COMMUNITY IN CONSERVATION
LATIN AMERICA
GENERAL
Aagesen,
D (1998). “Indigenous resource rights and conservation of the monkey-puzzle
tree (Araucaria araucana, Araucariaceae): A case study from southern Chile.” Economic
Botany 52(2): 146-160.
Annis,
S and P Hakim, Eds. (1988). Direct to the Poor: Grassroots Development in
Latin America. Boulder, Colo, Rienner.
Fifteen previously
published papers explore an approach to
economic and social development labeled "grassroots development,"
which suggests that the best way to help poor people is to give
money to the organizations that they themselves create and control. Papers focus on the idea of social energy;
social energy and uncommon individuals; processes of collective action;
organizations and making money; investing in culture; and the question of
scale. Specific topics are the
principle of conservation and mutation of social energy; a portrait of Ramon
Aybar; blindness and vision in Jamaica; the Campesino-controlled tourism of
Lake Titicaca; Indian colonization in
Paraguay; community participation in rural water supply; conservation in the
style of the Kuna Indians; a Bolivian guide to cooperatives; organizing the
means of consumption in rural Colombia; the experience of worker
self-management in Peru and Chile; cultural projects among Aymara and Quechua
Indians; wandering on the boundaries of development; self-history and
self-identity in Talamanca, Costa Rica; vertical integration in Bolivia; and
small-scale development as large-scale policy.
Contributors are mainly social scientists, anthropologists, public
policy specialists, and urban planners.
(Econlit)
Berger,
SA (1997). “Environmentalism in Guatemala: when fish have ears.” Latin
American Research Review 32(2): 99-117.
Blum, E
(1993). “Making biodiversity conservation profitable: a case study of the
Merck/INBIO agreement.” Environment 36(4): 17-46.
Brondizio,
E, P Mausel, et al. (1998). Integrating biogeography, remote sensing, and human
ecology in the study of land use/land cover dynamics in Amazonia. in Biogeography
and Remote Sensing. K Lulla, Ed. Hong Kong, Geocarto.
Brondizio,
ES, EF Moran, et al. (1994). “Land use change in the Amazon estuary: patterns
of caboclo settlement and landscape management.” Human Ecology 22:
249-278.
Part of a special issue on
recent advances in the regional analysis of indigenous land use and tropical
deforestation. A study was conducted to
examine land use change among three populations of the lower Amazon estuary at
Marajo Island, Brazil. The method used
combined spectral information and image classification with environmental and
ethnographic data. Mechanized
agriculture at one site has removed almost all the mature upland forest, and it
is now dominated by secondary successional vegetation. The more traditional system of diversified
land use at the second site reveals a subtle cycling of flooded forest to
managed palm forest through time in response to the price of palm fruit and
cycling in the use of fallow land. The
third site, based on palm fruit extractivism, demonstrates minimal changes in
land cover as a result of persistent specialization on management of flooded
forest extraction. There is little
evidence that the community with the greatest effect on forest cover is any
better off economically than the other two. (Author)
Browder,
J (1989). Fragile Lands of Latin America: Strategies for Sustainable
Development. Boulder, Westview Press.
Bunker,
SG (1981). The impact of deforestation on peasant communities. in Where Have
all the Flowers Gone? Vol 13Ed. Williamsburg, College of William and Mary,
Department of Anthropology. Third World Studies Publication.
Bunker,
SG (1985). Underdeveloping the Amazon; Extraction, Unequal Exchange, and the
Failure of the Modern State. Urbana, University of Illinois.
Burwell,
T (1995). “Bootlegging on a desert mountain: the political ecology of Agave
(Agave spp.) demographic change in the Sonora River Valley, Sonora, Mexico.” Human
Ecology 23(3): 407-432.
Recent studies suggest that wild
agave (Agave spp.) plants in Sonora, Mexico, are being over-harvested by mescal
makers on communal lands. Using the conceptual framework of regional political
ecology (Blaikie and Brookfield, 1987), I discuss the ecological processes of
agave depletion, and investigate the social, economic, and political contexts
in which unsustainable harvest practices arise. Whereas all the mescal makers
have knowledge of sustainable harvest methods, population growth, expansion of
agriculture onto ecologically marginal lands, and increasing dependence on wild
harvested products from communal lands created the socioeconomic context for
increased demand for mescal income. The ideology of household autonomy, and the
belief that the village has no right to internally regulate use of the commons,
created the political context for rapid, unsustainable harvesting - a tragedy
of the commons. However, recent cultural changes have caused a reversal of this
trend, and some wild agave populations may be recovering. (Journal)
Cleary,
D (1993). “After the frontier: problems with political economy in the modern
Brazilian Amazon.” Journal of Latin American Studies 25(2): 331-350.
Colchester,
M (1981). “Ecological modeling and indigenous systems of resource-use: some
examples from south Venezuela.” Anthropologica 55: 51-72.
Colvin,
JG (1994). “Ecotourism: a sustainable alternative.” NACLA Report on the
Americas 28: 9.
Capirona, a small Quichua rain
forest community in eastern Ecuador, has established one of the world's first
communally based, indigenous operated ecotourism initiatives. The villagers specify careful conditions on
the type and number of visitors in order to minimize damage to the environment
and disruption to community life. Although unlikely to match the profitability
of oil development, ecotourism, if it is controlled by indigenous peoples, may
serve as one facet of a diversified, sustainable economy. (Wilsonweb)
Conklin,
BA and LR Graham (1995). “Shifting middle ground: Amazonian Indians and
eco-politics.” American Anthropologist 97(4): 695-710.
Over the past decade in Brazil,
the convergence between international environmentalism and indigenous cultural
survival concerns led to an unprecedented internationalization of local native
struggles. The Indian-environmentalist alliance has benefited both parties, but
recent events suggest that it may be unstable and may pose political risks for
native people. The limitations of transnational
symbolic
politics as a vehicle for indigenous activism reflect tensions and
contradictions in outsiders' symbolic constructions of Indian identity. (SSCI)
Denevan,
W (1992). “The pristine myth: the landscape of the Americas in 1492.” Annals
of the Association of American Geographers 82(3): 369-385.
The myth persists that in 1492
the Americas were a sparsely populated wilderness, "a world of barely
perceptible human disturbance." There is substantial evidence, however,
that the Native American landscape of the early sixteenth century was a
humanized landscape almost everywhere. Populations were large. Forest
composition had been modified, grasslands had been created, wildlife disrupted,
and erosion was severe in places. Earthworks, roads, fields, and settlements
were ubiquitous. With Indian depopulation in the wake of Old World disease, the
environment recovered in many areas. A good argument can be made that the human
presence was less visible in 1750 than it was in 1492. (SSCI)
Descola,
P (1996). In the Society of Nature: A Native Ecology in Amazonia.
Cambridge, Cambridge University Press.
Downing,
TE, S Hecht, et al., Eds. (1992). Development or Destruction? The Conversion
of Tropical Forest to Pasture in Latin America. Boulder, Westview Press.
Fisher,
WH (1994). “Megadevelopment, environmentalism, and resistance: the institutional context of Kayapo indigenous
politics in Central Brazil.” Human Organization 53(3): 220-232.
Haney,
EB and WG Haney (1978). “Social and ecological contradictions of community
development and rural modernization in a Colombian peasant community.” Human
Organization 37(3): 225-234.
Hill, J
(1989). “Ritual production of environmental history among the Arawakan Wakuenai
ff Venezuela.” Human Ecology
17(1): 1-25.
Holmberg,
AR, HF Dobyns, et al. (1962). “Community and regional development: the joint
Cornell-Peru experiment.” Human Organization 21(2): 107-124.
Johnson,
A (1989). “How the Machiguenga manage resources: conservation or exploitation
of nature?” Advances in Economic Botany 7: 213-222.
Keese,
J (1998). “International NGOs and land use change in a southern highland region
of Ecuador.” Human Ecology 26(3): 451-468.
Nongovernmental organizations
are increasingly influencing resource management and land use in areas of small
farm agriculture in Latin America. A field study of NGOs working in upper
Canar, a region in the southern highlands of Ecuador, documents the changing
human-environment relations ire an indigenous area and the influence of NGOs in
the change process. Case studies of PLAN International and CARE indicate that
the NGOs are helping marginalized producers shift land use away from
traditional grains and tubers toward dairying and vegetables. Given current
needs and resource constraints, the new land uses represent effective adaptive
strategies. However the NGO work is having notable consequences for land use
intensity and labor utilization patterns. (Journal)
Lopez-Zent,
E (1998). “A creative perspective of environmental impacts by native Amazonian
human populations.” Intercienca 23(4): 232-.
This paper explores a working
hypothesis related to groups of human populations acting as disturbance agents
in the Amazon. Three theoretical premises framing the main argument are
presented (centered on concepts of environmental disturbance and eco-cultural
process). However, more than theoretical, this paper is descriptive and its
data come mostly from a non-exhaustive review of the human ecology literature.
The cultural as well as biological heterogeneity of the Amazon is underlined. A
brief overview of the possible human ways of life during the pre-European colonization
period is also offered here. The basic idea is to illustrate human activities
as potentially dynamic and central in the maintenance of the Amazonian
ecosystem, including its richness and complexities. In support of this
argument, the author selected seven examples to illustrate the ecological
behavior of some contemporary Amazonian human groups such as Ka'apor, Siriono,
Kayapo, Runa, Piaroa, Hoti, etc. Underlying the argument of this paper is the
attempt to contrast two ideological perspectives about human-nature
interactions: the viewpoint supported by the mainstream western belief than
humans form a system apart from nature, and the standpoint vindicated by more
ecologically attuned theories which considers humans to be a part of nature and
thus together comprising a rather dynamic system. The first ideology, has
usually conceived of human behavior toward nature as that of stewardship; thus,
this anthropocentric view considers man as a cardinal element to ecosystem
maintenance. The second ideology heralds a biocentric perspective, in which
humans are equal to other species except that their behavior is still often
perceived as damaging in general. The argument advanced here develops an
ecocentric perspective, but even further, it elaborated a holistic vision of
the human-nature relationship as art (in its literal meaning from Latin ars,
ability, expertise, skill), that is creative, triggering ecological processes
beyond those attempting to satisfy their needs. (Journal)
Nugent,
D (1989). “Are we not [civilized] men? The formation and devolution of
community in northern Mexico.” Journal of Historical Sociology 2(3):
206-239.
Obregon
Salido, FJ and V Corral Verdugo (1997). “Systems of beliefs and environmental
conservation behavior in a Mexican community.” Environment and Behavior 29: 213-235.
Part of a special issue on environmental psychology in Latin
America. A study was conducted to examine three categories of beliefs austerity beliefs, conservation beliefs, and
material waste beliefs related to
consumption refuse practices in a sample of Mexican housewives. Their self reports of reuse and recycling
practices were measured, and observations of reused/recycled items throughout
the households were conducted. It was
found that self reports of conservation behavior were best predicted by
beliefs, but there were also significant correlations between observations of
reuse/recycling and beliefs. Austerity
beliefs were found to be better predictors of self reports of reuse, whereas
conservation beliefs were significantly associated with observations of reuse.
Self reports of recycling were associated more with materialistic and
conservation beliefs, whereas the observed recycling was only predicted by
materialistic beliefs. (Source)
Olsen,
B (1997). “Environmentally sustainable development and tourism: lessons from
Negril, Jamaica.” Human Organization 56(3): 285-293.
Posey,
D and W Balee (1989). Resource Management in Amazonia: Indigenous and Folk
Strategies. New York, New York Botanical Garden.
Price,
M (1994). “Ecopolitics and environmental nongovernmental organizations in Latin
America.” The Geographical Review 84(1): 42-59.
More than five hundred
environmental nongovernmental organizations, most of them less than a decade
old, operate in Latin America. Their popularity as vehicles of social change, the inability of governments to
address environmental problems, new sources of international funding, and the
idea of sustainable development have contributed to the proliferation of these
organizations. Merits and limitations of this movement are assessed by case
studies from Mexico and Venezuela. Conservation strategies have shifted from
protectionist models to the politically popular notion of sustainable development. (Source)
Redford,
K (1990). “The ecologically noble savage.” Cultural Survival Quarterly 15(1): 46-48.
Schmink,
M (1992). Building institutions for sustainable development in Acre, Brazil. in
Conservation of Neotropical Forests. J Redford and C Padoch, Ed. New
York, Columbia University Press.
Schmink,
M and C Wood (1992). Contested Frontiers in Amazonia. New York, Columbia
University Press.
Schwartzmann,
S (1992). Social movements and natural resource conservation in the Brazilian
Amazon. in The Rainforest Harvest. S Counsell and T Rice, Ed. London,
Friends of the Earth Trust.
Sheriden,
T (1988). Where the Dove Calls: The Political Ecology of a Peasant-Corporate
Community in Northwestern Mexico. Tucson, University of Arizona Press.
Southgate,
D and HL Clark (1993). “Can conservation projects save biodiversity in South
America?” Ambio 22: 163-166.
Stocks,
A (1987). Resource management in an Amazon Varzea lake ecosystem: the Cocamilla
Case. in The Question of The Commons.
B McCay and J Acheson, Ed. Tucson, University of Arizona Press: 108-120.
Stonich,
S (1993). I Am Destroying the Land: The Political Ecology of Poverty and
Environmental Destruction in Honduras. Boulder, Westview Press.
Uquillas,
JE (1989). Social impacts of
modernization and public policy, and prospects for indigenous development in
Ecuador's Amazonia. in Human Ecology
of Tropical Land Settlement in Latin America. D Schumann and W Partridge,
Ed. Boulder, Westview Press.
Utting,
P (1994). “Social and political dimensions of environmental protection in
Central America.” Development and Change 25(1): 231-259.
Wheat,
S (1994). “Taming tourism.” The
Geographical Magazine 66: 16-19.
The tourism industry,
governments, and local communities must work together to counter the cultural
and environmental damage that is occurring from the ever increasing number of
tourists visiting environmentally rich countries. Ecotourism, the fastest growing sector in the tourism industry,
represents a niche market for tourists who are interested in the environment and
nature. The small Central American
state of Belize is probably the world's most famous ecotourist
destination. As its fragile natural
environment is being threatened by mass tourism, a number of conservation
initiatives are being encouraged.
Community based projects have been introduced in areas such as southern
Belize and Zimbabwe to overcome another hidden cost of tourism, the
exploitation of local communities and indigenous populations. The World Travel and Tourism Council
believes that voluntary codes of conduct are the best way to ensure
environmental protection. (Source)