South Asian Research Publishing Organization (SARPO)

Sotolu Rashidat Omolola*, Orsar Tyonzughul Joe, Tyowua Benjamin Terungwa

Department of Wildlife and Range Management, College of Forestry and Fisheries, Federal University of Agriculture, Makurdi, Nigeria.

P.M.B. 2373, Makurdi, Benue State, Nigeria

INTRODUCTION

Conservation in the 21st century needs to expand its dimension along spatial, temporal, and social scales owing to species and ecosystems extinction. Ravaging habitat loss has been highlighted to be responsible for approximately 80% of globally threatened species (Ervin et al., 2010) and has triggered concerns locally as well as globally towards evolving approaches to conservation. Strategic and timely expansion in the landmass of protected areas is the most immediate and effective response to the imminent biodiversity crisis in the world today.

Humans rely on vital ecosystem functions of protected areas. As an example, 33 out of 105 of the world’s largest cities source clean water from protected areas (Ervin et al., 2010). Economies of many developing countries especially in Africa; Latin America and The Caribbean, depend solely on tourism revenue associated with protected areas. As the human population booms, there is a resultant escalation in demand for a resource with its associated loom in tension due to inappropriate resource allocation and ecological injustice.

Prior to the 19th century, there has always been a ‘Fortress Conservation’ where people are completely excluded from nature. The birth of Yellow Stone National Park in the late 19th century, precisely 1872 put a turn in the paradigm. The experimental park was not completely participatory as it ejected locals from the resource though putting a dot on economic development.

However, there has been a metamorphosis of approaches since then, in the management of natural lands under political protection. Political protection comes with a level of enforcement. Renewable natural resources protection is not an exception. Rigid; and flexible; the result is always significant. In the bid to save existing protected areas and future ones from imminent extinction, this review serves as a reference for highlighting the critical factors that are fundamental to a successful conservation project.

This would be through addressing the rationale behind the participatory approach to conservation; the significance of policy in nature protection; and the necessity to strike a balance between conservation and rural development all in an atmosphere that spells locals’ participation and experiences in conservation projects under current policy environments. Rural communities of course benefit from biodiversity as explained by Ervin et al. (2010) many great cities and municipals across the globe tap their clean water from protected areas. However, this does not negate some externalities borne by the same people as a result of its protection. Overlooking this will turn the park into an ordinary print.

Significance of Protected Areas in Sustainable Conservation

Parks across the globe render not only ecosystem functions but also social, political, cultural, economic and peace functions. They are pools of biological diversity as well as zones of trade and cultural continuity. Some of the rural development strategies are summarized in Figure 1 where environmental education seems to be the most applied strategy. Although, it may not be as acceptable to park inhabitants as much as local empowerment would (Sotolu et al. 2016).

Figure 1. Strategies for Rural Development in Protected Areas in Brazil

Source: Adapted from Chiaravalloti et al. (2015) Key: 1: conservation unit’s job; 2: income generation from biodiversity exploitation; 3: environment education; 4: empowering local associations; 5: scientific research; 6: participatory monitoring. International Efforts towards Conservation and Development Parties to the Convention on Biological Diversity (CBD) in February 2004 committed to a strategic set of actions known as the Programme of Work on Protected Areas with the goal of establishing comprehensive, ecologically representative, and effectively managed networks of terrestrial protected areas by 2010 and marine protected areas by 2012.

Measurable targets and specific timelines were set for the programs and proposed to be a guiding framework for protected areas in the next decade. Presently, a global network of protected areas is directly or indirectly responsible for employment generations that rival in number with those provided by some global economy icons (Ervin et al. 2010).

Global Environmental Facility (GEF), the operating entity of the financial mechanism of the CBD, is globally recognized as the world’s leading facility for aiding nations in the implementation of their obligations under the CBD Programme of Work on Protected Areas.

Enhancing the sustainability of protected area systems is pivotal to the GEF biodiversity strategy. This is achieved through improving: financial sustainability; protected area coverage, representativeness, and connectivity; and protected area capacity and management effectiveness. Over 2,300 protected areas covering a land area of more than 634 million hectares have benefited from GEF funding. GEF has solely invested 1.89 billion in protected areas with an additional 4.5 billion in co-financing from project partners.

United Nations Development Programme (UNDP), one of the implementing agencies of GEF, is the world’s most significant contributor of technical assistance to protected areas. Since the ratification of the CBD Programme of Work on Protected Areas in 2004, UNDP has supported over 700 protected areas in 55 countries, covering nearly every goal, target and action of the Programme of Work on Protected Areas. UNDP has helped to improve protected area management effectiveness across more than 85 million hectares and to establish new protected areas covering more than 15 million hectares.

UNDP’s rationale for making such a significant investment in protected areas is simple: protected areas and community-conserved areas together represent as much as a quarter of the world’s land surface, and this land and sea mass represent an enormous potential to contribute to human development by securing ecosystem services, maintaining the livelihoods of hundreds of millions of people, and buffering humanity from the impacts of climate change. Nations across the globe benefit from activities of these international bodies and more.

Strength of a Legal Resolve

When wild animals raid farmlands within natural areas, farms owned by the impoverished locals; compensation for loss is not paid (Sotolu et al. 2017); locals are excluded from park management; and poverty lingers on in the communities, there is bound to be conflict not only involving park managers and the rurals (Ayivor et al. 2013), but also between the different land users in those communities. Hunting; encroachment; killing wild animals for their trophies, all lead to arrests and forced evictions which have raised eyebrows of the local victims and are seen as an impediment to putting a stop to illegal activities (Ayiyor et al. 2013).

This is because the people feel embittered, cheated and taken advantage of, on a land that was originally theirs. Human-wildlife conflict with its associated retaliatory killing of wild animals (Sotolu et al. 2017); Illegal Wildlife Trade; farmland encroachment into parks; and more will all need a resolve that involves legal facet as well as dialogue. As explained by Sotolu et al. (2016), park communities are unlikely to be satisfied with enforcement and park protection laws. Until and unless unlimited access is given for resource exploitation, there will always arise issues of concern between nature and people. Limitless access, however, is uncompromisingly unachievable, since no system

involving people can be sustainably functional without spelling out offenses with associated penalties that should be effectively instituted. From poaching and disagreement over park boundaries in Zakouma National Park in Chad, to eviction from Digya National Park in Ghana (Ayivor et al., 2013), to retaliatory killing of wild animals in Cross River National Park in Nigeria (Sotolu et al. 2016), friction continues and would always require resolution.

Dot on Participatory Conservation

Protected areas are vital to reducing, if not putting a halt to, biodiversity loss. They are in situ repositories of genetic materials and ancient relics of landscapes that are pivotal to socio-cultural, aesthetic, spiritual, and traditional relationships of human existence (Harmon and Putney, 2003). However, these roles are still blinking red hence, the terms ‘paper park’, ‘island parks’ describing failures (Laurance, 2008). Preservationists’ approach of ‘fences and fines’, ‘fences and guns’, and ‘colonial approach’ viewed people as exploiters of biodiversity and excluded them from resource protection (Vig and Kraft, 2012). A serious issue in nature protection is a conflict between protected area managers and support zone communities.

These include disagreements and disputes over access to resources and their control involving arrests, prosecutions, violent confrontations, and even deaths (Ayivor et al., 2013). As there are benefits from a collective system for multiple objectives of resource management, so also are there challenges to be overcome as depicted in Table 1.

Table 1. Potential benefits and risks in managing protected areas for multiple objectives.

Source: Adapted from Ervin et al. (2010)

Case Scenarios

From Ayivor et al. (2013), it was learned that ‘In 2006, a border dispute in Kyabobo National Park, Ghana resulted in the tragic death of two Wildlife Officials’ (Ghanaweb, 2006). Another incident occurred in Bui National Park, also in Ghana in 2007, when a poacher lost his life for resisting arrest and attacking a Wildlife Official (Ayivor, 2007). Local communities attacked Wildlife Officials and burnt down one of their campsites. Both incidents were resolved through the intervention of local chiefs and Wildlife Officials from the national headquarters.

In addition, ‘In 1989, 2002 and 2006, three major eviction exercises were carried out in Digya to move mainly migrant communities and their families (squatters) who were allowed entry into portions of the park by local chiefs. These chiefs claimed that cash compensation for the expropriation of their lands had been paid to wrongful claimants and, therefore, considered themselves as rightful owners of these portions of the park.

The exercises mostly targeted squatters who often resisted eviction, thus, compelling Wildlife Officials to seek the support of the military to evict them. During the 2006 eviction exercise, nine people lost their lives through a boat accident that occurred while they were being ferried across Volta Lake. The eviction exercise of 2006 was abandoned due to public outcry and a court injunction (Myjoyonline, 2006).’

Metamorphosis of Global Approaches to Conservation

In the bid for biodiversity protection, national parks were established across Sub-Saharan Africa primarily for hunting and tourism by the colonials. This did not go without the expulsion of the original custodians of the resource- the locals (Adams and Mulligan 2003; King

2007). The late 19th century witnessed the birth of a reconsideration of the ‘fortress’ approach by the establishment of Yellowstone National Park in 1872 in the United States of America. It was an ‘experiment park’, based on attempting to merge conservation with economic development (King, 2009). Of course, the transformation was not sudden but gradual, as even at this time people and the park were still mutually exclusive. Colonialism and the increasing promotion of the need for sustainable development aided further designation of nature for conservation across the globe (King, 2009).

Concern over loss of biodiversity and the fear of consequent extinction has greased the push for the establishment of more protected areas worldwide. From the beginning to the mid-20th century which marked the end of the Classic Model of Protected Area management (Table 2), a meager 600 protected areas were in operation.

In about 1999, there were nearly 3000 protected areas (Ghimire, 1994). Approximately 5% of the earth’s landmass was protected as a result of more than 25,000 protected areas towards the end of the 20th century characterized by the era of the Modern Model of protected area management as shown in Table 2. Currently, over 11.5% of the planet’s landmass is protected due to the creation of more than 100,000 protected areas (IUCN and UNEP, 2003). The Emerging Models as against Traditional models (Figure 2) have not been receiving so much attention from parks all over the globe (Ervin et al. 2010).

Regions of higher biological diversity have been established to also be areas of higher human population densities which manifest higher rates of social and economic poverty (King, 2009) but higher levels of cultural diversity. Thus, raising eyebrows over the alienation of the rural from the resource through which they derive sustenance. This resultantly makes the implementation of management strategies more difficult (Sotolu et al. 2016).

Table 2. The succession of models in protected areas management.

Source: Ervin et al. (2010)

Figure 2. Traditional versus Emerging Management Planning Issues As Conservation Strategies

Source: Adapted from Ervin et al. (2010)

Realization of the significance of the locals’ social and economic empowerment through conservation has led park management in the 21st century to pay more attention to that angle (Figure 3).

Impediments to a Collective System

Nature areas across the globe are characterized by human population pressure, putting a lot of stress on biodiversity through overexploitation. As noted by Ayivor et al. (2013), the high human population density of indigenous fishing and farming communities in addition to migrants who moved into the area with the creation of the Volta dam surround Digya National Park in Ghana, putting socio-economic pressure on the park.

Some of these are poverty, illegal entry, poaching and livestock grazing among others. Adequate well-trained and equipped staff per unit patrol area is essential for effective enforcement. This capacity is lagging especially in West African parks. Ghanaian Digya National Park and

Shai Hills Resource Reserve had 0.016 and 0.198 effective patrol staff per km2and operational budget of US$2.5/km2 and US$58/km2 respectively (Jachmann, 2008), while James et al. (2001) estimated the ideal cost for effective protected area management to be US$250/km2. Park officers often decry insufficient funds and equipment to access difficult terrains, sometimes requiring choppers or high-powered motorboats over lakes (Ayivor et al. 2013).

Figure 3. Evolution of park management planning issues across the globe.

Source: Adapted from Ervin et al. (2010)

KEY: Clim Adap- Climate Change Adaptation; Sus Liv- Sustainable Livelihood; Eco Serv- Ecosystem Services.

Figure 4. Schematic representation of the people-nature relationship.

Figure 5. Schematic representation of a people-park policy scenario.

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Figure 6. Schematic representation of a people-centered conservation initiative.

Ecological justice describes the fair treatment and meaningful involvement of all people regardless of race, color, national origin, or income with respect to the development, implementation and enforcement of environmental laws, regulations and policies. The participatory approach that fringes on ecological injustice are bound to collapse and lead to mistrust. Benefits from protected area management should be equitably shared and its challenges collectively accounted for. As narrated by Ayivor et al. (2013), an elderly woman reported ‘I derive no benefit from the park but instead crop losses.

When I get to my farm and encounter an elephant feeding on my crops, I can only create noise to drive it away. If that fails, I just look on helplessly as my farm is destroyed. Often, I get so devastated and have no option but to weep all the way back home. In another narration, locals were reported to have complained that, ‘We were served an eviction notice without us being told where to go. Two weeks after the notice, we were forcefully evicted and were not allowed even to salvage our belongings, including food crops and livestock. Wildlife officials were highhanded on us and there was no one to speak for us.

We had to move at night to the opposite side of the Sene River with our children without any protection against the harsh environment. We had to pitch tents using improvised local materials as temporary houses…….’ Situations like this do not exclude fatalities as was described during an eviction exercise in 2006 when settlers were overloaded in privately operated boats leading to deaths of tens of evacuees in a protected area in Ghana (Ayivor et al. 2013). The conservation that risks the lives of the communities will meet with public outcry and violence.

Synergy Itself

Most African nature lands were put under protection by the colonials who ruled their respective countries before the 1960s when those nations got their independence. Prior to park protection, people exploit biodiversity without fear of prosecution. Although resource use in most rural environments was guided by traditional and customary laws which were not based on empirical deductions, this kind of protection was not going to yield sustainable results as it did not involve arrest or prosecution. Moreover, traditional protection of resources only existed in few natural areas, not in all. At these periods, people relied solely on nature for sustenance.

There were killing of wild animals (hunt and kill); grazing by livestock; logging; wood collection; non-timber forest products (NTFPs) harvesting; farming; fishing; and encroachment which were all unrestricted (A). Wildlife on the other hand was a part of the people’s cultural and traditional setting (B). Then, issues were only between people and nature as depicted in Figure 4.

After protection, the policy comes in to act on both the people and the resource itself. People exert more pressure on nature alongside encroachment and urbanization, seeing the resource as a ‘lost glory’ (C). Wild animals raid locals’ farmlands; carnivores kill and transmit zoonosis to livestock and then to people (D). The policy sought to protect nature (E) while restraining the locals (F). The resultant scenario is that where people are evicted from ‘their lands’ and alienated from resource management; conflicts arose between park managers and rural communities over illegal resource exploitation; arrests are made, and offenders are prosecuted (G) although resources are protected and ‘fortress conservation is achieved (H) as seen in Figure 5.

There had to be adjustments on the part of the people and nature managers in order to bring a synergy tailored towards a combined and correlated action aimed at bringing harmony into the system with minimized friction. This requires inputs from other stakeholders as well – government; non-governmental organizations (NGOs), local and international conservation bodies; conservation researchers and research institutes; the private sectors; and the like, focusing people at the centre of conservation programs.

This will give locals a sense of ownership and stewardship over the resource, hence regulating exploitation to ensure sustainability (I). The resource remains a part of the people’s culture (J); policy protects lives, limbs (K), and nature (L); conservation goal is achieved (M), and people no more see park management as infringement but realize the need to support conservation efforts (N). Conservation-hinged benefits provided to the people on a regular basis would ensure that resources are safe with minimal enforcement and patrol duties as seen in Figure 6.

CONCLUSION

Biodiversity is an endowment for human development renewable, regenerative, but exhaustible and hence should be jealously protected. Parks are managed by people while policy guides and guards both towards a peaceful co-existence. Parks require adequate, well-armed paramilitary functions per square kilometers of the park territory for effective enforcement. People require alternative means of livelihood and involvement in park management for efficient participation.

The policy requires to be flexible towards sustainable conservation. Dialogue is a vital tool in finding ways forward. Regular outreach programs between the park and the people would create a soft pedestrian for mutual trust and cooperation. Creating alternative livelihoods like beekeeping, handicrafts using local materials and small-scale livestock production, would go a long way in synergizing economic development and sustainable conservation within the limits of effective enforcement.

Renewable natural resource under political and legal protection is more likely to be sustainable if guiding policy and principles are all-encompassing and effectively implemented. From the on-going, factors responsible for both the success and failure of conserving biodiversity in National Parks in various contexts were socioeconomic and cultural. These realizations pitch that future conservation approaches in parks should place more emphasis on the human dimension of biodiversity conservation rather than purely scientific studies of species and habitats.

REFERENCES

Adams, W. M.; and Mulligan, M. Decolonizing Nature: Strategies for Conservation In a Post Colonial Era, 1st eds.; Routledge: London, 2003; 320 pp.

Ayivor, J.S. An Exploration of Policy Implementation in Protected Watershed Areas: Case Study of Digya National Park in the Volta Lake Margins in Ghana. Master Thesis, College of Arts and Sciences, Ohio University, Athens, USA, 2007.

Ayivor, J.S.; Gordon, C.; Ntiamoa-Baidu, Y.; Protected Area Management and Livelihood Conflicts In Ghana: A Case Study of Digya National Park. PARKS. 2013, 19(1), Pp 37-50.

Ervin, J.; Sekhran, N.; Dinu, A.; Gidda, S.; Vergeichik, M.; Mee, J. Protected Areas for the 21st Century: Lessons from UNDP/GEF’s Portfolio. UNDP Convention on Biological Diversity: New York; 2010; Pp 132.

Ghanaweb, (2006). Assailants of Kyabobo Park Guards would face justice DC assures, Regional News, Hohoe, Ghana. 2006-07-12.

Ghimire, K. B. Parks and People: Livelihood Issues in National Parks Management in Thailand and Madagascar. IDEAS. 1994. Dept of Development and Change, International Institute of Social Studies. 25(1), pp. 195–229.

Harmon, D. and. Putney A.D. The Full Value of Parks: From Economics to the Intangible. Lanham, MD (Imprint): Rowman and Littlefield Publ. USA, 2003, pp xii+347+iII.

IUCN and UNEP. International Union for Conservation of Nature and United Nations Environment Program. United Nations List of Protected Areas. GLAND. Switzerland: IUCN and UNEP. 2003.

Jachmann, H.; Monitoring Law-Enforcement In Nine Protected Areas in Ghana. Bio Cons. 2008, 141(1), pp 89-99. 2008.

James, A.; Gaston, K. J.; Balmford, A. Can We Afford To Conserve Biodiversity? BioScience 2001, 51(1): pp 43–52.

King, B. Geography Compass. 4(1).; Blackwell Publishing Ltd, Researchgate: Pennsylvania. 1, Conservation Geographies in Sub-Saharan Africa: The Politics of National Parks, Community Conservation and Peace Parks, 2009, pp 14-27.

King, B.H. Conservation and Community In the New South Africa: A Case Study of the Mahushe Shongwe Game Reserve. Geoforum. 2007, 38(1), pp. 207– 219.

Laurance, W. F. 2008. Theory Meets Reality: How Habitat Fragmentation Research Has Transcended Island Biogeography Theory. Biol. Cons. Elsevier. In Press. Myjoyonline.com; Volta Lake Disaster Survivors Appeal for Food Aid. http://www.myjoyonline.com/news. 2006

Sotolu, R.O.; Akanbi, A.O.; Tyowua, B.T. Impact of Human-Wildlife Conflict on Socio-economy of Support Zone Communities of Cross River National Park, Nigeria. Journ. Res. in For., Wild. and Env. 2017. Vol. 9(1). Pp 75-84. ISBN: 2141-1778.

Sotolu, R.O.; Tyowua, B.T.; Akanbi, A.O. Impact of Wildlife Policy on Management of Wildlife Resources In Cross River National Park, Nigeria. PAT June 2016; 12(1):181-191. www.patnsukjournal.net/currentissue.

Vig, N. J. and Kraft, M. E.. Environmental Policy. New Direction for the Twenty-first Century, 8th ed.; SAGE: Washington DC: 2012; pp 480.