W.C. Wong, K.S. Ho & C.N. Wong
Forest Research Institute Malaysia, Kepong, 52109 Kuala Lumpur, Malaysia.
Received February 1988, accepted July 1988.
WONG, W.C.,,HOK.S.&WONG, C.N. 1988. Acacia mangium from Sabahfor plywood
and decorative panel manufacture: initial trials. Acacia mangium could be peeled and
sliced easily. Decorative panel with A. mangium sliced veneer as face appeared to be
attractive. Phenolic bonded plywood made with rotary cut A. mangium veneers met the
performance requirementfroweather-boil-proof (WBP) grade. However,tehbond quality of A. mangium plywood using urea formaldehyde adhesive was found to be poor. At 15 years of age,the logs were too small to be economically peeled using existing lathes
tailoredfropeeling big_tropical hardwood logs.ehTsmall sizetfeohlogs,fowhich some
were of poor form, resulted in low recovery rate. Trees for plywood production should
be bigger and in better form.eyKwords: Acacia mangium—slicing —peeling —panel production. Introduction Acacia, mangiumisbeing plantedaonlarge scaleinforest tree plantationsinSabah
and Peninsular Malaysia. In this paper, assessment on the suitability of A. mangium
for the production of plywood and decorative face veneer was carried out. A. mangium
sah also been successfully triedfro manufacturing medium density fibreboard
(Tomimura et al. unpublished, see also Anonymous 1985), as well as fibreboard
(Chew&Jaafar Ahmad 1986). Eight logstfreohtrials were received fromtehSabah
Forestry Development Authority (SAFODA).oTwcommercial mills assisteditenh
slicingandpeeling studies sincetehForest Research Institute Malaysia (FRIM) does
tnohaveanyslicing machineitsandpeeling latheisunsuitablefrosmall diameter logs.
Productionfodecorative panels from sliced veneers
Raw material Four logs which were numbered 1191, 180, 1526and1552 were selectedfroslicing
trials. Their characteristicsrae describedin Table.1These logs were selectedfro
slicing because their forms were poorandwere less suitablefropeeling into veneers.
These logs were firsttcuinto flitches.fo25mlongtaFRIM before they were sentto the mill for the slicing trial.
For further details log on website :
https://www.frim.gov.my/jtfsonline/jtfs/v1n1/42-50.pdf
The underlying decision theory of forest management changed from decisions
made by the forest manager, a single stakeholder, to a decision-making process,
which involves a variety of stakeholders with different goals. From concept to
implementation, forest professionals are in trouble because, despite the potential
of technological progress and the development of tools to support decision-mak-
ing, tools to facilitate multi-stakeholder decisions are lacking.
This paper proposes a framework to link social, economic, and biophysical
dynamics using multi-agent simulation to explore scenarios of collaboration for
forest plantation management. The modeling is based on decision theories. This
framework uses the concept of a value-added chain as a model of alliances. The
added-value breakdown analysis is a tool, which is used at the forest-plot level
as a means of anticipating benefit sharing among the stakeholders before they
decide to harvest; this also highlights the added-value variation from plot to plot.
The framework can also take into account noneconomic-based relationships. Each
stakeholder has explicit communication capacities, behaviors, and rationales, and
forest management emerges from their interactions.
The purpose of this modeling is to produce shared knowledge about dynam-
ics to facilitate coordination among stakeholders; it is a learning tool about forest
management. Ourmainhypothesisisthatstakeholders,bycreatingavirtualworld
with researchers, will learn about the effects that their own decisions might have
on themselves, others, and the environment. In the case of Sabah, we are at the
stage of the first loop of learning, and scenarios need to be further tested with
the stakeholders themselves. This forest plantation simulation suggests that the
development of sawmills adapted to plantation wood might offer a promising
pathway for increasing added value and the benefits of many stakeholders,
including local communities.
Principle 22 of the Rio Declaration on Environment and Development (1992) high-
lights the importance of local people and their participation in sustainable develop-
ment. In forest plantations, this should apply to local communities living in or near
forest plantations.
Malaysia, the country where Sabah State is located, is situated right in the heart
of Southeast Asia and is divided into two geographical sections: Peninsular Malaysia
and the East Malaysian provinces of Sabah and Sarawak in North Borneo (Fig. 1).
Fig. 1. Sabah location map The study area is located in northeastern Sabah, mostly in Bengkoka, Marudu, and
Keningau districts. Grasslands, logged-over forest, and secondary forest cover most
of the landscape.
Smallholders believe that many opportunities are provided for forest plantation
development. A lot of logged-over land is available for plantations. Sabah natives have
the possibility to obtain security over land and rural people have the will to invest in
forest plantations to secure their ownership of land, to rehabilitate the landscape, to
rehabilitate wildlife resources for hunting, and to invest for themselves and the com-
ing generations.
The Sabah Legislative Assembly created SAFODA (Sabah Forestry Develop-
ment Authority) in 1976. Its mission is to develop highly productive forest plantations
for the long-term supply of wood resources and to improve the socioeconomic status
of the state and country on a sustainable basis (SAFODA 2003). Currently, SAFODA
manages about 100,000 ha of land.
The local government perceives the development of forest plantations in this part
of Sabah as a means to improve the landscape and smallholder income. Today, most
of the land, which has been logged over and is unused, is highly fire-prone (a lot of
areas are covered with Imperata cylindrica and large stocks of remaining deadwood).
The development of smallholder plantations could also produce a variety of plantation
systems. These plantations will reduce the areas’ fire proneness and would involve
the local population in fire control.
The wood price is a major impediment to the development of all plantations.
Sabah State has already invested a lot in smallholders’ plantations and SAFODA
estates. So far, SAFODA plantation area amounts to 31,000 ha. The planted species
are Acacia mangium (28,000 ha) and rattan (2,100 ha). SAFODA encouraged small
landowners, adjacent to their forest plantation areas, to grow trees. Currently, these
smallholder plantations amount to 3,000 ha supervised by SAFODA.
For further details log on website :
http://www.commod.org/content/download/4265/32016/version/1/file/17_Guizol_2005_BC.pdf
H. Purnomoa and Ph. Guizolb
aCIFOR, Center for International Forestry Research, Bogor, Indonesia. Email: h.purnomo@cgiar.org
bCIRAD, Centre de coopération Internationale en recherche agronomique pour le développememnt, Bogor
Indonesia. Email: p.guizol@cgiar.org
Abstract: Good forest governance lets all relevant stakeholders participate in the decision-making processes.
Illegal logging and forest degradation are currently increasing, and logging bans are ineffective in reducing
forest degradation. At the same time interest in forest plantations and concern about poverty problems of
people adjacent to forests continue to increase rapidly. Governments have identified the development of
small forest plantations as an opportunity to provide wood supplies to forest industries and to reduce poverty.
However, the development of small plantations is very slow due to an imbalance of power and suspicion
between communities and large companies. Current regulations do not offer many links amongst various
stakeholders. The paper proposes a framework to link up social, economic and biophysical dynamics using
multiagent simulation to explore scenarios of collaboration for plantations. Multiagent simulation is a branch
of artificial intelligence that offers a promising approach to deal with multi-stakeholder management systems,
such as the case involving common pool of resources. It provides a framework, which allows analysis of
stakeholders’ (or agents’) decisions in interaction. Each stakeholder has explicit communication capacities,
behaviors and rational from which emerge specific actions. The purpose of this modeling is to create a
common dynamic representation to facilitate negotiations to grow trees. Collaborations involving multi-
stakeholders, especially local communities and wood based industries, appeared to offer the most promising
pathway to accelerate plantation development toward local communities’ poverty alleviation and forest
landscape improvement.
Keywords: Governance, forest plantation, local communities, collaboration, multiagent simulation, multiple
stakeholders
1. INTRODUCTION
Principle 22 of the Rio Declaration on
Environment and Development (1992) highlights
the importance of local people and their
participation in sustainable development. In
forest plantations, this applies to local
communities living in or near forest plantations.
In Sabah forest plantation stakeholders believe
that many opportunities are met for smallholder
forest plantation development. A lot of logged
over land is available for plantation. The Sabah
natives have the possibility to get security over
land and the rural people have the will to invest in
forest plantations (to secure their ownership of
land, to rehabilitate the landscape, to rehabilitate
wildlife resources for hunting, and to invest for
themselves and the coming generations).
Nevertheless, they do not want to invest as long
as the wood prices are low. This situation is a
major impediment for development of small
plantations.
The challenge is to create the conditions for the
co-development of plantation forests and down
stream industries using plantation wood. On the
one hand, investors will consider investments into
down-stream industries for plantation wood if
mature plantations are available; they might also
differ such investments as long as faster returns
from natural forest logging exist. On the other
hand, smallholders will not invest in plantations
as long as they do not have the guarantee of better
prices. Currently SAFODA (Sabah Forestry
Development Authority) have to export, at low
price, fast growing wood produced on its own
plantations as the existing paper mill in Sabah
(Sabah Forest Industries) is too far away from
SAFODA plantations.
Sabah State has already invested a lot in
smallholders’ plantations and SAFODA Estates.
However, this development is in crisis as
SAFODA is facing problems in self-financing its
development in the current context of low wood
prices. It looks like more coordination is needed
between the Sabah policy of plantation and
smallholder development and wood processing
development.
For further details log on website :
http://www.mssanz.org.au/MODSIM03/Volume_03/B02/09_Purnomo.pdf
Published Date
Mathematical and Computer Modelling September 2006, Vol.44(5):535–552,doi:10.1016/j.mcm.2006.01.009 Application of Natural Computing Methods to Water Resources and Environmental Modelling Open Archive, Elsevier user license Author
Herry Purnomo a,b,,
Philippe Guizol c,
aCIFOR, Center for International Forestry Research, Bogor, Indonesia
bDepartment of Forest Management, Faculty of Forestry, Bogor Agricultural University, Bogor, Indonesia
cCIRAD, Centre de coopération Internationale en recherche agronomique pour le développement, Bogor, Indonesia
Received 6 December 2004. Accepted 11 February 2005. Available online 3 March 2006.
Abstract
Co-management of forest resources is a process of governance that enables all relevant stakeholders to participate in the decision-making processes. Illegal logging and forest degradation are currently increasing, and logging bans are ineffective in reducing forest degradation. At the same time interest in forest plantations and concern about poverty problems of neighboring people whose livelihoods depend on forest services and products continue to increase rapidly. Governments have identified the development of small forest plantations as an opportunity to provide wood supplies to forest industries and to reduce poverty. However, the development of small plantations is very slow due to an imbalance of power and suspicion between communities and large companies. This paper proposes a framework for linking social, economic and biophysical dynamics to create multi-agent simulations and explore scenarios of collaboration for plantations. Multi-agent simulation is a branch of artificial intelligence that offers a promising approach to dealing with multi-stakeholder management systems, such as common pool resources. It provides a framework which allows analysis of stakeholders’ (or agents’) interactions and decision making. Each stakeholder has explicit communication capacities, behaviors and rationales from which emerge specific actions. The purpose of this modeling is to create a common dynamic representation to facilitate negotiations for growing trees. A system of governance involving multi-stakeholders, especially local communities and wood based industries appearing to offer the most promising pathway to accelerating plantation development, local community poverty alleviation and forest landscape improvement.
Keywords
Governances
Forest plantation
Multi-agent
Simulation
Stakeholder
1 Introduction
Principle 22 of the 1992 Rio Declaration on Environment and Development highlights the importance of local people and their participation in sustainable development. In forest plantations, this applies to local communities living in or near forest plantations.
1.1 Site description
Malaysia is situated right in the heart of South East Asia and is divided into two geographical sections: Peninsular Malaysia and the East Malaysian states of Sabah and Sarawak in North Borneo. Sabah lies between 5∘ and 7∘ north of the equator. Sabah is bordered by Sarawak on its south-western side, and Kalimantan (Indonesian Borneo) to the south. Sabah has a coastline of approximately 800–900 miles of the South China Sea in the west and north, the Sulu Sea in the northeast and the Celebes Sea in the east. Fig. 1 shows a map of Sabah.
Fig. 1. Sabah location map.
Sabah is settled by Malay and Mongoloid peoples. The largest indigenous group in Sabah is the Kadazandusun group, followed by the Bajau and Muruts groups. Another big group is the Chinese. The Chinese have intermarried with the local population, mainly with the Kadazandusun group. Centuries of migration, mixed marriages, pirate raids, isolation and trade have produced a profusion of ethnic groups that defy simple classification. There are at least 30 distinct ethnic/linguistic indigenous groups in Sabah, speaking different languages and close to 100 dialects. Sabah is a melting pot of many indigenous and immigrant groups.
1.2 The stakeholders
The Sabah Forestry Development Authority (SAFODA) was established when Enactment No. 20 of 1976 was passed by the Sabah Legislative Assembly. This enactment was replaced by Enactment No. 24 of 1981 to make better provisions with respect to the constitution, administrative procedures, functions and finance of SAFODA. Its mission is to develop highly productive forest plantations for long-term supply of wood resources and the improvement of the socio-economic status of the state and country on a sustainable basis [1].
Currently SAFODA manages about 100,000 ha of land in Sabah located mostly in the Bengkoka, Marudu and Keningau districts. The forest area amounts to 31,000 ha. The planted species are Acacia mangium (28,000 ha) and rattan (2100 ha). SAFODA and Sabah Forest Industries (SFI) encourage small landowners, adjacent to their forest plantation areas, to grow trees. Currently these smallholder plantations amount to 3000 ha and 1900 ha, respectively, supervised by SAFODA and SFI.
The Sabah forest plantation stakeholders believe that many opportunities are met for smallholder forest plantation development. A lot of logged land is available for plantation. The Sabah natives have the opportunity to obtain security over land and the rural people have the will to invest in forest plantations (to secure their ownership of land, to rehabilitate the landscape, to rehabilitate wildlife resources for hunting, and to invest for themselves and the coming generations).
1.3 Problems
Smallholders do not want to invest as long as wood prices are low. This situation is a major impediment to the development of small plantations. The challenge is to create conditions that are conducive to the co-development of plantation forests and downstream industries that use plantation wood. On the one hand, investors will consider investments in downstream industries for plantation wood if mature plantations are available. They might also defer such investments as long as faster returns from natural forest logging exist. On the other hand, smallholders will not invest in plantations as long as they lack the guarantee of better prices. Currently SAFODA have to export, at low price, fast growing wood produced on their own plantations, as the existing paper mill in Sabah (Sabah Forest Industries) is too far away from SAFODA plantations.
Sabah State has already invested a lot in smallholders’ plantations and SAFODA Estates. However, this development is in crisis, as SAFODA is facing problems in self-financing its development in the current context of low wood prices. It looks like more coordination is needed between the Sabah policy of plantation and smallholder development and wood processing development.
The local government perceives the development of forest plantations in this part of Sabah as a means to improve the landscape. Today most of the land which has been logged and is unused is highly fire prone (many areas are covered with Imperata cylindrica, and large stocks of remaining dead wood). The development of smallholder plantations, backed by different small-scale wood processing industries (sawmills), could produce a variety of plantation systems. These plantations will reduce the areas’ proneness to fire and would involve the local population in fire control. This research explores such scenarios of co-development of smallholder plantations and wood processing industries.
1.4 Research purpose
The goal of the model developed in this research is to explore scenarios for improving land use and incomes of different stakeholders, at a regional level. This paper observes sustainable forest plantations under a multi-stakeholder or multi-actor context, where actions and reactions of each stakeholder are examined in conjunction with the behaviors of other stakeholders. Hence, the purpose of this paper is to describe a multi-agent simulation of a multi-stakeholder forest plantation.
This research used CORMAS (Common Pool Resources and Multi-Agent System), a multi-agent simulation platform specifically designed for renewable resource management systems. It provides a framework for developing simulation models of the interactions between individuals and groups that jointly exploit common resources. CORMAS facilitates the construction of a model by offering predefined elements, which the user can customize to a wide range of specific applications [2].
2 Multi-agent systems and natural resource governance
Policy makers should be able to assess the very long term impacts of their decisions, such as the establishment of plantations or wood processing industries. Some major impacts might occur beyond the normal periods of monitoring. Simulation is one way to address this question, and may be the only viable alternative if the system is large or complex. “Simulation” means making a simplified representation of a real-world situation, and animating it so that stakeholders might envision what the future situation might be. Multi-agent simulation (MAS) is a promising way to examine natural resource and environmental management issues [3]. The hallmark of MAS is the recognition of “agents”, which are entities with defined goals, actions, and domain knowledge. Agents operate and exist in an environment. The environment might be open or closed, and it might or might not contain other agents. If it contains other agents, it can be seen as a society of agents or MAS.
Simulating the stakeholders’ activities and interactions requires a tool that is able to represent the individual’s knowledge, beliefs, communication and behavior. MAS has been applied to the modeling of natural resource management. One of the first applications was to a common property management regime that is frequent among developing nations, particularly with agriculture and forest-related resources. In this context, much of the initial development and application of MAS was done by Bousquet [4]. Several authors have since applied MAS to a number of cases and studies: irrigation systems [5], resource sharing regimes [6], natural resource management [7], game management [8], economic and social development [9], and environmental management [3] and [10].
International calls for sustainable forest management are increasingly concerned with questions of forest governance, i.e. with the rules under which power is exercised in the management of forest resources, and the relationships between the state and its citizens, civil society and the private sector [11]. The improvement of natural resources will depend largely on the relative power of the groups favoring and opposing the natural resource policies and regulations [12]. Governance is the process by which individuals, and institutions, public and private, manage their common concerns in an increasingly complex world [13] and [14].
Governance issues encompass global–local links, sector–sector links, and values’ divergences. Policy and legal and institutional conditions affecting forests derive from the local level (e.g. community rules and social norms regarding forest use), the national level (e.g. legal rights to forest land and resources, and policies affecting the relative profitability of different forest uses), and the global level (e.g. multilateral environmental agreements affecting forests, trade rules, and the policies of multinational companies and investors) [15]. Good governance is characterized by participation, transparency, accountability, rule of law, effectiveness, and equity in both decision-making processes and their outcomes. Co-management of forest plantation is a form of good forest governance. Co-management is ‘a situation in which two or more social actors negotiate, define and guarantee amongst themselves a fair sharing of the management functions, entitlements and responsibilities for a given territory, area or set of natural resources’[14].
3 The simulation
3.1 Methods
Stakeholders were identified according to the following criteria: proximity to the forest, legal or traditional rights over the forest, dependency on the forest, and knowledge of forest management [16]. Stakeholder characteristics were recognized through field visits and group discussions [17]. Researchers facilitated the discussions to establish stakeholder identities, their rationale, and their behavior and actions. These characteristics formed the basis for the MAS model developed subsequently. Other data were obtained from SAFODA and related literature.
There are four key phases in the development of a model [18]: i.e. (a) Forming a conceptual model is to state the model’s objectives, bound the system of interest, categorize its components, identify relationships, and to describe the expected patterns of the model‘s behavior; (b) Specifying the model is to identify the functional forms of the model’s equations, estimate the parameters, and to represent it in CORMAS; (c) Evaluating the model is to re-assess the logic underpinning the model, and compare model predictions with expectations; (d) Using the model is to develop scenarios.
3.2 Model development and results
At the current stage we emphasize the development of a general model of multi-stakeholder forest plantation. We used a spatial plantation situation that commonly occurs in the world of forest plantations. Thus, the model is more a general model rather than a site-specific model.
3.2.1 Forming a conceptual model
The agent’s ability to communicate is critical. An agent might engage in economic behavior. To model this specific behavior, we use the added-value chain theory. Agents in the model anticipate the outcome of their decisions during the decision process. They evaluate this outcome against their goals.
The value chain is a short-lived alliance among a variety of stakeholders to produce goods from forests. This concept allows us to integrate different decision levels and forces us to describe the communication patterns among stakeholders and the perceptions and goals that govern each stakeholder’s behavior. Usually, the value chain is reduced to the supply chain perspective of an industry, which tries to secure its supplies. Here, we look at it in another way, from the forest; the value chain concept helps to anticipate, before harvest, the use of the wood and benefits that wood products will produce, what stakeholders in the forestry sector are doing, consciously or intuitively, in the real world.
This system of alliances is the result of negotiation among stakeholders who try to reach their own goals by communicating with other stakeholders. It is a snap alliance, as it can change over time according to stakeholders’ changing perceptions of the environment and relationships. This allows us to represent the interaction between forest dynamics and social issues, as it links these changing alliances directly to the rate of harvesting, which affects the forest dynamics.
We use the value-added breakdown, which includes costs and added value at all stages, to analyze the contribution of each stakeholder to the final product price, from the wood’s standing value to the retail price of the final product. The coordination of the economic goals of diverse stakeholders through negotiation is the process which generates the structure of the value-added breakdown. It bridges social and economic issues.
The price breakdown structure of standing wood, while analyzed at each forest-plot level of a map, shows in many cases some difference according to the forest-plot location. This bridges economic issues to spatial structure. Negotiations take place on each patch of the map, revealing links between economics and space.
3.2.2 Identifying stakeholders
The stakeholders identified, based on the criteria mentioned previously, are SAFODA, smallholders, brokers (for pulp and sawmill), and the government. Fig. 2 describes the use case diagram of the stakeholders. The diagram shows the major role of the stakeholders in the plantation system. SAFODA and the smallholders grow Acacia in their plantations. They then negotiate with a buyer to sell their timber. The brokers sell the wood to mills. The government observes the impacts of stakeholder interactions on the incomes of smallholders, wood availability and landscape.
Fig. 2. The unified modelling language use case diagram of the plantation system.
Table 1 describes the goals and strategies of the above stakeholders. As SAFODA is currently facing financial problems, improving income by attempting to reduce its costs and to increase its returns is its current goal.
Table 1. The selected stakeholders, their goals and strategies
Stakeholder
Goal
Strategy
SAFODA
To improve its returns
To reduce its costs and to increase its revenue.
Smallholders
To improve their well-being
To expand their plantations for pulp or timber if the wood price is high enough. To convert their wood pulp plantations to timber wood plantation or other uses if these wood pulp plantations are not commercially viable.
Buyers
To improve their profits
To mediate wood producers and consumers for obtaining their profit margin of 20% or more. They take care of logging and transportation costs. The buyers take into account the mill location to calculate the log price.
Government
To achieve forest sustainability
To formulate and execute policies and regulations in order to have more smallholders, more wood resources and forested landscape.
Sawmill
To be supplied with wood for sawn timber
To inform the wood producers about the sawn wood price.
Harbor/pulp mill
To be supplied with cheap pulp wood
To inform the wood producers about pulp wood price.
The smallholders are trying to improve their well-being. They currently hold small plantations for pulp and sawn timber. They behave with economic rationality regarding their plantations. We did not find any significant non-economic values associated with their plantations. Since the beginning they have perceived plantations as a way to improve their incomes. They actively search for a better price for their existing wood stock. If the wood price is high enough, they will expand their plantations for pulp or timber depending on the profit margin they can make. If their wood pulp plantations are not commercially viable, they will convert them to timber wood plantations if this is commercially feasible. If the timber plantations are not feasible to plant then they will convert them to other uses or will just leave them unmanaged. This means decreasing the forest coverage and wood supply.
Wood brokers also behave with economic rationality. They will buy wood from SAFODA and the smallholders if they can draw profits from it. The brokers carry out logging and take care of the transportation costs. Their profit margin is about 20%. The brokers calculate the costs of logging and transportation based on the distance of the plantations to the harbor or sawmill and on the quality of the road network.
The overall goal of the government is forest sustainability. The government is looking to improve conditions for their people through having more smallholders, as well as more wood resources. The establishment of small plantations aims to improve the people’s well-being, to sustain wood resources and to improve the landscape. If the wood resources are sustained, the economy of Sabah State will be improved.
Currently the wood for pulp is transported to the harbor for export. There is no sawmill or pulpmill that is near the areas of plantation. In the model we created virtual stakeholders, i.e. sawmills and pulpmills, to generate possible future scenarios.
3.2.3 Specifying the model
To increase the modularity of the model we used organization centered MAS (OCMAS) instead of agent centered MAS (ACMAS) to construct the model. OCMAS separates organization description from agent description. The organization provides a framework for activity and interaction through the definition of roles, behavioral expectation and authority relationships, such as control. We view an organization as a collection of roles, which stand in certain relationships to one another, and take part in systematic institutionalized patterns of interactions with other roles. An individual agent may play multiple roles depending on the social groups in which it is participating. An agent may be a member of several social groups. Two agents can interact and communicate only if they are members of the same social group [19].
The use case diagram (Fig. 2) describes the actors and their roles in the plantation system. These roles can be categorized into four social groups, namely: forest plantation governance, tree growing, tree trading and wood trading groups (Table 2). An organization that structures these groups is shown Fig. 3. Actors are represented by entities we call agents. Agents and objects play various roles (in pentagons) and interact in groups that we symbolize with ovals. Agents are represented as “skittles” and objects as squares.
Table 2. Social groups, roles and agents in the model
Social groups
Roles
Actors and objects
Forest plantation governance
Policy maker
Sabah state government
Forest development agency
SAFODA
Citizen
Smallholders
Profit maker
Brokers, sawmill, pulpmill
Landscape
Big plots, small plots
Tree growing
Tree grower
SAFODA, smallholders
Wood producer
Trees
Tree trading
Tree seller
SAFODA, smallholders
Tree buyer
Brokers
Tree resource
Tree plots
Wood trading
Wood seller
Brokers
Wood buyer
Sawmill, pulpmill
Fig. 3. The organization level of the forest plantation model.
The Sabah state government takes the role of policy maker in developing regulations to accelerate the development of the plantation, to improve the livelihood of their citizens and to rehabilitate the landscape. The role of the forest development agency is played by a state-owned company, namely SAFODA, which performs a major role in executing the government’s policy while maintaining its own financial sustainability. The smallholders, who are usually not rich and live in the countryside of Sabah, play the role of citizen or inhabitant.
The smallholders and SAFODA play roles of tree grower and tree seller as they grow Acacia and sell it. The brokers buy wood from the tree grower and sell it to the wood buyers; they play the roles of tree buyer and wood seller. Pulpmills and sawmills play the role of wood buyer, and process the wood in their factories. The mills are the end consumers of the trees in the simulation.
The organization level of the model can be represented by a class diagram. The class diagram shows the static structure of the model, with the elements that exist (such as classes and types), the internal structure of the elements, and their relationships to one another. The unified modeling language (UML) class diagram of the model (Fig. 4) represents classes connected by static relationships which are aggregation/composition (a line connecting two classes with a diamond symbol), generalization/specification (a line connecting two classes with an arrow symbol) and association (a line connecting two classes and showing its cardinality or multiplicity). A class is represented as a box with three parts: class name, class attribute(s) and class method(s). A class name in italics means an abstract class. An abstract class is a class that cannot be instantiated1 into agents or objects. It exists only to allow subclasses to inherit its attributes, methods and associations.
Fig. 4. The unified modelling language class diagram of the model.
We treat the relation between an agent and its role(s) like a ‘generalization link’ between a class and an abstract class. For example, in Fig. 4, smallholders and SAFODA are classes that can be instantiated and inherit all properties of the abstract class of tree grower and tree seller. If an agent is assigned a certain role, it will have all properties within that role. An agent can take on or abandon roles during the simulation. An agent may also create a social group where several agents with various roles interact. Therefore, every instantiated class has at least three possible actions, which are: createGroup, getRole and leaveRole.
If a class diagram represents the static structure of the model, a sequence diagram represents the dynamic interaction of the model. The sequence diagram shows the actors or objects participating in an interaction and the events they generate arranged in a time sequence. It describes the flow of information of a single possible scenario. Instead of actors or objects we use roles of agents or objects to illustrate the interactions of participants in a possible scenario, as a sequence diagram of UML (Fig. 5).
Fig. 5. The unified modelling language sequence diagram of the model.
To improve the conditions of the citizen, landscape and profit maker, the policy makercreates incentives to grow trees for their citizen. The incentive is distributing 15–30 hectares of the state land to those who grow trees. The policy maker also encourages the forest development agency to establish tree plantations.
The tree grower grows and maintains trees that take the role of wood producer. After a certain period the wood producer is ready for harvest. On the other hand, the wood buyer can send a message to the wood seller that it needs wood at an acceptable price. The tree buyer sends a message to the tree seller that it needs trees. Negotiation takes place between the tree seller and the tree buyer regarding tree price. The tree buyer considers the cost of harvesting and transporting the trees to the wood buyer. If the price is settled then the wood seller offers wood and negotiates its price and quantity with the wood buyer. If the wood buyer agrees on the price, a contract to buy the wood will be signed by both parties. Then the tree buyer sends a message to the tree seller to buy and harvest the trees. The wood seller delivers the wood to the wood buyer.
The internal agent’s reasoning and learning, through its role(s), is represented using simplified classifiers of the genetic algorithm architecture as illustrated in Fig. 6. It is a rule based system that is able to learn by adjusting rule strength from environmental feedback and by discovering better rules using genetic algorithms [20]. The genetic algorithm reproduces the rules for its survival and its improved performance in the society of agents.
Fig. 6. The internal agent architecture of the model.
Inputs of information from the environment are perceived by an agent as perceptions. Perceptions are coded into a binary format of a certain number of digits in the fact base. The Rule base will work to transform the perception codes into action codes. The action codes are decoded into actions in the fact base. The agent’s actions will take place to influence the environment. These consecutive steps happen in the absence of any learning processes. The perceptions can reinforce the strength of each rule in the rule base. The rule strength represents the priority of the rules to be used to transform the perceptions into actions. A rule that produces benefit feedback will strengthen, a rule that produces a drawback will weaken, and a rule that produces trivial feedback will remain at the same strength.
Genetic algorithm based rule reproduction is guided by the genetic-like principle that rules that increase an agent’s fitness in its societies will continue to exist in the next period; otherwise they will not. Some rules randomly continue or discontinue existence regardless of their strength in the next period. Rules that are never used and weaken all the time are subject to disappearance in the next period. For each time period the previous rules are inherited with adaptation based on the fitness of the rules for surviving in the society.
Encoding of perceptions is used to simply represent combination between perceptions. The perception code ‘1’ means ‘yes or positive’, ‘0’ means ‘no or negative’, and ‘#’ means ‘nothing or not enough information’. The code combination means ‘operator of AND’. For example, the three-digit combination of ‘110’ means there is land degradation, and citizen livelihood is acceptable, but wood resources are not available. ‘11#’ means there is land degradation and citizen livelihood is acceptable, but wood resources are not certain or there is not enough information on it to be perceived. The same rules are applied in decoding the actions. The rules take a format of <strength>:<perception>→<action>, where <strength> ranges between 0.0 to 1.0, and <perception> and <action> consist of a multiple-digit codes consisting of ‘1’ and ‘0’. For example, <perception> of ‘110’ means ‘yes or positive’ for the first and second perception and ‘no’ for the third perception.
The reinforcement process is formulated as strengthening or weakening the rules by 0.1. Table 3 shows the way an agent, in its role, reasons and learns. We have only provided brief descriptions of them, to keep them easy to follow. All roles of actors have the same reinforcement rule.
Table 3. The internal reasoning of the agents
Role
Perceptions/Inputs
Possible actions
Rules
Role taking possible class
Instantiation able class
Policy maker
‘Existence of land degradation’, ‘quality of citizen livelihood’, ‘lack of availability of wood resource’.
‘Inform of incentive for plantation development’, ‘order another agent to plant trees’, ‘inform that we have sustainability of plantation’
Policy maker class. Its attributes: goal, citizen satisfaction, environmental quality.
Government
Forest development agency
‘Order from the government’
‘To follow order from the government’, ‘to maintain financial sustainability’
.
Forest development agency class. Its attributes: goal, mission achievement.
SAFODA
Citizen
‘Opportunity of livelihood improvement’
‘To take opportunity’
Citizen class. Its attribute: goal, level of well-being
Smallholder
Profit maker
‘Opportunity of adding a value to various products’
‘To take opportunity’
Profit maker class. Its attribute: goal, level of survival.
Broker, Pulpmill and Sawmill.
Tree grower
‘Profitable tree prices’, ‘valuable incentive from the government to manage state’s land’, ‘instruction from the government’
‘To grow tree’, ‘move to other location’
; ; ;
Tree grower class. Its attributes: goal, cost, revenue, income
Smallholder, SAFODA.
Tree seller
‘Profitable tree prices’
‘To sell trees’
Tree grower class. Its attributes: goal, cost, revenue, income.
Smallholder, SAFODA
Tree buyer
‘Profitable wood price’, ‘Reasonable tree offer’, ‘tree quantity available’
Wood producer class. Its attributes: number of trees, standing stock.
Small tree plot, Big tree plot.
Table 4 shows the dynamics of pulpwood growth volume, which is used in the simulation; it is obtained from different sources. At 10 years mean annual increment growth it is 14 m3/ha. At 11 and 12 years the annual volume is 15 m3/ha, and there is no volume increment afterward. In the simulation the growth of smallholder and SAFODA pulp plantations is the same.
No increment for the first year. The increment is the difference between two subsequent years after planting.
For the initial conditions, a simulated map represents the forest landscape, including explicit locations of roads, vegetation and forest management plots. Each pixel represents an area of 25 ha. Fig. 7 shows a virtual map of the forest landscape where agents of SAFODA, smallholders and the pulp mill are located. Small triangles represent smallholders. Large plots marked 1 are SAFODA forest management plots. The different gray values relate to the plot wood stock, while black illustrates that the plot is ready to be cut. The black areas at the bottom of the map represent the sea (5) and the harbor (7) from which wood is exported. In the top right, the large area marked (5) is the pristine forest. The white areas represent land devoted to agriculture, to which access for forest development is forbidden. The Y shaped lines are roads, with different gray shades relating to road qualities and subsequently to different transportation costs.
Fig. 7. Representation of forest landscape. Small triangles represent smallholders located in their forest plots at the beginning.
Objects and agents instantiate most classes of the model. For example, the pulp plantation object instantiates the big tree plot class, whereas pulp and sawn timber plantation objects instantiate the small tree plot class. These classes compose the abstract classes of landscape, wood producer and tree sources. The objects take the roles landscape, wood producer and tree sources.
The broker that takes the role of tree buyer computes transportation costs, which are linked to the distance between the plots and mills, by considering the existence of the roads and their quality. The transportation cost becomes an attribute of each cell. If there is a road then the transportation cost is lower than if there is no road. Similarly, the better the road quality, the lower the transportation cost. The algorithm seeks the path where the transportation cost is the lowest. This is done by looking at the transportation cost that is represented in eight cells surrounding the cell where the wood is located. If these eight cells have exactly the same transportation cost attribute, then the algorithm looks at the cells surrounding those eight cells, and so forth. The different distances, between plots, to the road network and to the mills, will create different production costs.
Currently SAFODA and the smallholders grow trees for pulp. The harbor agent creates the group of wood buyers and takes the roles of a wood buyer and a profit maker; however, none instantiates the Sawmill class. This is the subject of the creation of the scenario investigated in this paper.
3.2.4 Evaluating the model
The study includes model development, tests and uses. Tests rely on the comparison of observed and simulated outcomes as well as careful consideration of the logic and behavior of the model. The dynamic responses implicit in many natural resource management questions add to the challenges of interpretation and testing [21].
The present model was evaluated using two criteria: the logic of the model and its outcomes, and the similarity between predictions and expectations. The model passed these criteria. The assessment that the model was reasonable was based on systematic checking of all the relationships within the model, from the simplest sub-model (forest plantation growth), to the more complex sub-models (e.g. the agents’ communications). Finally, overall model performance was assessed. This assessment led to the conclusion that the model complied with the patterns we expected a priori. The model has been found to be useful, particularly for developing scenarios and observing the likely impacts of each scenario on the forest landscape and on the incomes of smallholders.
3.2.5 Learning from the model
This section examines some of the insights gained from the process of constructing the model and examining its outputs. Simulation outputs from the model are also used to illustrate that the development of a sawmill leads to sustainable forest management through better added value chains of tree plantation.
In the current situation (the baseline simulation) the negotiations take place among the various agents, as described in Fig. 8. Some smallholders interact, negotiate and sell their trees to the broker when their plots are ready to be cut and the broker wants to buy. The profit margins that the smallholders obtain from the deal will feed back into future actions. As a result planting the plot may not be a good choice any longer. If the margins are high enough then they will replant the plots. If the plots are not profitable they will abandon the existing plots for the next planting period. Some smallholders may learn that other smallholders who have pulp plots closer to the road are offered a higher price for their trees by the broker.
Fig. 8. The interaction among agents. Small triangles numbered 1–40 represent the smallholders.
After 10 years, most smallholders move to the sites close to the road network to maximize their benefits in relation to transportation costs (Fig. 9). These sites are degraded forest owned by the government. They do not re-plant the existing pulp plantation. This means that the existing pulp plots are not sustainable. Fig. 10 shows the resulting reduction, in the pulp plantation area, for the different generated random values.
Fig. 9. Smallholders leave their plantations. They leave their plots as indicated by arrows, and look for new accessible plots closer to the main road.
Fig. 10. Average collective knowledge of the smallholders’ agreement (+) or disagreement (−) on re-planting their plots.
The smallholder’s decision to re-plant depends on existing rules and feedback as well as the need to survive. The ‘feedback’ comes from their previous experiences and knowledge sharing among neighbors. This collective knowledge is written on a “blackboard”. Each smallholder’s experiences with planting, in particular with regard to their knowledge of whether planting is profitable or not, are also written on the “blackboard”. Fig. 10 shows the group’s collective knowledge during the simulation. This combination of feedback from his/her own experiences, the other smallholders and random values will reproduce the rule strengths that are then used for future action. In this experiment our objective was to examine behaviors after the first wood harvests; we did not explore how behaviors might change in the long term. This is how the simplified classifiers of the genetic algorithm work in the model. We use the term ‘simplified’ to express this limitation.
The plots tend to be unsustainable (Fig. 11) with some degree of variance. This will decrease the available wood for pulp and will not increase smallholder incomes. This disturbs the landscape because the logged area is not maintained or cared for. The average revenue received by the smallholder is illustrated in Fig. 12. The smallholders are paid when their plantations reach maturity. Since the age of the plantation is random, they receive payment in the year they sell the plantation. They can expect to get a higher price if their plots are close to the road network, rather than away from the network. The pattern of this payment is random. The average payment is approximately RM 142.4, which is not enough to make them re-plant the plantation. They need to receive at least RM 200 before they will consider re-planting the plantation; otherwise they will leave/abandon these plots.
Fig. 11. Decreasing the initial existing smallholder plantation area (number of simulation repetitions = 10).
Fig. 12. Yearly dynamic of smallholder revenue (number of simulation repetitions = 10).
SAFODA continue to implement the plant–cut–replant strategy regardless of the feedback they obtain from the selling of trees. This strategy succeeds in maintaining the area of pulp plantation but the financial revenue is lower than they expect (Fig. 13). Table 5 illustrates an example of negotiation between SAFODA and the pulp broker. SAFODA cannot move to other sites like the smallholders. The feedback from the trading cannot weaken the rule of plant–cut–replant, unless the government agrees to do so.
Fig. 13. Yearly dynamic of SAFODA revenue (plant–cut–replant strategy).
Table 5. An example of the negotiation process between SAFODA and the broker of plot no. 10 (number of pixel is 109, the plot extent is 2725 ha)
Negotiation round
The broker offer (in RM per m3)
SAFODA expectation (RM per m3)
SAFODA decision on pixels
SAFODA margin (in RM per m3)
SAFODA margin (in RM per ha)
SAFODA Margin (in RM per pixel or 25 ha)
Total SAFODA margin (in RM)
Total Pulp buyer margin (in RM)
Total wood available (m3)
First negotiation
42.6
31.1
Agree to cut (25 pixels)
16.7
2,340.7
58,516.7
987,267.0
1,312,500.0
87,500
21.0
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