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Kerodon

Kerodon is a of in the family , consisting of two species of rock cavies endemic to the semi-arid and seasonally dry tropical . These medium-sized, tailless herbivores are adapted for life in rocky outcrops, where their agile climbing abilities allow them to navigate steep terrains and forage in trees and shrubs. Related to guinea pigs () and capybaras (), Kerodon species exhibit crepuscular behavior, social hierarchies, and a diet primarily composed of leaves, buds, flowers, and bark. The genus includes Kerodon rupestris, the rock cavy or mocó, which inhabits the biome in northeastern , particularly in arid, rocky areas with granitic boulders and low annual rainfall of 400-1000 mm. This species features a grayish coat with white or black mottling, a white throat, yellowish-white belly, and padded feet with blunt nails suited for gripping slick rocks; adults measure 200-400 mm in length and weigh around 1000 g. They live in social groups, communicate via chirps, squeaks, and whistles, and reproduce year-round with litters of 1-3 precocial young after a 76-day . Kerodon rupestris is classified as Least Concern by conservation assessments, though it benefits from protected areas in its range. The second species, Kerodon acrobata (acrobatic cavy), was described in and is endemic to the domain in central , from to states, favoring rocky outcrops in open, dry tropical forests. Larger than its congener, it averages 384 mm in head-body length, 72 mm hindfoot, and 1 kg in weight, with adaptations for climbing similar to K. rupestris. Limited data exist on its behavior and , but it emerges to in trees and is considered endemic and specialized to mesic environments. Both species highlight the of Brazil's dry biomes, with ongoing revealing their roles in local ecosystems despite sparse historical records.

Taxonomy and Phylogeny

Genus Overview

Kerodon is a of South American in the Caviidae, first described by French zoologist Frédéric Cuvier in 1825 based on specimens from . There are two extant in the . Historically, Kerodon was classified within the subfamily Caviinae alongside guinea pigs ( Cavia), but molecular analyses prompted its reclassification to the subfamily Hydrochoerinae, which also includes the capybaras ( Hydrochoerus), in 2002. This shift was based on genetic data demonstrating a closer relationship between Kerodon and Hydrochoerus than to Cavia. Phylogenetically, Kerodon belongs to the and diverged from other caviids during the late Middle , approximately 11–13 million years ago, as estimated from molecular evidence including cytochrome b and 12S rRNA genes. This positioning highlights its evolutionary ties to larger, semi-aquatic like capybaras within the Cavioidea superfamily. The fossil record of Kerodon extends to the in , with remains recovered from cave deposits in regions such as , indicating its long-standing presence in South American ecosystems. These fossils, including skeletal elements of K. rupestris, suggest continuity with modern populations in semi-arid environments.

Species

The genus Kerodon includes two recognized : K. rupestris, the and (also known as mocó), and K. acrobata, the acrobatic cavy or climbing cavy. These are distinguished primarily by morphological traits adapted to their respective habitats, with K. rupestris favoring rocky outcrops in semiarid regions and K. acrobata exhibiting greater arboreal tendencies in dry forest enclaves. Kerodon rupestris was described by Maximilian zu Wied-Neuwied in 1820 based on specimens from , , making it the of the . Adults typically measure 200–400 mm in head-body length and weigh 600–1000 g, with a robust build suited to navigating rugged terrain. The species is native to northeastern , particularly in the , and was introduced to the island of during the 20th century, where it has established populations. Kerodon acrobata was described in 1997 by João Moojen, Marilena Locks, and Alfredo Langguth from specimens collected in , . Larger than its congener, it averages 384 mm in head-body length and 1 kg in weight, and is endemic to the northeastern Cerrado domain in and states. This species is noted for its enhanced climbing ability, attributed to proportionally longer limbs that facilitate vertical movement on trees and rocky faces. Diagnostic differences between the species include body proportions and skeletal features: K. rupestris possesses a more robust build with shorter, sturdier limbs optimized for leaping and maneuvering on horizontal rocky surfaces, while K. acrobata has elongated limbs and stronger, more curved claws enabling greater agility in climbing and foraging in arboreal environments. Both species share a diploid chromosome number of 2n=52, but differ in karyotype details such as the number of acrocentric versus metacentric chromosome pairs and patterns of heterochromatin distribution. Regarding synonymy and nomenclature, K. rupestris has no major synonyms beyond early combinations like Kerodon moco; it remains the valid name for the type species. K. acrobata was initially considered a potential subspecies of K. rupestris due to morphological similarities but was elevated to full status based on distinct cranial measurements, limb proportions, and genetic markers, including subtle karyotypic variations.

Physical Description

Morphology

Kerodon species are hystricomorph rodents characterized by a rabbit-like elongated body, with an average head-body length of approximately 300 mm. The tail is vestigial and short, typically less than 20 mm in length or absent. Adults exhibit a squirrel-like head profile with rounded ears measuring 30–35 mm. Average adult weight ranges from 600 to 1000 g across the genus. The fur is coarse and features an agouti pattern, typically grayish-yellow or grayish-orange, spattered with white and black hairs; the throat is whitish, the dorsum grayish, and the ventral side yellowish-brown. Sexual dimorphism is minimal, with sexes alike in overall appearance and males only slightly larger on average. Limbs are robust, with strong hindlimbs and padded soles on hands and feet providing grip; all digits bear blunted nails except for a small grooming claw on the hind foot. The dental formula is 1/1:0/0:1/1:3/3 = 20, featuring a longer rostrum and greater incisor-to-premolar diastema than other caviids; the ever-growing molars are adapted for grinding vegetation. Sensory organs include large eyes with an axial diameter of about 10.7 mm and a vertical slit pupil, suited for low-light conditions, along with prominent vibrissae for navigation in confined spaces.

Adaptations

Kerodon species exhibit specialized locomotor adaptations suited to their rocky, arid habitats, enabling efficient navigation of boulder fields and inselbergs. Powerful hind legs facilitate a hopping gait and bipedal leaps between boulders, while padded feet with blunt nails provide traction on slick rock surfaces, enhancing climbing agility. These traits allow individuals to traverse vertical terrain rapidly, evading predators and accessing resources in fragmented landscapes. In Kerodon acrobata, morphological features support more pronounced arboreal tendencies compared to K. rupestris, reflecting adaptations to dry forest patches with climbing opportunities. Physiological adaptations in Kerodon promote survival in semi-arid conditions with limited . The kidneys feature a complex vascularization pattern, supporting renal function in water-scarce environments, while composition in lactating females—high in total solids (20%) with varying and protein levels—minimizes water loss to offspring. Crepuscular activity is facilitated by eye structures including a vertical slit (3.6 mm × 2.38 mm) that enhances in low-illumination dawn and periods, alongside a rod-dominated for . Heat tolerance is achieved through behavioral , with individuals active across 23–45 °C but seeking rocky shelters or vegetation shade during peak heat to avoid overheating, and occasionally basking on sun-exposed rocks. Dental and digestive systems are optimized for processing tough, fibrous vegetation prevalent in arid regions. The dentition consists of 20 hypsodont teeth, which continuously grow to cope with abrasive plant material like bark and leaves. A well-developed caecum, lined with mucous glands and Lieberkühn crypts, enables fermentation, allowing efficient breakdown of cellulose-rich foods such as cacti and bromeliads into usable nutrients. Sensory enhancements aid predator detection and social interactions in challenging environments. Acute hearing supports the use of vocalizations, including piercing alarm whistles that signal threats and elicit escape responses across rocky terrains. Olfactory capabilities are bolstered by , which facilitate territorial marking and social communication, as evidenced in transmission dynamics of associated parasites.

Distribution and Habitat

Geographic Range

The genus Kerodon is endemic to , with both recognized species exhibiting restricted and fragmented distributions tied to specific biomes in the country's eastern and central regions. Kerodon rupestris inhabits the semiarid biome of northeastern , where it is associated with extensive rocky outcrops that fragment its range into isolated populations. This species occurs across several states, including , , , , , and northern , typically at elevations from approximately 200 to 600 meters. In contrast, Kerodon acrobata is confined to the in central , favoring seasonally dry patches and open areas within this domain. Its known distribution centers on the states of and , with records from northeastern portions of the , including localities near the Serra Geral de . Beyond its native range, K. rupestris has established introduced populations on the archipelago off 's northeastern coast, where it persists as a species following human-mediated translocation. records of Kerodon are limited but indicate the genus' presence in during the , consistent with its current eastern .

Habitat Preferences

Kerodon species exhibit a strong preference for semi-arid biomes characterized by rocky outcrops, including the for K. rupestris and dry forest enclaves within the for K. acrobata. These rodents are specialized rock-dwellers, favoring boulder-strewn slopes, inselbergs, and or hills that provide crevices and rifts for shelter. In the , K. rupestris occupies granitic boulder outcroppings amid thorny scrub vegetation, avoiding open grasslands and selecting sites with natural wind protection from elevated rock formations. Similarly, K. acrobata is associated with discontinuous-canopy dry forests on outcrops in the northeastern , where rocky features integrate with cerrado sensu stricto vegetation for cover. Microhabitats consist of fissures and hollows within these rock structures, where individuals seek refuge from predators and ; burrows are often excavated under boulders or within crevices, supplemented by thorny scrub for additional concealment. Soil conditions are typically shallow and rocky, comprising lithosols and regosols with low content, which limit vegetation to drought-resistant species and reinforce the reliance on lithic substrates. These features support a saxicolous lifestyle, with rock piles serving as persistent refugia during dry periods. Abiotic conditions include annual rainfall of 300–800 mm in the semi-arid portions of both biomes, with pronounced dry seasons and erratic patterns that shape suitability. Temperatures typically range from 20–35°C, though peaks can exceed 40°C, prompting use of shaded crevices for . The dependence on isolated formations exposes populations to fragmentation from loss, resulting in disjointed distributions where between sites is limited by surrounding unsuitable .

Behavior

Social Structure

Kerodon populations live in colonies typically comprising 5–20 individuals, including 1–3 adult males, multiple adult females, and juveniles, organized in a polygynous system where the dominant male maintains a of females. This structure facilitates resource sharing within rock outcrop habitats while promoting for the dominant male. Male hierarchies are linear and established through aggressive interactions, such as chasing and biting, which determine access to females and resources. In contrast, females form stable matrilineal kin groups characterized by lower levels of conflict, though dominance relationships still influence feeding and resting priorities. Groups exhibit strong territoriality, defending rock piles ranging from 0.5 to 2 hectares against intruders; adult males and females contribute to collective defense through aggressive interactions, particularly of juveniles. Data on the of K. acrobata remain limited. Interspecific differences are notable, with K. rupestris forming larger and more stable groups adapted to semi-arid rock formations.

Activity Patterns and Communication

Kerodon species, particularly K. rupestris, exhibit primarily diurnal activity patterns based on recent studies, with approximately 81% of observed activity occurring between 06:00 and 18:00 hours, though earlier observations describe crepuscular peaks and . This rhythm aligns with their reliance on rocky outcrops for during hotter midday periods, though activity may extend into crepuscular periods and for and vigilance in cooler conditions. Locomotion in Kerodon is adapted to rugged, rocky terrains, featuring agile quadrupedal gaits in open areas and bipedal bounding or hopping on steep rock faces, where the hind limbs propel the body while the forelimbs aid in balance and grasping. This bipedal mode utilizes the vestigial tail for minor stabilization during jumps between boulders, enabling efficient navigation over distances typically within stable home ranges averaging 0.28–0.35 hectares for females and males, respectively, though daily movements often span 200–500 meters during excursions. Such patterns support energy-efficient traversal in resource-scarce environments, with individuals covering ground in short bursts to minimize exposure. Communication in Kerodon relies on a repertoire, including vocal, tactile, and postural signals for coordination within small groups. The vocal repertoire encompasses whistles, which vary in acoustic structure to convey urgency: slow whistles (longer duration, higher pitch in some contexts) for distant or low-urgency threats like humans, dogs, or , and fast whistles (shorter pulse intervals, lower pitch) exclusively for proximate high-urgency dangers such as nearby ocelots. Additional calls include snort-like vocalizations for agonistic interactions, snorts signaling submission, whines during (often by juveniles), and screams in response to , with whistles comprising over 73% of recorded emissions in disturbed habitats. Tactile interactions, such as mutual grooming and huddling, reinforce bonds and , particularly among closely associated individuals in rock pile colonies. Visual signals involve postural displays, like upright stances on hind legs for vigilance or alert postures (body tilted at 90° with head forward) during threats, facilitating rapid group coordination without reliance on prominent movements due to the vestigial . Antipredator behavior in Kerodon integrates vocal signaling with use and group responses to mitigate risks from aerial predators like hawks and ground threats such as foxes or ocelots. Individuals emit modulated alarm whistles to alert conspecifics, with call rates and frequencies increasing in anthropogenically disturbed areas (e.g., 2.6 calls/hour versus 1.6 in undisturbed sites), indicating heightened emotional to novel threats like feral dogs. For aerial predators, a freeze response—immobilizing on rocks to blend with the —reduces detection, while ground predator encounters prompt group through collective whistling and postural displays to deter approach. Reliance on rock crevices for rapid evasion further enhances survival, as this vocal plasticity functions as an adaptive strategy tailored to predator proximity and type.

Ecology

Diet and Foraging

Kerodon species are primarily folivorous herbivores, with leaves constituting the bulk of their , supplemented by buds, flowers, fruits, , branches, and sprouts from a variety of native plants. In Kerodon rupestris, the rock cavy endemic to the Brazilian , the includes at least 23 plant , dominated by leaves of Bauhinia cheilantha and fallen flowers of Cenostigma pyramidale, reflecting a specialized trophic niche with low breadth. Food selection in K. rupestris is influenced by leaf nutrient content, particularly , calcium, and , which correlate positively with consumption rates, allowing the species to modify its in response to variations in plant abundance and quality. For Kerodon acrobata, the acrobatic cavy found in the domain, the diet is more , encompassing leaves from at least 16 native plant families along with flowers, fruits, branches, and bark. Seasonal shifts occur, with greater reliance on litterfall such as flowers of Handroanthus serratifolius (comprising up to 44% of feeding records) during the , when the trophic niche narrows due to reduced resource availability. Both exhibit dietary plasticity to cope with the resource-poor, semiarid environments, opportunistically exploiting available vegetation without expanding behavioral repertoires beyond ground-level and low-arboreal foraging. Foraging strategies in Kerodon emphasize to rocky, xeric habitats, where individuals scan from elevated rock outcrops before descending to feed on ground litter or climbing low vegetation for accessible parts. Group occurs in social units, potentially reducing predation risk through collective vigilance, though specific roles remain undocumented. Daily intake supports maintenance in arid conditions, estimated to approach 10% of body weight based on observed consumption patterns in folivorous caviids, prioritizing nitrogen-rich foliage to optimize energy gain. Nutritional adaptations include coprophagy, a that aids in re-ingesting to recycle vitamins and minerals from fibrous matter. Interspecific differences highlight ecological divergence: K. rupestris functions primarily as a terrestrial grazer, focusing on ground-level leaves and bark in open scrub, while K. acrobata incorporates more arboreal elements, such as climbing for higher branches in dry forest patches, broadening its resource acquisition in patchy habitats.

Reproduction and Life History

Kerodon rupestris exhibits a polygynous characterized by formation, where dominant males maintain access to multiple females within groups. Breeding occurs year-round, though conceptions and births peak during the rainy season from to in their native habitat, aligning with increased resource availability. The period lasts approximately 76 days, longer than in most other caviids, reflecting adaptations to their specialized rock-dwelling lifestyle. Females typically produce 1-3 precocial young per , with singletons being the most common; eyes are open and young are mobile at birth, enabling immediate evasion of threats. Females can have 1-3 annually due to postpartum estrus, maintaining a 1:1 across litters. involves communal nursing within colonies, where both males and females contribute through grooming, huddling, and protection, though lone females provide more direct physical contact to accelerate offspring weight gain. occurs around 33-35 days, after which young begin independently by day 2 postpartum. [Sexual maturity](/page/Sexual maturity) is reached at 4-6 months, averaging 133 days. In the wild, lifespan averages 4-6 years, with high juvenile mortality primarily from predation by raptors and carnivores, though female in groups also contributes. In captivity, individuals can live up to 11 years, with 91% surviving to at least 3 years. Post-weaning growth is rapid, supporting early independence in harsh, arid environments. Reproductive biology for K. acrobata remains poorly documented.

Conservation

Status and Threats

Kerodon rupestris, the rock cavy, is classified as Least Concern on the due to its wide distribution and stable populations across its range in the . In contrast, Kerodon acrobata, the acrobatic cavy, is listed as , reflecting limited data on its population size, which is unknown, and its . The primary anthropogenic threats to both species include habitat loss driven by and activities in the , where natural vegetation has experienced an approximately 11% reduction from 1985 to 2019. Hunting for and the pet trade further pressures populations, particularly in rural areas where local communities rely on these as a protein source. On the island of , where K. rupestris occurs, introduced predators such as feral cats pose a significant risk through direct predation and competition for resources. Natural threats exacerbate these issues, with recurrent drought cycles in the semi-arid reducing available forage and water, leading to periodic population fluctuations. into isolated inselbergs promotes and potential genetic bottlenecks in some K. rupestris populations. Population trends indicate stability for K. rupestris overall, though fragmentation limits connectivity and resilience in smaller subpopulations. For K. acrobata, trends are unknown due to its limited geographic range restricted to dry forest patches in the domain, compounded by ongoing habitat degradation. As of 2025, no updates to IUCN statuses have been made, with further research recommended particularly for K. acrobata.

Protection Efforts

Kerodon species benefit from occurrence within several protected areas across , providing essential refuges amid ongoing habitat pressures. For instance, Kerodon rupestris is documented in Serra da Capivara National Park in state, a that safeguards ecosystems and supports populations through measures and preservation. Similarly, Kerodon acrobata inhabits regions including in , where conservation units protect dry forest patches critical to its survival. These reserves, numbering numerous across the species' ranges, collectively cover portions of their distributions, though exact percentages vary by ongoing assessments. Research and monitoring efforts have intensified since 2010 to address knowledge gaps, particularly for the less-studied K. acrobata. Genetic and morphological analyses by Bezerra et al. examined specimens from dry forest enclaves, revealing specificity and recommending a Vulnerable classification due to restricted range and fragmentation risks, despite its current IUCN status. For K. rupestris, surveys in sites have tracked activity patterns and relative abundances, informing population viability amid pressures, with densities estimated around 12 individuals per hectare in surveyed semiarid areas. Management actions target both native and introduced populations to mitigate threats. In the , initiatives promote sustainable use and hunting reduction through local engagement, recognizing K. rupestris as a traditional food source while aiming to prevent . On Archipelago, where K. rupestris was introduced and now impacts native biodiversity as an , control programs evaluate removal strategies, including simulations of harvest efforts to assess population reduction feasibility without full eradication. Experimental reintroduction trials on degraded habitats have been proposed for K. rupestris to restore local populations, though implementation remains limited. Future conservation priorities emphasize enhanced monitoring for K. acrobata to refine its status beyond , including expanded genetic surveys and density estimates via non-invasive methods like camera traps. Proposals for habitat corridors linking fragmented and reserves aim to boost , potentially stabilizing populations by connecting isolated inselbergs.

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