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Primates in Peril

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Delacour’s Langur<br />

Trachypithecus delacouri (Osgood, 1932)<br />

Vietnam<br />

(2000, 2002, 2004, 2006, 2008, 2010, 2012, 2014)<br />

Tilo Nadler<br />

Delacour’s langur is endemic to Vietnam, occurr<strong>in</strong>g <strong>in</strong><br />

a very restricted area <strong>in</strong> the north of the country that<br />

comprises about 5,000 km² between 20º–20.40ºN and<br />

105º–106ºE. The distribution is closely related to the<br />

limestone mounta<strong>in</strong> ranges <strong>in</strong> the Prov<strong>in</strong>ces N<strong>in</strong>h B<strong>in</strong>h,<br />

Thanh Hoa, Hoa B<strong>in</strong>h and Ha Nam.<br />

Dur<strong>in</strong>g the decades follow<strong>in</strong>g the discovery of Delacour’s<br />

langur <strong>in</strong> 1930 there was only scant <strong>in</strong>formation on its<br />

existence and distribution. In 1987, the first sight<strong>in</strong>gs of<br />

live animals were reported from Cuc Phuong National<br />

Park (Ratajszczak et al. 1990). Intensive surveys by the<br />

Frankfurt Zoological Society <strong>in</strong> the decade before 2000<br />

confirmed 18 completely isolated populations with<br />

a total of 280 to 320 <strong>in</strong>dividuals. Five localities were<br />

found where local people reported that this species had<br />

been extirpated.<br />

Trachypithecus delacouri is listed as Critically<br />

Endangered (Nadler et al. 2008). The most important<br />

factor <strong>in</strong> the decl<strong>in</strong>e <strong>in</strong> numbers is poach<strong>in</strong>g, which is<br />

not primarily for meat, but for bones, organs and tissues<br />

that are used <strong>in</strong> the preparation of traditional medic<strong>in</strong>es.<br />

The recorded numbers of animals hunted over 10 years<br />

Delacour’s langur (Trachypithecus delacouri)<br />

(Illustration: Stephen D. Nash)<br />

53<br />

(1990–1999) totalled 320, an annual loss of more than<br />

30 <strong>in</strong>dividuals, but the real number is undoubtedly<br />

higher (Nadler 2004; Nadler et al. 2003).<br />

Monitor<strong>in</strong>g of selected populations carried out after<br />

2000 shows a cont<strong>in</strong>uously dramatic decl<strong>in</strong>e of some<br />

subpopulations. Two important subpopulations, <strong>in</strong> Cuc<br />

Phuong National Park and Pu Luong Nature Reserve,<br />

decreased <strong>in</strong> numbers by 20% dur<strong>in</strong>g five years (2000-<br />

2004) (Luong Van Hao and Le Trong Dat 2008). The<br />

population <strong>in</strong> Ngoc Son Nature Reserve was extirpated<br />

(Le Trong Dat et al. 2008). Dur<strong>in</strong>g one decade (2000 to<br />

2010) n<strong>in</strong>e subpopulations were eradicated.<br />

Between 2012 and 2015, 20 surveys were carried out<br />

for a status assessment <strong>in</strong> all n<strong>in</strong>e areas with rema<strong>in</strong><strong>in</strong>g<br />

subpopulations. The surveys were organized with major<br />

support from Ocean Park Conservation Foundation,<br />

Hong Kong. The results show aga<strong>in</strong> a further decl<strong>in</strong>e<br />

compared to the last decade. The total number is<br />

estimated at 234-275 <strong>in</strong>dividuals (Nadler 2015). The<br />

majority of the <strong>in</strong>dividuals occurs <strong>in</strong> Van Long Nature<br />

Reserve and comb<strong>in</strong>ed with the population <strong>in</strong> the<br />

adjacent planned extension area the number totals

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