Casuistry of primates in a veterinary center in Paraguay: retrospective report 2004-2025
Joerg Richard Vetter1,2* , and Mauricio E. Martínez3 .
1Departamento de Recursos Faunísticos y Medio Natural, Facultad de Ciencias Veterinarias, Universidad Nacional de Asunción, San Lorenzo – Paraguay.
2Refugio Silvestre Urutau, Filadelfia – Paraguay.
3Grupo de Iniciación Científica, Facultad de Ciencias Veterinarias, Universidad Nacional de Asunción, San Lorenzo – Paraguay. E-mail: mauricioddo70@gmail.com (MEM)
*Corresponding author: jvetter@vet.una.py
Non-human primates play a fundamental role in tropical ecosystems, contributing to key ecological processes such as seed dispersal and the maintenance of community structure, while also holding significant evolutionary, cultural, and social value. Despite their importance, illegal trafficking of primates is rife. In Paraguay, five native primate species are recognized, several of which are affected by illegal trade and inadequate captive management. This study reports the species and main clinical findings of non-human primates transferred to the Departamento de Recursos Faunísticos y Medio Natural of the Facultad de Ciencias Veterinarias, Universidad Nacional de Asunción, between 2004 and 2025. Data were obtained from individual medical records, considering only primary diagnoses, and included information on taxonomy, origin, diet, and clinical condition of individuals. A total of 292 primates of seven genera were registered, with Sapajus cay being the most frequent species (50%), followed by Alouatta caraya (31.8%) and Aotus azarae (10.6%). Across all species, the most common reasons for consultation were routine check-ups, trauma, digestive disorders, infectious diseases, and respiratory conditions. Trauma and tetanus were recurrent findings, highlighting the impact of poor management and exposure to anthropogenic risks. In more than 88% of cases, diets were classified as incomplete or inappropriate, typically characterized by excessive sweet fruits, processed foods, and a lack of fiber, contrasting sharply with species-specific nutritional requirements. Information on animal origin was frequently missing, although available data indicated widespread national and transboundary illegal trafficking. The results emphasize the consequences of illegal possession and inadequate captive conditions on primate health and welfare, as well as the associated risks to conservation and public health due to zoonotic and anthropozoonotic diseases. Strengthening wildlife law enforcement, improving public awareness, and developing standardized protocols for rescue and rehabilitation are urgently needed in Paraguay.
Keywords: Anthropozoonosis, illegal wildlife traffic, Paraguay, primates, zoonosis.
Los primates no humanos desempeñan un papel fundamental en los ecosistemas tropicales, ya que contribuyen a procesos ecológicos clave, como la dispersión de semillas y el mantenimiento de la estructura de las comunidades, al tiempo que tienen un importante valor evolutivo, cultural y social. A pesar de su importancia, el tráfico ilegal de primates es muy frecuente. En Paraguay se reconocen cinco especies de primates nativos, varias de las cuales se ven afectadas por el comercio ilegal y la gestión inadecuada en cautividad. Este estudio informa sobre la composición de las especies y los principales hallazgos clínicos de los primates no humanos trasladados al Departamento de Recursos Faunísticos y Medio Natural de la Facultad de Ciencias Veterinarias de la Universidad Nacional de Asunción entre 2004 y 2025. Los datos se obtuvieron de los expedientes médicos individuales, teniendo en cuenta únicamente los diagnósticos primarios, e incluyeron información sobre taxonomía, origen, dieta y estado clínico. Se registraron un total de 292 primates, siendo Sapajus cay la especie más frecuente (50 %), seguida de Alouatta caraya (31,8 %) y Aotus azarae (10,6 %). En todas las especies, los motivos más comunes de consulta fueron revisiones rutinarias, traumatismos, trastornos digestivos, enfermedades infecciosas y afecciones respiratorias. Los traumatismos y el tétanos fueron hallazgos recurrentes, lo que pone de relieve el impacto de la mala gestión y la exposición a riesgos antropogénicos. En más del 88 % de los casos, las dietas se clasificaron como incompletas o inadecuadas, caracterizadas típicamente por un exceso de frutas dulces, alimentos procesados y una falta de fibra, lo que contrasta fuertemente con los requisitos nutricionales específicos de cada especie. A menudo faltaba información sobre el origen de los animales, aunque los datos disponibles indicaban un tráfico ilegal generalizado a nivel nacional y transfronterizo. Los resultados ponen de relieve las consecuencias de la posesión ilegal y las condiciones inadecuadas de cautiverio para la salud y el bienestar de los primates, así como los riesgos asociados para la conservación y la salud pública debido a las enfermedades zoonóticas y antropozoonóticas. En Paraguay es urgente reforzar la aplicación de la legislación sobre fauna silvestre, mejorar la sensibilización del público y elaborar protocolos normalizados para el rescate y la rehabilitación.
Palabras clave: antropozoonosis, Paraguay, primates, tráfico ilegal de fauna, zoonosis.
© 2026 Asociación Mexicana de Mastozoología, www.mastozoologiamexicana.org
Non-human primates (hereafter primates) are vitally important to tropical biodiversity and to many ecosystem functions, processes, and services, such as seed dispersal and the maintenance of community structures (Estrada et al. 2017; Fergnani et al. 2020). They are our closest living bio-
logical relatives, provide us with fundamental information about human evolution, and play an important role in the livelihoods, cultures, and religions of many societies. Paradoxically, unsustainable human activities are now the main force threatening primate populations (Estrada et al. 2017).
Primates face an imminent extinction crisis, with around 93% of species characterized by declining populations and 65% of species classified as Vulnerable, Endangered, or Critically Endangered (Estrada and Garber 2022). Population declines in approximately 75% of species are associated with deforestation and habitat loss resulting from agricultural expansion, livestock farming, and natural resource extraction. Other pressures that negatively affect primate populations include unsustainable hunting of wild animals, the illegal pet trade, expansion of road networks, transmission of zoonotic diseases, and climate change (Estrada et al. 2020).
There are five species of primates recorded in Paraguay: Alouatta caraya (Atelidae), Aotus azarae (Aotidae), Mico melanurus (Callithrichidae), Sapajus cay (Cebidae), and Plecturocebus pallescens (Pitheciidae). Two species (A. azarae and P. pallescens) have been classified as Least Concern (LC), while A. caraya and M. melanurus are classified as Near Threatened (NT), and S. cay is classified as Vulnerable (Vu) (Bicca-Marques et al. 2021; Milagres et al. 2021; Rímoli et al. 2021; Rumiz et al. 2021; Rímoli et al. 2022). On a national level, S. cay, A. caraya and A. azarae are classified as LC, although it has been suggested that S. cay be upgraded to Vulnerable (Cartes et al. 2017; Smith and Lusseau 2024). On the other hand, M. melanurus was categorized as Vulnerable due to habitat loss from land conversion and fragmentation of remaining forests, and probable hunting for the pet trade is mentioned (Cartes et al. 2017). In contrast, P. pallescens is categorized as Near Threatened (NT) due to the severe deforestation process affecting the Paraguayan Chaco (Cartes et al. 2017).
In South America, illegal primate trafficking is a major factor in the decline of native primate populations, but the absence of clear legal frameworks, insufficient financial and human resources allocated to controlling and combating trafficking, and the lack of established protocols for the rescue, rehabilitation, and reintroduction of animals hinder any effort to eliminate established trafficking schemes (Estrada-Cely and González 2008; Tirira 2013; Shanee et al. 2017; Shanee et al. 2023). Paraguay has been a member of the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) since 1976, and the Law 96/92 “On Wildlife” prohibits the trade of wild animals that do not come from legally authorized breeding facilities. As such, there is currently no legal way to obtain a primate for domestic ownership in the country.
The objective of this study is to report on the main clinical findings of the primate species transferred to the Departamento de Recursos Faunísticos y Medio Natural of the Facultad de Ciencias Veterinarias, Universidad Nacional de Asunción, in the city of San Lorenzo, over a twenty-year period (2004-2025).
Materials and methods
The data were obtained from the individual medical records of primates stored in the Departamento de Recursos Faunísticos y Medio Natural of the Facultad de Ciencias Veterinarias (FCV), Universidad Nacional de Asunción (UNA) from 2004 to 2025. All medical records are annual, and in most years the department was closed during the month of January. For all medical records, only the primary diagnosis was considered.
From each medical record we obtained the date of consultation, annual individual medical record number, taxon, weight in grams (if recorded), sex (if recorded), age as recorded (if recorded), origin (if recorded), time with current owner, description of the diet offered by current owner, diagnosis, and subclassification of the diagnosis (e.g., trauma, caused by a vehicle or by another animal). All the data were obtained as registered in the medical records. The diagnosis of the primate upon arrival was established based on the available information and classified into the following categories: routine check-up, dermatological, digestive, unspecified (when a definitive diagnosis could not be reached), poisoning, management (e.g., problems caused by inappropriate housing or husbandry), neoplasia, nutritional (e.g., metabolic bone disease or diabetes), reproductive, respiratory, trauma, infectious, or undefined (when left blank).
As for the food provided, given that the food offered to different animals varied greatly, diets were classified as “incomplete or inadequate” or “adequate,” based on the species’ known feeding ecology.
To analyze the data, measures of central tendency and dispersion were calculated for quantitative data, and absolute frequency and relative frequency (as percentages) were analyzed for qualitative data.
Results
Between 2004 and 2025, 292 primates were registered in the Departamento de Recursos Faunísticos y Medio Natural, FCV-UNA. The number of individuals per taxon is shown in Table 1.
The most common species was Azara’s capuchin monkey (Sapajus cay), recorded in 146 clinical records (50% of the total). Of these, 78 were male, 41 were female, and 28 records did not specify sex. Weight was recorded in 107 records, with an average weight of 1350.8 ± ٩٠٦.٦ grams. Age was not recorded uniformly: in 114 records, age was reported numerically, with an average age of 44.3 months; some records reported age by standard classifications, where 12 were recorded as “juvenile” and 10 as “adult”; and in 10 records, age was not recorded. The main reason for consultation was routine check-up (25.3%, n=37), followed by trauma (17.1%, n=25) (Table 2). Trauma was sub-classified according to cause, with four cases due to electricity (Figure 1A), four due to dog attacks, three due to human attacks, two due to burns, and 12 cases with no established cause. Infectious processes accounted for 13% (n=19) of the records, with 16 cases of tetanus (Figure 1B), one case of Mycobacterium tuberculosis infection, and two unspecified infections. Finally, 16 cases (11%) of various dermatological conditions (ectoparasites, abscesses, and mycosis) (Figure 1C), 13 cases (8.9%) of digestive disorders (mainly undefined gastroenteritis), and 13 (8.9%) cases of undefined respiratory disorders were reported.
The diet offered to capuchin individuals varied greatly between patients. In 89.7% (n=131) of cases, the capuchin monkeys were provided with an incomplete or inappropriate diet, consisting of an excess of sweet fruits, sweets, cold cuts and sausages, soft drinks, coffee and caffeinated beverages, dairy products, and/or fried foods. Only in four cases was a diet reported that could be considered appropriate for the species. In three files, only “varied diet” is reported, and in eight files, the diet was not described.
Eighty-six (58.9%) records did not include information on the origin of the individuals. However, six records mentioned “Chaco”, nine cases reported municipal markets (mainly Mercado N°4 in Asunción), and 45 records reported 35 different cities in the Oriental Region of Paraguay as the origin.
The second most common species recorded was the black-and-gold howler monkey (Alouatta caraya), recorded for 93 clinical records (31.8% of total records). Of these, 39 were male, 39 female, and 15 records did not specify sex. Weight was recorded in 78 records, with a mean weight of 2,182.9 ± ٢١٠.٨ grams. Age was recorded numerically in 77 records, with a mean of 18.8 ± ٣١.٢ months. Other records reported the age by standard classifications, where five were recorded as “juvenile,” six as “adult,” and in five records, the age was not recorded. The main reason for consultation was digestive disorders, reported for 28 records (30.1%), with six cases of parasitic gastroenteritis, three cases of bacterial gastroenteritis, nine cases of undefined gastroenteritis, one case of stomatitis, one case of hemorrhoids, and eight undefined cases. Routine check-ups were recorded in 21 files (22%). This was followed by trauma in 17 files (18.3%), mainly due to undefined causes (10/17) and electricity (3/17), dermatological conditions in six files, respiratory conditions in five files, three cases of tetanus, and six files without diagnosis (Table 2).
Eighty-two records (88.2%) described a diet that was incomplete or inadequate for the species, mainly due to an excess of sweet fruits, lean meat, pasta, white rice, dairy products, and a general lack of fiber. Only four files reported a diet that could be considered appropriate, and 7 files did not describe the food.
Fifty files (53.8%) did not record the origin of the indi-
viduals. However, eleven forms mentioned “Chaco”, seven report municipal markets (mainly Mercado N° 4 in Asunción), three mention the city of Acahay, and 22 report 17 different cities in the Oriental Region of Paraguay as the origin.
The Azara’s owl monkey (Aotus azarae, called Ka’i Pyharé in the Guaraní language), was recorded in 31 clinical records (10.6% of total records). Of these, 18 were female, 7 male, and 6 records did not specify the sex. Weight was recorded in 27 records, with a mean of 570.85 ±256.5 grams. Age was recorded numerically in 22 records, with a mean of 8.7 months (±٥.٤); and some records reported age by standard classifications, where four were recorded as “juvenile”, one as “adult”, and in four records age was not recorded. The main reason for consultation was undefined respiratory condition (n=9), followed by trauma (n=7), and infectious disease (n=4), including three cases of encephalitis caused by Herpes Simplex Virus (Figure 2) and one case of tetanus. Six records were registered as routine check-ups (19.4%), and two records did not report a diagnosis (Table 2).
Twenty-eight records (90.3%), described an incomplete or inadequate diet for the species, mainly consisting of homemade food, sweets, dairy products, lean meat, bread, and excessive amounts of sweet fruits. Only one clinical record described a diet that could be considered appropriate, and two records did not describe the diet at all.
Sixteen records (51.6%) did not include information on the origin of the individuals. Five records mentioned “Chaco”; six records mentioned four cities in the Oriental Region of Paraguay (Asunción, San Lorenzo, Emboscada, and Loma Grande); two records mentioned municipal markets (Asunción and the other unidentified); and two medical records report two different cities in the Occidental Region of Paraguay (Puerto José Falcón and Pozo Colorado) as the origin.
The medical records of individuals of the genus Callithrix did not contain sufficient data. The white-coated titi, Plecturocebus pallescens (Ka’i ygau in Guaraní language), was recorded in four medical records. Of these, three were female and one was male, with a mean weight of 338.75 grams (195 - 600) and an average age of 8.8 months (5 - 12). Two records did not indicate the origin of the animals; one mentioned the city of Villarrica, and another mentioned the city of Pozo Colorado. Three patients of the genus Saimiri (species not identified) were recorded (two females and one male), with a mean weight of 331.6 grams (305-360), all reported as originating in Bolivia.
It is worth mentioning that one adult female was recorded under the species Saguinus fuscicollis. The animal’s weight was not recorded, but it was reported as originating from Brazil and was diagnosed with a nonspecific respiratory infection.
Discussion
The Azara’s capuchin monkey (S. cay) is a species distributed throughout eastern Paraguay, including Asunción (MADES et al. 2021), as well as part of the humid Chaco, matching the reported origin of the animals in this manuscript. The species’ feeding habits are plastic and opportunistic. Its diet in the wild is complex, consisting of a wide variety of food items, and is closely related to the availability of food in the ecosystem (Smith et al. 2022), unlike the limited and nutritionally inadequate range of food items reported in clinical records, including dairy products, excess sweet fruits, lean meat, processed foods, fried foods, sweets, and soft drinks, among others. The mean weight reported in the findings is within the expected mean weight for the species (1200 g in females, 4500 g in males), although closer to the minimum range (Verona and Pissinatti 2014), which could be related to the inadequate diet or to the fact that the published mean weight refers to adult weight.
The black howler monkey (A. caraya) is distributed in humid ecosystems associated with riparian forests, mainly present in the Pantanal and Lower Chaco ecoregions, although it has a wide distribution in eastern Paraguay (Cartes et al. 2018), matching the origin of the animals recorded. The mean weight reported in the findings is below the expected minimum weight for the species (5800 g), which may be related to the fact that the mean age of the animals was still far from sexual maturity, when they should reach adult weight (Verona and Pissinatti 2014), or inadequate management, due to the complexities of managing the species in captivity and the negative impact on the animals’ health (Cubas 1996; Pastor-Nieto 2014).
Regarding these two species, our findings match reports from other countries in that the families Cebidae and Atelidae present the highest number of cases under human care, with trauma also being one of the main reasons for veterinary consultation, albeit also putting particular emphasis on the impact of infectious diseases on the animals’ quality of life (Cubas 1996; Varela et al. 2010; Nolasco 2017; Yllescas Barrientos 2019).
Azara’s owl monkey (A. azarae) is an arboreal species that inhabits tropical and xerophytic forests, with its Paraguayan distribution limited to the humid Chaco and the semi-arid forests of the dry Chaco (Cartes et al. 2018; Weiler et al. 2019). The reported origins of the species indicate widespread trafficking at the national level. The species’ diet is flexible and includes flowers, fruits, leaves, and invertebrates (Weiler et al. 2019; van der Heide et al. 2023), which is very different from the visibly inappropriate diet reported in this study. The mean weight reported is similar to the known lower range expected for the species (600 to 1000 grams), although this range involved a predominance of young individuals, still far from sexual maturity (Calle and Joslin 2014; Verona and Pissinatti 2014), which can differ from the expected adult weight.
The genus Callithrix currently comprises six species, all endemic to southern and eastern Brazil, associated with the Atlantic Forest, the Cerrado, and the Caatinga (Malukiewicz et al. 2020). C. jacchus is one of the smallest species in the genus and is native to the Atlantic Forest and Caatinga (in the states of Maranhao, Piauí, Ceará, Rio Grande do Norte, Paraíba, Pernambuco, Alagoas, Bahia, and Tocantins; Rylands et al. 2009), so the presence of the species in Paraguay is indicative of illegal transnational trafficking. These species feed on fruits, gum, and invertebrates (Castro and Araújo 2007; Abreu et al. 2016), representing great complexities for captive management due to the particularities of their digestive system (Caton et al. 1996). As for animals classified only as genus Callithrix spp., the following alternatives can be assumed: (1) individuals of the species C. jacchus, or some other species of the current genus, or (2) individuals classified according to the old nomenclature of Mico melanurus (formerly Callithrix argentata) (Rylands et al. 2009).
White-coated titi, P. pallescens, is an arboreal and gregarious species associated with the northern Paraguayan Chaco. It inhabits xerophytic forests as well as transitional Chaco-Chiquitano forests, and feeds mainly on fruits, although it also eats leaves and insects (Cartes et al. 2018; Weiler et al. 2019; Tomas et al. 2022). The mean weight of the species ranges between 510 and 730 grams, notably higher than the values reported in the present study, although this could be associated with the young mean age reported (Calle and Joslin 2014; Tomas et al. 2022). The genus Saimiri is widely distributed in South America, strongly associated with the Amazon basin, even reaching Central America (Thorington 1985). They weigh between 750 and 1100 grams, depending on the species, and feed on insects, fruits, flowers, and leaves (May 2013; Calle and Joslin 2014). Regardless of the species in question, the animals reported originate from illegal cross-border trafficking, matching with what is reported in the clinical records.
With regard to the report of Saguinus fuscicollis, the species’ range is far from Paraguayan territory (Buckner et al. 2015), and to the authors’ knowledge, no other individuals of this species have been reported in the country. There are no morphometric data to corroborate the coincidence with the aforementioned species, and it has not been possible to contact the person responsible for the animal, probably because it is an old clinical record. Considering these limitations, we believe that this report most likely represents a misidentification of a specimen belonging to another species.
Regarding the various digestive disorders reported in different species, in most cases a definitive diagnosis could not be made. Among the etiologies that cause digestive disorders in non-human primates, various forms of viral hepatitis are described; bacterial disorders caused by Shigella spp., Salmonella spp., Yersinia spp., Campylobacter spp., Mycobacterium spp., various parasitic infections, including those caused by Acanthocephala and Entamoebidae, and even dental caries (Verona and Pissinatti 2014; Dib et al. 2023). In captivity, the predisposition to digestive system conditions can increase mainly due to stress, confinement, and inadequate diets offered to animals (Suleman et al. 1995; Tarara et al. 1995; Suleman et al. 2000). In A. caraya, for example, the diet in the wild is based mainly on leaves from various plant families, followed by fruits and flowers (Ludwig et al. 2008), requiring high amounts of fiber, in stark contrast to what is offered to animals in captivity. Diets high in fiber are essential for maintaining the intestinal microbiota in folivorous species, promoting the development of more diverse microbial populations, which increases nutrient utilization and improves food passage through the digestive tract. This, together with greater foraging opportunities, ultimately results in greater animal welfare (Edwards and Ullrey 1999; Nijboer 2006; Kišidayová et al. 2009; Lawless et al. 2025).
With regard to respiratory conditions, although in most cases no causative agent is identified, the diagnosis of Mycobacterium tuberculosis in one animal was noted. Disease by Mycobacterium spp. has already been reported in primates of the genus Sapajus in Argentina and Brazil, highlighting the potential impact on public health associated with the fact that these species are often kept as pets (Ehlers et al. 2020; Lamattina et al. 2025; Vetter and Insfrán 2025). Other microorganisms associated with respiratory conditions in non-human primates are Klebsiella pneumoniae, Staphylococcus spp., Streptococcus spp., Pasteurella multocida, and Bordetella bronchiseptica (Verona and Pissinatti 2014), with the possible presence of K. pneumoniae in non-human primates being of particular importance, as it is a zoonotic agent capable of causing severe respiratory symptoms, leading to multisystemic disease and sepsis (Soto et al. 2012; Anzai et al. 2017; Saputro et al. 2023; Strich et al. 2025).
Among the dermatological conditions reported in non-human primates are dermatophytosis (caused by Trichophyton spp., Microsporum spp., or Epidermophyton spp.), dermatophilosis, nocardiosis (Migaki 1986), scabies (caused by Demodex spp., Sarcoptes scabiei, or Psorergates spp.; Bernstein and Didiert 2009), and leishmaniasis (Garcez et al. 2002; Voltarelli et al. 2009; Santos and de Oliveira 2020), all of which have zoonotic potential. Bacterial infections usually occur as secondary infections following injuries or fights, although under certain conditions, infections can occur from the skin’s natural microbiota, such as Staphylococcus spp. and Streptococcus spp., as well as Pseudomonas spp. (Bernstein and Didiert 2009; Oliveira and Santos 2023). Apparently, some species are natural carriers of Malassezia spp. (Neves et al. 2017; Coutinho et al. 2020). Nutritional deficiencies, allergies, and some neoplasms can also have cutaneous manifestations in primates, although there is not much information on this subject (Beniashvili 1989; Juan-Sallés et al. 2001; Bernstein and Didiert 2009; Miller 2012; Díaz-Delgado et al. 2018; Ehlers et al. 2022).
A study from Brazil cites trauma as the leading cause of death in primates, with trauma from vehicle collisions, interspecific aggression, and electrocution being the most common causes in free-living animals (Ehlers et al. 2022), matching the present report. In other studies, the casuistry varies, but trauma remains among the three main conditions affecting primates, along with infectious diseases and nutritional disorders (Varela et al. 2010; Yllescas Barrientos 2019). Gram-positive anaerobic bacillus Clostridium tetani, present in the soil, can enter the body through skin lesions caused by trauma and produce toxins that cause a condition known as tetanus, causing trismus, opisthotonos, and epileptiform seizures (Luisto 1993; Kessler et al. 2006; Springer et al. 2009; Oliveira and Santos 2023).
Although not many diagnoses accompanied by the etiological agent are mentioned, it should be noted that non-human primates can be carriers and transmitters of important zoonoses such as the rabies virus (particularly in Callithrix spp.), Alphavirus, Trypanosoma spp., Leishmania spp., Toxoplasma gondii, Plasmodium spp., as well as suffer from anthropozoonoses such as SARS-CoV-2, Herpes Simplex Virus-1, and Mycobacterium tuberculosis (Diaz et al. 2007; Estrada-Cely et al. 2011; Kotait et al. 2019; Ehlers et al. 2020; Dubey et al. 2021; Rondón et al. 2021; Diaz et al. 2024; Mendoza et al. 2024; Vetter et al. 2025). The potential impact of zoonoses and anthropozoonoses on conservation efforts, as well as on public health, must be considered.
In addition to this, debate should be generated regarding the ethical and legal questions surrounding the captive possession of non-human primates outside accredited zoological institutions. In Paraguay, the legal framework prohibits the sale and purchase of wild animals, including primates. Despite this prohibition, there is a provision that allows for the legal registration of wild animals kept in human care without the need to prove their origin beyond a sworn statement. This, combined with the ease of sale and limited oversight, has led to the normalization of domestic ownership of many species, including their display on social media. This fosters a culture of impulsive acquisition of juvenile primates, which are abandoned once they reach puberty. To date, there have been no final convictions for primate trafficking in Paraguay. The constant exposure of primates of unknown origin, with an unknown microbial load and subjected to extremely stressful conditions, combined with a lack of understanding regarding their environmental and nutritional needs, as well as their behavioral requirements, creates conditions conducive to the transmission of pathogens between humans and animals. These pathogens can cause serious illness in both humans and primates and can easily become sources of infection (Mendoza et al. 2024). As a countermeasure, various law enforcement agencies must be integrated, and they can utilize new animal welfare laws to discourage the keeping of these animals in homes. The enforcement of exemplary sentences, such as those handed down for animal abuse, combined with educational campaigns featuring real-life cases of zoonoses and anthropozoonoses, can be the first step toward reducing the impact of primate trafficking in the country.
Conclusions
The objective of this study was to report the main clinical findings regarding primates transferred to the Departamento de Recursos Faunísticos y Medio Natural at the Universidad Nacional de Asunción. The data indicate that four of the five species recorded in Paraguay are affected by illegal trafficking and unregulated private ownership, although Sapajus cay and Alouatta caraya are the most affected. Routine checkups are frequent, but various cases of health issues are also recorded, primarily trauma, digestive and respiratory conditions, and infectious diseases. It is worth noting that many medical records contain incomplete data and/or remain undiagnosed. This is the first case report on primates in Paraguay and may help identify key species for controlling illegal trafficking.
Acknowledgements
JRV thanks the SISNI program of CONACYT Paraguay for their financial support.
Declaration of Artificial Intelligence use
No artificial intelligence tools were used in the preparation of this manuscript.
Author contributions
Joerg Richard Vetter contributed to the manuscript’s conception, design, data analysis, and writing. Mauricio E. Martínez contributed to the data collection, data analysis, and writing.
Literature cited
Abreu F, De la Fuente MFC, Schiel N, and Souto A. 2016. Feeding ecology and behavioral adjustments: flexibility of a small neotropical primate (Callithrix jacchus) to survive in a semiarid environment. Mammal Research 61:221—229. https://doi.org/10.1007/s13364-016-0262-4
Anzai EK, de Souza Júnior JC, Peruchi AR, Fonseca JM, Gumpl EK, Pignatari ACC, et al. 2017. First case report of non‐human primates (Alouatta clamitans) with the hypervirulent Klebsiella pneumoniae serotype K1 strain ST 23: a possible emerging wildlife pathogen. Journal of Medical Primatology 46:337—342. https://doi.org/10.1111/jmp.12296
Beniashvili DS. 1989. An overview of the world literatura on spontaneous tumors in nonhuman primates. Journal of Medical Primatology 18:423—437. https://doi.org/10.1111/j.1600-0684.1989.tb00410.x
Bernstein JA, and Didier PJ. 2009. Nonhuman primate dermatology: a literature review. Veterinary Dermatology 20:145 ̶ 156. https://doi.org/10.1111/j.1365-3164.2009.00742.x
Bicca-Marques JC, Rumiz DI, Ludwig G, Rímoli J, Martins V, da Cunha RGT, et al. 2021. Alouatta caraya (amended version of 2020 assessment). The IUCN Red List of Threatened Species; 2021. [Accessed May 23rd, 2026]. https://dx.doi.org/10.2305/IUCN.UK.2021-1.RLTS.T41545A190414715.en
Buckner JC, Alfaro JWL, Rylands AB, and Alfaro ME. 2015. Biogeography of the marmosets and tamarins (Callitrichidae). Molecular Phylogenetics and Evolution 82:413 ̶ 425. https://doi.org/10.1016/j.ympev.2014.04.031
Calle PP, and Joslin JO. 2014. New World and Old World monkeys. In: Miller E, and Fowler M, editors. Fowler’s Zoo and Wild Animal Medicine. Vol. 8. St. Louis (USA): Elsevier; p. 301—335.
Cartes JL, del Castillo H, Kowaleski M, Thompson JJ, and Velilla M. 2017. Primates: los monos. In: Asociación Paraguaya de Mastozoología, and Secretaría del Ambiente, editors. Libro Rojo de los mamíferos del Paraguay: especies amenazadas de extinción. Asunción (PRY): Editorial CREATIO; p. 55—60.
Cartes JL, Velilla M, Valerio-Campos I, González-Brítez N, and Thompson JJ. 2018. Estado de conservación de los primates en Paraguay. In: Urbani B, Kowalewski M, Cunha RGT, de la Torre S, and Cortés-Ortiz L, editors. La primatología en Latinoamerica 2. Tomo II Costa Rica-Venezuela. Caracas (VEN): Ediciones IVIC (Instituto Venezolano de Investigaciones Científicas); p. 583—596.
Castro CSS, and Araújo A. 2007. Diet and feeding behavior of marmoset, Callithrix jacchus. Brazilian Journal of Ecology 7:14—19.
Caton JM, Hill DM, Hume ID, and Crook GA. 1996. The digestive strategy of the common marmoset, Callithrix jacchus. Comparative Biochemistry and Physiology Part A: Physiology 114:1—8. https://doi.org/10.1016/0300-9629(95)02013-6
Coutinho SDA, Sacristán C, Bueno MG, Marigo J, Pissinatti A, Kierulff MC, et al. 2020. Malassezia japonica is part of the cutaneous microbiome of free-ranging golden-headed lion tamarins (Leontopithecus chrysomelas–Kuhl, 1820). Medical Mycology 58:133—136. https://doi.org/10.1093/mmy/myz017
Cubas ZS. 1996. Special challenges of maintaining wild animals in captivity in South America. Revue Scientifique et Technique (Office International des Épizooties) ١٥:٢٦٧—٢٨٨.
Díaz-Delgado J, Sanches TC, Cirqueira CS, Coimbra ACC, Guerra JM, Olivares V, et al. 2018. Multicentric cutaneous keratoacanthomas in a free-living marmoset (Callithrix sp.). Journal of Medical Primatology 47:205–208. https://doi.org/10.1111/jmp.12341
Diaz EA, Sáenz C, Cabrera F, Rodríguez J, Carvajal M, and Barragán V. 2024. COVID‐19 in a common woolly monkey (Lagothrix lagothricha): First evidence of fatal outcome in a nonhuman primate after natural SARS‐CoV‐2 infection. American Journal of Primatology 86:e23654. https://doi.org/10.1002/ajp.23654
Díaz LA, del Pilar Díaz M, Almirón WR, and Contigiani MS. 2007. Infection by UNA virus (Alphavirus; Togaviridae) and risk factor analysis in black howler monkeys (Alouatta caraya) from Paraguay and Argentina. Transactions of the Royal Society of Tropical Medicine and Hygiene 101:1039—1041. https://doi.org/10.1016/j.trstmh.2007.04.009
Dib LV, Barbosa A, da Silva B, Pissinatti A, Moreira S, Tavares MC, et al. 2023. Gastrointestinal parasites affecting non-human primates that are kept ex situ and their handlers in different Brazilian institutions: diagnosis and analysis of risk factors. Pathogens 12:1410. https://doi.org/10.3390/pathogens12121410
Dubey JP, Murata FH, Cerqueira-Cézar CK, Kwok OC, Yang Y, and Su C. 2021. Recent epidemiologic, clinical, and genetic diversity of Toxoplasma gondii infections in non-human primates. Research in Veterinary Science 136:631—641.
Edwards MS, and Ullrey DE. 1999. Effect of dietary fiber concentration on apparent digestibility and digesta passage in non‐human primates. II. Hindgut‐and foregut‐fermenting folivores. Zoo Biology 18:537—549. https://doi.org/10.1002/(SICI)1098-2361(1999)18:6%3C537::AID-ZOO8%3E3.0.CO;2-F
Ehlers LP, Bianchi MV, Argenta FF, Lopes BC, Taunde PA, Wagner PGC, et al. 2020. Mycobacterium tuberculosis var. tuberculosis infection in two captive black capuchins (Sapajus nigritus) in Southern Brazil. Brazilian Journal of Microbiology 51:2169—2173. https://doi.org/10.1007/s42770-020-00339-5
Ehlers LP, Slaviero M, Bianchi MV, de Mello LS, De Lorenzo C, Surita LE, et al. 2022. Causes of death in neotropical primates in Rio Grande do Sul State, Southern Brazil. Journal of Medical Primatology 51:85—92. https://doi.org/10.1111/jmp.12557
Estrada A, Garber P, Rylands AB, Roos C, Fernandez-Duque E, Di Fiore A, et al. 2017. Impending extinction crisis of the world’s primates: Why primates matter. Science Advances 3:e1600946. https://doi.org/10.1126/sciadv.1600946
Estrada A, Garber P, and Chaudhary A. 2020. Current and future trends in socio-economic, demographic and governance factors affecting global primate conservation. PeerJ 8:e9816. https://doi.org/10.7717/peerj.9816
Estrada A, and Garber PA. 2022. Principal drivers and conservation solutions to the impending primate extinction crisis: Introduction to the special issue. International Journal of Primatology 43:1—14. https://doi.org/10.1007/s10764-022-00283-1
Estrada-Cely GE, and González CAE. 2008. La antropización en primates no humanos, un riesgo para su conservación. Revista CES Medicina Veterinaria y Zootecnia 3:21—29.
Estrada-Cely GE, Valencia-Aguirre S, and Vega-Lugo WO. 2011. Prevalencia de tuberculosis en primates en cautiverio en el municipio de Florencia, Caquetá. Revista CES Medicina Veterinaria y Zootecnia ٦:٦١—٧٢.
Fergnani DM, Kowalewski MM, and Fernández VA. ٢٠٢٠. Germination of native and exotic seeds dispersed by wild black-and-gold howler monkeys (Alouatta caraya): assessing deinhibition and scarification effects. Primates 61:519 ̶ 527. https://doi.org/10.1007/s10329-020-00791-9
Garcez LM, Goto H, Ramos PK, do Carmo Brigido M, Gomes PA, Souza RA, et al. 2002. Leishmania (Leishmania) amazonensis-induced cutaneous leishmaniasis in the primate Cebus apella: a model for vaccine trials. International Journal for Parasitology 32:1755—1764. https://doi.org/10.1016/S0020-7519(02)00138-8
Juan‐Sallés C, Vergés J, Valls X, Prats N, Marco A, Ruiz JM, et al. 2001. Dermatosis in talapoin monkeys (Miopithecus talapoin) with response to zinc and animal protein. Veterinary Record 149:24—25. https://doi.org/10.1136/vr.149.1.24
Kessler MJ, Berard JD, Rawlins RG, Bercovitch FB, Gerald MS, Laudenslager ML, et al. 2006. Tetanus antibody titers and duration of immunity to clinical tetanus infections in free‐ranging rhesus monkeys (Macaca mulatta). American Journal of Primatology 68:725—731. https://doi.org/10.1002/ajp.20262
Kišidayová S, Váradyová Z, Pristaš P, Piknová M, Nigutová K, Petrželková KJ, et al. 2009. Effects of high‐and low‐fiber diets on fecal fermentation and fecal microbial populations of captive chimpanzees. American Journal of Primatology 71:548—557. https://doi.org/10.1002/ajp.20687
Kotait I, Oliveira RDN, Carrieri ML, Castilho JG, Macedo CI, Pereira PMC, et al. 2019. Non‐human primates as a reservoir for rabies virus in Brazil. Zoonoses and Public Health 66:47 ̶ 59. https://doi.org/10.1111/zph.12527
Lamattina D, Martinez MF, Couto EM, Scarry C, Tujague MP, Arrabal JP, et al. 2025. Detection of Mycobacterium bovis in Free‐Ranging Sapajus nigritus, Argentina. Zoonoses and Public Health 72:95—99. https://doi.org/10.1111/zph.13189
Lawless C, Kovacs K, Mohammadi Dehcheshmeh M, Ebrahimie E, Messele YE, Snowball M, et al. 2025. Higher dietary fibre increases the faecal microbiome diversity of Golden Lion Tamarins (Leontopithecus rosalia). Animals 15:1831. https://doi.org/10.3390/ani15131831
Ludwig G, Aguiar LM, Svoboda WK, Hilst CL, Navarro IT, Vitule JR, et al. 2008. Comparison of the diet of Alouatta caraya (Primates: Atelidae) between a riparian island and mainland on the Upper Parana River, southern Brazil. Revista Brasileira de Zoologia 25:419—426. https://doi.org/10.1590/S0101-81752008000300006
Luisto M. 1993. Unusual and iatrogenic sources of tetanus. Annales Chirurgiae et Gynaecologiae 82:25—29.
MADES, Municipalidad de Asunción, PNUD, FMAM. 2021. Guías de Biodiversidad de Asunción y su área metropolitana - Mamíferos. Proyecto “Asunción Ciudad Verde de las Américas - vías a la sustentabilidad”. Asunción: PNUD.
Malukiewicz J, Boere V, De Oliveira MA, D’arc M, Ferreira JV, French J, et al. 2020. An introduction to the Callithrix genus and overview of recent advances in marmoset research. ILAR Journal 61:110—138. https://doi.org/10.1093/ilar/ilab027
May A. 2013. Feeding strategies in sympatric red howler monkeys (Alouatta seniculus), saddleback tamarins (Saguinus fuscicollis) and squirrel monkeys (Saimiri boliviensis), in the Pacaya-Samiria national reserve, Peru. The Plymouth Student Scientist 6:4 ̶ 19.
Mendoza AP, Muñoz-Maceda A, Ghersi BM, De La Puente M, Zariquiey C, Cavero N, et al. 2024. Diversity and prevalence of zoonotic infections at the animal-human interface of primate trafficking in Peru. PLoS ONE ١٩:e٠٢٨٧٨٩٣. https://doi.org/١٠.١٣٧١/journal.pone.٠٢٨٧٨٩٣
Migaki G. ١٩٨٦. Mycotic infections in nonhuman primates. In: Benirschke K, editor. Primates: The Road to Self-Sustaining Populations. New York (USA): Springer; p. 557—570. https://doi.org/10.1007/978-1-4612-4918-4_44
Miller AD. 2012. Neoplasia and proliferative disorders of nonhuman primates. In: Abee CR, Mansfield K, Tardif S, Morris T, editors. Nonhuman primates in biomedical research. St. Louis (USA): Elsevier; p. 325—356. https://doi.org/10.1016/B978-0-12-381366-4.00006-7
Milagres AP, Rímoli J, dos Santos MC, Wallace RB, Rumiz DI, Mollinedo J, and Rylands AB. 2021. Mico melanurus (amended version of 2020 assessment). The IUCN Red List of Threatened Species; 2021. [Accessed May 23rd, 2026]. https://dx.doi.org/10.2305/IUCN.UK.2021-1.RLTS.T136294A192400781.en
Neves JJ, Francelino M, Silva FG, Baptista LC, Bueno MG, Catão‐Dias JL, et al. 2017. Survey of Malassezia sp and dermatophytes in the cutaneous microbiome of free‐ranging golden‐headed lion tamarins (Leontopithecus chrysomelas‐Kuhl, 1820). Journal of Medical Primatology 46:65—69. https://doi.org/10.1111/jmp.12259
Nijboer J. 2006. Fibre intake and faeces quality in leaf-eating primates [PhD thesis]. [Utrecht (NLD)]: Utrecht University.
Nolasco CE. 2017. Estudio retrospectivo de las historias clínicas de primates atendidos en el consultorio de animales silvestres y exóticos de la Facultad de Medicina Veterinaria, Universidad Mayor de San Marcos, durante el período 2005-2014 [Undergraduate thesis]. [Lima (PER)]: Universidad Nacional Mayor de San Marcos.
Oliveira AR and Santos RL. 2023. Infectious diseases of neotropical primates. Brazilian Journal of Veterinary Pathology 16:1–34. https://doi.org/10.24070/bjvp.1983-0246.v16i1p1-34
Pastor-Nieto R. 2014. Health and welfare of howler monkeys in captivity. In: Kowalewski M, Garber P, Cortés-Ortíz L, Urbani B, Youlatos D, editors. Howler monkeys: Behavior, ecology, and conservation. New York (USA): Springer; p. 313–355. https://doi.org/10.1007/978-1-4939-1960-4_12
Rímoli J, Pinto T, Romero-Valenzuela D, Rumiz DI, Lynch Alfaro JW, and Ravetta AL. 2021. Aotus azarae (amended version of 2018 assessment). The IUCN Red List of Threatened Species; 2021. [Accessed May 23rd, 2026]. https://dx.doi.org/10.2305/IUCN.UK.2021-1.RLTS.T41539A190450485.en
Rímoli J, Smith RL, Ludwig G, Martinez M, Kowalewski M, Melo FR, and Lynch W. 2022. Sapajus cay (errata version published in 2022). The IUCN Red List of Threatened Species; 2022. [Accessed May 23rd, 2026]. https://dx.doi.org/10.2305/IUCN.UK.2022-1.RLTS.T136366A222944655.en
Rondón S, Cavallero S, Renzi E, Link A, González C, and D’Amelio S. 2021. Parasites of free-ranging and captive American primates: a systematic review. Microorganisms 9:2546. https://doi.org/10.3390/microorganisms9122546
Rumiz DI, Mollinedo J, Wallace RB, Rímoli J, and Buss G. 2021. Plecturocebus pallescens (amended version of 2020 assessment). The IUCN Red List of Threatened Species, 2021. [Accessed May 23rd, 2026]. https://dx.doi.org/10.2305/IUCN.UK.2021-1.RLTS.T41549A192452042.en
Rylands AB, Coimbra-Filho AF, and Mittermeier RA. 2009. The systematics and distributions of the marmosets (Callithrix, Callibella, Cebuella, and Mico) and callimico (Callimico)(Callitrichidae, Primates). In: Ford SM, Porter LM, Davis LC, editors. The smallest anthropoids. Boston (USA): Springer; p. 25—61. https://doi.org/10.1007/978-1-4419-0293-1_2
Santos RL, and de Oliveira AR. 2020. Leishmaniasis in non‐human primates: Clinical and pathological manifestations and potential as reservoirs. Journal of Medical Primatology 49:34—39. https://doi.org/10.1111/jmp.12441
Saputro S, Saepuloh U, Darusman HS, Putriyani W, Permanawati, Ayuningsih ED, et al. 2023. Klebsiella pneumoniae infection in cynomolgus monkeys at primate research center facility in Indonesia. Journal of Medical Primatology 52:361–368. https://doi.org/10.1111/jmp.12665
Shanee N, Mendoza AP, and Shanee S. 2017. Diagnostic overview of the illegal trade in primates and law enforcement in Peru. American Journal of Primatology 79:e22516. https://doi.org/10.1002/ajp.22516
Shanee S, Mendoza AP, Maldonado AM, Fernández-Hidalgo L, and Svensson MS. 2023. Traffic and trade in Owl Monkeys. In: Fernandez-Duque E, editor. Owl Monkeys. Developments in Primatology: Progress and Prospects. Cham (CHE): Springer; p. 673–692. https://doi.org/10.1007/978-3-031-13555-2_23
Smith RL, and Lusseau D. 2024. The Hooded Capuchin Monkey (Sapajus cay) is Vulnerable in Paraguay and at Least Near Threatened Globally According to Red List Criteria. International Journal of Primatology 45:259–281. https://doi.org/10.1007/s10764-023-00400-8
Smith RL, Rebergen K, Payne C, Megapanos E, and Lusseau D. 2022. Dietary plasticity of an understudied primate (Sapajus cay) in a biodiversity hotspot: applying ecological traits to habitat conservation in the Upper Paraná Atlantic Forest. Folia Primatologica 93:53—68. https://doi.org/10.1163/14219980-20210407
Soto E, LaMon V, Griffin M, Keirstead N, Beierschmitt A, and Palmour R. 2012. Phenotypic and genotypic characterization of Klebsiella pneumoniae isolates recovered from nonhuman primates. Journal of Wildlife Diseases 48:603–611. https://doi.org/10.7589/0090-3558-48.3.603
Springer DA, Phillippi-Falkenstein K, and Smith G. 2009. Retrospective analysis of wound characteristics and tetanus development in captive macaques. Journal of Zoo and Wildlife Medicine 40:95. https://doi.org/10.1638/2008-0055.1
Strich JR, Ramos-Benitez MJ, Warner S, Kendall H, Stein S, Platt AP, et al. 2025. Klebsiella pneumoniae induces dose-dependent shock, organ dysfunction, and coagulopathy in a nonhuman primate critical care model. mBio 16:e01943–24. https://doi.org/10.1128/mbio.01943-24
Suleman MA, Tarara RP, Else JG, and Sayer PD. 1995. Spontaneous acute gastric mucosal erosions and ulcerations in vervet monkeys (Cercopithecus aethiops). Part I. Journal of Zoo and Wildlife Medicine 26:67—71.
Suleman MA, Wango E, Farah IO, and Hau J. 2000. Adrenal cortex and stomach lesions associated with stress in wild male African green monkeys (Cercopithecus aethiops) in the post‐capture period. Journal of Medical Primatology 29:338–342. https://doi.org/10.1034/j.1600-0684.2000.290505.x
Tarara EB, Tarara RP, and Suleman MA. 1995. Stress-induced gastric ulcers in vervet monkeys (Cercopithecus aethiops): the influence of life history factors. Part II. Journal of Zoo and Wildlife Medicine 26:72—75.
Thorington Jr RW. 1985. The taxonomy and distribution of squirrel monkeys (Saimiri). In Rosenblum LA, Coe CL, editors. Handbook of squirrel monkey research. Boston (USA): Springer; p. 1—32. https://doi.org/10.1007/978-1-4757-0812-7_1
Tirira DG. 2013. Tráfico de primates nativos en el Ecuador. Boletín Técnico 11, Serie Zoológica 8-9:36—57.
Tomas WM, de Camargo Timo TP, Camilo AR, da Rosa Oliveira M, Tortato FR, Mamede S, et al. 2022. Primatas ocorrentes na Bacia do Alto Paraguai e Pantanal, Brasil. Boletim do Museu Paraense Emílio Goeldi: Ciências Naturais 17:701–724. https://doi.org/10.46357/bcnaturais.v17i3.882
van der Heide G, Dávalos VM, and Fernandez-Duque E. 2023. Flexibility in the diet and feeding ecology of nocturnal and cathemeral Aotus. In: Fernández-Duque E, editor. Owl Monkeys. Developments in Primatology: Progress and Prospects. Cham (CHE): Springer; p. ٥٣٥—٥٧٣. https://doi.org/١٠.١٠٠٧/٩٧٨-٣-٠٣١-١٣٥٥٥-٢_١٨
Varela N, Brieva C, and Galindo V. ٢٠١٠. Causas de morbilidad y mortalidad en primates de la Unidad de Rescate y Rehabilitación de Animales Silvestres (URRAS) entre ١٩٩٦ y ٢٠٠٣. In: Pereira V, Stevenson P, Bueno ML and Nassar-Montoya F, editors. Primatología en Colombia: Avances al principio del milenio. Bogotá (COL): Fundación Universitaria San Martín; p. ١٧١—١٨٩.
Verona CE, and Pissinatti A. ٢٠١٤. Primates – Primatas do Novo Mundo. In: Cubas ZS, Ramos Silva JC, Catão Dias JL, editors. Tratado de animais selvagens. ٢nd ed. Sao Paulo (BRA): Roca Ltds; p. ٧٢٣—٧٤٣.
Vetter JR, Florentín-Morel M, Riera-Domínguez MG, and Cañiza RG. ٢٠٢٥. Lethal infection by herpes simplex virus 1 (HSV-1) in a captive Azara’s owl monkey (Aotus azarae) in Paraguay. Revista Colombiana de Ciencias Pecuarias ٣٨:e٣٨٣٥. https://doi.org/10.17533/udea.rccp.38n3a5
Vetter Hiebert JR, and Insfrán Segovia ML. 2025. Reporte retrospectivo de casuística en un consultorio de animales silvestres y exóticos en Paraguay. Revista de Investigaciones Veterinarias del Perú 36:e29637. https://doi.org/10.15381/rivep.v36i4.29637
Voltarelli EM, Arraes SM, Lonardoni MV, Teodoro U, and Silveira TG. 2009. Serological survey for Leishmania sp. infection in wild animals from the municipality of Maringá, Paraná state, Brazil. Journal of Venomous Animals and Toxins Including Tropical Diseases 15:732 ̶ 744. https://doi.org/10.1590/S1678-91992009000400011
Weiler A, Núñez K, Peris S, Silla F, Airaldi K, González de Weston G, et al. 2019. Guía para la identificación de mamíferos medianos y grandes del Chaco Seco. San Lorenzo (PRY): Facultad de Ciencias Exactas y Naturales, Universidad Nacional de Asunción.
Yllescas Barrientos MG. 2019. Causas de morbilidad y mortalidad en primates neotropicales de un centro de conservación entre los años 2008 y 2018. [Undergraduate thesis]. [Lima (PER)]: Universidad Alas Peruanas.
Associated editor: Luz Irene Loría
Submitted: January 27, 2025; Reviewed: May 18, 2026
Accepted: July 8, 2026; Published on line: August 14, 2026.
THERYA, 2026, Vol. 17(3):XXX-XXX
DOI: 10.12933/therya.2026.6280 ISSN 2007-3364
Table 1. The number of individuals per primate species registered in clinical files.
|
Taxon |
Number |
|
Sapajus cay |
146 |
|
Alouatta caraya |
93 |
|
Aotus azarae |
31 |
|
Callithrix jacchus |
8 |
|
Callithrix spp. |
4 |
|
Plecturocebus pallescens |
4 |
|
Saimiri spp. |
3 |
|
Saguinus fuscicollis |
1 |
|
No Data |
2 |
|
Total |
292 |
Figure 1. Individuals of Sapajus cay affected by electrocution (A), tetanus (B), and dermatologic affection (C).
Table 2. Most frequent causes of consultation for the main species transferred to the FCV-UNA from 2004 – 2025.
|
S. cay (n=146) |
A. caraya (n=93) |
A. azarae (n=31) |
|
|
Routine check-up |
37 (25.3%) |
21 (22%) |
6 (19.4%) |
|
Dermatological |
16 (11%) |
6 (6.5%) |
0 |
|
Digestive |
13 (8.9%) |
28 (30.1%) |
1 (3.2%) |
|
Respiratory |
13 (8.9%) |
5 (5.4%) |
9 (29%) |
|
Trauma |
25 (17.1%) |
17 (18.3%) |
7 (22.6%) |
|
Infectious |
19 (13%) |
3 (3.2%) |
4 (12.9%) |
|
Undefined |
18 (12.3%) |
6 (6.5%) |
2 (6.5%) |
Figure 2. Individual of Aotus azarae positive to HSV-1 presenting a characteristic palpebral ulcer.