|Scientific Name:||Callicebus oenanthe|
|Species Authority:||Thomas, 1924|
|Taxonomic Notes:||Recognized as a valid species by Hershkovitz (1990). Kobayashi and Langguth (1999) and van Roosmalen et al. (2002) recognize five species groups – cupreus, donacophilus, moloch, personatus and torquatus. Van Roosmalen et al. (2002) place it in the donacophilus group, along with: Callicebus donacophilus, C. pallescens, C. modestus and C. olallae.|
|Red List Category & Criteria:||Critically Endangered A2cd ver 3.1|
|Assessor(s):||Veiga, L., Bóveda-Penalba, A., Vermeer, J., Tello-Alvarado, J.C. & Cornejo, F.|
|Reviewer(s):||Mittermeier, R.A. & Rylands, A.B.|
Listed as Critically Endangered as it is estimated that a population reduction of ≥80% has occurred over the last 25 years due to massive deforestation of this species' preferred habitat as a result of increased human population pressure and intensification of agricultural activities and a lack of concrete conservation activities .
|Previously published Red List assessments:||
Until 2007, this species was thought to be endemic to the upper Rio Mayo valley or Alto Mayo (Hershkovitz 1990). However, a recent study by Bóveda-Penalba et al. 2009, undertaken over six months at 96 localities, revealed that its distribution extends much further to the south of the Department of San Martin, extending into the Bajo Mayo and Huallaga Central, almost reaching the Rio Huallabamba (known locally as the rio Huayabamba). This area is heavily deforested, and to date only one area was found where a viable population might live, although further research is needed to confirm this.
Mark (2003) and DeLuycker (2006) suggested that the species’ altitudinal range may be restricted to below 1,000 m. The study undertaken by Bóveda-Penalba et al. (2009) registered the species between 252 and 1,053 metres asl. Results from research undertaken in the Proyecto Mono Tocón show that at least 60% of the species’ original habitat has already been lost.
There is an urgent need for additional surveys of all potential habitats in San Martin, and larger tracts of forest. Mark (2003) notes that subpopulations near the banks of the Rio Mayo differ in colour from those in the Aguaruna territory in the north-east. DeLuycker (2006) reported a marked difference in pelage colour between a group she studied in a fragment near Moyobamba and those photographed by Noel Rowe. During surveys, attention should be given to the distributions of the different colour morphs (Mark 2003). Bóveda-Penalba et al. (2009) detected little difference in colour in individuals of the Alto Mayo, they argue that pelage colour varies depending on the lighting conditions. Some darker animals appeared much lighter when their bodies were turned in a different direction, making it difficult to determine differences in colour between Alto Mayo populations and the same was true for the quantity of white hair on the face. However, animals in the southern part of San Martin appear to be somewhat greyer than animals near Alto Mayo and usually do not have a a white mask (Tello-Alvarado J. C. pers comm). Bóveda-Penalba et al. (2009) claim that the species lives in sympatry with another, undescribed species of Callicebus in the southern part of its range. Recent research carried out by the same team suggests it is just a morphological variation of C. oenanthe (A.J. Bóveda-Penalba pers. comm).
|Estimated area of occupancy (AOO) - km2:||3600|
|Upper elevation limit (metres):||1000|
|Range Map:||Click here to open the map viewer and explore range.|
A few short surveys were undertaken (Rowe and Martinez 2003, Mark 2003, DeLuycker 2006) and interviews conducted with communities of Aguaruna Amerindians to confirm the presence or absence of the species in different parts of its range.
Aldrich (2006) undertook a song-based survey of a population at Tarangue (a 74 ha private reserve near Moyobamba) and estimated a population density of 1.4 individuals per ha. Group sizes were unusually large for Titi Monkeys, with 20% of groups containing six to eight individuals. Rowe and Martinez (2003) carried out a four-day survey, and although they did not observe the species in the wild, they heard several groups of Titi Monkeys (presumed to be C. oenanthe) vocalizing in a forest remnant at 925 m. They photographed a family being sold at a local market that had been captured near Rioja. Mark (2003) carried out surveys at five sites and observed monkeys in fragments as small as 2 ha (804 m asl).
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||
This species is known to occur in low secondary forests and remnant forest and has been seen in bamboo stands, viney thickets, fruit crops and palm-dominated semi-flooded forests (“aguajales” and “renacales”) (DeLuycker 2006, 2007). Mark (2003) noted that occurrence records (both sightings and calls) were frequently located near rivers and streams (distance of et al. (2009), also found the species in forests located far away from rivers and claim that the species does not seem to be bound to a specific habitat, and confirmed their presence in inundated areas with aguajales (Mauritia flexuosa) and renacales (Ficus trigona), but also drier zones with ojés (Ficus anthelmintica), tangaranas (Triplaris sp.), zapotes (Ponteria mimosa), and ceticos (Cecropia sp.).These Titi Monkeys appear to be able to survive (at least in the short term in the absence of hunting) in forest fragments and relatively large groups have been registered in fragments of
|Generation Length (years):||8|
|Use and Trade:||It is locally hunted for food, and animals are taken as pets.|
The main threats to this species are habitat loss and fragmentation, and hunting pressure. The region has suffered intense human colonization over the last 30 years because of a major agrarian programme, which has attracted huge numbers of immigrants. Agricultural activities include the cultivation of rice and coffee; cattle ranching and selective timber extraction also occur. The region is characterized by rapid rates of deforestation (estimates vary from 40,000 to 100,000 ha per year) and fragmentation, and has lost at least 40% of its forest cover, mainly from the low-altitude river basins (the preferred habitat of this species) over the last 20 years (Mark 2003, DeLuycker 2006). The construction of a two-lane all-weather road, which was asphalted in 2003 - La Carretera Marginal, Via Marginal, or Carretera Fernando Belaunde Terry - which runs all the way to the coast (Chiclayo) and past Tarapoto has contributed to the influx of immigrants and a change from subsistence to small-scale farming. It has also altered the spatial distribution of human settlers, who now follow the highway far into the valley and high forests, and the lack planning or state-regulated land occupation and use puts protected areas and remaining forests at risk (DeLuycker 2006).
Very little attention has been given to forest conservation in this region. This species’ range may include the Bosque de Protección de Alto Mayo, which extends from the town of Rioja north along the border between the departments of San Martín and Amazonas, however more surveys are needed to confirm this as there species was registered once in a buffer zone of this protected area. During short surveys of the Reserve, no titis were detected in the high-altitude areas which make up most of the reserve. It is likely that the species only occurs in the low-altitude areas on the edges of the reserve (<1%) (Rowe and Martinez 2003, DeLuycker 2006). Other protected areas in this species’ range include, Tarangue (74 ha), which belongs to a conservation organization called IKAMA Peru. The species also occurs in the Pabloyacu Reserve (640 ha) of the Universidad de San Martín, but despite its name this is not a protected area.
Mark (2003) and DeLuycker (2006) have emphasized the potential importance of both privately owned reserves and Amerindian reservations for the long-term conservation of this species. There are 14 indigenous Aguaruna communities located throughout the Alto Mayo region. The large tracts of forested land allocated to these well-organized communities could play a key role in conservation initiatives (Mark 2003).
Proyecto Mono Tocón, started in 2007 as an initiative of Le Conservatoire pour la Protection des Primates, French foundation created by the park primates La Vallée des Singes. The main objective of this project is the conservation of San Martin Titi Monkey (C. oenanthe) and its habitat. This local NGO has launched a long-term project which has three well-defined lines of work: Conservation, Research and Environmental Education. The Proyecto Mono Tocón works directly with local people, local governments and other NGOs in establishing community conservation areas.
It is listed on CITES Appendix II.
|Citation:||Veiga, L., Bóveda-Penalba, A., Vermeer, J., Tello-Alvarado, J.C. & Cornejo, F. 2013. Callicebus oenanthe. The IUCN Red List of Threatened Species 2013: e.T3553A9939083. http://dx.doi.org/10.2305/IUCN.UK.2011-1.RLTS.T3553A9939083.en . Downloaded on 04 October 2015.|
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