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International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Vol XXXV, Part B7. Istanbul 2004
management plan. Application of several image classification
methods to obtain landscape and forest type map and spatial
analysis in determination of the spatial distribution, status and
threats of identified HCVF are some of potential techniques to
support the identification of HCVF.
Overall objective of this research is to identify the presence of
High Conservation Value Forest (HCVF) in Natural Production
Forest, using optical satellite data, different image classification
techniques and spatial analysis, to support Sustainable Forest
Management Certification process.
2. STUDY AREA
Forest area managed by PT Hutansanggam Labanan Lestari
(previously PT Inhutani ! Labanan) is situated in the Berau
District, part of East Kalimantan Province in Indonesia.
Previous management of PT Hutansanggam Labanan Lestari,
which is PT Inhutani I, also manages some other sites
surrounding. Geographically, the forest management unit lies
between 1° 45’ to 2° 10° N, and 116° 55 and 117° 20’ E (Figure
7 in page 19). The land use status of PT Hutansanggam
Labanan Lestari is presented in table 1 (Smartwood 2001)
Being mandged by PT Inhutani I since 1976, most of the natural
forest in Labanan area has been logged. Logging activities have
been done under Indonesian selective cutting and planting
system (TPTI). According to TPTI system, the forest
management unit can only harvest commercial timber species
with diameter (DBH) > 50 cm in the production forest. Logging
intensity in this site ranges from 42-173 m°/ha (Fauzi 2001).
The annual allowable cut for PT Inhutani I is approximately
50000 m? per year within a rotational logging block of
approximately 1500 ha. However, the company is implementing
conservative logging regime, resulting in the average timber
harvest rate as low as 31208 m? per year (Smartwood 2001).
Threats to the forest management unit are illegal logging and
conversion of forest to agriculture as implication of area
opening by the forest management unit. Up to now, there are
two villages inside the Labanan concession boundary; both are
under spontaneous resettlement promoted by the government.
The forest areas are increasingly converted to agriculture field
(Fauzi 2001). Labanan forest is managed under adaptive
collaborative management (ACM). PT Inhutani I, local
cooperatives, district government and provincial government
are the shareholders. However, PT Inhutani I is responsible for
all technical aspects related to forest management operations
(Wastono 2003).
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165
3. METHOD
3.1 Preliminary Assessment of High Conservation Value
Forest (HCVF)
Assessment of High Conservation Value Forest comprises
preliminary assessment and full assessment. Preliminary
assessment emphasis on the identification of (spatial)
occurrence of forest containing High Conservation Values
(HCV). This process involves analysis of spatial information.
Full assessment refers to verification the identified HCV.
However, the full assessment is beyond the scope of this study,
since it requires the preliminary assessment of HCVF to be
done first. Because of the limitation of this study, only HCV
elements related to soil and water conservation are assessed.
Information requirements and output maps representing these
elements are described in Table 1.
3.2 Identifying Forest Areas Function as Unique Sources of
Drinking Water
Some of the regulatory functions of forest, related to water
conservation, are absorption, storage and release of water,
which are extremely important. In situation that a particular
forest area protects and maintains water supplies for people or
communities, without any other alternative sources of drinking
water (i.e. unique), then the forest areas are critical and should
be considered as High Conservation Value Forest, as presented
in Figure 1. The sources of drinking water means also water for
other essential daily needs. However, an exception should be
made when the communities have access to a ready replacement
source of water that not influenced directly by the existence of
forest area within the forest management unit (e.g. supplied by
local drinking water company that use other source of water
intake, that can fulfil communities’ needs in reliable way and at
an acceptable cost).
3.3 dentifying Forest Areas as part of Critical Major
Catchments
If a forest area comprises large proportion of a catchment, then
it has critical role in maintaining water quality and quantity.
According to the similar HCVF study, forest area comprises
38% of a critical catchments was defined as HCVF. As the
importance of the catchment increased, in terms of flooding or
drought risk or water usage, the services provided by the forest
become more critical. According to the HCVF guideline, all
forest areas lies within super-priority catchment and priority
catchment areas (i.e. in Indonesia’s case are catchment priority
I and II) should be considered as High Conservation Value
Forest. In case of Indonesia, major catchment prioritisation was
done by Ministry of Forestry of Indonesia, in particular by
Directorate General of Reforestation and Land Rehabilitation.
The decision scheme in identifying the presence of HCV
element 4.2 is described in the flowchart in Figure 2. Spatially
and operationally, vector editing and table operation functions
were extensively used to select water catchment partitions that
fulfil the criteria to be assigned as areas containing HCV
elements 4.1 and 4.2. The spatial analysis done to determine the
presence of HCV elements 4.1 and 4.2 are described in Figure
3.