Community Participation in Forest Management in the Yilo Krobo District, Eastern Ghana - Gerardo Oscar Paez

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    Community Participation in

    Forest Management in the Yilo

    Krobo District

    Gerardo Oscar Paez

    November 2009

    This dissertation is submitted to the University of Ghana in partial

    fulfillment of the requirement for the award of MA in Development

    Studies degree

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    DECLARATION

    I declare that this work has been my original research project carried out under

    the Supervision of Dr. Daniel Kwabena Twerefou of the Department of

    Economics and Dr. George Owusu of Institute of Statistical, Social and Economic

    Research, University of Ghana, Legon, Accra

    All references cited in this work are duly acknowledged. However, I am solely

    responsible for any errors and omissions.

    Supervisor Date Signature

    Dr. Daniel Kwabena Twerefow ................... ..........................

    Dr. George Owusu ................... ..........................

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    DEDICATION

    I wish to dedicate this work to my two major sources of inspiration, Amanda

    and Nestor. Also to my family as this work would not have been possible

    without their support.

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    ACKNOWLEDGEMENTS

    I wish to thank Dr. Daniel Kwabena Twerefou for his invaluable contributions

    and time spent. Also thank the Director of ISSER Prof. Ernest Aryeetey for his

    support.

    I am grateful to all the respondents of the survey and the members of all the

    institutions that kindly participated. Special thanks to the members of the Yilo

    Krobo District Authority, the Regional Forestry Commission Office and the

    Ministry of Food and Agriculture for providing me with valuable data.

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    ABSTRACT

    This study addresses the challenges of participation in forest management in

    the context of political decentralization in the Yilo Krobo District of Ghana in

    order to debate the possible implications of an inclusive natural resource

    management approach for the local livelihoods.

    This paper argues that capacity in the communities studied ought to be built up

    by providing the UCs with the physical as well as educational infrastructure that

    would enable the communities to be included in the participation process.

    Moreover, District Authorities should establish a process of negotiation with

    members of the community with regards to the best uses the community can

    give to the forest reserve.

    It also supports a shift to empowerment that ought to be sought by the District

    Authorities to allow people to take part in the decisions taken with regards to

    forest management as well as providing women with special mechanisms for

    participation, that adjust to their necessities and time availability.

    The study recommends actions in four priority areas: setting up mechanisms

    for indigenous practices and institutions, provision of capacity to the Unit

    Committees, encouraging participation of women and other excluded groups

    and clarifying land tenure.

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    TABLE OF CONTENTS

    CHAPTER 1 ........................... .......................... ......................... .......................... .......................... 11

    INTRODUCTION OF THE STUDY .......................... .......................... ......................... ...................... 11

    1.1. Introduction ........................... ......................... .......................... .......................... ................. 11

    1.2. Problem Statement ........................ .......................... .......................... ......................... ......... 12

    1.3. Objective of the study .............................................. ......................... .......................... ......... 13

    1.4. Justification ....................... .......................... .......................... ......................... ...................... 14

    1.5. Structure of the study ........................ .......................... ......................... ........................... .... 15

    CHAPTER 2 ........................... .......................... ......................... .......................... .......................... 16

    LITERATURE REVIEW ......................... ......................... .......................... .......................... ............. 16

    2.1. Introduction ........................... ......................... .......................... .......................... ................. 16

    2.2. Participation General Concepts ....................... .......................... .......................... ................. 17

    2.3. The Ghanaian Context ........................ .......................... ......................... ........................... .... 22

    2.4. Problems Found in Forest Management Globally ....................................... .......................... 30

    2.5. Alternative approaches to participation in forest management ........................... ................. 32

    CHAPTER 3 ........................... .......................... ......................... .......................... .......................... 36

    METHODOLOGY ....................... .......................... .......................... ......................... ...................... 36

    3.1. Introduction ........................... ......................... .......................... .......................... ................. 36

    3.2. General description of the study area and sites .............................................. ...................... 37

    3.3. Methods applied ........................ ......................... .......................... .......................... ............. 42

    3.4. Data analysis .......................... ......................... .......................... .......................... ................. 48

    3.5. Some methodological issues in research design ................................ ........................... ........ 49

    CHAPTER 4 ........................... .......................... ......................... .......................... .......................... 52

    DISCUSSION OF FINDINGS ......................... .......................... ......................... ........................... .... 52

    4.1. Introduction ........................... ......................... .......................... .......................... ................. 52

    4.2. Demographic Characteristics ....................... .......................... ......................... ...................... 52

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    4.3. Extent and nature of participation ............................... .......................... .......................... .... 55

    4.4. Capacity for effective participation ..................... .......................... .......................... ............. 58

    4.5. Forest Resource Management and political decentralization ....................... ......................... 59

    4.6. Forest Resource Management and the Boti Falls Reserve ....................... .......................... .... 61

    4.7. Discussion of findings ......................... .......................... ......................... ........................... .... 66

    CHAPTER 5 ........................... .......................... ......................... .......................... .......................... 72

    CONCLUSION AND RECOMMENDATIONS ........................ .......................... ......................... ......... 72

    5.1. Introduction ........................... ......................... .......................... .......................... ................. 72

    5.2. Recommendations ......................... .......................... .......................... ......................... ......... 72

    5.3. Conclusion ........................................................................................................................... 74

    BIBLIOGRAPHY ......................... .......................... .......................... ......................... ...................... 77

    APPENDIX ...................................................................................................................................81

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    LIST OF TABLES

    Number Description

    Table 2.2.3 Typology of Participation

    Table 3.2.2.4 Population Distribution by Area Council

    Table 4.2.2 Level of education by sex (Percentages)

    Table 4.2.3 Occupation of respondents

    Table 4.5.1 Perception of participation in decision

    making

    Table 4.5.2 Perception of political participation by sex

    Table 4.6.2 Location of the Forest Reserve

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    LIST OF FIGURES

    Number DescriptionFigure 4.2.1 Age distribution forest users interviewed

    Figure 4.3.1 Participation in FRM projects

    Figure 4.3.2 Participation in FRM projects by sex

    Figure 4.3.2 Participation in FRM projects Sort of

    Project

    Figure 4.3.3 Project activities description

    Figure 4.4 Proposition of projects perception

    Figure 4.6.2 Perceptions of best use of reserved land

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    LIST OF ACRONYMS/ABREVIATIONS

    ACs Area Councils

    FC Forestry Commission

    NTFP Non-Timber Forest Products

    RFD Rural Forestry Division

    RRA Rapid Rural Appraisal

    UCs Unit Committees

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    CHAPTER 1

    INTRODUCTION OF THE STUDY

    1.1. Introduction

    Forest histories are revealed as mutually constituting interplays of ecological

    process, social practice, policy intervention and response. Policy makers often

    do not see this, and are thus surprised when their schemes fail. (Leach, 2008:1)

    Amanor (2003) observes that contemporary environmental policies in West

    Africa are increasingly becoming decentralized, arguing that these policies are

    not more democratic. In Ghana, Wiggins et al. (2004) argue that with the 1994

    Forest and Wildlife Policy, communities were given a central role in

    participation in natural resource management. In addition, the authors suggest

    that despite the good intentions and effort put in formulating environmental

    policy, little of this translates into effective action in the field.

    This work aims to study the degree of participation of forest communities in

    natural resource management in the Yilo Krobo District in order to debate the

    possible implications of an inclusive natural resource management approach

    for the local livelihoods.

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    As an introduction to the thesis, this chapter provides a background to the

    study and clarifies the research problem seeking to introduce the concepts that

    inform and guide the study. After situating the study within the broader concept

    of political community participation in Ghana in general and the district in

    particular, the study objectives are presented. The last part of the chapter

    briefly introduces the chapter-by-chapter organization of the thesis.

    1.2. Problem Statement

    This study explores the interactions of people living in the Boti Forest Reserve

    margins of the Yilo Krobo District with its environment, authorities and

    institutions. In particular it focuses on identifying the key tensions of the

    decentralization process in order to address the causes of the low community

    participation in forest management in the district.

    According to the Medium Term Development Plan 2006-2009 (Yilo Krobo

    2006:15) community participation in governance is generally low in the

    district. There is high level of apathy among some people. The situation is more

    serious with the women, than their male counterparts. The same document

    states that the River Ponpong, which supplies water to the fall (Boti waterfall),

    dries up at certain times of the year, especially between December and April

    due to problems with the maintenance of the reserve protecting the river. There

    are illegal farming and felling of trees for fuel wood and charcoal in the reserve

    and along the river upstream. (Yilo Krobo 2006:63)

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    Ribot (2003) suggests that decentralization takes place when a central

    government formally transfers powers to actors and institutions at lower levels

    in a political-administrative and territorial hierarchy. In order to increase both

    efficiency and equity in natural resource management, decentralization is being

    promoted by development agents, natural resource managers and some

    environmentalists. However, Ribot argues that the implementation of

    environmental decentralization laws fall short of producing the most basic

    conditions necessary for effective decentralization. Research questions that

    arise are how do forest users interact with their environment and with the

    environmental authorities in the conservation of their forests? what are

    people's perceptions of their relationship with the authorities regarding forest

    management? what are the barriers to participation in forest management in

    the area studied and what may be the possible solutions?

    1.3. Objective of the study

    The objective of this study is to explore the different interactions that the Yilo

    Krobo residents have with the local forests and the environmental authorities

    in order to examine their actual participation in forest management. I aim to

    contribute to research that could be used by the district authorities and

    conservation bodies in order to achieve the outcome of sustainable

    development with social justice in the Yilo Krobo District.

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    1.4. Justification

    According to Forsyth et al. (1998), since the United Nations Conference on the

    Human Environment in 1972, the role of poverty in both causing and being

    caused by environmental degradation was acknowledged. In the Yilo Krobo

    District, where according to the Medium Term Development Plan 2006-2009

    (Yilo Krobo 2006) more than 60% of the population live in rural areas and the

    average per capita income ... is very low and cannot pay for individuals basic

    necessities, the conservation of the environment represents a key priority for

    the District authorities.

    In addition, since the year 2000 Ghana has adopted the targets of the

    Millennium Development Goals as the minimum requirements for socio

    economic development and poverty reduction (Republic of Ghana, 2006). This

    research contributes to the realization of MDG's 1 (eradicate extreme poverty

    and hunger), MDG3 (Promote gender equality and empower women) and

    MDG7 (ensuring environmental sustainability).

    This research will also contribute at the national level to the strategies of the

    Growth and Poverty Reduction Strategy II (Republic of Ghana, 2006) towards

    decentralization of powers.

    At the local level, this study will contribute to the District priorities in

    promoting good governance, civic responsibility and the objective of ensuring

    ...transparency, accountability, rule of law, public participation in decision-

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    making and improve service delivery of public institutions and security (Yilo

    Krobo, 2006:18).

    1.5. Structure of the study

    The study is divided in 5 chapters, where chapter 1 is the introduction; the

    review of literature on similar issues occurring worldwide is analyzed in

    chapter 2; in chapter 3 the study describes the methodology applied to collect

    and analyze the information necessary; chapter 4 contains the analysis of the

    data and chapter 5 contains the conclusion and recommendations.

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    CHAPTER 2

    LITERATURE REVIEW

    2.1. Introduction

    The importance of forests and of non-timber forest products (NTFPs) to the

    quality of life and even survival of very large numbers of poor rural people in

    tropical developing countries now seems indisputable. Trees and forests

    contribute in many ways to improving diets, combating hunger and increasing

    incomes in local communities and rural households in developing countries.

    Thus, food security, income, employment, energy sources and overall well being

    of rural people in these countries are linked to the forests (Shand, 1997).

    Since 1994 a number of policies have been put in place to promote community

    participation in forest management in Ghana, however, these policies have had

    little impact on their implementation. Several studies highlighted the need to go

    beyond increasing participation for its own sake to making participation

    effective. These studies concluded that in Ghana despite the fact that policies on

    forest decentralization are well developed, its implementation has been slow

    (Oppon Sasu, unpublished; Wiggins et al. 2004).

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    This chapter reviews relevant literature on the interactions of forest users with

    their environment and with political systems. This review seeks to both build

    on the strengths of relevant studies as well as to bring together the information

    available on community participation in forest management in the West African

    and the global contexts.

    2.2. Participation General Concepts

    2.2.1 Terms used in this studyParticipation: According to Agarwal (2001: p. 1624), views diverge on how

    participation is defined, whom it is expected to involve, what is expected to

    achieve, and how it is brought about. At its narrowest, participation in a group

    is defined in terms of nominal membership and at its broadest, in terms of a

    dynamic interactive process in which the disadvantaged have voice and

    influence decision making. In terms of objectives, at its narrowest participation

    is judged almost entirely by its potential efficiency effects and at its broadest by

    its ability to enhance equity, efficiency, empowerment and environmental

    sustainability. This study adopts the broadest definition of participation that,

    as suggested by Agarwal, it is believed to achieve the outcomes of sustainable

    forest management in the communities studied.

    Decentralization: Mawhood and Smith define decentralization as any political

    act in which a central government formally cedes powers to actors and

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    institutions at lower levels in a political-administrative and territorial

    hierarchy (Mawhood, 1983; Smith, 1985; cited in Ribot et al., 2006: 2).

    Institutions: O'Donell defines them as regularized patterns of interaction that

    are known, practiced, and regularly accepted (if not necessarily normatively

    approved) by given social agents who by virtue of those characteristics, expect

    to continue interacting under the rules and norms formally or informally

    embodied in those patterns. Sometimes, but not necessarily, institutions

    become formal organizations: they materialize in buildings, seals, rituals, and

    persons in roles that authorize them to speak for the organization (O'Donell,

    1993:4).

    Forest management: According to Wiersum, it refers to the total set of

    technical and social arrangements involved in the protection and maintenance

    of forest management for specific purposes, and the harvesting and distribution

    of forest products. In this respect, the author suggests that forest management

    should therefore be considered to include all conscious human activities

    directed at maintaining its production capacity. (Wiersum 1997: 7)

    2.2.2. Political DecentralizationDecentralized institutions are viewed as likely to perform better on the criteria

    of efficiency and equity for several reasons. Local authorities are presumed to

    have better time- and place-specific information which leads to better-targeted

    policies and lower transaction costs (World Bank, 1997). According to Ribot et

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    al. (2006), decentralization improves competition among jurisdictions and

    promotes greater political participation.

    Olowu (2001) argues that by simply assuming that a more democratic

    participation will be possible by bringing the power closer to the people we are

    excluding the political aspects of decentralization. In this sense, devolutionary

    decentralization confronts two major political problems. The first one is the

    unwillingness of political and administrative leaders to share the power

    inherited from colonial times. The second political issue is that in many

    instances is the local elite who may capture decentralized power and utilize it to

    repress the local minorities, women and foreigners in the various communities.

    Agarwal (2001) suggests that there are limits to what participation alone can

    achieve in terms of efficiency, given pre-existing socio-economic inequalities

    and relations of power. In this respect, Boone also observes the pre-existence of

    a social context as influencing decentralization schemes. The author states that

    governments may have important stakes in established power-brokers as well

    as in local-level social and political hierarchies that can extend beyond the reach

    of the state (Boone, 1998: 25; cited in Crook & Sverrison, 1999)

    2.2.3. Decentralization and Community Participation

    According to Ribot (2003) decentralization takes place when a central

    government formally transfers powers to actors and institutions at lower levels

    in a political-administrative and territorial hierarchy. In order to increase both

    efficiency and equity in natural resource management decentralization is being

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    promoted by development agents, natural resource managers and

    environmentalists. However, Ribot argues that the implementation of

    environmental decentralization laws fall short of producing the most basic

    conditions necessary for effective decentralization.

    Ribot (2007) suggests that representative local authorities can be strengthened

    through recognition; however, they may be weakened if they receive too little

    power to be effective, or if parallel institutions overshadow or appropriate their

    ability to serve public interest. Manor (2005), in this sense, provides the

    example of under-funded local governments with a mandate to manage natural

    resources operating in an arena with over-funded environment committees.

    As a result, Ribot (2003) concludes that countries and agencies claiming to

    undertake or support democratic decentralization of natural resources have

    widely failed to empower democratic local governments as they transfer just a

    few public powers over natural resources to existing and new democratic local

    governments. As a result, governments, international agencies and international

    non-governmental organizations (NGOs) are choosing to transfer these powers

    to a wide array of other local institutions, empowering chiefs, headmen and

    other customary leaders across Africa, in some cases threatening democratic

    decentralization reform efforts.

    2.2.4. Community Participation Typology

    Agarwal (2001) provides a typology of participation (see table 2.2.3). According

    to the author, achieving effective participation would involve a shift from the

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    lower level (Nominal Participation) to the higher level (Empowerment), with

    levels defined not by how a group is initiated but by the extent of peoples

    activeness.

    Mathbor (2008) suggests that local peoples involvement in all stages of

    development projects enhances effective participation.

    Table 2.2.3 Typology of Participation

    Form/Level of participation Characteristic features

    Nominal Participation Membership in the group

    Passive Participation Being informed of decisions ex facto;

    or attending meetings and listeningin on decision making, without

    speaking-up.

    Consultative Participation Being asked and opinion in specific

    matters without guarantee of

    influencing decisions.

    Activity-Specific Participation Being asked to (or volunteering to)undertake specific tasks.

    Interactive (empowering) Having voice and influence in the

    Participation groups decisions.

    Source: Agarwal (2001)

    2.2.5. Decentralization and the role of indigenous institutions

    Korten and Alfonso (1983) suggest that the most effective way to ensure

    success of development efforts is through encouraging local participation in

    development planning decisions. The authors suggest that an alternative to

    Western approaches to environmental project planning in developing countries

    may be developed by exploring and improving indigenous approaches to

    environmental conservation.

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    According to development scholars, historically, the use of improper planning

    strategies with little use of indigenous local knowledge has often resulted in

    inefficient allocation of resources and manpower resulting in failed attempts to

    alleviate rural poverty. In this regard, Appiah-Opoku & Mulamootil (1997)

    observe that the Western concept of development is widely interpreted as

    necessitating change, and is often characterized as a movement from the old or

    archaic (traditional) to the new (modern). This concept has proved unsuitable

    to be applied in the African context and brings the necessity for development

    planners of the introduction of traditional and indigenous institutions in

    development processes.

    2.3. The Ghanaian Context

    2.3.1. Political Decentralization in Ghana

    According to Owusu (2004), the present form of decentralization being

    implemented in Ghana can be traced back to 1988 when a comprehensive set of

    policies were designed to decentralize the system of Government. The aim of

    these policies is to promote popular participation and ownership of the

    machinery of government by shifting the process of governance from command

    to consultative processes, and by devolving power, competence and resources

    to the district level.

    In this context of decentralized government, Owusu (2004) suggests that

    District Assemblies were given responsibilities for the development of the

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    districts. For this purpose, they were provided with executive, legislative and

    deliberative powers, as well as administrative and technical support in order to

    articulate the views and aspirations of the people within districts. On a lower

    level are the sub-district structures, Unit Committees (UCs) and Area Councils

    (ACs) that are local organs of the District Assemblies with no independent

    powers. UCs and ACs are essentially consultative bodies with no budgets of

    their own.

    According to Oppon Sasu, (unpublished) UCs are the base structure of the local

    government system, which play the important roles of education, organization

    of communal labor, revenue raising, ensuring environmental cleanliness, and

    implementing and monitoring self-help projects among others. Oppon Sasu

    (unpublished), observes that District assemblies are made up of 67 percent

    elected representative and 33 percent government appointees. This split

    between elected and appointed members leaves a significant participation and

    accountability deficit, with the appointment system encouraging upward

    accountability to the Central Government rather downward accountability to

    the local electorate.

    Owusu (2004) mentions two different sources of revenue for the District

    Assemblies, internal and external, the latter includes grants from central

    governments, whilst internal ones includes rates, fees, licenses, and trading

    services. However, Owusu suggests that in many districts these internal

    revenue generating resources are either inadequate or poorly developed due to

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    the general poverty level and the underdevelopment of infrastructure and

    services. Therefore most District Assemblies depend on government revenue

    for the implementation of their development projects.

    Evaluating the effectiveness of Ghanas decentralization process, Korateng &

    Larbi (2008) argue that notwithstanding all the institutional and legal backing

    to decentralization, in practice there has been an increased concentration of

    power and resources in key sector Ministries, Departments and Agencies. The

    authors affirm that key actors in the process have been competing rather than

    cooperating, resulting in a weakening of the local governments capacity to

    manage the decentralization process.

    In addition, Wardell & Lund (2006) suggest that recent decentralization

    initiatives in Ghana have witnessed a proliferation of actors with the

    maintenance of central government controls that are aimed to limit the political

    and fiscal autonomy of the District Assemblies. This has led to an increasing

    reliance of District assemblies on the central government and/or external

    funding. As a result, the authors conclude, District Assemblies are now more

    dependent on central government assistance and/or external funding to meet

    their recurrent expenditure than they were in the 1960s.

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    2.3.2. Forest management and participation in Ghana2.3.2.1. Background

    Wiggins et al. (2004) highlight the importance of sound environmental policies

    for rural communities of the forest margins suggesting that given the high

    degree to which they depend on the use of local natural resources,

    inappropriate environmental policy may reduce jobs and incomes of people,

    most of whom are already poor by any definition.

    According to Appiah-Opoku & Mulamoottil (1997) Ghana has experienced

    development planning without systematic analysis of the potential

    environmental impacts since 1919 when the colonial British government

    introduced a 5-year development plan. According to the authors, this trend

    continued after the countrys independence from the British with a strong

    reliance on modernization theory as the major development strategy which

    focused on urban industrialization and rejected indigenous life-styles in favor of

    modern systems.

    In the late 1980s under the auspices of the Forest Resource Management

    Project, a Rural Forestry Division (RFD) was established with a specific

    mandate to promote community participation in forestry activities in

    northern Ghana. The RFD channeled much-needed resources to the regional

    and district forest offices to support the maintenance and patrolling of forest

    reserve boundaries as well as the establishment of village woodlots. RFD was

    dissolved as part of the major sectoral reforms implemented in the late 1990s

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    through the Forest Sector Development Project that culminated in the creation

    of a Forest Services Division accountable to a revamped Forestry Commission

    (Forestry Commission, 2001; cited in Wardell & Lund 2006). The FC formed

    community forestry committees at the unit level to enhance community

    empowerment and participation in resource management (Oppon Sasu,

    unpublished).

    2.3.2.2. Problems faced in forest management in Ghana

    Oppon Sasu (unpublished) suggests that in Ghana decentralization policies in

    the forest sector have been evaluated by several studies, which in many

    occasions concluded that implementation of policies on decentralization of

    forest management has been slow despite the fact that policies are well

    developed.

    Major problems outlined by the literature are: top-down approaches from

    government, the capture of power by local elites, under-resourcing of local

    institutions, under-value of indigenous knowledge, low women participation in

    decision making processes.

    2.3.2.2.1. Top-Down approaches to Natural Resources Management

    Amanor (2003) suggests that most West African states have initiated

    decentralization programs, with devolution of natural resource management as

    an important component. Most national forestry services in the region now

    recognize the importance of community forestry, collaborative forestry, or joint

    forest management and have developed a critique of previous practices based

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    on exclusionary top-down approaches. However, the author argues that global

    and national agencies aim to get rural communities to participate in the

    programs, rather than creating a platform where rural people can make their

    own inputs into natural resource policy. (Amanor 2003:1)

    Moreover, the author highlights that participatory forest management policies

    applied are rooted in neoliberal economic philosophy which needs to make

    forestry management more efficient by involving communities therefore

    lowering the transaction costs of management (Amanor 2003:1). This, in the

    authors opinion would explain the low participation in forestry projects of

    many local communities.

    2.3.2.2.2. Capture of power by the local elites

    The problem of local elites capture ofpower in Ghanaian communities has been

    described by Crook (2003). The author observes that even though in recent

    years local peoples participation in community development associations has

    thriven, these are run by local elites that do not necessarily enhance

    representation of the poor. Thus, existing social hierarchies are seldom

    challenged in decisions taken in public meetings called by such associations.

    Wardell and Lund (2005) study on access to forest reserves in Northern Ghana

    shows that the restrictive laws on access to land and resources in forest

    reserves and policies put in place by the government as well as regulations of

    the Forestry Department, have provided a context for monetary and political

    rent seeking for other political agents (Wardell and Lund, 2005: 1888) who

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    may use central government policy and directives to reinforce their authority at

    the local level. The authors demonstrate in their study that access to land is not

    a right but a tolerated crime.

    2.3.2.2.3. Under-resourcing of local institutions

    Agrawal and Gibson (1999) suggest that effective institutionalization of

    community-based conservation requires that local groups have access to

    adequate funds for implementing the rules they create. In addition, Amanor and

    Brown (2003) in a review of the impact of decentralization and local

    environmental management observed that the performance of the

    decentralized structures have been weak as far as environmental management

    is concerned due probably to the chronic under-resourcing of the

    decentralization process and its resulting incapacity.

    Oppon Sasu (unpublished) further suggests that the weaknesses of local

    institutions in the Ghanaian decentralization process and effective

    implementation of collaborative forest management approaches are one of the

    key shortfalls of the decentralization process.

    2.3.2.2.4. Low women participation in forest management

    The importance of including women in forest management in West African

    Countries is highlighted by several studies. A major reason is, as Agrawal et al.

    (2006) point out, that women are active users of forest management. This has

    to do, in large part, with social and cultural expectations which accord women

    primary responsibility for collecting forest products for household use.

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    Elmhirst & Resurreccion (2008) suggest that sustainable development policy

    initiatives that seek to ameliorate environmental degradation and its negative

    livelihood effects not only bring gendered impacts and responses, but also

    produce particular framings of gender and gendered power relations. In this

    sense, Agrawal et al. (2006) suggest that the state plays a very important role in

    ensuring the interests of women are protected.

    Someshwar (1993) emphasizes the importance of the state on facilitating the

    formation of institutions that give voice to the disempowered groups suggesting

    that in unequal societies, decentralization of decision-making does not

    necessarily result in increased participation by all sections of the population,

    the disempowered groups would likely continue to be outside such process.

    Someshwar argues that contrary to current perceptions, management of natural

    resources cannot and should not be completely divorced from the state.

    Leach (1994) points out that a gender-sensitive forest management strategy

    accounts for gender-differentiated activities, property rights, and forest

    resource claims, and situates them within the context of a web of social

    relations. A gendered approach to community-based resource management

    recognizes that questions of rights and control, above all others, implicate the

    social relationships within which resources are managed and used.

    Furthermore, focusing exclusively on women obscures their relations with men,

    implying that womens and mens resource-management activities proceed

    along isolated, parallel tracks.

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    2.4. Problems Found in Forest Management Globally

    2.4.1. Communities seen as static bodies

    According to Biesbrouck (2002) working with communities has become a

    cultural policy paradigm alongside linked to attempts at sustainable forest

    management. Mearns et al (1999) suggest that communities are assumed to be

    relatively homogeneous, with members' shared characteristics that distinguish

    them from 'outsiders'. Equally fundamental is the assumption of a distinct and

    relatively stable local environment which may have succumbed to degradation

    or deterioration, but has the potential to be restored and managed sustainably.

    The community is seen as the appropriate unit to carry out such restoration and

    care, and is envisaged as being capable of acting collectively towards common

    environmental interests.

    Agrawal & Gibson (1999) expand on this matter suggesting that the vision of a

    community as a homogeneous whole fails to attend to differences within

    communities. This vision ignores how these differences affect resource

    management outcomes, local politics, and strategic interactions within

    communities as well as the possibility of layered alliances that can span

    multiple levels of politics. The authors conclude that the term community must

    be examined in the context of development and conservation by focusing on the

    multiple interests and actors within communities, on how these actors

    influence decision-making, and on the internal and external institutions that

    shape the decision-making process. The authors suggest that a focus on

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    institutions rather than community is likely to be more fruitful for those

    interested in community-based natural resource management.

    2.4.2. Assumptions about deforestation and forest cover

    Leach & Fairhead (2000) suggest that analyses of determination of past forest

    cover in Ghanaian forests used in today's estimates are highly questionable.

    Many authors have simply assumed that the entire forest zone (around 8

    million hectares) was forest. Such statistics are usually linked to images of rapid

    population growth from and initially low baseline, swelled by immigration into

    forest areas. The authors argue that in fact even as early as 1933, the forester

    Meniaud suggested that statistics exaggerated the extent of forest cover.

    Moreover, study renders invalid the notion that an equilibrium of low (or no)

    population and undisturbed forest existed throughout the West African forest

    zone at the turn of the twentieth century.

    Leach & Fairhead (2000) argue that neo-Malthusian deforestation narratives

    misrepresent the relationships between people and forests and obscure

    processes by which people have enriched landscapes with trees, and in which

    the peopling of a landscape has sometimes meant an expansion of tree and

    forest cover. These perspectives usually result in policies and programs that fail

    to include local people from taking part on decision making processes, and end

    up excluding local peoples access to their property (to combat or redress forest

    loss) in the name of biodiversity and resources preservation or climate change.

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    2.5. Alternative approaches to participation in forest management

    Mathbor (2008) suggests thatpeoples involvement in all stages of development

    projects (such as needs assessment, decision making, implementation and

    evaluation) enhances effective participation. Taking into account the problems

    faced by mainstream participatory approaches put in practice by the central

    and local governments of Ghana, this study reviews alternative approaches that

    may be incorporated to address the issues of sustainable forest uses and

    practices.

    2.5.1. Indigenous approaches or Endogenous Development

    According to Wiersum (1997) several studies have indicated that local people

    living in or near forests should not be considered as mere gatherers of forest

    products and/or as people who are transforming forests into agriculture. In

    many cases they are active forest managers who are involved in purposeful

    activities to safeguard the continuous availability of the valuable forest

    management.

    Wiersum (1997: 9) suggests that for common property forest management

    regimes to function properly there should exist an indigenous institution for

    forest management with the following characteristics:

    A structure for group members to make decisions on the required resource

    management practices;

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    Group control over the behavior of the group members, which ensures that

    the planned management practices are carried out;

    Control over the distribution of collected forest products;

    Ability to exclude outsiders.

    Such an institution need not be a formal forest management organization. A

    cultural/religious institution may ensure a similar effect (Wiersum 1997: 9).

    Appiah-Opoku & Mulamoottil (1997) highlight some limitations that can be

    found in the integration of indigenous systems in environmental assessment.

    The barriers include the higher illiteracy rate among members of indigenous

    institutions, language problems, and the difficulty in changing entrenched

    attitudes. There is also skepticism on the part of government officials and

    scientists that indigenous institutions and their ecological knowledge systems

    have been almost irreversibly eroded by the assimilation of indigenous peoples

    into Western culture. The authors observe that some of these barriers could be

    removed through community-based action research and intensive public

    education through the media, formal education system, and with the help of

    non-governmental organizations.

    2.5.2. Adaptive and Deliberative governance approaches

    According to Leach (2008), moves towards alternative governance approaches

    that respond adaptively and reflexively must be seen as essentially political.

    Such politics is in part a politics of knowledge, which can be informed by

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    scientific analyses of contexts, systems, and their properties, but fundamentally

    requires an opening up of debate through a diversification of knowledge bases.

    But it is also a politics linked to the real political economy of environment and

    development.

    Leach (2008) suggests that science policy processes which have emerged

    historically through the intersection of national and globalised needs and

    practices, have produced a set of dominant concepts and approaches which

    strongly drive environmental development in relation to tropical forests. By

    contrast, the author observes that recent work on adaptive governance offers

    suggestions for addressing some of the challenges of dealing with intertwined

    and dynamic socio-ecological systems. Rather than the implementation of

    singular plans, adaptive governance emphasizes the interaction of multiple

    institutions in guiding a complex system towards an improved state or

    trajectory (transformability) or maintaining it in a desired state or trajectory

    (resilience) (Leach, 2008: 1791).

    Leach (2008) emphasizes that adaptive governance emphasizes flexibility,

    experimentation and learning as strategies for anticipating and dealing with

    unintended consequences. Such governance approaches are thus deemed

    appropriate to situations of rapid change and high uncertainty. Nevertheless,

    they tend to assume that there are shared goals around what system properties

    should remain resilient, or that consensus can be built through the governance

    process. To address these, it could be argued, requires approaches to forest

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    governance that are also deliberative and reflexive which emphasize bringing

    together diverse actors to render explicit, and discuss and negotiate, their

    particular views of the world.

    Leach (2008) suggests that deliberation would need to bring local forest users

    into dialogue with policy makers and scientists of both equilibrial and

    nonequilibrial persuasions. Reflexive governance goes further to engage with

    the implications of plural framings of what constitutes the social-ecological

    system, and the implications of sustainability goals, recognizing that these are

    contingent and conditioned by divergent social values, historical experiences,

    interests, and institutional commitments. Goals are thus rarely determined once

    and for all, since knowledge, values and interests in social-ecological systems

    evolve and develop over time.

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    CHAPTER 3

    METHODOLOGY

    3.1. Introduction

    Models and policies could go awry if intra-household dynamics are assumed

    (as they often are) to exist in isolation, without examining the extra household

    socio-economic and legal institutions within which households are embedded,

    and how these institutions might themselves be subject to change (Agarwal,

    1997: 2).

    In order to gather information which would contribute to an understanding of

    the complexity of issues surrounding community participation and local

    people's use of forest management, no one method is sufficient. Thus, a multiple

    methodology is required in order to clearly understand the complex

    relationship between nature (forests), society (human activities) and the

    authorities.

    This chapter discusses the strategy and the various methods of data collection

    employed in this study. Some methodological issues in research design and

    fieldwork have also been considered. The chapter begins with a description of

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    the study area and choice of the study sites. The final section discusses the main

    methods of data analysis applied in this study.

    3.2. General description of the study area and sites

    The study was conducted in the Yilo Krobo District which covers an estimated

    area of 805 sq km. It shares boundaries with Manya Krobo District in the North

    and East, Damgbe West and Akwapim North Districts in the South; New

    Juabeng, East Akim and Fanteakwa Districts in the West (Yilo Krobo, 2006).

    There are two forest reserves in the district. These are the Boti Falls Forest

    Reserve and the Volta River Block 2 Forest Reserve at Klo-Begoro. Together,

    they add up to 21.83sq km. The specific area of study lays in the surrounding

    communities of the Boti Forest Reserve specifically the villages of Boti, Amanfro

    and Huhunya.

    According to the District's Authority (Yilo Krobo, 2006) one of the most

    important items of aesthetic and scientific importance in the district is the

    forest reserve of Boti. In this reserve, there are various tree species of scientific

    importance due to conservation of biodiversity. These forest reserves also serve

    as habitats for wildlife and as water sheds for the rivers.

    3.2.1. Selection of the study area

    A number of factors influenced the selection of the Boti Forest Reserve

    surrounding villages for the purpose of this study.

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    Firstly, Boti is a rural area. According to the 2000 Census the Boti area council

    has the lowest per capita income of the seven area councils in the district (Yilo

    Krobo, 2006), which means that many households rely on subsistence farming

    in order to provide for their basic needs. Therefore the reserve provides a great

    potential for land use, subsistence farming and trade in non-timber forest

    products (NTFP) for the communities of the area.

    Secondly, as the Medium Term Development Plan (Yilo Krobo, 2006) shows, the

    Boti Falls Forest Reserve is one of the most important items of aes thetic and

    scientific importance in the district. However, as the same document states,

    problems with the maintenance of the reserves include illegal farming and

    illegal felling of trees. The extraction of wood is done for fuel-wood and

    charcoal burning. Therefore this zone offered the opportunity to uncover or

    reveal possible conflicts and divergent opinions (regarding use rights) between

    the local people who depend on the forests for NTFPs and the district

    authorities whose motive has been to raise revenue by utilizing the Forest

    Reserve as a tourist attraction.

    Thirdly, Chambers analysis of project biases on field research notes that

    research generate more research, and investment by donors draws research

    after and funds it (Chambers, 1983: 17). As a consequence of what he calls

    project bias, the area has not yet attracted the attention of researchers, more

    attracted to study areas that have already been supported by donors funds (e.g.

    areas utilized for commercial timber production or that have already been

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    exploited as tourist attraction). Hence, the Boti Falls Forest Reserve is an area

    where little information has been previously gathered.

    In order to capture the full set of issues about how forest and tree resources

    form part of livelihood structures, data was collected from communities around

    the Boti forest reserve area for a period of five months - between February and

    June 2009. The communities studied are Boti Falls Village, Asiafo Amanfro and

    Huhunya, which are situated near the forest reserve margins.

    3.2.2. General description of the Yilo Krobo District

    3.2.2.1. TopographyThe district lies within the semi-deciduous rain forest and the coastal savanna

    zone of the country. There is the dry semi-deciduous (fire zone) which stretches

    from the district to the lower part of the Manya Krobo District covering 855

    square kilometers.

    The area is predominantly mountainous. The Akwapim Ranges stretch into the

    district from south-west to north-east across the district. With its

    accompanying deep valleys, it provides an undulating landscape.

    There are two main watersheds forming three river basins in the district. One of

    the watersheds is located on the Akwapim Ranges where rivers flow in the

    eastward direction on the lowlands into the Volta River. On the west of the

    ranges, the rivers flow into he Ponpong River, which empties into the Volta

    Lake.

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    3.2.2.2. Climate and drainageThe Yilo Krobo District lays within the dry equatorial climatic zone which

    experiences substantial amount of precipitation. This is characterized by a bi-

    modal rainy season, which reaches its maximum during the two peak periods of

    May June and September October. The annual rainfall is between 750mm in

    the southeast and 1600mm on the slopes of the ranges in the northwest.

    Temperature ranges between a minimum of 24.90 C and a maximum of 29.90 C.

    A relative humidity of 60 93 percent is characteristic of the district.

    3.2.2.3. Local natural resourcesThe Akwapim Range stretches into the district and divides it into a series of

    highlands starting from the west of Somanya. There are several other isolated

    rock outcrops depicting an undulating landscape. In between these highlands,

    there are relatively flatlands of about 800ft above see level. Most of the

    settlements are found on these lowlands.

    Part of the Volta Lake stretches into the district at Bukunor. This has provided

    opportunities for fishing and fishing related activities in the area. Numerous

    streams and rivers drain into the lake. River Ponpong is the major river that

    runs through the district.

    There are two forest reserves in the district. These are the Boti Falls Forest

    Reserve and the Volta River Block 2 Forest Reserve at Klo-Begoro. Together,

    they add up to 21.83sq km. There are herbal species in these forest reserves.

    Apart from individual herbalists who have been collecting some species from

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    here, the Mampong Centre for Herbal Research is known to have harvested

    some plants there for the purpose of preparing herbal medicine. Other species

    that are found in these reserves are Wawa, Odum, Onyina and Mahogany.

    The District is endowed with deposits of quality limestone and other stones that

    are good for constructional works. There are also clay deposits in several parts

    of the district including Okwenya.

    3.2.2.4. Population, settlements and roadsThe district total population, according to the 2000 population Census was

    86,107 signifying a 4.1% increase over the population in 1984. With a growth

    rate of 2.6%, the districts population is currently estimated at 97,898. The

    district is predominantly rural with more than 67% of its population living in

    rural areas. The district is divided into seven area councils namely, Somanya,

    Oterkpolu, Boti, Nkurakan, Nsutapong, Klo-Agogo and Obawale (Yilo Krobo,

    2006). Table 3.2.2.4 shows the population distribution for selected Area

    councils.

    Table 3.2.2.4 - Population Distribution by Area Council (selected)

    Area Council Total Population % No. of % hhold

    households size

    Somanya 33,080 38.42 8,065 4.1

    Nkurakan 16,078 18.67 3,343 4.8

    Boti 12,321 14.31 2,347 5.3

    Source: Yilo Krobo Medium Term Development Plan, 2006; Compiled from

    2000 Population Census.

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    3.3. Methods applied

    The complexity of the issues investigated, the use of both quantitative and

    qualitative methodologies was needed and a less standardized and more

    flexible approach.

    A desktop data search was conducted in various institutions resources during

    the initial stages of the study. Other methods of data collection applied included,

    focused groups, interviews with key informants, survey and participant

    observation. These methods are described in detail below.

    3.3.1. Use of Rapid Appraisal Techniques

    Rapid appraisal (RA) refers to a family of methodologies designed to

    encourage the participation of local communities in the collection and use of

    information to improve their livelihoods (Freudenberger, 1994: 1).

    Given the nature of the study and the kind of information to be collected, the

    research was based on qualitative data and complemented by the use of

    quantitative methods. According to Bryman (1988), the advantages of

    combining quantitative and qualitative research include:

    The logic of 'triangulation'. This is an approach in which multiple

    observers, theoretical perspectives, sources of data, and methodologies

    are combined. Within this context, quantitative and qualitative research

    may be perceived as different ways of examining the same research

    problem albeit with differing objectives. By combining the two, the

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    researcher's claims for the validity of his or her conclusions are

    enhanced if they can be shown to provide mutual confirmation.

    Quantitative and qualitative research can be combined in order to

    produce a general picture

    Structure and process - qualitative research presents a processual view

    of social life whereas quantitative research provides a static account.

    RRA has been considered an appropriate tool to be applied throughout this

    study, as it helped to identify the competing, convergent, complementary and

    conflicting interests and knowledge base among individuals as well as among

    the 'experts' and 'locals', in the overall environmental/forest management and

    community participation issues.

    Furthermore, adopting on field work a learning principle has enabled the

    researcher to obtain important and sensitive information about the local setting

    and to reduce the influence of ethnocentrism. This principle is based on the

    premise that rural forest dwellers are a repository of knowledge about their

    local environment, trees, management skills and utilization of resources,

    therefore, researchers should be able to open their mind, be good listeners and

    be open to learn from the local people respecting their culture and traditions.

    Sampling, data collection and analysis techniques are described in the following

    sections.

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    3.3.2. Sampling Methods

    The communities studied were selected considering their location near Boti

    Falls Forest Reserve. However, it was not possible to obtain adequate sample

    frame from the District authorities, as no such list was readily available. In

    addition, it would have been very time consuming and expensive to survey all

    the households and population features, hence the use of purposive sampling.

    Considering these aspects, a sample of 50 people willing to participate in the

    survey were selected, which would be the sample frame of the study. Following

    this, 24 forest users were selected using a systematic random sampling

    technique.

    Participants from the District Assembly, Forestry Commission, Ministry of Food

    and Agriculture and Traditional Authorities were purposively selected. The

    same applies for participants of the focused group discussion. Discussions were

    held with the district Planning Officer and Assembly Person, the Forestry

    Commission Regional Manager and field and administrative officers as well as

    the Director of the Ministry of Food and Agriculture.

    3.3.3. Methods of data collection

    In investigating how local people interact with their environment and the local

    authorities it seemed that neither qualitative nor quantitative methodology

    alone were able to achieve the research objectives. Therefore, an integration of

    quantitative and qualitative methods was chosen to help unpack the

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    interlocking deep-seated structures and processes that influence decision

    making in the communities studied.

    Methods of data collection applied include focused group discussions, desktop

    data search, key informant interview, survey and participant observation.

    3.3.3.1. Desk-top data search

    A literature search was conducted in various institutions in Ghana, including the

    districts Forestry Commission Office and Achimota Headquarters, District

    Assembly offices and the Traditional council as well as the University of Ghana

    and ISSER libraries to bring together what has already been done relating to

    forestry and local livelihood security in Ghana. Also on-line journals and foreign

    academic institutions' on-line sources were searched. Relevant documents

    (such as policy and legislation materials) obtained from the search were

    analyzed, in order to provide the framework for evaluating the situation on the

    ground.

    3.3.3.2. Focused group discussions

    Focused group discussions and transect walks were used in the initial stages of

    data collection to gain an initial understanding of the rural setting and to

    establish rapport with the local people as well as village leaders and key

    informants. After the initial participation by the researcher in community

    meetings as an outsider, separate meetings were held with different groups

    such as women, men and youths.

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    In addition, individual meetings with the 'experts' of each village were

    organized in order to give them the opportunity to talk freely and to capture a

    wide range of issues relating to forest use and participation. These meetings

    were aimed at capturing information relating to aspects of culture, attitudes

    and perceptions regarding farming practices and forest product use, land rights

    and access issues and local people's perception of participatory approaches.

    3.3.3.3. Key informant interview

    Key informants are persons with particular occupational skills, persons in

    positions of leadership in village political and/or administrative units, activists

    or representatives of particular groups in the community and individuals who

    for one reason or another are in a position to know 'something special' about

    the community.

    Following the forest user questionnaire interviews and analysis of the data,

    semi-structured interviews were conducted with selected respondents and key

    informants to further investigate key issues that emerged from the analysis of

    the data. Interviews were held in different places and times with teachers,

    members of the traditional authority, the director of the Ministry of food and

    Agriculture and older residents living in the area.

    3.3.3.4. Survey

    A household is usually defined as a set of persons most of whom are linked by

    kinship and marriage, acting as a joint consumption/residential unit having a

    single budget; operationally, members of the group, whose core is a "family",

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    eat from the same pot and live under the same roof (Almeida, 1996: 122). Elson

    recognizes that households are in some sense pooling and sharing

    organizations, but instead, she argues that this intra-household interaction is

    problematic as there is considerable evidence that while women typically pool

    and share their income, especially with their children, men are more inclined to

    reserve part of their income for discretionary personal spending (Elson, 1995 in

    Agarwal, 1997). In Addition, Agarwal (1997) argues that households are

    comprised of a variety actors, with often conflicting preferences and interests.

    They are arenas where decisions are made with respect to consumption,

    production and investment of labor and resource allocation.

    In this sense, ignoring the gender division of labor that happens intra-

    household would have undermined the results of this study, hence interviewing

    forest users at an individual level has been considered a more appropriate

    approach. For the reasons above presented, the Forest User Questionnaire was

    designed and administered to even number of male and female forest users

    randomly selected from the villages studied and in depth interviews were

    conducted to gather the data used in the analysis.

    The questionnaire contains relevant sections for this study such as Socio-

    demographic Characteristics, Economic Activities, Community Participation and

    Forest Perceptions. The Forest User Questionnaire is enclosed to this study as

    Appendix I. In order to interview the district authorities and other officials the

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    Forest User Questionnaire was adapted to cover all the relevant information

    needed. Open ended questions were used to collect qualitative data.

    3.3.3.5. Participant observation

    To supplement the above methods, I have also conducted my own detailed

    direct observation and assessment of the environment as pertains to the

    condition of the forests and forest management use, farm and off-farm activities

    of the villagers, and product gathering in the forest reserve whilst engaging in

    informal talks and discussions with the villagers. These informal discussions

    were an essential component of this study as they allowed the researcher to

    gain the confidence from the community and get informed of cultural and

    everyday life issues villagers live.

    According to May (2001), one of the main advantages of participant observation

    is its flexibility. May suggests that participant observation is a continual

    process of reflection and alteration of the focus of observations in accordance

    with analytic developments. It permits researchers to witness people's actions

    in different settings and routinely ask themselves a myriad of questions

    concerning motivations, belief, and actions (May 2001: p.159).

    3.4. Data analysis

    The data was analyzed both quantitatively and qualitatively using statistical and

    non-statistical techniques. The various responses for the close ended questions

    were edited and coded accordingly. The open ended questions were classified

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    into categories after studying the responses and analysis was based on

    discussion and interpretation of trends and patterns in target participants

    perceptions. Thereafter the Statistical Package for Social Sciences (SPSS) was

    used for data entry and analysis. The analysis yielded frequency tables and

    cross tabulations to facilitate examination of relationship between variables.

    Some of the results are presented in tables, diagrams and figures where it was

    considered necessary.

    The conclusions drawn from the statistical analysis supplemented qualitative

    assessments conducted in each community. These assessments allowed for

    checks on indicators against the perceptions of community members to ensure

    that they were accurate and reflected the reality of each community.

    3.5. Some methodological issues in research design

    An important issue has been how to become an insidee of the communities

    studied, so as to achieve a thorough observation and acquire a deep and

    comprehensive understanding of the issues being studied.

    In order to identify potential informants and introduce myself to the

    communities, assistance from the Forestry Commission District Manager and

    officers was required given their experience working with the communities.

    Prior to the field visit, a series of meetings were held with the District Forestry

    Commission Manager, Forestry Officials and MOFA Officers aimed to ensure

    that the study is focused on relevant themes and to establish the relevance of

    the study objectives. After these initial discussions, mostly held in Somanya,

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    permission to enter the communities was first sought from the District

    Assembly's Planning Officer. After gaining permission from him, permission

    was sought from the local chiefs and their elders followed by the local

    committee chairman and its members.

    3.5.1. Ethics in the interviewing process

    Problems concerning the privacy and anonymity of sensitive issues that arose

    during the interviews were avoided by maintaining constant neutrality and a

    careful use of the information provided throughout the interviewing process

    and subsequent stages of the research.

    Despite the precautions taken, difficulties were found in communicating with

    some members of the community given the fact that I can not speak Krobo, the

    language used by most members of the communities for communication. In

    these cases, I mediated these difficulties through the use of an interpreter and

    cultural translator.

    3.5.2. Limitations

    Understanding in what ways values and research practice interact is the

    beginning of the process of pursuing maximum accuracy. In this sense, May

    (2001:47) suggests that an awareness of the limitations of our work, as well as

    its strengths, enables us to reflect upon them in a productive fashion and take

    appropriate action. In this respect, I am conscious that the research dynamic

    and the data I collected have been influenced by my status as a white, male

    researcher.

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    CHAPTER 4

    DISCUSSION OF FINDINGS

    4.1. Introduction

    This chapter presents critical, objective and systematic analysis of empirical

    data collected from a survey on Community Participation in Forest Management

    in Yilo Krobo District. The research findings are presented in 7 sections that

    reflect the studys objectives. The first section deals with the socio-demographic

    characteristics of the population surveyed. The chapter is further organized into

    sections and sub-sections that deal with forest management and community

    participation issues in Yilo Krobo District.

    4.2. Demographic Characteristics

    Before discussing the main issues this research presents the demographic

    characteristics of respondents.

    4.2.1. Age distribution of forest users interviewedIn order to undertake systematic analyses, the study surveyed respondents of

    varying backgrounds and occupations.The age distribution of the twenty-four

    forest users interviewed is given in figure 4.2.1

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    Source: Authors survey , 2009.

    Figure 4.2.1 shows that majority of interviewees occupied age groups 25-34

    and 35-44, forming 50% of forest users interviewed. In the 25-34 group, 12.5%

    of women and 16.7 % of males were interviewed, whilst for the age group 35

    44, 12.5% of women and 8.3% of men were interviewed. This implies the

    survey covered more youthful respondents with a cumulative response rate of

    66.7% when we include the 15-24 group.

    4.2.2. Educational level of respondents by sexAccording to Mohamed-Anwar (unpublished), education is usually associated

    with greater knowledge and participation in decision making at both the

    household and community levels. Table 4.2.2 below shows the educational level

    of respondents disaggregated by sex. From this table it is clear that 21% have

    completed primary school and 58% of the respondents have completed

    secondary school. 8% of the respondents have completed post secondary

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    education and 13% had no formal education. 88% of respondents had

    completed at least one form of formal education. Level of education is an

    important variable to consider as it has positive relationship with participation.

    Table 4.2.2 shows the level of education disaggregated by sex.

    Table 4.2.2 Level of education by sex (Percentages)

    Educational level (Percentage)

    TotalNone Primary Secondary

    Post

    secondary

    Sex Male 4% 13% 29% 4% 50%

    Female 8% 8% 29% 4% 50%

    Total 13% 21% 58% 8% 100%

    Source: Authors survey , 2009.

    4.2.3. Occupational Distribution of respondents

    Farming was the occupation of 29% of the people interviewed. The second most

    common occupation of interviewees was trading with 21% of the survey

    respondents. These occupational groups represent 50% of the respondents

    against a remaining 50% composed of occupations such as charcoal burners,

    teachers and civil servants among others. Table 4.2.3 shows the occupational

    distribution of respondents.

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    Table 4.2.3 Occupation of respondents

    Frequency Percent

    Farmer 7 29

    Charcoal burner 2 8

    Teacher 2 8

    Civil servant 2 8

    Student 2 8

    Trader 5 21

    Tour guide 2 8

    Other 2 8

    Total 24 100

    Source: Authors survey , 2009.

    4.3. Extent and nature of participation

    4.3.1. Participation in forest management projects

    Participation in Forest Management in Yilo Krobo District is described in Figure

    4.3.1 which shows that 29.2% of the people interviewed participate in Forest

    Resource Management projects, whilst 70.8% do not. This number does not

    show the extent and character of participation, which is analyzed in section

    4.3.4.

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    Source: Authors survey , 2009.

    4.3.2. Participation in forest management by sex

    Figure 4.3.2 below shows the participation in forest management projects

    disaggregated by sex; the majority of interviewees that participate in forest

    resource management are male (57% of participants).

    Source: Authors Survey, 2009.

    4.3.3. Project ActivitiesAs shown in Figure 4.3.3, from the respondents that have participated in forest

    activities, 42.9% participated in tree planting, 28.6% participated in workshops,

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    14.3% participated in afforestation projects and 14.3% in environmental

    education projects.

    Source: Authors Survey, 2009.

    4.3.4. Character of activities performed by participants.As shown in figure 4.3.4 , 57% of the respondents described their participation

    as manual labor,, 29% described their participation as attending project

    meetings and 14% participated in the financial management.

    Source: Authors Survey, 2009.

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    4.4. Capacity for effective participation

    The decentralized model of forest management that Ghana adopted relies

    largely on the ability of the Unit Committees to identify the community

    priorities (see Owusu, 2004). In this light, how projects are proposed is one of

    the variables that this study seeks to analyze. From the projects in which people

    participated, 42.9% were brought to the community by NGOs, 14.3% of

    projects were brought by the Forestry Commission and 14.3% by the District

    Assembly.

    It is important to highlight that, according to the district authorities, Unit

    Committees (UCs) have not been set up in the Yilo Krobo District. This would

    mean that district authorities have limited information on the communitys

    needs at the time of decision making as UCs, as we have seen in previous

    sections, are the structures put in place that take the decentralization process to

    the grass-root level.

    Another problem highlighted by the district authorities is the lack of competent

    personnel working for the District Assembly. This was identified as a

    contributory factor to the UCs ineffectiveness in mobilizing community

    participation. This situation is unlikely to change in the shorter term as the

    district authorities have not planned any major training for their personnel on

    participatory practices. District authorities cited persistent lack of resources for

    the implementation of the decentralization process as one of the main reasons

    they did not provide capacity-building in participatory methods for UCs staff.

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    Source: Authors Survey, 2009.

    4.5. Forest Resource Management and political decentralization

    It is not possible to separate participation in forest management from the

    broader context of political decentralization in which it happens. For this

    reason, this study evaluated the perception of political decentralization of the

    inhabitants of the villages selected. In particular, perceptions of measures that

    promote participation of women were analyzed.

    4.5.1. Perception of participation in decision makingWhen participants were asked about their ability to influence political decisions

    in their communities, 75% answered yes,, and no in 20.8% (See Table 4.5.1)

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    Table 4.5.1 - Perception of participation

    in decision making

    Do you influence

    decision-making? Frequency Percent

    Yes 18 75.0

    No 5 20.8N/A 1 4.2

    Total 24 100.0

    Source: Authors Survey, 2009.

    4.5.2. Perceptions of Community Meetings by SexAn important finding of this study arose when we cross-checked peoples

    perceptions of their political participation by asking them about their

    participation in community meetings, one of the key arenas of participation in

    rural towns. The results, cross tabulated by sex, were that women perceive

    their opinions in community meetings are not as valued as male participants.

    While 75% of respondents perceive that participate in decision making, only

    20% of women think their opinions are as valued as men s. This discrepancy

    may in some way be explained by the fact that participation in decision-making

    takes place largely through community meetings, in which mens opinions were

    felt to hold greater weight.

    Table 4.5.2 - Perception of Consideration Given to Opinions in

    Community Meetings by sex

    Do you perceive your opinion is

    considered in community

    meetings?Yes No

    Sex Male 80% 11%

    Female 20% 89%

    Total 100% 100%

    Source: Authors Survey, 2009.

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    It seems unlikely that womens opinion will be increasingly considered in the

    short term as 91% of the respondents were not aware of mechanisms for

    womens participation in the Yilo Krobo District, including district authorities

    and Forestry Commission officers.

    4.6. Forest Resource Management and the Boti Falls Reserve

    4.6.1. Brief description of the Forest ReserveAccording to the Districts Medium Term Development Plan 2006-2009, the

    Boti Falls Forest Reserve, serves as habitat for wildlife and as watershed for

    the river (Yilo Krobo,2006: 121). The ecological purpose of the reserve is

    complemented by the use of the site as a tourist attraction.

    The reserve is, according to the district authorities, a strictly reserved site. The

    area is demarcated with boundary pillars, walls around the entrance, and lines

    of trees along the back perimeter. Staff is paid by the local government to

    control these boundaries, enforce laws governing use and access, and to carry

    out management activities. According to the caretakers, there are also Forestry

    Commission wildlife officers patrolling the site, although they were not

    available to meet with the researcher at the time of surveying the reserve.

    As a consequence of access restrictions, villagers are not allowed to enter the

    reserve to enjoy the ecological benefits of the site unless they pay an entry fee

    to the district authorities; an entry fee that due to the level of poverty of the

    villages studied many villagers cannot pay.

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    It is important to point that even though the Boti Forest Reserve has been kept

    by the district authorities for conservation purposes, there are noticeable signs

    of human activity inside the reserve. For example, there ar