Close Home
iForest - Biogeosciences and Forestry
vol. 7, pp. 216-226
Copyright © 2014 by the Italian Society of Silviculture and Forest Ecology
doi: 10.3832/ifor0979-007

Review Papers

Public participation: a need of forest planning

Xabier Bruña-GarcíaCorresponding author, Manuel Francisco Marey-Pérez


“Forest resource planning is a very complex problem mainly due to the multiplicity of wide-ranging criteria involved in the underlying decision-making process” ([30]). One of the criteria to be taken into account is the social aspect. Public participation is one of the questions that is raising more interest within social aspects. As other articles on the same topic ([22], [103]), this paper reviews the state of the art in research on public participation within the forest sector and its possible application in forest resource planning, focusing on regional planning.

The aim of this work is to show to forest planners the importance and the progress made in public participation in forest planning in the last forty years. It also aims to show how these social techniques have been modified, increased and adapted to the different social and territorial realities through time.

We started with a review of research papers related to public participation in forestry. The search for information focused on three topics: (1) from a conceptual perspective, the concepts of society, democracy and public participation, their historical evolution and their relation with forest planning; (2) key elements for the development and success of a public participation process in forestry; (3) most widely-used models, methods and tools. The paper ends with a discussion section and conclusions that reflect the lessons learned from the literature.

Brief review of the conceptual framework 

There have been important social changes worldwide in the last forty years. On the one hand, in western Europe, north America, Japan and Australia, post-industrial societies have lost their connection with forest land ([114]). They have incorporated a bigger network of connections among its citizens by means of new information technologies, which implies a higher level of information and interest of participation in social and environmental issues on a global, national, regional and local scale. On the other hand, there have been fewer changes in pre-industrial societies in Asia, Latin America and Africa ([4]). However, there is an increasing interest in participating in decision-making regarding the management of closer and necessary forest resources.

Claims for participation are often made in terms of democracy. From a democratic perspective, the equitable inclusion of different interests is a key issue in public participation ([91]).

There are different approaches to the definition of public participation. According to the Cost Action FP0804 ([27]) FORSYS, public participation means that citizens are involved in the environmental or natural resource decision-making that affects them. In more general terms, public participation is a process by which people make decisions about the institutions, the programmes and the environments that affect them ([43], [102]).

In an initial proposal, participation is considered an awareness process by which people begin to understand their political role and the need for a legitimate conciliation of opinions and for a contribution to the planning process ([101]). This makes participation a requirement to build consensus and a basic principle which brings about transparency and an exchange of information ([43], [102], [48]). Thus, participation brings about a sense of self-realisation and property ([35]). In a modern sense, public participation is a voluntary process where people, individually or by means of organized groups, can exchange information, express opinions, articulate interests and have the potential to influence the end result ([53], [1], [12]).

From the point of view of citizens, participation in the forest sector must become a method used by the whole forest organization instead of making it a pre-requisite for forest management ([12]). The process of forest policy implies a set of private interests, public agencies, legal framework, groups of lawyers and judicial organizations and non-profit organizations which represent the expansion actions of the public ([55]). These non-profit organizations gained influence in forest policy ([120]), so resource management agencies worldwide are increasingly using processes of public participation to involve those citizens affected by planning decisions ([52]).

From the point of view of the administration, participation is the effort of the forest planning and management team to provide people with a wide range of opportunities to influence planning and forest management. Participation also enables them to systematically analyze, assess and subsequently incorporate the resulting public contributions into forest plans as often as possible ([32], [70]). “The quality of the process is seen as key to high quality appraisal outcomes” ([40]).

From the point of view of landscape, participation is the capacity of the local population to decide and develop their own rules and structures ([42]). These will guarantee the use, the maintenance and the development of the landscapes that satisfy their needs and those of their offspring ([87]).

Participatory approaches focus on people. They must be implemented with caution. It is necessary to take into account key concepts such as “empowerment, respect, localization of resources, enjoyment and inclusiveness of people” ([90]).

Antecedents and evolution of public participation in forest planning 

Society claimed a more important role in the decisions related to public land and forests in the 1960s due to the beginning of the environmental movement ([97]). Since the 1970s, there has been a reassessment of the value of local knowledge leading to petitions of participation in projects in which experts and local knowledge were complementary. It is necessary that research into environmental decision considers the different scenarios of construction of knowledge, as this will provide insights into people’s response to matters like forest loss or species preference ([71]). The report by the Brundtland Commission in the 1980s showed that equity would be favored by political systems in which public participation ensures decision-making. Thus, public participation was directly joined with sustainable development ([122]). In the same way, and according to Primmer & Kyllönen ([91]), participation is essential for sustainable development as a source of pertinent environmental information for decision-making. Therefore, it is now central to the concept of sustainable development. Currently, public participation in decision- making in the forest sector is considered an important part in sustainable forest management ([59], [61], [23]).

The preamble of the Agenda 21, approved in the United Nations Conference on Environment and Development (Río de Janeiro 1992), states that a high participation of the public opinion in decision-making is a basic requirement for sustainable development. Moreover, the need for new means of participation became obvious in the more specific context of environment and development. “Participatory approaches are argued to be an essential part in applying the precautionary” ([91]).

The reinforcement of the public role in planning has its roots in philosophical and pragmatic considerations. From a philosophical point of view, democratic societies believe that citizens are entitled to being provided with information and asked about their opinion regarding issues that affect them ([41]). The ideal would be to have a democratic government which is representative and designated to channel and assimilate information between the government and those governed ([101], [41]).

Some economists defend environmental methods for participative decisions in which the public are considered as citizens instead of consumers ([112]). It is widely accepted nowadays that participative methods are the most efficient ones to get sustainable resource management. Local communities are asking for more voice and influence in the management of their resources ([66], [81]). This requires a more direct and active participation of a higher number of stakeholders and the incorporation into planning of the interests, perceptions and visions that society has about forest resources.

Although public participation is not a new concept, its presence in forest planning is relatively new, being an uncommon practice at local level in non-industrial private forest land (NIPF - [66]). People are gradually more interested in having more control over the decision-making process and in influencing forest practice. There is also a growing interest in a change in forestry practices ([22]). This is the reason why those professionals in forestry need to communicate their ideas and actions, not only to other professionals, but also to a higher number of non-professionals ([116]). Sugimura & Howard ([111]) recommend the participation of stakeholders in the final phases of forest zoning.

According to Ojha et al. ([85]), the search for efficient strategies to protect forests and improve the lives of those who depend on them lead to several participative approaches to forest government worldwide in the last decades. In this sense, public participation is key in the forest sector and constitutes a new framework for any type of decision-making in forestry ([63]). Public participation can also be a tool to improve sustainable forest management ([53], [12]). This makes it an important tool in many countries to promote sustainable forest management on a strategic level, especially in public or state forests ([50], [61], [23]).

Foundations for the success of public participation in the forest sector 

Principles and aims

Participation can be considered as an end or as a means to an end, as ethics of performance or as a management tool ([22]).

On the one hand, according to Buchy & Hoverman ([22]), good participative planning presents four basic principles: (i) commitment and clarity; (ii) time assigned to the process; (iii) representativeness of the people involved; (iv) transfer of competences and knowledge. On the other hand, many studies show that learning, relationship building, exchange of knowledge and representation of interests are the measures of the success of public participation ([104], [93], [115], [75], [66]).

It is necessary to guarantee equity, representativeness and transparency in public participation processes ([59]). Participative planning may be used to avoid conflict, share information among participants and promote good relations with the organization that promotes the planning ([47], [57], [55], [51]). The development of a National Forest Program (NFP) is a challenge. It may contribute to the processes of democratization in different ways: by reinforcing the transparency of political decisions, by making communication and decision processes more pluralistic, by stimulating mutual knowledge and by increasing awareness of collective responsibility for forest issues ([38], [61]). Public participation is increasingly recognized as an instrument for environmental management through the building of consensus, conflict management and collaboration for problem-solving and negotiation in decision-making ([52]).

Public engagement in forest management decisions will bring about an increase in the value of landscapes and the recognition of sustainable forests. As landscapes start to be perceived differently, this new perceptions will help “address ecological sustainability and will embrace the new ecological aesthetic idea” ([86]). To this regard, goals for public participation have been developed founded on sustainable development and on development policies. They include the generation of new pertinent information, the inclusion of different interest and the contribution to reach a public consensus ([91]).

Types of public participation in forest planning

Four types of public participation can be found in forest-planning processes:

  • None: there is no chance of participating in the decision-making process.
  • Public: open access and input into the decision process, such as in a public forum ([60], [77]).
  • Restricted Public: invited access, however no specific knowledge is required to inform and enter the decision process, such as community group participation ([99], [68], [80]).
  • Stakeholder: Experts or stakeholders provide information and participate in the decision process ([2], [117], [118], [79]).

There are several degrees of participation from passive participation, in which stakeholders are informed about the decisions made by others, to interactive participation which requires joint decisions and shared responsibilities ([41], [38], [49]). Therefore, participation may have different forms which range from public meetings and audiences, questionnaires (focused on groups) to deliberative processes with the final aim of enabling participants to have a higher degree of involvement in decision processes ([49]). Martins & Borges ([73]) interpret the collaborative planning “as a special case of participatory planning when all participants involved share decision-making power and are directly affected by management options”.

The literature offers several typologies of public participation. It often shows a scale which stems from a unidirectional information flow until it completes the power of decision of the citizens in self-organization ([10], [89], [37], [41], [35], [111], [108]). Taking this into account, we propose the five levels below:

  1. Information: unidirectional information flow without public participation to obtain feedback and without negotiation.
  2. Consultation: the role of citizens is to review and comment the planning proposals by means of audiences and consultations, while the authority retains the power of decision.
  3. Decision: citizens and authority become partners. Citizens begin to have influence in the decisions. They can negotiate and be involved in compensations with the authorities.
  4. Performance: citizens have a dominant control over the decision-making of the authorities and they are also responsible for the decisions.
  5. Self-organization: citizens have full control, so it is the highest expression of citizen power. They take initiatives which are independent from the authorities.

Public participation implies the egalitarian participation of the different stakeholders, “including industry, labor unions or other non-governmental organizations” ([91]). Moreover, their contemporary use implies more direct ways of public participation than just voting in the elections, the membership to a political party or the affiliation to an interest group involved in political decision-making. Limiting participation to owners leaves too many groups out of the decision space in many decisions concerning natural resources.

Phases of public participation

The work by Martins & Borges ([73]) suggests a simplification of the collaborative planning process in three steps:

  • The identification of the problem involves the gathering and analysis of information to understand and define the management of territorial problems.
  • The modeling problem consists on the construction of models to represent the relationships between the management alternatives and the results and the policy management scenarios.
  • Problem solving implies the design of a forest management plan.

According to Collier & Scott ([26]) the participation of stakeholders, consultation, participation and inclusion are some of the most commonly-used descriptors of the collaboration, planning and management process. New methods of reconciliation of social and ecological differences are becoming increasingly important in restoration ecology, collaborative planning and management. These new methods are adequate tools to reach agreements, mend trust relations and encourage mutual learning.

Advantages and disadvantages of public participation

Public participation has many advantages that have been exposed in different articles. They can be grouped in the following categories: improvement of communication, generation of knowledge, rapprochement between the administration and government and citizens, involvement of all agents, integration of society in management, improvement of sustainable development, prevention and solution of conflicts, legitimization of decision-making, easier execution of the plan and step towards forest governance.

Improvement of communication

Public participation is more efficient when it is based on mutual confidence. It improves the communication and cooperation among all those involved in the process. This will contribute to sustainable forestry, increasing public awareness. It will also contribute to the increase in forest benefits, to the fair distribution of costs and profits and to the improvement of the social acceptance of sustainable forestry ([36]). The use of social movements can cause a decrease of prejudices against the forest sector ([25], [111]).

Generation of knowledge

Hansmann et al. ([46]) state that participative processes with more widely-spread marketing campaigns may be a source of information for the Swiss population about the forest sector. Information can contribute to a certain improvement in the quality of decisions ([25], [111]). Additionally, there is an educational dimension as an advantage, which may bring long-term benefits ([22]) and, therefore, public participation can incorporate new data and generate knowledge ([18], [19], [94]).

Rapprochement between the administration and government and citizens

The study by Berninger et al. ([15]) states that the consequences of different management options should be discussed and effectively communicated to improve the attitudes of the locals towards forestry. This will improve the understanding of the complexity of the task of managing a big forest area with socio-economic and environmental criteria and increasing their confidence on forest professionals.

Involvement of all agents

Selman ([100]) considers the collaboration of stakeholders as a key element in landscape management and planning. Undoubtedly, it offers the opportunity to participate in the forest planning process, which will make more people consider the importance of forests ([111]). Among the reasons why industry is interested in public participation, we find good public relations, a good relationship with stakeholders and a decrease of criticism in the media ([18], [19]).

Integration of society in management

Public participation improves the effective management of resources ([18], [19], [22], [23]). The study by Brody et al. ([19]) identifies some of the most important factors that encourage forestry and the wood industry to take part in the participative management of ecosystems. It concludes that the participation of industry can bring about an improvement in the results of the management of the ecosystem and a contribution to the achievement of the goals in the management of natural resources by companies.

Currently, public participation must help create synergies between stakeholders and managers, achieving a better integration between environment, economy and society ([83], [86]) and facilitating future management by consensus ([17]).

Improvement of sustainable development

Public participation is important in successful strategies of conservation ([3]). Participative methods are the most effective ones to achieve sustainable resource management ([66], [81]). Moreover, Brody et al. ([19]) studied the thirty-eight biggest forest companies in the US and found that the use of participative management to create collaborations and associations with stakeholders results into more effective resource management.

Prevention and solution of conflicts

According to Dovie ([35]) “Local participation should not be seen as means of reducing cost, engaging cheap labor and/or the opportunity to tap free knowledge. However, it should be seen as a foundation for conflict resolution, benefit sharing and partnership development. It is also meant to enhance the socio-economic lives of the people, bringing hope and in the long term, providing them with opportunities to be accountable for their environment”. An example of public participation as an effective way of managing forest conflicts is the Mountain Forest Tending Group in Switzerland. This is where the representatives of the Federal Forest Services discuss the way to combine the management of natural stands, the protection against risks (especially landslides) and the preservation of biodiversity ([84]). Therefore, public participation can be used to reduce the conflicts between stakeholders ([25], [111], [23]) and it is an attractive alternative to litigation and to regulation control ([18], [19]).

Legitimization of decision-making

A rational technical-scientific model that does not include the preoccupation of the public makes it difficult to reach decisions that are acceptable for citizens ([105], [111]). Therefore, public participation in the decision- making process improves the possibility to reach a consensus by enabling the stakeholders to take into account different perspectives. This makes the decision-making process more transparent by giving more responsibility to those who make the decision and adds more weight to the final decision ([49]). The legitimacy of the final decision can be better when the different stakeholders participate in decision-making ([121]).

Easier execution of the plan

Even if participative planning requires a higher initial investment, the involvement of the residents in the planning phase can lead to lower costs later because it avoids complaints in the execution phase ([107]). Therefore, the involvement of citizens will cause lesser stakeholder opposition to the execution of forest plans ([111])

Step towards forest governance

This new variable should be incorporated and accepted in the planning of forest resources since it is the only way to achieve forest governance. There will be a strengthening of democracy and an expansion of citizens rights ([49]). Participative planning can also improve the quality of life of the residents with positive experiences of participation and empowerment and improve their lives in a more tangible way once the plan is carried out ([107]).

Nowadays public participation presents some problems with its implementation, which will be solved by applied research. In this line, Conrad et al. ([24]) illustrate the inadequacy of present legal requirements for ensuring effective participation, and a related need for institutionalizing review mechanisms in Mediterranean countries. In Canada, Stewart & Sinclair ([109]) detected some problems in the processes of public participation in environmental assessment.

Some of the problems detected by different studies are described below. First, public participation is costly and lengthy ([108]). Moreover, the politicians and scientists responsible for management have criticized participative approaches in relation to their highly-qualitative orientation and their apparent lack of rigor, structure and a systematic process to analyze and interpret the data from the stakeholders ([80]).

The planning of natural resources is complex in itself and it often implies a set of participants with different perspectives about the means and ends applied ([52]). Several participation processes related to environmental issues in the USA fail to establish a constructive dialogue among society and stakeholders, which hinders the solution of conflicts ([112]). This may be due to the possibility of being influenced by the participants, their self-organization, their possible implication in hierarchies, the coordination and the rules of decision within discussion groups ([38]).

Suárez de Vivero et al. ([110]) make reference to the paradox of participation: the higher the number of actors, the smaller the role that each one has and the lesser importance of the traditional sector. The increasing number of participants and the complex relations between them due to their different interests make it necessary to redefine the rules of participation. Therefore, some clear rules of negotiation and participation are necessary in order to overcome obstacles and achieve effective participation ([38]).

The negligent application of public participation could cause conflicts with local societies with long term effects on relationships and on the local capacity to collaborate ([108]), as it could be used as a channel of opposition. Participation can also raise too many expectations if the essence of planning is not understood or if the principles of decision-making are not clear. In practical terms, participative planning sometimes leads to compromises where individual expectations are not fully satisfied ([116], [107]). Local participation in the management of cultural landscape is very efficient when focused on specific areas. However, it cannot substitute politics and administrative organization when it comes to global strategies for areas on a big scale ([100], [108]).

Models, methods and tools 

According to Sheppard & Meitner ([103]), “while there is an increasing demand for active public involvement in forestry decision-making”, there are still few successful models to reach this goal in new sustainable forest management ([69]). The methods described as “hard” are consistent with the traditional and rational scientific management approach based on mathematical models. “Soft” methods and knowledge-based system approaches are introduced as having potential, particularly in participatory modeling as they are applied to forest and natural resource management planning ([82]). The participation models can be used as independent tools or they can be integrated in planning to make it stronger and more flexible ([81]).There is no method that is universally best or even applicable for all situations ([58]). Based on the nature of the alternatives, Hajkowicz et al. ([44]) classify Multi-Criteria Decision-Making (MCDM) methods under two major categories: continuous and discrete. That is why their election requires the consideration of the needs in each particular case. Not all techniques can be applied on every level of participation. Therefore, the planner’s goals should not be ambiguous, especially when interacting with the public ([22]). In this regard, as stated in Cost Action FP0804 ([27]), there are different types of methods and tools in each phase of public participation, as can be seen in Tab. 1. The revision of collaborative methods and tools that can be used in the elaboration of the management plans of Non-Industrial Private Forests (NIPF) reveals new research needs, the development of hybrid methods and technological platforms for the integration of tools and methods ([73]). The methods used should be comprehensible for all those involved in the process. The results and their analysis should not be difficult to evaluate and explain ([58]).

Tab. 1 - Models, methods and tools in each phase of public participation.

According to Sheppard & Meitner ([103]), information can be conveyed easily and fast by public processes that introduce prospective schemes with justified solutions.

In the same way, Higgs et al. ([49]) highlight the potential of the approaches that include IT (Information Technologies) in public participation, in particular of those that that show the possibilities of the use of Geographic Information Systems (GIS) to include the needs and preferences in the decision-making process. Using distributed networks is supposed to allow for a broader application of public participation. An example of this is the use of decision support systems with the tool Mesta (⇒ http:/­/­www.­mesta.­metla.­fi) in the participative process NRP in the region of Laponia in Finland. An advantage of Mesta was the inclusion of preferences with the realistic production possibilities of the planning regions ([51]).

We propose a review of some of the most widely-used processes of public participation below.

SCT/GDM (Social Choice Theory/Group Decision Making) models without MCDM skills

Social Choice Theory

Social Choice Theory as a systematic subject emerged during the French Revolution. Marquis de Condorcet, a French mathematician, started the discipline of social choice in terms of simple majority voting and related procedures, and discovered the paradox of cyclic voting, commonly known as the Condorcet paradox ([11]).

According to Kangas et al. ([60]) “the basic objective of social choice is to combine individual preferences into a collective choice. The social choice situation can be described with four components or parts: (i) voters or players; (ii) choice alternatives; (iii) the information of voters’ preferences over the alternatives; (iv) an aggregation device (voting model, procedure or voting method)”.

Kant & Lee ([62]) state the four stages in the implementation of Social Choice Theory in the context of sustainable forest management: “(i) identification of all possible forest values; (ii) revelation of the preferences of the stakeholders by different sectors and social strata; (iii) aggregation within the preference group; and (iv) aggregation among the preference groups”. Voting is a well-known way of exerting influence and expressing opinions: “The voting approach can be applied in multiple-criteria decision support by voting on criteria” ([58]).

The methods based on social choice theory have been applied in group decision-making for natural resource management, such as in Martin et al. ([72]), Laukkanen et al. ([65]), Hiltunen et al. ([51]), Vainikainen et al. ([119]). In fact, Martin et al. ([72]) published one of the first studies about the application of this technique in the USA in the management of forest land rented for oil and gas exploitation. It consisted of two systems of voting regulations (Condorcet and Borda), seven stakeholders and seven alternatives.

Social Choice Theory has been recently applied in Laponia to the decision-making group in the revelation of preferences of the participants in participative forest planning ([119]) or in the participative planning in forest strategy in state-owned forests in Finland with five methods of voting ([50]). Most of the voting techniques are also transparent and the results are easy to apply by decision- makers and easy to interpret by participants. Contrary to this and according to Vainikainen et al. ([119]), in practice, voting is believed to be fair as each voter is supposed to have the same influence on the end result. However, voters do not have the same power, as it can be seen in the results. This is referred to as strategic behavior and it has not been studied deep enough in public participation. Therefore, the use of several voting methods is recommended.

SCT/GDM (Social Choice Theory/Group Decision Making) models using MCDM skills: discrete methods

Discrete MCDM methods can be defined as decision support techniques that have a finite number of alternatives, a set of objectives and criteria by which the alternatives are to be judged and a method of ranking alternatives, based on how well they satisfy the objectives and the criteria ([45], [8]).


Group preferences can be analyzed using Analytic Hierarchy Process (AHP) or utility functions, as shown in Kangas ([56]), Martin et al. ([72]) and Ananda & Herath ([5]). AHP is a mathematical method for the analysis of complex decisions with multiple attributes ([95], [96]). Mau-Crimmins et al. ([74]) show in their study in the Colorado National Forest (Arizona, USA) that AHP can successfully be applied to the experimental problem of the location of wild natural areas, offering thus possibilities for its effective application as a tool of public participation. In the same way, the work by Ananda & Herath ([7]) concludes that “the AHP and other conventional public consultation procedures are effective ways to improve participatory decision-making in complex decision situations, such as regional forest planning”. Kurttila et al. ([64]) describe a method that fused SWOT and AHP in a case of forest certification in Finland. Silvennionen et al. ([106]) applied an AHP approach provoking preference weights in a case of landscape of forest management. Schmoldt & Peterson ([98]) used a technique based on AHP as a component of fire research planning for forest fires, the Fire-Disturbance Workshop of the USDA Forest Service.

Integrated approach

A method to integrate the opinion of the residents in relation with forest management is the planning with a participative focus ([116]). The integrated approach proposed by Belton & Stewart ([14]) presents a mixture between the qualitative approaches of the social aspects and the structural approaches of the more statistical aspects. The work by Tyrväinen et al. ([116]) analyzes two possible methods to improve the planning of public participation and its design in Europe, based mainly on acquired experiences in Nordic countries. The methods are related to the use of: (i) methods of visualization by computer; and (ii) model forests and landscape labs. Their combination can cause a considerable improvement in forest planning and design. Alternatively, Mendoza & Prabhu ([80]) describe the application of the integrated model in the management of communal forests in Mafungautsi (Zimbabwe). It proposes an approach to simulate different scenarios combining MCA and participative modeling that uses cognitive mapping, first, and system dynamics, later. By means of a study of the drawbacks of traditional models, they call for new trends of thought concerning Multi-Criteria Decision Analysis (MCDA) when implemented in forest and natural resource management planning.

SCT/GDM (Social Choice Theory/Group Decision Making) models using MCDM skills: continuous methods

Continuous methods aim to identify an optimal quantity, which can vary infinitely in a decision problem. Techniques such as linear programming, goal programming and aspiration-based models are considered continuous ([8]).

MCDA and hybrid methods

These hybrid methods provide the synergistic accumulation of insights from different methods. Traditional participative approaches were criticized for their lack of rigor, so at the end of the 20th century alternatives were presented to correct this deficiency ([80]). The work by Mendoza & Martins ([82]) reviews the limitations of traditional MCDA approaches to incorporate public participation, analyzing soft systems and the alternative paradigms and aiming for a modeling that is transparent, participative and accessible for decision-makers. Concerning this, it has been shown that hybrid methods like Multi-Criteria Decision Support (MCDS) and participative approaches by means of information networks enhance the effectiveness of the process. Moreover, regardless of the planning task or the MCDS method, education and learning improve ([58]).

It has also been concluded that the planning process will be more efficient using interactive methods. This requires a clearer modeling process ([82]). Díaz-Balteiro & Romero ([30]) consider that the application of techniques of Group Decision-Making methods (GDM) in the forest sector has a large potential for research. Leskinen & Kangas ([67]) analyzed the use of MCDM methods on a theoretical level when the participating criteria are interdependent and proposed the use of statistical models to avoid the uncritical acceptance of the assumption of independence criteria.

Mendoza & Prabhu ([78]) exemplify the integration of the MCDM methods with a soft qualitative model of dynamic system. Recently, Mendoza & Prabhu ([81]) described the dynamics of three general types of soft systems linked to participation models: (1) cognitive mapping; (2) dynamic qualitative system; and (3) Fuzzy Cognitive Mapping (FCM). The last one has more advantages in its application due to its transparency and simplicity.

Tikkanen et al. ([113]) analyzed the real objectives of a sample of forest owners following a cognitive mapping approach. Finally, Martins & Borges ([73]) examined different GDM approaches with an MCDM orientation and its potential use in the management of forest problems in Portugal.

Other models

The Social Evaluation approach (SE) proposed by Sugimura & Howard ([111]) reduces the number of comparisons by pairs of AHP. It simplifies the answering process and lowers survey costs. The Q method is a research approach defended by the advocates of discursive democracy to assess the attitudes about a specific topic from their own perspective. It was used in the north-eastern Pacific area of the US to support public participation ([112]). It also included the feelings of the participants towards the process in the making of the Regional Forest Programme in Finland ([61]).

Multi-Attribute Utility Theory (MAUT) is an approach which can simplify and structure the forest management problem and facilitate explicit incorporation of multiple values and risk preferences of stakeholders in decision-making ([6]).

The work by Côté & Bouthillier ([25]) shows that the use of compared scenarios is an interesting tool to evaluate the opinion of participants about the repercussion of the initiatives of public participation in order to identify the weaknesses of the processes and for the increase in the knowledge of the participants about the possibilities of such exercise.

Dovie ([35]) thinks that the Hierarchic Valuation Scheme (HVS) is more suitable for the evaluation of local resource use than other participatory schemes (among them Participatory Rural Appraisal - PRA), as it is more accurate and reliable. HVS may be used as complementary to other techniques. Purnomo et al. ([92]) applied a system of soft approaches to the management of a communal property forest with a surface of 30 000 ha in Indonesia, selecting six indicators related with the management plan and several defined strategies, in fifteen scenarios assessed by a group of stakeholders.

Díaz-Balteiro et al. ([31]) adapted and applied a method for aggregating individual preferences expressed through pairwise comparison matrices to elicit social weights in the context of a forest management problem to two public forests in Spain.

Internet-based methods and tools

“Teledemocracy” uses distance communication technologies to add possibilities to citizen participation in decision-making. It solves the problems of geographical isolation, reduces distances and gathers a great number of opinions very fast. It offers opportunities of participation to citizens that cannot attend face-to-face events ([57]).

Public Participation Geographic Information Systems (PPGIS) methods increase the rates of participation ([88]), strengthening confidence and increasing cooperation in forest management ([20]). They are an important tool to attract people ([21]). In the forest sector, the Canadian Forest Service developed the first PPGIS to gather data about the first location of the values of forest landscape through a study area of 2.4 million ha in Alberta ([16]) and the Nova Forest Alliance in Nova Scotia ([9]). Other internet-based studies for national forest management have been recently developed in the USA ([20], [28]).

The latest trends in information technologies show that citizens are willing to share information with “web 2.0” tools and crowd sourcing platforms to describe events with social impact ([29], [39]).

Brown & Reed ([20]) in their assessment of the advantages and disadvantages of internet conclude that results depend on the subpopulation sampled and that their use must be complemented with traditional methods. Cantiani ([23]) states that the use of internet must be carefully considered, since, depending on local conditions and the questions under discussion, could lead to the overestimation of the opinions of organized groups.

Discussion and conclusions 

According to Buchy & Hoverman ([22]), it is not possible to categorically answer the question of whether public participation is successful or not. The answer is closely related to the aim of participation. However, we believe that it is possible to determine indicators that can measure the success of public participation, its contributions and that respond to the intensity and scope formulated in the initial conditions of the process. Our work presents the following trends of thought concerning the importance and advances obtained in public participation in forest planning in the past decades:

  1. From a theoretical and philosophical perspective, there is no doubt that public participation is a need for democratic societies nowadays ([10], [22], [103], [1], [91]). It is an important tool to reach consensus ([121], [105], [49], [111]), manage conflicts ([35], [25], [84], [111], [23]) and improve forest management ([3], [19], [66], [81]). However, this theoretical clarity is not translated into its application to the territory. On the one hand, public participation is severely conditioned in its development by the interests of power groups that see it as a threat for their interests. On the other hand, there is a lack of training which prevents the public interested from facing the participative processes with guarantees.
  2. From a historical perspective, considering the extensive bibliography consulted and more than 40 years of scientific development, public participation has not been included as a necessary element for the development of forest planning. However, there has been a growing interest in public participation and its application, as seen in Fig. 1, which shows the highest concentration of work in the last decade regarding public participation. This fact confirms that public participation represents one of the future fields of development and innovation in forest planning.
  3. Fig. 1 - Number of articles published in the literature about public participation, grouped by year of publication.
  4. From a methodological perspective, despite the advantages of public participation ([121], [3], [22], [25], [105], [35], [36], [66], [84], [19], [81], [49], [111]), it is necessary to make a bigger effort to specify some aspects of its application in the territory and methodology. In this sense, it is necessary to continue to advance in the development of flexible public participation methodologies to be applied in different contexts and by different organizations. In particular, some issues need to be dealt with in a process of public participation in forest planning: diffusion and communication ([54]); representativeness ([13], [91], [49]); cost and time ([108]); methodological rigor ([80]); intensity ([13]) and optimum number of participants ([110]).
  5. From a territorial perspective, the application of public participation in the processes of forest planning does not have enough tradition or experience ([12]). Its application in the different regions and countries is linked to areas that present more fully developed democratic processes and to countries with more resources and forest tradition (Fig. 2). Therefore, the main criticism towards public participation in forestry is that it should be linked to the basic principles that define sustainable forest management. It is also worth noting, within a territorial perspective, that there are public participation experiences on a local level even if the majority of the processes have been on a regional and/or national level ([107]). In this sense, it is necessary to identify the key elements in the processes of public participation on a regional or national level that make them viable. The success of forest plans depends on the representativeness and involvement of the different stakeholders.
  6. Fig. 2 - Number of articles published in the literature about public participation, grouped by country.
  7. From a social perspective, taking into account the need to integrate social and technical aspects, the most advanced methods of public participation apply a mix of soft and hard methods ([103], [80], [58], [82]). However, these methods are still too rigid to obtain clear information about the different preferences and needs of stakeholders, which are essential for the success of public participation processes ([34]).
  8. From a future perspective, new information technologies can make the decision- making more transparent, fluent and equal ([58], [49], [51], [23]). The identification of significant functional groups is necessary for impact assessment because groups supporting particular functions in a particular network of actors and practices have much influence. They condition the impacts considered ([48]). However, it is necessary to apply and develop more “intense” processes of public participation. By “intense” we mean a higher involvement of participants in final decision-making. In the coming years, citizen contributions will have more and more relevance in the planning process in the forestry sector.

Public participation in forest planning has been developed and applied differently in time and space. Current experiences are an interesting starting point, but it is necessary to develop contrasted and flexible technologies to be included in the whole process of making forest plans. Methodologies used so far have originated as an answer to the problems and interests of some social groups seeking to influence the process. No methodology was previously designed to be validated in different areas. Therefore, it is necessary to establish the general guidelines for public participation processes with flexible methodologies, so that they can be adapted to different territories. The final result will contribute to the advance in two of the challenges of the 21st century: sustainability and governance.


We would like to thank the Ministerio de Ciencia e Innovación of the Spanish Government for their financial aid through the Proyecto Sectorial Estratégico - Restauración Forestal, subproyecto Implica-Explica (PSS- 310000-2009-22) and COST Action FP0804: FORSYS.


Aasetre J (2006). Perceptions of communication in Norwegian forest management. Forest Policy and Economics 8: 81-92.
::CrossRef::Google Scholar::
Acuña S, Juristo N, Recio B (1997). Knowledge-based system for generating administrative grant alternatives applying the IDEAL methodology. Computers and Electronics in Agriculture 18: 1-28.
::CrossRef::Google Scholar::
Alexander SE (2000). Resident attitudes towards conservation and black howler monkeys in Belize: the Community Baboon Sanctuary. Environmental Conservation 27 (4): 341-350.
::CrossRef::Google Scholar::
Alexander JC, Thompson K (2008). A contemporary introduction to sociology: culture and society in transition. The Yale Cultural Sociology Series, Paradigm Publishers, Boulder, CO, USA.
::Google Scholar::
Ananda J, Herath G (2003). The use of analytic hierarchy process to incorporate stakeholder preferences into regional forest planning. Forest Policy and Economics 5: 13-26.
::CrossRef::Google Scholar::
Ananda J, Herath G (2005). Evaluating public risk preferences in forest land-use choices using multi-attribute utility theory. Ecological Economics 55: 408-419.
::CrossRef::Google Scholar::
Ananda J, Herath G (2008). Multi-attribute preference modelling and regional land-use planning. Ecological Economics 65: 325-335.
::CrossRef::Google Scholar::
Ananda J, Herath G (2009). A critical review of multi-criteria decision making methods with special reference to forest management and planning. Ecological Economics 68: 2535-2548.
::CrossRef::Google Scholar::
Anderson C, Bezley K, Boxall J (2009). Lessons for PPGIS from the application of a decision- support tool in the Nova Forest Alliance of Nova Scotia, Canada. Journal of Environmental Management 90: 2081-2089.
::CrossRef::Google Scholar::
Arnstein SR (1969). A ladder of citizen participation. Journal of American Institute of Planners 35: 216-224.
::CrossRef::Google Scholar::
Arrow KJ, Sen AK, Suzumura K (2002). Handbook of social choice and welfare (vol. 1). Elsevier, Amsterdam, The Netherlands.
::Google Scholar::
Atmis E, Özden S, Lise W (2007). Public participation in forestry in Turkey. Ecological Economics 62: 352-359.
::CrossRef::Google Scholar::
Beierle TC, Cayford J (2002). Democracy in practice: public participation in environmental decisions. Resources for the future, Washington, DC, USA.
::Google Scholar::
Belton S, Stewart TS (2002). Multiple criteria decision analysis. An integrated approach. Kluwer Academic Publishers, Massachusetts, USA.
::Google Scholar::
Berninger K, Kneeshaw D, Messier C (2009). Effects of presenting forest simulation results on the forest values and attitudes of forestry professionals and other forest users in Central Labrador. Forest Policy and Economics 11: 126-133.
::CrossRef::Google Scholar::
Beverly J, Uto K, Wilkes J, Bothwell P (2008). Assessing spatial attributes of forest landscape values: An internet-based participatory mapping approach. Canadian Journal of Forest Research 38: 289-303.
::CrossRef::Google Scholar::
Booth A, Halseth G (2011). Why the public thinks natural resources public participation processes fail: a case study of British Columbia communities. Land Use Policy 28: 898-906.
::CrossRef::Google Scholar::
Brody SD, Cash SB (2004). Why resource-based industries should participate in collaborative ecosystem approaches to management: a conceptual framework. Hazard Reduction and Recovery Center. Technical Report No. 04-01R, Texas A&M University, College Station, TX, USA.
::Google Scholar::
Brody SD, Cash SB, Dyke J, Thornton S (2006). Motivations for the forestry industry to participate in collaborative ecosystem management initiatives. Forest Policy and Economics 8: 123-134.
::CrossRef::Google Scholar::
Brown G, Reed P (2009). Public Participation GIS: a new method for national forest planning. Forest Science 55: 166-182.
::Google Scholar::
Brown G, Weber X (2011). Public Participation GIS: a new method for national park planning. Landscape and Urban Planning 102: 1-15.
::CrossRef::Google Scholar::
Buchy M, Hoverman S (2000). Understanding public participation in forest planning: a review. Forest Policy and Economics 1: 15-25.
::CrossRef::Google Scholar::
Cantiani MG (2012). Forest planning and public participation: a possible methodological approach. iForest 5: 72-82.
::CrossRef::Google Scholar::
Conrad E, Cassar LF, Christie M, Fazey I (2011). Hearing but not listening? A participatory assessment of public participation in planning. Environment and Planning C: Government and Policy 29: 761-782
::CrossRef::Google Scholar::
Côté M, Bouthillier L (2002). Assessing the effect of public involvement processes in forest management in Quebec. Forest Policy and Economics 4: 213-225.
::CrossRef::Google Scholar::
Collier MJ, Scott M (2009). Conflicting rationalities, knowledge and values in scarred landscapes. Journal of Rural Studies 25: 267-277.
::CrossRef::Google Scholar::
Cost Action FP0804 (2010). Forests Management Decisión Support Systems (FORSYS).
::Online::Google Scholar::
Clement JM, Cheng AS (2010). Using analyses of public value orientations, attitudes and preferences to inform national forest planning in Colorado and Wyoming. Applied Geography 31: 393-400.
::CrossRef::Google Scholar::
Díaz L, Granell C, Huerta J, Gould M (2012). Web 2.0 broker: a standards-based service for spatio-temporal search of crowd-sourced information. Applied Geography 35: 448-459.
::CrossRef::Google Scholar::
Díaz-Balteiro L, Romero C (2008). Making forestry decisions with multiple criteria: a review and an assessment. Forest Ecology and Management 255: 3222-3241.
::CrossRef::Google Scholar::
Díaz-Balteiro L, Gonzalez-Pachón J, Romero C (2009). Forest management with multiple criteria and multiple stakeholders: An application to two public forests in Spain. Scandinavian Journal of Forest Research 24: 87-93.
::CrossRef::Google Scholar::
Domínguez G, Carbonell X, Plana E, Pecurul M, Rodríguez I (2005). Participación pública en el Plan General de Política Forestal en Cataluña [Public participation in the Forest Policy General Plan of Catalonia]. In: Proceedings of the “IV Congreso Forestal Español”. Zaragoza (Spain) 26-30 Sep 2005, pp. 7. [in Spanish]
::Google Scholar::
Domínguez Torres G (2008). A wish, a fear and a complaint: understanding the (dis)engagement of forest owners in forest management. European Journal of Forest Research 130: 435-450.
::CrossRef::Google Scholar::
Domínguez G, Shannon M (2009). Understanding forest owners in a Mediterranean context. Constructing theory through descriptive and interpretational analysis. A study case in Catalonia. Msc Thesis, University of Freiburg, Germany.
::Google Scholar::
Dovie DBK (2003). Whose involvement? Can hierarchical valuation scheme intercede for participatory methods for evaluating secondary forest resource use? Forest Policy and Economics 5: 265-283.
::CrossRef::Google Scholar::
Düzgün M (2003). Advancement of forest village communities through effective participation and partnership in state-owned forestry administration: Turkey’s case. In: Proceedings of the “XIIth World Forestry Congress”. Québec City (Canada) 21-28 Sep 2003.
::Online::Google Scholar::
Elcome D, Baines J (1999). Steps to success. Working with residents and neighbours to develop and implement plans for protected areas. IUCN, Commission on Education and Communication, European Committee for EE, Gland, Switzerland, pp. 42.
::Google Scholar::
Elsasser P (2002). Rules for participation and negotiation and their possible influence on the content of a national forest program. Forest Policy and Economics 4: 291-300.
::CrossRef::Google Scholar::
Faehnle M, Tyrväinen L (2013). A framework for evaluating and designing collaborative planning. Land Use Policy 34: 332-341
::CrossRef::Google Scholar::
Garmendia E, Stagl S (2010). Public participation for sustainability and social learning: concepts and lessons from three case studies in Europe. Ecological Economics 69: 1712-1722.
::CrossRef::Google Scholar::
Germain RH, Floyd DW, Stehman SV (2001). Public perceptions of the USDA Forest Service public participation process. Forest Policy and Economics 3: 113-124.
::CrossRef::Google Scholar::
Gómez-Vázquez I, Álvarez-Álvarez P, Marey-Pérez MF (2009). Conflicts as enhancers or barriers to the management of privately owned common land: a method to analyze the role of conflicts on a regional basis. Forest Policy and Economics 11: 617-627.
::CrossRef::Google Scholar::
Glück P (1999). National Forest Programmes - significance of a forest policy framework. In: “Formulation and Implementation of National Forest Programmes” (Glueck P, OEsten G, Schanz H, Colz K-R eds). European Forest Institute Proceedings, Joensuu, Finland, pp. 39-51.
::Google Scholar::
Hajkowicz SA, Young M, Wheeler S, MacDonald DH, Young D (2000a). Supporting decisions: understanding natural resource management assessment techniques. A Report to the Land and Water Resources Research and Development Corporation, CSIRO, Canberra, Australia, pp. 136.
::Online::Google Scholar::
Hajkowicz, SA, Wheeler S, Young D (2000b). An evaluation of options for the Lower Murray reclaimed irrigation areas using multiple criteria analysis. In: Proceedings of the “Australian Agricultural and Resource Economics Society Conference”. Canberra (Australia) 12-15 Feb 2002, pp. 13.
::Online::Google Scholar::
Hansmann R, Koellner T, Scholz RW (2006). Influence of consumers’ socioecological and economic orientations on preferences for wood products with sustainability labels. Policy and Economics 8: 239-250.
::CrossRef::Google Scholar::
Hellström E (2001). Conflict cultures - qualitative comparative analysis of environmental conflicts in forestry. Silva Fennica Monographs 2, pp. 109.
::Google Scholar::
Hiedanpää J (2005). The edges of conflict and consensus: a case for creativity in regional forest policy in southwest Finland. Ecological Economics 55: 485- 498.
::CrossRef::Google Scholar::
Higgs G, Berry R, Kidner D, Langford M (2008). Using IT approaches to promote public participation in renewable energy planning: prospects and challenges. Land Use Policy 25: 596-607.
::CrossRef::Google Scholar::
Hiltunen V, Kangas J, Pykäläinen J (2008). Voting methods in strategic forest planning experiences from Metsähallitus. Forest Policy and Economics 10: 117-127.
::CrossRef::Google Scholar::
Hiltunen V, Kurttila M, Leskinen P, Pasanen K, Pykäläinen J (2009). Mesta: an internet-based decision-support application for participatory strategic-level natural resources planning. Forest Policy and Economics 11: 1-9.
::CrossRef::Google Scholar::
Hjortsø CN (2004). Enhancing public participation in natural resource management using Soft OR - an application of strategic option development and analysis in tactical forest planning. European Journal of Operational Research 152: 667-683.
::CrossRef::Google Scholar::
ILO (2000). Public participation in forestry in Europe and North America: Report of the team of specialists on participation in forestry. Report WP 163, FAO/ECE/ILO Joint Committee Team, International Labour Office, Geneva, Switzerland.
::Google Scholar::
Janse G (2008). Communication between forest scientists and forest policy-makers in Europe - a survey on both sides of the science/policy interface. Forest Policy and Economics 10: 183-194.
::CrossRef::Google Scholar::
Janse G, Konijnendijk C (2007). Communication between science, policy and citizens in public participation in urban forestry - experiences from the Neighbourwoods project. Urban Forestry and Urban Greening 6: 23-40.
::CrossRef::Google Scholar::
Kangas J (1994). An approach to public participation in strategic forest management planning. Forest Ecology and Management 70: 75-88.
::CrossRef::Google Scholar::
Kangas J, Store R (2003). Internet and teledemocracy in participatory planning of natural resources management. Landscape and Urban Planning 62: 89-101.
::CrossRef::Google Scholar::
Kangas J, Kangas A (2005). Multiple criteria decision support in forest management - the approach, methods applied, and experiences gained. Forest Ecology and Management 207: 133-143.
::CrossRef::Google Scholar::
Kangas J, Store R, Kangas R (2005). Socioecological landscape planning approach and multicriteria acceptability analysis in multiple-purpose forest management. Forest Policy and Economics 7: 603-614.
::CrossRef::Google Scholar::
Kangas A, Laukkanen S, Kangas J (2006). Social choice theory and its applications in sustainable forest management - a review. Forest Policy and Economics 9: 77-92.
::CrossRef::Google Scholar::
Kangas A, Saarinen N, Saarikoski H, Leskinen LA, Hujala T, Tikkanen J (2010). Stakeholder perspectives about proper participation for Regional Forest Programmes in Finland. Forest Policy and Economics 12: 213-222.
::CrossRef::Google Scholar::
Kant S, Lee S (2004). A social choice approach to sustainable forest management: an analysis of multiple forest values in northwestern Ontario. Forest Policy and Economics 6: 215- 227.
::CrossRef::Google Scholar::
Kouplevatskaya-Yunusova I, Buttoud G (2006). Assessment of an iterative process: The double spiral of re-designing participation. Forest Policy and Economics 8: 529-541.
::CrossRef::Google Scholar::
Kurttila M, Pesonen M, Kangas J, Kajanus M (2000). Utilizing the analytic hierarchy process (AHP) in SWOT analysis - a hybrid method and its application to a forest-certification case. Forest Policy and Economics 1: 41-52.
::CrossRef::Google Scholar::
Laukkanen S, Palander T, Kangas J, Kangas A (2005). Evaluation of the multicriteria approval method for timber-harvesting group decision support. Silva Fennica 39: 249-264.
::Google Scholar::
Leskinen LA (2004). Purposes and challenges of public participation in regional and local forestry in Finland. Forest Policy and Economics 6: 605-618.
::CrossRef::Google Scholar::
Leskinen P, Kangas J (2005). Multi-criteria natural resource management with preferentially dependent decision criteria. Journal of Environmental Management 77: 244-251.
::CrossRef::Google Scholar::
Lexer MJ, Vacik H, Palmetzhofer D, Oitzinger G (2005). A decision support tool to improve forestry extension services for small private landowners in southern Austria. Computers and Electronics in Agriculture 49: 81-102.
::CrossRef::Google Scholar::
Marey-Pérez MF, Rodríguez-Vicente V, Crecente-Maseda R (2006). Using GIS to measure changes in temporal and spatial dynamics of forestland: experiences from north-west Spain. Forestry 79: 409-423.
::CrossRef::Google Scholar::
Marey-Pérez MF, Rodríguez-Vicente V (2009). Forest transition in northern Spain: local responses on large-scale programmes of field afforestation. Land Use Policy 26: 139-156.
::CrossRef::Google Scholar::
Martin A (2003). On knowing what trees to plant: local and expert perspectives in the Western Ghats of Karnataka. Geoforum 34: 57-69.
::CrossRef::Google Scholar::
Martin WE, Shields DJ, Tolwinski B, Kent B (1996). An application of social choice theory to U.S.D.A. Forest Service decision making. Journal of Policy Modeling 18 (6): 603-621.
::CrossRef::Google Scholar::
Martins H, Borges JG (2007). Addressing collaborative planning methods and tools in forest management. Forest Ecology Management 248: 107-118.
::CrossRef::Google Scholar::
Mau-Crimmins T, Steigure JE, Dennis D (2005). AHP as a means for improving public participation: a pre-post experiment with university students. Forest Policy and Economics 7: 501-514.
::CrossRef::Google Scholar::
McCool SF, Guthrie K (2001). Mapping the dimensions of successful public participation in messy natural resources management situations. Society and Natural Resources 14: 309- 323.
::CrossRef::Google Scholar::
McDaniels TL, Roessler C (1998). Multiattribute elicitation of wilderness preservation benefits: a constructive approach. Ecological Economics 27: 299-312.
::CrossRef::Google Scholar::
Meitner MJ, Sheppard SRJ, Cavens D, Gandy R, Picard P, Harshaw H, Harrison D (2005). The multiple roles of environmental data visualization in evaluating alternative forest management strategies. Computers and Electronics in Agriculture 49: 192-205.
::CrossRef::Google Scholar::
Mendoza GA, Prabhu R (2002). Enhancing participatory planning of community-managed forest using problem structuring models and approaches: experiences from a case study. Working Paper GAM-2003-1, Department of Natural Resources and Environmental Sciences, University of Illinois, Champaign, IL, USA.
::Google Scholar::
Mendoza GA, Prabhu R (2003). Qualitative multi-criteria approaches to assessing indicators of sustainable forest resource management. Forest Ecology and Management 174: 329-343.
::CrossRef::Google Scholar::
Mendoza GA, Prabhu R (2005). Combining participatory modeling and multi-criteria analysis for community-based forest management. Forest Ecology and Management 207: 145-156.
::CrossRef::Google Scholar::
Mendoza GA, Prabhu R (2006). Participatory modeling and analysis for sustainable forest management: overview of soft system dynamics models and applications. Forest Policy and Economics 9: 179-196.
::CrossRef::Google Scholar::
Mendoza GA, Martins H (2006). Multi-criteria decision analysis in natural resource management: a critical review of methods and new modelling paradigms. Forest Ecology and Management 230: 1-22.
::CrossRef::Google Scholar::
Mose I, Weixlbauner N (2007). A new paradigm for protected areas in Europe? In: “Protected areas and regional development in Europe: towards a new model for the 21st century” (Mose I, Weixelbumer N eds). Ashgate, Aldershot, UK, pp. 3-20.
::Google Scholar::
Niemelä, J, Young J, Alard D, Askasibar M, Henle K, Johnson R, Kurttila M, Larsson T, Matouch S, Nowicki P, Paiva R, Portoghesi L, Smulders R, Stevenson A, Tartes U, Watt A (2005). Identifying, managing and monitoring conflicts between forest biodiversity conservation and other human interests in Europe Forest. Policy and Economics 7: 877- 890.
::CrossRef::Google Scholar::
Ojha HR, Cameron J, Kumar C (2009). Deliberation or symbolic violence? The governance of community forestry in Nepal. Forest Policy and Economics 11: 365-374.
::CrossRef::Google Scholar::
Panagopoulos T (2009). Linking forestry, sustainability and aesthetics. Ecological Economics 68: 2485-2489.
::CrossRef::Google Scholar::
Penker M (2009). Landscape governance for or by the local population? A property rights analysis in Austria. Land Use Policy 26: 947-953.
::CrossRef::Google Scholar::
Pocewicz A, Schnitzer R, Nielsen-Pincus M (2010). The social geography of southern Wyoming: Important places, development, and natural resource management, The Nature Conservancy, Lander, WY, USA, pp. 16.
::Online::Google Scholar::
Pretty JN (1994). Alternative systems of inquiry for sustainable agriculture. IDS Bulletin 25 (2): 37-48.
::CrossRef::Google Scholar::
Pretty J, Scoones IC, Guijt I, Thompson J (1995). A trainers guide for participatory learning and action. IIED, London, UK.
::Google Scholar::
Primmer E, Kyllönen S (2006). Goals for public participation implied by sustainable development, and the preparatory process of the Finnish National Forest Programme. Forest Policy and Economics 8: 838-853.
::CrossRef::Google Scholar::
Purnomo H, Mendoza G, Prabhu R (2004). Model of collaborative planning of community-managed resources based on qualitative soft systems approach. Journal of Tropical Forest Science 16: 106-131.
::Google Scholar::
Richard T, Burns S (1998). Beyond “scoping”. Citizens and San Juan National forest managers, learning together. Journal of Forestry: 39-43.
::Online::Google Scholar::
Saarikoski H, Tikkanen J, Leskinen LA (2010). Public participation in practice: assessing public participation in the preparation of regional forest programs in northern Finland. Forest Policy and Economics 12: 349-356.
::CrossRef::Google Scholar::
Saaty TL (1977). A scaling method for priorities in hierarchical structures. Journal of Mathematical Psychology 15: 234-281.
::CrossRef::Google Scholar::
Saaty TL (1980). The analytic hierarchy process. McGraw-Hill, New York, USA, pp. 287.
::Google Scholar::
Scardina AV, Mortimer MJ, Dudley L (2007). Getting past the who and how many to the how and why in USDA Forest Service public involvement processes. Forest Policy and Economics 9: 883-902.
::CrossRef::Google Scholar::
Schmoldt DL, Peterson DL (2000). Analytical group decision making in natural resources: methodology and application. Forest Science 46: 62-75.
::Google Scholar::
Seely B, Nelson J, Wells R, Peter B, Meitner M, Anderson A, Harshaw H, Sheppard S, Bunnell FL, Kimmins H, Harrison D (2004). The application of a hierarchical, decision-support system to evaluate multi-objective forest management strategies: a case study in northeastern British Columbia, Canada. Forest Ecology and Management 199: 283-305.
::CrossRef::Google Scholar::
Selman P (2004). Community participation in the planning and management of cultural landscapes. Journal of Environmental Planning and Management 47: 365-395.
::CrossRef::Google Scholar::
Sewell WRD, O’Riordan T (1976). Natural resources for a democratic society: public participation in decision-making. Westview Press, Boulder, CO, USA.
::Google Scholar::
Shannon M (1999). Moving from the limits and problems of rational planning toward a collaborative and participatory planning approach. In: “Formulation and Implementation of National Forest Programmes” (Glück P, Oesten G, Schanz H, Colz K-R eds). European Forest Institute Proceedings, Joensuu, Finland, pp. 139-151.
::Google Scholar::
Sheppard SRJ, Meitner M (2005). Using multi-criteria analysis and visualisation for sustainable forest management planning with stakeholder groups. Forest Ecology and Management 207: 171-187.
::CrossRef::Google Scholar::
Shindler B, Neburka J (1997). Public participation in forest planning. Journal of Forestry 17-19.
::Google Scholar::
Shindler BA, Brunson M, Stankey GH (2002). Social acceptability of forest conditions and management practices: a problem analysis. General Technical Report PNW-GTR-537, Pacific Northwest Research Station, USDA Forest Service, Portland, OR, USA, pp. 73.
::Online::Google Scholar::
Silvennionen H, Alho J, Kolehmainen O (2001). Prediction models of landscape preferences at the forest stand level. Landscape Urban Planning 56: 11-20.
::CrossRef::Google Scholar::
Sipilä M, Tyrväinen L (2005). Evaluation of collaborative urban forest planning in Helsinki, Finland. Urban Forestry and Urban Greening 4: 1-12.
::CrossRef::Google Scholar::
Stenseke M (2009). Local participation in cultural landscape maintenance: lessons from Sweden. Land Use Policy 26: 214-223.
::CrossRef::Google Scholar::
Stewart JMP, Sinclair AJ (2007). Meaningful public participation in environmental assessment: perspectives from Canadian participants, proponents and government. Journal of Environmental Assessment Policy and Management 9 (2): 161-183.
::CrossRef::Google Scholar::
Suárez de Vivero J, Rodríguez Mateos JC, Florido del Corral D (2008). The paradox of public participation in fisheries governance. The rising number of actors and the devolution process. Marine Policy 32: 319-325.
::CrossRef::Google Scholar::
Sugimura K, Howard TE (2008). Incorporating social factors to improve the Japanese forest zoning process. Forest Policy and Economics 10: 161-173.
::CrossRef::Google Scholar::
Swedeen P (2006). Post-normal science in practice: a Q study of the potential for sustainable forestry in Washington State, USA. Ecological Economics 57: 190-208.
::CrossRef::Google Scholar::
Tikkanen J, Isokääntä T, Pykäläinen, Leskinen P (2006). Applying cognitive mapping approach to explore the objective-structure of forest owners in a northern Finnish case area. Forest Policy and Economics 9: 139-152.
::CrossRef::Google Scholar::
Tourain A (1969). La societé post-industrialle. Bibliothèque Médiations 61, Denoël, Paris, France.
::Google Scholar::
Tuler S, Webler T (1999). Voices from the forest: what participants expect of a public participation process. Society and Natural Resources 12: 437-453.
::CrossRef::Google Scholar::
Tyrväinen L, Gustavsson R, Konijnendijk C, Ode A (2006). Visualization and landscape laboratories in planning, design and management of urban woodlands. Forest Policy and Economics 8: 811- 823.
::CrossRef::Google Scholar::
Twery MJ, Hornbeck JW (2001). Incorporating water goals into forest management decisions at a local level. Forest Ecology and Management 143: 87-93.
::CrossRef::Google Scholar::
Vacik H, Lexer MJ (2001). Application of a spatial decision support system in managing the protection forests of Vienna for sustained yield of water resources. Forest Ecology and Management 143: 65-76.
::CrossRef::Google Scholar::
Vainikainen N, Kangas A, Kangas J (2008). Empirical study on voting power in participatory forest planning. Journal of Environmental Management 88: 173-180.
::CrossRef::Google Scholar::
Weber N, Christophersen T (2002). The influence of nongovernmental organizations on the creation of Natura 2000 during the European Policy process. Forest Policy and Economics 4: 1-12.
::CrossRef::Google Scholar::
Webler T, Kastenholz H, Renn O (1995). Public participation in impact assessment: a social learning perspective. Environmental Impact Assessment Review 15: 443-463.
::CrossRef::Google Scholar::
World Commission on Environment and Development (1987). Our common future. Oxford University Press, Oxford, UK, pp. 416.
::Google Scholar::


Bruña-García X, Marey-Pérez MF (2014).
Public participation: a need of forest planning
iForest - Biogeosciences and Forestry 7: 216-226. - doi: 10.3832/ifor0979-007
First Previous Next Last
© iForest

Download Reference

Paper ID# ifor0979-007
Title Public participation: a need of forest planning
Authors Bruña-García X, Marey-Pérez MF
Close Download