chagas Disease: A Silent Threat for Dogs and Humans. International Journal of Molecular Sciences . 2024;25(7) doi: 10.3390/ijms25073840.3840 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 67.Jimenez-Coello M., Ortega-Pacheco A., Guzman-Marin E., Guiris-Andrade D. M., Martinez-Figueroa L., Acosta-Viana K. Y. Stray Dogs as Reservoirs of the Zoonotic Agents Leptospira interrogans, Trypanosoma cruzi, and Aspergillus spp. in an Urban Area of Chiapas in Southern Mexico. Vector-Borne and Zoonotic Diseases . 2010;10(2):135–141. doi: 10.1089/vbz.2008.0170. [DOI] [PubMed] [Google Scholar]
- 68.Day M. J., Breitschwerdt E., Cleaveland S., et al. Surveillance of Zoonotic Infectious Disease Transmitted by Small Companion Animals. Emerging Infectious Diseases . 2012;18(12) doi: 10.3201/eid1812.120664.120664 [DOI] [Google Scholar]
- 69.Stull J. W., Brophy J., Weese J. S. Reducing the Risk of Pet-Associated Zoonotic Infections. Canadian Medical Association Journal . 2015;187(10):736–743. doi: 10.1503/cmaj.141020. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 70.Morters M. K., McKinley T. J., Restif O., et al. The Demography of Free-Roaming Dog Populations and Applications to Disease and Population Control. Journal of Applied Ecology . 2014;51(4):1096–1106. doi: 10.1111/1365-2664.12279. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 71.Silva-Rodríguez E. A., Cortés E. I., Zambrano B., Naughton-Treves L., Farías A. A. On the Causes and Consequences of the Free-Roaming Dog Problem in Southern Chile. Science of the Total Environment . 2023;891 doi: 10.1016/j.scitotenv.2023.164324.164324 [DOI] [PubMed] [Google Scholar]
- 72.Plowright R. K., Parrish C. R., McCallum H., et al. Pathways to Zoonotic Spillover. Nature Reviews Microbiology . 2017;15(8):502–510. doi: 10.1038/nrmicro.2017.45. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 73.Majewska A. A., Huang T., Han B., Drake J. M. Predictors of Zoonotic Potential in Helminths. Philosophical Transactions of the Royal Society B: Biological Sciences . 2021;376(1837) doi: 10.1098/rstb.2020.0356.20200356 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 74.Hopkins S. R., Jones I. J., Buck J. C., et al. Environmental Persistence of the World’s Most Burdensome Infectious and Parasitic Diseases. Frontiers in Public Health . 2022;10 doi: 10.3389/fpubh.2022.892366.892366 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 75.Nijsse R., Overgaauw P., Ploeger H., Mughini-Gras L. Advances in Parasitology . Vol. 109. Academic Press; 2020. Sources of Environmental Contamination With, Toxocara, Spp.: An Omnipresent Parasite; pp. 585–614. [DOI] [PubMed] [Google Scholar]
- 76.Tylkowska A., Mocha N., Kołnierzak M. M., Szenejko M. Risk Factors Associated With Soil-Transmitted Helminths in Dog Feces That Contaminate Public Areas of Warsaw, Poland. Animals . 2024;14(3) doi: 10.3390/ani14030450.450 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 77.Traversa D., Frangipane di Regalbono A., Di Cesare A., La Torre F., Drake J., Pietrobelli M. Environmental Contamination by Canine Geohelminths. Parasites & Vectors . 2014;7(1) doi: 10.1186/1756-3305-7-67.67 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 78.Penakalapati G., Swarthout J., Delahoy M. J., et al. Exposure to Animal Feces and Human Health: A Systematic Review and Proposed Research Priorities. Environmental Science & Technology . 2017;51(20):11537–11552. doi: 10.1021/acs.est.7b02811. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 79.Kamani J., Massetti L., Olubade T., et al. Canine Gastrointestinal Parasites as a Potential Source of Zoonotic Infections in Nigeria: A Nationwide Survey. Preventive Veterinary Medicine . 2021;192 doi: 10.1016/j.prevetmed.2021.105385.105385 [DOI] [PubMed] [Google Scholar]
- 80.Sukupayo P. R., Tamang S. Prevalence of Zoonotic Gastrointestinal Helminth Parasite Among Dogs in Suryabinayak, Nepal. Veterinary Medicine International . 2023;2023 doi: 10.1155/2023/3624593.3624593 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 81.Khalifa M. M., Fouad E. A., Kamel N. O., Auda H. M., El-Bahy M. M., Ramadan R. M. Dogs as a Source for the Spreading of Enteric Parasites Including Zoonotic Ones in Giza Province, Egypt. Research in Veterinary Science . 2023;161:122–131. doi: 10.1016/j.rvsc.2023.06.015. [DOI] [PubMed] [Google Scholar]
- 82.Nguyen T. L. A., Nguyen T. P., Johansen M. V., et al. Prevalence and Risks for Fishborne Zoonotic Trematode Infections in Domestic Animals in a Highly Endemic Area of North Vietnam. Acta Tropica . 2009;112(2):198–203. doi: 10.1016/j.actatropica.2009.07.027. [DOI] [PubMed] [Google Scholar]
- 83.Vaniscotte A., Raoul F., Poulle M. L., et al. Role of Dog Behaviour and Environmental Fecal Contamination in Transmission of Echinococcus multilocularis in Tibetan Communities. Parasitology . 2011;138(10):1316–1329. doi: 10.1017/S0031182011000874. [DOI] [PubMed] [Google Scholar]
- 84.Hung N. M., Dung D. T., Lan Anh N. T., et al. Current Status of Fish-Borne Zoonotic Trematode Infections in Gia Vien District, Ninh Binh Province, Vietnam. Parasites & Vectors . 2015;8(1) doi: 10.1186/s13071-015-0643-6.21 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 85.Garde E., Acosta-Jamett G., Bronsvoort B. M. Review of the Risks of Some Canine Zoonoses From Free-Roaming Dogs in the Post-Disaster Setting of Latin America. Animals . 2013;3(3):855–865. doi: 10.3390/ani3030855. [DOI] [Google Scholar]
- 86.Nocerino M., Pepe P., Bosco A., et al. An Innovative Strategy for Deworming Dogs in Mediterranean Areas Highly Endemic for Cystic Echinococcosis. Parasites & Vectors . 2024;17(1) doi: 10.1186/s13071-024-06184-x.86 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 87.Cinquepalmi V., Monno R., Fumarola L., et al. Environmental Contamination by Dog’s Faeces: A Public Health Problem? International Journal of Environmental Research and Public Health . 2013;10(1):72–84. doi: 10.3390/ijerph10010072. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 88.Rubel D., Carbajo A. Dogs in Public Spaces of Buenos Aires, Argentina: Exploring Patterns of the Abundance of Dogs, the Canine Faecal Contamination, the Behaviour of People With Dogs, and Its Relationships With Demographic/Economic Variables. Preventive Veterinary Medicine . 2019;170 doi: 10.1016/j.prevetmed.2019.104713.104713 [DOI] [PubMed] [Google Scholar]
- 89.Lezama-García K., Domínguez-Oliva A., Buenhombre J., et al. Exploring the Stray Dog Crisis: When the Human-Canine Relationships Breakdown. Journal of Animal Behaviour and Biometeorology . 2025;13(1) doi: 10.31893/jabb.2025003.2025003 [DOI] [Google Scholar]
- 90.Singh R., Singh K. P., Cherian S., et al. Rabies—Epidemiology, Pathogenesis, Public Health Concerns and Advances in Diagnosis and Control: A Comprehensive Review. Veterinary Quarterly . 2017;37(1):212–251. doi: 10.1080/01652176.2017.1343516. [DOI] [PubMed] [Google Scholar]
- 91.Olival K. J., Hosseini P. R., Zambrana-Torrelio C., Ross N., Bogich T. L., Daszak P. Host and Viral Traits Predict Zoonotic Spillover from Mammals. Nature . 2017;546(7660):646–650. doi: 10.1038/nature22975. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 92.Han B. A., Castellanos A. A., Schmidt J. P., Fischhoff I. R., Drake J. M. The Ecology of Zoonotic Parasites in the Carnivora. Trends in Parasitology . 2021;37(12):1096–1110. doi: 10.1016/j.pt.2021.08.006. [DOI] [PubMed] [Google Scholar]
- 93.Ryder J. J., Miller M. R., White A., Knell R. J., Boots M. Host-Parasite Population Dynamics Under Combined Frequency- and Density-Dependent Transmission. Oikos . 2007;116(12):2017–2026. doi: 10.1111/j.2007.0030-1299.15863.x. [DOI] [Google Scholar]
- 94.Espira L. M., Brouwer A. F., Han B. A., Foufopoulos J., Eisenberg J. N. S. Dilution of Epidemic Potential of Environmentally Transmitted Infectious Diseases for Species With Partially Overlapping Habitats. The American Naturalist . 2022;199(2):E43–E56. doi: 10.1086/717413. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 95.Mackenzie J. S., Childs J. E., Field H. E., Wang L.-F., Breed A. C. The Role of Bats as Reservoir Hosts of Emerging Neuroviruses. Neurotropic Viral Infections . 2016:403–454. doi: 10.1007/978-3-319-33189-8. [DOI] [Google Scholar]
- 96.Mennerat A., Nilsen F., Ebert D., Skorping A. Intensive Farming: Evolutionary Implications for Parasites and Pathogens. Evolutionary Biology . 2010;37(2-3):59–67. doi: 10.1007/s11692-010-9089-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 97.Zhang T., Nickerson R., Zhang W., et al. The Impacts of Animal Agriculture on One Health—Bacterial Zoonosis, Antimicrobial Resistance, and Beyond. One Health . 2024;18 doi: 10.1016/j.onehlt.2024.100748.100748 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 98.Damborg P., Broens E. M., Chomel B. B., et al. Bacterial Zoonoses Transmitted by Household Pets: State-of-the-Art and Future Perspectives for Targeted Research and Policy Actions. Journal of Comparative Pathology . 2016;155(1):S27–S40. doi: 10.1016/j.jcpa.2015.03.004. [DOI] [PubMed] [Google Scholar]
- 99.Klous G., Huss A., Heederik D. J. J., Coutinho R. A. Human-Livestock Contacts and Their Relationship to Transmission of Zoonotic Pathogens, a Systematic Review of Literature. One Health . 2016;2:65–76. doi: 10.1016/j.onehlt.2016.03.001. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 100.Zanen L. A., Kusters J. G., Overgaauw P. A. M. Zoonotic Risks of Sleeping With Pets. Pathogens . 2022;11(10) doi: 10.3390/pathogens11101149.1149 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 101.González J. L. C., Poveda S., Sosa A. L., et al. Dog Bites as a Zoonotic Risk in Ecuador: Need for the Implementation of a One Health Approach. One Health . 2023;16 doi: 10.1016/j.onehlt.2023.100544.100544 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 102.Beaulac K., Fellman C. L., Wayne A. S., McDermott L. A., Snydman D. R., Doron S. Impact of Antimicrobial Use in Dogs on Antimicrobial Resistance and Shared Flora With Human Owners. Antimicrobial Stewardship & Healthcare Epidemiology . 2023;3(1) doi: 10.1017/ash.2022.323.e1 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 103.Stull J. W., Peregrine A. S., Sargeant J. M., Weese J. S. Pet Husbandry and Infection Control Practices Related to Zoonotic Disease Risks in Ontario, Canada. BMC Public Health . 2013;13(1) doi: 10.1186/1471-2458-13-520.520 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 104.Julien D. A., Sargeant J. M., Filejski C., Versluis A. M., Waind V., Harper S. L. Unleashing the Literature: A Scoping Review of Canine Zoonotic and Vectorborne Disease Research in Canis Familiaris in North America. Animal Health Research Reviews . 2021;22(1):26–39. doi: 10.1017/S1466252320000237. [DOI] [PubMed] [Google Scholar]
- 105.Otranto D., Mendoza-Roldan J. A., Beugnet F., Baneth G., Dantas-Torres F. New Paradigms in the Prevention of Canine Vector-Borne Diseases. Trends in Parasitology . 2024;40(6):500–510. doi: 10.1016/j.pt.2024.04.009. [DOI] [PubMed] [Google Scholar]
- 106.Nair A. D. S., Cheng C., Ganta C. K., et al. Comparative Experimental Infection Study in Dogs With Ehrlichia canis, E. chaffeensis, Anaplasma platys and A. phagocytophilum. PLoS ONE . 2016;11(2) doi: 10.1371/journal.pone.0148239.e0148239 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 107.Simpson J. E., Hurtado P. J., Medlock J., et al. Vector Host-Feeding Preferences Drive Transmission of Multi-Host Pathogens: West Nile Virus as a Model System. Proceedings of the Royal Society B: Biological Sciences . 2012;279(1730):925–933. doi: 10.1098/rspb.2011.1282. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 108.McCoy K. D., Léger E., Dietrich M. Host Specialization in Ticks and Transmission of Tick-Borne Diseases: A Review. Frontiers in Cellular and Infection Microbiology . 2013;3 doi: 10.3389/fcimb.2013.00057.57 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 109.Jitsamai W., Piromkij P., Kamkong P., Chungpivat S., Taweethavonsawat P. Seasonal Distribution and Environmental Parameters Associated With Brugia Pahangi and Dirofilaria Immitis in Naturally Infected Dogs in Bangkok and Vicinity, Thailand. Scientific Reports . 2021;11(1) doi: 10.1038/s41598-021-84215-8.4594 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 110.Ghouse Peer G. D., Priyadarshini A., Gupta A., et al. A Systematic Assessment of Leishmania Donovani Infection in Domestic and Wild Animal Reservoir Hosts of Zoonotic Visceral Leishmaniasis in India. Microbiology Research . 2024;15(3):1645–1654. doi: 10.3390/microbiolres15030109. [DOI] [Google Scholar]
- 111.Maggi R. G., Krämer F. A Review on the Occurrence of Companion Vector-Borne Diseases in Pet Animals in Latin America. Parasites & Vectors . 2019;12(1) doi: 10.1186/s13071-019-3407-x.145 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 112.Luong N. H., Kamyingkird K., Thammasonthijarern N., et al. Companion Vector-Borne Pathogens and Associated Risk Factors in Apparently Healthy Pet Animals (Dogs and Cats) in Khukhot City Municipality, Pathum Thani Province, Thailand. Pathogens . 2023;12(3) doi: 10.3390/pathogens12030391.391 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 113.Colella V., Nguyen V. L., Tan D. Y., et al. Zoonotic Vectorborne Pathogens and Ectoparasites of Dogs and Cats in Eastern and Southeast Asia. Emerging Infectious Diseases . 2020;26(6):1221–1233. doi: 10.3201/eid2606.191832. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 114.Diakou A., Sofroniou D., Paoletti B., et al. Ticks, Fleas, and Harboured Pathogens from Dogs and Cats in Cyprus. Pathogens . 2022;11(12) doi: 10.3390/pathogens11121403.1403 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 115.Ahmad T., Imran M., Ahmad K., et al. A Bibliometric Analysis and Global Trends in Fascioliasis Research: A Neglected Tropical Disease. Animals . 2021;11(12) doi: 10.3390/ani11123385.3385 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 116.Miao L., Li H., Ding W., et al. Research Priorities on One Health: A Bibliometric Analysis. Frontiers in Public Health . 2022;10 doi: 10.3389/fpubh.2022.889854.889854 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 117.Baclic O., Tunis M., Young K., Doan C., Swerdfeger H., Schonfeld J. Challenges and Opportunities for Public Health Made Possible by Advances in Natural Language Processing. Canada Communicable Disease Report . 2020;46(6):161–168. doi: 10.14745/ccdr.v46i06a02. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 118.Raza S., Reji D. J., Shajan F., Bashir S. R. Large-Scale Application of Named Entity Recognition to Biomedicine and Epidemiology. PLoS Digital Health . 2022;1(12) doi: 10.1371/journal.pdig.0000152.e0000152 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 119.Song Y., Yoon B., Elbassuoni S. Prediction of Infectious Diseases Using Sentiment Analysis on Social Media Data. PLoS One . 2024;19(9) doi: 10.1371/journal.pone.0309842.e0309842 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 120.Szwabe K., Blaszkowska J. Stray Dogs and Cats as Potential Sources of Soil Contamination With Zoonotic Parasites. Annals of Agricultural and Environmental Medicine . 2017;24(1):39–43. doi: 10.5604/12321966.1234003. [DOI] [PubMed] [Google Scholar]
- 121.Ferreira A., Alho A. M., Otero D., et al. Urban Dog Parks as Sources of Canine Parasites: Contamination Rates and Pet Owner Behaviours in Lisbon, Portugal. Journal of Environmental and Public Health . 2017;2017 doi: 10.1155/2017/5984086.5984086 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 122.Alegría-Morán R., Pastenes Á., Cabrera G., Fredes F., Ramírez-Toloza G. Urban Public Squares as Potential Hotspots of Dog-Human Contact: A Spatial Analysis of Zoonotic Parasites Detection in Gran Santiago, Chile. Veterinary Parasitology: Regional Studies and Reports . 2021;24 doi: 10.1016/j.vprsr.2021.100579.100579 [DOI] [PubMed] [Google Scholar]
- 123.Mori K., Rock M., McCormack G., et al. Fecal Contamination of Urban Parks by Domestic Dogs and Tragedy of the Commons. Scientific Reports . 2023;13(1) doi: 10.1038/s41598-023-30225-7.3462 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 124.Trasviña-Muñoz E., López-Valencia G., Monge-Navarro F. J., et al. Detection of Intestinal Parasites in Stray Dogs From a Farming and Cattle Region of Northwestern Mexico. Pathogens . 2020;9(7) doi: 10.3390/pathogens9070516.516 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 125.Regidor-Cerrillo J., Arranz-Solís D., Moreno-Gonzalo J., et al. Prevalence of Intestinal Parasite Infections in Stray and Farm Dogs from Spain. Revista Brasileira de Parasitologia Veterinária . 2020;29(3) doi: 10.1590/s1984-29612020063.e014920 [DOI] [PubMed] [Google Scholar]
- 126.Anh N. T. L., Phuong N. T., Murrell K. D., et al. Animal Reservoir Hosts and Fish-Borne Zoonotic Trematode Infections on Fish Farms. Emerging Infectious Diseases . 2009;15(4):540–546. doi: 10.3201/eid1504.081147. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 127.Yu Q., Xiao N., Yang S.-J., Han S. Deworming of Stray Dogs and Wild Canines With Praziquantel-Laced Baits Delivered by an Unmanned Aerial Vehicle in Areas Highly Endemic for Echinococcosis in China. Infectious Diseases of Poverty . 2017;6(1) doi: 10.1186/s40249-017-0329-8.117 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 128.Wright N., Subedi D., Pantha S., Acharya K. P., Nel L. H. The Role of Waste Management in Control of Rabies: A Neglected Issue. Viruses . 2021;13(2) doi: 10.3390/v13020225.225 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 129.Fulford M. B. Companion Animal Zoonoses . John Wiley & Sons, Ltd.; 2011. Pet Bites; pp. 311–315. [DOI] [Google Scholar]
- 130.Sikana L., Lembo T., Hampson K., et al. Dog Ownership Practices and Responsibilities for Children’s Health in Terms of Rabies Control and Prevention in Rural Communities in Tanzania. PLoS Neglected Tropical Diseases . 2021;15(3) doi: 10.1371/journal.pntd.0009220.e0009220 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 131.Cleaveland S., Meslin F. X., Breiman R. Dogs Can Play Useful Role as Sentinel Hosts for Disease. Nature . 2006;440(7084):605–605. doi: 10.1038/440605b. [DOI] [PubMed] [Google Scholar]
- 132.Schurer J. M., Hill J. E., Fernando C., Jenkins E. J. Sentinel Surveillance for Zoonotic Parasites in Companion Animals in Indigenous Communities of Saskatchewan. The American Society of Tropical Medicine and Hygiene . 2012;87(3):495–498. doi: 10.4269/ajtmh.2012.12-0273. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 133.Bowser N. H., Anderson N. E. Dogs (Canis Familiaris) as Sentinels for Human Infectious Disease and Application to Canadian Populations: A Systematic Review. Veterinary Sciences . 2018;5(4) doi: 10.3390/vetsci5040083.83 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 134.Capellà Miternique H., Gaunet F. Coexistence of Diversified Dog Socialities and Territorialities in the City of Concepción, Chile. Animals . 2020;10(2) doi: 10.3390/ani10020298.298 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 135.Marshall H. E., Gore M. L., Ngoprasert D., Savini T. Free-Ranging Dogs and Their Owners: Evaluating Demographics, Husbandry Practices and Local Attitudes Towards Canine Management and Dog-Wildlife Conflict. Integrative Conservation . 2023;2(4):255–270. doi: 10.1002/inc3.37. [DOI] [Google Scholar]
- 136.Moran N. E., Ferketich A. K., Wittum T. E., Stull J. W. Dogs on Livestock Farms: A Cross-Sectional Study Investigating Potential Roles in Zoonotic Pathogen Transmission. Zoonoses and Public Health . 2018;65(1):80–87. doi: 10.1111/zph.12373. [DOI] [PubMed] [Google Scholar]
- 137.Wilson-Aggarwal J. K., Ozella L., Tizzoni M., et al. High-Resolution Contact Networks of Free-Ranging Domestic Dogs Canis Familiaris and Implications for Transmission of Infection. PLoS Neglected Tropical Diseases . 2019;13(7) doi: 10.1371/journal.pntd.0007565.e0007565 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 138.Belsare A., Vanak A. T. Modelling the Challenges of Managing Free-Ranging Dog Populations. Scientific Reports . 2020;10(1) doi: 10.1038/s41598-020-75828-6.18874 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 139.Espejo L. A., Costard S., Zagmutt F. J. Modelling Canine Leishmaniasis Spread to Non-Endemic Areas of Europe. Epidemiology and Infection . 2015;143(9):1936–1949. doi: 10.1017/S0950268814002726. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 140.Raynor B., De la Puente-León M., Johnson A., et al. Movement Patterns of Free-Roaming Dogs on Heterogeneous Urban Landscapes: Implications for Rabies Control. Preventive Veterinary Medicine . 2020;178 doi: 10.1016/j.prevetmed.2020.104978.104978 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 141.Mutwiri T., Muigai A. W. T., Magambo J., et al. The Potential Role of Roaming Dogs in Establishing a Geographically Novel Life Cycle of Taeniids (Echinococcus spp. and Taenia spp.) in a Non-Endemic Area. Veterinary Parasitology: Regional Studies and Reports . 2023;38 doi: 10.1016/j.vprsr.2022.100829.100829 [DOI] [PubMed] [Google Scholar]
- 142.Dürr S., Wera E., Brookes V. J., Warembourg C., Griss S., Fahrion A. S. One Health for Dog-Mediated Rabies Elimination in Asia . CABI Books; 2023. The Role of Dog Ecology in Canine Rabies Prevention and Control in Asia: Lessons from Indonesia and the Oceanic Region; pp. 142–159. [DOI] [Google Scholar]
- 143.Mauti S. Contribution to Dog Ecology and Dog-Related Zoonoses in Bamako, Mali . University_of_Basel; 2015. Thesis. [DOI] [Google Scholar]
- 144.Mbilo C., Kabongo J.-B., Pyana P. P., et al. Bite Incidence, and Disease Awareness: A Cross-Sectional Survey Among a Rabies-Affected Community in the Democratic Republic of the Congo. Vaccines . 2019;7(3) doi: 10.3390/vaccines7030098.98 [DOI] [PMC free article] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Table S1: List of zoonotic pathogens.
χ2 adjusted standardized residuals. Probability graph of citing “dogs” and “pigs” on the total by transmission pathways. Summary, Results, Analysis of deviance, and Predicted probabilities of Model 1. Summary, Results, Analysis of deviance, and Predicted probabilities of Model 2. Summary, Results, Analysis of deviance, and Predicted probabilities of Model 3. Zoonotic pathogens list analysis code. Bibliometric analysis code.
Data Availability Statement
All data used in this study are publicly available through the Web of Science Core Collection bibliographic database (Clarivate). The list of publications included in the bibliometric analysis is compiled and referenced in Table 1 of the manuscript.
