Other Prooosals. 11. Class: Dicotyledoneae

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AMENDMENTS TO APPENDICES AND H OF THE CONVENTION Other Prooosals A. PROPOSAL Inclusion of Intsia spp. in Appendix II. B PROPONENTS Denmark and the Netherlands. C. SUPPORTING STATEMENT 1. Taxonomy 11. Class: Dicotyledoneae 12. Order: Fabales 13. Family: Leguminosae 14. Genus: Intsia Thouars 15. Species: 1. acuminate Merr. I. bijuga (Colebr.) O.Kuntze I. palembanica Miq. 1 6. Common Names: English: Borneo teak, Moluccan ironwood French: Spanish: L bi7uga: Fijian: Vesi Indonesien: Malaysian: lpii Papua New Guinean: Kwila, Bendora Philippine: pu Sarawakian: IpiI Sabahian: IpiI Laut Solomon Islandian: U Ula Thailandian: Lumpho thale, Makhamong, Pradu thale Vietnamian: Go Nuoe I. palembanica: Indonesien: Malaysian: Sarawakian: Thailandian: lpii Lumpho, Salumpho. 99

2. Biological Data 21. Distribution: Intsia acuminata is restricted to the Philippines. Intsia b~uga has a widespread distribution in South-East Asia and the south-west Pacific. It occurs in the United Republic of Tanzania (Lock, 1989>, Madagascar, Mauritius, Seychelles, India, Sri Lanka, Bangladesh, Myanmar, Thailand (Chanthaburi, Trat, Narathiwat), Cambodia, Viet Nam, Malaysia (Peninsular, Sabah, Sarawak), Brunei Darussalam, Indonesia, Philippines, Papua New Guinea, Australia, Solomon Islands, Fiji, American Samoa, Samoa, Guam, Federated States of Micronesia and other Pacific islands (Balgooy, 1 966>.!ntsia pa/embanica occurs in Bangladesh, Myanmar, Thailand (Surat-thanee, Phuket, Trang, Krabi, Pattani, Trat), Malaysia (Peninsular, Sabah and Sarawak), Brunei Darussalam and Indonesia (Sumatra, Kalimantan, Sulawesi, Moluccas and Irian Jaya) (Balgooy, 1966). 22. Ponulation: Intsia acuminata: Philippines: Recorded as Endangered/Rare. Intsia bj/uga: This species produces one of the most valuable timbers of South East Asia. It has been exploited so intensively for timber that in most countries few trees are left in natural stands. There have been few attempts to cultivate the species in plantations and in 1 979 it was stated that it faced imminent disappearance as an economic plant (National Academy of Sciences, 1 979). Federated States of Micronesia: According to Fosberg (1973), the species used to be a common swamp tree in the Caroline Islands. However, some destruction had occurred and the extent of remaining swamp vegetation was uncertain. Indonesia: Recorded as Indeterminate in Indonesia in the Tropical Timber Conservation (TTC) database established for ITTO. Malaysia: It was stated to be not abundant anywhere in Peninsular Malaysia and to rarely achieve timber size (Ser, 1982). In Sarawak, where the species is usually no more than a small tree, it was found to be frequent along tidal river banks (Anderson, 1 980). Papua New Guinea: It is found throughout the lowland rainforests with the main commercial stands in Sepik (East and West) and Madang. Philippines: Recorded as EndangeredNulnerable in the Tropical Timber Conservation (TTC) database established for ITTO. Thailand: The species is rare in Thailand. Intsia pa/embanica: Indonesia: Recorded as Indeterminate. Malaysia: In Peninsular Malaysia it is restricted mainly to more fertile areas of lowland dipterocarp forests and is threatened by the clearance of such forest for agriculture (Anon, 1985). It is occasional, but localised, in mixed dipterocarp forest throughout Sarawak but more common in Balingian-Bintulu area (Anderson, 1980). In the early 1980s a total of 0.02 tree per hectare 100

(representing 0.02m3 of timber) was calculated to be present in the FAO Unit 3 area in Sarawak (Phang, 1983). The decline of!ntsia spp. (mainly I. palembanica) in virgin forests in Peninsular Malaysia can be quantified using data from the First and Second National Forest Inventories carried out in 1971-72 and 1981-82 respectively: the number of trees per hectare declined from 0.3 to 0.25 (45+cm diameter class) and from 0.55 to 0.35 (15+cm diameter class); the volume per hectare declined from 1.64m3 to 1.34m3 (45 +cm diameter class) and from 1.9m3 to 1.44m3 (15 +cm diameter class) (Anon., 1989). Thailand: The species is rare in Thailand. 23. Habitat: Intsia bi~uga and Intsia palembanica are tropical rainforest species.!ntsia b~uga occurs in lowlands and is often found in coastal areas bordering mangrove swamps, rivers, or floodplains. Intsia palembanica is usually found farther inland or on low hilltops or well-drained river flats. Both species tolerate a wide range of soil conditions. 3. Trade Data 32. Legal International Trade: It has proved difficult to locate comprehensive statistical information on international trade in these species, as most countries do not record sufficiently detailed information to species level. The main importing country within Europe is the Netherlands. In a recent survey conducted for ITTO no UK traders reported importing this species. Kwila is one of the major species exported from Papua New Guinea as sawn timber. The average FOB price in 1990 for rough sawn timber was K380-480m3. The overall volume of sawn timber was low - in 1990 only 4480m3. The main markets for sawn timber from Papua New Guinea are Australia and New Zealand. Kwila is the most highly priced timber exported from Papua New Guinea in log form. Kwila logs are exported from Papua New Guinea to India (PNG Department of Forests, 1990) Trade data for exports of logs of Intsia spp. from Papua New Guinea 1985# 1986 1987 1988 VOL (%) FOB FOB VOL (%) VOL (m3) FOB 1.30 79.40 125.OOJ 3.50 41114.50 154.44 1989 f 1990 VOL (%) VOL (m3) FOB VOL (rn3) VOL (%) FOB 2.00 25184.00 136.58 38596.61 4.05 155.67 Sources: 1 986, 1 987, 1988 and 1989 prices - FIC cited in Amin; 1990. 1990 - FIC cited in DOF 1990 Marketing Report. 1988% - Fl~ cited in Eddowes, 71989. 1989% - FtC Sources: 1985 - FIC in Review of the Sawmilling Industry - First six months only FIC Papua New Guinea Forest Industries Council VOL (%) is the percentage of total log exports for that year. 101

Kwila is one of the major types of sawn timber used domestically in Papua New Guinea and is used in furniture production. Sawn timber indicative prices (in Kira) for Kwila are as follows: 1985 1986 1987 1888 1889 Dressed 375 380 400 445 450 Undressed 315 330 350 387 390 In 1989 Peninsular Malaysia exported 84,560m3 of Intsiapalembanica as sawn timber (Malaysian Timber Industry Board, 1989>. In 1987 Sabah exported 7239.1m3 of Intsia spp. in log form (Sabah Forestry Department, 1989). 33. IlIeaaI Trade: Not known. 34. Potential Trade Threats: No information available. 4. &~t~.ctionta.tus 41. National: Indonesia: the minimum diameter limit for Intsiapa/embanica is O.6m. Intsia bi~uga occurs within the following protected areas in Indonesia: Ujung Kulon National Park, Java, Manusela Wai Nua/Wai Mual National Park, Seram, Moluccas. I. palembanica occurs in the Lorentz Nature Reserve in Irian Jaya. Peninsular Malaysia: the export of!ntsia palembanica in log form is banned. Intsia palembanica occurs within Taman Nagara National Park, Kerau Game Reserve and Endau Rompin proposed reserve in Peninsular Malaysia. Philippines: Intsia bi7uga is classified as a premium hardwood under the DENR Administrative Order No. 78 Series of 1987, Interim Guidelines on the cutting/gathering of Narra and other premium hardwood species. Under this Order speäial permission from the Secretary of the Department of Environment and Natural Resources is required to fell Intsia bi7uga, and various conditions are specified. It occurs in St Paul Subterranean River National Park, Quezon National Park and Calauit Island National Park. Thailand: Conserved under the Royal Forestry Department Act and not allowed for export. 42. International: No information available. 43. Additional Protection Needs: In situ conservation for Intsia spp. in South-East Asia is considered to be a priority by FAQ (1 990>. 5. Information on Similar $Decies Some species of the genus Afzella are closely related to Intsia and produce wood of similar quality. 102

6. Comments from Countries of Origin Comments on a draft of the proposal were solicited from Bangladesh, India, Indonesia, Madagascar, Philippines and United Republic of Tanzania. 7. Additional remarks None. 8. References Anon. (1985). in situ conservation of forest genetic resources in Peninsular Malaysia. Forest Genetic Resources Information. No. 14:32-49. FAO, Rome. Anon. (1989). ITTO study on the ecological effects of bringing greater numbers of lesser known species into trade. Amin, M.N. (1990). Papua New Guinea market for timber products: Trends and Prospects. Asia Pacific Forest Industries Development Group. FAQ, Kuala Lumpur. Anderson, J.A.R. (1980). A checklist of the trees of Sarawak. Forest Department, Sarawak. Balgooy, M.M.J. van (1966). Pacific plant maps. Blumea 5 Suppl.: 158-159. FAO (1990). Report of the Seventh Session of the FAQ Panel of Experts on Forest Gene Resources. December, 1989. FAQ, Rome. Fosberg, F.R. (1973). On present condition and conservation of forests in Micronesia. In: Pac. Sci. Assoc. Standing Comm. on Pac. Bot. Symposium: Planned Utilisation of the Lowland Tropical Forests. Aug. 1971. Bogor, Indonesia. Lock, J.M. (1989). Legumes of Africa. A check list. Royal Botanic Gardens, Kew. Malaysian Timber Industry Board (1989). Annual export of timber products and furniture. National Academy of Sciences (1979). Tropical Legumes: Resources for the future. National Academy of Sciences, Washington D.C. Papua New Guinea, Department of Forests Marketing Branch (1990). 1990 Activity Report. Phang, C. (1983). Under-utilised timber species of Sarawak. Paper presented at the National Workshop on Under Utilised Timbers, 1 5 and 1 6 August 1983, Kuala Lumpur. Sabah Forestry Department (1989). Forestry in Sabah. Ser, C.S. (1982). Malaysian timbers -. Malaysian Forest Service Trade Leaflet No. 65. Malaysian Timber Industry Board, Kuala Lumpur. 103