southeast asia’s biodiversity, post 2015: what is at stake?

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THINKING beyond the canopy THINKING beyond the canopy Southeast Asia’s Biodiversity, Post 2015: What is at stake? Terry Sunderland, Principal Scientist Enhancing and Promoting the Real Values of Tropical Biodiversity of Southeast Asia BIOTROP October 4 th 2013 IPB Convention Centre, Bogor

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This presentation by Terry Sunderland from CIFOR focuses on the value of biodiversity in Southeast Asia, what role protected areas play, what the drivers of change are, wildlife trade, food security, the segregation of land use and how multi-functionality can be achieved.

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Page 1: Southeast Asia’s Biodiversity, Post 2015: What is at stake?

THINKING beyond the canopy THINKING beyond the canopy

Southeast Asia’s Biodiversity, Post 2015:

What is at stake?

Terry Sunderland, Principal Scientist Enhancing and Promoting the Real Values of Tropical Biodiversity of Southeast Asia BIOTROP October 4th 2013 IPB Convention Centre, Bogor

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Context •  SE Asia: biodiversity “hot spots” •  Yet has the highest relative rate of

deforestation in the tropics •  Major drivers include illegal logging,

conversion to agriculture, the wildlife trade etc.

•  Future for Asia’s biodiversity look bleak for many reasons (population growth, changing demographics)

•  Other challenges: achieving food security •  What role for research??

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Global biodiversity hot spots

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The current state of biodiversityThree plant and eight animal species have been listed as‘extinct’ in Southeast Asia by the International Union forthe Conservation of Nature and Natural Resources(IUCN) [12]. Because Southeast Asia has a fairly recenthistory of large-scale deforestation (i.e. over the past twocenturies), many of the native species of the region, suchas rare long-lived trees, might be persisting as ‘living dead’and are doomed to extinction owing to isolation caused bythe fragmentation of habitats [3]. Therefore, although theactual number of extinct species in the region is notpresently alarming, the level of endangerment of extantspecies reveals the seriousness of threats, such asdeforestation, that are faced by the regional biota. Thenumber of threatened species in Southeast Asia, includingthose in the IUCN categories of ‘critically endangered’(CE), ‘endangered’ (EN) and ‘vulnerable’ (VU) ranges from20 (CE) to 686 (VU) species for vascular plants, six to 91species for fish, zero to 23 species for amphibians, four to28 species for reptiles, seven to 116 species for birds, andfive to 147 species for mammals (see Online Supplemen-tary Material) [12]. The loss of many of these regionalpopulations is likely to result in global extinctions because

of the high proportion of endemic species (Figure 1; seeOnline Supplementary Material) [13]. For example,59.6% of the 29 375 vascular plant species in Indonesiado not occur anywhere else (see Online SupplementaryMaterial) [13].

Drivers of biodiversity threatHere, we discuss the drivers of biodiversity loss andendangerment in Southeast Asia, which might act eitheralone or in concert.

Forest conversionThe conversion of natural habitat to other land uses is themajor driving force behind worldwide biodiversity loss[14–17]. Most of Southeast Asia was under forest cover8000 years ago (see Online Supplementary Material) [18],but large-scale deforestation in the region began duringthe 1800s as a result of agricultural expansion that wasneeded to meet the increasing local and global demand forrice Oryza sativa [19]. The planting of perennial exportcrops, including rubberHevea brasiliensis, oil palm Elaeisguineensis and coconut Cocos nucifera, also accounted for20–30% of the total cultivated area of the region [19]. After

Figure 1. Species richness and endemism in Southeast Asia. The four biodiversity hotspots overlapping Southeast Asia are highlighted in red. Bars represent the percentageof species endemic to the respective hotspot. Numbers in parentheses represent total and endemic species known to science, respectively. The island of Borneo includes thepolitical divisions of Brunei, Malaysia and Indonesia. The Indo-Burma hotspot includes part of Bhutan, Nepal, eastern India, southern China, as well as islands suchas Hainan and the Andamans. Details of biodiversity hotspot boundaries, and numbers of total and endemic species within each hotspot were taken fromConservation International [74].

Review TRENDS in Ecology and Evolution Vol.19 No.12 December 2004 655

www.sciencedirect.com

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Biodiversity under threat

of the Convention on International Trade in EndangeredSpecies (CITES) in 1970 and having been protected inIndonesia since 1971, 19 individuals were observed beingsold illicitly in shops in Singapore in 1979 and 16individuals were observed in cages in Denpasar (Bali,Indonesia) in 1982 [54].

Many animal and plant products are used in traditionalChinese medicine, which dates back 5000 years. Trade inthe raw materials of traditional Chinese medicine has adetrimental impact on many vertebrates in SoutheastAsia, including tigers, bears, rhinos, turtles, snakes, tokaygeckos, pangolins, monkeys and swiftlets [5]. This isexemplified by the Sumatran tiger Panthera tigrissumatrae, from which body parts such as bones andpenises are used in traditional medicine. Between 1975

and 1992, South Korea imported 6128 kg of tiger bones(340 kg yK1), of which 60% originated from Indonesia [55].The demand for the Sumatran tiger continues to threatenthe remaining wild population of an estimated 500individuals [56].

Other potential driversSala et al. [14] showed that, relative to the overwhelmingimpact of forest conversion, other drivers, such as climatechange, nitrogen deposition, invasive species and atmos-pheric CO2 change, are not expected to have significanteffects on biodiversity in tropical terrestrial ecosystems.Climate change was shown to have the largest pro-portional effect on biodiversity in extreme environments,such as the arctic and boreal zones, and the least effect in

Box 1. Singapore case study: a recipe for disaster

From both a scientific and management perspective, it would beinformative if we could excise hypothetically a representative South-east Asian site, allow it to fulfil its economic potential, and documentthe consequent losses of natural habitats and biodiversity, all within agreatly accelerated time frame. Perhaps it is both depressing andfortunate that Singapore is one such ecological ‘worst case scenario’.

Singapore has experienced exponential population growth, fromw150 subsistence-economy villagers in the early 1800s to four millionpeople in 2002 [13,72]. In particular, Singapore has transformed itselffrom a developing country of squatters and slums to a developedmetropolis of economic prosperity within the past few decades and,thus, has been widely regarded by the leaders of regional developingcountries as the ideal economic model.

However, the success of Singapore came with a hefty price, paidfor by its biodiversity. The island has suffered massive

deforestation (O95%), initially from the cultivation of short-termcash crops (e.g. gambier Uncaria gambir and rubber Heveabrasiliensis) and subsequently from urbanization and industrializ-ation [72]. A recent study by Brook et al. [3] showed substantialrates of documented (observed) and inferred (based on what couldhave occurred in Singapore before habitat loss) extinctions, withmost extinct taxa (34–87%) being species of butterflies, fish, birdsand mammals (Figure I). Similar environmental scenarios arealready unfolding on a much larger scale in other SoutheastAsian countries, such as Indonesia [73]. Extrapolations based onthe species–area model calibrated to the biodiversity losses inSingapore indicate that the current rate of habitat destruction inSoutheast Asia will result in the loss of 13–42% of regionalpopulations of all species by 2100, at least half of which couldrepresent global species extinctions (Figure I) [3].

Figure I. Population extinctions in Singapore and Southeast Asia. Green and blue bars represent recorded and inferred extinctions in Singapore, respectively. Yellow andred bars represent minimum and maximum projected extinctions in Southeast Asia, respectively.

Review TRENDS in Ecology and Evolution Vol.19 No.12 December 2004 657

www.sciencedirect.com

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Protected areas?

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Drivers of change: logging

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Drivers of change: agriculture

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Oil palm expansion and forest loss

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A green desert

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Wildlife trade

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Food security

•  Changing demographics

•  Changing appetites •  How to grow enough

nutritious food for future populations without compromising environmental outcomes?

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Segregation of land use is the norm

Plantation Forest

Agriculture

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Land sparing/sharing within landscapes

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Multi-functionality •  Combination of separate

land units with different functions (spatial segregation)

•  Different functions on the same unit of land but separated in time (temporal segregation)

•  Different functions on the same unit of land at the same time (functional integration or “real multi-functionality)

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Landscape assessment for development

•  Collecting economic data at various levels, engaging most stakeholders

•  Spatial data: administrative boundaries, land cover change and current land uses

•  “Governance landscape” including local (traditional) institutions

•  Focus on ecosystem services and agricultural productivity and away from protected areas alone

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The role of research

•  Biodiversity research in SE Asia has lagged behind rest of the tropics

•  Distribution of research is taxonomically biased (e.g. emphasis on mammals)

•  Integrated research looking at socio-economic factors greatly needed

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How are we doing?

The MDG’s

What hope for the SDG’s post-2015??

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The environment: more than $$ alone!

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The Center for International Forestry Research (CIFOR) is one of the 15 centres supported by the Consultative Group on International Agricultural Research (CGIAR)