ORYX VOL 28 NO 3 JULY 1994 A last chance for National Park - local industry support for conservation

Kathy MacKinnon, Alan Irving and Memet A. Bachruddin

Kutai National Park in was originally established as a game reserve in 1936 and became a national park in 1982. The park's lowland forests have suffered from logging, agricultural encroachment and extensive fires during the prolonged dry season in 1982 and 1983. During the 1980s a new coal mine opened at Sangatta to exploit rich coal deposits along the northern boundary of the park. The new mine could have been the 'last straw' for Kutai. Instead, industrial development has provided a new and exciting opportunity to strengthen park protection and management.

Introduction such as Sumatran rhino Dicerorhinus sumatren- sis, * and orang-utan (Cockburn and Kutai National Park encompasses 2000 sq km Sumardja, 1979). The original reserve ex- of lowland rain forests, 90 km north of tended over 3060 sq km but in 1969 1000 sq in the province of East Kalimantan, km in the eastern coastal area were excised for Indonesian . East Kalimantan is the sec- oil exploitation and logging. The logging was ond largest province in and covers stopped in 1971 and the logged-over forest an area of 202,440 sq km, yet supports a popu- was restored to the reserve. Shortly afterwards lation of only 1.9 million people (Hull, 1991). It another 1060 sq km of pristine rain forest and might be expected that the low population some previously logged coastal forest were ex- density would have ensured that the province cised from the southern part of the reserve remained one great wilderness area, un- and allocated to the PT Kayu Mas Timber touched by human influence. This is far from Concession and two natural gas industries, PT the case. East Kalimantan is rich in natural re- Badak and PT Pupuk Kaltim (Wirawan, 1985). sources, especially oil and gas, timber and By 1980 the reserve area included logged coal, all of which are being exploited on a coastal forest, unlogged forest in the west large scale. The province accounts for 25 per (which was further disturbed by logging in- cent of the country's timber export revenues cursions within the southern boundary), and (Repetto and Gillis, 1988). Even gazetted pro- some coastal . The eastern third of tected areas like Kutai have not escaped un- the reserve, along the coast, was already badly scathed from these developments (MacKinnon, disturbed by logging, oil developments, the 1990). expansion of and Sangatta townships and ladang (agricultural fields) created by new settlers. To compensate for these areas, pro- History of the park posals were made to realign and enlarge re- serve boundaries to include the Banumuda catchment area in the north and the PT Kayu Kutai was the first protected area to be estab- Mas and PT Sylva Duta logging concessions in lished in Kalimantan (Petocz et al, 1990). the south and west (Cockburn and Sumardja, Originally proposed as an area of 2 million 1979; Wirawan, 1985). These proposals have hectares by the Dutch geologist Witkamp, the Kutai area was declared a game reserve in 1936 by the Sultan of Kutai to protect species * Scientific names of species are found in Table 1. 191

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Fertilizer plant Bontang LNG plant

Boundaries of the reserve:

As proposed by o Witkamp (1932) As proposed by Cockburn o and Sumardjo (1979) Current Boundary

As decreed by sultan of Kutai (1936) and confirmed o by Minister of Agriculture New Highway -——(Bontang-Sangatta- )

0 10 20 30 40 km

Figure 1. Kutai National Park: historical development

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not yet been implemented. Figure 1 shows the ging concessions. Kutai National Park is one past, proposed and current park boundaries of the few areas in Kalimantan where lowland and the location of major industries. tropical rain forest can still be conserved. The Government of Indonesia announced These are the most species-rich forests in the that Kutai would become one of Indonesia's world, with as many as 240 different species first national parks at the Third World of trees growing in 1.5 hectares of forest National Parks Congress in Bali 1982. The (Kartawinata et ah, 1981). 2000-sq-km park includes part of the original Kutai is recognized as a centre of biodiver- Kutai Wildlife Reserve. sity (BAPPENAS, 1991). The park's high bio- In 1982/83 fire swept through Kutai during logical value is a consequence of the species an abnormal drought and destroyed large richness of lowland forests and the fact that areas of forest (Lennertz and Panzer, 1983; the park includes a wide spectrum of lowland Leighton and Wirawan, 1986). The areas forest habitats: alluvial forests, dipterocarp where logging had already occurred were forests, ironwood stands, kerangas (heath for- damaged more severely than the undisturbed est), freshwater swamp forests, forest because the advancing fire fed on dead and limestone hills with caves (Cockburn and trees and other debris left behind after log- Sumardja, 1979; Wirawan, 1985). Floristically ging. About half the park, some 1000 sq km of Kutai is very rich, with more than 500 species lowland forest in the west, escaped the fire but of trees, including at least 20 species of dip- even here the drought killed many old emerg- terocarps, the valuable ironwood Eusideroxylon ent trees. In 1984 the IUCN (International zwageri and wild fruit trees such as durians Union for Conservation of Nature and Natural Durio spp., mango Mangifera spp. and man- Resources) included Kutai National Park in its gosteen Garcinia mangostana (Wirawan, 1985). list of most threatened protected areas because In addition, Kutai is rich in palms (including of damage caused by fire, logging, mineral ex- spiny rattans), orchids and pitcher plants ploitation and human settlement (IUCN, Nepenthes spp. 1985). Since that time encroachment and agri- The park supports a rich fauna. Half of all cultural clearance have continued to degrade Bornean mammals are recorded from the re- the eastern part of the park. serve, including 16 of the 43 mammal species endemic to the island (MacKinnon, 1990). All but two of the 13 species of primates found in Biological and environmental values of Borneo occur here, including five island en- the park demics: the , Bornean gib- bon, red langur or leaf monkey, grey langur In spite of its unfortunate history Kutai is still and white-fronted langur. The park also con- an important conservation area and has been tains viable populations of several endangered recognized as such in several major reviews of species: orang-utan, banteng and clouded conservation in Indonesia (MacKinnon and leopard (Table 1). Indeed, Kutai is the largest Artha, 1981; MacKinnon and MacKinnon, gazetted reserve within the home range of the 1986; Petocz, 1987; RePPProT, 1990; MoF, Bornean subspecies of the orang-utan. Kutai is 1991; BAPPENAS, 1991). It encompasses the known to harbour 275 species of birds largest remaining tracts of the lowland rain (Pearson, 1975), more than half the Bornean forests and ironwood forests that were once list (Smythies, 1981), and 3 per cent of the en- typical of East Kalimantan. tire world total. The coastal mangrove fringe Borneo is a centre of diversity for diptero- harbours populations of saltwater crocodiles carps, with 267 species, 155 of them unique to and false gharials. this island (Ashton, 1988). Kalimantan forests In addition to its value for species conser- are dominated by dipterocarps, some of the vation, the park provides important environ- most valuable timber trees in South East Asia, mental services to surrounding areas. It and most lowland forests are given out as log- protects the natural aquifer that supplies vital ORYX VOL 28 NO 3 JULY 1994 193

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RDB Table 1. Some rare and Species English name Endemic Status endangered animal species in Kutai National Park

Mammals Pongo pygmaeus Orang-utan * E Hylobates muelleri Bornean gibbon * V Nasalis larvatus Proboscis monkey * V Presbytis rubicunda Red langur * Presbytis hosei Grey langur * Presbytis frontata White-fronted langur * Tarsius bancanus Western tarsier I Tupaia splendidula Ruddy tree shrew * Callosciurus orestes Black-banded squirrel * Sundasciurus brookei Brooke's squirrel * Exilisciurus exilis Plain pigmy squirrel * Aeromys thomasi Thomas's flying squirrel * Hystrix crassispinis Thick-spined porcupine * Maxomys ochraceiventer Spiny rat * Haeromys pusillus Lesser ranee mouse * Haeromys margarettae Ranee mouse * Chiropodomys muroides Grey-bellied pencil-tailed tree mouse * Neofelis nebulosa Clouded leopard V Felis marmorata V Felis planiceps Flat-headed cat V Bos javanicus Banteng V Muntiacus atherodes Yellow muntjak * Birds Lonchura fuscans Dusky munia * Pityriasis gymnocephala Bornean bristlehead * Ptilocichla leucogrammica Bornean wren babbler * Lophura ignita Crested fireback V Aceros corrugatus Wrinkled hornbill R Rhinoplax vigil Helmeted hornbill K Reptiles Crocodylus porosus Saltwater crocodile V Totnistoma schlegelii False gharial E

Red Data Book Status: E, endangered; V, vulnerable; R, rare; I, indeterminate; K, insufficiently known

Sources: Wirawan, 1985; IUCN, 1990; Indonesian Red Data Book (in prep.)

freshwater supplies for domestic and indus- park is also dependent on park sources for ad- trial use to the towns of Bontang and Sangatta equate water supplies. and their natural gas and oil industries (Wirawan, 1985). The two natural-gas indus- tries in Bontang require 30,000^0,000 cu. m of A need for action ground water daily; the sustainability of this supply depends on maintaining adequate for- Recognizing the important biological and en- est cover in the park (MoF/PHPA, 1991). The vironmental values of Kutai National Park, new Sangatta coal mine to the north of the the World Wide Fund for Nature (WWF)

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assisted the park management authority, the exciting new conservation initiative, Kaltim Directorate of Forest Protection and Nature Prima Coal (KPC) and other industrial firms Conservation (PHPA), to produce two man- working around the park have expressed an agement plans for the park (Cockburn and interest in developing a partnership between Sumardja, 1979; Wirawan, 1985). Unfortunately, PHPA and the private sector to conserve even though there was strong provincial sup- Kutai. port for the plans, neither was implemented due to lack of funds and other resources. Although the Kutai forests are slowly recov- Coal mining development: a threat or an ering from the ravages of logging and fire, the opportunity park is threatened by other development pressures. East Kalimantan has the highest In the late 1970s the government of Indonesia population growth rate in Indonesia (Hull, adopted a policy aimed at substituting coal for 1991) and the expanding towns of Bontang oil as fuel for electricity generation. South and and Sangatta are encroaching on reserve East Kalimantan were known to have poten- boundaries. Bontang, already one of the tially large Tertiary coal deposits and foreign fastest growing towns in Indonesia, is set to companies were invited to tender for areas in expand further due to an expansion of PT which to carry out exploration. By late 1982 Badak's natural-gas liquefaction plant. The six companies had signed Coal Co-operation newly opened coal mine near Sangatta will ul- Agreements, covering a total area of 40,000 sq timately have a work-force of 2300 people, km, with the state mining company. plus families and support staff. The Trans- PT Kaltim Prima Coal, an Indonesian-regis- Kalimantan Highway is being extended from tered company that is jointly owned by CRA Bontang to Sangatta and will cut through the Ltd (Australia) and the British Petroleum park, opening up new lands to shifting culti- Company (UK), was granted a 7900-sq-km vators. Already much of the land in the coastal concession between Samarinda and zone of the park has been settled illegally and Sangkulirang, 200 km to the north. The Kutai converted to agriculture (MacKinnon, 1990; Wildlife Reserve, as it then was, and an area to Petocz et ah, 1990). the south between the reserve's southern Nevertheless, there is a new mood of opti- boundary and the Santan River [part of the ex- mism for the future of Kutai. The provincial tension proposed by Cockburn and Sumardja government has long appreciated the value of (1979)] were specifically excluded from the the park, not only for its role in protecting concession because of their high biological natural resources, but as a valuable water- and conservation values. Coal exploration by shed, safeguarding the water supplies essen- another group has recently been permitted in tial to the industries of Bontang. Development the Santan area. of the new road has acted as a stimulus to re- KPC's exploration activities resulted in the assess the park's status and provides an op- discovery of high-quality thermal coal in an portunity to develop the area's potential for area just north of the Sangatta River, the tourism, with visitor facilities and field posts northern boundary of the park. A feasibility along its route (Petocz et ah, 1990). Plans are in study found that the resources would support preparation for better protection of the un- a large-scale export operation and the decision burned western sector of the park and the to proceed with the required investment was coastal mangroves. The severely disturbed taken in late 1988. Mining is by conventional agricultural lands between the road and the open-pit methods and production is sched- coast will be developed as a buffer zone to the uled to rise from 2 million tonnes in 1991 to 7 park proper (Petocz et ah, 1990; MoF/PHPA, million tonnes per year from 1994 onwards. 1991). These activities will require consider- Resources exist for a 30-year mine life. At full able funds and effort but encouragement and operation a work-force of 2300 people will be support is coming from new quarters. In an directly employed by KPC. Their families, to-

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gether with people in the service and retail itiative that combined the resources of local sectors, are expected to total about 10,000 ad- industry and the international donor com- ditional people. KPC houses the large majority munity to help the PHPA attain a high level of of its own employees in planned and fully ser- managerial capability to run the park success- viced residential areas within the company's fully. lease but a large number of other newcomers The KPC's first step was to talk to the have occupied land between the KPC lease Conservation Department authorities (PHPA) boundary and the park boundary (in an area in Kutai and Jakarta and relevant regional known as Teluk Lingga). Aware of the in- agencies, such as the Regional Planning Board creased pressure that development of the (BAPPEDA), and gauge their reaction. This mine and increased settlement will put on the was encouraging and KPC funded a prepara- park, the KPC management determined to tory mission (Petocz et al., 1990) and later a play the role of helpful neighbour to the park. formulation mission to work with PHPA to: (i) review existing documentation about Kutai; (ii) prioritize conservation activities and needs Local industries as park neighbours and for immediate implementation; and (iii) pre- friends pare a 5-year development plan and first-year operating plan, as well as a general frame- Within their own sphere of operation, the work for management and development. large gas, oil and coal industries can manage These KPC-sponsored teams comprised mem- their environmental impacts. For example, bers from the PHPA, the WWF-Indonesia KPC follows environmental monitoring and Programme and Dutch technical expertise environmental management plans designed to from Euroconsult, the Research Institute for minimize the impact of large-scale mining and Nature Management (the Netherlands) and associated activities. However, the company is the Research Institute for Forestry and Urban fully aware that its activities for many years to Ecology (the Netherlands). The Formulation come could entail certain risks to the conser- Mission's report (MoF/PHPA, 1991) was en- vation and fauna of the park. KPC manages its dorsed by the Director General of PHPA in own employees, for example by including a September 1991. During the two missions, clause in labour contracts that enables the dis- KPC representatives were also establishing missal of employees who violate park regu- contact with potential international donors. lations. Nevertheless, other newcomers in the Other local industries neighbouring the park, unplanned communities pose a threat to the in particular PNG Bontang (natural gas) and park should they turn to hunting, timber- Pupuk Kaltim (fertilizer), also agreed to help, felling or farming activities within the park. initially by providing a camping ground and Disturbance along the new Bontang-Sangatta other facilities. road corridor caused by spontaneous immi- grants and settlements would be a threat to the park and is incompatible with its status as The plans a protected area. Given the development surrounding the The MoF/PHPA (1991) report contains pro- park, the new internal road, and the inad- posals for 17 projects, which consider the equate human and material resources of the park's needs in the areas of conservation man- park management authority, KPC concluded agement, estate management, recreation man- that the park faced a dire future if constructive agement, training, extension and public measures were not taken quickly. Co-ordi- relations. Each project is justified and de- nated support from some of the park's indus- scribed in terms of duration, objectives, activi- trial neighbours seemed essential to provide a ties, outputs, location, inputs (technical, sound basis for the long-term management of staffing, material, financial, schedule, monitor- the protected area. KPC saw scope for an in- ing and evaluation, implementing agency and

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potential donor). First and foremost are gen- management (8), recreation management (2), eral projects, which together constitute the extension and public awareness programmes first-year Operating Plan. Of these, the pri- (1), and training (1) are described in the mary one is the installation of a Steering Action Plan. Potential donors will have the Committee (SC) and the appointment of an opportunity to target their assistance to pro- Operating Committee (OC) for the implemen- posals that appeal to them. For example, a tation of approved projects. The SC will con- buffer zone development project next to a par- sist of representatives from PHP A, provincial ticular industrial activity would be more likely and regional government, managing directors to attract funding and involvement from the of local industries, and representatives from industry concerned than a more distant proj- other donors. The OC is envisaged as a small ect. Similarly, proposals for extension activi- group comprising senior PHPA representa- ties and training may best meet the objectives tives, technical and financial specialists, and of potential international donors. major donors. The OC will have authority and One interesting project proposal is for low- responsibility within the budget to implement land forest restoration plantings in the zone projects and will make quarterly progress re- between the coastal mangrove belt and the un- ports to the SC and donors. dulating hills further inland. This area sup- The other crucial first-year projects are: (i) ported a unique forest type but has been the provision of management advice; (ii) the prime target of agricultural settlers. Some 40 analysis of aerial photography of the park and sq km require reforestation in order to stimu- land-use for management planning purposes; late vegetation succession towards a closed (iii) boundary establishment and guard-post dipterocarp-dominated forest. The succession construction; and (iv) management of the process will be slow, but the restoration of a Bontang road corridor. A senior national large area of cleared and degraded forest to a parks advisor is required to update the man- quasi-natural state within this protected area agement plan, provide training for park plan- will be highly beneficial from an ecological ning and management, and provide advice on point of view. A potential donor for this proj- work plans, administration, financial manage- ect was identified in 1992 - the Dutch ment, fund-raising and external relations. Association of Electricity-producing Companies Aerial photography is an essential prerequi- (SEP) through its Forests Absorbing Carbon- site for future planning and management pur- dioxide Emission (FACE) foundation. The poses and boundary demarcation is essential source of funds for FACE is tax on some in- for protection. If left unchecked, settlement dustrial carbon dioxide producers in the will spontaneously follow the construction of Netherlands. It seemed highly appropriate to the Bontang-Sangatta road throughout its direct some of these funds to reforestation in- length. Park resources must be supplemented side a protected area in a coal-producing to be sufficient to mount regular mobile pa- province of Indonesia. trols to control encroachment. The costs of im- In early 1992 the future looked promising plementing the first-year Operating Plan total for Kutai. Large sums of money were almost $US700,000. Funds for these initial ac- promised from the Netherlands: a happy end- tivities will probably come from industry and ing seemed assured. Then politics intervened. international donors. A Dutch minister made one criticism too The 5-year Development Plan is aimed at many. Indonesia declined all further assist- achieving the following objectives: (i) main- ance from the Netherlands and terminated on- tenance of biological values of the park; (ii) going aid projects. Attempts are still being restoration of ecological integrity where made to identify other international donors necessary; (iii) accommodation and control of for Kutai. visitors; and (iv) control of access to the park The anticipated cost of the planning and im- from public and corporate facilities. Twelve plementation phases of the 12 proposed pro- project proposals, which cover conservation jects in the 5-year Development Plan is in the ORYX VOL 28 NO 3 JULY 1994 197

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order of $US8.5 million. Whether such funds drought and fire in Borneo tropical rainforest as- can be attracted remains to be seen, but sociated with the 1982-1983 El-Nino Southern progress is not dependent on all projects being Oscillation Event. In Tropical Rain Forests and the World Atmosphere. AAAS Symposium, 101. fully funded from the outset. It is hoped that Westbury Press, Boulder. once support starts to accumulate it will Lennertz, R. and Panzer, K.F. 1983. Preliminary gather momentum. Assessment of the Drought and Forest Fire Damage in Kalimantan Timur. Transmigration Areas Develop- ment Project, German Agency for International Conclusion Cooperation (GTZ). MacKinnon, J.R. and Artha, B. 1981. National Conservation Plan for Indonesia. Vol. V: Kalimantan. Kutai National Park has been recognized both FO/INS/78/061 Field Report, FAO, Bogor. nationally and internationally as a park of MacKinnon, J.R. and MacKinnon, K.S. 1986. Review high biodiversity and global conservation im- of the Protected Areas System in the Indo-Malayan portance. Nevertheless, with limited resources Realm. IUCN, Gland, Switzerland. 284 pp. and increasing pressures on park lands, the MacKinnon, K. 1990. Kutai National Park. Voice of future of the park has, at times, looked uncer- Nature, 80, April. tain. Now the park's neighbours, the firms re- MoF. 1991. Indonesian Tropical Forestry Action Plan. 3 vols. (Second draft). Ministry of Forestry, Jakarta. sponsible for much of the province's economic MoF/PHPA. 1991. Kutai National Park, Kalimantan development, are turning their attention to Timur, Indonesia. Development Plan 1992—1996; conservation. With friends in industry and Operating Plan 1992. Ministry of Forestry/ local government, Kutai could still reclaim its Directorate General of Forest Protection and rightful role as one of the most important con- Nature Conservation, Jakarta. servation areas in Kalimantan. The Kutai in- Pearson, D.L. 1975. A preliminary survey of the itiative was the first example of private birds of the Kutai Reserve, Kalimantan Timur, industry assisting PHPA with conservation Indonesia. Treubia, 28(4), 151-162. Petocz, R. 1987. Conservation in Indonesia: Current and management, an exciting innovation that Status and Development of an Action Strategy. is likely to be repeated elsewhere in Indonesia. Report to World Bank. Petocz, R., Wirawan, N. and MacKinnon, K. 1990. The Kutai National Park, Planning for Action. WWF, References Bogor. Ashton, P. 1988. Dipterocarp biology as a window Repetto, R. and Gillis. M. (eds). 1988. Public Policies and the Misuse of Forest Resources. Cambridge to the understanding of tropical forest structure. University Press. Ann. Rev. Ecol. Syst. 19,347-70. BAPPENAS, 1991. Biodiversity Action Plan for RePPProT, 1990. The Land Resources of Indonesia. ODA/Ministry of Transmigration. Indonesia. Government of Indonesia. Cockburn, P. and Sumardja, E. 1979. Proposed Smythies, B.E. 1981. The Birds of Borneo, 3rd edn. The Management Plan for Kutai Nature Reserve, East Sabah Society and the Malayan Nature Society, Kuala Lumpur. 473 pp. Kalimantan. WWF, Bogor. Hull, T.H. 1991. Population growth rates falling in Wirawan, N. 1985. Kutai National Park, Management Plan 1985-1990. WWF, Bogor. Indonesia: preliminary results of the 1990 census. Bull. Indon. Econ. Studies, 27(2), 137-142. IUCN, 1985. Threatened natural areas, plants and Kathy MacKinnon, former Conservation Advisor, animals of the world. Parks, 10(1), 15-17. WWF Indonesia Programme. Address for corre- IUCN, 1990. IUCN Red List of Threatened Animals. spondence: Herewake, 86 Aldreth Road, IUCN, Gland, Switzerland. Haddenham, Near Ely, Cambs CB6 3PN, UK. Kartawinata, K., Abdulhadi, R. and Partomihardjo, Alan Irving, Kaltim Prima Coal, PO Box 718 Kby, T. 1981. Composition and structure of a lowland Jakarta 12001, Indonesia. dipterocarp forest at Wanariset, East Kalimantan. Memet A. Bachruddin, D-G PHPA, Jl. H. Juanda 15, Malay Forester, 44,397-406. Bogor 16001, West Java, Indonesia. Leighton, M. and Wirawan, N. 1986. Catastrophic

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