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Urban Ecological Enclosures: Conservation Planning, Peri‐urban Displacement, and Local State Formations in China


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Across contemporary China, city governments are unevenly territorializing peri‐urban villagers’ land and housing by creating new urban ecological conservation sites. I analyze this emerging form of what I call ‘ecological territorialization’ through three interrelated spatial practices: comprehensive urban–rural planning, peri‐urban ‘ecological migration’, and the distribution of institutional responsibility for conservation site financing, construction and management. Detailing this triad of territorializing practices renews attention to the relationship between conservation classifications that justify state intervention, uneven displacements of people from rural land and housing, and site‐specific capitalizations that collectively consolidate urban government control over rural spaces. These practices emerge stochastically as state, private, and semi‐state institutions capitalize on conservation projects in the context of legally and constitutionally underdefined land use rights and ecological land designations. In the current post‐socialist moment of urban ‘greening’, these practices are key to producing frontiers of land‐based accumulation and extending local state control across the peri‐urban fringe. Urban ecological enclosures not only remake city‐level state power but also shape rural people's relationships to land, labor and housing.
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This research was supported by fellowships from the Center for Chinese Studies, Chiang-Ching Kuo Foundation,
Confucius China Studies Program, Fulbright-Hays DDRA, Institute of International Studies, and Social Science
Research Council. I presented an early version of this article at a workshop hosted by Guangzhou University and
South China Normal University called ‘China in an Era of Mobilities’ where I received valuable feedback from
Heidi Østbø Haugen, Junxi Qian, Paul Statham and other participants. I also presented a version of this article at
Stanford University with the Stanford Center for East Asian Studies and am grateful for comments from Matthew
Kohrman, Adam Liebman, Tim McLellan, Yan Long, Jean Oi, and Andrew Walder. Many thanks for comments on
earlier versions of this article from You-tien Hsing, Juliet Lu, Andrea Marston, Jeff Martin, Chris Mizes, Lana Salman,
Kristin Sangren, Michael Watts and Alex Werth. Finally, I thank three anonymous IJURR reviewers for their insightful
Conservation Planning, Peri-urban Displacement, and
Local State Formations in China
 
Across contemporary China, city governments are unevenly territorializing
peri-urban villagers’ land and housing by creating new urban ecological conservation
sites. I analyze this emerging form of what I call ‘ecological territorialization’ through
three interrelated spatial practices: comprehensive urban–rural planning, peri-urban
‘ecological migration’, and the distribution of institutional responsibility for conservation
site financing, construction and management. Detailing this triad of territorializing
practices renews attention to the relationship between conservation classifications that
justify state intervention, uneven displacements of people from rural land and housing,
and site-specific capitalizations that collectively consolidate urban government control
over rural spaces. These practices emerge stochastically as state, private, and semi-state
institutions capitalize on conservation projects in the context of legally and constitutionally
underdefined land use rights and ecological land designations. In the current post-socialist
moment of urban ‘greening’, these practices are key to producing frontiers of land-based
accumulation and extending local state control across the peri-urban fringe. Urban
ecological enclosures not only remake city-level state power but also shape rural people’s
relationships to land, labor and housing.
Ecological migration (EM) (shengtai yimin), often conceived of in relation to
large-scale ecological conservation and social displacement in China, has become a
central aspect of land enclosure. An official state term, EM refers to the involuntary
migration of people as part of government efforts to conserve or restore degraded lands,
ecosystems, as well as multi-scalar ecological engineering projects. The practice
emerged in the 1990s and 2000s, often in relation to anti-desertification and grassland
management policies in China’s North and West. In its early phases EM entailed large-
scale movements from grasslands to concentrated settlement areas, particularly in
Inner Mongolia (Xun and Bao, 2007) and Tibet (Yeh, 2009).
Debates about the environmental benefits surrounding large-scale EM have been
waged between scholars who are clear proponents of state intervention for conservation
purposes (Liu and Wang, 2008; Wang et al., 2010) and those critical of the social and
cultural losses that accompany large-scale migratory displacement (Banks et al., 2003;
Shi et al., 2007; Foggin, 2008; Seki and Hu, 2011). The bulk of extant scholarship
discusses EM through large-scale conservation efforts to mitigate environmental
degradation (Bao, 2006; Liu and Wang, 2008; Wang et al., 2010). These eorts generally
entail the mass movement of entire communities to new settlements constructed
©     
through government support. There has been comparatively little assessment of the
numerous small-scale displacements brought about through urban ecological protection
zoning projects across peri-urban China. I coin the term peri-urban ecological migration
to refer to processes of displacement from land and housing activated when a peri-
urban area is designated for ecological protection. While peri-urban displacements
through ecological zoning are not officially referred to as EM in state policy, some
urban-level government officials use EM to describe the peri-urban displacements
caused by urban ecological protection projects. Utilizing this term in relation to urban
ecological protection displacements indexes similarities between large-scale EM
across China and the much more numerous small-scale displacements in peri-urban
China, which aect millions of peri-urban villagers dislocated in the name of ecological
protection. Moreover, it points to interconnections between social displacement in the
name of ecological protection land designations across scales and state territorialization
of predominantly rural spaces.
I use the term ecological territorialization to refer to the ensemble of spatial
practices through which control over land is wrested in the name of ecological protection.
While this term may be readily applied to the large-scale ecological protection
projects in China’s North and West, noted above, in this account I detail a specific
configuration of ecological territorialization in China’s urban areas, wherein peri-urban
EM, environmental planning, and state-private governance relations figure centrally.
I argue that ecological territorialization constitutes an emerging form of enclosure
wherein urban governments extend their reach over peri-urban regions. China’s peri-
urban fringe does not resemble patterns of industrial agglomeration or suburbanization
common in the history of Western urbanization. Instead, China’s peri-urban fringes
developed over decades of post-socialist transitions including decollectivization (Oi,
1992), township-village enterprise industrialization (Buck, 2012), and rural–urban
migrations shaped by uneven mobilities linked to household registration benefits
and restrictions (Chan, 1994; Naughton, 1995; He, 2007; Wu and Ye, 2016). These
created socially dierentiated desakota-like landscapes across cities where rural land
designations and agricultural production are interspersed with urban land designations
and urbanized areas (Sui and Zeng, 2001; Xie et al., 2007). Of key importance for this
account is conceptualizing the ‘peri-urban’ in China as patchworks of urban and rural
governmental jurisdictions.1
Land in China is a socialized asset with constitutionally demarcated divisions
between rural and urban land. Even though all land is socialized and therefore belongs
to the state, control of urban land is generally vested within city government hierarchies,
while rural land belongs to the village government personified in village collectives,
Chinese Communist Party (CCP)-appointed cadres, and township governments.2
In both law and the PRC constitution, the particular state institutions and actors in
control of rural and urban land are underdefined, which leads to structural ambiguities
surrounding land governance and land use (Ho, 2001). Under such conditions, urban
governments have sought for decades to appropriate rural land for urban development
(Ma, 2004; Hsing, 2010; Lin, 2014), while peri-urban villagers have developed village
land for farming, licit and illicit developmental enterprises, rural housing and public
facilities (Oi, 1992; Unger, 2002). Incorporating large swaths of rural land into urban
areas has occurred through urban development, economic and jurisdictional zoning,
and intra-governmental competition (Hsing, 2010; Cartier, 2015). With the rise of urban
land values over the last decade and shortage of urban land for development, peri-urban
1 For additional context on China’s urban development, peri-urban features, or comparisons with urban development
processes in the industrial West, see Ma (2005), Walker and Buck (2007), Wei and Zhao (2009), Lin (2014) and
Abramson (2016).
2 See Ho (2001), Hsing (2010), and article 2 section10 of the CCP constitution for clarification on the ambiguities of
socialized land in China.
village land close to cities has become extremely valuable, contributing to forced land
acquisition and migration (Sargeson, 2013; Chuang, 2015). In this account, I illustrate
conservation-oriented spatial practices crucial to urban government enclosure of peri-
urban village land. Since the central state placed restrictions on making ‘development
zones’ (kaifaqu), from around 2010 onwards, the practices I discuss have become key to
facilitating urban government enclosure of peri-urban village land and conservation-
oriented development.
This article is organized as follows. I first discuss the interconnections between
territorialization and enclosure, highlighting how ecological forms of territorialization
are central to contemporary processes of enclosure across China’s peri-urban fringe.
This corroborates scholarship that discusses how classification, displacement and
capitalization are integral to enacting control over space. Then, I discuss the methods
on which this article is based. Next, I empirically illustrate the key findings by
detailing interrelated spatial practices of ecological territorialization that facilitate
urban ecological enclosure: (1) comprehensive urban–rural planning with overlapping
functional land use designations, such as ‘ecological’ and ‘agricultural’ land; (2) peri-
urban EM involving the state-led displacement and concentration of peri-urban villagers
and the uneven incorporation of village land and housing; and (3) assigning responsibility
to state, semi-state and non-state entities to finance, construct and manage conservation
sites. Respectively, these spatial practices justify state actions under logics of ecological
improvement, forcefully and unevenly displace rural people, and consolidate control
over rural land through ecological construction (shengtai jianshe) projects. I conclude by
highlighting future directions for research, which include greater attention to political
economic forces and environmental justice. Additionally, I reflect on the importance
of multi-sited research that attends to a range of social actors involved in conservation
Ecological territorialization and enclosure
Under broad calls for ‘building an ecological civilization’, written into the CCP
constitution in 2012, China’s central state is redirecting economic development in
conjunction with environmental conservation. In China’s 13th five-year plan (2016–20),
the central state mandated that 20% of land within city jurisdictions be zoned for
ecological protection (UNDP, 2016; Interviews DX 2016, 2017; FTL 2017; LNT 2017).
Such mandates are emerging alongside projects of nation-wide ecological protection
zoning (Lü et al., 2013) in response to unbridled reform-era economic growth (Economy,
2010). Urban environmental protection policies are being put forward simultaneously
with the remaking of urban planning practices through the 2014–20 National New Type
Urbanization Plan. This urban planning directive promotes urbanization by increasing
the number of rural migrants to cities, particularly medium-sized cities (Wang et al.,
2015). As part of this new policy direction, the 2014–20 National New Type Urbanization
Plan integrated urban and rural planning (chengzhenhua guihua), including rural areas
surrounding the city (Bray, 2013; Wilczak, 2017). Throughout this planning process
cities must maintain static ocial figures for land areas designated for ‘construction’
and ‘agriculture’ (Zhang and Wu, 2017), which poses challenges for making new urban
conservation sites and developing land.
Land development has been the primary mode of accumulation for municipal
governments operating under structural conditions that drive accumulation from land
rents. Local governments transformed into profit-oriented interest groups in the wake
of early 1990s financial decentralization and the 1994 tax assignments that gave city
governments soft budgetary constraints. Since then, land became the primary means
through which local governments generated revenues for service provisioning. From the
early 2000s, the bulk of cities’ extra-budgetary revenues were generated through urban
development (Hsing, 2010). Territorial annexations of surrounding rural land came to
include vast swaths of village land and smaller cities (Ma, 2005; Cartier, 2015). Although
peri-urban land was incorporated in many dierent ways during the reform era (Shue,
1988; Naughton, 1995; Chung and Lam, 2004; Ma, 2005), within the last decade much
of this land-based accumulation occurs through urban ecological zoning. New modes
of city-government-led peri-urban territorialization have emerged under conditions
of stronger central state fiscal control that limit development zones (kaifaqu)––the
predominant form of urban-based accumulation from the early 2000s––and mandate
new requirements for urban–rural comprehensive planning. Central state mandates
for urban conservation translate into opportunities for city governments to continue to
generate revenues from land-based transactions through urban ecological protection
Under these conditions, the relationships between comprehensive urban–
rural planning, peri-urban EM, and the assignation of institutional responsibility for
conservation finance, construction and management––each of which I detail in this
article––became key to municipal state territorialization of and accumulation from
peri-urban village land. The confluence of conservation mandates and new urban
planning practices that incorporate rural areas facilitates the enclosure of village land
and the concentration of rural people into resettlement housing complexes. Ecological
territorialization marks a shift in the ways urban governments extend socio-economic
control over the surrounding countryside.3 The spatial practices I discuss are departures
from accumulation practices of recent decades, wherein city governments obtained
control over extra-budgetary revenues through administrative extension into peri-
urban jurisdictions (Chung and Lam, 2004; Ma, 2005) or through rural enterprise
taxation (Oi, 1992). As I discuss in this article, municipal government enclosures of
villagers’ agricultural, housing and construction land enrolls state, semi-state and
private institutions. To purchase or lease land, these institutions form mutualistic
contractual relationships that facilitate the remaking of land designated ‘rural’ and
‘agricultural’ for multiple and overlapping economic and conservation functions.
The enduring focus of EM scholarship on large-scale environmental projects
(Foggin, 2008; Wang et al., 2010; Chen et al., 2014; Wang et al., 2015) overlooks the
ubiquity of these recent city-level practices that consolidate control over peri-urban
village land. Directing attention from the relatively few large-scale EM displacements, to
the literal millions of small-scale EM displacements, refocuses EM scholarship towards
what is undoubtedly among the world’s largest conservation-oriented displacement by
population. There are few publicly available statistics, which makes estimating those
dislocated a challenge. But, by way of example, Kunming, a single city with a population
of approximately three million, has already dislocated over 200,000 villagers with many
more awaiting dispossession.4 China has over 15 cities with populations of between nine
and 28 million. According to China’s 13th five-year plan, the country plans to increase
the percentage of the urbanized population from 52% to 60% by 2020. To achieve
this goal, an additional 8% of the rural population would need to move from rural to
urban areas, which entails bringing tens of millions from China’s rural population into
the folds of urban life. The scale of incorporation of village land is staggering as most
medium and large sized cities include numerous sub-counties and villages within
urban jurisdictions (Fan, 1999). Additionally, I want to draw attention to the spaces
opened up through ecological land classifications, as well as the mass dislocation and
centralization of village housing that occurs through territorializing peri-urban villages
3 My usage of the term ‘ecological territorialization’ emphasizes how ecological spatial practices facilitate
territorialization. This differs from Hung’s (2020) usage, which emphasizes discursive and nonlinear materializations
within environmental discourses and green social movements.
4 The figure demarcating the number of dislocated was corroborated through interviews with municipal government
officials from 2014 to 2017. For additional government sources on the extensive number of planned dislocations,
see Kunming Government (2013).
and transforming village land into ecological protection areas. In the context of China,
designating land ecological sanitizes and normalizes social displacement while paving
way for conservation-based development and local state formation. These phenomena
present an opportunity for reconsidering the relationship between territorialization and
enclosure, which are intimately interconnected.
In the Marxist political economic tradition, the process of ‘enclosure’ is often
theorized with reference to British land reforms starting in the sixteenth century. In
this literature, enclosure figures as a necessary precondition for capital accumulation.
Marx called this process ‘primitive accumulation’, which he detailed through the
privatization of the commons, the proletarianization of labor and global colonization
(Marx, [1867] 1976: 874–6; [1939] 2005: 459–516). Following Marx, enclosures became
a central topic of political economy, which E.P. Thompson (1975) theorized in relation
to the formation of agrarian capitalism and an industrial proletariat. Thompson shows
how legal land classifications denoting private property relations are crucial in justifying
English enclosures. More recent engagements draw on the concept ‘accumulation
by dispossession’, which reformulates primitive accumulation to emphasize that
accumulation requires ongoing processes of social and material displacements (Harvey,
2005; 2010; Glassman, 2006; Perreault, 2013). For instance, many works have detailed
the relationships between capitalist expansion and migration, thereby illustrating how
frontiers of displacement form in conjunction with uneven development (Massey etal.,
1993; Hyndman, 2000; Black, 2018). Other works highlight the role of capitalization in
shaping concurrent processes of enclosure and resource extraction, wherein land is
unevenly territorialized with continuously emerging frontiers of accumulation (Watts,
2012; Ballvé, 2012; Levien, 2012; 2018; Klinger, 2018). In contemporary China, processes
are at play through peri-urban ecological conservation projects that mirror many
accounts of enclosure: loss of access to agricultural land, forced migration, (semi-)
proletarianization and land territorialization.
‘Green’ or ‘sustainable’ development classifications have been shown
to contribute to processes of dispossession, capital accumulation and uneven
territorialization by generating sustainability fixes in which capital finds a sink in
‘green’ projects (While etal., 2004; Yeh, 2009; Corson, 2011; Fairhead et al., 2012; Pow
and Neo, 2013; Knuth, 2016; Lin, 2017; Rodenbiker, 2017, Chung et al., 2018). As Chung
et al. (2018) detail, urban sustainability and the production of green spaces in China
are inextricable from the landed interests of municipal governments, rural villages and
real estate-oriented entrepreneurialism, thereby making government intervention in
land management and rural communities of key importance. Technical approaches
to socio-environmental management enroll state, corporate and public actors, the
configuration of which shapes how rural land and housing are incorporated into urban
conservation and the migratory trajectories of dislocated villagers. Peri-urban EM
emerges from a range of practices by which villagers’ land and housing are included
in government projects of conservation and resettlement. Forms of peri-urban EM
are site contingent. In what follow, I will point to some of the dierential ways in
which peri-urban EM occurs, thus building on studies that show internal migration
as crucial to urban processes (Beaverstock, 2002; Schiller and Çağlar, 2009). I also
build on scholarship that problematizes the contingent spatial formations through
which enclosure operates (Vasudeven et al., 2008) by highlighting ensembles of
territorializing practices emerging through ecological protection zoning. In this vein, I
point to the productive facets of ecology in shaping land-based accumulation, local state
formations, and dierential forms of incorporation into urban conservation zones. This
highlights how ecological classifications, displacements and capitalizations condition
land enclosure. This triad of spatial practices justify displacement, unevenly displace
people, and consolidate control over newly designated ecological areas. Therefore,
I contend that it is the intersections of territorializing practices, undertaken in the
name of ecological protection, that conditions the field of possibility for land-based
accumulation and local state formation.
Although I consider territoriality as ‘spatial strategies to consolidate power in
a given place and time’ that bring about ‘the occupation and domination of a territory’
(Hsing, 2010: 8), I do not conceptualize ecological territorialization to be the result
of coordinated or masterminded sets of practices led by a monolithic state. Instead,
as Chung and Xu (2016) point out, China’s state is multi-scalar and environmental
governance traverses dierent levels of state power, each with its own set of interests
often causing alliances and tensions across institutional arenas. Urban governance in
China and the extent of city-regionalist administrative reach are historically configured
through the interplay of top-down central state mandates and bottom-up processes of
implementation initiated by local governments (Li and Wu, 2018). As these authors point
out, the CCP and central government maintain ultimate authority. Yet underspecified
central state mandates leave room for interpretation and local implementation. Hence,
I detail a Janus-faced state, one that is centrally coordinated, locally adaptive and self-
interested, striving to follow mandates, while simultaneously generating opportunities
for accumulation. Spatial practices that include the creation of measures and documents,
peri-urban EM, and additional institutional support for capital mobilization figure
centrally in ecological territorialization.
I use the term ‘spatial practice’ in a way that crosses the fields of geography
and urban planning. Geographers consider spatial practices through the social
production of intersecting spatial modalities including Euclidian spaces, symbolic
spaces, representations of space, and the material reproduction of daily life (Lefebvre,
1991). The field of urban planning considers spatial practice through practical work that
planners do in designing, organizing, financing and managing the built environment
(Glaeser, 2011). Therefore, spatial practices in this article are constituted, in part, through
technical apparatuses to justify land enclosure, such as the comprehensive urban–rural
master plan, peri-urban EM mobilizations and narratives, and the enrollment of private
institutions for financing, constructing and managing land. I illustrate this ensemble
of spatial practices as ‘coordinated but dispersed set(s) of regulations, calculative
arrangements, infrastructural and technical procedures, that render certain objects
or flows governable’ (Watts, 2012: 443). Each city has its own configuration that is
historically and geographically contingent based on their own political economic and
institutional relationships (Peluso and Watts, 2001; Death, 2013: 184) mediated through
national discourses, policies and site-specific practices of conservation.5 However, each
configuration entails rural land territorialization with highly uneven outcomes for
villagers (Chuang, 2015; Shin, 2016) contingent on how land is valuated and compensated
(Zhao and Webster, 2011; Rodenbiker, 2019). Hence, in this distillation, I detail spatial
practices central to urban ecological enclosures that hold across China’s cities.
The content for this article draws on 15 months of fieldwork over three years from
June 2014 to August 2017 during which I adopted an ethnographic approach grounded
in the practices and experiences of peri-urban conservation zoning. This research
involved 15 villages across three cities: Chengdu, Kunming and Dali. These three cities
are all located in southwest China. They vary drastically in terms of population, area
and regional political economies. Collectively, they represent a range of possibilities for
peri-urban conservation zoning. Detailing practices common across cities of dierent
5 Projects of restoration in essence are projects of defining the limits of what is included and excluded in the
historical ecological reconstruction of place, a process of establishing what is included and excluded from
ecological baseline estimates, which is often fraught by decisions on what to include and exclude (Alagona etal.,
2012). In my cases the history of agricultural land use is commonly excluded, which bolsters narratives of peasant
deficiency (Day, 2013; Schneider, 2015) thereby justifying mass displacement.
size and location departs from the single case study paradigm, prevalent in studies of
urban China, thereby reinforcing applicability beyond these cities.
Within each city I conducted interviews and observations across peri-urban
conservation sites, resettlement housing complexes and peri-urban villages at dierent
stages in the process of dislocation. Identifying common features within and across
sites entailed interviews and observations conducted at conservation and resettlement
sites where relocation was underway and sites where relocation was already complete,
interviews with the managers of institutions involved, and interviews with municipal
government ocials across bureaus. Sites of resettlement are not visually distinct from
vernacular landscapes. Therefore, locating sites of resettlement involved triangulating
between interviews with local government, villagers and resettlement migrants. My
methodological approach to researching sustainability projects in practice samples from
the ‘top down’ and the ‘ground up’. The experiences of diverse actors involved provided
crucial insights into how sustainability practices aect those enrolled in sustainability
projects, as well as environmental governance relations that emerge through planning
and implementing conservation projects.
In total, I interviewed 223 peri-urban villagers, 130 resettlement complex
migrants, 90 local government ocials across the city, township and village levels, 15
representatives from companies involved in building conservation infrastructure, and
23 ecologists involved in conservation planning and delimiting historical ecological
records.6 My multi-method approach provided a range of data sucient to pinpoint
common features across cases. I triangulated across sites of conservation displacement,
resettlement and construction to achieve a multidimensional understanding of urban
ecological protection zoning. While configurations of actors and institutions are site
specific and conjunctural, over the course of research I identified spatial practices
consistent across cases.
Spatial practices
The vice president of the environmental planning bureau loomed over the
city map several meters in diameter, pointing to green markings of varied shades. He
explained that these green areas on the map were sites where the city was creating
urban ecological protection sites as part of their comprehensive urban–rural master
From the perspective of environmental protection and development, we have
to restrict and control space … This is a form of control from the top … Then
secondly, we try to improve the ecology. Previously the [rural] area was in
total disarray [luanqibazao], but now we pushed all that mess out of the area.
We moved out over 50,000 mu7 of farmers from their agricultural land and
homes … Multiple bureaus do the planning, then we distribute the areas to
institutions in order to carry out ecological construction. But, if you would
have seen it 10 years ago, the whole area was a total mess. It had all sorts
of agricultural fields, houses, animal husbandry … you name it (FL Kunming,
October 2016).
This quote from an environmental planner highlights key processes of urban ecological
enclosure, including comprehensive urban ecological planning, which entails distributed
planning across multiple bureaus, peri-urban EM and the allotment of institutional
responsibility. In the following sections I detail these interconnected spatial practices.
6 I use pseudonyms and alternative place names throughout to protect the anonymity of those involved in this
research. I provide months that correspond to interviews, but do not provide exact dates of to avoid exploitation
by cellular locational tracking technologies.
7 6.07 mu is roughly equivalent to one acre. 50,000 mu is roughly 8,240 acres of land.
Comprehensive urban–rural planning and overlapping functional land zoning
Comprehensive urban–rural planning, beginning with the 2014–20 National
New Type Urbanization Plan, synthesizes plans across multiple jurisdictions. During
interviews, high and mid-level municipal state ocials and environmental scientists
consistently stressed the importance of comprehensive planning (duoguiheyi)
within urban–rural planning. This involved the consolidation and synthetization of
multiple kinds of city and township-level planning, which were previously conducted
independently. Through this centralized process, urban and rural planning became
part of a single municipal master plan. This included land use planning, environmental
protection planning, economic planning, tourist planning and other forms of planning.
Despite its somewhat sprawling and inherently contested nature, the comprehensive
planning process invests the power to determine final decisions over planning in the
municipal government hierarchy.
First, each urban and county bureau involved drafts up parts of the plan
independently based on each bureau’s assigned tasks. During collective meetings over
the course of a year, they discuss and synthesize preliminary plans and assessments.
Within this process concerted eorts are taken to respond to multiple central state
policies, including the mandate to maintain consistent fixed measurements of
agricultural land within the city jurisdiction and more recently policies mandating
the maintenance of static total amounts of construction land across cities and villages
within city limits.8
Comprehensive planning also includes central mandates for ecological redlines
and control lines, and other conservation site demarcations within the city region (Lü
et al., 2013). However, the demarcation of ecological land (shengtai yongdi) or ecological
protection land (shengtai baohuquyu) are not legal demarcations, thus making these land
use types legally underdefined. In lieu of legal definitions, there are general guidelines
set forth by the Ministry of Land and Resources for ecological constructions that
include developing ecological principles and education, strengthening national resource
surveillance, strengthening land use through functional zoning, building ecological
service systems, and land conservation (Deng et al., 2009; Central Government, 2015).
This ambiguity lends itself to disputes within the planning process.
Disputes over land zoning are frequent in these multi-bureau meetings. When
disputes arise, environmental planning bureaus often interject to ensure ecological
protection areas remain part of the plan at the rate of 20% land area coverage mandated
by the central state. This indicates an increase in power for environmental bureaus, which
have historically been relatively weak within the municipal governance structure9. At the
top of this distributed yet hierarchical pyramid are municipal government cadres. These
appointed party ocials approve the comprehensive plan, though rarely participate in
multi-bureau meetings. If there are disagreements about the form of the plan after a
year of meetings, the municipal cadres make final decisions, reconciling any outstanding
internal conflicts. Hence, the centralized planning process delimits which forms of land
use designations are allowed and which fall outside of the plan, both within the built-up
regions of the city and the surrounding rural areas. This planning process subsumes
county-level planning within the urban government hierarchy.
In the planning process, municipal bureaus make concerted eorts towards
zoning ecological protection areas with overlapping land use designations, which
allows them to respond to central state conservation mandates while producing
8 For a detailed account of key national land designation policies, such as ‘balancing farmland occupation with
farmland reclamation’ (zhanbu pingheng), which is a no net loss of agricultural land policy and ‘linking up the
increase in urban construction land with the decrease in rural construction land’ (zengjian guagou), which is a no
net gain of construction land policy, see Zhang and Wu (2017).
9 This also mirrors central government bureau reconfigurations since 2018 as the powers of multiple ministries,
particularly the Ministry of Land Resources, are invested in the newly created Ministry of Ecology and Environment
new avenues for generating land-based revenues. Within the planning processes,
multiple overlapping functions (gongneng) are ascribed to parcels of land demarcated
for ecological protection. This centralized planning process therefore consolidates
functional planning and introduces overlapping functionalities wherein ecological
land use designations overlap with, most commonly, limited development use, tourist
land use, or agricultural land designations. In some cases, this is coordinated through
tiered protection zoning. In these cases, first tier zones, within the plan, are supposed
to have no human activity or development. In second tier protection zones there is
limited development designated within the comprehensive plan. In third tier zones,
developments are also limited, but less restricted than tier two. Government ocials
describe second tier and third tier zones as having ‘cautious’ or ‘chosen’ developments,
allowed only after approval in the comprehensive plan.
This comprehensive planning process has become a way to develop land
without having to designate it as ‘construction’ land (e.g. housing or commercial
land uses), a land use designation that would be legible to the central government
and therefore subject to scrutiny. Instead, ecological land designations (shengtai
yongdi) allow for ‘ecological construction’ (shengtai jianshe) to occur. That is to say,
environmental land designations have economically viable adjuncts demarcated in
the comprehensive master plan via overlapping functional land uses. This conjoining
of, for instance, ecological functions with agricultural or tourism functions, open land
to the political economy of ecological construction. In my interviews, overlapping
functional zoning was frequently discussed as a way to ‘optimize’ (youhua) the spatial
layout of the city (F.L. Kunming, September 2016; Y.J. Kunming, October 2016; X.P.
Chengdu, September 2016; X.J. Dali, February 2017; J.Y. Dali, February 2017). In the
process of making the comprehensive plan, government bureaus fold in previously
existing green spaces into new ecological site designations, thus transforming existing
designations into new multi-functional sites. These overlapping spatial designations
open sites to be economically productive within the bounds of the comprehensive
plan (Z.J. Kunming, November 2016; P.L. Dali, January 2017; T.Y.L. Chengdu, February
2017). Ecological protection sites are ‘developed’ in a variety of ways, including
wetland parks catering to urban tourists, resettlement housing, and heritage museums.
But given the ongoing process of development, sites may even look like empty fields
or dilapidated villages filled with rubble and items left behind by displaced residents.
There are three important aspects to stress about the process of comprehensive
urban–rural planning. First, the planning process enables city governments to determine
land use activities across urban and rural spaces, which extends unprecedented control
over counties and villages. This occurs through a mechanistic approach to socio-
environmental management that facilitates the demarcation of overlapping land use
functions within which ecological land classifications figure centrally. Within this
approach to nature, urban modernity and ecological civilization can be ‘built’ through
technical management, modelling and planning. However, determining the plan’s
content is not sucient to bring the plan into action. As I will show in the following
sections, under fiscal constraints and with a dearth of regulatory and managerial
capacity, city governments rely on multiple institutions.
Second, assigning overlapping functionality within conservation sites allows city
governments to maintain nationally mandated amounts of construction and agricultural
land within their jurisdiction, while following central mandates for making ecological
protection areas. However, the demarcation of basic agricultural lands (jiben nongtian)
does not necessarily indicate that land is agriculturally productive, meaning land that
produces food for human or animal consumption. Instead, even building agriculturally
‘unproductive’ wetlands is officially counted towards ‘basic agricultural land’. It is
crucial within the comprehensive planning process that the sum total of ‘construction’
land in the city jurisdiction remains the same.
Finally, the plan operates as a spatial apparatus that legitimizes new forms of
land control. As a document, made collectively by multiple government bureaus, it
remains internal to the state, with only several city-scale maps and broad descriptions
shared with the wider public. The internal character of the plan adds an additional layer
of ambiguity as persons without access to the master plan are unable to independently
verify plan contents. Given the veiled existence of the comprehensive plan as an
internal state document, it becomes a mechanism to exert spatial claims regarding the
boundaries of ecological protection and therefore claims over land. The production of
the comprehensive master plan, therefore, is a spatial practice that justifies land and
housing dispossession on the peri-urban fringe. As the municipal government hierarchy
extends control over village land villagers are unevenly displaced.
Peri-urban ecological migration
I obtained a rare glimpse of the comprehensive urban–rural master plan as I
sat in the oce of a high-level municipal ocial in Kunming. He thumbed through the
book-sized plan to point out several maps of villages inside conservation zones. Flipping
pages back and forth from the small-scale map to a city-scale map, he pinpointed a
village slotted to move into high-rise resettlement apartments and said:
The village and the city are not the same. The city is [concentrated] like this,
but villages are really dispersed [fensan]. Their surface area is really wide.
So up until now, they have not matured [chengshu]. Regarding this form of
governance, it is not only a calculated plan, it is also a structure of the city and
countryside in which we take the dispersed and concentrate it vertically. When
the scale [of incorporation] is very large it is much easier … We have tried
to move villages to a point [qiancunbingdian] which involves concentrating
many villages together. This is one way we transform villages. The other way
is to export their labor. We take dispersed built areas and concentrate them
through ecological migration in order to deal with them [lai chuli] (Y.Y. Kunming,
February 2017).
Another high-level municipal ocial discussed peri-urban EM and the transformation
of rural land as forms of environmental and social improvement:
When there is an ecological protection development we have to move villages
out, … [otherwise] they will become like a village-in-the-city [chengzhongcun].
We give them an improved living situation. Previously the village did not have
comprehensive planning. Wherever the village headman said to build, there
something was built. With this kind of comprehensive planning and planned
construction, their living situation improves (Z.L. Kunming, March 2017).
Across municipal government ocials and planners, there is a pervasive sense
that facilitating peri-urban EM initiates socio-environmental improvement. However,
the reality is that villagers are differentially affected by how they are incorporated
into conservation sites. That is to say, divergent forms of uneven incorporation into
conservation projects shape patterns of peri-urban EM.
Villagers’ experiences of peri-urban EM are shaped by whether village land is
purchased outright with a one-time payment, leased by a bureau of the city government
or an institution approved by the city, or consolidated into village shareholding
corporations that lease land to institutions and distribute shares of the profits.10 These
dierent forms of incorporation elicit non-uniform peri-urban EM as agricultural land,
village housing construction land and village housing are enrolled into projects of peri-
urban conservation.
Those forced to sell land receive one-time capital influxes that facilitate petty
entrepreneurialism and inter-village land lease markets. Land leases provided annual
capital payments that spur transitions from self-directed agricultural production into
migratory labor, wage labor or into agrarian managerial sectors. This contributes to the
gendered and age-contingent hollowing out of villages as those in prime working age seek
work opportunities elsewhere (Wu and Ye, 2016). Corporatized villages most frequently
receive the highest amount of compensation and the highest quality resettlement housing.
Villagers from corporatized villages incorporated into conservation sites often
used the phrase ‘moving into richness’ (banfuyou) to discuss the process of becoming
relatively wealthy from land and housing compensation. These are essentially
instances of accumulation through dislocation as villagers are able to accumulate
through processes of land and housing valuation and compensation linked with socio-
environmental displacement. The social cohesion and market-oriented organization
of village collectives facilitates relatively favorable contractual relations under
state-led ecological protection zoning. Village corporatization proved a key factor
in maintaining a degree of control over land and often facilitated close-proximity
migrations to housing on or near village construction land, which allowed their new
homes to double as a site of social reproduction. These findings echo Zhang’s (2015)
claim that village corporatization facilitates movement into the capitalist employer
class. Table1 summarizes the general relationships between the means of land and
housing incorporation into sites of ecological protection and patterns of peri-urban
EM. This table communicates general patterns within which there is much variability,
including dierent capacities to cope with transitions shaped by individual class and
social positionality, as well as discrepancies between village land holdings, housing
spaces, and the amounts and forms of compensation obtained for them. Each of these
forms of village incorporation shape social dierentiation and constraints within which
villagers navigate socio-spatial transitions (Rodenbiker, 2019). Despite these dierences,
it is possible to generalize common features across cases.
Each form of peri-urban EM entails a process of prohibiting small-scale
agriculture on village land and territorializing villagers’ housing space. The spatial
  Relationships between the means of land and housing incorporation into
sites of ecological protection and patterns of peri-urban ecological migration
Means of Incorporation into
Ecological Protection Area Relation to Land and Housing Patterns of Peri-urban Ecological Migration
Individual Land Sale Sale of land conveyance;
immediate or eventual sale of
original rural housing; one-time
capital compensation for land and
housing sales.
High variation in amounts of land and housing
compensation; high levels of compensation promote
petty entrepreneurism and resettlement complex
landlordism; low compensation contributes to poverty
and psychological stress; urban proletarianization in low
quality resettlement housing is common.
Land Lease Land lease to an institution
ranging from state, semi-state,
and private; villagers may or may
not retain original rural housing.
Annual land lease payments vary across sites; loss of
access to agricultural land forecloses independent
agricultural production, stimulates inter-village land
leases, labor migration, semi-proletarianization,
working-age flight from villages, and agrarian wage
Corporatized Village Land
Sale or Lease
Sale of land conveyance or
land leased to an institution
ranging from state, semi-state
and private by a corporatized
village with centralized financial
management; may or may not
retain original rural housing.
Highest amounts of compensation; ‘moving into
richness’ (banfuyou); close-proximity displacement into
better-than-average resettlement housing; localized
entrepreneurialism with capital from corporatized
village assets; new relocation housing doubles as sites
of social reproduction.
10 As I will discuss more below, leasing and allocating land to institutions also generates fees for municipalities that
can be used for urban services (see Lin, 2009; 2014).
concentration of villagers in resettlement housing complexes (anzhifang), and
withdrawal of their access to agricultural land, opens up rural land for conservation-
oriented development. City governments control village land through moratoriums on
village agricultural production inscribed into the land sale or lease. As villagers move
into new housing, city governments obtain control of rural housing, rural construction
land, and agricultural land.11 This process does not instigate a net gain or loss of either
rural construction or agricultural land according to ocial figures.
As part of the process, land and housing contracts are drawn up between the
village council and leasing institution. When these contracts are signed, rural areas
can undergo ecological construction. Most ecological constructions involve forms of
perennial vegetative cover, such as wetlands, aorestation or grassland, as designated
by multifunctional land demarcations within the urban–rural comprehensive plan. This
allows for conservation eorts to overlap with commercial enterprises analogous to the
dual-function forests that serve both environmental and economic functions (Zinda et al.,
2017). The process of enacting spatial control over village land entails removing villagers’
control of land through lease or purchase and ‘restoring’ or constructing an ‘ecological’
landscape. By concentrating otherwise dispersed village housing, under which rests
village housing land (a form of rural construction land), city governments are able to
territorialize rural construction land, without increasing the sum-total of construction
land within municipal jurisdictions.
Resettlement complex housing often resembles urban high-rises in architectural
form. Such housing is frequently built on rural housing construction land or agricultural
land that has had its land designation swapped with a site previously designated as rural
housing construction land, which is then designated agricultural land. This migratory
transition to high-rise resettlement apartments often occurs in close proximity to
original, more dispersed, village housing land. Thus, village construction land is used to
maintain land quotas. In most cases, the municipal government also requires acquisition
of village housing. Rural housing is owned by villagers, but the land on which it is built is
owned by the collective. Short-term use of this land can be allotted to villagers, but it is
not the villagers’ private property (CCP Constitutional Amendment 10, 1982; Ho, 2017).
Despite this, village housing compensation and valuation are key sites of struggle and
sources of social dierentiation between those villagers who obtain high compensation
versus those who do not. The compensation for each is site specific and contingent
on land and housing’s market value, the bargaining capacity of the village council, the
council’s relationships (guanxi) with bargaining institutions, and higher levels of local
Some villages are able to obtain high prices for land and housing that provide
them with multiple units in resettlement complexes, essentially ‘moving into richness’
through migrations that facilitate upward social mobility as middle-class resettlement
complex landlords. For many, this oers dual sources of employment as migrants enter
into other forms of labor in addition to renting out apartment units. In contrast, other
villagers are undercompensated for land and housing far below market prices. In some
cases, they are not compensated for land. Many undercompensated villagers lament
moving into poorly constructed resettlement units and entering migratory labor streams
as they transition out of agricultural production under precarious structural conditions.
Those undercompensated and newly proletarianized experience severe psychological
stress as they transitioned into high-rise resettlement.
Land leases to municipal bureaus or other institutions entail varied migratory
processes. Land leases, across cases, remove control of agricultural land from the village
collective. De facto control then resides in either a bureau within the urban government
11 For an account of all types of ‘village’ land designations, see Zhang and Wu (2017). In this article, I highlight only
those essential to illustrate the processes of urban ecological enclosures.
or an institution. The agricultural land remains legally part of the village, but under
lease by an institution. In cases of villager housing removal, this can also include village
housing land, but not in all cases. Villagers may either retain their housing, but without
access to agricultural production, or their housing may be purchased in which case they
will be concentrated into resettlement complexes. The municipal government’s control
of land hinges on wresting land control from village councils through lease or purchase.
Much of the decision-making power in villages rests with the CCP-appointed village
party cadres and the village party secretary. These actors are positioned to help protect
collective interests (Cai, 2003). They also stand to benefit from village land transactions.
It is well documented that village cadres capitalize on land for housing and construction
purposes. Outside of the allegiances of village government, strategies for protecting
village interests are deployed by village shareholding groups and elite civil society
organizations (Mattingly, 2016). These village shareholding groups can breed strong
shared interests across the village, binding the interests of villagers under collective
management (Cai, 2003: 673; Zhang, 2015).
As noted above, cases of peri-urban EM in villages that have formed village
shareholding corporations tend to produce the most socio-economically favorable
outcomes. In most cases, corporatized villages are able to maintain a degree of control
over village land as the corporatized collective leases the land to a private enterprise,
semi-state institution or a municipal state bureau. Much like the case of land leasing
outside of village collectives, noted above, members of shareholding groups are then
able to maintain a shared income stream through assets derived from land. Many village
collectives are able to obtain relatively well built resettlement housing, including single-
family standalone housing units (bieshu), and higher than average payments for land
leases. These often facilitate labor transitions that utilize the domestic space of the
standalone home to remake labor. Village shareholding resettlement areas resemble
patterns of agglomeration clusters organized around service provisioning. Resettlement
homes are often turned into service shops, teahouses, rural-themed restaurants and
guesthouses (nongjiale), and other spaces of leisure-based tourist provisioning to
capitalize on the newly made conservation site.12 This form of proximal migration,
mediated through the village shareholding company, often facilitates the highest degree
of village autonomy across forms of incorporation.
While removing villagers is a key spatial practice to open land frontiers,
financing, building and managing ecological land are key to enacting control over these
village spaces. In the following section I turn to the third spatial practice: assigning
institutional responsibility.
Assigning institutional responsibility
Under financial constraints, city governments are unable to provide the capital
to obtain villagers’ land, build resettlement housing, and construct ecological protection
infrastructures without institutional support. Additionally, city governments can
generate revenues by leasing land use rights to institutions. The process of village land
and housing territorialization is site specific and contingent on obtaining the necessary
capital for acquiring village land and building resettlement housing. The municipal
government assigns a series of dierent institutions responsibility for financing, building
and managing ecological construction areas. These institutions include state-owned
enterprises, municipal-level government bureaus, private managerial companies,
real estate companies and semi-private state-owned enterprises. Institutional
responsibilities vary at each site but can include infrastructural financing, construction
of resettlement complexes and conservation sites, as well as daily environmental land
12 For an account of China's emerging political economies of tourism linked with nongjiale see Chio (2014).
management. Opportunistic urban government ocials allocate or grant land to a single
institution at each site. Enrolling these institutions is integral to the regime of land-
based accumulation and crucial to enclosing peri-urban village land.
In interviews, municipal government ocials would refer to these institutions
as the ‘owners’ of the land. They told me to look for ‘the owner’ (zhao yezhu) to
understand who controls land. They were referring to the institution that is able to
gain de facto control of responsibilities for infrastructural construction, financing and
economic activities within the parcel zoned for ecological protection. Government
ocials referred to the process by which institutions obtain control as one of assigning
‘institutional responsibility’ (fuze jigou).
It is important to note that there are multiple ways to express ownership in the
Chinese language. The word deployed by government bureaucrats for ‘owner’ (yezhu)
denotes proprietary ownership of the material surface of an area. Officials used a
dierent word for ‘owner’ (dizhu) to express sovereign land control. Yezhu is the owner
of a property or a form of proprietary ownership, while dizhu denotes the land owner,
literally the sovereign holder or landlord. City government bureaucrats reserve the
use the term ‘dizhu’ for themselves. According to the PRC constitution, article two,
section10, the ownership of land rests with the state (shuyu guojia). However, the
utilization of the language of ownership (yezhu) in this context indicates the indelible
role of institutions in enacting control over rural land newly designated for ecological
protection. Institutions are able to obtain proprietary ownership over land through
obtaining the use right of the land, without ever vesting land ownership with an entity
outside the state. Table 2 summarizes types of land ownership in relation to processes
of ecological territorialization.
Through allotting institutional responsibility, the city government is able to
accumulate through land transactions surrounding land conveyances (Lin, 2009). Use
rights to state-owned land are leasable; they operate like a legally transferable property
use right, albeit with use and time restrictions put in place by the municipality. According
to article three of the 1990 Provision Ordinance for Granting and Transferring Land Use
Rights over State-owned Land in Cities and Towns, companies, enterprises, individuals
or organizations can obtain the right to use land and engage in development after paying
the appropriate land premiums, which correlate to the market price of land. When land
use rights come through the payment of land premiums in a fixed sum, the municipality
grants land use to an institution. This can occur through land auction or through closed-
door arrangements. When land use is applied for by government institutions, land use
rights can be allocated to that entity (Cao, 2015: 56–8). Fully private entities are generally
granted land use through full payment of land premiums. State-owned enterprises are
readily allocated land use rights, without paying the full land rent premiums; that is, they
either pay a reduced land premium or have the premium waived. The latter occurs for
state-owned enterprises because they are formal state institutions that have historically
provided infrastructural services upon which municipal governments rely.
  Types of land ‘ownership’ in relation to processes of ecological
Types of Land ‘Ownership’ Before Urban Ecological Enclosure After Urban Ecological Enclosure
Yezhu: a land use right, proprietary
ownership, leasable and purchasable
Villagers, appointed and elected
members of the village collective
Institutions, ranging from state,
semi-state and private
Dizhu: legal land ownership, vested in a
state entity
Township government, appointed
cadres and elected members
representing the village collective
City government hierarchy, through
land lease, sale of land conveyance, or
To assign responsibility to one of these institutions, the first step is to complete
comprehensive urban–rural planning as outlined above and then appropriate land
from villages through purchase or leasing. When comprehensive plans are approved,
responsibilities are distributed to different institutions for financing, service
provisioning and infrastructural construction for different parcels of land. As each
institution becomes involved, they take on risks that come with overtaking ‘ownership’
of the land. With de facto ‘ownership’ comes the responsibility for managing market
risks. Many sites require large amounts of financial capital. The cost alone of building
some larger projects have exceeded US $164 million.
Financing is site specific but may be arranged through any combination of state
support, private financing and public–private partnerships. Each site is independently
funded, with financing linked to each site’s institutional land manager. In discussing
financing and management of peri-urban conservation sites, a middle-level government
ocial observed that:
Public–private partnerships (gongsi heying) are widely sought after. We also
consider private financing. These are different channels for financing adopted
according to the particular project. We start by designing the project, making
it official in the comprehensive plan, and providing an expert review. When
it is ready, we go on to find financing. Once we find it, then it is built. Now as
for which department or institution has responsibility over these steps, this is
divided between different institutions (Y.Z.L. Kunming, March 2017).
As long as financing comes from state-owned enterprises, private capital or semi-private
enterprises, the municipal government is able to reduce city budget expenditures
and potentially generate revenues from land conveyances, while responding to the
central government mandates for urban ecological protection zoning. When municipal
bureaus are assigned responsibility, they can more readily draw on state funds to finance
construction. A mid-level municipal official described the capital bed for an urban
ecological area as coming from that which was allocated to his bureau from central and
provincial levels of government. The rest of the capital came from sales of land within
the urban ecological area. Many municipal officials whose bureaus were assigned
institutional responsibility indicated that leasing adjacent land parcels for development
was a crucial source of capital financing for construction and administrative maintenance
of conservation sites. In cases where a state institution has responsibility, ‘the capital can
also come from that earmarked [by the state] for infrastructure, repairing roads, water,
electricity, gas … in addition to the selling of land’ (P.Z. Chengdu, April 2017).
While municipal governments are able to profit from land transfer fees and
save funds through obtaining financing support from institutions involved, institutions
assigned responsibility also aim to make their involvement in ecological construction
profitable. Institutions provide infrastructure and services with the market impetus to
capitalize on land. In practice, daily management and infrastructural provisioning for
urban ecological areas is dispersed across institutions and with this dispersal comes
de facto economic governance of the land parcel, albeit under the restrictions of the
comprehensive urban–rural plan. One municipal ocial who ‘owns’ two ecological sites
turned into treatment wetlands put it quite succinctly, ‘whoever gets the investment
decides how to build the wetlands. Whoever builds the wetlands governs the wetlands’
(Y.Z.L. Kunming, March 2017). In taking on responsibilities for ecological construction,
institutions can act like umbrella corporations. Other entities operate through contracts
with the umbrella institution assigned ‘institutional responsibility’. Under the umbrella
institution (i.e. the ‘owner’ [yezhu]) there is a variegated economic geography wherein
dierent organizations conduct economic activities in addition to building and managing
the conservation site. These institutions are supposed to align their conservation and
developmental practices with the comprehensive urban–rural master plan under the
authority of the municipal government.
Institutions profit from their control of ecological protection zones in four ways:
land sales and rents, housing sales, state subsidies and leisure capital. Institutions can
profit from the value markup from land adjacent to an environmental protection area.
Multi-functional zoning allows institutions to lease land or rent spaces within and near
conservation sites for economic enterprises in accordance with the comprehensive plan.
Some institutions build commodity housing as well as resettlement housing. In many sites
there is construction of high-price single villa homes as well as high-rise resettlement
apartments within or adjacent to the areas zoned for conservation. State subsidies are
available for ecological constructions, often coming from the central state that can
oset the costs of these projects. Estimates for central state subsidies for ecological
construction, c. 2011, were upwards of US $4.8 billion (Lü et al., 2013: 349). At the very
least, these subsidies contribute to infrastructural and management costs. In some cases,
subsidies can even become a source of profit for ‘owners’. Finally, institutions benefit
from leisure capital, including renting store fronts within and around the conservation
site, leasing land within and adjacent to the site, selling access fees such as entrance
tickets or parking fees, and other practices related to the land use designation, including
commercial orchards, on-site restaurants, and pick it yourself agricultural plots.
Under market conditions, there is competition between institutions for obtaining
control over sites and to make them profitable. The provisioning of central state and
provincial subsidies linked to these projects are limited. Therefore, there is impetus for
protection areas to become profitable in the short term. One middle-level institutional
manager noted how, ‘there are many [subsidies] available because the government
considers this very important, but they will not be there for the long-term, the sites
still need to run independently of subsidies’ (Z.L. Chengdu, September 2016). The
financial demands of the ecological construction projects and continued management, in
conjunction with the drive to profit from land rents, incentivizes institutions to carry out
economic development projects that fall outside the restrictions of the comprehensive
urban–rural plan. It is not uncommon for institutions to build private commercial
housing that violates the comprehensive plan.
Institutional managers discussed both successes and struggles to profit from
involvement in urban ecological construction. One ocial who is part of a bureau with
institutional responsibility explained that their work of building and maintaining an
ecological protection area requires a mix of state capital and profits from tourism and
land rents. He elaborated:
The government offers us 1,500,000 RMB a year for financing our ecological
construction and management, but in reality, the capital should be around
3,000,000 RMB. We run in a deficit, but we only run in a slight deficit currently
because we can profit from the site. We also get funds from the parking lots, we
rent out the service provision areas, and in another two years we will make more
profits because we can raise the prices for parking and rental fees (Z.Y. Kunming,
October 2016).
Even institutions that are municipal bureaus and not private entities finance projects
through a combination of formal state channels and eorts to turn a profit from peri-
urban environmental protection.
A mid-level government official explained how obtaining institutional
responsibility for peri-urban conservation sites is the same as obtaining a ‘development
zone’ (shijishang jiu dou shi kaifaqu). This manager discussed how his bureau was
granted two large parcels of land within two different urban ecological protection
areas. However, to successfully finance the infrastructure and manage each site, they
treated portions of the land parcels like development zones (kaifaqu), building villa-
style homes on newly garnered land despite the on-paper moratorium against this
form of development. Ambiguities in interpreting the comprehensive plans’ land
use designations, market conditions that incentivize capitalizing on land, and weak
oversight from city governments are lubricants that facilitate accumulation through this
form of urban ecological enclosure.
Ecological territorialization is central to contemporary processes of enclosure
on China’s peri-urban fringe. This article detailed how comprehensive urban–rural
planning, peri-urban ecological migration and ‘assigning institutional responsibility’
constitute a green regime of urban land-based accumulation. Detailing these practices
of classification, displacement and capitalization revealed important aspects of multi-
tiered institutional governance relationships. In this moment of post-socialist transition,
wherein urban greening comes to the countryside, a host of new ambiguities surrounding
the demarcation and use of ecological land (shengtai yongdi) set the conditions for
opportunist urban bureaucrats to form tenuous mutualistic alliances with opportunistic
institutions. Frontiers of land accumulation and local state formation are produced
through these spatial practices and state–private governance relations, within which
are multi-scalar nested economic geographies. The resulting distributive governance
spans private to state-operated enterprises crossing a multitude of interests, aspirations
and motivations. Each entity involved, whether it be a village corporation, a private
institution or a branch of the municipal state, aims to generate revenues through their
The case of urban ecological enclosures in China provides a sobering example of
the ways ecological conservation practices facilitate social displacement, accumulation
and process-orientated formations of local state power. Detailing a triad of practices,
not only advances understanding of China’s current moment of urban greening, but
also points to the continued need to elucidate interconnections between urban planning,
conservation, political economy and enclosure. This leads me to three final points. First,
future research on conservation and sustainability practices needs to take into account
political economic forces and the multiplicity of processes and outcomes embroiled
therein. At stake in this endeavor is the recognition, or lack thereof, of the situated
geographical forces underlying conservation that shape social processes, flows of capital,
and the ways that actors enact control over space. In detailing these interconnections in
peri-urban China, I aim to bring attention to peri-urban ecological migrations central
to green urban regimes of accumulation, which unevenly incorporate millions of peri-
urban villagers, yet remain understudied.
Second, without substantial policy changes, those forced into peri-urban EM
will continue to experience a range of dierential trajectories with substantial socio-
economic pressures on poorly compensated and newly landless migrants. At the very
least, equitable compensation based on market prices for land and housing should
be universalized if displacement is to continue at all. In making this endorsement, I
echo scholarship that proposes equitable compensation and inclusion for those that
undergo ecological displacement (Bao, 2006; Shi et al., 2007). But I build on these
calls by advocating for deeper consideration of reform and redress within the complex
political economic context of state-led displacement and land development. The nexus
of local state and private profits from land development are clear routes through which
compensatory capital can and should be derived. Yet, it is not only necessary to consider
compensatory equity within political economic context, but also environmental
justice more broadly. In addition to monetary aspects of compensation, psychological
violence stemming from the total transformation of lifeways must be part of the debates
surrounding ecological protection zoning. As this article and other research has shown,
villagers often experience severe psychological stresses in leaving the security of their
land and homes (Sargeson, 2013; Chuang, 2015; Rodenbiker, 2019).13 Many have lived
in village housing and worked on village land for generations. Forced migration into
resettlement complexes completely transforms villagers’ daily lives and socio-economic
conditions. The notion that urbanizing rural people is integral to making China’s cities
sustainable and modern has become a kind of ‘common sense’. This work calls this
common sense into question. More critical research and attention should be given to the
service provisioning imperatives of the local state tasked with implementing ‘ecological’
urbanization policies, the political economic context surrounding land development
and housing that incentivize institutions to profit from their involvement, as well as
the socially, economically and environmentally uneven outcomes such policies produce.
Finally, this account reflects the importance of multi-sited research that draws
on the perspectives of diverse actors located at dierent positions in the constellation
of ecological territorialization. Researching the lived experiences of peri-urban EM
provided valuable information regarding how conservation practices aect villagers
and shape transitional relationships to land, labor and housing. Triangulating between
interviews with villagers at dierent sites and stages of inclusion revealed how dierent
forms of peri-urban EM shaped their socio-economic transitions, the lack of uniformity
across localized experiences of dislocation, and generalizable facets of village land and
housing incorporation. In contrast, researching across bureaus and institutions ‘from the
top’ of the municipal government hierarchy to the village revealed ambiguities central to
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... China's environmental scientists and state representatives frame national development as a series of progressive stages of improvement that entail the state to be actively involved in urbanizing the rural population as the logical path to building an ecological and civilized future. The practical effects of these logics produce an array of population control mechanisms and green developmental practices, many of which unevenly displace rural populations through state-led projects coded as improvement (Chan and Zhang 1999;Xun and Bao 2007;Yeh 2009Yeh , 2013Pow 2018;Rodenbiker 2019Rodenbiker , 2020. The aim of this article is to demonstrate how the production of scientific knowledge became embroiled in exclusionary technocratic polices central to China's ecological modernization and state power. ...
... During the 1990s, ecosystem engineering principles coupled with administrative planning led to demarcations of "ecological cities," "ecological provinces," and "ecological counties," which served as models of ecological construction (R. S. Wang and Ouyang 2012, 342). In the 2000s a wide array of ecological demarcations began to span administrative levels from villages and municipalities to provinces (Zhao 2011;L€ u et al. 2013;Rodenbiker 2020). Parceling cities and land into planned functional areas is a central feature of systems scientists' environmental management legacy. ...
... Parceling cities and land into planned functional areas is a central feature of systems scientists' environmental management legacy. Functional land zoning became a prominent feature of China's state scientific approaches to sustainable land management nationwide (Fan and Li 2009) and remains so during the Xi Jinping era (Rodenbiker 2020). Currently, Ouyang Zhiyun is the director of the Research Center of Eco-Environmental Sciences in the Chinese Academy of Sciences and director of the State Key Laboratory of Urban and Regional Ecology. ...
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Although the science of ecology is often understood in antimodernizing terms, this article shows how ecology in China has become a means to articulate green modernization and sustainable development. As scholars predominantly focus on the policy rhetoric surrounding China’s national modernization and sustainable development program called “ecological civilization building,” the origins of how ecology came to take on developmental meanings remain obscure. This article highlights moments of global exchange and knowledge production by Chinese Marxists, earth systems scientists, and economists that produced eco- developmental logics. These logics define an interventionist role for the state, frame urbanization as moral progress, and refashion the role of the peasantry from the revolutionary vanguard to a backward social force impeding modernization. Ecological sciences in China, therefore, lay an epistemological foundation for legitimizing state-led technocratic practices of socioenvironmental engineering and naturalizing social inequalities between “urban” and “rural” people. In highlighting Chinese scientists’ agency in producing knowledge, this article counters diffusionist accounts of science as singular systematically organized branches of knowledge that emanate from the West. Instead, I demonstrate how ecology is contingent on the historical and political conditions through which it takes on meaning. In the context of China, ecology has become integral to environmental governance, state formation, and uneven relations of power.
... Urban and regional planning practices, therefore, have tended to extend the reach of municipal states over rural areas. Coordinated urban-rural planning entails a set of spatial planning mechanisms and administrative practices through which rural land on the fringe of cities is brought into the reach of municipal government hierarchies (Rodenbiker, 2020). Because of the high value of their land and few legal protections of land use rights, rural people, particularly those residing in peri-urban areas, are vulnerable to land acquisition and forced migration. ...
... Since 2012, the beginning of the Xi Jinping era, harmonious society discourses have largely been subsumed into those aimed at "building an ecological civilization" (Rodenbiker, 2021a;Zhang and Wu, 2022). Mechanisms advanced under these national planning campaigns include green building programs (Zhou, 2015), eco-cities (Chen, 2013;Chang, 2019), and ecological protection (Rodenbiker, 2020). Nevertheless, urban planning continues to operate under logics of economic-growth and contribute to municipal government territoriality. ...
... Economic growth and development remain paramount within recent experiments in participatory planning and ecological protection. Recent work details how green zoning reconfigures the territorial relationships between city and country in ways that extend the reach of municipal states (Chen, 2013;Rodenbiker, 2019Rodenbiker, , 2020. Regarding the ecological ends of such projects, Zhang and Wu (2022) suggest that, in pursuit of ecological civilization under state entrepreneurialism, local states perform an ecological fix. ...
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Research on China’s urban planning sector has largely focused on its role in delivering economic growth and state objectives. Yet China’s urban planning practices are producing new forms of social injustice, which few studies explicitly examine. The paper details three types of social injustice stemming from urban planning and urbanization processes: 1) economic disparities related to land and housing dispossession and speculation, 2) dissolution of social networks and relative precarity for rural-to-urban resettlement migrants, and 3) in-situ marginalization for residents excluded from urban planning. It further proposes that these types of social injustice can be addressed through distributional, participatory, and recognition-oriented mechanisms. Centering justice can reconfigure the aims, processes, and outcomes of planning practice, thereby reducing inequalities embedded within China’s urbanization. Without deprioritizing economic growth and state-led entrepreneurialism, however, justice-oriented planning can offer but partial remedies. The conclusion discusses pathways for researchers and planners to contribute to a just planning transition and advance social justice in China’s cities.
... A major finding from my research is that social and environmental engineering underlying ecological civilisation building deepens social inequalities. The process of creating urban ecological protection zones-an undertaking that is envisioned as a solution to environmental degradation-sharpens inequalities and differentially shapes access to cities (Rodenbiker 2020 daily lives, as well as their underlying material and socioeconomic conditions. ...
This research addresses the issue of the just city in China, from the point of view of equity and resource allocation in the market-oriented urban redevelopment process.
... ending hunger (SDGs-No.2) and stimulating local economic growth . For example, Principle 4 in the 13th Five-year Plan on Poverty-alleviation Oriented Displacement and Resettlement requires resettlees to live sustainably, obtain a sustainable income and increase development opportunities after resettlement (State Council, 2016b;Guo et al., 2020;Minkoff-Zern et al., 2020;Rodenbiker, 2020). Fig. 1 connects the SDGs, based on the definition of the United Nations (2015a), with the policy goals and principles (Tables S1-1 of Supplementary Document 1) of three popular DIDR resettlement forms in China. ...
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Most studies and influential agencies propose a shift to sustainability thinking and regard it as an important means of coordinating economic, social and environmental development. However, much less research focusses on conflicts over resources, the issue of asymmetrical power, and value-and-cultural conflicts behind the trajectories of sustainable development. For countries speeding up transitions such as China, it can be asked how and why might accelerating sustainability transitions through resettlement become a new utopia or a poverty trap? To examine the significance of this question for sustainability, we explore three development-induced displacement and resettlement (DIDR) programs in China: dam-induced resettlement, poverty-alleviation oriented relocation (including ecological migration) and agglomeration of villages. This research examines normative issues of Chinese policies for sustainability. We find that building sustainability via DIDR will not be as easy as projected and could lead to new poverty traps that disadvantage some groups of people, such as resettlees. We highlight three themes, the change of resettlees’ financial conditions, land access and local governance, to explore how competition is skewed between resettlees and local governments while speeding up to pursue more ambitious goals. We find that with the increased pace of implementation of quick sustainability policies that power lies with local governments to the detriment of resettlees. DIDR can become a just governance tool to build sustainability, but only if there is sufficient agreement among all stakeholders on a transparent, accountable and collaborative approach. Without inclusion and equality in transitions, potential risks and challenges can eclipse sustainable development.
... In Australia, several metropolitan and federal initiatives are targeted at regional (non-urban) greenspaces, including the Metropolitan Greenspace Program (New South Wales Government, 2020) and the Department of Agriculture's Water and Environment Grants (Australian Government, 2020). And in China, cities are creating new greenspace in peri-urban areas, which is not serving the country's urban populations directly and displacing villagers farming those lands (Rodenbiker, 2020). These funding sources should consider having a balance of urban and rural greenspace preservation investments given rapid urbanization and the potential that greenspace has stronger protective associations with health for residents of more urban areas than those of less urban areas. ...
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Greenspace in urban areas may have greater protective health effects than elsewhere. Urban dwellers experience more environmental harmful exposures, attentional demands, and stressors than their suburban/rural counterparts. In this systematic review, we synthesize the results of studies that examined how the greenspace and health relationship varies by urbanicity. We searched for articles in April 2019 that found positive associations between greenspace and physical health. Included articles tested for effect modification by urbanicity among one or more (of eight total) outcomes relevant to health and environmental equity. We coded results as 1 = stronger association in more urban areas, −1 = stronger association in less urban areas, or 0 = no difference. We found 57 analyses in 37 articles that met our inclusion criteria. Among these analyses, 50.9% showed no difference, 38.6% showed a stronger association for more urban areas, and 10.5% showed a stronger association for less urban areas. More urban areas had stronger associations for cardiovascular-related, birth, and mortality outcomes and for greenspace measured within 500 m. Stronger greenspace-health associations in more urban areas might be explained in part by the mechanistic pathways underlying these associations. Greenspace can reduce harms from environmental exposures (i.e., air pollution, noise, heat, and artificial light at night) in addition to alleviating attentional demands, reducing chronic stressors, and promoting healthy behavior - factors which might be more necessary, prevalent, or stronger in urban areas. These potential explanations warrant further investigation. The findings of this review inform public health policy and planning professionals who are attempting to make cities livable for all residents.
... Alongside calls for greater public participation, and the foregrounding of Black, indigenous, and subaltern experiences (Finney, 2014;Taylor, 2016), are critical accounts that rethink the universality of sustainability's core tenants and approaches to environmental management. In particular, scholars argue that environmental justice be considered a key component of sustainability (Agyeman, 2013;Rodenbiker, 2020aRodenbiker, , 2020bSze, 2018). In addition, researchers have shown how particular social and political contexts within which sustainability takes on meaning shape environmental management practices and the social effects of sustainability projects (Rodenbiker, 2021;Sze, 2018). ...
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This article discusses methodological adaptations to participatory methods for reflexive environmental management. Reflexive approaches to research methods as process, this article contends, can elucidate social dynamics that standard sampling frames and rote procedures may elide. This argument is supported through a discussion of key insights from scholarship about participatory research methods, as well as auto-reflections on methodical adaptations undertaken while conducting photovoice research on environmental management in peri-urban villages of Southwest China. Reflexive adaptations to participatory methods discussed in this paper include ethnographic attention to forms of refusal, suspended participation, and individual interviews with and without visual aids. These methodological adaptations highlight relations of power between researchers and participants, as well as amongst participants. They also highlight diverse social needs and uneven environmental management processes. Although reflexive approaches to participatory methods are key to producing more widely representational findings and socially just sustainability practices, they are not a panacea for universal inclusivity. Reflexive methodological adaptations have their own limitations and introduce new power relations between participants and researchers. The article concludes with a discussion of how reflexive methodological adaptations bear on research praxis. In particular, the conclusion highlights how reflexive adaptations to research methods are crucial to socially just environmental management and sustainability practices.
There has been growing research interest in processes of selective ‘ecological gentrification’ and ‘environmental enclosure’ in cities where environmental controls are used to attract and retain more affluent residents and attract higher value economic development. This dimension of urban policy might be increasingly relevant to major Chinese cities, which are facing increasing competitive pressures to reorient modes of growth and development around ecological security and quality of life in social and environmental domains. In that context, we examine the development and implementation of the ‘basic ecological control line’ policy (BECL) in the fast-growing city of Shenzhen. In essence the BECL marks a rezoning of the city to enhance ecology and reverse previous environmental degradation, but in doing so it also does political work in reordering space in line with changing economic and social priorities. The question we ask is how the BECL might be read in the context of ecological gentrification and the wider political context of Chinese urban policy. Through detailed empirical investigation, we trace the political economy of the BECL and draw out the insights it offers on transitional urban economy-ecology relations in China and theories of urban environmentalism more generally.
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China's Sponge City Programme (SCP) is one of the world's most ambitious sustainable urban drainage programmes. By 2030, Chinese cities must have 80% of their land drained by Blue–Green Infrastructure (BGI) to build critically needed flood resilience. Costs must be met from municipal and private finance, but BGI lacks the revenue streams of public assets like utilities, so has limited appeal to public–private partnerships. Finance options, including Green Bonds targeting institutional investors, and Payment for Urban Ecosystem Service schemes targeting local citizens and businesses, need developing. Green city branding could lever such finance but despite widespread use of green branding to attract investment, sponge branding strategies are immature, and alignment is needed in green branding between sponge project type (e.g., flagship and retrofit), financial instrument, and target financier, to develop differentiated brands that appeal to a diversity of SCP investors. With little grassroots input into city branding, and SCP problems of green gentrification, local support for SCP implementation may be at risk. This is concerning, because cities need local citizens and businesses to invest in the SCP to achieve the extensive retrofit needed, as retrofit (using small-scale BGI such as stormwater planters, de-paving, and raingardens) has little appeal for institutional investors.
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Two main approaches have emerged in current debates about water management: a bottom-up approach emphasing ‘indigenous’ knowledge, and a top-down, ‘scientific’ approach, typically led by the authorities. In China, indigenous knowledge, accumulated and practiced at the local level across generations, might be summarised in the idiom ‘living with nature’ (天人合一). As this type of practice is relatively moderate and non-interventionist on the local landscape, it was seen as inefficient by those advocating modern water management practices based on ‘hard science’, especially since the onset of the reforms in the 1980s.
Environmental displacement can be defined as forced migration occurring entirely or partly from local environmental restructuring. This includes displacement from sudden environmental events, such as storms, earthquakes, and tsunamis, or from long term changes related to the impacts of climate change, development, conservation‐related residential displacement, and environmental gentrification. Over the past decade, investigating the human impacts of displacement has become an emerging focus within displacement research. The idea of displacement is not only difficult to define but challenging to measure, due in part to a multitude of influences environmental factors have on the ability to stay put. Displacement throughout history has occurred from many factors, including social, political, environmental, and economic. Environmentally related displacement is arguably the most unpredictable form of displacement and is increasingly a problem for both the Global North and the Global South. Geographers have not always focused on these issues, although researchers are increasingly exploring this inherently spatial and temporal problem. A more thorough understanding of environmental displacement is possible by exploring available and relevant interdisciplinary research methods and methodologies used for analyses. This review focuses on literature that links both event‐driven and ongoing change‐driven displacement to environmental change to reveal the patterns across several subfields of displacement research and suggest areas for further development.
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Ecological migration conducted by the government is a typical process of governmental intervention , and the relevant resettlement planning and rehabilitation mode reflect the government ' s plan of development. From the point of view of the function of ecological migration system and setting the Tarim river ecological migration as an example , the stakeholders include national government , individual, sector management department , and the local government of migration are a and relocation area. Each stakeholder has his own unique and un-substitutable social and economic interests and needs.The main rights and interests for ecological migration include the right of development and survival, the right of social welfare, the right of public participation and the right of property compensation.The limitation of the compensation system, especially lack of the compensation for the non economic costs and the occupation of the resource of the relocation areas, and some other issues which will cause social unfairness are the reason for social conflicts. It has suggested that the government should establish the mechanism of interest balancing and grievance appeal, build the legal system, and made a clear orientation of the government ' s function in order to take the responsibility of the government. Key words: ecological migration; protection of rights and interests; government 's responsibilities; stakeholders; social conflicts; Tarim river migration
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This paper analyzes the linkages between urban waterscapes, nature aesthetics, and sustainability by delineating the re-emergence of shan-shui, translatable as ‘mountain-water,’ or ‘landscape,’ within contemporary urban China. I show how this aesthetic concept, originally emerging in third century Chinese landscape poetry, is used to reconfigure and reimagine sustainability and contemporary China’s urban landscapes. I draw on original mixed methods fieldwork, including interviews over a two-year period, digital archiving, historical texts and discourse analysis. Through these methods, I detail the emergence of shan-shui aesthetics then draw on the concept of superscription, the historical process of layering symbolic meanings, to understand the contemporary superscription of shan-shui with urban sustainability through the writings of prominent Chinese scientists and urban planning experts. Their productive work generated a new imaginary of teleological urban modernity that superscribes shan-shui with urban sustainability as the “shan-shui city.” Through two primary case studies, Tangshan Nanhu Eco-city and Meixi Lake, I show how the production of new sustainable urban waterscapes is linked with place making practices, territorial processes, and localized entrepreneurialism. Finally, I point to the limits of superscription, by highlighting the significant disconnect between the state framing of urban space and the lived experiences of urban residents, which I conceptualize as the osculation of the state. The paper, thus, intervenes in literatures regarding the historical transformations of cultural symbols, aesthetics, urban political ecology, and the political economy of place-making in China.
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Land-centred urbanisation has precipitated shortage of green space in Chinese cities. However, in the Pearl River Delta, an ambitious greenway system has recently managed to flourish. It is intriguing to ask how this has become possible. Informed by the perspective of urban political ecology, this paper finds that the greenway project in the Pearl River Delta represents a set of politically realistic endeavours to alleviate urban green space shortage by adapting to, rather than challenging, powerful landed interests. Three interlocking dimensions about land—municipal land quota, rural land use claims, and real estate development—have influenced why, where and how greenways have been created. Based on these findings, we argue that research on China's politics of urban sustainability necessarily needs to understand the country's land politics.
The development of offshore wind farms has been a way for the state to repackage national development projects using green energy discourses. In Taiwan, where the further development of nuclear power is suspended due to public antinuclear sentiment, offshore wind farms have been heavily promoted as a way of meeting electricity demand. The planned site for offshore wind farms, mainly the intertidal zone along the coast of Changhua County, overlaps with both oyster farms and the habitat of Taiwanese humpbacked dolphins, categorized as a critically endangered species by the International Union for Conservation of Nature. This has resulted in a clash between conserving the oyster farming landscape, protecting an endangered species, and developing green energy. Facing this dilemma, pro–wind farm discourses that highlight concerns about global climate change have gradually supplanted those stressing the welfare of oysters and dolphins, even though the latter have been used successfully as local icons by movements opposing previous development projects on the intertidal zone. This article reconsiders the politics of territorialization implied by the “green” label affixed to offshore wind farm projects and other forms of green energy in general. As such, the meaning of offshore wind farms, as a newly discovered energy resource, is intertwined with the changing meanings of both dolphins and oyster farms, as rival nonhuman objects of resource exploitation and natural conservation. The territorialization of such resources in the emerging discursive space of green energy has proceeded via relational placemaking with nonlinear connections among multiple human and nonhuman elements. Key Words: conservation, intertidal zone, landscape, renewable resources, resource frontier.
A central feature of China's “green” development plan has been the creation of conservation zones across the peri-urban fringes of major cities. In these conservation zones, rural land and housing are being unevenly incorporated into urban space, leading to a diverse set of experiences for dislocated villagers. In this paper, I develop a volumetric approach to analyze the spatial politics of agricultural and urban transitions in China's conservation zones. I advance theories of vertical and volumetric space, which consider relations across heights, depths, and surfaces, through attention to the temporalities and everyday experiences of volumes. My volumetric approach provides a foundation for delineating how the uneven valuation and compensation of rural land and housing shapes social differentiation, as well as how villagers navigate and experience rural-urban transitions. Furthermore, I argue that a volumetric account of three-dimensional space exposes the interconnections between agrarian and urban questions, which are usually considered discretely. The central contribution of this paper, therefore, is to reorient the agrarian and urban questions in relation to one another across horizontal, vertical, and temporal axes.
Purpose: Automated synthetic computed tomography (sCT) generation based on magnetic resonance imaging (MRI) images would allow for MRI-only based treatment planning in radiation therapy, eliminating the need for CT simulation and simplifying the patient treatment workflow. In this work, the authors propose a novel method for generation of sCT based on dense cycle-consistent generative adversarial networks (cycle GAN), a deep-learning based model that trains two transformation mappings (MRI to CT and CT to MRI) simultaneously. Methods and materials: The cycle GAN-based model was developed to generate sCT images in a patch-based framework. Cycle GAN was applied to this problem because it includes an inverse transformation from CT to MRI, which helps constrain the model to learn a one-to-one mapping. Dense block-based networks were used to construct generator of cycle GAN. The network weights and variables were optimized via a gradient difference (GD) loss and a novel distance loss metric between sCT and original CT. Results: Leave-one-out cross-validation was performed to validate the proposed model. The mean absolute error (MAE), peak signal-to-noise ratio (PSNR), and normalized cross correlation (NCC) indexes were used to quantify the differences between the sCT and original planning CT images. For the proposed method, the mean MAE between sCT and CT were 55.7 Hounsfield units (HU) for 24 brain cancer patients and 50.8 HU for 20 prostate cancer patients. The mean PSNR and NCC were 26.6 dB and 0.963 in the brain cases, and 24.5 dB and 0.929 in the pelvis. Conclusion: We developed and validated a novel learning-based approach to generate CT images from routine MRIs based on dense cycle GAN model to effectively capture the relationship between the CT and MRIs. The proposed method can generate robust, high-quality sCT in minutes. The proposed method offers strong potential for supporting near real-time MRI-only treatment planning in the brain and pelvis.
Since the mid-2000s, India has been beset by widespread farmer protests against “land grabs.” Dispossession without Development argues that beneath these conflicts lay a profound transformation in the political economy of land dispossession. While the Indian state dispossessed land for public-sector industry and infrastructure for much of the 20th century, the adoption of neoliberal economic policies since the early 1990s prompted India’s state governments to become land brokers for private real estate capital-most controversially, for Special Economic Zones (SEZs). Using long-term ethnographic research, the book demonstrates the consequences of this new regime of dispossession for a village in Rajasthan. Taking us into the diverse lives of villagers dispossessed for one of North India’s largest SEZs, it shows how the SEZ destroyed their agricultural livelihoods, marginalized their labor, and excluded them from “world-class” infrastructure-but absorbed them into a dramatic real estate boom. Real estate speculation generated a class of rural neo-rentiers, but excluded many and compounded pre-existing class, caste, and gender inequalities. While the SEZ disappointed most villagers’ expectations of “development,” land speculation fractured the village and disabled collective action. The case of “Rajpura” helps to illuminate the exclusionary trajectory of capitalism that underlay land conflicts in contemporary India-and explain why the Indian state is struggling to pacify farmers with real estate payouts. Using the extended case method, Dispossession without Development advances a sociological theory of dispossession that has relevance beyond India.