A never-before-photographed black jaguar, recently documented in the jungle of western Belize.


Principal Threats
Deforestation rates are highest in Latin America (FAO 1993), and fragmentation of forest habitat isolates jaguar populations so that they are more vulnerable to the predations of man. People compete with jaguars for prey (Jorgenson and Redford 1993), and jaguars are frequently shot on sight, despite protective legislation. The most urgent conservation issue is the current intolerance of ranchers for jaguars (see Part II Chapter 2 for more discussion of this issue). In many cattle-ranching operations in the region, livestock roam widely and become essentially feral (Schaller 1983, Quigley and Crawshaw 1992). Cattle have been shown to constitute a major portion of jaguar diet in studies carried out on ranches in seasonally flooded savanna woodland (Hoogesteijn et al. 1993, Crawshaw and Quigley in prep.). The vulnerability of the jaguar to persecution is demonstrated by its disappearance by the mid-1900s from the south-western US and northern Mexico, areas which are today home to important puma populations (Brown 1991). A conservation plan has been developed for jaguars in the Brazilian Pantanal (Quigley and Crawshaw 1992), and the Brazilian government is planning to establish a National Center for Research, Management and Conservation of Predators in Brazil to address livestock-predator problems (P. Crawshaw pers. comm.). Swank and Teer (1988) emphasize the potential benefits of controlled sport hunting as an element of national jaguar conservation strategies, arguing that trophy fees would be an incentive for some ranchers to maintain jaguars on their land. Translocation of problem jaguars has also been recommended (Anon. 1992c, 1993c). Preliminary results from one such attempt in Brazil have been good (P. Crawshaw in litt. 1993), but Rabinowitz (1986) found that translocated jaguars in Belize often returned to stock killing.

Commercial hunting and trapping of jaguars for their pelts has declined drastically since the mid-1970s, when anti-fur campaigns gathered steam and CITES controls progressively shut down international markets (see Part II Chapter 4). Organized poaching rings, in which fur buyers travelled through the country supplying traps and buying pelts from local people, are a thing of the past (Swank and Teer 1987)







© 1996 IUCN - The World Conservation Union

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