Abstract
Background
Mesoamerica, a biodiversity hotspot extending from Mexico to Panama, faces intersecting health challenges rooted in colonial-era transformations and amplified by contemporary environmental change. This perspective paper demonstrates how historical legacies interact with current ecological and social drivers to shape zoonotic disease vulnerability across the region.
Approach
We integrate historical analysis of colonial disease introduction with an examination of current environmental, climatic, and social determinants of disease transmission. Findings from a structured multisectoral participatory workshop organized by the GLACIER Project Consortium in Guatemala in 2023, involving participants from academia, government, non-governmental organizations, and community representatives across Mesoamerica, were synthesized together with a narrative review to develop community-centered One Health strategies for the region.
Key findings
European colonization of the Americas during the 15th–18th centuries, introduced devastating pathogens and fundamentally altered disease ecology through the introduction of livestock, human-associated pathogens, vectors, and reservoirs, establishing transmission patterns that persist today. Contemporary vulnerabilities arise from: deforestation and agricultural expansion facilitating vector proliferation and wildlife-human contact; informal and unregulated animal movement enabling the spread of transboundary diseases; climate change altering vector distribution and creating novel health threats; fragmented health systems with inequitable access; and poverty-linked structural conditions amplifying disease transmission. Despite growing One Health discourse regionally, meaningful integration across human, animal, plant, and environmental health sectors remains limited, as evidenced by recent disease resurgences and continued institutional gaps in surveillance and cross-border coordination.
Strategic recommendations
Six priority action lines emerged from the workshop discussions and their thematic synthesis: strengthening intersectoral governance and regional cooperation; implementing integrated surveillance systems; ensuring community participation and intercultural inclusion of Indigenous knowledge; expanding culturally appropriate health education; promoting community-engaged applied research; and integrating sustainable territorial management. Success requires political commitment beyond economic capacity, positioning communities as decision-makers, and alignment with international frameworks including the FAO-WOAH-WHO-UNEP Joint Plan of Action.
Conclusions
Mesoamerica’s interconnected health challenges demand One Health approaches acknowledging historical context while centering vulnerable communities. Regional cooperation, community empowerment, and sustained political will—rather than wealth alone—determine effective disease prevention and health equity.
Graphical Abstract
Keywords: One Health, Zoonotic diseases, Mesoamerica, Land-use change, Social determinants of health, Health governance, Indigenous people, Poverty
Introduction
Mesoamerica, a region of remarkable biogeographic and cultural richness extending from southern Mexico to the Darién region of Panama, is recognized as one of the world’s 25 biodiversity hotspots. Its strategic location encompasses over 40 terrestrial ecoregions and a wide array of subtropical and tropical ecosystems. Recent estimates indicate that the region harbors approximately 17,000 species of vascular plants, with around 3,000 endemic species, and more than 440 species of mammals, of which over 65 are endemic to the region [1, 2]. This exceptional richness makes Mesoamerica a global priority for biodiversity conservation and ecosystem-based health strategies which is also highly relevant to zoonotic disease risk because species-rich taxonomic orders are supposed to host a greater diversity of zoonotic pathogens [3], Fig. 1). The region is also known for its rich Indigenous cultural legacy, encompassing diverse Peoples such as the Maya, Garífuna, Ngäbe, Bribri, Cabécar, and Guna, among many others, each with distinct cultural traditions, languages, and relationships with their territories [4, 5]. Throughout this paper, Mesoamerica is treated as a distinct biocultural region within the broader Latin American context. Consequently, although the primary focus is on Mesoamerica, evidence from Latin America is incorporated where appropriate to provide regional context and inform broader One Health discussions.
Fig. 1.
Conceptual representation of the dilution effect in Mesoamerican and temperate landscapes. Although disturbed Mesoamerican landscapes may exhibit higher baseline zoonotic risk due to elevated vector density, they also show a more pronounced dilution effect. As biodiversity increases, ecological filtering by non-competent hosts reduces pathogen transmission and lowers the risk of human spillover more effectively than in temperate systems
In this complex context of ecological, social, and health challenges in Mesoamerica, the One Health approach gains relevance as an integrated and systemic framework. Rather than simply linking human, animal, and environmental health, One Health aims to sustainably balance and optimize the health of people, animals, plants, and ecosystems, recognizing their interdependence while mobilizing multiple sectors, disciplines, and communities to collaboratively address shared risks and underlying drivers (One Health High-Level Expert Panel -OHHLEP [6]). Recent regional assessments indicate that although One Health initiatives have expanded considerably across Latin America and the Caribbean, implementation remains uneven across the region, with persistent challenges related to governance, institutionalization, sustainable financing, and cross-sectoral integration [7]. This includes not only zoonotic disease emergence, but also broader challenges such as land-use change, biodiversity loss, food systems, and climate change, emphasizing prevention, equity, and coordinated action across scales [8, 9].
This perspectives paper aims to demonstrate the interconnectedness of human, animal, and environmental health in disease transmission in Mesoamerica. By i) providing an in-depth narrative review of the historical legacy of colonization and the region’s current ecological and sociocultural threats, and ii) integrating priorities identified through a structured inter- and transdisciplinary multisectorial workshop on zoonotic diseases, the paper seeks to suggest strategies and recommendations for disease prevention and control that not only reduce transmission, but also strengthen local and regional public health within a One Health framework. We particularly advocate for Indigenous and local communities to be active decision-makers in health policies, while respecting the region’s rich cultural diversity and unique ecological contexts.
Historical context: colonial legacy and disease introduction
The European colonization of Mesoamerica brought not only profound political, economic, and ecological disruptions, but also introduced previously absent infectious diseases that proved devastating to immunologically naïve Indigenous populations. Smallpox, measles, and hemorrhagic fevers rapidly spread across the region, triggering demographic collapse on an unprecedented scale. Estimations show that between 60 and 90% of the Indigenous population perished within the first decades of contact due to these epidemics [10, 11]. Historical records and epidemiological reconstructions have documented large-scale outbreaks of hemorrhagic fevers, possibly linked to zoonotic or vector-borne pathogens, during the 16th to 18th centuries [12, 13]. These events, often exacerbated by concurrent megadroughts, intensified the collapse of preexisting socioecological systems [14].
Smallpox played a central role in this demographic catastrophe, with high transmission rates via respiratory droplets and contaminated items, and extreme virulence in naïve populations [15]. The impact of these diseases cannot be overstated, as they not only decimated populations but also restructured landscapes, settlement patterns, and human–animal–environment interactions in ways that would define the region’s disease ecology for centuries.
Introduction of livestock and transformation of disease ecology
Beyond the immediate mortality from introduced pathogens, European colonization permanently altered the region’s disease ecology through the introduction of new domesticated animal species. Prior to European contact, only two domesticated species were widely recognized in Mesoamerica: the dog which has been essential for hunting, and the turkey which was valued for its meat and feathers [16]. Following the conquest, European settlers introduced cattle, pigs, sheep, and horses, fundamentally reshaping both ecological and cultural landscapes [17]. These introductions brought a suite of new infectious agents, many of them zoonotic, which posed health risks to both humans and animals and established novel transmission cycles that persist today.
Among the most significant zoonoses introduced during this period was brucellosis. Cattle became primary reservoirs of Brucella spp. throughout Central America, while pigs and dogs served as secondary hosts. This colonial-era introduction established endemic transmission patterns that would shape the region’s epidemiological landscape for centuries. The transformation of human-animal relationships, from limited contact with dogs and turkeys to intensive interaction with multiple livestock species, created new pathways for pathogen spillover and fundamentally altered disease risk profiles across Mesoamerica [18, 19].
Contemporary impacts of historical legacies
The colonial transformations described above established structural vulnerabilities that continue to amplify disease risk in the face of contemporary environmental and social change. The epidemiological consequences of colonial-era pathogen and livestock introductions remain evident in contemporary disease patterns, with diseases such as brucellosis continuing to pose significant public health challenges across the region. This persistent burden reflects how colonial transformations continue to shape health outcomes through the biological legacy of introduced pathogens and reservoir species, cultural practices such as consumption of unpasteurized dairy products and occupational exposure to infected livestock, and socioeconomic structures that determine access to veterinary services and healthcare [18, 19]. Rural and Indigenous communities who are often those with highest zoonotic disease exposure, face substantial barriers to care due to health system limitations rooted in colonial-era inequalities [20].
Beyond these direct disease legacies, Mesoamerican communities today face compounding health threats from deforestation [21], rapid urban expansion [22], and climate change [23]. These multiple environmental pressures do not affect all populations equally. The pressures interact with colonial-era patterns of land dispossession and marginalization to disproportionately burden Indigenous and rural communities [24]. Deforestation driven by agricultural expansion often occurs in territories occupied by communities that were historically displaced to marginal lands, simultaneously destroying traditional resource bases while increasing contact with wildlife reservoirs and disease vectors [25]. Rapid, unplanned urban growth concentrates populations in areas with inadequate water and sanitation infrastructure, creating conditions favorable for both vector-borne and waterborne disease transmission [26]. Climate change further shifts the geographic range of disease vectors and reservoirs, expanding transmission into communities with limited immunity and healthcare access [27]. These converging pressures place mounting strain on healthcare systems whose spatial distribution of facilities, diagnostic capacity, and personnel still reflects colonial administrative priorities, e.g. such as particularly the historical concentration of services in major urban centers, rather than current epidemiological needs [24, 28].
Socioeconomic inequalities, political and social marginalization rooted in colonial hierarchies, and limited access to healthcare continue to exacerbate vulnerability to both emerging and reemerging diseases [29, 30]. Addressing these interconnected challenges requires comprehensive care models grounded in equity, cultural relevance, and social justice. Such approaches that recognize Indigenous and local communities not only as beneficiaries of health interventions, but also as key stakeholders whose traditional knowledge and lived experience can contribute meaningfully to informing culturally relevant and equitable policy and practice [31, 32]. This perspective is also consistent with recent One Health frameworks that recognize social determinants, equity, and community participation as essential components of effective health interventions [33].
Current environmental and ecological drivers of disease
Land use change, deforestation, and ecosystem disruption
Land-use change processes have profound implications for public health and socio-environmental resilience in Mesoamerica. The human-environment relationships in this region have been studied for decades, revealing a continuous interaction dating back at least 10,000 years [4, 5, 34]. Agriculture profoundly transformed the landscape during the Maya civilization, with up to 75% of the land altered by intensive agricultural practices including forest burning, specialized techniques, and infrastructure such as raised fields, canals, and terraces [35–37].
Many tropical forest areas recovered following the decline of Classic Maya society (1200–1000 BP) and subsequent population decline after the Spanish Conquest. Today’s ecosystems, such as those in Panama’s Darién or Guatemala’s northern Petén, represent mature secondary forests regenerating for approximately 350 years, though still undergoing gradual changes due to long canopy tree life cycles [34, 38]. In contrast to this historical recovery, contemporary deforestation is driven by accelerated socioeconomic changes including agro-industrial expansion, migration, and infrastructure development, generating new ecological and public health threats [39, 40].
As of the late 2000s, natural vegetation covers only 57% of Mesoamerican territory, while 42% is dedicated to agriculture and livestock, and 1–2% to urban areas [34; 38], Fig. 2. These landscape transformations reduce biodiversity and alter disease vector and host dynamics. Deforestation and ecosystem disturbances facilitate interactions between humans, domestic animals, and wildlife, increasing infectious disease transmission risk [41–43]. The scale and pace of current change distinguish it from historical patterns: Mesoamerica exhibits some of the highest deforestation rates worldwide, with Guatemala and Honduras experiencing particularly rapid forest loss. Mexico likewise faces alarmingly high deforestation relative to its land area, has experienced sustained forest loss over recent decades, driven by agricultural expansion, wildfires, and illegal logging in critical biomes [44, 45].
Fig. 2.
Degree of urbanization in Mesoamerica. Spatial distribution of urbanization levels across Mesoamerica based on population density and settlement size (GHS-SMOD R2023A), illustrating regional gradients of anthropogenic pressure from urban centers to low-density rural landscapes
Vector-borne diseases and land-use transformation
The conversion of forests to agricultural and urban landscapes directly facilitates vector proliferation and disease transmission. For arboviruses such as dengue, zika, and chikungunya, forest conversion to monocultures or urban areas promotes vectors like Aedes aegypti and Aedes albopictus [43]. In Costa Rica, these vectors have increased in pineapple-dominated landscapes, where colonizing mosquitoes in fragmented areas feed on accessible hosts including humans and domestic animals, elevating transmission risk [46, 47].
Export-oriented crops such as oil palm and banana have significantly contributed to habitat loss in the Pacific and Caribbean lowlands [48–51], creating favorable conditions for wild vectors including Haemagogus and Sabethes, which transmit yellow fever [52, 53]. The presence of Sa. chloropterus in deforested Costa Rican areas raises concern about yellow fever reemergence in Mesoamerica, where the disease has not been reported since the 1960s [54, 55]. This concern is reinforced by antibody findings in Mexican non-human primates [56]. The proximity of altered habitats to human settlements could facilitate urban transmission cycle reestablishment, directly linking forest cover loss to modified zoonotic pathogen transmission cycles [57, 58].
The transformation of forests into agricultural and livestock areas, combined with intensive pesticide use, has been linked to increased malaria cases across the isthmus. In Panama, Nyssorhynchus spp. (previously Anopheles) as the main malaria vector there, occurs in greater abundance in deforested areas [59]. Since the 1970s, Guatemala, El Salvador, Belize, and Nicaragua have reported insecticide-resistant vector populations, further complicating control efforts [60, 61]. Landscape transformations are also evident in Mexico’s Yucatan Peninsula. Development policies implemented since the 1970s have driven major changes in land use, reducing forest cover and biodiversity [62]. Between 2001 and 2018, forest cover dynamics in southern Quintana Roo were characterized by higher rates of degradation than deforestation. In the Bacalar–Río Hondo region, commercial agriculture and cattle ranching drove a net annual forest loss of 1.6%, whereas in central Quintana Roo with particular areas inhabited and managed by Maya communities, shifting cultivation and community forest management were associated with forest recovery and dynamic cycles of loss and regrowth. Overall, degradation processes exceeded outright deforestation, highlighting complex landscape transformations rather than uniform forest decline [63].
Costa Rica stands as a notable exception due to strict forest protection laws and payment-for-ecosystem-services programs [64, 65], yet even there, land-use changes have had health repercussions, underscoring that conservation advances alone cannot fully mitigate the public health consequences of historical landscape transformation.
Livestock production and rabies Dynamics
Intensive livestock production has significantly impacted interactions between wildlife, domestic animals, and humans, facilitating zoonotic disease spread such as rabies [66]. While historical records suggest bat-associated rabies predated colonization, rabies went largely unnoticed due to low host density and absent documentation. Colonization, deforestation, and livestock introduction enabled bat population growth and rabies virus persistence, as domestic animals provided abundant food for vampire bats (Desmodus rotundus), increasing bite frequency in humans and livestock [67, 68]. These epidemiological changes represent the transition from urban dog-mediated cycles to sylvatic cycles shaped by anthropogenic environmental change [66, 67]. Within this context, vampire bat-cattle interactions have become a key mechanism facilitating rabies spillover into livestock populations [69].
Road infrastructure construction has also profoundly impacted landscape connectivity and disease ecology. The Inter-American Highway opening in 1956 facilitated rabies virus reintroduction into Costa Rica [70]. Several outbreaks between 1956 and the late 1960s prompted coordinated public health responses including mass canine vaccination, stray dog removal, and cross-border control agreements [71]. This case illustrates how historical and contemporary anthropogenic processes, from colonization to infrastructure development, have shaped regional infectious disease ecology.
Conservation responses: biological corridors and their limitations
Biological corridors in Mesoamerica were originally promoted as conservation and sustainable development strategies, rather than as explicit public health interventions. Regional initiatives such as the Central American System of Protected Areas (SICAP) and the Mesoamerican Biological Corridor (CBM) were designed to enhance landscape connectivity, facilitate species movement, and maintain ecological processes across fragmented habitats. By supporting species dispersal, access to resources, and gene flow, these corridors contribute to the maintenance of resilient wildlife populations and overall ecosystem integrity. More recently, the links between habitat fragmentation, biodiversity loss, and infectious disease risk have gained increasing attention; in this context, biological corridors may also provide indirect health-related benefits by regulating ecological interactions among hosts, vectors, and pathogens. Although the evidence is still emerging, improved ecosystem functioning and higher biodiversity may reduce host susceptibility and influence transmission dynamics [72, 73].
However, the effectiveness of these corridors has been limited by weak management structures and lack of coordination among sectors [34, 74–76]. The contrast between the conservation promise of biological corridors and their implementation challenges reflects broader tensions in Mesoamerican environmental governance: while the ecological rationale for connectivity is well-established, translating this into effective disease prevention requires sustained cross-sectoral collaboration and resources that often remain elusive. This gap between conservation planning and public health outcomes underscores the need for integrated approaches that explicitly address both ecological integrity and disease risk—a core principle of the One Health framework discussed later in this paper.
Climate change and disease dynamics
Beyond landscape transformation, climate change amplifies disease risk across Mesoamerica by altering the environmental conditions that govern vector survival, pathogen development, and disease transmission. Climate change has become a major driver of public health outcomes, particularly in vulnerable regions such as the so-called Mesoamerican Dry Corridor, which extends from southern Mexico and Guatemala through Honduras, El Salvador, and potentially into Panama. Prolonged droughts, extreme rainfall events, rising temperatures, and dehydration are among the climate change effects that directly impact the health of local populations [77, 78]. These climatic shifts not only compound challenges in the Dry Corridor, but also jeopardize food security and water availability [77], further deteriorating living conditions in affected communities.
The Mesoamerican Dry Corridor experienced five consecutive years of drought between 2015 and 2019, punctuated by torrential rains. This severely impacted agriculture, increased food insecurity and malnutrition, accelerated urban migration and human displacement, and heightened susceptibility to vector-borne tropical diseases [78]. Vector-borne diseases emerge as a major concern in Mesoamerica, as extreme weather events such as rising temperatures and extreme precipitation promote the reproduction and spatial expansion of mosquito vectors such as Aedes aegypti. This relationship has been documented globally [79] and is increasingly evident across Mesoamerica [80]. These conditions have also likely facilitated the expansion of Oropouche virus (OROV) beyond the Amazon, highlighting the broader impact of climate variability on arboviral disease dynamics [81].
Climate-mediated neglected tropical diseases
The multifactorial relationship between climate change, deforestation, and overcrowding has altered the distribution and seasonality of several neglected tropical diseases throughout Latin America, including Mesoamerica. Malaria transmission has been associated with environmental change and deforestation [41, 82], while climate change related processes have also influenced the distribution of leishmaniasis and Chagas disease [83–85]. These vector-borne illnesses are transmitted by Nyssorhynchus mosquitoes (formerly treated as the Anopheles Nyssorhynchus subgenus), sand flies, and triatomine bugs, respectively. Ecological changes with deforestation in regions such as the Amazon, have created new breeding sites, facilitating the expansion also of malaria risk [82]. Within Mesoamerica, although malaria has declined in some areas, the disease remains a public health concern in countries such as Guatemala and Honduras, where ecological conditions and lack of healthcare access contribute to its persistence [78].
Climate and environmental drivers of rickettsial disease
Environmental change also influences the emergence of rickettsial diseases. Rickettsial diseases are bacterial infections transmitted by arthropod vectors such as ticks and mites. These diseases are strongly shaped by environmental conditions that influence vector abundance, distribution, and host contact. Key drivers include climate variability, vegetation cover, vertebrate diversity, and human activities such as deforestation and agricultural expansion [86, 87]. Environmental alteration increases the likelihood of contact between vectors, wildlife, domestic animals, and humans in both rural and peri-urban settings, thereby elevating the risk of zoonotic disease transmission [88], [89; 90]).
Recent evidence from Mesoamerica demonstrates the region’s vulnerability to emerging rickettsial threats. In Belize, researchers detected Rickettsia sp. of the Atlantic rainforest strain in Amblyomma ovale ticks, with 33.3% of sampled ticks testing positive and with this the first documentation of this pathogen in Central America [91]. Previously known only from Brazil, Colombia, and Argentina [92], this spotted fever-associated strain now represents a potential emerging health risk in Mesoamerica [91]. The same study identified Rickettsia amblyommii for the first time in Amblyomma pacae, as well as endosymbiotic rickettsiae in Ixodes affinis, underscoring the widespread circulation of rickettsial agents in Latin American tick fauna [91].
Evidence from El Salvador further supports this pattern of disease emergence. Five tick species were found infesting domestic dogs, with Rhipicephalus sanguineus sensu lato being the most prevalent. Molecular screening identified three spotted fever group rickettsiae in El Salvador: Rickettsia amblyommatis in Amblyomma mixtum [89], Rickettsia parkeri in Amblyomma ovale [90], and an unidentified Rickettsia agent in Amblyomma cf. parvum [90]. These findings suggest that R. parkeri, a recognized human pathogen in other regions, may also be circulating in El Salvador, highlighting the role of domestic animals and environmental change in shaping zoonotic risk in Mesoamerica.
Social determinants and health system challenges
Healthcare system limitations
Mesoamerica’s social security systems face numerous challenges that hinder access to healthcare and limit population coverage. Despite governmental efforts, a significant portion of the population remains unprotected against disease. Marked disparities persist in access to medical care, particularly in rural and marginalized communities, where health services are scarce [20, 33]. The rise in dengue cases throughout the region is also driven by poor sanitation conditions, poor urban planning, and overcrowding. These factors are compounded by climate change that create favorable environments for disease proliferation [93–95].
Healthcare quality varies significantly across Mesoamerican countries due to resource shortages, limited medical personnel, and inadequate infrastructure. These deficiencies negatively impact diagnostics and treatment outcomes. Additionally, social security systems face persistent financing difficulties, which restrict the expansion of coverage and the ability to improve service quality [8, 96]. The trajectory of dengue in Costa Rica illustrates this dynamic. Between 1993 and 2016, dengue incidence rose from 14 to 48 cases per 10,000 inhabitants, partly reflecting improvements in diagnostic capacity and disease surveillance. Despite this threefold increase in detected cases, the overall case fatality rate remained extremely low at 0.62 deaths per 10,000 confirmed cases, demonstrating that enhanced surveillance and clinical management prevented rising incidence from translating into higher mortality [97]. This pattern, initially observed for dengue, is also relevant for other zoonotic diseases with complex transmission cycles involving domestic and wild animals. Rabies and leptospirosis illustrate how veterinary and public health interventions directly influence disease dynamics [98, 99], while brucellosis, cysticercosis, and toxoplasmosis continue to require coordinated surveillance across human and animal health sectors [100–102]. For SARS-CoV-2, although the virus can infect carnivores, deer, and other animals, and there are anecdotal reports of animal-to-human transmission, its main transmission cycle remains human-to-human [103, 104].
Prevention and health promotion have historically received limited investment, despite growing recognition that preventive, multisectoral approaches are essential for strengthening health systems in Latin America and the Caribbean [7]. Non-communicable diseases (NCDs) such as cardiovascular disease, diabetes, and cancer pose significant challenges due to difficulties in diagnosis and long-term management. Despite progress in reducing maternal and infant mortality, gaps persist in access to quality prenatal and obstetric care, underscoring the need to strengthen public health strategies [8, 20, 96].
Social human poverty and endemic diseases
The relationship between poverty and disease transmission is exemplified by Chagas disease in Mesoamerica. Central America is estimated to host approximately 385,000 individuals infected with Trypanosoma cruzi, with persistent vector-borne transmission foci, particularly in socially and politically vulnerable settings. Although vector-borne transmission remains the predominant route in Mesoamerica, foodborne transmission through contaminated food and beverages has also been documented, highlighting the diversity of transmission pathways and reinforcing the need for integrated prevention strategies. Migration, poverty, and limited access to healthcare exacerbate vulnerability to zoonotic diseases, linking human movement and social inequities to the ongoing risk of Chagas transmission [33, 105–107]. Mexico ranks third globally in terms of Chagas disease burden, with an estimated 876,000 people infected. This high prevalence reflects the country’s ecological diversity and the presence of multiple reservoirs and vectors [108]. The majority of the approximately 300,000 people infected with T. cruzi in the United States are migrants from Mexico, Central America, and South America, although autochthonous cases have also been documented in the southern U.S. which seems to be a sign that local transmission may have been historically underestimated [106, 109].
Poverty, substandard housing and limited access to medical care are well-recognized drivers of Chagas disease transmission, particularly among socioeconomically vulnerable populations [85, 110]. Oral transmission of Chagas disease illustrates why One Health prevention in Mesoamerica should not be limited to vector control, but should also consider food safety, wildlife–human interactions, reservoir ecology, cultural food practices, and community-level prevention. Although confirmed outbreaks of orally acquired Chagas disease have been reported mainly in South America, WHO and PAHO recognize foodborne transmission through food or beverages contaminated with Trypanosoma cruzi as an important route capable of causing outbreaks and deaths, and PAHO recommends best practices in food handling and preparation as part of prevention strategies [111–114]. For Mesoamerica, direct contemporary evidence remains limited; however, a putative 14th-century outbreak in Coyoacán, central Mexico, has been proposed as a possible foodborne Chagas outbreak associated with food shortage, disrupted fish supply, and the hunting and consumption of alternative reservoir animals, particularly infected opossums (Didelphis spp.) [115]. This pattern of vulnerability and the way migration shapes disease spread are reflected in a 2017 study that screened 389 migrants for Chagas disease, finding a 3.1% positivity rate for T. cruzi. Most migrants came from highly endemic countries such as Guatemala, Honduras, and El Salvador. Although seropositive individuals were more knowledgeable about the disease, significant gaps remained. For instance, only 56% could identify triatomines as the vectors, underscoring the urgent need for improved education and prevention strategies in vulnerable populations to reduce disease transmission [116].
These poverty-driven conditions including inadequate housing, limited access to safe drinking water, poor sanitation infrastructure, and weak public health services extend beyond vector-borne diseases to facilitate outbreaks of waterborne infections, including amebiasis and giardiasis [117, 118]. Giardiasis, an intestinal parasitic infection, particularly affects low-income communities and is transmitted through the ingestion of water contaminated with feces containing the parasite [117–119]. This convergence of structural determinants creates conditions where multiple transmission pathways overlap in the same vulnerable populations, amplifying disease burden [120, 121]. Such transmission pathways are for example vector-borne through triatomine bugs, and waterborne through contaminated water sources.
Migration and disease transmission
Migration dynamics play a critical role in disease transmission patterns across Mesoamerica. Human trafficking routes through forested regions like La Mosquitia, along the Honduras–Nicaragua border, increase the risk of malaria reemergence, including severe Plasmodium falciparum infections [122, 123]. Migration corridors often overlap with deforestation fronts driven by illegal activities such as drug trafficking and mining, creating converging ecological and epidemiological pressures that amplify disease risk [121].
The Central American isthmus and Mexico form a major migratory corridor connecting thousands of people from Latin America and the Caribbean, Africa, and Asia with the United States and Canada. Irregular transit along this corridor generates humanitarian and public health crises, particularly at the U.S. southern border. In 2020, more than 450,000 people from the Northern Triangle (Honduras, Guatemala, and El Salvador) applied for asylum in other countries, primarily in the United States [124]. Drivers of migration include poverty, violence, insecurity, family reunification, political instability, and natural disasters [125, 126]. Migrant populations are highly vulnerable to infectious diseases due to malnutrition, lack of immunity, disrupted medical treatments, and broader social determinants that influence exposure and access to healthcare [33]. Unsanitary and overcrowded conditions during transit or at destination points promote disease outbreaks. Many migrants originate from regions with high burdens of infectious diseases and may carry pathogens not endemic in the countries they reach [127].
Climate change, occupational health, and chronic disease
The convergence of climate change, poverty, and occupational vulnerability has given rise to novel health threats in Mesoamerica. Mesoamerican nephropathy as a form of chronic kidney disease exemplifies this intersection of social and environmental determinants. This poorly understood condition primarily affects agricultural workers along nearly 1,000 kilometers of the Pacific coast of Central America, from southern Mexico through El Salvador, Nicaragua, Honduras, and Costa Rica [78]. The condition disproportionately impacts young male workers in physically demanding occupations, e.g. particularly sugarcane harvesters who labor for extended hours under extreme heat with limited access to water and rest. Although the precise etiology of Mesoamerican nephropathy remains unresolved, growing evidence links the condition to recurrent heat exposure, dehydration, and strenuous labor. These factors are increasingly exacerbated by climate change [78]. Chronic kidney disease has been reported as a leading cause of death in El Salvador and Nicaragua, particularly among working-age males [128].
Exposure to agrochemicals and other environmental contaminants is also being investigated as a contributing factor, as several studies suggest that chronic contact with such substances may cause long-term kidney damage, particularly in genetically susceptible individuals [129–132]. The condition illustrates quintessential aspects of climate-sensitive disease: prevalence grows with environmental exposures directly influenced by climate change, the condition disproportionately affects socially and economically vulnerable populations, and is exacerbated by poor healthcare, limited public health infrastructure, and incomplete surveillance.
This occupational health crisis demonstrates how the structural determinants discussed throughout this section including poverty, inadequate access to healthcare, hazardous working conditions, and marginalization interact with environmental change to create new disease burdens. Like the infectious diseases described above, Mesoamerican nephropathy reflects the profound ways in which social inequalities shape health outcomes in the region, underscoring the need for comprehensive interventions that address both immediate occupational hazards and the underlying social and environmental determinants of health. This perspective aligns with the One Health framework, which increasingly recognizes that environmental change, occupational exposures, and social determinants jointly influence health outcomes and should therefore be addressed through integrated, multisectoral interventions [33].
Broader social determinants and disease spread
The outlined structural factors that drive Chagas disease, waterborne infections, and Mesoamerican nephropathy are increasingly recognized as fundamental social determinants within the One Health framework [33]. These conditions conducive to the spread of tuberculosis, leprosy, HIV/AIDS, and other diseases strongly influenced by social determinants. Although not all are directly linked to environmental changes like vector-borne diseases, these conditions are amplified by poverty. Poor living conditions, including overcrowding and malnutrition, weaken immune function and increase susceptibility to infectious diseases [133, 134]. Environmental degradation and resource scarcity further exacerbate these conditions, facilitating disease transmission and reinforcing health inequities [135–137].
Tuberculosis exemplifies these dynamics. Lack of access to healthcare, malnutrition, and coinfection with HIV significantly worsen outcomes, making TB a persistent public health concern in the region [138, 139]. HIV/AIDS similarly reflects the intersection of biological, behavioral, and structural determinants. In Costa Rica, a 2014 assessment indicated a prevalence of 0.027% (2.7 per 10,000 inhabitants) with transmission associated with limited awareness, early sexual debut, and social inequalities [140]. Limited sexual education, migration, and restricted access to health services facilitate HIV spread across the region. While control programs emphasize prevention, early diagnosis, and antiretroviral therapy availability, addressing the underlying structural and social determinants remains essential for epidemic control [141].
The challenges documented in this section subsummarized as inadequate health system coverage to climate-driven occupational diseases to poverty-amplified infectious disease transmission underscore a fundamental reality: health outcomes in Mesoamerica are profoundly shaped by social inequalities rooted in colonial-era structures and perpetuated by contemporary economic and political systems. Effective interventions must therefore address not only immediate disease risks but also the structural determinants that make certain populations systematically more vulnerable than others.
Transboundary animal health threats and One health gaps
Although human migration across Mesoamerica has been widely studied for its social and health implications, the movement of animals, particularly the informal or illegal transport of domestic and wild species, remains comparatively underexplored. As discussed in the preceding sections, animal movements linked to informal livestock practices, environmental change, and limited veterinary oversight can facilitate the cross-border spread of zoonotic diseases, representing an important but insufficiently documented pathway of disease emergence in the region [142, 143]. The region’s high biodiversity, structural weaknesses in sanitary control systems, and sociopolitical instability that facilitates unregulated mobility make Mesoamerica highly vulnerable to the introduction and reemergence of infectious agents that impact public health, animal health, and regional economies [7].
Despite growing regional discourse around the One Health approach, meaningful integration of human, animal, and environmental health remains fragmented across Mesoamerica [76, 144] due to multiple challenges [9]. Several emerging and re-emerging animal health threats—such as avian influenza, foot-and-mouth disease, bovine tuberculosis, brucellosis, canine distemper, and the reappearance of the New World screwworm—pose serious risks to animal health, food production systems, and international trade. Some of these conditions are zoonotic, yet comprehensive and coordinated planning remains limited, weakening early detection and response mechanisms [145]. Two recent cases—the resurgence of New World screwworm and the spread of canine distemper virus—illustrate both the consequences of these institutional gaps and the urgent need for coordinated regional surveillance.
New World screwworm Resurgence
The New World screwworm (Cochliomyia hominivorax) exemplifies the consequences of fragmented One Health integration. This parasitic fly represents a significant transboundary One Health threat to both animal and human health, causing severe myiasis and considerable economic losses [146]. Although it was previously eradicated from Mexico and Central America through a successful eradication campaign initiated in 1957, the parasite has made a dramatic comeback. Since 2021, more than 7,000 outbreaks and at least 24,000 confirmed cases in domestic animals have been reported. The resurgence began in Panama and had since spread across Costa Rica, Nicaragua, Honduras, Guatemala, and even reached Mexico once again [147–150].
Analysis of the dispersal pattern reveals an advance of approximately 1,500 km from the endemic region in Darién, Panamá to southern Mexico which is a far greater area as what would have been expected from natural dispersal alone. These dispersal pattern strongly suggests that the primary driver of regional spread is the unregulated movement of domestic animals, also reflecting persistent weaknesses in animal traceability and cross-border sanitary controls. A threshold of 50 km has been proposed to distinguish atypical dispersal events likely linked to informal transport lacking sanitary controls [147]. The detection of outbreaks in southeastern Mexican states such as Chiapas, Tabasco, and Campeche confirms reintroduction of the parasite into previously screwworm-free zones, placing livestock production areas in Mexico and beyond at risk [149].
The current outbreak has also documented screwworm infections in wild animals in Central America (e.g., Costa Rica; SENASA, 2025) [148]. This interspecies transmission raises growing concerns about the risk of infectious diseases spilling from domestic to wild fauna, threatening already vulnerable wildlife populations. The pattern of long-distance parasite dispersal driven by unregulated animal movement demonstrates the urgent need to strengthen regional surveillance, animal traceability, cross-border coordination, and sanitary movement controls to contain this and other diseases spreading across countries and regions.
Canine distemper virus and wildlife conservation
Canine distemper virus (CDV; Morbillivirus canis) further illustrates how inadequate management of domestic animals can facilitate pathogen transmission across multiple species, with implications for animal health, biodiversity, and ecosystem integrity. This globally distributed morbillivirus primarily affects domestic dogs but is also capable of infecting a wide range of wild terrestrial and aquatic mammals, demonstrating its capacity for cross-species transmission. In Mesoamerica, CDV has been detected in wild carnivores, including wild felids, raising concerns about its impact on wildlife conservation [151, 152].
Beyond carnivores, recent evidence from South America indicates that CDV can also infect neotropical primates. Natural infections and lethal outbreaks have been documented in free-ranging marmosets (Callithrix spp.) in Brazil, including cases of coinfection with yellow fever virus and outbreaks associated with neurological disease and high mortality [153, 154]. These findings highlight the expanding host range of CDV and underscore its relevance from a One Health perspective particularly in regions where domestic animals, wildlife, and humans coexist in close proximity. The findings also emphasize the importance of integrated wildlife and domestic animal surveillance for early pathogen detection and prevention of cross-species transmission. Transmission is facilitated by irresponsible pet ownership, illegal wildlife trade, and lack of regulation in animal transport.
The region’s ecological connectivity amplifies these risks. As discussed earlier in the context of conservation responses to habitat fragmentation, Mesoamerica features ecological corridors such as the Jaguar Corridor and the Mesoamerican Biological Corridor, which connect populations of large carnivores and other sensitive species across countries [74, 155]. While these corridors are essential for maintaining ecological connectivity and genetic exchange, they may also facilitate pathogen spread when infected wildlife move naturally across connected habitats. This risk is then further amplified by anthropogenic factors such as human migration and informal domestic animal transport [156]. The spread of the “South America/North America-4” lineage of CDV, detected from Ecuador to the United States [157], illustrates an active continental transmission route that connects Mesoamerica to broader disease dynamics.
Implications for regional One health integration
Together, these examples illustrate how contemporary health threats in Mesoamerica increasingly transcend disciplinary and national boundaries, reinforcing the need for integrated One Health approaches capable of addressing the interconnected human, animal, and environmental drivers of disease emergence. Both screwworm and CDV demonstrate how the absence of coordinated surveillance, weak enforcement of animal movement regulations, and limited integration between veterinary and public health sectors create vulnerabilities that transcend national borders. The resurgence of a previously eradicated parasite and the continental spread of a viral pathogen underscore the urgent need to strengthen health surveillance and regional cooperation. Without sustained cross-border collaboration, improved animal traceability systems, and institutional frameworks that explicitly integrate human, animal, and environmental health dimensions through effective stakeholder engagement and multisectoral governance [158], Mesoamerica will remain vulnerable to recurring cycles of disease emergence and reemergence that threaten both public health and wildlife conservation.
International and regional responses
The disease challenges documented throughout this paper from colonial-era pathogen introductions to contemporary climate-driven health crises have prompted responses from international organizations, national governments, and community actors. However, the persistence and reemergence of zoonotic diseases across Mesoamerica reveal critical gaps between institutional mandates and implementation capacity, consistent with recent regional assessments highlighting persistent challenges in governance, institutionalization, financing, and cross-sectoral implementation of One Health across Latin America and the Caribbean [7]. This section examines current response frameworks and argues that effective One Health strategies require not only international technical support but also deep community engagement and political commitment that transcends economic constraints.
Institutional actors and current limitations
International organizations and global One Health initiatives can play important roles in addressing Mesoamerica’s interconnected health challenges. Recent global One Health initiatives including Preventing Zoonotic Disease Emergence (PREZODE), the UNEP Nature for Health (N4H) initiative, and the Alliance against Health Risks in Wildlife Trade illustrate the growing international commitment to strengthening One Health implementation through multisectoral collaboration, prevention, and coordinated action across the human–animal–environment interface. The Food and Agriculture Organization of the United Nations (FAO) focuses on improving animal health, promoting responsible agricultural practices, and strengthening surveillance systems in collaboration with regional partners [159, 160]. The US Centers for Disease Control and Prevention (CDC) emphasizes surveillance, prevention, and control strategies for zoonotic diseases, recognizing the complex interactions among humans, animals, and the environment as key to preventing outbreaks [161, 162]. International research initiatives examine how climate change influences vector distribution, disease emergence, and population vulnerability across the region.
Yet these efforts, while valuable, continue to face structural constraints, including weaknesses in governance, institutionalization, financing, and cross-sectoral coordination, which remain persistent barriers to One Health implementation across Latin America and the Caribbean [7]. International organizations typically work through national governments, whose capacity and political will vary substantially. Technical recommendations may not translate into policy action when domestic priorities diverge or when implementation requires resources that exceed available budgets. Surveillance systems remain fragmented across sectors and national borders, impeding the coordinated regional response that transboundary threats demand [76]. The screwworm resurgence and canine distemper spread documented earlier exemplify how institutional gaps—weak animal movement regulations, limited cross-border coordination, insufficient integration between veterinary and public health sectors—enable disease emergence despite international technical guidance.
Community engagement as essential foundation
Vulnerable populations in rural and low-resource areas face the highest exposure to risks driven by environmental degradation and vector proliferation. As outlined above, in many of these settings, poverty, inadequate housing, and limited access to healthcare increase susceptibility to infectious diseases, including Chagas disease and waterborne infections [110, 117–119]. Limited community participation and health education continue to constrain the effectiveness of disease prevention strategies [85, 116, 120]. Effective disease prevention therefore requires moving beyond top-down technical assistance toward collaborative approaches that position communities as active participants rather than passive beneficiaries, consistent with recent One Health implementation frameworks emphasizing stakeholder engagement and participatory governance [158]. Community engagement and educational programmes prove essential for promoting preventive practices, delivering culturally appropriate health education, strengthening local surveillance systems, and improving living conditions. Only through comprehensive approaches that combine international technical support, national policy frameworks, local government action, and community participation can disease transmission risks be effectively mitigated ([163, 164], Fig. 3).
Fig. 3.
Biotic pressure, zoonotic risk, and the mitigating effect of the One health approach. Increasing biotic pressure—driven by environmental degradation and vector proliferation—leads to a nonlinear rise in zoonotic spillover probability (magenta line). Integrated One health interventions reduce the slope of this trajectory (orange line), highlighting the role of coordinated action, community participation, and multilevel governance in mitigating transmission risk
A qualitative study from Guatemala demonstrates this principle in practice. Researchers at the Laboratory of Entomology and Applied Parasitology at the University of San Carlos documented how integrating social innovation into household improvement strategies for Chagas disease control generated positive changes in community health [165]. Through interviews and direct observation, the study showed that improvements such as wall and floor repairs promoted new social dynamics supporting household economies and hygiene practices. Active community participation and dialogue between traditional and public health approaches proved key to intervention success.
From a One Health perspective, this case highlights the value of community-based, interdisciplinary, and intersectoral approaches that integrate human health, animal health, and environmental dimensions to promote sustainability and local empowerment. Such approaches recognize communities as key actors in disease prevention, surveillance, and risk mitigation at the human-animal-environment interface. The findings suggest this model could be adapted to strengthen community health across Latin America while also providing valuable lessons for other regions, including the Global North, particularly where zoonotic and environmentally mediated diseases pose similar challenges. However, the study also underscores that addressing complex disease transmission dynamics requires more than local action alone. Effective One Health implementation depends on strong governmental commitment, clear institutional mandates, and coordinated regional leadership to support, scale, and integrate community-driven initiatives into broader public health and environmental governance frameworks. Without these enabling structures, community-based interventions risk remaining fragmented and unsustainable [166, 167].
Political will and health system performance beyond economic capacity
Mesoamerican countries exhibit marked heterogeneity in economic development and socioeconomic conditions, which profoundly shape health system capacity and population health outcomes [168, 169]. However, economic constraints alone do not fully explain differences in public health investment or performance across the region. Evidence from Latin America demonstrates that even resource-limited countries can achieve substantial health gains when strong political commitment, public investment, and equitable health policies are prioritized.
Recent studies on SARS-CoV-2 testing capacity and transfusion-transmitted infection surveillance demonstrate that Cuba has maintained robust public health infrastructure and diagnostic capacity despite limited economic resources, underscoring the role of governance, social equity, and health system organization beyond national wealth [166, 167]. This example illustrates that the persistent health challenges documented throughout this paper reflect not only resource scarcity but also political choices about health system priorities, intersectoral coordination, and the degree to which marginalized populations are included in health planning and service delivery.
The gap between technical capacity and implementation emerged consistently from both the narrative literature review and the discussion held during a structured multisectoral workshop with results outlined below. Together, these sources indicate that Mesoamerica possesses substantial scientific expertise, established international partnerships, and growing awareness of One Health principles [7, 144]. What often remains insufficient is the sustained political will to translate this knowledge into policy action, the institutional frameworks to coordinate across sectors and borders, and the commitment to center the most vulnerable communities in intervention design and implementation. Addressing the region’s interconnected health threats therefore requires not only continued technical cooperation but also fundamental shifts in governance structures, resource allocation, and the recognition of health as a shared responsibility spanning human, animal, and environmental domains.
Workshop-derived One health strategy for Mesoamerica
Developing a One Health strategy for the Mesoamerican region requires a comprehensive approach that recognizes the region’s cultural, social, economic, ecological, and environmental complexity. Rather than relying on isolated interventions, effective One Health implementation demands a shared vision of health as a common good, intrinsically linked to people, animals, plants, and ecosystems.
To complement the narrative review presented in this perspective, we incorporate the outcomes of a structured participatory multisectoral workshop organized by the GLACIER Project Consortium (German Latin-American Center for Infection and Epidemiology Research) during the WDA Latin America meeting held in Guatemala in late 2023. The one-day workshop brought together 67 participants from 13 countries, including Guatemala, Mexico, Costa Rica, Chile, Colombia, Brazil, Ecuador, Honduras, El Salvador, the Dominican Republic, Argentina, Germany, and the United States. Participants represented universities, governmental institutions, non-governmental organizations, international research centers, undergraduate and graduate students, community representatives, and also Indigenous communities and community-based organizations. The participants’ expertise encompassed ecology, veterinary medicine, public health, environmental sciences, biology, education, social sciences, communication, and public policy.
The workshop followed a structured participatory design. The program combined thematic presentations delivered by invited experts with facilitated multidisciplinary working groups addressing ecological, biological, social, educational, and governance dimensions of One Health in Mesoamerica. Following each thematic block, participants worked in small interdisciplinary groups using predefined guiding questions to identify major regional challenges, key stakeholders, disciplinary needs, and potential implementation strategies. The outputs from each working group were subsequently presented during plenary discussions, where common themes were collectively discussed and integrated. The organizing team then grouped the recurring themes identified across the working groups and synthesized them through thematic analysis into six strategic action lines that form the basis of the recommendations presented in this manuscript.
Although the workshop was not designed as a formal consensus exercise, it provided a structured platform to capture perspectives from diverse sectors and countries. To reduce potential bias associated with participant composition, workshop outcomes were interpreted together with the evidence synthesized in the narrative literature review, allowing recommendations to emerge from both empirical discussion and published evidence.
Workshop discussions consistently highlighted that the principal barriers to One Health implementation in Mesoamerica extend beyond technical capacity. Participants emphasized the need to strengthen intersectoral coordination, improve communication among academia, governments, communities, and international organizations, expand access to funding for applied research and implementation, and institutionalize One Health through coordinated regulatory and operational frameworks. These priorities are consistent with recent regional assessments identifying governance, surveillance, intersectoral collaboration, and veterinary public health as major priorities for One Health implementation across Latin America and the Caribbean [76].
Across discussions, participants also recognized that these priorities were interconnected and operated across multiple governance levels, from local communities to regional and international institutions. The recurring themes were subsequently synthesized into the six strategic action lines presented in Table 1, which provide the conceptual basis for the proposed One Health framework for Mesoamerica.
Table 1.
Summary of strategic action lines for implementing the One health approach in Mesoamerica
| Action Line | Key Priorities |
|---|---|
| 1. Intersectoral Governance and Regional Cooperation | Establish permanent collaboration spaces integrating governments, academia, civil society, and international organizations into regulatory frameworks and public budgets through multisectoral working groups and ecosystem health observatories |
| 2. Surveillance, Prevention, and Disease Control | Implement regional integrated surveillance for zoonoses, vector-borne, and environmental diseases; strengthen rapid outbreak response; integrate wildlife health monitoring; establish animal registries and traceability systems |
| 3. Community Participation and Intercultural Inclusion | Integrate ancestral knowledge into health systems; train personnel in intercultural competencies; ensure Indigenous language use in services; engage health promoters as implementation allies |
| 4. Education, Communication, and Behavior Change | Design environmental health campaigns from schools through universities; promote culturally grounded behavior change interventions; strengthen community leadership in health promotion |
| 5. Applied Research and Local Knowledge | Promote context-specific research with community participation; apply innovative technologies (eDNA, remote sensing, spatial modeling); build regional scientific capacity |
| 6. Territorial Management and Sustainability | Integrate ecosystem health with sustainable production; encourage chemical-free agricultural practices; restore habitats and strengthen governance in biological corridors; create economic incentives for good practices |
Conclusions and strategic recommendations
This study highlights that addressing health challenges in Mesoamerica requires an integrated One Health approach that explicitly incorporates historical, ecological, and social dimensions. Building on the narrative review, recent regional evidence, and multisectoral dialogue, we propose key strategic actions to strengthen prevention, coordination, and health equity across the region.
Strategic framework and key stakeholders
Effective implementation of a One Health strategy requires the active participation of diverse sets of stakeholders: organized communities, Indigenous Peoples, researchers from multiple disciplines, decision-makers at all levels (from community leaders to public policy authorities), government officials, educators, grassroots organizations, and international bodies. Interdisciplinary collaboration is essential, integrating perspectives from human and veterinary medicine, biology, law, social sciences, communication, education, psychology, economics, territorial governance, and environmental management. Each discipline brings unique tools for understanding, addressing, and transforming health and ecosystem systems in a synergistic manner.
Based on structured multisectoral workshop discussions, recurrent themes were identified and synthesized through thematic analysis, and subsequently integrated with the findings from the narrative review. This process resulted in six strategic action lines for implementing the One Health approach in Mesoamerica, addressing governance, surveillance, community participation, education, research, and territorial management—each representing a critical dimension of integrated health strategy. These are summarized in Table 1, with key implementation components detailed below.
Core components of the strategy
Surveillance and disease prevention
A fundamental component is the development of integrated epidemiological surveillance systems capable of monitoring zoonoses, vector-borne diseases, and other health problems linked to environmental factors. These systems should be participatory, incorporate traditional and local knowledge, and function in a decentralized manner to ensure early outbreak detection and rapid response.
Recognizing the role of domestic and wild animals in disease emergence, the workshop proposed establishing national registries for companion animals and enhanced monitoring of wildlife health. Such registries would facilitate identification of zoonotic hotspots, support outbreak tracking, promote responsible pet ownership, and help manage exotic or invasive species, including illegally traded wildlife. This is particularly relevant in Mesoamerica, where porous borders and limited enforcement enable wildlife trafficking including exotic birds up to large mammals maintained in private collections. Integrating human, animal, and environmental health data through these systems supports proactive interventions and broader One Health goals [170].
Healthcare access and cultural competence
Improving access to medical and veterinary care in rural and peripheral communities is equally essential. Ensuring that both people and animals receive adequate preventive and curative care not only builds community resilience to outbreaks but also serves as a mechanism for social inclusion. Health education across all levels including schools, communities, institutions, and media should foster broad understanding of the interconnection between human, animal, and ecological systems.
One of the workshop’s most valuable contributions was the emphasis on respecting and revitalizing ancestral knowledge, including the incorporation of Indigenous languages into health services. This approach enhances communication and care quality while promoting epistemic justice and intercultural equity. It is particularly important when working with Indigenous communities, where traditional knowledge systems including those maintained and transmitted by women play a central role in environmental stewardship, food security, and community health [171]. Successfully implementing culturally appropriate and intercultural One Health approaches requires action across three structural dimensions: (1) political: ensuring legal recognition and protection of traditional practices; (2) organizational: adapting health services to cultural diversity; and (3) educational: training health personnel in intercultural competencies and reducing staff turnover in Indigenous communities.
Disease prevention and communication
For transmissible disease prevention, evidence-based control measures are essential, including integrated vector management and rapid response protocols for zoonotic emergencies. Communication campaigns must be culturally appropriate and multilingual, using accessible channels for different population groups and strengthening the role of community leaders and intercultural health promoters.
Strategic alliances and environmental action
Building strategic alliances among research centers, government institutions, community organizations, and private sector actors is critical for co-creating innovative, sustainable solutions adapted to local realities. The participation of scientists in policy development and sustained dialogue between knowledge producers and decision-makers emerged as priorities.
The environmental dimension must be closely linked to agroecological practices that reduce harmful agrochemical use and foster harmonious relationships with ecosystems. This linkage means actively conserving biological corridors, protecting water sources, and restoring degraded habitats. Such actions directly support zoonotic disease prevention while enhancing ecosystem health.
Addressing social determinants
A critical aspect identified was the need to understand and address social determinants of health, including educational level, poverty, housing conditions, gender, ethnic discrimination, and social support networks. These social determinants are increasingly recognized as fundamental components of One Health implementation because they directly influence exposure, vulnerability, and access to prevention and healthcare interventions [33]. Incorporating these determinants into intervention design allows strategies to be tailored to specific contexts, enabling sustainable changes in daily practices. These findings are consistent with broader evidence showing that exposure to zoonotic diseases in rural Latin America is strongly shaped by interacting social, ecological, and cultural determinants [121]. Behavioral studies have demonstrated that many health-related actions are socially learned, opening opportunities for interventions aimed at transforming collective habits [172]. Integrating these approaches into prevention programs significantly enhances their effectiveness, especially when combined with educational, regulatory, and strategic communication efforts [173].
To encourage community ownership of One Health strategies, economic incentives should support local initiatives focused on health prevention and sustainable environmental management. Such incentives may include subsidies, access to funding, tax benefits, or technical assistance, creating favorable environments for community action and strengthening co-responsibility mechanisms.
Evaluation and regional cooperation
Establishing systematic mechanisms for evaluation and feedback is essential for monitoring progress, identifying obstacles, and adjusting actions based on empirical evidence. Continuous evaluation reinforces strategy sustainability and ensures adaptability to changing contexts.
Workshop participants emphasized the importance of involving research centers in generating in-depth knowledge on biodiversity loss and the interconnectedness of human, animal, and environmental health. Collaboration between research institutions and communities enables development of evidence-based, locally relevant solutions. Moreover, clear communication to society about holistic health and environmental impacts of human activity is essential for building broad support. Participants further emphasized that sustained collaboration requires mechanisms for continuous stakeholder engagement and feedback to ensure that priorities remain responsive to local needs and regional realities.
Regional cooperation emerges as a cornerstone of the One Health approach in Mesoamerica. Sharing experiences, knowledge, tools, and resources among countries facilitates coordinated responses to common threats and strengthens the foundation for a regional health agenda based on equity, resilience, and sustainability.
Alignment with international and regional strategic frameworks
The proposed One Health strategy for Mesoamerica must explicitly align with guiding principles, priorities, and action frameworks defined within international and regional governance spaces related to human, animal, plant, and environmental health. This alignment ensures technical coherence, facilitates interinstitutional coordination, and enhances mobilization of strategic resources.
The strategy aligns with the FAO–WOAH–WHO–UNEP Joint Plan of Action on One Health (2022–2026), which establishes a collaborative, multisectoral, and transdisciplinary framework for prevention, detection, preparedness, and response to threats impacting multiple health dimensions [174]. At the regional level, the strategy must align with the Pan American Health Organization’s Strategy for International Health Cooperation for Central America and the Dominican Republic, which recognizes the interdependence of health, environment, and social systems [175, 176]. The strategy should also incorporate guidelines from the Regional Health Plan for Central America and the Dominican Republic, developed by the Council of Ministers of Health of Central America and the Dominican Republic (COMISCA), addressing transboundary health risks, strengthening institutional capacities, and promoting environmental health as a pillar of sustainable development [175].
The ecological and biodiversity dimensions require effective articulation with instruments such as the Mesoamerican Biological Corridor and the Regional Environmental Strategy of the Central American Integration System (ER-SICA) [177]. These platforms provide enabling frameworks for integrating sustainable ecosystem management and biodiversity conservation into health strategies while recognizing that deforestation, habitat fragmentation, and climate change amplify emerging infectious disease risk.
Finally, the strategy must align with the 2030 Agenda for Sustainable Development and its Sustainable Development Goals (SDGs) and in particularly with those SDGs that are related to good health and well-being (SDG 3), zero hunger (SDG 2), clean water and sanitation (SDG 6), climate action (SDG 13), life on land (SDG 15), reduced inequalities (SDG 10), and partnerships for the goals (SDG 17) [178].
Acknowledgements
We are grateful to the participants of the One Health workshop held during the WDA–Latin America 2023 meeting in Guatemala, whose discussions enriched the conceptual foundation of this work. We extend our sincere appreciation to the key speakers of the workshop, whose insights and expertise were instrumental in shaping the strategic vision presented in this article.
Abbreviations
- One Health
Integrated approach to human, animal, plant, and environmental health
- OHHLEP
One Health High-Level Expert Panel
- GLACIER
German Latin-American Center for Infection and Epidemiology Research
- CDV
Canine distemper virus
- FAO
Food and Agriculture Organization of the United Nations
- WOAH
World Organization for Animal Health
- WHO
World Health Organization
- UNEP
United Nations Environment Programme
- PAHO
Pan American Health Organization
- COMISCA
Council of Ministers of Health of Central America and the Dominican Republic
- ER-SICA
Regional Environmental Strategy of the Central American Integration System
- SDGs
Sustainable Development Goals
- CDC
Centers for Disease Control and Prevention
- OROV
Oropouche virus
Author contributions
BC-C: Writing – review & editing. ML: Writing – review & editing, AF: Writing – review & editing, JO-G: Writing – review & editing. CNI-C: Writing – review & editing. NK: Writing – review & editing. JFD: Writing – review & editing. GS: Conceptualization, Supervision, Writing – review & editing, AC: Conceptualization, Writing – original draft, review and editing.
Funding
This work was supported by German Academic Exchange Service (DAAD) through the GLACIER project. This work was further supported by European Union through the project ZOE – Zoonosis Emergence across Degraded and Restored Forest Ecosystems (101135094). Views and opinions expressed are, however, those of the author(s) only and do not necessarily reflect those of the European Union or European Research Executive Agency (REA). Neither the European Union nor the European Research Executive Agency (REA) can be held responsible for them.
Data availability
No datasets were generated or analysed during the current study.
Declarations
Ethics approval and consent to participate
Not applicable.
Consent for publication
Not applicable.
Competing interests
Jan Felix Drexler is an Associate Editor for One Health Outlook; however, this manuscript was handled independently by another Associate Editor in accordance with the journal’s editorial procedures. The authors declare that they have no other competing interests.
Footnotes
Publisher’s Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
References
- 1.CEPF - Critical Ecosystem Partnership Fund. Biodiversity hotspots: Mesoamerica. Conserv Int. 2023. Recuperado de: https://www.cepf.net/our-work/biodiversity-hotspots/mesoamerica.
- 2.López-Gallego C, Martínez-Balleza C, Morales-Mávil JE, Moreno-Casasola P, Dávila P. Vascular plant richness in the Usumacinta River Basin: a floristic synthesis. Bot Sci. 2023;101(2). 10.17129/botsci.3253.
- 3.Mollentze N, Streicker DG. Viral zoonotic risk is homogenous among taxonomic orders of mammalian and avian reservoir hosts. Proc Natl Acad Sci USA. 2020;117(17):9423–30. 10.1073/pnas.1919176117. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 4.Carmack RM. Mesoamerica at Spanish contact. In: Carmack RM, Gasco J, Gossen GH, editors. The legacy of Mesoamerica: history and culture of a native American civilization. Englewood Cliffs, New Jersey: Prentice Hall; 1996. p. 80–121. [Google Scholar]
- 5.Eshelman CG. Mesoamérica, cultura y cambio: conceptos problemáticos en el estudio etnográfico de los pueblos indígenas. Diario de Campo. 2007;93:78–83. [Google Scholar]
- 6.Mettenleiter TC, Markotter W, Charron DF, Adisasmito WB, Almuhairi S, Barton Behravesh C, et al. The one health high-level expert panel (OHHLEP). One Health Outlook. 2023;5(1):18. 10.1186/s42522-023-00085-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Molina-Flores B, Vigilato MAN, Rocha F, Cossivi O, Corrales M, Vásquez Niño GA, et al. Assessment of one health initiatives from a veterinary Public health approach in Latin America and the Caribbean. TropicalMed. 2025;10(11):315. 10.3390/tropicalmed10110315. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8.Mokdad AH, Palmisano EB, Zúñiga-Brenes P, Ríos-Zertuche D, Johanns CK, Schaefer A, et al. Supply-side interventions to improve health: findings from the salud Mesoamérica initiative. PLoS ONE. 2018;13(4):e0195292. 10.1371/journal.pone.0195292. [DOI] [PMC free article] [PubMed]
- 9.Kabisch N, Drexler J. Limited ecosystems research as a persistent gap in one health frameworks for emerging infectious diseases. BioScience. 2026. 10.1093/biosci/biag111.
- 10.Brooks FJ. Revising the conquest of Mexico: smallpox, sources, and populations. J Interdiscip Hist. 1993;24(1):1–29. 10.2307/205099. [Google Scholar]
- 11.McCaa R. Spanish and Nahuatl views on smallpox and demographic catastrophe in Mexico. J Interdiscip Hist. 1995;25(3):397–431. 10.2307/205693. [Google Scholar]
- 12.Acuña-Soto R, Romero LC, Maguire JH. Large epidemics of hemorrhagic fevers in Mexico 1545-1815. Am J Trop Med Hyg. 2000;62(6):733–39. 10.4269/ajtmh.2000.62.733. [DOI] [PubMed] [Google Scholar]
- 13.Acuña-Soto R, Stahle DW, Cleaveland MK, Therrell MD. Megadrought and megadeath in 16th century Mexico. Emerg Infect Dis. 2002;8(4):360. 10.3201/eid0804.010175. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Gasco J. Spanish colonialism and processes of social change in Mesoamerica. In: Gil J. Stein, editor. The archaeology of colonial encounters: comparative perspectives. School of American Research Advanced Seminar Series, Santa Fe; 2005. p. 69–108.
- 15.Thèves C, Crubézy, Biagini P. History of smallpox and its spread in human populations. Paleomicrobiology Humans. 2016;161–72. [DOI] [PubMed]
- 16.Manin A, Lefèvre C. The use of animals in Northern Mesoamerica, between the classic and the conquest (200-1521 AD). An attempt at regional synthesis on central Mexico. Anthropozoologica. 2016;51(2):127–47. 10.5252/az2016n2a5. [Google Scholar]
- 17.Valadez Azúa M. The Man-Fauna relationship in Mesoamerica before and after the europeans. Diogenes (Engl. Ed.). 1992;40(159):51–56. 10.1177/039219219204015905. [Google Scholar]
- 18.Memish ZA, Balkhy HH. Brucellosis and international travel. J Travel Med. 2004;11(1):49–55. 10.2310/7060.2004.13551. [DOI] [PubMed] [Google Scholar]
- 19.Lozano-López E, Austreberta-Nazar-Beutelspacher D, Nahed-Toral J. Brucelosis bovina y humana en el sur de México: una zoonosis desatendida. Rev Chil Infectol. 2022;39(2):157–65. 10.4067/S0716-10182022000200157. [DOI] [PubMed] [Google Scholar]
- 20.Lizama MS. Access to the Social Security System in Honduras compared to countries in Mesoamerica and Colombia. Rev Méd Hondur. 2024;92(1):51–58. 10.5377/rmh.v92i1.18218. [Google Scholar]
- 21.Cook BI, Anchukaitis KJ, Kaplan JO, Puma MJ, Kelley M, Gueyffier D. Pre-Columbian deforestation as an amplifier of drought in Mesoamerica. Geophys Res Lett. 2012;39(16). 10.1029/2012GL052565.
- 22.García NM. Consideraciones teóricas sobre el proceso de urbanización en Mesoamérica. Boletín de AntropologíAmericana. 1991;23:137–59. [Google Scholar]
- 23.Mardero S, Schmook B, Calmé S, White RM, Chang JCJ, Casanova G, et al. Traditional knowledge for climate change adaptation in Mesoamerica: a systematic review. Soc Sci Humanit Open. 2023;7(1):100473. 10.1016/j.ssaho.2023.100473. [Google Scholar]
- 24.Gabbert W. Marginación, asimilación y resurgimiento. El Man Oxford de Historia de Centroamérica. 2022;107.
- 25.Barrera-Bassols N, de la Torre Gb. Land use in Mesoamerica in the colonial period. Anth As Multiple Crisis: Perspectives Latin Am. 2024;123.
- 26.Chase DZ, Lobo J, Feinman GM, Carballo DM, Chase AF, Chase ASZ, et al. Mesoamerican urbanism revisited: Environmental change, adaptation, resilience, persistence, and collapse. Proc Natl Acad Sci USA. 2023;120(31):e2211558120. 10.1073/pnas.2211558120. [DOI] [PMC free article] [PubMed]
- 27.Adeniyi Ayinde A, Yusuff Adebayo YA, Ashiru Mustapha AM, Taiwo O, Omotayo Faith OF, Agwuna Favour O, et al. Climate change, vector-borne diseases, and conflict: intersecting challenges in vulnerable states. J Infect Dis Epidemiol. 2024;10(8):326. 10.23937/2474-3658/1510326. [Google Scholar]
- 28.Guégan JF, Ayouba A, Cappelle J, De Thoisy B. Forests and emerging infectious diseases: unleashing the beast within. Environ Res Lett. 2020;15(8):083007. 10.1088/1748-9326/ab8dd7. [Google Scholar]
- 29.Quijano A. Coloniality of power, Eurocentrism, and Latin America. Nepantla: Views South. 2000;1(3):533–80. [Google Scholar]
- 30.Pan American Health Organization. Health of Indigenous Peoples in the Americas. Washington (DC): Pan American Health Organization; 2017.
- 31.Veliz-Rojas L, Bianchetti-Saavedra AF, Silva-Fernández M. Competencias interculturales en la atención primaria de salud: un desafío para la educación superior frente a contextos de diversidad cultural. Cad. Saúde Pública. 2019;35(1):e00120818. 10.1590/0102-311X00120818. [DOI] [PubMed]
- 32.Aguilar-Peña MF, Blandón MF, Garciía-Perdomo HA. Salud intercultural y el modelo de salud propio indígena Intercultural health and the Indigenous health model. Rev salud pública. 2020;22(4):1–5. 10.15446/rsap.V22n4.87320. [DOI] [PubMed] [Google Scholar]
- 33.Cediel Becerra NM, M G-Z, Castro AM, Navas Panadero A, Jiménez, Collins R. Social determinants of health at the human-animal-ecosystem interface. In: Principles of one health for a better planet. Wallingford: CAB International; 2025. p. 137–50.
- 34.DeClerck FAJ, Chazdon R, Holl KD, Milder JC, Finegan B, Martinez-Salinas A, et al. Biodiversity conservation in human-modified landscapes of Mesoamerica: past, present and future. Biol Conserv. 2010;143(10):2301–13. 10.1016/j.biocon.2010.03.026. [Google Scholar]
- 35.Fedick S, Allen M, Gomez-Pompa A. (Eds.).The lowland Maya area: three millennia at the human-wildland interface. CRC Press. 2024. 10.1201/9781003578604.
- 36.Ito T, Sugiura M. Satoyama landscapes as ecological mosaics of biodiversity: local knowledge, environmental Education, and the future of Japan’s rural areas. Environ: Sci Policy Sustain Devel. 2021;63(5):14–25. 10.1080/00139157.2021.1953911. [Google Scholar]
- 37.Beach T, Dunning N, Luzzadder-Beach S, Cook DE, Lohse J. Impacts of the ancient Maya on soils and soil erosion in the central Maya Lowlands. Catena. 2006;65(2):166–78. 10.1016/j.catena.2005.11.007. [Google Scholar]
- 38.Mueller AD, Islebe GA, Anselmetti FS, Ariztegui D, Brenner M, Hodell DA, et al. Recovery of the forest ecosystem in the tropical lowlands of northern Guatemala after disintegration of classic Maya polities. Geology. 2010;38(6):523–26. 10.1130/G30797.1. [Google Scholar]
- 39.Gandy M. Zoonotic urbanisation: multispecies urbanism and the rescaling of urban epidemiology. Urban Stud. 2023;60(13):2529–49. 10.1177/00420980231154802. [Google Scholar]
- 40.Salajegheh-Tazerji S, Magalhães-Duarte P, Gharieb R, Szarpak L, Pruc M, Rahman MT, et al. Migratory wave due to conflicts: risk of increased infection from zoonotic diseases. Transboundary Emerging Dis. 2025;2025(1):5571316. 10.1155/tbed/5571316. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 41.Rodríguez-Morales AJ, Risquez A, Echezuria L. Impact of climate change on health and disease in Latin America. Climate change and variability. Croatia. Sciyo. 2010;463–86.
- 42.White RJ, Razgour O. Emerging zoonotic diseases originating in mammals: a systematic review of effects of anthropogenic land-use change. Mammal Rev. 2020;50(4):336–52. 10.1111/mam.12201. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 43.Ortiz DI, Piche-Ovares M, Romero-Vega LM, Wagman J, Troyo A. The impact of deforestation, urbanization, and changing land use patterns on the ecology of mosquito and tick-borne diseases in Central America. Insects. 2021;13(1):20. 10.3390/insects13010020. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 44.Velázquez A, Mas JF, Gallegos JRD, Mayorga-Saucedo R, Alcántara PC, Castro R, et al. Patrones y tasas de cambio de uso del suelo en México. Gaceta ecológica. 2002;62:21–37. [Google Scholar]
- 45.Bray DB. Forest cover dynamics and forest transitions in Mexico and Central America: Towards a “great restoration”? Reforesting landscapes: linking pattern and processes. Landscape Ser. 2010;85–120. 10.1007/978-1-4020-9656-3_5.
- 46.Calderón-Arguedas O, Troyo A, Moreira-Soto RD, Marín R, Taylor L. Dengue viruses in aedes albopictus Skuse from a Pineapple Plantation in Costa Rica. J Vector Ecol. 2015;40(1):184–86. 10.1111/jvec.12149. [DOI] [PubMed] [Google Scholar]
- 47.Calderón-Arguedas Ã, Moreira-Soto RD, Vicente-Santos A, Corrales-Aguilar E, Rojas-Araya D, Troyo A. Papel potencial de aedes albopictus skuse en la transmisión de virus dengue (DENV) en una zona de actividad piñera de costa rica. Rev Biomed. 2019;30(2):33–41. 10.32776/revbiomed.v30i2.640. [Google Scholar]
- 48.Gallmetzer N, Schulze CH. Impact of oil palm agriculture on understory amphibians and reptiles: a Mesoamerican perspective. Global Ecol Conserv. 2015;4:95–109. 10.1016/j.gecco.2015.05.008. [Google Scholar]
- 49.Furumo PR, Aide TM. Caracterización de la expansión de la palma de aceite para uso comercial en América Latina: cambio en el uso del suelo y comercialización. Palmas. 2017;38(2):27–48. [Google Scholar]
- 50.Goettsch B, Urquiza-Haas T, Koleff P, Acevedo-Gasman F, Aguilar-Meléndez A, Alavez V, et al. Extinction risk of Mesoamerican crop wild relatives. Plants People Planet. 2021;3(6):775–95. 10.1002/ppp3.10225. [Google Scholar]
- 51.Sánchez-Porras R. Desenvolvimento de pontes aéreas para a movimentação segura de macacos na Costa Rica. Rev. Ambientales. 2024;59(1):1–14. 10.15359/rca.59-1.1. [Google Scholar]
- 52.Alencar J, Lorosa ES, Dégallier N, Serra-Freire NM, Pacheco JB, Guimarães AÉ. Feeding patterns of Haemagogus janthinomys (Diptera: Culicidae) in different regions of Brazil. J Med Entomol. 2005;42(6):981–85. 10.1603/0022-2585(2005)042[0981:FPOHJD]2.0.CO;2. [PubMed] [Google Scholar]
- 53.Alencar J, de Mello CFD, Morone F, Albuquerque HG, Serra-Freire NM, Gleiser RM, et al. Distribution of Haemagogus and sabethes species in relation to forest cover and climatic factors in the Chapada Dos Guimarães National Park, state of Mato Grosso, Brazil. J Am Mosq Control Assoc. 2018;34(2):85–92. 10.2987/18-6739.1. [DOI] [PubMed] [Google Scholar]
- 54.Chaverri LG, Dillenbeck C, Lewis D, Rivera C, Romero LM, Chaves LF. Mosquito species (Diptera: Culicidae) diversity from Ovitraps in a Mesoamerican tropical rainforest. J Med Entomol. 2018;55(3):646–53. 10.1093/jme/tjx254. [DOI] [PubMed] [Google Scholar]
- 55.Soper FL. The 1964 status of aedes aegypti eradication and yellow fever in the Americas. Am J Trop Med Hyg. 1965;14(6):887–91. 10.4269/ajtmh.1965.14.887. [DOI] [PubMed] [Google Scholar]
- 56.Salas-Rojas M, de Oliveira-Filho EF, Almazán-Marín C, Rodas-Martínez AZ, Á Á, Drexler JF. Serological evidence for potential yellow fever virus infection in non-human primates, southeastern Mexico. One Health Outlook. 2023;5(1):14. 10.1186/s42522-023-00090-5. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 57.Karjalainen E, Sarjala T, Raitio H. Promoting human health through forests: overview and major challenges. Environ Health Prev Med. 2010;15(1):1–8. 10.1007/s12199-008-0069-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 58.Garg T. Ecosystems and human health: the local benefits of forest cover in Indonesia. J Environ Econ Manag. 2019;98:102271. 10.1016/j.jeem.2019.102271. [Google Scholar]
- 59.Loaiza JR, Dutari LC, Rovira JR, Sanjur OI, Laporta GZ, Pecor J, et al. Disturbance and mosquito diversity in the lowland tropical rainforest of Central Panama. Sci Rep. 2017;7(1):1–13. 10.1038/s41598-017-07476-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Chapin G, Wasserstrom R. Agricultural production and malaria resurgence in Central America and India. Nature. 1981;293(5829):181–85. 10.1038/293181a0. [DOI] [PubMed] [Google Scholar]
- 61.Dusfour I, Achee NL, Briceno I, King R, Grieco JP. Comparative data on the insecticide resistance of anopheles albimanus in relation to agricultural practices in Northern Belize, CA. J Pest Sci. 2010;83(1):41–46. 10.1007/s10340-009-0268-7. [Google Scholar]
- 62.Opportunities for environmentally healthy, inclusive, and resilient growth in Mexico’s Yucatán Peninsula. In: Sánchez-Triana E, Ruitenbeek J, Enriquez S & Siegmann K, editors. World bank publications. 2019.
- 63.Ellis EA, Navarro Martínez A, García Ortega M, Hernández Gómez IU, Chacón Castillo D. Forest cover dynamics in the selva Maya of central and Southern Quintana roo, Mexico: Deforestation or degradation? J Land use Sci. 2020;15(1):25–51. 10.1080/1747423X.2020.1732489. [Google Scholar]
- 64.Tucker CM, Munroe DK, Nagendra H, Southworth J. Comparative spatial analyses of forest conservation and change in Honduras and Guatemala. Conserv Soc. 2005;3(1):174–200. [Google Scholar]
- 65.Moran MD, Monroe A, Stallcup L. A proposal for practical and effective biological corridors to connect protected areas in northwest Costa Rica. NC. 2019;36:113–37. 10.3897/natureconservation.36.27430. [Google Scholar]
- 66.Loza-Rubio E, Montaño-Hirose. A History of paralytic bovine rabies transmitted by vampire Bats in Mexico. In: Rupprecht CE, editor. History of rabies in the Americas: from the Pre-Columbian to the present, volume II. fascinating life sciences. Springer; 2024. 10.1007/978-3-031-25405-5_4Cham.
- 67.León, Moran D. Rabies in Central America: an historical review. In: Rupprecht CE, editor. History of rabies in the Americas: from the Pre-Columbian to the present, volume II. fascinating life sciences. Springer, Cham. 2024. 10.1007/978-3-031-25405-5_5.
- 68.Gutiérrez-Cedillo V, Vargas-Pino F, Chavez-Flores IA, Lecuona L. History of rabies in Mexico. In: Rupprecht CE, editor. History of rabies in the Americas: from the Pre-Columbian to the present, volume II. fascinating life sciences. Springer, Cham; 2024. 10.1007/978-3-031-25405-5_3. [Google Scholar]
- 69.Zarza H, Martínez-Meyer E, Suzán G, Ceballos G. Geographic distribution of Desmodus rotundus in Mexico under current and future climate change scenarios: implications for bovine paralytic rabies infection. Veterinaria México OA. 2017;4(3). 10.21753/vmoa.4.3.390.
- 70.Miller MJ, Loaiza JR. Geographic expansion of the invasive mosquito aedes albopictus across Panama—implications for control of dengue and Chikungunya viruses. PLoS Negl Trop Dis. 2015;9(1):e0003383. 10.1371/journal.pntd.0003383. [DOI] [PMC free article] [PubMed]
- 71.Cartín DMP. La rabia invade Costa Rica. Acta Médica Costarricense. 1968;110(20):210. [Google Scholar]
- 72.Cushman SA, McRae B, Adriaensen F, Beier P, Shirley M, Zeller K. Biological corridors and connectivity. Key Top Conserv Biol. 2013;2:384–404. 10.1002/9781118520178.ch21. [Google Scholar]
- 73.Gatti RC. Ecological peace corridors: a new conservation strategy to protect human and biological diversity. Biol Conserv. 2025;302:110947. 10.1016/j.biocon.2024.110947. [Google Scholar]
- 74.Holland MB,” in Climate and Conservation, eds J. A. Hilty, C. C. Chester, and M. S. Cross “Mesoamerican biological corridor. Washington, DC: Island Press; 2012. p. 56–66. 10.5822/978-1-61091-203-7_5.
- 75.Patel R. Paper plans and possibility: a critical analysis of landscape conservation policy in the Mesoamerican biological corridor. Environ Dev. 2021;37:100600. 10.1016/j.envdev.2020.100600. [Google Scholar]
- 76.Rocha F, Sibim AC, Molina-Flores B, Chiba de Castro WA, Kmetiuk LB, Alves RV, et al. One health priorities: advancing veterinary Public health in Latin America and the Caribbean. One Health Priorities: Advancing Vet Public Health Latin Am Caribb. Pathog. 2024;13(8):710. 10.3390/pathogens13080710. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 77.Misra AK. Climate change and challenges of water and food security. Int J Sustain Built Environ. 2014;3(1):153–65. 10.1016/j.ijsbe.2014.04.006. [Google Scholar]
- 78.Hotez PJ, Damania A, Bottazzi ME. Central Latin America: two decades of challenges in neglected tropical disease control. PLoS neglected tropical diseases. PLoS Neglected Trop Dis. 2020;14(3):e0007962. 10.1371/journal.pntd.0007962. [DOI] [PMC free article] [PubMed]
- 79.Pandey V, Ranjan MR, Tripathi A. Climate change and its impact on the outbreak of vector-borne diseases. In: Recent technologies for disaster management and risk reduction: sustainable community resilience & responses. Cham: Springer International Publishing; 2021. p. 203–28. 10.1007/978-3-030-76116-5_13.
- 80.Zavaleta-Monestel E, Rojas-Chinchilla C, Molina-Sojo P, Murillo-Castro MF, Rojas-Molina JP, Martínez-Vargas E. Impact of climate change on the global dynamics of vector-borne infectious diseases: a narrative review. Cureus. 2025;17(1). 10.7759/cureus.77972. [DOI] [PMC free article] [PubMed]
- 81.Wesselmann KM, Postigo-Hidalgo I, Pezzi L, de Oliveira-Filho EF, Fischer C, de Lamballerie X, et al. Emergence of oropouche fever in Latin America: a narrative review. The Lancet Infect Dis. 2024;24(7):e439–52. 10.1016/S1473-3099(23)00740-5. [DOI] [PubMed]
- 82.Arisco NJ, Peterka C, Diniz C, Singer BH, Castro MC. Ecological change increases malaria risk in the Brazilian Amazon. Proc Natl Acad Sci USA. 2024;121(44):e2409583121. 10.1073/pnas.2409583121. [DOI] [PMC free article] [PubMed]
- 83.Zúñiga MA, Rubio-Palis Y, Brochero H. Updating the bionomy and geographical distribution of anopheles (Nyssorhynchus) albitarsis F: a vector of malaria parasites in northern South America. PLoS ONE. 2021;16(6):e0253230. 10.1371/journal.pone.0253230. [DOI] [PMC free article] [PubMed]
- 84.Forsyth C, Higuita NIA, Hamer SA, Ibarra-Cerdeña CN, Valdez-Tah A, Granados PS, et al. Climate change and Trypanosoma cruzi transmission in north and Central America. Lancet Microbe. 2024;5(10):100946. 10.1016/j.lanmic.2024.07.009. [DOI] [PubMed] [Google Scholar]
- 85.Hernández-Flores A, Elías-Díaz D, Cubillo-Cervantes B, Ibarra-Cerdeña CN, Morán D, Arnal A, et al. Fighting strategies against chagas’ disease: a review. Pathogens. 2025;14(2):183. 10.3390/pathogens14020183. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 86.Ogrzewalska M, Uezu A, Jenkins CN, Labruna MB. Effect of forest fragmentation on tick infestations of birds and tick infection rates by Rickettsia in the Atlantic forest of Brazil. EcoHealth. 2011;8(3):320–31. 10.1007/s10393-011-0726-6. [DOI] [PubMed] [Google Scholar]
- 87.Shultz L, López-Pérez AM, Jasuja R, Helman S, Prager K, Tokuyama A, et al. Vector-borne disease in wild mammals impacted by urban expansion and climate change. EcoHealth. 2023;20(3):286–99. 10.1007/s10393-023-01650-x. [DOI] [PubMed] [Google Scholar]
- 88.Szabó MPJ, Olegário MMM, Santos ALQ. Tick fauna from two locations in the Brazilian savannah. Exp Appl Acarol. 2007;43(1):73–84. 10.1007/s10493-007-9096-8. [DOI] [PubMed] [Google Scholar]
- 89.Romero LE, Binder LC, Marcili A, Labruna MB. Ticks and tick-borne rickettsiae from dogs in El Salvador, with report of the human pathogen rickettsia parkeri. Ticks and tick-borne diseases. Ticks Tick Borne Dis. 2023;14(5):102206. 10.1016/j.ttbdis.2023.102206. [DOI] [PubMed] [Google Scholar]
- 90.Romero-Vidal P, Blanco G, Barbosa JM, Carrete M, Hiraldo F, Pacífico EC, et al. The widespread keeping of wild pets in the Neotropics: an overlooked risk for human, livestock and wildlife health. People Nat. 2024;6(3):1023–35. 10.1002/pan3.10625. [Google Scholar]
- 91.Lopes MG, Junior JM, Foster RJ, et al. Garrapatas y rickettsiae de la vida silvestre en Belice. América Central. Parásitos Vectores. 2016;9:62. 10.1186/s13071-016-1348-1. [Google Scholar]
- 92.Parola P, Paddock CD, Socolovschi C, Labruna MB, Mediannikov O, Kernif T, et al. Update on tick-borne rickettsioses around the world: a geographic approach. Clin Microbiol Rev. 2013;26(4):657–702. 10.1128/cmr.00032-13. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 93.Gómez-Dantés H, Martín JLS, Danis-Lozano R, Manrique-Saide P. Integrated prevention and control strategy for dengue in Mesoamerica. Salud Pública de México. 2011;53:S349–57. [PubMed]
- 94.Valencia-Mendoza A, Danese-DlSantos LG, Sosa-Rubí SG, Aracena-Genao B. Costo-efectividad de prácticas en salud pública: revisión bibliográfica de las intervenciones de la Iniciativa Mesoamericana de Salud. Salud pública Méx. 2011;53:S375–85. 10.1590/S0036-36342011000900011. [DOI] [PubMed]
- 95.Ayala VMC, Perez JM, Besares KC, Lara IFM, Arias SM, Izaba BS, et al. Características clínicas y epidemiológicas de casos probables de síndrome congénito por Zika y los niveles de anticuerpos anti-dengue, Tuxtla Gutiérrez, Chiapas, México. Población y Salud en Mesoamérica. 2022;20(1):2. 10.15517/psm.v20i1.48339. [Google Scholar]
- 96.Mokdad AH, Gagnier MC, Colson KE, Zúñiga-Brenes P, Ríos-Zertuche D, Haakenstad A, et al. Health and wealth in Mesoamerica: findings from Salud Mesomérica 2015. BMC Med. 2015;13(1):1–13. 10.1186/s12916-015-0393-5. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 97.Gutiérrez-Albenda DA. Situación actual del dengue como enfermedad reemergente en Costa Rica. Revista Costarricense de Salud Pública. 2018;27(1):35–41. [Google Scholar]
- 98.Rodriguez-Morales A. Climate change, climate variability and brucellosis. Recent patents on anti-infective drug discovery. 2013. Recent Pat Antiinfect Drug Discov. 2013;8(1):4–12. 10.2174/157489113805290791. [DOI] [PubMed] [Google Scholar]
- 99.Yan C, Liang LJ, Zheng KY, Zhu XQ. Impact of environmental factors on the emergence, transmission and distribution of Toxoplasma gondii. Parasites Vectors. 2016;9(1):1–7. 10.1186/s13071-016-1432-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 100.Cardoso TDS, Simões RO, Luque JLF, Maldonado A, Gentile R. The influence of habitat fragmentation on helminth communities in rodent populations from a Brazilian Mountain Atlantic Forest. J Helminthol. 2016;90(4):460–68. 10.1017/S0022149X15000589. [DOI] [PubMed] [Google Scholar]
- 101.Sánchez MDP, Sanmiguel RA, Díaz Sanchez OA, Ramirez AA, Escobar L. Rabia en las Américas, varios desafíos y “Una Sola Salud”: artículo de revisión. Rev. Investig. Vet. Perú. 2020;30(4):1361–81. 10.15381/rivep.v30i4.17150. [Google Scholar]
- 102.Dos Santos EO, Klain VF, Manrique S, Rodrigues RO, Dos Santos HF, Sangioni LA, et al. Influence of landscape structure on previous exposure to leptospira spp. And Brucella abortus in free-living neotropical primates from southern Brazil. Am J Primatol. 2023;85(4):e23472. 10.1002/ajp.23472. [DOI] [PubMed]
- 103.Ul-Rahman A, Sbabbir MAB, Rasheed M, Bano N, Shahid MF, Habib M, et al. Zoonotic and reverse zoonotic transmission of SARS-CoV-2 virus: a perspective on human-animal interface. Vol. 3. Faisalabad, Pakistan: Zoonosis, Unique Scientific Publishers; 2023. p. 269–82. [Google Scholar]
- 104.Moreira-Soto A, Gade N, Hoffmann B, Drexler JF. Strengthening diagnostic services in Latin America requires regional leadership, sustainable funding, and enhanced data sharing. Health Policy (New Y). 2025;155:105287. 10.1016/j.healthpol.2025.105287. [DOI] [PubMed] [Google Scholar]
- 105.Guhl F, Ramírez JD. Poverty, migration, and chagas disease. Curr Trop Med Rep. 2021;8(1):52–58. 10.1007/s40475-020-00225-y. [Google Scholar]
- 106.Aké-Chan M, Chaves A, Arnal A, Ibarra-Cerdeña CN. Chagas disease in context: how social, economic, and cultural realities shape risk. Disease Biol, Genet, Socioecology. 2025;1(4):11. 10.53941/dbgs.2025.100011. [Google Scholar]
- 107.Aké-Chan M, Sanmartino M, Castillo-Burguete MT, González-Martínez A, Ibarra-Cerdeña CN. (In)coherence between chagas disease policy and the experiences of those affected in Mexico: the need for a transdisciplinary approach. PLoS Negl Trop Dis. 2025;19(5):e0013052. 10.1371/journal.pntd.0013052. [DOI] [PMC free article] [PubMed]
- 108.Bryson JM, Bishop-Williams KE, Berrang-Ford L, Nunez EC, Lwasa S, Namanya DB, et al. Indigenous health adaptation to climate change research team, Harper SL. Neglected tropical diseases in the context of climate change in East Africa: a systematic scoping review. Am J Trop Med Hyg. 2020;102(6):1443–54. 10.4269/ajtmh.19-0380. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 109.Beatty NL, Forsyth CJ, Burkett-Cadena N, Wisely SM. Our current understanding of chagas disease and Trypanosoma cruzi infection in the state of Florida — an update on research in this region of the USA. Curr Trop Med Rep. 2022;9(4):150–59. 10.1007/s40475-022-00261-w. [Google Scholar]
- 110.Ramírez-Solano, Chamizo-García. Determinantes sociales de la enfermedad de Chagas en Costa Rica. Población y Salud en Mesoamérica. 2023;21(1):80–98.10.15517/psm.v21i1.53024.
- 111.Pan American Health Organization. Strategy and Plan of action for Chagas disease prevention, control and care. 50th Directing Council, CD50/16. Washington (DC): Pan American Health Organization; 2010.
- 112.World Health Organization. Chagas disease (also known as American trypanosomiasis). 2026. Available from: https://www.who.int/news-room/fact-sheets/detail/chagas-disease-(american-trypanosomiasis). 18 Jul 2026. Geneva: World Health Organization.
- 113.Velásquez-Ortiz N, Ramírez JD. Understanding the oral transmission of trypanosoma cruzi as a veterinary and medical foodborne zoonosis. Res Vet Sci. 2020;132:448–61. 10.1016/j.rvsc.2020.07.024. [DOI] [PubMed] [Google Scholar]
- 114.López-García A, Gilabert JA. Oral transmission of chagas disease from a one health approach: a systematic review. Trop Med Int Health. 2023;28(9):689–98. 10.1111/tmi.13915. [DOI] [PubMed] [Google Scholar]
- 115.Reperant LA. Putative 14th century outbreak of foodborne chagas disease, Mexico. Vector-Borne Zoonotic Dis. 2023;23(7):390–92. 10.1089/vbz.2022.0092. [DOI] [PubMed] [Google Scholar]
- 116.Conners EE, Ordoñez TL, Cordon-Rosales C, Casanueva CF, Miranda SM, Brouwer KC. Chagas disease infection among migrants at the Mexico/guatemala border. Am J Trop Med Hyg. 2017;97(4):1134. 10.4269/ajtmh.16-0777. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 117.Omarova A, Tussupova K, Berndtsson R, Kalishev M, Sharapatova K. Protozoan parasites in drinking water: a system approach for improved water, sanitation and hygiene in developing countries. IJERPH. 2018;15(3):495. 10.3390/ijerph15030495. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 118.Corrêa CRT, Oliveira-Arbex AP, David É, Guimarães S. Genetic analysis of giardia duodenalis isolates from children of low-income families living in an economically successful region in Southeastern Brazil. Rev Inst Med Trop S Paulo. 2020;62:E20. 10.1590/s1678-9946202062020. [DOI] [PMC free article] [PubMed]
- 119.Sarria-Guzmán Y, Chávez-Romero Y, Bernal JE, González-Jiménez FE, Serrano-Silva N, Fusaro C. Molecular identification of giardia spp. In Latin America: an updated systematic review on reports from 2017 to 2021. J Infect Dev Ctries. 2022;16(3):392–401. 10.3855/jidc.15806. [DOI] [PubMed] [Google Scholar]
- 120.Krumrie S, Capewell P, Smith-Palmer A, Mellor D, Weir W, Alexander CL. A scoping review of risk factors and transmission routes associated with human giardiasis outbreaks in high-income settings. Curr Res Parasitol Vector-Borne Dis. 2022;2:100084. 10.1016/j.crpvbd.2022.100084. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 121.Palomares Velosa JE, S RS, A A, Cediel Becerra NM. Prevention of exposure to zoonoses in rural Latin America: social ecological factors in a diverse regional context. One Health. 2022;15:100444. 10.1016/j.onehlt.2022.100444. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 122.Cáceres L, Rovira J, Torres R, García A, Calzada J, Cruz MD. Caracterización de la transmisión de la malaria por Plasmodium vivax en la región fronteriza de Panamá con Costa Rica en el municipio de Barú, Panamá. Biomedica. 2012;32(4):557–69. 10.7705/biomedica.v32i4.773. [DOI] [PubMed] [Google Scholar]
- 123.Larrañaga N, Mejía RE, Hormaza JI, Montoya A, Soto A, Fontecha GA. Genetic structure of Plasmodium falciparum populations across the Honduras-Nicaragua border. Malar J. 2013;12(1):354. 10.1186/1475-2875-12-354. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 124.McAuliffe M, Triandafyllidou A. (Eds. Informe sobre la migración mundial 2022. Organización Internacional para las Migraciones. Vol. 23. 2022. p. 107–10.
- 125.United Nations Network on Migration. Report on the regional review of the implementation of the global compact for safe. Orderly Regular Migr Latin Am Caribb. 2022. https://migrationnetwork.un.org/system/files/docs/Report%20on%20GCM%20Regional%20Review%20LAC%20%28final%29_0.pdf.
- 126.Wilke ABB, Farina P, Ajelli M, Canale A, Dantas-Torres F, Otranto D, et al. Human migrations, anthropogenic changes, and insect-borne diseases in Latin America. Parasites Vectors. 2025;18(1):4. 10.1186/s13071-024-06598-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 127.Cortes CP, Rodríguez MF, Sued O, Ville R. Infectious diseases and migration in Latin America. In: Handbook of health and migration in Latin America and the Caribbean. Vol. 1. Cham: Springer Nature Switzerland; 2025. p. 79–104. 10.1007/978-3-031-84315-0_5.
- 128.Wesseling C, Crowe J, Hogstedt C, Jakobsson K, Lucas R, Wegman DH. The epidemic of chronic kidney disease of unknown etiology in Mesoamerica: a call for interdisciplinary research and action. Am J Public Health. 2013;103(11):1927–30. 10.2105/AJPH.2013.301594. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 129.Raines N, Gonzalez M, Wyatt C, Kurzrok M, Pool C, Lemma T, et al. Risk factors for reduced glomerular filtration rate in a Nicaraguan community affected by Mesoamerican nephropathy. MEDICC Rev. 2014;16:16–22. [DOI] [PubMed] [Google Scholar]
- 130.Roncal-Jimenez CA, García-Trabanino R, Wesseling C, Johnson RJ. Mesoamerican nephropathy or global warming nephropathy? Blood Purif. 2016;41(1–3):135–38. 10.1159/000441265. [DOI] [PubMed] [Google Scholar]
- 131.Correa-Rotter R. Mesoamerican nephropathy or chronic kidney disease of unknown origin. Chronic Kidney Disease Disadvantaged Populations. Academic Press. 2017;221–28. 10.1016/B978-0-12-804311-0.00022-4.
- 132.Rotter RC, Trabanino RG. Nefropatía mesoamericana: una nueva enfermedad renal crónica de alta relevancia regional. Acta Médica Grupo Ángeles. 2018;16(S1):16–22. [Google Scholar]
- 133.Tladi LS. Poverty and HIV/AIDS in South Africa: an empirical contribution. SAHARA-J: J Soc Aspects HIV/AIDS. 2006;3(1):369–81. 10.1080/17290376.2006.9724863. [DOI] [PubMed] [Google Scholar]
- 134.Badmus O, Camorlinga S, Simpson O. Poverty and the emergence of tuberculosis: an agent-based modelling approach. 2016 IEEE-EMBS International Conference on Biomedical and Health Informatics (BHI). IEEE; 2016, 561–64. 10.1109/BHI.2016.7455959.
- 135.Prakoeswa FRS, Soebono H, Husada D, Notobroto HB, Listiawan MY, Endaryanto A, et al. Towards prevention and eradication of leprosy: current status and research needed in community health & immune dysregulation. Indian J Lepr. 2020;92:257–78. [Google Scholar]
- 136.Venkatakrishnan Y, Thangaraju P, Jeganathan S, Sankaran SK, Kannan R. Nutritional status and morbidity profile of children with leprosy contact in a rural community. Trop Doct. 2020;50(4):311–17. 10.1177/0049475520932193. [DOI] [PubMed] [Google Scholar]
- 137.Kirk E. An underlying affliction: how the 1918 influenza Pandemic affected Socio-economically disadvantaged Canadians. Mirror-Undergrad Hist J. 2024;44(1):140–56. 10.5206/mirror.v44i1.17077. [Google Scholar]
- 138.Gómez i Prat J, Souza SMFMD. Prehistoric tuberculosis in America: adding comments to a literature review. Mem Inst Oswaldo Cruz. 2003;98(suppl 1):151–59. 10.1590/S0074-02762003000900023. [DOI] [PubMed] [Google Scholar]
- 139.Reyes-González MP, Álvarez Gordillo Á-G. Formación de promotores para la prevención y control de la tuberculosis en la región fronteriza de Chiapas, México. PSM. 2014;11(2):130–46. 10.15517/psm.v11i2.12739. [Google Scholar]
- 140.Gutiérrez-Sandí W, Blanco-Chan C. Las enfermedades de transmisión sexual y la salud sexual del costarricense Tema I. SIDA/VIH. TM. 2016;29(3):117–131.10.18845/tm.v29i3.2892.
- 141.García-González J. Análisis de la Comunicación estratégica y organizacional para la prevención de VIH/SIDA:caso proyecto mesoamericano. Revista Electrónica Medicina, Salud y Soc. 2014;5(1):48–58. [Google Scholar]
- 142.Fèvre EM, Bronsvoort BMDC, Hamilton KA, Cleaveland S. Animal movements and the spread of infectious diseases. Trends Microbiol. 2006;14(3):125–31. 10.1016/j.tim.2006.01.004. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 143.Hassan OA, de Balogh K, Winkler AS. One health early warning and response system for zoonotic diseases outbreaks: emphasis on the involvement of grassroots actors. Vet Med & Sci. 2023;9(4):1881–89. 10.1002/vms3.1135. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 144.Pettan-Brewer C, Martins AF, Abreu DPBD, Brandão APD, Barbosa DS, Figueroa DP, et al. From the approach to the concept: one health in Latin America-experiences and perspectives in Brazil, Chile, and Colombia. Front Public Health. 2021;9:687110. 10.3389/fpubh.2021.687110. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 145.Davis A, Sharp J. Rethinking one health: emergent human, animal and environmental assemblages. Soc Sci Med. 2020;258:113093. 10.1016/j.socscimed.2020.113093. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 146.World Organisation of Animal Health (WOAH). New world screwworm (cochliomyia hominivorax) and Old world screwworm (Chrysomya Bezziana). Man Diagnostic Tests Vaccines Terr Anim (OMSA). 2022.
- 147.Zaldivar-Gomez A, Gomez-Vazquez JP, Iniesta-Valencia AJ, Figueroa-Martínez LG, Rico-Chávez O. Estimation the reinvasion of new world screwworm (Cochliomyia hominivorax) in Central America: the role of animal movement in disease dispersal and control measures. Vet Parasitol: Reg Stud Rep. 2025;59:101220. 10.1016/j.vprsr.2025.101220. [DOI] [PubMed] [Google Scholar]
- 148.Venegas-Montero DP, Alfaro-Vellanero MJ, Rojas-Araya D, Calderón-Arguedas Ó, Vargas-Castro CM, Baldioceda-Villarreal A, et al. Case report: Re-emergence of cochliomyia hominivorax in Costa Rica: report of a human myiasis case 23 years after elimination. Am J Trop Med Hyg. 2024;111(5):1020–23. 10.4269/ajtmh.24-0342. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 149.Servicio Nacional de Sanidad, Inocuidad y Calidad Agroalimentaria (SENASICA). Atlas Sanitario: Gusano Barrenador del Ganado (GBG). 2025. n.d. https://dj.senasica.gob.mx/AtlasSanitario/storymaps/miagbg.html.
- 150.United States Department of Agriculture, Animal and Plant Health Inspection Service (APHIS). Outbreak of New world screwworm in Central America and Mexico. 2025. https://www.aphis.usda.gov/livestock-poultry-disease/cattle/ticks/screwworm/outbreak-central-america.
- 151.Avendaño R, Barrueta F, Soto-Fournier S, Chavarria M, Monge O, Gutierrez-Espeleta GA, et al. Canine distemper virus in wild felids of Costa Rica. J Wildl Dis. 2016;52(2):373–77. 10.7589/2015-02-041. [DOI] [PubMed] [Google Scholar]
- 152.Martínez-Gutiérrez M, Ruiz-Saenz J. Diversity of susceptible hosts in canine distemper virus infection: a systematic review and data synthesis. BMC Vet Res. 2016;12(1):78. 10.1186/s12917-016-0702-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 153.Mares-Guia MAMD, Furtado MC, Chalhoub FLL, Portugal MD, de Oliveira Coelho JMC, de Filippis Amb AMB, et al. Coinfection with canine distemper virus and yellow fever virus in a neotropical primate in Brazil. Viruses. 2024;16(11):1670. 10.3390/v16111670. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 154.De Campos BH, dos Santos D, Duarte DJRA, Amaral VHB, Figueiredo CDCC, Vieira AD, et al. Lethal canine distemper virus (Morbillivirus canis) outbreak in free-ranging black-tufted marmosets (Callithrix penicillata) in Brazil: clinical, pathological, genotypical evaluation, and assessment of viral tropism. Transboundary Emerging Dis. 2025;2025(1):4701926. 10.1155/tbed/4701926. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 155.Zeller KA, Rabinowitz A, Salom-Perez R, Quigley H. The Jaguar Corridor Initiative: a range-wide conservation strategy. In: Molecular population genetics, evolutionary biology and biological conservation of neotropical carnivores. New York (NY): Nova Science Publishers; 2013. p. 629–57.
- 156.Rendon-Marin S, Martinez-Gutierrez M, Suarez JA, Ruiz-Saenz J. Canine distemper virus (CDV) transit through the Americas: need to assess the impact of CDV infection on species conservation. Front Microbiol. 2020;11:810. 10.3389/fmicb.2020.00810. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 157.Duque-Valencia J, Forero-Munoz NR, Diaz FJ, Martins E, Barato P, Ruiz-Saenz J. Phylogenetic evidence of the intercontinental circulation of a canine distemper virus lineage in the Americas. Sci Rep. 2019;9(1):15747. 10.1038/s41598-019-52345-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 158.Rüegg S, Traore T, Pettan-Brewer C, Figueroa D, Cediel-Becerra N, Ormea V, et al. One health implementation cycle, stakeholder analysis and engagement. In: Principles of one health for a better planet. Wallingford: CABI; 2025. 10.1079/9781800623002.0011.
- 159.FAO/WHO Joint Expert Committee on Food Additives (JECFA). Caramel colours. in: combined compendium of food additive specifications. In: Monograph. Vol. 11. Rome: Food and Agriculture Organization of the United Nations; 2011.
- 160.Pernet CA, Ribi Forclaz A. Revisiting the food and agriculture organization (FAO): International histories of agriculture, Nutrition,and development. Int Hist Rev. 2019;41(2):345–50. 10.1080/07075332.2018.1460386. [Google Scholar]
- 161.Lozier M, Turcios-Ruiz RM, Noonan G, Ordunez P. Chronic kidney disease of nontraditional etiology in Central America: a provisional epidemiologic case definition for surveillance and epidemiologic studies. Rev Panamericana de Salud Pública. 2016;40:294–300. [PMC free article] [PubMed] [Google Scholar]
- 162.Carpenter A, Waltenburg MA, Hall A, Kile J, Killerby M, Knust B, et al. & vaccine preventable zoonotic disease working group. Vaccine preventable zoonotic diseases: challenges and opportunities for public health progress. Nato Adv Sci Inst Se. 2022;10(7):993. 10.3390/vaccines10070993. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 163.Feinman GM, Carballo DM. Collaborative and competitive strategies in the variability and resiliency of large-scale societies in Mesoamerica. Econ Anthropol. 2018;5(1):7–19. 10.1002/sea2.12098. [Google Scholar]
- 164.Bcheraoui C, Kamath AM, Dansereau E, Palmisano EB, Schaefer A, Hernandez B, et al. Results-based aid with lasting effects: sustainability in the Salud Mesoamérica Initiative. Globalizat Health. 2018;14(1):1–14. 10.1186/s12992-018-0418-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 165.Castro-Arroyave D, Monroy MC, Irurita MI. Integrated vector control of chagas disease in Guatemala: a case of social innovation in health. Infect Dis Poverty. 2020;9(1):1–9. 10.1186/s40249-020-00639-w. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 166.Moreira-Soto A, Beuchel C, Tabares X, Wulf B, Gade N, Fischer C, et al. Socioeconomic determinants potentially underlying differential global SARS-CoV-2 testing capacity: an ecological study. BMJ Open. 2025;15(3):e090804. 10.1136/bmjopen-2024-090804. [DOI] [PMC free article] [PubMed]
- 167.Moreira-Soto A, Postigo-Hidalgo I, Tabares X, Roell Y, Fischer C, Gotuzzo E, et al. Drexler JF.Transfusion-transmitted infections: risks and mitigation strategies for oropouche virus and other emerging arboviruses in Latin America and the Caribbean. Lancet Reg Health - Americas. 2025;46:100. 10.1016/j.lana.2025.101089. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 168.Hirth KG. The structure of Mesoamerican economy. Aztec Econ World: Merchants Mark Ancient Mesoam. Cambridge Univ Press. 2016;19–58.
- 169.Novelo AF, Montiel-Méndez. An entrepreneurial perspective of the Mesoamerican civilizations: implications for Latin America. Emerald Handb Entrep Latin Am: Unleashing Millennial Potential. Emerald Publishing Ltd. 2022;275–96.
- 170.Sordi C. Mobilização e predação: a guerra contra espécies invasoras sob duas perspectivas. Horiz. Antropol. 2020;26(57):207–37. 10.1590/s0104-71832020000200008. [Google Scholar]
- 171.Cediel N, Prieto-Quintero S, Garzon ADM, Villafañe-Izquierdo M, Rúa C, Jimenez N, et al. Woman-sensitive one health perspective in four tribes of indigenous people from Latin America: Arhuaco, Wayuú, Nahua, and Kamëntsá. Front Public Health. 2022;10:774713. 10.3389/fpubh.2022.774713. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 172.Gardner B, Arden MA, Brown D, Eves FF, Green J, Hamilton K, et al. Desarrollo de intervenciones de cambio de comportamiento saludable basadas en hábitos: Veintiuna preguntas para guiar futuras investigaciones. Psicologíy salud. 2023;38(4):518–40. [Google Scholar]
- 173.Kreps GL. Addressing resistance to adopting relevant health promotion recommendations with strategic health communication. Inf Serv Use. 2023;43(2):131–42. 10.3233/ISU-230187. [Google Scholar]
- 174.World Health Organization, United Nations Environment Programme, & World Organisation for Animal Health. One health joint plan of action (2022-2026): working together for the health of humans, animals, plants and the environment. World Health Organ. 2022.
- 175.Miranda J, Barahona OM, Krüger AB, Lagos P, Moreno-Serra R. Central America and the Dominican Republic at crossroads: the importance of regional cooperation and health economic research to address current health challenges. Value Health Reg Issues. 2024;39:107–14. 10.1016/j.vhri.2023.11.001. [DOI] [PubMed] [Google Scholar]
- 176.Auer A, Guerrero Espinel JE. The Pan American health organization and international health: a history of training, conceptualization, and collective development. Rev Panam Salud Publica. 2011;30(2):111–21. [PubMed] [Google Scholar]
- 177.Hernández ACC, Ortega-Argueta A, Campillo LMG, Bello-Baltazar E, Nieto RR. Effectiveness of management of the Mesoamerican biological corridor in Mexico. Landsc Urban Plan. 2022;226:104504. 10.1016/j.landurbplan.2022.104504. [Google Scholar]
- 178.Weiland S, Hickmann T, Lederer M, Marquardt J, Schwindenhammer S. The 2030 agenda for sustainable development: Transformative change through the sustainable development goals? PaG. 2021;9(1):90–95. 10.17645/pag.v9i1.4191. [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Availability Statement
No datasets were generated or analysed during the current study.




