COMMUNITY IN CONSERVATION
THEORETICAL
GENERAL
Agarwal,
B (1997). “Environmental action, gender equity and women's participation.” Development
and Change 28(1): 1-44.
Agrawal,
A (1994). Rules, rule-making and rule-breaking: examining the fit between rule
systems and resource use. in Rules, Games and Common-Pool Resources. E
Ostrom, R Gardner and J Walker, Ed. Ann Arbor, University of Michigan Press:
267-282.
Agrawal,
A (1995). “Dismantling the divide between indigenous and scientific knowledge.”
Development and Change 26: 413-439.
In the past few years scholarly
discussions have characterized indigenous knowledge as a significant resource
for development. This article interrogates the concept of indigenous knowledge
and the strategies its advocates present to promote development. The article
suggests that both the concept of indigenous knowledge, and its role in
development, are problematic issues as currently conceptualized. To
productively engage indigenous knowledge in development, we must go beyond the
dichotomy of indigenous vs. scientific, and work towards greater autonomy for
'indigenous' peoples. (Journal)
Agrawal,
A (1995). Institutions for disadvantaged groups. Paper prepared for the Department of Policy Coordination and
Sustainable Development, United Nations. Mimeo. Pp. 40.
Alcorn,
J (1993). “Indigenous peoples and conservation.” Conservation Biology
7(2): 424-426.
Alpert,
P (1995). “Integrated conservation and development.” Ecological Applications
5(4): 857-861.
Anonymous
(1997). “Environmental disruption and social change.” Current Sociology 45: 1-193.
A special issue on environmental disruption and social
change. Topics discussed include the
relationship between sociology, extreme environments, and social change; an
overview of contamination, corrosion, and the social order; communities,
policy, and chronic technological disaster; the social shaping of radioactive
waste management in Sweden and Finland; diffuse chemical use in broadacre
farming systems in Australia; a review of the literature on environmental
inequalities and proposals for new directions in research and theory; the
multiple effects, in terms of movement outcomes and social change, of local
mobilizations; a revised conception of popular epidemiology; and gender,
hazardous facility workers, and community responses to technological hazards.
(Journal)
Antonsen,
P (1974). “Natural resources and problems of development: the challenge of new
territories.” Cooperation and Conflict 9(2/3): 127.
Baland,
J-M and J-P Platteau (1996). Halting Degradation of Natural Resources: Is
There a Role for Rural Communities? Oxford, Oxford University Press.
Bandy,
J (1996). “Managing the other of nature: sustainability, spectacle and global
regimes of capital in ecotourism.” Public Culture 8: 539-566.
Batterbury,
S, T Forsyth, et al. (1997). “Environmental transformations in developing
countries: hybrid research and democratic policy.” The Geographical Journal
163: 126-132.
Part of a special section on
environmental transformations in developing countries that contains papers
presented at a conference convened by the Environment and Developing Areas
Research Groups of the Institute of British Geographers at the Royal
Geographical Society on October 16, 1996.
The writers introduce the wider themes discussed in detail in the
articles comprising the special section.
They summarize the arguments made by the contributors to the special
section as stating that environmental research that does not query physical and
human factors simultaneously may reiterate environmental orthodoxies; the
identification of environmental problems must be democratized at a number of
scales; the formulation of environmental management demands a critical stance
to knowledge claims; and the need to seek local governance on the reflexive
identification of expert knowledge. (Journal)
Becker,
CD and E Ostrom (1995). “Human ecology and resource sustainability: The
importance of institutional diversity.” Annual Review of Ecology and
Systematics 26: 113-133.
We define the concept of a
common-pool resource based on two attributes: the difficulty of excluding
beneficiaries and the subtractability of use. We present similarities and
differences among common-pool resources in regard to their ecological and
institutional significance. The design principles that characterize
long-surviving, delicately balanced resource systems governed by local rules
systems are presented, as is a synthesis of the research on factors affecting
institutional change. More complex biological resources are a greater challenge
to the design of sustainable institutions, but the same general principles
appear to carry over to more complex systems. We present initial findings from
pilot studies in Uganda related to the effects of institutions on forest
conditions. (SSCI)
Berkes,
F and C Folke (1998). Linking Social and Ecological Systems: Management
Practices and Social Mechanisms for Building Resilience. Cambridge,
Cambridge University Press.
Berlin,
B (1973). “Relation of folk systematics to biological classification and
nomenclature.” Annual Review of Systematics and Ecology 4: 259-271.
Berlin,
B, DE Breedlove, et al. (1973). “General principles of classification and
nomenclature in folk biology.” American Anthropologist 75(1): 214-242.
Bhaskar,
V and A Glyn (1995). The North, the South, and the Environment: Ecological
Constraints and the Global Economy. London, Earthscan.
Bird,
EAR (1987). “The social construction of nature: theoretical approaches to the
history of environmental problems.” Environmental Review 11: 255-264.
Blaikie,
P (1995). “Changing environments or changing views? A political ecology for developing countries.” Geography
80.
Landscapes and environments are
perceived and interpreted from many different and contested points of view which
reflect the particular experience, culture and values of the viewer. A more
'interactionist' approach to the study of society and environment has recently
gained acceptance and converges with other developments in the social sciences
(actor-orientated approaches, structure and agency issues and the sociology of
scientific knowledge). In the place of scientific 'truths' about the
environment, discourses allow a critical evaluation of different versions of
environmental issues. Appeals to better and more environmental science, better
law and governance and to the logic of the market, in order to re-establish
certainty and order in global management, are only partly successful. They,
too, are vulnerable to the same evaluation. The author calls for a more politically
aware understanding of the plurality of points of view regarding the
environment, for 'environmental brokerage' and the opening up of spaces for
negotiation between different parties. (SSCI)
Blaikie,
P, K Brown, et al. (1997). “Knowledge in action: local knowledge as a
development resource and barriers to its incorporation in natural resource
research and development.” Agricultural Systems 55(2): 217-237.
Local knowledge (LK) cannot be
assumed to be a necessary resource in development. The case must be argued
successfully in the face of other development approaches which are indifferent
or hostile to it. This paper identifies three distinct development approaches
(or paradigms), the classic, neo-liberal, and neo-populist, which view the role
of LK in the dynamics of technical change in different ways. Each approach
often incorporates elements of various paradigms into strategy statements and
policy or project documents. This paper focuses on the role of LK in natural
resource (NR) research and development at the 'development interface'. Here,
stakeholders bring both local and scientific knowledge to the interface and, in
relation to the dominant paradigm within which external actors operate,
together produce an outcome termed 'Knowledge-in-Action' (KIA). Six ways in
which KIA is produced are characterised, and it is recommended that priority be
given to those likely to produce synergy. The paper also reviews the degree to
which the ODA (UK) has so far integrated LK into natural resource development
projects. The paper identifies a number of structural and behavioural barriers
to a greater role for LK in natural resource research and development.
(Journal)
Borghese,
E (1987). “Third world development: the role of non-governmental
organizations.” The OECD Observer 145.
Borrini-Feyerabend,
G (1996). Beyond Fences: Seeking Social Sustainability in Conservation.
Washington, Biodiversity Support Program.
Boyden,
S (1992). Biohistory: The Interplay between Human Society and the Biosphere.
Paris, UNESCO Man and Biosphere Series Vol 8.
Brandon,
K (1997). Policy and practical considerations in land-use strategies for
biodiversity conservation. in Last Stand: Protected Areas and the Defense of
Tropical Biodiversity. RA Kramer, CP vanSchaik and J Johnson, Ed. New York,
Oxford University Press.
Brick,
PD and RM Cawley, Eds. (1996). A Wolf in the Garden: the Land Rights
Movement and the New Environmental Debate. Lanham, MD, Rowman &
Littlefield.
Broad,
R (1994). “The poor and the environment: friends or foes?” World Development
22(6): 881-893.
The conventional literature in
the environment and development field often presents a rather deterministic
view of the relationship between poverty and the environment, revolving around
the negative impact of the poor on the environment. Based on extensive
fieldwork in rural communities across the Philippines, this article is a case
study of that relationship between the poor and the environment in a country
with severe poverty rates, significant environmental degradation, and a highly
organized civil society. As a country where large numbers of poorer people have
been transformed into environmental activists, the Philippines offers both a
refutation of the traditional paradigm of poor people as environmental destroyers
and enormous insights into the conditions under which poor people become
environmental protectors. This case study leads the author to posit a set of conditions under which
poor people become environmental activists rather than environmental degraders. Suggestions are made as to the relevance of
the Philippine case study for understanding the relationship between the poor
and the environment in other parts of the Third World. (Econlit)
Brokensha,
Dea, Ed. (1980). Indigenous Knowledge Systems and Development. Lanham,
MD, University Press of America.
Bromley,
D (1994). Economic dimensions of community-based conservation. in Natural
Connections: Perspectives in Community-based Conservation. D Western and RM
Wright, Ed. Washington DC, Island Press.
Brosius,
J, A Tsing, et al. (1998). “Representing communities: histories and politics of
community-based natural resource management.” Society and Natural Resources
11(2): 157-168.
Recent years have witnessed the
emergence of a loosely woven transnational movement, based particularly on
advocacy by nongovernmental organizations working with local groups and
communities, on the one hand, and national and transnational organizations, on
the other, to build and extend new versions of environmental and social
advocacy that link social justice and environmental management agendas. One of
the most significant developments has been the promotion of community-based
natural resource management programs and policies. However the success of
disseminating this paradigm has raised new challenges, as concepts of
community, territory, conservation, and indigenous are worked into politically
varied plans and programs in disparate sites. We outline a series of themes,
questions, and concerns that we believe should be addressed both in the work of
scholars engaged in analyzing this emergent agenda, and in the efforts of
advocates and donor institutions who are engaged in designing and implementing
such programs. (Authors)
Brown,
M and B Wyckoff-Baird (1995). Designing Integrated Conservation and Development
Projects. Washington, Biodiversity Support Program.
Brownrigg,
LA (1985). Native cultures and protected areas: management options. in Culture
and Conservation: The Human Dimension in Environmental Planning. JA McNeely
and D.Pitt, Ed. New York, Croom Helm: 33-44.
Brush,
S (1993). “Indigenous knowledge of biological resources and intellectual
property rights: the role of anthropology.” American Anthropologist
95(3): 653-686.
Bryant,
R (1992). “Political ecology: an emerging research agenda in Third World
studies.” Political Geography 11(1): 12-36.
This paper is a preliminary
exploration of Third-World political ecology. In the first part of the paper, a
framework for understanding the emerging research agenda is developed that
embraces three critical areas of inquiry. These are: the contextual sources of
environmental change; conflict over access; and the political ramifications of
environmental change. Each of these areas of inquiry is addressed by way of a
two-fold strategy-the relevant literature is first reviewed, and then central
analytical issues are discussed. Throughout, it is suggested that Third-World
political ecology represents an attempt to develop an integrated understanding
of how environmental and political forces interact to mediate social and
environmental change. In a world where environmental problems assume growing
political significance, this form of integrated understanding is long overdue.
(SSCI)
Bryant,
RL (1997). “Beyond the impasse: the power of political ecology in Third World
environmental research.” Area 29(1): 5-19.
In the context of a deepening
impasse in Third World environmental research, this paper suggests that
researchers should adopt a Political ecology perspective to ensure that research
addresses the political and economic issues that underlie the Third World's
environmental problems. Since an understanding of unequal power relations is
central to political ecology, the paper considers how questions of power influence human-environmental interaction,
before assessing briefly how research of this kind might contribute to a
resolution of the Third World's environmental problems. (Source)
Bryant,
RL (1998). “Power, knowledge and political ecology in the third world: a
review.” Progress in Physical Geography 22(1): 79-94.
Political ecology examines the
political dynamics surrounding material and discursive struggles over the
environment in the third world. The role of unequal power relations in
constituting a politicized environment is a central theme. Particular attention
is given to the ways in which conflict over access to environmental resources
is linked to systems of political and economic control first elaborated during
the colonial era. Studies emphasize the increased marginality and vulnerability
of the poor as an outcome of such conflict. The impact of perceptions and
discourses on the specification of environmental problems and interventions is
also explored leading on to debates about the relative merits of indigenous and
western scientific knowledge. Future research needs also to address issues
linked to changing air and water quality, urban processes, organizational
attributes and the human body. (SSCI)
Bryant,
RL and S Bailey (1997). Third World Political Ecology. New York,
Routledge.
Bryant,
RL and G Wilson (1998). “Rethinking environmental management.” Progress in
Human Geography 22(3): 321-343.
The field of environmental
management developed as a technocentric problem-solving initiative, providing
'practical' assistance to state officials involved in environmental management.
Since the field was largely associated with what state officials and associated
experts 'do', little effort was devoted to understanding the political,
economic or cultural forces conditioning the process of environmental
management The potentially significant contribution of diverse nonstate
actors-for example, farmers, shifting cultivators, businesses or
nongovernmental organizations - to this process was notably neglected. The
field has recently become the target of mounting criticism with 'environmental
managerialism' dismissed as a research agenda divorced from key issues in
human-environment interaction. This article argues that a recognition of the
limitations of traditional understandings of environmental management ought to
serve as the basis for a rethink of this field of study. This argument is
developed in two stages. The article first explores how the traditional
approach understands environmental management as a state-centred process, assesses
diverse problems with that understanding and sketches an alternative way of
thinking about this issue. The article then assesses how environmental
management as a field of study is usually understood, the pitfalls of that
understanding and the possible contours of an alternative appreciation of the
field of environmental management. By adopting a more inclusive understanding
of what environmental management is as a process, a broader appreciation of the
nature of environmental management as a field of study can be obtained. The
article concludes that a revitalized field can overcome existing deficiencies
so as to be in a position to make thereafter an important contribution to
research on human-environment interaction. (SSCI)
Buell,
J and T DeLuca (1996). Sustainable Democracy: Individuality and the Politics
of the Environment. London, Sage.
Bunker,
SG (1992). Natural resource extraction and power differentials in a global
economy. in Understanding Economic Process, Lanham, Maryland: University
of Press of America: 61-84.
Burton,
R (1991). Nature's Last Strongholds. New York, Oxford University Press.
Callicott,
JB and K Mumford (1997). “Ecological sustainability as a conservation concept.”
Conservation Biology 11(1): 32-40.
Neither the classic resource
management concept of maximum sustainable yield nor the concept of sustainable
development are useful to contemporary, nonanthropocentric, ecologically
informed conservation biology. As an alternative, we advance an ecological
definition of sustainability, that is in better accord with biological
conservation: meeting human needs without compromising the health of
ecosystems. In addition to familiar benefit-cost constraints on human economic
activity, we urge adding ecologic constraints. Projects are not choice-worthy
if they compromise the health of the ecosystems in which human economic systems
are embedded. Sustainability, so defined, is proffered as an approach to
conservation that would complement wildlands preservations for ecological integrity,
not substitute for wildlands preservations. (SSCI)
Carpenter,
L (1997). “Disinformation campaigns and indigenous peoples.” Oryx 31(2):
92-93.
Cernea,
M (1985). Putting People First: Sociological Variables in Rural Development. New York,
Oxford University Press.
Chambers,
R (1979). “ Rural Development: Whose Knowledge Counts?” IDS Bulletin
10(2).
Chambers,
R and MK McBeth (1992). “Community encouragement: returning to the basis for
community development.” Journal of the Community Development Society
23(2): 20-38.
Chekki,
D (1997). Research in Community Sociology: Environment and Community
Empowerment. JAI Press.
Chowdhry,
Kea (1989). “Poverty, environment, development.” Daedalus 118: 141-154.
Clark,
J (1991). Democratizing Development: The Role of Voluntary Organizations.
West Hartford, Connecticut, Kumarian Press.
Clark,
J (1995). “Economic-development vs sustainable societies - reflections on the
players in a crucial contest.” Annual Review of Ecology and Systematics
26: 225- 248.
The World Commission on
Environment and Development adopted and legitimated the idea of sustainable
development in its report Our Common Future. Without substantiation, WCED
claimed that economic growth and environmental protection were compatible. The
1992 UN Conference on Environment and Development at Rio de Janeiro adopted the
idea, without further testing, as its intellectual core. Since 1992, the United
Nations, the United States, and many other nations have created agencies to
track progress toward sustainable development. In favor of the idea are
individuals, including, it appears, most economists, who advocate
centralization, internationalization, and rapid economic development. The
opposition consists principally of people from academic disciplines, especially
ecologists and humanists. This group does not communicate effectively, but if
it did, it might agree that: economic development and environmental protection
are not compatible; insistence by economists that all natural resources be
given a dollar value is useless, if not harmful; biodiversity has intrinsic
value; sustainable development weakens local autonomy; and social welfare is a
key component of environmental health. To strengthen the defense of ecosystems,
ecologists, humanists, and others should apply their knowledge to practical
environmental problems. By making their knowledge accessible in local political
arenas, they will concurrently shore up the ability of local units to protect
their environments and speak with force in larger political arenas. All
proponents of environmental health must become advocates of environmental
justice. (Author)
Critchley,
W, C Reij, et al. (1994). “Indigenous soil and water conservation: a review of
the state of knowledge and prospects for building on traditions.” Land Degradation and Rehabilitation 5(4):
293-314.
After half a century of failed
soil and water conservation projects in tropical developing countries,
technical specialists and policy makers are reconsidering their strategy. It is
increasingly recognised that the land users have valuable environmental
knowledge themselves. This review explores two hypotheses: first, that much can
be learned from previously ignored indigenous soil and water conservation
(ISWC) practices; second, that ISWC can often act as a suitable starting point
for the development of technologies and programmes. However, information on
ISWC is patchy and scattered. Many ancient, derelict systems are better
described than traditions which still persist today. ISWC has been most commonly
developed under dry and marginal conditions, and/or on steep hillsides.
Sustained population pressure has often tended to stimulate ISWC. There is a
need for more incorporation of ISWC into resource conservation programmes: many
projects have ignored local traditions to their detriment. It is widely agreed
that further study and research on ISWC is required and justified as a logical
starting point towards developing adoptable and sustainable soil and water
conservation systems for small-scale farmers. (SSCI)
Crosby,
A (1985). Ecological Imperialism. Cambridge, Cambridge University Press.
Cutter,
SL (1994). “Environmental issues: green rage, social change and the new
environmentalism.” Progress in Human Geography 18: 217-226.
Davis,
SH, Ed. (1993). Indigenous views of land and the environment. World Bank
Discussion Papers, no. 188. Washington, D.C., World Bank.
Deacon,
RT and P Murphy (1997). “The structure of an environmental transaction: the
debt-for-nature swap.” Land Economics 73: 1-24.
Deutsch,
KW (1977). Ecosocial systems and ecopolitics: a reader on human and social
implications of environmental management in developing countries. Paris,
UNESCO.
DeWalt,
BR (1994). “Using indigenous knowledge to improve agriculture and natural
resource management.” Human Organization 53(2): 123-131.
Dodds,
K (1998). “The geopolitics of regionalism: the Valdivia Group and southern
hemispheric environmental co-operation.” Third World Quarterly 19(4):
725-743.
Dravnieks,
D and DC Pitcher (1982). Public participation in resource planning: selected
literature abstracts. Berkeley, CA, Management Sciences Staff, Forest
Service, USDA.
Durning,
AB (1989). Action at the grassroots: fighting poverty and environmental
decline. Washington, DC, Worldwatch Institute.
Durning,
AB (1989). “People, power, and development.” Foreign Policy Fall(76):
66-83.
Dwivedi,
O (1996). “Environmental stewardship: our spiritual heritage for sustainable
development.” Journal of Developing Societies 12: 217-231.
Dwivedi,
OP and D Vajpeyi (1995). Environmental Policies in the Third World: A
Comparative Analysis. Westport, CT, Greenwood Press.
Dye, T
(1998). “On tribal conservationists.” Current Anthropology 39(3):
352-353.
Edgerton,
R (1992). Sick Societies: Challenging the Myth of Primitive Harmony. New York Free Press.
Ellen,
R and K Fukui, Eds. (1995). Redefining Nature: Ecology, Culture and
Domestication. Oxford, Berg Publishers.
Escobar,
A (1996). Constructing nature: elements for a poststructural political ecology.
in Liberation Ecologies: Environment, Development, Social Movements. R
Peet and M Watts, Ed. London, Routledge.
Etzioni,
A (1996). “ Positive aspects of community and the dangers of fragmentation.” Development
and Change 27: 301-314.
Feldmann,
F (1994). Community environmental action: the national policy context. in Natural
Connections: Perspectives in Community-based Conservation. R Western and RM
Wright, Ed. Washington DC, Island Press: 393-402.
Fellizar,
F and K Oya (1994). “Achieving sustainable development through community-based
resource management.” Regional Development Dialogue 15(1): 201-217.
Quality of life in any
particular context depends on resource endowment (land, water, forests) &
the manner in which resources are allocated & utilized. Participants can
opt to derive maximum short-term benefit or to plan for future needs. While the
latter is the essence of sustainable development, there is a growing
recognition among aid planners, academics, decisionmakers, & development
workers that sustainable development requires a better understanding of the
role of communities in the management & conservation of resources. The
concept of community-based resource management (CBRM) - its elements,
preconditions, & underlying assumptions - is therefore clarified. CBRM
projects throughout the Philippines are offered as illustrative examples. In
Comment, Kenji Oya (UN Center for Regional Development) comments that the
success of CBRM projects depends on the extent to which institutional
arrangements support local resource management groups. (Copyright 1995,
Sociological Abstracts, Inc., all rights reserved.)
Ferraro,
PJ and RA Kramer (1995). A framework for affecting household behavior to
promote biodiversity conservation. Arlington VA, Environmental and Natural
Resources Policy and Training, Winrock International Environmental Alliance.
Folke,
C, C Perrings, et al. (1993). “Biodiversity conservation with a human face:
ecology, economics and policy.” Ambio 22(2-3): 62-63.
Fonseca,
Cd, F Sunimal, et al. (1994). “Economy, ecology and spirituality: toward a
theory and practice of sustainability (part II).” Development 4: 67-72.
Fowler,
A (1998). “Authentic NGDO partnerships in the new policy agenda for
international aid: dead end or light ahead?” Development and Change 29(1): 137-159.
Since the 1970s,'partnership'
has been an aspiration for relationships amongst non-governmental organizations
involved in international development (NGDOs). Unfortunately, NGDOs have shown
little ability to form equitable relations, or true partnership, amongst
themselves. The first part of this article examines why. The new policy agenda
for international aid emphasizes contract-based relationships which will make
real partnerships even more difficult to achieve. The second part of the
analysis argues that trust-based authentic partnerships remain vital for
development, and outlines some steps that NGOs might take towards forming them.
In the long term: however, NGDOs must radically rethink their roles, which
calls for a transformation from intermediaries in a funding chain to
facilitators of international co-operation between the diverse groups which
comprise civil society. NGDOs unwilling to take this step could be classified
as hypocrites if they continue to employ the term 'partnership' for what is
essentially old wine in re-labelled civic bottles. (SSCI)
Fox, J
(1992). “Democratic rural development.” Development and Change 23:
201-244.
Freeman,
M and L Carbyn (1988). Traditional Knowledge and Renewable Resource Management.
Geneva, IUCN Commission on Ecology.
French,
HF (1992). After the earth summit: The future of environmental governance,
Worldwatch Institute.
Gadgil,
M, F Berkes, et al. (1993). “Indigenous knowledge for biodiversity
conservation.” Ambio 22(2-3): 151-156.
Indigenous peoples with a
historical continuity of resource-use practices often possess a broad knowledge
base of the behavior of complex ecological systems in their own localities.
This knowledge has accumulated through a long series of observations
transmitted from generation to generation. Such ''diachronic'' observations can
be of great value and complement the ''synchronic''observations on which
western science is based. Where indigenous peoples have depended, for long
periods of time, on local environments for the provision of a variety of
resources, they have developed a stake in conserving, and in some cases,
enhancing, biodiversity. They are aware that biological diversity is a crucial
factor in generating the ecological services and natural resources on which
they depend. Some indigenous groups manipulate the local landscape to augment
its heterogeneity, and some have been found to be motivated to restore
biodiversity in degraded landscapes. Their practices for the conservation of
biodiversity were grounded in a series of rules of thumb which are apparently
arrived at through a trial and error process over a long historical time
period. This implies that their knowledge base is indefinite and their
implementation involves an intimate relationship with the belief system. Such
knowledge is difficult for western science to understand. It is vital, however,
that the value of the knowledge-practice-belief complex of indigenous peoples
relating to conservation of biodiversity is fully recognized if ecosystems and
biodiversity are to be managed sustainably. Conserving this knowledge would be
most appropriately accomplished through promoting the community-based
resource-management systems of indigenous peoples. (Journal)
Gardner,
SS (1995). “Major themes in the study of grassroots environmentalism in
developing countries.” Journal of Third World Studies 12(2): 200(245).
Grassroots environmental
organizations (GEOs) have proliferated
in the Third World. Although diverse in the political and environmental
aspirations, these GEOs have several major common themes. GEOs seek to challenge the notion that people from developing countries have no concern for the
environment and often start off as
local defenders of the environment but soon
branch out to different social
goals. Most GEOs are headed by women
and are viewed by their native governments with hostility or indifference. Many GEOs bask in the
financial and political support of international non-government organizations
and religious groups. (Wilsonweb)
Gasper,
D (1996). “Culture and development ethics: needs, women's rights, and western
theories.” Development and Change 27(4): 627-661.
Can development ethics avoid
presuming that European cultures have universal validity and yet also avoid treating
every distinct culture as sacrosanct and beyond criticism? While work on
'culture and development' valuably stresses the importance of cultural
differences and identity it has often been hindered by conceptual limitations
when faced with the ambiguities, variety, conflict and change within societies.
This article queries a communitarian belief, that morality cannot be anything
other than whatever a community's norms are, and suggests that recent
development ethics work usefully blends universalist ethics with room for local
traditions and choices. As advances on both (a) forms of liberalism that are
universalist in scope but Eurocentric and over-individualistic in content, and
(b) relativist forms of communitarian or post-modern ethics, three current approaches
are noted: new work on Basic Human Needs theory, including Amartya Sen's
capabilities approach; Martha Nussbaum's Aristotelian extension of Sen; and
Onora O'Neill's Kantian development ethic. Particular attention is paid in the
article to disputes concerning women's rights. (Journal)
Ghai, D
and J Vivian (1992). Grassroots Environmental Action: People's Participation
in Sustainable Development. London, Routledge.
Goldstein,
B (1994). Community based conservation: an annotated bibliographic database.
New York, Art Ortenberg and Liz Claiborne Foundation.
Gould,
KA, A Schnaiberg, et al. (1996). Local Environmental Struggles: Citizen
Activism in the Treadmill of Production. New York, Cambridge University
Press.
Goulet,
D (1989). “Participation in development: new avenues.” World Development
17(2): 165-178.
Gowdy,
J (1997). “The value of biodiversity: markets, society and ecosystems.” Land
Economics 73: 25-41.
Greenberg,
J and T Park (1994). “Political ecology.” Journal of Political Ecology 1:
1-9.
Grigsby
, WJ and JE Force (1993). “Where credit is due: forests, women and rural
development.” Journal of Forestry
June: 29.
Grove,
R (1990). Colonial conservation, ecological hegemony, and popular resistance:
towards a global synthesis. in Imperialism and the Natural World. J
MacKenzie, Ed. Manchester, Manchester University Press: 15-50.
Grove,
R (1995). Green Imperialism. Cambridge, Cambridge University Press.
Herrmann,
P (1995). “Human environmental crisis and the transnational corporation - the
question of culpability.” Human
Ecology 23(2): 285-289.
This commentary outlines the
conflict of interests inherent in the state-transnational corporation
relationship, and briefly discusses the failure of bilateral and multilateral
mechanisms to ensure corporate accountability and compliance with basic human
rights and international environmental laws. (Journal)
Hillborn,
R, CJ Walters, et al. (1995). “Sustainable exploitation of renewable
resources.” Annual Review of Ecology and Systematics 26: 45-67.
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GAJ (1955). “Definitions of community: areas of agreement.” Rural Sociology
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Based on field research from
three regions with distinct variations in environment, population density,
livelihood bases and levels of resource dependency, this study investigates the
gender aspects of environmental change. It seeks to illustrate the relevance of
gender factors for the patterns of adaptation to change, for the welfare impact
of changes on the population, and for the ramifications for resource management
and livelihood generation at the community level. It employs a gender analysis to examine the impact of such
changes on population variables, particularly on health and nutrition, and to
explore the more general question of whether women's socio-economic status is
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Johnston,
B (1995). “Human rights and the environment.” Human Ecology 23(2): 111-123.
This issue of Human Ecology
focuses on the interrelated-nature of crisis in human and environmental systems
and argues that the right to a healthy environment is a fundamental human
right. In this article I present a conceptual framework for the ''human rights
and environment'' special issue, followed by a brief review of significant
insights offered by each contributor. Collectively the cases presented in this
issue explore connections between international and national policy, government
action or sanctioned action, and human environmental crises. Cultural notions
are seen to play a key role in influencing social relations, legitimizing power
relations, and justifying the production and reproduction of human
environmental crises. And finally, these cases explore the ways in which
political, economic, and cultural forces influence and at times inhibit efforts
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28(4): 4.
Recent approaches to
community-based natural resource management frequently present 'communities' as
consensual units, able to act collectively in restoring population-resource
imbalances or reestablishing harmonious relations between local livelihoods and
stable environments. Arguing that these underlying assumptions and policy
narratives are flawed as guidelines for policy, this article presents an
alternative perspective which starts from the politics of resource access and
central among diverse social actors, and sees patterns of environmental change
as the outcomes of negotiation or contestation between their conflicting
perspectives. The notion of 'environmental entitlements' encapsulates this
shift in perspective, and provides analytical tools to specify the benefits
that people gain from the environment which contribute to their well-being. The
processes by which people gain environmental endowments and entitlements are,
in rum, shaped by diverse institutions, both formal and informal. (SSCI)
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There is a limit to
"self-help" or
community-based" schemes. External intermediary institutions are
needed to provide support to communities in mobilizing internal resources and
gain access to outside inputs that enhance their capacities to improve their
habitat. The paper first presents a framework that links intermediary institutions,
community organizations, and communal actions on environmental management and
then uses this framework to explore the findings of a case study of three
low-income communities in Bangkok. The analysis shows that intermediary
institutions have played a crucial role in facilitating the development of
community capacity to deal with environmental and other communal problems. (C)
1998 Elsevier Science Ltd. All rights reserved.
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UJ (1981). “Cooperatives and the poor: A comparative perspective.” World
Development 9(1): 55-72.
Lind, A
(1997). “Gender development and urban social change: women's community action
in global cities.” World Development
25(8): 1205-1223.
This article addresses the
gender dimensions of women's community action in global cities. it focuses on
two types of women's organizations (food provision and anti-violence) and draws
our their implications for community and national development frameworks in the
context of economic restructuring and urban poverty. The article undertakes
three tasks: First, it rethinks
frameworks
of development and urban social change from a gender perspective. Second, it
analyzes the ways in which local women's organizations have acted
proactively-rather than merely reactively-to processes of urban restructuring.
Third, it proposes an approach in which women's informal political and economic
participation is better accounted for in national development frameworks and
related community development initiatives. (C) 1997 Elsevier Science Ltd.
Machlis,
GE (1992). “The contribution of sociology to biodiversity research and
management.” Biological Conservation
62(3): 161-170.
As the loss of biodiversity is a
serious ecological problem, biodiversity research and management are important
components of current conservation biology. This paper describes how sociology
can contribute to biodiversity research and management. Biodiversity is, like
all scientific and environmental issues, partially a socially constructed
problem. Case study and comparative multinational data suggest that the causes
of biodiversity decline are largely socio-economic, and solutions will require
interdisciplinary approaches. Sociology can make several contributions to
biodiversity research and management, including (1) a better understanding and
management of habitat change; (2) improved research and decision-making
methodologies; (3) development of a theoretical synthesis; and (4) analysis of
the social organization of conservation and conservation biology. (Author)
Martin,
G (1994). “Ethnoecology and postmodernism:
Friends or foes?” Journal of Ethnobiology 14(2): 265-272.
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621-634.
Discussions concerning
environmental aspects of the New World Order ever-emphasize the roles of
national governments and international organizations. While these large groups
are important, the command-and-control regulations they tend to employ do not
fit all situations and may fail to recognize solutions developed on the local
level. Effective management of natural resources and the environment must
involve changes at the state and local level where environmental problems are felt by the people. (Econlit)
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J (1989). Reclaiming Paradise: The Global Environmental Movement.
Bloomington, University of Indiana Press.
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JA (1995). Expanding Partnerships in Conservation. Washington DC, Island
Press.
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property rights.” Development and Change 27(3): 453-474.
NGOs are linked to environmental
objectives for good reason: non-profit NGOs provide a flexible, private-sector
answer to the provision of international environmental public goods. The
non-profit sector can link for-profit, non-profit, and public-sector objectives
in complex contracts. This article examines how, for the case of the National
Biodiversity Institute (INBio) in Costa Pica, such complex contracts with both
domestic and international parties provide partial solutions to public goods
problems in the absence of private property rights over genetic resources.
INBio's 'monopoly' position, legitimized by the local government, brings in
rents from genetic resources which are reinvested in the production of public
goods. (Journal)
Meyer,
C and F Moosang, Eds. (1992). Living with the Land: Communities Restoring
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M, R Gale, et al. (1987). Social
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Conservation programs for
protected areas and plant genetic resources have evolved in similar ways,
beginning with a focus on single species and expanding to ecosystem strategies
that involve the participation of local people. Anthropologists have described
the increasing importance of the participation of local people in conservation
programs, both of local populations in protected area management and of farmers
in plant genetic resources. Both protected areas and plant genetic resources
link local populations, national agencies, and international organizations.
Anthropological research (a) documents local knowledge and practices that
influence the selection and maintenance of crop varieties and the conservation
of rare and endangered species in protected areas, and (b) clarifies the
different concerns and definitions of biodiversity held by local populations
and international conservationists. In addition, anthropologists operate in
nongovernmental organizations (NGOs) and international agencies, participating
in policy debates and acting as advocates and allies of local populations of
farmers and indigenous peoples. (Source)
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E, J Walker, et al. (1992). “Covenants with and without a sword -
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404-417.
Contemporary political theory
often assumes that individuals cannot make credible commitments where
substantial temptations exist to break them unless such commitments are
enforced by an external agent. One such situation may occur in relation to
common pool resources, which are natural or man-made resources whose yield is subtractable
and whose exclusion is nontrivial (but not necessarily impossible). Examples
include fisheries, forests, grazing ranges, irrigation systems, and groundwater
basins. Empirical evidence, however, suggests that appropriators in common pool
resources develop credible commitments in many cases without relying on
external authorities. We present findings from a series of experiments
exploring (1) covenants alone (both one-shot and repeated communication
opportunities); (2) swords alone (repeated opportunities to sanction each
other); and (3) covenants combined with an internal sword (one-shot
communication followed by repeated opportunities to sanction each other).
(Journal)
Otto, J
and K Elbow (1994). The background to community-based conservation. in Natural
Connections: Perspectives in Community-based Conservation. D Western and RM
Wright, Ed. Washington DC, Island Press.
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instructive case from the Third World.” Dialectical Anthropology 17(3):
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analysis of current activities and opportunities for applying geomatics
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P (1991). Winners and losers in the
twentieth-century struggle to survive. in Resources, Environment, and
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M (1995). “Towards a new paradigm of community development.” Community
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D, B Thomas-Slayter, et al. (1996). Feminist Political Ecology. London,
Routledge.
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P (1998). “The development of indigenous knowledge - A new applied anthropology.”
Current Anthropology 39(2):
223-252.
The widespread adoption of
bottom-up participation as opposed to top-down modernisation approaches has
opened up challenging opportunities for anthropology in development. The new
focus on indigenous knowledge augurs the next revolution in anthropological
method, informants becoming collaborators and their communities participating
user-groups, and touches upon such contemporary issues as the crisis of
representation, ethnography's status with regard to intellectual property
rights, and interdisciplinary cooperation between natural and social
scientists. Indigenous-knowledge studies are challenging not only because of
difficulties in cross-cultural communication and understanding but also because
of their inevitable political dimensions. Contributing to development which
intervenes in people's Lives, these studies engage with them in novel ways.
(SSCI)
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K and V Ballabh (1996). Cooperative Management of Natural Resources. New
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Planning Review 15(4): 411-428.
Discusses a holistic concept of sustainable
development in which economic, ecological, social, & political factors are
simultaneously considered. Participation by individuals, particularly at the
community level, is seen as an important means for achieving sustainable
development & formulating development goals. These goals grow out of an
organic interactive participatory process. Methods of project appraisal are
reviewed in the light of sustainable development concepts, & the role of
research & foreign aid in promoting sustainable development is addressed.
The analysis is illustrated utilizing the case of the South Pacific in general,
along with a specific research project, ie, giant clam farming. 1 Table, 1
Figure. Adapted from the source document. (Copyright 1994, Sociological
Abstracts, Inc., all rights reserved.)
Taylor,
M (1998). “Natural connections. Perspectives in community-based conservation.” Society
and Natural Resources 11(3): 251-258.
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C (1985). 15 Years Of Community-Based Development - An Annotated-Bibliography,
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BL, WC Clark, et al., Eds. (1990). The Earth as Transformed by Human Action:
Global and Regional Changes in the Biosphere over the Past 300 Years.
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USAID
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Wapner,
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DM, Ed. (1991). Indigenous Knowledge Systems: The Cultural Dimensions of
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International.
Warren,
DM (1991). Using Indigenous Knowledge in Agricultural Development. World Bank Discussion Paper 127. Washington,
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M and R Peet (1996). Conclusion: towards a theory of liberation ecology. in Liberation
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and benefits and efforts to remedy them.” Ambio 21(3): 237-243.
Considerable progress has been
made recently in identifying and measuring protected area economic costs and
benefits in developing countries. This paper departs from this approach by
concentrating not on the measurement of total economic costs and benefits from
protected areas but on their distribution, Protected area benefits and costs
are discussed at three separate spatial scales: local, national/regional, and
global/transnational. The overall picture shows that economic benefits-although
difficult to measure and varying from site to site-are limited on a local
scale, increase somewhat on a regional/national level and then become
potentially substantial on a transnational/global scale. The economic costs
follow an opposite trend, from being locally significant, regionally and
nationally moderate, and globally small. It is evident that there are few local
incentives and very limited regional and national incentives for protected area
establishment and management in developing countries. Very little, if any,
empirical work has been done on the distribution of protected area costs and
benefits. The conclusion of this paper is that such analysis can provide an
essential bridge between economic valuation studies and the identification of
necessary and practical action steps. (Journal)
Wells,
M (1995). Biodiversity conservation and local development aspirations: new
priorities for the 1990s. in Biodiversity Conservation. CA Perrings, KG
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Wells,
M (1998). “Institutions and incentives for biodiversity conservation.” Biodiversity
and Conservation 7(6): 815-835.
Incentive measures for
biodiversity conservation cannot be evaluated and compared outside the context
of institutional performance and relationships. The institutional framework for
biodiversity incentives includes a variety of organizations operating on
different spatial scales. The institutional actors with an impact on
biodiversity include community groups, local and national governmental
structures, NGOs, business enterprises and international organizations. But the
positive influence of conservation-oriented organizations is often
significantly outweighed by the negative influence of other sets of
institutional actors who are largely unaware of biodiversity as a concept and
not unduly concerned with its conservation. There are several options for
improving the institutional framework for biodiversity incentives: (1)
decentralization of resource management decision making to local levels; (2)
engaging and reorienting government institutions; (3) establishing new national
and international institutions; and (4) establishing functional linkages
between key institutional actors. The role of local, national and international
institutions in designing and implementing effective incentive measures for biodiversity conservation will be
critical. But- the dynamics within and between institutional actors influencing biodiversity conservation are complex,
variable and insufficiently understood, somewhat like biodiversity itself.
(Source)
West, P
(1989). “Collective adoption of natural resource practices in developing
nations.” Rural Sociology 48(1): 44-59.
Sociological barriers to
achieving collective adoption of natural resource conservation &
development projects in rural areas of developing nations are discussed &
include the following: (1) the contrast among equity issues in optional &
collective adoption; (2) the special importance of property rights
considerations in collectively adopted resource development projects; (3) the
problems that community factions present for collective adoption; (4) the role
of community organizing & social learning; & (5) the role of indigenous
leadership. Modified HA (Copyright 1983, Sociological Abstracts, Inc., all
rights reserved.)
Western,
D (1994). Linking conservation and community aspirations. in Natural
Connections: Perspectives in Community-based Conservation. D Western and RM
Wright, Ed. Washington DC, Island Press.
Western,
D and RM Wright (1994). The background to community-based conservation. in Natural
Connections: Perspectives in Community-based Conservation. D Western and RM
Wright, Ed. Washington DC, Island Press.
Western,
D and RM Wright, Eds. (1994). Natural Connections: Perspectives in
Community-based Conservation. Washington DC, Island Press.
Winterhalder,
BL, F (1997). “A forager resource population ecology model and implications for
indigenous conservation.” Conservation Biology 11(6): 1354-1364.
Population ecology and foraging
theory can be combined to simulate the population dynamics of hunter-gatherers
and their prey resources. Such simulation study is important to issues of
conservation because many of the population processes that link human foragers
and their prey occur over time scales that elude both ethnographic and
archaeological fieldwork. To demonstrate, we used the model to examine
hunter-gatherer population dynamics. We focused on a prey characteristic that
affects its susceptibility to over-exploitation: the intrinsic rate of
increase, r. We found that forager-prey systems can stabilize without
intentional conservation behavior and that prey ''switching,'' fall-back foods,
and in certain circumstances, a higher r contribute to resource species
persistence. Furthermore, a prey's vulnerability to local depletion or
extinction may depend on the demographic characteristics of the suite of
resources harvested along with it. The model can serve as a ''null hypothesis''
for examining intentional resource conservation and presents points in
concordance with, as well as divergent from tenets in conservation biology. In
particular, we discuss the implications of these findings for indigenous
resource conservation in Amazonia (e.g., the overhunting of large primates and
avifauna and the adoption of new procurement technologies) as well as the
''Pleistocene Overkill Hypothesis.'' (Source)
Yacoob,
M, E Brantly, et al. (1994). Public Participation in Urban Environmental
Management: A Model for Promoting Community-Based Environmental Management in
Peri-Urban Areas. WASH Technical Reports, 90.
Zimmerer,
K (1994). “Human geography and the "New Ecology": the prospect and
promise of integration.” Annals of the Association of American Geographers
84(1): 108-125.
The ''new ecology'' underscores the role of nonequilibrium conditions in biophysical environments, a reorientation of biological ecology based in part on biogeography. This paper describes the contributions of the ''new ecology'' and examines their implications for the analysis of biophysical environments in human geography, the most notable of which is a reformulation of certain key ecological postulates (generalized carrying capacity, area-biodiversity postulate, biodiversity-stability postulate). The irony of these reformulations is that our advanced understandings of biophysical environments come at the expense of the perceived certainty of prediction and possible justification for human-induced environmental degradation. These difficulties are not insuperable, however, as is readily demonstrated by the applications of the ''new ecology'' in landscape ecology and agroecology. Their example may prove instructive as geographers integrate the ''new ecology's perspectives on biophysical environments and interpret the relations between environmental conservation and economic development. (SSCI)