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Area, 2014, doi: 10.1111/area.12128
Modelling green urbanism in China
C P Pow and Harvey Neo
Department of Geography, National University of Singapore, Kent Ridge, Singapore 117570
Email: powcp@nus.edu.sg
Revised manuscript received 28 May 2014
This paper examines how the modelling of green urbanism is spatially manifested in flagship eco-city
projects such as the Sino-Singapore Tianjin eco-city (SSTE) project. As part of a multi-scalar process that
taps into a host of mobile policy networks and ‘quick fix’ urban policy solutions that circulate around the
world, such eco-flagship prestige projects serve as powerful sites for the convergence of the boundaries
between the social and technical and are highly symbolic places charged with the formidable task of
constructing purportedly new forms of ecological urban imagineering and socio-ecological lifeworlds.
But to the extent that these eco-flagship projects are often underwritten by state-business growth
coalition and driven by (green) entrepreneurial objectives, these urban ecological spaces are also
necessarily implicated in broader normative debates and the challenge of constructing sustainable and
socially just urban futures. As David Harvey has pointed out, insofar as all environmental-ecological
arguments are arguments about society and, therefore, complex refractions of all sorts of struggles being
waged on other realms, eco-cities in China both reflect and embody the multiple contradictory tensions
inherent in contemporary Chinese society.
Key words: green urbanism, urban sustainability, China, policy mobility
Green modelling as ‘urban sustainability fix’
What exactly is an (Asian) eco-city and how does it speak
to broader debates on the modelling of green urbanism
and the circulation of (contested) forms of sustainable
urban future? Drawing on insights from the literature on
policy mobility debates, this paper examines the construction of eco-cities and its ecological imagineering in
China. To the extent that ‘nature’ (and alongside its social
construction and production) has always been a necessary
precondition for capital accumulation, sustainable development itself can be interpreted as part of the search for a
spatio-institutional fix to safeguard growth trajectories in
the wake of industrial capitalism’s long downturn, the
global ‘ecological crisis’ and the rise of popular environmentalism (Krueger and Gibbs 2007; While et al. 2004,
551). In this context, While et al.’s (2004) notion of urban
sustainability fix is a useful starting point to understand
the governance dilemmas, compromises and opportunities created by the current era of state restructuring and
ecological modernisation. Drawing on David Harvey’s
(1982) insight on the spatial fix – more specifically the
idea that the geographical reproduction of the capitalist
mode of production requires the fixing of spaces (only to
have it destroyed or devalued at a later point), the notion
of a sustainability fix draws attention to the selective
incorporation of ecological goals in the greening of urban
governance and the transformation of the city landscape
in the image of a purportedly sustainable ‘green’ city.
While an effective institutional or spatial fix for a given
locale, the notion of an urban sustainability fix is also
necessarily part of a multi-scalar process that taps into a
host of mobile policy networks and ‘quick fix’ policy
solutions that circulate around the world, that in turn get
internalised and recast within national boundaries. Here,
the recent burgeoning scholarship on policy mobilities or
policy tourism is instructive (Ward 2006; Peck and
Theodore 2010; Gonzales 2011). As McCann and Ward
have shown, in the world of ‘fast policy transfer’, policy
actors including politicians, policy professionals, urban
planners, consultants and activists act as transfer agents in
‘shuttling policies and knowledge . . . around the world
through conferences, fact-finding study trips, consultancy
work’ (2011, X). Seemingly moving seamlessly from place
to place, ‘tried and tested’ policy solutions and urban
‘best practices’ are being touted to address a range of
issues from urban regeneration (e.g. the ‘Bilbao effect’ or
‘Barcelona model’), business improvement districts,
welfare provision, crime and drug control, urban transport
management, enhancing quality of life and creative
The information, practices and views in this article are those of the author(s) and do not
necessarily reflect the opinion of the Royal Geographical Society (with IBG).
© 2014 Royal Geographical Society (with the Institute of British Geographers)
2
Modelling green urbanism in China
economy and, of course, urban sustainability practices
(see Peck 2002 2005; McCann 2004; Gonzales 2011;
Ward 2010). In the arena of environmental policymaking, cities such as Curitiba, Portland, Copenhagen
and Munich have often been held up by global ranking
agencies as ‘model cities’ to be emulated (or ‘copied’) by
other aspiring green cities. In the 2012 ‘Asian Green City
Index’ commissioned by Siemens, cities such as Singapore, Yokohama, Tokyo, Osaka, Taipei, Hong Kong have
been listed as Asian role models. What these rankings
hope to achieve is not just an attempt to provide an
‘objective’ ranking of sustainable urban practices around
the world. These rankings have often been strategically
appropriated by entrepreneurial urban regimes as a
means of branding cities in the bid to create attractive
healthy places to entice capital. These so-called best practices and international rankings have quickly become
‘industry standards’ that urban authorities readily adopt as
a way of benchmarking and ‘improving’ their city’s relative performances in the global arena.
In this respect, cities can no longer be considered as
analytically discrete objects but are constituted through
complex inter-connections with other places that are in
turn shaped and transformed by mobile policy networks
(Massey 2010; Ward 2006 2010). The adoption and
enactment of these mobile policies, to be certain, is not a
wholly deterritorialised process but entails converting and
translating these globally mobile policies into what are
deemed ‘locally appropriate’ strategies and, in the
process, reconfiguring the territoriality and relationality of
these urban places. As McCann and Ward have argued, to
the extent that urban policies remain bound up territorially to a whole set of locally dependent interests and
urban growth coalitions, ‘policy making must be understood as both relational and territorial, as both in motion
and simultaneously fixed, or embedded in place’ (2011,
xv). In other words, notwithstanding the universalistic
tendencies of such global green urbanism practices,
policy mobility does not occur in a socio-political
vacuum.
Hence, it is timely to ask how urban policy mobility
and, more specifically, the modelling of green urbanism
in China are shaped by the local particularities of place
and history, as much as contemporary global forces such
as inter-urban referencing and learning (Roy and Ong
2011). The term urban modelling suggests not only an
attempt by local city officials to (selectively) adopt and
emulate ‘urban best practices’ from elsewhere, but also
serves as a mechanism for the local state to construct a
‘new regime of green urbanism’ by shaping, disciplining
and producing particular kinds of spaces and citizensubjects deemed desirable (Hoffman 2011). In this sense,
urban modelling embodies the dialectical tension
between universalistic ideas of global green urbanism and
Area 2014 doi: 10.1111/area.12128
© 2014 Royal Geographical Society (with the Institute of British Geographers)
the territorial imperatives of local national/urban growth.
However, the notion of modelling is not a foreign or novel
practice in China because in both traditional Confucian
and Maoist thoughts, emulating successful individuals or
processes were often celebrated as an exemplary form of
learning (Bakken 2000). Indeed, it may be argued that in
contemporary urban China, the modelling of green urbanism is increasingly bound up with global practices of
inter-referencing and the emulation of ‘successful’ cities
across Asia and beyond. As Hoffman noted: ‘urban governments across China have been encouraged to reach
environmental targets by adopting measures and governmental rationalities proven elsewhere’ (2011, 57) to the
extent that the inter-referencing of cities has come to be
defined as an end in itself. In this sense, urban modelling
is hence tied to place-marketing and driven by the logic of
urban entrepreneurialism.
It is in this context that this paper situates the empirical
discussion on ecological place-making and the search for
an urban sustainability fix in Chinese cities. As will be
shown, the mobilising of green urbanism and the ‘rolling
out’ of such urban ecological policies in the form of
flagship eco-city prestige projects are not neutral transfers
of technical knowledge but are inherently a social–spatial
process inflected with criss-crossing power politics and
networks. As Ward alluded, departing from the politicalscience oriented notion of ‘policy transfer’, the critical
study on policy mobility or policy tourism
sought to uncover how – through what practices, where,
when and by whom – urban policies are transferred and
reproduced from place to place, and are negotiated politically in various territories. (2011, 73)
Specifically, the paper will address how green urban policies manifested in China’s eco-city projects are symptomatic of such market-driven ‘fast policy transfer’ (Peck
and Theodore 2010) that circulates in and around the
world as quick fix ‘green urban solutions’, but are also
territorially grounded and subject to changes, contradictions and political struggles as they circulate and ‘touch
down’ in specific locales.
Based on fieldwork conducted in Tianjin Eco-city
between 2011 and 2012, this paper draws on interviews
with planners and residents of the eco-city and also observations made at planning workshops and seminars where
planners share their views on planning experiences and
knowledge transfer in the Tianjin eco city. On 18 May
2012, we also attended a public exhibition on ‘Urban
transformations: overseas planning and urban design
works done by Singapore consultancy firms’ organised by
the URA and the Singapore Institute of Planners. The
exhibition held at the URA Centre showcases the overseas
planning projects of Singapore firms including Surbana
Modelling green urbanism in China
International Consultants who are the lead masterplanners of the Tianjin Eco city projects. In addition, secondary data sources such as guidebooks and brochures on
eco-cities were also collated and analysed.
In the ensuing discussion, the paper critically considers
how the ecological imagineering of a key eco-flagship
project – the Sino-Singapore Tianjin eco-city – draws
selectively on the philosophical and ideological framing
of eco-urban ideals. We conclude by interrogating the
contradictions inherent in some of the normative ideals of
the eco-city within the socio-political context of China.
Insofar as the Tianjin eco-city represents and embodies
transnational utopian visions of ecologically sustainable
urban futures, we argue that it contains within it the very
social-ecological contradictions and tensions that it purportedly intends to resolve.
Ecological cities and China’s
‘environmental turn’
The extent and depth of China’s environmental problems
were key challenges that the Chinese leadership recognised and vowed to address as early as the late 1990s.
More recently, Muldavin (2013, 260) writes of the crisis
narratives on China’s environment, which illustrate the
increasing urgency and dismay that citizens and
policymakers (both within and beyond China) view the
socio-environmental problems caused by, among other
things, over-population and air pollution in the country. In
what can be described as an environmental turn in China
that has moderated the growth at all costs model in the
early years of opening up, Francesch-Huidobro et al. illustrate how, since 2000,
the national government has shown a stronger commitment to improving environmental conditions in China by
enacting many new environmental laws, increasing
investment in green technologies, enhancing the official
status of environmental protection agencies throughout its
administrative system and including environmental protection as a key criterion in the annual performance evaluation of local leaders. (2012, 2496; see also Cook and
Murray 2002)
Yeh (2009) however cautions an overly triumphant
reading of the greening of China, rooted in a particularistic interpretation of ecological modernisation that
assumes outcomes will necessarily benefit the economy,
the environment and society (see also Caprotti 2014).
In this context, where policymakers in China are
cognisant of the intensifying social-environmental problems and coupled with their underlying faith in the use of
technology, it is unsurprising that the eco-city (生态城)
model or other policy buzzwords such as ‘low carbon
city’ (低碳城) are seen as comprehensive solutions for
China’s myriad environmental problems (Wu, 2012).
3
Underpinning the eco-flagship projects sprouting up all
over China (see Table 1), a few commonalities run
through many of them. First, these projects often involve
mobilising an internationalised network of policy experts,
professional planners, architects, engineers, etc. who
engage in technical ‘knowledge transfers’ (see Rapoport
2014). In addition, these projects are also driven strongly
by entrepreneurial/commercial objectives and ideals of
ecological modernisation. The latter is increasingly seen
as a catalyst to even greater growth, especially when
focusing on creating new environmental technologies (for
example, green buildings and clean energy). According to
a recent report published by the China Society for Urban
Studies, there are well over 200 ‘eco-city’ projects in
China with more than 80 per cent of prefecture-level
cities having at least one eco-city project (http://www
.chinasus.org/chinasus/).
Within the relational framework of policy mobility
analysis (McCann and Ward 2011), many of these ecocity flagship projects in China claim to ‘hook up’ to international ‘best practices’ of ‘ecologically advanced’ cities
elsewhere and are assembled through a transnational
network of ‘idea brokers’ and ‘transfer agents’ that hails
from Europe, the USA and Asia. As Hoffman (2011, 55)
points out in the case of Dalian, Chinese municipal officials often referenced other cities such as Singapore and
Kitakyushu in Japan for ideas on developing a ‘garden
city’ and ‘environmentally friendly city’.
As noted earlier, the idea of modelling has deep historical roots in the Chinese context and indeed, the Chinese
language has many words for ‘model’ and its attendant
meaning of replicability. During the course of our fieldwork, we have often encountered Chinese officials using
terms such as mofan (exemplar), dianxing (typical),
bangyang (model), biaozhun (standard) to describe their
urban environmental projects. For the Tianjin eco-city
project, it is significant that the development has been
designated a shifan project, literally a successful demonstration project that is set to be replicated throughout
other parts of China. As a local official emphatically stated
to us:
the significance of the Tianjin eco city goes beyond just
the Binghai area . . . the ultimate goal is for such sustainable urban models to be replicated to all parts of China, to
build on the success of what we have here in Tianjin
and elevate China’s urban environmental management
nationally.
It is interesting to note that the modelling of ‘successful’
urban visions of green living and future models of ‘sustainable’ urban development are not always bound up in
the usual dichotomy between ‘Western’ versus ‘nonWestern’ urban worlds or even intra-Asia dynamics (see
for example, Roy and Ong 2011), but (re)produced
Area 2014 doi: 10.1111/area.12128
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Table 1
Modelling green urbanism in China
Some high-profile eco-city projects in China
Eco city
project/
location
Year project
started/size and
estimated cost
Dongtan
eco-city,
Shanghai
Sino-China
Tianjin
eco-city
Projected
population
Local agencies and foreign
‘transfer agents’
1998
84.64 km2
Registered capital:
RMB 2.8 billion
650,000
residents
2007
30 km2
Registered capital:
RMB 4 billion
350,000
residents by
2020
Project halted
Shanghai Industrial Investment
awaiting review;
Cooperation (上实集团); planning
news of the
undertaken by Shanghai Urban
project being
Planning and Design Research Institute
revived but scaled
and Arup global consultancy firm from
down and
the United Kingdom; speared headed
undertaken by
by Peter Head (Arup project director);
local agencies
named by Time Magazine as one of
(e.g. East China
the top 30 global ‘eco-heroes’ in
Normal
2008; closely associated with deposed
University)
mayor and former Shanghai
Communist party-chief Chen Liangyu
In progress (phase
Sino-Singapore Tianjin Eco-city
II, 2011–2015)
Development Co., Ltd; joint venture
between Tianjin TEDA Investment
Holding Co., Ltd and Singapore
Keppel Corporation. Involvement of
key political figures in Singapore
(Senior Minister Goh Chok Tong) and
Chinese Premier Wen Jiabao
In the phase of
Sino-Singapore Nanjing Eco High-tech
regulatory
Island Development Co., Ltd; joint
detailed planning
venture between Singapore Intelligent
Eco Island Development Pte Ltd and
Nanjing Jiangdao Investment &
Development Co., Ltd
Singapore-Nanjing 2009
15.21 km2
Jiangxinzhou,
Registered capital:
eco-high-tech
US$99 million
island
(expected total
investment: RMB
90 billion)
Kunming
2008
eco-city
By 2015, the total
investment on 67
key construction
projects in
Kunming will
amount to RMB 54
billion
2005
Huangbaiyu eco
3000 acres (including
village,
400 houses with
Liaoning
each one
occupying
103.5 m2);
Total investment RMB
30 million in 2008
(most investment
from the Chinese
government and
corporations)
2008
Caofeidian
150 km2
eco-city,
Expected total
Tangshan
investment by
2009: RMB 20.67
billion
100,000
residents by
2020
Current status
In progress; key
The population Kunming Municipal government,
‘breakthrough’
Kunming Research Academy of
of urban
phase completed
Environmental Sciences & Nankai
dwellers is
(2008–2010)
University; Swiss support, in particular
projected to
Zürich and Kunming had initiated a
reach over 5
twinning partnership programme
million by
2020
Only 42 out of
1400 residents China-US Center for Sustainable
planned 400
Development; the board comprised
houses have been
members from the Chinese and the US
built; since 2008,
government as well as companies and
the project has
NGOs (mainly from the US side). Two
been suspended
key figures associated with the project
are Deng Nan (Deng Xiao Ping’s
daughter) and William McDonough
(renowned American architect and
‘green guru’ who specialises in green
architecture and sustainable urban
design)
1,000,000
Tangshan Municipal government; Beijing In the phase of
constructing
residents
Tsinghua Urban Planning & Design
infrastructure and
Institute; SWECO (Sweden)
other public
facilities
Area 2014 doi: 10.1111/area.12128
© 2014 Royal Geographical Society (with the Institute of British Geographers)
Modelling green urbanism in China
domestically by the local state in China. While we do not
want to overstate such ‘localist’ forms of policymaking,
what is being highlighted here is the salient role of local
government in generating models and striving to meet
national policy targets. In these terms, the paper will now
examine how green entrepreneurial urbanism and the
selective incorporation of ecological goals are being
mobilised and assembled in the flagship eco-city project
in Tianjin.
Assembling eco-cities in China: the
‘Singapore transfer’
As a joint venture between Singapore’s Keppel Group and
a Chinese consortium led by Tianjin TEDA Investment
Holding, the 34.2 square kilometre Sino-Singapore
Tianjin Eco-city (SSTE) is the result of a collaborative
agreement between the governments of China and Singapore to jointly develop a ‘socially harmonious’, environmentally friendly and resource-conserving city in China
(Figures 1 and 2). First mooted in 2007 by Singapore’s
former Senior Minister Goh Chok Tong as a showcase of
Singapore’s strengths in housing, environmental services
and water technology, the SSTE is ostensibly an economic
venture that aims to build a prototype city that can be
‘replicated in other cities in China’ (Keppel Corporation
2014). Specific features of the eco-city are mostly the
products of advanced environmental technologies,
including the provision of good thermal insulation for
buildings and use of solar energy to reduce energy consumption, rain water collection for irrigation and extensive landscaping features such as sky gardens (The Straits
Times 21 July 2009).
Seen in this light, the SSTE exemplifies the transnational
entrepreneurial ‘greening project’ of the Singapore devel-
Figure 1
Entrance to the SSTE flagship project
(Source: C.P. Pow)
5
opmental state as it forges global policy connections with
Chinese cities. Evidence of such eco-technological ambition of the Singaporean state is extensive, but we will
highlight here one of the most significant steps it has
undertaken in recent years. Singapore’s efforts to develop
and export environmental technologies culminated in the
establishment of what Peck calls policy ‘transfer agents’ in
the form of the Centre for Liveable Cities in 2009. The
Centre’s main goal is to ‘distil Singapore’s expertise in
urban management’, drawing from ‘Singapore’s experiences over the last half-century, while creating knowledge
to address emerging challenges’ (Centre for Liveable
Cities 2012). In this regard, two socio-environmental technologies which are tied intimately with a particular discourse of sustainable development and aggressively
exported by Singapore are water desalination and ecocities. Indeed it is precisely Singapore’s ‘wealth of experience in water conservation’ that prompted China to pick
it as a partner to build an eco-city in Tianjin (The Straits
Times 25 August 2009).
In terms of masterplanning and design, the SSTE was
jointly developed by the China Academy of Urban Planning and Design, the Tianjin Institute of Urban Planning
and Design and the Singapore planning firm Surbana
International Consultants. Like many of the ‘global intelligence corps’ firms (Olds 2001) that operate around the
world, Surbana’s global operation in masterplanning and
design work is ‘driven by an economic imperative either
to grow or simply to maintain turnover levels in response
to shrinking local market (Rapoport 2014, 3). In the case
of Surbana (the corporatised arm of the Housing Development Board that was subsequently acquired by the
state-owned Temasek Holdings), the company is also
charged with the mission of selling the ‘Singapore model’
Figure 2 Scaled model of the SSTE project that promises
a ‘socially harmonious’ and ‘environmentally friendly’
development
(Source: C.P. Pow)
Area 2014 doi: 10.1111/area.12128
© 2014 Royal Geographical Society (with the Institute of British Geographers)
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Modelling green urbanism in China
of successful ‘green’ urban development to the world (see
also Pow 2014). It is important to note that the involvement of Singapore goes beyond the participation of
private and/or government-linked companies to include
many lead public agencies. Notably, Singapore’s Ministry
of National Development maintains an ‘Eco-city Project
Office’ (with about 10 employees) to drive the Tianjin
project and shape its outcome.
Significantly, one of the main guiding principles in the
SSTE was to adopt a holistic approach towards creating
and designing a liveable, efficient and compact city,
which would be developed in an ecologically sound and
environmentally sustainable manner. The final master
plan is said to promote the ‘three harmonies’ (三合) – man
living in harmony with man, now and for future generations; man living in harmony with economic activities;
and man living in harmony with the environment.
Such eco-philosophical thought aligns with the Singapore garden city model with its attendant beautification of
urban landscape, underpinned by a strong dose of social
engineering. The crux of such thinking is to create socioenvironmental landscapes that are concomitantly economically productive (Savage 1992). To that end, the
erstwhile prioritising of green spaces in SSTE as part of the
garden city model does not preclude the embodiment of
a ‘a vigorous developmentalist orientation’.
To keep track of the development of the eco-city, a set
of 26 key performance indicators (KPIs) is formulated
drawing on national standards in China and also with
reference to Singapore as well as internationally defined
yardsticks. These 26 KPIs were divided by four groups:
1
2
3
4
good natural environment
healthy balance in the man-made environment
good lifestyle habits
developing a dynamic and efficient economy.
In our interviews with planners and officials involved
in the SSTE, it is interesting to note that such KPIs
have often been highlighted as ‘major milestones’
achieved in the implementation of the project. For the
local Chinese officials in the SSTE, striving to meet such
internationally defined environmental (and economic)
policy targets is clearly an important means of benchmarking the Tianjin eco-city to an external model to the
extent that such urban inter-referencing has almost
become an ‘embodiment of the implementation of
urban sustainable development’ itself (Hoffman 2011,
57).
Another distinctive feature of SSTE is that it is not meant
to be just another green city but one that is set to fundamentally transform how cities in China will be built in the
future. Unsurprisingly, such a rhetoric can be found in
other eco-cities like Dongtan in Shanghai, which has
Area 2014 doi: 10.1111/area.12128
© 2014 Royal Geographical Society (with the Institute of British Geographers)
since been significantly downsized (Pow and Neo 2013).
Indeed, Mr Ho Tong Yen, CEO of the Tianjin Eco-City
project, in expressing his interest in utilising the eco-city
project as a policy learning tool, remarks:
I think that in time to come, this will be a model that many
people will study, some cities will replicate certain aspects
of the concept we have developed here. They may not
replicate eco-city in its whole but I think as long as some
ideas are replicated elsewhere, then I think we would
have made a very big contribution to sustainable
development.
In a seminar on eco-city planning that we attended,
planners from Surbana and URA spoke about the excitement of ‘building a city from scratch’, literally from ‘a
clean slate’. A planner further remarked that with the
high-level support from the government from both sides,
the SSTE projects allows them to be ‘innovative and
experimental . . . something that cannot be done in
Singapore where land is scarce with most land being
already developed’.
Another planner we interviewed shared that
except for some existing villages, the area we are given is
essentially an empty plot of land to experiment with . . .
this is not a luxury planners have in Singapore. We are
able to be bold and creative by coming up with innovative
design ideas such as the integrated eco-cells and eco
spines . . . this enables us be differentiated from other
eco-city models out there.
Importantly, as the interviews revealed, the modelling of
green urbanism is driven as much by place marketing and entrepreneurial logic for global capital
accumulation.
Notwithstanding that, many of the planners we interviewed also highlighted the urgency to take control of and
address the declining quality of the urban environment in
China. For them, the eco-city is seen as an attempt to
provide a set of planning solutions to manage and control
the ‘runaway problem of urbanization in China’. As one
planner justified:
just take a look at Chinese cities with all the choking smog
and pollution . . . we are not just building another ordinary city, the SSTE is designed to be a totally different way
of living that balances the environment and urbanization
in China.
However, the development of high-profile flagship projects is not without problems and brings into question
whether the pursuit of urban sustainability and the ecocity is simply a legitimisation strategy for pro-growth
entrepreneurial cities. More critically, to what extent is
urban sustainability being mainstreamed or normalised as
part of neoliberal urbanism?
Modelling green urbanism in China
Contesting sustainabilities and
diverging plans
Insofar as all environmental-ecological arguments are
arguments about society and, therefore, complex refractions of all sorts of struggles being waged on other realms
(Harvey 1996, 372), eco-cities in China both reflect and
manifest the multiple contradictory tensions inherent in
contemporary Chinese society. The questions remain
whether the pursuit of urban sustainability and flagship
eco-city projects are simply local forms of legitimisation
strategy for cities and urban government that are otherwise
engaged in the pursuit of economic growth/boosterism;
and to what extent is urban sustainability being ‘domesticated’ and normalised as part of neoliberal urbanism
(While et al. 2004; Krueger and Gibbs 2007)? As evinced
from the SSTE, despite the support from both the central
government in China and Singapore, the project is reportedly beleaguered by delays. Teething problems persist in
the translation of Singapore’s ‘garden city’ model onto
what is essentially a silted marshland in the Binhai development site. The Straits Times, the leading daily broadsheet
in Singapore, highlighted in a critical report that ‘it may not
all be smooth sailing’ for the project with Singapore.
Among other problems, Chinese officials are reportedly
not seeing ‘eye to eye on such things as work priorities and
timing’. Indeed, a source of tension was that local Chinese
officials are ‘no longer willing disciples of the foreign
experts’. This is an unsurprising development given that
many of the Chinese officials have been trained overseas,
including in Singapore (Ng 2009).
A Singapore planner we interviewed noted that:
[The] Chinese planners are not ignorant; in fact they are
catching up very fast. They are very quick to take what you
offer and replicate [it] elsewhere in other parts of China.
But for us, we try to have a ‘win-win’ mentality because
when they take these ideas elsewhere, they are also
helping to spread the Singapore brand name.
However, in the same report, Chinese planners and
officials in Tianjin (who do not necessarily follow directives from the Central government) are said to prefer eyecatching grandiose projects such as larger scale housing
estates and industrial parks rather than Singapore-stylepublic housing that caters to low-income Chinese. One
anonymous Tianjin official was quoted as saying that:
By the time the public housing project is completed, many
of us Tianjin officials would likely be promoted elsewhere.
Who would still be around to ensure that it is really the
poor people who are relocated to this public housing
estate. (Ng 2009)
Evidently, insofar as the urban sustainability fix in China
is being assembled and mobilised through fast-track green
7
urban policies, they can also be disassembled and unravelled by the contradictory global–local forces that constitute them. As McCann and Ward (2011, xv) suggested,
these contradictions point precisely to the tension
between mobile urban policies as being relational, global
and dynamic on the one hand, and locally fixed and
territorial on the other hand, hence underscoring the
contested ecological place-making and its spatial
imagineering in contemporary urban China.
Yet to what extent do residents in SSTE readily subscribe
to the green lifestyle that the planners had envisioned? As
Hoffman (2011, 67) observed, urban modelling practices
are not only about assembling technical expertise and
policy transfer, but also entail fostering particular kinds of
citizen-subject and instilling certain civic values, be it
about being socially responsible, entrepreneurial or sustainable. Regardless of the motivations of both the
Chinese authorities and Singaporean agencies in building
the eco-city, residents we spoke to were relatively measured in their response. While most people we spoke to
welcome the supposed ‘eco features’ in their homes, most
are more concerned with affordability of the housing, the
appreciation of their property and having adequate facilities in and around the eco-city. A female respondent puts
it best when asked about the attractiveness of the eco-city:
I will definitely consider this place (the Tianjin eco-city) if
the prices are reasonable. Of course, having green
housing is good but if it is too expensive it will be difficult
for us. Also, right now, the place looks like it is not
completely finished yet. People need markets, schools and
other shopping facilities. These are all inadequate right
now. But I believe once these amenities are ready, the
housing prices will rise also.
Interestingly, several respondents have also purchased
the houses in SSTE as a second home for investment
purposes. Indeed, it is not an unusual practice for the
Chinese upper-middle class to own several properties. As
one resident shared with us:
You don’t see many people here every day, even though
we are told that the housing development has been sold
out! It is very obvious at night when you see many of the
unlit homes. Most of the buyers use this as a second
holiday home or as a form of property speculation. You
can’t really prevent that . . . It’s everywhere in China.
Arguably, eco-cities such as SSTE may risk becoming
another real-estate speculation project. As Chien argues,
rather than truly sustainable communities, eco-city projects in China are better understood as entrepreneurial
projects carried out according to ‘flexible local discretion in line with central policies and novel narratives of
land commodification under the green economy’ (2013,
176). More critically, for Asian developmental states
Area 2014 doi: 10.1111/area.12128
© 2014 Royal Geographical Society (with the Institute of British Geographers)
8
Modelling green urbanism in China
engaging in policy learning and knowledge transfer, the
environment is yet another field to be tamed, managed
and mobilised to sustain capital accumulation while
complex social-environmental contradictions are being
suppressed and incorporated into the built environment
through the very act of building such ‘eco-cities’. More
pointedly, as Hoffman (2011, 64) notes, in this new
regime of green urbanism in Asia, techniques of green
city-building are reflective of national economic
agendas and local entrepreneurial goals as well as more
benign concerns for ecological and environmental wellbeing of the city.
In the final analysis, the SSTE project profiled in this
paper raises the larger question of what exactly is an
(Asian) eco-city and how does it speak to broader
debates on policy mobility and green urbanism. To be
sure, many of the social-economic and environmental
contradictions that we have highlighted earlier in the
paper are not unique to Asian cities and have in fact
plagued almost all modern industrialising cities around
the world. However, these contradictions and tensions
are arguably magnified and accentuated in eco-cities
such as SSTE due to the underlying imperative of the
developmental states (in this case Singapore and Tianjin/
China) who derive their political legitimacy from sustained economic growth and the continual exploitation
of the environment while ‘balancing’ economicenvironmental growth. In other words, solving the urban
‘sustainability fix’ through ecological modernisation is
arguably more pronounced and fraught with socialenvironmental
contradictions
in Asia’s
rapidly
globalising cities. To this extent, what the SSTE ultimately signifies is the ecological imagineering of green
urbanism and policy networks forged between entrepreneurial urban regimes (and transnational capital) eager
to reinvent themselves with a purported eco-city model
that is ‘future proof’ against looming environmental
crisis.
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