Biodiversity & Reduced Impact Logging: y p gg g The Sabah - - PowerPoint PPT Presentation

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Biodiversity & Reduced Impact Logging: y p gg g The Sabah - - PowerPoint PPT Presentation

Biodiversity & Reduced Impact Logging: y p gg g The Sabah Forestry Department Experience Y.F. Lee, Anuar M. A. Y. C. Chung E. Khoo Forest Research Centre Forestry Department, Sabah, Malaysia C Contents t t Sustainable


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Biodiversity & Reduced Impact Logging: y p gg g The Sabah Forestry Department Experience

Y.F. Lee, Anuar M.、A. Y. C. Chung & E. Khoo

Forest Research Centre Forestry Department, Sabah, Malaysia

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SLIDE 2

C t t Contents

Sustainable forest management (SFM) in

l general

Reduced impact logging (RIL) as a tool

  • p

gg g ( ) for SFM

S

lt f h RIL

Some results of research on RIL Ongoing research for refinement of RIL

g g

Conclusions

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Definition of sustainable forest management (SFM)

ITTO: “Th f f l d “The process of managing permanent forest land to achieve one or more clearly specified objectives of h d h d f management with regard to the production of a continuous flow of desired forest products and h d d h services without undue reduction in its inherent values and future productivity and without undue id bl ff h h i l d i l considerable effects on the physical and social environment“

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FOREST RESERVES AND OTHER FOREST LAND IN SABAH

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Classification of forested areas in Sabah

No. Forest types Area (ha) 1 Forest Reserves 3 594 516 1. Forest Reserves 3,594,516 2. Plantation forests 150,492 , 3. Parks (under Sabah Parks) 245,172 4. Other forested areas (State 429,820 land, forests allocated for plantation forests, rehabilitated forests) rehabilitated forests) TOTAL 4,420,000

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SUSTAI NABLE FOREST MANAGEMENT I N DERAMAKOT FOREST RESERVE

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Deramakot Forest Reserve (55,000 Ha) Deramakot Forest Reserve (55,000 Ha)

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Forest management practices in Deram akot F R h b d b SGS Forest Reserve have been assessed by SGS under the QUALIFOR programme and certified by Forest Steward Council as a by Forest Steward Council as a

w ell-m anaged forest

in July 1997. The certificate is valid until 2008

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CONDITIONS FOR SUSTAINABLE FOREST CONDITIONS FOR SUSTAINABLE FOREST MANAGEMENT IN SABAH

  • 1. Adequate provisions for planning procedures,

implementing guidelines and monitoring task at different levels, i.e. forestry sector, forest management unit and levels, i.e. forestry sector, forest management unit and compartment 2 A forest management plan for a ten ear period that

  • 2. A forest management plan for a ten year period that

incorporates multiple-use forest management concept and supported by various studies.

  • 3. Management criteria to categorize major functions of the

forest in preparation of forest management plan. forest in preparation of forest management plan.

  • 4. Comprehensive resource inventory to determine the

quantities and qualities of timber stocking quantities and qualities of timber stocking.

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CONDITIONS FOR SUSTAINABLE FOREST MANAGEMENT IN SABAH

5 S i tifi ll b k d th d l i th Di t

  • 5. Scientifically backed growth models, i.e. the Dipterocarp

Simulation Model (DIPSIM) to determine the annual allowable cut (AAC). ( )

  • 6. Subdivision into operational compartments at the size of

300 600 h h f hi h i i d ifi f ti 300-600 ha, each of which is assigned specific functions.

  • 7. Annual Work Plan and Comprehensive Harvesting Plan
  • 7. Annual Work Plan and Comprehensive Harvesting Plan

(CHP) prepared at the compartment level.

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CONDITIONS FOR SUSTAINABLE FOREST MANAGEMENT IN SABAH MANAGEMENT IN SABAH

  • 8. Environmentally friendly harvesting system, such as

Reduced Impact Logging and Skyline Yarding. 9 Well defined technical guidelines and specifications for

  • 9. Well defined technical guidelines and specifications for

both harvesting systems as well as other forest activities such as rehabilitation and silvicultural treatmen t. 10 Areas high conservation values (e g high in biodiversity

  • 10. Areas high conservation values (e.g. high in biodiversity,

endemism, important watershed) will be identified from the Comprehensive Harvesting Plan and will be set aside as p g protected areas.

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Major components of forest

M Pl i M j

j p management system in Sabah

Management level Planning period Major components St t 10 20

  • Forest policy

L i l i State 10-20 years

  • Legislation
  • Forest sector plan

F t 5 10

  • Resource assessment (e.g. inventories)

F i ( i d i Forest Management Unit (FMU) 5-10 years

  • Forest zoning (conservation, production,

community, recreation areas)

  • Yield regulation (annual allowable cut)

Compartment Annual

  • Silviculture
  • Harvesting
  • Non timber products
  • Non-timber products
  • Resource accounting:input &

output

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Some management criteria used in categorizing the major functions of forests j

Category Management criteria Production

  • Areas for timber production confined to flat areas

p and moderately steep slopes of <25 degrees

  • Industrial tree plantation may be recommended in

poorly stocked or severely degraded areas p y y g Conservation

  • Priority on areas which are of steep slopes (>25

degrees)

  • Critical water catchment areas to protect the water

Critical water catchment areas to protect the water resources and to prevent soil erosion

  • Forest area <25 degrees (for conservation of

wildlife) wildlife) Recreation

  • Areas with natural esthetic values e.g. waterfalls,

scenic view, etc. that have potential for recreation and ecotourism development and ecotourism development Community forestry

  • Areas adjacent to human settlements
  • Areas suitable for traditional community land-use,

for example rattan production damar (resin) and for example rattan production, damar (resin) and honey collection

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Steps in Reduced Impact Logging (RIL) Steps in Reduced Impact Logging (RIL)

i. Pre-harvest operation

Comprehensive harvesting plan Detailed road planning & marking Tree marking & directional felling marking

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Steps in Reduced Impact Logging (RIL) Steps in Reduced Impact Logging (RIL)

  • ii. Harvesting operation

Construction of road, bridge, opening of main skid trails, directional felling and log skidding. Construction of all harvesting infrastructure is in accordance with h ifi i l id d i h RIL id li the specification laid down in the RIL guidelines.

  • iii. Post-harvest operation

Cross drain installation bridge and culvert removal and landing Cross drain installation, bridge and culvert removal and landing (temporary log storage area) reshaping.

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REDUCED IMPACT LOGGING (RIL) VS CONVENTIONAL LOGGING

Pinard, Putz, Tay & Sullivan (1995)

y ( ) Reduction of damage to soil and residual trees up to 50% Preliminary Studies by Lohuji & Martin (2001) (%the total harvested area): ( ) Skid trails only occupied about 3 - 4% Feeder roads covered about 1.2% Landings covered about 0.7%

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REDUCED IMPACT LOGGING (RIL) VS CONVENTIONAL LOGGING

Eltz and Bruhl (2001): no clear relationship b t th it f th f t di t b between the severity of the forest disturbance and the magnitude of the effect on stingless bee and ant communities and ant communities

  • Mohd. Fairus (2000): diversity indices on

butterflies decreased in more disturbed butterflies decreased in more disturbed habitats

Chey( 2002): Moth diversity was higher in the Chey( 2002): Moth diversity was higher in the lightly logged sites; more individuals but fewer species in the heavily logged area species in the heavily logged area

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RIL Research Programme funded by RIL Research Programme funded by Malaysian Government

  • 1. The effects of different cutting limits on timber

yield, residual stand damage and regeneration in l l d di f a lowland dipterocarp forest Januarius Gobilik & Robert Ong

  • 2. The effects of different cutting limits and slopes
  • n stream river water quality and quantity

S i S li Samin Salim

  • 3. The impact of forest harvesting on soil and leaf-

p g litter beetle assemblage Arthur Chung

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RIL Research Programme funded by RIL Research Programme funded by Malaysian Government

4.The effect of forest harvesting at different slope on soil erosion Jupiri Titin 5 Quantification of nutrient loss under reduced

  • 5. Quantification of nutrient loss under reduced

impact logging Noreen Majalap

  • 6. Wood quality in relation to diameter sizes of trees

and hill slopes and hill slopes James Josue & Zamrie Imiyabir

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Centre for Ecological Research, Kyoto University Disturbance and Recovery of Tropical Forests

Sustainability of biomass and floristic composition in Sustainability of biomass and floristic composition in

Reduced-Impact Logged (RIL) forests

Dr Tatsuyuki Seino (Kyoto University) Dr Tatsuyuki Seino (Kyoto University) Dr Shin-ichiro Aiba (Kagoshima University) Dr Masaaki Takyu (Tokyo University of Agriculture)

  • Prof. Kanehiro Kitayama (Kyoto University)
  • Mr. Robert Ong (FRC)
  • Mr. John Sugau (FRC)

C i l i f h i l b

Comparative analysis of the nutrient loss between a

lightly logged versus an intensively logged forest in the Deramakot Forest Reserve Deramakot Forest Reserve

  • Prof. Kanehiro Kitayama (Kyoto University)

Dr Noreen Majalap (FRC) j p ( )

  • Mr. Jupiri Titin (FRC)
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Centre for Ecological Research, Kyoto University Disturbance and Recovery of Tropical Forests

Effect of forest management on the diversity and

g y community structure of the soil fauna in the Deramakot Forest Reserve

Dr Masamichi Ito (Yokohama National University)

  • Prof. Motohiro Hasegawa (Kiso Experiment Station, FFPRI)

Dr Arthur Y. C. Chung (FRC)

Assessment of forest-use impact on insect biodiversity in

tropical lowland rain forests of Sabah

  • Prof. Masanori J. Toda (Hokkaido University)
  • Mr. Kosuke Akutsu (Hokkaido University)

Dr Chey Vun Khen (FRC)

A study on the abundance of seed dispersing animals and

its effects on forest ecosystems

  • Ms. Rina Kotte (Tokyo University)
  • Mr. Reuben Nilus (FRC)
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Centre for Ecological Research, Kyoto University Disturbance and Recovery of Tropical Forests

Study on the ecology of ground herbivores and their role

in tropical forest ecosystem: Check of ground herbivores by camera trap and direct observation in Deramakot by camera trap and direct observation in Deramakot

Dr Hisashi Matsubayashi (Kyoto University)

  • Mr. Joseph Tangah (FRC)

p g ( )

  • Mr. Julius Kodoh (FRC)

Economic evaluation on forest ecosystem under different

y utilization

  • Prof. Hiroshi Hasegawa (Hiroshima Shudo University)
  • Mr. Anuar Mohammad (FRC)
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C l i Conclusions

  • 1. Holistic approach in managing the entire forest

ecosystem: goal of forest management ecosystem: goal of forest management

  • 2. Full adoption of this holistic approach, encompassing
  • 2. Full adoption of this holistic approach, encompassing

sustainable forest management and reduced impact logging practice, in Deramakot Forest Reserve logging practice, in Deramakot Forest Reserve

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C l i Conclusions

  • 3. Long-term approach ensures the environmental,

social and economic benefits of the forests will be sustained.

  • 4. Many gaps in the understanding of biodiversity in

forests subjected to different degree of j g

  • disturbance. Ongoing studies on biodiversity in

Sabah will fill some of these gaps and further g p enhance forest management in Sabah.

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Th k Th k Thank you Thank you

Sabah Forestry Department Website: http://www.sabah.gov.my/htan/