9
Chile is Timber Country
Citizenship, Justice and Scale in
the Chilean Native Forest Market Campaign
Adam Henne and Teena Gabrielson
Quien no conoce el bosque chileno no conoce este planeta.
—Pablo Neruda, 1974
Neruda’s famous claim, ‘Anyone who hasn’t been in the Chilean forest
doesn’t know this planet’, is used widely in Chile by environmentalists, travel
agents and chambers of commerce. In its simplicity, the line is appealing,
but also deceptive. ‘The Chilean Forest’ is not by any means a single entity,
and attempts to cast it in that light are deeply political projects, with serious implications for citizenship and social natures. As Bruce Braun (2002)
noted in the context of Canadian forestry, the forest that is an object of
forest conflicts is actually an assemblage of shifting discourses and political
practices. What piece of landscape can even be considered as ‘forest’ is in
part a product of the political activity of variously situated actors. At the
same time, different political actors are constituted out of conflicts over forest landscapes. In this way, timber companies, international environmental
NGOs and indigenous activists are all part of a larger Chilean social ecology.
Moreover, the forest is an assemblage of people, non-human nature, artefacts
and technologies within larger ecological, economic, cultural, discursive and
political networks. In conceptualizing the Chilean forest as a technonature,
we draw on the recent work of Damian White and Chris Wilbert (2009, 6) to
examine the diverse social natures of the forest and the extent to which these
natures are ‘technologically mediated, produced, enacted, and contested’.
By attending to the mediation and production of the forest, we highlight
the ways in which specific forms of knowledge are bound to particular scaleframes. Thus, they come to serve as axes of inclusion and exclusion within the
discourses of citizenship that are articulated in and through the construction
of specific technonatures.
In particular, we are concerned with the implications for citizenship and
justice that are written into forest conflicts, often elided in nature discourse
like that of Neruda’s poem. What version of ‘Chilean’ do we understand
when we speak of ‘the Chilean forest’? Somewhat surprisingly, academic
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studies of environmental citizenship and environmental justice have not been
well integrated (Dobson 2003; Agyeman and Evans 2006), although a number of recent normative and empirical works seek to bridge this gap (Kurtz
2005; Latta 2007a, 2008; Sandler and Pezzullo 2007; Smith and Pangsapa
2008; Sze et al. 2009; see also de Castro, this volume). The concept of scale
emerges in these studies as a particularly trenchant means of examining the
complex power dynamics of environmental conflict. As Erik Swyngedouw
(2007, 24) explains, ‘socio-environmental projects are predicated upon scalar
tactics and strategies.’
In what follows, we envision the Chilean forest as a ‘technonature’ open to
diverse but unequal constructions of citizenship subjectivity, socio-spatial relations, political economies and environmental value. Using the Chilean Native Forest Market Campaign as an example,1 we turn to the concept of scale
to illuminate the ways in which discourses of citizenship come to articulate
logics of inclusion and exclusion through the construction of ‘environmental
formations’ or the ‘historically contingent articulations between environmental imaginaries, natural resource allocations, and political economies’ (Sundberg 2008, 569). In our analysis, both Chilean environmental NGOs and
the timber industry construct environmental formations that bind scale and
science to legitimate the exclusion of the Mapuche. In contrast, the Mapuche
articulate an understanding of citizenship that draws together community
self-determination with a traditional concept of territory that includes both
humans and non-humans. Our ‘technonatural’ analysis shows the pivotal role
of scale in negotiating the claims of justice within competing discourses of
citizenship.
The Technonatural Assemblage
White and Wilbert (2009) propose ‘technonatures’ as a concept that captures
the increasing extent to which technologies saturate the everyday experience
of socially produced natures. The authors use the term to highlight
a growing range of voices ruminating over the claim not only that we are
inhabiting diverse social natures but also that knowledges of our worlds are,
within such social natures, ever more technologically mediated, produced,
enacted, and contested, and, furthermore, that diverse peoples find themselves, or perceive themselves as ever more entangled with things – that
is, with technological, ecological, cultural, urban, and ecological networks
and diverse hybrid materialities and non-human agencies. (6)
Such entanglements are deeply political in that technonatures both articulate
and embody social, cultural, economic and political power relations. Thus,
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the construction of any particular technonature relies on the mobilization
of power networks or ‘allied group[s] of social elites, together with particular discursive and material enrolments of nature, around a distinct socioenvironmental project’ (Swyngedouw 2007, 10). While ‘technonatures’ can
describe the co-constructive action of subalterns as well as social elites, as
becomes clear with the case of the Mapuche, elites often dominate the political process. At the time of the Chilean Native Forest Market Campaign,
the dominant voices in the technonatural construction of the Chilean Forest
belonged to the Chilean state and timber industries.
It would be difficult to overstate the importance of the forest industry to
the Chilean economy. Wood products have been a major growth industry for
decades; export volume has grown from 2.2 billion dollars in 2002 to 5.5
billion dollars in 2008 (falling to 4.2 billion dollars with the downturn in
2009). This growth puts the forest product industry second only to copper
mining in terms of contribution to the Chilean economy (INFOR 2010).
Driven by this overwhelming profitability, the plantation sector has expanded
rapidly. Chile’s forestry agency calculated that plantations, overwhelmingly
made up of exotic Monterey pine (Pinus radiata), covered more than 14 per
cent of Chile’s total forested land for a total of more than 2.3 million hectares
(INFOR 2010). This marks a staggering increase from fifteen thousand hectares in 1940 and only eighty thousand hectares even into the 1980s (Clapp
1998). Supporters of the plantation model of forestry production describe
plantations as replacement forests, taking harvesting pressure off native forests (Hartwig 1994; Sedjo and Botkin 1997); at least in Chile, though, research suggests that the lack of incentive to conserve native forest continues
to promote their exploitation and eventual conversion to plantation (Clapp
2001).
Most of the remaining native forests in Chile are temperate rainforests, an
increasingly threatened ecotype. Chile possesses about a third of the world’s
remaining intact temperate rainforest (Wilcox 1996; Neira, Verscheure and
Revenga 2002). While not as rich in biodiversity as their tropical cousins
due to their geographic isolation, Chilean forests show a very high degree
of species endemism (Aagesen 1995). Twenty-eight out of eighty-four plant
species are endemic, as well as eleven species of mammals, twenty-four species
of amphibians and thirteen species each of birds and fish (Neira, Verscheure
and Revenga 2002, 13). In addition to their biodiversity, Chilean forests
serve important ecosystemic functions, maintaining hydrological cycles and
soil stability, protecting watersheds and even acting as a carbon sink due to
their exceptionally large standing biomass (Neira, Verscheure and Revenga
2002).
Native forest cover is currently being lost at a rate of 120,000 to 200,000
hectares each year; at this rate, all native forest throughout the central re-
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gion of the country could be gone within twenty-five years (Echeverria et
al. 2006; Wilcox 1996). A number of factors are at work in this deforestation process, including agricultural clearing, firewood harvesting and forest
fires. The greatest single factor driving the loss of native forest, however, is
the growth of the plantation timber industry (Catalán 1999) – an industry
deeply indebted to technological innovation, largely through the support of
the Chilean state.
Dating back to the Pinochet regime, the state has used a variety of mechanisms to support the timber industry. The state funds research into silvicultural chemicals, harvest and management modelling and tree improvement,
including quite advanced biotechnology via Chile’s Instituto Forestal and
well-funded university forestry departments, which were notably immune
to criticism during the dictatorship’s purging of universities. Management
research includes social as well as biological technologies: integrative modelling software that can simulate forest growth and harvest patterns alongside
labour cycles and transportation costs (Bluth 2002; Camus 2006). The state
has also provided and/or protected land for forestry to the extent of confiscating it from indigenous or campesino cooperatives, while providing significant tax incentives to cover land purchases and other start-up costs of timber
production (Hartwig 1994; Aylwin 2001; Frias 2003; Quiroga 2003; Camus
2006). Finally, the state has prevented the interference of organized labour
or indigenous claims through a variety of union-busting actions, typically
framed as ‘anti-terrorist’ police actions (McFall 2001; Frias 2003; Klubock
2004; Ray 2007).
Unlike forest conflicts in Southeast Asia or the Amazon, which revolve
around multinational timber companies, the Chilean Native Forest Market
Campaign targeted domestic companies. The owners of Compañía Manufacturera de Papeles y Cartones (CMPC) and Arauco (Grupo Matte and the
Angelini family, respectively) constitute some of the greatest concentrations
of wealth in Chile, with extensive holdings in manufacturing, petrochemicals,
mining and hydroelectric generation. These industry leaders make political
capital from their dominant position in the Chilean economy, maintaining a
great deal of influence in parliamentary politics. While the military dictatorship made this influence most explicit, Matte and Angelini have had a hand
in the crafting of state economic policy since their emergence among the
small group of families in Chile’s socio-economic elite in the early twentieth
century (Fazio 2005). Post-dictatorship governments have grappled with this
legacy of interventionist capital, with varying degrees of commitment and
limited success at insulating themselves from its influence (Carruthers 2001;
Ffrench-Davis 2002; Silva 2002). It is the thorough and persistent intermingling of state and capital that has underwritten the economic and political
projects linked to the plantation sector’s dramatic expansion.
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Chile’s environmental movement, as noted, has framed the issue of forest
protection and loss primarily around the conversion of native forest to timber
plantation. At stake in that conversion is the national patrimony of biodiversity that native forests represent. Biodiversity as a concept in forest conflicts has global resonance and a thorny history (Zerner 1996; Escobar 1998;
Braun 2002); some have suggested that the quantitative underpinnings of
biodiversity conservation serve as a sort of scientific proxy for fuzzier notions
like wilderness or the sublime landscape that drove earlier periods of nature
conservation (Song and M’Gonigle 2001; Whitten, Holmes and Mackinnon
2001; Carolan 2006). The Chilean movement does not carry the history of
colonial preservationism that characterizes the field in North America and
Europe; the birth of the movement is often dated to the founding of the
Comité Pro-Defensa de la Fauna y Flora (Fauna and Flora Defence Committee, or CODEFF) in 1968, when many of the current leaders were graduate
students in the biological sciences (CODEFF 2005). Current efforts to protect Chile’s forests draw discursively and materially on biodiversity conservation as a global and highly technology-mediated phenomenon:
The global significance of Chile’s forests has been recognized by multiple
well-known international conservation organizations such as World Wildlife Fund, Conservation International and the World Conservation Union.
WWF, for example, has catalogued Chile’s temperate forests as one of the
top conservation-priority forest ecoregions in the Southern Hemisphere
[Global 200], while CI and IUCN have identified Chile’s forests as one of
the 25 ‘hot spots’ for biodiversity conservation in the world. (Neira, Verscheure and Revenga 2002, 18)
‘Biodiversity hot spots’ and the ‘Global 200’ are systems developed by the
largest international environmental NGOs for setting biodiversity priorities
at a global scale. This view from above is accomplished via a complex array
of species population algorithms, satellite imaging and GIS modelling. Ecoregional planning as a conservation and management strategy is explicit about
its commitment to visualizing and acting upon biodiversity across national borders, despite the political and epistemological problems this entails (Brosius
and Russell 2003; Brosius 2004). For Chilean NGOs to cast their national
patrimony, the ‘Chilean forest’, in this global technocratic frame is a tense but
unambiguous statement about what sort of technonature they aim to defend.
Where environmentalists are concerned with the threat plantations pose
to biodiverse native forests, the establishment of new plantations on nonforested land is not without controversy. The majority of pine plantations are
located in Chile’s VIII, IX and X regions, an area that corresponds closely
to the territory recognized by the Spanish crown during the colonial period
as belonging to the indigenous Mapuche. While population and land ten-
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ure have of course shifted dramatically in the three hundred years since that
recognition, more than 200,000 Mapuche, or nearly a third of those living
in Chile, still live in the rural areas of these three regions (INE 2003). With
a large and marginalized indigenous population already confined to small
reducciones (reservations) and facing population pressure on their lands, the
arrival of a land-hungry new industry was bound to lead to conflict.
Mapuche activists and community leaders argue that the expansion of the
plantation sector comes at the expense of their territorial, environmental and
political rights. Many of the properties currently being converted into plantations are located within territory returned to the Mapuche under Spanish
‘títulos de merced’, or claimed by Mapuche cooperatives under the socialist
Allende administration and ratified according to the agrarian reform laws.
These lands became available to timber companies only after having been
taken by force during the military dictatorship’s ‘rollback’ of the land reform (Bengoa 1999; Frias 2003). Even in cases where rights to the lands
themselves are not in question, activists claim that the environmental impacts
of industrial tree farming on neighbouring properties are threatening the
health and livelihoods of indigenous communities. This may take the form
of pesticides, erosion, floods, drought, or the lack of access to firewood and
wild plants (Catalán 1999; McFall 2001; Rohter 2004). Mapuche concerns
overlap with a variety of expert domains and technologies – hydrology and
geomorphology in terms of flooding and drought, forest ecology in terms of
the extirpation of native food and medicinal species, toxicology in terms of
the leaching of pesticides into community water tables and so on. Measuring
the extent of these impacts scientifically becomes a challenge to the resources,
flexibility and interdisciplinary expertise of researchers and community advocates. As a result, the process of evaluating and documenting impacts and
introducing them to public-policy arenas has called for alternative models
of doing science, integrating expert research with community monitoring,
participatory methods and public activism. Through activist bodies including
the Latin American Observatory of Environmental Conflicts (OLCA) and
the Institute for Indigenous Studies, Mapuche organizations are attempting
to build a network of scientists to document the impact of plantations on
their communities by incorporating participatory community research and
the first-hand accounts of individuals who have been dislocated or injured
(see, for example, Frias 2003; Catalán et al. 2006). This model of ‘citizen science’ (Irwin 1995; Corburn 2005; Leach, Scoones and Wynne 2005) resonates with the network of expertise and activism familiar to environmental
justice circles in North America and also with similar kinds of emerging activism in other parts of Latin America (see Merlinsky and Latta, this volume).
Significantly, however, citizenship discourse as such does not appear in the
repertoire of the Mapuche organizations engaged with this campaign. For
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these activists, as for many contemporary Mapuche, the term Chilean refers
specifically to non-Mapuche – to white Chileans, a category from which they
are excluded a priori. Rather than appeal to their rights as citizens of Chile,
these activists frame the forest conflict in terms of autonomy and territory.
In particular, the concept of wallmapu, usually translated as ‘territory’, explicitly refers to all traditional Mapuche territory on both sides of the Chile–
Argentina border (Toledo 2006). With equally subversive implications, wallmapu also includes non-human persons: animals, trees, rivers and soils, the
spirit world. Contemporary activists invoke traditions of solidarity building
through reciprocal exchanges of tobacco, dyes, foodstuffs and sacrificial offerings; these circuits historically extended from Pacific to Atlantic coasts,
and incorporated mountains, rivers and animal spirits as well as neighbours
and extended kin groups (Coña 1930; Hilger 1966). By renovating a territorial principle outside the Chilean state on so many levels, Mapuche activists
critique Chile’s nexus of state and capital, while positioning themselves as
historically and culturally privileged environmental subjects.
As these rich and differing understandings of the Chilean forest suggest,
forest landscapes are neither homogeneous entities nor abstract spaces, but
spaces of technonature open to multiple imaginings and discursive constructions that bind together non-human nature, citizen subjectivities, artefacts,
socio-spatial relations and technological understandings within larger networks of cultural and material flows. In what follows, we demonstrate the
centrality of a politics of scale to the different political fortunes of these alternate technonatures in the context of a conflict over the future of Chile’s
forests in the Chilean Native Forest Market Campaign.
Citizenship, Justice and the Politics of Scale
Originating in the fields of political and radical geography, the concept of
scale refers to a fragment of landscape that is understood to be socially produced (Agnew 1997). While conceptions of scale may overlap with ontologically defined geographical boundaries, as in the familiar conceptions of local,
urban, regional, national and global, scale is the product of social relations
and political contestation. The politics of scale, or the ‘production, reconfiguration, or contestation of particular differentiations, orderings and hierarchies among geographical scales’, permeates discussions of environment
(Brenner 2001, 600). Questions of scale are critical to understanding the
discursive framing of environmental problems and solutions, the mobilization
and counter-mobilization of constituencies and the construction and adoption of political strategies by various parties to environmental conflict (Williams 1999; Towers 2000; Kurtz 2003; Bickerstaff and Agyeman 2009; Sze
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et al. 2009). In an effort to identify how activists contend with the ‘social
complexity and spatial ambiguity inherent in environmental justice disputes’,
Hilda Kurtz (2003, 892, 894) turns to ‘scale frames’ or ‘the discursive practices that construct meaningful (and actionable) linkages between the scale
at which a social problem is experienced and the scale(s) at which it could be
politically addressed or resolved’.
The frame of particular interest here is scale as means of inclusion/exclusion, primarily because of its bearing on questions of citizenship. As critics
often note, as much as citizenship defines a community of equals empowered
to engage in decision making regarding collective welfare, it also establishes
the boundaries of that community and marks those excluded. It should come
as no surprise, then, that actors in environmental conflict often draw on discourses of citizenship to articulate scale frames of inclusion and exclusion so
as to advance their own interests. Such frames can integrate aggrieved parties
into larger social movements, or they may legitimate the exclusion of the
aggrieved by marginalizing and circumscribing their claims (Towers 2000;
Kurtz 2003, 2005; Sundberg 2008; Sze et al. 2009).
The processes by which exclusionary scale frames become legitimized are
often deeply intertwined with processes of racialization. It seems wise to approach this point with caution, as Latin America’s racial regimes do not map
neatly onto the models of racial discrimination developed by environmental
justice scholars in North America. Nonetheless, if we consider race as an
historical process rather than a demographic category (Pulido 1996), the relevance to the Chilean context becomes clearer. As Juanita Sundberg (2008,
571) explains, ‘White supremacy and white privilege inform legal systems,
and everyday understandings of self and other, as well as the organization of
space, place, and, I argue, conceptions of appropriate natural resource management.’ Drawing upon several distinct historical examples from Latin
America, Sundberg shows the intertwining of processes of racialization and
the construction of environmental formations. In the modern era, such articulations are often central to defining the boundaries of citizenship (see also
Sundberg’s contribution to this volume).
In the environmental formations that emerge, the ideal citizen is often depicted as one who is positioned to know or imagine, and potentially engage
in, a very particular green ‘good life’ that draws heavily on Western conceptions of the non-human natural world and humans’ appropriate relation
to it (Gabrielson and Parady 2010). With an intellectual history based in colonialism and industrial urbanization, such green ideals often depend upon a
deeply entrenched nature/culture dualism, a vision of the non-human natural
world as either ripe for development or as pristine nature to be protected and
defended (Latta 2007b). As it travels from Global North to Global South, or
from affluent white Chile to marginal indigenous Chile, the dualistic ethics
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resonate with existing hierarchies of value. Across these formations, expert,
abstract and scientific forms of knowledge often come to legitimate exclusions rooted in misrecognition (Kurtz 2009). In a discussion of the racialized
state, Kurtz (2009) explains how the particular and experiential knowledge
of environmental justice activists is often pitted against the more abstract, scientific and expert knowledge of the state that reinforces a ‘liberal universality
that does no small disservice to non-white populations’ (693).
Exclusionary discourses that privilege expert forms of knowledge are often
central to the construction of specific environmental formations and deeply
bound up with a politics of scale. Scale is not ontologically given, but constructed through political conflict and articulated discursively, politically and
geographically. These articulations are key in constituting the environmental
imaginary or discursive ideal that defines a particular environmental formation; from them emerge the networks necessary to mobilize a constituency
that can institute and maintain that particular ideal. Further, ‘these relational
scalar networks articulate with produced territorial or geographical configurations that also exhibit scalar dimensions’ (Swyngedouw 2007). In the case
of the Chilean Native Forest Market Campaign, the politics of scale reveal
an underlying consensus between the Chilean timber industry and environmental NGOs. On the face of it, the two groups’ environmental formations
would seem to pit preservation against development. However, underlying
this surface conflict exists a shared reliance on an international scalar dimension that includes networks of transnational environmental NGOs, North
American consumers and an international timber market. Attending to the
conflicting scalar dimensions at work in this case illuminates the ways in which
the geo-political networks binding the Global North and South prompt a
construction of Chilean citizenship conducive to the interests of both native
forest preservation and plantation development. This underlying consensus
develops at the expense of the community autonomy and territorial sovereignty of the Mapuche.
The Chilean Native Forest Market Campaign
The roots of the campaign lie in earlier attempts to pressure wood retailers in
the United States to raise their environmental standards for wood products.
Beginning in 1997, Rainforest Action Network (RAN) launched a campaign
against Home Depot and other United States retailers of forest products.
The campaign consisted of boycotts and letter writing, as well as dramatic
street theatre events involving banner hangings, lockdowns, a giant inflatable
dinosaur and so on. A number of celebrities, including R.E.M. and the Dave
Matthews Band, added to the pressure. In 1999, Home Depot responded to
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the extended campaign by announcing a commitment to stop selling wood
from ‘environmentally sensitive areas’. The home improvement megastore
denied that they were responding to pressure from environmentalists, and
described the policy change as the result of lengthy consideration of their
‘responsibility as a global leader to help protect endangered forests’ (Hagerty
1999). Nonetheless, environmental activists used this victory as a point of
leverage to encourage Home Depot to pursue more proactive policies and to
pressure other retailers to follow their example.
In 2002, Chilean environmental NGOs (Defensores del Bosque Chileno,
CODEFF and Fundación Terram, among others) began writing letters to
‘more than 100 forestry businesses speaking of the necessity of putting an
end to the replacement of native forests by forest plantations’ (Sanger, in
Anderson 2003). Only one responded, in the negative, and indeed there had
been precious little dialogue in Chile at that point on the subject of more
sustainable logging practices. Another controversial aspect of the campaign
at this point was the participation of famed Chilean novelist Isabel Allende,
who joined Defensores del Bosque Chileno in encouraging Chilean producers to harvest more sustainably, and called on North American consumers to
purchase only sustainable wood products. Allende’s participation was decried
as treason (González 2002).
On 13 September 2002, North American NGO ForestEthics, cosponsored by a large alliance of environmental groups, placed a full-page advertisement in the New York Times asking North American consumers to avoid
buying wood products unsustainably harvested in Chile. While the environmentalists were at pains to point out that the ad was calling for educated consumerism rather than an outright boycott of Chilean wood (Anderson 2003),
this did little to protect them from criticism. Chilean timber companies were
outraged, lambasting the Chilean cosponsors of the advertisement as traitors
to Chile. As anthropologist Julia Paley (2001) points out, such attacks are
a common strategy used against critics of government or corporate policy
in post-dictatorship Chile; any form of dissent is seen as a threat to fragile
democratic and development projects.
Before the end of 2002, however, the tide began to turn. At the request
of Aaron Sanger of ForestEthics, Home Depot officially approached their
suppliers in Chile asking them to reconsider their position. After the original
RAN Old Growth Campaign against them, the North American corporation
had learned its lesson about environmental politics. Newly appointed ‘environmental global project manager’ Ron Jarvis was explicitly tasked with the
mission of maintaining the corporation’s credibility as an environmentally
sound retailer. He had demonstrated the ability to negotiate complex environmental issues in earlier work with Indonesian suppliers, and led Home
Depot to take a principled stand against that country’s unsustainable logging
practices (Carlton 2004).
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At Jarvis’s urging, and with the threat of a pullout by Home Depot hanging over them, Chile’s two largest timber companies, CMPC and Arauco,
agreed to meet with the coalition behind the market campaign. The first set
of meetings took place at Home Depot’s main offices in Atlanta, with Ron
Jarvis as mediator. Representatives from United States groups ForestEthics,
RAN and American Lands Alliance joined Chilean environmentalists from
Defensores del Bosque Chileno, Greenpeace Chile and Instituto del Ecología
Política in pressing CMPC and Arauco for dramatic changes in their practices.
According to several of the representatives present, the companies surprised
the environmentalists with their willingness to discuss sustainable harvesting.
The principal of non-substitution (that is, not converting native forest to
plantation) became central to the discussion. The companies claimed not to
have been engaged in substitution for many years, a claim the environmentalists contested vigorously, but both parties agreed that eliminating substitution was a positive goal. No documents were signed at this point, and
all parties seemed to agree that the discussions were tense, productive, but
largely preliminary. Towards the end of the meetings, the timber companies
proposed that the second round of discussions take place in Chile, along with
a visit to their properties to demonstrate their conservation and sustainable
harvest practices.
Thus in July 2003, North American environmentalists joined their Chilean counterparts on a walking tour of CMPC and Arauco’s forestry operations. Jason Tockman, taking part as a representative of the American Lands
Alliance, later described the event as a ‘dog and pony show’. The other environmentalists generally agreed that the event was a careful public relations
operation, and that the private parks and selective harvest experiments on
display were not representative of the companies’ practices in general. Nonetheless, the discussions established the grounds for compromise. While the
content remained uncertain, it was clear that both sectors would at some
point sign an agreement putting an end to the campaign and committing the
companies to more sustainable practices. Negotiations over the content of
the agreement continued by email and teleconference for several months.
Significant differences of opinion appeared among interview subjects as
far as when and to what extent the interests of Mapuche activists entered
into the campaign. Mapuche activists argued that they had lent information
and support to the campaign from the beginning. Chilean environmentalists say that from the start, the campaign was based on native forests and
never addressed issues of Mapuche territorial rights. As the negotiations towards a final agreement progressed, the contested role of Mapuche activists
in the campaign became more salient. In September 2003, ForestEthics and
American Lands Alliance invited Alfredo Seguel, of the Mapuche organization Konapewman, to speak about Chilean forest issues at the counterforum outside the WTO ministerial in Cancún. Jason Tockman of American
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Lands Alliance accompanied Seguel and handled his travel arrangements; in
the process, the two became friends. Towards the end of the forum, Seguel
expressed his concern to Tockman that the environmentalists in the campaign were negotiating with the timber companies. How, he asked, could
environmentalists sign deals regarding the sustainable use of territories that
by right belonged to the Mapuche, especially when the timber companies at
the table were primary actors in the repression of those rights? Tockman took
this concern very much to heart, and brought the issue back to his colleagues
in the United States. While all agreed that the issue was important, Tockman
says he was the only one who felt that it might require calling off negotiations.Towards the end of September, American Lands Alliance invited Pablo
Huaiquilao, another member of Konapewman, to take part in a speaking tour
of the United States. Huaiquilao travelled the Southeast with Tockman and
an indigenous Mexican activist, speaking about the impact of pine plantations
on Mapuche communities. He was also concerned about the negotiations
still taking place, and asked Tockman to pressure his colleagues to withdraw.
So late in the game withdrawal seemed improbable, but Tockman encouraged Huaiquilao and others in Konapewman to put their concerns in writing
as soon as possible. The North American environmental activists emphasized
that they were anticipating a written intervention from the Mapuche activists
and further dialogue from their Chilean NGO counterparts; unfortunately,
neither of these written communiqués appeared until after the agreement
was signed.
In November 2003 the environmentalists and the timber companies (along
with Home Depot) signed an agreement. CMPC and Arauco committed
to end substitution on their properties, to end the promotion of substitution by other contracted parties and to refuse to purchase timber from lands
converted after a given period of time. In return, the environmentalists lent
their support to the companies’ harvesting practices and private conservation
on their own properties. According to many of the environmentalists interviewed, the content had been agreed on from the early stages of negotiation;
the remaining contention revolved around the language of the agreement:
‘It’s just a matter of working out the details, just a few words of disagreement. Of course the companies wanted us to sing praises of them and talk
about how wonderful their forest operations were, where environmentalists,
their objective was to get as many commitments and statements out of the
company, so we both had an agenda. … So the objective was to find common ground.’ The language of the agreement is indeed quite non-specific,
including statements such as ‘NGOs recognize the leadership that CMPC
and Arauco have in the Chilean forestry industry’ and ‘Companies recognize
that collaborating with NGOs on the Conservation Assessments can help
them continue their commitment to environmental responsibility.’ Echoing
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the language of Home Depot’s concessions in 1999, the timber companies
gave no indication that they were pressured into signing the agreement by
the campaign: ‘These initiatives reflect CMPC’s and Arauco’s interest in protecting Chile’s native forests’ (Defensores del Bosque Chileno 2003).
The environmental organizations announced the agreement as a victory
for Chile’s forests, and put an end to the more visible aspects of their campaign against the timber industry. The signing of the agreement, however,
marked a transitional rather than a final phase of the campaign. Defensores
del Bosque Chileno began describing the new phase of the campaign as the
‘Chilean Joint Solutions Process’; as their communications director described
it, the ‘campaign with the timber companies, together’. The companies are
collaborating with university researchers to define maps of conservation targets within their properties, while the environmental organizations prepare
local ‘community monitoring’ groups to oversee compliance with the standards of the agreement.
As the timber companies and the environmental movement formalized
this new stage of their relationship, the Mapuche activists finally went public
with their complaints. An open letter to the NGO members of the campaign
appeared in a number of print and online venues, in which a Mapuche coalition (the Coordination of Mapuche Organizations and Territorial Identities,
CITEM) denounced the agreement and called for a new and more critical
wave in the campaign against the timber companies:
To establish any negotiation with these companies is to contribute to the
washing of their image, to continue consolidation of the international wood
export markets, and to continue to ignore the fundamental problems that
exist in these territories. … Our spirit and interest is to stop the forestry
expansion for the protection of the natural resources in these areas and to
transform the current social, political and legislative relationships that the
Mapuche communities face with the Chilean State. … We believe in the
path that you had shown, involving a campaign of criticism and awareness
that you generated in the US. Therefore, we encourage you to continue in
that way, and not to negotiate, and we urge you to engage in strategies that
can be taken accordingly. (CITEM 2003)
Inclusion and Exclusion in the Chilean
Native Forest Market Campaign
In the realm of public discourse, timber companies present themselves as benevolent caretakers of the Chilean landscape, transforming degraded pastures
and ‘wasted space’ into productive forests that benefit all citizens. Particularly noteworthy here are the advertising campaigns, including the afore-
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mentioned billboards, ‘Chile: País Forestal’ (Chile: Timber Country) and the
more recent campaign, ‘Bosques para Chile’ (Forests for Chile). In a series of
TV and radio spots, a child asks her doting father how plants grow in their
garden. The father describes how a good gardener nurtures plants and soil,
stepping in at just the right time to lend nature a helping hand. A kindly
voiceover completes the analogy between forestry and gardening, explaining
that timber companies nurture the forests to help nature provide her bounty
to all of Chile.
In spite of intensive state investment in the industry, timber companies
continue to argue that private property is the paramount value of democracy; as in most liberal discourses, the role of the state is to empower individuals. This is best illustrated by the production of Chile’s ‘weak or absent
regulation’; as Alex Clapp (1998) notes, there is persistent political pressure
against regulating the forest industry in any way that might threaten this
critical source of revenue. The 2007 Native Forest Law was the product of
fifteen years of bitter debate and backroom dealing; many of Chile’s environmentalists consider it already dangerously compromised (Firmani 2008). In
summary, a discourse of benevolent private interests is mobilized to cover
the intervention of a cronyist state in support of a high-tech, rationalized
industry. The timber industry cultivates natural resources to provide for all
Chilean citizens and thereby fulfils both a paternalistic and nationalist role.
But, in doing so, we see here that cutting-edge forest technologies are just
one part of a citizenship model that Neil Harvey (2001) refers to as neoliberal or market citizenship, ‘in which subjects are created by the extension of
individual property rights and capitalist rationality’ (1046; see also Schild
1998; Baldwin and Meltzer, this volume). As the campaign and its outcome
suggest, Chilean environmentalists have mostly been willing to engage with
the model of market-based citizenship that the timber companies promote.
The communications director of Defensores del Bosque told me, when I
asked about the organization’s strategies towards government environmental
regulation, ‘We believe that the international market generating conscience
in the consumers, generating pressures on the distributors of Chilean wood,
can serve someday to change the situation within Chile.’ As noted, environmentalists actively rejected any reference to the earlier boycott campaign as a
campaign ‘against’ the timber companies: ‘No no, this is a campaign with the
timber companies, together.’
The campaign itself cast the fundamental conflict between environmentalists and timber companies in a shared conceptual language with an agreedupon technonatural object – the fate of the Chilean forest – that enabled
explicit disagreement, negotiation, agreement and subsequent collaboration.
Linked to this shared vision of the forest was a citizenship discourse that made
Mapuche claims latent to the negotiation over its future, their place within
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the campaign marginal and easily erased. Consistent with the Chilean state’s
long-standing commitment to an ‘ideology of national homogeneity’ (Latta
2007a, 232), both the timber companies and Chilean environmental NGOs
involved in the campaign constructed environmental formations that tied the
future of Chile’s forests to the good of all of its citizens. This nationalist environmental imaginary, whether it privileged economic development or the
preservation of native forests, became projected into international networks
of power in such a way as to discredit the more local and culturally specific
claims of the indigenous Mapuche. Thus, while North American consumers
are empowered to pressure the Chilean timber industry, the distributional
inequities in the treatment of the Mapuche are obscured by removing from
discussion the question of timber plantations’ encroachment on Mapuche
lands. More pointedly, the Mapuche’s deeply political claims for community, autonomy and territorial sovereignty are bracketed from a negotiation
in which the key players share a common understanding of the forest as a
technonature to be managed and administered by political elites and technological experts.
While environmentalists in Chile and elsewhere described the agreement
as a historic breakthrough, it corresponds to a familiar pattern in Chilean
politics known as ‘democracia de acuerdos’ (democracy by agreement), also
known as ‘gentleman’s democracy’, ‘democracy from above’ or ‘democracy
behind closed doors’ (Paley 2001). The irony of these qualified ‘democracies’ is not lost on the Chileans who use the terms. And yet environmental
organizations have represented themselves as spokespeople for all of Chile in
this sort of negotiation, without seeking to engender a process for broader
democratic participation or representation. When asked why the Mapuche
did not have an active stake in the campaign, environmental activists frequently replied, ‘We are protecting biodiversity for all Chileans, not just one
class.’ This is a complex situation with multiple implications for who counts
as Chilean at all; statements like these clearly cast the Mapuche as not part
of ‘all Chileans’, while simultaneously promoting negotiations over the protection of biodiversity as a legitimate venue for that decision. The conflicting scalar dimensions at work in this process of marginalization reveal the
extent to which neoliberal frameworks, universal conceptions of citizenship
and preservationist objectives can become articulated through scientific discourse. Such discourse, in turn, effectively depoliticizes nature, further delegitimizing community claims to autonomy and calls for more participatory
democratic process.
The story of Mapuche involvement with the Chilean Native Forest Market
Campaign demonstrates that while collaborations between indigenous activists and environmentalists can be rhetorically powerful in some settings, they
can run aground in a number of ways. Potential problems include not just
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the incommensurable views of nature noted by environmental anthropologists (see, for example, Brosius 1997; West 2006) or the structural conflicts
of interest debated by conservationists (Redford and Sanderson 2000; Berkes
2004; also compare Chapin 2004). Equally salient are the mundane and often unintentional issues of who is invited to which meetings and what types
of organizations and leaderships should be consulted – everyday forms of
racism and exclusion.
Notes
1. The material on the Chilean Native Forest market campaign is based on ethnographic interviews with Mapuche activists and Chilean and North American environmental activists
conducted by Adam Henne in 2003. Unless otherwise cited, quoted statements are drawn
from these interviews.
References
Aagesen, D. (1995) ‘On the Northern Fringe of the South American Temperate Forest,’ Environmental History, Vol. 3, No. 1, pp. 64–85.
Agnew, J. (1997) ‘The Dramaturgy of Horizons: Geographical scale in the ‘Reconstruction of
Italy’ by the New Italian Parties, 1992–95,’ Political Geography, Vol. 16, pp. 99–121.
Agyeman, J., and B. Evans. (2006) ‘Justice, Governance, and Sustainability: Perspectives on Environmental Citizenship from North America and Europe,’ in A. Dobson and D. Bell (eds),
Environmental Citizenship. Cambridge: MIT Press, pp. 185–206.
Anderson, S. (2003) ‘Aaron Sanger’s El Mercurio Interview,’ Santiago Times, 11 December.
Aylwin, J. (ed.). (2001) Políticas Públicas y Pueblo Mapuche. Concepción: Ediciones Escaparate.
Bengoa, J. (1999) Historia de un Conflicto: El Estado y los Mapuches en el Siglo XX. Santiago:
Planeta.
Berkes, F. (2004) ‘Rethinking Community-Based Conservation,’ Conservation Biology, Vol. 18,
No. 3, pp. 621–630.
Bickerstaff, K., and J. Agyeman. (2009) ‘Assembling Justice Spaces: The Scalar Politics of Environmental Justice in North-east England,’ Antipode, Vol. 41, No. 4, pp. 781–806.
Bluth, A. (2002) Chile, País Forestal. Santiago: Corporación Nacional de la Madera.
Braun, B. (2002) The Intemperate Rainforest: Nature, Culture and Power on Canada’s West
Coast. Minneapolis: University of Minnesota Press.
Brenner, N. (2001) ‘The Limits to Scale? Methodological Reflections on Scalar Structuration,’
Progress in Human Geography, Vol. 25, No. 4, pp. 591–614.
Brosius, J. P. (1997) ‘Endangered Forests, Endangered Peoples: Environmentalist Representations of Indigenous Knowledge,’ Human Ecology, Vol. 25, No. 1, pp. 47–69.
———. (2004) ‘Seeing Natural and Cultural Communities: Technologies of Visualization in
Conservation.’ Paper presented to the Berkeley Environmental Politics Working Group, 2
February.
Brosius, J. P., and D. Russell. (2003) ‘Conservation from Above: Transboundary Protected
Areas and Ecoregional Planning,’ Journal of Sustainable Forestry, Vol. 17, No. 1/2, pp.
39–65.
Camus, P. (2006) Ambiente, Bosques y Gestión Forestal en Chile, 1541–2005. Santiago: LOM.
C h i l e i s Ti m b er C o u n tr y
|
165
Carolan, M. (2006) ‘The Value and Vulnerabilities of Metaphors within the Environmental Sciences,’ Society and Natural Resources, Vol. 19, No. 10, pp. 921–930.
Carlton, J. (2004) ‘Once Targeted by Protesters, Home Depot Plays a Green Role,’ Wall Street
Journal, 6 August, pp. A1, A6.
Carruthers, D. (2001) ‘Environmental Politics in Chile: Legacies of Dictatorship and Democracy,’ Third World Quarterly, Vol. 22, No. 3, pp. 343–358.
Catalán, R. (1999) Pueblo Mapuche, Bosque Nativo y Plantaciones Forestales. Temuco: Ediciones
Universidad Católica.
Catalán, R., et al. (eds). (2006) Bosques y Comunidades del sur de Chile. Santiago: Editorial
Universitaria.
Chapin, M. (2004) ‘A Challenge to Conservationists,’ Worldwatch Magazine November–
December, pp. 17–31.
Clapp, R. A. (1998) ‘Waiting for the Forest Law: Resource-Led Development and Environmental Politics in Chile,’ Latin American Research Review, Vol. 33, No. 2, pp. 3–37.
———. (2001) ‘Tree Farming and Forest Conservation in Chile? Do Replacement Forests Leave
any Originals Behind?’ Society and Natural Resources, Vol. 14, pp. 341–356.
Coordinación de Identidades Territoriales Mapuche (CITEM). (2003) ‘Carta de las Organizaciones Mapuches,’ online report, http://www.wrm.org.uy/paises/Chile/articulo3.html
(accessed May 2011).
Comité pro Defensa de la Fauna y Flora (CODEFF). (2005) Ciudadanos de la Tierra: Construyendos Sueños 1968–2005. Santiago: CODEFF.
Coña, P. (1930) Vida y Costumbres de los Indígenas Araucanos en la Segunda Mitad del Siglo
XIX. Santiago: Imprenta Cervantes.
Corburn, J. (2005) Street Science: Community Knowledge and Environmental Health Justice.
Cambridge, MA: MIT Press.
Defensores del Bosque Chileno. (2003) ’Documento de Acuerdo,’ online report, http://www
.mipapel.cmpc.cl/mipapel69/p2.html (accessed May 2011).
Dobson, A. (2003) Citizenship and the Environment. New York: Oxford University Press.
Echeverria, C., et al. (2006) ‘Rapid Deforestation and Fragmentation of Chilean Temperate
Forests,’ Biological Conservation, Vol. 130, No. 4, pp. 481–494.
Escobar, A. (1998) ‘Whose Knowledge, Whose Nature? Biodiversity, Conservation, and the
Political Ecology of Social Movements,’ Journal of Political Ecology, Vol. 5, pp. 53–82.
Fazio, H. (2005) Mapa Actual de la Extrema Riqueza en Chile al año 2005. Santiago: LOM
Ediciones.
Ffrench-Davis, R. (2002) Economic Reforms in Chile: From Dictatorship to Democracy. Ann Arbor: University of Michigan Press.
Firmani, C. (2008) ‘El Bosque Nativo Tiene Ley,’ Biblioteca de Congresa Nacional de Chile,
4 April, online report, http://www.bcn.cl/carpeta_temas_profundidad/ley-bosque-nativo
(accessed May 2011).
Frias, G. (2003) Invasión Forestal: Khla Nagnegai taíñ Weichangepan. Toronto: IDRC.
Gabrielson, T., and K. Parady. (2010) ‘Corporeal Citizenship: Rethinking Green Citizenship
through the Body,’ Environmental Politics, Vol. 19, No. 3, pp. 374–391.
González, G. (2002) ‘Isabel Allende Helps Defend Native Forests,’ Environment Chile, 24 July,
online report, http://www.mapuche-nation.org/english/html/news/n-50.htm (accessed
May 2011).
Hagerty, J. (1999) ‘Home Depot Vows to Change Policy on “Sensitive” Wood Use,’ Wall Street
Journal, 27 August.
Hartwig, F. (1994) La Tierra que Recuperamos. Santiago: Editorial Los Andes.
Harvey, N. (2001) ‘Globalization and Resistance in Post-Cold War Mexico,’ Third World Quarterly, Vol. 22, No. 6, pp. 1045–1061.
166
|
En vi ron m e n t a l M a rg i n a l i ty a n d th e S tr u g g l e f o r J u s ti ce
Hilger, I. (1966) Huenun Ñamku: An Araucanian Indian Remembers the Past. Norman: University of Oklahoma Press.
Instituto Nacional de Estadísticas (INE). (2003) ‘Censo 2002: Síntesis de Resultados.’ Santiago:
INE Chile.
Instituto Nacional Forestal (INFOR). (2010) ‘Estadísticas Forestales 2009,’ Boletín Estadístico
126. Santiago: INFOR.
Irwin, A. (1995) Citizen Science: Studies of People, Expertise and Sustainable Development. London: Routledge.
Klubock, T. M. (2004) ‘Labor, Land, and Environmental Change in the Forestry Sector in
Chile, 1973–1998,’ in P. Winn (ed.), Victims of the Chilean Miracle. Durham: Duke University Press, pp. 337–388.
Kurtz, H. (2003) ‘Scale Frames and Counter-Scale Frames: Constructing the Problem of Environmental Injustice,’ Political Geography, Vol. 22, pp. 887–916.
———. (2005) ‘Alternative Visions for Citizenship Practice in an Environmental Justice Dispute,’ Space and Polity, Vol. 9, No. 1, pp. 77–91.
———. (2009) ‘Acknowledging the Racial State: An Agenda for Environmental Justice Research,’ Antipode, Vol. 41, No. 4, pp. 684–704.
Latta, P. A. (2007a) ‘Citizenship and the Politics of Nature: The Case of Chile’s Alto Bío Bío,’
Citizenship Studies, Vol. 11, No. 3, pp. 229-246.
———. (2007b) ‘Locating Democratic Politics in Ecological Citizenship,’ Environmental Politics, Vol. 16, No. 3, pp. 377–393.
———. (2008) ‘The Ecological Citizen,’ in E. Isin (ed.), Recasting the Social in Citizenship.
Toronto: University of Toronto Press, pp. 239–260.
Leach, M., I. Scoones and B. Wynne. (2005) Science and Citizens: Globalization and the Challenge of Engagement. London: Zed Books.
McFall, S. (ed.). (2001) Territorio Mapuche y Expansión Forestal. Temuco: Ediciones Escaparate.
Neira, E., H. Verscheure and C. Revenga. (2002) Bosques Frontera de Chile: Un Patrimonio
Natural a Conservar. Santiago: Instituto de Recursos Mundiales.
Paley, J. (2001) Marketing Democracy: Power and Social Movements in Post-Dictatorship Chile.
Berkeley: University of California Press.
Pulido, L. (1996) ‘A Critical Review of the Methodology of Environmental Racism Research,’
Antipode, Vol. 28, No. 2, pp. 142–159.
Quiroga, R. (2003) Comercio, Inversiones y Sustentabilidad: El caso de Chile. Santiago: LOM.
Ray, L. (2007) Language of the Land: The Mapuche People in Argentina and Chile. Copenhagen:
IWGIA.
Redford, K., and S. E. Sanderson. (2000) ‘Extracting Humans from Nature,’ Conservation Biology, Vol. 14, No. 5, pp. 1362–1364.
Rohter, L. (2004) ‘Mapuche Indians in Chile Struggle to Take Back Forests,’ New York Times,
11 August.
Sandler, R.,. and P. Pezzullo (eds). (2007) Environmental Justice and Environmentalism: The
Social Justice Challenge to the Environmental Movement. Cambridge: MIT Press.
Schild, V. (1998) ‘Market Citizenship and the ‘New Democracies’: The Ambiguous Legacies of
Contemporary Chilean Women’s Movements,’ Social Politics, Vol. 5, No. 2, pp. 232–249.
Sedjo, R., and D. Botkin. (1997) ‘Forest Plantations to Spare Natural Forests,’ Environment,
Vol. 39, No. 10, pp. 14–20.
Silva, E. (2002) ‘Capital and the Lagos Presidency: Business as Usual?’ Bulletin of Latin American Research, Vol. 21, No. 3, pp. 339–357.
Smith, M., and P. Pangsapa. (2008) Environment and Citizenship: Integrating Justice, Responsibility, and Civic Engagement. London: Zed Books.
Song, S., and R. M’Gonigle. (2001) ‘Science, Power, and System Dynamics: The Political Economy of Conservation Biology,’ Conservation Biology, Vol. 15, No. 4, pp. 980–989.
C h i l e i s Ti m b er C o u n tr y
|
167
Sundberg, J. (2008) ‘Placing Race in Environmental Justice Research in Latin America,’ Society
and Natural Resources, Vol. 21, No. 7, pp. 569–582.
Swyngedouw, E., 2007. ‘Technonatural Revolutions: The Scalar Politics of Franco’s HydroSocial Dream for Spain, 1939–1975.’ Transactions of the Institute of British Geographers, Vol.
32, 9–28.
Sze, J., et al. (2009) ‘Defining and Contesting Environmental Justice: Socio-natures and the
Politics of Scale in the Delta,’ Antipode, Vol. 41, No. 4, pp. 807–843.
Toledo, V. L. (2006) Pueblo Mapuche, Derechos Colectivos y Territorio. Santiago: LOM Ediciones / Chile Sustentable.
Towers, G. (2000) ‘Applying the Political Geography of Scale: Grassroots Strategies and Environmental Justice,’ The Professional Geographer, Vol. 52, No. 1, pp. 23–36.
West, P. (2006) Conservation is Our Government Now: The Politics of Ecology in Papua New
Guinea. Durham: Duke University Press.
White, D., and C. Wilbert. (2009) ‘Inhabiting Technonatural Time/Spaces,’ in D. White and
C. Wilbert (eds), Technonatures Environments, Technologies, Spaces, and Places in the Twentyfirst Century. Waterloo: Wilfrid Laurier University Press, pp. 1–32.
Whitten, T., D. Holmes and K. Mackinnon. (2001) ‘Conservation Biology: A Displacement
Behavior for Academia?’ Conservation Biology, Vol. 15, No. 1, pp. 1–3.
Wilcox, K. (1996) Chile’s Ancient Forest: A Conservation Legacy. Redway: Ancient Forests
International.
Williams, R. (1999) ‘Environmental Injustice in America and its Politics of Scale,’ Political Geography, Vol. 18, No. 1, pp. 49–73.
Zerner, C. (1996) ‘Telling Stories about Biological Diversity,’ in S. B. Brush and D. Stabinsky
(eds), Valuing Local Knowledge. Washington, DC: Island Press, pp. 68–101.