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Species: S. oedipus
Other names: cotton-headed tamarin or white-plumed bare-face tamarin; paryk-pinché (Danish); gewone pincheaap (Dutch); valkotöyhtötamariini (Finnish); tamarin d’Oedipe, tamarin à perruque, or tamarin pinché (French); lisztäffchen (German); bichichi, mono tití cabeciblanco, tití, titis, tití blanco, tití leoncito, or tití pielroja (Spanish); bomullshuvudtamarin or pinché (Swedish)
Total population: 1800 (captive), 6000 (wild)
Gestation: 6 months (183 days)
Height: 232 mm (M & F)
Weight: 411 g (M), 430 g (F)
These New World monkeys are small-bodied and easily recognized by the characteristic fan of long, white hair on their heads. They have very fine hair on their black-skinned faces such that their faces appear naked. Tamarins are characterized by their facial appearances and are divided into three groups: the hairy-face, mottled-face, and bare-face groups. Cotton-top tamarins are categorized in the bare-face group (Garber 1993). They have mottled gray-brown shoulders, back, and rump while their stomach and limbs are white. They have reddish-brown hair on the back of their thighs and base of their tail but the rest of the tail is gray-brown-black (Rowe 1996; Groves 2001). Cotton-top tamarins are not sexually dimorphic and the average height of both males and females is 232 mm (9.13 in) (Rowe 1996). Wild males and females weigh between 410 and 450 g (14.5 and 15.9 oz) but average 416.5 g (14.7 oz), while captive cotton-top tamarins are significantly heavier and weigh, on average, 565.7 g (19.9 oz) (Savage 1990).
The most common modes of locomotion for cotton-top tamarins include quadrupedal running, bounding, or galloping along medium to small branches as well as clinging and leaping between trees on thin or small branches (Rowe 1996; Kinzey 1997). Members of the subfamily Callitrichinae have claw-like nails (called tegulae) that resemble a squirrel’s rather than the flat nails (called ungulae) characteristic of other primates, including humans. These claw-like nails aid in clinging, running, and leaping through trees (Kinzey 1997). Cotton-top tamarins also exhibit the trait of primarily giving birth to non-identical twins, as is seen in other callitrichines (Rowe 1996).
Cotton-top tamarins live for an average of 13.5 years, but the oldest recorded cotton-top tamarin lived to be 24 years old in captivity (Rowe 1996; Savage pers. comm.).
CURRENT RANGE MAPS (IUCN REDLIST):
Cotton-top tamarins are one of three Amazonian species of tamarin and are found in a small area of northwest Colombia in a range bound by the Cauca and Magdalena Rivers and the Atlantic coast (Snowdon & Soini 1988; Groves 2001). Though the overall area bound to the north by the Magdalena River and the west by the Cauca River has historically been suitable habitat for cotton-top tamarins, they are now only found in fragmented parks and reserves throughout this area. One of the strongholds of the remaining cotton-top tamarins is in Paramillo National Park, a 540 km² (208 mi²) park containing primary and secondary forest (Mast et al. 1993).
One of the only long-term studies of wild cotton-top tamarins was started in the mid-1970s by primatologist Patricia Neyman. Not only did she habituate wild groups but she also live-trapped and marked them, allowing for qualitative research on group membership changes and life history characteristics of individual animals (Neyman 1977). More recently, Anne Savage and her colleagues began working on a long-term research and conservation project in La Reserva Forestal Protectora Serranía de Coraza-Montes de Marìa in Colombia, another principal refuge for cotton-top tamarins (Savage et al. 1996a).
It is estimated that there are between 300 and 1000 cotton-top tamarins left in Colombia (Savage 1990). There are 1800 cotton-top tamarins in captivity and of those, 64% are found in research laboratories (Savage et al. 1997a).
Cotton-top tamarins are found in humid tropical forest, dry deciduous forest, and secondary growth forest (Hernández-Camacho & Cooper 1976; Snowdon & Soini 1988; Mast et al. 1993; Kinzey 1997). Tropical forests have multiple vertical layers of growth, from the short understory (less than 5 meters) to the tallest trees in the canopy (over 20 meters). Cotton-top tamarins use multiple layers of the tropical forests in which they are found, moving vertically between the understory and canopy, but preferentially utilizing the lower vertical levels of the forest. They are most commonly found in trees but can be seen on the ground, foraging among leaf litter (Snowdon & Soini 1988). These tamarins are also highly adaptable to secondary or remnant forest fringes or patches and can live in relatively disturbed habitats. They are found primarily at elevations below 1500 m (4921 ft), but rarely above 400 m (1312 ft) (Hernández-Camacho & Cooper 1976).
In the deciduous or dry forest parts of their range, rainfall is highly seasonal, with the dry season lasting from December to April and heavy rainfall from August to November. Annual average rainfall varies between 500 and 1000 mm (1.64 and 3.28 ft) and there are periods when the forest floor is flooded (Neyman 1977). In the humid rainforest where they are found, annual rainfall can be as high as 1300 mm (4.27 ft) (Mast et al. 1993).
The primary components of cotton-top tamarin diet are insects, fruit, plant exudates, and nectar, but they have also been recorded eating reptiles and amphibians. It is important for tamarins to have a high-quality, high-energy diet because of their small-body size, limited gut volume, and rapid rate of food passage (Garber 1993). The role of plant exudates in the diet of callitrichines is important as a source of minerals, water, and other nutrients though tamarins do not have the same specialized adaptations to feeding on gum, sap, resin, and latex as do marmosets (Callithrix species) and are therefore primarily dependent on insects and fruits (Snowdon & Soini 1988; Kinzey 1997). When they do eat gum, cotton-top tamarins rely on more indirect means to obtain exudates than their marmoset (Callithrix species) counterparts; they depend on natural weathering of bark, the holes left by wood-boring insects or rodents, and re-gouging of hardened gum holes to stimulate flow (Snowdon & Soini 1988; Kinzey 1997). Insectivory is also important in their ecology. Some insect-hunting techniques employed by cotton-top tamarins include stealth, turning over leaves, exploring crevices, pouncing, and moving rapidly to the ground to seize prey. Like foraging for other foods, hunting for insects is an individualistic behavior (Garber 1993). Foraging occurs in the middle layer of the canopy from five to 15 m (16 to 49 ft), and while cotton-top tamarins select a feeding site because of its fruit availability, they also hunt for insects and utilize gum in the vicinity (Neyman 1977). Cotton-top tamarins clearly compete for access to some foods with squirrels, other diurnal primate species, and various birds. They also may be competing for access to food resources with nocturnal fruit and insect-eating species including bats (Neyman 1977).
Tamarins are highly important seed dispersers in tropical ecosystems. They ingest and void seeds larger than those consumed by much larger species of primates, including chimpanzees (Pan troglodytes and Pan paniscus), baboons (Papio species), and macaques (Macaca species). Voided seeds show high germination success compared to others, but there may be another benefit to this seed-swallowing behavior (Snowdon & Soini 1988; Garber 1993; Sussman 2000). One function of swallowing such disproportionately large seeds may be to mechanically expel intestinal parasites from their digestive tract. Certain worms, caused by consuming orthopteran prey, attach to the lining of the gut and cause inflammation, lesions, and death. By swallowing and expelling seeds, these may, as they work their way through the gastrointestinal tract, dislodge intestinal parasites (Sussman 2000).
The typical daily routine of cotton-tops involves an alternating pattern of foraging, resting, and traveling. They sleep in a group and start their day about an hour and 20 minutes after dawn when the entire party leaves the sleeping tree at the same time. Cotton-top tamarins follow established routes to find available foods, moving between .12 and .24 (.07 and .15 mi) per hour and covering about 1.5 and 1.9 km (.93 and 1.18 mi) per day over home ranges of between .078 and .10 km² (.03 and .04 mi²) (Neyman 1977). After about an hour of foraging, they begin to rest for a few minutes at a time, either stretching out on a branch or grooming within the social group. They continue to travel and forage throughout the day, taking increasingly longer resting periods, the longest being around midday. In late afternoon, they begin to travel more quickly and more cohesively with limited foraging stops until they reach a sleeping tree (Neyman 1977). Cotton-top tamarins prefer to sleep in trees with some foliage cover such as broad leaves, vines, epiphytes, or lianas. They repeatedly use trees within their home range for sleeping sites, but do not generally use the same tree on consecutive nights (Savage 1990). By selectively choosing sleeping trees, getting a relatively late start to their day compared to other primates, and hastening foraging and traveling speed before dusk, cotton-top tamarins may be avoiding many crepuscular and nocturnal predators. Some of the main predators of cotton-top tamarins include raptors, mustelids, felids, and snakes (Snowdon & Soini 1988; Sussman 2000). Cotton-top tamarins are extremely vigilant, constantly scanning for potential predators above and around them and even in captivity can be observed stopping their activities to look around (Price 1992). In the wild, when the group rests during the day, one group member separates itself from the resting animals and remains vigilant, alarming the group through vocalizations if it detects danger (Savage 1990).
Content last modified: May 18, 2005
Cite this page as:
Cawthon Lang KA. 2005 May 18. Primate Factsheets: Cotton-top tamarin (Saguinus oedipus) Taxonomy, Morphology, & Ecology . <http://pin.primate.wisc.edu/factsheets/entry/cotton-top_tamarin/taxon>. Accessed 2020 July 30.
For individual primate species conservation status, please search the IUCN Red List.
Also search the current scientific literature for primate conservation status (overall as well as for individual species), and visit CITES (Convention on International Trade in Endangered Species of Wild Fauna and Flora).
Conservation information last updated in 2005 follows, for comparison:
Saguinus oedipusWhile they were exported for use in biomedical research in the tens of thousands in the 1960s and early 1970s, the cotton-top tamarin is now restricted from international trade and has, since 1976, the highest level of protection afforded by CITES (Mast et al. 1993). Surveys reveal that there are only between 300 and 1000 cotton-top tamarins left in the wild (Savage 1990).
CONSERVATION THREATS & POTENTIAL SOLUTIONS
Threat: Human-Induced Habitat Loss and Degradation
Losing more than 4000 km² (1544 mi²) of forest or 5% of the tropical habitat per year, Colombia is one of the top ten countries worldwide in terms of deforestation (Savage et al. 1989; Mast et al. 1993). This astonishing rate of deforestation can be attributed to removal of forest products for subsistence and traditional uses, swidden agriculture, and large-scale clearing for industrial agriculture and cattle grazing (Savage et al. 1989; Mast et al. 1993). The lowland forest on which the cotton-top tamarin depends has been reduced to a mere 5% of its former geographic range, posing a considerable threat to the monkey. The northern part of Colombia is the most densely populated area in the country and only three blocks of high-quality forest remain (Alderman 1989). Fragmentsof forest dispersed across the landscape in this part of the country hold remnant populations of primates, and luckily, cotton-top tamarins seem to adjust and can live in these disturbed habitats (Alderman 1989). If deforestation does not stop or if restoration does not become a top priority, the cotton-top tamarin will simply not have a place to live (Defler 2004).
The major cause behind deforestation is the overuse of forest products by an exploding human population. Whether pressure from subsistence users, swidden farmers, or exploitative timber corporations, large-scale forest loss has occurred in Colombia and other parts of the world at unprecedented and ever-increasing rates (Mittermeier et al. 1989; Mast et al. 1993; Defler 2004). Removal of selected plant products by traditional means in Colombia does not involve the same kind of overt destruction of habitat as is seen with large-scale clearance, but it does pose a threat to cotton-top tamarins because some of the targeted tree species are important to the feeding ecology of the tamarins (Alderman 1989). Specifically, removal of plants that are important dry season resources can be detrimental to monkeys that depend on those species during stressful times of year. Clearance or damage to the understory for obtaining subsistence usage firewood and charcoal may have detrimental side effects as well, damaging the layers of forest important for insect foraging (Alderman 1989). In particularly poor areas where the only available cooking fuel is wood, a family of five consumes about 15 logs of wood per day (Savage et al. 1996/1997). If these logs are cleared from an area and no replanting occurs, it is understandable that large swaths of land may be cleared over time, resulting in significant habitat loss for the tamarins.
On a larger scale, commercial logging can result in massive forest removal through clear-cutting. Forests take a long time to recover from clear-cutting while the ecosystem is completely disrupted and may not recover. Commercial logging also directly affects colonization rates because as timber companies go deeper into forests, they clear roads for their trucks and leave tracts of land cleared and ready for human settlement (Marsh et al. 1987). This process occurs in Colombia because, like in many clear-cut areas, vacant tracts are not being replanted (Alderman 1989). Land cleared for agriculture, both small-scale shifting cultivation and large-scale plantations and ranching, is also increasing in Colombia.
Exploring for oil in the lowlands of Colombia is a growing threat to cotton-top tamarins as well. The area is rich in hydrocarbon reserves and the economic boom associated with oil extraction certainly will bring even more people to the area in search of jobs as well as opening up forests to roads and settlement (Mittermeier et al. 1999).
Another serious human-induced threat is damming for hydroelectric power. Proposed dams would flood the forest and destroy about 540 km² (208 mi²) of primary and secondary forests within Paramillo National Park, one of the last protected areas in which the tamarins are found (Mast et al. 1993). Hydroelectric power is an inexpensive, renewable source of energy for Colombia, but damming areas of high biodiversity not only wipes out fragile ecosystems but also displaces indigenous peoples living in the forest, forcing them into remaining forest fragments and increasing pressure on those areas of forest that are not flooded (Mast el al. 1993).
While 10% of the land in Colombia is legally protected in national parks, at least 30% of national parks are invaded by colonists or subject to other claims (Defler 2004). The protection of these parks on paper must be translated to real regulation to make them more effective. Even more important is to find ways of providing services that the forest would provide to colonists including fuel, protein sources, and income.
Providing alternate fuel sources is an important step in reducing the amount of forest products used on a daily basis in Colombia. Proyecto Tití, a conservation project sponsored by Roger Williams Park Zoo, the Ministerio de Ambiente (the environmental protection agency of Colombia), and CARSUCRE (a regional environmental organization), has worked to provide alternate cooking methods that minimize the amount of non-sustainable forest product usage. By working with local communities to see which cooking methods worked best and which they preferred, the project managers determined that by modifying a traditional clay oven, they could use corn husks, coconut shells, and other vegetative waste products as efficient fuel sources and decrease pressure on surrounding forests (Savage et al. 1997c). These low-cost ovens have been distributed to community members and are being used with great success. Similar technology could be used in other villages that border cotton-top tamarin habitats. If alternate fuel sources cannot be obtained or cooking methods do not change, some effort should be concentrated into replanting frequently harvested areas to hasten the regeneration of important food sources for the tamarins as well as provide future resources for local communities.
Hydroelectricity makes up about 70% of Colombia’s electric power while only 6% of the hydroelectric potential is currently being exploited. Power companies as well as the Colombian government must take into consideration environmental and socioeconomic factors when building dams. Fortunately, Colombia’s power sector has historically avoided major negative environmental and social impacts resulting from erecting dams, but as the human population grows and the demand for electricity also increases, this record will be difficult to maintain (Mast et. al 1993). Power companies must work with the Colombian government to assess impacts on biodiversity and Colombian citizens to avoid disastrous engineering decisions.
Threat: Harvesting (hunting/gathering)
Primates have little value in Colombia other than for their meat and as export commodities (Defler 2004). Live capture for biomedical research and the pet trade has historically been a serious threat to cotton-top tamarins. By the early 1970s, as many as 40,000 cotton-tops had been caught and exported from Colombia, with about 14,000 of those animals imported into the US (Mittermeier et al. 1994). This massive exportation of tamarins seriously reduced the wild population.
Though cotton-top tamarins are now protected under Appendix I of CITES, and importation into the US has ceased, they are still being used in biomedical research. The captive population outnumbers the wild population and has been carefully maintained through selective captive breeding programs so that animals do not need to be taken from the wild to supplement captive populations (Savage 1997). At the present time, the captive populations are self-sustaining and one of the goals is that the captive populations may be sufficient enough to supply animals for reintroduction in Colombia in the future (Mittermeier et al. 1994).
Another facet of Proyecto Tití which has decreased hunting of wildlife is an innovative exchange program. Members of a community living close to the forest were able to exchange their slingshots, a common hunting implement, for stuffed cotton-top tamarin toys (Savage et al. 1997c). Plush stuffed animals are a rarity in this small village and interest in the exchange was very high. By retiring their slingshots, members of the community significantly decreased the amount of hunting and capture of wildlife for the pet trade, certainly benefiting the cotton-top tamarins in the nearby forest (Savage 1997). Programs like this that discourage hunting and wildlife capture and provide a commodity for local community members are important to increase awareness. They also are easily replicated in other areas and may be one part of the solution to decrease poaching of endangered species.
Threat: Natural Disasters
During periods of severe drought, pregnant cotton-top tamarins overwhelmingly fail to deliver viable offspring (Savage et al. 1996a). During one drought, none of the pregnant females in the study groups gave birth to viable infants. Environmental stress such as drought could have potentially harmful effects on small populations of cotton-top tamarins, though even after fetal loss, they can conceive again within the breeding season (Savage et al. 1996a).
Intermittent severe droughts that lead to fetal loss cannot be solved or planned for but will likely not have enormous detrimental effects on the size of the cotton-top tamarin population because of their high fertility rates and ability to conceive more than once per year (Savage et al. 1996a; Achenbach & Snowdon 2002).
Threat: Intrinsic Factors
With offspring survivorship around 86% in the wild, cotton-top tamarins are well-equipped to maintain the size of their population if they have habitat in which to live (Savage et al. 1996a). As habitat disappears and becomes more fragmented, though, dispersal may be limited and offspring survivorship may decrease as inbreeding increases. The potential problems associated with inbreeding are particularly devastating in small communities and include inbreeding depression and genetic drift (Marsh 2003).
Threat: Human Disturbance
Civil disturbance by guerrilla fighters and paramilitary operations have actually resulted in positive results for the cotton-top tamarin population in some areas of Colombia. Because local people have been removed from their land by these rebels, fuelwood acquisition has ceased and they are not able to clear land for planting gardens. While these circumstances are very unfortunate for the victims of these paramilitary operations, cotton-top tamarins are benefiting through decreased pressure on their habitat (Defler et al. 2003). Generally speaking, guerrilla fighters and civil instability are bad for primates and other forest-dwelling animals because operations taking place primarily in the forests results in increased hunting pressure by fighters and displaced people. This is especially prevalent in Africa, but could also be the case in South American countries as well (see Coxe et al. 2000). Furthermore, areas governed by armed fighters are often used to cultivate crops of illegal drugs, requiring that forest is cleared and habitat is destroyed. As the market for these drugs continues to be lucrative both within Colombia and abroad, economic incentives to plant these types of crops persists and larger amounts of land will be converted to maintain the supply (Álvarez 2002).
Instability due to civil unrest has prevented researchers from maintaining their presence in some areas of the cotton-top tamarin’s range. Satellite imaging of unstable areas has continued, allowing researchers to remotely collect data on forest destruction and fragmentation. Work on cotton-top tamarins continues in safer regions of Colombia that have populations (Defler et al. 2003).
Decreasing the demand for illegal drugs is an ongoing battle in the United States and elsewhere. Until demand decreases, incentives will continue to exist to clear forest and grow drugs.
Cotton-top tamarins have been used in biomedical research because they are especially useful as models for the study of Epstein-Barr virus, colitis, and colon cancer (Mittermeier et al. 1994). In captivity, as many as half of the adult cotton-top tamarins spontaneously develop colitis, characterized by prolonged, repeated bouts of diarrhea, severe weight loss and even death (King et al. 1993). This type of colitis is linked to an increased risk of developing a certain type of colon cancer, colonic adenocarcinoma (Clapp et al. 1993). Since these diseases affect humans, cotton-top tamarins have been studied extensively in captivity to understand the causes of these diseases and how they relate to one another, as well seeking potential cures (Clapp et al. 1993).
LINKS TO MORE ABOUT CONSERVATION
- Tiny primate ‘punk’ in danger of extinction (PhysOrg; July 12, 2010)
- Conservationists Fight to Save Tiny Colombian Monkey (National Geographic News; May 27, 2003)
- Links for all species
ORGANIZATIONS INVOLVED IN Saguinus oedipus CONSERVATION
- Primarily Primates
- Monkey World – Ape Rescue Center
- Monkeyland Primate Sanctuary
- Small World Zoological Gardens and Sanctuary
- Sonora Desert Primate Conservancy
Content last modified: May 18, 2005
Cite this page as:
Cawthon Lang KA. 2005 May 18. Primate Factsheets: Cotton-top tamarin (Saguinus oedipus) Conservation . <http://pin.primate.wisc.edu/factsheets/entry/cotton-top_tamarin/cons>. Accessed 2020 July 30.
The following references were used in the writing of this factsheet. To find current references for Saguinus oedipus, search PrimateLit.
Achenbach GG, Snowdon CT. 2002. Costs of caregiving: weight loss in captive adult male cotton-top tamarins (Saguinus oedipus) following the birth of infants. Int J Primatol 23(1): 179-89.
Alderman CL. 1989. A general introduction to primate conservation in Colombia. Prim Cons 10: 44-51.
Bardi M, Petto AJ, Lee-Parritz DE. 2001. Parental failure in captive cotton-top tamarins (Saguinus oedipus). Am J Primatol 54(3): 159-69.
Clapp NK, Henke MA, Hansard RM, Carson RL, Adams LJ, Nardi RV. 1993. Natural history, time course, and pathogenesis of idiopathic colitis in cotton-top tamarins (Saguinus oedipus). In: Clapp NK, editor. A primate model for the study of colitis and colonic carcinoma: the cotton-top tamarin Saguinus oedipus. Boca Raton (FL): CRC Pr. p 83-99.
Coxe S, Rosen N, Miller P, Seal U, editors. Bonobo conservation assessment workshop final report; 1999 Nov 21-22; Inuyama, Japan. Apple Valley (MN): IUCN/SSC Conservation Breeding Specialist Group. 51 p.
Defler TR. 2004. Primates of Columbia. 5, Conservation International tropical field guide series. Bogotá (Columbia): Conservation International. 550 p.
Defler TR, Rodriguez-M JV, Hernández-Camacho JI. 2003. Conservation priorities for Colombian primates. Prim Cons. 19: 10-18.
Garber PA. 1993. Feeding ecology and behaviour of the genus Saguinus. In: Rylands AB, editor. Marmosets and tamarins: systematics, behaviour, and ecology. Oxford (England): Oxford Univ Press.
Garber PA. 1997. One for all and breeding for one: cooperation and competition as a tamarin reproductive strategy. Evol Anthro 5(6): 187-99.
Groves C. 2001. Primate taxonomy. Washington DC: Smithsonian Inst Pr. 350 p.
Heistermann M, Kleis E, Pröve E, Wolters HJ. 1989. Fertility status, dominance, and scent marking behavior of family-housed cotton-top tamarins (Saguinus oedipus) in absence of their mothers. Am J Primatol 18(3): 177-89.
Hernández-Camacho J, Cooper RW. 1976. The nonhuman primates of Colombia. In: Thorington, Jr. JR, Heltne PG, editors. Neotropical primates: field studies and conservation. Washington DC: National Acad Sciences. p 35-69.
King NW, Johnson LD, Sehgal PK. 1993. The prevalence of idiopathic colitis in the New England Regional Primate Research Center cotton-top tamarin (Saguinus oedipus) colony. In: Clapp NK, editor. A primate model for the study of colitis and colonic carcinoma: the cotton-top tamarin Saguinus oedipus. Boca Raton (FL): CRC Pr. p 101-12.
Kinzey WG. 1997. Synopsis of New World primates (16 genera). In: Kinzey WG, editor. New world primates: ecology, evolution, and behavior. New York: Aldine de Gruyter. p 169-324.
Marsh LK. 2003. Primates in fragments: ecology and conservation. New York: Kluwer Academic/Plenum. Section I: genetics and population dynamics. p 11-16.
Marsh CW, Johns AD, Ayres JM. 1987. Effects of habitat disturbance on rain forest primates. In: Marsh CW, Mittermeier RA, editors. Primate conservation in the tropical rainforest. New York: Alan R. Liss. p 83-107.
Mast RB, Rodriguez JV, Mittermeier RA. 1993. The Colombian cotton-top tamarin in the wild. In: Clapp NK, editor. A primate model for the study of colitis and colonic carcinoma: the cotton-top tamarin Saguinus oedipus. Boca Raton (FL): CRC Pr. p 4- 43.
McGrew WC, Webster J. 1995. Birth seasonality in cotton-top tamarins (Saguinus oedipus) despite constant food supply and body weight. Primates 36(2): 241-8.
Mittermeier RA, Kinzey WG, Mast RB. 1989. Neotropical primate conservation. J Hum Evol 18(7): 597-610.
Mittermeier RA, Myers N, Mittermeier CG. 1999. Hotspots: Earth’s biologically richest and most endangered terrestrial ecoregions. Mexico City: CEMEX. 430 p.
Neyman PF. 1977. Aspects of the ecology and social organization of free-ranging cotton-top tamarins (Saguinus oedipus) and the conservation status of the species. In: Kleiman DG, editor. The biology and conservation of the Callitrichidae; 1975 Aug 18-20; Washington DC. Washington DC: Smithsonian Inst Pr. p 39-71.
Price EC. 1990. Parturition and perinatal behaviour in captive cotton-top tamarins (Saguinus oedipus). Primates 31(4): 523-35.
Price EC. 1992. The costs of infant carrying in captive cotton-top tamarins. Am J Primatol 26(1): 23-33.
Rowe N. 1996. The pictorial guide to the living primates. East Hampton (NY): Pogonias Pr. 263 p.
Savage A. 1990. The reproductive biology of the cotton-top tamarin (Saguinus oedipus oedipus) in Colombia. Ph.D dissertation, University of Wisconsin. 166 p.
Savage A. 1997. Proyecto Titi: conservation of the cotton-top tamarin in Colombia. The Conservationist Newsletter 2(1): 10-13.
Savage A, Giraldo LH, Soto LH, Snowdon CT. 1996a. Demography, group composition, and dispersal in wild cotton-top tamarin (Saguinus oedipus) groups. Am J Primatol 38(1): 85-100.
Savage A, Soto LH, Giraldo LH. 1996/1997. Proyecto Titi: developing alternatives to forest destruction. Primate Cons 17: 127-30.
Savage A, Giraldo H, Soto L. 1997a. Developing a conservation action program for the cotton-top tamarin (Saguinus oedipus). In: Wallis J, editor. Primate conservation: the role of zoological parks. Special topics in primatology, Volume 1. United States: Am Soc Primatol. p 97- 111.
Savage A, Shideler SE, Soto LH, Causado J, Giraldo LH, Lasley BL, Snowdon CT. 1997b. Reproductive events of wild cotton-top tamarins (Saguinus oedipus) in Columbia. Am J Primatol 43(4): 329-37.
Savage A, Snowdon CT, Giraldo LH. 1989. Proyecto Titi: a hands on approach to conservation education in Colombia. AAZPA: 1989 Annual Conference Proceedings; 1989 Sept 24-28; Pittsburgh. American Assoc Zoological Parks Aquariums. P 605-6.
Savage A, Snowdon CT, Giraldo LH, Soto LH. 1996b. Parental care patterns and vigilance in wild cotton-top tamarins (Saguinus oedipus). In: Norconk MA, Rosenberger AL, Garber PA, editors. Adaptive radiations of neotropical primates. New York: Plenum Pr. p 187-99.
Savage A, Ziegler TE, Snowdon CT. 1988. Sociosexual development, pair bond formation, and mechanisms of fertility suppression in female cotton-top tamarins (Saguinus oedipus oedipus). Am J Primatol 14 (4):345-59.
Savage A, Zirofsky DS, Soto LH, Giraldo LH, Causado J. 1997c. Proyecto Tití: an integrated approach to conserving the cotton-top tamarin. Int Zoo News 43(8): 544-52.
Snowdon CT, Soini P. 1988. The tamarins, genus Saguinus. In: Mittermeier RA, Coimbra-Filho AF, da Fonseca GAB, editors. Ecology and behavior of neotropical primates, Volume 2. Washington DC: World Wildlife Fund. p 223-98.
Sussman RW. 2000. Primate ecology and social structure. Volume 2, New world monkeys. Needham Heights (MA): Pearson Custom. 207 p.
Tardif SD. 1984. Social influences on sexual maturation of female Saguinus oedipus oedipus. Am J Primatol 6(3): 199-209.
Washabaugh K, Snowdon CT. 1998. Chemical communication of reproductive status in female cotton-top tamarins (Saguinus oedipus oedipus). Am J Primatol 45(4): 337-49.
Ziegler TE, Epple G, Snowdon CT, Porter TA, Belcher AM, Küderling I. 1993. Detection of the chemical signals of ovulation in the cotton-top tamarin, Saguinus oedipus. Anim Beh 45(2): 313-22.
Ziegler TE, Savage A, Scheffler G, Snowdon CT. 1987. The endocrinology of puberty and reproductive functioning in female cotton-top tamarins (Saguinus oedipus) under varying social conditions. Biol Reprod 37(3): 618-27.
Content last modified: May 18, 2005
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Photo: Anne Savage
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