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Posts tagged “Malaysia

ENDANGERED SPECIES MONDAY | SUNDASCIURUS HIPPURUS

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ENDANGERED SPECIES MONDAY | SUNDASCIURUS HIPPURUS

This Mondays (E.S.P) post - [Endangered Species watch Post] I am documenting on the horse tailed squirrel, scientifically identified as Sundasciurus hippurus. (Image: Horse tailed squirrel. Credits: Con Foley)

Listed as [near threatened] the species was first discovered back in 1831 by French Dr Étienne Geoffroy Saint-Hilaire (15 April 1772 – 19 June 1844) who was a French naturalist who established the principle of “unity of composition”. He was a colleague of Jean-Baptiste Lamarck and expanded and defended Lamarck’s evolutionary theories.

Geoffroy’s scientific views had a transcendental flavor (unlike Lamarck’s materialistic views) and were similar to those of German morphologists like Lorenz Oken. He believed in the underlying unity of organismal design, and the possibility of the transmutation of species in time, amassing evidence for his claims through research in comparative anatomy, paleontology, and embryology.

Dr Geoffroy ‘allegedly’ named the squirrel ‘the horse tailed squirrel’ because the squirrels tail resembled that of a horse tail, although even I myself find that somewhat difficult to digest, as in all due honesty the tail looks more like a bushy tail, which horses don’t really host. Horses tend to have long, slender and non-bushy tails, while others do host a type of busy but lose tail. I could be wrong?!

While as yet I cannot prove this, I do believe that Dr Geoffroy may have named the squirrel after a wild dwarf Asiatic horse endemic to South East Asia - that as yet we environmentalists have as yet to discover more about, furthermore that species of horse is likely to be extinct.

Moving on and (as explained) the horse tailed squirrel has been listed as [near threatened]. From 1996-2012 the species was placed into the category of [lower risk/least concern]. Lower risk/least concern is defined as: A taxon is Least Concern when it has been evaluated against the criteria and does not qualify for Critically Endangered, Endangered, Vulnerable or Near Threatened. Widespread and abundant taxa are included in this category.

International Animal Rescue Foundation Asian Environmental Scientists have been studying this species (among others) and can confirm from camera traps that the mammal’s populations are still declining significantly. However to what extent we’re still unsure.

As yet there have been ‘no reported extinctions’ within anyone of the species endemic countries being: Brunei Darussalam; Indonesia (Kalimantan, Sumatera); Malaysia (Peninsular Malaysia, Sabah, Sarawak) and Thailand. Since 2012 environmental fauna scientists have tried in vain to establish a mean population count, unfortunately as yet we (the organisation) and non-related organisations cannot determine a true population count.

Back in 2004 Dr’s Han and Giman pers. comm stated that the species was common, furthermore there was no evidence to prove the species was severely fragmented, or nearing endangered. The species prefers to inhabits lowland forests, however is also located in secondary forests too. Scientists reported that within these secondary forests species populations were on the decline. 

Unlike your normal European squirrel the species can commonly be  located at ground level foraging for food ranging from nuts, fruits, seeds and insects. Interestingly the species is diurnal (again unlike the European squirrel). Diurnal means the species will be active either during the day or night. Whereas the European squirrel is normally pretty active during the daytime, then rests during the night. 

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Image: Horse tailed squirrel: Photographer unknown

While the species ‘often lives within the trees’, horse tailed squirrels will spend a majority of their time at ground level. It has been suggested that one of the reasons for low densities of this species in Malaysian tropical rain forest is competition from the great variety of other arboreal vertebrates (such as birds, and especially primates) for food, especially fruits and leaves, which are among the food items preferred by squirrels. 

There are by few very few threats actually known, however don’t take that as positive news. The species is threatened by habitat loss due to logging and agricultural conversion. I expect the first extinctions are likely to be witnessed within Malaysia (based on past and current research). Malaysian deforestation and palm oil plantations all pose a very high threat to the horse tailed squirrel as well as many other species of flora and fauna. 

Nearly 60% of Malaysia is still covered with natural rain forest, unfortunately much of Malaysia forests are devoted to cash crop plantations, particularly oil palm and rubber, with tree crops occupying 17% of Malaysia’s land area. These are ideally suited to Malaysia’s hot, wet, and humid climate.

While many of us are aware of ‘palm oil devastation’ which is probably by far the biggest threat to a wide number of animals and plants - including the horse tailed squirrel. I would also like to point out to many non-meat and dairy consumers (I.e: Vegans), that while coconut plantations are for now considerably small. These plantations are still being developed and farmed within areas that once saw pristine green forests - now nothing more than a brown churned up heap of land growing and harvesting coconuts too.

In Malaysia, coconut is the fourth important industrial crop after oil palm, rubber and paddy in terms of total planted area. It is also one of the oldest agro-based industries. As an industry, coconut contributes very little to the overall economy of Malaysia (contribution to export earnings of about 0.08% in 2006).

Recent competition with oil palm for land has also resulted in the decline of the total area under coconut cultivation: in 2001, the area was about 151,000 ha and this has gradually decreased to the acreage of 109,185 ha in 2007. Based on the estimates given under the 9th Malaysia Plan, it is anticipated that the acreage will consolidate to around 80,000 ha by 2010. However regardless of this ‘alleged decline’ most if not all coconut plantations are farmed within forests where species such as the horse tailed squirrel is inhabiting

The species is found in several protected areas, including Pasoh Forest Reserve. Environmentalists state the need for further comparative study on this species’ abundance, density and distribution and its relationship to forest structure or habitat quality, spatially and temporally, in hill dipterocarp forest of Malaysia is greatly needed.

For now the future of the horse tailed squirrel is uncertain. I’m doubtful the species will remain extant within Malaysia for much longer - with possible localized extinctions witnessed here soon. More research needs to be undertaken on the species, furthermore we also need to research just how much ‘pristine green forest is being converted for fruit, cereal crops, oils and plant milk crops’ rather than just palm oil. While I find palm oil agriculture incredibly concerning. Knowing that anyone of our vegan, vegetable and fruit crops is originating from areas where animals are being killed - is just as concerning too.

Thank you for reading. 

Dr Jose C. Depre PhD. MEnvSc. BSc(Hons) Botany, PhD(NeuroSci) D.V.M. 

Master of Environmental Botanical & Human Science.

(Environmental, Botanical & Human Scientist). 


Endangered Species Friday - Bos javanicus

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Endangered Species Friday - Bos javanicus

“Thus, the hunting is the proximate cause of decline”

Hunters often demand that we prove to them such a sport or just hunting for food say hasn’t ever pushed a species into nearing extinction or extinction within the wild. The Bos javanicus is under threat from hunters and poachers. (image above - female Banteng)

This Friday’s endangered species article we focus our attention on the Banteng as its commonly known identified back in 1823 by Dr Joseph Wilhelm Eduard d’Alton (August 11, 1772 – May 11, 1840). Mr d’Alton was a German engraver and naturalist who was a native of Aquileia (today part of Italy). He was the father of anatomist Johann Samuel Eduard d’Alton (1803–1854).

He studied in Vienna, and later worked in several locations, including Weimar and Jena. Afterwards he moved to Würzburg, where he worked with embryologist Christian Heinrich Pander (1794–1865). He later taught art history and architectural theory at the University of Bonn, where in 1827 he became a “full professor” of art history. From 1831 to 1840, d’Alton was a member of the Prussian Academy of Arts. One of his famous students in Bonn was Karl Marx. ~Wiki.

The Banteng is listed as (endangered) and is endemic to the countries of Cambodia, Indonesia (Bali, Jawa, Kalimantan), Lao People’s Democratic Republic, Malaysia (Peninsular Malaysia - Regionally Extinct, Sabah), Myanmar, Thailand and lastly Viet Nam.

Unfortunately the species is now known to be “regionally extinct” within the countries of Bangladesh, Brunei Darussalam and India. From 1986 to 1994 the species was listed only as (vulnerable) however, due to mass deforestation, poaching, habitat destruction and unregulated hunting not forgetting increasing human population the species has since been listed as (endangered) from 1996 to 2000.

Recent surveys have since established where localized extinctions have occurred (listed above). Furthermore new observations of this rather unique and stunning wild cattle is still considered to be (endangered) despite new evidence of increasing populations emerging in Thailand.

The species historically occurred throughout China in the Yunnan province. Historical data proves the Banteng was present within the Peninsular Malaysia to the islands of Borneo, Java, and probably Bali (please note that in Bali both domestic and wild cattle are known to coexist).

There is no evidence that the species originated from Bali due to there being no fossil evidence being located thus far. Some “populations” on the island are therefore classified as (domestic) rather than all wild. A point of concern has been noted from Dr Watling that quoted “interbreeding with domestic Bali cattle is a problem and the population is unlikely to consist solely of pure-bred animals”. Dr Wind and Dr Amir had earlier raised similar fears too back in 1977.

The species known to inhabit the island of Bali was introduced and did not originate as explained above.  Furthermore the “domestic” Banteng have been introduced into Sulawesi, Sumbawa, and Sumba. Feral Banteng occur in Kalimantan. Introduced Banteng (probably feral animals) occurs on the Indonesian islands of Enggano (off Sumatra) and Sangihe (off Sulawesi).

Domestic Banteng has also been introduced to New Guinea and Australia and there are now large feral herds in the Northern Territory. One may have noticed in local Australian hunting magazines, online or within farms in the Northern Territory hunters now paying large sums of money to kill and trophy mount the species within their homes. Despite the “wild” populations suffering and nearing extinction little money from such hunting projects is even provided to conservation organisations and local communities to preserve the species within its native habitat.

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Image: Male Banteng Bull (Males are mostly black whereas females are brown)

Wild Banteng are known to live on the island of Bali (please remember not to confuse domestic with wild populations). Furthermore wild Banteng are known to inhabit the island of Java, Kalimantan [Indonesian Borneo], Sabah (although in Sabah extinctions have been noted but not as yet fully confirmed).

A few populations remain in Sarawak however the species is completely extinct within Brunei. Banteng are extinct within Bangladesh and, in India. There are some conflicting reports that the species never even existed within Manipur (northern India - to note).

Extinctions have occurred sadly in Western Malaysia since the 1950’s. southeast Yunnan around Tongbiguan Nature Reserve, along the border with Myanmar; however, the source for this is unclear; and presence in China should be considered tentative at best. Its quite likely the Banteng in China is extinct too however this must not be taken as confirmed. We remain open on this case until further proof is made available of populations being present within the range as explained above.

The species is still wildly inhabiting within Cambodia, Cardamoms Mountain range, with the bulk of the population remaining in the eastern forests, centered on Mondulkiri Province.

The entire “worlds” population is said to be no fewer than 8,000 mature individuals however could be no fewer than 5,000 if that. In Cambodia, Banteng probably declined by 90% . Listed on Cites Appendix II population trends are declining rapidly despite the fact there are some four sub-species and the largest strong hold of sub-populations is on the island of Java.

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Threats

The major threats to Banteng are hunting and habitat loss. In Sabah habitat loss to permanent agriculture is a serious threat, although hunting is equally significant and the species has been rapidly exterminated from many areas there. Habitat loss has also been serious in Java since 1998. Elsewhere, hunting is the most widespread and significant threat, and is exacerbated especially in mainland Southeast Asia by human repopulation of lowland forest areas and associated habitat fragmentation, that is, the very areas where most Bantengs occur.

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Image: Domestic Banteng are hung to death every year within Baojiang, Rongshui, Guangxi China. The ceremony is yet another listed threat to the species as it also includes wild Banteng that the locals “and foreign tourists” consider non-cruel, a tradition that’s been ongoing for over 500 years. Wild Banteng are considered more important than domestic - of which places a considerable threat to the population despite some conflicting evidence that wild Banteng populations and few and little within China. Nevertheless the species is under immense threat.   

Although huge tracts of suitable habitat were lost in the twentieth century, and continue to be converted, this has probably largely occurred after Banteng have been hunted out. Thus, the hunting is the proximate cause of decline, but habitat loss is continually reducing the maximum population possible if hunting issues were to be controlled.

The magnitude of the threat posed to Banteng by international trade in trophy horns is difficult to quantify. Nevertheless, given the small size of the remaining Banteng population and the number of trophies found for sale in Cambodia, the Lao PDR, Thailand, and Viet Nam, during what were essentially opportunistic surveys, it is clearly a major threat on the Asian mainland. The threat posed by use of traditional medicinal substances derived from wild oxen is even harder to determine in the case of Banteng and essentially remains unknown, although it is thought to be a source of significant threat to Gaur.

The most important population in Cambodia is scattered through a forest landscape that encompasses four provinces (Mondulkiri, Kratie, Stung Treng and Ratanakiri) and five conservation areas (Lomphat Wildlife Sanctuary, Phnom Prich Wildlife Sanctuary, Siema Biodiversity Conservation Area, Mondulkiri Protection Forest (including the Srepok Wilderness Area) and Phnom Nam Lyr Wildlife Sanctuary).

Hunting is still rife in much of this area, and forest fragmentation is rapidly accelerating with human population in-migration, infrastructural developments (especially roads), commercial agricultural expansion, economic land speculation and mineral extraction. However, although perhaps less than 20% of this area is well protected from the aforementioned threats and protected area management is only close to effective in two areas, the most significant issue concerning the area is the long-term uncertainty of continuation of effective conservation management of the Srepok Wilderness Area and Siema Biodiversity Conservation Area.

Although conservation efforts for Banteng and many other species have been, in both areas, extremely encouraging for the last few years, both areas face an uncertain future with the possibility of de-gazettment of conservation status of parts of them, the possible loss of adequate external funding necessary to maintain high standards of management, the possible loss of political support necessary to uphold high protection standards and the uncertainties of maintaining a motivated and well-trained staff.

On Java some populations are potentially threatened by heavy predation from Dholes Cuon alphinus (a species I spoke about this Monday). All populations are also threatened by poaching and some, perhaps most, are threatened by habitat loss and degradation. During the 1980s–1990s, when poaching and land conversion were relatively well under control in Javan national parks, the chief threat to the large population of Banteng in Baluran National Park was loss of grazing area to invasion by the introduced tree Acacia nilotica (Leguminosae) that converts open grassland to dense thorny scrub-forest.

Banteng-Hunting - Click to view more.

Image: Introduced into Australia in the last century the species is hunted for sport despite the species being listed as endangered within its native range - very little money is raised for preservation of the species within Australasia. Hunting remains outside of Australia as the major number number one threat pushing the species and sub-species into more decline. 

This plant was introduced (without adequate risk assessment) as part of an attempt to create a living fire-break around the park’s grasslands, wild fire then being adjudged the major threat to the park’s monsoon forests. Since that introduction, repeated cutting of the acacia has led to coppicing into very dense thickets that contain little or no grass or other herbs and are difficult for the cattle to penetrate. Thus habitat loss and poaching are now serious limiting factors in Baluran National Park, and habitat loss/degradation remains a severe long-term threat to be addressed. Lantana camara (Verbenaceae) is also a problem in Banteng habitat in Baluran National Park and elsewhere on Java.

Bali cattle have long been interbred with other cattle: Banteng and Bali cattle can interbreed with both common cattle and mithan (Bos frontalis). Hybrids between Banteng and common cattle (Bos Taurus) of the zebu type are fully fertile; in hybrids between Banteng and Bos Taurus of the European type the males are sterile. Domestic and feral livestock are thus a potential threat to the genetic integrity of wild Banteng populations and a number of reports suggest that wild Banteng does interbreed with domestic cattle.

For example, Hoogerwerf (1970) referred to several sources from the 1930s and 1940s which mention that many groups of Banteng in Kalimantan (particularly East Kalimantan) were no longer pure-bred having interbred with stray domestic cattle. Wharton (1957) also found evidence of interbreeding with domestic cattle in Cambodia; and reports from Myanmar mention that Banteng feed alongside village cattle and occasionally interbreed with them.

In addition to the genetic threat, domestic livestock are a potential source of diseases and parasites. This can have very serious consequences for Banteng which appear to be particularly susceptible to a number of cattle diseases; for example, Banteng populations in Myanmar have been very badly affected by diseases from domestic cattle.

Introgression with domestic cattle is not presently an issue in Sabah; there have been imports of Bali cattle mostly by large cattle farms who house animals in feedlots away from wild populations. Ahmad AH is unaware of any instances of deliberate introduction of Bali cattle or other domestic oxen into forest areas, or of any plantation holders that have deliberately introduced their cattle into the range of wild Banteng. Although integration of livestock into oil palm plantation has been discussed for many years, this has not yet been put into practice.

In all due respects its quite likely were going to lose the species due to unregulated hunting, controlled over hunting, poaching, traditional medicine trade, habitat destruction and fragmentation, land conversion and agriculture.

Video: Female Banteng

Thank you for reading.

 

Dr Jose C. Depre

info@international-animalrescue-foundation.org.uk

With thanks and much appreciation to the Environmental Team at - International Animal Rescue Foundation Asia.