The number of banteng remaining in its native range is estimated to be only 3,000 to 5,000 individuals and the species is experiencing a rapid decline across its entire range. There has been at least an 80% reduction in the global banteng range in only 20 years (Hedges, 1996) due to massive increases in human populations in south-east Asia. Moreover, only a handful of large herds remain and other populations are at risk of extinction due to both demographic and genetic stochasticity. The main threats to this species are poaching, habitat destruction and human encroachment, overgrazing by domestic cattle, genetic introgression and disease transmission from livestock. Poaching to sell the horns as trophies constitutes the main cause of overexploitation of remnant populations even though the banteng is legally protected across all its range. In 1849, 20 domesticated banteng from Bali were introduced in Arnhem Land, Northern Territory, Australia, during an unsuccessful attempt at European settlement in the Cobourg Peninsula (Calaby, 1975). This founder population of banteng has since proliferated and now numbers around 6000 individuals, still ranging on the 2200 km2 of this remote peninsula (Bradshaw et al., 2005). Molecular analysis has demonstrated that Australian banteng are pure-strain of B. javanicus (Bradshaw et al., 2006). Although non-native, these individuals constitute the world’s largest population of banteng and number more than the rest of the native banteng populations combined. Thus, they represent an important demographic and genetic reservoir of this endangered species and they could be use to reinforce declining populations of banteng or to reintroduce this species in its former range. However, this population has been affected by a severe bottleneck during its introduction in Australia, and as such, its level of genetic variability is probably reduced (Bradshaw et al., 2006). Ex situ conservation programs are implemented for banteng in US, Europe and Asia. Most of these captive individuals belong to B. j. javanicus. Finally, several applications of assisted breeding technology have been tried in this species, including semen cryopreservation, artificial insemination, and interspecies embryo transfer (Johnston et al., 2002). In 2003, an attempt was made to clone banteng in US, using DNA from frozen banteng cells kept by San Diego Wild Animal Park.