Next Article in Journal
Genetic Diversity of Enterocytozoon bieneusi in Diarrheic Shelter Dogs in Romania: First Molecular and Phylogenetic Evidence
Previous Article in Journal
Emergence of Dengue Virus Serotypes 1 and 3 in Mahottari and Adjacent Areas of Southern Nepal
Previous Article in Special Issue
Role of Molecular Diagnosis in Imported Cutaneous Leishmaniasis and Its Public Health Significance in India
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Healing with Risks: How Zoonotic Potential Influences the Use of Wild Mammals in Traditional Medicine

by
Heliene Mota Pereira
1,*,
Mayara Guimarães Beltrão
2,
Anna Karolina Martins Borges
1,3,
Weslley Ruan Guimarães da Silva
4,
Danilo Vicente Batista Oliveira
5 and
Rômulo Romeu Nóbrega Alves
6
1
Programa de Pós-Graduação em Etnobiologia e Conservação da Natureza, Universidade Federal Rural de Pernambuco, Recife 52171-900, Brazil
2
Laboratório de Biologia da Conservação, Departamento de Biodiversidade, Universidade Estadual Paulista “Júlio de Mesquita Filho”, Rio Claro 13506-900, Brazil
3
LAPEC—Laboratório de Peixes e Conservação Marinha, Universidade Estadual da Paraíba, João Pessoa 58071-160, Brazil
4
Bioinformatics Multidisciplinary Environment, BioME, Federal University of Rio Grande do Norte, Natal 59000-000, Brazil
5
ESG e Compliance, Masterboi, Av. da Recuperação, 7380 Dois Irmãos, Recife 52171-340, Brazil
6
Centro de Ciências Biológicas e Sociais Aplicadas, Universidade Estadual da Paraíba, João Pessoa 58071-160, Brazil
*
Author to whom correspondence should be addressed.
Pathogens 2025, 14(7), 640; https://doi.org/10.3390/pathogens14070640
Submission received: 8 May 2025 / Revised: 13 June 2025 / Accepted: 24 June 2025 / Published: 27 June 2025
(This article belongs to the Special Issue Zoonotic Vector-Borne Infectious Diseases: The One Health Perspective)

Abstract

Most infectious diseases affecting humans are zoonotic in origin, with mammals serving as the main reservoirs. Frequent interactions between humans and animals, especially in the context of their use for food, medicine, and other purposes, pose significant public health risks, as recently demonstrated by the SARS-CoV-2 pandemic. In traditional medicine, many species—some of which are also used as food—are valued for their therapeutic versatility, that is, the diversity of medicinal uses attributed to each species. This study investigates the role of zoonotic potential in the selection of mammals used in traditional medicine at a global scale. We compiled data on 411 wild mammal species across 17 orders, identifying 5.146 associated pathogens, of which 2.778 (53.9%) also infect humans. Most diseases transmitted by these species are caused by viruses (33.4%), bacteria (23.3%), and helminths (22.3%). These mammals are used to treat at least 500 diseases or symptoms, and 4.3% of the species show high therapeutic versatility (RI > 1). Our results indicate that species selection is shaped by both biological and cultural factors, with zoonotic potential being the most influential: species with a higher risk of disease transmission tend to be less used. These findings highlight the importance of incorporating zoonotic risk into research and policies regarding the medicinal use of wildlife.

1. Introduction

Emerging infectious diseases, especially zoonotic ones, are a global concern due to their impact on public health. The COVID-19 pandemic, caused by the SARS-CoV-2 virus, illustrates how such diseases can lead to significant global health, economic and social disruptions. Zoonotic pathogens account for approximately 60% of known human infections and 75% of emerging infectious diseases, and are often associated with the global wildlife trade [1,2,3]. Part of this trade involves the use of wild animals in traditional medicine, a practice shaped by cultural and economic factors, which often contributes to illegal hunting [4,5,6].
Human contact with wild animals during hunting, slaughter, transport and consumption increases the risk of zoonosis transmission [4,7,8,9]. Bites, scratches and exposure to bodily fluids can facilitate infection, especially when injuries are caused during handling [10]. Medicinal uses include organs, fat, blood, skins, feathers, bones, glands and excrement, which can serve as potential sources of disease [10,11,12,13]. Recurrent exposure to wild animals and their bodily fluids can drive evolutionary adaptations in pathogens, increasing the likelihood of zoonotic spillover, defined as the transmission of animal-derived pathogens to humans [14,15]. Despite the risks involved, the use of wild fauna represents an important therapeutic alternative in many traditional medical systems around the world, especially in contexts of low availability or limited access to conventional drugs [16].
Mammals are often associated with the emergence of zoonoses due to evolutionary, biological and ecological factors which favor the transmission of pathogens [1,9,17,18,19]. Diseases such as Ebola, Influenza, Mpox, Plague, Acquired Immunodeficiency Syndrome (AIDS) and COVID-19 illustrate the recurrence of zoonotic emergencies in recent decades, reinforcing the need for epidemiological investigations [20]. In this scenario, monitoring human exposure to zoonoses associated with traditional medicine and other cultural practices is a relevant strategy for anticipating risks to public health [21,22]
Selecting animals for medicinal use involves myths, popular beliefs and traditional knowledge, along with characteristics of the species such as body mass, feeding habits, behavior and their accessibility [23,24,25]. These factors are dynamic and can be modified as new species are incorporated into human consumption [26]. The medicinal importance of a species can be assessed by its versatility, meaning by the number of therapeutic indications associated with it [24,27,28], which may also have implications for conservation and bioprospecting [29].
Although it remains unclear how the zoonotic potential influences species selection in traditional medicine, from an adaptive perspective, one might expect individuals to avoid species perceived as risky, even without formal scientific knowledge. Behavioral mechanisms such as disgust or aversion to certain animal traits, often shaped by empirical observation and cultural transmission, may act as proxies for risk, contributing to zoonosis avoidance [30,31]. However, traditional medical systems are shaped by a complex web of ecological, cultural and symbolic factors [32,33].
Biological and ecological aspects can be reflected in cultural perceptions, influencing the acceptance or rejection of species as therapeutic resources in zootherapeutic practices across different sociocultural contexts [34]. Zoonotic potential and ecological attributes, such as feeding habits and body mass, are recognized as relevant factors in the selection and valuation of species in traditional contexts, and may, either individually or in combination, help explain their therapeutic versatility. Large animals are more likely to host and transmit pathogens due to their greater longevity, large home range and greater complexity in ecological interactions [35,36]. Furthermore, dietary habits influence this risk: carnivorous and omnivorous species are more likely to be exposed to and infected by pathogens when consuming infected prey, while herbivores tend to have a reduced zoonotic risk [37].
This study uses medicinal mammals as a model to investigate how ecological characteristics relate to zoonotic risk and therapeutic versatility. Specifically, we seek to (1) assess the spatial distribution of zoonotic potential among wild medicinal mammals, and (2) examine how therapeutic versatility (defined as the range of medicinal uses attributed to an animal) is influenced by zoonotic potential, body mass, and feeding habits.
Although traditional knowledge systems do not use formal epidemiological indicators, perceptions of disease risk may arise from empirical observations, symbolic associations, and cultural transmission. Animals seen as unclean, aggressive, or foul-smelling are often avoided, reflecting intuitive strategies of risk avoidance. This aligns with the behavioral immune system theory, which highlights evolved responses like disgust to prevent infection [38] and has been observed in both primate behavior and traditional human contexts [39]. Based on this evidence, we hypothesize that species with higher zoonotic potential are less frequently used in traditional medicine, due to empirical perceptions of health risk, regardless of their therapeutic versatility, while species with greater body mass or herbivorous diets may be more versatile due to both practical (such as biomass availability) and cultural criteria (such as symbolisms associated with the diet or size of the animals) [6,24,32,33,34,35,36,37,38,39].

2. Materials and Methods

2.1. Data Collection

The data for this study were compiled from several previous investigations. First, we retrieved records from the database which records medicinal species and their respective uses [24]. We searched for host–parasite relationship data for all mammals using the “Mammal-pathogen-species-level associations” dataset [40] and identified which pathogens were zoonotic through the “SpeciesInteractions_EID2” resource [41]. Zoonotic status was determined computationally in R by matching pathogens associated with humans (Carrier.classification = “Human”) to the mammal–pathogen records. Both datasets were accessed programmatically in R (version 4.4.1) in April 2022.
We checked whether species were classified as domestic according to the list provided by the Food and Agriculture Organization (FAO) [42]. To standardize and harmonize the scientific names in the final dataset, we employed the R package Taxize version 4.4.1 [43], using the ‘classification’ function to retrieve hierarchical taxonomic records via the Global Biodiversity Information Facility (GBIF) [44], ensuring alignment with current and widely accepted classifications. This process allowed us to correct outdated names, resolve synonyms, and consistently assign each species to its respective genus, family and order, thus improving taxonomic accuracy and ecological comparability across analyses.
We subsequently compiled information on body mass (g) from the PanTHERIA database [45]. Data on dietary habits were collected from various published sources, including PanTHERIA [45], ANIMALIA [46] and GBIF [44]. We classified host mammals into four categories of feeding habits: herbivores, carnivores, insectivores, and omnivores. Information on the geographic distribution of species was obtained from the International Union for Conservation of Nature (IUCN) [47] database. To do this, we overlapped the IUCN species occurrence maps with the list of mammals used in traditional medicine compiled by [24], using scientific names as a matching criterion. For the spatial analyses, when the overlap of host mammal species distribution maps resulted in multiple distinct areas, only the largest area of occurrence was retained for each species. The usage frequency of each species by country was measured as the total number of independent medicinal use records documented in each country, based on our dataset (Table S1).

2.2. Data Analysis

First, we quantified the total pathogen richness by compiling the number of unique pathogen species reported for each mammalian species used in traditional medicine. We then estimated the zoonotic potential based on the number of pathogens shared between each mammalian species and humans, thus characterizing the zoonotic richness [36]. Finally, both values were aggregated by taxonomic order, resulting in estimates of total and zoonotic pathogen richness for each group.
We used the therapeutic versatility of the species as a response variable in our models. In this study, we define therapeutic versatility as the diversity of medicinal uses attributed to a species. This concept is operationalized through the Relative Importance Index (RI), which is used to identify the most versatile species considering the number of medicinal properties (uses) reported by informants [48]. The RI was calculated using the formula RI = NUC + NT, in which NUC represents the ratio between the number of disease categories associated with a species (NUCS) and the total number of disease categories of the most versatile species (NUCVS), while NT represents the number of types of uses attributed to each species (NTS). The RI value ranges from 0 (no medicinal use) to 2 (maximum versatility). Although cultural and symbolic values influence species selection, our statistical modeling focused on ecological and zoonotic variables due to the lack of standardized data across species and regions. These aspects are addressed qualitatively in the discussion.
Before fitting the models, we pre-treated the variables to ensure compliance with the statistical assumptions and improve interpretation of the results. The numerical variables (body mass and zoonotic potential) were log10-transformed to reduce skewness and stabilize variance. In addition, we transformed the continuous variable body mass, originally expressed in grams (g). Subsequently, the variables were rescaled (standardized) to meet the assumptions of the statistical models and to facilitate the interpretation of parameter estimates.
To control for potential inflation of versatility values in well-studied species, we adjusted the Relative Importance Index (RI) by dividing it by the number of bibliographic records per species. This correction accounts for uneven research effort and improves the comparability of versatility estimates across species. The resulting value represents the corrected versatility, referred to from now on as “versatility weighted”. This variable was adjusted to minimize the impact of possible inequalities. The results of these values are presented in Table S1.
Next, we tested the data normality and checked the variance inflation factor (VIF) to detect whether there was collinearity between the predictor variables. Based on the values (all below the threshold of 3), we verified that there were no multicollinearity problems in the model [49]. We used the residuals of a multiple linear regression model evaluating the effects of the predictor variables on versatility weighted to verify whether there was the presence of spatial autocorrelation using the testSpatialAutocorrelation function of the DHARMa package (version 0.4.6) [50].
Due to detecting spatial autocorrelation in the data, we used a mixed additive model fitted by approximate maximum likelihood to evaluate the relationship between therapeutic versatility (=versatility weighted) and its potential explanatory factors, implemented through the fitme function of the spaMM package in R [51]. The response variable (=versatility weighted) was modeled using a Gamma distribution and a logarithmic link Γ(link = log), appropriate for positive and asymmetric data. In the general model, the predictor variables included zoonotic potential, body mass and feeding habits as fixed covariates with additive relations. Based on this, the remaining models were constructed, including three univariate models, three bivariate models with additive relationships, and one null model. Then, we included a spatial correlation term based on the Matérn kernel (1|X + Y) to account for the spatial structure of the data considering the centroid of the geographic distribution coordinates (X and Y) of the hosts as spatial variables using the “adespatial” package in R [52]. Additionally, we included a random effect term for host genus (1∣Genus) capturing variation associated with taxonomy, considering that phylogenetically close species are more likely to spill over [53]. The general model specification was as follows:
General model <- fitme (Versatility weighted ~ Zoonotic potential + Body Mass (g) + Feed habit + Matern (1|X + Y) + (1|Genus), family = Gamma (link = “log”).
The models’ fit was assessed based on the Akaike information criterion (AIC) and the relevance of the parameters was determined by the estimated confidence intervals. The mean of the models with ΔAIC ≤ 2 highlighted estimates whose intervals do not include zero, enabling the identification of relevant predictors and discarding those without a significant association with the response variable [54]. In addition, we calculated the Relative Importance Index (RI) of each predictor variable, corresponding to the sum of the Akaike weights in the models in which each predictor was included. Predictors with higher RI indicate greater support within the set of models tested, as they are associated with models with better acceptability.

3. Results

3.1. Dataset Overview

From an initial set of 411 mammal species used in traditional medicine, 39 were excluded due to missing information about the country where the use was registered, and 21 were identified as domestic species. With this, we obtained data on the types of zoonotic pathogens (bacteria, fungi, protozoa, viruses, and helminths) associated with 351 species of wild mammals used for medicinal purposes (Table S1). Of these, 129 species (36.7%) lack information on the body parts used in the treatment of diseases, leading to their exclusion from modeling. The final dataset used in the analyses comprised 222 wild mammal species. A flowchart summarizing the data selection process is presented in Figure 1.

3.2. Trends in Zoonotic Pathogens Among Medicinal Mammals

We recorded 411 mammal species used in medicinal practices worldwide, including domestic and wild species. Of these, 351 wild species were analyzed in our study, representing 17 of the 27 existing orders (Figure 2A). The most representative orders were Carnivora (n = 93 species, 26%), Artiodactyla (n = 65, 19%), Primates (n = 54, 15%), Chiroptera (n = 46, 13%) and Rodentia (n = 36, 10%). The other orders comprised the remaining 17%.
We identified 5.146 pathogens associated with the 351 mammals analyzed. Of these, 2.778 (53.9%) were classified as zoonotic, as they had already been detected in humans. Among all recorded pathogens, 33% were viruses, 23% bacteria, 22% helminths, 17% protozoa and 4% fungi (Figure 3). The Carnivora order contained the largest proportion of zoonotic pathogens (33.7%), followed by Primates (26.2%), Artiodactyla (15.8%), Rodentia (6.8%) and Chiroptera (4.2%) (Figure 2B). The orders with the lowest zoonotic richness were Pholidota (0.1%), Hyracoidea (0.3%) and Soricomorpha (0.6%) (Figure 2B). The distribution of pathogens varied among taxonomic groups: Primates had the highest number of zoonotic viruses; Carnivora, of helminths; and Artiodactyla, of zoonotic protozoa (Figure 4).
Medicinal use of wild mammals was recorded in 132 of the 195 existing countries. The five countries with the largest number of species used were China (n = 66), India (n = 66), Nigeria (n = 63), Brazil (n = 55) and Benin (n = 53) (Figure 5). The species with the greatest distribution of medicinal use were Loxondonta africana—“African Savanna Elephant” (44); Panthera pardus—“Leopard” (41); Ursus arctos—“Brown Bear” (32); Ursus thibetanus—“Asiatic Black Bear” (30); Melursus ursinus—“Sloth Bear” and Panthera tigris—“Tiger” (29).
The species with the greatest therapeutic versatility based on the RI values (Table 1) were Ursus arctos—“Brown bear” (RI = 1.54); Mephitis macroura—“Hooded Skunk” (RI = 1.55); Ursus americanus—“American Black Bear” (RI = 1.58); Ursus maritimus—“Polar Bear” (RI = 1.58); Dasypus novemcinctus—“Nine-banded Armadillo” (RI = 1.65); and Manis gigantea—“Giant Ground Pangolin” (RI = 1.8).

3.3. Determinants of Therapeutic Versatility in Medicinal Mammals

When investigating how the therapeutic versatility of mammals relates to zoonotic potential, body mass and feeding habits, we observed that four models presented ΔAIC ≤ 2, indicating equivalent explanatory power. These models include three with a single predictor variable and one with two variables (Table 2), covering all evaluated factors. The results indicate that zoonotic potential presented a negative relationship with therapeutic versatility, with a relative importance (RI) of 60%, being the most influential variable. This suggests that species associated with greater zoonotic risk tend to be less used medicinally (Table 2; Figure 6B). Body mass had a positive relationship with versatility with an RI of approximately 40%, indicating that larger species are more widely used for therapeutic purposes. Although feeding habits were also positive, they had a lesser influence (RI of 20%), suggesting a more limited contribution.
The seven models evaluated presented substantial empirical evidence (Table 2). However, all the explanatory variables included zero overlap within their standard error ranges, indicating limitations in the strength of the associations. For example, the effect of frugivorous eating habits crossed zero (Figure 6A), being considered a non-informative parameter. The null model, with a weight of only 2.9%, had little support, which reinforces the relevance of the variables tested. Zoonotic potential emerged from among the analyzed factors as the main modulator of the versatility of medicinal mammals. The inclusion of this variable in models with greater support, such as the one combining “Zoonotic potential + Body mass (g)”, increased the explanatory capacity, reinforcing its importance as a determining factor in therapeutic versatility.
In terms of predictive hierarchy, zoonotic potential is the main predictor of versatility, followed by body mass and dietary habits, with decreasing influence. Furthermore, while mass and dietary habits showed positive effects, zoonotic potential demonstrated an opposite effect, indicating it as a limiting factor of therapeutic versatility (Table 2).

4. Discussion

4.1. Trends in Zoonotic Pathogens Among Medicinal Mammals

Our results indicate that mammals used in traditional medicine harbor a wide diversity of zoonotic pathogens. Carnivores, primates and ungulates concentrate the largest number of medicinal species with high zoonotic burden, reflecting both their ecological role and their cultural and medicinal value in different regions of the world [55,56]. These findings reinforce the need to include the therapeutic use of wild mammals in epidemiological surveillance and zoonotic risk management strategies.
Carnivores are often exposed to multiple pathogens due to their generalist diet and high trophic role, acting as reservoirs for helminths, bacteria and fungi [57,58,59,60]. In turn, primates are highly associated with virus transmission, especially due to their phylogenetic proximity to humans, which facilitates bidirectional transmission of pathogens [61,62,63]. Vulnerability to zoonotic transmission by primates is compounded by their widespread use in medicinal contexts. Studies report the presence of simian immunodeficiency virus (SIV) in meat, pets and primate hunters in West Africa [64,65], reinforcing the need for regulation and surveillance. Furthermore, the recent outbreak of Monkeypox (Mpox), even after the COVID-19 pandemic, illustrates the persistent threat of zoonoses emerging through human interaction with and exploitation of wildlife [66].
Large mammals also stand out as species with high therapeutic versatility and a high zoonotic load. For example, bears are hosts to several infectious agents, such as Alphacoronavirus 1, which can infect humans [67]. The nine-banded armadillo (Dasypus novemcinctus) is associated with the transmission of Mycobacterium leprae, which causes leprosy [68,69]. The pangolin (Manis gigantea) is widely used in different Asian cultures, and has been associated with the wildlife trade and concerns regarding its potential role in the transmission of emerging infectious diseases, although specific data on this species are lacking [70,71,72].
Viruses and bacteria were the most prevalent among the types of pathogens among mammals used in medicine, constituting a pattern consistent with the recent history of health emergencies such as HIV, SARS, MERS, Ebola, H1N1, and COVID-19 [73,74,75]. In this context, traditional medicine should be considered a relevant exposure route to zoonoses, especially in widely used taxonomic groups, such as primates and carnivores. Because the latter occupy high trophic levels and consume several species, they act as important “pathogen deposits” [56,76] and present a high diversity of bacteria, fungi and helminths in our data. On the other hand, primates mainly stood out as viral reservoirs, reflecting already documented patterns in the literature [77,78].
Despite these risks, little attention has been given to the management of wild animals used in traditional medicine and the potential associated health impacts [4,11,79,80]. Large species, such as ungulates, not only deserve attention because of the zoonotic risk, but also because they are widely exploited due to the abundance of biomass and proximity to humans and domesticated animals, which can favor pathogen sharing [35,81]. In addition to the considerable volume of tissue and organs available, their larger body size is generally associated with greater mobility and geographic distribution, constituting factors which increase the interface with human populations, and therefore increase the risk of zoonosis transmission, especially when compared to smaller species, such as rodents.
The global usage distribution of medicinal mammals with records in 132 countries reflects a strong cultural dependence on these resources, especially in regions with rich biodiversity and consolidated traditions of traditional medicine, such as Asia, Latin America and Africa. More specifically, China, India, Nigeria, Brazil and Benin lead in the number of species used, indicating the relationship between biological diversity and cultural history. These findings reinforce the importance of local and regional analyses to identify usage patterns and guide conservation strategies adapted to sociocultural contexts.

4.2. Determinants of Therapeutic Versatility in Medicinal Mammals

Our results show that zoonotic potential exerts a negative influence on the therapeutic versatility of medicinal mammals, indicating that empirical perceptions of health risk shape species selection practices. Although anchored in deep cultural traditions, these practices appear to integrate adaptive strategies aimed at minimizing risks, even in the absence of formal biomedical knowledge [82]. This pattern can be interpreted in light of evolutionary theories of pathogen avoidance behavior, such as the “behavioral immune system,” in which emotional responses such as disgust, aversion, and fear function as psychological defenses against exposure to infectious agents [30,31,83]. Thus, considering that many traditional medical systems have developed over millennia with direct interaction with wildlife, it is plausible to assume that zoonotic risk has directly or indirectly influenced the selection of the most appropriate species for therapeutic use. Wild animals take on functions in traditional medicine which go beyond the simple treatment of illnesses, incorporating symbolic, social and spiritual values. Products such as pangolin meat, rhino horns and shark fins continue to be valued, even with a high zoonotic risk [6,84]. This persistence shows that the choice of medicinal resources operates in a multifactorial system, where therapeutic efficacy, social status and symbolic value often override perceptions of risk.
The use of wild animals for medicinal purposes, often as a byproduct of hunting [85,86,87], involves different zoonotic risks, depending on the species and the product handled. Tissues such as the liver, kidneys and brain concentrate a high pathogenic load, including viruses such as Ebola in primates [88], bacteria such as Brucella abortus in ungulates [89,90] and coronaviruses in bats [91]. These examples illustrate how decisions about which species and parts to use may not only reflect cultural preferences, but also adaptive strategies (albeit implicit) to minimize health risks.
From an evolutionary perspective, it would be disadvantageous to select species whose use entailed high risks, reducing the potential benefits of the resource [92,93]. Thus, it would be expected that animals with greater zoonotic potential would be avoided. However, traditional medical systems operate under multiple factors, which are not always linear or utilitarian, and are influenced by different biocultural and ecological factors [94]. Studies on selection patterns demonstrate that organoleptic properties, such as taste and odor, influence selection of medicinal species [95,96,97]. In addition, perceptions of risk and toxicity are also considered, which may lead to excluding or restricting certain species [98,99].
In addition to zoonotic potential, factors such as body mass and feeding habits also influence therapeutic versatility, although to a lesser extent. Larger species tend to be used more, which may reflect both their greater yield in terms of biomass (organs, fat, bones) and a symbolic perception of strength or therapeutic efficacy [82,100,101]. However, this preference can be contradictory from a health point of view, as larger animals often host a greater diversity of pathogens, increasing the risk of zoonotic transmission [102,103]. Herbivorous and frugivorous species showed a slight tendency to be more versatile regarding eating habits, possibly due to cultural value and positive symbolic associations with purity, balance and health [104,105,106].
The integrated analysis of statistical models highlights that versatility results from the interaction between ecological, cultural and health risk factors. Zoonotic potential stands out as a significant barrier to use, so that species associated with a higher risk of transmission tend to be less versatile from a medicinal point of view and thus less used, reflecting an empirical logic of risk aversion. This trend suggests an interface between traditional knowledge and perceptions of safety that, even if not formalized, can act as filters in the selection process [107]. Communities have developed cultural strategies, such as cooking and smoking animals, to reduce biological risks, although these methods do not completely eliminate pathogens [108,109]. This reinforces the need to integrate traditional and scientific knowledge to promote safer practices that are compatible with biodiversity conservation.

4.3. Health and Conservation Implications and Study Limitations

The results of this study reinforce that the medicinal use of wild mammals represents a complex interface between public health, biodiversity conservation and sociocultural systems. The high diversity of species involved and the selection patterns observed indicate that although traditional medicinal practices are culturally legitimate, they can generate significant impacts on animal populations and on ecological balance, especially when associated with unregulated exploitation.
Overexploitation for medicinal purposes can contribute to the population decline of already vulnerable species, intensifying the risk of local and regional extinction [110,111]. Furthermore, as many of these mammals perform fundamental ecological functions, such as seed dispersal [112,113,114], the control of invertebrate populations [114] and the maintenance of the trophic structure [115]; their reduction can directly affect the integrity of ecosystems. Therefore, understanding the usage patterns and the factors which influence selection of these species is an essential step to support public policies for sustainable management and health surveillance [34,116].
Our results also highlight the need to incorporate the zoonotic dimension into conservation strategies. When species with a high potential for pathogen transmission are used in traditional contexts without adequate hygiene or processing measures, they represent a risk pathway for the health of human communities, especially those that directly depend on wildlife for subsistence [13,117,118]. Integrating ecological, ethnozoological and health data can serve as a basis for more integrated action plans aimed at both biodiversity protection and the safety of human populations. Formulated surveillance policies should consider the ecological and geographic context in which species occur. In addition, measures such as educational campaigns, review of management practices or the proposal of safe therapeutic alternatives can be essential to mitigate risks in areas where certain species overlap with vulnerable human communities. Localized strategies based on scientific evidence and intercultural dialogue are especially relevant given the complexity of traditional medical systems.
The disparity in the distribution and accessibility of species also influences their usage pressure. Species widely available in certain regions, such as Loxodonta africana and Panthera pardus, are associated with multiple medicinal uses with the use of various body parts (e.g., fat, stomach, skin, teeth, testicles and kidneys), which can intensify their extraction pressure [119,120,121]. In contrast, species with more restricted distribution or low population density, such as Spilogale gracilis and Paradoxurus hermaphroditus, tend to be less used, possibly due to their lower local availability [122,123,124]. The scarcity of ethnobiological records related to these species reinforces the hypothesis that ecological accessibility—determined by abundance and distribution—directly influences their inclusion or exclusion in medicinal practices. This disparity in use combined with the scarcity of data in some regions can mask critical exploitation patterns and compromise the effectiveness of conservation actions.
As with all studies based on secondary data, this analysis has inherent limitations in the quality and scope of the information available. The taxonomic, geographic and ecological accuracy of records may vary between sources and countries, reflecting both inequalities in monitoring capacity and knowledge gaps in less-studied regions [125]. Furthermore, by assuming that pathogens associated with a host species are uniformly distributed throughout its range (as defined by the IUCN), we disregard contextual factors important to transmission dynamics, such as the presence of vectors, local environmental conditions, seasonality and population density [126,127]. Although this simplification is methodologically necessary to enable analyses on a global scale, it represents an important limitation to be considered, especially when interpreting the results in regional and local contexts.

5. Conclusions

This study demonstrated that the therapeutic versatility of mammals used in traditional medicine is influenced by a combination of ecological, health and cultural factors. Zoonotic potential emerged as the main limiting factor, indicating that species with a higher risk of disease transmission tend to be avoided, even when they have multiple therapeutic applications. Factors such as body mass and dietary habits also contributed to explaining versatility, reflecting practical criteria for use and symbolic values associated with the species. These findings highlight the importance of local and regional analyses which reveal specific usage patterns, help identify species at greater risk and guide culturally sensitive conservation strategies. Thus, it becomes possible to develop more effective interventions by integrating ecological, health and sociocultural aspects to both preserve biodiversity and to protect the health of human communities that depend on it.

Supplementary Materials

The following supporting information can be downloaded at https://www.mdpi.com/article/10.3390/pathogens14070640/s1. Table S1. Wild mammals with medicinal uses recorded globally.

Author Contributions

Conceptualization, H.M.P. and R.R.N.A.; supervision, R.R.N.A.; data sourcing, H.M.P. and R.R.N.A.; data processing, H.M.P., D.V.B.O., W.R.G.d.S. and M.G.B.; data analysis, H.M.P. and M.G.B.; writing—original draft preparation, H.M.P.; writing—review and editing, M.G.B., H.M.P., A.K.M.B. and R.R.N.A. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Paraíba State Research Support Foundation (FAPESQ-PB), which awarded a doctoral scholarship to Heliene Mota Pereira (3390.18-07/2021), and by the Brazilian National Council for Scientific and Technological Development (CNPq), which granted a research productivity fellowship to Rômulo Romeu Nóbrega Alves (307011/2022-4). Additional financial support was provided by Paraíba State University (UEPB) and FAPESQ-PB.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

The original contributions presented in this study are included in the article. Further inquiries can be directed to the corresponding author.

Acknowledgments

We thank the Paraíba State Research Support Foundation (FAPESQ-PB) for their support, as well as all collaborators and colleagues who contributed—directly or indirectly—at various stages of this work, from its initial conception to its completion.

Conflicts of Interest

Author Danilo Vicente Batista Oliveira was employed by the company Masterboi. The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

References

  1. Cleaveland, S.; Laurenson, M.K.; Taylor, L.H. Diseases of Humans and Their Domestic Mammals: Pathogen Characteristics, Host Range and the Risk of Emergence. Philos. Trans. R. Soc. B Biol. Sci. 2001, 356, 991–999. [Google Scholar] [CrossRef] [PubMed]
  2. Shivaprakash, K.N.; Sen, S.; Paul, S.; Kiesecker, J.M.; Bawa, K.S. Mammals, Wildlife Trade, and the next Global Pandemic. Curr. Biol. 2021, 31, 3671–3677.e3. [Google Scholar] [CrossRef] [PubMed]
  3. Karesh, W.B.; Dobson, A.; Lloyd-Smith, J.O.; Lubroth, J.; Dixon, M.A.; Bennett, M.; Aldrich, S.; Harrington, T.; Formenty, P.; Loh, E.H.; et al. Ecology of Zoonoses: Natural and Unnatural Histories. Lancet 2012, 380, 1936–1945. [Google Scholar] [CrossRef]
  4. Fernandesferreira, H.; Alves, R.R.N. The Researches on the Hunting in Brazil: A Brief Overview. Ethnobiol. Conserv. 2017, 1–7. [Google Scholar] [CrossRef]
  5. Sexton, R.; Nguyen, T.; Roberts, D.L. The Use and Prescription of Pangolin in Traditional Vietnamese Medicine. Trop. Conserv. Sci. 2021, 14. [Google Scholar] [CrossRef]
  6. Wolfe, N.D.; Daszak, P.; Kilpatrick, A.M. Bushmeat Hunting, Deforestation, and Prediction of Zoonotic Disease Emergence. Emerg. Infect. Dis. 2005, 11, 1822–1827. [Google Scholar] [CrossRef]
  7. Paige, S.B.; Frost, S.D.W.; Gibson, M.A.; Jones, J.H.; Shankar, A.; Switzer, W.M.; Ting, N.; Goldberg, T.L. Beyond Bushmeat: Animal Contact, Injury, and Zoonotic Disease Risk in Western Uganda. Ecohealth 2014, 11, 534–543. [Google Scholar] [CrossRef]
  8. Tomley, F.M.; Shirley, M.W. Livestock Infectious Diseases and Zoonoses. Philos. Trans. R. Soc. B Biol. Sci. 2009, 364, 2637–2642. [Google Scholar] [CrossRef]
  9. Van Vliet, N.; Moreno, J.; Gómez, J.; Zhou, W.; Fa, J.E.; Golden, C.; Alves, R.R.N.; Nasi, R. Bushmeat and Human Health: Assessing the Evidence in Tropical and Sub-Tropical Forests. Ethnobiol. Conserv. 2017, 6. [Google Scholar] [CrossRef]
  10. Linder, A.K.; Jamieson, D.; Nadzam, B.; Jamieson, D.; Stilten, K. Animal Markets and Zoonotic Disease Risk a Global Synthesis of a 15 Country Study; Ministère de l'Aménagement du Territoire et de la Transition Écologique: Paris, France, 2024. [Google Scholar]
  11. Friant, S.; Paige, S.B.; Goldberg, T.L. Drivers of Bushmeat Hunting and Perceptions of Zoonoses in Nigerian Hunting Communities. PLoS Negl. Trop. Dis. 2015, 9, e0003792. [Google Scholar] [CrossRef]
  12. Friant, S.; Bonwitt, J.; Ayambem, W.A.; Ifebueme, N.M.; Alobi, A.O.; Otukpa, O.M.; Bennett, A.J.; Shea, C.; Rothman, J.M.; Goldberg, T.L.; et al. Zootherapy as a Potential Pathway for Zoonotic Spillover: A Mixed-Methods Study of the Use of Animal Products in Medicinal and Cultural Practices in Nigeria. One Health Outlook 2022, 4, 5. [Google Scholar] [CrossRef]
  13. Zeppelini, C.G.; Carneiro, I.d.O.; Mascarenhas de Abreu, P.; Linder, A.K.; Alves, R.R.N.; Costa, F. Wildlife as Food and Medicine in Brazil: A Neglected Zoonotic Risk? Pathogens 2024, 13, 222. [Google Scholar] [CrossRef] [PubMed]
  14. González-Barrio, D. Zoonoses and Wildlife: One Health Approach. Animals 2022, 12, 480. [Google Scholar] [CrossRef]
  15. Ellwanger, J.H.; Chies, J.A.B. Zoonotic Spillover: Understanding Basic Aspects for Better Prevention. Genet. Mol. Biol. 2021, 44, e20200355. [Google Scholar] [CrossRef]
  16. Alves, R.R.N. Relationships between Fauna and People and the Role of Ethnozoology in Animal Conservation. Ethnobiol. Conserv. 2012, 1. [Google Scholar] [CrossRef]
  17. 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, 646–650. [Google Scholar] [CrossRef] [PubMed]
  18. Perkins, S.E.; Cattadori, I.; Hudson, P.J. The Role of Mammals in Emerging Zoonoses. Mammal. Study 2005, 30, S67–S71. [Google Scholar] [CrossRef]
  19. Xu, R.-H.; He, J.-F.; Meirion, R.E. Epidemiologic Clues to SARS Origin in China. Emerg. Infect. Dis. 2004, 10, 1030–1037. [Google Scholar] [CrossRef] [PubMed]
  20. Bhadoria, P.; Gupta, G.; Agarwal, A. Viral Pandemics in the Past Two Decades: An Overview. J. Fam. Med. Prim. Care 2021, 10, 2745. [Google Scholar] [CrossRef]
  21. Da Silva Policarpo Brito, I.; Borges, A.K.M.; De Faria Lopes, S.; Dias, T.L.P.; Alves, R.R.N. Environmental Influence on the Choice of Medicinal Animals: A Case Study from Northeastern Brazil. J. Ethnobiol. Ethnomed. 2019, 15, 55. [Google Scholar] [CrossRef]
  22. Duonamou, L.; Konate, A.; Djossou, S.D.; Mensah, G.A.; Xu, J.; Humle, T. Consumer Perceptions and Reported Wild and Domestic Meat and Fish Consumption Behavior during the Ebola Epidemic in Guinea, West Africa. PeerJ 2020, 8, e9229. [Google Scholar] [CrossRef]
  23. Adeola, M.O. Importance of Wild Animals and Their Parts in the Culture, Religious Festivals, and Traditional Medicine, of Nigeria. Environ. Conserv. 1992, 19, 125–134. [Google Scholar] [CrossRef]
  24. Alves, R.R.N.; Borges, A.K.M.; Barboza, R.R.D.; Souto, W.M.S.; Gonçalves-Souza, T.; Provete, D.B.; Albuquerque, U.P. A Global Analysis of Ecological and Evolutionary Drivers of the Use of Wild Mammals in Traditional Medicine. Mamm. Rev. 2021, 51, 293–306. [Google Scholar] [CrossRef]
  25. Alves, R.R.N.; Rosa, I.L. From Cnidarians to Mammals: The Use of Animals as Remedies in Fishing Communities in NE Brazil. J. Ethnopharmacol. 2006, 107, 259–276. [Google Scholar] [CrossRef]
  26. Huffman, M.A. Folklore, Animal Self-Medication, and Phytotherapy-Something Old, Something New, Something Borrowed, Some Things True. Planta Med. 2022, 88, 187–199. [Google Scholar] [CrossRef]
  27. Alonso-Castro, A.J.; Carranza-Álvarez, C.; Maldonado-Miranda, J.J.; Del Rosario Jacobo-Salcedo, M.; Quezada-Rivera, D.A.; Lorenzo-Márquez, H.; Figueroa-Zúñiga, L.A.; Fernández-Galicia, C.; Ríos-Reyes, N.A.; De León-Rubio, M.Á.; et al. Zootherapeutic Practices in Aquismón, San Luis Potosí, México. J. Ethnopharmacol. 2011, 138, 233–237. [Google Scholar] [CrossRef]
  28. Caetano, R.d.A.; de Albuquerque, U.P.; de Medeiros, P.M. What Are the Drivers of Popularity and Versatility of Medicinal Plants in Local Medical Systems? Acta Bot. Bras. 2020, 34, 256–265. [Google Scholar] [CrossRef]
  29. Cartaxo, S.L.; de Almeida Souza, M.M.; de Albuquerque, U.P. Medicinal Plants with Bioprospecting Potential Used in Semi-Arid Northeastern Brazil. J. Ethnopharmacol. 2010, 131, 326–342. [Google Scholar] [CrossRef]
  30. Schaller, M. Parasites, Behavioral Defenses, and the Social Psychological Mechanisms Through Which Cultures Are Evoked; Lawrence Erlbaum Associates, Inc.: Mahwah, NJ, USA, 2006; Volume 17. [Google Scholar]
  31. Sarabian, C.; Curtis, V.; McMullan, R. Evolution of Pathogen and Parasite Avoidance Behaviours. Philos. Trans. R. Soc. B Biol. Sci. 2018, 373, 20170256. [Google Scholar] [CrossRef]
  32. Boccuto, D.P.P.; Mor, A.C.M.B.L.; Teixeira, D.V. The Cultural System Biomedical Health in Perspective in the Community Ilé Alákétu Asè Ifá Omo Oyá. Cienc. Saude Coletiva 2022, 27, 989–998. [Google Scholar] [CrossRef]
  33. Fialho, J. A Eficácia Simbólica Nos Sistemas Tradicionais de Saúde. Cad. Estud. Afr. 2003, 4, 121–133. [Google Scholar] [CrossRef]
  34. Alves, R.R.N.; Rosa, I.L. Introduction: Toward a Plural Approach to the Study of Medicinal Animals. In Animals in Traditional Folk Medicine: Implications for Conservation; Springer: Berlin/Heidelberg, Germany, 2013; pp. 1–9. ISBN 9783642290268. [Google Scholar]
  35. Han, B.A.; Kramer, A.M.; Drake, J.M. Global Patterns of Zoonotic Disease in Mammals. Trends Parasitol. 2016, 32, 565–577. [Google Scholar] [CrossRef]
  36. Johnson, C.K.; Hitchens, P.L.; Pandit, P.S.; Rushmore, J.; Evans, T.S.; Young, C.C.W.; Doyle, M.M. Global Shifts in Mammalian Population Trends Reveal Key Predictors of Virus Spillover Risk. Proc. R. Soc. B Biol. Sci. 2020, 287, 20192736. [Google Scholar] [CrossRef]
  37. Gibb, R.; Redding, D.W.; Chin, K.Q.; Donnelly, C.A.; Blackburn, T.M.; Newbold, T.; Jones, K.E. Zoonotic Host Diversity Increases in Human-Dominated Ecosystems. Nature 2020, 584, 398–402. [Google Scholar] [CrossRef]
  38. Schaller, M.; Murray, D.R.; Bangerter, A. Implications of the Behavioural Immune System for Social Behaviour and Human Health in the Modern World. Philos. Trans. R. Soc. B Biol. Sci. 2015, 370, 20140105. [Google Scholar] [CrossRef]
  39. Sarabian, C.; Ngoubangoye, B.; Macintosh, A.J. Avoidance of Biological Contaminants through Sight, Smell and Touch in Chimpanzees. R. Soc. Open Sci. 2017, 4, 170968. [Google Scholar] [CrossRef]
  40. Wardeh, M.; Sharkey, K.J.; Baylis, M. Integration of Shared-Pathogen Networks and Machine Learning Reveals the Key Aspects of Zoonoses and Predicts Mammalian Reservoirs. Proc. R. Soc. B Biol. Sci. 2020, 287, 20192882. [Google Scholar] [CrossRef]
  41. Wardeh, M.; Risley, C.; Mcintyre, M.K.; Setzkorn, C.; Baylis, M. Database of Host-Pathogen and Related Species Interactions, and Their Global Distribution. Sci. Data 2015, 2, 1500490. [Google Scholar] [CrossRef]
  42. Scherf, B.D. World Watch List for Domestic Animal Diversity, 3rd ed.; FAO: Rome, Italy, 2000. [Google Scholar]
  43. Chamberlain, S.; Szoecs, E.; Foster, Z.; Arendsee, Z.; Boettiger, C.; Ram, K. Taxize: Taxonomic Information from Around the Web; R Package Version 0.9.98; rOpenSci 2020. Available online: https://github.com/ropensci/taxize (accessed on 25 January 2024).
  44. GBIF. The GBIF Network. Available online: https://www.gbif.org/the-gbif-network (accessed on 18 October 2022).
  45. Jones, K.E.; Bielby, J.; Cardillo, M.; Fritz, S.A.; O’Dell, J.; Orme, C.D.L.; Safi, K.; Sechrest, W.; Boakes, E.H.; Carbone, C.; et al. PanTHERIA: A Species-level Database of Life History, Ecology, and Geography of Extant and Recently Extinct Mammals. Ecology 2009, 90, 2648. [Google Scholar] [CrossRef]
  46. Animalia ANIMALIA.Bio. Available online: https://animalia.bio/ (accessed on 28 October 2022).
  47. IUCN. Spatial Data Download. Available online: https://www.iucnredlist.org/en (accessed on 3 May 2025).
  48. Bennett, B.C.; Prance, G.T. Introduced Plants in the Indigenous Pharmacopoeia of Northern South America. Econ. Bot. 2000, 54, 90–102. [Google Scholar] [CrossRef]
  49. Zuur, A. Generalised Additive Models Applied on Northern Gannets. In A Beginners Guide to Generalized Additive Models with R; Highland Statistics Ltd.: Newburgh, UK, 2012; pp. 1–15. [Google Scholar]
  50. Hartig, F. DHARMa: Residual Diagnostics for Hierarchical (Multi-Level/Mixed) Regression Models; CRAN: Contributed Packages; [R package version 0.4.6]; Comprehensive R Archive Network (CRAN): Vienna, Austria, 2023; Available online: https://cran.r-project.org/package=DHARMa (accessed on 1 January 2025).
  51. Rousset, F.; Ferdy, J.B. Testing Environmental and Genetic Effects in the Presence of Spatial Autocorrelation. Ecography 2014, 37, 781–790. [Google Scholar] [CrossRef]
  52. Dray, S. Adespatial: Multivariate Multiscale Spatial Analysis R Package Version 0.3-22; CRAN: Contributed Packages; 2024. https://CRAN.R-project.org/package=adespatial (accessed on 1 January 2025).
  53. Albery, G.F.; Eskew, E.A.; Ross, N.; Olival, K.J. Predicting the Global Mammalian Viral Sharing Network Using Phylogeography. Nat. Commun. 2020, 11, 2260. [Google Scholar] [CrossRef]
  54. Leroux, S.J. On the Prevalence of Uninformative Parameters in Statistical Models Applying Model Selection in Applied Ecology. PLoS ONE 2019, 14, e0206711. [Google Scholar] [CrossRef]
  55. Choo, J.; Nghiem, L.T.P.; Chng, S.; Carrasco, L.R.; Benítez-López, A. Hotspots of Zoonotic Disease Risk from Wildlife Hunting and Trade in the Tropics. Integr. Conserv. 2023, 2, 165–175. [Google Scholar] [CrossRef]
  56. Han, B.A.; Castellanos, A.A.; Schmidt, J.P.; Fischhoff, I.R.; Drake, J.M. The Ecology of Zoonotic Parasites in the Carnivora. Trends Parasitol. 2021, 37, 1096–1110. [Google Scholar] [CrossRef]
  57. Veronesi, F.; Deak, G.; Diakou, A. Wild Mesocarnivores as Reservoirs of Endoparasites Causing Important Zoonoses and Emerging Bridging Infections across Europe. Pathogens 2023, 12, 178. [Google Scholar] [CrossRef]
  58. Park, A.W. Food Web Structure Selects for Parasite Host Range. Proc. R. Soc. B Biol. Sci. 2019, 286, 20191277. [Google Scholar] [CrossRef]
  59. Byers, J.E.; Schmidt, J.P.; Pappalardo, P.; Haas, S.E.; Stephens, P.R. What Factors Explain the Geographical Range of Mammalian Parasites? Proc. R. Soc. B Biol. Sci. 2019, 286, 20190673. [Google Scholar] [CrossRef]
  60. Rojas, A.; Germitsch, N.; Oren, S.; Sazmand, A.; Deak, G. Wildlife Parasitology: Sample Collection and Processing, Diagnostic Constraints, and Methodological Challenges in Terrestrial Carnivores. Parasit Vectors 2024, 17, 127. [Google Scholar] [CrossRef]
  61. Pedersen, A.B.; Davies, T.J. Cross-Species Pathogen Transmission and Disease Emergence in Primates. Ecohealth 2009, 6, 496–508. [Google Scholar] [CrossRef]
  62. Apetrei, C.; Kaur, A.; Lerche, N.W.; Metzger, M.; Pandrea, I.; Hardcastle, J.; Falkenstein, S.; Bohm, R.; Koehler, J.; Traina-Dorge, V.; et al. Molecular Epidemiology of Simian Immunodeficiency Virus SIVsm in U.S. Primate Centers Unravels the Origin of SIVmac and SIVstm. J. Virol. 2005, 79, 8991–9005. [Google Scholar] [CrossRef]
  63. Muehlenbein, M.P.; Ancrenaz, M.; Sakong, R.; Ambu, L.; Prall, S.; Fuller, G.; Raghanti, M.A. Ape Conservation Physiology: Fecal Glucocorticoid Responses in Wild Pongo Pygmaeus Morio Following Human Visitation. PLoS ONE 2012, 7, e33357. [Google Scholar] [CrossRef]
  64. Kalish, M.L.; Wolfe, N.D.; Ndongmo, C.B.; Mcnicholl, J.; Robbins, K.E.; Aidoo, M.; Fonjungo, P.N.; Alemnji, G.; Zeh, C.; Djoko, C.F.; et al. Central African Hunters Exposed to Simian Immunodeficiency Virus. Emerg. Infect. Dis. 2005, 11, 1928–1930. [Google Scholar] [CrossRef]
  65. Peeters, M.; Courgnaud, V.; Abela, B.; Auzel, P.; Pourrut, X.; Bibollet-Ruche, F.; Loul, S.; Liegeois, F.; Butel, C.; Koulagna, D.; et al. Risk to Human Health from a Plethora of Simian Immunodeficiency Viruses in Primate Bushmeat. Emerg. Infect. Dis. 2002, 8, 451. [Google Scholar] [CrossRef]
  66. Letafati, A.; Sakhavarz, T. Monkeypox Virus: A Review. Microb. Pathog. 2023, 176, 106027. [Google Scholar] [CrossRef]
  67. Srinivas, K.; Gagana Sri, R.; Pravallika, K.; Nishitha, K.; Polamuri, S.R. COVID-19 Prediction Based on Hybrid Inception V3 with VGG16 Using Chest X-Ray Images. Multimed. Tools Appl. 2024, 83, 36665–36682. [Google Scholar] [CrossRef]
  68. da Silva, M.B.; Portela, J.M.; Li, W.; Jackson, M.; Gonzalez-Juarrero, M.; Hidalgo, A.S.; Belisle, J.T.; Bouth, R.C.; Gobbo, A.R.; Barreto, J.G.; et al. Evidence of Zoonotic Leprosy in Pará, Brazilian Amazon, and Risks Associated with Human Contact or Consumption of Armadillos. PLoS Negl. Trop. Dis. 2018, 12, e0006532. [Google Scholar] [CrossRef]
  69. Deps, P.D.; Alves, B.L.; Gripp, C.G.; Aragão, R.L.; Guedes, B.V.S.; Filho, J.B.; Andreatta, M.K.; Marcari, R.S.; Prates, I.C.A.; Rodrigues, L.C. Contact with Armadillos Increases the Risk of Leprosy in Brazil: A Case Contact with Armadillos Increases the Risk of Leprosy in Brazil: A Case Control Study Control Study. Indian J. Dermatol. Venereol. Leprol. 2008, 74, 338. [Google Scholar] [CrossRef]
  70. Nash, H.C.; Wong, M.H.G.; Turvey, S.T. Using Local Ecological Knowledge to Determine Status and Threats of the Critically Endangered Chinese Pangolin (Manis Pentadactyla) in Hainan, China. Biol. Conserv. 2016, 196, 189–195. [Google Scholar] [CrossRef]
  71. Shairp, R.; Veríssimo, D.; Fraser, I.; Challender, D.; Macmillan, D. Understanding Urban Demand for Wild Meat in Vietnam: Implications for Conservation Actions. PLoS ONE 2016, 11, e0134787. [Google Scholar] [CrossRef]
  72. Xu, L.; Jing, G.; Lau, W.; Xiao, Y. An Overview of Pangolin Trade in China. Traffic Breafing 2016, 1–10. Available online: https://www.pangolinsg.org/wp-content/uploads/sites/35/2018/06/Xu-et-al_-2016_An-Overview-of-Pangolin-Trade-in-China.pdf (accessed on 10 June 2024).
  73. Roychoudhury, S.; Das, A.; Sengupta, P.; Dutta, S.; Roychoudhury, S.; Choudhury, A.P.; Fuzayel Ahmed, A.B.; Bhattacharjee, S.; Slama, P. Viral Pandemics of the Last Four Decades: Pathophysiology, Health Impacts and Perspectives. Int. J. Environ. Res. Public Health 2020, 17, 9411. [Google Scholar] [CrossRef]
  74. Coccolini, F.; Sartelli, M.; Kluger, Y.; Pikoulis, E.; Karamagioli, E.; Moore, E.E.; Biffl, W.L.; Peitzman, A.; Hecker, A.; Chirica, M.; et al. COVID-19 the Showdown for Mass Casualty Preparedness and Management: The Cassandra Syndrome. World J. Emerg. Surg. 2020, 15, 26. [Google Scholar] [CrossRef]
  75. Neumann, G.; Kawaoka, Y. The COVID-19 Pandemic—A Potential Role for Antivirals in Mitigating Pandemics. Viruses 2023, 15, 303. [Google Scholar] [CrossRef]
  76. Plourde, B.T.; Burgess, T.L.; Eskew, E.A.; Roth, T.M.; Stephenson, N.; Foley, J.E. Are Disease Reservoirs Special? Taxonomic and Life History Characteristics. PLoS ONE 2017, 12, e0180716. [Google Scholar] [CrossRef]
  77. Jiang, X.; Fan, Z.; Li, S.; Yin, H. A Review on Zoonotic Pathogens Associated with Non-Human Primates: Understanding the Potential Threats to Humans. Microorganisms 2023, 11, 246. [Google Scholar] [CrossRef]
  78. Liu, Z.J.; Qian, X.K.; Hong, M.H.; Zhang, J.L.; Li, D.Y.; Wang, T.H.; Yang, Z.M.; Zhang, L.Y.; Wang, Z.M.; Nie, H.J.; et al. Global View on Virus Infection in Non-Human Primates and Implications for Public Health and Wildlife Conservation. Zool. Res. 2021, 42, 626–632. [Google Scholar] [CrossRef]
  79. Alves, R.R.N.; Rosa, I.M.L. Biodiversity, Traditional Medicine and Public Health: Where Do They Meet? J. Ethnobiol. Ethnomed. 2007, 3, 14. [Google Scholar] [CrossRef]
  80. Bonwitt, J.; Kandeh, M.; Dawson, M.; Ansumana, R.; Sahr, F.; Kelly, A.H.; Brown, H. Participation of Women and Children in Hunting Activities in Sierra Leone and Implications for Control of Zoonotic Infections. PLoS Negl. Trop. Dis. 2017, 11, e0005699. [Google Scholar] [CrossRef]
  81. Morand, S.; McIntyre, K.M.; Baylis, M. Domesticated Animals and Human Infectious Diseases of Zoonotic Origins: Domestication Time Matters. Infect. Genet. Evol. 2014, 24, 76–81. [Google Scholar] [CrossRef]
  82. Fa, J.E.; Funk, S.M.; Nasi, R. Hunting Wildlife in the Tropics and Subtropics; Cambridge University Press: Cambridge, UK, 2022. [Google Scholar]
  83. Hlay, J.K.; Albert, G.; Batres, C.; Richardson, G.; Placek, C.; Arnocky, S.; Lieberman, D.; Hodges-Simeon, C.R. The Evolution of Disgust for Pathogen Detection and Avoidance. Sci. Rep. 2021, 11, 13468. [Google Scholar] [CrossRef]
  84. Biggs, D.; Courchamp, F.; Martin, R.; Possingham, H.P. Legal Trade of Africa’s Rhino Horns. Science 2013, 339, 1038–1039. [Google Scholar] [CrossRef]
  85. Júnior, W.S.F.; Albuquerque, U.P. A Theoretical Review on the Origin of Medicinal Practices in Humans: Echoes from Evolution. Ethnobiol. Conserv. 2018, 7, 3. [Google Scholar] [CrossRef]
  86. Moura, F.D.B.P.; Marques, J.G.W. Zooterapia popular na Chapada Diamantina: Uma medicina incidental? Ciênc. Saúde Coletiva 2008, 13 (Suppl. 2). [Google Scholar] [CrossRef]
  87. Santoro, F.R.; Chaves, L.S.; Albuquerque, U.P. Evolutionary Aspects That Guide the Cultural Transmission Pathways in a Local Medical System in Northeast Brazil. Heliyon 2020, 6, e04109. [Google Scholar] [CrossRef]
  88. Leroy, E.M.; Rouquet, P.; Formenty, P.; Souquière, S.; Kilbourne, A.; Froment, J.M.; Bermejo, M.; Smit, S.; Karesh, W.; Swanepoel, R.; et al. Multiple Ebola Virus Transmission Events and Rapid Decline of Central African Wildlife. Science 2004, 303, 387–390. [Google Scholar] [CrossRef]
  89. de Macedo, G.C.; Herrera, H.M.; de Oliveira Porfírio, G.E.; Santos, F.M.; de Assis, W.O.; de Andrade, G.B.; Nantes, W.A.G.; de Mendoza, J.H.; Fernández-Llario, P.; de Oliveira, C.E. Brucellosis in the Brazilian Pantanal Wetland: Threat to Animal Production and Wildlife Conservation. Braz. J. Microbiol. 2022, 53, 2287–2297. [Google Scholar] [CrossRef]
  90. Real, V.V.; Dutra, V.; Nakazato, L.d.F.; Keuroghlian, A. PCR of Salmonella spp., Streptococcus Suis, Brucella Abortus and Porcine Circovirus Type 2 in Free-Living and Captive Peccaries. Rev. Bras. Saúde Prod. Anim. 2010, 11, 858–864. [Google Scholar]
  91. Chua, K.; Bellini, W.; Rota, P.; Harcourt, B. Nipah Virus: A Recently Emergent Deadly Paramyxovirus. Science 2000, 288, 1432–1435. [Google Scholar] [CrossRef]
  92. Gama, A.D.S.; de Paula, M.; da Silva, R.R.V.; Ferreira, W.S.; de Medeiros, P.M. Exotic Species as Models to Understand Biocultural Adaptation: Challenges to Mainstream Views of Human-Nature Relations. PLoS ONE 2018, 13, e0196091. [Google Scholar] [CrossRef]
  93. Albuquerque, U.P.; de Medeiros, P.M.; Ferreira Júnior, W.S.; da Silva, T.C.; da Silva, R.R.V.; Gonçalves-Souza, T. Social-Ecological Theory of Maximization: Basic Concepts and Two Initial Models. Biol. Theory 2019, 14, 73–85. [Google Scholar] [CrossRef]
  94. de Medeiros, P.; Ladio, A.H.; Albuquerque, U.P. Critérios Locais de Seleção e Uso Diferencial de Plantas Medicinais: Porque Nos Escolhemos o Que Escolhemos; NUPEEA: Montreal, QC, Canada, 2013; ISBN 978-85-63756-21-3. [Google Scholar]
  95. Casagrande, D.G. Human Taste and Cognition in Tzeltal Maya Medicinal Plant Use. J. Ecol. Anthr. 2000, 4, 57–69. [Google Scholar] [CrossRef]
  96. Molares, S.; Ladio, A. The Usefulness of Edible and Medicinal Fabaceae in Argentine and Chilean Patagonia: Environmental Availability and Other Sources of Supply. Evid.-Based Complement. Altern. Med. 2012, 2012, 901918. [Google Scholar] [CrossRef]
  97. Leonti, M.; Sticher, O.; Heinrich, M. Medicinal Plants of the Popoluca, México: Organoleptic Properties as Indigenous Selection Criteria. J. Ethnopharmacol. 2002, 81, 307–315. [Google Scholar] [CrossRef]
  98. Henrich, J.; Henrich, N. The Evolution of Cultural Adaptations: Fijian Food Taboos Protect against Dangerous Marine Toxins. Proc. R. Soc. B Biol. Sci. 2010, 277, 3715–3724. [Google Scholar] [CrossRef]
  99. Martin, A.; Caro, T.; Kiffner, C. Prey Preferences of Bushmeat Hunters in an East African Savannah Ecosystem. Eur. J. Wildl. Res. 2013, 59, 137–145. [Google Scholar] [CrossRef]
  100. Brammer, J.R.; Menzies, A.K.; Carter, L.S.; Giroux-Bougard, X.; Landry-Cuerrier, M.; Leblanc, M.L.; Neelin, M.N.; Studd, E.K.; Humphries, M.M. Weighing the Importance of Animal Body Size in Traditional Food Systems. Facets 2022, 7, 286–318. [Google Scholar] [CrossRef]
  101. Souto, W.M.S.; Barboza, R.R.D.; Fernandes-Ferreira, H.; Júnior, A.J.C.M.; Monteiro, J.M.; Abi-Chacra, É.d.A.; Alves, R.R.N. Zootherapeutic Uses of Wildmeat and associated Products in the Semiarid region of Brazil: General Aspects and Challenges For. J. Ethnobiol. Ethnomed. 2018, 14, 60. [Google Scholar] [CrossRef]
  102. Lindenfors, P.; Nunn, C.L.; Jones, K.E.; Cunningham, A.A.; Sechrest, W.; Gittleman, J.L. Parasite Species Richness in Carnivores: Effects of Host Body Mass, Latitude, Geographical Range and Population Density. Glob. Ecol. Biogeogr. 2007, 16, 496–509. [Google Scholar] [CrossRef]
  103. Poulin, R.; George-Nascimento, M. The Scaling of Total Parasite Biomass with Host Body Mass. Int. J. Parasitol. 2007, 37, 359–364. [Google Scholar] [CrossRef]
  104. Bezerra, D.M.M.; de Araujo, H.F.P.; Alves, Â.G.C.; Alves, R.R.N. Birds and People in Semiarid Northeastern Brazil: Symbolic and Medicinal Relationships. J. Ethnobiol. Ethnomed. 2013, 9, 3. [Google Scholar] [CrossRef] [PubMed]
  105. Frazão-Moreira, A. The Symbolic Efficacy of Medicinal Plants: Practices, Knowledge, and Religious Beliefs amongst the Nalu Healers of Guinea-Bissau. J. Ethnobiol. Ethnomed. 2016, 12, 24. [Google Scholar] [CrossRef]
  106. Pilnik, M.S.; Argentim, T.; Kinupp, V.F.; Haverroth, M.; Ming, L.C. Traditional Botanical Knowledge: Food Plants from the Huni Kuĩ Indigenous People, Acre, Western Brazilian Amazon. Rodriguesia 2023, 74, 1–23. [Google Scholar] [CrossRef]
  107. Ulicsni, V.; Babai, D.; Vadász, C.; Vadász-Besnyői, V.; Báldi, A.; Molnár, Z. Bridging Conservation Science and Traditional Knowledge of Wild Animals: The Need for Expert Guidance and Inclusion of Local Knowledge Holders. Ambio 2019, 48, 769–778. [Google Scholar] [CrossRef]
  108. Alhaji, N.B.; Yatswako, S.; Oddoh, E.Y. Knowledge, Risk Perception and Mitigation Measures towards Ebola Virus Disease by Potentially Exposed Bushmeat Handlers in North-Central Nigeria: Any Critical Gap? Zoonoses Public Health 2018, 65, 158–167. [Google Scholar] [CrossRef] [PubMed]
  109. van Vliet, N.; Muhindo, J.; Nyumu, J.; Enns, C.; Massé, F.; Bersaglio, B.; Cerutti, P.; Nasi, R. Understanding Factors That Shape Exposure to Zoonotic and Food-Borne Diseases Across Wild Meat Trade Chains. Hum. Ecol. 2022, 50, 983–995. [Google Scholar] [CrossRef]
  110. Haq, S.M.; Waheed, M.; Bussmann, R.W. “Traditional” Use in a Global World: Unsustainable Ethnozoological Usage among Himalayan Ethnic Groups Drives Species to Extinction. Biodivers. Conserv. 2024, 33, 1125–1144. [Google Scholar] [CrossRef]
  111. Romanelli, C.; Cooper, D.; Campbell-Lendrum, D.; Maiero, M.; Karesh, B. Connecting Global Priorities: Biodiversity and Human Health a State of Knowledge Review; World Health Organization and Secretariat for the Convention on Biological Diversity: Geneva, Switzerland, 2015. [Google Scholar]
  112. Rubalcava-Castillo, F.A.; Sosa-Ramírez, J.; Luna-Ruíz, J.d.J.; Valdivia-Flores, A.G.; Íñiguez-Dávalos, L.I. Seed Dispersal by Carnivores in Temperate and Tropical Dry Forests. Ecol. Evol. 2021, 11, 3794–3807. [Google Scholar] [CrossRef]
  113. Ruxton, G.D.; Martin Schaefer, H. The Conservation Physiology of Seed Dispersal. Philos. Trans. R. Soc. B Biol. Sci. 2012, 367, 1708–1718. [Google Scholar] [CrossRef]
  114. Kunz, T.H.; de Torrez, E.B.; Bauer, D.; Lobova, T.; Fleming, T.H. Ecosystem Services Provided by Bats. Ann. N. Y. Acad. Sci. 2011, 1223, 1–38. [Google Scholar] [CrossRef] [PubMed]
  115. Lacher, T.E.; Davidson, A.D.; Fleming, T.H.; Gómez-Ruiz, E.P.; McCracken, G.F.; Owen-Smith, N.; Peres, C.A.; Vander Wall, S.B. The Functional Roles of Mammals in Ecosystems. J. Mammal. 2019, 100, 942–964. [Google Scholar] [CrossRef]
  116. Ryser-Degiorgis, M.P. Wildlife Health Investigations: Needs, Challenges and Recommendations. BMC Veter Res. 2013, 9, 223. [Google Scholar] [CrossRef]
  117. Winck, G.R.; Raimundo, R.L.G.; Fernandes-Ferreira, H.; Bueno, M.G.; D’Andrea, P.S.; Rocha, F.L.; Cruz, G.L.T.; Vilar, E.M.; Brandão, M.; Cordeiro, J.L.P.; et al. Socioecological Vulnerability and the Risk of Zoonotic Disease Emergence in Brazil. Sci. Adv. 2022, 8, eabo5774. [Google Scholar] [CrossRef] [PubMed]
  118. Cantlay, J.C.; Ingram, D.J.; Meredith, A.L. A Review of Zoonotic Infection Risks Associated with the Wild Meat Trade in Malaysia. Ecohealth 2017, 14, 361–388. [Google Scholar] [CrossRef]
  119. Nieman, W.A.; Leslie, A.J.; Wilkinson, A. Traditional Medicinal Animal Use by Xhosa and Sotho Communities in the Western Cape Province, South Africa. J. Ethnobiol. Ethnomed. 2019, 15, 34. [Google Scholar] [CrossRef] [PubMed]
  120. Djagoun, C.A.M.S.; Akpona, H.A.; Mensah, G.A.; Nuttman, C.; Sinsin, B. Wild Mammals Trade for Zootherapeutic and Mythic Purposes in Benin (West Africa): Capitalizing Species Involved, Provision Sources, and Implications for Conservation. In Animals in Traditional Folk Medicine: Implications for Conservation; Springer: Berlin/Heidelberg, Germany, 2013; pp. 367–381. ISBN 9783642290268. [Google Scholar]
  121. Assefa, A.; Mesfin, K.; Girmay, T. A Comprehensive Review on Animals and Their Products Used in Traditional Folk Medicine in Ethiopia. J. Ethnobiol. Ethnomed. 2025, 21, 24. [Google Scholar] [CrossRef] [PubMed]
  122. Dehaudt, B.; Amir, Z.; Decoeur, H.; Gibson, L.; Mendes, C.; Moore, J.H.; Nursamsi, I.; Sovie, A.; Luskin, M.S. Common Palm Civets Paradoxurus Hermaphroditus Are Positively Associated with Humans and Forest Degradation with Implications for Seed Dispersal and Zoonotic Diseases. J. Anim. Ecol. 2022, 91, 794–804. [Google Scholar] [CrossRef]
  123. Souto, W.M.S.; Mourão, J.S.; Barboza, R.R.D.; Mendonça, L.E.T.; Lucena, R.F.P.; Confessor, M.V.A.; Vieira, W.L.S.; Montenegro, P.F.G.P.; Lopez, L.C.S.; Alves, R.R.N. Medicinal Animals Used in Ethnoveterinary Practices of the “Cariri Paraibano”, NE Brazil. J. Ethnobiol. Ethnomed. 2011, 7, 30. [Google Scholar] [CrossRef]
  124. Teixeira, J.V.D.S.; Dos Santos, J.S.; Guanaes, D.H.A.; da Rocha, W.D.; Schiavetti, A. Uses of Wild Vertebrates in Traditional Medicine by Farmers in the Region Surrounding the Serra Do Conduru State Park (Bahia, Brazil). Biota Neotrop. 2020, 20, 1–12. [Google Scholar] [CrossRef]
  125. Meyer, C.; Kreft, H.; Guralnick, R.; Jetz, W. Global Priorities for an Effective Information Basis of Biodiversity Distributions. Nat. Commun. 2015, 6, 8221. [Google Scholar] [CrossRef]
  126. Plowright, R.K.; Parrish, C.R.; McCallum, H.; Hudson, P.J.; Ko, A.I.; Graham, A.L.; Lloyd-Smith, J.O. Pathways to Zoonotic Spillover. Nat. Rev. Microbiol. 2017, 15, 502–510. [Google Scholar] [CrossRef] [PubMed]
  127. Carlson, C.J.; Zipfel, C.M.; Garnier, R.; Bansal, S. Global Estimates of Mammalian Viral Diversity Accounting for Host Sharing. Nat. Ecol. Evol. 2019, 3, 1070–1075. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Overview of inclusion and exclusion criteria applied during dataset construction.
Figure 1. Overview of inclusion and exclusion criteria applied during dataset construction.
Pathogens 14 00640 g001
Figure 2. Distribution of host species and richness of zoonotic pathogens among mammalian orders. (A) Number of host mammalian species used in traditional medicine, grouped by taxonomic order. (B) Total richness of recorded pathogens and number of zoonotic pathogens associated with these species, by mammalian order.
Figure 2. Distribution of host species and richness of zoonotic pathogens among mammalian orders. (A) Number of host mammalian species used in traditional medicine, grouped by taxonomic order. (B) Total richness of recorded pathogens and number of zoonotic pathogens associated with these species, by mammalian order.
Pathogens 14 00640 g002
Figure 3. Number of zoonoses associated with the five main groups of pathogens based on their taxonomic classification.
Figure 3. Number of zoonoses associated with the five main groups of pathogens based on their taxonomic classification.
Pathogens 14 00640 g003
Figure 4. Number of zoonotic diseases attributed to viruses, bacteria, protozoa, helminths and fungi recorded in the 17 taxonomic orders of mammals used in traditional medicine. (A) Total number of zoonotic pathogens across all mammal orders (combined pathogen types). (B) Number of viruses reported per mammal order. (C) Number of protozoa reported per mammal order. (D) Number of bacteria reported per mammal order. (E) Number of fungi reported per mammal order. (F) Number of helminths reported per mammal order.
Figure 4. Number of zoonotic diseases attributed to viruses, bacteria, protozoa, helminths and fungi recorded in the 17 taxonomic orders of mammals used in traditional medicine. (A) Total number of zoonotic pathogens across all mammal orders (combined pathogen types). (B) Number of viruses reported per mammal order. (C) Number of protozoa reported per mammal order. (D) Number of bacteria reported per mammal order. (E) Number of fungi reported per mammal order. (F) Number of helminths reported per mammal order.
Pathogens 14 00640 g004
Figure 5. Global occurrence of medicinal use of wild mammals. The map shows countries where at least one medicinal use of a wild mammal species has been reported.
Figure 5. Global occurrence of medicinal use of wild mammals. The map shows countries where at least one medicinal use of a wild mammal species has been reported.
Pathogens 14 00640 g005
Figure 6. Average of candidate models with ΔAIC ≤ 2 for predicting the therapeutic versatility of mammals. (A) Average coefficients (±standard error) of the explanatory variables: zoonotic potential, body mass and feeding habits; (B) relative importance of variables (RVI) based on the frequency of inclusion in the models.
Figure 6. Average of candidate models with ΔAIC ≤ 2 for predicting the therapeutic versatility of mammals. (A) Average coefficients (±standard error) of the explanatory variables: zoonotic potential, body mass and feeding habits; (B) relative importance of variables (RVI) based on the frequency of inclusion in the models.
Pathogens 14 00640 g006
Table 1. Medicinal mammal species with the greatest therapeutic versatility, ordered by relative importance (RI).
Table 1. Medicinal mammal species with the greatest therapeutic versatility, ordered by relative importance (RI).
SpeciesOrderRIBody Part UsedVirus (n)Protozoa (n)Bacteria (n)Fungi (n)Helminths (n)
Ursus arctosCarnivora1.54Unspecified725212
Mephitis
macroura
Carnivora1.55Meat, fat10000
Ursus
americanus
Carnivora1.58Unspecified923112
Ursus maritimusCarnivora1.58Blood, Carapace, Nails, Fat, Lard, Feet, Flesh, Skin, Tail, Urine, Whole Animal64114
Dasypus
novemcinctus
Cingulata1.66Blood, Carapace, Nails, Fat, Lard, Feet, Meat, Skin, Tail, Urine, Whole Animal33102
Manis giganteaPholidota1.8Blood, Bones, Brain, Eyes, Fat, Flesh, Head, Scales, Whole animal, Body, Claws, Meat, Scales00100
Mammalian species with IR > 5. Therapeutic versatility is expressed through the Relative Importance Index (RI), which considers both the number of use categories (NUC) and the number of therapeutic indications (NT) reported for each species.
Table 2. Candidate models with ΔAIC ≤ 2 explaining the therapeutic versatility of medicinal mammals based on zoonotic potential, body mass and feeding habits.
Table 2. Candidate models with ΔAIC ≤ 2 explaining the therapeutic versatility of medicinal mammals based on zoonotic potential, body mass and feeding habits.
ModelkLogLikAICcΔWeight
1. Zoonotic potential0.295367.191−720.3810.0000.295
2. Body mass (g)0.169366.635−719.2711.1100.169
3. Feeding habitat0.152367.529−719.0581.3230.152
4. Zoonotic potential + body mass (g)0.146369.487−718.9741.4070.146
5. Zoonotic potential + feeding habit0.090370.003−718.0062.3750.090
6. Body mass (g) + feeding habitat0.068369.732−717.4642.9170.068
Gamma (zoonotic potential + body mass (g) + feeding habit)0.048370.380−716.7613.6200.048
Null0.029362.891−715.7834.5980.029
Models with substantial empirical evidence (ΔAIC ≤ 2); k = number of parameters in the model; Loglik = log-likelihood; AIC = second-order Akaike information criterion; Δ = AIC difference between the model under concern and the best model; Weight = Akaike weight, i.e., the likelihood of the model being the best in the set of candidate models.
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Pereira, H.M.; Beltrão, M.G.; Borges, A.K.M.; Silva, W.R.G.d.; Oliveira, D.V.B.; Alves, R.R.N. Healing with Risks: How Zoonotic Potential Influences the Use of Wild Mammals in Traditional Medicine. Pathogens 2025, 14, 640. https://doi.org/10.3390/pathogens14070640

AMA Style

Pereira HM, Beltrão MG, Borges AKM, Silva WRGd, Oliveira DVB, Alves RRN. Healing with Risks: How Zoonotic Potential Influences the Use of Wild Mammals in Traditional Medicine. Pathogens. 2025; 14(7):640. https://doi.org/10.3390/pathogens14070640

Chicago/Turabian Style

Pereira, Heliene Mota, Mayara Guimarães Beltrão, Anna Karolina Martins Borges, Weslley Ruan Guimarães da Silva, Danilo Vicente Batista Oliveira, and Rômulo Romeu Nóbrega Alves. 2025. "Healing with Risks: How Zoonotic Potential Influences the Use of Wild Mammals in Traditional Medicine" Pathogens 14, no. 7: 640. https://doi.org/10.3390/pathogens14070640

APA Style

Pereira, H. M., Beltrão, M. G., Borges, A. K. M., Silva, W. R. G. d., Oliveira, D. V. B., & Alves, R. R. N. (2025). Healing with Risks: How Zoonotic Potential Influences the Use of Wild Mammals in Traditional Medicine. Pathogens, 14(7), 640. https://doi.org/10.3390/pathogens14070640

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop