USTICE,
QUITY +
PROJECTIONS volume 8
USTAINABILITY MIT JOURNAL OF PLANNING
FOUNDER
Eryn Deeming
EDITORS
Isabelle Anguelovski
Anna Livia Brand
Rachel Healy
DESIGN + LAYOUT
Marissa Cheng
FACULTY ADVISOR
Lawrence J Vale
MIT JOURNAL OF PLANNING
EDITORIAL BOARD
Professor Julian Agyeman
Department of Urban and Environmental Policy and Planning, Tufts University
Professor Gianpaolo Baiocchi
Department of Sociology, Brown University
Professor Marcel Bursztyn
Kennedy School of Government, Sustainability Science Program, Harvard University
Professor JoAnn Carmin
Department of Urban Studies and Planning, MIT
Professor Susan S. Fainstein
Graduate School of Design, Harvard University
Professor John Forester
Department of City and Regional Planning, Cornell University
Professor Susan Holcombe
The Heller School for Social Policy and Management, Brandeis University
Professor Peter Marcuse
Graduate School of Architecture, Planning, and Preservation, Columbia University
Professor David Pellow
Department of Sociology, University of Minnesota
Professor J. Phillip Thompson
Department of Urban Studies and Planning, MIT
PROJECTIONS volume 8
JUSTICE, EQUITY + SUSTAINABILITY
(c) 2008 MIT DEPARTMENT OF URBAN STUDIES + PLANNING
All rights reserved. No part of this journal may be reproduced in any form by any electronic or mechanical means without prior written
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TEXT SET Univers 57 Condensed, Univers 47 Condensed. Digitally published using Adobe InDesign. Printed and bound
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COVER IMAGE “Untitled” Rebuilding Series, mixed media on wood. Painting + image, Anna Livia Brand.
TABLE OF CONTENTS
0 EDITORIAL 6
Isabelle Anguelovski, Anna Livia Brand, Rachel Healy
1 INTRODUCTION EQUITY? “THAT’S NOT AN ISSUE FOR US: WE’RE HERE TO SAVE
THE WORLD” 10
Professor Julian Agyeman
2 THE THIRD E : EQUITY + REDISTRIBUTION AS CONDITIONS OF SUSTAINABILITY 16
Dr. Murtaza Baxamusa
3 ADDRESSING NEEDS AS RIGHTS : IMPLEMENTING A RIGHTS-BASED APPROACH TO
DEVELOPMENT IN CAMBODIA 32
Amy Lint
4 BEYOND LAND REFORM TO ACHIEVE RURAL COMMUNITY DEVELOPMENT: THE
CASE OF THE SAN JOSE AGRARIAN MUNICIPAL COOPERATIVE IN THE PHILIPPINES
50
Camille Tuason Mata
5 EXPLORING ENVIRONMENTAL JUSTICE IN SWEDEN : HOW TO IMPROVE PLANNING
FOR ENVIRONMENTAL SUSTAINABILITY + SOCIAL EQUITY IN AN “ECO-FRIENDLY”
CONTEXT 70
Karin Bradley, Ulrika Gunnarsson-Östling, and Professor Karolina Isaksson
6 ANALYSIS OF COSMOLOGY, PRAXIS + HISTORICAL INEQUALITIES IN THE
CONSTRUCTION OF SOCIONATURAL DISASTER IN THE MAM GUATEMALAN
ALTIPLANO 86
Julie Hermesse
7 PROJECTIONS SEMINAR AND FILM SERIES, SPRING 2008 100
8 FROM SOCIAL PROTECTION TO ENVIRONMENTAL PROTECTION 102
Professor Marcel Bursztyn
9 CAPABILITIES AND HUMAN RIGHTS APPROACHES : COMPETING PARADIGMS OR
RE-ENFORCING MODELS 108
Professor Susan H. Holcombe
10 BARRIERS TO CHANGING ALBERTA’S OIL + GAS TENURE SYSTEM : LESSONS
FROM AN OIL-DEPENDENT STATE 120
Colette Fluet and Professor Naomi T. Krogman
11 CREATING AN ENVIRONMENTALLY JUST PARK SYSTEM IN LOUISVILLE,
KENTUCKY 140
Carrie Beth Lasley
12 ENVIRONMENTAL INJUSTICE IN THE PASO DEL NORTE 162
Professor Timothy W. Collins, Professor Sara E. Grineski, Martha I. Flores
13 SEWAGE IN OUR BACKYARD : THE POLITICS OF RACE, CLASS, + WATER IN
ATLANTA, GEORGIA 180
Na’Taki Osborne Jelks
14 TREMÉ : THE CHALLENGES OF AN EQUITABLE RECOVERY IN NEW ORLEANS 200
Professor Isabelle Maret and Professor Barbara Allen
15 ART IS CHANGE : PUBLIC ART AS A MEANS OF ECOLOGICAL HEALING 224
Tory Foster
16 CONCLUSION CAN JUSTICE BE PLANNED? EXPLORING THE INTERSECTION OF
POLICY, POLITICS, + PLANNING 238
Professor Gianpaolo Baiocchi
Isabelle Anguelovski
Anna Livia Brand
Rachel Healy
EDITORIAL
Justice, Equity, and Sustainability are values and goals that planners and urbanists hold in high
esteem. History has shown, however, that achieving those goals is incredibly complicated and
that unjust, inequitable, and unsustainable policies and plans are implemented at every scale of
government and citizen action. Similarly, history continues to show that achieving justice, equity, and
sustainability requires coming to terms with varying and competing definitions of these terms, making
their achievement all the more complex. For instance, civil society organizations have questioned
unjust policies and development models and advocated for programs and projects based on ideas of
justice, equity and sustainability that directly benefit local communities. In the 1990s, for example,
environmental advocates in the United States began to redefine, re-envision, and reclaim open
spaces as community spaces, sites of empowerment for local communities. Several community and
environmental groups embraced community gardens, farmers’ markets in low-income communities,
landscaping projects, and park and recreational opportunities in high-density areas. In Los Angeles,
the local organization Friends of the L.A. River, together with other Asian and Latino neighborhood
activists, environmental groups, and public interest lawyers launched a battle against a powerful
ANGUELOVSKI, BRAND, HEALY
developer over a plan to develop warehouses and light industry in a large undeveloped lot adjacent
to the river.1 Their mobilization eventually saved the site, known as the Cornfield, and the developer
sold it to the state of California to establish a new park. More broadly, this struggle exhibits the
emblematic power of community-environment alliances to renew and reinvent nature in the city; to
allow marginalized groups to have access to public spaces and greater environmental goods; and to
create a higher quality of life for migrant and minority communities.
This case is one among many of failures of planners and decision-makers, who often celebrate
economic development and macro-economic growth models over projects that will directly benefit
7
local communities. Furthermore, this project exhibits the failure to understand and address the
tensions between justice, equity and sustainability and the tradeoffs that it will take to reach these
commendable goals. Across different planning contexts, we continue to see urban policies fail to
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
benefit the underprivileged because they do not address underlying reasons for citizens’ distrust;
because they fail to unearth deeper issues of inequity and exclusion; and because they fail to question
how institutional barriers maintain inequity or prohibit sustainable practices. Both in academic training
programs and in planning practice, we see the repetition of proposals that ignore the nuance and
history of communities and their environments; the micro and macro forces at work to establish
patterns of inequity, injustice, and unsustainable practices. In many ways, we are hinged to our ideals
of justice, equity, and sustainability without understanding how we undermine these ideals; we are
locked in our thinking about growth models, participatory planning, and design.
However, emerging research and work, and recent conversations among and between students,
researchers, and practitioners have raised critical questions about these ideals, both in practice and
theory. These conversations encourage us to engage in multidisciplinary scholarship and contribute
to the development of theories that are based, for instance, on the intersection of social movement
theories, natural resource management research, and city planning scholarship. Similarly, we are
challenged to conceive of the tensions between and the complexity of achieving the underlying values
we embrace as academics and practioners.
This volume of Projections attempts to ref lect these recent conversations and offer emerging scholarship
on the nexus between environmental sustainability, social equity, and justice. Our assumptions and
beliefs are that sustainable communities need to be built on a foundation of justice and equity. In
theory and in practice, this means that environmental and social degradation are closely coupled to
power inequities, thus compelling academics, researchers, and practitioners to conceptualize and build
sustainable communities and places with these essential elements in mind. Within and between rural
and urban communities and places, in developed and developing nations, we believe that achieving
sustainability demands putting equity rights at the center of planning and implementation. However,
the intersection of these values does not provide an easy road map for thought or for action. There are
real tensions between sustainability, justice, and equity and at times, tradeoffs between them.
In Volume 8 of Projections, MIT’s Journal of Planning, we are excited to bring together articles from
academics and practitioners, who theorize, critically ref lect on past experiences, and examine the
intersection of justice, equity, and sustainability as a framework for planning and action. In this
volume, we have welcomed a variety of papers, including critical analyses, theoretical critiques, plans,
observations, photo essays and other forms of ref lection to encourage a broad approach to how we
might understand the complexities and possibilities of achieving sustainability, justice, and equity.
This volume includes detailed analyses and what we have found to be thought provoking work focused
ANGUELOVSKI, BRAND, HEALY
on rights and community development in the Philippines; urban sustainability and the just and equitable
allocation of parks in Louisville, KY; cases of environmental (in)justice and racism in the United States
and in Sweden; rights-based planning and development in Cambodia; the role and contribution of arts
to sustainability; the relation between urban sprawl, sewage delivery, and waste water treatment
in poor communities in Atlanta; oil and gas extraction as related to land management practices in
Canada; social and cultural constructions of natural disasters in Guatemala; and the potential for
sustainable community rebuilding after Hurricane Katrina in New Orleans. We are honored to have
these papers introduced by Professor Julian Agyeman in a piece entitled, “Equity? That’s not an issue
8 for us. We’re here to save the world.” And we are equally honored to present a concluding ref lection
by Professor Gianpaolo Baiocchi in “Can Justice be Planned? Exploring the Intersections of Policy,
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Politics, and Planning.” We have also included in this volume two additional papers from Professor
Susan Holcombe and Professor Marcel Burzstyn who participated in a seminar and film series at MIT
in the Spring of 2008. This series was crafted around the theme of the journal, justice, equity, and
sustainability, and we were privileged to have such speakers as the above mentioned Professors
Burzstyn and Holcombe, as well as Professor Nancy Jacobs and Professor John Forester. In this
volume, Professors Burzstyn and Holcombe present their own research as related to the theme of
justice, equity, and sustainability.
We hope you will enjoy this wealth of innovative and cross-boundary work and research. It has been
quite an honor to work with all of our authors and we are grateful to the professors who agreed to
deepen the discussion in our seminar series. We would also like to thank our editorial board for their
support and time. And finally, our deepest gratitude is to our faculty advisor, Professor Larry Vale,
and also to Ezra Glenn and past Projections editors for their guidance and much needed help.
Isabelle Anguelovski
Anna Livia Brand
Rachel Healy
Summer, 2008
ANGUELOVSKI, BRAND, HEALY
9
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
[REFERENCES]
1 See Gottlieb, Robert. 2005. Forcing the spring: The transformation of the American environmental
movement. Washington, DC: Island Press. Introduction.
Professor Julian Agyeman
Department of Urban and Environmental Policy and Planning, Tufts University
EQUITY?
“THAT’S NOT FOR US. WE’RE HERE
TO SAVE THE WORLD.”
People often ask me “why should race, class, culture, justice and equity play a role in sustainability;
isn’t sustainability about ‘green’ things, you know, ‘the environment’?” My response is usually along
the lines that irrespective of whether we take a global, statewide or more local focus, a moral or
practical approach, inequity and injustice resulting from, among other things, racism and classism
are bad for the environment and bad for sustainability. What is more, the environmental or green
sustainability discourse, which includes most of the social movement and institutional discourses that
dominate the sustainability and sustainable development discourse today, does not have an analysis or
theory of change with strategies for dealing with current or intra-generational (in)equity and (in)justice
issues. While researching a BBC TV program in the early 1990s, I asked a Greenpeace U.K. staffer if
she felt that her organization’s employees ref lected multicultural Britain. She replied calmly, “No, but
that’s not an issue for us. We’re here to save the world”.
Yet, research has shown how, globally, nations with a greater commitment to equity and a
correspondingly more equitable society tend to also have a greater commitment to environmental
quality (Torras and Boyce, 1998). Good examples here are the Nordic countries of Sweden, Denmark,
Norway and Finland. Similarly, in a survey of the fifty U.S. states, Boyce et al. (1999) found that those
with greater inequalities in power distribution (measured by voter participation, tax fairness, Medicaid
access and educational attainment levels) had less stringent environmental policies, greater levels of
environmental stress and higher rates of infant mortality and premature deaths. At a more local level,
a study by Morello-Frosch (1997) of counties in California showed that highly segregated counties,
AGYEMAN
in terms of income, class and race, had higher levels of hazardous air pollutants. The message? From
global to local, human inequity is bad for environmental quality and if sustainability is to become a
process with the power to transform, as opposed to its current environmental, stewardship or reform
11
focus, justice and equity issues need to be incorporated to its very core.
With this in mind, it is my great pleasure to write this introduction to Volume 8 of MIT Projections
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
focusing on Justice and Sustainability as a Framework for Planning and Action because, as a long
time researcher in the fields of environmental justice and sustainability in both the UK and US, I’m
always struck by the ability of many, such as the Greenpeace UK staffer, to dissociate what I believe
are two inextricably linked concepts. And this reductionism, or silo-based thinking and policy making/
planning is not limited to social movement organizations. For example, Warner (2002, p. 37), in an
internet-based survey, found that “more than 40 percent of the largest cities (33 of 77) in the U.S. had
sustainability projects on the web, but only five of these dealt with environmental justice on their web
pages.” He argued that: “few communities were building environmental justice into local definitions
of sustainability. Only five local sustainability projects made these connections: Albuquerque, New
Mexico; Austin, Texas; Cleveland, Ohio; San Francisco, California and Seattle, Washington.”
This clearly illustrates the pervasiveness of what I call the equity deficit in much current U.S. (and
global) sustainability discourse and consequent policy and planning practice. Only one of Warner’s
case study cities, San Francisco, appeared to fully integrate the two concepts in its Sustainability
Plan, which was adopted in 1997. It has five environmental justice goals and its suite of sustainability
indicators includes three environmental justice indicators. This integration is what the Europeans call
‘joined-up thinking’. Indeed, the European Union trend is to talk of sustainable development policy
making and planning as ‘joined up’ or ‘connected’ policy making and planning: that is, policy making
and planning in specific areas, e.g., housing, economic development, environmental justice or ‘green’
issues, with an eye to its effect on policy and planning outputs, outcomes and frameworks as a
whole. Warner’s conclusion was that “while environmental justice seemed to be having an impact on
mainstream environmental organizations and on government agencies, this did not apparently extend
to groups working on sustainability projects” (38). Backing up Warner’s research, Portney (2003,
p.57) argues that “most [U.S.] cities that have sustainability indicators do not explicitly use social or
environmental equity.”
Maybe they just ‘get it’ in the Bay Area? For example Urban Ecology, a local not- for-profit from
Oakland says on its website that:
“Urban Ecology has not focused on the traditional environmental priorities of
preserving land, air and water. Neither have we had a traditional community
development focus aimed at, for example, generating affordable housing. Rather, our
work has integrated elements of these disciplines and others, with healthy “human
habitats” as the common denominator. We have sought to advance sustainability
in the Bay Area using three main strategies -- alternative visioning, education and
policy advocacy, with all of our work grounded in the three E’s of environment,
economy and social equity.” (http://www.urbanecology.org).
Healthy “human habitats” I would argue, can only be achieved through what I call ‘just sustainability’:
“the need to ensure a better quality of life for all, now and into the future, in a just and equitable
manner, whilst living within the limits of supporting ecosystems” (Agyeman et al., 2003, p.5). Just
AGYEMAN
sustainability prioritizes justice and equity in the development of sustainable communities, but, and
fundamentally, does not downplay the environment, our life support system. Our present ‘green’ or
‘environmental’ orientation of sustainability is basically ‘green washing’: tweaking our existing policies
12 and plans but not altering the capitalist economic mode of production. This orientation fits squarely
within the heavily critiqued ecological modernization thesis (Hajer, 1995; Fisher and Freudenberg,
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
2001). On the other hand, transformative sustainability or just sustainability implies a paradigm shift
which in turn requires that sustainability takes on a redistributive function, as Baxamusa argues in
his paper in this volume. To do this, justice and equity must move to the center stage in sustainability
discourses, if we are to have any chance of a more just and sustainable, as opposed to environmentally
sustainable future.
Let me offer an example. Most cities in the global North emphasize firstly the environmentally friendly
nature of their urban public transit schemes--their ability to get car drivers off the road and their
ability to cut pollution loads – with equity issues being a lower priority. For example, in Germany,
Mayor Beate Weber’s ‘Heidelberg City Development Plan 2010’ has the following key objectives: to
reduce environmental burdens, create and preserve liberties, grant the same mobility opportunities to
everyone and account for the special situation of persons with mobility handicaps, and reduce dangers
and impairments. Equity issues are there, but unlike environmental issues, they are not listed first. By
contrast, most mayors in cities in the global South, who have developed innovative bus rapid transit
(BRT) schemes, such as former mayors Enrique Peñalosa of Bogotá, Colombia with its Transmilenio,
or Jaime Lerner of Curitiba, Brazil, with its Rede Integrada de Transporte, emphasize the equity of
such schemes. They note that car ownership and use in their cities is generally the preserve of the
rich and exemplar BRT schemes such as theirs allow access to facilities and services irrespective
of car ownership. As Peñalosa said, “Do you know what you can achieve when you cut the roads
budget in your city and spend it on other, better things”? (Peñalosa pers. comm.) Peñalosa’s point, like
Baxamusa’s, is one of redistribution. Indeed, I would argue that the reason why Bogota and Curitiba
have become poster children for sustainable city development is precisely because they have focused
on redistributive/transformative or just, as opposed to purely environmental sustainability.
So, how do the articles in this volume address facets of the paradigm of just sustainability as I’ve
brief ly described it above? Clearly I can’t fully describe all the papers, but I’d like to raise three key
and interrelated issues foregrounded by many of the authors, in addition to my points above about the
redistributive nature of just sustainability, a point made by Baxamusa in this volume.
The first facet is the critical issue of spatial justice. Lasley argues that:
“urban parks serve as community backyards, business catalysts and tools for a
healthy population while adding nature to unnaturally paved environments. A just
city should consider equal access to such municipal benefits as integral to policy.
Louisville, Ky., is expanding park acreage and promoting healthy living under its
City of Parks expansion policy. This study examines access to parkland by race and
evaluates the expansion policy to determine if it improves access or exacerbates
inequity”.
Although Lasley argues that this access/accessibility issue is about environmental justice, I see this
in wider context, as a case study in spatial (in)justice because, as British Member of Parliament (MP)
David Lammy (2004) has argued “just as social justice requires that life chances are not distributed
along class lines, spatial justice requires that they are not distributed geographically”. As Lasley
argues:
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“Louisville could set an example for other cities by expanding the park system in
a manner that improves the lives of all residents…… The City of Parks plan, in its
current form does little to improve accessibility to parks for minority residents.” 13
I also think that the concept of spatial justice offers politicians, policy makers and planners a more
robust, joined-up concept, one that, unlike environmental justice, they cannot ignore so easily.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
The second facet is the issue of ‘rights’. I am hearing all kinds of rights-based discourses associated
with just sustainability: the ‘Right to the City’ movement and discourse (Mitchell, 2003); the ‘per
capita environmental rights’ discourse surrounding the resource allocation concept of ‘environmental
space’ (Spangenberg, 1995; Carley and Spapens, 1997: McLaren, 2003; Buhrs, 2004); and the
‘Greenhouse Development Rights Framework’ (Baer, Athanasiou and Kartha, 2007) to name but a
few. In this volume, Osborne-Jelks evaluates the impact of urban sprawl on the right to city services,
namely sewage delivery and wastewater treatment in poor communities in Atlanta while Lint looks at
Addressing Needs as Rights. She examines a rights-based approach to development, through a case
study of communities and dams in Cambodia and the struggle between development and community
rights. She argues that:
“The rights-based approach gives development practitioners opportunity for
sustainable change by facing the difficult question of power. Development
organizations need commitment to change, beginning from the very place they
work everyday by supporting the voices of the poor and refraining from reproducing
inequalities and social hierarchies. Development practitioners and their respective
agencies must be accountable and transparent to network partners and communities
to the extent they demand of the others. A rights-based approach enables this kind
of accountability by encouraging partnerships with multidirectional communication,
and sharing in decision making, planning and evaluation efforts of strategies”
The third facet is the role of art, or more broadly the role of ‘creative industries’ and ‘creative cities’
in helping us toward a just sustainability. Foster’s paper cities Miles (1997, p.164) who argues that
the role of art is:
“… to initiate a continuing process of social criticism, and to engage defined publics
on issues from homelessness to the survival of the rain forests, domestic violence
and AIDS, whilst its purpose is not to fill museums… but to resist the structures of
power and money which have caused abjection, and in so doing create imaginative
spaces in which to construct, or enable others to construct, diverse possible
futures”
While I’m not certain of any empirical work on the linkages, I think there are probably great
commonalities between those cities that take their creative industries seriously and those that, to
paraphrase my colleague Kent Portney (2003) are “taking sustainability seriously.” One only has
to think of overlapping creativity and sustainability initiatives in cities like London, San Francisco,
Sydney, Vancouver, Seattle or Curitiba to see the point.
Again, it is my pleasure to introduce such a wealth of engaging scholarship. I hope you enjoy these
papers as much as I did.
AGYEMAN
Julian Agyeman, Ph.D.
14
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
REFERENCES
Agyeman, J, Bullard, R. and Evans, B. (2003). Just Sustainabilities: Development in an unequal world. Cambridge, MA
and London: MIT Press.
Baer, P, Athanasiou, T and Kartha, S. (2007). The right to development in a climate constrained world. The Greenhouse
Development Rights Framework. Berlin: Heinrich Böll Foundation, Christian Aid, EcoEquity, Stockholm Environment
Institute.
Boyce, J.K., Klemer, A.R., Templet, P.H. and Willis, C.E. (1999). Power distribution, the environment, and public health:
A state level analysis. Ecological Economics 29, 127-140.
Buhrs, T. (2004). Sharing environmental space: The role of law, economics and politics. Journal of Environmental
Planning and Management 47 3, 429-447.
Carley, M. and Spapens, P. (1997). Sharing our world. London: Earthscan.
Fisher, D.R., and Freudenburg, W.R. (2001). Ecological modernization and its critics: Assessing the past and looking
toward the future, Society and Natural Resources, 14, 701-709.
Hajer, M.A. (1995). The Politics of environmental discourse: Ecological modernization and the policy process. Oxford,
UK: Oxford University Press.
Lammy, D (2004) Spatial Justice and the Inner City: a key component of Labour’s third term narrative? http://www.
AGYEMAN
davidlammy.co.uk/da/21598. Accessed June 6 2008.
McLaren, D. (2003). Environmental space, equity and the ecological debt. In J. Agyeman, R. Bullard, and B. Evans (Eds.),
Just Sustainabilities: Development in an Unequal World (19-37). Cambridge, MA and London: MIT Press.
15
Miles, M. (1997). Art, space, and the city: Public art and urban futures. New York: Routledge.
Mitchell, D. (2003). The Right to the city: Social justice and the fight for public space. New York: Guilford.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Morello-Frosch, R. (1997). Environmental justice and California’s ‘Riskscape’. The distribution of air toxics and associated
cancer and non cancer risks among diverse communities. Unpublished dissertation. Department of Health Sciences.
University of California, Berkeley.
Portney, K. (2003). Taking sustainable cities seriously. Economic development, the environment, and quality of life in
American cities. Cambridge, MA: MIT Press.
Spangenberg, J. (1995). Towards a sustainable Europe. Brussels: Friends of the Earth Europe.
Torras, M. and Boyce, J.K. (1998). Income, inequality and pollution: A reassessment of the environmental Kuznets curve.
Ecological Economics 25. 147-160.
Warner, K. (2002). Linking local sustainability initiatives with environmental justice. Local Environment 7 1, 35-47.
Dr. Murtaza H. Baxamusa
THE THIRD E : EQUITY AS A
CONDITION OF SUSTAINABILITY
BAXAMUSA
17
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
ABSTRACT
Although the linkage between redistributive justice and sustainability is debatable, a significant
contribution of the sustainable development paradigm is to elevate social equity as a normative
value of growth. This article posits that this paradigm comes into direct conf lict with the value-free
development promoted by powerful urban growth coalitions. Challenging these entrenched forces
makes redistribution of power a primary condition for sustainability. This article presents a conceptual
framework linking empowerment, engagement, and equity in sustainability.
INTRODUCTION
This paper identifies and argues for the theoretical relationship between sustainability and equity.
Although textbook definitions of sustainability (Wheeler 2004; Portney 2003) have placed equity on
the same plane as the environment and the economy, there is tension related to the dominance of any
one E over the others. Despite the theoretical link between sustainability and justice being weak,
recent scholarly work in the field of environmental justice is attempting to strengthen this. This paper
argues that, in the seesaw between economy and the environment, distributional justice is a primary
condition of sustainability. This is because redistribution creates a stable state of sustainability by
impacting the primary causes of the imbalance. A deliberative process that engages the community
can shift power, which leads to long-term social change. On the other hand, “sustainability” without
the Third E is easily co-opted by entrenched power forces promoting value-free growth.
I. Plural Dimensions Of Development
One of the main contributions of the sustainability movement is the formal embracement of social
equity as a pillar of development.1 Equity has its own apex in many depictions of the sustainability
triangle along with the environment and the economy (Campbell, 1996; Serageldin, 1993; Wheeler,
2004), often referred to as the Three Es of sustainability. Toman (1994, p. 405) concludes that
“sustainability ultimately is intimately wrapped up with human values and institutions, not just
ecological functions” and underscores the importance of “balance” between all views on sustainability
BAXAMUSA
{Toman, 1994 #45}. Clark (1995, p. 242) agrees that “an argument that rejects equity must be
considered as morally reprehensible as an argument that rejects ecological sustainability”. Even
though the economy and the ecology have been the dominant players in the crucial “contest” on
solving global problems, social welfare is a key component of environmental health because of access
18
to health or welfare services {Clark, 1995 #137}.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Nevertheless, the term “sustainable development” has been a contentious one in theoretical debates
on what constitutes sustainability (Giddings, Hopwood & O’Brien, 2002). Goodland and Daly (1996,
p. 1002) staked their ground over environmental sustainability, stating: “Sustainability must not
become a landfill dump for everyone’s environmental and social wishes”. They sought to clearly
demarcate the differences between environmental, economic and social sustainability. Economic and
social sustainability were critical to sustainable development as a means of reaching the goal of
environmental sustainability.
But the claim of dominance of any one E over the others falls prey to the same singularity in the
paradigm of growth that sustainability is attempting to overcome (Gunder, 2006). The ontology of
sustainability is predicated upon reconciliation of these essential conf licts. For example, the holistic
intersection (Levins & Lewontin, 1994) or Kuhnian tensions (Verma, 1996) inherent in development
paradigms define the emergence of sustainability that is beyond just one or two dimensions. The
emerging functional form of sustainability (see Barbier, 1987; Berke, 2002; Healey & Shaw, 1993)
thus relies on “simultaneous achievement” of all the Three Es of sustainability (Jepson, 2001). The
Third E, equity, is a social dimension of sustainability, often conf lated with community empowerment
and civic engagement.
If sustainability is recognized as a “balance” between irreconcilable ideologies {Verma, 1996 #118}
or competing interests (Campbell, 1996), then there is a need for an open debate on development
without the presumed “economics imperialism” {Fine, 2002 #94}. Sustainable development is
therefore not just a constant-sum compromise between ecologists and economists, but a societal
deliberation, partly political and partly scientific {Dasgupta, 2000 #89} that restructures the way
we develop (Carvalho, 2001). In this vein, economic productivity is inextricably linked with social
welfare {Arrow, 2003 #90}, and human health with natural capital such as greenery {de Vries, 2003
#92}. There is recognition of feedback loops between the social welfare, natural resource base and
economic development {Dasgupta, 2002 #91}.
With sustainability, planners have redefined the reductivist notion of development as growth to include
socio-ecological dimensions.2 This is a paradigm shift from positivist obsessions with technique and
technological innovation {Ellul, 1967 #81}; and Lockean conceptions of social exclusion with respect
to natural property. Spurred by a global consciousness that was lacking a couple of decades ago,
recent writings of Hawken (2007), Shiva (2005), Massey (2007), and Korten (2006) have argued for
balancing the social costs of development with the economic gains. In this genre, the conditions of
the environment are webbed within social movements inextricably linked with distributional justice.
Planning for sustainability has also made a significant impact on development theory by “greening” the
agenda of development programs {Mestrum, 2003 #82}, and bringing into its fold as diverse subjects
as transport systems {Newman, 1999 #61}, settlement patterns, labor, population, basic needs and
human rights {Satterthwaite, 1997 #46; Drakakis-Smith, 1997 #58; Drakakis-Smith, 1996 #59;
Drakakis-Smith, 1995 #60}.
II. Is Sustainable Development Just?
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There are weak theoretical links between justice and sustainability. Dobson (1998) found that the
objectives between the theories of environmental sustainability and social justice are fundamentally
different as the latter is primarily concerned with distributional justice within the current generation
of human species, whereas the former transcends both time and species. Cross-sectional theories of
19
distributive justice that range from the Nozickian distribution of liberties to the Marxian distribution of
income have rarely addressed issues that span across generations or across species. Even John Rawls’
Theory of Justice, which talks about inter-generational equity, admits that “how the burden of capital
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
accumulation and of raising the standard of civilization is to be shared between generations seems to
admit of no definite answer” (Rawls, 1971, p. 284). Furthermore, according to Scott Campbell, justice
and the environment are not necessarily compatible:
…nature is inherently neither equal nor unequal, and at times can be downright
brutal…To gain a sense of historical legitimacy, we project our socially constructed
sense of equality onto the past, creating revisionist history in which nature is fair
and compassionate…The laws of nature are not the same thing however, as natural
law, nor does ecological equilibrium necessarily generate normative principles of
equity. (Campbell, 1996, p. 303)
The theoretical hiatus between the two has hurt planning for sustainability. With a few exceptions
(e.g. the Endangered Species Act in the United States) the current body of environmental law is based
mainly on anthropocentric factors as opposed to ecocentric factors.3 And in an era of dueling property
rights, conservation group’s efforts to buy up land in order to protect them reinforces the need for
property-owners to be compensated for providing environmental benefits (Frefogle 2007).
As justice is divorced from sustainability, equity becomes the forgotten child often adopted by the
occasional advocacy planner. With some notable exceptions (Agyeman, Bullard & Evans, 2002, 2003),
the equity component of sustainability is either omitted (Drakakis-Smith, 1995, Fig. 2, p. 665), or has
been relegated to a subsidiary position (Daly & Cobb, 1989) both in planning theory and in practice.
This has resulted in the lackluster economic justice policies in serious sustainability programs (see
Portney, 2003, pp. 174-5). Equity indicators are weak, superficial and non-actionable. For example,
cities do not typically measure or monitor the varying environmental risks of some groups over others.
Thus equity remains the most neglected component of sustainability:
Equity is the third and by far the least developed of the Three Es. To be sure, it
has long been a focus of many community activists, labor unions and social justice
organizers. However, these constituencies often have relatively little power, and
equity concerns frequently take a back seat in planning and political discussions.
(Wheeler 2004, 60)
The field of environmental justice is attempting to bridge the gap between sustainability and justice
by linking the origin of environmental problems to social and political drivers, such as exploitation and
power (Pellow & Brulle, 2005). It has evolved from a civil rights movement in the U.S. to an international
movement of environmental rights of women, colored and disadvantaged groups (Agyeman, 2005, pp.
14-19). Building up on the more recent theories by Fraser (1997), Nussbaum (2000), Sen (1999)
and Young (1990), allows activists and social movements to use multiple conceptions of justice that
overcome the limitations of Rawlsian redistribution to include procedural dimensions of justice such as
participation and recognition (Schlosberg, 2007). Schlosberg (2007, pp. 103-163) further claims that
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“justice to nature” is possible by extending the concepts of distribution, recognition, participation, and
capability to include both humans and nonhumans.
There is a fundamental link between economic deprivation and environmental degradation (Gandhi,
20 2007) that needs to be recognized within the framework of environmental ethics, that goes beyond
environmental justice. Physical planning challenges are symptoms of deeper geo-social problems such
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
as overcrowded schools and chronic unemployment concentrated in “distressed” urban areas {Pyatok,
2000 #172}. The deeply entrenched regional inequities in American cities mentioned by Orfield
(1997) and Rusk (2003) cannot be solved by rezoning and design guidelines alone. This calls for a
“broader agenda” that addresses class and racial issues, concentration of poverty and disinvestments,
especially in the inner-cities {Katz, 2000 #174}.
It is also important to critically examine the related concept of “smart growth” through the prism
of social justice. The underlying concept of sustainability that is relevant here is that land is a finite
resource, which leads to conf licts among uses.4 Smart growth often ties physical planning problems
to socio-economic issues such as lack of affordability and loss of community (Jackson, 1985). Yet
neither Downs (2001) or Burchel, Listokin and Galley (2000) in their enumeration of smart growth
principles mention social equity. Also missing from this discussion is the issue of ownership of land
and property rights.
Finally, the compilation of sustainability indicators is often the yardstick of distributive justice
within the practice of sustainable development. Certain indicators such as the Ecological Footprint
Index (Redefining Progress) and the Ecosystem Well-being Index (Prescott-Allen, 2001) are more
focused on environmental issues than their counterparts in the Genuine Progress Indicator and the
Human Well-being Index. Portney’s “Taking Sustainable Cities Seriously” indicator has 34 elements
(Portney, 2003, p. 65) none of which address social equity issues directly, but rather indirectly (e.g.
cluster or targeted economic development). Other indicators such as the Dashboard of Sustainability
(International Institute of Sustainable Development) and the Environmental Sustainability Index are
composite indicators with varying weights given to equity variables.
III. Redistribution As A Primary Condition Of Sustainability
It could be argued that the distribution of power and inf luence within society lies at
the heart of most environment and development challenges. (WCED, 1987, p. 49)
Sustainable development cannot occur without redistribution of power, since it challenges the
dominant power regimes promoting value-free growth. One of the most organized powers in a city
is the “growth machine coalition” (Molotch, 1976, 1988). There is considerable business interest,
particularly among those investing in property investment, development and real estate finance,
to spearhead this coalition (Molotch, 1988). Moreover, growth policies are created through closed
decision-making processes involving prestigious businessmen through a centralized system (Peterson
1981, 132). The planner relents, because elected officials are confronted with the systemic power of
organized businesses aligned with politicians, local media, and utility companies that stand to benefit
from growth. The “business-friendly” mantra of the growth machine makes value-free growth itself
a virtue:
Perhaps most important of all, local publics should favor growth and support the
ideology of value-free development. This attitude reassures investors that the
concrete enticements of a locality will be upheld by future politicians. (Logan &
Molotch, 1987, p. 60)
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The seesaw of power is ref lected in the values underpinning development. Empowerment creates a
stable state of sustainability by impacting the primary causes of the imbalance. It has been defined as
a process by which people, organizations, and communities gain mastery over their affairs (Rappaport, 21
1981, 1985, 1990; Rappaport, Swift & Hess, 1984). Thus, empowerment is about self-determination
(Himmelmann, 1996, p. 30) and democratic participation of individuals in the life of their community
(Rappaport, 1981, 1990; Rappaport, Swift, & Hess, 1984).
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
In the context of sustainability, redistribution of power is not only multi-dimensional, taking on a
different form in different people, contexts and time; it is also multi-level, at the individual, group, and
community scale (see Zimmerman & Rappaport, 1988; Zimmerman, 1990). An example of this is the
Alameda Corridor, a twenty-one mile railroad tunnel project in Los Angeles, California. The communities
around the impacted corridor organized to ensure that not only were environmental impacts from the
project addressed, but that residents were employed in the construction jobs created (Hartman, 2001,
p. 253). This same model of organizing and some of the same actors later engaged in negotiating
community benefits during the expansion of the Los Angeles International Airport (Baxamusa, 2008)
and the Los Angeles Ports Clean Truck Program.
A planner that uses “sustainability” without the condition of redistribution becomes an agent for the
growth machine. This is because “sustainable” development acquires political legitimacy that removes
process uncertainty, a prime motivator for deliberation and community inclusion (Cohen & Rogers,
2003). In fact, the distribution of uncertainty itself determines power relations (Marris, 1996).
Therefore, when a project encounters a sufficient quantum of uncertainty, it merits appropriate
political support and resources for deliberation and approval. On the other hand, if a public agency
offers a streamlined development approval process without accurate assessment and redress of the
socio-economic impacts of new development, it is shifting the uncertainty from the developer to the
community (Baxamusa, 2008).
The terms “equity”, “empowerment” and “engagement” are often used without distinction, as
components of sustainability. However there is a clear dynamic that occurs between these concepts,
each of which has its separate theoretical foundation (see Figure 1).
Working towards equity involves addressing geo-social imbalances within a community. This
motivates greater engagement of the community in planning and becomes a vehicle for empowerment.
As redistribution of power occurs, this leads to a deeper consideration of equity in sustainability
planning.
IV. Participation As A Vehicle Of Empowerment
In planning practice, cities in the United States with sustainability programs generally include
participatory processes (Portney, 2003), and there is general agreement that these processes
are necessary for sustainability (Portney, 2005; Kupcu, 2005; Wheeler, 2000).5 This necessity is
being ref lected in plans, policies and development agreements, both nationally and internationally.
To illustrate, an international agreement on the Mekong River in Southeast Asia demonstrated
environmental management and public participation to be “inextricably inter-twined” (Mullikin, Smith
& Champion, 2005). Even though some participating countries6 in this agreement are not democratic,
they have agreed to an open process, and established taskforces for soliciting public input.
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However, what is not clear is the type of participatory processes that are effective and the conditions
that make them effective. Effective means of involving stakeholders leading to the sharing of power
into project-specific decisions is generally missing from U.S. planning system (Blackburn, 2000, p.
182). According to Kent Portney, if the sustainability paradigm is to be seriously implemented, civic
22
participation must lead to community building that goes well beyond physical planning:
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Locally organized public involvement efforts, whether focused on local, statewide, or
national issues, not only provide mechanisms for residents to have their voices heard,
and for government to respond on specific issues, they also provide mechanisms of
civil society that actually change the people who participate in them.
(Portney, 2003, p. 146)
OWERME
EMP NT
S
SE DIS
ES T
OC
RIB
R
YP
UT
OR
IVE
IP A T
JU
S T IC E
P A R TI C
NT
EME
EQ
G
UI
GA
Y T
N
E AD
DR
ES S
ES ST NCE
RUCTURAL IMBALA
FIGURE 1. A Conceptual Framework on the Social Dynamic within Planning for Sustainability.
The transformative qualities of civic engagement are manifest in community empowerment,
wherein public policy responds to the mounting ecological and social problems amid
competing political interests (Orr, 2004). The sustainable development paradigm to a great
extent depends on the power dynamics within society, and the ability of the process to
generate power:
Sustainability planning will necessarily include efforts to build alternative forms of
political power though grassroots organizing, coalition, urban social movements,
lobbying, occasional litigation, and political leadership. Hard- edged political
organizing has always been necessary to bring about progressive change, whether
in civil rights, environmental, women’s or peace movements. (Wheeler, 2004, p.
239)
Unfortunately communicative practitioners relying on public discourse techniques, particularly in the
U.S., are facing an uphill battle in empowering civil society. This is partly because of the declining
participation of Americans in most aspects of civic life, and especially in politics (Putnam, 2000;
Macedo et al., 2005). This lack of involvement in civic life has led to a declining effectiveness of
democratic institutions, and in turn has weakened the justification of an affirmative state (Fung &
Wright, 2001). Recent experiments in direct citizen participation seek to reverse this trend by actively
soliciting participation, and empowering the civil deliberators with some action-making authority
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(Fung, 2001; Roberts, 2004). For example, the Habitat Conservation Planning component of the 1973
Endangered Species Act empowers local stakeholders to develop governance mechanisms and build
large-scale habitat conservation plans in fragile ecosystems around the country, and, as of 2002, 379
plans covering tens of millions of acres had been approved (Thomas, 2003). 23
The problem in defining the role of participatory processes in sustainability planning arises from a
deeper tension between the primacy of power and the primacy of process in planning theory. In order
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
to reconcile the conf licting goals of development, communicative theorists prescribe participatory
processes that allow diverse interests to compete equally using rational deliberation. Where as
participatory processes could transform power relations (see Forester, 1989; Fischer, 2006; Booher
& Innes, 2002; Stein & Harper, 2003), alternatively, existing power structures could corrupt any
process (Flyvbjerg, 1998, 2002) making participatory processes meaningless. In the latter case,
planning itself becomes a vehicle for consolidating current business-dominated power regimes (Hester,
1996).
CONCLUSION
The Third E of sustainability is essentially a just distribution of power. This should not be surprising,
since planning itself is a political activity aimed at redistribution of power (Douglass & Friedmann,
p. 1998). Nevertheless, there is a tendency to omit this dimension in the theory and practice of
sustainability. This omission is not just a compromise aimed at balancing the economic cost of providing
environmental benefits, but is a Machiavellian attempt by the “growth coalition” to consolidate its
power. Planners become instruments of this coalition, when they apply the “sustainable” adjective
to plans, policies and projects that disempower the community. The key challenge for sustainability
planning is to embrace redistribution of power, without losing its broad support amongst developers.
After a long struggle, the environmental movement has succeeded in creating global currency on
issues such as climate change and natural resource protection. This currency needs to be invested
in systemic change that tilts the balance of power towards a progressive agenda for generations to
come. This socio-economic agenda, however tangential to deep ecological concerns, is necessary to
keep broader coalitions alive that will bolster the cause of their constituents in the halls of democracy
in the United States and elsewhere.
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24
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
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25
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
AUTHOR’S BIOGRAPHY
Murtaza H. Baxamusa holds a Ph.D. in Planning from the University of Southern California and a
planning certification from the American Planning Association. His dissertation focused on participatory
empowerment in Community Benefits Agreements. He currently works as the Director of Research
and Policy at the Center on Policy Initiatives in San Diego and serves on the Board of Directors of the
San Diego City-County Reinvestment Taskforce.
ACKNOWLEDGMENTS
The author would like to thank Projections editors Isabelle Anguelovski and Anna Livia Brand of
Massachusetts Institute of Technology for extensive comments, inputs and suggestions on previous
drafts of this paper.
[ENDNOTES]
1. For example, the 2005 United Nations World Summit Outcome states: “…promote the integration of the three
components of sustainable development — economic development, social development and environmental protection —
as interdependent and mutually reinforcing pillars.” (Para 48, p. 12)
2. There are several examples of this shift to include broader socio-economic dimensions in planning practice. The
Ahwahnee Principles for Economic Development (adopted 1997), explicitly aim at embracing social responsibility and
increasing social equity. The Policy Guide on Smart Growth (American Planning Association, adopted 2002) states that
an objective of smart growth is to “equitably distribute the costs and benefits of development”. The California Planning
Guide (The Governor’s Office of Planning and Research, 2005, p. 1) states: “The planning process involves analyzing the
environmental and socio-economic impacts of development and infrastructure projects.”
3. This is due to policy decisions based on quantifying impacts in monetary terms (Davos, 1998, p. 384)
4 The “smart growth” movement is rooted in the early-mid twentieth century search for a compact, utopian urban form
that included Ebenezer Howard, Le Corbusier and F.L. Wright. In the 1990s “smart growth” in the U.S. has emerged as a
catch-all slogan for transit-oriented development, urban infill, growth management policies, anti-sprawling suburbs, and
is often conf lated with “new urbanist” design.
5. Cities ranking high in terms of Portney’s Index of Seriousness of Sustainable Communities are Seattle, Scottsdale,
San Jose, Boulder, Santa Monica and Portland. Each of these cities scored full points in the “involvement” questions, 31
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through 34 (Portney, 2003, pp. 65-71).
6 Viet Nam, Thailand, Cambodia and Lao PDR.
26
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1667-1692.
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BAXAMUSA
31
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Amy Lint
ADDRESSING NEEDS AS RIGHTS :
IMPLEMENTING A RIGHTS-BASED
APPROACH TO DEVELOPMENT IN
CAMBODIA
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33
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
ABSTRACT
Implementing a rights-based approach to development in the Global South requires tackling deeply-
structured issues of power, inequality, and justice. In the past, this focus has not been central in
development models and in the practice of development agencies. To understand what rights-based
development programming in the field entails in practice, this paper examines the Mekong Community
Rights Project. Empowering affected people to claim their own rights and manage their own lives
translates to much more than only agreeing upon international human rights laws, standards, and
treaties. In addition, it requires a substantial change in development program implementation and
organizational design. Practically speaking, advocacy efforts are needed together with grassroots
mobilization and alliance building, amplifying the voice of affected people, and applying pressure at
multiple levels. This will create the circumstances necessary for equitable development and social
justice for all.
Rights-Based Approaches : Theory vs. Practice
Early development programming is rooted in the notion that poverty stems from a lack of public goods
or technical knowledge. For 50 years, international development has focused on better managing public
welfare and social goods, without questioning the core of this approach (Offenheiser & Holcombe,
2003, p.270). Meanwhile, “the numbers of people living in poverty are increasing in many parts of the
world, and hundreds of millions are trapped in conditions that pose long term dangers (Ibid, 2003).”
By 1986, the UN General Assembly adopted the Right to Development, which expanded the definition
of poverty to mean much more than just low income. It now includes being affected by discrimination,
lack of participatory opportunities, insufficient access to resources, and a disregard to human dignity
(Wardenbach, 2004). With this understanding, in the last decade of poverty alleviation efforts, we
have witnessed development organizations and UN bodies acknowledge the link between poverty and
human rights. The World Conference on Human Rights held in Vienna in 1993 affirms this relation
by stating “a person for whom a number of human rights remain unfilled --such as the right to food,
health, education, information, participation, etc. -- is a poor person. Poverty is thus more than a lack
of resources- it is the manifestation of exclusion and powerlessness.” (as cited in Ljungman, 2004,
p.6).
More precisely, the failure to respect, protect, or fulfil human rights is a “fundamental and leading
obstacle” to social justice and to securing sustainable livelihoods for poverty reduction (Rand &
Watson, 2005, Foreward). Thus, the rights-based approach (RBA) has become the latest commitment
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pledged by the wider development community and this was set in motion by the creation of the
34 Office of High Comission on Human Rights (OHCHR) in 1993, which is mandated by the UN General
Assembly to mainstream human rights into all the UN’s development programming. Efforts continued
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to spread when International Non-Governmental Organizations (INGOs) such as Save the Children,
Oxfam International and CARE, and bilateral donors, including the UK, Denmark, Sweden, Norway,
and Canada additionally agreed to adopt a rights-based approach to development. Additionally, even
international financial organizations such as the World Bank have recognized and acknowledged
human rights and its relation to it development work: In 1998, the Bank issued statements indicating
“creating the conditions for the attainment of human rights is a central and irreducible goal of
development” (World Bank, 1998).
For these agencies, moving towards a rights-based agenda has mostly consisted in defining norms,
standards and principles of international human rights treaties. However, focusing exclusively on
technical definitions and expert based initiatives will not be enough (Uvin, 2001, p.23). Adopting
a rights-based agenda requires a commitment to addressing underlying root causes of poverty and
identifying “key systemic obstacles that keep people from accessing opportunity and improving their
own lives” (Center for Economic and Social Rights, 1995 as cited in Offenheiser & Holcombe, 2003,
p.271). Attempting to remove “structural barriers that impede communities from exercising rights,
building capabilities, and having the capacity to choose” (Offenheiser and Holcombe, 2003, p.271)
will require a complete paradigm shift.
Furthermore, moving beyond distributing more social goods in an attempt to eradicate poverty requires
a change in practice as well as substantial organizational changes. This begins with a mission in
line with a vision of sustainability with justice and equality for all. Development agencies will need
to examine how well their own policies align with what they envision for other actors to respect.
Additionally, communities being assisted will need to understand their rights and claim them by
pressuring decision-makers to change policies, laws, and budget allocations. Mobilizing for demands
to change resource allocation and establish systems of monitoring standards for accountability is
needed, and, if necessary, use the courts to claim entitlements and achieve justice and equality
(Theis, 2004, p.6). Practically speaking, today, the development community continues to struggle
to understand what adopting a rights-based approach truly requires in terms of implementation and
document field based examples that highlight this approach (Ibid, 2004).
In a country like Cambodia, complex development issues are exacerbated by an extensive history of
human rights abuses, years of instability, and lack of civil society. Cambodia survived a four-year
genocide by the Khmer Rouge from 1975-1979, when over one million people died as a direct result
of the government’s policies and actions (Chandler, 1993, p. 212). In the 1980s, Cambodia went
through several transitional governments and, in the early nineties, after United Nations Transitional
Authority of Cambodia (UNTAC) elections in 1993, a new constitution was drafted, promising market
economics, parliamentary democracy, and respect for human rights. This paved the way for the
entrance of international and national NGOs, which pledged to rebuild and develop the country. Money
and technical advice poured in to improve degraded infrastructure, alleviate poverty, and allow for the
development of a civil society.
However, today, several organizations, international and local, recognize that the road to recovery
and poverty alleviation runs deeper than repairing failing infrastructure. Development practitioners in
Cambodia are looking critically at how to effectively transform old relief approaches and act upon past
failures by implementing a rights-based strategy to improving the situation. Several agencies have
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spearheaded this rights-based approach in Cambodia, including: four Oxfam International affiliates
(all guided by the Oxfam International rights-based strategic plan), CARE, Save the Children, and 35
their local partners which are now exploring how their programs can also address rights. Additionally,
bilateral donor agencies, the UN and the World Bank all make some level of commitment to a RBA
by mainstreaming human rights policies within their organizations and attached to various project
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funding.
A commitment to a rights-based approach is the first step towards addressing inequality in Cambodia,
but have the new ideals changed anything in practice? Have they led to poverty being recognized as a
massive human rights violation from which millions suffer? Have they resulted in bringing to account
those who are responsible for the impoverishment of the rural poor? Has this commitment resulted
in international agencies reallocating resources towards empowering victims of damming to exercise
their collective power in support of their claims? What real difference has it made in the right to
determine one’s own future in Cambodia? In reality, the work towards eliminating structural causes
for global poverty and creating justice for the poor villagers remains compromised because the human
rights approach continues to be dominated by multiple ambiguous definitions interpreted and defined by
each agencies own interests (Manji, 2006; Uvin, 2002). This paper highlights new initiatives towards
addressing power imbalances and social injustice faced by people living in Northeast Cambodia by
examining the Mekong Community Rights Project (MCRP) within the Environment Programme. In
efforts to move beyond standard rights-based elements which are essentially top-down, and assumes
“rights” can be given to people, rather than recognizing that people must be enabled to claim their
rights, this case study highlights field-based examples that emphasize more effective and practical
approaches towards achieving real change in power that leads to more sustainable, socially just
change in the development field.
This paper is the result of a seven-month practicum working with the NGO Forum on Cambodia’s (NGOF)
Mekong Community Rights Project within the Environment Programme in Phnom Penh, Cambodia
during 2004-2005. Data was gathered by conducting participant observation and interviews with
NGOFs and donor organizations, and contributing to drafting national network advocacy strategies.
Additionally, active participation and observation of the 3S Working Group (3SWG) network through
attending regular meetings related to the current program and campaign provided the needed insight.
In the first section of this paper, I introduce the specific case of hydropower projects in Cambodia
and the problems that have occurred with their construction, leading to using a rights approach. In
the second section, I present the elements commonly described as part of a rights-based approach in
the Mekong Community Rights Project. In the third section, I examine the efforts and challenges of
the Mekong Community Rights Project to address factors of unequal power relations and exclusion
that prevent local people from achieving environmental, social, and cultural sustainability. In the final
section, I call for additional programming in development organizations, in ways that analyzes power,
advocates for policy and practice change, builds alliances, and works at multiple levels to address
development with sustainability in mind.
Rights Violations in Cambodia : The Case of Hydropower
In Cambodia, infrastructural development and particularly dam construction, funded by international
donors, has violated the rights of large numbers of rural Cambodian farmers and fishermen. For
instance, the $1 billion Yali Falls hydropower project (HPP), built 80 kilometres upstream in Vietnam,
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has not offered development benefits of shared resources to communities downstream on the Se San
36 River, and severely impacted the sustainability of peoples livelihoods. The pleas for assistance by
those affected has led the NGO Forum on Cambodia, a national advocacy organization, to investigate
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these rights violations and understand how much people are unaware of their rights or how to claim
them.
Precisely, the numerous international violations of rights and standards caused by large-scale
hydropower projects (HPP) being constructed and proposed along the Mekong sub-region has been
a growing issue. International finance institutions (IFIs), including the World Bank (WB) and the Asia
Development Bank (ADB), as well as bilateral donors such as the Swedish and Nordic governments are
financing enormous loans to Vietnam in efforts to serve the ‘so-called’ growing power market and to
deliver cheaper electricity. The problems associated with these large-scale, non-participatory projects
can be clearly seen in the case of the Yali Falls hydropower project. The Yali Falls project dammed
the Se San River, one of the largest tributaries of the Mekong River. Tens of thousands of villagers
traditionally depend on the area for fishing and small riverside farming for subsistence living (Rutkow,
Crider, & Giannini, 2005, p.14). The impact on villagers became apparent in November 1993, during
the construction phase of the dam.
In 1996, major f looding hit northeastern Cambodia, including Ratanakiri and Stung Treng Provinces.
Villagers reported a coffer dam bursting and other signs emerged to show dam construction was
affecting the river f low, even before the Yali Falls Dam reservoir was completed in 1998. Frequent
dam releases caused massive sporadic surges of water to f lood communities downstream. Several
lives were lost and livestock, the main possessions of all real value, were drowned. Combined with
river garden plots washed away and depleted fish stocks, food insecurity became a major issue. All
water releases, spills, and surges caused by the dam caused indigenous ethnic minority people of this
region to fear the river and its potential destruction. In early 2000, The Mekong River Commission
(MRC) Secretariat sent a mission to investigate after media had reported past deaths, damages
caused, and vulnerability of people’s livelihoods. These communities were offered no compensation
and were unsure as to how to assist themselves in order to sustain their livelihoods.
In response, the NGO Forum on Cambodia, (NGOF) with support from Oxfam America, became involved
in mobilizing efforts and building NGO cooperation towards advocacy on key development issues in
order to support indigenous people who had been victims of the dam construction and advocate for
their rights.
The Mekong Community Rights Project: Elements of a Rights-Based Approach
In the Mekong River Basin, the agencies responsible for managing the dam project have not followed
“Best Practices,” as defined by the World Commission on Dams. As a result, cultural, environmental,
and socio-economical rights have been deteriorating rapidly. To support affected communities in
demanding protection and restoration of river-based livelihoods in Northeast Cambodia the Mekong
Community Rights Project (MCRP) was established within NGO Forum on Cambodia’s Environment
Program, shortly after community consultation in 1997. In this section, the elements of the commonly-
agreed upon rights-based framework - links to the law, inclusion, participation, empowerment, and
good governance- are defined.
Reference to International Treaties and National Laws, and Standards
The most agreed upon element by the development community for utilizing the rights-based approach
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is linked to standards, policies, or rights a state commits to, yet does not respect, protect, or fulfil
as mandated. The Yali Falls Dam has clearly caused severe rights violations against the Cambodian 37
people, if we consider the multiple obligations of Cambodian and Vietnamese governments to its
citizens. These obligations range from international law and human rights agreements, cross-boundary
agreements, and national standards which include:
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1. The Mekong Agreement of 1995 -- a regional multilateral treaty between lower
Mekong countries enforced by The Mekong River Commission (MRC).
2. International environmental law stemming from the Stockholm Conference in
1972 and, more recently, the 1992 United Nations Conference on Environment
and Development
3. International treaties including the International Covenant on Civil and Political
Rights (ICCPR) and International Convention on Economic Social and Cultural
Rights (ICESCR)
4. World Commission on Dams (WCD) International Standards
In April 2000, the Vietnamese government publicly announced that the Yali Falls Dam had been
releasing dammed water, causing f loods and surges; yet it did this without notification to Cambodian
downstream communities. Vietnam accepted accountability for five deaths, though estimates by
villagers state that several dozen had died (Rutkow, Crider, & Giannini, 2005, p. 63). Releasing of
water without notification is a violation in terms of the Mekong Agreement, and, although Vietnam
made attempts to issue a notification system in the spring of 2000, all releases before then are in
violation.
The Environmental Impact Assessment (EIA), designed to expose any potential environmental and
socio-cultural risks and possible mitigation measures, is an essential document for making sound
decisions and incorporating environmental sustainability as well as equity in the planning process.
However, the EIA that Vietnam commissioned for the Yali Falls dam considered only eight kilometres
downstream. Additionally, the Cambodian government has not taken significant action in response
to the harms produced by Vietnamese dams. The MRC has a commitment to “make every effort to
resolve the issue,” (Ibid, p.67) yet the Yali Falls issue has largely been ignored and no discussion has
been initiated.
Cambodia and Vietnam are signatories to the ICCPR and ICESCR, which state clear obligations
towards the people of their states. Although Cambodia did not play a role in the construction or
operation process of the dams, the government bears the responsibility for protecting its people. With
regards to the ICESCR, the Cambodian government has the obligation to protect, respect, and fulfil
the rights of its citizens under Article 11 which emphasizes the right to food. This has clearly been
violated as the villagers’ food security comes solely from the fish obtained from the river and that
the dam project prevents local people from achieving sustainable livelihoods. Much needed efforts to
remedy the harms suffered in these communities are required to bring Cambodia in compliance with
ICESCR rights to food, water, and livelihood (Ibid, p.82).
The World Commission on Dams (WCD), created from efforts of an IUCN and WB workshop,
developed internationally acceptable criteria, guidelines and standards, where appropriate, for the
planning, design, construction, operation, monitoring, and decommissioning of dams” (WCD, 2000).
International standards were created listing strategic priorities and guidelines for equitable and
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sustainable development of water and energy resources (Ibid, p. 278). The Yali Falls dam violations
38 and many of the other upcoming 3S dams have not been in compliance with important guidelines
actually developed by some of the same agencies funding the projects.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Inclusion, Non-Discrimination and Attention to Marginalized Groups
As a standard element of the rights-based approach in theory, particular efforts are made to identify
and reach those who are most vulnerable (Theis, 2006, p.5). In Cambodia, 90 percent of the general
population is ethnic Khmer (Swift, 2006, p.10). In contrast, the communities dependent on the
Northeast Cambodian Rivers for their livelihoods and food sources are not the Khmer ethnic majority.
Villages in Ratanakiri are comprised of several minority groups and indigenous peoples that include Lao,
Brou, Kreung, Kachok, Jarai, Tampuon, Kavet, and Chinese. Ethnic minorities in Cambodia continue to
suffer great injustices. Physically separated, Ratanakiri province is over 300kms from the capital city,
and is approximately 14 hours by bus on roads that are often impassable during the rainy season. This
creates economic barriers as trade of goods and supplies remains difficult and expensive. Additionally,
numerous NGOs work on health and education issues because the standards are far below the national
level (Middleborg, 2005, p. 7).
The Mekong Community Rights project is addressing discrimination and seeking to support ethnic
minority populations that do not live in decent conditions. Despite this, the negative effects of dams
mushrooming all over the entire country is leading the national network to look at a broader picture
of “dam control,” which may not necessarily address communities most vulnerable. Therefore, it is
important when developing new rights programming, that a proper analysis is done with consideration
of seeking those who are most marginalized and putting them at the forefront.
Participation
Active, free, and meaningful participation is essential in development programming because it serves
as a basic requirement of the rights approach (UNHCHR, 1996). Participation includes control of
planning, process, outcome, and evaluation (Hamm, 2001, p.1019). Within the Mekong Community
Rights Project, putting affected communities at the center of participation has proved to be challenging
and there is no certainty that NGO staff understand this concept well or even would want such a
change in their programming structure. This has not been the current method of operation, thus major
transitions and new strategies by NGOs involved are required.
The main activities of the MCRP project concentrate on actively engaging the 3S Rivers Working
Group (3SWG) network, consisting of over ten different member organizations represented. Efforts at
widening this circle of organizations have been discussed due to its limitation to only representation
by NGO staff, one University professor, but no community members. The recently drafted Terms of
Reference (TOR) of the 3SWG expands membership to all civil society members, although the TOR has
not yet been approved by members, nor has any promotion been done to recruit different members.
One local network member organization, 3S Protection Network (3SPN) does make efforts to meet
with community representatives regularly to inform them of activities happening within the national
level strategy, but this dialogue remains dominated by a top-down, one-way communication process
consisting of informing the community rather than giving them the opportunity to voice their concerns
to the national level. Having people at the center of their own development will be a process requiring
gradual increases in responsibilities and opportunities and the NGO staff will need to be ready to
engage in this process.
The 3SWG network within the Mekong Community Rights Project has proved far better at advocating
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for community participation and civil society involvement in the larger development sphere than
being able to recognize the importance of affected people being the drivers of their own development
activities. Such was the case of the January 12th 2006 stakeholders meeting regarding an upcoming 39
dam project on the Sre Pok River. Because civil society had not been given the official Sre Pok
River EIA or much opportunity to comment on its contents, the network lobbied the funders, the
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Swedish Agency for Development (SIDA) and the Norwegian Agency for Development (NORAD), for
a participatory meeting as required by several WCD best practice guidelines. After several months of
letter writing and demands by network members, SIDA and NORAD agreed to fund such a meeting in
Phnom Penh, but they were not the organizers of the event. The actual organizing was done by the
recipients of the Nordic governments’ development aid, Electricity of Vietnam (EVN) and coordination
assistance from the CNMC and VNMC, representing the government agencies.1 With the support
of the national 3SWG network, twenty community members, ten from each province, were able to
engage in meaningful participation at a very high level stakeholder meeting discussing the impacts of
their own villages and water resources.
Empowerment
Specific instances highlighting empowerment can be recognized in the work in the Mekong Community
Rights Project. At the Sre Pok stakeholder meeting, mentioned above, community members wrote a
petition in order to collectively voice their concerns and presented it at the workshop for all participants.
Furthermore, despite intimidating conditions at the workshop, several community members stood
up amongst the 150 participants, to raise comments and concerns with relevant authorities.2 The
community was able to do this thanks to a two-day EIA training held for community members.
Additional programming made by provincial NGO organizations highlighted effective ways to empower
community members as part of their rights-based approach which includes: opportunities for community
exchange visits, community-based research, short documentary videos of community members telling
their personal life story, and a dam fighters educational guide written in the national language to be
distributed to community members. The process of “giving people the power, capabilities, and access
needed to change their own lives, or improve their own communities and inf luence their own destinies”
(UNHCHR, 1996), is a challenging task at hand requiring a complete shift in adopting programming
mentioned above with empowerment at the core of a rights- approach.
Good Governance and Accountability
As illustrated, more than enough written commitments exist for the obligations upon which responsible
actors have agreed. The Mekong Community Rights Project seeks to hold the multiple stakeholders
accountable for their obligations to affected communities. Holding the government, and specifically
the Cambodian National Mekong Committee, (CNMC) accountable for their obligations regarding
water resource use has proved challenging and requires various methods and actors applying
consistent and long-term pressure on decision-makers. Government officials show little respect for
dialogue with indigenous community minorities and rarely respond to requests for communication by
the national network, 3SWG. Despite current challenges, persistent efforts are being made by 3SWG
members to engage high ranking authoritative government officials. Negotiation for a Memorandum
of Understanding (MOU) is considered a first step in cultivating the relationship between civil society
and relevant government authorities and is slowly underway.
Actively engaging the full range of relevant and responsible actors is essential in a rights-based
approach. Within the MCRP, bilateral donors have been identified as key players with responsibility
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for upholding rights-based commitments and only result in merely rhetoric when NORAD and SIDA’s
40 own human rights policies are ignored. These specific donors are responsible for several upcoming
hydropower projects implemented by Electricity of Vietnam, which is state-owned and controlled. No
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human rights assessment or analysis, such as the guiding framework by NORAD, has been shared
with community members.
Does a Rights based Approach Make a Difference? The Added Value of the Mekong Community
Rights Project
In addition to the commonly agreed framework for implementing a rights-based approach, the MCRP
believes that bold new approaches are needed in order to address how rights will be claimed and to
make lasting change in the lives of the Cambodian poor. Addressing power inequalities is at this core
of the approach and specific strategies include understanding and analyzing power, advocacy, alliance
building, and working at local, state, and national and international levels.
Power Analysis
Power relations exist at all levels of development, even when unintended or unwanted. Different tools
have been developed to map out these existing power relationships, to understand them better, and
analyze the complex web of interactions and multi dimensions of power. In the case of the Mekong
Community Rights Project, donors and International Non-Governmental Organizations (INGOS)
recognize the importance of understanding the power outside inf luential development agencies hold.
Yet, efforts to build the capacity of national level partners to understand and analyze power structures,
have not been tackled. In 2007, the donor organization Oxfam America facilitated a participatory two-
day strategic action plan workshop for members of the national 3SWG network. The results were
meant to guide network members in formulating their national action plan for the year, although it is
questionable how much the members of the 3SWG were able to inf luence the national action plan.
Findings were heavily inf luenced by the donor’s (Oxfam America) strategic interests and the outcomes
identified were most often those already determined by the donor’s headquarters staff. This important
exercise was not formally documented for further reference and explanation to guide new members,
beyond poster sheets of the activity and a few photos taken, implying it has little future relevance
to those who just underwent the exercise. Additionally, a power analysis through the lens of the
community has not yet been done or prioritized.
Despite this less than perfect attempt, the 3SWG network should be recognized for its initial first steps
to identify and address power as the underlying cause of rights’ violations. This is significant because
it goes beyond the limited legal emphasis that other organizations hold central to the rights-based
approach. The power analysis undertaken by the 3SWG as part of the action plan workshop proved to
find IFIs, government, and donors appropriate targets for their advocacy efforts. Frustratingly enough,
efforts towards this were again reshuff led by the hands of the donor. On the basis of a separate
contextual analysis determined by the Oxfam International sister organizations working in the Mekong
region, the donor told the 3SWG that new strategies should target foreign investors.3 How Oxfam’s
new target approach will now be incorporated into the national action by the 3SWG network members
is still to be determined.
The ability of the Mekong Community Rights Project to begin thinking about analyzing power is a step
in the right direction, but a deeper ongoing comprehensive analysis done by all relevant stakeholders
is long overdue. This scenario provides several valuable opportunities to achieve more inclusive
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practices, involving the full range of people who will be included in advocating for their rights. This is
important for three main reasons: a) to ensure more dynamism and depth to the discussion (different
41
people will add new information and perspectives); b) to make the exercise part of the empowerment
process; and c) to build, from the start, democratic ownership of the advocacy strategy (Chapman et
al., 2005a, p. 56).
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Advocacy for Sustainable Change Policy
The rights-based approach takes empowerment a step further in aiming not only for the ability to
sustain oneself, but also for the additional capacity to inf luence public policies and make claims in
defense of one’s rights (Rand & Watson, 2005, Jochnick, 2002, p.21).
This is done through advocacy, which “is the art of inf luence and changing power structures and
decision-making systems” (Chapman et al, 2005a, p.21). In Cambodia, advocacy is a relatively new,
not deeply understood, and literally translates to “struggle for an idea,” which creates a slightly
controversial meaning (Mansfield & MacLeod, 2003). Thus local activists engaging in advocacy are
often subjected to various threats or even become victims of violence. Nonetheless, Cambodian
nationals are boldly taking steps towards this change. In the case of the MCRP, the MRC, multilateral
donors and other agencies have actually created policies that should protect the rights of people
affected by dam construction and that clearly indicate a trans-boundary commitment to effective
water governance policies, but the policies are not adequately implemented.
The network has built a growing relationship with mass media4 to raise awareness on these policies,
share current information, and to report abuses of power throughout the country. Numerous articles
have been published in 2007 specifically highlighting the controversial dam developments. As part of
the advocacy strategy, visits by outsiders, such as government officials, journalists, and donors to
local communities, is a priority in the MCRP budget for two different outcomes. The first includes
cultivating the relationship and dialogue with decision makers in order to expose policy f laws to those
who are in position of power and can lobby for change. Secondly, journalists and media specialists are
welcomed and encouraged to publish stories that raise public awareness of ongoing investigations of
dam project potential problems faced by communities.
Alliance Building
An alliance of several NGOs can have a dramatic effect on building voice, diffusing risk, and bringing
different skills sets to the campaign, as well as leverage information about issues that would otherwise
not be accessible (Chapman, 2005a, p.94).
The 3SWG network members are committed to ensuring that existing and future hydropower dam
projects respect the rights of affected people and ensure the sustainability of the environment and
livelihoods. The process to achieve these objectives requires public participation in the planning and
decision-making process in order to guarantee that the interests, needs, and benefits of affected people
are included as well as addressed. As a network of several members consisting mostly of national
organizations, the 3SWG does have two international agencies that are normally present, including the
funder of the project. The alliance of organizations forming the network tackles several controversial
activities including enabling people to better understand their rights; inf luence policy makers; build
capacity of activists; enhance communication between actors; and develop new methodologies, tools
and resources. However, there is much space for improvement within the 3SWG alliances. The level
of experience varies dramatically within the network and several members need further training in
order to better balance each alliance member’s power and inf luence. Furthermore, decisions made by
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the unity of these alliances often require top-level management commitment and decision-making from
organizational heads who are often too busy to fulfil the commitment.
42
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Working at Multiple Levels
As demonstrated by the rights violations of communities affected by dams, “global economic and
political factors are entrenching poverty and inequality and reducing the agency of citizens to
inf luence the processes that affect their lives” (Eyben, Harris, & Pettit, 2006, p. 1). Various actors
are responsible for the violations and can be inf luenced in different ways, which makes working at
multiple levels, including local, national, and international, within an advocacy strategy necessary.
By helping forge links of solidarity among affected communities, NGO Forum, Oxfam America, and
others at multiple levels will contribute to a better understanding of relationships between citizens
and government, and within global and national institutions – in efforts towards effectively changing
them.
Efforts at the local level are spearheaded by two provincial organizations, the 3S Protection Network,
(3SPN) and the Cultural, Environment, Protection Association (CEPA). Both are responsible for working
with communities affected or potentially affected by poor river basin management and damming
issues. CEPA and 3SPN have developed different approaches during their participation in damming
issues over the past five years. CEPA has only recently tried to incorporate more advocacy and rights
awareness into their more traditional water resources management programming, whereas 3SPN
was formed as a specific response to address critical damming issues. NGO Forum plays a critical role
coordinating partners and inf luencing national level actors.
At the international level, small, but powerful advocacy activities are taking place and new efforts
are being made to strengthen regionally-based work that involves all Mekong basin countries. Several
international advisors from INGOs in Canada, Japan, Thailand, and Philippines have made a commitment
to assist by providing technical assistance and capacity building, regional and international exchange
and updates of information, and provide additional ways for pressure to be exerted on some of the
various actors responsible for continual injustices towards indigenous people.
The close relationship with international media sources in the Nordic countries is a good example
of the importance of multi-level interventions. Reporters of Development Today, a Norway-based
magazine, regularly receive controversial news stories from remote villages not easily reached, such
as rural Northeast Cambodia, and, in response, publishes news articles to expose Nordic citizens to
their governments foreign aid spending not otherwise accounted for.
In sum, the Mekong Community Rights Project is on course for leading development projects focusing
on root causes and making structural change. Despite several challenges, MCRP is making important
efforts to address factors of unequal power relations and exclusion that prevent local people from
achieving environmental, social, and cultural sustainability.
Rights-Based Approaches: The Way Forward
Adding human rights language to programming priorities is the first step in recognizing the importance
of equity and justice in sustainable development. Yet, as the case study on the Mekong Community
Rights Project concludes, there are profound concerns that the new language may be accepted without
the shift in ideology and programming needed. To achieve equity, justice, and freedom from want for
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the rural poor in Cambodia, there remains more to be attempted and then ref lected upon from field-
based programming. Most importantly, “There is a real need to gain a “deeper understanding of poverty
43
and exclusion on a global scale” and then change the focus of strategy in a manner that moves beyond
empty rhetoric (Offenheiser & Holcombe 2003, p.295). This includes programming in development
agencies that recognizes power relations, puts people at the centre of struggle for claiming their
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
rights, as well as internalizing the rights-based approach in their own work and relations.
Address the Real Issues- Power and Inequality
Globally, widespread poverty, marginalization, and gross violation of human rights is the result of
uneven concentration of power that works to privilege some people while oppressing many others
(Chapman et al. 2005a, p.19). Power must be recognized in its full multidimensional complexity,
existing at multiple levels, in order to be used to the advantage of social change. Power can be
exercised by preventing grievances - by shaping perceptions, cognitions, and preferences in such a
way as to secure the acceptance of the status quo since no alternative appears to exist (Lukes, 2005).
Through a rights-based approach, practitioners are obligated to address critical questions regarding
“matters of power and politics, exclusion and discrimination, structure and policy, and the systems
of thought and practice that justify them” (Uvin, 2004, p.3). Unraveling these intricate more hidden
levels of power and the compelling attention it deserves by the numerous actors at play has largely
been ignored (Uvin, p.4). In the few instances where power is considered, it is only seen from a one
directional view, consisting of a win-lose relationship that is a struggle between the all good, righteous
social movements and the evil, villains that hold all the power (Ibid, p.4).
Organizations are challenged to create new ways to redistribute power, which can start with a good
look internally at their own role in handing over power. As Chapman et al. (2005a) rightfully points
out, the “primary role of development NGOs and donors shifts from being implementers and drivers of
development to being allies and fellow partners… in a collective struggle for change, including sharing
and negotiating power in new ways” (p.14). Once power is better understood at various levels, the
process of mapping power dynamics should be the fundamental starting point of designing advocacy
strategies involving issues of poverty, inequality and injustice. Agencies who are attempting to take
a rights approach need to prioritize skills in power analysis for staff who can then transfer this
understanding to local level partners, who are the main players in this struggle.
People as the Drivers of Sustainable Development
As development agencies recognize power at play, they will be more equipped to develop strategies
towards addressing it in various ways. Yet it is imperative to also consider who decides which issues
are of most importance, who then carries these strategies out, on and using what approaches are used
(Chapman et al. 2005a, p.13) As Offenheiser and Holcombe (2003) reaffirm, “a rights-based agenda
will be meaningless if Southern partners and marginalized communities cannot speak in their own voice
and act in their own behalf” (p.289). Advocacy for sustainable change under a rights agenda requires
citizens’ activism and participation in the claiming of their rights. If we allow advocacy to become
purely the domain of a professional elite of NGO policy experts - as well-intentioned and committed as
they might be - it will become yet another dynamic that undermines the empowerment and leadership
of the poor and marginalized (Chapman et al., 2005b, p. 10). Additionally, understanding the rights and
polices affecting peoples’ lives and providing assistance with organizing and leadership development
is needed.
Collective Action at Multiple Levels
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The realization that people are being controlled by decisions made by institutions and organizations
44 they have never encountered or been aware of is critical. Creating a web of action through efforts
made at multiple levels is a necessary step towards redressing power inequalities and adopting a
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
rights-based approach. The formation of a unified, yet diverse coalition can have a powerful effect
in popularizing and vocalizing issues which in turn exerts pressure on responsible actors to see that
justice is done.
In order to create momentum and power to address the organizations who have become the main
decision makers responsible for violations of rights, networks are also needed. Networks or alliances
are based on the assumption that together more can be done in order to be sure peoples concerns are
amplified (Chapman, 2005a, p.94). A combination of the joint power of NGOs, community groups and
donor organizations creates the stability and force for demanding justice. Rights-Based programs must
seek to blend the different skills, perspectives, and strengths to create a collective powerful body
demanding change (Chapman et al. 2005b, p. 10).
Conclusion
The rights-based approach gives development practitioners opportunity for developing equity, more
sustainability in development, and creating social justice by facing the difficult question of unequal
power relations. Development organizations need commitment to change, which begins from the
very place they work everyday. This means supporting the voices of the poor and refraining from
reproducing inequalities and social hierarchies. Development practitioners and their respective agencies
must be accountable to network partners and communities. A rights-based approach enables this kind
of accountability by encouraging partnerships with multidirectional communication, and sharing in
decision making, planning and evaluation efforts of strategies.
Actors implementing a rights-based approach need to constantly ask if their programming is making
steps towards enabling people to have freedom and capability to control their own lives and make
their own choices. If this is not occurring, practitioners must go back to the drawing board and further
consider the implications of a rights-based approach. Only the process of recognizing, challenging and
changing inequalities of power will lead to global and local sustainability and create conditions for all
to obtain justice, equity, and human dignity rightfully deserved.
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45
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
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46
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
AUTHOR’S BIOGRAPHY
Amy C. Lint is currently a Community Development Coordinator with the International Rescue
Committee in San Diego, CA. She received an MA in Sustainable International Development from
Brandeis University and previously worked with grassroots projects in Southeast Asia and East Africa
for almost five years.
[ENDNOTES]
1. The Cambodian National Mekong Committee (CNMC) is the lead national institution in Cambodia for advising the MRC
and operates directly under the Royal Government of Cambodia. Members consist of heads of the various Ministries and
assist and advise the latter in all matters relating to the formulation of water policy, strategy, management, preservation,
investigation, planning, restoration and the development of the water and other related natural resources of the Mekong
River Basin (http://www.cnmc.gov, 2006).
2. This meeting was held in the capital city, which most community participants rarely receive visit. Out of 150
representatives 20 community members were present. Several high ranking government officials from Cambodia and
Vietnamese governments were facilitating this meeting.
3. This focus on private investors corresponds to the Oxfam’s own strategic plan.
4. There are a few media sources available in Cambodia. Three main newspapers comprise the most popular and widely
spread form of mass media in Cambodia.
REFERENCES
Chandler, D. (1993). A history of Cambodia. Bangkok: Westview Press.
Chapman, J., Pereira, A., Uprety, L., Okwaare, S., Azumah, V, Miller, V. (2005a). Section 1: Rights Based Approaches
(p. 9-26). Critical webs of power and change. [Electronic Version] Action Aid International. Retrieved from http://www.
actionaid.org/main.aspx?pageId=283
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Chapman, J., Pereira, A., Uprety, L., Okwaare, S., Azumah, V, Miller, V. (2005b). Action research on planning, assessing
and learning in people-centered advocacy. Summary of Learning (Working Paper #1). Action Aid International. 47
Eyben, R., Harris, C., & Pettit, J. (2006). Introduction: Exploring the power of change. IDS Bulletin, Vol.37, pp. 1-10.
Retrieved on January 5, 2007 from http://www.ids.ac.uk/ids/bookshop/bulletin/1Intro37.6.pdf.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Hamm, B. I. (2001). A human rights approach to development. Human Rights Quarterly, 23 (4), John Hopkins University
Press, p.1005-1031.
Lukes, S. (2005). Power: A radical view. New York: Palgrave Macmillan.
Manji, F. (2006) Reinventing development: New Spin on old story? [Electronic Version] September edition, Alliance
magazine.
Mansfield, C., MacLeod, Kurt, Greenleaf, M., Alexander, P. (2003) Advocacy handbook in Cambodia: Increasing
democratic space. Brickford, A., Monirith, L., Sophal, S., Sotha, R., Viraakbot, Y. (Ed.) Phnom Penh: PACT.
Middleborg, J. (2005). Highland children’s education project: A pilot project on bilingual education in Cambodia. Bangkok:
UNESCO.
Miller, V., VeneKlasen, L. Reilly, M. & Clark, C. (2006) Making change happen: Power concepts for revisioning justice,
equality, and peace. Washington, D.C. Just Associates.
Norwegian Agency for Development Cooperation (2001): Handbook in Human Rights Assessment: State obligations,
awareness and empowerment, Oslo: Norwegian Agency for Development Cooperation.
Offenheiser, R. & Holcombe, S. (2003). Challenges and opportunities in implementing a rights-based approach to
development: An Oxfam America perspective. Nonprofit& Voluntary Sector Quarterly 32 (2), p. 268-301.
Rand, J., & Watson, G. (2005). Rights-based approaches learning project. USA: Oxfam America and Cooperative for
Assistance and Relief Everywhere.
Rutkow, E., Crider, C. & Giannini T. (2005) Down river report: The consequences of Vietnam’s Sesan River dams on life
in Cambodia and their meaning in international law. Phnom Penh: NGO Forum on Cambodia.
Swift, P. (2006) Livelihoods in the SrePok River Basin in Cambodia: A baseline survey. Phnom Penh: NGO Forum on
Cambodia.
Theis, J., (2004). Promoting rights-based approaches: Experiences and ideas from Asia ad the Pacific. Stockholm: Save
the Children. Retrieved from http://www.crin.org/docs/resources/publications/hrbap/promoting.pdf on February 12,
2006
Tsikata, D. (2004). The rights based approach to development: Potential for change or more of the same? Institute for
Development Studies. IDS Bulletin, Vol 35, (4), p. 130-133.
Office of the High Commissioner for Human Rights. (UNHCHR) (1996). Rights based approaches, New York: UN. Retrieved
June 15, 2006 from http://www.unhchr.ch/development/approaches-04.html.
Uvin, P. (2002). „On high moral ground: The incorporation of human rights by the development enterprise“, in Praxis,
The Fletcher Journal of Development Studies Vol XVII. Retrieved on, June 23, 2006 from http://f letcher.tufts.edu/praxis/
archives/xvii/Uvin.pdf.
Uvin, P. (2004). Human rights and development: Bloomfield CT: Kumarian Press.
World Commission on Dams. (2000). Dams and development A new framework for decision-making. London and Sterling,
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VA: Earthscan Publications Ltd.
48 World Bank. (1998). Development and human rights: The role of the World Bank. World Bank: Washington DC.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
49
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY LINT
Camille Tuason Mata
BEYOND LAND REFORM TO
ACHIEVE RURAL COMMUNITY
DEVELOPMENT : THE CASE
OF THE SAN JOSE AGRARIAN
MUNICIPAL COOPERATIVE IN THE
PHILIPPINES1
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51
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
ABSTRACT
Land reform has been viewed as a vehicle for reducing poverty, as land ownership and title rights
generally enable the poor to establish food-generating projects, which help them attain some degree
of socio-economic equity. Land reform has also been equated with social justice because land title
renders power to independent farming, giving farmers the freedom to define their work conditions.
However, the community development experience of the San Jose Agrarian Municipal Cooperative
(SJAMCO) in the Philippines shows that land reform is only the first step towards equity and justice.
Although the SJAMCO had title to 2.14 hectares of land, they remained food insecure. This research
finds that a strong partnership, ref lecting rich social capital, between the SJAMCO and federal
agencies responsible for implementing land reform, is an effective way to develop a collaborative
relationship, in which all parties engage in a comprehensive planning process that carefully maps out
sustainable livelihood projects and strengthens community relations.
INTRODUCTION
Much of the earlier studies on poverty in low income countries have linked up land reform with
poverty alleviation, suggesting that, when broadly implemented land reform is the panacea to reducing
economic inequalities and the key to empowering poor households in granting land ownership or title
(Herring, 1999; Food and Agriculture Organization, n.d.; Besley & Burgess, 1998). Amartya Sen
(2000) interlaced entitlements, like land ownership, with poverty reduction and freedom. However,
a growing body of literature has emerged, which questions the linearity of this relationship (Rohde,
Benjaminsen, & Hoffman, 2001; Balisacan, 2007; Baas & Ali, 2005), showing that, while it is
true that land reform secures assets to the poor, land ownership or title rights needs also to be
accompanied by other factors. In illuminating the intersection of social capital and land reform, the
community development experience of the San Jose Agrarian Municipal Cooperative (SJAMCO), a
peri-urban agriculture cooperative in Mindanao Island, the Philippines, contributes to this growing
body of literature. The SJAMCO’s case illustrates that alleviating poverty conditions and achieving
sustainable livelihoods for the household members would be better accomplished by creating and
nurturing a strong partnership between government and community, exemplified by collaborative
network f lows that establish trust and promote a comprehensive community development planning
process.
The community development goal of the SJAMCO households was to secure food with livelihood
projects from which they could harvest sufficient volumes of foods for consumption and income.
However, they were not able to complete their nascent livelihood projects in large part because the
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vertical relationship that would have brought about collaboration between community and government,
52 ref lected weak social capital. Resultantly, they have not made the transition from food insecurity
to food security despite having gained 2.14 hectares of land from the passage of former President
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Corazon Aquino’s land reform initiative, the 1988 Comprehensive Agrarian Reform law (Republic Act
6657). In this paper, I trace the reasons to two factors: (1) failed collaboration between government
and community, evident in the absence of a community planning process in the livelihood-building
stages after winning land title, and (2) the lack of political legitimacy for not meeting the quorum
standard of fifteen household members. These factors are the basis for weak social capital between
community and government. If the relevant government officials had engaged the households in
the community planning process, they might have identified how the households could have begun
moving out of poverty and towards food security. Along the same lines, if the households had met
quorum standards, they would have received a stronger commitment from the government since
complying with the “rules” indicates reciprocity on the part of the community. The presence of these
social capital dimensions would likely have built up the trust and resulting productivity that so aptly
characterizes strong social capital relations (Wilson, 1996, 1997; Putnam, 1993, 2000; Fukuyama,
1999, 2002). Instead, the SJAMCO households harbored suspicion because they perceived the
government as playing political games. The experience of the SJAMCO households reinforces the
argument that land access is only the first step towards achieving food security.
This research relied heavily on focus groups, household, and individual interviews. The household
participants were members of the SJAMCO community. Two focus group interviews were held with
all the members to understand (1) the historical development of the SJAMCO community, (2) the
bottlenecks in the community development efforts, and (3) the problems associated with SJAMCO’s
relationship with government agencies. The heads of households were then interviewed to ascertain
their level of food security. I also conducted interviews with four volunteer community organizers for
the Partnership for Human Rights and Development (PaHRD), a priest with the Arch Diocese Church of
Valencia City, and two government officials, which disclosed the differences in perspectives between
the SJAMCO members and the federal agencies regarding the reasons behind the incompletion of
the livelihood projects. These individual and focus group interviews brought to light the obstacles
to poverty alleviation, despite land reform, in the context of weak social capital ties between the
government and community.
This paper is organized as follows: the first section illustrates the various approaches to defining
social capital and explains the community benefits generated when social capital is abundant. The
second section presents the difficulty the SJAMCO household members faced in reaching food security
without engaging them in the community planning process, and describes the rationale behind the
formation of the SJAMCO. The third section examines land reform’s ambiguous connection to poverty
alleviation, highlighting the important role community planning can play in building up social capital
between community and government. Finally, the discussion section derives four learning principles
from the SJAMCO’s community development experience, tying the value of social capital into the
collaborative partnerships that promote comprehensive planning, into community empowerment, and
into long-term social and economic sustainability.
I. The Value of Social Capital for Community Development
In very broad terms, social capital is grounded in a collective, social identity, which materializes
as a complex network of public associations of mutual recognition or acquaintances between
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neighbors, groups, and institutions (Fukuyama, 1999; Putnam, 1993; Franke, 2005). In the most
ideal form, social capital is said to be holistic and inclusive, conditions under which individuals feel
53
motivated to perpetuate several dimensions of public participation and civic engagement (Franke,
2005, p. 2; Wilson, 1997): feelings of trust, the lubricant of social capital (Putnam, 1993) inspire
acts of cooperation, information sharing, and collaboration between actors, leading to behaviors that
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
induce reciprocity.2 The abundance of these networks create the spiritual connectedness between
community residents, that is, the emotional aspects of social capital which increase inter-personal
trust, motivating community members to share resources, information, and give assistance to each
other. The strength of the trust, the sharing, and overall the internal cohesion propagated among
community members through investing in the network ultimately begets what Osberg (2003) called
a “bonding effect” (p.45).3 Bowles and Gintis (2003), in an economic paper studying the costs and
benefits of networks sustained through parochial contacts, called this type of bonding ‘parochialism’.4
They argued that within parochial systems, social capital is a normative feature and, therefore, is
regarded as a preventative antidote against the dissolution of trust in the community (p. 6). The
magnitude of social capital’s benefits is conditional upon the strength of the networks, therein.
Other scholars have made note of accumulated benefits generated from the rich presence of social
capital. Grootaert (1998) and Wilson (1996, 1997) highlighted social capital’s impact on economic
prosperity. Grootaeert (1998) pointed out that villagers bound to each other through informal
networks such as “friendship” associations in Ukraine could stabilize their fragile economic conditions
(pp.7-14). Exchanges or reciprocities, such as bartering or giving without expecting compensation,
between friends or associates are necessities in Ukraine’s asset-starved economy because these
networks help poor households survive. Correspondingly, Wilson (1996) observed that in a trust-
based economy, the economy can be more than stable – it can be prosperous. An abundance of social
capital networks causes individuals to join forces and engage in collaborative business ventures that
mold project management processes, such as community development and community forums, from
which arise material outcomes like community benefits agreements, memoranda of understanding,
jobs, investments, and income. The productivity visible during prosperity allows the poor to overcome
joblessness, which would otherwise become burdensome if social capital were weak.
The value of an environment rich in social capital is apparent in studies juxtaposing societies exhibiting
high levels of social capital against those manifesting low levels. The latter incubates political,
social, and economic dysfunctions between individuals and across communities because it lacks
vast networks of trust (Putnam, 1993, 2000; Fukuyama, 1999, pp.3-5). Under sparse social capital
conditions, violence and manipulative behaviors are outcomes. In other scenarios, households may
plunge deeper into poverty, hunger, or other socio-economic depressions. Residents may thereby
choose not to interact with each other, creating little opportunity for enriching social interactions.
Another impact of lack of social capital is distance from and separation of communities from government
institutions and centers of power. This type of isolation erects barriers between government agencies
and communities, disconnecting the former from the community’s needs and inhibiting socio-economic
improvements. With isolation, social capital weaknesses rest in the macro, vertical networks
between government and community. But, as Fukuyama (2002) wrote: it is not sufficient to go into
a [community], note the existence of networks, label it social capital, and pronounce it a good thing
. . . needed are (sic) more modern, broad-radius-organizations that connect across traditional ethnic,
class, or status boundaries and serve as the basis for modern political and economic organizations (p.
34). Social capital is more the result of extending and nurturing human and institutional relationships,
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rather than being a state of superficial, simple everyday interactions that, in my interpretation, one
54 would see at a grocery store or at a cocktail party.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
In the case of the Philippines, weak social capital is ref lected in a culture of elitism that sustains
a government-society hierarchy in which government does not, in practice, collaborate – that is,
coordinate knowledge, skills, funds, and best practices – with community groups as a vehicle for
generating socio-economic benefits to members of that community. Although times are changing,
patronage continues to be a major determinant of social capital in the Philippines, as are patron-client
relationships (Sison, 2006; Sidel, 1999). Patronage relationships involve the extension of benefits
or regulated rights from the patron, a person holding a position of power, to individuals or groups
(client) in exchange for their loyalty and compliance. In Philippine political culture, these relationships
become more entrenched when transacted in the public political domain because Filipino citizens see
political service as the government’s role, preferring instead to “retreat into their ‘private’ lives” and
let the government take care of policy details (Sison, 2006, p. 12). Though patron-client connections
are difficult to challenge in Philippine society, the introduction of foreign non-profits, research co-
operations between university and government, churches, and/or local advocacy organizations into
community-based work has helped to dilute the rigidity of the patron-client nexus to some extent.
These entities can operate as effective negotiators between government and community because they
offer something (knowledge, training, etc.) at little or no cost to the government, which earns them
status and respect.5 Nonetheless, the culturally embedded hierarchical value system continues to
distance the government from the full scope of collaborative practices necessary for identifying direct
needs and making progress on poverty alleviation projects.
The case of the San Jose Agrarian Municipal Cooperative (SJAMCO), a peri-urban agriculture
cooperative in Mindanao Island whose households received land title but did not benefit from a
community planning process, is a classic example of this isolation. A community planning process
incorporating community forums, where SJAMCO household members could (1) articulate their visions
of productive, livelihood projects that produce food continuously, and (2) identify stages of progress
consisting of measurements benchmarks, which signify states of accomplishments, could have further
aided the community in envisioning the pathway(s) towards their goals of food security. However,
as I show in this paper, the relevant government actors did not guide them through the planning
process. Thus, the SJAMCO households lost the opportunity to develop a road map steering them
towards a food-secure future. In the next section, I establish the rationale underlying land reform and
social capital building by describing the scope and depth of poverty in the Quezon Municipality and its
surrounding barangays.
II. Hunger and Poverty in the Quezon Municipality: A Rationale for Community Development
Before the 1988 Comprehensive Agrarian Land Reform Law (CARL) in the Philippines, the SJAMCO
households were employed as farmers for the Sunshine Farms hacienda (farm plantation). After the
passage of the law, the SJAMCO households received land title to 2.14 hectares with the help of the
Partnership for Human Rights and Development (PaHRD)6, a non-profit advocacy group based at the
Archdiocese Church of Valencia City (Mindanao, Philippines). Land title represented freedom from the
difficult working conditions they endured while employed at Sunshine Farms. The new law further
signified an opportunity to establish self-sustaining livelihoods.
A Socio-economic Snapshot of the Quezon Municipality
The most common indicators used to give a picture of poverty in a region are (1) incidence of poverty
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among households7 and (2) poverty income threshold. In Bukidnon Province (Mindanao Island), where
both Quezon Municipality and San Jose Barangay (the home of the SJAMCO) are located, the annual 55
poverty income threshold per capita was only about PhP12,186 (US$285)8 per annum in 2006.
Poverty incidence among families was 29.6% of the total population, slightly higher than the national
average of 26.9%. Generally speaking, these indicators convey the job climate of the region and the
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
quality of life, as they were linked to families’ ability to purchase foods, farm inputs, and other basic-
needs increments.
In Quezon Municipality, the jobs were largely concentrated in farming and manufacturing, two
important commercial sectors in Quezon Municipality. The manufacturing sector employed about 800
people in the Municipality (Figure 1). It consisted of a piggery, a corn and rice mill, an organic fertilizer,
a vulcanizing welding industry, the Naredico Logging Company, and the Bukidnon Sugar Company
(BUSCO), the largest employer in the area. Other types of businesses included lending institutions,
public markets, commercial retail centers, and sari-sari (mom-and-pop) stores (Quezon CLUP, 1999-09,
p. 38). The farming industry specialized in growing the export crops corn, rice, and sugarcane. In terms
FIGURE 1. Breakdown of Employee by Industry
Industry Number of Employees
BUSCO 607
Organic Fertilizer Industry 5
Vulcanizing Welding 40
Commercial Poultry 2
Commercial Piggery 8
Rice Mill 80
Corn Mill 80
Source: Quezon CLUP, 1999-09
of sales receipts, the sugarcane industry (constituting 11.25% of the total commercial industries in
Quezon) is the Municipality’s greatest asset, having garnered PhP502,695,000 (US$11,600) in 2000
(Quezon CLUP, 1999-09, p. 87).
The employment opportunities offered by the farming and commercial industries attracted a number of
migrants from around the region to join the earliest indigenous settlers of the Manobos, the Talaandigs,
the Higa-onons, and the Bukidnons. The biggest movement of migrants into the Municipality occurred
between 1970 and 1975, which showed a growth spurt of 38.6%, after the BUSCO and the Naredico
Logging Company invested in the area (Figure 2) (Quezon CLUP 1999-09, p. 22-24).9
FIGURE 2. Population Trends Table, 1970-1995
Year Population Increase Growth Rate
1970 38,084 ----- ----
1975 52,324 14,240 6.56%
1980 59,819 7,495 2.71%
1990 70,239 10,420 3.26%
1995 74,141 3,902 1.09%
Source: Quezon CLUP, 1999-09
However, much of Filipino labor is still bound up in agriculture in spite of the rise of commercial
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industries and the trend towards urbanization. The numerous haciendas in the area were evidence
that farm work was one of the primary occupations (see Image 1 below). Don Fortich, the wealthy
56 owner of a multitude of large-scale haciendas, propagated this farming model when he arrived in the
early 1920s to permanently settle in Quezon, leaving a legacy that remains visible today.10 Reliance
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
on patronage from the hacienda owner enabled the farmers to scrape by, but inadequate wages
and harsh working conditions forced them to reside in shacks along the edges of the haciendas.
The landlessness and poverty of the farmers placed them in a weak bargaining position to demand
better working conditions and wages, circumstances under which the 1988 Comprehensive Agrarian
Reform Law was passed. This law aimed to ameliorate farmers’ poverty by allocating to them land
allotments, where they can cultivate livelihood projects for income and for consumption.
IMAGE 1. Sugarcane Hacienda near the SJAMCO PUA Village. Source: Camille Tuason Mata.
The Beginnings of the SJAMCO Peri-Urban Agriculture Community
The poverty of Quezon Municipality was mirrored in San Jose Barangay and the life conditions of the
SJAMCO households. The poverty of San Jose barangay was marked strongly by a weak economy and
run-down infrastructure. The roads throughout the barangay are unpaved, aggravated by protruding
rocks and deep potholes carved out by torrential rains. And, like most of Quezon Municipality, the
economy was farm-based, albeit displayed a small cluster of agriculture manufacturing industries.
Corn and sugar haciendas, sari-sari stores, a rice mill, and a corn grits store were the main employers
(Quezon CLUP, 1999-09, p. 34). Moreover, water was a scarcity throughout the barangay. One
main point source, the Luan Luan Springs, serviced different barangays in the Municipality, but it
only provided about 956,300 liters of water per day. In San Jose Barangay, only 64% of the total
households were served (Quezon CLUP, 1999-09, p. 162), and they had to obtain their water from a
communal faucet.
The SJAMCO households’ poverty was ref lected in the uncomfortable conditions of their homes,
in their food shed, and in their unsanitary lifestyle (see Image 2 and Figure 3 below). Some of the
houses were built directly on the dirt with wood from the forest, while others were balanced on
stilts to protect them from the f looding caused by heavy down pours during rainy season. One toilet
serving the entire community was a simple hole in the ground covered by a Japanese porcelain toilet
seat. Because there was no central sewerage system, the residents could not dispose of waste in a
sanitary manner, thus exposing the residents to a number of transmittable pathogens. Most of the
2.14 hectares the households received was dedicated primarily to growing cash crops in order to
make payments on their farm loans, rather than on cultivating the crops grown for self-consumption.
Sugarcane, the biggest earner, was sold to BUSCO, while corn was sold at school or on the roadside.
A smaller plot of land was reserved for subsistence crops, such as camote (squash), mungo (mung
beans), sitaw (string beans), calabasa (pumpkin), or camatis (tomatoes).
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The SJAMCO peri-urban farms are 145 kilometers north of the center of Davao and 75 kilometers
57
south of Malaybalay, Bukidnon Province’s capital city (Quezon CLUP, 1999-09, p. 5). The SJAMCO’s
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
IMAGE 2. Dirt road leading away from the SJAMCO PUA Community. Source: Camille Tuason Mata.
Urban Market
Non-food Items
Urban Market
Rice SJAMCO Gardens
Meat Households Non-staple crops
Coffee Corn, sugarcane
Sugar (cash crops)
Salt
FIGURE 3. The SJAMCO Community Food Shed. Source: Camille Tuason Mata.
household members were employed at Sunshine Farms, but lived like squatters, earning a meager
income of PhP120 (US$2.80) per day, and with no benefits. The seasonality of work indicated
little job stability because they rotated between employers after harvest seasons without guaranteed
employment. The CARL was intended to assist farm workers like the SJAMCO households as a
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means of promoting “social justice . . . to move the nation toward sound rural development and
industrialization” (Republic Act 6657, 1988, Chapter I, Section 2, par.1) by decentralizing farm
58 cultivation into economy-sized operations.11 The social justice aspect was also inhered in the
decentralized model of land ownership, giving the farm workers independence and freedom from
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
the exploitative worker conditions they faced under the hacienda ownership model. Additionally,
rendering ownership of land either individually or collectively was the first step towards social and
environmental sustainability for landless communities, giving greater dignity to landless farmers and
poor farm workers, empowering them with the control of determining the terms of crop production,
choosing their own working conditions, and receiving a more proportional compensation of foods
produced on the farm.
The lands denoted in the CARL included all agricultural lands regardless of type of ownership or
commodity generated (1986, Chapter II, Sec. 4)12; the designated beneficiaries were all farmers and
farm workers as long as they were landless and expressed willingness to farm.13 As beneficiaries of
land reform, the SJAMCO households held land title for ten years, but could re-apply to regain title
within two years, thereafter. Upon receiving land, the LandBank, the lending arm of the DAR, assisted
with loans for the purchase of seeds and other farm implements. The disadvantage of this lending
program was the high interest rate of 6%, forcing the households to either search for supplemental
employment elsewhere or to focus on growing cash crops to pay off the loan.
The SJAMCO’s battle to obtain land rights lasted four years (1995-1999) because the management
at Sunshine Farms fought against their claims. The deluge of paperwork and mandatory follow-ups
inf lated the claims application period. Despite not having the required standard quorum of fifteen
members, the PaHRD recommended the farmers form into a cooperative, so they could claim funds
from the Department of Labor and Employment (DOLE) and the Department of Agrarian Reform
(DAR). When it became clear that the SJAMCO did not reach the fifteen households quorum, the
federal agencies became resistant to relinquishing additional funds because their Cooperative was
not considered legitimate. In sum, achieving ownership of land was the first step towards achieving
sustainable livelihoods and lifting community members out of poverty, but administrative and financial
barriers rendered this process much more cumbersome.
III. Obstacles in Community Development
Funding and bureaucratic inertia characterized the initial attempts of the SJAMCO households at
community development. At times, funding and bureaucratic obstacles were inseparable. When the
SJAMCO households campaigned for additional funds to complete already-started livelihood projects,
government red tape delayed the titling process and exhausted the household members. The lack of
political legitimacy for not having the fifteen-member quorum also appeared to depress morale, as this
status seemed to overturn what the SJAMCO members and PaHRD had already accomplished. These
frustrations, however, merely compounded the food security problems facing the households; in spite
of the initial monies, they produced insufficient volumes of foods. The root of their food insecurity lay
in the failure to plan properly for sustainable, long-term livelihood goals.
Government’s Approach to Community Development: The Obvious Initial Gaps
The government’s approach to community development was incremental rather than holistic and
comprehensive. Primarily, they provided seed capital and technical assistance whenever necessary.
Funding appropriations in the early stages targeted nascent commercial and farming projects. The
technical assistance the SJAMCO community received was in the form of a carabao (water buffalo)
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for transporting water and other materials into town and across the community, and for laying the
ground for crop plantings. 59
Interviews with a DAR agrarian officer and a PaHRD volunteer community organizer revealed that
the SJAMCO households received a combination of grants and loans for livelihood projects from the
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Quezon Municipal Government, the PaHRD, the DOLE, and the Governor of Quezon. Together, the
SJAMCO community received amounts that ranged from PhP250 (US$5.80) to PhP1.2 million (US$
27,660). The money was invested in other livelihood projects of their choosing. One investment was
in a sari sari store, but it eventually dissolved because the community did not have the consumer
base to sustain steady commercial transactions. The initial funding also catalyzed a piggery project
intended to raise piglets for consumption and for sale on the local market. The SJAMCO community
reserved 2000 square meters (0.28 hectares) on their land for this. However, the SJAMCO households
spent much of the money on their more imminent food needs, and therefore were not able to complete
or to expand on these livelihood projects to the degree at which they could produce enough food
to adequately support themselves. When the government restricted the disbursements of further
funds to the SJAMCO community because they were not a legitimate cooperative, tensions arose and
resulted in finger pointing and blaming.
Mutuality in Complaints: Blaming the Other
Winning land title represented a milestone in the Philippine land reform, as it laid down the foundation
for securing people’s access to their own food production and the anticipated outcome of overturning
household poverty. However, the relationship between the SJAMCO households and government
agencies turned sour when progress on the livelihood projects stalled. Accounts of the reasons for the
problems were different. The community’s version substantiated the narratives given by the volunteer
community organizers for the PaHRD, but disputed the claims of the agrarian officer assigned to their
case.
One constant complaint raised during the interviews with community members was the government’s
reluctance to buttress the livelihood projects with additional financial support and infrastructure
improvements. The households complained that the government dragged its feet instead of readily
supporting the households’ desire to enhance the food projects with, for instance, a poultry farm to
expand their food base and income. They also felt they had contributed a tremendous amount of
personal labor and money for additional necessities. To prove their sacrifices, the household members
complained about having to buy supplemental seeds and about building the pig-pen themselves. The
SJAMCO households further bemoaned the government’s failure to help them acquire other material
needs for their farms, like proper farming tools and a small truck for transporting their cash crops to
BUSCO and to the San Jose poblacion (city center), where the crops could be sold. The money they
requested to buy the truck never materialized.
Several members expressed the need for potable water for drinking and bathing. They mentioned
wanting a better engineered water well because the one they had built was often dry. Others
brought up much-needed farming and irrigation tools. A proper irrigation system would allow them
to comfortably sustain their farming operations even during dry season instead of relying solely on
rainfall.
The agrarian officer, however, gave a different account, insisting that the Department of Agrarian
Reform and the Department of Labor and Employment had been generous to the households with
funds and other assistance, especially with the toilet and piggery project. Furthermore, the agrarian
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officer argued that, being given assistance despite not having political legitimacy, since the SJAMCO
60 households were allowed to circumvent the standard quorum of fifteen household members required
of cooperatives, was a strong sign of the government agencies’ generosity. Rather, the agrarian
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
officer characterized the SJAMCO’s continuing needs as the result of general incompetence and
financial mismanagement.
The dispute provoked feelings of mistrust and uncertainty among the household members regarding
the government’s apparent lack of commitment towards the SJAMCO’s food projects. The SJAMCO
households’ sentiments were corroborated by the inadequate oversight from the DAR, as there was
no division within DAR assigned to guiding and aiding them with irrigation systems, expanded funds,
information sharing, cooperation, and training.14 More pertinently, the CARL makes no provisions for
integrating community planning into the land reform process. Although the Quezon’s Comprehensive
Land Use Plan (1999-09, p. 105) underscored the admirable goal of devolving haciendas into economy-
sized farms, aimed at empowering farm workers through independent farming and generating higher
returns in terms of income, self-sufficiency (§4.2.14), food security, and reduced poverty (§4.2.1.5),
these goals were not substantiated by a community planning process mandate that would have
woven land ownership rights into successively progressive food project outcomes. The planning
process would have helped the households delineate their food security goals, identify desired levels
of accomplishments, and uncover resources and assets that the households already possessed in
order to pinpoint a repertoire of need-gaps. These might have included material assets as well as
human capital ones, such as skills (farming, technical, etc.), and knowledge (in organic agriculture,
business, etc.) to achieve sustainable livelihoods. The community planning process might have also
brought attention to certain partnership-building needs and elicited ideas on how to create novel social
networks or strengthen existing, albeit weak ones, in order to meet the Comprehensive Agrarian
Reform Law’s objective of empowering and uplifting poor farmers from poverty.
DISCUSSION : The Significance of Planning for Food Security and Sustainable Livelihoods
Examining the SJAMCO experience revealed four principles about community development, which
in combination explain how social capital links the community planning process to empowerment
and poverty alleviation. First, community empowerment was derived from, de rigueur, possessing
resources and assets to realize aspirations for self-sustaining livelihood projects. Entitlements are
not a birthright for poor households, suggesting that, although land title is an important first step
towards social and economic sustainability, various forms of support from federal agencies are equally
imperative for enabling deprived households to overcome poverty and become food secure. The
continuing need for various forms of support further suggests that the community planning process
would have been invaluable for identifying where and how the government should intervene.
Secondly, empowerment coincides with stalwart community-government partnerships, indicated by
rich social capital that f lows dialectically between both entities. This relationship must be cultivated
and nurtured with unequivocal government commitment, as there are (1) financial reinforcements
needed by the community, and (2) government-administered services inaccessible to the community
that represented constraints on their social and economic progress. These constraints are financial
and infrastructural amenities, such as potable water, a well-functioning sewerage system, and
viable transportation networks, all of which speak about the quality of life for people and about
their ability to achieve sustainable living conditions. Failing to overcome both financial obstacles and
infrastructural constraints inhibit the growth of and enhancement of community empowerment. Thus,
strengthening the social capital between government and community through partnership-building
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would bridge the community to these services and render continued reinforcements in the form of
funding and materials.
61
Thirdly, the community planning process was an integral component of the pathway to food security.
In Cary’s (1970) very general definition, community development evolved out of organizing efforts to
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
adequately respond to specific needs for bettering society. At times, doing so has meant challenging
well-established, normative social systems. Irwin Sanders (1970, pp.19-26) added that community
development is multidimensional. It is (1) a process, describing f lows and exchanges between
stakeholders and agents that enact change; (2) a method, referring to how and what steps to take in
order to achieve some end; (3) a program, designed to raise a community’s social, economic, or natural
capital; and (4) a movement, or rather the coordinating of local leadership and resources, to attain a
“best outcome”. At the very core of these dimensions is the community planning process, an important
mechanism for ascertaining potential internal and external resources, active and sympathetic partners,
and need-gaps, all of which help to articulate community goals and benefits. The planning process
is, above all, integral to analyzing the feasibility of sustainable outcomes, especially when progress
is measured against short-term, medium-term, and long-term standards of achievement. In order for
community development to achieve “best outcome”, it must therefore be planned.
A fourth principle derived from examining the SJAMCO experience was recognizing the role of a
facilitator, in light of the patron-client relationships defining the government-civic nexus in the
Philippines, who possessed the familiarity with agrarian policies and the connections to centers of
power to instruct community planners on navigating the community planning process through the
fog of government bureaucracy. Community planners can here-to-fore shape or build social capital
relations with key stakeholders in government by illustrating to them how well-conceived project plans
can be both successful and beneficial for everyone involved. These project plans should communicate
the expected improvements, such as structural changes, essential materials, areas and levels of
government intervention, and other factors that contribute to project sustainability.
In the SJAMCO’s situation, the planning process never advanced beyond the funding disbursement
stage after the household members expressed their wants and needs. Although the members were
careful to think about income-generating projects, the government agencies failed to acknowledge the
dual importance of fulfilling the SAMCO households’ more immediate food and income needs along
with preparing for the sustainability of their livelihoods. This oversight resulted in the funds being
spent as if they were for emergency purposes, rather than as the first of many investments into a
sound economic foundation. In preparation for development, community planning might have looked
like this: identify what the households needed to purchase in the early stages, and then ascertained
how to organize and manage resources into self-sustaining, iterative food projects. Community
planners could have facilitated the brain-storming of ideas surrounding each livelihood project that
responded to questions about budgeting, the time line for project completion, and amount of funding
required of each project; linked up cash crops to new markets; elaborated on the full scope of the
projects to federal agents and compassionate investors; built a partnership with the government, while
seeking opportunities to fully exploit these relationships to the SJAMCO community’s advantage.
Unfortunately, these layers of community development were notably overlooked in the beginning, and
prevented the households from transitioning into a more sustainable existence.
CONCLUSION
The case of the San Jose Agrarian Municipal Cooperative teaches us that winning land rights, in
and of itself, is not enough to overcome impoverishment and to attain a food secure, sustainable
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quality of life. In fact, land reform is deeply embedded in the complex scope of community planning
62 processes, held together by strong partnerships with agencies that have the power to make decisions.
These partnerships are significant for engaging the SJAMCO households in a planning process that
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
would have guided them in developing sustainable livelihood projects and ensuring their successful
completion. Because the vertical social capital linkages were weak, a collaborative partnership never
evolved between the community and the Department of Agrarian Reform (DAR) and the Department of
Labor and Employment (DOLE), government agencies responsible for implementing the Comprehensive
Agrarian Reform Law. The lack of collaboration in light of weak social capital circumvented the
community planning process, and neither the DAR nor the DOLE accomplished community development
as well as they could have despite opportunities to steer the SJAMCO households toward a clear and
sustainable food security plan. Consequently, because of the cavalier manner in which the livelihood
projects were conceived and prepared, they remained food insecure, were unable to overcome poverty,
and thus their quality of life suffered.
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63
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
AUTHOR’S BIOGRAPHY
Camille Tuason Mata has a Master of Urban and Regional Planning from the University of Hawai’i
at Manoa and a Master of Arts from the University of Wollongong in Australia. She most recently
worked as an Environmental Justice Coordinator for the Mary Queen of Viet Nam Community
Development Corporation (MQVN CDC) on a number of neighborhood-based environmental remediation
efforts to improve the livability of the Vietnamese-American community in New Orleans East. She
will be completing a M.A in Interdisciplinary Studies with a concentration in Environmental Studies
at Goddard College.
ACKNOWLEDGMENTS
I am extremely grateful to the Archdiocese Church of Valencia City, the volunteers for the Partnership
for Human Rights and Development, agents for the Department of Agrarian Reform and the
Department of Labor and Employment for taking time out of their busy schedule to welcome me,
grant me interviews, and provide me with room and board. Most of all, I thank the San Jose Agrarian
Municipal Cooperative households for accommodating me more than once to help me complete this
thesis. I still plan to return and to help expand their livelihood projects.
(ENDNOTES)
1. This paper was based on a seven-week fieldwork and was part of the author’s completed thesis for the Master of
Urban and Regional Planning at the University of Hawai’i at Manoa. The author is deeply indebted to the individuals,
who agreed to be interviewed for this research, and to the Archdiocese Church of Valencia City, Mindanao, Philippines
for introducing me to the San Jose Agrarian Municipal Cooperative.
2. Although there was a unifying theme in writings about social capital’s dimensions, scholars differ slightly on their
approaches. Narayan and Cassidy (2001) emphasized the group feelings generated when social capital was present;
Woolcock (1998) approached the dimensions from a more comprehensive framework, looking also at the role of social
institutions. I stress behavior, and the positive reinforcements that are produced when actors behave inclusively. I also
take my cue from Auranen (2005), who drew the link between information sharing (what he saw as a dimension of social
capital) to developing innovations in science. The information-sharing dimension was key here to enabling the SJAMCO
households to cultivate livelihood projects that are sustainable. Information sharing between the SJAMCO households
and government officials could have identified the desires of the community and the challenges facing government
officials as far as what more information they needed from other sources to help steer the SJAMCO households towards
sustainable and self-sufficient development.
3. Osberg (2003) cited Dick Stanley’s invaluable work on social cohesion benefits to the community. Stanley explains how
the bonding effect occurs. He wrote: ‘social cohesion was the bonding effect within a society that arises spontaneously
from unforced willingness of individual members of society to enter into relationships with one another in their efforts to
survive and prosper’; ‘[it] was strengthened by the existence and creation of social capital (p.45).
4. While Bowles and Gintis (2003) proved that parochialism carries benefits to communities with strong inter-groups
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networks, which capitalize on the feeling of unity and trust among group members, their study was confined to in-group
micro-units and do not consider networks in the form of collaborative alliances with pertinent macro institutions. They
also do not pay much attention to the underside of parochial relationships, which is that social capital gives way to
64 nepotism in the context of such relationships.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
5. The complexity of undertaking community-based work aimed at reducing poverty through food security projects was
deeply rooted in the patron-client relationships, but this discussion was too expansive for the scope of this paper.
6. PaHRD is an advocacy group, established in 1994, that builds the internal capacity of farmers, peasants, and
indigenous communities by providing training on political topics, such as human rights, gender sensitivity and equality,
and community empowerment.
7. The percentage of people in poverty for a designated area.
8. Poverty income level was not available for Quezon Municipality or San Jose Barangay, specifically, because the
Philippine statistical data do not generally report on sub-island performance.
9. The growth rate was calculated using the formula r = Yt+1 – Yt / Yt.
10. Exact data regarding how much of Quezon Municipality was under hacienda ownership was unavailable. The city
planning office does not have land use classifications distinguishing hacienda lands as a separate category.
11. The CARL also protects the rights of (subsistence) fishermen, but this element of the law will not be discussed
here.
12. The re-distribution of land was to be completed within ten years. Re-distribution was therefore divided into four
phases. The first targeted rice, corn, idle, foreclosed, abandoned, and voluntarily donated private lands. The second
phase targeted private agriculture lands larger than 50 hectares, ‘alienable and disposable” (A&D) public agriculture
lands. The third phase encompassed private lands between 24 and 50 hectares, as well as the land sizes between 5 and
24 hectares (Balisacan, May 20, 2007, p. 8).
13. The CARL distinguished between the definitions of “farmer” and “farm worker”. A farmer is defined as one whose
main livelihood is growing crops (Chapter I, Sec. 3(f)). Farm worker means one, who farms as a means of receiving wages
or other benefits, employed part-time, full-time, or seasonally (Chapter I, Sec. 3(g),(h),(i)).
14. A new amendment to the CARL (Republic Act No. 7905) was added (§35) to provide greater support to beneficiaries
with government subsidies, training in cooperative management, improvements in infrastructure and public works,
but language for a comprehensive community planning process remains missing. <http://www.chanrobles.com/
republicactno7905.html>.
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Karin Bradley
Ulrika Gunnarsson-Östling
Professor Karolina Isaksson
EXPLORING ENVIRONMENTAL
JUSTICE IN SWEDEN - HOW TO
IMPROVE PLANNING FOR
ENVIRONMENTAL SUSTAINABILITY
AND SOCIAL EQUITY IN AN
“ECO-FRIENDLY” CONTEXT
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
69
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
ABSTRACT
Environmental challenges, especially climate change, are highly discussed topics in the Swedish public
debate, but questions about who is causing the problems and who is affected by them are seldom
asked. This also applies to questions of who defines what should be regarded as acute environmental
problems and what constitutes high-quality environments. This paper explores how environmental
(in)justice issues can be framed in a Swedish social context, drawing from three cases: municipal
promotion of eco-friendly lifestyles, large-scale infrastructure planning, and planners’ attitudes
towards justice. The three cases deal not only with distributional, procedural, and substantive aspects
of justice, as is common within the US environmental justice framework, but also with discursive
dimensions of justice. We argue that elucidating such examples of environmental (in)justices is crucial
to nuance the mainstream, consensus-oriented sustainability discourse in Sweden.
INTRODUCTION: Environmental Justice: From the United States to Northern Europe
One of the principles expressed in the 1992 Rio Declaration is that equity is at the core of sustainable
development on a global level. This perspective is also ref lected in policies and planning in Sweden
where sustainable development has been high on the agenda for the past 15 years. But, while justice
between the global North and South is generally acknowledged in Sweden, promoting justice among
different groups within the national boundaries has not been emphasized in the national sustainability
debate. This might relate to the fact that it is difficult for Swedish citizens to see the environmental
impact caused by their mobility, consumption, or housing choices. Complex problems like air and water
pollution, for instance, are not always tangible on the local level. When environmental problems do
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
not appear to directly affect the people who cause them, their high-energy lifestyles are more likely
to continue. Thus, in a planning context, studying the (a)symmetry between the origin and impacts
of environmental problems could be a way of recognizing socially and environmentally unsustainable
planning, thus providing important input into current strategies for sustainable development.
Several studies in the United States have shown that disenfranchised, low-income, and/or minority
populations are generally more at risk of being exposed to environmental hazards than other groups
(Bullard, 1993, 2000; Hofrichter, 1993; Faber, 1998). For this reason, grassroots groups, policy-
makers, and academics have attempted to address such environmental injustices by reducing the
exposure of marginalized communities to toxic industries, hazardous waste sites, or landfills (see,
e.g., Faber, 1998). Environmental justice perspectives have also recently been explored in the British
context, where they have been identified as crucial to the development of efficient strategies for
sustainable development (see Agyeman, 2005; Agyeman & Evans, 2004; Mitchell & Dorling, 2003;
70 Scandrett, Dunion, & McBride, 2000). Until now, however, Swedish policy-makers, researchers and
NGOs have, overall, not paid any attention to such perspectives (Bradley, 2004; Isaksson, 2001).
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Sweden is known historically for its welfare system and progressive environmental policies;
international evaluations from the early 2000s, for instance, identified Swedish administrative and
institutional structures as one of the most successful platforms for the implementation of Agenda 21
(Eckerberg, 2001) and thus for achieving sustainable development. The current Swedish strategy for
sustainable development, formulated by the Central Government in 2004, emphasizes the interrelation
between social, economic, and environmental sustainability, and highlights the importance of social
justice in this context (Swedish Government, 2004). Although a great deal of attention is paid to
social issues in the formal strategy, it is unclear what this means in the planning practice. The overall
message being communicated in the strategy document is consensus and win-win solutions, in which
economic development, social justice, and environmental protection fit smoothly together in the
endeavor for green growth (Hilding-Rydevik, Håkansson & Isaksson, forthcoming). Nothing concrete
is said about potential conf licts, controversies, or power issues embedded in sustainable development
policy and planning practice (ibid.).
In this paper, we understand sustainable development as focusing both on protecting the resource
base and enhancing social justice, and – not the least – on the connection between the two. It is
therefore necessary to consider how natural resources are distributed, how decisions affecting the
environment are made, and how environmental qualities are defined. The objective of the paper, is
to show how environmental (in)justice issues can manifest in a Swedish urban context. To do so,
we will leave the policy documents behind and focus on planning practice, exploring three cases
from our research on planning in Stockholm: municipal promotion of eco-friendly lifestyles, large-
scale infrastructure planning, and the attitudes of Stockholm City planners towards justice. The
cases highlight different aspects of justice: Whose voices are acknowledged in planning processes?
Who gains and who loses from planning outcomes? How are environmental qualities and problems
distributed among different social groups and generations? Lastly, how are notions of environmental
benefits/drawbacks constructed? These three cases illustrate procedural, distributive, and substantive
aspects of justice, which are common in US and UK environmental justice research (e.g., Turner & Wu,
2002; Agyeman, 2005). However, our last question adds a discursive approach to justice: we focus on
the framing of environmental problems and the consequences of this framing in terms of what issues
and whose impact(s) are considered in policy and planning. To use a discursive approach thus means
shedding light on tacit preconditions and underlying norms and assumptions in planning. It also means
illuminating questions of what environmental goods and externalities are to be distributed, amongst
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
whom (people within a community, all people living now, or future generations,), and according to what
principles of justice (everybody being equal, justice according to needs, or according to performance).
Regarding substantive justice, a discursive approach adds questions about what should be regulated
by minimum standards. These types of questions appear to be important, as we will see, for an
analysis of environmental justice in Sweden.
Case 1: Eco-friendliness—According to Whom?
Swedish urban regions, like most other European cities, are becoming increasingly multicultural and
diverse in terms of lifestyles, socio-economic conditions, and gender roles. This implies that people
already have, and continue to develop, a variety of relations to environmental issues such as energy
use and perspectives on nature and the ecosystem. A current research project (Bradley, forthcoming)
looks at how urban planning strategies in Sweden, promoting eco-friendly living, relate to the
71
increasingly multicultural and socially diverse population, focusing on the following questions: What
notions of eco-friendly lifestyles are being encouraged in the rhetoric of current planning strategies?
How do the strategies reinforce, or conf lict with, the everyday lives of people with differing cultural
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backgrounds and socio-economic conditions?
The goal of the project is to comment and elaborate on the existing planning strategies in terms
of justice within the environment (i.e., among different groups) and justice to the environment (i.e.,
to non-humans and future generations). Our first case study took place in Spånga-Tensta, a city
district in northern Stockholm. Spånga-Tensta is one administrative unit, but is divided into two quite
different residential areas: Tensta and Gamla Spånga (see Images 1 and 2 below). Tensta is an area
with multi-family houses from the 1960s where 85% of the residents have foreign background1 —
compared to an average of 26 % in Stockholm.2 Income and education levels in Tensta are furthermore
considerably lower compared to the Stockholm average.3 The adjacent area of Gamla Spånga consists
of mainly one-family houses, built at the turn of the last century and onward, and a population with
ethnic background, incomes and levels of education similar to that of the overall Stockholm region.4
This case study is based on interviews with local residents (both individual interviews and focus
groups), a resident postal survey5, interviews with planners and officials, and an analysis of strategic
planning documents. In total 45 residents and five officials have been interviewed and 175 residents
have responded to the survey.
This study reveals a prevalence of a discourse in which the commonly-accepted “Swedish” ethnic
identity is connected with a general notion of environmental responsibility in the form of tidiness,
recycling, and familiarity with nature and animal species. This is a notion that warrants criticism,
however, since the residents termed “Swedes” give off not only some of the largest ecological
footprints per capita in the world,6 but their footprints are also larger than those of non-Swedes in
Sweden, who often reside in multi-family houses, and do not own cars, etc. (Bradley, forthcoming).
In other words, what has been defined as environmentally-friendly behavior appears to have been
framed by Swedish middle-class norms and habits. It is also worth noting that the public strategies
for sustainable development used in the case study area have primarily been directed toward low-
income and immigrant households in multi-family houses residing in Tensta rather than at the energy-
consuming lifestyles and travel habits of the more aff luent “Swedes” who reside in one-family houses
in Gamla Spånga. According to the city official in charge of sustainability work, 90% of his time
and resources was devoted to promoting change in the low-income areas, where the predominantly
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
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IMAGE 1. Housing in Tensta. Photo: Karin Bradley.
IMAGE 2. Housing in Gamla Spånga. Photo: Karin Bradley.
foreign-born population was encouraged to recycle, keep the area tidy, and use public transport and
low-energy light bulbs, etc., while hardly any of his time was used for advancing eco-friendly living in
the more aff luent area nearby. Furthermore, the urban development plans for Tensta have primarily
focused on improving the low-income high-rise area, making it denser and more “urban,” partly
motivated by environmental concerns. Paradoxically, this poorer area is already very dense and the
use of public transportation is considerably higher than in the more aff luent neighboring area.
Altogether, this research raises the question as to whether the discourse on planning for eco-friendly
living entails processes of normalization, perhaps unintentional, by which “the Others” -- foreign
and/or “troublesome” residents -- are to be transformed into “well-behaving Swedes” (ibid.). In this
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
study, the discursive aspect of (in)justice lies in how complex societal interactions, in which planners
and planning play an active role, have come to produce notions of desirable lifestyles that suit and
reinforce the preferences of the dominant Swedish middle classes. This reinforcement of the Swedish
middle-class high-energy life styles does not directly affect less aff luent neighboring communities, but
it affects global warming and environmental degradation on a global level. Thus, what we are dealing
with here is an issue of “(un)fair share in environmental space,” i.e., how the consumption of the
earth’s resources is divided amongst different groups and generations.7
Another suggestion as to why the policy focus is skewed towards low-income areas may be related
to the fact that local tidiness gets mixed up with eco-efficient living. For instance, the municipality
has, within its budget for local sustainability work, initiated a project called “Spånga-Tensta Nice and
Tidy” where local organized residents are reimbursed for regularly cleaning a part of the neighborhood.8
The assumption underpinning this project is that this activity leads to “greater awareness of waste
management and an attractive and healthy outdoor environment,” as well as overall “environmental 73
gains”. 9 This is an example of “sustainability policies” which include both measures to improve the
local environment towards more greenery and tidiness, and measures to reduce the use of resources.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
These two types of sustainability measures are often treated as one package with the assumption
that improvement in the first type goes hand in hand with improvement in the second. However, in
the case study, the wealthier area of Gamla Spånga is green, attractive, and tidy, and thus seemingly
“unproblematic” from the visible sustainability policy point of view, but it is nonetheless an area of
high resource consumption, thus qualifying for the promotion of more eco-friendly lifestyles even more
than the “untidy” and poor area of Tensta.
In summary, through a clearer definition of what type of “environmental improvement” is intended,
with which goal, and for whom, and through learning from different ways of saving natural resources,
urban planning policies could be better attuned with social and cultural diversity (justice within the
environment) and could become more environmentally progressive (justice to the environment) (ibid.).
Case 2: Traffic Infrastructure—At Whose Expense?
Another example that illustrates environmental justice in Sweden comes from the field of infrastructure
planning in urban areas. “The Dennis Package,” one of Sweden’s most extensive infrastructure
projects to be planned and implemented (in part) in the 1990s, was an initiative by the Swedish
Government, which commissioned the Director of the Bank of Sweden, Bengt Dennis, to lead the
negotiations between the State, the Stockholm County Council, and the municipalities of Stockholm.
The goal of these negotiations was to reach an agreement on infrastructure investments that would
improve environmental conditions, accessibility, and economic development in the Stockholm region
(Isaksson, 2001, p. 49).
The ensuing Dennis Package was the result of more than two years of negotiations. It was a large-
scale scheme of infrastructure investments -- including a ring road and a bypass (as shown in Figure 1)
-- and public transportation system investments. The Package also introduced toll roads on the most
costly new roads, namely, the western link (part of the bypass) and the eastern link (part of the ring
road) (ibid).
The analysis of the Dennis Package was based empirically on an analysis of local, regional and
national planning and policy documents, interviews with planners, policy-makers and stakeholders,
newspaper material, and statistics about the Stockholm area (Isaksson, 2001). The environmental
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
justice aspects in this project are related to the location and design of the new major roads. To reduce
the negative environmental effects of the projects, the western link bypass and the eastern link were
planned with the construction of a system of tunnels. The aff luent central parts of Stockholm, as well
as the well-to-do municipality of Ekerö, would receive the most direct benefit from these measures
of environmental harm reduction, which were being paid for by a massive national budget, including
revenues from toll roads. Meanwhile, other roads in the Dennis package were planned to be built
above ground in municipalities and districts where the average income was considerably lower, such
as the Northwestern districts of Stockholm (Hjulsta, Tensta, and Akalla). These areas have a higher
rate of unemployment (more than 8% in 1994, as compared to 5,5% for the region at large), a larger
percentage of residents of foreign background (more than 20% in 1993, compared to 7% in the region
at large), of lower income (more than 20% of the inhabitants were dependent on social welfare in
1993, compared to 8,5% in the region at large), with health problems (in parts of these areas, more
than 35% of the residents had been ill over long periods of time or were not working at all due to
74 sickness pension in 1993, compared to 22% in the region at large) (The Office of Regional Planning
and Urban Transportation, 1995).
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
In many cases, the new roads would cut through local green field sites of importance to outdoor life
and recreation for the inhabitants of these poorer districts. Worth noting is that the residents in these
areas have a lower level of car-ownership than in many other parts of the city and the region, thus
they would not benefit as much from the investments in new road infrastructure.
Part of the explanation for the uneven distribution of benefits and burdens in the Dennis Package
relates to the different values given to different environmental qualities and areas of special interest.
In general, areas with well-known cultural heritage qualities such as royal castles and parks – like the
Drottningholm Castle located in Ekerö, as well as the old royal parks and castles in Djurgården and Haga
in the Eastern and Northeastern parts of Stockholm – attracted much media attention. Meanwhile,
several areas of importance to outdoor life and recreation in the poorer neighborhoods were not
considered, for example the green areas of Järvafältet in the Northwestern parts of Stockholm, or
Gömmaren, Glömsta and Hanveden in the Southern parts of the region. At some point during the planning
process, concerns were raised about the environmental consequences for the affected suburbs. In one
of the political debates in the city hall of Stockholm in 1994, one Social-Democrat politician addressed
the issue of unequal distribution of negative environmental consequences (Stockholm Municipality,
1994). However, there were only a handful of similar statements in the extensive political discussion
and media debate (Isaksson, 2001, p. 160).
In 1997, the government put an end to the plans to construct the western link of the bypass and the
eastern link of the ring road. However, several of the roads that were planned to go above ground in
the Southern parts of Stockholm were built, as well as most parts of the roads in the Northwestern
and Northern parts of the region. Today, the western link, now called “The Stockholm Bypass”, is
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
75
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
FIGURE 1. The ring road and bypass included in the Dennis Package. Source: Isaksson, 2001.
once again included in current infrastructure plans. The environmental justice consequences are as
obvious today as in the 1990s, but the issues remain unaddressed in the general policy debate.
Case 3. Planners’ Attitudes Towards Justice
Our third case of environmental justice aspects in Swedish policy and planning is taken from a series
of seminars organized by our research group for planners in leading positions at Stockholm’s City
Planning Office (documented in Orrskog, 2008; Zimm, 2007). We held six seminars in 2006 on the
theme “Planning for Good Environment and Justice under Diffuse Circumstances,” with a follow-up
seminar in 2007. The initiative of the seminars came from the planners and were meant to give both
planners and researchers a deeper understanding of contemporary challenges in planning (Orrskog,
2008, p. 3-7). The seminars consisted of a series of focused conversations on how discourse,
mobility, justice, and diversity can be understood in the context of various ongoing planning projects
in Stockholm, urban planning trends in other European countries, and how the future role of planners
could be shaped. Seven-eight planners and three-four researchers participated in the seminars. The
planners experienced the seminars as a forum for ref lection and have expressed their interest in
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
maintaining and spreading the scope and content of their discussion through the Planning Office (ibid.,
p. 69).
It was apparent from the conversations that the planners perceive their work as touching upon
issues of justice, even if this is seldom expressed in an explicit way in their daily practice. However,
these discussions revealed how the planners worked especially with issues related to procedural
and substantive justice, as illustrated in the description that follows. The planners worked actively
to apply new methods of involving different groups in the planning process with the intention to
understand their viewpoints on the local environment and its future. One planner expressed it as
follows: “We have worked with in-depth interviews, focus groups, neighborhood walk-throughs, and
meetings with representatives of different groups. [And] we have actually become much better at
this. (ibid., p. 63).”
76 However, the planners also became aware of shortcomings, such as the difficulty of getting residents
of foreign background involved and how to handle “emotional expressions” from, e.g., mothers with
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
children (ibid, p. 63). Thus, we see that the planners worked with procedural justice, even though
it could be further developed through efforts to increase the ability of underrepresented groups to
participate and become empowered to participate in the planning process.
Among the planners, the issue of procedural justice appeared to be the least contested, and the
general standpoint was that procedural justice can be safeguarded through the process of broad
public participation. Less attention was given to whether a formally just process necessarily results
in environmental just outcomes. In other words, less attention was given to distributive aspects of
environmental justice. However, this does not imply that environmental issues as such were neglected.
According to the planners, environmental issues like noise and air quality were best managed by
respecting environmental norms and regulations10. Thus, the planners were on the whole satisfied with
the substantive environmental justice and argued that current planning practice gave higher priority to
environmental sustainability than to social sustainability, even if this was changing (ibid., p. 15). One
planner said: “Nature had higher intrinsic value in the 90s. Nonetheless, the Swedish National Road
Administration still has shelf after shelf of official reports about the expected environmental effects
of Route E18, but hardly a sheet on its social impact, such as barrier effects.” (ibid., p. 15)
In sum, the planners underlined procedural justice and believed that substantive justice is (or could be)
fulfilled by norms and regulations, while they paid less attention to distributional justice. Discursive
aspects such as what constitutes a good or bad environment and who defines them were not subjects
of focus.
Furthermore, the planners saw planning as a situated practice, closely related to normative and ethical
issues such as environmental justice, but in the beginning of the seminar series, they seemed blind
to their own potential role or responsibility in relation to this. Rather, they tended to hide behind
their formal role of merely executing political, and therefore often shortsighted, decisions. One of the
planners stated that: “[…] Politics today involves very little problematizing. It’s very one-dimensional,
very short-sighted and very limited—and we know all that so well. That often makes our issues very
simple, too simple”. (Planner at Stockholm’s City Planning Office at the follow-up seminar, October
26, 2007). At the end of the seminar series, we noticed a slight shift in the planners’ opinions and
they started raising the idea that they could be more pro-active by trying to put vital issues as related
to environmental justice on the political agenda (Orrskog, 2008, p. 67). They had no desire to bypass
democratically elected politicians, but they began to see an opportunity to raise political awareness,
e.g., on environmental justice issues that are not normally elucidated or discussed in the political
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
debate.
A past example of where they did try to inf luence the outcome is when the local government of
Stockholm decided that 20,000 new residences would be built between 2003 and 2006. Not only
were the planners under stress to fulfill this goal in such a short time, but they felt it was difficult
to do it in a socially acceptable way. In an attempt to be able to defend “their” plans, they tried to
take justice concerns by mixing different forms of rental/owner-occupied dwellings to facilitate for
different income groups to dwell in the same area (ibid., p. 17). Thus, the planners tried to adapt the
plans to more just principles, or, as one planner put it, “By being good at providing [what the politicians
demand], the result can also be adapted to what we think is good.” (ibid., p. 17).
Another situation when the planners expressed their will to become more proactive, is when they
have knowledge of undesired environmental or social consequences of political decisions, which they
77
can more actively communicate to the politicians, who might then decide to redefine their “order”
to the planners so that the outcome becomes more environmental just. An example that came up
during the seminars was the Swedish school reform that changed a long-standing situation by which
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
children had almost always enrolled in the school that was physically closest to them, to allow
parents to choose the school they wanted for their children11. The planners noticed that this reform
had caused increased travel and thereby increased pollution, as well as more traffic in proximity
to the schools, which was harmful to the local school environment. None of these issues had been
brought up when the political decision was taken. During the seminars, the planners suggested that
the spatio-environmental consequences of political reforms should be investigated more thoroughly
before implementation (ibid., p. 25-27).
The above discussion shows an opening on the part of both planning and decision-making for increased
ref lection and action regarding environmental justice.
CONCLUSION: Environmental Contestations for the Future
The three cases explored in this paper illustrate issues of environmental (in)justices in a Swedish
planning context. The first case involves distributive justice in terms of resource use and discursive
justice in terms of the production and reproduction of notions of eco-friendliness, in which “Swedish”
high energy consuming middle class norms and habits remain unchallenged. The case of The Dennis
Package deals with distributive justice in infrastructure planning. The case illustrates how adverse
environmental impacts mainly affect disenfranchised communities. The third case shows how planners
work actively with procedural justice and see substantive justice as fulfilled by environmental norms
and regulations. However, when analyzing the second and third cases in more depth, the discursive
dimensions of justice become evident. For instance, procedural justice is not only about a fair process
but also about issues preceding the process, i.e., which issues are brought up, defined as relevant,
irrelevant or not even thought of. A discursive approach to substantive and distributive justice thus
adds questions of what is to be regulated and what is to be distributed and who defines and formulates
them.
The findings on environmental (in)justices are in themselves a critique and contestation of the currently
dominant Swedish sustainability discourse and its strong focus on consensus and win-win strategies.
Our three cases show that environmental planning is far from a consensus affair. Sustainability policy
and planning entails fundamental conf licts and justice issues that need to be considered. However, the
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
currently dominant sustainability discourse provides no help in identifying, acknowledging or discussing
justice aspects—on the contrary. For this reason, we argue that environmental justice research is an
important contribution to the Swedish sustainability debate and it needs to inform more greatly the
work of planners and policy-makers. Shedding light on environmental justice issues, as we have done
in this paper, is a means of revealing fundamental political and ethical dimensions of sustainability
politics and planning, and of making them more tangible and engaging—not only for researchers, but
for politicians, planning professionals, laypeople, and all of the many other social actors who have and
will continue to have important roles in the quest for sustainable development.
78
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BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
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AUTHORS’ BIOGRAPHIES
Karin Bradley is a Ph.D. student at the Department of Urban Planning and Environment, Royal Institute
of Technology (KTH), Stockholm, Sweden. Her dissertation deals with how planning for ecological
sustainability relates to increasingly socially and ethnically diverse populations in European cities.
Ulrika Gunnarsson-Östling is a Ph.D. student at the Department of Urban Planning and Environment,
Royal Institute of Technology (KTH). Her interests lie primarily in the fields of images of the future,
environmental justice, and gender.
Karolina Isaksson is an Assistant Professor at the Department of Urban Planning and Environment,
Royal Institute of Technology (KTH) and her research deals with issues of power and justice in
planning and decision-making.
[ENDNOTES]
1. “Foreign background” is defined as foreign citizens born abroad or in Sweden, and Swedish citizens born abroad,
data from Dec 31, 2003. Stockholm’s Municipality: Spånga-Tensta – Ditt stadsdelsområde i Stockholm 2004-2005.
Information folder.
2. The Statistical Office of Stockholm’s Municipality. Data from Dec 31, 2006: http://www.usk.stockholm.se/internet/
omrfakta/tabellappl.asp?omrade=sdo03&appl=Omradesjmf&resultat=Andel, Accessed, March 18, 2008.
3. In Tensta around 20% of the inhabitants in the ages 25-64 have an education level above high school-level, which
can be compared to around 50% in Gamla Spånga and 52 % in the municipality of Stockholm as a whole (The Statistical
BRADLEY, GUNNARSSON-ÖSTLING, ISAKSSON
Office of Stockholm Municipality, Data from Dec 31, 2006).
4. Ibid.
5. The resident postal survey was conducted by the Stockholm Municipality Statistical Office, USK (2005) and consisted
of 175 responses from residents of Spånga-Tensta. 300 persons received the survey among the 35,000 residents in the
city district).
6. The ecological footprint per capita in Sweden is 67 global hectares, which can be compared with the West European
average of 61 global hectares, the North American average of 109, the African average of 8.5, and the average of
the Middle East and Central Asia of 13.6 global hectares per capita. For a detailed explanation of how the ecological
footprints have been calculated, see the report by Redefining Progress, “The Ecological Footprint of Nations – 2005
Update,” which is available at: http://www.rprogress.org/publications/2006/Footprint%20of%20Nations%202005.pdf.
7. The concept “fair shares in environmental space” has been developed by Friends of the Earth International. For a more
detailed description of the concept see: http://www.foei.org/en/publications/sustainability/sustain.html.
80
8. See the project description of ”Spånga-Tensta rent och snyggt”: http://www.miljobarometern.stockholm.se/content/
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
pdf/hu/godaexempel/rentsnyggt_beskr.pdf, Accessed, Feb 21, 2008.
9. Ibid.
10. Norms and regulations, such as the 16 Swedish Environmental Quality Objectives adopted by the Swedish Parliament
in 1999 and in 2005, the Swedish Environmental Code (SFS 1998:808) and the Swedish Planning and Building Act (SFS
1987:10).
11. Private schools started to appear with the Social-Democrat government, but when the right-wing coalition came
into power in 1991 the Conservative Prime Minister declared a major change (Swedish National Agency for Education,
2003:34). From then on, parents have been able to chose to put their children in municipal or private schools, but also
schools in other municipalities.
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Julie Hermesse
ANALYSIS OF COSMOLOGY, PRAXIS
AND HISTORICAL INEQUALITIES
IN THE CONSTRUCTION OF
SOCIONATURAL DISASTER IN THE
MAM GUATEMALAN ALTIPLANO
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ABSTRACT
This article critically examines the mechanisms of inequality that perpetuate vulnerability to extreme
natural phenomena. It demonstrates that the catastrophic consequences of a natural disaster result
more from a social process than the event itself. The analysis, based on ethnographic research in a
municipality of the Mam Guatemalan Altiplano, first considers the construction of social and cultural
vulnerability to disasters. It then provides an analysis of the tensions between a traditional Mayan
discourse and respect for nature and the unsustainable practices of land management as exhibited
in this context. Finally, I ref lect on the unjust historical distribution of land in Guatemala and the
dominant ideology of the global market, both of which render impossible a sustainable relationship
with the natural environment. These unsustainable environmental practices, caused by economical
and social inequalities, produce an unjust distribution of vulnerabilities to disasters.
INTRODUCTION
This article demonstrates the necessity of breaking down the term “natural disaster” by examining
the repercussions of extreme events as both social and natural phenomena. I first question religious,
cultural and social representations of the Maya Mam population of the Guatemalan Altiplano1 faced
with the latest extreme natural phenomena: Tropical Storm Stan2. From the ethnoecology perspective,
developed by V. M. Toledo (1992) as “the ecological evaluation of the intellectual and practical activities
that certain human groups execute during their appropriation of natural resources” ( p. 10), I approach
the Mayan Mam cosmology (Kosmos) relating to the universe and in particular relating to extreme
natural phenomena. I observe that representations of disasters can induce fatalist attitudes when
residents are faced with catastrophes. I next analyze the relationship between religious belonging
and unsustainable environmental practices, focusing on the praxis of the inhabitants of the Altiplano
Mam with regard to their activities involving the natural environment. Finally, I examine the inf luence
of historical and structural contexts on the construction of economical inequity and unsustainable
environmental practices. This article attempts to illuminate the elements inf luencing environmental
and social practices. A holistic and comprehensive anthropological approach allows me to examine the
complex development of disaster vulnerability construction. Environmentally unsustainable practices
originating in economic inequalities create uneven vulnerabilities to extreme natural phenomena.
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“Natural” Disasters: Phenomena at the Interface of Society and the Natural Environment
Guatemala, known in the tourist industry for its eternal spring, is also known for its eternal violence3
(Le Bot, 1992; Bataillon, 2003) and its vulnerability to natural disasters4 (Hernández Pico, 2005;
84 Gellert, 2003). The ethnographic work forming the basis of this research began in the Mam Guatemalan
Altiplano of the Quetzaltenango County six months after Tropical Storm Stan devastated this area
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
in October 2005 (Figure 1). In this Northwest, rural zone of Guatemala, I was based in the center
of the municipality of San Martín Sacatepéquez (SMS), located in the “cold lands” of the mountains
(2,400 meter altitude), rather than in a lowland municipality with a tropical climate. This article
is based on 6 months of field work in SMS. The data was collected from participant observations
and interviews with inhabitants of all generations and religious convictions. The municipality,
which is populated 95% by Mayan Mams communities, suffered human, material and agricultural
devastation from Tropical Storm Stan. The municipal authorities estimate that 21,500 of the 29,000
inhabitants of the municipality were directly or indirectly affected by Stan5. Stan generated a state
of catastrophe in SMS, with damages far more extensive than those of previous disasters and those
of other municipalities of Quetzaltenango County, caused by the same storm.
The frequency of extreme natural phenomena in Guatemala (hurricanes, volcanic eruptions and
earthquakes) renders these natural events also as cultural and historical events in the history of the
people, even though the consequences of these disasters have not always been catastrophic. The
ancients, regarded as guardians of the memory of the community, tell, for instance, that other storms
and hurricanes passing through SMS did not produce as much damage as Stan. This event provides a
recent lens through which to analyze how natural disasters are understood in the community and how
we might view disasters as not only as natural, but also social and cultural events.
Religious, Cultural and Social Representation of “Natural” Disasters
Differently experienced by different communities, disasters generate multiple interpretations based
on religious convictions and cultural representations (Prado, 1990; Hoffman, 2002). In an analysis of
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FIGURE 1. Guatemala and Quetzaltenango, according to linguistic divisions. Source: Bryan Long.
my interviews, religious belonging seems to distinguish the inhabitants of SMS’ interpretations of the
passage of Tropical Storm Stan.
With a four decade presence in SMS, the Protestant Pentecostal religion rejects the religious and
cultural heritage of ancestral Mayan spirituality6. The Pentecostal Churches reject animist beliefs
and with shamanist practices, which they perceive as witchcraft. Conversations with Pentecostals
interviewed intensely stressed millenarian beliefs that God will destroy the terrestrial world and that
Christ will return to establish a new world. According to the Pentecostals, Tropical Storm Stan was
a precursory sign of the arrival of Christ.
However, respondents of the Mayan ancestral religion believe that the forces living in their natural
environment have always acted through natural disasters. According to the Mayan animist conception,
a harmonious communication can be established between humans, natural spirits, and the Creator
Ajaw through a shaman intermediary. Tropical Storm Stan, compelled natural forces to alert humans
of their lack of respect towards “Mother Earth”, and therefore ref lected an imbalance between
humans, their environment, the spirits living in it, and God. According to respondents of the Mayan
ancestral religion, the inhabitants of SMS were not taking sufficient care of the land, both from an
economic practice viewpoint and a spiritual viewpoint. In exchange for what they extract from the
ground to feed themselves, the ancestral conception of the sacred earth encourages man to naturally
fertilize the land, both because it is an economic resource, but also because it is in need of spiritual
nourishment by ceremony and prayer. Today, however, this reciprocity relationship with the land
is more defined by subsistence utilitarian constraints and by production oriented capitalist logics:
chemical fertilizer substitutes for spiritual nourishment.
Moreover, as a key figure of the community, the shaman intermediary is responsible for restoring the
biological, climatic or even social stability of the community by working directly with God, demons,
ancestors and other invisible beings (Freidel, Schele & Parker, 2001, p. 33). For indigenous people,
clinging to their ancestral Mayan religion, the shamans of SMS, forgetful of their work with the
mountain spirits to maintain good relations, were thus held responsible for the imbalance revealed
by Stan’s passing. Residents believed that the mountains lacked spiritual support and therefore did
not avert landslides on their slopes. Certain inhabitants also mentioned other unbalancing factors
contributing to Stan’s devastation, including a lack of communication with the young, thus pointing to
the failure of the shaman’s failures in community; the inhabitants’ lost ability to hear the mountains’
alarm signals; and the desecration of Mayan altars by extremist Pentecostal groups.
According to A. Oliver-Smith (1996), anthropologists writing in the field of risk conceptualize risk in
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its socio-cultural context far differently from traditional risk approaches related to the probability
of a “real” risk, determined scientifically and objectively (p. 319). A major contribution in this field
is that of M. Douglas and A. Wildavsky, in their work Risk and Culture (1982). They begin with the
86 assumption that various characteristics connected to social life produce judgments about what is
to be considered “dangerous”. Relation to risk depends on culturally rooted conceptions of time and
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
is socially differentiated (Douglas & Wildavsky, 1984, p. 87). Indeed, beyond the differentiation of
disaster representations according to religious belonging, the results of my ethnographic research
showed that the whole community of SMS, without religious distinction, has a conception of time
impregnated by Mayan cosmology. The inhabitants of the Altiplano Mam share a common 52 year
cyclic and prophetic representation of natural disasters. Time, therefore, takes on the form of
repetitive cycles, allowing the forecasting of certain events, including natural disasters. I observed,
for example, SMS inhabitants rebuilding their houses on the ruins of their old dwellings in zones of high
risks to landslides. Conscious of the incurred risks, inhabitants justified this “risky” reconstruction by
their understanding that in their human lifespan they will only know one 52 year cycle. Thus adults
will experience no further cycle disasters such as the one embodied in Tropical Storm Stan in 2005.
Beyond the cultural perception of time, the social perception of time also inf luences risk perceptions.
The deprived and dire situations of the inhabitants of the Altiplano shorten their temporal horizon,
instilling in them a sense of precariousness which anchors them in the present and deprives them of the
capacity of projecting into the future. That precariousness forces inhabitants to concentrate, above
all, on daily survival and not on the durability of their housing or of their land. During previous decades,
the lack of cultivable land and population growth pushed local farmers to advance the agricultural
borders at the expense of forests. Many peasants now cultivate cheap land at the edge of riverbeds
and mountainsides. Therefore, the economical vulnerability accentuates, and even sometimes causes,
their environmental vulnerability to threats from extreme natural phenomena.
Causal explanations of disasters have a practical role, suggesting or failing to suggest preventive
actions, questioning the ethical and political problem of a community’s fatalistic attitude. Indeed,
the disaster’s cyclic representation and, for others, an apocalyptic perception adds to this precarious
population’s perception of the brevity of life, and anchors the inhabitants of SMS in a kind of fatalism
with regard to natural disasters. For S. M. Hoffman (2002), psychologically, a cyclic symbolism offers
a particular comfort to the victims, because what happens can be considered planned. In addition,
politically, cyclic symbolism leaves the populations particularly vulnerable. For individuals living in risk
zones, they believe their destiny determines all and therefore preventive acts are rendered useless.
The religious and cultural representations of disasters together with socioeconomically precarious
living conditions accentuate the degree of vulnerability of the inhabitants of SMS to natural disasters.
The cultural argument justifying the rapid rebuilding on ground having just suffered from landslides or
f loods coincides with the material and economic impossibility of buying other lands for rebuilding their
dwellings. If it is said that the cultural practices and representations are irrational, it should also be
said that regional and national economic policies are unjust and inequitable. Their lack of support for
these precarious populations increases the vulnerability of the populations to disasters.
Relationships of Religious Belonging and Environmental Practices
Human communities are simultaneously the product of their natural environment and their conceptions
of “nature”, as the natural environment is inf luenced by human activities and their conceptions of
nature (Descola, 2005; Casteñeda Salguero, 1991). This mutual construction provides a theoretical
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basis for affirming that natural disasters are also social.
Tropical Storm Stan caused landslides and f loods in SMS because the sandy soil was eroded from
87
massive deforestation of the surrounding mountains and saturated by the excessive use of chemical
fertilizers and dwellings built on ill-suited sites. This land deterioration ref lects a modification in
ecological cultural traditions. Ancestral Mayan culture promotes a relation of reciprocity and harmony
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
with the environment, particularly with the mountains. My respondents, mainly the shamans, affirm
the importance of this respect and the conservation of their natural environment. Attached to Mayan
spirituality, the shamans assert their ancestral ethnic identity anchored in the past and in the local
environment. The mountains and the volcanoes, places of ceremony inhabited by the ancestors’
spirits and natural forces, are perceived as the roots of their cultural identity. During discussions with
shamans of SMS, they called for increased efforts to safeguard their natural environment, not only
for its economic resources, but also for its spiritual and cultural inheritances. The shamans believe
in the immanence7 of divine being in creation. The Pentecostals of the area reject animist relations
with living entities, such as mountains, animals, the vegetable kingdom and they saw little sense and
interest in the fight for safeguarding the mountains as a cultural inheritance. Furthermore, the majority
of them operate on a millenarian reading of natural disasters; the end of the world is imminent. Rather
than fighting for the conservation of the terrestrial world, their efforts are concentrated on their own
salvation and proselytism campaigns aimed at reaching the celestial and eternal world.
However, several elements complicate these assumptions about the differentiated environmental
management and the religious belonging of the inhabitants. First, in spite of the prevalence of
ecological respect for the natural environment among the shaman’s discourses, I noted that this
talk was not restricted to the followers of the Mayan religion. Ecological consciousness, ranging
from an ancestral mythical consciousness to more modern concerns, is shared to varying degrees
by all inhabitants of SMS. Secondly, the sacred character of the land as the heritage of a millenary
civilization, as presented in shaman interviews, is idealized and doesn’t ref lect daily practices. The
exploitation of farmlands and forests remains, in practice, incompatible with the conservation of
the natural resources in the long term. Whereas Mayan spirituality gives attention to the harmony
between human communities and others non-human living entities, their actual daily practices are
mainly unsustainable. Like all SMS inhabitants, they are caught up in a capitalist process which
promotes high-yield production practices in the farmlands and forests and disregards the ecosystem.
Belying the conversations in the interviews, observation of the actual practices of the inhabitants
of SMS relativizes the link between individuals of the Mayan religion and their ecological practices
and the unsustainable practices of the inhabitants of SMS are first subject to economic, political and
social realities and pressures.
Historical and Structural Construction of Economic and Environmental Vulnerabilities
My research demonstrates that the catastrophic consequences of an extreme natural phenomenon
like Tropical Storm Stan are also the product of the relationship between a human society and their
environment. Therefore, beyond the social construction of a disaster, it is necessary to analyze the
historical and structural construction of economic vulnerability which exacerbates the environmental
conditions.
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From pre-Columbian times until today, land has been the fundamental factor in the formation of wealth,
power, and conf lict in Guatemala. Due to the expansion of coffee growing and the Reform of 1871,
the populations of the Altiplano Occidental experienced the effects of private property expansion to
the detriment of the ancestral collective uses and properties (Palma Murga, 1997 and 2002). Those
88 expansions allocated low-lying, high output land to the rich and high-lying, low output land mainly to
small property owners (Guzmán-Böckler, 1997; Grünberg, 2003; Melville T. & M. Melville, 1982).
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
These transformations benefited the productive sector and deeply modified the agrarian landscape.
The laws promulgated deprived the villages of their territorial inheritances and because the agricultural
lands left to rural populations were not sufficient for survival, the peasants became dependent on
work in the coffee plantations. Moreover, according to G. Palma Murga (1997), “These measures put
an end, in many cases, to the spare spaces that permitted the rotation of crops, extraction of wood,
fruit, fishing, hunting etc.” (p. 31).
These economic and social historical inequalities involved practices which today accentuate the
vulnerability of the population to the threats of extreme natural phenomena. The unjust distribution
of the land shares in terms of size and quality contributed to deforestation and an overuse of
nonagricultural land. In addition to the retreat of the forest border, the small farmers of the Altiplano
could only practice intensive agricultural production on inadequate land by excessive use and
dependency on artificial fertilizers.
Land reform having never occurred, these land use patterns have, to date, not been modified. The
Guatemalan population continues, “to cramp with the land as a single option for survival” (Palma
Murga, 1997, p. 19). Moreover, the 36 year civil war which ended in 1996, stimulated by the most
conservative groups of the dominant classes, caused not only the death, exile and forced migration of
thousands of Guatemalans, but, also an anxiety about owning one’s own land and potentially falling
victim to violence.
Illegal economic migrations to the U.S. seemed an alternative to chronic poverty8. For C. Guzmán-
Böckler (1997), Guatemala has become a country exporting peasants without land. The financial
repercussions of these exoduses are considerable for the economic development of the country9 and
these migratory phenomena in turn modify the landscape of the municipality. Returning migrants,
with new economic capacity, are now able to buy land and to build their own dwellings. However,
an unprecedented rise in land prices and the decreasing availability of buildable land pushed migrants
to build on unsafe, cheaper land, in unstable lowlands or riverbeds. Thus, the construction and
rebuilding of houses after Tropical Storm Stan was subject to the consequences of this inf lation
and to the increased the vulnerability of owners and communities by situating their new homes on
the cheapest lands. Migrations create new socio-economic inequalities between the inhabitants. In
this configuration, those not having the financial resources to leave Guatemala for the U.S. become
even poorer and more vulnerable to the disasters. Moreover, the urban landscape of the municipality
has changed due to the increasing number of multi-story houses, symbols of the economic success
of returning migrants. Nevertheless, this type of multi-story architecture endangers the community
because it is often not built to seismic safety regulations, which advise low level house construction.
In Guatemala, the impact of Tropical Storm Stan was felt by the marginalized population which is
mainly indigenous. As J.P. Van Ypersele underscored (2006):
The poor often have no other choice than installing themselves on small
holdings without value in zones prone to natural disasters, such as riverbanks,
unstable hillsides of deforested zones or fragile f lood prone zones. These are
the conditions which predetermine not only the vulnerability of those most
exposed to natural disasters, but also their capacity to face the consequences
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(p. 12).
The poverty, in which the populations of Guatemala live and which contributes to patterns of
89
deforestation, construction of inadequate dwellings, and the occupation of high risks zones are
the product of many years of exclusionary economic models. It is also the product of dominant
ideologies.
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In order to explore how socially produced vulnerabilities manifest themselves in the natural
environment, A. Oliver-Smith (2002) suggests establishing links between the increase and expansion
of catastrophes and the ideas, institutions, and dominant practices of our contemporary world
(p. 27). In SMS, short-term profitability, land overuse, and individual, high-yield output practices
created unprecedented levels of environmental destruction. In short, the characteristics of capitalist
economies provoke the amplification of human vulnerability to disasters and ecosystem destruction.
For the poor, natural resources constitute above all their economic survival. The municipalities of the
Altiplano Mam, formerly protectors of their traditionally collectively lands, are today diverted from the
management of those lands and the inexistence of municipal policies of land management contributes
to the destruction of ecosystems. The inexistence of government policies in support of an integral rural
development with land reform generates continued impoverishment of the population10. In Guatemala,
policies to reduce disaster risk in the long run would essentially have to regulate land reform. This
reform could help attend to the injustices of populations relegated to the least fertile land.
CONCLUSION: The Inequality and Responsibility of Human Communities in Facing Disasters
The ethnographic investigation of a given geographical and ethnic place helps us to understand a
community’s vulnerabilities. The representations one has of the world and the conception of natural
threats result from religious, cultural, economic, and social systems. In my research, I observed
that the representations of the cyclic patterns of disasters and the fatalistic attitude towards
those disasters confined the inhabitants of SMS to an inevitable reproduction of the vulnerabilities.
Furthermore, despite the ecological and cultural traditions of the Mayans, the current farming and
forestry activities observed in SMS are principally based on a short-term land use models with little
ecological respect of the natural environment. This situation of environmental blight, produced by
socially and historically induced unsustainable practices, perpetuates environmental vulnerability to
extreme natural phenomena.
But an analysis must go beyond diagnosing strictly human responsibilities for a disaster to reveal the
mechanisms of inequality at play in the construction of vulnerability to socio-natural disasters. At the
origin of unsustainable environmental practices lie historical and structural contexts, generators of
deep social and economic inequalities. Historical, economic exclusion from the fertile national land
areas produced, for instance, an overexploitation of farmlands and forests. These practices have led
to the continuous reproduction of a social system exploitative of the environment and of poor people.
Social relations, inscribed in the environment, ref lect the contradictions that are inherent in the social
system and in the relationship between people and their environment.
For A. Oliver-Smith (2002), “Disasters are perhaps the most graphic expression of those contradictions”
(p. 36). An idea of sustainable communitarian development, defined by V. M. Toledo (2001) as, “the
process of endogenous character in which a community takes (or recovers) the control of the processes
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that determine it and affect it” (p. 1) reveals that contemporary society exploits the land because it
has lost control both over nature and over itself. Thus, risk is not given but built (M. Douglas and A.
Wildawsky, 1982) and risk reveals the uneven character of our societies. As P. Peretti-Watel (2000)
90 says, “To speak about ‘undergone risk’ does not make sense, unless it includes an argument aimed at
denouncing the inequality of chances, the asymmetry of the individual situations” (p. 19).
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
If the inhabitants of SMS are “responsible” for the ecosystem degradation generating environmental
vulnerability, we must also recognize that there is no real liberty in their practices in dealing with the
land. This then reveals the governmental irresponsibility in just and equitable land reform and requires
that inequalities to the risks of disaster must first be opposed by a struggle for more equality in land
distribution. Support for a revalorization of ancestral Mayan ecological practices with the land can
only be made effective by a more equitable land distribution.
Whereas practices with regard to risk management continue to be eminently reactionary and
conservative (Gellert, 2003), such problems also question the responsibility of the experts in disasters.
Most often, disaster management models are preconceived and uniform. They do not take local
ideologies and vulnerabilities into consideration in their understanding of how risk evolved inequitably.
Unfortunately, serious socio-cultural data concerning comprehension of local contexts are seldom
required. This continues to remain a challenge for anthropologists concerned about injustices in
vulnerability distribution and therefore more grounded work is needed to understand how preventative
assistance can be approached in such situations where disaster risk is socially and historically
produced and unequally and unjustly perpetuated.
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AUTHOR’S BIOGRAPHY
Currently completing Ph.D. at the Belgian Scientific Research Funds, Julie Hermesse is a member of
the Laboratory for Prospective Anthropology of the Université Catholique de Louvain, a board member
of the Belgian Society of American studies, and a member of the Sociological Studies Center of Saint-
Louis University.
[ENDNOTES]
1. Twenty-four linguistic groups cohabitate in the national territory, of whom twenty-one are Mayan including the Mams.
The ethnic and lingustic area Mam covers the Quetzaltenango, Huehuetenango and San Marcos Counties. The area of
study, San Martín Sacatepéquez, is one of the twenty-four municipalities of Quetzaltenango, located in the Southern
Mam speaking region of Guatemala.
2. Stan made landfall in Mexico as a Category One hurricane on the Saffir-Simpson scale. Such a hurricane rating is
characterized by its slow movement and a great amount of rain produced over a short time. Stan was nothing but a
tropical storm as it moved across Guatemala between October 3 and 6, 2005.
3. Guatemala suffered from a civil war of 36 years qualified, according to adequate legal terms, as genocide. The peace
accords of 1996 having officially put an end to those decades of violence, do not prove to be reliable in terms of land
reforms and the fight against impunity.
4. The geography of Guatemala predisposes it to a threat level. This country is indeed located at the junction of three
tectonic plates with many faults, bathed between the Pacific Oceans and the Atlantic and endowed with a diversified
morphology made up of high mountains, volcanoes, alluvial and coastal plains.
5. According to the Center for Research on the Epidemiology of Disasters (CRED) based at the Catholic University of
Louvain, 455,314 Guatemalans were affected by the tropical depression. Retrieved June 23, 2008, from http://www.
em-dat-net/disasters/Visualisation/profiles/countryprofile.php.
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6. In the last few decades, the whole religious landscape of the Guatemalan society has been radically transformed.
Churches and sects, mainly Protestant, have known an extraordinary expansion. This change in the religious field is
a phenomenon which is found on a global scale in the Latin-American and the Caribbean societies (Garcia Ruiz, 1997).
In about thirty years, Protestantism in its essentially Pentecostal current was established in SMS. Its growth is such
92 that today approximately 50-60% of the 5,000 inhabitants of the semi-urbanized municipality center would have been
converted to one of the dozen Pentecostal churches.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
7. D. Freidel, L. Schele and J. Parker (2001) again taking into account the remarks of a follower of the Warao shamanism
of Venezuela, underline two ways of considering the divine: one as a transcendent Creator coming from the outside, or as
an immanent Creation potentially manifested everywhere. They estimate that this last pattern formed part of the basic
premises of shamanism and that it consolidates the direction of belonging in the world and the cosmos (Freidel, Schele
&. Parker, 2001, p. 12).
8. No official statistics on migrations exist in SMS. However, local officials estimate that between 12 to 20% of the
inhabitants, mainly young men, may have emigrated to the United States.
9. According to M. A. Bastenier, in 2005, the financial transactions sent by the emigrants (46% of the Guatemalan
population have a family member in the United States) constituted the primary source of national income (3 billion dollars,
so three times more than the exports generated by the 300,000 micro-companies in the country) (Courrier International,
23 to March 29, 2006, p.28).
10. According to the last census available from the National Statistics Institute of Guatemala (INE), the index of Gini on
land distribution inequality hardly moved between 1979 and 2003, going from 0.848 with a light modification of 0.834.
These data make Guatemala one of the most unequal countries in the world. Recalling that a perfect equality in land
distribution would correspond to 0 and one perfect inequality would be equal to 1.
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Oliver-Smith, A. (2002). Theorizing disasters. Nature, power and culture. In S. Hoffman & A. Oliver-Smith (Eds.),
Catastrophe & culture: the anthropology of disaster (pp. 23-47). Santa Fe: School of American Research Press / Oxford:
James Currey.
Palma Murga, G. (1997). La problemática agraria en Guatemala. Algunos apuntes para la comprensión de los procesos de
apropiación de la tierra entre los pueblos Mames de Quetzaltenango. In R. Hosting (Ed.), Esta tierra es nuestra. Área Mam
de Quetzaltenango. Tomo 1 (11-34). Quetzaltenango: Centro de Capacitación e investigación Campesina.
Palma Murga, G., Taracena Arriola, A., & Alwin Oyarzum, J. (2002). Procesos agrarios desde el siglo XVI a los Acuerdos
de Paz. Guatemala: FLACSO, MINUGUA, CONTIERRA.
Peretti-Watel, P. (2000). Sociologie du risque. Paris: Armand Colin.
Pédron-Colombani, S. (1998). Le pentecôtisme au Guatemala. Conversion et identité. Paris: CNRS.
Prado, P. (1990). Paysage après la tempête. Les retombées d’une catastrophe naturelle : ordre et désordre dans le
culturel. Etudes rurales, 118-119, 31-43.
HERMESSE
PNUD Guatemala, (2005). Informe nacional de desarrollo humano. Diversidad étnico-cultural: La ciudadanía en un estado
plural. Guatemala: EDISUR.
Smith, D. A. (1991). Coming of age: a ref lection on Pentecostals, politics and popular religion in Guatemala. The Journal
94 of the Society for Pentecostal Studies, 13(2), 131-139.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Toledo, V. M. (1992). What is ethnoecology ? Origins, scope and implications of a rising discipline. Etnoecológica, 1(1),
5-21. Retrieved November 16, 2007, from http://www.etnoecologica.org.mx/Etnoecologica_vol1_n1/articulos.htm
Toledo, V. M. (2001). Principios etnoecologicos para el desarollo sustenable de comunidades campesinas e indigenas.
Red Latino Americana y Caribeña de Ecología social. Retrieved November 30, 2007, from http://www.ambiental.net/
biblioteca/ToledoEtnoecologia.htm
Van Ypersele, J.-P., (2006). L’injustice fondamentale des changements climatiques. Alternatives Sud, 13(2), 7-20.
Yamin, F., Rahman, A., & Huq, S. (2006). Vulnérabilité, adaptation et catastrophes climatiques Alternatives Sud, 13(2),
113-138.
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JUSTICE,
EQUITY, +
SUSTAINABILITY
96 SPEAKER AND FILM SERIES, SPRING 2008
DEPARTMENT OF URBAN STUDIES + PLANNING, MIT
PROJECTIONS SPEAKER + FILM SERIES, SPRING 2008
During the Spring of 2008, the Projections editorial team invited speakers and hosted film screenings
focused on the theme of Volume 8: Justice, Equity, and Sustainability. The presentations and films
provided the focus for students and faculty at the Department of Urban Studies and Planning to
deepen their discussions surrounding the intersection of these ideas and engage each other on these
themes and their own work and research. Two of our speakers, Professor Marcel Bursztyn and
Professor Susan H. Holcombe, have graciously agreed to write and analytical summary of their talks
for this volume. We are excited to include “From Social Protection to Environmental Protection” and
“Capabilities and Human Rights Approaches: Competing Paradigms or Re-enforcing Models” as part
of the discussion on Justice, Equity, and Sustainability.
J U S T I C E, E Q U IT Y, A N D S U S T A I N A B I L I T Y
Tuesday, February 12
FILM SERIES
SPRING 2008
“Governance and Local (Sustainable) Development in Brazil:
Between Specific Realities and General Responses”
Professor Marcel Bursztyn, University of Brasilia
Co-sponsored by Projections and EPP
Location: Stella Room, 7-338, 12:30 pm
Tuesday, February 19
“The Social Requirements of Sustainability”
Professor Phillip Thompson, MIT
Co-sponsored by Projections and HCED
Location: Stella Room, 7-338, 12.30 pm
Wednesday, February 27
Enemies of Happiness
AND
Film by Eva Mulvad
World Cinema Jury Prize for Best Documentary at the Sundance Film Festival, 2007
Sponsored by Projections
Location: 9-554, 6:00 pm
SPEAKER
Tuesday, March 4
“Rights, Capabilities, and Sustainable Development”
Professor Susan Holcombe, Brandeis University 97
Sponsored by Projections
Location: Stella Room, 7-338, 12.30 pm
Tuesday, March 11
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“Winged Networks: Bird Migration and Science Between Europe and Africa”
Professor Nancy Jacobs, Brown University
Co-sponsored by Projections and EPP
Location: Stella Room, 7-338, 12:30 pm
Wednesday, March 12
Choropampa, The Price of Gold
Film by Ernest Cabellos and Stephanie Boyd
Audience Prize at the Barcelona Human Rights Film Festival, 2003
Discussant: Professor Saleem Ali, University of Vermont
Sponsored by Projections
Location: 9-554, 6:00 pm
Wednesday, April 2
Tsotsi
Film by Gavin Hood
Academy Award for Best Foreign Language Film, 2006
Discussant: Zoe Wilson, University of University of KwaZulu-Natal, Durban
Sponsored by Projections
Location: 9-554, 6:00 pm
Tuesday, April 8
“Participation, Deliberation, and Sustainability”
Professor Gianpaolo Baiocchi, Brown University
Sponsored by Projections
Location: Stella Room, 7-338, 12:30 pm
Tuesday, April 15
“Creating Spaces of (Im)Possibility in Planning”
Professor John Forester, Cornell University
Co-sponsored by Projections and EPP
Location: Stella Room, 7-338, 12:30 pm
Professor Marcel Bursztyn
FROM A PRESENTATION GIVEN ON MARCH 12, 2008 AT DUSP, MIT
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FROM SOCIAL PROTECTION TO
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ENVIRONMENTAL PROTECTION
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Social policies, such as we know nowadays, are almost as old as the modern state itself. For example,
in the 17th century, the British established laws for the protection of the poor (the poor laws). While
these instruments have evolved since then, their aims did have not changed substantially and until the
late 19th century they focused on basic issues of work, housing, orphanages, and food access (i.e. the
corn laws). In different moments throughout history, these policies and political doctrines have given
more or less importance to the protection of the poor. People living in dire conditions were seen from
two different perspectives: as victims and therefore deserving of charity or as threats and therefore
deserving of condemnation or control.
Until the 1970s, public policies regarding the poor were characterized by protection by the State.
Early in the Industrial Revolution, the poor, the less favored class, were always lacking in assistance.
However, since the 1870s, though, the situation started to change, on account of structural reforms
adopted in some European countries and in Japan. This opened a period of history that is remarkable
for the progressive improvement in general living conditions, particularly in the currently developed
countries.
A series of important initiatives was undertaken in these countries, especially as a consequence of
politically related issues. These early socially oriented public policies deeply changed the social profile
of several societies located in the Northern hemisphere and had important political consequences, since
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the years that preceded them were marked by revolutionary disturbances (the 1871 Paris Commune,
for example). Higher classes feared that the working classes would adhere to revolutionary ideals
and in this context, even conservative elites gradually agreed that the State should conduct social
protection policies. Paternalism, inherent to the old patriarchal regime typical of feudalism, was no
99
longer enough, and the adoption of public mechanisms aimed at the well-being of less favored classes
became the new agenda.
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Therefore, the population, especially the poorest, ideally would have some degree of certainty about
their existence and the existence of their children, and would be supported by some form of security
provided by the government. This happened in many different dimensions. The first was education,
which became a universal right. In the dimension of labor, employees in the job market began to
have some degree of certainty about job security, unemployment benefits, rights to paid vacations,
retirement, and of some type of insurance in case of work-related accidents. None of this existed
before 1870.
This was the context 130 years ago, marking the beginning of a phase that ended in the 1970s,
in a context marked by an especially traumatic episode: the first oil shock (Rosanvallon, 1981;
Esping-Andersen, 1999; Pierson, 1991). The first oil shock opened an era of retreat by the States
in terms of policies focused on social well-being. This retreat has been gradual, but in some cases
radical, reaching a peak in the Northern hemisphere during the 1980s and in the Southern hemisphere
during the 1990s. In developing countries, there was an actual dismantling of governmental public
structures, in such a manner that the existing social protections became weaker and weaker and, in
some cases, nonexistent. The liberal principle that regulation should be conducted by market forces
prevailed as the basis for this retreat (D’Intignano, 1993). Of course, this process occured in quite
different contexts, according to the characteristics of each country.
In spite of the predictions made by some authors that social differences would be reduced during
the 20th century (Hobsbawm, 1994), the fact is, after one hundred years of social protection, the
differences between the less included and the well-to-do in each society only increased and the
differences between different societies are colossal.
Without doubt, when we refer to the construction of the Welfare State, we need to consider differences
among the many groups of nations in the world. Therefore, what we call first world is a group of
nations that were able to build an important social protection system during these one hundred years,
with varying degrees of consistency. Some countries built a system more focused on regulations that
forced companies to organize some sort of protection for their employees. Other countries, notably the
ones that adopted social-democracy, made this kind of responsibility an attribute of the State.
The second world – comprised by the former socialist countries – is today practically an empty group.
The number of countries that remained in this category is very low. In them, social protection made
great advances, but the legitimacy of the economic and political regime did not.
The third world is an interesting group because it comprises a wide range of situations. For example,
Brazil, Mexico, Argentina and Chile implemented many traditional instruments of social protection.
Brazil arguably adopted all the typical instruments of the Welfare State, although with varying degrees
of coverage: social security, universal public education, labor legislation, unemployment insurance,
etc. There are, however, third world countries in which none of these instruments were adopted and
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others in which some of them were adopted with very little effectiveness.
Between 1870 and 1970 the construction of public regulation instruments focused on the reduction of
100 social inequality and on social protection, not only in developed counties, but also in many developing
ones. Beginning in the 1970s, there has been an inversion of what is called protection. People and
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society are no longer the main focus. Protection is now aimed at the general context – namely,
markets and resources used in production - in which society is inserted. In the context of a more
integrated and globalized world, the rules concerning the relations between people and processes
seem to be more important than people themselves.
The resources that have become the object of protection, as defined by economists, are the resources
necessary for production: land, capital and labor. Capital includes technology and financial resources
and the land comprises all natural features. Capital is protected by a complex network of rules and
mechanisms that are deeply rooted in national legislations since the times of the Industrial Revolution.
With the emergence of neo-liberalism in the 1970s, labor, protected since the late 19th century, was
relegated to a lesser status as an object of protection. The major innovation is that the land, taken
as a representation of natural environment, acquired importance exactly when labor protection was
reduced.
The protection of nature, concern with the environment, and concern with the quality of life are
remarkable traits of the end of the 20th century. In the context of environmental concern, the major
objects are water, sources of raw materials, climate, and energy. It is important to remember that
the energy crisis of the 1970s – the first oil shock – was at the center of the process that defined
this transformation.
In reference to the protection of capital, during this period a series of multilateral organisms and
institutions have been consolidated, such as the World Trade Organization, the International Monetary
Fund and other international mechanisms and conventions, including legislation about intellectual
property, which protects knowledge. This knowledge is not the result of social-cultural historical
processes (which have only use value), but knowledge directly or indirectly associated to market
relations (which have trade value).
In the case of labor, this period has been a time of retreat for protection instruments. Labor laws
suffered reversals and there was a decline in the modes of organization and of generating pressure by
the working classes, traditionally centered around unions. Job security deteriorated, as did the direct
correlation between economic growth and employment. In contrast with the preceding decades, when
the rhythm of economy also dictated the rhythm of job creation, the last years have shown that it is
quite possible for economic growth to happen as employment levels fall.
The net result of the period that begins with the energy crisis of the 1970s – with strong effects on
public policies in general – is a change of focus in the State’s regulatory actions. On the one hand,
the protection of capital is maintained; but, on the other hand, the protection of work decreases and
concern with the environment grows.
Therefore, a major question to be considered in the context of globalized environmental governance
is: How can we expect success in environmental protection without previously or simultaneously
assuring social protection? This question can be extended to the behavior of individuals: How can we
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expect that they develop visions and expectations about the future when they are not sure about the
present?
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102
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AUTHOR’S BIOGRAPHY
Dr. Marcel Bursztyn is the Giorgio Ruffolo Senior Research Fellow at the Kennedy School of Government,
Center for International Development, Sustainability Science Program, at Harvard University. He is
also a Professor at the Center for Sustainable Development at the Universidade de Brasília, Brazil.
His work includes evaluation of public policies, environmental management, science and technology
policy, the state and planning, agriculture and development, economics and regional development,
urban and regional planning. He received his doctorates in social and economic development from the
Université de Paris I (Sorbonne) and in economics from the Université de Picardie.
ACKNOWLEDGMENTS
The author would like to thank to Capes-Brazil and Fulbright Foundation.
REFERENCES
D’ Intignano, B. M. (1993). La Protection Sociale, Paris: De Fallois.
Esping-Andersen, Gøsta. (1999). Les 3 mondes de l’État-providence, essai sur le capitalisme moderne. Paris: PUF, 1999.
Hobsbawm, Eric J. (1995). The Age of Extremes: The Short Twentieth Century, 1914-1991. London, UK: Michael
Joseph.
Pierson, C. (1991). Beyond the Welfare State? Pennsylvania, PE: The Pennsylvania State University Press.
Rosanvallon, Pierre. (1981). La crise de l’État-providence, Paris: Editions du Seuil.
BURSZTYN
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Professor Susan H. Holcombe
FROM A PRESENTATION GIVEN ON MARCH 4, 2008 AT DUSP, MIT
CAPABILITIES AND HUMAN RIGHTS
APPROACHES : COMPETING
HOLCOMBE
PARADIGMS OR
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RE-ENFORCING MODELS
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Human rights and human development/capabilities approaches have emerged as contending alternatives
to the neoliberal model for development. Neither of them has yet replaced economics and the
Washington Consensus1 as the guiding model for development. On separate but similar tracks, rights-
based and capabilities approaches demand that ‘development’ be guided by values of human rights and
expanding human choice, and that they contribute to achieving those valued outcomes. Though their
origins lie outside the profession of development, rights and capabilities approaches have profound
appeal to development practitioners concerned about the poverty, exclusion, and deepening inequality
that economic models of development have yet failed to address. Donor agencies, from governments
to international NGOs, claim to have rights-based approaches. Most express commitment to achieving
the Millennium Development Goals. They have been less successful in articulating what human rights
and human development/capabilities approaches mean in practice (Uvin).
This essay explores the rights and capabilities approaches, asking in what ways they are similar
and different and whether they are approaches that can and should be explicitly integrated in policy
and practical models that will shape a new paradigm of how development occurs. Rights-based
approaches, emphasizing the role of the state as duty-bearer, can be top down. Capability approaches,
emphasizing individual capabilities and agency, have the potential to be bottom up, particularly when
agency is exercised collectively. The essay suggests that integrating rights and capability approaches
is effectively done by recognizing that development is a highly political process, and that change
HOLCOMBE
efforts need to identify the power of key stakeholders and support the emergence of new institutions
that allow the currently excluded poor to access opportunities. Development is a process that needs
to go beyond top down state obligations for protecting or providing rights (from fear of torture and
to food, water, education). The process needs to incorporate the bottom up capabilities or freedoms
105
that allow individuals and groups to access and expand the opportunities they value. Development
needs explicitly to contribute to the ability of states to assure rights, and to the ability of individuals
and groups to demand rights and capabilities.
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Power is an uncomfortable (and invisible) concept for most development practitioners; yet development
takes place within the state, which, by definition, has coercive power used at best to assure minimum
functions of security, law and order. Global development actors, from the World Bank to international
NGOs work directly through government or with government approval. Local development actors
operate within the state and are subject to state power, benign or malevolent. States, charged as the
duty-bearers for guarantee of human rights and committed by international agreement to achieving
the MDGs, more often than not, do not deliver on human rights or on the functionings promised in the
MDGs. This failure may be due to lack of capacity, or to corruption and venality. The questions thus
become: how can and how should, rights and capabilities approaches challenge the ineffective or the
unwilling state?
Emergence of human rights approaches2
Human rights standards emerged and were codified as international law following the experiences of
World War II. States ratified a series of international agreements that charged them with the legal
obligation of protecting the rights of all citizens and assuring a life of freedom and dignity. Human
rights are sometimes divided into civil and political rights versus economic, social and cultural rights.
The role of the state is paramount as the duty-bearer:
• to honor human rights obligations (e.g. not to torture, deny the vote or
interfere with freedom of thought or religion);
• to protect citizens from rights violations (e.g. to assure that citizens are not
trafficked or that children obliged to work); and
• to provide access to human rights (e.g. to provide the rights to water, education
or food — particularly if these are not being supplied by the market).
In this way, rights can be seen as a top-down process, with the state as the duty-bearer. Because
rights are a legal obligation of the state, they should be able to be adjudicated, but the state holds
the obligation to act.
Human rights have other characteristics. They are individual, not community rights. They are
the same for all people (universal), and no one right can be said to be more important that another
(indivisibility) and we cannot suspend one right in order to achieve another. We have rights because
we are human (inalienability). Rights represent universally agreed upon standards or human values.
There is less clarity in the human rights literature about how rights are achieved in the absence of
state fulfillment of its obligations.
Peter Uvin has made the argument (2004) that this extraordinary development of rights standards
remained largely divorced from the development enterprise —until very recently. Human rights
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specialists thought development was about economics and service delivery and did not make
connections between the conditions of human well-being and achievement of rights. Development
professionals had nothing against human rights. If they were informed about human rights, they saw
106 them as a legal and political issue and not their responsibility. Since the late 1990s, a large number
of development agencies has adopted a rights based approach to development planning and funding
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over the past 10 to15 years. It remains unclear what a rights-based approach to development means
in practice.
One often cited definition of the rights-based approach comes from the UN High Commissioner for
Human Rights focuses on rights as a conceptual framework —a vision of what development should
produce. While it talks about operations, the focus is on promoting and protecting:
A rights-based approach to development is a conceptual framework for the
process of human development that is normatively based on international rights
standards and operationally directed to promoting and protecting human rights.
(UNHCHR)
The UNHCHR definition goes on to cite principles of equality, equity, accountability, empowerment
and participation that should guide rights based approaches, and says that any development approach
should be explicit about the link to rights and pay particular attention to vulnerable groups and others
that may be marginalized by discrimination.
Because human rights are tied to the obligations of the state as the duty-bearer, a human rights
approach may be difficult in contexts where the state is unwilling to uphold its obligations. Norway,
with its rights-based approach, chooses to work with countries and institutions that “share the
same values” and promote “democratic institutions, good governance, rule of law and fundamental
freedoms”. (Skarstein) The Norwegian position illustrates the links between democratic governance
and rights, and acknowledges the need for empowerment, but it says little about how this works
when the state is not ready.
International NGOs3 have increasingly committed themselves to rights based approaches. Oxfam
International, for example, began work in the late 1990s on defining a rights focus for a strategic
plan for its progam, education and policy advocacy work. It selected five rights: to a livelihood; to
basic services; to security in the family, the community and the nation from violence, armed conf lict
and natural disasters; to a voice and to participation; and to identity and protection from exclusion
because of gender, ethnicity, disability. Many in Oxfam who worked on the rights based approach
were inf luenced by the work of Amartya Sen (see below). Individually and together, the Oxfams
worked to understand what difference a rights based approach would mean for their work. As the
discussion below will suggest, the Oxfams moved beyond the concept of a rights based approach as
being about the obligations of the state. They also looked at the capabilities of people, as individuals
and groups, to inf luence the state and other centers of power in order to claim their rights.
Human Development and Capabilities Approach
Human Development and Capabilities Approaches have been termed a ‘paradign shift’ and as “…
the leading alternative to standard economic frameworks for thinking about poverty, inequality and
human development” (Clark, 2; see also Kuonqi, Shahyd). Indeed, former World Bank economist
Mahbub-ul-Huq was one of the leading forces behind the Humand Development Reports, launched in
1990, and the Human Development Index as an alternative to GDP for measuring development. UNDP
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continues to pursue human development/capabilities approaches, but at the same time as it also
focuses on a rights based approach.
Intellectually, the human development and capabilities approaches are grounded on the work particularly
107
of Amartya Sen and others, particularly Martha Nussbaum. For Amartya Sen, development should
be seen as a kind of freedom, or the capabilities “to lead the kind of life she or he has reason to
value” (87). Development is about expanding substantive human freedoms or capabilities to do the
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kinds of things, or functionings, that one values. Functionings are broad and indeterminate. They
may range from being adequately nourished, to being respected. Capabilities represent the ability of
the individual to achieve certain functionings and the freedom to choose whether to exercise those
functionings. Sen often gives the example of having the capability of adequate nutrition and choosing
to fast. Such a person has the same functioning as a starving person, but a vastly different set of
capabilities. (75) This distinction is important because it asks the development practitioner to think
about individual choice.
Capabilities have substantive value and are legitimate goals. Sen also argues that capabilities are
at the same time instruments. They can be used in order to achieve or expand other functionings
and capabilities. He lists five instrumental capabilities or freedoms: political, economic, social,
transparency guarantees and protective security (18, 36-40). The instrumental function of a capability
implies agency, or the ability of individuals, and groups, to act to expand their own range of choices,
and not simply to rely on the state to guarantee rights. This, too, is an important distinction. It says
that individuals are not just objects of state or duty bearer actions, but agents who are actors, who
participate, and whop are agents of change. Individuals and groups have agency and can use their
capabilities to demand, from the bottom up.
Sen goes further, arguing that development is an expansion of people’s capabilities that enables
participation in decision-making. Thus development is not just about achieving outcomes one values,
but about the freedom to participate in the process of decision-making about choices being made.
(Sen, 291) This has implications for development interventions.
Peter Evans (and others) extend Sen’s arguments about participation in the processes of decision-
making (“thick” democracy) by noting the importance of collective action and the role of “mobilizing”
organizations, such as labor unions, political parties or other entities that use the power of groups
to make voices heard. The implication of this for development is important. Not only does it imply
that participation in policy making is important for human development, but that participation may be
enabled through collective action. Development interventions, thus, may extend to work with groups
and to group capacity building to enable the capabilities for participation.
Capabilities, Rights and the MDGs
As noted above, Mahbub-ul-Haq, a major force behind the UNDP Human Development Reports, wanted
an alternative to economic models that focused on growth and used GDP (gross domestic product)
as a measure of changes in development. The Human Development Index (HDI), a composite of
consumption, literacy and life expectancy, was launched by the first Human Development Report as
the competitor to GDP. UNDP continued to refine the HDI in successive HDRs, and to add additional
indicators (gender) both to track change and to motivate governments and others to seek improvements
in the well-being of those who have traditionally been excluded or at the bottom. Recognition of the
power of indicators and goals contributed to the emergence of a global commitment of governments
to the Millennium Development Goals. Heads of State agreed in 2000 to reduce poverty by one half
by 2015, and to meet other very specific goals related to human well-being. These MDGs ref lect
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specific capabilities and mirror human rights established in international agreements. Where rights
set broad standards, the MDGs provide operational benchmarks. The MDGs also set priorities among
rights—naming goals we should achieve by 2015. Because the goals are measureable and timebound,
108 they provide a mechanism by which governments can be held accountable. The MDGs seem to be a
practical way to make progress on rights and human development.4
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The MDGs depend largely on governments for their achievement. As approved by governments, they
are indeed a set of measures that can be used to pressure governments to act, but they lack an
analysis of the institutions and practices that may constrain achievement of the goals and they lack
an analysis of power differences among the different actors. The MDGs
• Make no direct reference to rights
• Ignore inequalities (except for gender);
• Ref lect global power inequalities: the Summit agreements focus on changes
in developing countries in seven goals and set less specific obligations for
developed countries in goal eight;
• Focus accountability for results on developing country governments and at
the state level.
• Represent quick fixes; they measure achievement of outcomes but don’t
challenge underlying causes or constraints on sustainability.
The MDGs have potential to produce remarkable reductions improvements in human well-being that
meet basic human rights standards and that contribute to building substantive and instrumental
capabilities. It is less clear that the MDGs will produce the individual and collective capabilities for
participation in the political process of decision-making and the capacity for sustainability.
Incorporating Capabilities into a Rights –based Approach: Oxfam America and Care USA
Oxfam America5 and Care USA separately adopted a rights-based approach as they sought to move
from “a development model based on filling poor people’s needs to one in which people are able to
claim what is rightfully theirs…” (Care Oxfam America 2007: 4). Care and Oxfam undertook an RBA
Learning Project6, starting in 2002, in order to identify what distinguished rights-based approaches
from what they called ‘traditional’ development interventions and to explore what difference a rights-
based approach made for project impact. From the start, the language of Care and Oxfam incorporated
both the rights emphasis on the state as the duty bearer and capabilities of rights-holders as agents
or actors who can claim rights. Care and Oxfam recognize individuals as agents, with the right and
potential to be actors at the local and at the policy levels. They use a definition from Jochnick and
Garzon:
The rights-based approach requires that people be regarded as active agents….
the rights-based approach takes empowerment a step further in aiming for not
only the ability to sustain oneself but the additional capacity to inf luence public
policies and make claims in defense of one’s rights. (Care and Oxfam America
2007: 20)
Thus a major output of the Learning Project,— eight essential elements of rights-based projects,—
ref lects the integration of support to both rights holders and the duty bearer (the state). The eight
elements confront power distribution as an underlying cause of poverty. The elements, listed below,
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emphasize the importance of working at all levels: from the bottom up and the top down:
Oxfam-Care: ’Essential’ Elements of RBA Projects
1. Poverty analysis; including explicit and ongoing analyses of power, gender and risk
109
2. Community centered development; including building sustainable capacity to claim
rights and drive decision-making
3. ‘Duty-bearers’ engaged, held accountable
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4. Advocacy for sustainable change in policy and practice
5. Alliance building
6. Working at multiple levels
7. Focus on groups that are marginalized, excluded
8. Problems framed as rights issues and linked to national or international standards.
(Ibid. 20)
These eight elements suggest that Care and Oxfam America take on power disparities in many ways.
Taken as a whole, the eight elements contribute to individual and collective capabilities to participate
in the political process of policy making or decision-making. It is noteworthy that the elements begin
with a call for an analysis of the poverty situation, including its power dimensions. Who are the
relevant stakeholders; what their interests and relative power; and how do they exercise power.
Power distributions are not static, but can be changed. Change starts with awareness, for example
of structural constraints to gaining land titles or lack of access to information about prices or markets
that bar the freedom or capability of individuals and groups to propose and demand change in policies
and practice that limit attainment of rights (and capabilities).
The Care/Oxfam elements are politically sophisticated in approaches to addressing structural issues
and rights violations. They call for (shifting) alliances at different levels and for engagement with
government in addressing problems or rights violations. The elements avoid a traditional ‘naming and
shaming’ of governments that fail to meet human rights standards. Instead, the Care/Oxfam approach
suggests working toward making governments a partner in and owner of the solution.
The learning emerging from the Care and Oxfam America project incorporates both individuals and
groups as rights holders and states as duty bearers. What is distinctive about the Care/Oxfam
framework is the significance it gives to collective civil society actors, particularly NGOs. Civil society
actors have potential freedom to confront the power inequities and structural constraints that cause
and sustain poverty and injustice. States themselves, and inter-governmental agencies like the UN,
which are creatures of states, lack this freedom. Civil society, if representing the interests of the
rights holders is an important collective counter-balance to the power of state actors as duty bearers.
How it does this will be inf luenced by the context.
CONCLUSION
Rights and capabilities approaches have not yet replaced economic paradigms as the theory driving
development choices. Together they have the potential to re-shape our thinking about the nature
of sustainable development in the 21st century. Rights and capabilities approaches are linked but
different. They share clarity about human values and about the outcomes of development being greater
than economic changes. One key difference resides in the emphasis placed on the responsibility of
the state as duty bearer (RBA), and the potential of individuals and collectives to be actors (CA) in
achieving rights and capabilities.
HOLCOMBE
Implementing a capabilities approach, where building capabilities is seen not just as an end, but also as
a means for achieving rights and greater capabilities, has profound implications for the ways in which
development actors operate. This brief essay suggests a few changes. Development actors need to
110 include a power analysis in their assessments of poverty and exclusion. And then to contribute to
building the capabilities of individuals and groups, who are excluded, to organize and participate in
PROJECTIONS SPEAKER + FILM SERIES, SPRING 2008
decision-making on development choices. Development actors need to build partnerships, including
with governments and the business sector, to expand ownership of rights and capabilities. Donors
may need to recognize the difference between achieving service delivery goals, like school enrolment
or mortality reductions, and building capabilities of excluded groups to participate. We need to know
how to measure this expansion of capabilities. Development workers, from managers to field workers,
need to give up control over the outcomes and play the role of facilitating the capacities to make the
changes needed to allow all actors in a society to participate in delivering rights and capabilities.
HOLCOMBE
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AUTHOR’S BIOGRAPHY
Professor Susan Holcombe’s teaching and publications builds on a career of practice and a focus on
building capabilities for human development. She is a Professor of the Practice at The Heller School
for Social Policy and Management at Brandeis University.
[ENDNOTES]
1. For discussion of the Washington consensus, see: John Williamson. 2000. “What should the World Bank think about
the Washington Consensus?” in The World Bank Research Observer. Vol. 15, no. 2 (August 2000), pp. pp. 251-64. http://
www.worldbank.org/research/journals/wbro/obsaug00/pdf/(6)Williamson.pdf. Accessed 8-2-06.
John Williamson. 1990. “What Washington Means by Policy Reform”. In Latin American adjustment: How much has
happened? http://www.iie.com/publications/papers/paper.cfm?ResearchID=86. Accessed on 8-2-06.
Dani Rodrik. 2002. “After Neoliberalism, What?” In After neoliberalism: economic policies that work for the poor (pp.
9-20). Collection of Papers Presented at a Conference on Alternatives to Neoliberalism. Washington, DC: The New Rules
for Global Finance Coalition, 2002.
2. The evolution of human rights standards in the post World War II period is described in detail in many locations. Peter
Uvin (2004) has a useful discussion on rights and development; see specifically pp. 9-43.
3. See, for example, the work of INTRAC on European NGOs and rights based approaches.
4. See “Human Rights and the Millenium Development Goals: Making the Link. 2006. http://www.hurilink.org/Primer-
HR-MDGs.pdf.
5. The author was director of programs at Oxfam America in the late 1990s when Oxfam began adopting the rights
based approach.
HOLCOMBE
6. The RBA Learning Project first developed eight case studies of Care and Oxfam Projects that had used a rights based
approach. Using this evidence base, it assembled a workshop of Care and Oxfam Program staff from 12 countries to
analyze the cases. They went on to identify, from a practitioner perspective, the ‘essential’ elements of a rights based
approach.
112
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REFERENCES
Care – Oxfam America. 2007. Rights-based Approaches Learning Project. Boston: Oxfam America.
David A. Clark. (2005). “The Capability Approach: Its Development, Critiques and Recent Advances” Manchester:
Global Poverty Research Group. GPRG=WPS-032. http://www.gprg.org/pubs/workingpapers/pdfs/gprg-wps-032.pdf.
Accessed June 5, 2008.
Sakiko Fukuda-Parr. (2003). “The Human Development Paradigm: Operationalizing Sen’s Ideas on Capabilities”. in
Feminist Economics 9(2-3) 301-317.
Sarah Harris-Curtis. 2003. “The Implications of Adopting Rights-Based Approaches for Northern NGOs: A Preliminary
Explanation”. Oxford: INTRAC.
Christopher Kuonqui. (2006). “Is Human Development a New Paradigm for Development? Capabilities Approach,
Neoliberalism and Pradigm Shifts”. Paper presented at the August 2006 international conference Freedom and Justice,
Human Development and Capabilities Association, Groningen, the Netherlands.
Paul Nelson, Human Rights, the Millennium Development Goals and the Future of Development Cooperation. World
Development, Vol. 35, No. 12.
Raymond C. Offenheiser and Susan H. Holcombe. 2003. “Challenges and Opportunities in Implementing a Rights-Based
Approach to Development: An Oxfam America Perspective”. Nonprofit and Voluntary Sector Quaterly. Vol 32, No. 2.
268-301.
Amartya Sen. 1999. Development as Freedom. New York: Alfred A. Knopf.
Tove Skarstein. “Norwegian Development Cooperation and Human Rights.” http://www.norvegia.bg/culture/
roundtableone.htm. Accessed June 5, 2008
UK Interagency Group of Rights-based Approaches. 2006. Analysis Workshop Report: Does implementing a rights-based
approach increase impact on poverty reduction? http://www.crin.org/docs/iap_workshop.pdf. Accessed May 28,
2008.
United Nations Development Program. (1990, 2000) Human Development Reports. New York: Oxford University Press.
______. 2006. “Human Rights and the Millennium Development Goals: Making the Link.” http://www.huri.Primer-HR-
MDGs.pdf. Accessed May 28, 2008.
United Nations High Commissioner for Human Rights. “Rights-based Approaches.” http://www.unhchr.ch/development/
approaches-04.html. Accessed June 5, 2008.
Peter Uvin. 2004. Human Rights and Development. Bloomfield CT: Kumarian Press.
HOLCOMBE
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Colette Fluet
Professor Naomi T. Krogman
BARRIERS TO CHANGING ALBERTA’S
OIL AND GAS TENURE SYSTEM :
LESSONS FROM AN OIL-DEPENDENT
STATE
FLUET, KROGMAN
115
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ABSTRACT
This paper explores shortcomings of the oil and gas industry tenure to address the common values of
integrated resource management, and barriers to changing this system as indicated in 33 key informant
interviews in Alberta, Canada. The results indicate that key actors responsible for integrated resource
management in Alberta have differential inf luence on land use. In essence, the oil and gas industry not
only has privileged access to land, and privileged accounts of reasonable mitigation actions, but also
tolerance of a broader public that has generally viewed oil and gas expansion as fixed and essential to
economic growth. Barriers to changing the system include the provinces’ preference for immediate
economic benefits through resource extractive activities; the reluctance of critical groups to pursue
legislative reform; industry’s aversion to legislation; and the difficulty of altering a complex tenure
system. The authors conclude that potential reforms to the oil and gas tenure system fail to address
cumulative impacts and public land management values that include ecological objectives. Core
issues of social justice, supported by an increasing public understanding of land as a place of social
history and future habitation, are likely to expose the nature of the oil and gas allocation system, the
privileges it confers, and the facilitative role the tenure system plays in short term decision-making
that precludes integrated resource management. We conclude that the myth that Albertans can
have multiple industrial and social activities on the land base, and continued economic growth, with
few limits placed on oil and gas development will likely be challenged by core issues of social justice,
equity and sustainability.
INTRODUCTION
Integrated resource management, as defined in the Alberta context, generally involves the coordination
of two or more industries operating on the same land base, with the goal of reducing the over all impact
of industrial activity and incorporating a range of ecological, social and economic values (Mitchell,
1986; Alberta Environment, 1999). Ecological values, such as maintaining ecosystem functions
and healthy habitat for wildlife; economic values, such as maintaining residential property values and
future options for other economic activities, such as farming or tourism; and social values, such as
protecting justice and equity in the allocation and development of land into industrial land uses, are
hotly debated in the Alberta context. Justice and equity issues are discussed in this paper by examining
the mechanisms through which access to resources are gained and access privileges are sustained.
We argue that social scientists should pay closer attention to the structure of property rights and
tenure systems, particularly for petroleum resources, to understand how access to resources is gained
and maintained and how this perpetuates privileges for a few at the expense of the broader public.
Thus, this paper identifies the shortcomings of the oil and gas industry tenure system in Alberta at
addressing common values of interest in integrated resource management. Our broader framework
recognizes that the natural resource policy process should “clarify and secure the common interest”
FLUET, KROGMAN
(Clark, 2002, p.15) and it is the social processes, i.e., interaction among individuals, groups and
institutions, and decision-making processes, that effect and ref lect how values are shaped and shared
in society. We describe the barriers to integrated resource management in the province of Alberta as
articulated by thirty-three respondents in key informant interviews. Our guiding research question is:
What are the opportunities and barriers to a provincial-led effort at integrated resource management?
116 While there are legal scholars (Kennet, 1999 and 2002; Ross, 2002) who have done considerable
work on Alberta’s policy shortcomings for public land management, and other social scientists who
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
have critiqued the state’s role in the overall pace and nature of resource development in Alberta
(Urquhart and Pratt, 1994; Urquhart, 1998; Epp and Whitson, 2001; Davidson and MacKendrick,
2004) there is a dearth of scholarship that incorporates the views of agents of social change, the very
people involved with integrated resource management, to describe the existing impediments to reduce
the industrial footprint on the land, particularly in terms of the oil and gas tenure system. These
agents of social change are in critical positions to send signals back to their organizations, to respond
to such impediments within their positions of authority, and to make integrated resource management
a decision-making processes that contributes to sustainability.
This paper exposes the ways in which the tenure system, the social organization of ownership or
legal access to a particular resource, hinders the possibility for integrated resource management, yet
remains “off limits” as a focus for change. Ribot and Peluso (2003) argue that justice and equity in
any resource tenure system must be addressed by examining the mechanisms through which access
to resources is gained and access privileges are sustained. Such mechanisms permit differential
ability for some resource users to gain, maintain, and limit other resource users’ access to particular
resources. The role of oil and gas development in larger land management efforts, in general, has
received scant attention from social scientists, apart from the important exceptions that focus on
off-shore, or coastal oil and gas impacts (Freudenburg and Gramling, 1994b; Gramling, 1996, Picou,
Gill and Cohen, 1997). We contend that the Provincial government’s preference for economic growth
over the distant ecological costs deters changes to the oil and gas tenure and regulatory system.
Additionally, we argue that respondents in our study tended to refer to landscapes as commodity
zones first, above other uses, and thus accept mitigation and “best [industrial] practices”, in lieu
of any fundamental changes to slow oil and gas development. In fact, we argue that justice and
equity around the allocation of oil and gas leases and the environmental impacts that follow have
been overlooked given the powerful storylines in Alberta about “oil as king.” This paper contributes
to scholarship that exposes equity issues in one of the most destructive, but most lucrative and
economically critical, activities in the world.
Background
Access to and management of resources is an ideal focus to examine equity and justice, particularly
when such resources are publicly owned. Such is the case in Alberta where the majority of land in
the province is “Crown land” or held in public trust. Subsurface rights in Alberta are also held by the
Crown, allocated to mineral-based companies through a leasing and royalty payment system. The
goal of integrated resource management recognizes that many people share a land base, and the land
base itself holds within it layers of public and private rights to access. Walther (1987) addressed
difficulties for integrated resource management in the boreal forest nearly 20 years ago by focusing
on the importance of regional planning bodies who had the authority to limit resource allocations and
new development activities, but he did not discuss the details of oil and gas tenure systems as a key
part of those difficulties.
FLUET, KROGMAN
The province of Alberta is the wealthiest province in Canada, with the highest per capita income, one
of the lowest unemployment rates, and the lowest business and personal tax rates of all Canadian
provinces (Government of Canada, 2002; Statistics Canada, 2003; Frontier Centre for Public Policy,
2003). Since the 1940s, the economic strength of Alberta has been largely attributed to the successful
extraction, production, and sale of oil, gas, and, more recently, oil sands resources (Government of
117
Alberta, 2005). While the agriculture and forestry industries make significant contributions to the
provincial economy and employment, the economic dominance of the province is due to its wealth
under the surface, in the form of conventional oil, gas, and oil sands deposits. For example, whereas
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
the Alberta government collected $72 million in timber dues and fees from the forestry industry in
2001 (Ministry of Sustainable Resource Development, 2002a), the government collected $10.6 billion
from energy royalties and fees in the same year (Alberta Finance, 2001). Conventional oil and gas
resource harvests are expected to continue near current levels for the next 30 years, and the mining
of oil sands bitumen is expected to go on well into the next century (Schneider, Stelfox, Boutin, and
Wasel, 2003).
The province of Alberta owns 81% of the province’s mineral rights (Alberta Energy, 2002a), a system
that differs from the United States where mineral rights are generally held by private landowners or
the federal government. The provincial government manages these rights on behalf of Albertans.1 Oil
and gas companies wanting to drill an oil or natural gas well must obtain both surface and subsurface
rights from the Government of Alberta. The subsurface rights are granted by the Department of
Energy in the form of either a license (for two to five years) or a lease (for five years). Companies are
required to prove that the resource is productive within the time frame of their tenure agreement or
they will lose the rights to that resource (Alberta Energy, 2002b).
To obtain subsurface rights, companies will submit a request to the Crown (i.e., provincial) Mineral
Disposition Review Committee that mineral rights to a certain parcel of land be offered for sale.
During the eight weeks of notice prior to the sale, companies interested in the subsurface rights of
that parcel may conduct seismic exploration (or purchase seismic information from other companies)
to prepare a competitive bid for the sale, which requires no public review. Once a company has
purchased subsurface mineral rights, they must then obtain the corresponding surface rights, from
the Sustainable Resource Development Department, in order to access the resource. It is at this
stage of the permit process the province requires the company to address the ways in which land
disturbance will be mitigated and reclaimed after the extraction is complete. It generally takes the
Sustainable Resource Development Department 13 days to review an application for the development
of a proposed well site, road or pipeline (Graham, 2001). If the land in question is part of a Forest
Management Agreement area, an area-based disposition allocating the right to harvest timber, written
consent must be obtained from the forestry company, though a Right of Entry may be obtained if the
occupant declines to give consent (MacKendrick et al., 2001). Once subsurface and surface rights
have been acquired, a company must then obtain drilling licenses from the Alberta Energy and Utilities
Board (EUB), a quasi-judicial agency that operates independent of the Government of Alberta, and
requires applicants to identify sensitive areas, document efforts to notify landowners, occupants, and
other sectors of the public, and address any outstanding concerns (MacKendrick et al., 2001).
Government revenue from the oil and gas industry is composed of the bids made by companies to
purchase the mineral rights plus the royalty payments that are made over the production life of a
well (Alberta Energy, 2003). The rate of royalties collected for both conventional oil, as opposed to
FLUET, KROGMAN
heavy oil from the tar sands, and natural gas are sensitive to current market prices, the quality of the
product being extracted, and the productivity of the lease. The royalty system also consists of various
“royalty holidays” to encourage certain types of oil and gas developments (Alberta Energy, 2003).
118 Cumulative Effects of Industrial Development
Alberta is currently realizing the cumulative environmental and social impacts of the development of
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
its oil and natural gas reserves over the last half century. Along with other industrial impacts on the
land surface, the exploration, drilling, and infrastructure development of the oil and gas industries
have had significant impacts in the boreal forest of northern Alberta. Much of the northern half of
Alberta is Crown land, leased out to forestry companies for timber harvest. Timber harvest levels are
20.5 million cubic meters annually - nearly double the harvest levels of thirteen years ago (Ministry
of Sustainable Resource Development, 2002b), an increase largely due to new technologies that
have allowed for commercial harvesting of additional species. Forestry industry clearings along
with approximately 200,000 well-sites (Alberta Energy and Utilities Board, 2002) and hundreds of
thousands of kilometers of linear disturbances in the form of seismic lines, access roads, and pipelines
have greatly changed the face of Alberta’s boreal forest in the last few decades, with unknown
consequences for many of the species that live there and for northern communities (MacCrimmon
& Marr-Laing, 2000; Natural Resources Services, 1998; Schneider, 2001). Some predict that the
cumulative industrial footprint, in terms of density of linear disturbance and total area disturbed,
could quadruple over the next 20 to 30 years (Timoney & Lee, 2001). How to best manage the
cumulative social and environmental effects of all resource users in the boreal forest is currently the
focus of many government, industry, and environmental organization initiatives, and is the focus of
the interviews we held with members of these same groups.
Methods
The findings of this paper were generated from interviews with thirty-three respondents from the oil
and gas and forestry industries, various government departments, and environmental organizations
in Alberta in the Summer of 2001. More specifically, interviews were conducted with six forestry
industry representatives, ten oil and gas industry representatives, twelve government representatives
from various departments, and five representatives from environmental organizations active in the
province. The interviews were part of a qualitative study in which respondents were asked, through a
series of more detailed questions, “What are the opportunities and constraints for integrated resource
management in Alberta’s boreal forest?” “How does your organization address ecological, social and
economic values in your resource management plans and activities?”22
Findings
Above all, our key informants highlighted several problems with the oil and gas tenure system that
result in negative impacts on the land base and conf licts between different resource users in a
region. In particular, the short term planning horizon, the small size of the leased parcels, the lack of
coordination with forestry, and the absence of tenure reform within recognized solutions for better
integrated resource management exposes the inf lexibility of a tenure system that maintains privileges
for the oil and gas sector.
PROBLEMS WITH THE TENURE SYSTEM
FLUET, KROGMAN
Short-Term Planning Horizon
One characteristic of the oil and gas industry tenure system noted by the majority of respondents
as a major impediment to integrated resource planning was the industries’ short-term land-based
planning horizon. As one forestry respondent said, “The oil industry, they get an approval in about
eight days when they need it bad enough and more often than not, that’s kinda the way they operate.” 119
Land-based planning is done in the short-term by these industries for two reasons, the nature of the
resource and the market-sensitive design of the tenure system.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Oil and gas reserves, being underground, are not visible and require seismic exploration to determine
their location and quantity, making the timing of harvest unpredictable. Exploration for petroleum
and natural gas is done by private companies and it is not until market forces provide the incentive
for companies to locate resources that their whereabouts are known. In this respect, the oil and gas
industries contrast with the forestry industry, which possess knowledge about the volume of their
timber resources, conducts inventories, and thus can make long term plans for resource harvest.
We submit a management plan to the government for this FMA [forest management
area] that has wood sequence for 10 or 15 years, minimum, probably more, and
when we get down to operational planning we submit our plans, typically two years
ahead of time to have them reviewed by government. (Forestry respondent)
In addition to the invisible nature of oil and gas resources leading to short-term land-based planning,
the tenure system of these industries is specifically designed to be responsive to market forces.
[The oil and gas tenure system] is set up by the provincial government…in such
a way that the government can derive as much revenue from the land sales as
possible, which doesn’t really lead…to good planning because it puts pressure on
the industry to get out there and get their information, which usually means doing
seismic, in some cases it may even mean going in and drilling a well….It also puts
pressure on government to get their approvals done…And so it doesn’t really give as
much lead…for planning those activities. (Government respondent)
The sale of mineral rights takes place eight weeks after notice of a sale is given, with sales happening
every two weeks. Within the eight week period between the notice and the sale, several companies
with interest in the area may conduct seismic activities. The company whose bid wins the parcel of
rights may begin activity a few weeks after the sale as surface access approvals are generally granted
in under two weeks (Graham 2001). Thus a company’s planning horizon for a given well-site may be
less than three months.
Being market driven, industry activity can occur at a frenzied pace when oil or gas prices are high,
and at a much slower pace when the profit margin for developments is lower. During times when
prices are high, government departments are under great pressure not to slow down the activities
on the land base with administrative procedures. As one oil industry respondent noted, “A lot of
those applications are dealt with in a routine fashion…it’s a bit of a rubber stamp.” Routine approval
procedures may indeed be the only way that as many as 18,310 wells were drilled in 2003 alone
(Government of Alberta, 2005).
Forestry companies representatives, by contrast, noted their requirements to do long-term forest
management planning and to be responsible for several aspects of land management for the entire
FLUET, KROGMAN
Forest Management Area (FMA, a 20 year, renewable area-based agreement for the establishment,
growth and harvesting of timber), including reforestation and environmental protection (Ross, 1995).
Their long-term planning includes the development of annual operating plans that describe harvesting
methods and proposed developments for the coming year, as well as strategic plans that describe
management objectives and proposed developments for the lifetime of the FMA (MacKendrick et al.,
2001).
120
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
While forestry companies are responsible for managing the forest in their FMA, they do not have
authority over any other users. Their investments in their long-term plans are undermined by
overlapping tenures in the forest. To not account for the activities of other land users in a forest
management plan is “like burying your head in the sand,” to use the words of one forestry industry
respondent. This is especially true in certain areas where oil and gas companies may be clearing an
equivalent amount of trees as the forestry company operating in the area (MacKendrick et al., 2001;
Edmonton Journal, 2002). Unless oil and gas companies make longer-term land based plans and
communicate their intentions with forestry companies, their activities cannot be considered in the
forestry industry’s FMA plans.
Space: Small Size of the Tenure Area
Nearly all respondents from forestry and environmental groups, and several oil and gas representatives
also noted another feature of the tenure system that was problematic for integrated land management:
tenure is allotted for small areas of land on a parcel-by-parcel basis. When companies request the sale
of mineral rights, the area of land can be as small as 256 hectares of land (one section) or as large
as 9,216 hectares (36 sections), depending on the region of the province (Alberta Energy, n.d.). In
practice, most parcels are well below the maximum size (Schneider, 2001) with the average parcel
area being around 500 hectares (less than two sections) (Alberta Energy, 2002c).
Companies who have a development in an area often wish to purchase adjacent subsurface rights to
take advantage of the roads, pipelines and other infrastructure they have developed and to continue
the development of the oil or gas field into which they have tapped. While companies can attempt to
consolidate a larger area of land, there is no guarantee that the mineral rights they requested will not
be bought by another company on the day of the sale, thus generally numerous companies are usually
working in the same area.
We go on almost a section by section basis for mineral rights, so we’re competing
for every section around there with somebody else. And all somebody has to do is
you drill a well, you find something, the neighbor posts the section next to it and
all of sudden you’re in a race for the section next to it, the section next to that, the
section next to that. So it’s the tenure system itself leads to some problems….We
find that once you get to the point where you consolidate a fairly substantial chunk
of land…then…you have control over your road system, you have control over your
infrastructure, pipelines, you can manage access, you can start doing a lot more
things there. (Oil and gas industry respondent)
Respondents argued that while this system of selling mineral rights in small parcels is beneficial from
the perspective that it allows for many companies of all sizes to be involved in the industry, thus
preventing any monopolization of the market by larger companies (Haley and Luckert, 1990), as well
as giving companies greater f lexibility in responding to market forces, it also leads to several problems
FLUET, KROGMAN
with regards to land management. The sheer number of companies that may be working in an area
makes it an onerous task for government and forestry staff to attempt any landscape planning with
involvement of the oil and gas industry. One forestry company in Alberta reports having 200 oil
and gas companies working in their Forest Management Agreement Area (Edmonton Journal, 2002),
thereby prohibiting effective communication for the purposes of integrating planning. To add to this,
these companies change on a frequent basis as take-overs and mergers are common in the industry, 121
and tend to be in one place for a short duration.
Coordination of activities on the land base may also be impeded by poor intra-company integration of
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
activities, as one oil and gas industry respondent suggested.
The normal structure within petroleum and natural gas companies [is that
they] have an exploration or development group and a construction group and
a pipeline group and a processing group. And they are…independent divisions
of each other…. and make decisions based on the best interest of their group
rather than the best interest of the overall group.
Because both approvals and development occur in several phases - exploration, drilling, production,
and reclamation - companies may not have a complete plan for a development when activity begins.
This may result in multiple access corridors to the well-site if, for example, transmission line routes
are not considered at the time of building the access road.
Land Withdrawals for Forestry Tenure Holders
Forestry respondents in particular spoke about significant consequences of oil and gas activities on
the land for the forestry industry. Replete throughout the interviews with forestry personnel are
voiced concerns about the potential of land withdrawals for oil and gas activity to greatly diminish a
company’s forest management area that can result in a reduced annual allowable cut (timber volume
the province allows to be taken from a particular FMA). If their productive land base becomes too
small, the annual allowable cut for the company may be reduced which, in some cases, may lead to
the closing of production facilities.
Forestry respondents in particular noted that the trees cut for seismic lines are often not salvaged by
forestry companies. In many cases, this wood cannot be salvaged simply because coordinating pick-up
on such short notice, with activities often happening far from where the forestry company is operating
at the time, is logistically difficult and expensive. Much of the wood is also damaged and consequently
left to rot where it was placed. Though this is of concern to forestry companies who would prefer
that this wood be brought to their mills to be processed, the bigger concern in the interviews was
the impacts of long term permanent land withdrawals from pipeline and well-site developments that
follow seismic activity, given the slowness of reclamation (replanting and regrowth) processes.
SUGGESTED SOLUTIONS
When asked how the integration of activities in the boreal forest, particularly those of the oil and gas
and forestry industries, could be better achieved, the most common responses among our respondents
was to bring different players together so they can learn more about each other’s operations, and
thus find ways to better coordinate their activities, although none of the environmental organization
respondents suggested this. This is likely because the focus of environmental organization respondents
was largely on policy level issues, as opposed to operational level coordination. Environmental
FLUET, KROGMAN
organizational respondents were strong supporters of the need for public involvement to further
integrated resource management (IRM) and suggested that the starting point for IRM should be to
identify public values and goals for land management.
Two respondents commented on the how collaborative policy processes were undermined by
122 backdoor lobbying on the part of oil and gas industry, to which the environmental respondents did
not feel they had access; three respondents believed that government was neglecting their role as a
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
steward of public lands; and four respondents spoke of a bias in the province towards economic values
that supersedes environmental considerations. These comments were unique to the environmental
organization respondents, illustrating that their perspectives on land management may be different than
those of other respondent groups and suggesting that their perceived inf luence over policy decision-
makers differs as well. For example, one environmental organizational respondent commented after
participating in an integrated land use initiative that did not inf luence any land use decisions,
The answer that we came up with is that we’re not on the same political playing
field, that the power dynamics are not even. So, ultimately, when the real decisions
are to be made - not the ones that were made around the table, where all of us
were…arguing lots but eventually we came to things we all agreed on - but those
were not the real decisions. The real decisions came afterwards, and they were
based on where the true power dynamics lie.
Suggestions to change the tenure system and regulatory regime of the oil and gas industry were not as
common as one might expect given the numerous criticisms of the system articulated by respondents.
Only two forestry respondents, both of whom were involved with integrated resource management
efforts, and one government respondent who was also involved with an IRM initiative, suggested
that reforming the oil and gas tenure system was necessary to significantly reduce industrial impacts
on the land base. When these same respondents were queried further about possibilities to change
the tenure system, their responses were generally fatalistic, suggesting that changing the current
system was not politically possible given the province’s dependence on oil and gas revenues and
employment.
By and large, [Albertans] like the benefits we’re getting from oil and gas; we’re
not going to shut down what’s going on…because of what it’s doing to the
environment. (Forestry respondent)
DISCUSSION
If it is the case that there are characteristics of the oil and gas tenure system in Alberta that lead to
negative impacts on the land base and to conf licts with other resource users, then why was changing
the tenure system not considered a more reasonable solution by our respondents? This portion of the
paper will discuss possible answers to this question.
First, we contend that the Provincial government’s preference for the immediate, tangible economic
benefits over the uncertain, distant ecological costs deters changes to the oil and gas tenure and
regulatory system. The problems discussed in the Findings section of this paper illustrate that the
oil and gas tenure system in Alberta is not designed for land management objectives as much as it
is to encourage oil and gas extraction and development and to make efficient use of the petroleum
and natural gas resources in the province (Alberta Energy, 2002b). Indeed, the oil and gas industry’s
central economic role in the provincial economy, for over 50 years, is the most obvious factor that
FLUET, KROGMAN
insulates the industry and its policy regime from change. In 2003, revenues to the province from
crude oil and natural gas accounted for more than 30% of Alberta’s total revenues (CAPP, 2005) and
employed 95,400 jobs (Government of Alberta, 2005).
With such enormous benefits coming from the oil and gas industry for the province, it is
123
understandable that the general population and government alike would be willing to accept some
amount of environmental degradation in exchange for the economic returns from the industry, and
that widespread delayed recognition of the impacts, and the tenure and regulatory changes such
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
impacts portend, might follow. However, the accelerated nature of oil and gas development in the
past 20 years, with the additional intensity of forestry, has permitted corporate owners to dominate
land use decisions in the boreal forest of Alberta and they have not been beholden to any larger land
use framework or set of thresholds, to stay under specific limits for ecological impacts. Both the oil
and gas tenure system and the forest management lease system has incorporated no (oil and gas)
or limited (forestry) public involvement in the initial set up the of the lease system that allocates
numerous (oil and gas) or large (forestry) tenure privileges.
Another potential explanation why reform of the tenure system is not currently being considered
is that our respondents were somewhat fatalistic about government responsiveness to requested
changes in the tenure systems, arguing that many of planning processes have been symbolic in nature,
followed by no meaningful government action. All of the environmental organization respondents in this
study spoke about their frustrations with past policy processes around forest management planning,
and protected areas in Alberta, where public input was solicited but largely disregarded in the final
outcome of the process. As one member of an environmental organization involved in past public
involvement processes in Alberta said, “After all is said and done, all they’ve done is said” (Timoney
& Lee, 2001, p. 389); which indicates that despite public consultation and debate, implementation of
integrated resource management has not occurred. Environmental groups’ respondents indicated a
lack of trust in government processes to the point that they refuse to take part in further initiatives
until significant changes are made in the processes (Fluet, 2003).
The frustration of these groups was evident in other comments made by the environmental organization
respondents. Indeed, their perception of an uneven political playing field has led them to the conclusion
that lobbying for legislative reform without altering the political playing field through broad public
involvement would be fruitless. Without pressure from the forest sector, regional interest groups,
and environmental groups to change the regulatory regime of the oil and gas industry, provincial oil
and gas tenure policies continue to be accepted as unchangeable in discussions of integrated resource
management.
While environmental groups may not be promoting tenure reform out of frustration, we suspect
industry would like to avoid tenure reform out of fear. Security, with regard to tenure agreements,
is “a function of trust tenure holders have in the socio-political system within which their rights have
been granted” which “depends on their past experiences with the system and the probabilities they
attach to the chance of detrimental changes taking place in the future” (Haley and Luckert, 1990).
Several industry respondents in our research asserted that additional regulations would compromise
the company’s f lexibility to find creative solutions to reducing their industrial footprint, and
coordinating land use with others. These same respondents often cited the recent Forest Practices
Code in British Columbia as overly restrictive legislation, where they claim industry is unable to use
FLUET, KROGMAN
their individual company ingenuity and forest management expertise to use various options to reach
the same desirable outcomes as intended by the Forest Practices Code. These industry respondents
held that they do not want to see similar legislation in Alberta. For this reason, the suggestions from
industry as to how to mitigate the negative impacts of the tenure system were focused on working
within the system, rather than opening the door to uncertainty by considering legislative changes.
124
The anti-regulation argument and support for voluntary measures for improved industrial environmental
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
performance has been cited in several other environmental conf lict cases (Krogman, 1998; Schnaiberg
and Gould, 1994; Freudenburg and Gramling 1994a; 1994b). The exceptions to this generalization
were two respondents from forestry companies who are actively engaging in integrated resource
management efforts. Davidson & MacKendrick (2004) argue that industry’s ability to use language
around “best practices” combined with Alberta government’s use of ambiguous goals such as
sustainable development, cooperation, and communication obscure the issues around regulatory reform
to address cumulative industrial development effects. Our research supports this argument in that
the vast majority of respondents made suggestions about tinkering with the system, and voluntary
efforts, rather than changing the tenure system, the very structure of the resource allocations, to
reduce the industrial footprint on the landscape.
Another barrier to changing the oil and gas industry tenure system is the uncertainty regarding which
changes would rectify the shortcomings of the tenure system with regard to land management
objectives. The current tenure system, involving multiple phases of development of the resource as
well as multiple government departments, is the product of decades of decisions. As Freeman (1992)
suggests, the cumulative outcome was not the result of an explicit decision, rather, the outcome has
resulted from a “tyranny of small decisions”. A multitude of subsequent decisions has created an
organizational hierarchy and elaborate process for oil and gas development – it is difficult for those
invested in the process to entertain options that reverse this long pro-development trajectory.
Charles Lindblom’s (1959) “science of muddling through” suggests that although ideally policy
analysts would go through a comprehensive, rational consideration of all possible policy alternatives
that take into account a large number of values, the reality is that policy analysts are too limited in
time, resources, and ability to undertake such a comprehensive analysis of any policy decision. In
fact, attention to an issue may wane when studies reveal the complexities of the problem, the great
expense to address the problem, and the lack of easy solutions (Cobb & Ross, 1997). Thus, because
the impacts of any large changes in policy cannot be accurately predicted, it is safer to either stay
with known problems or to make incremental changes in policy whose outcome is easier to predict and
potentially reverse, but which may be insufficient to address the root of a problem.
Attempts to reform the oil and gas tenure system in Alberta are additionally hindered by the limitations
of policy making. The volume and complexity of legislation and policy for the oil and gas industry
alone may make it difficult to predict the consequences of any reforms or to find easy and inexpensive
solutions. Add to that the legislation and policy for the other resources and activities on the land base
and the complexity multiplies. The elaborate structure of the oil and gas industry tenure system has
built up over time so that industry and government actors have developed specialized, routinized, and
interdependent pro-production processes that cannot be easily altered.
Finally, social constructionists offer another perspective as to why the oil and gas tenure system is
protected from change in Alberta. Hajer argues that “social constructionism and discourse analysis
add essential insight to our understandings of contemporary environmental politics” (1995, p. 263).
FLUET, KROGMAN
Similarly, Cobb and Ross suggest that attention must be paid to the “political uses of culturally rooted
resources” to understand the outcomes of conf lict (1997, p.4). Both of these works suggest that
in addition to the material basis for the protection of the oil and gas industry, there is an ideological
basis about rightful access to a land base for its development. The repeated “storylines” (Hajer,
1995) of the supremacy of the oil and gas industry in the province serve to sustain the legitimacy of
125
the industry’s regulatory institutions, despite the concerns many Albertans have over the impacts of
the industry in the boreal forest (Nikiforuk, 2001). Comments from respondents in this study indicate
that the oil and gas industry has effectively been placed in a “black box”, that is, the activities of
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
the oil and gas industry have been made to appear as “fixed, natural, or essential”, no longer in need
of consideration (Hajer, 1995, p. 272). Constructionist perspectives on environmental conf lict are
important to consider in the Alberta case in order to understand how certain courses of action, such as
reforming the oil and gas industry tenure system, may be excluded from discussion (Krogman, 1996).
Bridge’s (2001) work on primary resource spaces also supports this perspective, as he argues that a
place’s character and identity may be claimed by invoking the commodity as its defining characteristic.
Bridge suggests that, “A frequent construction of the commodity space…is that of the asocial void,
a depopulated space without socioecological complexity existing outside time and space” (p. 2,154).
Thus, a process of “erasure” takes place, where social and ecological complexities are erased from the
landscape, along with a process of “reimagination”, where the commodity is invoked as the defining
characteristic of the landscape. These processes of erasure and reimagination may be applicable to
the Alberta setting, where the defining characteristic of the province is often portrayed as captured
in the abundance of oil and gas resources, and its cornucopia of spin-off benefits, while the human
populations and ecosystems of the boreal forest are under-emphasized.
The privileged status of oil and gas companies, and the public acquiescence to this privilege, has
generally obscured the justice, equity and sustainability issues embedded in the oil and gas tenure
system. However, we see many frames of injustice that increasingly expose how the allocation
process disproportionately confers disadvantages or risks to rural residents. For example, many
Aboriginal bands have ardently pointed out how oil and gas activities threaten their people’s ability to
continue hunting, fishing, and trapping on their traditional territory, which is linked to their Aboriginal
Treaty rights, identity, and more centrally, their overall well-being (Fluet and Krogman, 2009). As
social justice issues are continually exposed, and the relationship between rights and responsibilities
become more apparent, we suspect the average person in Alberta will challenge the current trends
of oil and gas allocations, and call for a different set of assessment criteria to permit its expansion.
Current public debates around the water shortages (oil and gas development is heavily dependent on
water) and eventual post-oil economy may also prompt Alberta residents to question Alberta’s role in
maintaining its high standard of living to extract a resource in a landscape that will need to be used in
future by many other people, and for other purposes, such as food production. As Clark (2002) points
out, “When conditions and environmental relations change, the supporting myths also change” (p. 23).
We argue that the issues of human respect and dignity, as linked to government responsibilities to
protect human safety and health, will continue to move the oil and gas tenure system into the fore of
public discussion as a necessarily changeable allocation system.
CONCLUSION
The context in which energy policy must be formulated- a context of powerful
FLUET, KROGMAN
vested interests, of great demands upon society’s limited resources, and of
undeniable costs as well as benefits for society – argues that decision-making
with respect to energy policy can no longer be the sole preserve of a small,
technically oriented, and largely non-elected (and non-accountable) group of
individuals; rather it must be broadened for debate and discussion by much
126 larger numbers of people in a process of a political nature.
(Macdonald, 1979, p. 202)
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
This paper addresses the hidden equity and justice issues in the current tenure system for the oil and
gas industry in Alberta in terms of the limited opportunities for multiple values of the land base to be
protected through integrated resource management. In particular, the short term planning horizon,
the small size of the leased parcels, the lack of coordination with forestry, and the absence of tenure
reform within recognized solutions for better integrated resource management involves social and
decision-making processes that maintain privileges of access and control for the oil and gas sector.
While the current tenure system is successful in promoting oil and gas production - the task for which
it was designed - it is failing to address current land management issues that have arisen as a result
of the densely occupied land base where industrial operations frequently overlap, as well as a shift in
public values that now include ecological objectives and increasingly recognized social values of land
as a place of social history and potentiality.
In Alberta, oil and gas resources are a Crown resource, as is most of the land surface from which
it is taken and developed. The surface is now the subject of significant public concern, increasingly
identified with multiple social and ecological values. While more research is needed to further
understand ways in which the short-comings of the current tenure system could be addressed, as the
above quotation suggests, the trade-offs need to be debated by the public at large whose values the
tenure system should be upholding.
While people in Alberta may be well socialized to accept the notion that ‘oil is king’, the environmental
impacts, in particular, of oil and gas development are increasingly exposed through science, social
movements, and media-covered controversies describing contested spaces of confrontation between
the cultural construction of land as a commodity, and land as a place of social history or potentiality.
Tensions among an increasing number of land users and self-appointed land stewards will likely
prompt challenges to the allocation of the leases that originally permitted oil and gas activity in
specific places of contestation. Thus, as Clark (2002) notes, “myths…sometimes become outdated
and maladaptive so that mythic residues from past times may no longer explain and integrate people’s
current experiences meaningfully” (p. 23). In this case, the myth is that Albertans can have multiple
industrial and social activities on the land base, and continued economic growth, with few limits
placed on oil and gas development. We believe the issues of social justice, equity and sustainability
will constitute the key challenges to bust this myth.
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FLUET, KROGMAN
128
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
AUTHORS’ BIOGRAPHIES
Colette Fluet-Howrish completed a Master of Science degree in Rural Sociology at the University
of Alberta in 2003. She has worked as a Research Officer at the Alberta Alcohol and Drug Abuse
Commission, and is currently looking after her two young boys.
Naomi Krogman is an Associate Professor in the Department of Rural Economy at the University
of Alberta. She teaches Environmental Sociology, Natural Resource Sociology, Sociology of
Agriculture, and an interdisciplinary course on key topics, such as Water in Western Canada, and
Integrated Resource Management in Alberta. Her research is in the social perceptions of landscape
change, social impacts of industrial development, and ecological and social resilience across local and
provincial scales.
ACKNOWLEDGMENTS
The authors gratefully acknowledge the Sustainable Forest Management Network for funding for this
research. We would also like to thank Martin Luckert for his review of an earlier draft of this paper.
[ENDNOTES]
1. The tenure system and regulations for the oil and gas industry have evolved into a complex structure since Alberta
was given jurisdiction over Crown mineral rights by the federal government in 1930. The basic structure of the current
system has been in place since 1976, with various amendments having been made as recently as five years ago (Alberta
Energy 2002b).
2. We generated the sample of interviewees starting with a list of frequently identified experts on oil and gas, as indicated
by initial government, industry and academic contacts, and then, using a purposive sampling technique, individuals were
selected by the researchers because of special knowledge they possess with respect to the research topic (Neuman
2000) and referrals by the interview participants themselves for others “who may share a different perspective than
their own.” All individuals were directly involved in land use decision-making, planning, or land policy advocacy. We
felt confident in reaching “key informants” given the repeat suggestions from the interviewees that we interview those
we already included in our sample, as there are a limited number of people in Alberta who work in these key roles.
The majority of the respondents from industry and government were mid-level managers involved in coordinating the
operational aspects of the two industries, where as the environmental organizational respondents were generally key
leaders of those organizations.
We generally made initial contact by phone, then arranged one-on-one, semi-structured interviews with respondents in
an office setting. Interviews generally lasted about an hour; the transcribed interviews were coded and analyzed using
NVivo, a qualitative data analysis software in a set of iterations that began with multiple codes, the later condensed into
FLUET, KROGMAN
key themes most frequently represented in the interviews. The researchers identified major themes in the responses and
made comparisons within and across the environmental organizations, industry and government participants’ responses.
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133
Carrie Beth Lasley
CREATING AN ENVIRONMENTALLY
JUST PARK SYSTEM IN LOUISVILLE,
KENTUCKY
LASLEY
135
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ABSTRACT
Louisville, Kentucky, is undergoing one of the nation’s largest park expansion initiatives. The City
of Parks Plan will add 8,000 acres of parkland to the city by the time it is completed. Principles
of environmental justice suggest that new policy should consider issues of access and balance
with nature as it relates to all people. A sustainable park system brings additional environmental,
economic, social and health benefits to communities near them, helping to stabilize communities and
build sustainable neighborhoods. This study examines park access for minorities in the current Metro
Parks system, evaluates the City of Parks policy as it relates to access and makes recommendations
as to how the municipality might alter the City of Parks initiative to improve park access for its
minority population.
INTRODUCTION
Urban parks serve as community backyards, business catalysts and tools for a healthy population
while adding nature to unnaturally paved environments. A just city should consider equal access
to such municipal benefits as integral to policy (Fainstein, 1999). Parks serve an important social
role in low-income communities. They offer recreational opportunities, serve as meeting places,
and contribute to public health by offering sites for exercise. They have been associated with crime
reduction. They are amenities which contribute to the attractiveness of an area for businesses. Parks
also serve a variety of environmental goals by reducing pollution and absorbing carbon.
Louisville, Ky. is expanding park acreage and promoting healthy living under its City of Parks expansion
policy. This study examines access to parkland by race and evaluates expansion policy to determine
if it improves access or exacerbates inequity. This paper outlines the benefits of parks and addresses
the implications of environmental justice in minority access to public space. Louisville’s park expansion
plan then will be discussed and evaluated through the lens of environmental justice. The final section
will highlight areas of opportunity for the city to improve park equity. Through planning these places
to improve environmental, transportation and social needs, parks can create more stable, sustainable
and environmentally just neighborhoods.
The Benefits of Parks
LASLEY
With health, social, economic and environmental benefits, a park can be an anchor for an active,
connected neighborhood that supports small locally owned businesses. Parks promote health by
136 serving as green oases and outlets for recreation. They help reduce the effects of the urban heat
island, hold stormwater, and serve as community gathering spaces. Together these aspects help
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
create neighborhoods that are more sustainable, that mitigate their environmental problems, and
support their own economies. Resident’s needs for nature, interaction and recreation are met in a
sustainable neighborhood. Well-planned community parks can connect residents to employment sites,
and decrease the number of car trips made by residents. Community parks contribute to sustainable
neighborhoods, where residents can meet their needs without leaving, and where environmental and
social problems can be mitigated within the neighborhood.
Parks are essential to low-income and minority neighborhoods. Bogota, Colombia recently expanded
its parks system with that in mind. As Bogota Mayor Enrique Penalosa said, “At first it may seem
that in Third World cities, with so many unmet needs, parks would be a frivolity. But in practice,
where citizens lack so much in terms of amenities and consumption, it is quicker and more effective
to elevate the quality of life through public goods, such as parks, than by increasing people’s incomes”
(Penalosa, 2003, p.31). A 2006 London study showed that parks were essential for social cohesion
because of their impact on an individual’s sense of belonging and, because they encourage social
interaction (Dines and Cattell, 2006). Sociological studies have demonstrated that parks help create
stable neighborhoods with strong social ties (Gies, 2006). A study that examined minority use patterns
in Chicago’s Lincoln Park in the 1990s determined that minority users were more likely to visit in large
groups (Gobster, 2002). Hispanics tend to visit in large family groups averaging 4 people and prefer
picnicking, while black park visitors tend to come in peer groups averaging 3.7 people and participate
in athletic activities (Forsyth, 2005). Studies have found that minorities tend to visit parks for more
social reasons, so structures such as community centers, bandshells, bleachers near sports grounds,
plazas, game tables and benches and picnic tables of various sizes will see higher traffic in minority
areas (Forsyth, 2005). The Chicago study found that socializing, festivals, and spectator sports were
popular among minorities and that individual sports, such as biking and walking were less popular.
Basketball, soccer, swimming, volleyball and baseball were the most popular sports for minorities.
Fishing was more popular among minorities than whites. Furthermore, the social atmosphere of the
park, with activities and engaging spaces was much more important to minorities than was the natural
beauty of the area.
Parks contribute to public health. Lack of exercise and poor diet have been cited as the second-leading
cause of preventable death in the United States, and it was found that low-income Americans are
more likely to be sedentary and eat poorly (Kuo and Sullivan, 2001). The U.S. Office for Minority
Health claims that while national health improves, American minorities continue to have higher rates
of diabetes, cancer, cardiovascular disease, cancer, infant mortality, low birth rate and have a shorter
life expectancy; these health disparities exist for a number of reasons, including environmental reasons
(CDC, 2008). Black children are 60 percent more likely to suffer from asthma than white children,
but are more than three times as likely to visit the emergency room and 7 times more likely to die
as a result of asthma (CDC, 2007). Minorities are 79 percent more likely to live in areas with heavy
industrial pollution (Pace, 2008).
Minority areas and areas with higher poverty rates are nationally less likely to offer parks and trails
to residents (Gies, 2006). Physical activity is essential to a healthy population. Many Americans are
sedentary, and this lifestyle leads to an increase in obesity, high blood pressure, heart failure, stroke,
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diabetes and depression. Medical studies have shown that access to nearby recreational areas leads
to an increase in frequency of physical activity by about 48 percent (Gies, 2006). Simply, having an
enjoyable and close place to exercise encourages people to take advantage of the resource. Additional
137
studies have demonstrated that access to nature may lower stress levels, decrease healing time
and improve Attention Deficit Disorder. Parks and playgrounds also develop muscles, coordination,
language and reason in children.
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Crime reduction is another benefit of parks. The presence of parks and recreation facilities have
been tied to decreased levels of juvenile delinquency and violent crime in Florida, Texas and Chicago
(Sherer, 2003). Add youth programming to a parks, and further reductions in crime were witnessed
in cities as different as Los Angeles, Forth Worth, Texas, and Cincinnati, Ohio (Witt and Crompton,
1996).
Parks also serve as catalysts to the business community. Parks are mentioned as the most important
element of quality of life in numerous studies (Crompton, 2007). Quality of life is considered the main
draw for small businesses and creative industries when choosing where to relocate or expand. Chicago
Mayor Richard M. Daley understood the importance of quality of life when he invested heavily in the
park system, saying, “Trees, f lowers, parks, attractive open spaces: these things are contagious.
When people experience them, they want more of them. And they are willing to pay for these places,
because they know they are getting something for their money. I believe that cities that pay real
attention to quality of life will be those that thrive” (Daley, 2003, 26).
Crompton (2007) evaluated the proximate principle as it relates to parks and other urban open space.
This principle, that properties near parks are more desirable, and therefore have higher property
values, was popular during early park development around the turn of the 20th Century. The increase
in property values leads to an increase in property tax revenue of about 20 percent (Crompton, 2007).
This increase in property values allows parks to quickly pay for themselves while benefiting the city in
the tax rolls and enhancing the wealth of homeowners near parks for years after the parks break even
(Crompton, 2007). This has occurred in Louisville with prior park development, and can be witnessed
in the Highlands neighborhood and more recently in Butchertown.
Parks also serve a variety of environmental benefits. Green areas serve as carbon sinks to counteract
industry and fossil-fuel consumption from cars. Connected greenways also can encourage alternatives
to vehicle use, and decrease miles driven and fossil fuels burned. Natural areas also counteract urban
heat islands, filter water and control erosion. They absorb stormwater runoff, improving conditions of
urban streets during periods of excessive rain (Sherer, 2003).
Defining access is complicated. No one is shut out of parks; however, there must be some consideration
of willingness to travel. Past studies have concluded that white residents are more willing and able to
travel, and to travel farther to visit parks. Urban white residents are more likely to own a car, giving
them the luxury or ease of travel to parks. In the Lincoln Park study, Hispanic residents were the only
minority to choose mass transit to get to the park. Other minorities simply did not visit a park if it was
too far to access by foot. Residents living further from parks tend to use them less frequently, and
therefore, underserved and minority areas will not experience the same benefits (Gobster, 2002).
A well-tailored neighborhood park adds to the community by producing healthy, active residents.
Parks help reduce the environmental problems associated with urbanization, and stimulate the local
economy creating a natural mix of uses that reduce dependency on gasoline to meet individual needs.
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The result is a sustainable neighborhood anchored by a common community front yard – the local
park.
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PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Parks and Their Role in Improving Environmental Justice
The Principles of Environmental Justice, adopted at The First People of Color Environmental Leadership
Summit, are divided into 17 guiding statements. Two of these principles ask that new policy be
evaluated on the basis of racial equity as it relates to nature. They are:
• 2) Environmental Justice demands that public policy be based on mutual
respect and justice for all peoples, free from discrimination or bias. …
• 12) Environmental Justice affirms the need for urban and rural ecological
policies to clean up and rebuild our cities and rural areas in balance with nature,
honoring the cultural integrity of the communities and providing fair access for
all to the full range of resources. (First National People of Color Environmental
Leadership Summit, 1991, p. 1)
Although many urban park systems in the United States were developed in the early part of the
20th Century, when segregation and overt government racism were common, the expansion of a
park system gives public servants the opportunity to evaluate the justice of its park system and
improve upon past municipal biases. Concepts of mutual respect and justice for all residents may
have been excluded in city park systems in the past, however the second principle of environmental
justice requests that governments uncover bias and previous discrimination and direct current policy
to improve the situation. Comprehensive plan updates offer cities the opportunity to set goals and
objectives to improve access for all residents.
The second principle implies that environmental burdens and benefits be shared among neighborhoods
of all races. By this standard, the areas of cities that have the largest burden due to heavy
concentration of dirty industry and energy production should be entitled to at least a proportionate
share of environmental benefits, and possibly more in compensation for the uneven burden shouldered
by these communities.
The 12th principle calls on public policy to improve access to nature in our most urbanized and most
densely settled areas and to provide a full range of resources. An environmentally just park policy
would add green space to the most urbanized areas of the city to counteract the removal of nature due
to paving. Such a policy would strive to offer a variety of activities to all people in all neighborhoods
and would seek an equitable distribution of nature.
The 12th principle addresses the responsibility of policymakers to clean up and rebuild in balance
with nature. Such policies should direct us to consider the greening of toxic urbanized land as a
primary objective because it decreases burdens to minority and low-income communities while adding
benefits. Not only would this add to the overall greenscape, but it could clean areas that continue
to spread toxins into the air and water. As toxic industries, such as chemical companies and heavy
manufacturing vacates urban areas, this land should be rebuilt both clean the environment and to
incorporate nature. This practice of redeveloping industrial land into parks is not new. Excellent
examples include the conversion of a former gas factory to a culture and recreational park in
western Amsterdam. Westergasfabriek Cultuurpark maintained many of the clean structures in the
large brownfield, converting them into a large showcase area, housing, offices for artists and civic
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groups and restaurants. Polluted areas were cleaned and turned into expansive lawns, recreational
grounds, pathways and waterways. It became a place of interest for residents and visitors. It began
attracting festivals, theater, and fashion shows, even hosting a performance by the local opera troupe
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(Koekebakker, 2003).
In Louisville, the Waterfront Development Corporation acquired former scrap yards along the
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Ohio River just east of downtown to develop the current Louisville Waterfront Park to stimulate
development and improve the waterfront. The 85-acre park is being developed in three phases (Phase
III opens in 2010) as land is acquired and redeveloped. The park has served as a catalyst for events
and development in the east waterfront and adjacent downtown areas. Since the announcement
of the plan to develop the area into a park, almost 5,000 jobs have been created nearby with the
jobs shifting from low-skilled manufacturing sector to high-tech and creative businesses and the
services that cater to them, mirroring a shift in the local economy away from manufacturing. The
Community@emain, a technological workforce-training center, opened two blocks from Waterfront
Park. Current and completed investment along the waterfront tops $1 billion, and the waterfront is
now home to the Muhammad Ali Center, Louisville Slugger Field, and a growing community of high-
end condominiums and lofts near the baseball stadium, where industry and scrap yards were once
typical. However, redevelopment projects such as this do not have to necessarily mean gentrification.
Near Waterfront Park, housing tends to be small, with shotgun housing and small apartments in older
buildings. Neighboring Butchertown and Phoenix Hill, once run-down, have seen increased commercial
development and the emergence of a gallery district (Bartlestein, 2007). This was all done without
significant displacement of existing residents. Newer developments drew new residents, but the older
shotgun-style houses and their residents were relatively undisturbed.
Waterfront Park now serves as home to some of the city’s signature events. It’s the front yard for
Thunder over Louisville, the fireworks kickoff event of the Kentucky Derby Festival, which brings
tourists from around the country. Musicians get Independence Day crowds ready for the city’s annual
July 4th fireworks. Its amphitheater is the main stage for the locally conceived Lebowski Fest, a quirky
music-and-bowling weekend inspired by the movie, The Big Lebowski. Sporting events launch from
the site. Summer concert series bring in the after-work crowd. Cultural events such as the Irish Fest,
Reggae Festival, the activist Forecastle Festival, the Soul Festival and the Bluegrass Music Festival
are just some of the regular attractions to the site. The development of Waterfront Park turned a
scrap-yard waterfront into a bustling front door to the community by turning an environmentally
degrading industrial land use into a mix of open space, commercial and residential space that improves
nearby neighborhoods and brings people to the river. It demonstrates what is possible throughout
Louisville.
City of Parks Initiative
The City of Parks initiative in Louisville is a multimillion-dollar park expansion plan that includes a
Floyds Fork Greenway in the east; an expansion of Jefferson Memorial Forest in the southwest;
an expansion of park lands along the river in the south; the creation of the Portland Wharf Park;
acquisition and development of parkland for the River Road Recreation Corridor along the river east of
downtown to the county line; and a 100-mile paved Metro Loop Trail that more or less encircles the
city along the periphery. Included in the plan are also upgrades to existing parks. This expansion is the
result of the Cornerstone 2020 plan developed in 2000, which called for an increase of 8,800 park
acres to meet the needs of community growth. Funding and cooperation for the plan have come from
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partner agencies, which raise funds or acquire land. Additional funding has come from $38 million in
federal and state grants. Private donations to the Floyds Fork Greenway alone total $20 million. It is,
140 however, a city initiative with significant city money invested (Metro Parks, 2005).
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The City of Parks Plan (Figure 1) highlights some of the expansion efforts. As the city expands its
park system, it should evaluate issues of environmental justice and incorporate needed changes.
Louisville has the opportunity to set an example for other cities by not just expanding its park system,
but by making it a more just park system in a manner that stimulates the economy sustainably by
encouraging small local businesses and improving neighborhoods and by addressing critical issues of
equitable access to parks and open space for all residents.
Louisville Metro Government has created a public-private partnership to raise money for new parklands
and it advertises the economic benefits that it expects to receive. The City of Parks Plan cites the
Trust for Public Land’s Economic Benefits of Parks on its main Web page. This document states the
following benefits: the increase in property value and tax revenues from nearby properties; interest
from businesses and employees who seek a high quality of life; tourism and recreation spending;
reduction in health care costs by residents who live healthier lives; income from working park lands;
the protection of water and land; and f lood mitigation properties gained by open space (Louisville
Metro Government, 2007).
In unveiling the plan, Louisville Metro Mayor Jerry Abramson justified not just the creation of parks
but the use of parks as a unifying social agent and a business catalyst. He said: “Parks draw people
together who might not otherwise encounter one another, bridging the gaps between city and suburb,
between rich and poor, between white and black. Parks raise property values and make our community
more attractive to new residents, businesses and visitors. Parks preserve irreplaceable landscapes.
Parks give our kids a place to play, and they allow each of us to take a break from the daily hustle
and bustle” (Metro Parks, 2005).
Humana, Inc. CEO David Jones donated $5 million to kick the program off and called the parks plan,
“the most exciting and significant civic project of my lifetime.” His son, a developer, and one of
the initiator’s of the project cited the effects that Cherokee Park had on the business and social
community of the nearby Highlands neighborhood, as well as the increase in property values and
vibrancy of local small businesses in the walkable neighborhood anchored by the 400-acre Olmsted
Park (Northern, 2006).
As part of the plan, the Floyds Fork Greenway adds 2,000 acres of parkland in east Louisville, which
is white. Planning is under way on the project as of November 2007. The concept includes a number
of connected parks with a canoe and kayak “water trail” and a mix of recreational and conservation
uses. Included in the Floyds Fork corridor is a sports complex for disabled residents. In all, a large
complex of new parks will span a number of areas, all in the east and south ends, which are white
areas.
More than 600 acres have been acquired from neighbors to Jefferson Memorial Forest in southwest
Louisville, which is white, boosting the forest to more than 6,000 acres under the plan. Riverside, the
Farnsley-Moremen Landing is a historic property located in Southwest Louisville on the river in a white
area. Anchored by the 1830s Riverside estate, the property was acquired by the city in 1999, and
will be doubled to 200 acres under the City of Parks Plan. Riverview Park, has been increased from
16 acres to 87 acres and will add athletic fields and landmarks as well as landscaping to its white
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neighborhood. The River Road Recreational Corridor, created by the plan, runs along River Road. The
corridor will include 34 game fields for sports and other amenities in more than 400 acres of parks.
Included will by a new Cyclocross track and bike lanes that cut through the parks along the river. An
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off-leash dog park is also included. The only new park in Louisville’s diverse West End is a riverfront
park in Portland, a white area. Portland Wharf Park is located on the river northwest of downtown.
It will be a 56-acre passive and historical park connected to the Riverwalk.
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The Metro Loop Trail is a 100-mile path around the city that incorporates parkland and trails. Where
available, the Metro Loop takes advantage of existing parkland (Figure 1). Expansion in minority areas
includes the Ohio River Levee Trail, which will follow the levee easement and existing parks in the
West End of Louisville, a largely minority area. Parks along the Loop will be upgraded. Improvements
to the Olmsted Parkway system will upgrade existing pedestrian and bike paths along Algonquin and
Southwestern Parkways in the West End. However, no new parks are proposed for the area.
Cornerstone 2020 lists goals and objectives for public open space and parks. Among those objectives
are:
• Provide a network of parks of varying sizes and functions equitably distributed
throughout Jefferson County.
• Ensure that people of all interests, age groups and abilities have ready access
to the recreational, cultural and leisure facilities and programs of their choice
(Louisville Metro Government Planning & Design, 2000, 58).
These goals are similar and congruous with the envrionmental justice principles cited earlier, that acts
of public policy should consider the needs of a wide range of residents and that urban areas grow
in balance with nature with fair access to a full range of resources. Since Cornerstone 2020 is the
document that mandated park expansion, it should and does seek environmental justice within its
language. The expansion plans that evolve from it should meet these objectives in practice. The City
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142 FIGURE 1. City of Parks Plan. Source: Louisville/Jefferson County Information Consortium and Louisville Metro Parks
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
of Parks Plan adds parks, bike paths, trails, a recreation corridor, historical offerings and amenities
new to Metro Parks in white areas. In minority areas, bike paths and trail improvements on existing
easements are the only additions.
Findings
In Louisville, some of the most economically and environmentally depressed areas are those in which
the majority of the population is minority. Three zip codes contain only minority-area census block
groups. Figure 2 shows Louisville’s minority neighborhoods have fewer college graduates, earn less
money, have higher rates of poverty and typically have lower housing values than Louisville as a whole.
The exception is the Old Louisville Neighborhood, which has higher property values, but a largely
tenant-occupied. Louisville is also a highly segregated city. Three-quarters of the 2000 census block
groups were 90 percent white or equally non-white; few areas are highly racially mixed. Due to the
high segregation, this study focuses on the more specific Census block groups rather than aggregated
FIGURE 2. Indicators in Minority Zip Codes
Louisville 40211 40202 40210
Bachelor’s Degree 21.3% 8.0% 14.5% 6.6%
Median Household Income $28,843 $21,906 $8,495 $20,722
Percent Below Poverty Line 21.6% 31.8% 59.7% 33.4%
Median Property Value $82,300 $56,300 $120,500 $56,600
Source: U.S. Census 2000
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FIGURE 3. Industrial Land Use by Race and Census Block Group. Source: Louisville/Jefferson County 143
Information Consortium, U.S. Census 2000
zip codes or Census tracts, which would allow for parks in abutting white areas to be classified as
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
minority parks. Louisville is divided into 557 Census block groups. For each of these block groups,
population data about race from the 2000 Census were used to determine percent minority.1
Minority areas also shoulder the majority of industrial development. Figure 3 shows industrial
development and areas with a higher minority population. Nearly a third (32 percent) of the industrial
land use in Louisville is within a minority census block group.
Metro Louisville’s borders coincide with Jefferson County. However, this was not the case until 2003
when city and county governments merged. Some facets of the two governments were combined
much earlier, including the park system. The combined park service, Metro Parks, united county and
city parks in 1968. The 123 parks in the Metro Parks system were considered in this study.2
According to the 2000 Census, Jefferson County had a population of 693,604. Of that, 23 percent
were minority. The largest minority was black at 19 percent, followed by Hispanic (2 percent) and
Asian (1 percent). Non-Hispanic whites make up 77 percent of the population. There is reason to
expect that Louisville is becoming larger and more diverse. The 2006 American Community Survey
did not track the Hispanic population in Louisville, but showed the total population likely surpassed
700,000, with a 2 percent decrease in non-Hispanic whites.
Minority census block groups in Louisville comprise 7.3 percent of the land acreage and 16.2 percent
of the population. Louisville’s geographic information systems portal, LOJIC, identifies 168 Metro
FIGURE 4. City of Parks Evaluation
Pct of Pct of COP Total Total
Park Pct of
Park Land Acres Park Park
Acres Population
Acres Acres Added Acres Pct.
Non-Minority
11,383 94.3 92.7 83.8 2,890 14,273 95.4
Block Group
Minority Block
694 5.7 7.3 16.2 0 694 4.6
Group
Total 12,077 100 100 100 2,890 14,967 100
Source: Louisville Metro Parks
Park polygons. Although Metro Parks identifies 123 parks, the data separates some features, such as
golf courses and community centers. A Metro Park is considered to be serving a minority population if
it is in or abuts a minority census block group.
By number of parks, access is fairly just. With 32 park polygons, minority census block groups are
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home to 19 percent of parks. However, parks in Louisville vary widely in size and amenity, from the
two benches that make tiny Gnadinger Park a place to rest tired feet to the 6,191-acre Jefferson
144
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
FIGURE 5. Existing Parks by Census Block Groups. Source: Louisville/Jefferson County Information
Consortium, U.S. Census 2000
Memorial Forest which offers an educational center, a Boy Scout camp and a variety of trails and
programming (see Figure 4). Clearly, the recreational and environmental value of the two parks
differs greatly. Simply counting parks does little to demonstrate true access or equitable distribution.
Louisville’s 123 parks comprise 12,077 acres. White area parks account for 10,689 of park acres, or
94.3 percent of the city’s parks. The remaining 694 acres are located in minority areas, 5.7 percent
of the city’s parks.
Louisville’s suburban developments are largely white. In the less densely settled suburbs, larger parks
can be built before development can shape the space. Development of the largest urban forest in the
United States, Jefferson Memorial, is an initiative that began in 1946, well after most of the city’s
current minority areas had been developed. The site chosen was on the Jefferson-Bullitt county line
in southwest Metro Louisville. In minority block groups, the median park size is 3.61 acres whereas
white parks have a median of 24, more than six times the size of the median park size in minority
areas (see Figure 5).3
Master-planned renovations are underway as part of the City of Parks Plan. Figure 6 shows the
breakdown of completed and scheduled renovations by area type. If compared against available
parkland, the City of Parks Plan does improve a proportional share of minority-area parks. Minority
areas are set to receive 15 percent of upgrades completed or scheduled in area parks. These upgrades
include improvements to baseketball and tennis facilities in Black Mudd Park near Buechel, restoration
to tennis facilities and a pavillion at Shawnee Park, and complete renovations to Shelby and Algonquin
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Parks.
FIGURE 6. Renovations to Existing Parks 145
Completed Scheduled Total Renovations
Non-Minority Area 25 8 33
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Minority Area 3 3 6
Percent Minority 11 27 15
Source: Louisville Metro Parks, U.S. Census Bureau
In 2008, as the city celebrated the opening of part of the Metro Loop and the Floyds Fork as part of
the City of Parks public-private partnership, budget cuts kept five of the nine city pools closed, three
with no plans to reopen. Two of these pools were in minority census block groups (Klepal, 2008). The
result were packed pools, with Algonquin in the West End more than doubling in attendance (Leonard,
2008). Poor children are hit especially hard by the closing of public pools. Poor families cannot provide
the money needed for membership to semi-public pools (Klepal, 2008).
However, no new pools or parks are planned for minority areas under the City of Parks Plan. A trail
to connect minority-area parks to parks in white neighborhoods across an existing levee easement is
being constructed, but this adds no new open-space acreage. The City of Parks initiative adds 2,890
acres to the park system, all in white areas. This would drop the minority stake in parks more than a
full percent, from 5.7 to 4.6 percent of the acreage in the new parks system after City of Parks.
A More Just Parks Plan
In undergoing one of the largest park system expansion efforts in the United States, politicians and
others involved have expressed a great deal of pride. While the greening of a city is noteworthy,
Louisville could set an example for other cities by expanding the park system in a manner that improves
the lives of all residents, attends to historical injustice and inequity, and promotes environmental and
economic sustainability. It is this desire to set an example of justice that inspires this study. The City
of Parks Plan, in its current form, does little to improve accessibility to parks for minority residents.
How might a more just plan be accomplished? Minority areas are some of the older, more developed
areas of the city, areas that do not include vast amounts of open space ready to be developed.
However, at this time in the city’s history, many large plots of industrial land have been vacated.
Companies such as Phillip-Morris and Rhodia have left the city with industrial brownfields. A just city
(Fainstein, 1999) should aspire to clean these properties quickly so that the toxins on site do not travel
by air, water, or curious child into neighboring minority communities. A park expansion plan that turns
brown into green in a way that brings green into the heart of the minority community and connects it
to areas of interest would demonstrate to the minority community that the City of Parks includes all
areas of the city. Vacant properties offer opportunities for redevelopment that minimize disturbance
and reduce opportunities for vandalism and other crimes. These actions also demonstrate that the
government is willing to make efforts to counteract the effects of institutional and environmental
racism that predate current officials.
Figures 7 through 13 demonstrate the author’s suggested park expansion for minority areas. This
plan would add up to 863 acres of parkland, a 124 percent increase in minority parks (see Figure 7).
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The sizable increase is still modest; it fails to offset the additional expansion in white areas under the
City of Parks Plan.
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FIGURE 7. Proposed Park Plan
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
City of Parks Minority Expansion Percent
Current
(2008) Expansion Total Expansion
Minority Parks 694 0 863 863 124.4%
Parks Total 12,077 14,967 15,830 3,754 23.7%
Source: Louisville Metro Parks
Figure 8 shows the targeted park area. Location is important, and this target area would create
greenways in the heart of the minority community, while connecting Shawnee and South Central
to downtown, and Russell to the University of Louisville. This greenway touches some of the main
business thoroughfares in the city’s minority neighborhoods by greening the old bourbon warehouses
of Seventh Street and passing through the center of Broadway, the main thoroughfare through many
minority neighborhoods, near businesses and transit lines. Wherever possible, these target park areas
connect residents to other areas without disrupting commercial or residential areas and maintain
connectivity through parks, a format from the City of Parks Plan. The northern edge would allow
connectivity to the developing Riverwalk through a single bike lane. Additional possible connections
exist in the conversion of abandoned rail lines into greened bicycle lanes within these areas. Such a
conversion would help further connect the proposed parks to areas of employment since many of
these abandoned rail lines abut properties in our target area. Where connectivity was not possible
because land is unavailable, in such areas as the minority-serving Buechel neighborhood, parks are
placed to anchor subdivisions.
The suggested expansion would redevelop 61.8 acres of vacant industrial vacant land and 146 total
acres of vacant land (see Figure 9). In addition to cleaning up brownfields and removing vacant land,
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FIGURE 8. Proposed Park Expansion Step 1: Target an Area. Source: Louisville/Jefferson County 147
Information Consortium, U.S. Census 2000
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FIGURE 9. Proposed Park Expansion Step 2: Add Vacant Lands. Source: Louisville/Jefferson County
Information Consortium, U.S. Census 2000
this plan suggests removing warehouses in the area to areas closer to expressways and farther from
densely settled neighborhoods. In many cases, this land is available; in cases where it is not, public-
private partnerships could be sought to help acquire suitable land as part of the park expansion plan.
This should further improve the environment and safety of the neighborhood.
Figure 9 shows the second step. Using parcel land use data, vacant land in the target area is identified
and added to the proposed park area. Figure 10 shows the evaluation of this land. Industrial land
accounts for 42 percent of the vacant land in the area; this would mean the cleaning of 62 acres
of brownfields. Vacant residential land (30 percent), if capable of being purchased, adds another 44
acres and commercial (28 percent) adds another 41 acres for 146 acres of vacant land available in
the target area.
FIGURE 10. Vacant Land Opportunities
Industrial Commercial Residential Total
Acreage 61.8 40.5 44 146.3
Source: Louisville/Jefferson County Information Consortium
Added to the 146 acres of land, Step 3 (see Figure 11) shows the warehouses in the target area.
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This area is in the heart of the minority community. This area is largely two- and three-lane streets,
uncomfortable trucks, which make wide right turns and often must use sidewalks and driveways to
back into loading docks. Better infrastructure and highway opportunities exist within Louisville in
148
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
FIGURE 11. Proposed Park Expansion Step 3: Logistics Opportunities. Source: Louisville/Jefferson
County Information Consortium, U.S. Census 2000
less densely settled areas, some with additional connections to airports and rail freight yards. Land
transfers would allow these jobs to stay within Louisville, but move their externalities to areas with
less development. Current locations require trucks to navigate two-lane roads and stop at numerous
lights before reaching highways, further dispersing diesel exhaust in minority neighborhoods. Offering
tax incentives or land transfers to relocate to outlying and easily accessible areas would improve local
air quality. The diversion of logistics, storage and transport businesses and its accompanying traffic
could add up to 286 acres of future parkland, nearly a third of the target area (see Figure 12).
FIGURE 12. Logistics Opportunities
Warehouse Vacant Lands Total
Acreage 286.2 146.3 432.5
Source: Louisville/Jefferson County Information Consortium
Figure 13 evaluates the use of the remaining parcels in the target area (see Figure 14). Some of these
uses may fit into a new greenway. A school or religious institution can share space with a park. In
fact, they may welcome the amenities the park offers to provide such as safe ways for children to
travel to school and gathering and recreational spaces. Other properties require a closer look. A large
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f lea market property with two old industrial water towers may offer a unique opportunity to meet
resident needs. Within the target area, 8 percent of the land is held by state or local governments
149
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
FIGURE 13. Proposed Park Expansion Step 4: Evaluate Target Area. Source: Louisville/Jefferson
County Information Consortium, U.S. Census 2000
FIGURE 13. Existing Land Use in Target Area
Acreage
Agricultural 1.2
Commercial 146.4
Government 33.7
Industrial 122.4
Infrastructure 9.5
Religious/Non-Profit 57.9
Residential 57.1
School 3.8
Total 432
Source: Louisville/Jefferson County Information Consortium
and may be made more easily available. Some storefronts may make nice partners within the park. A
restaurant or corner store may offer a unique benefit to park visitors. In addition, job growth should be
expected nearby as vacant parcels near the parks become more appealing as foot traffic and quality
of life increases.
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Figure 14 shows the breakdown of the current Metro Parks system, City of Parks Plan, and the
proposed minority area expansion plan. The addition proposed, would still fall short of maintaining
150
the ratio of park acreage that existed prior to the City of Parks Plan. This study does not propose
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scaling back the City of Parks Plan. The plan protects valuable waterways, unique features and
virgin lands. However, the established partnership must consider issues of environmental justice and
equity as it continues forward. Concurrent expansion in all areas of the community is a proper course.
Consideration as to how parks may be best designed to meet the social needs of the likely users and
generate additional income can be explored. Renting park facilities, partnerships with caterers, as
well as the rental of small shops or kiosks may generate maintenance funds. Usage fees and parking
meters are possibilities. The establishment of small-business assistance or programs could help jump-
start and support small businesses choosing to locate near the new parks.
FIGURE 14. Park Expansion Addition Adjustment
Current COP Minority
Minority Areas 5.7 4.6 5.5
White Areas 94.3 95.4 94.5
Source: Louisville/Jefferson County Information Consortium, U.S. Census 2000
The final product should be a park system that promotes sustainable transportation and environmental
mitigation measures. Amenities, recreation options and design are products the residents that use
the parks should help determine. However, with a well-developed expansion plan that considers the
needs of the residents, as well as improving the health of the environment in which they live, work
and play can help improve economic and environmental sustainability and encourage land use equity
and environmental justice.
CONCLUSION
Louisville has the opportunity to transform the character of its minority communities by expanding
parks in a way that enhances the life of minority residents while recognizing and attending to past
environmental injustices. By converting vacated industrial lands and warehouses into parks, minority
communities in Louisville should expect to see benefits including health improvements, social cohesion,
higher property values, and business startups, while at the same time seeing decreases in crime. This
can be done in a manner that does not economically oust residents in favor of gentrification, although
this is a problem the city needs to pay special attention to ensure.
A City of Parks Plan that properly considers minority needs has the possibility of developing a green
heart in the West End where abandoned industrial land now exists. This would serve to offset the
uneven environmental burden placed upon these minority neighborhoods. Proper location would
allow minority areas to connect easily by bicycle or walking to jobs in south central, downtown and
to the University of Louisville. The City of Parks Plan, in its current form, does little for minority
residents, merely adding a trail along the existing levee. Opportunities exist to tailor the plan to
consider improved park access for minorities. Establishing a park system that supports sustainable
neighborhoods in all communities, regardless of race, would send a powerful message to residents.
A well-planned park expansion plan can improve equity by ensuring equal and ease of access to
minority residents. Attention to land use and encouraging density-appropriate clean industry, retail
and service through creative government incentives can not only improve the environment but improve
LASLEY
the economic vitality of residents. Considering the environmental needs of residents and problems
accompanying urbanization, including cleaning of polluted land, mitigation of stormwater problems
and cooling of the urban heat island allow neighborhoods to be more environmentally sustainable. In
151
addition, by developing parks that help connect people to useful destinations encourages sustainable
modes of transportation and improves public health. To create a more environmentally just park system
planners must be mindful of the people, land uses, equity issues and environments in question. The
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results can be much-needed anchors that serve as social hubs, business catalysts and civic centers
for more sustainable urban neighborhoods.
LASLEY
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PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
AUTHOR’S BIOGRAPHY
Carrie Beth Lasley is finishing her Master of Urban Planning degree at the University of Louisville
and plans to pursue her Ph.D. in Urban Studies. The Louisville native is a recovering journalist and
a graduate of the University of Missouri-Columbia and the City University of New York-Lehman
College.
[ENDNOTES]
1. For this study, minorities were people who identified themselves as black, Asian or Hispanic. A non-minority was
someone who was identified as a non-Hispanic white. People identified as American Indian, Pacific Islander, Hawaiian
or of two or more races were considered white for this study. Their combined numbers were less than 1 percent of the
total population. A block group was considered a minority area if the population totaled 33 percent or more minority. This
threshold was kept low due to the length of time since the last Census (seven years), established trends of an increasingly
diverse population and the expectation that diverse areas become more diverse over time. Since block groups are small
areas, an assumption of even dispersal was in play.
2. Parks belonging to formerly suburban cities, such as St. Matthews, Shively and Jeffersontown were not included in
this study. As sub- cities within Louisville they can tax residents and provide services that may include parks not in the
Metro Parks system. E.P. “Tom” Sawyer State Park, in the county’s far east end, also was not included. Additional
recreational and natural areas offered by private and non-profit agencies were not considered, such as the Americana
Center, which offers a community center and recreational facilities in south Louisville at the old Holy Rosary campus,
and the Garvin Brown Nature Preserve, a sizable nature preserve located along the river just north of Hays Kennedy Park.
These have funding streams not supported by Metro government. There is no reason to believe that inclusion of this data
would have dramatically changed the results.
3. A median park size is a better measure than mean to determine the types and character of parks available to our two
race groups.
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LASLEY
Abramson, J. (2007, November 6). Mayor’s Healthy Hometown Movement: Letter from Mayor Abramson. Retrieved
December 10, 2007, from Louisville Metro Government: http://www.louisvilleky.gov/Health/MHHM/LetterFromMayor. 153
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Bartlestein, P. (2007). The Impact of Waterfront Park. Louisville, Ky.: Waterfront Development Corporation.
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CDC. (2006). The State of Childhood Asthma, United States, 1980–2005.: U.S. Department of Health and Human
Services.
CDC. (2008). Health Disparities-Closing the Gap.: U.S. Department of Health and Human Services.
Crompton, J. L. (2007). Competitiveness: Parks and Open Space as Factors Shaping a Location’s Success in Attracting
Companies, Labor Supplies and Retirees. In C. T. Brun, The Economic Benefits of Land Conservation (pp. 48-54). San
Francisco: The Trust for Public Land.
Crompton, J. L. (2007). The Imapct of Parks and Open Spaces on Property Taxes. In C. T. Brun, The Economic Benefits
of Land Conservation (pp. 1-12). San Francisco: The Trust for Public Land.
Daley, R.M. (2003) Revitalizing Chicago Through Parks and Public Spaces. Places, 26-27.
Dines, N. and Cattell, V. (2006) Public spaces, social relations and well-being in East London. London: The Policy Press.
Fainstein, S. S. (1999) Can We Make the Cities We Want? The Urban Movement (pp. 249-72) in Sophie Body-Gendrot
and Robert Beauregard, eds. Thousand Oaks: Sage, 1999.
First National People of Color Environmental Leadership Summit. (1991). The Principles of Environmental Justice. The
Principles of Environmental Justice Guiding Principles (p. 2). Washington, D.C.: Environmental Justice Network.
Forsyth, A. A. (2005). Designing Small Parks: A Manual Addressing Social and Ecological Concerns. New York City:
Wiley.
Gies, E. (2006). The Health Benefits of Parks. San Francisco: The Trust for Public Lands.
Gobster, P. H. (2002). Managing Urban Parks for a Racially Diverse Clientele. Leisure Sciences , 143-159.
Horn, D. (2001, December 31). Cincinnati: 2001 Year of Unrest. Retrieved December 10, 2007, from Cincinnati Enquirer:
http://www.enquirer.com/unrest2001/.
Klepal, D. (2008, May 3). Louisville pool closings spur complaints. Retrieved June 23, 2008, from The Courier-Journal:
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Koekebakker, O. (2003). Westergasfabriek Culture Park: Transformation of an Industrial Site in Amsterdam. Rotterdam:
NAI Publishers.
Kuo, F.E., and Sullivan, W.C. (2001) Actual Causes of Death in the United States, 2000. The Journal of the American
Medical Association. 343-367.
Leonard, C. (2008, June 12). Closures of some city pools leads to big crowds at others. Retrieved on June 23, 2008, from
WAVE: http://www.wave3.com/global/story.asp?s=8484732.
Louisville Metro Government. (2007, December 10). City of Parks: Louisville’s Greenprint. Retrieved December 10, 2007,
from Louisville Metro Government: http://www.louisvilleky.gov/MetroParks/City of Parks/.
Louisville Metro Government. (2006). Mayor’s Healthy Hometown Movement Resource Guide. Louisville, Ky.: Louisville
Metro Government.
Louisville Metro Government Planning & Design. (2000). Cornerstone 2020. Louisville, Ky.: Louisville Metro
Government.
LASLEY
Meredith v. Jefferson County Board of Education, 05-915 (U.S. Supreme Court June 28, 2007).
154 Metro Parks. (2005, February 22). Abramson unveils ‘City of Parks’ Vision. Retrieved December 10, 2007, from Metro
Parks: http://www.louisvilleky.gov/MetroParks/News/2005/cityofparks.htm.
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Northern, M.L. (Spring 2006) City of Parks: Adding a Green Ring to Olmsted’s Emerald Necklace. U of L Magazine.
Pace, D. Minorities suffer most from industrial pollution. 14 December 2005. Retrieved June 18, 2008 from MSNBC:
http://www.msnbc.msn.com/id/10452037/.
Penalosa, E. (2003) Parks for Livable Cities: Lessons from a Radical Mayor. Places, 30-33.
Sherer, P. M. (2003). The Benefits of Parks: Why American Needs More City Parks and Open Space. San Francisco:
Trust for Public Land.
Witt, P.A. and Crompton, J.L. (1996) The at-risk youth recreation project. Journal of Park and Recreation Administration,
1-9.
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155
Professor Timothy W. Collins
Professor Sara E. Grineski
Martha I. Flores
ENVIRONMENTAL INJUSTICE IN
THE PASO DEL NORTE
COLLINS, GRINESKI, FLORES
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ABSTRACT
In February 2008 American Smelting and Refining Company (ASARCO) was granted an air permit to
reopen its El Paso, Texas copper smelter through the Texas Commission on Environmental Quality
(TCEQ). This is a unique environmental justice case because the ASARCO smelter is located in a
densely populated minority community at the junction of three states and two countries. If the facility
resumes operations, it will be the only copper smelter operating within a US metropolitan area. This
essay employs archival and visual methods to situate a case of transnational environmental injustice.
The 16 images present powerful representations of the situation in El Paso that contextualize the
case study, and highlight the potential of images to reveal alternative perspectives and mobilize
community action.
In February 2008 American Smelting and Refining Company (ASARCO) was granted an air permit to
reopen its El Paso, Texas copper smelter through the Texas Commission on Environmental Quality
(TCEQ) (Images 1 and 2). This is a unique environmental justice case because the ASARCO smelter is
located in a densely populated minority community at the junction of three states and two countries
(Figure 1). The permit entitles the multinational corporation to emit 7,000 tons of pollution annually –
including 4.7 tons of lead (more than any other facility in the U.S.) – into an airshed shared by Texas,
New Mexico, and Chihuahua, Mexico (TCEQ, 2007; O’Rourke, 2007; Shapleigh, 2007a). If the facility
resumes operations, it will be the only copper smelter operating within a U.S. metropolitan area.
This essay employs archival and visual methods to situate a case of transnational environmental
injustice. We believe visual methods are a powerful tool for environmental justice because of the
COLLINS, GRINESKI, FLORES
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IMAGE 1. The 828 foot ASARCO stack with contaminated soil at its base.
COLLINS, GRINESKI, FLORES
IMAGE 2. The ASARCO stack is visible in valley to the right in this view from El Paso’s Franklin Mountains
southward to Ciudad Juárez.
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FIGURE 1. This map of the Paso del Norte region, which includes three states in two countries, shows the
ASARCO facility at center; public schools and early childhood centers identified as points. Schools are of
particular concern because lead is especially damaging to children’s development (Landrigan, 1975).
unique capacity of imagery to present information in a concrete manner accessible to a wide social
spectrum. Visual methods are also effective in arousing emotions, shaping opinions, and catalyzing
action (Hannigan, 1995), as the ASARCO case reveals. Images have figured into this case (as they
have in others), yet they remain largely unexamined in the environmental justice literature. We selected
the 16 images presented in this essay because we found them to be powerful representations of
the situation in El Paso, because they demonstrate the utility of visual methods for contextualizing
case study, and because they highlight the potential of images to reveal alternative perspectives and
mobilize community action.
ASARCO operated the copper smelter continuously in El Paso from 1887 until 1999, when the price of
copper dropped to $.60 per pound (Image 3). Until 1973, residents lived in Smeltertown, the company
community located at the base of the stack. ASARCO had neglected to include this community its
air pollution monitoring. In 1973, Smeltertown was razed after it was documented by non-company
sources that 53% of children had lead levels considered dangerous (Landrigan et al., 1975). All that
COLLINS, GRINESKI, FLORES
remains of Smeltertown is the cemetery (Image 4).
ASARCO has long history of toxic pollution and corporate irresponsibility in the U.S. The corporation
has saddled citizens from 75 communities and 16 states across the country with at least $6 billion,
perhaps as much as $20 billion, in environmental remediation and cleanup costs (Blumenthal, 2007;
Milan, 2007). It is projected that remediation of soil and groundwater at the El Paso facility site
will cost at least $27 million; costs could increase once the extent of contamination of surface and
groundwater supplies is fully documented (El Paso Times, 2007; Johnson, 2007). Reliable sources
160 report that more comprehensive cleanup (of current contamination) in the Paso del Norte will cost in
excess of $250 million (Shapleigh, 2007b). If the smelter does reopen and pollute once again, estimates
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
of remediation costs will surely escalate. While ASARCO’s public relations campaign incorporates a
dose of green rhetoric (ASARCO, 2007a), the deleterious effects of their copper smelting on human
health and the environment do not point toward a model of sustainability.
Two questions arise. First, why has ASARCO sought to open a facility that will release 7,000 tons of
pollutants known to produce adverse health effects in the middle of a metropolis of 3 million people?
After all, ASARCO has decommissioned urban smelters in Tacoma and Omaha. While the push to get
back in the smelting business has surely been inf luenced by spiking copper prices, which are currently
$2.70 per pound (ASARCO, 2007b), ASARCO’s desire to resume operations in the Paso del Norte is
undeniably connected with the characteristics of the people in the region. The vast majority of nearby
U.S. residents in the City of El Paso (El Paso County, Texas) and Sunland Park (Doña Ana County,
New Mexico) are Hispanic (77% and 98%, respectively, compared with 13% for the U.S. and 32% for
Texas). El Paso and Sunland Park have considerably lower median household incomes ($32,124 and
$20,164, respectively) than Texas ($39,927) and national levels ($41,994), and poverty rates (22%
and 39%, respectively) well above the U.S. rate (12%) (U.S. Bureau of the Census, 2000) (Images 5 and
6). In addition, the portion of Ciudad Juárez abutting the facility is home to this Mexican metropolis’
most socially marginal colonias (i.e. neighborhoods) (Ward, 1999; Frontera NorteSur, 2005).
To be sure, ASARCO’s public relations staff has attempted to seize on El Paso’s relatively depressed
economic conditions by packaging the reopening of the smelter in terms of job creation and economic
growth (in part through the use of images, see ASARCO, 2007c), and a recent ASARCO-funded
economic impact analysis has endowed the company’s economic promises with aura of legitimacy
(ASARCO, 2007d). A recent public opinion poll suggests that ASARCO’s campaign has been
COLLINS, GRINESKI, FLORES
IMAGE 3. The ASARCO copper smelter in El Paso, 1899. Source: Aultman Collection, B198, El Paso Public Library
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IMAGE 4. All that remains of ASARCO’s company town is the Smeltertown Cemetery.
COLLINS, GRINESKI, FLORES
IMAGE 5. Several apartment complexes catering to low income El Pasoans (like this one) are located near
the ASARCO facility.
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IMAGE 6. Low income residents also live in single family housing near the ASARCO facility; this neighborhood
is located near Sunland Park, New Mexico.
COLLINS, GRINESKI, FLORES
IMAGE 7. Socially marginal Ciudad Juárez colonias are proximate to the ASARCO facility.
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IMAGE 8. When standing on the US side of the international border, Ciudad Juárez dwellings are visible
adjacent to the ASARCO facility.
successful: 50 percent of registered voters responded “yes” to the question of whether ASARCO
should be allowed to re-open (Meritz, 2007). Results from a pilot survey (conducted by the authors)
of four El Paso neighborhoods reveal that the majority of residents believe that ASARCO will harm
health; findings also indicate that public support for ASARCO hinges on the belief that it will create
jobs, regardless of corresponding beliefs about negative health effects.
Now the second question: Why did the TCEQ grant ASARCO a permit to pollute? A simple response
COLLINS, GRINESKI, FLORES
164 IMAGE 9. During a bi-national anti-ASARCO rally, protesters from the US and Mexico joined together,
despite being separated by the border fence. Source: Mariana Chew-Sanchez
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FIGURE 10. Dedicated ACORN and GTLO members from the US and Mexico protested in Austin, Texas (in
February 2006) after a 10 hour bus ride from El Paso. Source: Jose Manuel Escobedo
is that the TCEQ has never denied an air permit. The commission is viewed by many as a regulatory
body designed to facilitate the profit motives of big industry. It must also be realized that El Paso is
marginal in relation to the Texas’ centralized political engine, located over 500 miles away in Austin,
which means that local voices are less likely to be listened to if heard.
Local opponents of ASARCO realize that they must be loud, and residents and elected officials from
the State of New Mexico and nearby cities (including Ciudad Juárez) have voiced clear opposition to
ASARCO’s reopening (see City of El Paso, 2007). Civil society groups on both sides of the border –
including the Association of Community Organizations for Reform Now (ACORN), Get The Lead Out
Coalition (GTLO), and the Sierra Club – have collaborated in protest against ASARCO’s proposed
reopening (Images 9 and 10) (see GTLO, 2007; Sierra Club, 2007; ACORN, 2007). In March 2007,
ACORN and GTLO activists took direct action in Austin by storming the Capitol and demanding inclusion
in the air permitting process (Image 11). Over the summer, ACORN canvassed local neighborhoods to
inform residents of the imminent threat of the smelter and to enlist people in their petition drive
COLLINS, GRINESKI, FLORES
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IMAGE 11. ACORN and GTLO activists take direct action by storming the Capitol in Austin, Texas (March
2007). Source: Jose Manuel Escobedo
COLLINS, GRINESKI, FLORES
IMAGE 12. More than 1,000 Paso del Norte residents gathered in protest for the community photo “Faces
166 Against ASARCO.” Source: GTLO 2007
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IMAGE 13. Residents raise their hands to show opposition against the renewal of the ASARCO air permit
at the “Faces Against ASARCO” event.
to deliver local voices of opposition to Austin. During the public comment period for ASARCO’s air
permit (which ended in June 2007), over 10,480 letters were submitted to the TCEQ; 9,600 letters
were in opposition to, and only 880 in support of, the proposed reopening of the facility (City of El
Paso, 2007). In September 2007, local groups organized a community photo entitled “Faces Against
ASARCO” as part of their mobilization effort (Image 12). The event further catalyzed opposition
against ASARCO in the Paso del Norte by bringing together a diverse range of residents, opening
channels of communication, and reaffirming shared values (Byrd, 2007) (Image 13). Vociferous
opposition proved to be an unsuccessful inf luence in the permitting process as the decision to approve
the air permit was ultimately made by three governor-appointed TCEQ commissioners. This provides
another example of how “current environmental decision-making practices have not been effective in
providing meaningful participation opportunities for those most burdened by environmental decisions”
(Cole and Foster, 2001, p. 16).
Now that the air permit has been granted, opposition must rely on litigation in which claims
of transnational inequity, environmental degradation, and environmental racism should figure
COLLINS, GRINESKI, FLORES
prominently. Since ASARCO’s El Paso facility is located within a kilometer of Mexico and New Mexico,
transboundary pollution would negatively effect the primarily lower income Hispanic populations
in these jurisdictions. The transnational movement of toxic pollution from the Global North to the
South has received attention in the environmental justice literature (Adeola, 2000, Frey, 2003,
Pellow, 2007); the ASARCO case provides an example of this trend. The fact that the air permit has
been authorized in Austin, Texas and the facility would acutely impact adjacent state and national
jurisdictions – without consent of appropriate territorial governing bodies – may provide a fulcrum of
legal leverage for ASARCO’s opponents.
167
In addition, the TCEQ permit pertains to air, but ASARCO’s pollution has already affected, and will
further impact, water and soil resources to the detriment of human and ecological health. ASARCO’s
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facility is located within meters of the Rio Grande/Bravo, which provides irrigation water used by
the region’s farmers and between 40 to 50 percent of El Paso’s drinking water (Images 14 and 15).
It must be noted that ASARCO filed for Chapter 11 Bankruptcy in 2005 and is now enmeshed in an
extremely complex court case. The U.S. International Boundary and Water Commission (USIBWC)
recently filed a pre-trial brief in the bankruptcy case, which states “continuing contamination from
the ASARCO property has forced USIBWC to address the dangers of lead and arsenic in carrying out
its responsibility to regulate and conserve the waters of the Rio Grande…due to the high contaminant
levels that exist” (U.S. Bankruptcy Court, 2007, p. 2).
Finally, it is difficult to contemplate this case without seriously considering the role of environmental
racism, particularly in its institutional guise, as a factor. A predominantly working class, dark-skinned
metropolitan community is now engaged in a seemingly rational public debate about the prospect of
opening one of the U.S.’s single most noxious facilities in its midst, a fact that generates a sense
of surrealism among visitors from other parts of the country. Residents of wealthier and whiter
communities are spared the experience of being forced to engage in such debates.
The environmental injustices related to El Paso’s ASARCO smelter are many. The lead emissions
will be most damaging to young children and pregnant women. El Paso is one of the poorest cities
in the U.S. with a majority minority population that lacks power within the state of Texas and is
socially marginal within the American context. Located on the edge of Global North, residents of semi-
peripheral Mexico will be unfairly impacted by ASARCO without receiving a single benefit.
IMAGE 14. View of Texas in foreground, Mount Cristo Rey in New Mexico (behind lower stack), the Rio
Grande/Bravo (lower left), and Ciudad Juárez (far left).
COLLINS, GRINESKI, FLORES
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IMAGE 15. The Rio Grande/Bravo just upstream of the ASARCO facility.
COLLINS, GRINESKI, FLORES
169
AUTHORS’ BIOGRAPHIES
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Timothy W. Collins is an Assistant Professor in the Department of Sociology & Anthropology at the
University of Texas at El Paso. His research interests include human risk to environmental hazards,
issues of social vulnerability and environmental justice, and urban governance. Direct correspondence
to Timothy W. Collins, Department of Sociology & Anthropology, University of Texas at El Paso, 500
West University Avenue, El Paso TX 79968; Phone: 915-747-6526; e-mail: twcollins@utep.edu.
Professor Sara E. Grineksi is an Assistant Professor in the Department of Sociology & Anthropology
at the University of Texas at El Paso. Her research centers on the topics of environmental justice and
environmental health. Phone: 915-747-8471; e-mail: segrineski@utep.edu.
Martha I. Flores graduated from the Sociology Master’s program at the University of Texas at El
Paso in May 2008. Her research interests include environmental justice and visual sociology. Her
thesis focuses on the use of images in the social construction of environmental problems, specifically
the debate surrounding the reopening of the ASARCO copper smelter described in this paper. E-mail:
marthaisabel.f lores@gmail.com.
ACKNOWLEDGMENTS
We would like to acknowledge Alma Hernandez and Mauricio Austin for their assistance with the
neighborhood survey referenced in this piece. We also are thankful for the images provided by local
activists (who are identified in captions), which contributed greatly to our essay.
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ASARCO. (2007d). Economic Study Reveals 6.75:1 job ratio and billions in economic impact if Asarco re-opens. Retrieved
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Blumenthal, L. (2007, February 2). Embattled mining company Asarco enters into settlement talks. McClatchy Newspapers.
Retrieved December 11, 2007, from Web site: http://www.mcclatchydc.com/staff/les_blumenthal/story/15526.html.
Byrd, S. (2007, September 29). Letter: Story ignored on Asarco mass gathering. El Paso Times.
City of El Paso. (2007). City of El Paso opposes the re-opening of ASARCO. Retrieved December 11, 2007, from Web
site: http://www.elpasotexas.gov/asarco.asp.
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Cole, L. and S. Foster. (2001). From the Ground Up: Environmental Racism and the Rise of the Environmental Justice
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Hannigan, John A. (1995). Environmental Sociology: A Social Constructionist Perspective. London: Routledge.
Johnson, E. (2007, December 6). U.S. says Asarco owes $27 million. El Paso Times.
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Meritz, D. (2007, October 28). Majority of El Pasoans say Asarco should be allowed to reopen. El Paso Times.
Milan, T. (2007, March 9). The dark side of the Rio Grande: Tika Milan reports on Asarco’s Texas refinery. Rolling
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O’Rourke, B. (2007, October 28). City opposes Asarco over its emissions. El Paso Times.
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Shapleigh, E. (2007a). ASARCO in El Paso. El Paso: State of Texas, El Paso County, 29th Senatorial District Office.
Shapleigh, E. (2007b, December 1). Commentary: Asarco bankruptcy passes $11 billion tab to taxpayers. Newspaper
Tree: El Paso’s Original News Source. Retrieved December 11, 2007, from Web site: http://newspapertree.com/
opinion/1865-asarco-bankruptcy-passes-11-billion-tab-to-taxpayers.
Sierra Club. (2007). Environmental justice, U.S.-Mexico border: Taking aim at toxic pollution from ASARCO factory.
Retrieved December 11, 2007, from Web site: http://www.sierraclub.org/environmental_justice/projects_mexico.asp.
TCEQ (Texas Commission on Environmental Quality). (2007). Executive Director’s Report to the Commission on the
Renewal of ASARCO Incorporated’s Air Quality Permit No. 20345, TCEQ Docket No. 2004-0049-AIR, 1 May 2007.
Retrieved December 11, 2007, from Web site: http://www.tceq.state.tx.us/assets/public/agency/ed_report_arasco.pdf.
US Bankruptcy Court. (2007). US International Boundary and Water Commission claims against ASARCO, LLC, et al.
Southern District of Texas, Corpus Christi Division, Case 05-21207, Document 6381, 29 November 2007. Retrieved
December 11, 2007, from Web site: http://newspapertree.com/system/news_article/document1/1883/12.5.07_
asarco_1.pdf.
COLLINS, GRINESKI, FLORES
US Bureau of the Census. (2000). United States Census 2000, summary tape files 1 and 3. Retrieved December 11,
2007, from Web site: http://www.census.gov/main/www/cen2000.html.
Ward, P. (1999). Colonias and Public Policy in Texas and Mexico: Urbanization by Stealth.
Austin: University of Texas Press.
171
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Na’Taki Osborne Jelks
SEWAGE IN OUR BACKYARDS :
THE POLITICS OF RACE, CLASS, +
WATER IN ATLANTA, GEORGIA
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PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
ABSTRACT
This article considers the centrality of equity and justice and the importance of meaningfully engaging
those most affected by planning decisions at the outset of the environmental planning process in two
cases where African American communities in southwest Atlanta challenged the City of Atlanta to
implement alternative solutions to wastewater treatment improvement proposals that were initially
developed without community engagement. Ultimately, these proposals would have adversely affected
their already overburdened neighborhoods. The two cases are examples of successful community
education, mobilization, and advocacy that changed the course of public policy decisions. Poor access
to environmental planning and public participation processes in the initial proposal development process
led to plans that would have negatively impacted and increased existing disparities in the quality of life
for impacted communities. The meaningful involvement in the planning and decision-making process
by these two communities resulted in a more equitable, just, and ecologically sustainable solutions to
Atlanta’s wastewater infrastructure and environmental challenges.
INTRODUCTION
This article examines the centrality of equity and justice and the importance of meaningfully engaging
those most affected by planning decisions at the outset of the environmental planning process in two
cases in which African American communities in southwest Atlanta challenged the city government
to implement alternative solutions to wastewater treatment improvement proposals. These proposals
were initially developed without community engagement and ultimately would have adversely affected
their already overburdened neighborhoods. The two cases are examples of successful community
education, mobilization, and advocacy that changed the course of public policy decisions. Poor access
to environmental planning and public participation processes in the initial proposal development process
led to plans that would have negatively impacted and increased existing disparities in the quality of life
for the affected communities. The meaningful involvement in the planning and decision-making process
by the impacted communities resulted in more equitable, just, and ecologically sustainable solutions to
Atlanta’s wastewater infrastructure and environmental challenges than the initial proposal.
Every city must deal with issues of sanitation and sewage disposal. Often considered a less than
glamorous public policy issue, wastewater treatment is critical to the economic and public health
of communities. Citizens and policy makers are usually most comfortable leaving the solutions to
wastewater treatment problems to public works officials, civil engineers, city planners, and other
professionals. When such policies are developed in this traditional manner and potentially affected
communities are not engaged to represent their own interests, communities of color can and
historically have often been on the losing side of the equation. However, in an attempt in to achieve
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environmental justice for citizens living in environmentally burdened neighborhoods, communities of
174 color in Atlanta, Georgia chose to alter this typical scenario when they entered the public policy
debate concerning wastewater treatment and infrastructure in the early 1990s.
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In the 1990s, the Atlanta metropolitan area, nicknamed the “sprawl capital of the world,” grew more
than any other American city, except Los Angeles, California (Bullard, 2000). Efforts by the City of
Atlanta to improve and expand its wastewater treatment system to accommodate growth caused
major controversy and intense public debate. This controversy centered on the City’s strategies
for meeting state and federal environmental mandates in two areas: abatement of combined sewer
overf lows (CSOs) and reduction of phosphorus levels in wastewater discharges (Sanders, 1995). A
major controversy developed in response to the lack of equity and justice underpinning the processes
by which the City initially chose to implement these strategies.
Southwest Atlanta neighborhoods, led by the Environmental Trust, a grassroots African American
environmental justice organization, joined forces to address inadequacies in the environmental
planning processes that birthed these two policies. Inequitable processes helped perpetuate a legacy
of injustice and adverse health and quality-of-life impacts on southwest Atlanta communities, dating
back to the late 1800s. The implementation of newly proposed sewage treatment policies for these
same communities in the 1990s would have only exacerbated the pre-existing issues of environmental
and social inequity already facing the community. At the heart of the citizens’ arguments against
the City’s proposals were the following questions that have relevance to all environmental and city
planning processes: (1) Did the potentially impacted community have adequate access to information
about the proposed policies?; (2) Was the potentially impacted community engaged from the outset
of the planning process?; and (3) Was there an equitable distribution of benefits vs. risks and burdens
for the proposed policy?
Through a review of historical and archival data, first person accounts, and personal interviews with
community activists and public officials, this article demonstrates through two distinct, yet related
cases, the critical role that concerned and involved citizens played to ensure equity in environmental
planning processes that impacted their quality of life. In both cases, the disproportionate impact of the
City’s wastewater treatment policies on disadvantaged, low-to-moderate income, and communities
of color were only considered when members of these communities brought the issues, “front and
center,” into the public dialogue and decision-making processes.
Specifically, this article highlights the ways in which low-income and communities of color “turned
the tables” on over a century of discrimination by effectively inserting themselves into the public
participation process and introducing the absent elements of equity and justice---positively changing the
course of wastewater policy decisions that impacted African American and low-to-moderate income
residents. Finally, this article offers important lessons for all city planners and other government
officials on ensuring that racial and class inequities are not exacerbated through the implementation
of essential urban policies.
Environmental Justice Framework
According to environmental sociologist Dr. Robert Bullard (1990), environmental racism encompasses
any environmental policy, practice, or directive that, intentionally or unintentionally, differentially
impacts or disadvantages (intended or unintended) individuals, groups, or communities based on race,
color, or ethnicity. These policies and practices include: (1) unequal enforcement of environmental,
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civil rights, and public health laws; (2) differential exposure of some populations to harmful chemicals,
pesticides, and other toxins in the home, school, neighborhood, and workplace; (3) faulty assumptions
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in calculating and assessing risks; (4) discriminatory zoning and land-use practices; and (5) exclusionary
policies and practices that limit some individuals and groups from participating in decision-making
(Allen & Neal, 1998).
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Substantial evidence demonstrates that communities of color in the United States bear a disproportionate
share of environmental hazards, in comparison to other groups (Braithwaite, Taylor, & Martin, 1999).
A landmark study, Toxic Wastes and Race in the United States (1987), published by the United Church
of Christ Commission on Racial Justice, was the first to assert that there is a correlation between
race and disproportionate exposure to environmental hazards. The findings of this study became
a catalyst for communities of color to identify environmental hazards in their communities and to
seek environmental justice by initiating struggles for clean and healthy environments where they, or
their families, lived, worked, played, attended school, or worshiped (Bullard, Mohai, Saha & Wright,
2007). Three years later, The United States Environmental Protection Agency (EPA) incorporated
environmental justice (initially referred to as environmental equity) in its programs, defining it as,
“equal protection from environmental hazards for individuals, groups, or communities regardless of
race, ethnicity, or economic status” (U.S. EPA, 1997).
At a historic gathering of grassroots environmental justice activists in 1991, the First National People
of Color Leadership Summit held in Washington, DC, seventeen Principles of Environmental Justice
were adopted. These wide-ranging principles cover issues such as protection from the production,
use, and disposal of toxic wastes to affirming the need for, “…the fundamental political, economic,
cultural, and environmental self-determination of all peoples.” The Principles also call for “…the rights
[of communities] to participate as equal partners at every level of decision-making, including needs
assessment, planning, implementation, enforcement and evaluation,” (First National People of Color
Environmental Leadership Summit, 1991) which have particular relevance to the two cases presented
in this article. Furthermore, members of the environmental justice movement have advocated for the
need for all citizens to have full disclosure with respect to the quality of their local environments and
to have full access to participation, as informed partners, in the development of decisions that impact
their lives (Sullivan & Warburton, 2003).
As the environmental justice movement has continued to take root, low income and communities of
color have challenged many cities and municipalities concerning the location and operation of waste
facilities, including sewage treatment plants (Bullard et al., 2007). Recent literature on sewage in low-
income and communities of color confirms that the typical scenario involves communities protesting
the siting and operation of sewage treatment facilities because of air quality concerns. Examples of
these practices include the cases of Camden, New Jersey neighborhoods tackling odors from a large
treatment plant and an open-air sewage-sludge-composting facility in the 1990s (Pomar, 2002), and
West Harlem communities waging a successful battle against the North River Sewage Treatment
Plant because of foul odors, toxic emissions, respiratory health of their children, and depressed real
estate values, in the late 1980s and early 1990s (Shepard, 2007).
Although less represented in environmental justice literature, published articles and case studies are
beginning to demonstrate the impact of sewage overf lows from wastewater treatment systems on
low-income and communities of color. These cases are now being documented as environmental racism
claims and civil rights actions in cities like Indianapolis, Indiana (Neltner, 2005) Syracuse, New York
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(Parsons, 2008), and San Francisco’s Bayview/Hunters Point community (The Environmental Justice
Coalition for Water, 2005). This article adds to the growing number of case studies on proactive
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community action to address sewage overf lows in an environmental justice context.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Wastewater pollution and other forms of municipal refuse (i.e. municipal landfill garbage, incinerated
waste, and waste from transfer stations, etc.) present unique challenges for communities because the
culprits are the very governing bodies that theoretically represent them. While potentially impacted
communities do not have to contend with powerful companies with deep pockets and seemingly
limitless technical resources, in these cases, the old adage, “You can’t beat city hall,” implies that
municipal challenges can be just as or more daunting for concerned citizens (Natural Resources
Defense Council, 2006).
During the 1990s, City of Atlanta public works officials ignored the environmental justice implications
of locating combined sewer overf low treatment facilities and of siting a sewage tunnel. By
compiling their own technical data on wastewater engineering best management practices, studying
environmental and health impacts of the City’s proposed plans, and raising arguments for environmental
justice, African American community groups developed and advocated for the implementation of two
alternate “citizens’ plans” that promoted more just, equitable, and sustainable decision-making than
the City’s proposals. Through the implementation of carefully planned action strategies, including
educating residents, city council members, county commissioners, planners, and city administrators
over a three-year period, the Environmental Trust and its coalition of southwest Atlanta communities
successfully inf luenced public policy decisions that challenged the injustice perpetuated through the
city’s outdated sewage system policies.
Tracing the Legacy of Injustice: The Atlanta Sewer System
Historically, the City of Atlanta developed wastewater treatment policies to meet the needs of
its growing population; however these policies often adversely impacted the health of low-income
and minority communities. As late as the 1980s, precedents set by the City at the turn of the
twentieth century were still prevalent in Atlanta’s oldest neighborhoods. While typhoid, dysentery,
and other waterborne diseases no longer plagued the city’s poor and minority neighborhoods, remnant
wastewater policies continued to adversely impact these communities through increased sewer back-
ups, f looding in homes and overf lows of raw sewage in yards, public parks, and school grounds
(Galishoff, 1985).
Before the turn of the 20th century, it was a common practice in many American cities to discharge
household excrement and industrial wastes openly into the streets. As a result of this practice,
Atlanta faced many serious health problems (Galishoff, 1985).
In the late 1870s, when sanitation districts were implemented in Atlanta, sewer services were
limited to the central business district and adjacent upper-class, white neighborhoods. Waste
transported through sewer lines from the central city’s hotel and finance centers was often dumped
above the water reservoirs and on surrounding land in Atlanta’s heavily populated poor and minority
neighborhoods (Russell, 1988).
Although all Atlanta taxpayers financed the sewage system, there was an obvious bias toward the use
of these fees to benefit the business elite and aff luent neighborhoods. Historical data indicate that
as the water supply system expanded in Atlanta, the system intentionally expanded in a north-south
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direction, serving primarily middle and upper-class whites. Meanwhile, wells supplying water to the
low-lying areas of the City, predominantly inhabited by poor whites and African Americans, were
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contaminated with sewage carried by surface runoff (Russell, 1988).
In 1911, when Atlanta’s first wastewater treatment plant was built, both stormwater and sewage
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
were piped to treatment plants. After rainfall events, overf low pipes from the plants emptied into
creeks and streams to act as safety valves releasing a toxic combination of storm water and raw
sewage, called combined sewer overf lows (CSOs). Since the early 1900s, new developments in the
metropolitan Atlanta area have been served by a separated sewer system in which sewage and storm
water are collected in separate pipes, sewage is treated and discharged into a designated receiving
stream, and untreated storm water is discharged directly into a receiving stream. The areas that
make up Atlanta’s original city limits, however, continue to primarily operate combined sewers.
In the early 1990s, 17% of Atlanta’s sewage was still collected in combined sewer systems (United
States District Court, 1997). In these areas, CSOs contribute a combination of untreated sewage
and storm water to Atlanta’s creeks and streams during heavy rainfall events. These waterways are
all tributaries to the Chattahoochee River and typically run through residential areas, school grounds,
public parks, and other areas easily accessible to citizens, particularly children.
A River in Peril, Communities at Risk
Combined sewer systems collect wastewater and storm water in a single pipe. During dry weather,
combined sewer systems transport wastewater directly to a wastewater treatment plant. In heavy
rainfall events, the volume of the mixed storm water and wastewater eff luent can overwhelm the
capacity of a municipality’s sewer system or network of wastewater treatment plants. When the
capacity of the main wastewater treatment plants are exceeded, combined sewer systems overf low
and discharge untreated sewage mixed with storm water directly into a nearby receiving creek,
stream, river, lake, or estuary (U.S. EPA, 2007).
Because of intense population growth in the 1990s, significant numbers of new wastewater customers
in the City of Atlanta resulted in an overburden of the sewage treatment system’s capacity (Seabrook,
1997b). This increased usage combined with an increased volume of storm water washing into the
system, from the construction of new roads and other impervious surfaces, caused increased sewage
spills into the Chattahoochee River from overf lows of wastewater treatment facilities, particularly
during heavy rain events (Seabrook). Sewage contamination containing hazardous fecal coliform
bacteria also entered the River and its urban and suburban tributaries from old, broken and leaking
sewer pipes, resulting from years of infrastructure neglect.
In the 1990s, the river conservation group, American Rivers, listed the Chattahoochee River as
one of the most polluted rivers in the country five times in its annual report on Endangered and
Threatened Rivers (American Rivers, 1998). Furthermore, EPA studies identified the 70 miles of the
Chattahoochee River below Atlanta as one of the five most polluted river stretches in the nation.
In the 1990s, the City of Atlanta was the single biggest polluter of the Chattahoochee River with
inadequately treated sewage, from the City’s CSO system, f lowing into the River between 60 and 80
times a year (United States District Court, 1997).
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TABLE 1. Atlanta Combines Sewer Overf low Outfall Points and Demographic Characteristics
% Pop.
178 % % %
Below
CSO at Total Population Population Population Median
Poverty
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
1-mile Radius Population Black White Other Income
Level
Clear Creek 9,390 9.1 88.8 3.9 $54,551 14%
Tanyard Branch 11,053 10.4 86.7 5.2 $50,899 13%
North Avenue 5,948 80.5 18.4 2.9 $13,865 33%
Greensferry 17,135 99.3 0.3 0.8 $15,718 33%
Utoy Creek* –
12,561 98.2 1.6 0.3 $26,360 21%
North
Utoy Creek* –
14,280 97.8 2.0 0.4 $28,256 20%
South
McDaniel
16,077 93.3 6.3 1.1 $14,045 41%
Street
Custer Avenue 10,864 54.6 33.0 28.0 $25,098 34%
Intrench-ment
5,846 87.5 11.6 36.4 $22,422 34%
Creek
*Combined sewer overf low outfalls eliminated April 1998
Source: U.S. EPA (1996). Retrieved from Landview III CD-ROM, 1992 Census data.
Not only is the River negatively impacted by Atlanta’s CSO pollution, but also Atlanta’s low-to-moderate
income residents and people of color who live in the Chattahoochee River Watershed and along major
stream corridors. Atlanta’s CSO impacted streams f low through front and backyards, school grounds,
and public parks, and these low-to-moderate income and communities of color bear a disproportionate
burden from CSOs. In 1992, seven of nine or 78% of Atlanta’s CSO outfall points (See Table 1) were
located within a 1-mile radius of communities that were at least 50% African American and had
median incomes of less than $30,000 per year (Bullard, Johnson & Mitchell, 2000).
CSO-contaminated waters contain pathogenic organisms from untreated human, animal, and industrial
waste; toxic materials like petroleum products, heavy metals, pesticides, and other organic compounds;
and f loating trash and debris washed into the sewer system (US EPA, 1995). Raw sewage carries a
variety of human bacteria and viruses. Depending on the amount and concentration of the sewage and
the mode of people’s exposure to it, these accompanying bacteria and viruses cause illnesses ranging
from hepatitis and gastroenteritis to cholera, skin rashes, and infections like giardiasis (CDC, 2002).
In addition to potential public health risks, Atlanta’s CSO problems greatly impact Atlantans financially.
Atlanta residents have had to pay for the City’s neglect of its wastewater infrastructure and for
burdens caused by the region’s growth and the associated overloading of the wastewater treatment
system. From October 1990 to March 1994, the City of Atlanta was penalized a total of $1,720,148
in wastewater-related fines (GA EPD, 1994). As of March 1994, Atlanta paid a daily fine of $7,000
for non-compliance with national and state mandates regarding the release of eff luents from five
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CSOs. A year earlier, regulatory pressure from the Georgia Environmental Protection Division (GA
EPD), concerning releases from Atlanta’s CSOs, prompted members of the Atlanta City Council to
seek solutions to improve the City’s compliance record. The Council authorized the sale of $270 179
million in bonds for the construction of five CSO mini treatment facilities. Unfortunately for the
impacted communities, equity and justice considerations were absent from the process by which the
solutions were developed. The CSO facilities solution lacked early community involvement and input,
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
and the affected communities were not convinced that it was the most effective alternative to correct
Atlanta’s CSO dilemmas. Therefore, a coalition of impacted citizens challenged the implementation of
the CSO treatment plants (Russell & Mitchell, 1994).
Case I - Utoy Creek Sewer Separation Campaign
In 1991, plans for two proposed CSO mini treatment facilities faced a great deal of community
opposition. The City’s proposal to construct the Utoy Creek CSO treatment facility met the heaviest
challenge from the impacted community. This proposed CSO facility was slated to be built in John A.
White Park, public property located in a mixed-income, predominantly African American neighborhood
in southwest Atlanta. Residents first heard of the City’s CSO plan from one of southwest Atlanta’s
City Council representatives, Jim Maddox. At a community meeting held in the home of one of his
constituents, Councilman Maddox alerted southwest Atlanta residents that a CSO treatment facility
had been designed and planned for John A. White Park. The surrounding neighborhoods were already
concerned about raw sewage and storm water previously overf lowing from an open culvert in the
park, running through areas where southwest Atlanta children frequently played, and putting them
at potential risk for illness and disease including hepatitis, gastroenteritis, cholera, giardisis or skin
rashes (Russell & Mitchell, 1994).
The Utoy Creek combined sewer system, constructed between 1900 and 1930, served approximately
5,500 homes and businesses (CH2M Hill & TOC, 2000). Here three combined sewer lines converged
into a single 35-foot open concrete culvert near the middle of John A. White Park. The channel
transported untreated, combined sewer overf lows to a discharge point in Utoy Creek. The City
proposed to remedy this problem by constructing a CSO mini treatment facility, but alternatively the
impacted communities wanted complete separation of the combined sewer system.
In the early 1990s, residents frequently complained about foul odors coming from sewage in the fork
of Utoy Creek that f lowed through John A. White Park and the accompanying open culvert. These
residents questioned the safety of park use because of its close proximity to untreated sewage. Their
concern about the placement of a mini treatment plant in the park was that it would reduce, but not
necessarily eliminate, the f low of untreated sewage. Additionally, they questioned the safety and
effectiveness of the use of the “strain and spray” method of treatment that would be used because it
would bring into community streets truckloads of chlorine to disinfect strained fecal matter (Russell
& Mitchell, 1994).
But perhaps more importantly, the CSO plant had been planned without their input, and no consideration
was given to the environmental stressors already present in the community, including the Utoy Creek
Wastewater Treatment Plant, superfund sites, landfills, and other polluting industries that exerted
undue and disproportionate burdens on community residents. In addition to the open culvert, pre-
existing CSO-related problems and nuisances identified by residents that would not be addressed in
the proposed plan included: bad odors coming from storm drains (particularly during summer or fall
dry weather conditions); rodents traveling through storm drains to above ground residential areas;
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sewage f lowing from sewer manholes; sewage backing up in toilets and bathtubs; clogged sewers
180 during heavy rains; f looding in basements and yards; street f looding; street cave-ins due to collapsing,
aging sewers; and house settling and foundation cracking possibly due to construction atop “hidden”
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
streams (Russell & Mitchell, 1994).
The Environmental Trust (Trust), a community-based African American environmental organization,
was established in 1993 by southwest Atlanta residents to fight the Utoy CSO battle (S. Marcus,
personal communication, June 6, 2001). Members of the Trust had expertise in community and
civil rights organizing, engineering and environmental health sciences, as well as other professional
fields. The Trust mobilized southwest Atlanta residents to oppose the CSO facility in John A. White
Park and the planned strain and spray technology. The Trust also joined forces with predominantly
white environmental organizations: Safely Treating Our Pollution (STOP) and Save Atlanta’s Fragile
Environment (SAFE) as well as southwest Atlanta neighborhood associations, and neighborhood
planning units who were also opposed to CSO facilities in Atlanta. The coalition invited experts from
other cities and countries to share examples of successful wastewater treatment technologies, used
in their municipalities, with the group. Based on information gathered from these exchanges and other
technical research, the Trust and its coalition members compiled examples of alternatives to the City’s
plan, performed cost-benefit analyses of each alternative, and advocated for a more environmentally
friendly and just solution than the City’s plan (S. Marcus, personal communication, June 6, 2001).
Members of the Trust and its coalition of environmental groups and neighborhood organizations
argued that sewer separation was the healthiest and most environmentally sound option to correct
the sewage pollution problem in the Utoy Creek Watershed. The coalition focused its efforts on
the Public Utilities Committee and its chair, Councilwoman Mary Davis, because the committee’s
recommendation to the full City Council would greatly inf luence the final decision. The coalition also
utilized the media to draw attention to their cause by sending them photographs of sewage f lowing
through John A. White Park, crumbling sewer pipes, and other failures of the system. For more
poignant effects, members of the Trust and its coalition held press conferences at strategic locations
where raw sewage could be seen f lowing through streets or yards in their neighborhoods (Braithwaite
et al., 1999).
The Trust used its own expertise and that of its partners to develop a plan to totally eliminate combined
sewer overf lows in John A. White Park through sewer separation. In the proposed separated system,
new, separate pipes would carry storm water directly to a receiving stream and sewage would remain
in the existing pipes and f low to a treatment facility. According to the Trust, the citizens’ plan
would cost less than the City’s proposed CSO treatment facility and would also address needed
improvements that the City’s plan did not, including the replacement of deteriorating sewer lines in
southwest Atlanta (S. Marcus, personal communication, June 6, 2001).
Former Mayor Maynard H. Jackson and his administration supported the CSO plan, providing formidable
obstacles for residents who were opposed to it. CSO treatment plants were already in use in Atlanta
and were therefore an accepted technology by city officials. The City planned to address all of its
CSO problems with the same technology, and had already expended significant design costs before the
affected community became aware of the City’s intentions. The high-intensity, citizen-led campaign
for sewer separation in the Utoy Creek Watershed continued for two years before the City of Atlanta
decided to construct a separated sewer network instead of a CSO treatment facility in John A. White
Park. The Trust, in collaboration with its partners, successfully lobbied the Atlanta City Council to
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override Mayor Jackson’s veto three times, an unprecedented feat. Former City Councilman Bill
Campbell who voted on the side of the community activists conceded that, “…the community has
181
spent considerable time and energy. Their technical expertise has overwhelmed our own expertise.
That raises questions in itself” (Blackmon, 1993). The community coalition was determined to be
involved in the CSO planning process despite their initial lack of information about it and exclusion
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
from it. It is important to note that their sustained involvement, development of alternative solutions
to the City’s proposed plan, compelling documentation of community health concerns (risks and
burdens), and persistent advocacy led to environmental justice for the impacted communities and
to the elimination of combined sewers in the Utoy Creek Watershed, thereby eliminating 2% of the
existing CSOs in Atlanta at that time.
Implementation of the Citizen’s Sewer Separation Plan
The combined sewers were completely separated in the Utoy Creek Watershed in 1998. After the city
completed the two-year, $45 million project at the park, no other non-compliance fines were levied
against the City, by the Georgia Environmental Protection Division, for CSO contamination in the Utoy
Creek Watershed (Associated Press, 1998).
A water quality assessment of the north fork of Utoy Creek was conducted in November 1999 in
order to determine if, and to what extent, water quality had improved as a result of separating the
combined sewers in the Utoy Creek Watershed. Within a year of sewer separation, the health of the
fish and aquatic insects directly downstream from the former CSO discharge had improved, and there
was an increased number of native fish species---both good indications of improving water quality
(CH2M Hill, 2000b). Moreover, the study attributed these improvements to separation of the CSO
system (CH2M Hill, 2000b).
In addition to these improved environmental parameters, residents living in neighborhoods in close
proximity to John A. White Park no longer complained about foul odors from raw sewage nor were
they concerned about the health and safety of park users because sewage contaminated waters no
longer f lowed openly through the park (S. Marcus, personal communication, June 6, 2001) .
Case II - Strategies to Halt Construction of a Sewage Tunnel
In 1994, during the time of large expenditures on sewage infrastructure and rapid city growth, the City
of Atlanta received pressure from the Atlanta Regional Commission to comply with a state order to
reduce phosphorus levels in wastewater. The City was threatened with a sewer hook-up moratorium
that could stif le further city growth if it failed to act quickly. Sewer service would also be impacted
in DeKalb, Fulton, and Gwinnett counties, three neighboring municipalities that relied on three Atlanta
sewage treatment plants to help treat their wastewater (Atlanta Journal Constitution, 1994).
High phosphorus levels in wastewater are a common result of wastewater customers’ use of household
products that contain phosphorus, incuding detergents and fertilizers. Treatment plants can remove
much of the phosphorus in wastewater, but they cannot treat and remove it all. The phosphorus
that cannot be removed is released into receiving waterways in treated wastewater (United States
Geological Survey, 2006). What is noteworthy here is that Atlanta’s increased phosphorus discharge
levels, alone, did not have environmental justice implications; however as in the Utoy Creek CSO case,
the City’s proposed remedy for addressing them did.
In this case, the same southwest Atlanta neighborhoods that were impacted by the proposed CSO
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mini treatment plant in John A. White Park publicly resisted the placement of an eight-mile, deep-rock
sewage tunnel in their neighborhoods. The tunnel would transport untreated waste from the R.M.
182 Clayton Wastewater Treatment Plant, on the north side of town, directly underneath low-to-moderate
income and predominantly African American neighborhoods, to an expanded facility at Utoy Creek in
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
southwest Atlanta for treatment.
The City of Atlanta operates four wastewater treatment plants: R.M. Clayton, Utoy Creek, South
River, and Entrenchment Creek. The City signed an agreement with the Georgia Environmental
Protection Division (GA EPD) in 1991 to treat wastewater at these facilities for phosphorus and faced
fines if it did not reduce its phosphorus releases into Atlanta creeks and streams f lowing into the
Chattahoochee River. To address the increasing levels of phosphorus releases related to population
growth and increasing fines, the City hired engineering consultants who in turn recommended the
construction of an 8-mile-long, 20-foot-wide, deep-rock sewage tunnel to connect R.M. Clayton in
northwest Atlanta to Utoy Creek in southwest Atlanta/South Fulton County (Sanders, 1995). The
proposed tunnel would be constructed 200 feet below ground and would cost an estimated $114
million. Under the City’s plan, the capacity of the Utoy Creek Wastewater Treatment Plant would also
be expanded to treat wastewater eff luents from two neighboring municipalities, DeKalb and Gwinnett
Counties, in addition to wastes from Atlanta’s north side (Sanders, 1995), thus making Utoy Creek
carry the wastewater treatment burden of predominantly white and aff luent communities who were
sheltered from the environmental impacts of their waste.
As in the Utoy Creek sewer separation case, the Trust worked in coalition with other environmental
and southwest Atlanta community groups to challenge the tunnel plan. The coalition believed that
construction of the tunnel would force predominantly African American southwest Atlanta to store
and treat waste from white aff luent communities on the north side of town as well as neighboring
municipalities. Southwest Atlanta and South Fulton County residents were concerned about locating
a sewer line the size of the proposed tunnel under their homes, the potential for methane gas releases
and explosions, and the potential reduced property values (Russell & Mitchell, 1994). These residents
also argued that deep-rock sewage tunnels could lead to further environmental problems because of
the potential for leakage to ground water aquifers as well as inf low and infiltration of water through
leakage (Russell & Mitchell).
Once again, the Trust and its coalition of partners introduced an alternative plan to the City’s proposed
plan. This four point plan included: (1) placing filters at both the Utoy Creek and R.M. Clayton
wastewater treatment plants; (2) preparing for future growth by building a modern state-of-the-art
sewage treatment plant upstream from R.M. Clayton and close to the source of population growth;
(3) recommending a modern water reuse system at the new treatment plant; and (4) placing modern
clarifiers and odor control mechanisms at the new treatment plant (Russell & Mitchell, 1994).
The Trust and its coalition gained the assistance of County Commissioner Emma Darnell whose
southwest Atlanta and South Fulton County constituents would be affected by construction and use
of the tunnel. According to Darnell, these communities would bear increased health risks. To support
her argument, she cited findings of a 1995 Fulton County Health Department study stating that
residents were already at increased risks for lung and other cancers, asthma, and other respiratory
and pulmonary diseases (Pendered, 1994). According to the study, additional burdens associated
with the wastewater treatment, including devalued properties, damaged parks and public spaces, and
unpleasant odors, would further decrease the quality of life for residents.
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On the community level, members of the Trust gathered technical data on phosphorus treatment
methods, educated residents on alternative treatment methods, mobilized community support for the
183
“citizens’ plan,” and prepared southwest Atlanta community members to debate effectively at public
meetings. Residents attended City Council meetings to follow the status of the City’s proposal,
studied documents introduced to relevant City Council committees, and thus resisted the City’s
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continuous attempts to convince citizens that the issues were too technical for them to understand
(Braithwaite et al., 1999). In 1994, in one dramatic demonstration of opposition to the proposed
tunnel plan, hundreds of residents filled the Atlanta City Council Chambers and gathered outside City
Hall to publicly voice their opposition (Russell & Mitchell, 1994).
At a critical point in the Utoy Tunnel conf lict, a 90-day moratorium on construction was proposed to
allow members of the City Council adequate time to review the tunnel proposal and phosphorus control
plan in-depth before moving forward with implementation. However, Councilman Jared Samples, who
represented low-income and African American citizens in some of the impacted neighborhoods, was
convinced by the citizens’ technical data and inf luenced by their activism. As a result, he introduced
legislation to halt the tunnel plan. With several hundred southwest Atlanta residents showing up
at a city council meeting to support Councilman Samples’ ordinance, it passed in a vote of 12 to 6,
signaling a victory for residents of southwest Atlanta and South Fulton County. After this crucial
vote, one south Fulton resident, Mike Harper, commented that if the community had been involved
from the start, the contentiousness of the issue might have been avoided (Russell & Mitchell, 1994).
Also, Fulton County Commissioner, Gordon Joyner said of some Atlanta City Council members, “They
thought this was a done deal. But they miscalculated the power of the informed citizens” (Coleman,
1994).
Not including the community from the outset, in the plans for the proposed Utoy Tunnel and the
associated phosphorus control plan, proved to be a costly mistake for the City of Atlanta. Before the
tunnel plan was halted, the City had already invested $2 million in design costs (The Atlanta Journal
Constitution, 1994). As in the Utoy Creek sewer separation case, the City did not intentionally
engage the affected communities in the planning process about decisions that impacted their lives,
and the risks and burdens to these communities outweighed the benefits of implementing the proposed
plan. These inequities prompted community resistance and advocacy. In the end, the weight of the
impacted neighborhoods’ proposal for an alternate plan, coupled with advocacy to gain City Council
support for that plan, proved to be an effective means to change public policy decisions in favor of
environmental justice.
CONCLUSION
As illustrated in the aforementioned Atlanta cases, correcting CSO problems is a major environmental
and quality-of-life challenge for urban areas that are operating with aging infrastructure and century-
old technology. To meet the growing needs of major metropolitan areas, planned growth and
development that incorporates forward thinking, the input of citizens who are impacted by policy
decisions, and principles of environmental justice, are necessary. Since the construction of the
combined sewer system in Atlanta at the turn of the 20th Century, new wastewater infrastructure
improvements and policy decisions related to the combined sewer system have not been proactive,
have not included considerations of justice and equity from the outset, have continued to be in non-
compliance with state and federal laws, and have therefore been challenged by communities, court
mandates, and state levied fines.
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184 Attempts have been made to improve Atlanta’s combined sewer system, but the associated
environmental planning and decision making processes have not always proactively involved meaningful
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citizen input. In both the Utoy Creek sewer separation and Utoy Tunnel cases, the City failed to
involve affected communities in environmental planning from the onset of the processes and did not
adequately consider the potential negative impacts of the initial proposals on local communities,
ultimately costing taxpayers millions of dollars and a great deal of time. In both cases, however,
the development of alternate citizens’ plans and grassroots tactics proved to be viable forces against
discriminatory policies (Russell & Mitchell, 1994). Solutions to wastewater infrastructure problems
which were compiled and proposed, by the affected southwest Atlanta citizens and activists working
with the community, were successful in improving the City’s compliance record for state and federal
water quality and pollution control laws, and in eliminating a disproportionate, environmental and
quality-of-life burden on low-income and communities of color.
When those making infrastructure policy decisions in cities and municipalities do not proactively
account for the social and community impacts of infrastructure neglect, weigh considerations of
fairness or equity in their decision-making, or meaningfully engage the affected communities in the
planning processes, there is potential for adverse impacts on these communities. Although not sought
intentionally by politicians, planners and other city officials in the Atlanta cases, environmental justice
was ultimately realized because citizens demanded a place at the decision-making table and made their
voices heard.
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AUTHOR’S BIOGRAPHY
Na’Taki Osborne Jelks is a community activist, West Atlanta resident, and member of the West
Atlanta Watershed Alliance, a community-based organization committed to ensuring environmental
justice in southwest and northwest Atlanta, Georgia’s African American neighborhoods. Na’Taki is
also Manager for Community and Leadership Development Programs at the National Wildlife Federation
and a Senior Fellow with the Environmental Leadership Program.
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Professor Isabelle Maret
Professor Barbara Allen
TREMÉ : THE CHALLENGES OF AN
EQUITABLE RECOVERY IN NEW
ORLEANS
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191
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
ABSTRACT
The current rebuilding of New Orleans’ neighborhoods and communities faces the dual dangers of
environmental and social injustice amplified by the slowness of the process as well as inadequate
programs for needy citizens. Devastated by the effects of the hurricane and its consequences,
weakened by improper emergency management, destabilized by uncoordinated recovery strategies,
the city is still, 3 years after the storm, in a difficult situation. Nevertheless, communities like Tremé
demonstrate the beginnings of a successful repatriation thanks to appropriate rebuilding programs
focusing on the culture and needs of the local neighborhood. By helping long term residents to return,
the Qatar Tremé Renewal Project exemplifies the effort to achieve a fair and robust community
rebirth. But even in this context of reconstruction, this case study exposes the tensions between
sustainability, justice, and recovery. Hence, in order to plan and implement an equitable revival, the
rebuilding has to be systemic and encompass the entire society, from renters to homeowners, from
musicians to school teachers - a challenge yet to be fully met by the many organizations and programs
at work in this fragile city.
INTRODUCTION
When Hurricane Katrina’s water f looded 80 % of the city, reaching the edge of the French Quarter,
New Orleans became iconic among environmental and social justice scholars and activists for its
revelatory images and the immediate uncovering of racial disparities in the U.S. Nearly three years
after the storm, questions regarding the social equity, justice, and sustainability of the recovery are
more crucial than ever. By far the largest group impacted by these failures have been the poor and
minority residents of New Orleans who were driven out of their homes in record numbers. The initial
U.S. government failures of FEMA, followed by similarly poorly organized programs such as the Road
Home program - designed to compensate owners and help with rebuilding - have left New Orleanians
looking elsewhere for help. More than 380,000 residents, homeowners, and renters were displaced
and nearly 105,000 residents1 suffered damage to their property. The underlying questions continue to
be: Who can come back? Can social justice be achieve in the recovery of this devastated environment?
How can criteria of sustainability help New Orleans communities recover? One neighbourhood in New
Orleans, Faubourg Tremé, exemplifies the challenges of this revival. Its former residents are struggling
to return, and many families (predominantly African-Americans) are still evacuated nearly three years
after the storm. One of the main issues is ensuring that opportunities are provided to minorities
so that they can successfully achieve a sustainable repatriation of their neighborhood. The choices
made in this historic older neighbourhood, echoing those made in other neighborhoods across the city,
MARET, ALLEN
inf luence its future and the equity of its resurgence.
Community revival and sustainability: why rebuild Tremé?
192 Tremé is one of the oldest African-American neighborhoods in the U.S. dating back to the late
eighteenth century when free people of color and refugees from what is now Haiti and the Dominican
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Republic populated the area (Figure 1). Annexed by the city in 1812, it soon emerged as one of the
most prosperous and politically active black communities in the U.S.
Tremé represents a treasure-trove of New Orleans’ cultural heritage. It contained much of the city’s
skilled labor force in the 19th century, including many free people of color before the Civil War (and
their descendants in later years). Tremé is also the birthplace of Louis Armstrong, Jelly Roll Morton,
and other jazz greats. Its heritage is also visible in its amazingly rich architecture, most of which
remained intact after the hurricane, but it had suffered from long-term physical neglect which was
exacerbated by the storm. Within its bounds is Congo Square, a gathering place and market where
free blacks and slaves congregated in the antebellum south, and very likely the original cradle of jazz.
Additionally, Tremé is known for vibrant second-line parades and jazz funeral traditions, performative
events that help define New Orleans’ culture as different from other southern cities (Allen, 2007).
There are also a number of historically significant museums, churches, parks and other 19th century
structures, marking it as both an incubator and living center of African-American culture in the city.
During the 19th century blacks, whites and mixed-race people lived side by side, creating the Creole
culture that defines New Orleans exceptionality today. While Tremé’s population was ethnically
diverse, segregation came incrementally as a result of political choices, as well as social and economic
pressures. The gradual spatial segregation of Tremé’s residential areas was further reinforced and
institutionalized in a local segregation case, Plessy vs. Ferguson. Homer Plessy, one of many notable
Tremé residents, was the plaintiff in this landmark case. Plessy was a Creole and “octoroon” (7/8
white), and became famous when he tried to show the unfairness of the Separate Car Law and other
early attempts at legally mandated segregation on public transportation. His unsuccessful challenge of
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193
FIGURE 1. Tremé, a challenged neighborhood in New Orleans.
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IMAGE 1. New Orleans African American Museum of Art in the Meilleur-Goldthwaite House, c. 1828-29.
Source: Isabelle Maret
MARET, ALLEN
194
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
IMAGE 2. St. Augustine’s Church, one of the oldest African American Catholic churches in the U.S., built
by Creoles and free people of color, c. 1841-42. Source: Isabelle Maret
IMAGE 3. The interior of the St. Augustine’s Church. Source: Isabelle Maret
the Separate Car Act went to the Supreme Court where the court maintained that there was nothing
unconstitutional about providing ‘separate but equal’ public and private facilities.
If Tremé was ethnically diverse and prosperous in the 1800’s, a series of urban design and planning
assaults on the community led to its decline from the 1930’s to the 1970’s. Even if some of these
projects seemed to benefit the greater city of New Orleans (for example, the Municipal Auditorium
was built over the Tremé Market, which had been the city’s 4th largest market), they nevertheless
destroyed the physical and social cohesion of the neighborhood. The Lafitte housing development, built
in 1941, housed only African-American tenants. Across Claiborne Avenue, the Iberville development
housed only Caucasian tenants. Such segregation of spaces became ubiquitous, reinforcing
segregation in a neighborhood that had once been heterogeneous. Partially as a result of the public
housing developments, aff luent residents began to sell their homes, resulting in large houses being
sub-divided into multi-family rental units, accommodating poor and working class residents.
The downward trend in property values was worsened in the 1960s by the decision to route Interstate
10 (I-10) through Tremé. The original plan, developed by the infamous Robert Moses, proposed an
elevated expressway along the Mississippi river, dividing the French Quarter from the river. While
the choice of location for the new elevated interstate saved the New Orleans riverfront, a victory for
preservationists, it dealt a divisive blow to Tremé. The highway overpass was built above Claiborne
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Avenue, the “St. Charles Avenue” of Tremé—a shady tree-lined thoroughfare lined with grand houses
and much of the area’s business storefronts, bisecting the neighborhood and Tremé (Figure 5). In
addition to effectively erasing a major business corridor, the elevated freeway challenged the many
cultural practices rooted along this avenue. Mardi Gras Indians still parade under the highway, but
the day-to-day socializing that took place under the shade of the neutral ground’s mature live-oaks 195
has since ceased. This neighborhood was cut in two (Figure 1), and the former heart of its socializing
became a noisy, polluted, and unwelcoming corridor of asphalt.
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Another unfortunate project was the building of Louis Armstrong Park which is now walled-off,
open only to the desirable French Quarter side of Tremé (Image 4). What was once a culturally
diverse gathering place lost its accessibility and at the same time, its socializing and creativity
incubator functions. However, while urban renewal created urban blight and economic hardship in the
neighborhood, it also proved a catalyst for strengthening community groups dedicated to preserving
Tremé and its traditions. The people realized that Tremé’s identity depended both on its architectural
history (Images 6-8) and cultural-spatial practices (Crutcher, 2001) (Images 9-10).
These unique cultural, social, and historic elements that comprise Tremé are what planners and
heritage conservationists have tried to protect and rebuild after Katrina. The challenge is to redevelop
a sustainable neighborhood while increasing social equity and thus also guarding the ability of former
residents to live there. Planners need to focus on approaches that incorporate concepts of justice,
equity, and sustainability into the rebuilding process. Some of the major challenges include developing
sustainable strategies to help homeowners restore their homes and helping low-income renters return
to their neighborhood. Infill rebuilding could also provide housing possibilities for residents of other
communities whose houses were totally destroyed and who choose to stay in New Orleans (though
relocate on higher ground), without impeding the return of former residents. The resurgence of Tremé
as an attractive and diverse neighborhood depends on the ability to develop equitable and sustainable
rebuilding strategies while avoiding the total destruction of the integrity of the neighborhood.
Prior to Katrina, many of the homes and buildings in Tremé were in mild to moderate disrepair,
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IMAGE 4. Interstate I-10 cutting Tremé’s community. Source: Isabelle Maret
196
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IMAGE 5. Louis Amstrong Park, a walled enclave in the Tremé neighborhood. Source: Isabelle Maret
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IMAGE 6. A typical ‘double shotgun’ house, c. 1890s. Currently being rehabilitated by the QTRP. Source:
Isabelle Maret 197
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IMAGE 7. A typical Creole cottage in Tremé being repaired by the QTRC in collaboration with the owner,
Mr. Thomas, c. 1850s. Source: Isabelle Maret
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IMAGE 8. A corner store and residence (with owner) being rehabilitated by the QPRP, c. 1850s. Source:
198 Isabelle Maret
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IMAGE 9. The Backstreet Cultural Museum has exhibits and events dedicated to preserving the performance
traditions of New Orleans including the Mardi Gras Indians, Jazz funerals, and Social Aid and Pleasure
Clubs. Source: Isabelle Maret
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199
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IMAGE 10. Example of elaborate Mardi Gras Indian costumes from the Backstreet Museum. Source:
Isabelle Maret
due to a lack of community resources. According to Census 2000, 92.4 % of the population was
African-American, with the average resident earning just $19,564 per year and 44 % earning less
than $10,000. Homeownership in Tremé was relatively low with just 22% of the households owner-
occupied. A closer examination of the housing stock shows that 69 % of the structures in Tremé were
built before 19502. More than 20% of all housing in Tremé was listed as vacant and a significant
portion of these also appeared on the City of New Orleans’ listing of blighted and abandoned properties
(Dominick, 2007).
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IMAGE 11. House with significant with damage being repaired by QTRP. Source: Isabelle Maret
IMAGE 12. New condominiums on Rampart Street which divides Tremé from the French Quarter. Source:
Isabelle Maret
The neighborhood sustained significant damage from wind and rain (Image 11) during and after
Hurricane Katrina though it received only a small amount of damage from f looding.3 An estimated
52% of the homes received “severe damage” (over $30,000) and an additional 17% received “major
damage” (between $5,200 and $30,000).4 Placing it in further peril, Tremé is currently a prime target
for both new development and gentrification because of its location on high ground and adjacency to
the French Quarter (Image 12). The houses in disrepair are good deals for investors who can afford
to rebuild them and sell them for high profits, thus making the neighbourhood unaffordable for many
of its former residents.
Although renters represented 72% of the population in 2000, their share dropped to 44.5% by
20065. Rents in New Orleans have increased dramatically since hurricane Katrina, but especially in
neighborhoods like Tremé which did not dramatically f lood and which enjoy proximity to the French
Quarter and Central Business District. Newcomers, especially middle class whites, are increasingly
settling in the city, especially in the blocks close to the French Quarter and to Esplanade Avenue.
This raises critical issues of gentrification and social equity as former residents feel that they are
being denied the right to return and rebuild their neighborhood’s identity. Similarly, if parents can’t
repatriate their homes, children will also remain displaced. And as entire families are displaced, the
social sustainability of the community is endangered. Jerome Smith6 states, “Tremé will never come
back if folks that use to make the culture happen are not here …. It can’t come back without the
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children.” The kids who used to play music after school in the streets are gone, and Jerome Smith
mentioned there is a “heavy silence” currently present in the neighborhood. Planners need to avoid
what Al Harris, another resident declares: “the rebuilding could be a physical success, but you will
lose the soul of the buildings.”
201
Justice, equity and rebuilding strategies: is the Qatar Tremé Renewal project a recipe for
success?
Tremé captures what is happening throughout the city in regards to federal aid. Nearly three years
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after the storm, homeowners are finally receiving financial assistance from the federal/state program
reimbursing them for storm related damages, the Road Home program. As of April 14, 2008, out
of the 154,946 eligible homeowner’s applicants, 106,174 had ‘closed’, with an average award
disbursed of $58,664. This shows clear progress of the reimbursement process, especially between
2007 and 2008. However, even though the money is at last coming in, New Orleans and Tremé
contain many houses waiting for repairs. Residents have to finalize their choices, find contractors,
and dig up other financial resources, which sadly, many are not eligible for. The program rules, which
were quite stringent mainly to avoid corruption and facilitate the process, did not have the expected
results. Instead of enabling the rebuilding, the bureaucratic nightmare tied to the financial help mostly
served to frustrate residents and slow down rebuilding progress. It is one of the main reasons for the
continued state of decay of many houses in New Orleans today. Moreover, the Road Home program
has different programs. The major one is geared towards helping homeowners who agree to stay in
Louisiana for 3 years after they receive assistance and have the financial capacity to rebuild quickly
or buy a new house, as the funds provided are usually not sufficient to rehabilitate a damaged home.
In Tremé, however, many residents were renters. The failure to quickly organize a program for rental
properties has potentially major consequences for the housing stock in Tremé and throughout the city.
If these houses are not fixed, renters can’t come back. The small rental property program “provides
incentives to property owners to repair their storm damaged, small-scale rental properties, and make
their units available to low- and moderate-income tenants at affordable rates7.” The first round of
closings for the rental program took place in May 2007, and only 2,693 small-scale rental properties
were awarded money across the whole city. Rental property owners need more help to be able to
repair their properties. In neighborhoods like Tremé, there is a substantial fear about seeing investors
come into the city, lavishly restore historic buildings, and make it quickly unaffordable for previous
residents to come back. Tremé is a prime location, and investors can make good deals, buying at
relatively low prices and selling them after some work. Renting or acquiring these properties will
be too expensive for previous residents. This situation is even more problematic since Mayor Ray
Nagin gave the go-ahead, on March 24th 2008 to demolish the Lafitte Housing Project. This decision
was criticized by many housing advocates: “we’re really disappointed,” said Walter Gallas, head of
the New Orleans field office of the National Trust for Historic Preservation. “We believe that the city,
HUD and HANO are making a big mistake8.” We can only hope that the redesigned mixed-income public
housing development includes choices for former residents.
Until the Spring of 2008, the recovery process in Tremé as a whole has been slow. The Office of
Recovery and Development Administration (ORDA), headed by Dr. Ed Blakely, has planned to redevelop
the North Broad Street corridor (see Figure 1), which borders Tremé, but progress remains to be
seen. A careful integration of these strategies and other efforts focused on these issues and coming,
for instance, via international support, could help redevelop Tremé as an equitable and sustainable
neighborhood. The ORDA has been willing to integrate different community rehabilitation efforts, but
it does not currently have the capacity to achieve its goals. There is, at present, a lack of coordination
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between the different strategies and groups. This integration would be key for a sustainable and
equitable redevelopment process. The international help is, in the short run, crucial to get things
going as the funds can be used quickly via foundations. The federal funds, when finally granted are
detrimentally slow and bureaucratic. Thus, international help is absolutely essential for rebuilding as
202 it quickly brings local actors the ability to efficiently achieve progress.
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Foreign Aid
From television images of people waving at rescue helicopters from their roofs to the trapped victims
living in squalor in the New Orleans Convention Center, America’s poverty and racial inequity was
broadcast around the globe. Immediately after Katrina, offers of foreign aid came pouring in to
Washington. Other nations came forward with offers of aid, both cash and in-kind. Of the $854
million offered by foreign governments to the U.S, however, only $40 million has been claimed and
used (Solomon and Hsu, 2007). While some aid was wasted due to the inability to coordinate and get
the aid to the people in a timely manner, other funds were f lat-out refused. The Bush administration
told other nations, in so many words: ‘Thanks, but no thanks.’ Whether this reaction was inspired by
pride or commitment to ‘personally’ help the city, it obstructed the rate and timeline of the recovery.
As the federal government continued to act slowly and the money was slow to arrive, the city neither
had the financial capacity to rebuild efficient basic services in a timely manner nor the possibility to
plan short and long term strategies. Nearly three years after the storm, New Orleanians suffer from
a major barrier: investment. After four planning processes the issue is not ideas or vision; but the
lack of capacity to move forward - without money and leadership, the best plans stay on the shelves.
As no remediation plan was in place when the hurricane struck the city, the rebuilding process has
been tedious and controversial. First, the Bring New Orleans Back Commission’s plan, drafted in
January 2006 without citizen participation, proposed a smaller footprint with vast parks throughout
the neighborhoods, supposed to retain f lood water. It was strongly rejected by the citizens, most
of whom were still evacuated. Then, the New Orleans Neighborhoods Rebuilding Plans, led by the
City Council, framed neighborhood plans for the 47th of the 49th most f looded neighborhoods, with
a real effort to get residents input. As the state agency, the Louisiana Recovery Authority needed a
citywide plan to distribute federal funds, the Unified New Orleans Plan was produced. It represented a
comprehensive strategy, integrating the previous planning efforts and including all the neighborhoods
of the city. At last, the ORDA (former Office of Recovery Management) took these recommendations
and identified 17th targeted investment zones to be used as catalyst for redevelopment. Most of these
targeted zones are still, in June 2008, waiting for funding to be implemented.
These figures, however, do not tell the entire story. Some governments effectively gave their donations
to outside groups, such as the Red Cross, instead. The government of Qatar made another decision:
to give $100 million to help rebuild the Gulf Coast after Katrina via the establishment of the Qatar
Katrina Relief Fund. The Fund provided direct cash assistance to groups and institutions to rebuild
homes, to provide medical care, and to pay for student scholarships to local colleges and universities.
They began disbursing the funds in May of 2006 and gave the final grants out in January 2007, $1.7
million of which went to repair two schools and five mosques serving the Muslim community in New
Orleans.
Qatar’s Ambassador to the U.S., Nasser Bin Hamad Al-Khalifa, led the effort to identify local
organizations that could efficiently and effectively distribute the funds. He solicited advice from
governors, mayors and the congressional delegations of the affected areas, as well as forming a
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distinguished advisory committee that included community leaders. The success of this careful
selection strategy is evidenced in the success of one of its grantees: The Qatar Tremé Renewal
Project.9 The aim of this project was to help low-to-moderate income homeowners return to their
houses. The project was executed by Covenant House New Orleans, taking initiative even before
funds were fully available, and even though the aims of the project were only peripheral to their
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traditional mission.
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The Qatar Tremé Renewal Project
For over 20 years, the Covenant House New Orleans (CHNO), located in Tremé, has been providing
comprehensive services to homeless and at-risk youth for the Greater New Orleans area. Their
secondary mission is the stability and preservation of families and they offer services to the community
to foster this goal as well. CHNO was concerned that many families were not moving back, or were
moving back into unsafe conditions, such as into homes with improper plumbing, leaky roofs, or even
onto streets with many vacant houses. Citizens were pressured all over the city to prove the viability
of their homes10, and this was a critical issue, especially for low to moderate income homeowners
who needed the resources to make the repairs or renters who were dependent on their landlords’
situations. There was also a looming deadline of one year after the storm set by the City Council for
owners to complete gutting and remediation lest their property be declared blighted and seized by the
city and sold at auction. This was a special concern Tremé residents, given Tremé’s attractive “high
and dry” proximity to the French Quarter. It was perceived by the community that prospective home
buyers as well as big developers were circling, looking to buy properties that were declared blighted
and available for purchase.
The CHNO proposed a project to rehabilitate 100 homes of low and middle-income families in Tremé.
They envisioned helping long-time residents, key community leaders, and others re-inhabit their
homes, thus stabilizing the community and encouraging others to return home. Their application was
accepted by the Qatar Katrina Relief Fund and they were given $2.5 million to complete the project.
At that point the CHNO decided to step out of the project as home building was outside of its area
of expertise and primary mission of helping at-risk youth. In early 2007 they formed the Qatar Tremé
Renewal Project (QTRP) as a separate entity to carry out the grant.
In May 2007 they hired a project director, Cathy Puett, a licensed social worker with a background
in non-profit organizations (Images 13-14). While having no construction experience, Puett has the
ability to build trust in the community and a practical notion of how to get things done. The QTRP
developed a simple application for homeowners, primarily to determine if they: 1) had lived in the
house prior to Katrina; 2) were within the project’s income guidelines; and 3) were unable to re-inhabit
their homes without outside funds. The projects were also approved upon the capacity of the resident
to complete the other costs if needed, and to show its stability and willingness to stay in their house
for three years. Applications were vetted by a selection committee which was a heterogeneous group,
including a school principal, representatives of the CHNO board and other local NGOs, an attorney, an
accountant, and citizens from Tremé active in neighborhood groups.
Construction began on the first homes two months later, in July 2007, lightning-speed by post-Katrina
New Orleans standards.11 The residents of Tremé welcomed Qatar’s generosity and many felt that
non-profit groups were actually driving the repatriation effort, especially given the poor performance
of federal agencies.12 The project averaged about $25,000 per home and the first few homes were
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a learning experience for Puett, allowing her to tighten the process along the way. The money spent
by the QTRP is a “soft second mortgage” that is forgiven after the owner has lived in the house for
3 years.
At first it was difficult to balance all the variables of renovating storm damaged homes, particularly
204
since other NGOs and homeowners themselves did work on the house at the same time. Since
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
QTRP had such limited funds they chose to fund work that included basic services and stabilization,
such as plumbing, electric, and house-levelling. Other granting agencies, such as the State Historic
Preservation Office, focused on the specific historic elements of the house, notably those that would
keep the structure contributing to the Historic District status of the neighborhood (Image 15). Other
NGOs, such as Rebuilding Together, relied on large groups of volunteers from out-of-town. They
typically did construction that lay people with some expert help could do: painting, f looring, some
carpentry and dry walling. A combination of rebuilding funds and volunteers, along with the owners
themselves, often working together, were needed to bring a home to habitable status—a challenge
for any project manager.
The process from application to completion was straight-forward but offered some unexpected
benefits to the homeowners and the community. The first stage of the project was geared towards
key members of the neighborhoods (teachers, police, community leaders) who had returned or plan on
returning and could act as a major strength and by example inspire other residents to return to their
community. They exemplified the possibility of a successful homecoming while bringing stability and
empowerment to the area. First, the homeowner completed a simple one-page application that was
sent to the selection committee. After careful examination, a yes/no decision was made. Next, one of
QTRP’s two part-time construction managers wrote a scope of work document, specifying the work
for bid. Puett then walked through the scope of work with the homeowner as some trade-offs and
material choices may have needed to be made. The work plan was submitted by QTRP to the Historic
District Landmarks Commission (HDLC) for preliminary approval, as Tremé is a National Register
Historic District. A licensed, insured contractor was selected among bids by the QTRP and they were
responsible for obtaining building permits and HDLC compliance documents. The contractors were
paid by QTRP at the end of every month for work completed and therefore did not disappear before
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IMAGE 13. Cathy Puett, Director of the QTRP, in front of one of the houses being rehabilitated. Source:
Isabelle Maret
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IMAGE 14. Puett at a progress meeting with a Tremé homeowner. Source: Isabelle Maret
work was completed, as often happened throughout the Gulf Coast. Hence, the residents were helped
throughout the process, the work was completed, and it was achieved by competent workers.
The fact that the QTRP managed and paid the contractors is important. New Orleans has been
fraught with contractor incompetence and fraud since Katrina and homeowners feel secure that the
QTRP process has properly identified honest, qualified contractors. Many homeowners go on to
negotiate for additional services with the same contractor and they help their neighbors do the same.
The QTRP has now produced a simple document for local homeowners on how to locate an honest
contractor, what to look for, and what to expect.
As of early December 2007, 28 homes were completed or well into the process of completion,
an amazing feat by a small non-profit. As applications come in, they will select and complete the
remainder of the 100 houses in the next year. As more and more houses are rebuilt, more applications
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FIGURE 15. Dumee-Brasco House (c. 1845) now owned by a local schoolteacher and her family is being
repaired thanks to both the QTRP and the State Historic Preservation Office. Source: Isabelle Maret
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
are coming in. The speed and energy of the QTRP, and their ability to garner community trust and
support, are commendable. They are carefully choosing the houses to rebuild in the hopes that they
will bring with them many former long-term residents and, in turn, that other residents will follow. As
Mr. Thomas13 stated, coming out of a house originally built by his ancestors, now in the process of
renovation, “this gives us the opportunity to come back to our neighborhood.” This rebuilding effort
provides energy in the neighborhood as residents not only see the changes but believe in the fairness
of the process. House by house, brick by brick, resident by resident, they know that patience and
perseverance will prove successful in the long run. The aim is thus to help former residents to come
back, and to encourage stability in the neighborhood.
CONCLUSION
To date, assessing the total population in New Orleans is a challenge. Some estimates figure that New
Orleans has about 300,000 residents, 65% of its original population (Dunbar, 2007). This number
probably includes some who have moved to the city for construction jobs or those who came to clean
up after the storm and decided to stay. The US Census Bureau estimated that 239,124 residents had
returned by July 2007, a total challenged by Orleans Parish. Nevertheless, the post-Katrina population
loss, comprised so heavily of low-income African-Americans, combined with gains from other races
after the storm, has left New Orleans both whiter and more Latino than before14. The fate of many
former residents from more damaged neighborhoods than Tremé remains uncertain. As Road Home
money has started to f low and NGOs gain momentum and utilize experience and hindsight to improve
rebuilding efforts, we are hopeful that more repatriation will occur. However, these programs have
focused mainly on homeowners, and most of the low-income renters continue to be left behind. This
issue exemplifies the challenge of equitably rebuilding, since many low income New Orleanians have
not been given the opportunity to move back. As the rents and prices of non-f looded houses sky
rocket, former residents are not left much alternative in term of accessibility to affordable housing,
which is an explicit issue of justice, equity and sustainability. Some are returning without help,
worsening the already large number of homeless people. “Recently released estimates by Unity for
the Homeless show that 150 people are living in tents under the I-10 overpass, 31 % of whom are
recently homeless because of the loss of federal rental assistance or their removal from temporary
trailers” (Liu, Plyer, 2008). To achieve a sustainable reconstruction, the recovery has to be equitable,
and embrace the whole population, from children and the elderly to energetic artists and musicians.
But in the real world of New Orleans, the reality is far from equitable, and this shows the tensions
between sustainability, equity, and justice. On the one hand, as numerous basic services, facilities
and housing capabilities are still lacking, it might not be sustainable or equitable for many low-income
citizens to repatriate the city as their quality of life could be deplorable. On the other hand, impeding
residents to come back demonstrates the tensions of justice and equity in this context as the “right to
return is in itself a claim of justice” (Brand, 2008, p3).
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Tremé is one of the critical neighborhoods that needs to be rebuilt in an equitable and sustainable way.
The vulnerability of the population before the storm makes these statements all the more meaningful,
as buildings could be bought by investors, revamped and sold to new residents, thus excluding those
208 who lived in and made this neighborhood what is was before. This neighborhood is a major facet of the
heritage and identity of the city. We can rebuild the buildings, but if we don’t allow former residents
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
to come back, the soul will be lost; we will just create a Disneyland version of the city. Social and
economic sustainability are two major goals of the rebuilding process. Housing is a key element to
rebuilding intangible entities like ‘community’ and enterprises like the Qatar Tremé Community Revival
Project show a just approach. Still, these efforts need to be linked to wider efforts by the city itself.
Appropriate infrastructures have to come hand in hand with efforts targeted at individual homeowners
and renters. Both have to be accompanied by the reopening of key community spaces. In Tremé, the
reopening of St Augustine Church, or L’il Dizzy’s restaurant has begun to pave the way. Obviously,
many other fronts needs to be addressed, too, one being to facilitate the return of renters, providing
them also with a sustainable quality of life.
Tremé still has a long way to go, but conscientious work is now being done to spark a more equitable
revival of the neighborhood that includes help for long-time residents. The community needs to be
empowered to lessen its vulnerability and tighten healthy social networks. Sustainability will depend
on the capacity of the city to provide adequate services and the return of residents. The different
strategies currently in place from the federal government, the state, the city, or international help
should be integrated so as to maximize the results. A coordination of the QTRP’s type of effort with
the city’s long term recovery plan would help re-create a sustainable community capable of retaining
neighborhoods’ historic characters and soul… what makes New Orleans unique and attractive.
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AUTHORS’ BIOGRAPHIES
Isabelle Maret, formerly on the faculty at the University of New Orleans, is now an Associate
Professor of Urban Planning at the University of Montreal. Her publications include a recent book,
Etalement urbain et friches industrielles, revers de l’idéal américain (2004), on brownfields and urban
sustainability. She is currently analyzing issues related to urban vulnerability, community resilience
as well as sustainable urban planning. GIS specialist, she continues her research on post-disaster
recovery in New Orleans. She lost her home due to massive f looding after Katrina.
Barbara Allen, formerly the Executive Editor of the Journal of Architectural Education, has written
extensively on the politics of knowledge in urban environmental activism, including a book on
environmental justice in Louisiana titled, Uneasy Alchemy: Citizens and Experts in Louisiana’s
Chemical Corridor Disputes (2003). She is currently an Associate Professor and Director of the
Graduate program in Science and Technology Studies at Virginia Tech’s Northern Virginia Campus,
near Washington, D.C..
[ENDNOTES]
1. MIT Center for Real Estate.
2. From the Greater New Orleans Community Data Center, http://www.gnocdc.org.
3. There is also evidence that at least one tornado touched down after the storm, wiping out entire buildings along a
linear path through the community.
4. From the Greater New Orleans Community Data Center, http://www.gnocdc.org.
5. Recovery Action Learning Laboratory, Final Report on the Summer 2006 – Survey for the Department of Justice’s
Weed and Speed Project, New Orleans, Nov. 2006.
6. Jerome Smith and Al Harris, residents of Tremé were interviewed by Barbara Allen and Isabelle Maret on October
18, 2007.
7. http://road2la.org/rental/default.htm.
8. Rechdahl, K., Nagin Oks demolition of the Lafitte Housing Complex, Times Picayune, March 25, 2008.
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9. The original name of the group was The Qatar Tremé’/Lafitte Renewal Project, but the Lafitte Public Housing Project
became a very contentious political issue and the group felt its work could best be accomplished by concentrating on
private housing in the Tremé’ neighborhood.
10. The Bring New Orleans Back Commission gave a deadline of May 20, 2006, for each neighborhood group to submit
a rebuilding plan. These groups have to show who can, and/or wants to come back, and how they envision the rebuilding
210 of their neighborhoods. The task is a major challenge as many residents had been and continue to be unable to return to
their communities. (Maret, 2006, p 12.)
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
11. According to many citizens and NGO representatives that we interviewed, the Road Home program, funded by the
federal government to rebuild Louisiana, has been a huge disappointment. It was mid-2007, almost 2 years after the
storm, before some people began seeing their Road Home money. Because of this, the QTRP did not count the potential
Road Home funds when assessing what resources the applicant homeowners had.
12. All government agencies are not alike. While FEMA and the Road Home program are abysmal examples of managing
aid, the State Historic Preservation Office, funded by a U.S. National Park Service program, has done exemplary work, in
a timely manner, in rehabilitating older homes in New Orleans.
13. Mr. Thomas, resident of Tremé was interviewed by Barbara Allen and Isabelle Maret on October 19, 2007.
14. See Katrina’s index, http://www.gnodc.com.
REFERENCES
Allen, Barbara L. (2007). On performative regionalism. In V.B. Canizaro (Ed.), Architectural regionalism (pp.417-426).
New York: Princeton Architectural Press.
Brand, Anna Livia. (2008). “Restructuring social and spatial justice in dialectical time.” Retrieved from final paper course
web site: http://ocw.mit.edu/NR/rdonlyres/Urban-Studies-and-Planning/11-469Spring-2007/Assignments/brand.pdf.
Crutcher, Michael E. Jr. (2001). Protecting place in African-American neighborhoods: Urban public space, privatization,
and protest in Louis Armstrong Park and the Tremé, New Orleans (Doctoral dissertation, Louisiana State University,
2001). UMI Microform 3016535.
Dominick, Steven (2007). Rebuilding Tremé – Recovery in a historic neighborhood, University of New Orleans, (Research
report under the direction of Isabelle Maret), Spring 2007.
Dunbar, John (2007, December 27). New census data shows Louisiana rebound. The Washington Post. Website http://
www.washingtonpost.com/, accessed December 27, 2007.
Greater New Orleans Community Data Center, (Data file) Retrieved from http://www.gnocdc.org.
Liu, Amy Plyer Allison (2008). Executive Summary, The New Orleans Index, (April), Retrieved from: http://www.gnocdc.
org/NOLAIndex/ESNOLAIndex.pdf.
Maret, Isabelle. (2006). Washed away by hurricane Katrina?. Journal of Architectural Education, Vol. 60, Issue 1,
September, pp15-17.
Recovery Action Learning Laboratory (2006). Final Report on the Summer 2006 – Survey for the Department of Justice’s
Weed and Speed Project, New Orleans, Nov. 2006.
Rechdahl, Katy (2008, March 25). Nagin Oks demolition of the Lafitte Housing Complex, Times Picayune, March 25,
2008.
Solomon, John & Hsu, Spencer S. (2007, April 29). Most Katrina aid from overseas went unclaimed. The Washington
Post, pp. A01.
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Talen, Emily (2008). New urbanism, Social equity and the challenge of post-Katrina rebuilding in Mississipi, Journal of
Planning Education and Research, 27; 277.
The Road Home, Building a safer, stronger, smarter Louisiana, Retrieved from http://www.road2la.org.
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Tory Foster
ART IS CHANGE :
PUBLIC ART AS A MEANS OF
ECOLOGICAL HEALING
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PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
ABSTRACT
Public art provokes dialogue about environmental and social justice by focusing attention on issues
of justice, equity, and ecological sustainability for a diverse audience. This paper explores the ability
of public art to bring attention to these critical issues and to become a force of change by educating
the public, promoting awareness of the actions necessary to stop major environmental change, and
contributing to a sense of community that can motivate citizens to care for places.
INTRODUCTION
The role of public art in addressing justice, equity, and, specifically, ecological sustainability is
worthy of examination by planners and policymakers. Public art provokes dialogue about social and
environmental issues among diverse groups of citizens. This paper explores a “sense of place” that
is tied to local history and culture, social and environmental justice, equity in the built and natural
environments, and a rigorous public process as components of successful public art projects. Some of
the ever-problematic issues raised by the subjective nature of art and the particular role of public art
as sanctioned or promoted by state institutions are also brief ly considered.
What follows is an exploration of some of the basic and evolving theoretical foundations of public
art, particularly political public art; a discussion of the role of public art in “placemaking,” as defined
by urban designer Ronald Lee Fleming; and two case studies (the “Cool Globes” exhibit in Chicago,
Illinois and the “AMD&ART Park in Vintondale, Pennsylvania) which demonstrate the varying ways in
which public art can be used to promote environmental action and restoration. Finally, the consclusion
examines the idea of art as a force for change.
Problems, Solutions, and the Potential of Public Art
Healing the wounds of the earth and its people does not require saintliness or a
FOSTER
political party, only gumption and persistence. It is not a liberal or conservative
activity; it is a sacred act. It is a massive enterprise undertaken by ordinary
214 citizens everywhere, not by self-appointed governments or oligarchies.
-Paul Hawken, Blessed Unrest (2007, p. 5)
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Environmental problems such as loss of biodiversity, habitat destruction, and climate change threaten
not only the wild plants and animals we humans think of as “nature,” but also our cultures, our
societies, and perhaps even the very existence of our species. Increasingly, those involved in the
environmental and social justice movements recognize that their concerns are tied to one another,
that sustainability must be defined in terms of justice and equity within the built, natural, and social
environments. As Hawken writes, “Social justice and attending to the planet proceed in parallel;
the abuse of one entails the exploitation of the other” (p. 22). The solutions to these problems will
depend upon shifting deeply embedded cultural norms and assumptions, and that shift will require
individuals and organizations to work together, think together, and act together. Achieving social
and environmental justice will depend on the inclusion and inspiration of many members of society;
not only scientists, politicians, and activists, but also artists, whose work often critiques and affects
cultural practices.
As artist and activist Beth Carruthers (2006) writes, “precisely because environmental problems are
rooted in cultural practices and ideologies, it is artists, immersed in world and cultural practices, who
are ideally situated to locate and develop effective responses” (p. 24). Artists, Carruthers says, have
been doing this for years. But there is now “an increasing acknowledgment of the role of art and
artists in bringing about change” (p. 24). If public art contributes to the cultural changes necessary
to save our ailing planet, then planners and policymakers should recognize its role and commit to
its promotion, not necessarily in terms of a specific agenda or ideology, but by supporting artists in
creative endeavors that promote ecological healing and inspire public dialogues about these issues.
Art can educate the public, promote awareness of the actions necessary to stop major environmental
change, and contribute to a sense of community that can motivate citizens to care for places.
However, the power of art raises a critical concern, particularly in reference to public art: who decides
what the “message” of public art should be? While the commissioning process is beyond the scope
of this paper, it is important to note that promoting artistic freedom, an open public process, and
community involvement are essential components if art is to a spark critical, uncensored dialogue. Art
may inspire conversations and it may provoke more questions than it answers, but it must be viewed
critically, for its very power to persuade and incite passion may be reason for both excitement and
caution.
While the argument can be made that public art is a worthwhile component of any strategy to address
social issues, public art can specifically address environmental problems in several ways. First, public
art can contribute to heightened individual and cultural awareness of environmental problems, and
then offer solutions: empowering rather than commanding individuals to change their behavior. In this
way, art may serve as an educational force, a way to re-perceive the world and one’s role in it.
Secondly, public art may be used as a method for environmental restoration in projects that move
beyond the science of, for example, water purification, to include the historical and cultural context of
a community and its members. As a component of community revitalization, public art may serve as
a starting point in restoring a sense of pride in place and history, which can, in turn, lead to continued
stewardship of the built and natural environments.
Artists may interpret and translate information in a way that speaks to diverse groups and individuals,
FOSTER
reaching a broader audience through an alternative means of communication. Thus, art may lead to an
increasingly inclusive exchange of information and ideas, and that inclusiveness may promote a more
just, equitable society . Furthermore, the success of movements toward environmental sustainability 215
will likely be limited if the issues of social justice and equity – which ensure the sustainability of
human affairs – are not simultaneously addressed. Public art offers a means by which to expand the
dialogue of justice, equity, and sustainability within communities.
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Public Art Evolving
A particularly useful definition of the purpose of public art can be found in Making Places: Working With
Art in the Public Realm: “Public art is a principle. A principle of improving the changing environment
through the arts. Public art is not an art form; it utilizes the arts to assist those involved with
increasing the quality of the environment” (Powell & Stevenson, 2001, p. 1). “Environment” here
refers primarily to the built environment, but that role can be expanded in terms of public art that
carries a specifically environmental or social message. In such cases, public art may serve both to
enhance the built environment and to raise awareness of environmental problems, with the hope of
changing the individual and cultural behaviors that often contribute to those problems.
The concept of art as a catalyst for social change and a medium through which to address social
issues has been steadily evolving in its contemporary incarnation since the 1960s1. The value of this
increasingly political role of art, writes Malcolm Miles (1997) is
…to initiate a continuing process of social criticism, and to engage defined
publics on issues from homelessness to the survival of the rain forests, domestic
violence and AIDS, whilst its purpose is not to fill museums… but to resist the
structures of power and money which have caused abjection, and in so doing
create imaginative spaces in which to construct, or enable others to construct,
diverse possible futures. (p. 164)
If we are to change the cultural paradigms and practices that have led to the exploitation and
degradation of the environment, and the concurrent violations of justice and equity towards all peoples,
“diverse possible futures” must develop first in our imaginations, and then guide our actions.
Public art has the potential to serve as a key component of this shift. As Suzi Gablik (1991) argues,
the urgency of the current situation requires that the effectiveness of art needs
to be judged by how well it overturns the perception of the world we have been
taught, which has set our whole society on a course to biospheric destruction.
…I believe that what we will see in the next few years is a new paradigm based
on the notion of participation, in which art will begin to redefine itself in terms
of social relatedness and ecological healing. (p. 27)
In other words, both public art and the solutions it suggests may be a part of a participatory process,
a cultural shift which begins to acknowledge the interrelatedness of both problems and people. Art
provides a medium by which to address these problems and their solutions at a visceral, emotional
level. Art is, of course, not the only or even the most important means by which to identify problems or
work towards solutions; however, one of its roles may be the provocation that leads to the discussion
and examination of issues, and perhaps even to changes in individual behavior.
Similarly, but less specifically, Powell and Stevenson (2001) state that “public art can, at its best,
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provide models and strategies that are useful well beyond the confines of what art and artists have
traditionally been considered to be about” (p. 8). If one role of art is to speak for a ravaged environment,
216 as claimed by Gablik (1991), then art may convey scientific information in order to promote the
possible changes in cultural practices necessary for environmental sustainability. Likewise, as the
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concept of sustainability is expanded to include economic justice and social equity, art may provide a
means to raise awareness of these issues as well.
The Art of Placemaking
In recent years, an increasing number of planners and urban designers have recognized the need to
“create place” in America; that is, to emphasize various elements, such as architecture, public art,
and other urban design features, that distinguish one strip-malled, subdivided place from another. As
Ronald Lee Fleming (2007) writes, the increasing number of public art projects focused on placemaking
is “evidence of a changing attitude, and the argument for increased policy attention to the problem of
how to create ‘place’ in America” (p. 13). Fleming’s is not merely an aesthetic argument, for restoring
a sense of place in a community may also contribute to the restoration of community pride and
ownership within citizens. In calling for policy attention, Fleming specifically implies that those who
make city planning decisions should be attuned to the importance of public art in shaping place.
However, Fleming says, these efforts cannot merely “pay lip service” to the importance of place,
and to be successful, planners and design professionals must keep in mind that “place is not merely
what was there [in the past], but also the interaction of what is there and what happened there”
(p. 14). People’s memories of and attachments to places involve much more than mere scenery;
the most critical public art ref lects a sense of the history and the cultural context of a place. This
history should not be confined to that which is written down in books; rather, public art projects are
informed by the unique sense of place that only residents (often only longtime residents) of an area
can describe, even if that description is often nebulous and personal. The sustainability of a place
requires equitable attention to the experiences of those who have contributed, and indeed created,
that community.
Fleming also argues that “to create placemaking art, planning is almost a prerequisite” (p. 288).
Planning for placemaking requires the collaboration of public agencies, an understanding of the
commissioning process, and a commitment to linking people to places. Fleming goes on:
Planning for placemaking has two functions: the first is to foster the
community’s investment in art as a fixture of the community. It is a process
whereby people take ownership of their surroundings, staking a claim in the
narrative that brought them to this point, and reclaiming both their visual
environment and their community memory… The second purpose of public-art
planning is to focus the art around stated urban-design objectives, which the
planning process allows the community to define for itself. (p. 288)
This echoes Gablik’s (1991) notion that public art will increasingly involve public participation in
community-building and problem-solving, and in particular, “ecological healing.” Furthermore, as
Arlene Raven (1989) writes, “Public art isn’t a hero on a horse anymore… art in the public interest
extends the possibilities of public art to include a critique of the relations of art to the public domain”
(p. 1). Involving the public in the public art process at this level may increase the likelihood that an
inclusive public art will indeed pay homage to the past and build pride in the future of the community.
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By extension, art that takes on an explicitly political purpose can involve community members in
making the changes necessary to address social and environmental problems, as is demonstrated by
the following case studies.
217
“Cool Globes: Hot Ideas for a Cooler Planet,” Chicago, Illinois
In 2001, Chicago resident Wendy Abrams read a Time magazine article on climate change, which
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warned that the Earth’s average temperature could rise by three to eleven degrees Celsius in the
next one hundred years. As Abrams (2007) writes, “It then dawned on me that this was within my
children’s lifetime. As a mother, I became increasingly concerned about the problems my children
could inherit if we don’t act now” (p. 79). Abrams became an active member of environmental groups
and began to educate herself, and eventually others, on the issue of climate change. When she spoke
with people about the problem, many felt overwhelmed by its magnitude – what could just one person
really do about a problem of such immensity (Abrams, 2007)?
Such conversations motivated Abrams to find another way to teach people about the issue, and her
idea culminated in a public art project: the “Cool Globes” exhibit which ran in Chicago from June to
September of 2007. “‘Cool Globes,’” Abrams writes, “uses public art as a medium to get people to
think about global warming and do something about it” (p. 79).
The exhibit consisted of over 120 globes, each five feet in diameter and decorated by a different
artist to represent some solution to global warming: the globes “remind people of the many solutions
to climate change they can easily adopt in their day-to-day lives, such as washing clothes in cold
water, turning down the thermostat, using compact f luorescent bulbs, taking public transportation
and walking or riding a bike” (p. 79). The globes were displayed along the Chicago lakefront, where
bicyclists, runners, museum-goers, families, and tourists could discuss and enjoy them.
“Cool Globes” calls on the public to participate, at an individual level, in addressing critical environmental
problems. These environmental changes are, as Abrams notes, potentially overwhelming, and part
of the power of this public art project is to portray solutions in a concrete, aesthetically pleasing,
emotionally appealing form. The public was both delighted and indicted by the globes, for they were
at once beautiful and provocative, suggesting the peril of ignoring the issue, even on an individual
basis. Thus the problem is not framed only in scientific or in “doom-and-gloom” terms but in terms
of positive solutions to what is ultimately a social and cultural problem (Abrams, 2007, p. 79). While
change and leadership at all levels of society - whether governmental, grassroots, individual, or
otherwise - is clearly crucial in efforts to address climate change, the “Cool Globes” exhibit served as
a starting point for informing and, ideally, empowering individuals to implement small-scale solutions.
“AMD&ART Park,” Vintondale, Pennsylvania
Like many small Appalachian communities, Vintondale, Pennsylvania, was left economically and
ecologically ruined when a coal company abandoned it. One of the most devastating environmental
effects was “a poisonous discharge of sulfuric acid and iron known as acid mine drainage (AMD),”
according to Erik Reece (2007), author of “Putting Art to Work,” an article profiling the Vintondale
project. Furthermore, according to Reece, the phenomenon is so ubiquitous in the region that many
locals don’t even notice that the streams run orange with acid – for many people, the landscape has
always looked this way (p. 51).
In the case of Vintondale, T. Allan Comp, a historic preservationist working for the National Park
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Service and specializing in industrial sites, had been contemplating the idea “of a reclamation project
that would actually call attention to the problem and its solution” (Reece, 2007, p. 52). But Comp
did not want to merely swoop in with federal funding and a plan disconnected from the local people.
218 Instead, he began talking to residents about their community. He quickly discovered that Vintondale’s
citizens were disheartened, as he wrote in his AMD&ART founder’s statement:
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These are citizens who rarely, if ever, have the opportunity to participate and
learn from any kind of cultural or arts-related activities within their own town.
There is little sense of being special in Vintondale, no particular distinction to
boast of, only constant decline for half a century – typical for much of Coal
Country, too typical. (Reece, 2007, p. 53)
And so, with public participation as a primary goal, Comp went to work. In 1995, he introduced the
idea of cleaning up the polluted creek and surrounding area, and began talking to residents about their
vision for the project. Ten years later, Comp and the community had created the AMD&ART Park, a
public art and environmental restoration project that aimed “to re-create a sense of place by honoring
the past and instilling hope in the future” (Reece, 2007, p. 52). The park includes a series of passive
treatment ponds that remove the sulfuric acid and iron (acid mine drainage) from the stream, and the
ponds themselves are treated as an environmental art piece. Park organizers created a sort of “‘litmus
garden,’ where the fall color of the trees would ref lect the color of the acidic water as it turned from
reddish-orange, to yellow, to silver green” (Reece, 2007, p. 54). Thus an environmental clean-up
project creates an aesthetically pleasing natural environment and a place in which people can actually
observe the treatment process as it occurs. At a microcosmic level, this makes the restoration of the
natural landscape achievable.
The project ref lects one of those essential elements of placemaking outlined by Fleming: it has
acknowledged and incorporated the past into a contemporary effort at placemaking and environmental
restoration. It honors the historical experience of the place, achieving what could be termed a sort
of historical justice, an acknowledgement of the complex factors that created and continue to create
the community. The project has “transformed the town dump into what the AMD&ART mission
statement calls ‘a public place in which to explore, learn, and recreate’” (Reece, 2007, p. 52). In doing
so, it has contributed to restored pride in the past, present, and future of Vintondale.
Again, public participation in the public art and restoration process is essential. Comp is adamant in
his belief that “good design must include public engagement,” and maintains that “designers who work
in the isolation of their offices when doing community projects are designing in a vacuum” (Reece,
2007, p. 53). The lessons here reinforce the emphasis on public participation already present in
much of planning literature. In particular, public participation is important when addressing issues of
equity, justice, and sustainability, all of which have many potential incarnations and interpretations.
Public art projects are unlikely to encompass all of these views even with a rigorous effort at public
participation; however, public art, especially when controversial, may serve to further the dialogue
surrounding such issues.
Other artworks within the park include a porcelain tile mosaic, created by artist Jessica Liddel, which
envisions what the park looked like during the height of the coal boom, and the Miner’s Memorial, by
Anita Lucero, in which the ghostly figures of miners are etched into a slab of granite. Both pieces pay
tribute to the history of Vintondale, and to the often intangible nature of the feelings embodied by the
vague term “sense of place”:
Through the ritual of art, these ghost miners have made the history of
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Vintondale real again. The social theorist Michael Mayerfeld Bell has written
thoughtfully about what he calls the “ghosts of place,” defining ghosts as “felt
presences” or “the sense of a presence of those who are not physically there.” 219
In Vintondale, that dormant sense of being of a place – so characteristic of
Appalachia – has been revived through a work of public art in order to celebrate
it. And by laying claim to the past, a community has laid claim to a revived
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
sense of place. (Reece, 2007, p. 55)
Are such musings too abstract, too emotionally-based, to be worthy of consideration in city or
environmental planning practice? Perhaps the most convincing argument that such projects can
provoke the fundamental pride in and concern for a place that motivates more traditional methods of
planning is that in Vintondale, after thirty years of inactivity, the citizens have decided to restart the
Town Planning Commission. While linked to many factors, this decision was at least in part inspired
by the renewed interest in citizen participation stimulated by the AMD&ART Park project.
Art as a Force for Change
A common thread pervades the literature of environmental art: the idea that it is no longer enough for
art to exist only for itself. As Sam Bower, the director of greenmuseum.org, an online environmental
art showcase, says, “we urgently need a more constructive relationship between our species and the
natural world. We can no longer afford the vacationer’s emphasis on art for art’s sake. The new
catchphrase may actually be, art has a job to do” (Reece, 2007, p. 56).
The importance of using art to convey environmental messages or to translate scientific issues in a
way that helps the public understand and care about them is highlighted by the AMD&ART Park. Sue
Thering, a landscape architect who has spent significant time studying the project, “believes it was
the artistic components of the park that brought locals – especially the men – around. As she sees
it, most people don’t get too excited about the science of water purification” (Reece. 2007, p. 57).
Rather, the men of Vintondale now have a place and an art that connects them to the past – they can
show their grandchildren what the area was like when they themselves worked the mine, the legacy
of which is at once cleansed and honored by the park. Their own history, and, because of Comp’s
focus on public participation, their ideas, are ref lected by the public art.
Thus, one potential role of art in this context may be to educate, to motivate, and to affect change.
At the theoretical level, Malcolm Miles (1997) goes so far as to indict art which is not publicly and
socially engaged as a contributor to the problem:
Engagement means either resistance, through art which is social activism, or
the building of new, perhaps very local, models of healing and ecology within
the old order – models which may be small or ephemeral but at least do not
contribute to the deafening noise. Non-engagement, as in art which makes the
city an aesthetic object, by default, is complicity in further destruction…. (p.
187)
Miles argues that art can no longer be only an aesthetic object, nor can it treat the city as such. It
must challenge cultural conventions to create alternative visions of the future. While this is just one
role for art - and a controversial one at that - such diverse alternative visions seem necessary to the
process of re-imagining issues of justice, equity, and sustainability.
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Certainly there are artists and art-viewers who will take issue with such a claim. History provides
220 numerous examples of the creative and political dangers of art that is solely ideologically driven,
especially when it is state-sponsored or -censored. Additionally, the many views of what constitutes
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
justice, equity, and sustainability may directly conf lict with one another. Art focused primarily on a
“message” may sacrifice creativity or full artistic freedom in pursuit of that message. In the special
case of public art, and in light of the many important viewpoints that can never be equally represented,
who is to decide what that message should be? The argument presented here should not be taken to
apply to all art, but rather to the more limited scope of the possibilities that art offers to both enhance
the built environment and serve as an opportunity for education and expansion, for a more inclusive
dialogue regarding the issues that affect diverse members of society. Public participation and citizen
initiative, as demonstrated by the above case studies, are ways of ensuring that, in a relatively free
society, public art can be used to raise awareness of issues, to provoke contemplation and action.
But at what point does such work become propaganda? What ensures that art will be used only for
“good” causes? There is no assurance of this, as the creation and interpretation of art is as various
as our definitions of what is good. Instead, the power of art may be acknowledged and the creative
freedom of artists encouraged; the provocation of art may lead to increased education, dialogue, and
perhaps even cultural change.
Collaboration across disciplines, between the arts and sciences, is essential if either art or science
is to affect cultural change. Carruthers (2006) points out that “artists everywhere, but particularly
in North America, are generally undervalued as participants in art/science collaborations,” (p. 27)
but T. Allan Comp (in Reece, 2007) emphasizes that he “feels more certain than ever that ‘arts and
the humanities are absolutely necessary to environmental recovery.’ Science can change the water
chemistry, but for Comp, it is art and history, combined with the science, that will ultimately change
people’s minds” (Reece, 2007, p. 57).
Planners, in their position to affect both policy and design decisions, should be increasingly attuned
to the value of public art in affecting change. Policy and infrastructure changes can only go so far in
solving environmental problems; what is also needed is a change in the cultural and social practices
that have lead to the current state of environmental degradation, injustice, and inequity. While science
can tell us what changes need to be made, art is an essential element of conveying those changes to
the public, as the “Cool Globes” exhibit demonstrates.
A recent editorial in Orion magazine (2007) suggests that “the protection of our environment will be
wholly embraced only when we understand as a matter of principle – not just by scientific evidence
– the threat to all life, and then work to enact statutes that truly protect the environment” (p. 1).
Art is one effective means by which to convey this principle. That threat to all life - which drives the
current movement towards sustainability - can only be mitigated by addressing the related issues of
environmental degradation, social injustice, and inequity.
The same editorial points out that Al Gore’s film, An Inconvenient Truth, which is widely credited
with pushing climate change to the forefront of political discussions in the United States, “was not
a government-sponsored program, nor the effort of a nongovernmental organization, nor a protest
march, nor (apparently) a campaign platform. It was a movie” (2007, p. 1) – that is, a piece of art.
Finally, write the editors,
The best art can rock our world, and that’s just what the times demand. The
shift in consciousness that so many people have called for will not, we expect,
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be led by economists, lawyers, or politicians. It will be brought about by deep
understanding, and the will to think and act out of inner conviction. And that, in
all likelihood, will be catalyzed by the arts. Art doesn’t just bring about change. 221
Art is change. (p. 1)
Those of us in the position to make planning decisions must keep this in the forefront of our minds. We
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must make it possible, through policymaking and through advocacy, for art to do its potential work.
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222
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
AUTHOR’S BIOGRAPHY
Tory Foster is a graduate student in the University of Arizona’s Planning Degree Program. She is
pursuing a Master’s degree with a concentration in Land Use and Community Development, and is
interested in the relationship between land use planning and cultural planning, among other topics.
[ENDNOTES]
1. Art has played this role in varying ways throughout human history; thus the scope here is necessarily limited.
References
Abrams, W. (2007). Cool globes: Increase awareness and inspire action against global warming. UN Chronicle XLIV(2),
79.
Carruthers, B. (2006). Art, sweet art. Alternatives Journal, 32(4/5), 24-27.
Fleming, R.L. (2007). The art of placemaking: Interpreting community through public art and urban design. London, New
York: Merrell Publishing.
From the Editors. Orion Nov.-Dec. 2007: 1.
Gablik, S. (1991). The reenchantment of art. New York: Thames & Hudson.
Hawken, P. (2007). Blessed unrest: How the largest movement in the world came into being and why no one saw it
coming. New York: Viking.
Miles, M. (1997). Art, space, and the city: Public art and urban futures. New York: Routledge.
Powell, R., & Stephenson, N. (Eds.). (2001). Making places: Working with art in the public realm. The Orangery, Back
FOSTER
Lane, Wakefield: Public Arts.
Raven, A. (1989). Art in the public interest. Ann Arbor, MI: UMI Research Press.
223
Reece, E. (2007, Nov.-Dec.). Reclaiming a toxic legacy through art and science: Putting art to work. Orion, 50-57.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
Professor Gianpaolo Baiocchi
CAN JUSTICE BE PLANNED?
EXPLORING THE INTERSECTIONS
OF POLICY, POLITICS + PLANNING
By uncompromisingly reducing poverty to a technical problem and by promising
technical solutions to the sufferings of the powerless and oppressed people,
the hegemonic problematic of ‘development’ is the principal means through
which the question of poverty is depoliticized today. — James Ferguson1
The question of whether justice can be planned, or whether exercises in planning can ever have just
outcomes is one of the perennial questions that face progressive planners. A generation ago scholars
of a critical bent made the persuasive case for “no.” Focusing on the imperatives of the capitalist
mode of production and on the power asymmetries that expressed themselves in the capitalist state,
scholars argued that there was little room for progressives to maneuver within the machinations of
the capitalist bureaucracy. 2 As Foglesong has put it:
[I]f urban planning is necessary for the reproduction of the capitalist system
on the one hand, it threatens and is restrained by the capitalist system on
the other.” 3
In the end, the imperatives of the “growth machine” or logic of the contradictions inherent in the
production of urban space in capitalism, would trump whatever small efforts even seemed possible
in the direction of redistribution or social justice. More recently, another wave of critical scholarship
has come to shape discussions around planning and the state; emphasizing the political rationalities
BAIOCCHI
and modes of expertise rather than objective interests of the bourgeoisie, scholars have to criticize
the very discourses of planning as complicit in power.4 The very categories utilized by planners
or other reformers divide and categorize populations, bringing them within the purview of a power
structure. Critical planners have, pessimism notwithstanding, nevertheless continued in their work 225
in these past decades cognizant of both the rigged nature of the game toward the powerful and the
contradictory effects that reform can have. Attention to politics and struggles over both resources
and meanings has characterized much of the ref lexive and progressive practice within planning.5
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
The more specific question before us is whether justice can be planned today, in the era of
untrammeled markets and scaled back states.6 More than that, the new rationality of government
under neoliberalism is one that tends to downplay government solutions to social problems and avoids
politics altogether; instead it calls forward an entrepreneurial citizen whose main virtues are self-
regulation, taking responsibility for his or her own problems, and a non-conf lictive partnerships with
the state.7 But the answer is not a foregone conclusion. David Harvey, whose analysis of the
capitalist city was so important for the critical reading of urban planning in the 1970s and 1980s, for
example, has recently discussed the possibilities of utopian moments and spaces – spaces of hope
— in the current era of global capitalism. He provides a philosophical justification for a dialectical
utopianism – one grounded in not only temporal possibilities (such as that of an utopian future) but
also in spatial ones as well. He calls for a return to attention to “species being” as well as a new ethic
toward nature, and deploys the image of the “insurgent architect” as a call to this long revolution of
transformation of practices and imaginations, constantly bridging movements and platforms toward
the unknown destination of utopia. Importantly, for Harvey, spaces of hope represent utopian
possibilities and need not be already realized completed projects.
All of the contributions to this volume in one way or another address issues related to possibilities
for justice in the current moment. Some clearly try to offer the outlines of “spaces of hope,” such as
Foster’s essay on public art, while others discuss the way the context blocks such possibilities, such
as Fluet and Krogman’s essay on oil production in Alberta. Others still discuss normative imperatives,
like Baxamusa’s essay on redistribution and sustainability, which discusses the theoretical roadmap
that might take us closer to this destination. In this closing commentary to the volume I offer a
reading of these essays for what they say and imply about such possibilities, and connect them to
some of the distinctive features of the current context. I group the essays roughly into two groups:
those that address the limiting features of the current global moment, and those that address some
of the alternatives available that re-insert a political dimension to planning.
Globalization and the Scales of Democracy
The first distinctive feature of the current era is the heightened pace of globalization. Many scholars
and activists have faced these changes with alarm, and the list of ills attributed to these changes is a
long one. For our purposes, one salient feature is that globalization has produced a tension between
the idea of the state as a territorially circumscribed regulatory body and democracy as a form of free
political association.8 To put it differently, the scales of democracy and that of increasingly relevant
modes of regulation have become mismatched. As the state “hollows out,’ it does not just “wither
away’ but its functions are displaced into newer or altered lower- or upper-level state institutions,
where new dynamics of political contestation emerge. In many settings the local urban state has
emerged as an especially important site, because it is more porous than national states and is situated
“in the conf luence of globalization dynamics and increased local political action based in civil society”
(Keil 1998). Yet, despite the increasing autonomy and importance of the local vis-a-vis the national,
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both local and national agents operate in a context increasingly constrained by global contexts.
226 Many of the essays in this volume address, in one way or another, the way that these scales constrain
the local, and thus, room for agency at the local level on behalf of justice. Fluet and Krogman explore
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shortcomings and barriers to reforming the oil and gas industry in Alberta toward a system of
integrated resource management that is more equitable. They point to the “structure of property
rights and tenure systems, particularly for petroleum resources … [that] perpetuates the various layers
of organization across which undesirable environmental impacts must be addressed.” They discuss
the limited potential for reforms to address cumulative impacts, public land management values, and
ecological values. One environmental organizational respondent commented after participating in an
integrated land use initiative that did not inf luence any land use decisions,
The answer that we came up with is that we’re not on the same political playing
field, that the power dynamics are not even. So, ultimately, when the real decisions
are to be made---not the ones that were made around the table, where all of us
were…arguing lots but eventually we came to things we all agreed on—but those
were not the real decisions. The real decisions came afterwards, and they were
based on where the true power dynamics lie. (emphasis mine)
In a sense, the location of the “true power dynamics” as out of reach of local actors also pervades the
piece by Julie Hermesse, Cosmology and Disaster, which explores the cultural and social production
of disasters and continued vulnerability in Guatemala case study. Tropical Storm Stan passed through
communities in the Altiplano, but the essay underscores the point that much of the human suffering
was not a “natural” consequence. “If a catastrophe can be primed by a natural phenomenon, what are
the cultural, social, political and economical factors that make a particular human community more
likely to fall in a state of catastrophe?” As she discusses, “deforestation, construction of inadequate
dwellings and occupation of zones of high risks are the product of many years of exclusionary economic
models” which have their roots in a the history of Guatemala as a dependent country.”
Masa’s piece, “Beyond Land Reform,” describes a cooperative in the Philippines that acquired lands but
had difficulty in establishing food security despite winning land rights, which by themselves were “not
enough to mitigate impoverishment.” A series of constraints and difficulties manifested themselves
despite the good intentions of local actors. Notably, the challenges came from strained relationships
with local bureaucracies: “Both the Department of Agrarian Reform and the Department of Labor and
Employment did not properly carry out the community development process by overlooking community
planning’s important role.” The piece offers an important reminder that local political games matter
tremendously, and that local political contexts cannot be ignored in community planning.
The pieces on Tremé, in New Orleans by Isabelle Maret and Barbara Allen, on Paso del Norte, Texas,
by Timothy Collins, Sara Grineski, and Martha Flores and on Atlanta, Georgia, by Na’Taki Osborne
Jelks are also instructive as they turn our attention to the United States. Each piece details the ways
that environmental injustice, racism, and infrastructural inequalities are intertwined with particularly
pernicious consequences for communities of color in the United States. Although we may be tempted
to think of globalization having consequences “out there” in the developing world, many of the same
changes have taken place in the United States as well. As in much of the developing world, the
national state has scaled back its commitment to welfare provision over the last two decades, which
has increased the burden on local governments. Over the same period, property taxes and local
finances have become politicized in racially divisive ways. In the U.S., municipalities depend on local
tax revenues to provide local services to a very high degree, and because these taxes disproportionately
BAIOCCHI
come from property taxes, they institutionalize the inequitable distribution of funds, because property
taxes are only distributed at the localities where they come from. Poorer citizens thus are likely to
live in poorer municipalities, where the tax base is lower, and where schools, community development
227
funds, and social services are funded much less. Even with federal intervention, the disparities in
access to resources for services like public education are wildly divergent across districts.9 Adding
to these inequalities are institutional arrangements that facilitate municipal secession. The breaking
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up of a larger municipality into autonomous suburbs with their own tax base essentially creates
incentives for White Flight.”10
These dynamics have contributed to the emptying out, and de-funding, of core cities in favor of
suburbs, so that today virtually all metropolitan areas have impoverished inner cores and wealthier
suburbs, and are more racially segregated than before.11 Today, urban areas have higher tax rates but
are less funded than surrounding suburbs. And too often middle-class and upper-class whites have
rallied around property taxes, a discourse that often has pernicious racial overtones.12 The reigning
ethic that has emerged in the last decades is that, as Robert Reich has put it “if inhabitants of
another area are poorer, let them look to one another. Why should we pay for their schools?”13 These
dynamics form the background against which planners and activists must contest with to create more
just spaces, more just distributions of resources and infrastructure, and the ending of environmental
racism. As all the pieces suggest, these dynamics are deeply entrenched.
Or as Isabelle Maret and Barbara Allen put it on the piece on New Orleans, “More than two years after
the storm, New Orleanians suffer from a major barrier: investment. After four planning processes, the
issue is not ideas or vision; the major lack is the capacity to get going.”
Inserting Politics back in: Challenging the New Ideological Landscape of Governance
The rollback of government has not been the only change impacting planning practices in recent
decades. The meaning of government has changed as well. The ideological landscape – the discursive
parameters shaping what is thought to be possible has also shifted. A new lexicon around questions
of government has emerged, characterized by a now familiar constellation of concepts: good
governance, NGOs, civil society, grassroots action, decentralization, sustainability, local innovations,
social entrepreneurship, among others. The new common sense around governance has partially to
do justifications for the rollback of government; “big government” is not able to cope with today’s
problems, “bloated bureaucracies” and “red tape” are part of the problem, and so on. But it has also
to do with a new rationality of government that emphasizes horizontal linkages, societal creativity,
governance and participation. Governance, a new networked pattern of coordination of collective
action, has replaced government.
Central to this new common sense is the importance of participation. Though officially endorsed by
International Development agencies like the UN since the 1970s14, “participation in government” has
been advocated with particular vigor by a wide cast of characters since the late 1990s as panacea
for an ever wider set of ills. Critical scholarship has followed, not far behind, taking challenging the
“heroic claims” made on behalf of participatory approaches15, while taking participatory boosterism
to task for failing to address questions of power, inequality, and politics.16 More broadly, scholars
have begun to point to participation, and participatory prescriptions in particular, as part and parcel of
neoliberal governmentality. Absent from the new common sense is a recognition of the importance of
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politics. Because participation in government is seen as an alternative to conf lictive mobilization and
disruption, it has been argued that politics has no place in governance.
228 Several of the essays in this volume challenge the normative bases of this new development discourse.
Foster’s essay, Art is Change, discusses the potential for and role of art and artists in transforming
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
cultural practices and ideologies that are the root cause of environmental problems. She argues for
the importance of public art, and in particular, what she describes as placemaking art, art which
It is a process whereby people take ownership of their surroundings, staking
a claim in the narrative that brought them to this point, and reclaiming both
their visual environment and their community memory from the homogeneous
corporate forces and banal local development besieging the contemporary
landscape.
She describes two such projects, the “Cool Globes” project in Chicago, and the “AMD & ART Park” in
Vintonvalle, Pennsylvania. In both projects, “Public participation and citizen initiative, as demonstrated
the above case studies, are ways of ensuring that, in a relatively free society, public art is used to
raise awareness of issues, to provoke contemplation and perhaps action,” calling for “Planners, in
their unique position to affect both policy and design decisions, should be increasingly attuned to the
value of public art in affecting change.”
Redistribution and Sustainability, by Murtaza Baxamusa, which argues that redistribution of power
is a primary condition for sustainability, presents a conceptual framework for linking empowerment,
engagement, and equity in sustainability. The article by Karin Bradley, Ulrika Gunnarsson-Östling, and
Karolina Isaksson, on Swedish environmental discourses similarly calls for a challenge to apolitical
discourses that avoid discussing inequality. Lint’s essay, in a similar vein, Addressing Needs as
Rights, gets to the heart of the issue. Though the citizens in the piece are very much impacted by
the processes described above, by the rights violations of communities affected by dams, “global
economic and political factors are entrenching poverty and inequality and reducing the agency of
citizens to inf luence the processes that affect their lives” (Eyben, Harris, & Pettit, 2006, p.1), she
imagines an alternative. In the piece, she examines a rights-based approach to development, through
the case study of communities and dams in Cambodia and the struggle between development and
community rights. A rights-based approach, she writes:
requires tackling the real issue at hand - structural issues of power and
inequality, that has not been the central focus for development models of the
past.
The paper describes how a particular NGO, the Mekong Community Rights Project (MCRP), which
works on the protection and restoration of river-based livelihoods in Northeast Cambodia, has drawn
upon the rights-based approach, which, according to Lint, has the following elements: “links to the law,
inclusion, participation, empowerment, and good governance.” Calling for “the process of mapping the
power dynamics should be the fundamental starting point of designing advocacy strategies involving
issues of poverty, inequality and injustice.”
All four proposals – for public art, for empowerment/sustainability, for a more political discussion
of the environment, for rights-based approaches to development —find entry points into the current
discourse on good governance, but all subvert it in significant ways. They all connect with seemingly
“unobjectionable” elements of the discourse - no one would be against sustainability, or rights, for that
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matter – and push them to logical conclusions that open up spaces for politics and “tackling the real
issue(s) at hand.” These are very much calls for struggles at the interstices of power, but it is perhaps
there that spaces of hope can be opened up.
229
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230
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AUTHOR’S BIOGRAPHY
Professor Baiocchi, a Professor of Sociology at Brown University, received his MS and his PhD from
the University of Wisconsin-Madison. He has achieved international recognition for his scholarship
in comparative political sociology and is the editor of Radicals in Power: The Workers’ Party and
Experiments in Urban Democracy in Brazil and the author of Militants and Citizens: The Politics of
Participatory Democracy in Porto Alegre.
[ENDNOTES]
1. James Ferguson, 1994. The Anti-Politics Machine: Development, Depoliticization, and Bureaucratic Power in Lesotho.
((Minneapolis: University of Minnesota Press). 256
2. See Michael Dear and Allen Scott, 1981. Urbanization & urban planning in capitalist society. (London: Routledge).
3. Richard Foglesong, 1986. Planning the Capitalist City. Princeton University Press. Pp 20.
4. Racco, M. and Imrie, R. (2000) ‘Governmentality and rights and responsibilities in urban policy’, Environment and
Planning A 32: 2187-2204. For a recent statement on governmentality, see for example, Peter Miller and Nikolas Rose.
2008. Governing the Present. (London: Polity Press).
5. See Marris, P. “Planning and Civil Society in the Twenty-first Century.” In Cities for Citizens: Planning and the Rise
of Civil Society in a Global Age. Edited by M. Douglass and J. Friedmann. New York, NY: John Wiley, 1998, pp. 9-18.
Friedmann, J. (2002) “City of fear or open city?,” Journal of the American Planning Association, 68(3), pp. 237 – 243.
Progressive Planning Reader 2004, 2000. See also Fainstein, S. “Planning Theory and the City” in Journal of Planning
Education and Research, Vol. 25, No. 2, 121-130 (2005)
6. See Peck, J. (2001) ‘Neo-liberalizing states: thin policies/hard edges’, Progress in Human Geography 25 (3): 445-455.
See also Peck, J. and Tickell, N. (2002) ‘Neoliberalising space’, Antipode 34: 380-404. Brenner, N. and Theodore, M.
(2002) ‘Cities and the geographies of ‘actually existing neoliberalism’’, Antipode 34: 349-79
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7. See Ong, Aihwa and Stephen Collier (eds.) 2004. Global Assemblages:Technology, Politics and Ethics As Anthropological
Problems. Oxford:Blackwell.
8. See Held, David, Anthony McGrew, David Goldblatt, and Jonathan Perraton. 1999. Global Transformations: Politics,
Economics, and Culture. Stanford: Stanford University Press. 231
9. Kozol, Jonathan. 1991. Savage Inequalities. See also, Feldman, Bob. 2003 “Savage Inequalities Revisited” in Dollars
and Sense.
PROJECTIONS 8 JUSTICE, EQUITY, AND SUSTAINABILITY
10. Reich, Robert. 1992. The Work of Nations. Vintage. Pp 278.
11. See Massey, Doug and Nancy Denton. 1998. American Apartheid. Harvard UP.
12. Edsall, Thomas. 1992. Chain Reaction: The Impact of Race, Rights, and Taxes on American Politics. Norton. See
also Mike Davis. 1995. “The Social Origins of the Referendum” NACLA Report on the Americas, Vol. 29, 1995.
13. Reich, Robert. 1992. The Work of Nations. Vintage. Pp 278.
14. The UN endorsed participation in two documents in the 1970s: Popular Participation in Development (1971) and
Popular Participation in Decision Making for Development (1975).
15. Cleaver, Francis. (2001). “Institutions, Agency, and the Limitations of Participatory Approaches to Development.”
In Bill Cooke and Uma Kothari (eds.) Participation: The New Tyranny? New York: Zed Books: 597.
16. See Harriss, John, Kristian Stokke, and Olle Tornquist. 2005. Politicising Democracy: The New Local Politics of
Democratisation. Hampshire, UK: Palgrave McMillan; Hickey, Sam and Giles Mohan, eds. Participation: From Tyranny to
Transformation: Exploring New approaches to Participation in Development. London: Zed Books, 2004; and Bill Cooke
and Uma Kothari (eds.) Participation: The New Tyranny? New York: Zed Books.
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