Conference PaperPDF Available

Socio economic characteristics of community living in peatlands and their perception on peatland management: a case study of Jabiren, Central Kalimantan Province

Authors:
  • Badan Riset dan Inovasi Nasional

Figures

Content may be subject to copyright.
Sosio-economic characteristics of community living in peatlands .................................................................(Sumarhani & Hesti L. Tata)
IUFRO • INAFOR 2017- POSTER F5
Sosio-Economic Characteristics of Community Living in Peatlands and
Their Perceptions on Peatland Management: A Case Study of Jabiren,
Central Kalimantan Province
Sumarhani1 & Hesti L. Tata1
1Forest Research and Development Center, Jalan Gnung Batu 5, Bogor 16610, Indonesia
E-mail: sumarhani26@yahoo.co.id, hl.tata@gmail.com
ABSTRACT
Jabiren is one of the most prominent peatland areas in Central Kalimantan Province. We
conducted socio-economic study of the community of three villages of Jabiren sub-district, i.e.
Pulang Pisau, Pilang and Jabiren, using a semi-structured interview. Objectives of the study were
to describe socio-economic characteristics of Jabiren community and to describe their perceptions
on peatland management. Data were analyzed using quantitative descriptive analysis and followed
by Spearman’s analysis. Results showed that the main occupation of the respondents was farmer
of crops and paddy-rice. The farmers managed the land,both mineral soil and shallow peat-soil
for a mixed agriculture. Land holding of respondents varied among land covers: paddy-eld varied
from 2-3 ha, and farm varied from 3-21.3 ha. Rubber-tree based agroforesty with fruit trees was the
commonest agriculture practised by farmers. Proportion of revenue from on-farm was the highest
compared to home garden and paddy-eld. Correlation analysis showed that there is a positive
correlation between education level and participation in organization. The common problem of
on-farm activity was frequent re. According to farmers’ perception, irrigation is an important
factor for agriculture. However, large drainage (canal) would damage peatlands, drying peat and
peat become susceptible to re. Only 14% of respondents suggested building up pump-wells and
re-break to reduce re risk. Respondents who have already practiced crop planting since years
ago and had a wider network have a better perception on peatland management, compare with
respondents who used to be dependent on natural resources, as sherman and collecting forest
products.
Keywords: Agroforestry, farmer, sherman, Kahayan river
1. INTRODUCTION
Peatlands in Indonesia have signicant role in the functions of ecology, hidrology, bio-physics
and economic social of human being. The Government of Indonesia has been aware of these
important roles, the national strategy and master plan of sustainable management peatland was
launched in 2006. It aimed to (1) improve awareness and knowledge on peatlands, (2) overcome
peatland degradation, (3) accelerate wise and sustainable peatland management, (4) encourage
cooperation on the collective actions of sustainable peatland management among districts, cities
and provinces (Departemen Dalam Negeri, 2006).
Peatlands in Central Kalimantan has been suffering from re since years ago. Hoscillo et al. (2007)
reported that Block C of ex-mega rice project had burned from 1973 to 2005. The burned forest
has capability to revive through natural succession process (Rudel, 2009); however, retrieval
of the degraded ecosystem can be accelerated through restoration and rehabilitation (Lamb &
575
Draft Only
Gilmour, 2003; Bonn, Allott, Joosten, Stoneman, 2016). To preserve peatland ecosystem, to enrich
biodiversity and to increase carbon stocks, the degraded peatland should be replanted with native
tree species and multi-purposes tree species which are adaptable to grow on peatland and rewetted
peatland.
The communities, who are living on peatland, depend their life on peatland resources. Peatland
provide four categories of ecosystem services, such as provisioning, regulating, supporting and
cultural and recreational benets (Bonn et al., 2016). The communities who live in peatland in
Central Kalimantan usually have activities in agriculture, shing and forestry (Beukering, Schaafma,
Davies, Oskolokaite, 2008; Medrilzam, Dargusch, Herbohn, Smith, 2013; Suwarno, 2016). The
three villages of Jabiren sub-district were selected because they are located along the Kahayan river
and have a gradient of peat depth, from the very deep peat in Tumbang Nusa to moderate peat
depth in Jabiren (Wetlands International Indonesia, 2004). Natural resources in deep peat usually
limited, owing to biophysical properties of peat soils (Veloo, Paramananthan, van Rants, 2014).
Therefore we evaluate socio-economics of the community of Jabiren sub-district, in order to
describe socio-economic characteristics of community of Jabiren and to describe their perceptions
on peatland management.
2. METHODS
The socio-economic study in Jabiren sub-district was conducted using a semi-structured
questionnaire. The respondent was selected randomly from three villages of Jabiren sub-district,
i.e. Tumbang Nusa, Pilang and Jabiren villages. The three villages are located along the Kahayan
river and the communities reside both along the river and the main road of Palangka Raya and
Banjarmansin. Respondent number of the three villages was 35 persons. The study was conducted
in March to April 2012.
We observed some parameters, such as (i) farming identity, (ii) institutional and partnership, and (iii)
farmer’s perception on peatland management. Secondary data were collected from the Agency of
Statistics Bureau of Pulang Pisau district, and the Agriculture Extension Service ofce of Jabiren
sub-district. Data was analyzed using descriptive analysis, and Spearman correlation test between
farming types, and it was calculated using SPSS ver. 16.0.
3. RESULTS AND DISCUSSION
3.1 Results
Jabiren sub-district of Pulang Pisau district covers an area of 132.300 ha, consisted of 8 villages
and occupied by 8,300 populations (BPS Pulang Pisau, 2011). Among the three villages, Tumbang
Nusa covers the largest peatland (17,590 ha), followed by Pilang and Jabiren, with the total area of
14.550 ha and 1.250 ha, respectively (BPP Jabiren, 2010).
3.1.1 Characteristics of respondents
Respondent characteristics were shown at Table 1. Age of respondents varied from 33-76 years old,
which indicated many respondents were in the productive age. Total respondents were dominated
by men, and only 5.7% of respondents were women. About 74.3% of total respondents were local
people, while the rests were migrants from other provinces and have different tribes, such as Java,
Banjar, and Batak.
The main livelihood of the respondents was as rubber-farmers. Only few respondents (9.4 % of
total respondents), who lived along the river, were also collecting sh. The home garden of the
communities in Jabiren sub-district mainly consisted of mixed vegetation of vegetable, fruit trees
and tree-crops. Farmers like to plant fruit trees, such as pineapple, ‘rambutan’ (Nephelium lappaceum),
Proceedings of IUFRO – INAFOR Joint International Conference 2017
Yogyakarta, 24th– 27th July 2017
576
Draft Only
paken (Durio kutejensis), ‘cempedak’ (Artocarpus champeden), and petai (Parkia speciosa) as the fruit are
easy to be sold. Other tree crops, such as cacao and rubber trees, were also planted as home garden.
Table 1: Respondent’s characteristics
Respondent’s characteristics
Village
Jabiren (n= 12 ) Pilang (n=12) Tumbang Nusa
(n=11)
Age (years) 33-63 34-76 36-64
Education (the highest frequency) High school (50%) High & Junior school (25%) Junior school (45.45%)
Main livelihood Farmer (75%) Farmer (75%) Farmer (45.45%)
Number of dependent family (person) 1-3 (66.67%) 1-3 (41.67%) >3 (54.54%)
Land holding:
• Rice eld (ha) 3.0 ± 0.88 2.0 ± 1.69 0
• Farm (ha) 21.29 ± 21.0 5.73 ± 4.21 2.87 ± 2.05
• Home garden (ha) 1.44 ± 1.8 0.5 ± 0.6 2.76 ± 0.6
Source: primary data
3.1.2 Farming types and production
Beside rice eld, farmers of the three villages managed their land (both mineral and peatland) as
a mixed cultivation. Rubber tree is the main commodity that was planted in the villages, both in
smallholder monoculture and agroforest with other tree commodities (Figure 1). Rubber tree can
be planted in the mineral and organic soil (peatland).
Figure 1: Farming types in Jabiren
The main source of livelihood comes from rice eld, farm and home garden. Yield average from
the main livelihood varied among the villages. In Tumbang Nusa village, where there was no rice
eld, farmers optimised their home garden as nurseries. Hence, the yield was counted as number
of seedlings per hectare (Table 2).
Table 2: Yield average from rice eld, farm and home garden
Village Yield average (ton/ha/year)
Rice eld Farm Home garden
Jabiren 1098.33 0.31 21,250
Pilang 920.37 1.18 5,100
Tumbang Nusa 0 0.94 75,000*
Source: primary data; *: unit: seedlings/ha
Sosio-economic characteristics of community living in peatlands .................................................................(Sumarhani & Hesti L. Tata)
577
Draft Only
3.1.3 Spearman correlation analysis
The Spearman correlation analysis was conducted to analyze correlation between categorical
and numerical parameter, which is shown at Table 3. Results show that education is correlated
positively with participation in an organization; on the other hand, sex has negative correlation with
participation in organization. Gross revenue has signicant positive correlation with farm holding,
farm revenue and participation in organization.
Table 3: Spearman correlation analysis of categorical parameter and farm holding and revenue of
the respondents in the Jabiren sub-district
Correlation
coefcient
Sex Occupation Education Organization Origin of
Resident
Farm
Holding
Farm’s
Revenue
Gross
Revenue
Sex 1
Occupation -0.178 1
Education -0.126 0.300 1
Organization -0.341* -0.239 0.451** 1
Origin of
resident 0.145 0.150 0.258 -0.12 1
Farm holding 0.075 -0.209 0.120 0.209 0.053 1
Farm’s revenue 0.158 -0.155 0.252 0.548** 0.123 0.334 1
Gross Revenue 0.122 -0.298 0.169 0.542** 0.078 0.354** 0.860** 1
Remark: * = signicantly different at the 0.05 level (2-tailed); ** = signicantly different at the 0.01 level (2-tailed)
3.1.4 Farming problems
Peatland management for farming in Jabiren encountered some problems. Respondents have
identied some common problems, such as frequent re and limited capital. Most respondents
stated that there was no problem in rice eld cultivation (Figure 2).
Figure 2: Some problems encountered in farming types
3.1.5 Collective action and institution
In the farming system, about 34.3% of the respondents stated doing collective actions. Most
respondents were managing the land individually. The communities usually do collective actions in
the land preparation, irrigation and road development, and re ghting.
Several organizations were developed in the three villages, such as farmer group (FG), cooperation,
and religious group (such as pengajian’ group and prayer group). About 65.7% respondents
participated in at least one organization. Each group usually has a commitment to have a regular
Proceedings of IUFRO – INAFOR Joint International Conference 2017
Yogyakarta, 24th– 27th July 2017
578
Draft Only
meeting. Every village has developed farmer groups (FG); there were 9 FGs in Jabiren, 4 FGs in
Pilang and 5 FGs in Tumbang Nusa (BPP Jabiren, 2010). An extension activity was conducted
irregularly, ranging from 5-8 times per year. An extension was responsible for every village to give
a counselling on agricultural, poultry and shery practices.
3.1.6 Perception on peatland management
Farmers’ perception on the current condition of peatland is shown in Figure 3. The respondents
stated that the general condition of peat-soil and peatland in the year 2012 was much better than
in 5-10 years ago. The better quality of peat soil was indicated by level of peat maturity, which
peat has been decomposed well. The mature the peat, the better peatland to be cultivated. Local
farmers recognised maturity of peat-soil by clenching up the soil and identifying the colour of the
peat soil. The decomposed peat has more compact and darker colour compared to un-decomposed
peat.
Figure 3: Farmers’ perception on the current condition of peatland
Farmers’ recommendations for the government (both local and national government) are shown
in Figure 4. Most respondents (about 40%) recommended for irrigation and canal development.
They mentioned that irrigation is crucial in agricultural development and peatland management.
Only one respondent recommended establishing a canal blocking in a big canal that has been
established in the west of Jabiren in the era of Mega Rice Project. He argued that the canal drained
water, so that the peatland was drying and became susceptible for re. About 14% of respondents
recommended establishing pump-wells and re breaks for re prevention.
Figure 4: Farmers’ recommendation on peatland management
Sosio-economic characteristics of community living in peatlands .................................................................(Sumarhani & Hesti L. Tata)
579
Draft Only
3.2 Discussion
The peatland area affected farming types of the respondents. There was no irrigated paddy eld
in Tumbang Nusa village, where encompassed the largest peatland area. Farmers in the study
area were only planted rice eld on the alluvial soil, where usually positioned along the river
banks. Rubber is the priority commodity of the three villages. Rubber latex production from the
respondents was 0.81 ton/ha/year (stdv: 0.72). Farmers managed home garden and rubber farm
in mixed farming systems, to optimize the yields despite of limited labour and time. Fruit trees,
such as Nephelium lappaceum, Artocarpus champeden, Durio kutejensis, Mangifera odorata, Musa sp., and
Ananas comosus, are usually planted with rubber trees. Some farmers also plant woody tree species,
such as Shorea balangeran (kahui) and Dyera polyphylla (pantung). The seedlings were purchased from
a seedling vendor, or were granted by the forestry institutions
Land holding of respondents in Tumbang Nusa village was very low, however they have other
options of livelihood, such as off-farm (as vendor, handyman), shing, collecting rattan and ‘purun’
grass (Elaocharis dulcis) from the forest, and nursery. Collecting rattan from forest of mixed farm is
not widely practised by rattan collector, because rattan price was not attractive anymore. The same
problem on the value chain of rattan has reported by Bizard (2013) and Myers (2014). In addition,
villagers who live along the river, were also collecting ‘purun’ grass. The grass has an economic
value and can be used for handicraft as mats, bags, hats, and others (Tata & Susmianto, 2016). The
value of ‘purun’ grass can be improved through improving quality of the products, and replanting
more ‘purun’ grass in restoration programme for continues supply.
There was a number of smallholder nurseries that has been established in Tumbang Nusa village.
The villagers have their own initiative to establish smallholder nursery of forest tree species,
because many rehabilitation projects and research have been conducted in this province. The seeds
and seedling sources were collected from the remnant forests in Jabiren sub-district and outside
the sub-district. The nursery of forest tree species have a good prospective in Central Kalimantan
province (Page, Hoscillo, Wosten, Jauhiainen, Silvius, …, et al., 2009; Osaki, Setiadi, Takahashi,
Evri, 2016)
The communities living on peatland depend on both forest and river resources. River as an integral
part of the peatland hydrological unit, is used by the community of Dayak Ngaju, a tribe who
are living on Kahayan river, as a main resource of livelihood and transportation. They have local
knowledge on cultivating and raising sh in the rivulet or ponds, by preserving habitat of the sh
(Nahan, Saputra, Juli, 2014). The potency of fresh sh of the village can be improved by adopting
cultivation technique. Some respondents (8%) suggested to the local government for a community
development programme on shery. In Riau, shery has been proposed as one important aspect in
the sustainable peatland management model, alongside with forestry, agroforestry and agriculture
aspects (Gunawan, Kobayashi, Mizuno, Kono & Kozan, 2016).
During the interview, some villagers realized that re was often occurred in a dry season. However,
very few respondents understood about peatland hydrology, as many of them recommended for
irrigation and drainage, on the other hand, only single respondent asked for blocking canal. After
the re in 2015, current situation has changed, where the community has high awareness on the
importance of re prevention.
Total gross revenue has a positive correlation with farm land-holding and revenue from farming
activity. The participation of respondents in an organization has also a positive correlation to
total gross revenue. Most respondents (65.7%) were participated in an organization,such as farmer
group, religious group, and cooperation. The interrelationship between human and natural resources
involves identifying feedback relationships among people, resources and institutions (Folke, 2006).
Proceedings of IUFRO – INAFOR Joint International Conference 2017
Yogyakarta, 24th– 27th July 2017
580
Draft Only
The correlation analysis apparently showed that participation in an organization creates positive
feedback in the human social systems of peatland ecosystem in Jabiren sub-district.
4. CONCLUSIONS
The main livelihood of the community of Jabiren sub-district was rubber farmers. The production
of rubber latex was about 0,81 ton/ha/year. The rubber trees were planted on mineral soils and
shallow peatland. Most farmers practised a mixed farming system of rubber and fruit tree species,
which can optimize the land productivity and income. Some respondents (about 40%) had low
awareness on a sustainable peatland management.
5. REFERENCES
BPP [Balai Penyuluh Pertanian] Jabiren. 2010. Program Penyuluhan Pertanian Balai Penyuluh
Pertanian Jabiren Raya. Kecamatan Jabiren Raya. Kabupaten Pulang Pisau. Provinsi Kalimantan
Tengah.
BPS (Badan Pusat Statistik] Pulang Pisau. (2011). Pulang Pisau Dalam Angka 2010. Pulang Pisau:
Badan Pusat Statistik Kabupaten Pulang Pisau.
Bizard V. (2013). Rattan futures in Katingan: why do smallholders abandon or keep their gardens in Indonesia’s
‘rattan district’? Working Paper 175. Bogor, Indonesia: World Agroforestry Centre (ICRAF)
Southeast Asia Regional Program. 23p. DOI: 10.5716/WP13251.PDF
Bonn A, Allott T, Joosten H, & Stoneman R. (2016). Peatland Restoration and Ecosystem Services: Science,
Policy and Practices. UK: Cambridge Press.
Departemen Dalam Negeri. (2006). Strategi dan Rencana Tindak Nasional: Pengelolaan Lahan Gambut
Berkelanjutan. Kelompok Kerja Pengelolaan Lahan Gambut Nasional. Jakarta: Departement
Dalam Negeri.
Folke C. (2006). Resilience: The emergence of a perspective for social-ecological analysis. Global
Environmental Change. 16:253-267.
Gunawan H, Kobayashi S, Mizuno K, Kono Y, & Kozan O. (2016). Sustainable management
model for peatland ecosystem in the Riau, Sumatra. In: Osaki M, Tsuji N (eds). Tropical Peatland
Ecosysems. Tokyo: Springer. Pp:113-123.
Hoscilo A, Page SE, & Tansey K. (2007). The role of re in the degradation of tropical peatlands:
a case study from Central Kalimantan. In: Rieley JO, Banks CJ, Radjagukguk B. (eds). Carbon-
climate-human interaction on tropical peatland. Proceedings of the International Symposium
and Workshop on Tropical Peatland, Yogyakarta, 27-29 August 2007, EU CARBOPEAT and
RESTORPEAT Partnership, Gadjah Mada University, Indonesia and University of Leicester,
United Kingdom.
Lamb D, Gilmour D. (2003). Rehabilitation and Restoration of Degraded Forests. IUCN, Gland,
Switzerland and Cambridge, UK and WWF, Gland, Switzerland. x +110 pp.
Medrilzam M, Dargusch P. Herbohn J, & Smith C. (2014). The socio-ecological drivers of forest
degradation in part of the tropical peatlands of Central Kalimantan, Indonesia. Forestry. 87:
335-345.
Myers R. (2015). What the Indonesian rattan export ban means for domestic and international
markets, forests, and the livelihoods of rattan collectors. Forest Policy and Economics. 50:210-219.
Sosio-economic characteristics of community living in peatlands .................................................................(Sumarhani & Hesti L. Tata)
581
Draft Only
Nahan AF, Saputra A, & Juli LF. (2014). Getting to Know the Dayaks Lawangan, Ma’anya, Bakumpai and
Biaju. Jakarta: PT. Equatorial Persada.
Osaki M, Setiadi B, Takahashi H, & Evri M. (2016). Peatland in Kalimantan. In: Osaki M, Tsuji N
(eds). Tropical Peatland Ecosysems. Tokyo: Springer. Pp: 91-112.
Page S, Hoscilo A, Wosten H, Jauhiainen J, Silvius M, Vasandar H, & Limin S. (2009) Restoration
ecology of lowland tropical peatlands in Southeast Asia: current knowledge and future
directions. Ecosystems. 12: 888-905.
Suwarno A. (2016). Optimising Land Use in Central Kalimantan Province: Modelling ecosystem
benets and land use dynamics. Wageningen: Wageningen University. PhD thesis. DOI:
10.18174/387054.
Tata HL & Susmianto A. (2016). Prospek Paludikutur Ekosistem Gambut Indonesia. Bogor: Forda Press.
Van Beukering P, Schaafsma, Davies O, Oskolokaite I. (2008). The Economic Value of Peatland Resources
Within The Central Kalimantan Project in Indonesia. Amsterdam: Institute for International Studies.
Vrije University.
Veloo R, Paramananthan S, & Van Ranst E. (2014). Classication of tropical lowland peats revisited:
The case of Sarawak. Catena. 118: 179-185.
Wetlands International Indonesia. (2004). Peta Sebaran Lahan Gambut, Luas dan Kandungan Karbon
di Kalimantan, 2000-2002. Bogor: Wetlands International – Indonesia Programme & Wildlife
Habitat Canada (WHC).
Proceedings of IUFRO – INAFOR Joint International Conference 2017
Yogyakarta, 24th– 27th July 2017
582
Draft Only
... Agroforestry has also been defined as a planting pattern where woody plants (trees) are planted on farmers' lands to create ecological interactions between agricultural crops and trees. In this concept, the social as well as the economic aspect play a role in maintaining the farmers' income [24,25]. ...
Article
Full-text available
Agroforestry on peatlands in Pulau Hanaut sub-district of Kotawaringin Timur is an approach that combines agricultural crops with trees on peatlands. The location of this project is in Serambut and Babaung villages, Pulau Hanaut sub-district. Primary data were collected through Focus Group Discussions (FGD), interviews, and direct observation in the field, and secondary data were collected by studying the related documents that existed. All the data then were analyzed by qualitative descriptive analysis. This site has a peat depth of less than 50 cm and a maximum water table between -10 to -15 cm. Peatland is a unique ecosystem that requires specific considerations for agroforestry practices. Implementing proper water management techniques, such as controlled water levels and irrigation, can help maintain the hydrological balance. Tree species selection that are suitable for peatland conditions were chosen by the communities, such as fruit tree species, cashew nuts, and enrichment planting on the current coconut farm. In addition, fire prevention is also an important part of peatland management. Therefore, zero-burning and organic farming practices should be implemented. Implementing agroforestry on peatlands requires careful planning, considering the unique characteristics of peatland ecosystems, and the ecological, social, and economic aspects of the local community. Local stakeholders’ involvement in decision-making processes is highly recommended to ensure the success of agroforestry initiatives on peatlands in the sub-district, which is part of the Mentaya-Katingan Peat Hydrological Unit, Central Kalimantan.
Book
Full-text available
www.cambridge.org/9781107619708 Peatlands provide globally important ecosystem services through climate and water regulation or biodiversity conservation. While covering only 3% of the earth's surface, degrading peatlands are responsible for nearly a quarter of carbon emissions from the land use sector. Bringing together world-class experts from science, policy and practice to highlight and debate the importance of peatlands from an ecological, social and economic perspective, this book focuses on how peatland restoration can foster climate change mitigation. Featuring a range of global case studies, opportunities for reclamation and sustainable management are illustrated throughout against the challenges faced by conservation biologists. Written for a global audience of environmental scientists, practitioners and policy makers, as well as graduate students from natural and social sciences, this interdisciplinary book provides vital pointers towards managing peatland conservation in a changing environment.
Chapter
Full-text available
Peatland area in Indonesia was about 14.91 million ha spread out in Sumatra 6.44 million ha (43 %), in Kalimantan 4.78 million ha (32 %), and in Papua islands 3.69 million ha (25 %). In 1995, Mega Rice Project (MRP) in tropical peatland launched in Central Kalimantan, of which project failed because of knowledge gaps, especially on peatland hydrology, water management, peat subsidence, impacts of long term drainage, mechanization problems on peatland and socio-economic consequences. This paper focuses on the peatland ecosystem affected by climate change, specifically the rainfall, relating with the position of the Intertropical convergence zone (ITCZ), which has a strong influence on the seasonal variations, and the seasonal patterns of rainfall variation in different parts of Indonesia. Further, to gain a better understanding of El Niño related phenomena, we provide details of the relationship among the Southern Oscillation index (SOI), the rainfalls during dry season in Central Kalimantan, and the lowest annual groundwater level in the tropical peatlands. Kalimantan, Indonesia side of Borneo Island, has two big water storage system in peatland near costal area and humid forest of Hurt of Borneo at central mountain area. In Kalimantan, there are Main Three River Basins: the Kahayan, Mahakam, and Kapuas Rivers, which connect the Heart of Borneo with the Mountain Ranges in Borneo (Water Tower) and peatland downstream (Water Pool). As both Heart of Borneo (Water Tower) and peatland (Water Pool) interact mutually, both ecosystems destruction will induce the reduction of resilience and increase of vulnerability.
Article
Full-text available
Connections between human activities (social systems) and nature (ecological systems) are key factors affecting forest-cover change in tropical peatland ecosystems. However, the complexity of these socio-ecological factors is often poorly understood. This study identifies the socio-ecological factors influencing land-cover change in the ex-Mega Rice Project area of Central Kalimantan Province, Indonesia. A systems thinking approach was used to construct two causal loop diagrams to assess the interrelationships between land-cover change, actors' choice and their motivation to convert land cover. The analysis reveals that current community livelihood activities to improve welfare and maintain food availability are the main endogenous drivers of land-and forest-cover change in the study area. Unintentional fire resulting from uncontrolled slash-and-burn practices by local communities is the main mechanism of forest-cover change. Land tenure uncertainty has also accelerated community land claiming using fire. Our analysis indicates that forest access, commodity prices and rainfall patterns are dominant exogenous drivers of land-cover change. Programmes that emphasize sustainable sources of food and income for local communities in conjunction with physical peatland restoration activities, such as drainage canal-blocking and reforestation, should be the key features of interventions aimed at preventing further peatland degradation.
Chapter
The peat swamp forest of the Riau Biosphere Reserve has been degraded at an alarming rate. The development of large areas of peatland as timber estates and palm oil plantations has caused a serious threat to the remaining peat swamp forest ecosystems. Forest and land fires have occurred annually, especially in the dry season, and the remaining peat swamp forest is subject to illegal logging activities and natural disturbances. Villagers continuously convert the remaining natural peat swamp forest into jungle rubber gardens and oil palm plantations. Four objectives of the study: (1) to clarify the current condition and ecological characteristics of the remaining peat swamp forest ecosystems, (2) reestablishing typical canopy tree species and restoring degraded peat swamp forest and peatland areas, (3) to determine a mechanism or directions for the participation of the local population; and, (4) to discuss a model for the promotion of sustainable management of peat swamp forest ecosystems in the biosphere reserve. The improvement of management of remaining peat swamp forests and rehabilitation should consider the unique ecological characteristics particularly the dominant tree species, fast growing species as well as the peat characteristics. The remaining peat swamp forests should be kept in their natural conditions in order to provide continuous ecosystem services, given their unique biodiversity characteristics, protection could be enhanced by adding incentives to local communities including monetary incentives from biodiversity and climate change mitigation funds. The promotion of a sustainable management model should be the direction of actions to conserve the remaining natural forests, regenerate and restore the degraded peat swamp forests, and create economic incentives enabling sustainability for the local community.
Article
Rattan is a vine that grows in tropical forests and is used primarily in the furniture industry. It is a billion-dollar industry involving hundreds of countries but the raw material is overwhelmingly collected from forests. Indonesia is the world's largest supplier of rattan. This article uses a value chain approach to elucidate the market, environmental, and social implications of an Indonesian policy that bans the export of un- and semi-processed rattan, which started on 1 January, 2012. The justification for policy was to reduce competition so that domestic furniture producers would fare better in export markets. A year after the policy took effect, actors benefit differently depending on where they are in the value chain and the nature of their activities. Only the largest and highest-end furniture factories on Java have experienced increased in sales. Forest-adjacent rattan-supplying actors in Kalimantan, Sulawesi and Sumatera are adversely affected. Those engaged in rattan smuggling from Indonesia are receiving the most immediate benefits. Together, these findings show that in the short term, the policy serves elite interests, whose political prowess enabled the policy to pass. In the long term, the industry is at risk of suffocation and the forests are jeopardised.
Article
The publisher regrets that this article is an accidental duplication of an article that has already been published in Global Environ. Change 16 (2006) 253–267, doi: 10.1016/j.gloenvcha.2006.04.002 . The duplicate article has therefore been withdrawn.
Rattan futures in Katingan: why do smallholders abandon or keep their gardens in Indonesia's 'rattan district'? Working Paper 175
  • V Bizard
Bizard V. (2013). Rattan futures in Katingan: why do smallholders abandon or keep their gardens in Indonesia's 'rattan district'? Working Paper 175. Bogor, Indonesia: World Agroforestry Centre (ICRAF) Southeast Asia Regional Program. 23p. DOI: 10.5716/WP13251.PDF