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PRIORITIES FOR RESEARCH IN THE
      WETLAND FORESTS OF BRUNEI
    Paper presented at:

THE INTERNATIONAL CONFERENCE ON WETLAND
                 FORESTS
     “FORESTS FOR SUSTAINABLE LIVING”


   22-23 MARCH 2012, THE RIZQUN INTERNATIONAL HOTEL
        BANDAR SERI BEGAWAN, BRUNEI DARUSSALAM
STRUCTURE OF PRESENTATION

BRIEF OVERVIEW OF EACH WETLAND FOREST TYPE

RESEARCH PRIORITIES

DETAILS ON RESEARCH PRIORITIES

GENERAL RECOMMENDATIONS ON RESEARCH
ACTIVITIES
OVERVIEW OF WETLAND FORESTS IN BRUNEI
    FOUR TYPES OF WETLAND FOREST
MANGROVE
Classified into 5 types

FRESHWATER SWAMP FOREST
Unclassified (only levee and backswamp)

PEAT SWAMP FOREST
6 major types distinguished

KERAPAH
(Develops within waterlogged kerangas areas)
                              Based on Anderson & Marsden (1984)
SUMMARY OF AREA OF WETLAND FORESTS IN BRUNEI
      WETLAND               AREA (ha)             PERCENTAGE
      FOREST TYPE                                 OF AREA OF
                                                  BRUNEI

      MANGROVE              19,217                3.55

      MANGROVE/PEAT 3,343                         0.58
      SWAMP FOREST
      TRANSITION

      PEAT SWAMP            95,410                16.55
      FOREST
      FRESHWATER            12,761                2.22
      SWAMP FOREST


      TOTAL                 130,731               22.70


 Based mainly on Anderson & Marsden (1984) data
MANGROVES: MAINLY TEMBURONG DISTRICT:
ALL SUB-TYPES PLUS PSF:MANGROVE TRANSITION
SELIRONG ISLAND 1.1: RHIZOPHORA
OTHER MANGROVE SUBTYPES




NYIREH BUNGA
(Xylocarpus granatum)




                              NYPA / DUNGUN
                              Nypa fruticans /
                              Heritiera globosa
                              (Bornean endemic)
MANGROVE : PEAT SWAMP FOREST TRANSITION

COAST                                                     INLAND
                        Oncosperma
                                          Mixed peat swamp forest
    Nypa                TRANSITION
SUGGESTED RESEARCH PRIORITIES FOR MANGROVE
   UPDATED STATUS: INTACT , DISTURBED & CLEARED
 ECONOMIC VALUATION: esp IMPORTANCE AS FISH
AND SHELLFISH BREEDING, FEEDING & NURSERY AREAS (BRUNEI
BAY incl. SABAH & SARAWAK?)
   DISEASES / INFESTATIONS

       REHABILITATION STRATEGIES:
     LOGGED AREAS OF RHIZOPHORA: colonisation
     by fern Acrosthicum inhibits good
     regeneration of Rhizophora

     RE-VEGETATION ALONG CLEARED TIDAL
     CREEKS & SURVEY OF ACID SO4 SOIL
     DISTRIBUTION
     (PROBLEM WITH ACID SULPHATE SOILS)
     Sg DAMUAN (1998): The pH of the soil mean of 2.54
DISEASES & INFESTATIONS
DEFOLIATION OF RHIZOPHORA

BRUNEI BAY MARCH 2011
DISTURBANCE OF ACID SULPHATE SOILS:
OCHRE DEPOSITS IN CLEARED AREA OF MANGROVE ALONG Sg DAMUAN,
1998 (CANALISATION)
LARGE AREAS OF Rhizophora CLEARED RECENTLY: HOW TO REHABILITATE??
ACID SULPHATE SOIL LOCATIONS UNDERLYING MANGROVE AND PEAT




  GREALISH et al. (2008)
DISTURBED ACID SULPHATE SOILS:
REHABILITATION / REVEGETATION POSSIBILITIES:
                          Cerbera odollam
BRUNEI BAY-WIDE STUDY ON MANGROVE SUPPORT TO COASTAL
                       FISHERIES
RIVERINE VEGETATION
      ZONATION:




REHABILITATION
OF CLEARED
AREAS:

SUITABLE SPECIES?




                    GLUTA VELUTINA/
RESEARCH IN PROPAGATION OF
                            SUITABLE SPECIES
                         Barringtonia conoidea




   ALL 4 SPP PROMISING
   CANDIDATES                                    Gluta velutina


MIXED FRESHWATER
TIDAL ZONE:

Barringtonia
racemosa

Horsfieldia
iriya
FRESHWATER SWAMP FOREST




MANY DIFFERENT SUB-TYPES
Related to depth and frequency of flooding,
nutrient status of incoming water & type of soil
FSF ALONG MAJOR
                           RIVERS
                   FSF dominated
                    by Pternandra
                   corulescens & Syzygium




FSF dominated by
Vatica umbonata,
dry period
FSF DOMINATED BY RAMIN,
Gonystylus bancanus, TASEK
MERIMBUN
NUTRIENT-POOR FSF, BUKIT SAWAT
SUGGESTED RESEARCH PRIORITIES FOR FRESHWATER
               SWAMP FOREST
   VEGETATION TYPES IN RELATION TO EDAPHIC AND
  HYDROLOGICAL FACTORS
 (Water quality and depth and frequency of flooding, soil type)

   IMPORTANCE OF FSF AND TRIBUTARIES FOR SPAWNING,
 FEEDING AND NURSERY AREAS FOR FISHES:
 e.g. IKAN TAPAH (Wallago leerii)

   IMPORTANCE OF FRESHWATER FISHES FOR LOCAL PEOPLE

   REHABILITATION POSSIBILITIES
FISHERIES & FRESHWATER
                                  SWAMP FOREST




WALLAGO LEERII:
SOCIO-ECONOMIC IMPORTANCE


THOUGHT TO SPAWN IN TRIBUTARIES
OF MAJOR RIVERS
CREEK, BELAIT RIVER – LUAGAN LALAK




  MIGRATION OF FISHES AND USE OF FSF RESOURCES
  IMPORTANCE OF FISHERIES TO LOCAL PEOPLE
REHABILITATION POSSIBILITIES
         IDENTIFICATION & PROPAGATION OF SUITABLE SPECIES
Vatica umbonata

                                             Calophyllum macrocarpum
                     Teijsmanniodendron pteropodum
KERAPAH
AREA AND LOCATIONS NOT MAPPED, VEGETATION COMMUNITIES




    DISTURBED KERAPAH ON SAND RIDGE, LUMUT PIPELINE ROAD
PEAT SWAMP FOREST
MOST PEATLANDS FOUND IN LOWER BELAIT DISTRICT: SOME
       SHARED BETWEEN SARAWAK AND BRUNEI
MOSTLY OCCUR AS PEAT DOMES




LOWER
BELAIT
DISTRICT
                            Anderson and Marsden (1984)
PEAT DOMES

Profile from
Baram basin




               VERY FEW STUDIES ON PEAT
               DOMES IN BRUNEI


               DEPTH STUDIES



               Profile from shared peat
               dome between Baram &
               Belait rivers
Vegetation Communities on Peat
Sequence of vegetation with peat depth in northwest Borneo
(Sarawak & Brunei)

                                      Modified from Anderson (1961),
                                      shown in Whitmore (1984)
PHASIC COMMUNTY 3: THE DIPTEROCARP SHOREA
ALBIDA (alan bunga) FOREST FORMING PURE STANDS,
BELAIT DISTRICT, BRUNEI
PHASIC COMMUNITY 6




TOP OF HIGHLY DEVELOPED
PEAT DOMES
(ONLY ULU MENDARAM IN
BRUNEI)
FSF & PSF OFTEN OCCUR AS MOSAICS
     WITH OTHER FOREST TYPES
SUGGESTED RESEARCH PRIORITIES FOR PEAT SWAMP
              FOREST IN BRUNEI
   Carbon dynamics of intact and degraded
 areas (SMART-MIT)
  Hydrological dynamics Peatlands within whole
 catchments: effect of upstream activities on
 downstream peat areas
   Economic valuation – values taken into
 account in land use planning

    Whole dome studies: profiles (depth) &
 factors controlling vegetation
    Rehabilitation strategies, including research
 on propagation of potential reforestation
 species (UBD, BAP) - Shorea albida
Paleaobotanical studies

  Biodiversity: fish fauna

  Resource use by people

   Effects of projected climate change incl. sea
level rise

  Permanent plots - intact and disturbed
areas: Subsidence, succession…

  Sustainable forestry and agriculture on
rehabilitated peatlands: low impact use:
multi-cropping?
WHOLE DOME STUDIES

LOWER BELAIT:
TWO COMPLETELY UNDISTURBED
UPPER BELAIT VALLEY: INTACT PEAT BLOCKS IN A MOSAIC WITH
OTHER UNDISTURBED FOREST TYPES:
LINKAGES BETWEEN ECOSYSTEMS & MOVEMENT OF FAUNA
(Sg INGEI FAUNAL SURVEY PROJECT)
WHAT FACTORS CONTROL TYPE OF VEGETATION ON A DOME?




                          Sarawak data from Tie (pers comm)
PALAEOBOTANIC STUDIES:
WHAT IS THE VEGETATION SEQUENCE FOR PEAT OVER SAND?


ANDERSON & MULLER (1975):
BARAM BASIN STUDY OF PEAT
OVER MANGROVE CLAY
RESEARCH ON SHOREA ALBIDA (ALAN)
              “EXTREME” MAST-FRUITING SPECIES

              Last mast fruiting not known
              THREE TYPES OF COMMUNITIES Ided:
              ALAN BATU
              ALAN BUNGA
              PADANG ALAN

              WORK BY: Sukmaria & Salim (nd)

               DBH, tree height and crown width
             were significantly different between all
             Alan populations

               The Alan populations appear to be
             genetically similar

                Morphological variations did not seem
             to be related to biochemical or genetic
             variations
BUT: “LOCALISED GREGARIOUS FRUITING”


                 MARCH 2010




                                       WHAT FACTORS
                                       CONTROL
                                       FLOWERING?

                                       WHY LOCALISED
                                       FLOWERING?


                                        POSSIBLE TO
                                        RESTORE
                                        LOGGED OVER
                                        ALAN BUNGA
                                        AREAS?
POTENTIAL REFORESTATION SPECIES

   SHOREA ALBIDA
   SHOREA PACHYPHYLLA
   VATICA UMBONATA
   DRYOBALANOPS RAPPA
   DYERA POLYPHYLLA

   OTHERS:
   COMBRETOCARPUS ROTANDATUS
   JACKIA ORNATA
   AGLAIA RUBIGINOSA
   LITSEA spp
SUSTAINABLE FORESTRY & AGRICULTURE ON REHABILITATED
  PEATLANDS
Jelutong plantations?
(Central Kalimantan)




                             Forestry: Shorea spp., Dryobalanops rappa
                        Crops? Sago? Multi-cropping?:
                        Closed canopy desirable?

                        Jauliainen et al. (2012): CO2 emissions
                        Inevitable in any agricultural development
                        on peat
BIODIVERSITY
SURVEYS:
BLACKWATER FISH
DIVERSITY SURVEYS
      Fishes from blackwater sites,
      Peninsula Malaysia
Paedocypris
World’s smallest vertebrate
(Kottelat et al. 2005)
HEART OF BORNEO INITIATIVE
  95% OF WETLAND FORESTS WITHIN HoB AREA
  TWO OF HoB BRUNEI OBJECTIVES:
• To conserve  representative forest and freshwater habitats, as
well as the full range of biological diversity therein; for the
enjoyment and benefit of future generations of Bruneians.

 • To re-establish forest connectivity
                                     and the greening of
 degraded areas, through forest rehabilitation, afforestation,
 reforestation other rehabilitative means.
       INTERVENTIONS: BIODIVERSITY SURVEYS
       Survey of endangered cats in Brunei
       Survey of amphibians in Brunei
       Survey of insect biodiversity in Brunei
       Large mammal survey in the Inter-riverine Zone
       Survey of fish and aquatic invertebrates in Brunei
IMPORTANT ROLE OF MONITORING:
  FOR PHENOLOGY OF POTENTIAL REFORESTATION SPP.
(COLLECTION OF SEEDS & FRUITS): USE OF PERMANENT PLOTS?

  MONITORING HEALTH OF ECOSYSTEMS

  RECORDING OCCURRENCE OF SPECIES

e.g. PENAGA NATURAL HISTORY SOCIETY
BRUNEI NATURE SOCIETY
         PHNS DATA TO BIRDLIFE: IMPORTANT
         BIRD AREAS (IBAs)

MONITORING HEALTH OF ECOSYSTEMS IDENTIFIES ISSUES WHICH
               MAY NEED RESEARCH INPUT
MONITORING: PERMANENT PLOTS

                        PHENOLOGY OF POTENTIAL
                        REFORESTATION SPECIES: WHEN
                        TO COLLECT SEEDS & FRUITS

                       PEAT: DISTURBED AREAS:
                       SUBSIDENCE MEASURING POLES,
                       SUCCESSION



SET UP IN DIFFERENT VEGETATION COMMUNITIES
IN WETLAND FORESTS; e.g. the 6 phasic
communties on peat domes
SUMMARY
MAIN TRENDS IN SUGGESTED PRIORITIES:

BASE LINE DATA ON FUNCTIONING OF UNDISTURBED ECOSYSTEMS:
(INTACT NATURE & ACCESSIBILITY)

CARBON DYNAMICS
Including mangroves and FSF as well as PSF

BIODIVERSITY VALUES

INTER-LINKAGES OF ECOSYSTEMS AT LOCAL & CATCHMENT LEVEL

ECONOMIC VALUATION & RESOURCE USE BY LOCAL PEOPLE

RESTORATION & REHABILITATION OF WETLAND FORESTS

VEGETATIONAL HISTORY
GENERAL RECOMMENDATIONS
  DEVELOPMENT OF A NATIONAL WETLAND INVENTORY

   DEVELOPMENT OF A RESEARCH PLAN FOR WETLAND FORESTS
(In collaboration with regional and international institutions: e.g. FRIM,
universities)

  REGIONAL AND INTERNATIONAL COLLABORATION IN RESEARCH:
HEART OF BORNEO INITIATIVE; ASEAN (APFP); University to University
Partnerships, British High Commission….

 REGULAR CONSULTATION WITH RELEVANT GOVERNMENT IMPLEMENTING
AND PLANNING AGENCIES DURING LIFE OF PROJECTS
  INFORMATION PRESENTED IN SUCH A WAY AS TO EASILY FEED INTO
GOVERNMENT PLANNING PROCESSES AND TO FULFIL INTERNATIONAL
OBLIGATIONS
CBD: NATIONAL BIODIVERSITY STRATEGY
UNFCC: CARBON ACCOUNTING: EMISSION REDUCTION TARGETS etc
LAND USE MASTER PLANS & NATIONAL PROTECTED AREAS SYSTEM
THANK YOU FOR YOUR ATTENTION

        TERIMA KASIH

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Jonathan Davies: Priorities for Research in the Wetland Forests of Brunei

  • 1. PRIORITIES FOR RESEARCH IN THE WETLAND FORESTS OF BRUNEI Paper presented at: THE INTERNATIONAL CONFERENCE ON WETLAND FORESTS “FORESTS FOR SUSTAINABLE LIVING” 22-23 MARCH 2012, THE RIZQUN INTERNATIONAL HOTEL BANDAR SERI BEGAWAN, BRUNEI DARUSSALAM
  • 2. STRUCTURE OF PRESENTATION BRIEF OVERVIEW OF EACH WETLAND FOREST TYPE RESEARCH PRIORITIES DETAILS ON RESEARCH PRIORITIES GENERAL RECOMMENDATIONS ON RESEARCH ACTIVITIES
  • 3. OVERVIEW OF WETLAND FORESTS IN BRUNEI FOUR TYPES OF WETLAND FOREST MANGROVE Classified into 5 types FRESHWATER SWAMP FOREST Unclassified (only levee and backswamp) PEAT SWAMP FOREST 6 major types distinguished KERAPAH (Develops within waterlogged kerangas areas) Based on Anderson & Marsden (1984)
  • 4.
  • 5. SUMMARY OF AREA OF WETLAND FORESTS IN BRUNEI WETLAND AREA (ha) PERCENTAGE FOREST TYPE OF AREA OF BRUNEI MANGROVE 19,217 3.55 MANGROVE/PEAT 3,343 0.58 SWAMP FOREST TRANSITION PEAT SWAMP 95,410 16.55 FOREST FRESHWATER 12,761 2.22 SWAMP FOREST TOTAL 130,731 22.70 Based mainly on Anderson & Marsden (1984) data
  • 6. MANGROVES: MAINLY TEMBURONG DISTRICT: ALL SUB-TYPES PLUS PSF:MANGROVE TRANSITION
  • 7. SELIRONG ISLAND 1.1: RHIZOPHORA
  • 8. OTHER MANGROVE SUBTYPES NYIREH BUNGA (Xylocarpus granatum) NYPA / DUNGUN Nypa fruticans / Heritiera globosa (Bornean endemic)
  • 9. MANGROVE : PEAT SWAMP FOREST TRANSITION COAST INLAND Oncosperma Mixed peat swamp forest Nypa TRANSITION
  • 10. SUGGESTED RESEARCH PRIORITIES FOR MANGROVE UPDATED STATUS: INTACT , DISTURBED & CLEARED ECONOMIC VALUATION: esp IMPORTANCE AS FISH AND SHELLFISH BREEDING, FEEDING & NURSERY AREAS (BRUNEI BAY incl. SABAH & SARAWAK?) DISEASES / INFESTATIONS REHABILITATION STRATEGIES: LOGGED AREAS OF RHIZOPHORA: colonisation by fern Acrosthicum inhibits good regeneration of Rhizophora RE-VEGETATION ALONG CLEARED TIDAL CREEKS & SURVEY OF ACID SO4 SOIL DISTRIBUTION (PROBLEM WITH ACID SULPHATE SOILS) Sg DAMUAN (1998): The pH of the soil mean of 2.54
  • 11. DISEASES & INFESTATIONS DEFOLIATION OF RHIZOPHORA BRUNEI BAY MARCH 2011
  • 12. DISTURBANCE OF ACID SULPHATE SOILS: OCHRE DEPOSITS IN CLEARED AREA OF MANGROVE ALONG Sg DAMUAN, 1998 (CANALISATION) LARGE AREAS OF Rhizophora CLEARED RECENTLY: HOW TO REHABILITATE??
  • 13. ACID SULPHATE SOIL LOCATIONS UNDERLYING MANGROVE AND PEAT GREALISH et al. (2008)
  • 14. DISTURBED ACID SULPHATE SOILS: REHABILITATION / REVEGETATION POSSIBILITIES: Cerbera odollam
  • 15. BRUNEI BAY-WIDE STUDY ON MANGROVE SUPPORT TO COASTAL FISHERIES
  • 16. RIVERINE VEGETATION ZONATION: REHABILITATION OF CLEARED AREAS: SUITABLE SPECIES? GLUTA VELUTINA/
  • 17. RESEARCH IN PROPAGATION OF SUITABLE SPECIES Barringtonia conoidea ALL 4 SPP PROMISING CANDIDATES Gluta velutina MIXED FRESHWATER TIDAL ZONE: Barringtonia racemosa Horsfieldia iriya
  • 18. FRESHWATER SWAMP FOREST MANY DIFFERENT SUB-TYPES Related to depth and frequency of flooding, nutrient status of incoming water & type of soil
  • 19. FSF ALONG MAJOR RIVERS FSF dominated by Pternandra corulescens & Syzygium FSF dominated by Vatica umbonata, dry period
  • 20. FSF DOMINATED BY RAMIN, Gonystylus bancanus, TASEK MERIMBUN
  • 22. SUGGESTED RESEARCH PRIORITIES FOR FRESHWATER SWAMP FOREST VEGETATION TYPES IN RELATION TO EDAPHIC AND HYDROLOGICAL FACTORS (Water quality and depth and frequency of flooding, soil type) IMPORTANCE OF FSF AND TRIBUTARIES FOR SPAWNING, FEEDING AND NURSERY AREAS FOR FISHES: e.g. IKAN TAPAH (Wallago leerii) IMPORTANCE OF FRESHWATER FISHES FOR LOCAL PEOPLE REHABILITATION POSSIBILITIES
  • 23. FISHERIES & FRESHWATER SWAMP FOREST WALLAGO LEERII: SOCIO-ECONOMIC IMPORTANCE THOUGHT TO SPAWN IN TRIBUTARIES OF MAJOR RIVERS
  • 24. CREEK, BELAIT RIVER – LUAGAN LALAK MIGRATION OF FISHES AND USE OF FSF RESOURCES IMPORTANCE OF FISHERIES TO LOCAL PEOPLE
  • 25. REHABILITATION POSSIBILITIES IDENTIFICATION & PROPAGATION OF SUITABLE SPECIES Vatica umbonata Calophyllum macrocarpum Teijsmanniodendron pteropodum
  • 26. KERAPAH AREA AND LOCATIONS NOT MAPPED, VEGETATION COMMUNITIES DISTURBED KERAPAH ON SAND RIDGE, LUMUT PIPELINE ROAD
  • 27. PEAT SWAMP FOREST MOST PEATLANDS FOUND IN LOWER BELAIT DISTRICT: SOME SHARED BETWEEN SARAWAK AND BRUNEI
  • 28. MOSTLY OCCUR AS PEAT DOMES LOWER BELAIT DISTRICT Anderson and Marsden (1984)
  • 29. PEAT DOMES Profile from Baram basin VERY FEW STUDIES ON PEAT DOMES IN BRUNEI DEPTH STUDIES Profile from shared peat dome between Baram & Belait rivers
  • 30. Vegetation Communities on Peat Sequence of vegetation with peat depth in northwest Borneo (Sarawak & Brunei) Modified from Anderson (1961), shown in Whitmore (1984)
  • 31. PHASIC COMMUNTY 3: THE DIPTEROCARP SHOREA ALBIDA (alan bunga) FOREST FORMING PURE STANDS, BELAIT DISTRICT, BRUNEI
  • 32. PHASIC COMMUNITY 6 TOP OF HIGHLY DEVELOPED PEAT DOMES (ONLY ULU MENDARAM IN BRUNEI)
  • 33. FSF & PSF OFTEN OCCUR AS MOSAICS WITH OTHER FOREST TYPES
  • 34. SUGGESTED RESEARCH PRIORITIES FOR PEAT SWAMP FOREST IN BRUNEI Carbon dynamics of intact and degraded areas (SMART-MIT) Hydrological dynamics Peatlands within whole catchments: effect of upstream activities on downstream peat areas Economic valuation – values taken into account in land use planning Whole dome studies: profiles (depth) & factors controlling vegetation Rehabilitation strategies, including research on propagation of potential reforestation species (UBD, BAP) - Shorea albida
  • 35. Paleaobotanical studies Biodiversity: fish fauna Resource use by people Effects of projected climate change incl. sea level rise Permanent plots - intact and disturbed areas: Subsidence, succession… Sustainable forestry and agriculture on rehabilitated peatlands: low impact use: multi-cropping?
  • 36. WHOLE DOME STUDIES LOWER BELAIT: TWO COMPLETELY UNDISTURBED
  • 37. UPPER BELAIT VALLEY: INTACT PEAT BLOCKS IN A MOSAIC WITH OTHER UNDISTURBED FOREST TYPES: LINKAGES BETWEEN ECOSYSTEMS & MOVEMENT OF FAUNA (Sg INGEI FAUNAL SURVEY PROJECT)
  • 38. WHAT FACTORS CONTROL TYPE OF VEGETATION ON A DOME? Sarawak data from Tie (pers comm)
  • 39. PALAEOBOTANIC STUDIES: WHAT IS THE VEGETATION SEQUENCE FOR PEAT OVER SAND? ANDERSON & MULLER (1975): BARAM BASIN STUDY OF PEAT OVER MANGROVE CLAY
  • 40. RESEARCH ON SHOREA ALBIDA (ALAN) “EXTREME” MAST-FRUITING SPECIES Last mast fruiting not known THREE TYPES OF COMMUNITIES Ided: ALAN BATU ALAN BUNGA PADANG ALAN WORK BY: Sukmaria & Salim (nd) DBH, tree height and crown width were significantly different between all Alan populations The Alan populations appear to be genetically similar Morphological variations did not seem to be related to biochemical or genetic variations
  • 41. BUT: “LOCALISED GREGARIOUS FRUITING” MARCH 2010 WHAT FACTORS CONTROL FLOWERING? WHY LOCALISED FLOWERING? POSSIBLE TO RESTORE LOGGED OVER ALAN BUNGA AREAS?
  • 42. POTENTIAL REFORESTATION SPECIES SHOREA ALBIDA SHOREA PACHYPHYLLA VATICA UMBONATA DRYOBALANOPS RAPPA DYERA POLYPHYLLA OTHERS: COMBRETOCARPUS ROTANDATUS JACKIA ORNATA AGLAIA RUBIGINOSA LITSEA spp
  • 43. SUSTAINABLE FORESTRY & AGRICULTURE ON REHABILITATED PEATLANDS Jelutong plantations? (Central Kalimantan) Forestry: Shorea spp., Dryobalanops rappa Crops? Sago? Multi-cropping?: Closed canopy desirable? Jauliainen et al. (2012): CO2 emissions Inevitable in any agricultural development on peat
  • 44. BIODIVERSITY SURVEYS: BLACKWATER FISH DIVERSITY SURVEYS Fishes from blackwater sites, Peninsula Malaysia Paedocypris World’s smallest vertebrate (Kottelat et al. 2005)
  • 45. HEART OF BORNEO INITIATIVE 95% OF WETLAND FORESTS WITHIN HoB AREA TWO OF HoB BRUNEI OBJECTIVES: • To conserve representative forest and freshwater habitats, as well as the full range of biological diversity therein; for the enjoyment and benefit of future generations of Bruneians. • To re-establish forest connectivity and the greening of degraded areas, through forest rehabilitation, afforestation, reforestation other rehabilitative means. INTERVENTIONS: BIODIVERSITY SURVEYS Survey of endangered cats in Brunei Survey of amphibians in Brunei Survey of insect biodiversity in Brunei Large mammal survey in the Inter-riverine Zone Survey of fish and aquatic invertebrates in Brunei
  • 46. IMPORTANT ROLE OF MONITORING: FOR PHENOLOGY OF POTENTIAL REFORESTATION SPP. (COLLECTION OF SEEDS & FRUITS): USE OF PERMANENT PLOTS? MONITORING HEALTH OF ECOSYSTEMS RECORDING OCCURRENCE OF SPECIES e.g. PENAGA NATURAL HISTORY SOCIETY BRUNEI NATURE SOCIETY PHNS DATA TO BIRDLIFE: IMPORTANT BIRD AREAS (IBAs) MONITORING HEALTH OF ECOSYSTEMS IDENTIFIES ISSUES WHICH MAY NEED RESEARCH INPUT
  • 47. MONITORING: PERMANENT PLOTS PHENOLOGY OF POTENTIAL REFORESTATION SPECIES: WHEN TO COLLECT SEEDS & FRUITS PEAT: DISTURBED AREAS: SUBSIDENCE MEASURING POLES, SUCCESSION SET UP IN DIFFERENT VEGETATION COMMUNITIES IN WETLAND FORESTS; e.g. the 6 phasic communties on peat domes
  • 48. SUMMARY MAIN TRENDS IN SUGGESTED PRIORITIES: BASE LINE DATA ON FUNCTIONING OF UNDISTURBED ECOSYSTEMS: (INTACT NATURE & ACCESSIBILITY) CARBON DYNAMICS Including mangroves and FSF as well as PSF BIODIVERSITY VALUES INTER-LINKAGES OF ECOSYSTEMS AT LOCAL & CATCHMENT LEVEL ECONOMIC VALUATION & RESOURCE USE BY LOCAL PEOPLE RESTORATION & REHABILITATION OF WETLAND FORESTS VEGETATIONAL HISTORY
  • 49. GENERAL RECOMMENDATIONS DEVELOPMENT OF A NATIONAL WETLAND INVENTORY DEVELOPMENT OF A RESEARCH PLAN FOR WETLAND FORESTS (In collaboration with regional and international institutions: e.g. FRIM, universities) REGIONAL AND INTERNATIONAL COLLABORATION IN RESEARCH: HEART OF BORNEO INITIATIVE; ASEAN (APFP); University to University Partnerships, British High Commission…. REGULAR CONSULTATION WITH RELEVANT GOVERNMENT IMPLEMENTING AND PLANNING AGENCIES DURING LIFE OF PROJECTS INFORMATION PRESENTED IN SUCH A WAY AS TO EASILY FEED INTO GOVERNMENT PLANNING PROCESSES AND TO FULFIL INTERNATIONAL OBLIGATIONS CBD: NATIONAL BIODIVERSITY STRATEGY UNFCC: CARBON ACCOUNTING: EMISSION REDUCTION TARGETS etc LAND USE MASTER PLANS & NATIONAL PROTECTED AREAS SYSTEM
  • 50. THANK YOU FOR YOUR ATTENTION TERIMA KASIH