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NGO Landscapes: Conservation in the Maya Biosphere Reserve, Peten Guatemala
by Juanita Sundberg

PLANETA FORUM

This article was published in 1997.


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Biosphere reserves have been promoted as ideal solutions for environmental degradation and poverty in Third World countries. This paper examines the prevailing biosphere reserve model and analyzes its implementation in the Maya Biosphere Reserve, in the PetĖn, Guatemala. I suggest that the biosphere reserve model encourages the creation of 'NGO landscapes,' in which local cultural and political structures are replaced by NGO structures.

THE BIOSPHERE RESERVE MODEL

Environmentalists and development planners have advocated a variety of conservation models in Latin American countries, to protect remaining wilderness areas from degradation and depletion. In an endeavor to address economic as well as environmental needs, UNESCO's Man in the Biosphere Program developed the biosphere reserve model as an alternative to prevailing conservation models (Batisse 1986). In the 1970s, the creators of the biosphere reserve model saw conservation as a technical issue; they believed that scientific research and resource management would solve existing environmental problems (Vernhes 1987). The initial model was based upon the assumptions of island biogeography, to ensure the viable reproduction of species within the reserve (Diamond 1975). Thus, the 1974 biosphere reserve model was designed to encompass a large circular area divided into a series of concentric zones--nuclear zone, multiple use zone, buffer zone--each having different ecological functions, uses, and management structures (Goodier and Jeffers 1981).

A review of biosphere reserves created between 1974 and 1983 revealed that the research conducted at reserves was of an academic nature and did not address the source of environmental problems. Therefore, the First International Biosphere Reserve Congress adopted the "Action Plan for Biosphere Reserves" in 1984, which states that biosphere reserves should be "models of the harmonious marriage of conservation and development" (UNESCO 1984). As such, the management plans are to include non- governmental organizations (NGOs), with projects designed to balance community needs with the conservation of natural resources. Today, biosphere reserves are commonly perceived as a viable strategy to promote sustainable development at the local level (Annis et al. 1992; Batisse 1986; Vernhes 1987).

Although the biosphere reserve model is very seductive, it poses many challenges to those involved in its implementation. First, the process of spatial abstraction imposes random boundaries upon a complex landscape. Secondly, the model attempts to de-politicize the relationship between three complex and dynamic phenomena, the state, NGOs, and local communities, and their relationship with the environment--which is "strategically relevant" to all three human institutions (Knapp 1991). Due to this process of abstraction and de-politization, the biosphere reserve model does not provide a framework for dealing with the many layers of complications which arise throughout the implementation process.

THE CREATION OF THE RESERVE

To examine the model's implementation, I conducted fieldwork in the Maya Biosphere Reserve, in the PetĖn, the northern most department of Guatemala. In the 1970s, the department experienced dramatic changes in population and land use practices due to the government's policy of colonization, drawing thousands of migrants. The population jumped from 25,207 in 1964 to an estimated 311,314 in 1990 (Schwartz 1990:11; SEGEPLAN 1993a:1). Widespread and rapid deforestation led to national and international concern for the PetĖn's ecology. With the encouragement of environmentalists and international lending institutions, President Vinicio Cerezo signed legislation in 1990, creating the Maya Biosphere Reserve, which encompasses approximately 1.6 million hectares of Guatemala's tropical lowland forest and wetland ecosystems. The Reserve is administered by the Guatemalan National Council of Protected Areas (CONAP), in coordination with the United States Agency for International Development, The Nature Conservancy, Conservation International, and CARE International.

The primary goal of the Maya Biosphere Reserve's Master Plan is the following: "...to yield a harmonious and sustainable development in the region, guaranteeing the stability of the present natural and cultural resources" (CONAP 1996:11). The estimated cost of the seven year implementation process is $22,410,000 (CONAP 1993). The three NGOs are charged with providing institutional and financial support, as well as promoting sustainable resource management and environmental education through participatory projects at the community level. The Reserve has attracted a plethora of other NGOs to the PetĖn.

NGO PROJECTS

Myriad complications have arisen throughout the implementation process. For example, each NGO claims jurisdiction over a portion of the Reserve, leading to a 'balkanization' of the landscape. Secondly, individual NGO projects are too localized, creating economic and resource disparities between communities. Thirdly, the Reserve's spatial boundaries create a resource division between the northern and southern PetĖn, undermining the goals of the Reserve by attracting migrants to the Buffer Zone. Finally, I suggest that NGO projects are leading to the homogenization of two critical social realms: local cultural landscapes and the political actors within them. Today I would like to discuss the creation of NGO landscapes by analyzing the effects of development projects on local cultural and political landscapes.

Cultural landscapes embody the identity of the people that inhabit a given geographical area--they are both the arena of cultural practices and are constituted by beliefs and practices that are constantly reproduced and contested (Cosgrove 1993). A cultural landscape retains personal memories of a place; yet, its significance moves beyond the individual to affirm group identity (Butzer 1994; Knapp 1994). Particular places are given significance, as are everyday practices. Local resources and farming practices, planting and harvesting calendars, as well as the overall understanding of how the ecosystem functions, all form an integral part of the culture and the cultural landscape. Changes tend to occur incrementally, and may not result from formal planning processes (Doolittle 1984; Williams 1990); these changes are gradually incorporated into the cultural landscape.

NGO projects are often designed to alter various aspects of a given cultural landscape. Through participatory projects, NGO personnel attempt to impart their vision of natural resource management, environmental education, and community structure, and replace existing patterns with improved and more efficient practices. The implementation of these projects leads to cultural landscapes which reflect NGO conservation and development goals, and risks undermining existing local resource management strategies and community structures. Just as Escobar suggests that the "'development encounter' produces forms of consciousness that are more the property of organizations and ruling groups..." (Escobar 1991), I propose that the conservation encounter produces NGO landscapes.

The people living within the Maya Biosphere Reserve practice shifting cultivation; many collect the three non-timber resources--chicle, all-spice, xate palm--which are sold on the international market. Most supplement their diet with local flora and fauna. These communities are approximately ten to twenty years old, dating from the initial colonization period. A recent study found that the migrants are experimenting with strategies to meet their changing needs, including agroforestry techniques (CARE 1993b). The NGO literature, however, portrays these individuals as recent arrivals, whose unfamiliarity with the tropical forest environment has led to inappropriate land-use patterns. These communities are the 'targets' of NGO projects in the Maya Biosphere Reserve.

Each NGO employs slightly different management techniques and prioritizes selected species. For example, Conservation International promotes natural forestry management which features the sustainable collecting of non-timber products, and encourages the harvesting of a wider variety of tree species for timber needs (CI 1994). The Swedish and Norwegian Conservation Project for Sustainable Development in Central America has developed a complex thirty year model for the harvesting of valuable timber species such as cedar and mahogany (CATIE 1992). These NGO landscapes are visibly different from the surrounding landscapes. Several years from now, it may be possible to map the Reserve by examining the type of forestry management associated with each NGO.

CARE'S DEMONSTRATION AREA

In the Reserve, CARE International's agroforestry project is generally regarded as the most effective because it makes use of local knowledge and strategies. CARE collected information on both ancient and current practices throughout the PetĖn; this information was used to develop an ideal and supposedly appropriate agroforestry system which is combined with subsistence agriculture and livestock (CARE 1993a, 1993b). Local strategies are reformulated according to Western notions of resource management, and returned to communities with introduced innovations. Extensionists present farmers with a static subsistence package. The Buffer Zone of the Maya Biosphere Reserve is dotted with replicants of CARE's idealized landscape. Although it includes local strategies, the project's methodology excludes individual innovation and incremental change, which may be essential features of traditional resource management. Finally, the project attempts to impose a homogeneous landscape in an area thriving with highly individualistic and ethnically diverse people.

NGO AUTHORITY

After the creation of the Maya Biosphere Reserve, officials from the Guatemalan National Council of Protected Areas (CONAP) and international development personnel arrived in the northern PetĖn to introduce the new hierarchy of power. This process has reshaped space and society. Although cultural landscapes embody "relationships of power and authority" (Hugill and Foote 1994), the biosphere reserve model tends to de-politicize local political landscapes. As such, NGO personnel also tend to gloss over community power structures and inter-personal power struggles (Brower 1992; Glesne 1984).

During the first phase of a community project in the Maya Biosphere Reserve, NGO personnel visit the village to assess the leadership structure and identify potential leaders (CARE 1994; IUCN 1994). Enthusiastic strong men and women who fit Western ideals of leadership are targeted, encouraged, and supported (Van Orman 1989). The existing social and political fabric is disrupted by the changes in power structures; community leaders and specialists are often replaced by new leaders who conform to NGO standards. This process may engender intense conflict at the local level. Furthermore, the community is reorganized according to people who agree or refuse to participate in NGO programs. NGOs then establish separate projects for men, women, and children, thereby altering inter-personal relationships. Finally, once the community becomes identified as an NGO community, signs are often set up to publicly proclaim the community's allegiance and NGO authority in the area.

An example of local political conflict comes from San JosĖ, a lake-side village composed of Maya-Itzaj and immigrants. In 1992, six Itzaj leaders established the BioItza, a forest reserve on thirty-six km2 of municipal land, and then sought outside assistance to protect the reserve and create park facilities. A botanist with support from the Austrian government promised one million dollars to the BioItza over a three year period. During this time, San JosĖ was undergoing a cultural revitalization movement, which included the Itzaj Maya Language Rescue Project - an attempt to teach the dying Itzaj language (Hofling 1996).

Local enthusiasm about language and cultural revitalization prevailed in San JosĖ until the situation came to a head in 1993, when the mayor was removed from office for selling timber from the Reserve and selling municipal land along the lakeshore to foreigners. Furthermore, the Austrian funding had been lowered to $500,000 and had not yet arrived (Hofling 1996). The BioItza guards were working without pay. The motives of the various project personnel became suspect; there was a political split between two Itzaj leaders involved in the language project and the BioItza. One man withdrew from the language project but remained active in the BioItza. The other took over the language project and withdrew from the BioItza. The locals were disillusioned with the leaders, as well as the outsiders. In the end, a much lower sum arrived in 1994. A year later, the Austrian was accused of embezzling funds from the BioItza. Today, San JosĖ continues to be embroiled in political conflict over this issue.

Another example from San JosĖ involves Ixchel, a local women's organization, involved in the cultural revitalization of Maya-Itzaj cosmology and agrotechnologies. Ixchel has a 30 year contract to rent 50 acres of municipal land on which to carry out their activities. In 1994, a Guatemalan NGO--claiming to have millions of dollars--approached San JosĖ's municipal leader (alcalde), promising to build a university specializing in tropical forest ecology and management. The NGO selected Ixchel's land parcel as their ideal starting point.

Tempted by the NGO's promises of grandeur and financial reward, the alcalde began to pressure Ixchel to leave the property, assuming that the women would capitulate under threats of violence. The alcalde, and several important community leaders began to claim that Ixchel was standing in the way of the PetĖn's development and progress. This case engendered fear throughout San JosĖ; the community divided over the issues of local self- determination, progress, and financial rewards. Although Ixchel took this case to court, the alcalde prevailed. In the end, the conflict led to personal problems within the organization, the women stopped participating in the fall of 1995, and the group dissolved.

DISCUSSION

In conclusion, I suggest that the biosphere reserve model for conservation and development has several built-in contradictions. The model's framework has enabled NGOs to alter the dynamics of local politics, and transform the face of the landscape. In their attempts to conserve the northern PetĖn's forest, NGOs have set out to change local people's environmental consciousness and land management practices. These changes undermine many local structures and strategies that have emerged to deal with social and environmental changes. Some of the introduced techniques have no historical or cultural relevance; they become anomalies in local cultural landscapes. Due to their neglect of power structures, individual innovation, and cultural landscapes, NGO landscapes may not provide long-term solutions to environmental degradation.

The majority of people involved in the implementation of the Maya Biosphere Reserve regard the process as an experiment; it is a learning process within the international field of sustainable development. Projects are eliminated or adjusted as problems rise to the surface. The impact of experimentation, meanwhile, is deeply felt in local communities, wherein individuals have been asked to restructure their lives around NGO projects. My research has suggested that people have suffered from time lost in projects subsequently abandoned; raised expectations and unkept promises; indifference to local knowledge and practices; local dissent, and in several cases, increased violence. This leads me to question the ethics of experimentation within the field of conservation and development.

Although the success of the biosphere reserve model is problematic, the Maya Biosphere Reserve will not determine the fate of the PetĖn. In the end, solutions to resource depletion hinge upon changes in global social and economic structures, the commitment of the Guatemalan government, and the experience and creative energies of local people. Those of us interested in these issues must begin to question Western models of conservation, and challenge NGOs to support local people without undermining their knowledge and self-determination.


AUTHOR

A version of this essay was presented at the annual meeting of the Association of American Geographers, March 1995, Chicago, Il. Juanita Sundberg is a professor at the Univeristy of British Columbia in Vancouver, CANADA. She can be reached via email: email.



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