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Overview
Brief Summary
Biology
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Comprehensive Description
Description
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Distribution
Range Description
Baumgarten and Williamson (2007) provide the most recent review of the limits of the distributions of Alouatta palliata and A. pigra in Central America and Mexico. They found that the highland massif of northern Central America (including the Sierra Madre de Chiapas and central highland of Guatemala) and its associated coniferous and subalpine vegetation forms a geographic barrier separating A. pigra from A. palliata, and defines the southern limit of A. pigra. They discussed the two contact zones between them: the broad range of overlap north of the highland massif in Mexico over the lowlands of the states of Tabasco and Campeche, and a narrow area of contiguous, non-overlapping ranges in eastern Guatemala where the highlands extend almost the Caribbean. In the first, the localities where parapatry has been observed include Macuspana, Tabasco (Smith 1970; Horwich and Johnson 1986), around Zapata, Tabasco (Horwich and Johnson 1986) and the northern point of the Laguna de Términos in Campeche (Serio-Silva et al. 2006). There is no geographical barrier separating the species, both occur in the same forests and on both sides of the Rio Usamacinta, for example (Cortés-Ortiz et al. 2003). In the second, the ranges are narrowly parapatric, separated by the Río Dulce and the Lago Izabal: A. palliata to the south and A. pigra to the north and west. South-west of Lake Izabal, A. pigra occurs in the highlands of the Sierra de las Minas, but not in the lowlands, occupied by A. palliata. Any past range overlap in this region will have been lost by the extensive oss of forest; the area is heavily farmed. Baumgarten (2006) found no evidence to support sympatry supposed previously by Horwich and Johnson (1986), Curdts (1993) and Silva-López et al. (1998).
Serio-Silva et al. (2006) reported on a detailed survey of the occurrence of A. pigra in the Yucatán Peninsula.
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Geographic Range
Alouatta pigra is found in Belize, northern Guatemala, and southeastern Mexico ("Belize Zoo", 2007; Gonzalez-Kirchner, 1998). They are endemic to the largest tropical rain forest region of Mesoamerica, Selva Maya, which encompasses over 4 million hectares of land in these three countries (Estrada et al., 2004). They are the only howler monkey species on the Yucatan peninsula, and are found in a reduced area of the Yucatan (Estrada et al., 2004; Gonzalez-Kirchner, 1998). They inhabit the Mexican states of Campeche, Quintana Roo, and Chiapas (Estrada et al., 2004). Populations have been found and heavily studied at the Mayan sites of Calakmul and Yaxchilán, Mexico, and Tikal National Park, Guatemala (Estrada et al., 2004). They are widespread throughout Belize.
Biogeographic Regions: neotropical (Native )
- 2007. "Belize Zoo" (On-line). Black Howler Monkey: Alouatta pigra. Accessed May 03, 2007 at http://www.belizezoo.org/zoo/zoo/mammals/how/how1.html.
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Range
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Physical Description
Morphology
Physical Description
Alouatta pigra is one of the largest monkeys in the Americas. It averages 70 cm long, excluding the tail, which is slightly longer than its body length ("Belize Zoo", 2007). It is the largest and most sexually dimorphic of the howler monkeys, with an average weight of 11.4 kg for males and 6.4 kg for females (Fleagle, 1999). They are characteristically covered by black hair, which is a bit longer near the throat, and they have white genitalia (Treves, Drescher, & Snowdon, 2003). Males have a pink scrotum, which distinguishes Alouatta pigra from Alouatta palliata (Horwich, 1983a). Young retain pale fur until 9 to 10 weeks of age (Treves, Drescher, & Snowdon, 2003). Like other members of Atelidae, A. pigra has a prehensile tail with gripping pads (Fleagle, 1999).
Average mass: 6.4 - 11.4 kg.
Average length: 70 cm.
Other Physical Features: endothermic ; homoiothermic; bilateral symmetry
Sexual Dimorphism: male larger
- Fleagle, J. 1999. Primate Adaptation and Evolution. London: Elsevier Academic Press.
- Horwich, R. 1983. Species Status of the Black Howler Monkey, Alouatta pigra, of Belize. Primates, 24: 288-289.
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Ecology
Habitat
Habitat and Ecology
The howler monkeys are the large leaf-eaters of the South American primate communities. The molar teeth are particularly adapted for their chewing leaves through shearing. They spend up to 70% of their day lying and sitting about quietly among the branches, fermenting leaves in their enlarged caecums. Like the spider monkeys, they are prehensile-tailed, with a naked patch of skin on the under surface at the tip. Their most characteristic feature is the deep jaws which surround the enlarged larynx and hyoid apparatus, a resonating chamber. It is with this enlarged and highly specialized voice box that they produce their howls (grunts, roars and barks). Howling sessions, usually involving the entire group, can be heard particularly in the early morning and are audible at distances of 1-2 kms (Drubbel and Gautier 1993).
Howlers are the only New World primates which regularly include mature leaves in their diet, although softer, less fibrous, young leaves are preferred when they are available. Their folivory and ability to eat mature leaves is undoubtedly one of the keys to their wide distribution and the wide variety of vegetation types they inhabit. Mature fruit is the other important food item, especially wild figs (Ficus) in many regions, but they also eat leaf petioles, buds, flowers (sometimes seasonally very important), seeds, moss, stems and twigs, and termitaria. Silver et al. (1998, 2000) have studied the diet and feeding ecology of A. pigra in Belize.
Alouatta pigra lives in smaller groups than A. palliata: 2-10 individuals per group compared with 2-45 for A. palliata (mean of 12.3) (Crockett and Eisenberg 1986; Chapman and Balcomb 1998; Pavelka and Chapman 2006). Estrada et al. (2004) recorded a mean group size of 7.5±1.9 individuals (range 4-9, n=8) at Calakmul, Campeche; 6.6±2.1 individuals (range 4-10, n=8) at Yaxchilán, Chiapas; and 8.7±2.2 individuals (range 6-12, n=10) at Tikal, Guatemala. Unlike the spider monkeys, and related to the large proportion of leaves in the diet (up to 50% of the annual diet), the howler monkeys generally have quite small and broadly overlapping home ranges, of 5 ha up to 45 ha, depending on the type of habitat (Neville et al. 1988).
Infant Alouatta are probably born throughout the year in Suriname, but data are not yet sufficient to determine if there is a birth peak. In Suriname, newborn infants have been seen in March, April, and November, and January (Mittermeier 1977). Crockett and Rudran (1987a,b) examined seasonal variation in births in red howlers from northern Venezuela, and found that they were less frequent during the early wet season (weaning would occur at the time of greatest food shortage). The llanos forests are more seasonal, however, than in the Guianas, and it is possible that this is not the case elsewhere. Oestrus lasts 2-4 days, with intervals between oestrous periods of about 17 days. Interbirth intervals are generally about 16.6 months, although they may be shortened by the death of an infant to about 10.5 months (Crockett and Sekulic 1984).
Size:
Adult male weight 11.1-11.6 kg (mean 11.35 kg, n=2), adult female weight 6.3-6.6 kg (mean 6.4 kg, n=4) (Ford and Davis 1992)
Adult male weight 11.4 kg (n=2) (Peres 1994)
Adult female weight 6.43 kg (n=4) (Peres 1994).
Systems
- Terrestrial
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Habitat
The habitat of Alouatta pigra is varied, but is typically tropical forests. They are known from lowland, deciduous, semi-deciduous forests, and evergreen forests (Belize Zoo, 2007; Gonzalez-Kirchner, 1998). They are known from pristine tropical rainforest to riverine forests, and can be normally found at low elevations in riparian forests of less than 400 m, although black howlers have been found at elevations higher than 500 m (Estrada et al., 2004). In riverine habitats they usually avoid riverbank areas and inhabit inland areas (Estrada et al., 2004). They prefer larger trees and usually inhabit the middle to upper canopy (Gonzalez-Kirchner, 1998). Although they have a wide habitat range, A. pigra has lower rates of success in areas disturbed by humans (Gonzalez-Kirchner, 1998).
Average elevation: 400 m.
Habitat Regions: tropical ; terrestrial
Terrestrial Biomes: rainforest
Other Habitat Features: riparian
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Habitat
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Trophic Strategy
Food Habits
Mexican black howler monkey diet is varied. They are strict herbivores, consuming many plant parts, including flowers, fruits, and leaves ("Belize Zoo", 2007). All Alouatta species are highly folivorous. Alouatta pigra is one of the more frugivorous species in this genus. Their preferred food is fruit and they usually eat leaves only in conditions where frugivory is unfavorable (Behie & Pavelka, 2005). This allows them to have a flexible, adaptable diet that can adjust in cases of habitat change. Generally, a little more than 36% of their diet consists of fruits, followed by about 30% mature leaves, 25% new leaves and buds, and 5% flowers (Behie & Pavelka, 2005). Although they consume a significant amount of leaves, Alouatta pigra has a primitive digestive tract more suitable for frugivory; breaking down leaves therefore requires a longer digestion time, which explains the long inactive periods in their activity budget (Kitchen, Horwich, & James, 2004).
Plant Foods: leaves; fruit; flowers
Primary Diet: herbivore (Folivore , Frugivore )
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Associations
Ecosystem Roles
Mexican black howler monkeys are often found living in close conjunction with Ateles geoffroyi and other spider monkeys (Estrada et al., 2004). They are also important for the role they play in seed dispersal (Van Bell, 2006). Their frugivorous diet has helped disperse the seeds of some rainforest plants. Although they do not shy away from human contact and their presence is quite obvious due to their howling, Mexican black howler monkeys rarely interfere with human crops.
Ecosystem Impact: disperses seeds
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Predation
Mexican black howler monkeys can howl to frighten away predators or alert others of a predator's presence. Mothers aggressively protect their young for a year against predators and other dangers (Kitchen, Horwich, & James, 2004). The greatest predatory threat to young black howlers is infanticide by adult males. Otherwise, there are few natural predators for Mexican black howler monkeys. Occasionally they are preyed upon by jaguars, pumas, and harpy eagles (Knopff & Pavelka, 2006). Other cats, large birds of prey, and large arboreal snakes are also potential predators (Treves, Drescher, & Snowdon, 2003). Humans have been known to illegally catch individuals for pets, and they are occasionally eaten by humans (Kitchen, Horwich, & James, 2004).
Known Predators:
- jaguars (Panthera onca)
- pumas (Puma concolor)
- harpy eagles (Harpia harpyja)
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Life History and Behavior
Behavior
Communication and Perception
Mexican black howler monkeys announce and defend group territories through howling vocalizations ("Belize Zoo", 2007). They are highly social animals Adult howlers are less social, while infant and adolescent howlers engage in most of the social interactions (Behie & Pavelka, 2005). Adults in a group will often howl when approached by one or a few solitary males who may be trying to take over the alpha spot in the troop (Kitchen, Horwich, & James, 2004). Other threats include these solitary males trying to commit infanticide and thus lowering the reproductive success of the current alpha male (Kitchen, Horwich, & James, 2004). Howling can last for over an hour and is low frequency and loud: about 88 decibels at a 5 m distance (Kitchen, Horwich, & James, 2004). The energy used in howling is still less, and the risk smaller, than in physical confrontation. When more than one male is present howling occurs in staggered rounds and, as a result, howling can be used to indicate the number of males present (Kitchen, Horwich, & James, 2004). This information is useful to a group in deciding whether or not to approach another group and initiate a physical confrontation (Kitchen, Horwich, & James, 2004). The howls of females are aurally different from those of males, but they also participate in group howling.
Communication Channels: visual ; tactile ; acoustic ; chemical
Other Communication Modes: choruses
Perception Channels: visual ; acoustic
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Life Expectancy
Lifespan/Longevity
The average lifespan of Mexican black howler monkeys is 20 years ("Primate Info Net", 2004).
Average lifespan
Status: wild: 20 years.
- 2004. "Primate Info Net" (On-line). The Life Spans of Nonhuman Primates. Accessed May 08, 2007 at http://pin.primate.wisc.edu/aboutp/phys/lifespan.html.
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Lifespan, longevity, and ageing
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Reproduction
Reproduction
Generally, only the dominant males or other males with high social status in the troop will copulate with females. The alpha male copulates more frequently and with more females at the peak of their cycle, which lasts two to four days (Van Bell, 2006). As a result of the social standing necessary to have the privilege of mating, males often mate later in life than females (Van Bell, 2006). Females seem to have reproductive success at a younger age, and, regardless of social position, copulate multiple times per cycle (Van Bell, 2006).
Van Bell’s (2006) description of the mating behavior of Alouatta pigra begins with the male sniffing the urine of the female and licking the female genitalia to detect her stage in the estrus cycle. To demonstrate interest, both the male and the female flick their tongue in and out of their mouth. Observational studies also show that females may incite mating by grabbing the hairs on a male' face. During the mating period, the pair mutually stay together for a few days and perform multiple copulations. The male usually mounts the female, holding on to her shoulders with his hands, and sometimes will use his feet to grasp as well. Generally, copulation lasts 30 seconds to one minute (Horwich, 1983b).
Mating System: polygynous
Sexual maturity is reached at the age of four years old ("Belize Zoo", 2007). However, males from 3 to 4 months of age already have a pale pink pigmented scrotum with descended testes (Horwich, 1983a). Researchers have been unable to detect any visual indications of the female estrus cycle in Alouatta, and there has not been much research on reproductive behavior and biology in general. Most research on reproduction is based on hormones collected from fecal matter in conjunction with information about the ages of individuals from which the fecal samples were collected (Van Bell, 2006). The female estrus cycle lasts from 11 to 24 days, peak time for conception lasts 2 to 4 days (Van Bell, 2006).
Mexican black howler monkeys do not exhibit seasonality in reproduction, possibly because their diet of leaves and unripe fruits is not seasonal in availability (Crockett & Rudran, 1987). There are slightly fewer births when new leaves and fruits emerge (Van Bell, 2006). Pregnancy lasts about 180 days. Offspring of both sexes often do not stay with their original troop (Kitchen, Horwich, & James, 2004).
Breeding interval: Mexican black howler monkeys reproduce yearly.
Breeding season: Mexican black howler monkeys may breed throughout the year.
Average number of offspring: 1.
Average gestation period: 180 days.
Range age at sexual or reproductive maturity (female): 3 to 4 years.
Range age at sexual or reproductive maturity (male): 3 to 4 years.
Key Reproductive Features: iteroparous ; year-round breeding ; gonochoric/gonochoristic/dioecious (sexes separate); viviparous
Mexican black howler monkeys have single births ("Belize Zoo", 2007). Males in this species commit infanticide, possibly with the aim of limiting the sizes of their troops (Knopff & Pavelka, 2006). Females care for their young for 12 months after birth, providing direct care and protection from predators and adult males. Parenting is an individual role, as other members of the troop normally do not help raise offspring. Mothers are rarely far away from their newborns and are watchful for dangers to their young (Treves, Drescher, & Snowdon, 2003). However, as their young grow past the neonatal and infant stage, they are accorded a much greater range of freedom.
Parental Investment: altricial ; pre-fertilization (Provisioning, Protecting: Female); pre-hatching/birth (Provisioning: Female, Protecting: Female); pre-weaning/fledging (Provisioning: Female, Protecting: Female); pre-independence (Protecting: Female); post-independence association with parents
- Crockett, C., R. Rudran. 1987. Red howler monkey birth data I: seasonal variation.. American Journal of Primatology, 13: 347-368.
- Horwich, R. 1983. Species Status of the Black Howler Monkey, Alouatta pigra, of Belize. Primates, 24: 288-289.
- Horwich, R. 1983. Breeding behaviors in black howler monkey (Alouatta pigra) of Belize.. Primates, 24: 222-230.
- 2007. "Belize Zoo" (On-line). Black Howler Monkey: Alouatta pigra. Accessed May 03, 2007 at http://www.belizezoo.org/zoo/zoo/mammals/how/how1.html.
- Van Bell, S. 2006. Studies of hormonal cycles, sexual behavior and the phenology of reproduction in howler and spider monkeys.. Accessed May 03, 2007 at http://www.primatesmx.com/fecalhormones.htm.
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Conservation
Conservation Status
IUCN Red List Assessment
Red List Category
Red List Criteria
Version
Year Assessed
Assessor/s
Reviewer/s
Contributor/s
Justification
History
- 2003Endangered(IUCN 2003)
- 2000Lower Risk/least concern
- 1996Lower Risk/least concern
- 1994Insufficiently Known(Groombridge 1994)
- 1990Insufficiently Known(IUCN 1990)
- 1988Indeterminate(IUCN Conservation Monitoring Centre 1988)
- 1986Indeterminate(IUCN Conservation Monitoring Centre 1986)
- 1982Indeterminate(Thornback and Jenkins 1982)
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Conservation Status
Mexican black howler monkeys are endangered by hunting and habitat destruction. The forests in which they live and feed are often converted into pastures or agricultural plots. Human influence as a whole is causing significant fragmentation of A. pigra habitats (Estrada, 2006). Other factors resulting in declining populations are: disease, abnormal rainfall, human capture for pets, and natural disasters such as hurricanes (Gonzalez-Kirchner, 1998). In areas affected negatively by humans, Mexican black howler populations become smaller both in numbers and in area (Gonzalez-Kirchner, 1998). They have been listed by the IUCN as an endangered species since 2003. They were previously (as recently as 2000) considered lower risk/least concern (Cuarón et al., 2003). The U.S. Fish and Wildlife Service lists Alouatta pigra as a threatened species. In the next 30 years, the total population is predicted to decrease 74% (Cuarón et al., 2003). Primates from this region have been hunted and captured as pets, causing their populations to decline further (Estrada et al., 2004).
US Federal List: threatened
CITES: appendix i
IUCN Red List of Threatened Species: endangered
- Cuaron, A., P. de Grammont, L. Cortes-Ortiz, G. Wong, J. Silva. 2003. "2006 IUCN Red List of Threatened Species" (On-line). Alouatta pigra. Accessed May 08, 2007 at www.iucnredlist.org.
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Status: Threatened
Date Listed: 10/19/1976
Lead Region: Foreign (Region 10)
Where Listed:
Population detail:
Population location: entire
Listing status: T
For most current information and documents related to the conservation status and management of Alouatta pigra , see its USFWS Species Profile
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Status
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Trends
Population
Estrada et al. (2004, 2006) carried out surveys of A. pigra populations in a number of areas in Guatemala and Mexico: Calakmul Biosphere Reserve, Campeche, 15.2 individuals/km²; Yaxchilán Natural Monument, Chiapas, 12.8 individuals/km²; and Tikal National Park, Guatemala, 17.8 individuals/km²; Palenque, Chiapas 23 individuals/km². At 13 sites where Estrada et al. (2006) estimated densities of A. pigra, the mean density was 10.8±5.7 individuals/km² (range 3.5-23 individuals/km²).
Population Trend
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Threats
Threats
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Threats
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Management
Conservation Actions
Belize
Guanacaste National Park (32,512 ha) (R. Horwich pers. comm. to Rodríguez-Luna et al. 1996)
Blue Hole National Park (300 ha) (in range)
Mountain Pine Ridge (51,500 ha) (Dahl, 1987)
Cockscomb Basin Wildlife Sanctuary (40,000 ha) (Horwich et al. 1993; Horwich 1994; Koontz et al. 1994; Rodríguez-Luna et al. 1996)
Community Baboon Sanctuary (Horwich and Lyon 1990; Horwich 1994; Pavón 1994; Brockett et al. 1999, 2000; Horwich et al. 2000, 2001)
Upper Bladen (35,000 ha) (R. Horwich pers. comm. to Rodríguez-Luna et al. 1996)
Caracol Archeological Reserve (20,000 ha) (in range)
Monkey Bay Wildlife Sanctuary (Private Reserve) (443 ha) (in range)
Monkey Bay National Park (911 ha) (A. pigra reintroduced) (extinguished by yellow fever and hurricanes (1961 and 1978) (Clark and Brocket 1999)
Manatee Forest Reserve (in range)
Chiquibul National Park (107,607 ha) (Dahl 1987)
Bladen Branch Nature Reserve (39,256 ha) (Dahl 1987)
Rio Bravo Conservation and Management Area (61,513 ha) (Silva-López and Rumiz 1995)
Guatemala
Rio Dulce National Park (9,610 ha) (Silva-López et al. 1995; Silva-López 1998)
El Rosario National Park (1,105 ha) (in range)
Bahia Santo Tomas (1,000 ha) (in range)
Santa Rosalia (1,000 ha) (in range)
Cerro Miramundo (902 ha) (in range)
Las Victorias (82 ha) (in range)
El Reformador (60 ha) (in range)
Grutas Lanquin (in range)
Cuevas de Silvino (8 ha) (in range)
Laguna Lachua National Park (10,000 ha) (in range)
Biotopo Mario Dary Rivera Quetzal (1,153 ha) (A. pigra according to Curdts (1993) and Silva-López 1998; but A. palliata according to Silva-López et al. 1995; Matamoros and Seal 2001)
Biotopo de Chocon Machacas (7,000 ha) (Sympatric with A. palliata; Curdts 1993; Silva-López et al. 1995; Silva-López 1998; Matamoros and Seal 2001)
Biotopo San Miguel La Palotada (49,300 ha) (Sympatric with A. palliata; Curdts 1993; Silva-López et al. 1995; Matamoros and Seal 2001; possible occurrence Silva-López 1998)
Rio Escondido – Biotopo Laguna del Tigre (45,900 ha) (in range)
Dos Lagunas (45,950 ha) (in range)
Tikal National Park (57,600 ha) (Coelho et al. 1976; Schlichte 1978; Estrada et al. 2004)
Aguateca Cultural Monument (1,700 ha) (Silva-López et al. 1995; Silva-López 1998)
Ceibal Cultural Monument (1,700 ha) (in range)
Dos Pilas Cultural Monument (3,100 ha) (Silva-López et al. 1995; Silva-López 1998)
Rio Azul (28,900 ha) (in range)
Uaxactún (3,000 ha) (in range)
Ucanal (2,200 ha) (in range)
Xutilha (2,689 ha) (in range)
Ixcun Cultural Monument (400 ha)
El Peru (8,000 ha)
Biotopo San Miguel – El Zotz (42,000 ha) (in range)
Nakum (8,000 ha) (in range)
G48 Naranjo (1,200 ha)
Machaquilla Cultural Monument (2,500 ha) (in range)
Yaxha (9,000 ha) (in range)
Sierra de las Minas Biosphere Reserve (236,300 ha) (Sympatric with A. palliata; Curdts 1993; Silva-López et al. 1995; Silva-López 1998; Matamoros and Seal 2001)
Polochic (Sympatric with A. palliata; Curdts 1993; Silva-López et al. 1995; Matamoros and Seal 2001)
Sierra Lacandon National Park (200,000 ha) (in range)
Mirador / Dos Lagunas –Rio Azul National Park (147,000 ha) (in range)
El Tigre National Park (350,000 ha) (in range)
Trifinito National Park (4,000 ha)
Mexico
Palenque National Park (1,771 ha) (Estrada and Coates-Estrada 1984; Mexico, SEDUE, 1989; Estrada et al. 2000; Matamoros and Seal 2001)
Tulum National Park 664 ha) (in range)
Ria Lagartos Special Biosphere Reserve (47,840 ha) (in range)
Pantanos de Centla (290,397 ha) (Matamoros and Seal 2001)
Calakmul Biosphere Reserve (Mexico, SEDUE, 1989; Estrada et al. 2004; Serio-Silva et al. 2006)
Montes Azules Biosphere Reserve (Selva Lacandona) (331,200 ha) (Mexico SEDUE, 1989; Matamoros and Seal 2001)
Sian Ka’an Biosphere Reserve (528,147 ha) (Serio-Silva et al. 2006; Matamoros and Seal 2001)
Chan-kin Protection Area for Wild Flora and Fauna (12,184 ha) (Matamoros and Seal 2001)
Yaxchilán Natural Monument (2,621 ha) (Estrada and Coates-Estrada 1984; Estrada et al. 2002, 2004; Matamoros and Seal 2001)
Bonampak Natural Monument (4,357 ha) (Estrada and Coates-Estrada 1984; Matamoros and Seal 2001)
Metzaboc (Hernández-Yãnez pers. comm., in Rodríguez-Luna et al. 1996a)
It is listed on Appendix I of CITES.
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Conservation
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Relevance to Humans and Ecosystems
Benefits
Economic Importance for Humans: Negative
Mexican black howler monkeys occasionally raid crops, although this behavior is rare (Estrada, 2006).
Negative Impacts: crop pest
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Economic Importance for Humans: Positive
Mexican black howler monkeys are important members of the ecosystems in which they live. Their howling is a unique element of their Mesoamerican forests and their presence can attract ecotourism.
Positive Impacts: ecotourism
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Wikipedia
Guatemalan black howler
The Guatemalan black howler, or Yucatan black howler, (Alouatta pigra) is a species of howler monkey, a type of New World monkey, from Central America. It is found in Belize, Guatemala and Mexico, in and near the Yucatan Peninsula. It lives in evergreen, semi-deciduous and lowland rain forests.[2][3] It is also known as the Baboon in Belize, although it is not closely related to the baboons that live in Africa.[4]
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Description
The Guatemalan black howler is the largest of the howler monkey species and one of the largest of the New World Monkeys. Guatemalan black howler males are larger than those of any other Central American monkey species. On average, males weigh 11.4 kg (25 lb) and females weigh 6.4 kg (14 lb).[5] The body is between 521 and 639 mm (20.5 and 25.2 in) in length, excluding tail.[6] The tail is between 590 and 690 mm (23 and 27 in) long. Adults of both sexes have long, black hair and a prehensile tail, while infants have brown fur.[6] Males over 4 months old have a white scrotum.[3]
The Guatemalan black howler shares several adaptations with other species of howler monkey that allow it to pursue a folivorous diet, that is a diet with a large component of leaves. Its molars have high shearing crests, to help it eat the leaves,[5] and males have an enlarged hyoid bone near the vocal cords.[7] This hyoid bone amplifies the male howler's calls, allowing it to locate other males without expending much energy, which is important since leaves are a low-energy food. Howling occurs primarily at dawn and at dusk.[6]
The Guatemalan black howler is diurnal and arboreal.[3] It lives in groups that generally contain one or two adult males, with a ratio of about 1.3 females for every male.[5][6] Groups generally have between two and 10 members, including juveniles, but groups as large as 16 members have been studied.[3][5] The home range is between 3 and 25 hectares.[6] Population density can exceed 250 monkeys per square kilometer in the Community Baboon Sanctuary in Belize.[2]
The Guatemalan black howler's diet includes mostly leaves and fruit. Flowers also make up a small part of the diet. The breadnut tree can provide as much as 86% of the monkey's diet during some seasons.[5][6]
As with other howler monkey species, the majority of the Guatemalan black howler's day is spent resting. Eating makes up about a quarter of the day, moving about 10% of the day, and the remainder of the day is spent in socializing and other activities.[5]
Females reach sexual maturity at four years, and males reach sexual maturity between six and eight years. Males leave their natal group upon reaching sexual maturity, but females generally remain with their natal group. They can live up to 20 years.[6]
Conservation status
The species is considered to be endangered by the International Union for Conservation of Nature because it is believed that the species population will decline by up to 60% over the next 30 years. Threats to the species include habitat loss, hunting, and capture as pets.[2]
The Guatemalan black howler belongs to the New World monkey family Atelidae, which contains howler monkeys, spider monkeys, woolly monkeys and muriquis. It is a member of the howler monkey genus Alouatta. No subspecies are recognized.[1]
Sympatry
The Guatemalan black howler is sympatric with the mantled howler along the edges of its range in Mexico and Guatemala near the Yucatan Peninsula.[2][8] One theory for how this sympatry occurred and why the Guatemalan black howler has such a restricted range is that the ancestors of the Guatemalan black howler and the Central American squirrel monkey migrated to Central America from South America during the late Miocene or Pliocene. However, passage through the Isthmus of Panama then closed for a period due to rising sea levels, and later opened up to another wave of migration about 2 million years ago. These later migrants, ancestors to modern populations of white-headed capuchins, mantled howlers and Geoffroy's spider monkeys, out-competed the earlier migrants, leading to the restricted range of the Guatemalan black howler (and the Central American squirrel monkey).[9]
References
- ^ a b Groves, C. (2005). Wilson, D. E.; Reeder, D. M. eds. Mammal Species of the World (3rd ed.). Baltimore: Johns Hopkins University Press. pp. 149. OCLC 62265494. ISBN 0-801-88221-4. http://www.bucknell.edu/msw3/browse.asp?id=12100386.
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- ^ Rylands, A., Groves, C., Mittermeier, R., Cortes-Ortiz, L., & Hines, J. (2006). "Taxonomy and Distributions of Mesoamerican Primates". In Estrada, A.; Garber, P.A.; Pavelka, M.S.M.; Luecke, L.. New Perspectives in the Study of Mesoamerican Primates. New York: Springer. pp. 47–55. ISBN 978-0-387-25854-6.
- ^ Ford, S. (2006). "The Biogeographic History of Mesoamerican Primates". In Estrada, A.; Garber, P.A.; Pavelka, M.S.M.; Luecke, L.. New Perspectives in the Study of Mesoamerican Primates. New York: Springer. pp. 100–107. doi:10.1007/b136304. ISBN 978-0-387-25854-6. http://www.springerlink.com/content/xjt1852715606p45/.
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