Schipper J, Chanson JS, Chiozza F et al (2008) The status of the world’s land and marine mammals: diversity, threat, and knowledge. Sandalj M, Treydte AC, Ziegler S (2016) Is wild meat luxury? Quantifying wild meat demand and availability in Hue, Vietnam. Ripple WJ, Abernethy K, Betts MG et al (2016) Bushmeat hunting and extinction risk to the world’s mammals. Ripple WJ, Newsome TM, Wolf C et al (2015) Collapse of the world’s largest herbivores. Ripple WJ, Estes JA, Beschta RL et al (2014) Status and ecological effects of the world’s largest carnivores. Experimental estimation of snare detectability using mixture models. O’Kelly HJ, Rowcliffe JM, Durant SM et al (2017b). O’Kelly HJ, Rowcliffe JM, Durant SM et al (2017a) Robust estimation of snare prevalence within tropical forests. O’Kelly HJ, Evans TD, Stokes EJ et al (2012) Identifying conservation successes, failures and future opportunities assessing recovery potential of wild ungulates and tigers in Eastern Cambodia. Noss AJ (1998) The impacts of cable snare hunting on wildlife populations in the forests of the Central African Republic. Nijman V (2010) An overview of international wildlife trade from Southeast Asia. Milner-Gulland EJ, Bennett EL (2003) Wild meat: the bigger picture. Lindsey PA, Romañach SS, Tambling CJ et al (2011) Ecological and financial impacts of illegal bushmeat trade in Zimbabwe. Laurance WF, Clements GR, Sloan S et al (2014) A global strategy for road building. Johnson A, Goodrich J, Hansel T et al (2016) To protect or neglect? Design, monitoring, and evaluation of a law enforcement strategy to recover small populations of wild tigers and their prey. Hughes AC (2017b) Global roadless areas: hidden roads. Hughes AC (2017a) Understanding the drivers of Southeast Asian biodiversity loss. Hotte MH, Kolodin IA, Bereznuk S et al (2016) Indicators of success for smart law enforcement in protected areas: a case study for Russian Amur tiger (Panthera tigris altaica) reserves. Harrison RD, Sreekar R, Brodie JF et al (2016) Impacts of hunting on tropical forests in Southeast Asia. Gray TNE, Lynam AJ, Seng T et al (2017b) Wildlife-snaring crisis in Asian forests. Gray TNE, Marx N, Khem N et al (2017a) Holistic management of live animals confiscated from illegal wildlife trade. Gibbs C, Gore M, McGarrell E et al (2010) Introducing conservation criminology: toward interdisciplinary scholarship on environmental crimes and risk. Conserv Lett 2:263–270ĭuangchantrasiri S, Umponjan M, Simcharoen S et al (2015) Dynamics of a low-density tiger population in Southeast Asia in the context of improved law enforcement. Biotropica 39:292–303ĭrury R (2009) Reducing urban demand for wild animals in Vietnam: examining the potential of wildlife farming as a conservation tool. Biol Conserv 143:2808–2814Ĭorlett RT (2007) The impact of hunting on the mammalian fauna of tropical Asian forests. Biol Conserv 174:21–29īrooks EG, Roberton SI, Bell DJ (2010) The conservation impact of commercial wildlife farming of porcupines in Vietnam. Center for Conservation and Government, Conservation International, Washington DCīrook SM, Dudley N, Mahood SP et al (2014) Lessons learned from the loss of a flagship: the extinction of the Javan rhinoceros Rhinoceros sondaicus annamiticus from Vietnam. This must be combined with longer-term demand reduction activities aimed at changing cultural attitudes and behaviors related to the consumption of wildlife products in Southeast Asia.Īkella AS, Cannon JB (2004) Strengthening the weakest links: strategies for improving the enforcement of environmental laws globally, p. Consistent enforcement of such legislation is essential. Legislative reform that criminalises the possession of snares, and the materials used for their construction, inside and immediately adjacent to protected areas is also required. Without the proactive search, arrest and prosecution of snare-setters, along with incentives not to hunt, snares will continue to be replaced. However due to the low opportunity costs of replacing snares, removal alone is largely ineffective. The primary response to snaring is the removal of snares by patrol teams: more than 200,000 snares were removed from just five of the region’s protected areas between 20. Snares are cheaply constructed and easy to set but can be difficult to detect and are highly damaging to vertebrate populations due to their indiscriminate and wasteful nature. Though numerous hunting methods are used, capture with home-made snares is a major driver of this defaunation. Hunting constitutes the greatest current threat to the region’s threatened vertebrates and has resulted in many areas of largely intact forest losing much of their former vertebrate diversity and abundance. Southeast Asia, a region supporting more threatened species than any other comparable continental area, is in the midst of a conservation crisis.
0 Comments
Leave a Reply. |
AuthorWrite something about yourself. No need to be fancy, just an overview. ArchivesCategories |