Bryant - Political Ecology
Bryant - Political Ecology
1,January 1992,12-36
Political ecology
An emerging research agenda in Third-World studies
RAYMOND L. BRYANT
Introduction
In the future, the interaction between environmental and political forces will mediate
Third-World’ development in unprecedented ways. Thus, as environmental problems
assume greater political significance, the need for an analytical approach integrating
environmental and political understanding becomes more pressing. In the 198Os, scholars
from diverse academic and institutional backgrounds began to examine the links between
environmental and political activities in parts of Asia, Africa and Latin America.’
Correspondingly, a body of work that may be termed Third-World political ecology
emerged. This paper argues that such work suggests a fruitful research agenda in
Third-World studies.
Diverse scholarship has highlighted aspects of this agenda. Emel and Peet (1989), for
example, review work on resource management and natural hazards. Watts (1989) and
Berry (1989a) consider the literature of the African agrarian studies movement. Beinart
(1989, 1990) addresses recent research on hunting and conservation in colonial Africa.
Redclift (1984, 1987), Blaikie and Brookfield (1987b), Blaikie (1988b, 1989b) and Adams
(1990a) also explore aspects of Third-World political ecology.3 These works offer a
tantalizing glimpse of how political and environmental understanding is being integrated
The phrase ‘political ecology’ combines the concerns of ecology and a broadly
defined political economy. Together this encompasses the constantly shifting
dialectic between society and land-based resources, and also within classes and
groups within society itself.
Such a definition has much to commend it, particularly when extended to encompass not
only ‘land’, but more generally ‘environment’. In utilizing this interpretation, however,
economic reductionism must be avoided. As such reductionism has been a recurrent
feature in Third-World political ecology, it is therefore important to review briefly the ways
in which economic reductionism simplifies reality, diminishing analytical accuracy.
Economic reductionism can weaken research in Third-World political ecology in at least
three ways. First, reductionism fails to attribute explanatory significance to ecological
factors5 Thus, as Blaikie (1989a: 22) notes in the context of African desertification:
any attempt to attribute desertification to ‘natural forces’ other than the
penetration of capitalism is written off in some quarters as merely a bourgeois
red herring. This is a simplistic and unnecessary polarisation since it is the
dialectic between environmental and social change which must provide the
context in which land degradation is discussed.
14 Political ecology
than from its content, thereby highlighting the important role of local officials. Does policy
interpretation balance local expectations with official views? Are officials subject to
pressure from local elites, transnational corporations or peasant organizations? What role
does corruption play in policy implementation? To what extent are standardized
bureaucratic procedures attempts to minimize policy ‘leakage’? As Bunker (1982, 198513)
notes, however, the application of such procedures to socio-economically and ecologically
underdeveloped regions may in itself be problematic. How successful, then, are
bureaucratic structures in controlling the many location-specific policy expressions? These
questions highlight the importance of the implementation stage, local officials, and the
bureaucratic structures within which they operate.
Finally, the environmental impact of state policy should also be addressed. Does the
nature and extent of environmental change vary according to whether policy is
implemented directly by the state, or indirectly, through other social groups? Can policy
have an ‘environmental multiplier effect’, accelerating certain processes of human-
environmental interaction at the expense of others? How do different political, economic
and ecological settings influence policy impact?
While discussion has focused on the role of state policies in shaping environmental
change, states do not formulate policies in isolation from each other. As Skocpol(I985: 8)
observes, ‘the modern state has always been part of a system of competing and
mutually involved states’. Thus, conflict and competition between states has long
contributed to environmental modification. And yet, as the review highlighted, research in
this area is underdeveloped. How might the interstate dimensions of environmental
change best be approached? A useful beginning would be to distinguish between its
peaceful and violent variants, as they impinge on land, water and forest conditions,
As the literature highlights, violence between states often contributes to environmental
change. In exploring this relationship at greater depth, it was suggested that scholars need
to devote increased attention to the national and regional dimensions of such violence,
Recent international developments reinforce this point, as--East-West rapprochement
notwithstanding-the diffusion of military hardware, including nuclear weapons, to the
Third World, continues. Gill and Law (1988: 370) note that East-West rapprochement may
in fact encourage this trend; in the context of substantial reductions in domestic military
expenditures, the superpowers may attempt ‘to maintain their economies of scale in
certain types of military production’. How would this greater availability of armaments
alter the kind, extent and intensity of Third-World interstate violence and environmental
change?
The peaceful interaction between states is also laden with environmental implications,
Such interaction may accelerate development of non-state sources of environmental
change-global capitalism, for example. As the discussion of international aid and
watershed management highlighted, however, peaceful relations between states
contribute directly to environmental change. In the process, the costs and benefits of such
change may be inequitably distributed between states. Thus, does the political dependence
of one state on another translate into increased environmental degradation? Conversely,
may a politically ascendant state avoid such degradation by ‘exporting’ it to client states? Do
power imbalances among states arise, in part, from differential control over environmental
resources? Can disadvantaged states use internal processes of environmental change-tro-
pical deforestation, for example-to strengthen their position vz~&~zj- other states? In
recent years, concepts such as ‘debt-for-nature’ swap, and ‘global bargain’ have entered the
international political vocabulary.” Motivated by a perceived ‘crisis of the commons’,
First-World states have begun to consider making economic concessions to ensure
20 Political ecology
concern about ecological degradation in many parts of the Third World fostered a policy
milieu conducive to more stringent environmental regulation?
TNCs must also be sensitive to the socio-political conditions in their ‘home’ countries.
Typically located in the First World, home countries-and more particularly their
states-may also influence how TNCs affect Third-World environments. As in the Third
World, however, governments have shown less interest in regulating TNC practices. Thus,
to what extent have pro-business governments in the First World relaxed supervision of
TNCs? Moreover, how has a more competitive global business environment, and the
growing power of Japan and the newly industrializing countries, affected home
supervision? Conversely, what are the implications of the re-emergence of environmental
concerns (global warming, ozone depletion, etc.) on national and international political
agendas for relations between the home state and TNCs?
If attention so far has centred on the TNC-environmental relationship, a comparable set
of questions could inform analyses of national corporations and Third-World
environmental change. The differing constraints and opportunities facing national, as
opposed to transnational, corporations, must be addressed. Do national corporations have
greater freedom to manipulate the environment, while technologically more advanced
TNCs are expected to meet more exacting standards? Further, the ability of TNCs to move
into and out of a country may confer certain advantages not enjoyed by national
corporations. How, then, does mobility affect a corporation’s interaction with state, society
and environment?
These questions underscore the complex links between global capitalism and
Third-World environmental change. While transnational and national corporations play a
critical role in environmental transformation, the multifarious nature of that role must not
be forgotten. Moreover, this role must not only be understood in relation to other
contextual sources (state policies, interstate relations), but also the location-specific
dimensions of environmental change. Research addressing conflict over access, the
frameworks second area of inquiry, may further such understanding.
Research into questions of conflict over access examines the relationship between access
rights, local struggle and ecological transformation (Peluso, 1988; Hirsch, 1990). Thus, the
second element in the framework is concerned with the constraints and opportunities
facing peasants and other socially disadvantaged groups in struggles to protect the
environmental foundations of their livelihood. Specifically, in seeking to understand
conflict over access, both the historical and contemporary dynamics of struggle must be
addressed.
While much of the literature on conflict over access focuses on contemporary debates, a
number of scholars have adopted an historical perspective. To illustrate elements of
continuity and change in local struggle, several studies compare and contrast the colonial
and post-colonial experiences. Peluso (1988), Watts (1983b), Guha (1989a), Guha and
Gadgil (1989) and Nadkarni (1989) do so in the Javanese, Nigerian and Indian settings.
Peters (1984) and Worby (1988) examine the struggle for land and water rights in
Botswana. In different socio-political and ecological settings, these studies nevertheless
pinpoint the major transformation wrought by colonial rule, and the bitter legacy of
state-peasant antagonism over control of environmental resources that, even today, shows
few signs of dissipating.
For the post-colonial era, the nature of state-peasant and other types of conflict over
22 Political ecology
access has been extensively reviewed. Work by Shiva (1987), Agarwal and Narain (1985),
Fernandes (1990) Jodha (1986) Lohmann (1990) Leonard (1985), Thomson (1985) and
Schmink (1982) illustrates the breadth of issues addressed. The following review, then,
highlights only selected themes.
Conflict pitting peasants against state or economic elites not only involves questions of
‘land’, but may embrace the struggle over flora and fauna (Peluso, 1988; MacKenzie, 1988;
Dogra, 1985; Saldanha, 1990) soil conditions (Hirsch and Lohmann, 1989) and water
supplies (Peters, 1984). More work, however, needs to consider the roles that these and
other environmental resources play in the livelihoods of the rural poor (Chambers and
Leach, 1989; Hecht et al., 1988). Concomitantly, there is a need for greater knowledge of
how such groups interpret these roles (Chambers, 1983; Richards, 1985; Blauert, 1988).
The complexity of conflict over access is partially attributable to tenurial systems and
social institutions regulating access, control and use of environmental resources. Recent
work on the sociology of access in Africa is illustrative. As pertaining to an understanding
of broader agricultural and ecological issues, Okoth-Ogendo (1989), Blaikie (1989a) and
Berry (1989b) offer contrasting perspectives on resource access and use. Mackenzie (1986,
1989) Haugerud (1989), Carney and Watts (1990), Becker (1990) and Davison (1987),
provide empirical case-studies examining many of the ideas developed in these papers. In
this research, complexity of access is emphasized; multiple and overlapping rights
combine with formal and informal tenure to produce a complex web of dependencies.
Similarly, as Peters (1984) and Berry (1988) point out, struggle is equally complex. Given
the importance of social identity, for example, in the determination of access rights,
‘struggles over meaning are as much a part of the process of resource allocation as are
struggles over surplus or the labor process’ (Berry, 1988: 66). As Berry (1988) and
Haugerud (1989) emphasize, this complexity has important implications for both public
and private efforts to regulate land use.
The role of women in conflict over access is crucial, and yet, has typically been
neglected. Only recently has gender begun to receive systematic attention. Shiva (1987,
1988) B. Agarwal(1988a, 1988b, 1989), Mies (1984), Jain (1984) and A. Agarwal(1988), for
example, consider the role of Indian women in struggles to retain access to land, water and
forest resources, B. Agarwal (1990) analyses the relationship between such struggles and
individual/family security in the face of seasonal@ and calamity. In the Kenyan context,
Davison (1987) Mackenzie (1986,1989) and Maathai (1986) examine questions of tenure,
ecological change and women’s politicization. Similarly, Dankelman and Davidson (1988)
and Carney and Watts (1990) explore aspects of women’s struggle. Focused on
gender-derived inequalities, this research views household relations as a ‘deeply contested
terrain’ (Watts, 1989: 12) in which access to environmental resources remains a bitter
source of conflict.13
As illustrated, conflict over access to environmental resources is a powerful source of
social division. Apart from the household, however, conflict between socially
disadvantaged and ‘contextual’ groups is also significant. Embracing ‘peasant’ relations
with political and economic elites, this conflict may be formalized with the development of
environmental movements. As discussed below, environmental movements are an
important strategy for the poor attempting to preserve the environmental foundations of
their livelihood.
The preceding review highlights the complexities of conflict over access, as well as
literature only beginning to recognize that complexity. Analytically, however, the
frameworks second area of inquiry may best be approached by pursuing themes in the
historical and contemporary dynamics of conflict.
Rmmm L. BRYWT 23
Adopting an historical perspective serves as a useful reminder that conflict over access is
intrinsic to human development. Shaped by diverse political, social and ecological factors,
it has been expressed in innumerable location-specific ways. As such, the struggle for
access did not originate with capitalism and colonialism-the latter being simply the most
recent in a recurring motif of human struggle over the environment.‘*
And yet, the advent of colonialism and capitalism marks a qualitative change in the
history of Third-World struggle. Whereas pre-colonial conflict over access was tempered
by decentralized power relations, and by a relatively low level of technological
development, colonial and post-colonial struggle has faced few such constraints. How has
this transformation of political, economic and technological capabilities affected traditional
conflict patterns? To what extent have new patterns emerged, or traditional practices been
invoked?
An appreciation of the historical dimensions of conflict over access is essential to an
understanding of contemporary struggle. Inherently location-specific, such conflict
nevertheless brings together national and international, as well as local actors, and
embodies the struggle between diverse political, social and economic interests. The
management of such competing interests is an integral research theme.
In understanding the contemporary dynamics of conflict, however, a spatial distinction
should be drawn between actors at or near the conflict site, and those elsewhere-at
regional, national or international centres. How may this pattern influence the nature and
outcome of struggle, and be reflected in coalitions amongst actors? How are coalitions
constructed? What impact does the spatial fragmentation of ‘contextual’ actors, the state
and TNCs, have on location-specific conflict?
Spatially differentiated, actors also differ in their access to strategic resources. TNCs and
the state, for example, typically possess greater informational and technological resources
than local villagers. How these contextual actors deploy such resources in location-specific
struggles is among the more crucial research questions. To what extent may imbalances in
technological and informational capability affect the outcome? Is superiority in strategic
resources offset by other, perhaps intangible factors? In the Malaysian context, for instance,
Scott (1985) has shown that the ‘weapons of the weak’ are not inconsequential in the
conflict over access. When combined with overt resistance, the tenacity and desperation of
those faced with the loss of critical environmental resources may, to some extent,
counteract the forces of the powerful (Anderson and Huber, 1988; and below).
Kecognizing the spatial, technological and informational differentiation between actors
is but a preliminary step towards understanding the contemporary dynamics of conflict
over access. Although helpful, details of differentiation and conflict-prerequisites for a
more comprehensive treatment of access conflict-are not considered. A more adequate
inquiry, then, must deconstruct commonly used terms that typically conceal more than
they reveal (‘peasant’, ‘state’, ‘TNC’) in order to expose the complex reality embedded in
them.
An examination of the specifics, rather than generalities, of conflict over access, brings
into question widely-held beliefs about Third-World human-environmental interaction.
Conflict between poor villagers dependent for their well-being on local land, water and
forest resources, and various powerful coalitions attempting to deprive them of access to
those resources, recurs in the literature. And yet, this dichotomy masks a web of complex
power-relations (Hirsch, 1990; Bernstein, 1990). To what extent, for example, are villagers
an undifferentiated mass, united in their destitution? Are they not also caught up in
differentiated relations with the powerful and with each other, and does this not translate
into differing interests and objectives in conflict over access? In this sense, the role of
24 Political ecology
women merits particular scrutiny. In the household, how do gender-based, and often
unequal divisions of labour contribute to the complexities of social struggle for land, water
and forests? Comparable questions may be asked about contextual actors. Do political and
economic elites act unanimously? Is state unity jeopardized by divergent personal and
bureaucratic interests, and do TNCs and the state always concur?
Not only do these questions highlight the complexities of conflict over access, they also
indicate the difficulties associated with its management. Although the state plays a central
role in conflict management, its role is circumscribed by at least two factors. First, the state
is not an impartial observer in such struggles-indeed, it is often a leading participant.15
Secondly, the state is often riven by conflicting interests.
Given these circumstances, what roles do other actors play in conflict management? To
what extent do intimidation, coercion, avoidance behaviour, organized protest, theft and
bribery regulate the struggle for access? Moreover, how should TNC efforts to cultivate
local goodwill be interpreted? Research needs to be sensitive to the complexities of
conflict, the multifarious ways in which such conflict is managed, and ultimately, the
political ramifications of environmental change.
These ‘livelihood struggles’, then, have been the focus of much attention. Redclift (1987)
provides a useful introduction to Third-World environmental movements. In the Indian
setting, Agarwal and Narain (1985) and Omvedt (1989) survey the plethora of movements
that have emerged. In particular, Shiva (1987) Shiva and Bandyopadhyay (1988), Weber
(1987), Bahuguna (1985) and Guha (1989a) outline the development of India’s renowned
Chipko movement, Hirsch and Lohmann (1989) and Lohmann (1990) study various
movements launched by Thai people to contest eucalyptus plantations and hydro-electric
dams. Maathai (1986) traces the evolution of Kenya’s Green Belt Movement. Redclift (1987)
examines Mexican environmental movements, while Hecht and Cockburn (1989) and
Schwartzman (1989) discuss the rubber-tappers’ movement in the Brazilian Amazon.
Much of this research focuses on the livelihood struggles of ethnically-dominant, albeit
economically-subordinate, groups. But what of ethnic minorities and attendant forms of
protest? The link between ethnic&y, ecological change and political protest awaits
adequate exploration. Several studies, however, suggest the research possibilities. Hong
(1987) provides a detailed study of deforestation and indigenous protest in Sarawak.
Drucker (1985), Porter (1990) and Hurst (1990) also explore ethnic-minority resistance in
26 Political ecology
Southeast Asia. Hecht and Cockburn (1989) and Cummings (1990) briefly document the
genesis of Indian struggles in the Amazon. Blauert (1988) discusses emerging
autochthonous resistance in southern Mexico, and Anderson and Huber (1988) offer a
case-study of similar protest in central India.
The preceding review of work on the political ramifications of environmental change
emphasizes that such change not only exacerbates socio-economic inequalities, but also
serves as a catalyst for political protest, notably as manifested in environmental
movements. In analysing this third element in the framework, therefore, there is a need to
differentiate between socio-economic impact and political process.
An appreciation of the political ramifications of environmental change typically
necessitates location-specific understanding. As Blaikie (1985) Blaikie and Brookfield
(1987a) and others have noted, such understanding must be sensitive to the physical and
biological processes specific to a given locale. For the purposes of this paper, however,
development of a location-specific and technical approach is unnecessary.r6 In exploring
the political dimensions of environmental change, a more general schema is appropriate.
Thus, in referring to environmental change, a broad distinction is made between episodic
and everyday” changes. Episodic change includes flooding, drought and similar disasters,
while the everyday embraces soil erosion, salinization, deforestation and various types of
pollution. Although these two forms of environmental change may be interrelated, this
interrelationship remains open to debate (Hamilton and Pearce, 1988; Messerli, 1990).
Everyday forms of environmental change are, as their name would suggest, temporally
and spatially ubiquitous, having a gradual and cumulative impact on human communities
which may long go unrecognized (Blaikie, 1985). When such change is recognized, it may
then mingle with human interests, yielding competing perceptions and definitions (Blaikie
and Brookfield, 1987b). The complexities of everyday forms of environmental change,
however, should not obscure their differentiated socio-economic impact.
In addressing that impact, research should be sensitive to the social and ecological
marginality of the poor (Blaikie and Brookfield, 1987b). How do land managers, for
example, become spatially and economically marginalized? How does such marginal-
ization relate to ecological marginality-that is, lands of low and/or erratic capability?
Moreover, how do these forms of marginality interact to produce ‘socio-ecocide’-or a
downward spiral of human and environmental degradation? Most importantly, how can
individuals and groups caught in this trap organize resistance?
Everyday forms of environmental change must also be related to episodic forms of
change-the droughts, floods and other disasters that periodically threaten human
existence. Although episodic change occurs independently of human design, its impact on
social communities is by no means exclusively or even predominantly ‘natural’ (Watts,
1983a; Susman et al., 1983). Processes of social and ecological marginalization noted above
with respect to everyday change are also crucial to an understanding of the impact of
episodic change. Marginalization typically increases the vulnerability of the poor to
episodic change, breaking down previous defence mechanisms against ecological stress
(Shenton and Watts, 1979; Watts, 1984). As the recent history of famine in Africa attests, the
interplay between processes of marginalization, and everyday and episodic forms of
environmental change can have tragic human consequences.
As illustrated in the discussion of socio-economic impact, the unequal exposure of
groups and individuals to environmental change is imbued with political significance.
Environmental change may not only reflect existing inequalities, but it may also insidiously
reinforce them in the long-term. As Durning (1990: 135) says ‘poverty’s profile has
become increasingly environmental’.
RAYMONI~
L. BRYAKT 27
This paper offers a preliminary exploration of Third-World political ecology and, to this
end, a framework comprising three areas of inquiry has been developed. Although related,
the contextual sources of environmental change, conflict over access, and the political
ramifications of environmental change, were disaggregated in order to appreciate the
specific processes involved. In each case, the relevant literamre was reviewed, and the
central analytical issues examined. It should be reiterated, however, that neither the review
nor the analytical components purports to be comprehensive.
As embodied in this paper’s framework, the agenda for Third-World political ecology is
both complex and challenging, requiring analytical refinement as well as empirical
exploration. How may such work be encouraged? A first step must recognize that
28 Political ecology
Third-World political ecology does indeed constitute an emerging research agenda. Such
recognition, however, is hindered by low levels of awareness. Divided by disciplinary and
institutional affiliations, many scholars have been further isolated by the empirical and
policy-oriented bent of the research community. Where scholarly exchange has occurred,
it has tended to remain regionally based, with comprehensive Third-World exchange more
the exception than the rule (e.g. Little and Horowitz, 1987; Repetto and Gillis, 1988). A
growing sense of community, sustained by knowledge of a common research agenda,
might remove some obstacles to cooperation, and set the stage for a more intensive phase
in the development of Third-World political ecology.
As this agenda emerges, new issues will need to be addressed-the role of ideology and
culture in environmental change seems particularly important.‘” How the environment
and environmental change are perceived, and related to different aspects of human
development, influences the nature and extent of such change. Correspondingly, however,
these factors need to be integrated with the contextual and location-specific forces
discussed above.
In exploring these and other issues, political ecology must be situated in the broader
context of Third-World studies. Such integration will benefit the latter (Hettne, 1990),
while promoting more rigorous development of the former. Third-World political ecology
might be enriched by recent work in contiguous and often overlapping research agendas:
peasant studies and power analysis (Scott, 1985; Colburn, 1989; Hart et al., 1989);
household and gender studies (Watts, 1989; Whitehead, 1990); and the literature on the
politics of hunting and conservation (Beinart, 1989, 1990). As these agendas are refined,
their findings and implications need to be systematically incorporated into Third-World
political ecology, with particular reference to conflict over access and the political
ramifications of environmental change.
A more systematic definition of the research agenda is thus urgently required. Emerging
at a time of intense environmental change, Third-World political ecology attempts to
integrate environmental and political analysis to illustrate how these two activities, both
helping to shape human destiny, are interrelated, and more importantly, how the one
cannot be fully understood without the other. It is in the recognition and analysis of this
interdependence that Third-World political ecology could make its most crucial
contribution.
Acknowledgements
I am grateful to the editor, and three anonymous referees for their helpful comments. I also wish to
thank Mr. P. Stott and Professor R. H. Taylor for their constructive criticism, and the Overseas
Research Students Awards Scheme for their support of my research programme. Finally, special
appreciation to MS Shelagh J. Squire for her understanding and editorial assistance.
Notes
1. The term ‘Third World’ (as differentiated from ‘First World’) is used synonymously with
‘North-South’. In this instance, it refers to the developing countries of Asia, Africa and Latin
America.
R.4y~orm L. BRYANT 29
2. For example, see Blaikie and Brookfield (1987a), Little and Horowitz (1987) Redclift (1984,
1987) and Repetto and Gillis (1988).
3. See also Marston (1983) and Falkus (1990). Of general interest are Johnston (1989) Dryzek
(1987), Benton (1989) and Corbridge (1986).
4. Emel and Peet (1989) and Adams (1990a) critically examine several major works, notably Watts
(1983b) and Blaikie (1985).
5. See Richards (1983) and Blaikie (1989a).
6. For example, local resistance to dam construction in Thailand (Hirsch and Lohmann, 1989); and
other instances cited below.
7. See Blaikie (1985) on the integration of ‘place’- and ‘non-place’-based analyses.
8. A particularly vociferous critic of these agencies is ne Ecologist magazine (e.g. Rich, 1985). For a
mainstream critique, see Kasten Jr. (1986). Schneider (1989) also explores this subject.
9. Interstate antipathies may even derive from conflict over environmental resources; see Westing
(1986) and Mandel (1988).
10. See Adams (199Ob) and Fox (1988) on bureaucratic centralization and control in Kenya.
Evidently, such centralization and control varies between countries and regions.
11. Brown (1990), Ravenhill (1990), World Commission on Environment and Development (1987),
Angel1 et al. (1990); as environmental crises demonstrate, the growing need for international
action, equity, efficiency and sustainability are becoming increasingly intertwined, see Tolba
(1987).
12. Such is the contemporary power of TNCs that Gill and Law (1988) speak of an emerging
‘transnational stage’ in capitalist development.
13. See also Guyer and Peters (1987) and Whitehead (1990).
14. Allen and Crittenden (1987); Clarke (1990).
15. Dove (1986) and Blauert (1988) illustrate how state and local perceptions of development may
diverge.
16. For an introduction to environmental systems, see Johnston (1989).
17. This term refers to routine environmental change, and modifies Scott’s (1985) notion of peasant
resistance.
18. This weakness may be offset by linkages with international environmental groups (e.g.
Greenpeace), and with First-World non-governmental organizations sensitive to environmental
questions (Conroy and Litvinoff, 1988). On the growing importance of these groups in
international environmental diplomacy, see Caldwell (1988).
19. Ideological expression is discussed in Schmink and Wood (1987), Blaikie (1985), Beinart (1984)
and MacKenzie (1988). Another issue is the ambiguous relationship between population growth
and environmental change (Blaikie and Brookfield, 1987~). See also Adams (1990a) and
Corbridge (1986).
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