RUGU NATIONAL PARK, NIGERIA EVALUATION OF ITS BENEFITS USING PROTECTED AREA BENEFIT ASSESSMENT TOOL. (PA-BAT) IBRAHIM SADA RUFAI A thesis submitted in fulfilment of the requirements for the award of the degree of Master of Science (Planning-Resource and Environmental Management) FACULTY OF BUILT ENVIRONMENT UNIVERSITI TEKNOLOGI MALAYSIA NOVEMBER 2009 RUGU NATIONAL PARK, NIGERIA EVALUATION OF ITS BENEFITS USING PROTECTED AREA BENEFIT ASSESSMENT TOOL. (PA-BAT) IBRAHIM SADA RUFAI A thesis submitted in fulfilment of the requirements for the award of the degree of Master of Science (Planning-Resource and Environmental Management) FACULTY OF BUILT ENVIRONMENT UNIVERSITI TEKNOLOGI MALAYSIA NOVEMBER 2009 iii DEDICATION This project is dedicated to my late Grandfather Yarima Rufai and my family iv ACKNOWLEDGEMENTS I wish to express my profound gratitude to the Almighty Allah for his blessing and guidance throughout my master’s programme. My appreciation goes to my parents Alhaji Sada Rufai (Yariman Katsina), and Alhaji Bello Rufai, and also my Mum Hajiya Rabi whose support and affection can never be quantified. My sincere gratitude goes to my supervisors Dr Mohammad Rafee Majid for his kindly support and intellectual guidance and constructive criticisms throughout my studies. I am also grateful to my co-supervisor, Dr Foziah Johar for her support during the period under review. I am also indebted to all my lecturers and non-teaching staff that have contributed in the course of writing this project. I also want to acknowledge the financial support and moral advice i have received from numerous people like Dr Abba Sayyadi, Alhaji Murtala Safana, Late Dr Aminu Safana, Hon Ahmed Dayyabu, Alh Lawal Rufai, Alh Bello Abba (Ajiya), and Alh Isiyaku Rufai. My profound regards to friends especially Idris Medugu, Mukhtar, Dano, Engnr Samaila, Adamu Nguru, Abatcha, Abubakar Aminu Muazu, Mansir Aminu, Shahira Rosli, Sodangi, Alpano, Nima, Pooney and Evy. May i use this opportunity to extend my appreciation to my family members, Haj Hadiza, Alh Rabe Rufai, Haj Murja, Haj Umma, Haj Maryama, Haj Maijidda, Haj Maimuna, Haj Aisha, Haj Khadija, Haj hauwau, Haj Fadima, Haj Zainab, Haj Ashe and Adi. Finally my profound gratitude goes to Dr Abdu Aminu of the National Livestock Projects Division, and Alhaji Hassan Sharu, the Director Forestry in the Katsina state Ministry of Agriculture and Natural resources. v ABSTRACT Nowadays protected areas are increasingly expected to deliver so many benefits ranging from social, economic and environmental benefits in addition to conserving biodiversity. However, in most developing nations, local people who reside at the vicinity of the protected areas expect that it should also contribute to the social and economic well being of the people. Assurances that protected areas will supply these benefits are fundamental to attracting the support needed for their creation. Unless we comprehend and broadcast the full range of benefits from protected areas we risk not only reducing the possibility of new protected areas being but even of seeing some existing protected areas being degazetted and their values lost. This research evaluate the various contribution of Rugu National Park, Nigeria to the provision of various types of benefits and values ranging from economic, social and environmental benefits using the Protected Area Benefits Assessment Tool (PA-BAT). Personal interviews were conducted with 92 respondents in seven settlements within and around the Rugu National Park. The study shows that the park has contributed immensely in the provision of economic, social and environmental benefits to the local population, national population and the global community at large. Finally the project suggested a series of recommendations. vi ABSTRAK Pada masa kini, kawasan-kawasan perlindungan yang diwartakan sebagai dilindungi semakin diharapkan dapat memberikan banyak manfaat dari segi sosial, ekonomi dan alam sekitar di samping dapat melestarikan persekitaran biodiversiti. Namun, di kebanyakan negara-negara membangun, penduduk tempatan yang tinggal di sekitar kawasan yang dilindungi ini mengharapkan bahawa seharusnya ia dapat menyumbang kepada pembangunan sosial dan kesejahteraan ekonomi rakyat. Jaminan bahawa kawasan yang dilindungi ini akan turut menyediakan pelbagai manfaat sebagaimana yang diharapkan. adalah sangat penting untuk menarik sokongan yang diperlukan daripada penduduk bagi memelihara kepentingan kawasan tersebut. Sekiranya kita tidak memahami kepentingan wujudnya pelbagai manfaat daripada kawasan yang dilindungi ini, ia bukan sahaja mendatangkan risiko mengurangkan kemungkinan dalam mewujudkan kawasan perlindungan yang baru, malahan boleh menyebabkan kepupusan nilai-nilai keistimewaan di kawasan pemeliharaan sedia ada. Kajian ini menilai penglibatan Taman Negara Rugu, Nigeria dalam menyumbang kepada pemeliharaan kawasan perlindungan taman negara tersebut dari segi ekonomi, sosial dan persekitaran dengan menggunapakai analisis Protected Area Benefits Assessment Tool (PA-BAT). Satu kajiselidik telah dijalankan terhadap 92 responden di tujuh petempatan di dalam dan sekitar Taman Negara Rugu. Hasil kajian menunjukkan bahawa kawasan perlindungan taman negara ini telah memberikan sumbangan yang sangat besar dalam pembangunan ekonomi, sosial dan persekitaran kepada penduduk tempatan khususnya serta penduduk nasional dan komuniti global secara umumnya. Beberapa cadangan telah dikemukakan di akhir kajian ini. . vii TABLE OF CONTENTS CHAPTER 1 TITLE PAGE TITLE PAGE i DECLARATION ii DEDICATION iii ACKNOWLEDGEMENT iv ABSTRACT v ABSTRAK vi TABLE OF CONTENTS vii LIST OF TABLES xiii LIST OF FIGURES xv LIST OF ABBREVIATIONS xvii INTRODUCTION 1.1 BACKGROUND OF THE STUDY 1 1.2 STATEMENT OF RESEARCH PROBLEM 2 1.3 PURPOSE OF THE STUDY 4 1.4 OBJECTIVES OF THE STUDY 4 1.5 SCOPE OF THE STUDY 4 1.6 SIGNIFICANCE OF THE STUDY 5 viii 1.7 LIMITATION OF THE STUDY 2 3 5 THEORETICAL BACKGROUND 2.1 INTRODUCTION 6 2.2 PROTECTED AREAS: A REVIEW OF THE CONCEPT 6 2.2.1 DIFFERENT GOVERNANCE TYPES IN PA 8 2.2.2 CATEGORIES OF PROTECTED AREAS 8 2.3 PROTECTED AREAS IN NIGERIA 10 2.4 BENEFITS OF PROTECTED AREAS 13 METHODS OF EVALUATING BENEFITS OF PROTECTED AREAS 3.1 INTRODUCTION 21 3.2 CONTINGENT VALUATION METHOD (CVM) 21 3.3 HEDONIC PRICING METHOD (HPM) 22 3.4 PROTECTED AREA BENEFIT ASSESSMENT TOOL (PA-BAT) 23 3.4.1 HOW TO USE THE PA-BAT 24 3.4.1.1 WORKING WITH STAKEHOLDERS 24 3.4.1.2 HOW TO FILL THE QUESTIONNAIRE 25 3.4.1.3 CONDITION FOR THE USE OF PABAT 32 ix 4 THE STUDY AREA 4.1 INTRODUCTION 34 4.2 NIGERIA 34 4.3 KATSINA STATE 35 4.4 BACKGROUND OF RUGU NATIONAL PARK 36 4.4.1 HISTORY OF RUGU NATIONAL PARK 37 4.4.2 LOCATION AND SIZE OF RUGU NATIONAL PARK 37 4.4.3 VEGETATION AND CLIMATE 38 4.4.4 LAWS AND REGULATIONS OF RUGU PARK 42 4.4.4.1 OFFENCES AND LEGAL PROCEDURE 44 4.4.5 ADMINISTRATION 44 4.4.5.1 RANGE MANAGEMENT SCHEME 46 4.4.5.2 DIARY SCHEME 47 4.4.5.3 CLINIC SECTION (VETRINARY) 47 4.4.5.4 FACILITIES UTILITIES AND SERVICES 47 4.4.5.5 STAFFING 48 x 4.4.5.6 HOUSING 4.5 SETTLEMENT WITHIN AND AROUND THE PROTECTED AREA 5 49 49 METHODOLOGY 5.1 INTRODUCTION 52 5.2 BENEFIT EVALUATION 52 5.2.1 EVALUATION 52 5.2.2 BENEFITS 53 5.3 SOURCES OF DATA 5.3.1 PRIMARY SOURCE 53 53 5.3.1.1 QUESTIONNAIRE 54 5.3.1.2 FIELD OBSERVATION 55 5.3.1.3 INTERVIEW 55 5.3.2 SECONDARY SOURCE 5.4 SAMPLING 56 57 5.4.1 RESPONDENTS 57 5.4.2 SETTLEMENTS WITHIN THE PROTECTED AREA 58 5.4.3 SETTLEMENTS AROUND THE PROTECETD AREA 59 xi 6 FINDINGS AND DISCUSSIONS 6.1 INTRODUCTION 60 6.2 VALUES AND BENEFITS 60 6.2.1 ECONOMIC BENEFITS 61 6.2.1.1 GRAZING AND FODDER 61 6.2.1.2 FISHING 64 6.2.1.3 TIMBER 66 6.2.1.4 JOB OPPORTUNITY 67 6.2.1.5 NON COMMERCIAL WATER USE 69 6.2.1.6 MEDICINAL RESOURCES 69 6.2.1.7 HUNTING 71 6.2.1.8 RECREATION AND TOURISM 72 6.2.1.9 COLLECTION OF NON WOOD PRODUCTS 73 6.2.2 SOCIAL BENEFITS 6.2.2.1 KNOWLEDGE, RESEARCH AND EDUCATION 6.2.3 ENVIRONMENTAL BENEFITS 74 74 74 6.2.3.1 CARBON AND SOIL STABILISATION 75 6.2.3.2 WATER QUALITY AND QUANTITY 76 xii 6.3 SUMMARY 7 76 CONCLUSION AND RECOMMENDATION 7.1 INTRODUCTION 78 7.2 CONCLUSION 78 7.3 RECCOMENDATION 79 REFERENCES 81 APPENDIX A 84 APPENDIX B 98 APPENDIX C 111 xiii LIST OF TABLES TABLE NO TITLE PAGE 2.1 Distribution of National Parks by States 11 2.2 Distribution of Strict Nature Reserve by States 12 2.3 Distribution of Game Reserves by States 12 4.1 Dominant Species of Plants around the PA 39 4.2 Dams and Ponds Distribution in the PA 40 4.3 Distribution of Settlements and Population in the PA 50 4.4 Distribution of Settlements and Population Surrounding the PA 51 5.1 Indigenous Traditional People Living in the PA 58 5.2 Non Indigenous People Living in the PA 59 5.3 Indigenous People Living Around the PA 59 5.4 Different Tiers of Government Interviewed 59 6.1 Percentage of Grazing Beneficiaries and non Beneficiaries 63 6.2 Major Species of Fish Caught in the PA 64 6.3 Percentage of Fishing Beneficiaries and non Beneficiaries 66 6.4 Percentage of Timber Beneficiaries and non Beneficiaries 67 6.5 Percentage of Job Beneficiaries and non Beneficiaries 68 xiv 6.6 Percentage of Water use Beneficiaries and non Beneficiaries 69 6.7 Percentage of Medicinal Beneficiaries and non Beneficiaries 70 6.8 Percentage of Hunting Beneficiaries and non Beneficiaries 71 6.9 Percentage of Recreation Beneficiaries and non Beneficiaries 72 6.10 Percentage of Non-Wood Beneficiaries and non Beneficiaries 73 xv LIST OF FIGURES FIGURE NO TITLE PAGE 3.1 Background Information Data Sheet. 25 3.2 Data Sheet. 28 4.1 Map of Africa showing Nigeria. 35 4.2 Map of Nigeria showing Katsina state. 36 4.3 Rugu National Park 38 4.4 Deciduous Plants within the Park. 39 4.5 Kadaura Dam. 41 4.6 Rainfall Data for the Park. 41 4.7 A Wild Camel Feeding From the Pastures. 42 5.1 Sample Questionnaire. 54 5.2 The Researcher with a Respondent. 57 5.3 Indigenous People Living in the Protected Area. 58 6.1 Herds of cattle returning to base after grazing 62 xvi 6.2 Proportion of Protected Area in Supplying grazing Benefit 63 6.3 Some of the Types of Fish Caught in the PA 64 6.4 Map of Park Showing Location of Settlements 65 6.5 A Local Resident Collecting Fuel Wood from the Park 67 6.6 Some Indigenous People Employed as Forest Officers 68 6.7 Herbs Collectors 70 6.8 The Author and a Hunter 71 6.9 The Researcher Front Posing With a Non Wood Collector 73 6.10 Environmental Benefits Chart 75 6.11 Economic Benefits from the PA 77 xvii LIST OF ABBREVIATIONS CVM - Contingent Valuation Method DFID - Department for International Development DVO - Divisional Veterinary Officer FAO - Food and Agriculture Organisation FMANR - Federal Ministry of Agriculture and Natural Resources FUS - Facilities Utilities Services HA - Hectares HPM - Hedonic Pricing Method IUCN - International Union for Conservation of Nature KTMA - Katsina State Ministry of Agriculture NC - Nature Conservancy NGO - Non-Governmental Organisation NPC - National Population Commission NRCC - Natural Resource Conservative Council PA - Protected Area PABAT - Protected Area Benefit Assessment Tool xviii RRMC - Rugu Range Management Centre USAID - United State Agency for International Development USD - United States Dollar UN - United Nations UNEP - United Nations Environment Programme WDPA - World Database on Protected Area WWF - World Wide 1 CHAPTER 1 INTRODUCTION 1.1 Background of the study International commitments to the development of networks of protected areas dates from 1972, when the Stockholm declaration from the United Nations Conference on the Human Environment endorsed the protection of all major ecosystems types as a fundamental requirement of national conservation programmes. Since then, the protection of ecosystems has become a core principle of conservation biology, supported by key United Nations resolutions including the World charter for Nature 1982, Rio Declaration at the Earth Summit 1992, and the Johannesburg Declaration 2002 (Marrie, 2004). Protected area is defined as an area of land or sea especially dedicated to the protection and maintenance of biological diversity and of natural and associated cultural resources, managed through legal or other effective means (UNEP, 2004). A protected area, as defined by the International Union for Conservation of Nature "A clearly defined geographical space, recognised, dedicated and managed, through legal or other effective means, to achieve the long-term conservation of nature with associated ecosystem services and cultural values” (I U C N, 1998). There are over 108,000 protected areas in the world with more added daily, representing a total area of 30.43 million km2 (11.75 million square miles), or over 12 percent of the worlds land surface area greater than the entire land mass of Africa ( IUCN, 1998). 2 In Nigeria, regional game laws were enacted for the protection of protected areas. In 1982, the Federal Natural Resource conservative Council (NRCC) was created to provide coordination for the conservation of natural resources, develop policies, and to take direct measures to protect species and sites and also to provide funds for conservation and research work. The Federal Department of Forestry in the Federal Ministry of Agriculture and Natural Resources is responsible for Protected Areas development and extension. There are over 966 protected areas in Nigeria (WDPA, 2005). 1.2 Statement of Research Problem Under funding is a major problem facing protected areas, protected areas are only really protected if they receive funding which allows them to achieve their objectives. While the U.S. spends $2 billion on protected areas, most of the developing countries spend less than $500,000. In a survey of 98 national parks, 73% reported that they were understaffed and many protected areas don't have enough funds for equipment and supplies (John, 1992). Protected areas are also extremely small compared with the original extent of the type of habitat being preserved. Over the last decade, the challenge of reducing levels of global poverty has rocketed up in the priorities of politicians, development organisations, with good cause: despite the optimism of economists in the 1980s and 1990s, differences between the rich and the poor have in some respects continued to increase. In Nigeria extreme poverty has actually deepened. As of now, around 50 million of the population are estimated to live in abject poverty, living on less than one US dollar in a day (UNEP, 2004). Moreover, protected areas can play a vital role in poverty reduction. A survey of protected area managers at the 5th World Parks Congress in 2003 found that 78 per cent believed that economic benefits of protected areas benefits were significant to the broader community (Nigel et al, 2008). As stores of 3 environmental assets, protected areas can potentially play an enormous role in reducing poverty levels. Protected Areas are often mistakenly undervalued. Few people realize the range of benefits derived from Protected Areas habitats, food such as fish, and, medicinal plants, peat for fuel and gardens, poles for building materials, and grasses and reeds for making mats and baskets and thatching houses. These complex habitats act as giant sponges, absorbing rainfall and slowly releasing it over time. Protected Areas are like highly efficient sewage treatment works, absorbing chemicals, filtering pollutants and sediments, breaking down suspended solids and neutralizing harmful bacteria (World Wildlife Fund, 2005). Yet many of the world's Protected Areas have already been destroyed in the past 100 years alone (World Wildlife Fund, 2005). Conversion of swamps, marshes, lakes and floodplains for large-scale irrigated agriculture, ill-planned housing and industrial schemes, toxic pollutants from industrial waste and agricultural run-off high in nitrogen and phosphorous pose some of the main threats to Protected Areas. Among threatened species are several river dolphins, manatees, fish, amphibians, birds’ plants and animals. (World Wildlife Fund, 2005). Rugu National Park reflect a variety of habitats with fascinating landscape, the Protected Area support an incredibly high species biodiversity with a high level of endemism. It has been a major source of attraction to visitors from all over the world. In view of these problems Protected Area Benefit Assessment Tool (PA-BAT) can be regarded as a powerful tool used in assessing the benefits of Rugu Protected Areas Protected Area Benefit Assessment Tool (PA-BAT) is a powerful tool used in assessing the benefits of Protected Areas, it is designed to fill an important gap in the toolbox of protected area agencies and conservation institutions by providing a methodology to collate and build information about the overall benefit from protected areas (Nigel et al, 2008). Therefore the (PA-BAT) will be used in evaluating and assessing the benefits of Rugu national park situated in Katsina State 4 in Nigeria to the people and more importantly in assessing how the Rugu National Park help in the reduction of poverty within the study area. Benefits here refers to a resource that is being used to provide direct gains which could be in terms of money earned, or subsistence resources collected or less tangible gains such as spiritual peace or mental well-being to stakeholders. The resource of the protected area becomes a benefit when they are successfully used to provide such gains (Sue and Nigel, 2008). 1.3 Aim The aim of this project is to evaluate the benefits of the Rugu national park in Katsina state of Nigeria using Protected Area Benefit Assessment Tool. (PA-BAT) 1.4 OBJECTIVES The objectives of this project are as follows. 1. To study the concept of protected area and Protected Area Benefit Assessment Tool. 2. To evaluate the benefits of Rugu National Park, using Protected Area Benefit Assessment Tool. 3. To proffer possible recommendations towards improving the sustainable use of the Rugu National Park. 1.5 SCOPE OF THE STUDY The study is going to focus only on the evaluation of the economic, social and environmental benefits provided by Rugu National Park using Protected Area Benefit Assessment Tool (PA-BAT). They study is also going to cover the whole 5 National Park and some selected settlements and sampled stakeholders directly involved in one way or the other with the Park. 1.6 SIGNIFICANCE OF THE STUDY Recent research has shown that well managed protected area can potentially be successful in achieving a wide range of objectives, from conserving endangered species to delivering economic, environmental, and social benefits that contribute to the well being of local people which will subsequently reduce poverty (Nigel et al, 2008). So this study will explore in details the types of benefits offered by Rugu National Park and their potential contribution to poverty reduction. 1.7 LIMITATIONS OF THE STUDY This project will be restricted to evaluating the economic and environmental benefits and values in Rugu National Park only. Due to time constraint, not all the settlements will be covered in the protected area, household interview will only be conducted within seven (7) settlements in the protected area. 6 CHAPTER 2 THEORETICAL BACKGROUND 1.1 Introduction This chapter provides an impression on the literature regarding protected areas, their governance types, benefits and the different categories of protected areas, it also discuss the different types of protected area in Nigeria. This chapter goes a long way in providing deeper knowledge and understanding of the research. 1.2 Protected Areas: A Review of the Concept A protected area, as defined by the International Union for Conservation of Nature (IUCN). "is a clearly defined geographical space, recognised, dedicated and managed, through legal or other effective means, to achieve the long-term conservation of nature with associated ecosystem services and cultural values” (IUCN, 1998). Protected area can also be defined as an area of land or sea especially dedicated to the protection and maintenance of biological diversity and of natural and associated cultural resource, managed through legal or other effective means (UNEP, 2004). Protected areas are locations which receive protection because of their environmental, cultural or similar value. The term protected area includes marine 7 protected area, which refers to protected areas whose boundaries include some area of ocean. A large number of kinds of protected area exist which vary by level of protection and by the enabling laws of each country or rules of international organization. Examples include parks, reserves and wildlife sanctuaries. There are over 108,000 protected areas in the world with more added daily, representing a total area of 30.43 million km2 (11.75 million square miles), or over 12 percent of the worlds land surface area greater than the entire land mass of Africa ( IUCN, 2002). Protected areas arise through recognition of the benefits provided by natural ecosystems, or in some cases long established manipulated ecosystems, which cannot be replicated in intensively managed landscapes. Human societies have been protecting areas of land and water from long before the start of recorded history to protect grazing pasture (for example the Hima system in much of the Middle East), maintain timber supplies, stop avalanches or landslides, provide game for hunting, or to allow secure places for fish to breed. People have also protected land and water for less tangible reasons: because places were considered sacred or simply because they were recognised as aesthetically beautiful and worthy of preservation. The modern concept of a ‘protected area’ known variously as national park, wilderness area, game reserve etc developed in the last years of the nineteenth century as a response to the rapid changes brought to lands in former European colonies and concern at the loss of ‘wilderness’. Here protection was sometimes already driven by a desire to stop species disappearing, as is the case with some of the colonially established parks in India but also because the colonisers were trying to retain remnants of the original landscape (Nigel et al, 2008). They often incorrectly assumed this to be in an untouched state, although in most cases ecology had already been influenced by human activity for millennia. A handful of national parks in Africa, Asia and North America heralded a flood of protection that spread to Europe and Latin America and gathered momentum throughout the twentieth century, and the number of protected areas continues to increase in the 21st century. Most of today’s protected areas have been officially gazetted in the last fifty years many even more recently and the science and practice of management are both still at a relatively early stage(Nigel, 2008). 8 2.2.1 Different Governance Types in Protected Areas Governance of Protected Areas has to do with power, relationships and accountability, and reflects what a society sees as fair, or is prepared to accept as such, in terms of authority and responsibility. In a protected area context, governance affects the achievement of management objectives, the sharing of costs and benefits and the generation and sustenance of community, political and financial support. Since the World Congress on Protected Areas of 2003, a first cut at understanding governance is made on the basis of who holds relevant authority and responsibility and can be held accountable. Works by (Borrini, 2003) has shown that there are four main types of Protected Area governance. a. Government managed protected areas. Federal or national ministry or agency in charge Local / municipal ministry or agency in charge governmentdelegated management (e.g. to a Nongovernmental organisation). b. Co-managed protected areas. Transboundary management, collaborative management, joint management. c. Community conserved protected areas. Declared protected areas run by indigenous people and local community. d. Private protected areas. Declared and run by individual land owners. 2.2.2 Categories of Protected Areas Within the broad spectrum of the importance of the full range of Protected Areas from those that protect the world’s great natural areas to those that contain modified landscapes of outstanding scenic and cultural importance, that many names and categories have been applied to protected areas. Categories of Protected Areas are defined by the objectives of management and not by the title of the area. So generally there are six categories of protected areas (Lucas, 1994). 9 i. Strict nature reserve/wilderness area: area of land or sea possessing some outstanding or representative ecosystems, geological or physiological features and species, available primarily for scientific research and environmental monitoring. Ownership and control should be by the national or other level of government, acting through a professionally qualified agency, university or institution which has an established research or conservation function, or by owners working in cooperation with any of the foregoing government or private institutions. ii. National park: protected area managed mainly for ecosystem protection and recreation, they are natural and sea designated to protect the ecological integrity of one or more ecosystems for present and future generations, exclude exploitation inimical to the purpose of designation of the area, and to provide a foundation for spiritual, scientific, recreational and visitor opportunities, all of which must be environmentally and culturally compatible. Ownership and management is normally by the highest authority of the nation having control over it. iii. Natural Monument: protected area managed mainly for conservation of specific natural features. They are areas containing one, or more, specific natural or natural/cultural feature which is of outstanding or unique value because of its inherent shortage, representative or aesthetic qualities or cultural significance. iv. Habitat/Species Management Area: protected area managed mainly for conservation through management intervention. These are areas of land or sea subject to active intervention for management purposes so as to ensure the maintenance of habitats and to meet the requirements of specific species. Administration and ownership should be by the national government or, with appropriate safeguards and controls, by another level of government, nonprofit trust, corporation, private group or individuals. v. Protected Landscape/Seascape: protected area managed mainly for landscape/seascape protection and recreation. They are areas of land, with coast and sea, where the interaction of people and nature over time has produced an area of distinct character with significant aesthetic, ecological and cultural value, and often with high biological diversity. The area may be owned by a public authority, but is more likely to comprise a mixture of 10 private and public ownerships operating a variety of management regime. These regimes should be subject to a degree of planning or other control and supported, where appropriate, by public funding and other incentives, to ensure that the quality of the landscape/seascape and the relevant local customs and beliefs are maintained in the long term. vi. Managed Resource Protected Area: Protected area managed mainly for the sustainable use of natural ecosystems. Area containing predominantly unmodified natural systems, managed to ensure long term protection and maintenance of biological diversity, while providing at the same time a sustainable flow of natural products and services to meet community needs. Ownership may be by the national or other level of government, the community, private individuals, or a combination of these. 1.3 Protected Areas in Nigeria The protection of wildlife began with the creation of Nigeria, soon after the amalgamation of the northern and southern parts of the country in 1914. Regional game laws were enacted, initially by eastern Nigeria in 1916 and later by the western and northern regions in 1928 and 1963, respectively. In the late 1980s, the Federal Natural Resource Conservation Council (NRCC) was created. This Council is chaired by the President with representatives from a number of Ministries and from the Nigerian Conservation Foundation. This Council provides coordination for the conservation of natural resources, develops policies, can take direct measures to secure the status of species and sites, monitors conservation activities within the forestry and wildlife sectors, and provides funds for conservation and research work. At the national level, the mandate for wildlife conservation and protected areas management is the responsibility of the Federal Department of Forestry in the Ministry of Agriculture, Water Resources and Rural Development. Within this Department, is the Division of Wildlife and Conservation, which is responsible for 11 wildlife development and extension, and the enforcement of international wildlife conventions (UNEP, 2004). The three categories of protected areas in Nigeria recognized within the wildlife sector are national park, strict nature reserve, and all game reserve of which were formerly reserved forest. There is also one wetland of international importance (Ramsar) which is Nguru Wetland. National parks are Protected Areas managed mainly for ecosystem protection and recreation, they are natural and sea designated to protect the ecological integrity of one or more ecosystems. The distribution of national parks in Nigeria is evenly distributed across the sates as shown in the table below. Table 2.1: Distribution of National Parks by States States Name of Protected Area Yobe Baturiya Borno Chad-basin Cross River Cross-River Taraba Gashaka Yobe Gujba Niger Kainji Benue Kamuku Sokoto Kogo Kaduna Kuyambana Oyo Old Oyo Katsina Rugu Borno Sambisa Bauchi Yankari Source: WDPA (2005) 12 Strict Nature Reserve area of land or sea possessing some outstanding ecosystems, geological or physiological features and species, available primarily for scientific research and environmental monitoring. There distribution in Nigeria are shown below in table 2.2 Table 2.2: Distribution of Strict Nature Reserve by States States Name of Protected Area Yobe Bam Ngelzarma Lagos Lekki Enugu Milliken Hill Kaduna Ribako Edo Urhonigbe Source: WDPA (2005). Game Reserve is an area of land set aside for maintenance of wildlife for tourism or hunting purposes. Their distribution in Nigeria is also shown below on table 2.3 Table 2.3: Distribution of Game Reserves by States. States Name of Protected Area Edo Akpaka Ogun Alawa Anambra Anambra Edo Ankwe River Yobe Baturiya Wetlands Niger Dagida Abia Dagona Delta Ebbe Edo Gilli-Gilli Taraba Ibi Ondo Ifon 13 Lagos Iri Taraba Kambari Delta Kwale Bauchi Lame-Burra Yobe Margadu-Kabak Wetlands Ogun Meko Yobe Kogi Nguru Wetlands Num River Edo Ohosu Edo Ologbo Bayelsa Abia Taylor Creek Udi Plateau Wase Source: WDPA (2005). 1.4 Benefits of Protected Areas Protected areas are one of the cornerstones of conservation, safeguarding essential habitats. They preserve natural resources essential to people’s social and economic wellbeing such as drinking water, fisheries and forests. Indeed, it is hard to imagine a healthy future for our planet without the existence of protected areas. Clean water, clean air, access to food sources, buffers of weather events, cultural and spiritual values, and raw materials for consumers, are some of the ecosystem services that ensure the well-being of humanity, especially the poor who most directly rely on them. Degradation of land and seascapes triggers losses in biological diversity and ecosystem services, ultimately diminishing not only quality of life, but cultural and material wealth as well. Well managed protected areas are a proven mechanism in the conservation and maintenance of healthy ecosystems and the services they provide. The immense value of protected areas is such that they should be cherished, green emeralds of the terrestrial realm and blue sapphires of the oceans. Indeed, they 14 are of greater significance than any jewel. Without healthy ecosystems, lasting and sustained social and economic development is impossible (Ahmed, 2008). The numerous benefits of protected areas include. i. Knowledge Protected areas provide resources for research, including utilisation of traditional knowledge; formal and informal education; and prime sites for bioprospecting and for the collection of genetic materials. Protected areas are often the first choice for research by ecologists, because many are in a more-or-less natural state and there is also a reasonable guarantee that populations or habitats will remain undisturbed. Some protected areas have been established primarily as research sites and regions or countries have also dedicated certain reserves specifically to form networks for long-term research. Protected areas are also useful in providing baseline data for climate change studies. Some protected areas do provide conditions in which traditional knowledge survives and this can sometimes have economic or other material benefits, for example if local peoples are able to capitalise on traditional medicinal plants. Many protected areas are also primary sites for education. Urban reserves and those near centres of population are particularly important although an increasing number of schools and colleges also run trips to natural areas further away. Many protected areas in developing countries report that while in the past visits were mainly from outsiders, today an increasing number of visits are coming from schools within the country. In Madagascar, for example, in the recent past 90 per cent of visits to national parks came from foreign tourists whereas now most come from local Malagasy people, including many school students (Nigel et al, 2008). 15 ii. A Safe Haven for Natural Diversity National parks and protected areas provide refuge for plants and animals whose habitats are threatened elsewhere. For example La sepultara biosphere in southern Mexico is one of last places where cycads are found, a rare and ancient tropical flowering plant estimated to be at least 2,500 years old. Another example is the Arnavons marine protected areas in the South Pacific protects nesting sites for the endangered hawksbill turtle. By protecting key habitats, threatened species can be brought back from the brink. For example, preserving sections of the forests of Central America has helped foster the return of the magnificent harpy eagle (NC, 2009). iii. Food Many of the world’s poorest people rely on species and products from traditional cultural landscapes for a major part of their diet, particularly during shortages and political unrest. Animal food includes bush meat, fish and shellfish, bird and turtle eggs, invertebrates, honey and flavouring products. Wildlife is an important food for 150 million people (DFID 2006). Bush meat makes up more than a fifth of animal protein in rural diets in over 60 countries rising to 80 per cent in areas such as rural Kenya (Anon, 2006). Even if species have been hunted to low levels, as in much of West Africa, wild meat is popular 90 per cent of people in Ghana say they will eat bush meat if it is available. Decline in bush meat is a factor in lower dietary quality for instance the charity Save the Children cites evidence that people in rural Malawi eat substantial numbers of mice in the absence of any larger animals. A huge variety of plants are eaten, as fruit, nuts, leaves, roots and tubers. FAO estimates that 18,000-25,000 wild plant species are used as food in the tropics, collected from all ecosystems. In India, 50 million people are estimated to be directly dependent on forests for their subsistence. Traditional agriculture also remains 16 important and a third of the world’s farmers (450 million people) relies wholly on manual labour and do not use either commercial crop varieties or agrochemicals (Nigel et al, 2008). iv. Source of Drinking Water A recent study has found that more than a third of the world’s largest cities including New York, Los Angeles and Beijing, rely on the healthy watershed assured by protected forests for drinking water. The Condor Biosphere Reserve in Ecuador is the source of water for more than 1.8 million people living Quito, the country’s capital. Each month businesses and residents use about 4.5 billion gallons of water from the rivers that flow from the reserve (NC, 2009). v. Supporting Economies and Contributing to Poverty Reduction Protected areas can have significant economic benefits for both the communities which live within their boundaries and the wider society. Tourism fuelled by Bolivia’s beautiful national parks has generated roughly USD 200 million in the last decade, of which around USD14 million annually has gone to communities living within protected areas who work in the sector. By protecting fish spawning areas, marine protected areas can help replenish fish stocks and support fisheries. Fishermen living near Komodo National Park, for example, have seen catches increase since the protection of fish spawning areas. When forestry is managed sustainably within parks, such as the Great Bear rainforest in Canada, it can make an important contribution to the local economy (NC, 2009). vi. Combating Climate Change and its Impacts Every year deforestation releases millions of tons of carbon dioxide into the atmosphere. By protecting forests we can help stop this. In Brazil’s Atlantic Forest, 17 scientists calculate that preserving 17,000 acres of forest in protected areas can offset the emissions of roughly 750,000 cars, improving air quality and reducing global warming. Protecting key areas can also help mitigate the impact of climate change. In Palau we are helping to identify and protect areas of corals which are proving to be more resilient to bleaching caused by rising sea temperatures (NC, 2009). vii. An Area for Recreation and Spiritual Renewal The most visited national park in the U.S, Great Smoky Mountains, receives between eight and ten million visitors annually. Whether hiking, camping, fishing or scuba diving, protected areas can conserve places where people can relax, reconnect with nature and enjoy the natural splendour of our planet. Protected areas can also conserve areas of great cultural and spiritual significance. The Meilixueshan Conservation Area near the border with Tibet, for example, includes a mountain of great spiritual importance to Tibetan Buddhism (UN, 2003). viii. Cultural and Historical Values Many protected areas in some countries also have significant historical, cultural and spiritual values for local communities, nations or the global community as a whole. Historical values include important buildings, artefacts and archaeological remains, the continuation of traditional human cultures within a protected area, and land management systems that are themselves of important historical or cultural value. Some protected areas, such as the Ecosystem and Relict Cultural Landscapof Lopé-Okanda, Gabon, which is recognised as a World Heritage Site, have been designated at least in part because of their historical or cultural interest. Spiritual values are more complex, but can include built places of worship or much more commonly sacred natural sites (sacred groves, mountains, waterfalls etc) or pilgrimage routes that pass through protected areas. Although most commonly associated with indigenous peoples, sacred sites related to virtually all the world’s major faiths exist within protected areas and thus have an influence on 18 management. In some cases, their presence can also attract tourists, pilgrims and other visitors and thus provide direct economic benefits to local communities through ecotourism, guiding or provision of accommodation and other services. Examples might include guided walks to bushmen rock painting in the Drakensberg National Park in South Africa, tourist venues based around historical slate mining sites in the Snowdonia National Park, Wales, UK, and businesses linked around Mount Fuji, an extremely important sacred site in Japan (Bancet, 2007). The existence of people living traditional lifestyles within protected areas can also be part of the attraction for visiting and can provide local communities with cash opportunities through sale of crafts or home stay, such as in the case of the Maasai in Ngorongoro Crater in Tanzania. Some sacred sites also make money for the local community, particularly if many pilgrims visit. The millions of pilgrims visiting a sacred shrine in Periyar National Park in India all contribute to the Periyar Foundation which supports conservation and livelihood work gaining around USD 200,000 a year, in addition many more people have jobs relating to the pilgrimage. Income from these activities is probably lower than that made previously from smuggling and poaching, but overall quality of life is thought to have improved because villagers are no longer harassed by police or middlemen (Nigel et al, 2008). ix. Health Perhaps the broadest category of all; protected areas help to promote health in a wide variety of ways, ranging from the protection of plants and animals of medical use through to the health enhancing benefits of the protected area itself. Medicines from wild plants and animals play a key role in both the development of many commercially available pharmaceuticals and also directly through the provision of traditional herbal medicines, which are still the primary medicines for an estimated 80 per cent of the world’s people. One estimate suggests that up to 28 per cent of plant species have been used medically. Medicines based on wild species are also a significant source of revenue. It is estimated that global sales of pharmaceuticals based on materials of natural origin are worth USD75 billion a year and more directly the annual reported international trade in medicinal aromatic plants had a 19 value in excess of USD 1 billion per year during the 1990s. Collection of wild medicinal species is often carried out by the poorest members of society and can be a particularly important source of income for women; for example 70 per cent of medicinal plants on the Vietnamese market originate in the uplands and are a key money-making option for poor rural women (UNEP, 2004). x. Tourism Tourism, wildlife management and local communities can co-exist both within and close to protected areas if carefully planned. In Jordan, the Dana Reserve raised USD 380,000 in tourism receipts and sales between 1995 and 1998, creating 55 jobs and increased financial benefits for over 160 people. In Costa Rica, research as long ago as 1991 found that foreign exchange generated by tourism connected with protected areas generated more than USD 330 million for an outlay of about USD 12 million on management. Park generated tourism is the second largest industry in the country. In 1999, local guides from Tortuguero village in Costa Rica led 72 per cent of all night walks to see turtles nesting. The price of a tour ranges between USD 5 and USD 25, and the average visitor spends more than USD 255. The area has grossed nearly USD 7 million from the turtle tourism industry. In Apo Island, the Philippines, tourism is estimated to be worth around USD 500 per hectare of reef and is mixed in with community-managed fisheries agreements including controls on when and how to catch fish. In 2003, fees for watching whale sharks generated more than (USD 28,715) for the Donsol community in Sorsogon, also in the Philippines. Gains are not confined to the poorest countries; for example it is calculated that the presence of nesting ospreys (Pandionhaliaetus) in Scotland bring an addition USD 7 million per year into the area as a result of nature tourism. In some cases sport hunting can co-exist with conservation within protected areas: hunters are prepared to pay high fees and sport hunting organisations can afford to pay guards to maintain stable populations of key species. For example, 80 per cent of the protected areas in Tanzania allow controlled sport hunting, including 43 Game Control Areas and 23 Game Reserves, which together make up 22 per cent of the country’s mainland. Botswana has similar areas available for hunters (Nigel et al, 2008). 20 xi. Source of Materials Most of the people who rely on natural systems for food will also be collecting other materials such as building materials, fuel, adhesives and so on. Many of these are often lumped together under the term non timber forest products although similar products are found in other biomes. In developing nations, some 2.4 billion people more than a third of the world population rely on wood and other biomass fuels for cooking and heating and this is also increasingly seen as a source of income. In Kenya, the charcoal economy is estimated at about 23 billion Kenyan shillings per year (over USD 350 million). An increasing number of protected areas allow access to timber, non-timber forest products and other material so long as the species involved are not threatened by the process, indeed protected areas are being established in joint ventures between local communities and conservation bodies with sustainable off take as an underlying principle. For example the Kayan Mentarang National Park in Indonesian Borneo is home to 16,000 Dayak people who retain rights to collect rattan (Calamus spp.), sang (Licuala spp.) and hardwoods for construction, under guidelines that are controlled by customary law (Nigel et al, 2008). 21 CHAPTER 3 METHODS OF EVALUATING BENEFITS OF PROTECTED AREAS 3.1 Introduction This chapter is going to look at the various means and ways available for evaluating the benefits of protected areas and also to discuss in details on (PA-BAT) and also to explain how it is used. There are so many ways of evaluating the benefits of Protected Areas, which will be discussed below. 3.2 Contingent Valuation Method (CVM) The contingent valuation method (CVM) is used to assess economic values for all kinds of ecosystems and environmental services including protected areas. It can also be used to estimate both use and non use values, and it is the most widely used method for estimating non use values. The contingent valuation method involves asking people in a survey how much they would be willing to pay for specific environmental services. In some cases people are asked for the amount of compensation they would be willing to accept to give up specific environmental 22 services. Contingent valuation is one of the only ways to assign monetary to non use values of the environment, these are values that do not involve market purchases and may not involve direct participation. These values are sometimes referred to as passive use. They include everything from the basic life support functions associated with ecosystem health or biodiversity, to the enjoyment of a scenic vista or a wilderness experience or the right to bequest those options to your grandchildren. This evaluation method has been successfully used in some developing countries for evaluating the benefits of protected areas, like in Brazil; it has been used to evaluate the benefits of Morro do Diabo state park in Sao Paulo (Cristina et al, 2008). 3.3 Hedonic Pricing Method (HPM) The Hedonic Pricing Method is used to estimate values for ecosystems or environmental services that directly affect market prices. It is most commonly applied to variations in housing prices that reflect the value of local environmental attributes. It can be used to estimate economic benefits associated with. 1. Environmental quality, including air pollution, water or noise pollution. 2. Environmental amenities, such as aesthetic views or proximity to recreational sites. The basic premise of the hedonic pricing method is that price of a marketed good is related to its characteristics, or the services it provides. The Hedonic pricing method is relatively straightforward and uncontroversial to apply (Lisa, 1997). 23 3.4 Protected Area benefit Assessment Tool (PA-BAT) The Protected Area Benefit Assessment Tool (PA-BAT) is a tool that can be used to identify the some of the wider benefits that protected areas provide to human well being. It is designed to fill an important gap in the toolbox of protected area agencies and conservation institutions, by providing a methodology to collate and build information about the overall benefits from protected areas (Nigel et al, 2008). All the three above mentioned methods are very effective tools in evaluating the benefits of any protected area. But this study has chosen the Protected Area Benefit Assessment Tool (PA-BAT) in assessing the benefits of Rugu National Park. The protected area benefit assessment tool (PA-BAT) is a new tool developed and tested by World Wide Fund for Nature (WWF). The tool was developed first as a means of collecting information for safety net, protected areas and poverty reduction, the fourth volume in the arguments for protection series, looking at links between protected areas and poverty reduction. With the tool it can be used to identify the some of the wider benefits that protected areas provide to human well being and thus their contribution to poverty reduction. The tool aims to help collate information on the full range and potential benefits of protected areas. It is a contributory methodology that will be of wider use to the protected areas community. Although developed primarily for use in protected areas, protected area benefit assessment tool could have wider application, for example in assessing wider benefits of forest management units, agricultural landscapes or areas set aside for recreation, protected area benefit assessment tool can be useful for anyone interested in finding out about the range of benefits that protected areas provide. The (PABAT) uses a standard questionnaire to collate information from respondents. Protected area managers and protected area agencies are increasingly being asked to provide details of the wider social and environmental benefits of the lands and waters under their management. This tool provides a methodology for collating such information for individual protected areas. 24 3.4.1 How to Use the Protected Area benefit Assessment Tool The tool is a questionnaire which consists of a series of questions for the purpose of gathering information from the respondents. So there is the need to understand the kind of people you will work with in using the tool. 3.4.1.1 Working with Stakeholders First and famous is working with stakeholders. In an ideal situation, a broad range of stakeholders should be involved in carrying out the assessment, for example in a workshop involving park staff, local communities and others with an interest in the site. In this case there may be competing views about various benefits and it is possible that alternative views may have to be represented, for instance positive benefits for some stakeholders may be matched by negative impacts on others which will need to be recorded in the comments section of the report. So in the course of the research, the author involved some stakeholders in collating information by interviewing them, some of the stakeholders interviewed include the local communities and the staff of the national park. 25 3.4.2.2 How to Fill the Questionnaire The protected area benefit assessment tool has two sections, both of which should be filled in for each protected area assessed. 1. Section one: Background Information Data Sheet. This section states the category, and location of the protected area, along with an opportunity to identify key management objectives and to make a value judgement about how the protected area contributes to well being. Figure 3.1: Background Information Data Sheet. 26 There are some guidance notes on how to fill in the background information data sheet which are briefly discussed below a) Who took part in the assessment: the first section should record the main contact person i.e. the person who led the assessment when the protected area benefit assessment tool was completed and by whom. Ideally, as well as marking on the datasheet the range of people involved, a list of who took part should also be attached as an appendix to the datasheet. b) Basic Protected Area data: the next few sections record some basic information about the site, such name, size and location. Where possible the unique site code given to the protected area in the world database on protected area (WDPA) should also be provided. The WDPA can be accessed via the UNEP-World Conservation Monitoring Centre website at: www.unepwcmc.org/wdpa. c) Ownership and governance: The protected area benefit assessment tool includes two multiple-choice boxes to record ownership and governance of the protected area. The options provided in relation to governance are linked to the governance matrix developed by IUCN and key terms used. d) Management objective: This section provides an opportunity to list the two most important management objectives: these might be, for example, maintenance of a particular endangered species or habitat type, or restoration of threatened ecosystem, or maintenance of a particular ecological function such as a migration pathway. e) Homeland: a simple yes/no question about whether the protected area is currently a homeland for local indigenous or traditional people-recorded here it will have significant implications for much of the rest of the information collected. f) Peace Park: a yes/no question also provide the opportunity to record if the protected area is part of a transfrontier conservation area or peace park. g) Well-being: the data sheet gives compilers a chance to make an overall judgement on the extent to which the protected area has contributed to overall well being (it may be best to fill this section after the rest of the form has being completed.) The assessment of the well-being is made against the five aspect of poverty reduction identified by both the UK department of 27 international development; while these are not word-for word-identical they convey the same message, which was interpreted as. • Subsistence: non-economic benefits that contribute to well-being, i.e. health, nutrition, clean water and shelter. • Economic: benefits that provide the ability to earn an income, to consumer and to have assets. • Cultural and spiritual: pride in community and protected area, confidence, living culture, spiritual freedom, education. • Environmental services: role in environmental stability and provision of natural resources. • Political: relating to issues of governance and thus influence in decision-making processes. The data sheet gives an opportunity to measure against all these values. 2. Benefits to Protected Area Stakeholders Sheet. A set of data sheet which collect basic information about the types of benefits who they are important to, and qualitative information about their level of importance, their relationship to the protected area and the times of year in which they are important. 28 Figure 3.2: Data Sheet. 29 There are also some guidance notes in the second section of the questionnaire. That are related to values and their benefits to protected area stakeholder data sheet, and they include. a) Identification of values: the datasheets below identifies nine main groups of values and they are. • Biodiversity values: is the protected area valued for its biodiversity? • Protected area management: does management of the protected area provide jobs (e.g. for managers or rangers)? • Values related to food: which include hunting, wild food plants, fishing, and livestock grazing, whether they are allowed. • Values related to water: is non-commercial water use (e.g. subsistence agriculture, drinking, washing and/or cooking) or commercial water use (e.g. for large-scale irrigation, waterways, bottling plants, hydroelectric power or municipal drinking water source) permitted in the protected area? • Cultural and Spiritual Values: does the protected area have cultural and historical values (e.g. archaeology, historic buildings including temples, pilgrimage routes and/or historic/culturally important land use patterns)? does the protected area include sacred natural sites or landscapes (e.g. sacred groves, waterfalls and/or mountains)?, does the protected area contain wilderness values or other similar iconic values? • Health and Recreation Values: is the collection of medicinal resources (e.g. herbs) for local use or for the pharmaceuticals industry permitted from the protected area? is the protected area important for recreation and tourism? • Knowledge: is the protected area an important resource for building knowledge? Does the protected area contribute to education? • Environmental Services: can the protected area contribute to climate change mitigation (i.e. by providing significant carbon sequestration and / or by ameliorating local climate impacts)?, is the protected area 30 important for soil stabilisation (e.g. avalanche prevention, landslide and erosion)?, is the protected area important for coastal protection (e.g. mangroves, sand dunes, coral reefs)?, is the protected area important for flood prevention (e.g. mitigation in small watersheds, flood plains and wetland protection)?, is the protected area important for water quality and quantity (e.g. filtration, groundwater renewal, maintenance of natural flows)?, is the protected area an important resource for pollination of nearby crops or for pollination products such as honey? • Materials: is the management and removal of timber, including for fuel wood, permitted from the protected area? is the extraction of other materials (e.g. coral, shells, resin, rubber, grass, rattan, minerals, etc) permitted from the protected area? Together these values attempt to represent the main benefits to a wide range of stakeholders. As the PA-BAT has been designed to use globally, the range of values and the benefits they provide is necessarily generic and not all will apply to every protected area. b) Completing the datasheets: there are two steps in completing the data sheet; Step one: each data sheet start by asking if the value is permissible in the protected area. For each datasheet the assessment of benefits from each value is only made where the answer is yes. Step two: for each value, assessment then generally considers seven issues relating to who benefits and what benefits are supplied. c) The stakeholder group which benefits from the benefits from the values: the main stakeholders groups are listed along the top row of the assessment form and are divided into seven groups. • Indigenous/ traditional people living, either permanently or temporarily, in the protected area. • Other local people living, either permanently or temporarily, in the protected area. • Indigenous/ traditional/local people living near the protected area, this can include people living in other countries when the protected area is 31 located near national boundaries; local groupings of people including NGO’s and those living downstream of protected areas. • National population. • Government. • Industry, including national and international industries both within the protected area, such as the tourism industry, and those industries which rely on resources from a protected area such as water which then supplies hydro-electric power to the wider population. • Global community, who, for example, benefits from environmental services such as climate regulation, recreational values, etc. This category includes international organisations who work in protected areas. d) Types of benefits supplies: multiple choice answers are supplied and assessors are asked to mark relevant answers against particular stakeholder group. Note that more than one answer may be applicable for a particular stakeholder (for instance resources may have both subsistence and economic value), so all relevant boxes should be marked. Those boxes which would never be appropriate have been shaded and should not be completed. Generally three options for the level of importance are given: • Potential: this value exists and there are benefits which could arise from it that have not been exploited. • Minor: this could either reflect low importance for the stakeholder group or that importance is significant to only a small proportion of the stakeholder group, and thus overall the level of importance is minor. • Major: this assessment should be made where the benefit is of significance for a large proportion of the stakeholder group. This assessment will usually be a matter a judgement, particularly in the wider stakeholder groupings such as national population, industry or global community. At the local level the assessment can be strengthened by completing this section with, wherever possible, the 32 relevant stakeholder groups and by adding (in the box marked notes) supporting research and studies. e) Amount of protected area involved and period it is exploited: next, assessors identify how much of the protected area is involved in supplying a particular benefit, choosing from three options. In most of the datasheets the assessors are also asked to identify how much of the time the park supplies the benefits, once more choosing from three options for each relevant stakeholder group. If the assessors have the relevant information it would be possible to break this information down for each of the relevant stakeholder groups given above. f) Economic value: the next section looks at two economic elements, one is if the economic value of these benefits has been assessed and if so asks for the US$ value and the date the assessment was made and secondly asks for any information on whether the assessment of cost of managing this value has been made. g) Conservation Impact: this section provides the opportunity to give details as to whether the activities relating to the values/benefits are consistent with the area’s management objectives. h) Management issues: although the PA-BAT’s primary aim is to identify the range of values, their associated benefits and their importance to different stakeholder groups, space is also given to suggest both current and future management responses to particular issues that have been identified in the assessment. i) Notes: the assessment form also provides room to add notes, information of the courses used etc. 3.4.2.3: Condition for the Use of Protected Area Benefit Assessment Tool There are some rules and guides in using the PA-BAT, and they are hereby stated below a. The protected area benefit assessment tool monitors permitted use only. 33 The protected area benefit assessment tool aims to assess legal resources and the benefits that could accrue from that use, and thus is not a tool for the assessment of overall resource use, which would include illegal use. b. The protected area benefit assessment tool is not an evaluation tool. Although the protected area benefit assessment tool includes the option to record economic information in terms of values and benefits, the primary purpose of the tool is to record the types of benefits provided the by protected area and to whom they are provided, and not necessarily to put an economic value on these benefits. c. The protected area benefit assessment tool can help guide future monitoring and assessment. It may also help identify key areas for future more detailed monitoring and assessment if resources and capacity allow. d. The protected area benefit assessment tool has been primarily designed for use by protected area managers to work with stakeholders to identify important values and benefits that they bring to a range of stakeholders, from local to global. The tool can also be used by local communities to identify values/benefits and by protected area advocates, such as N.G.O, to help promote the range of benefits a protected area can bring. e. Protected area benefit assessment tool should not be used to provide score. The tool is meant to collect information about a wide range of benefits that accrue in protected areas; it is not designed to produce a score of how well the protected area is performing in this regard. Summing up all the result will produce a bias towards multipurpose reserve, so that category V and VI would be expected to routinely score higher than I and II; these reserves are by no means always the best from a conservation perspective and many excellent protected areas focus solely on biodiversity conservation with perhaps some minor role for visitors and research. 34 CHAPTER 4 THE STUDY AREA 4.1 Introduction This chapter provides information about the study area, so as to get general characteristics of the area. The chapter gives a brief geography of Nigeria, and Katsina state, and then gives a detailed study of the Rugu National Park in Safana local Government. 4.2 Nigeria The location of Nigeria is approximately between Latitudes 4o and 14o north of the Equator and between Longitudes 2o 2' and 14o 30' east of the Greenwich Meridian. Located at the extreme inner corner of the Gulf of Guinea on the west coast of Africa, Nigeria occupies an area of 923,768 sq. km, extending 1,127 East– West and 1,046 km North–South. It is bordered by Chad on the North East, by Cameroon on the East, by the Atlantic Ocean (Gulf of Guinea) on the South, by Benin (formerly Dahomey) on the West, and by Niger on the North West and North with a total boundary length of 4,900 km, of which 853 km is coastline (See Figure 3.1). 35 Source: (Thomson Gale, 2006). Figure 4.1: Map of Africa showing Nigeria. 4.3 Katsina State The study area is in Katsina state of Nigeria, hence the need for a brief history of the state. Katsina State, covering an area 23,938 sq. km., is located between latitudes 110 8'N and 13022'N and longitudes 60 52'E and 9020'E. The state is bounded by Niger Republic to the north, by Jigawa and Kano States to the east, by Kaduna State to the South and by Zarmfara State to the West. The state lies within the tropical zone, with a temperature of about 350 C, with very high humidity, with an average rainfall of about 500-1000mm (KTMA, 1999). The population of Katsina state in 2006 was 5,790,578 according to the head count of that very year (NPC, 2006). 36 NIGER Chad BENIN Gulf of Guinea CAMEROON Source: Salele, 2005. Figure 4.2 Map of Nigeria showing Katsina state. 4.4 Background of Rugu National Park A brief study of the National Park is discussed here including history, location and size, administration and laws. 37 4.4.1 History Rugu National Park was established in the year 1960 by the then Northern Nigerian government and Katsina native authority in conjunction with USAID. It was formally known as Ruma Kukar Jangarai reserve, and later on the Katsina native authority reserve No 2 and 11 respectively. The two areas (Ruma and Kukar Jangari) were merged together as Rugu National Park in 1960. They forest reserve was initially designed to serve the whole people in the Northern region for the following purposes. 1. To protect wild life and landscape values. 2. To provide a special grazing reserve for the nomadic and sedentary Fulani 3. To lessen or completely stop the conflict between crop farmers and the cattle rearers 4. To boost livestock husbandry in order to meet protein requirements 5. To enlighten the Fulani’s on new methods of livestock husbandry. 4.4.2 Location and Size Rugu National Park lies within the Sudan zones of Nigeria. It falls between longitude 70 22’ and latitude 120 25’. It is bounded on its Northern border by Niger Republic and on the West by Sokoto-Zamfara State, Kankara local government in the south, and Safana local government in the East. Rugu National Park covers an area of 475.56 square miles or 122,000 hectares or 304380 acres of land. Which was initially divided into ten 10 ranges and later ranges 4, 5, 6 and 7 were subdivided into 4 divisions for easier management. 38 Rugu National Park Source: Google Earth 2009 Figure 4.3: Rugu National Park 4.4.3 Vegetation and Climate Due to the climatic conditions in the state, which falls under the Sudan savannah, it consists of a modified vegetation transition consisting of light deciduous vegetation. There are many pastures planted by the Federal Government within the Protected Area which are meant for dry season feeding, these pastures are served free of charge and monitored by the grazing control assistants and attendants. Much of the Rugu national park reserve is occupied by range lands which provide an ideal ecosystem for plants and animals. The forest provide a shelter for many plants, birds, amphibians, mammals, reptiles and insect species of which some 120 are used locally as medicinal plants, and over 278 animal species have been recorded in the Rugu park. The National park is not subject to trypanosomiasis bearing infestation, for this reason, most of the animals are not subject to tryponosomiasis infestation. The presence of this disease only becomes apparent among animals that moved to the southern areas during the long dry season. 39 The Rugu Park climate is tropical with 500-1000mm of annual rainfall within 100130 days rainy period with August peak and up to seven months with rain less than 25mm. The soil is deep fine textured grey sands. Table 4.1: Dominant Species of Plants around the Park. Name of Plants Pedicellatum Local Name Kyasuwa Pyramidals Buruburwa Rufa Harkiya Andropogan gayanus Gamba Sporobolis pyramdalas Goga masu Penicettum pedicellum Kuka Gunnea senegaleusis Marke Annona senegaleusis Kanya Source (FMANR, 1998). The vegetation around the Forest is normally deciduous and fire resistant varieties as shown by figure 4.3, and extensive grasslands in the valleys, rocks, clay flats, river beds and flood plains. Figure 4.4: Deciduous Plants within the Park 40 After the rainy season abundant grass cover is available, including high quality fodder. There are three major Rivers in the reserve namely Jangare, Koto, Kadaura, and Lamba, which all flow westward direction until they reach Ruma river (outside the forest). There are thirty si (36) earth dams and ponds which were constructed at various locations within the forest to provide water year round for livestock and wild animals. Table 4.2: Dams and Ponds Distribution in the Park Range Dams Ponds 1 4 - 2 2 - 3 2 - 4 2 1 5 3 1 6 6 4 7 5 - 8 2 - 9 2 - 10 2 - Total 30 6 Source (RRMC, 2008). 41 Figure 4.5: Kadaura Dam 1000 900 860 800 740 700 Yearly Rainfall (mm) from 1999 - 2006 780 681 660 2001 2002 731 691 660 600 500 400 300 200 100 0 1999 2000 Year Figure 4.6: Rainfall Data for the Park. Source: (RMCR, 2007). 2003 2004 2005 2006 42 Figure 4.7: A Wild Camel Feeding From the Pastures 4.4.4 Laws and Regulations The first wildlife conservation law enacted in Nigeria was the Wild Animals Preservation Laws of Western Nigeria (CAP 132), in 1916. The Wild Animals preservation Laws of Eastern Nigeria followed this in 1928, the Wild Animal laws of Northern Nigeria was later on enacted in 1963. Essentially, all these legislation sought to control and regulate hunting and killing of animals and birds in their respective areas of jurisdiction (Lawan, 1999). The present day law for the preservation and control of protected areas came in force on the first day of January, 1990,which was prepared by professor Sam Scruton Richardson, A.O, C.B.E. (Oxf) and sir Niggel Vernon Reed, C.B.E, T.D., L.L.B. (NZ). A law for the Preservation and Control of forest and wild life. NN 1963 Cap 44. KDSLN 5 of 1982. KTSLN 1 of 1987. This law is cited as the Forestry Law Governor may constitute reserves and protected forest 43 It shall be lawful for the governor to constitute as government forest reserve any of the following lands, lands at the disposal of government, or any land in respect of which it appears to the governor on the advice of the chief conservator of forests that the forest growth on such lands should be protected or reserved or forest growth be established. The governor may by notice in the state gazette declare any such land to be government protected forest. Before constituting any lands as government forest reserve a notice shall be published by the governor in the state gazette, specifying as nearly as may be the situation and limits of the lands, declaring that the lands now form a protected forest, declaring whether the land are at the disposal of the government or are lands coming within section 4 (1) (b), appointing an officer, hereinafter referred to as the reserve settlement officer. If for any reason the reserve settlement officer appointed under this section is unable to perform his duties, the governor may, by notice in the state gazette, appoint any person to act on his behalf or as successor. The governor may make regulations for many purposes and may specify the area or areas to which all or any regulations shall apply. Like prohibiting or regulating the taking of forest produce or of any specified kind of forest produce on land at the disposal of government or communal lands, prohibiting the sale and purchase of forest produce or of any specified kind of forest produce by any person other than the holders of licences and permits granted under this law, or by any other persons or by any classes of persons specified in the regulations, providing for the survey and demarcation of forest reserves and forests, regulating the taking, collection and preparation of forest produce e.t.c. 44 4.4.4.1 Offences and Legal Procedure Whoever in any forest reserve, except with the authority in writing of the prescribed officer, takes any forest produce, uproot, burns, strips off the bark or leaves from, or otherwise damage any tree, Hunts or fishes, Pastures cattle or permit cattle to trespass, Resides or erects any building, shall be liable on summary conviction to a fine of one hundred naira or be imprisoned for 6 months and in addition thereof may required by the court to pay a sum equivalent to the fees and royalties payable on any forest produce removed or damaged and also such amount, if any, as the court may consider just as compensation. A full detail of the laws governing the Rugu national park is attached at the appendix of the project report. 4.4.5 Administration Since the establishment of the Rugu National Park in 1960, the Federal Ministry of Animal and Forest Resources, and the Katsina Native Authority, now Katsina State Government and USAID have been involved in projects aimed at improving the Rugu National Park. Initially funded by the Katsina provincial Government, later by subsequent governments, i.e state governments and federal government and donor agencies like USAID (RMCR, 2007). The Katsina state government is responsible for the running and maintenance of the forest reserve, the local governments i.e Safana, Batsari, and Kankara and traditional councils assist the state government to enforce rules and regulations governing the forest reserve, the pastoralist and their Ardos sometimes assist in maintaining and repairing broken down facilities like dams, wells etc within the reserve and report in some cases eject encroachments and control bush burning. When some part of the Forest was opened for grazing activities, the need for effective control of the resources becomes one of 45 cardinal programmes of management. The principal role of ten chiefs was foremost, to act as a go-between for herdsmen and the councillor for agriculture and animal resources, particularly in such areas as enlightment and dissemination of information on policy implementation and maintenance of law and order. In addition, they are also required to in collaboration with Wakilin Fulani to collect tax (Jangali). The tax through the wakilin Fulani and districts heads is remitted to the local government council. In case the district head receives a complain concerning a herdsmen (on such matters as unauthorised trespass into lands or other related matters capable of causing break of peace) it is their duty to bring the offender to the district head for adjudication. This does not preclude the district head referring the case to a court in case settlement cannot be affected through him. In real political terms these ten Chiefs act as village heads even though they are still under the jurisdiction of the later, the district head. The headquarters of the Rugu National Park is situated at Runka town exactly 3 kilometres away from the main town. Comprising of three sections 1. Range management section 2. Diary scheme 3. Veterinary Section Formally these sections were headed by one officer, but now each section is controlled by an officer. 46 4.4.5.1 Range Management Scheme The largest section of the three is headed by a range management officer with one range assistant seven grazing control assistant, three stock man, twelve labourers, ten range guards, two watchmen and a messenger under his control. There is also one clerical assistant; all in all, the total number of staff in this section is 38. Local grazing committee was formed and monthly grazing committee was formed and monthly grazing meeting was inaugurated to link the management of objectives with the wishes and aspirations of the herdsmen using the reserve. The committee comprised of the following. 1. Chairman of Dutsinman local government 2. District heads of Safana, Batsari, Yantumaki, and Danmusa 3. Councillor for agric and natural resources 4. Head of agriculture department 5. Wakilin daji d/ma 6. Senior livestock superintendent 7. Wakilin Fulani higher range management superintendent 8. Ten Fulani chiefs and Fulani opinion leaders and other Fulani interested groups. In the first National Development Plan (1962-1968) a sum of 2 million naira was allocated to the amenities programme, a large portion of the allocation was set aside for range management, and Rugu forest was selected for pilot scheme (1963). During the 3rd National Development Plan (1975-1980) another sum of 400,000 naira was further allocated for the improvement of the existing infrastructure and development of pastures in the forest. Based on this allocations, some commendable projects have been executed, this include the demarcation of the forest into 10 ranges. New access roads have been constructed and the existing ones improved. At present the Federal Government in collaboration with World Bank have embarked on pilot projects in ranges 8 and 9, total involvement on the project was estimated at 336.203 naira to be spread over a three year period. (Source: FMANR 2008). 47 4.4.5.2 Diary Scheme This section is headed by a livestock superintended with a livestock assistant, 10 labourers, 2 watch men and 1 operator under his control. The livestock superintended takes charge of the administrative and other operational activities, while the livestock assistant assists him in other operations. With a plant processing capacity of 500 litres per day to provide market for the excess milk produced by the cattle rearears. The milk purchased from the cattle rearers is processed into yoghurt, cheese, butter, cream and fresh milk for sale to institutions in the state. Big cold rooms at Runka and Katsina selling points were used for storing milk products. The diary equipments include Chuns, storage tanks (500 litres capacity, pasteurizer, sealing machine, separator, cold rooms. 4.4.5.3 Clinic Section (Veterinary) Veterinary clinics are located near Runka range management centre and in Dutsinmaa township and various sub clinics adjacent to the park at Safana, Batsari, Yar-malamai, Illela, and Dan-musa. The Divisional Veterinary Officer (DVO) at Dutsinma is in charge of this section, he is assisted by a livestock assistant, 2 invaculators, 2 labourers and a watchman. 4.4.5.4 Facilities, Utilities and Services The following Facilities Utilities and Services were put in place over the lifespan of the reserve. i. Access roads all over the ranges 48 ii. 36 earth dams for drinking water iii. One cattle dip, spray pumps for the treatment of outbreak of disease iv. Boreholes to provide clean drinking water to the pastoralist and their family. v. Machineries like heavy duty for dam’s construction and repairs, like bulldozer caterpillar D7 and D8, grader for road construction and scrapper. vi. Filling station which provides fuel to the heavy duty machineries, tractors and Lorries. vii. Generators that provide electricity for both the range and diary scheme. viii. Vehicles for the running of the day to day activities which include land rover jeep, Scrappers. 4.4.5.4 Staffing There are 32 staffs comprising of both junior and senior staff in running the administration of the park. They include i. 3 project officers ii. 4 assistant project officers having required qualification in the field of range management. iii. 10 grazing control assistants iv. 4 tractors operators v. 4 drivers vi. 3 extension officers vii. 2 botanist viii. 2 zoologist 49 4.4.5.6 Housing To accommodate the supporting staff of the Rugu National Park. The government built four types of staff quarters for the staffs. I. 6 senior staff quarters. II. 3 intermediate staff quarters. III. 2 junior staff quarters. IV. 2 labourers’ quarters. Labour lines were also constructed for labourers that provide the labour force at the project. 4.5 Settlements Within and Surrounding the Protected Area There are settlements located right inside the protected area, and there are other settlements located near the protected area. 50 Table 4.3: Distribution of Settlements and Population within the Protected Area Name of Settlements Population Figure Habul 408 Kinfau 732 Kunkunna 234 Garin Tunau 109 Salihawar haki 58 Dan-tudu 138 Gobirawa 325 Sabuwar duniya 451 Muniya 1,563 Makera 58 Bare-bari 1,210 Illela 981 Total 6,267 Source: (NPC, 2006). 51 Table 4.4: Distribution of Settlements and Population Surrounding the Protected Area Name of Settlements Population Figure Runka 1,810 Gimi 515 Marina 820 Tashar barau 114 Kuka tara 313 Guzurawa 1,217 Gidan Tsohuwa 197 Mara-zamfarawa 231 Hanki biri 75 Yarlilo 1,105 Daulai 561 Gora 1,298 Total 8256 Source: (NPC, 2006). 52 CHAPTHER 5 METHODOLOGY 5.1 Introduction The aim of this research is to evaluate the benefits of Rugu forest in Safana local government, Katsina state of Nigeria, using protected area benefit assessment tool. 5.2 5.2.1 Benefits Evaluation Evaluation Evaluation is a methodological area that is closely related to, but distinguishable from more traditional social research. Evaluation utilizes many of the same methodologies used in traditional social research, but because evaluation takes place within a political and organizational context, it requires group skills, management ability, and other skills that social research in general does not rely on as much (Williams, 2006). Evaluation is the systematic assessment of the worth or merit of some object. Evaluation can also be defined as the systematic acquisition and assessment of information to provide useful feedback about some object (Gunn, 53 2004). Evaluation offer information which helps people to know what happens after the initiation of a project or programme. (Medugu, 2007) 5.2.2 Benefits Benefits here refers here to a resource that is being used to provide direct gains (which could be in terms of money earned, or subsistence resources collected or less tangible gains such as spiritual peace or mental well-being) to stakeholders. The resources of the protected area become a benefit when they are successfully used to provide such gains. (Nigel et al, 2008). 5.3 Sources of Data Due to the fact that most of the respondents are illiterate, because they are mostly villagers and nomads, it will be unwise to give them questionnaire to fill themselves. This is because maximum information required may not be collected due to non response and misinterpretation of the questions. Therefore the author has to use the staffs in the Rugu National Park to fill some of the questionnaire, and also conduct interview in which respondents will be asked questions according to the questionnaire and their responses filled. 5.3.1 Primary Source Primary data collection was carried out by field observation using naked eyes, administering of questionnaires and also interviews. The methods of primary data collection used in this survey are. 54 5.3.1.1 Questionnaires Questionnaire are probably the most commonly used data collection methods and are extremely flexible and has the advantage of gathering information on almost any topic from large or small number of people, so questionnaires were administered to the respondents, and the standard questionnaire designed by the Protected Area Benefit Assessment Tool was adopted in this survey. Figure 5.1: Sample Questionnaire. 55 5.3.1.2 Field Observation A field trip was carried out in some part of the study area, so as to have a firsthand information and idea about the possible benefits of the protected area. 5.3.1.3 Interview As stated earlier in the beginning of this chapter, most of the target respondents are uneducated, they cannot understand and fill the questionnaire, so interview became necessary, in which respondents will be asked questions according to the questionnaire and their responses filled. There are mainly three types of interviewing, depending on the degree of being structured. a) Structured interview which are like questionnaires, instead of the questions being read by the respondents, they are asked by the researcher who also record the answers. The surveys are carried out like this for a number of reasons; the main reason is that it allows the researcher greater control over the sample of respondents, the other main advantage is that an interviewer can ask the respondent to explain an answer in a little more depth. This kind of interview was very important for this study because most respondents are illiterate. b) Semi-structured interview provide much more scope for the discussion and recording of respondents opinion and views. It consist of some open questions, this methods is basically used to collect such discursive information which usually contains a high degree of opinion or the expression of attitudes. 56 c) In-depth interview the purpose of this kind of interview is to collect complex information, containing a high proportion of opinion, attitude and personal experience. The topic used is usually the subject which both the respondent and interviewer are interested in. The structured interview was selected for this survey, because it provides the room needed for the researcher to ask the respondents questions from the questionnaire and record their responses accordingly. 5.3.2 Secondary Source Secondary information were drawn from the records of government ministries like Federal ministry of Agriculture and water resources, federal ministry of Environment, Katsina state ministry of agriculture, agriculture department of Safana local government, and also from literature reviews from journals, theories, books, publications, internet, and previous research work on the related field of protected areas and benefits of protected areas. 57 Figure 5.2: The Researcher with a Respondent after Being Interviewed. 5.4 Sampling In carrying out the research, sample population was selected from the whole population, which is intended to represent the whole population under survey. Simple random sampling was adopted because of its simplicity and effectiveness, in simple random sampling each person in the area under research has an almost equal chance of being selected (Tetsu, 2008). So all of the persons interviewed were selected by chance. 5.4.1 Respondents i. Indigenous traditional people living in the Rugu National Park. ii. Other people living in the Rugu National Park. iii. Indigenous people near the Rugu National Park. 58 iv. Government, three staffs of the federal ministry of agriculture and natural resources were interviewed, two staffs from the Katsina state ministry of agriculture and natural resources were also interviewed, and two staffs from agriculture department of Safana local government. These settlements were also sampled randomly; they were selected by chance. Figure5.3: Indigenous People Living Within the Protected Area. 5.3.1 Settlements Within the Protected Area These are settlements including helmets that are situated directly inside the National Park, and they include indigenous traditional people from the area living inside the park, and also non indigenous traditional people living inside the park. Table 5.1: Indigenous Traditional People Living in the Protected Area Name of settlement Muniya Kinfau Habul Total Population 1,563 732 408 2,703 No of Respondents 26 15 10 51 Source: (NPC, 2006). 59 Table 5.2: Non Indigenous People Living in the Protected Area Name of settlement Population No of Respondents Makera 58 5 Total 58 5 Source: (NPC, 2006). 5.3.2 Settlements Around the Protected Area These are settlements surrounding the National Park; they are located around the National Park. Table 5.3: Indigenous People Living Around the Protected Area Name of settlement Population No of Respondents Gimi Kuka Tara Gidan tsohuwa 515 313 197 12 9 8 Total 1,025 29 Source: (NPC, 2006) Governments There are also 7 respondents from the government, which makes up a total of 92 respondents. Table 5.4: Different Tiers of Government Interviewed Tier of Government Federal government State government Local government Total Portfolio Respondents Federal Min of Agriculture Min of Agriculture Dept of Agriculture 3 2 2 7 60 CHAPTER 6 FINDINGS AND DISCUSSIONS 6.1 Introduction The basic concern of this research is to identify the benefits of Rugu protected area in Katsina state Nigeria, using Protected Area Benefit Assessment Tool. This chapter discuss and explore what sort of benefits, and details on exactly who the beneficiaries are, either local indigenous people, or national population. 6.2 Values and Benefits Benefits here refers to a resource that is being used to provide direct gains which could be in terms of money earned, or subsistence resources collected or less tangible gains such as spiritual peace or mental well-being) to stakeholders. The resource of the protected area becomes a benefit when they are successfully used to provide such gains (Sue and Nigel, 2008). In the previous chapters much was discussed about protected areas and noted that a number of them appear to provide benefits to local people and also about Rugu national park, however, details on what sort of benefit are extracted from the Rugu National Park are explained here. In order to evaluate these benefits the (PA-BAT) was used to examine these kinds of benefits. So the tool which is a questionnaire was 61 used in the collation of information regarding the different types of benefits that the people get from the PA, after which it was analysed and the results of the analysis is shown below. The benefits evaluated in this study were classified into three main categories, namely i. Economic benefits. ii. Environmental benefits. iii. Social benefits. 6.2.1 Economic Benefits These are benefits that provide ability to earn an income, or benefits to consume and to have assets. Under which we have 6.2.1.1 Grazing and Fodder The Rugu Park has served as a rainy season grazing resort for the settled indigenous people, semi-settled non indigenous pastoralist residing in the area and migratory groups from surrounding environs, such as Funtua, Zaria and Sokoto state, and indigenous people living near the protected area. The Fulani are the major pastoralist, they migrate from the south to the park in search of fodder and water for their animals most of which are camels, cattles, sheeps, and goats. The pastoralists utilising the park are divided into three groups • Permanent indigenous traditional reserve settlers: these are indigenous people who live in the national park. • Indigenous traditional people pastoralists: those who stay in the reserve in the surrounding village close to the park. 62 • The non indigenous people living in the protected area: those who normally move from other areas to the park at the beginning of the rainy season and withdraw to their permanent site immediately the dry season begins. The largest concentration of livestock’s in the reserve occurs during the wet season from June to early November. From November onwards when the quality and quantity of herbage declines due to intensive grazing, leaching of soil, accidental bush fire and some climatic factors. So the use is not continuous rather regular. The benefit is subsistence. Livestock grazing and fodder occurs in a rotational pattern in the reserve. Figure 6.1: Herds of Cattle Returning to Base after Grazing 63 Percentage of PA involved in grazing 11% Indigenous People living in PA 5% Non-Indigenous People living in PA 8% Indigenous People living outside PA Buffer zone 76% Figure 6.2: Proportion of Protected Area in Supplying the Benefit. The indigenous people living in the protected area are allotted with range 1 and 2 to rear their animals, which makes up 11 % of the protected area. The non indigenous people living in the protected area are only allowed to graze their animals in range 1 which constitute 5 % of the protected area. The indigenous people living outside but near the protected area are allowed to graze on range 1 and some part of range 2 which make up 8 % of the protected area. Table 6.1: Percentage of Grazing Beneficiaries and non Beneficiaries Settlement Respondents Beneficiaries % Non Beneficiaries % Muniya Kinfau Habul Makera Gimi Kuka tara GidanTsohuwa Total 26 15 10 5 12 9 8 20 12 9 3 5 4 3 77 80 90 60 42 44 37 6 3 1 2 7 5 5 23 20 10 40 58 55 62 85 56 66 29 34 All settlements located within the PA have higher percentage of benefits because they are allocated with range 1 and 2 to graze their animals; these settlements include 64 Muniya, Kinfau, Habul and Makera. While the remaining settlements outside the PA do not have easy access to the PA and are allocated with range 1 only to rear their animals which include Gimi, Kuka-tara, and Gidan-tsohuwa. 6.2.1.2 Fishing There are four major lakes in the reserve used for fishing namely, Jangare, Koto, Kadaura, and Lamba 1 lakes, they flow westward direction until they reach Ruma river (outside the forest). Fishing is allowed in these lakes, Lamba 1 is situated at the North Eastern part of the protected area, Kadaura, jangare and Koto located at the North Western part of the reserve. Table 6.2: Major Species of Fish Caught in the Protected Area Scientific Name English Name Local Name Tilapia spp Synodontis eupterus Labeo pseudocoubie Alestes nurse Fundulopanchax gardneri nigerianus Parachanna obscura Tilapia Catfish African carp characins Nothobranchiidae Buku Kala Jigo Miki Nigerian Killi Snake Head Kan maciji Cat Fish Tilapia Fish Figure 6.3: some of the types of fish caught in the protected area. Fish provides subsistence and economic benefit to the people as they consume it and it’s a good source of protein, and the remaining surplus they sell it out and provide income of USD 61 in a month (Source, Sarfillu). This activity is usually a regular activity and not continuous, normally people are allowed to fish during the rainy season, and not allowed to catch during the dry season. 65 Map of Rugu Park Figure 6.4: Map of Rugu Park Showing the locations of Settlements and dams. Table 6.3: Percentage of Fishing Beneficiaries and non Beneficiaries 66 Settlement Respondents Beneficiaries % Non Beneficiaries % Muniya Kinfau Habul Makera Gimi Kuka tara Gidan Tsohuw 26 15 10 5 12 9 8 19 10 10 4 3 5 6 73 66 100 80 25 56 75 7 5 0 1 9 4 2 27 34 0 20 75 44 25 Total 85 57 67 28 33 Gimi has the lowest percentage of beneficiaries due to distance from the dams where fishing takes place, all other settlements located outside the PA have less percentage of benefits compared to settlements of Kinfau, Habul and Muniya which are located right in the PA and close to the dams in which fishing activities is carried out. 6.2.1.3 Timber Timber collection for fuel purposes is allowed within the protected area, any other use of timber apart from fuel purpose is not allowed, the reason behind this allowance for the collection of fuel wood is because gas and other source of energy are not affordable for the common man. The Northern part of the park is set aside for exploitation of this benefit; fuel wood is the major source of energy for the locals living in the area. 67 Figure 6.5: A Local Resident Collecting Fuel Wood from the Park Table 6.4: Percentage of Timber Beneficiaries and non Beneficiaries Settlement Respondents Beneficiaries % Non Beneficiaries % Muniya Kinfau Habul Makera Gimi Kuka tara Gidan Tsohuwa Total 26 15 10 5 12 9 8 85 21 14 10 5 11 9 7 77 81 93 100 100 92 100 87 90 5 1 0 0 1 0 1 8 19 67 0 0 8 0 13 10 Fuel wood provides economic benefits to the people as they sell it out and earn income of about USD 76 per month, it also provides subsistence benefits as they also use it for other domestic use like cooking and heating, it is also used as a building material. 6.2.1.4 Job Opportunity One of the major economic benefits of the Rugu national park is providing jobs to numerous people both the indigenous and local people in the protected area and non-indigenous people, including people living outside the protected area. During the survey, it was discovered 7 people living in the protected area were employed, 3 as tractor operators with a monthly income of USD 77, and 2 as 68 invaculators with a monthly income of USD 95, and 2 as livestock grazing control assistants with an income of USD 82 per month. Another 3 indigenous people living outside the protected area and 2 are non locals but reside close to the protected area were employed as forest officers, under the federal Ministry of Agriculture, their job is to regulate felling down of trees and also arrest offenders, with a monthly income of USD 100 per month, 1 indigenous person was also employed as livestock assistant with a monthly income of USD 120. Figure 6.6: Some Indigenous People Employed as Forest Officers. Table 6.5: Percentage of Job Beneficiaries and non Beneficiaries Settlement Respondents Beneficiaries % Non Beneficiaries % Muniya Kinfau Habul Makera Gimi Kuka tara Gidan Tsohuwa 26 15 10 5 12 9 8 4 2 1 0 2 0 1 15 13 10 0 17 0 13 22 13 9 5 10 9 7 85 87 90 100 83 100 87 Total 85 10 12 75 88 69 Makera which is a settlement of Fulani’s who are settlers are non-indigenes do not enjoy the opportunities of jobs provided by the PA, whereas they remaining settlements both within and outside the PA which include indigenous Hausa people have job opportunities. 6.2.1.5 Non Commercial Water Use This is the benefit that almost everyone living in and around the protected area enjoyed. The numerous benefits of non commercial water use includes domestic use of water like washing, drinking, cooking, and also irrigation farming, this usage became feasible due to the presence of various earth dams constructed all over the protected area. The Rugu River is purposely used for the irrigation farming which is situated at the Western part of the national park. The surplus produce is sold out which provides income from the irrigation farming. Table 6.6: Percentage of Water use Beneficiaries and non Beneficiaries Settlement Respondents Beneficiaries % Non Beneficiaries % Muniya Kinfau Habul Makera Gimi Kuka tara Gidan Tsohuwa 26 15 10 5 12 9 8 26 15 10 5 11 9 8 100 100 100 100 92 100 100 0 0 0 0 1 0 0 0 0 0 0 8 0 0 Total 85 84 99 1 1 Due to abundance of earth dams and various lakes within and around the PA, almost all the settlements have access to water provided by the dams and lakes. 6.2.1.6 Medicinal Resources Traditional herbs collection provides subsistence benefits and economic benefits to both indigenes and non indigenous inhabitants that live in and around the protected area, this has become possible due to dependence of traditional herbal medicine which are still the primary medicine for the residents, the discovery of 70 traditional use of herbs for the treatment of Pile, a disease which affects most Africans has greatly increase the benefits from the park. Gamji and Gawo are the most effective herbs used for the treatment of this disease, so people around the area use to sell and also make use of this herbs, amongst some of the widely used herbs for medication include gawasa, bedi, kanya, marke, guga masu, which effectively treats ailments ranging from malaria, cholera, body pain and body weakness. Figure 6.7: Herbs Collectors, From Left Sarfilu, Middle the Author and Right Bello. Table 6.7: Percentage of Medicinal Beneficiaries and non Beneficiaries Settlement Respondents Beneficiaries % Non Beneficiaries % Muniya Kinfau Habul Makera Gimi Kuka tara GidanTsohuwa 26 15 10 5 12 9 8 23 14 8 4 10 3 2 88 93 80 80 83 33 25 3 1 2 1 2 6 6 12 7 20 20 17 67 75 Total 85 64 75 21 25 Gidan-tsohuwa and Kuka-tara settlements’ always patronise government hospitals when they fall sick, hence the reason for low percentage of benefits, while the remaining settlements normally use local medicinal plants to cure their sickness, illiteracy is a major factor why these remaining settlements don’t visit hospitals. 71 6.2.1.7 Hunting Hunting of wild game for food and recreation is allowed within the protected area. Range 9 and range 10 are set aside for this purpose which is at the southern part of the park. Table 6.8: Percentage of Hunting Beneficiaries and non Beneficiaries Settlement Respondents Beneficiaries % Non Beneficiaries % Muniya Kinfau Habul Makera Gimi Kuka tara GidanTsohuwa 26 15 10 5 12 9 8 18 8 9 3 2 1 3 69 53 90 60 17 11 37 8 7 1 2 10 8 5 31 47 10 40 83 89 63 Total 85 44 52 41 48 Figure 6.8: The Author Left and Mallam Danlami a Hunter Right. 72 Accessibility is the major reason why Habul, Makera, and Muniya have a higher percentage of benefits as they are all situated right inside the PA, whereas Kuka tara, Gimi and Gidan-tsohuwa have lower percentage due to distance away from the PA. 6.2.1.8 Recreation and Tourism This is a two way benefits, one is the inhabitants enjoy the recreation provided by the protected area and at the same time the serve as guide to tourist that visits the national park which provides them with income, and it is the women that mostly engage in this act. In the 1980 s more than 1000 tourist from over 40 countries were hosted in the Rugu national park (RMC, 1987). But now they number of tourist is declining, the reason is wild life have move deep into the forest now due to human disturbance. But there are so many places near and around the protected area that are used for recreational purposes such as the Gimi waterfalls very close to it is a natural spring water coming out from a very big mountain also called Gimi mountain, which provides clean and portable drinking water for visitors and people living within and outside the protected area. Table 6.9: Percentage of Recreation Beneficiaries and non Beneficiaries Settlement Respondents Beneficiaries % Non Beneficiaries % Muniya Kinfau Habul Makera Gimi Kuka tara GidanTsohuwa Total 26 15 10 5 12 9 8 85 20 10 10 3 8 3 7 61 77 67 100 60 67 33 87 72 6 5 0 2 4 6 1 24 23 33 0 40 33 67 13 28 73 6.2.1.9 Collection of non Wood Products The collection of non-wood product is a very vital benefit, they non wood products includes thatch grasses like the gamba grass which is used as a building material, the grass is also gathered from the park and sold to other settlements Table 6.10: Percentage of Non-Wood Beneficiaries and non Beneficiaries Settlement Respondents Beneficiaries % Non Beneficiaries % Muniya Kinfau Habul Makera Gimi Kuka tara GidanTsohuwa 26 15 10 5 12 9 8 22 13 10 2 8 7 5 85 87 100 40 67 78 63 4 2 0 3 4 2 3 15 13 0 60 33 22 37 Total 85 67 79 18 21 The main reason why Makera settlement has the lowest percentage of benefits is due to the fact that they are settlers and none indigines, they are not allowed to exploit the PA as they wish, rather there is regulation on how the exploit the PA. Figure 6.9: The Researcher Front Posing With a Non Wood Collector. 74 6.2.2 Social Benefits These are benefits that bring about pride in the community and protected area, including confidence, spiritual freedom, and education. They include. 6.2.2.1 Knowledge, Research and Education The Rugu national park provides resources for research; however the benefits the protected area provides is not directly enjoyed by the inhabitants living in and around the protected area, rather by scientist and other technicians, an increasing number of schools and universities runs trips to the Rugu national park, students from the biological sciences and also from the pharmaceutical departments of Ahmadu Bello University Zaria have been visiting the park for educational purposes. There is a research which focuses on the use of a special plant known as kanya, the research is on how to use the plant as bio fuel, and the research was made possible due to abundance of kanya plant species in the protected area. The park is also used as a case study as a venue for workshops on the awareness of environmental protection. 6.2.3 Environmental Benefits These benefits refer to those benefits that play roles in environmental stability and the provision of natural resources, and they include. 75 6.2.3.1 Carbon Sequestration and Soil Stabilisation Protection Most of the trees that makes up the national park contributes immensely in the reduction of carbon within the atmosphere, because trees absorbs carbon and produce large amount of oxygen, so in essence this will go a long way in reducing or checking climate change and global warming, so the benefits here is a global benefits, and it is a continuous process, it has been discovered that in a year, one tree in the park can inhale 12 kilogramme of carbon and exhale enough oxygen to keep a family of four breathing for a year (IUCN, 2002). Another major benefit of the Rugu protected area from environmental perspective is in controlling soil erosion, soil erosion is a very rampant problem around the region, but the protected area has checked this menace, during the survey it was realised that there is the availability of cover crops and trees all over the place, which greatly reduce runoffs that causes soil erosion and also the trees serves as wind breakers which reduce the speed of winds and winds action in erosion process, rate of erosion when reduced will greatly increase crop yield and it will in turn reflects in the income of the inhabitants. Proportion of PA involved in the provision of environmental benefits 23% Amount of PA involved in the provision of environmental benefit 77% Figure 6.10: Environmental Benefits Chart. Amount of PA not involved in the provision of environmental benefit 76 6.2.3.2 Water Quality and Quantity The Rugu protected area provides rich sources of drinking water; this has become possible because of the natural vegetation which provides pure water. The park is an important source of water for the local communities who have observed that conservation of the park’s forests has improved water resources, all these have become possible because the park is a watershed protecting and stabilising stream flows, maintaining ecological cycles and micro climates. There are also many dams located in different parts of the park which is a good source of water to the people. Some of these dams include Lamba one, Kadaura dam, Koto dam, jangare dam, Muniya dam, kurkal dam, Bunsuru dam, 6.3 Summary The results of the analysis shows a clear relationship that exist between protected areas and human beings, these relationship which are benefits are provided by the Protected areas, these benefits include direct economic, environmental and social benefits, however these benefits are more often linked to aspect of well-being, such as the provision of food and clean water, maintenance of health and other benefits linked to cultural and spiritual values. They various benefits provided by the Rugu National Park were classified into three main benefits; namely economic benefits, social benefits and environmental benefits, which are shown by the figures below. 77 Economic Benefits Beneficiaries 90 88 Non-beneficiaries 99 79 75 67 66 72 52 48 34 33 25 10 12 21 1 Figure 6.11: Economic Benefits from the PA The above bar chart describes the holistic economic benefits that accrue from the PA to the people; these are benefits that provide the ability to earn income, to consume and to have assets. The first benefit is grazing with 66 % of the people benefitting from it and 34 % not benefiting, while fishing has 67% beneficiaries and 33% not benefiting from fishing, majority of the respondents interviewed shows significant benefit from timber resources with 90% of the respondents benefiting and 10% not benefiting, findings of this study also shows that a total of only 12% benefits from Job opportunities while 88% do not benefit, another benefit is non-commercial water use with a 99% of respondents benefiting from and just 1% not benefiting, and medicinal resources with a total of 75% of respondents benefiting from it and 25% not benefiting, the study also reveals 52% of the people benefiting from hunting activity while 48% are not benefiting from it, non-wood products benefits with 79% of the respondents benefiting from and 21%are not, lastly in economic benefit is recreation and tourism with 72% of the population benefiting and 28% not benefiting. 28 78 CHAPTER 7 CONCLUSION AND RECOMMENDATION 7.1 Introduction This chapter is the last chapter of the study; it includes recommendations based on the findings and conclusions. Based on the findings of the study recommendations are hereby presented. 7.2 Conclusion It has been stated that protected areas especially in developing countries address human concerns, ranging from benefits and values to other human needs (James, 1997). So this project set out to discover if protected areas can now be said to play a positive role in fundamentals of human concerns. At the end of the research it was clear that there is a strong relationship between protected areas and human beings, the protected areas provides important benefits that helps in addressing issues of poverty, these benefits include direct economic, environmental and social benefits, although these benefits are more often linked to aspect of well-being, such as the provision of food and pure water, maintenance of health and other benefits linked to cultural and spiritual values. Sometimes they also play a direct role in poverty reduction, but more commonly the PA provide a safety net for most of the poor people within and in the Rugu park and 79 stop them falling further into poverty and providing them with some of the requirement for improving their lifestyle. 7.3 Recommendation The Federal government of Nigeria should establish stiffer controls on fuel wood extraction from the national park, because along the line during the study, it was discovered that fuel wood collection is the major problem facing the park, it pose a threat to the park as people fell down trees indiscriminately. Community management of fuel wood resources should also be encouraged, there should be reform in forestry afforestation, land and tree tenure, and environmental education programmes should be promoted. The government should also develop economic incentives and policy commitments to support protected areas through the provision of economic incentives for local communities in and around protected areas so as to conserve biodiversity and reduce encroachment, conservation clubs and societies should also be formed. The international agencies along with the state government should strengthen capacity of national parks services to household protected areas and control encroachment. The government should also work towards establishing effective protected areas system and buffer zones management. Enforcement review and update of strong anti bushfire should be done. Also promotion of local participation in protected areas management should be done. Principle can be adopted to sustain parks existence because sustainable development attempts to bridge the gap between economic growth and environmental protection. If done, can support economic growth of the national park and enhance biodiversity at the same time. 80 Sustainable use of the National Park should be encouraged; since the local people have clearly recognised the park as a vital resource in their daily lives, they should therefore manage and safeguard the biodiversity of the protected area. Finally the federal government should totally surrender the entire park to the state government, as the case in Yankari game reserve where the federal government handed over the whole game reserve to Bauchi state. 81 REFERENCES Adamsa, C, et al. (2007). The Use of Contingent Valuation for Evaluating Protected Areas in the Developing World: Economic Valuation of Morro do Diabo State Park, Atlantic Rainforest, Sao Paulo State (Brazil). Ecological Economics. 66(2008) 359-370. Adeyoju, S. K. (1998). Forestry and the Nigerian Economy. Ibadan University Press. Ibadan. Agboola, S. A. (1979). An Agricultural Atlas of Nigeria, Oxford: University Press Oxford. Ahmed, T., (2004). Overgrazing in Rugu Forest: Implication for Biodiversity. ABU Press. Kaduna. Dalton, D.M. (2003). An Approach for Integrating Economic Impact Analysis into the Evaluation of Potential Marine Protected Area Sites. Environmental Management. 70 (2004)333-349. DOF. (2001). Report of Federal Ministry of Agriculture and Natural Resources on National Action Programme on Conserving Activities Within the Forestry and Wildlife Sectors.: FMANR. Dudley, N. et al. (2008). Protected Areas and Poverty Reductions: A research by WWF 978(2), 88085-279-5. Dudley.N. and Stolton. S. (2008). The Protected Area Benefit Assessment Tool. A Methodology. 978(2), 88085-284-9. Ezebilo, E.E., Mattson, L., (2009). Socio-Economic Benefits of Protected Areas as Perceived by Local People around Cross River National Park, Nigeria. Forest Policy and Economics. xxx (2009) xxx. Falade, J. B., (1998). The History of Park Development in Nigeria. Lagos State Horticultural Society. Lagos Nigeria. Gbadegesin, A. Ayileka, O. (1999). Avoiding the Mistake of the Past: Towards a Community Oriented Management Strategy for the Proposed National Park in Abuja, Nigeria. Land Use Policy. 17(2000)89-100. Godwin,H. J., (1996). In Pursuit of Ecotourims. Biodiversity and Conservation. 5(3)277-292. 82 Harrison. J, Lysenko. I., Spalding. M. (2005). Measuring the Extent and Effectiveness of Protected Areas as an Indicator For Meeting Global Biodiversity Target. 360, 443-455. Ibrahim, K. A. (2008). Forest Reserve in Katsina State-Their Distributions, Potential. , A B U Press, Kaduna. Janishevski, L, et al., (2008). Protected Areas in Today’s World: Their Values and Benefits for the Welfare of the Planet. 92-9225-082-5. John, D., (1990). Economics of Protected Areas: A New Look at Benefits and Costs. Island Press. John,P.(1992). Micro Development Plan for Rugu Grazing Reserve. Master’s Thesis. Ahmadu Bello University. Zaria. Katsina State. (1999)., Stock Routes, Control of Livestock Movement Prevention of Farmers/Herdsmen Clashes. Edict No 5 of 1999. and Kubota, T., (2008). Quantitative Methods in Planning. Lecture Notes on Introduction to Data Analysis. Lawan, R. (1990). National Parks: Man and Plants., Gaskiya Press, Zaria, Kaduna. Lucas, M., (1994). Towards Sustainable Governance of Protected Areas in Nigeria. KTSMANR. Medugu, I. N., (2007). A Comprehensive Approach to Addressing Drought and Desertification in Nigeria. Master’s Thesis. , University of Technology Malaysia. NPC. (2006). National Population Commission. Facts, Figures, and Discussions about Nigeria’s 2006 Population Census. Abuja Nigeria. Oduwaye, A. O., (1997). Urban Landscape Planning in Nigeria. Landscape and Urban Planning. 43(1998) 133-142. Poudyal, C.N., Hodges, D.G., Merrett, C.D. (2008). A Hedonic Analysis of the Demand for the Benefits of Urban National Parks. Land Use Policy. 26 (2009) 975-983. Richardson, S. S., Reed, V. N., Joseph, L. M. (1990). The Laws of Katsina State of Nigeria. Volume 1. 83 Richardson, S. S., Reed, V. N., Joseph, L. M. (1990). The Laws of Katsina State of Nigeria. Volume 2. Salele, N. (1998). Understanding the Dynamics and Parameters of Nigeria’s Pastoral Society: A Case Study of Rugu National Park. Doctor of Philosophy. Bayero University Kano, Nigeria. Trochim, M. K., (2006). Introduction to Evaluation. (6thed). London. Bath Press. Trzyna, T., (2003). The Urban Imperative: Urban Outreach Strategies for Protected Area Agencies. Proceedings of a Workshop at the World Parks Congress., Durban, South Africa. United Nations. (2000). Global Environment Outlook. Earthscan. London. United Nations. (2003). Compiling the UN List of Protected Areas: Criteria for Inclusion on the 2003 UN List. 5th World Parks Congress in Durban, South Africa. United Nations. (2004). Human Well-being and Ecosystem Services: Exploring the links. Nairobi, Kenya. United Nations. (2005). World Data Base on Protected Areas: Incorporating the UN List of Protected Areas. Published for the World Parks Congress. Velarde, J. S., et al. (2005). Valuing the Impacts of Climate Change on Protected Areas in Africa. Ecological Economics. 53 (2005) 21-33. 84 APPENDIX A LAWS The Laws of The Katsina State of Nigeria In force on the first day of January, 1990. Prepared by. Professor Sam Scruton Richardson, A.O, C.B.E. (Oxf). Sir Niggel Vernon Reed, C.B.E, T.D., L.L.B. (NZ). A Law for the Preservation and Control of Forests. NN 1963. Cap. 44. KDSLN 5 of 1982. KTSLN 1 of 1987. This law may be cited as the Forestry Law. PART 1- PRELIMINARY The civil service commission or the local government service board, may appoint such officers as may be considered necessary for the purpose of giving effect to the provision of this law. (Appointment of forestry officers). 1. In this law unless the context otherwise requires. (Interpretations) “forest” includes government forest reserves and protected forests, local government forest reserves and protected forests, and communal forestry areas; “enclave” means an area completely surrounded by a forest reserve and excluded from that forest reserve by an order made under this law. “community” means any group of persons occupying any lands in accordance with and subject to customary law. “commissioner” means the state commissioner for the time being charged with the responsibility for forests. “communal forestry area” means any land within the area occupied by a local community which land constituted a communal area under this law. “forest growth” includes anything growing or to be grown on land other than agricultural crops. “forestry officer” means any officer of the forestry division of the ministry of animal and forest resources or any officer appointed under section 3 for the purpose of giving effect to the provision of this law 85 “chairman of the local government” means the chairman of the local government council of the area within which the area, or the council in question, is situated. “forest produce” includes a. Timber, firewood, charcoal, rubber, gutta percha, latex, wood oil, gum, resin, natural vanish, tanning extracts, tanning barks, fruits, fibres, bark, and lac. Whether found in or brought from a forest or not. b. Trees and all other parts or produce of trees not otherwise herein mentioned, Plants, including climbers and grasses, creepers and all parts or produce of such plants. Wood ashes Peat surface soil and minerals other than minerals within the meaning of any enactment regulating the working of minerals Gravels, limestone, rock and laterite. Honey, beeswax, guano, silk-cocoons, humus and all produce from animals. When found or brought in the forest. “forestry property” means any stock, stores or materials owned by the government or a local government and used or intended to be used in any forest operation or any forestry work, and includes boundary marks and pillars, boundary or survey beacons or signs, name plates, machinery, scientific instruments, implements, tools, buildings, tents, fences, vehicles, roads and bridges. “tress” include palms. “forest reserve” means any area constituted a forest reserve under the law or under any enactment repealed by this law, which shall not have ceased to be a forest under any enactment. “girth” means the circumference of a tree measured either at height of four feet six inches from the ground measured at one foot above where the highest buttress merges with the bole. 86 “inquiry” means any inquiry by a reserve settlement officer. “minor forest produce” means any forest produce other than timber. “protected forest” includes a. any area declared to be, or constituted as protected forest under this law. b. any area proposed to be reserved, the preliminary notice in regard to which has already been published. “timber” includes all trees, whether standing, fallen or felled, stumps of trees and all wood, whether or not cut up of fashioned or hallowed out for any purpose. “to take timber” means to fell, lop or girdle trees or to carry away any timber from the lands upon which the trees have fallen or been felled, whether the trees have felled by cutting or by removing the soil from the roots or by any other method or combination of methods. “Working plan” means any plan of operation or work on any area whether in a forest or not so decided upon and described as such by the chief conservation of forest Preliminary Procedure for Constituting Government Forest Reserves. (notification of intention to create a reserve and appointment of reserve settlement officer). 2. 1. Before constituting any lands a government forest reserve a notice shall be published by the governor in the state gazette. a. Specifying as nearly as may be the situation and limits of the lands b. Declaring that the lands now form a protected forest c. Declaring whether the land are at the disposal of the government or are lands coming within section 4 (1) (b). d. Declaring that it is intended to constitute such lands a government forest reserve, either for the general purposes of government or for the particular use and benefit, wholly or in part, of any class of persons or for the benefit of any community or authority. e. Appointing an officer, hereinafter referred to as the reserve settlement officer, to inquire into and determine the existence, nature 87 and extent of any rights claimed by or alleged to exist in favour of any person or communities or brought to the knowledge of said officer affecting the lands or any other rights in or over the lands which it is proposed to constitute a government forest reserve. 2. If for any reason the reserve settlement officer appointed under this section is unable to perform his duties, the governor may, by notice in the state gazette, appoint any person to act on his behalf or as successor; such notice may have retrospective effects for a period not exceeding one month. 3. (Notice of inquiry). Upon publication of notice aforesaid the reserve settlement officer shall. a. Immediately cause the particulars contained therein to be made known in district or districts in which the lands are situated by causing the same to be read and interpreted in the local language in every area court in the said district or districts and also by far, as far as he considers essential, informing the chiefs of the communities dwelling on, and the local government having jurisdiction over, the lands aforesaid in writing, and b. Fix and, in the manner aforesaid, make known a period within which and place to or at which any person or community claiming any right in or over or affecting the lands which it is proposed to constitute a forest reserve shall either send in written statement of claims to him or appear before him and state orally the nature and extent of their alleged rights. The Inquiry 4. (Duty of reserve settlement officer at inquiry). 1. As soon as possible after the expiration of the period fixed by the reserve settlement officer he shall-: a. Inquire into and determine the limits of the lands specified in the notice aforesaid b. Determine the nature and extent of any claim or alleged rights affecting the land which have been preferred or brought to his notice. 2. The reserve settlement officer shall keep a record in writing of a. All such claims and alleged rights 88 b. All objections which may be made to such claims or alleged rights, and c. Any evidence in support of or in opposition to any claims or alleged right. 5. (Reserve settlement officer to have judicial powers.)For the purpose of the inquiry the reserve settlement officer shall have all the powers conferred upon a district judge. 6. (Reserve settlement officer may sever or join claims.) The reservation settlement officer may at any time during the inquiry join any number of vlaims or server any claims joined and in his judgement may give a decision which may join any number of claims or sever any claims which were formerly joined. Judgement 7. (Publication of judgement on completion of the inquiry). 1. Upon completion of the inquiry, the reserve settlement officer shall deliver his judgement, describing the limits of the land specified in the notice aforesaid and setting forth, with all such particulars as may be necessary to define their nature, duration, incidence and extent, all claims and alleged rights preferred or brought to his knowledge in respect of the lands and admitting or rejecting the same wholly or in part, and shall fill it at the land registry. 2. A notice shall be published in the state gazette specifying the land which it is intended to reserve, the privileges concede in respect of such lands and stating the special conditions intended to govern the reservation thereof. In addition such notice shall be made known so far as may be practicable to every person who, and the head of any community which, preferred any claim or in respect of which any claim was brought to the knowledge of the reserve settlement office. Appeal 8. (Appeals from judgement of reserve settlement officer.) 89 1. Any person who has made a claim on his own behalf, or where a claim has been made on behalf of the community may, within three months of the date delivery of the judgement, appeal to a district judge against that portion of the reserve settlement officers judgement which affects his claim or the claim made on behalf of the community which he represent. 2. An appeal shall lie to the high court within whose area of jurisdiction the forest reserve is situated from decision of a district judge on appeal against the judgement of the reserve settlement officer within thirty days of the date of the decision appealed against. The decision of the high court shall be final. Constitution of the Forest Reserve. 9. (Order of the governor constituting the forest reserve.) 1. The governor may make an order constituting the lands in respect of which an inquiry has been held a government forest reserve at the expiration of three months from the date of publication of notice in the state gazette under section 10. Provided that if an appeal has been made against the judgement of the reserve settlement officer no such order shall be made until such appeal has been determine or until the expiration of the time within which an appeal may be laid. 2. Such order shall, subject to the provisions of sub-section (3) set forth a. The limits of the lands which constitute the reverse; and b. All rights affecting the same as set forth in the judgement of the reserve settlement officer or established by the court upon appeal from such judgement; and c. Such additional rights as the governor shall consider it just and equitable to allow notwithstanding that such rights have not been allowed in the judgement of the reserve settlement officer. 3. Such order shall not include therein such rights as may have been allowed by the reserve settlement officer but which have been subsequently modified or extinguish as hereinafter provided and where the boundaries of the reserve have been modified as hereinafter provided the order shall set forth the boundaries as subsequently determined. 90 4. Such order shall be published in the state gazette and be made known in the same manner as was the judgement of the reserve settlement officer. 5. From the date of publication of such order in the state gazette such lands shall be a government forest reserve. 6. Any order made under this section may be revised or modified by the governor and such revision or modification may be given retrospective effects. 7. In any revision or modification made by the governor under subsection (6) the governor may, after such inquiry, if any, as he shall in his decision think fit:a. Exercise the powers conferred upon him by subparagraph (ii) of section 13: b. And such additional rights as he shall consider it just and equitable to allow notwithstanding that such rights had not been allowed in the judgement of the reserve settlement officer. Modification of the Reserve settlement Officers Judgement 10. (Rights may be extinguished or modified by commissioner). Where the reserve settlement officer has admittedly wholly or in part any right or claim and in the opinion of the commissioner the exercise of such right or claim or any part thereof:a. Would stultify the objects of any forest reserve. b. Would seriously hinder the efficient working of any forest reserve, or c. Would do serious damage to any forest reserve. The commissioners:I. May extinguish any such rights or claim and shall either give monetary compensation, grant in exchange similar rights on other similarly situated land either within or without the final boundaries of the forest reserve; II. May confine or restrict any right or claims to certain areas either within or without the forest reserve or the exercise of such rights to certain times of the year, or III. May adopt wholly or in part any one or any combination of the above methods of dealing with matter. 11. (Reserve may be made to exclude areas over which claims are admitted). 91 If the reserve settlement officer has admitted wholly or in part any right on any area which in the opinion of the chief conservator of forest could be excised from the reserve without materially altering the objects of the reserve, the governor may so amend the boundaries of the reserve or he may create such excluded areas or enclaves within the boundaries of the reserve. Provided that in altering the external boundaries of the reserve the officer shall not include any area which lies outside the original boundaries set out in the notice of the proposed reserve published in accordance with the provision of section 5. Further provisions Affecting Rights 12. (Government commissioner may close existing rights of way and water courses if alternatives exist). In any government forest reserve the commissioner may close any right of way of water course. Provided that in his opinion another right of way or watercourse equally convenient already exist or is provided. 13. (Extinguishment and revival of rights.) Every right in or over land in respect of which no claim shall have been made to the reserve settlement officer, or of which no knowledge shall have been acquired by that officer before delivery of his judgement shall be extinguish. Provided that if any person shall, within one year of the date of delivery of final judgement, claim and satisfy the commissioner that he was possessed of a right in respect of which he might have made a claim, and that through ignorance of the fact that an inquiry was being held or for other sufficient reason he failed to make such claims, the commissioner may direct-: a. That such right shall be revived b. That such claim shall be modified or extinguished in accordance with the provision of section 13. 14. If any right within a forest reserve shall not have been exercised for a period of ten years it shall be deemed to be extinguished. 15. It shall not be lawful for any person to alienate any right, affecting land included in a forest reserve, which has been established before the reserve settlement officer or before a court under section 11 or revived under section 92 16, by sale, mortgage or transfer without the consent of the commissioner first had and obtained. Any such sale, mortgage or transfer effected without such consent shall be null and void. 16. During the period between the dates of the publication by the governor of the notice of his intention to create a government forest reserve and of the order of governor constituting the reserve-: a. No right shall be acquired in or over the land comprised within such notice otherwise than by succession or under a grant or contract in writing entered into with the approval of the governor, and b. Save as hereinafter provide:I. II. III. No new house shall be built No trees shall be cut No forest produce shall be removed. Provided that nothing in this section shall be deemed to prohibit any act done with the permission in writing of the local government or a forestry officer of a rank not below that of assistant conservator of forest. Miscellaneous 17. (Power to reserve) Replaced by KDSLN 5 of 1982. 18. The governor may by order direct that from a date named therein any lands or any part thereof constituted a government forest reserve or a part of such reserve and thereupon from such date such lands shall cease to be a government forest reserve or a part of such reserve. Provided that the rights, if any, which may have been extinguished therein shall not revive in consequence of such cessation. PART 3- GENERAL PROVISIONS Entry upon lands 19. (Marking of boundaries. KDSLN 5 of 1982.) 93 Any person required so to do by the commissioner for local government in consultation with the ministry responsible for forest conservator of forests with necessary workmen may enter upon any land for the purpose of erecting any beacons or demarcating or cutting any boundary lines within and around any land which it is proposed to constitute a forest reserve or a protected forest and around any portion of land included as enclaves. 20. (Improvement of forest generally) Any forestry officer not below the rank of assistant conservator of forest may enter upon any land and may cut out and destroy any diseased, dead or dying tree or any tree likely to cause damage to any forestry property or to life or property. 21. (Prevention of offence). It shall be lawful for any forestry officer, or police officer to prevent the commission of any forestry offence. 22. (Power to exempt certain classes and districts). The governor may by notice in the state gazette withdraw from the operation of all or any of the provisions of this law any class of persons or any tribe or part of a tribe, or any area specified therein, either for the period mentioned in the notice or without period assigned. Miscellaneous 23. It shall be lawful for the commissioner to take from any local government forest reserve or protected forests any forest produce which may be required for public purposes upon payment of a fair and reasonable price thereof which price shall not exceed such fees and royalties as may be specified in regulations and are generally applicable in respect of the reserve or protected forest hence the forest produce was taken. 24. (Disposal of fees and royalties). 1. All fees received under this law shall be paid by the officer receiving them into the treasury of the state save that fees payable in respect of any local government forest reserve or any other area which the governor may y notice in the state gazette prescribed as an area in respect of which fees 94 are payable to the local government, shall be paid by the officer receiving them direct to the local government. 2. Royalties shall be paid to the person or persons entitled to receive them. Regulations 25. The governor may make regulations for all or any of the purposes following and may specify the area or areas to which all or any regulations shall apply. 1. Prohibiting or regulating the taking of forest produce or of any specified kind of forest produce on land at the disposal of government or communal lands. 2. Prohibiting the sale and purchase of forest produce or of any specified kind of forest produce by any person other than the holders of licences and permits granted under this law, or by any other persons or by any classes of persons specified in the regulations 3. Prohibiting the sale, purchase and possession of forest produce taken, collected or prepared in contravention of this law. 4. Prohibiting the destruction of, or any act which may tend to the destruction of or cause injury to, any forest produce or forest growth or forest property in any forest reserve or on lands at the disposal of the government or communal lands. 5. Regulating the grant and prescribing the form that any licences or permits may take in any particular case. 6. Prescribing the procedure for fixing and making known to the public the fees to be paid on the application for and the grant of any licence to permit and the royalties and fees to be paid by the holders thereof 7. Providing for the collections, payment and disposal of fees, royalties, tolls and costs of survey and demarcation. 8. Providing for the survey and demarcation of forest reserves and forests 9. Regulating the marketing of timber and the manufacture, use and possession of marking instruments. 10. Regulating the taking, collection and preparation of forest produce. 11. Providing for the seizure, detention and disposal of timber or forest produce taken, collected, prepared, sold, purchased, possessed or not 95 marked, in contravention of this law or in respect of which any offence against this law has been committed. 12. Requiring the holders of licences and permits to render returns and accounts and to submit their books for inspection. 13. Providing for the termination, revocation and forfeiture of licences and permits. 14. Regulating the transit of forest produce by land and water and by different means and classes of transport 15. Regulating the salving and disposal of drift timber 16. Providing for the establishment and maintenances of nurseries and for the forestation of lands, the preservation and production of forest produce and the introduction of new species of trees or other forest produce. 17. Providing for the management, utilisation and protection of forest reserve. 18. Prescribing the powers and duties of forestry officers 19. Authorising the payment of grants and bonuses out of the public revenue for the encouragement of forestry. 20. Generally for giving effect to the objects and purposes of this law. 26. The governor may make regulations for imposing tolls on forest produce or any kind of forest produce conveyed on any inland water ways opened or improved by the government. 27. The governor may by notice in the state gazette exclude from the operations made under section 46 or 47 any area prescribed in such offence. Offences and Legal Procedure 28. Whoever in any forest reserve, except with the authority in writing of the prescribed officer a) Takes any forest produce b) Uproot, burns, strips off the bark or leaves from, or otherwise damage any tree 96 c) Set fire to any grass or herbage, or kindles a fire without taking due precaution to prevent its spreading d) Smoke or lights a fire in any part of a forest reserve within which, or at a time when, smoking or the lighting of fires is prohibited by an order of the commissioner or a local government. e) Pastures cattle or permit cattle to trespass f) Digs, cuts, turns or cultivate the soil or makes a farm or plantation. g) Trespass in any part of the forest reserve in which trespass shall be prohibited by an order of the commissioner or a local government or during any period specified in an order of the commissioner or a local government. h) Construct any dam or weir across any river or stream or otherwise obstruct the channel of any river or stream i) Resides or erects any building j) Hunts or fishes k) Damages in any way or destroys any forestry property, shall be liable on summary conviction, to a fine of two hundred naira or to imprisonment of twelve months or both. 29. Whoever within a protected forest, except with the authority in writing of the prescribed officer a. Uproots, fell or otherwise damages any protected tree of over two feet in girth b. Otherwise than during the period of year allowed for this purpose, either sets fire to or allow fire to spread to any forest growth unless such forest growth is being or has been felled for farming purpose. c. Contravenes any of the provisions of paragraph (b) of section 19. Shall be liable on summary conviction to a fine of one hundred naira or be imprisoned for 6 months and in addition thereto may required by the court to pay a sum equivalent to the fees and royalties payable on any forest produce removed or damaged and also such amount, if any, as the court may consider just as compensation. 30. Any forest officer or police officer not below the rank of assistant superintended of police may himself or by any government employee acting 97 under his directions, seize any forest produce reasonably suspected of having been unlawfully obtained or removed. 31. It shall be lawful for any forestry officer to arrest without warrant any person who may be reasonably suspected of having committed any offence under this law, if such person refuses to give his name and address or gives a name and address which is believed to be false, or if there is reason to believe that he will abscond. Provided that any person so arrested shall be taken before a magistrate or to the nearest police station without necessary delay. 98 Appendix B: Questionnaires 99 100 101 102 103 104 105 106 107 108 109 110