Abstract
The “new urban governance” has made rapid inroads as an approach to govern the transition to more environmentally sustainable buildings and cities. It allows for a broad repertoire of actors and instruments in the governing of this transition and is expected to overcome some of the pervasive problems of mandatory regulation and legislation for urban development and transformation. This article studies six new urban governance practices in India based on a series of interviews with relevant actors. It seeks to better understand the opportunities and risks of this approach to urban governance for governing India’s rapid urbanization. It finds that the new urban governance holds some promise but is also critical of it. Particularly, the lack of mandatory urban regulation and legislation, the lack of institutional capital, and a culture of corruption in India undermine the promise that the new urban governance holds in this context.
Keywords
India faces unprecedented urbanization. This is requiring rapid growth in India’s cities in general and its building stock in particular, adding to the nation’s already unsustainable levels of resource consumption and carbon emissions. To make things more pressing, building-related resource consumption and carbon emissions in India are projected to grow faster than its urban population. The urbanization trend is combined with rapid economic development, the rise of India’s middle class, and a move toward suburbanization. It is therefore likely that people and firms in India will demand larger, more luxurious, and, thus, more resource and carbon-intensive buildings. This will only amplify the environmental pressures caused by urbanization (Sen, 2013).
Governing urban growth is one of India’s key environmental challenges (Evans, Shui, & Somasundaram, 2009). Fortunately, the technology exists to develop buildings that are more environmentally sustainable than conventional ones—that is, buildings that are resource efficient and less carbon intensive—and much knowledge is available on how to use buildings in more environmentally sustainable ways (van der Heijden, 2014). This knowledge and technology hold a huge potential for cost-effective reductions of resource consumption and carbon emissions in India (Sen, 2013). Unfortunately, in India, traditional governance instruments, such as building codes and planning legislation, have been unable to accelerate the transition to environmentally sustainable building and city development and transformation (Aijaz, 2012; Roy, 2009).
In seeking to address this issue, India has implemented reforms of its urban environmental governance regime and has begun to experiment with “new urban governance” processes and instruments (Boyd & Ghosh, 2013; Dubash & Jogesh, 2014). This new urban governance is characterized by, first, a shift away from government as the sole authority in governing urban problems toward the involvement of public and private sector stakeholders for that purpose. Second, there is a shift toward networks and collaborations of stakeholders to address these problems. Third, there is an interest in governance instruments that encourage self-organization, market solutions, or both as substitutes for or complements to mandatory command-and-control style instruments. Fourth, there is a shift toward instruments that reward voluntary compliance as opposed to enforcing mandated behavior (Bingham, 2006; Blanco, 2013; Hohn & Neuer, 2006; Holley, Gunningham, & Shearing, 2012).
This article seeks to better understand the opportunities and the risks of new urban governance practices for environmentally sustainable building and city development in India. The next section sets the scene and addresses the dominant urban governance approaches for sustainable building and city development in India and the complications they face. The article then briefly reviews the literature on the new urban governance and the broader and related literature on the new governance, seeking to understand what may be expected of this approach to governance in governing the expected urban growth in India. Then, it examines six examples of the new urban governance practices to gain insight into the opportunities and risks of this approach to governance in real-world settings in India. The article concludes by identifying the main lessons learned.
Dominant Urban Governance for Sustainable Building and City Development in India
Urban governance in India is a complex patchwork of tasks and responsibilities among national, state, and local governments (Aijaz, 2012; Baud & de Wit, 2009). The responsibility for governing environmentally sustainable building and city development is upon state governments, which can delegate these responsibilities to local governments. The key governance instruments in this area are building codes and zoning legislation. But there is much variety between cities (Aijaz, 2012); existing codes and legislation generally do not consider environmental sustainability (Murthy, 2010); codes and legislation are often dated or poorly enforced, which limits their effectiveness (Sen, 2013); and building control is often de facto inexistent in smaller cities because of a lack of funds (McKinsey, 2010).
The national government of India seeks to influence building and city development through national policies and framework legislation. It has, however, no statutory power to directly govern sustainable building and city development through building regulation and planning legislation. That being said, the national government has long sought to govern building and city development indirectly. A first key governance intervention was the National Housing and Habitat Policy of 1998. It primarily sought to address the housing shortage in India but had, as one of its objectives, increasing the use of then available technology to improve the energy efficiency of the housing sector (Government of India, 2001). In 2001, the Government of India implemented the Energy Conservation Act. This act promoted energy conservation and efficiency, mandated the foundation of the Bureau of Energy Efficiency, and authorized this Bureau to develop and implement an Energy Conservation Building Code. This code was established in 2007 and sets minimum energy efficiency requirements for buildings. The code is, however, voluntary, and state governments are not actively mandating it in their jurisdictions: By the end of 2014, only two states had fully adopted it (Vedela, Bilolokar, Jaiswal, Connolly, & Deol, 2014). Another dominant governance instrument was the Jawaharlal Nehru National Urban Renewal Mission, which was launched by the Government of India in 2005 and completed in 2014. It supported 67 selected cities in the implementation of infrastructure projects and governance reforms. It had a focus, among others, on urban environmental sustainability (Jain, 2010). In 2008, the Government of India launched the National Action Plan on Climate Change, which outlines existing and future policies and programs addressing climate change adaptation and mitigation (Government of India, 2008; Srinivasan, Ling, & Mori, 2012). 1
While scholars, practitioners, and policy makers are generally positive about the ambition of the Government of India to address environmentally sustainable building and city development, they are critical of the practicality of the governance instruments introduced and governance processes followed. First, they do not address the key problem of the weak and poorly organized government agencies responsible for urban affairs, including environmentally sustainable building development and use, nor do they address the problems of poor (law) enforcement and corruption in the construction and property sectors (Aijaz, 2012; KPMG, 2011). The instruments were further considered lenient in terms of energy efficiency and other environmental sustainability requirements (compared with other countries), were introduced fairly late (again compared with other countries), and were introduced as voluntary, rather than mandatory, requirements (International Energy Agency, 2013; Vedela et al., 2014). They are expected to achieve minimal results, especially because government officials, as well as individuals and firms in the construction and property sectors, often lack knowledge about how to construct, maintain, and use buildings in an environmentally sustainable manner (International Energy Agency, 2013). A final point of critique is that these governance instruments address only future buildings but do not apply (retrospectively) to existing buildings in India (Sen, 2013; The Energy and Resources Institute [TERI], 2009). This is problematic because India’s current building stock is already causing pressing environmental challenges.
The New Urban Governance: Characteristics and Expectations
In response to these complications, governments at different levels and throughout India have begun to experiment with alternative governance processes and instruments for environmentally sustainable building and city development. They fit a broader international trend that has become known as the “new urban governance” (Bingham, 2006; Blanco, 2013; Hohn & Neuer, 2006)—an approach to governance that itself fits broader changes in the governing of societal risks, which has been theorized as “new governance” and “new environmental governance” (Holley et al., 2012; Lobel, 2012; Wurzel, Zito, & Jordan, 2013). Broadly speaking, this new urban governance includes the addressing of urban problems through networks and collaborations of public and private stakeholders and allows for the inclusion of a broad palette of governance instruments—including market-based instruments and voluntary programs (Bulkeley & Betsill, 2013; van der Heijden, 2014).
This new urban governance has achieved much acclaim for what it is potentially able to achieve in terms of effective urban governance, particularly in the area of urban environmental sustainability. While scholars typically avoid drawing up a fixed definition for the phenomenon of the new urban governance, they have introduced a range of conditions that typify the processes and instruments of the new urban governance. In terms of the new urban governance as a process, scholars argue that it is less hierarchical and less government-centered than traditional governance processes. In the development of (new) urban governance instruments, governments are more open to collaborating with nongovernmental actors, consulting with them, or even allowing nongovernmental actors to take the lead in developing instruments (Bingham, 2006; Hohn & Neuer, 2006).
Such heterarchical processes are expected to come with a number of advantages over traditional hierarchical processes. By involving a wide range of stakeholders in the development of governance instruments, their tacit knowledge can be used. This is expected to result in instruments that are “smarter” than those developed by somewhat distant bureaucrats (De Búrca & Scott, 2006; Lobel, 2012). Also, by involving a range of stakeholders, instruments can be developed through a consensus-building process that allows for a reflection on the advantages and disadvantages of the instrument for the various parties involved. This is expected to bridge their diverse and sometimes rival views (Bulkeley & Mol, 2003; Holley et al., 2012). It is further expected to increase the acceptance of the instruments that are developed and implemented and, correspondingly, to improve compliance with them (Scott & Trubek, 2002; Walters, 2004).
In terms of the design of the new governance instruments, scholars focus particularly on the move away from traditional deterrence-based hard law instruments that penalize noncompliance, such as building codes, to soft law instruments that reward compliance and provide positive incentives. Such positive incentives come, for example, in the form of information, the ability to market compliant behavior, or some form of financial compensation. These positive incentives are, again, expected to increase compliance (Scott & Trubek, 2002). Scholars further point to a move away from mandatory governance instruments toward those that ask for voluntary commitments, again expecting that compliance is more likely when individuals and firms commit voluntarily to instruments than when they are mandated to do so (Borck & Coglianese, 2009; van der Heijden, 2014). Finally, they highlight a move away from prescriptive rules that specify how compliance should be achieved toward the use of performance-based standards that allow those subject to these instruments (some) flexibility in how to comply. This is expected to make those subject to these instruments more willing to move beyond mere bottom-line compliance (Carrigan & Coglianese, 2011; Jänicke & Jörgens, 2006).
That being said in praise of the new urban governance, an emerging empirical body of literature is critical of its capability to deliver on these normative expectations (Holley et al., 2012; van der Heijden, 2014). Empirical studies have often found that new governance arrangements are not able to attract large numbers of participants, fail to change the behavior of their participants, or are captured by self-interested private actors (Gupta, Pfeffer, Verrest, & Ros-Tonen, 2015; Read & Pekkanen, 2009). The effectiveness of the new urban governance appears to depend strongly on the design of the instruments, as well as the context in which they are implemented. In addition, the literature on the new urban governance is biased toward studying cases in the global North and lacks an understanding of the promise of this approach in governing rapidly developing countries in the global South, such as India (Blackman, 2008; Blackman, Uribe, van Hoof, & Lyon, 2013; but see Boyd & Ghosh, 2013). In the following sections, six new governance practices (instruments and processes) for sustainable building and city development in India are assessed in light of the expectations regarding new urban governance that have been expressed in the literature.
Six New Urban Governance Practices in India
The six examples of new urban governance practices for sustainable building development and use were studied as part of a larger research study on new governance for sustainable building development and use globally (van der Heijden, 2014). The examples were identified through Internet searches and desk research. They can be understood as illustrative of the broader trend of new urban governance practices (cf. Yin, 2003). By no means, however, does this article claim that the six examples are representative of all possible process and instrument designs and contexts of such new urban governance practices in India. The six examples were selected because they each show some or all of the key characteristics of the new (urban) governance: reliance on voluntary compliance mechanisms, inclusion of nongovernmental actors in their development and implementation, and the inclusion of market-based mechanisms and other incentives.
Overview of Interviewees.
The interviews were recorded, and based on the recording and notes taken during the interviews, a summary report was drafted that was sent back to the interviewees for validation. The interviewees were often aware of and involved in more than one new urban governance practice. It is expected that this (partly) helped overcome a sampling bias of the administrators (and the participants) who were overly enthusiastic about their “own” example (Sanderson, 2002). The interviews lasted approximately 1 hour each and were generally conducted at the interviewees’ work locations. The interview data and additional data were processed by means of a systematic coding scheme and qualitative data analysis software (Atlas.ti). Using this approach, the data were systematically explored, and insight was gained into the “repetitiveness” and “rarity” of experiences shared by the interviewees.
Broad Overview of New Urban Governance Practices Studied.
Note. LEED = Leadership in Energy and Environmental Design; USAID = United States Agency for International Development; GRIHA = Green Rating for Integrated Habitat Assessment; TERI = The Energy and Resources Institute; IIEC = International Institute for Energy Conservation; PEARL = Peer Experience and Reflective Learning.
LEED India, GRIHA, and Eco-Housing
The dominant new governance instrument for sustainable building and city development in India is certification. It allows the resource consumption of buildings, their carbon intensity, or both to be made visible and helps building developers and property owners to market the environmental sustainability credentials of their buildings. Often, certification is introduced as a voluntary alternative to existing mandatory governance instruments such as building codes—and around the globe, this is the prevailing design of new governance instruments for sustainable buildings (van der Heijden, 2014).
Various such voluntary certification instruments have been implemented in India. The government-supported TERI introduced the Green Rating for Integrated Habitat Assessment (GRIHA) certification scheme in 2007 (Ministry of New and Renewable Energy, 2012). The Pune Municipal Corporation (the building authority in the city of Pune) introduced a certification scheme for environmentally sustainable housing development in 2004 called Eco-Housing. This instrument was developed in collaboration with the United States Agency for International Development (USAID), the University of Pune, the University of Ahmedabad, the International Institute for Energy Conservation, and TERI (International Institute for Energy Conservation, 2009). Finally, the Green Building Council of India, a construction and property sector peak body, adopted a widely used international certification instrument, Leadership in Energy and Environmental Design (LEED), and adapted it to fit the Indian context (Indian Green Building Council, 2013). It was introduced under the name LEED India in 2001, and the Green Building Council of India was initially supported by the United States Green Building Council and USAID.
All of these instruments were introduced because of the lack of mandatory requirements for environmentally sustainable building development in India—and all of the instruments build on international examples of certification instruments. At the outset, these instruments produced promising performance. LEED India has, for example, been applied to close to 3,000 building projects, with a total built up space of more than 2.5 billion square feet throughout India (Indian Green Building Council, 2015), and the local Eco-Housing instrument has certified some 16 million square feet. 2 But what do these numbers actually mean? If we scratch a little under the surface of the performance reported, it becomes clear that the answer to that question is “not much.” As the interviewees explained, the numbers presented by instrument administrators reveal wishful thinking at best, and they often illustrate a reality that is only on paper. First, these instruments allow for the certification of building designs, as well as buildings that are built. The majority of certificates issued are awarded to building designs, but it remains to be seen whether these buildings will actually be constructed. Eco-Housing is illustrative here: Less than 3% of the certified buildings have been completed. The interviewees mentioned similar numbers for LEED India. “These programmes show intention,” the principal of an architectural firm mentioned, “but not actual performance. Probably less than one per cent of new buildings in India are certified” (interviewee 154).3,4
A second problem with these instruments is that they are prone to abuse—intended or unintended. During construction, a builder may deviate from the certified building design, or the occupants may use a certified building in ways that go against its sustainability credentials. This problem has been widely documented for building certification (van der Heijden, 2015). The interviewees warned that, particularly in contexts where corruption is the rule rather than the exception, such as the property and construction industries in India (Vittal, 2012), these voluntary certification programs run the risk of being violated. For the administrators of GRIHA, this was the reason why buildings should be certified only after completion, when the real performance of a building can be measured. “It is all about mind-set. People here are used to getting away with violations,” a GRIHA administrator said. “This is why GRIHA measures performance in operation and not expected performance as designed. This is especially important in a culture where lenient compliance is often the norm,” she continued (interviewee 199). This structure of checks and balances appears, however, to be appreciated less by property developers and owners: Fewer than 100 GRIHA-certified projects have been realized throughout India since 2007. 5
A final problem pointed out by the interviewees and the additional data is that these instruments are applied only to the absolute top end of the property sector—new flagship office buildings and housing projects in major cities—but not to ordinary buildings. This is where property developers see a market in which (future) property owners and occupants are willing to pay a premium for sustainable buildings. But in other areas, they do not see this profitable market. In addition to the limited uptake of this type of instrument, it may also result in a situation in which environmentally sustainable buildings and city districts are only achievable for a very small portion of the Indian population: The housing units developed under the Eco-Housing program in Pune sell at 10 million Indian rupees (US$150,000), a sum that is well out of reach for most of Pune’s citizens. 6
PEARL
Pearl Experience and Reflective Learning network, or PEARL, is India’s first formal network of cities. It served as a knowledge-sharing platform contribution to the implementation of the Jawaharlal Nehru National Urban Renewal Mission and has been continued as a capacity building and knowledge network (PEARL, 2010; Vaidya, Dhar, & Dasgupta Sur, 2010). PEARL brings together the 67 selected Jawaharlal Nehru National Urban Renewal Mission cities and seeks to ensure that these cities share knowledge and learn from each other and, by doing so, ensure that the goals of the mission are achieved. It was launched in 2007 by the National Institute of Urban Affairs and is supported by the Ministry of Urban Development, the World Bank, and Cities Alliances. One of the most innovative aspects of PEARL is the twinning of cities. This is a concept in which a better performing city is paired with a less well-performing city, and it aims to transfer the lessons learned by the former city to the latter.
PEARL collects and communicates lessons about the implementation of the Mission through a regular newsletter, documents best practices in reports, regularly organizes workshops and seminars for participating cities, and maintains a website that further communicates lessons about the implementation of the Mission. By 2015, close to 150 best practices were available on the PEARL website, and the website itself had been accessed close to 90,000 times.
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The broad and easy availability of information relevant to city officials is especially considered to be one of the key successes of the PEARL by the network’s administrators and participants. As a public official in New Delhi explained, One of the most positive outcomes is that it has set a lot of changes into motion. It has changed mindsets that a reform-linked funding scheme has the potential to achieve systemic changes in the way cites are governed and managed in India. (interviewee 198; see futher, Vaidya et al., 2010)
With this critique of the comptroller and auditor general in mind, it is somewhat surprising to see the praise that PEARL has received as a successful example of a new urban governance practice in rapidly developing economies by a range of international civil society organizations (International Council for Local Environmental Initiatives, 2011; Rockefeller Foundation, 2010; United Nations Development Programme, 2009), as well as by scholars and the media within and outside of India (Maher, 2012; Sharma, Nagar, & Sodhi, 2014; Sivaramakrishnan, 2011). While the complications of implementing the Jawaharlal Nehru National Urban Renewal Mission highlighted by the Comptroller and Auditor General were not caused by PEARL, it is relevant here to remember that PEARL was set up, among other things, specifically to prevent such complications from occurring in the first place. The general positive attention given to PEARL often lacks any form of critical inquiry in terms of whether, how, and what sort of success the program has achieved. The broad narrative of success, while arguably somewhat flawed, has nevertheless attracted the attention of international organizations such as the World Bank and Cities Alliance, which have been willing to provide financial support for PEARL (Cities Alliance, 2008; World Bank, 2011). Keeping in mind that these organizations have their own targets to meet, it makes sense for them to support a practice that has been evidenced to be “successful” rather than an unknown one (Hughes & Hutchings, 2011; Jepson, 2005).
Mumbai First
Mumbai First is a collaboration between local businesses and government in Mumbai. It was founded in 1995 by a number of major businesses, then under the name Bombay First.
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It builds on a similar initiative in the United Kingdom, London First, and during its start-up period, it received support from the British Council. This was a period of economic downturn in Mumbai. One of the key administrators of Mumbai First explained: Back then, the textile industry had collapsed, and the initiators of Mumbai First realised that Mumbai had lost its place as an area for investment, both nationally and internationally. The question then was: How can we get Mumbai back on the map? (interviewee 168)
In its first 5 years, Mumbai First predominantly focused on promoting the city as an international hub for investment, but it did not receive much response from local authorities. It then sought a change of course, and instead of trying to affect the government through reports and media campaigns, it sought to directly engage and collaborate with it. A group of private sector representatives started a conversation with the chief minister of the state of Maharashtra, of which Mumbai is the capital, to discuss the state of the built environment in Mumbai, including its environmental sustainability. In collaboration with the government (especially the Ministry of Planning), a research study was started to seek a future development strategy for the city (Mumbai First, 2014; Nallathiga, 2005). In 2003, together with the government of the state of Maharashtra, Mumbai First commissioned McKinsey, an international management consulting firm, to prepare a study that assessed Mumbai’s strengths and opportunities, and it created a vision for transforming the city. This vision document, Vision Mumbai – Transforming Mumbai Into a World-Class City (McKinsey, 2003), was endorsed by the government of the state of Maharashtra and the World Bank. With this endorsement, its transition from a private partnership into a private–public collaboration with international support was made (Nayar, 2010).
The vision document identified housing, among other things, as one of Mumbai’s most serious problems—in terms of quantity and quality. It addressed the problem of the city’s slums and called for a reduction of them. The document made a further call for the creation of urban housing zones with public housing for the urban poor over a 10-year period (McKinsey, 2003). By transforming the slums, it was expected that higher levels of built environment sustainability could be realized—through better designed and constructed housing, better city planning, and modern amenities. Unfortunately, the vision document was acted upon all too swiftly in 2004: In what has become known as the “Indian Tsunami,” government authorities demolished a range of slums in Mumbai before providing alternative housing possibilities. This rendered 300,000 people homeless (Roy, 2012).
Building on the vision document, the Government of Maharashtra developed an action plan, Transforming Mumbai Into a World-Class City (Government of Maharashtra, 2004). The goals and ambitions of the action plan largely overlap with those of the vision document but formalize them. The action plan, in turn, lies at the base of the “Mumbai Transformation Program,” which is a formal policy comprising more than 40 projects to improve economic growth in Mumbai, reduce poverty, and improve the quality of the built environment (Cities Alliance, 2013). The program was financially supported by the Jawaharlal Nehru National Urban Renewal Mission. It further receives financial, administrative, and technical support from Cities Alliance, the World Bank, and USAID. These organizations are further involved in documenting progress, and they serve as an interface between the various stakeholders involved. Particularly, the relatively short time to develop the program and the inclusion of local firms, local government, and international stakeholders in its development and implementation are considered key successes of Mumbai First (Chattaraj, 2012; Cities Alliance, 2013).
That being said in praise of Mumbai First, it goes without saying that the participants in Mumbai First also have a very strong private agenda. After all, if their vision of Mumbai as an international hub for investment is realized, they will be the first to welcome private investments. While this is the main incentive for participants to collaborate with governmental actors, there is a risk that the latter will be too easily captured or that Mumbai First will lack the level of public accountability and transparency that may be expected from public and governmental organizations. Particularly because this is a business-to-government collaboration, there is a risk that the business actors involved, rather than the governmental actors, will drive the agenda (cf. Gupta et al., 2015).
Open Mumbai
A final example of a new urban governance practice for environmentally sustainable building and city development in India is Open Mumbai. Open Mumbai is an ongoing project that seeks to highlight the link between formal city development, informal housing development, and environmental degradation in Mumbai (Das, 2012). Particularly, Mumbai’s green corridors, such as its waterways and mangroves, were traditionally not considered to be formal spaces for development or other planning activities in Mumbai’s planning documents. These informal spaces logically became the areas where slum dwellers set up their settlements. Yet, in doing so, they added to urban sprawl, water and soil pollution, and the clearing of green space for housing (Shah & Joshi, 2010).
It has long been unknown exactly how many urban poor live in Mumbai and exactly how much of the city’s land is taken up by informal housing and slums. The Mumbai Development Plan, the statutory document that lays out land use and development control in the city, did not adequately represent the urban poor and slum areas. This provided the Municipal Corporation of Greater Mumbai (MCGM), Mumbai’s primary agency responsible for urban governance in the city, with a unique opportunity to “play with the data” and to deny that the urban poor and slums amounted to a serious problem in Mumbai (SDI, 2014). The reality in Mumbai is, of course, different. Even when flying in to the city, one can see its slums spilling over onto the airport grounds. When taking a rickshaw, taxi, or train from the airport to the city center, one begins to get an idea of the amount of informal housing in the city. It appears to line every train track, border every highway, and take up much public and green space in the city (see also Mahadevia, Joshi, & Sharma, 2009; Shah & Joshi, 2010).
Open Mumbai influences the development process of Mumbai’s planning process through interactions with policy makers and the public. For some 15 years, it has been led by a Mumbai-based architect. Along with a team of people, he has mapped and documented Mumbai’s slums and has written extensively on the relationship between urban development, slums, and environmental risks. In 2012, this work was brought together in an exhibition held at the National Gallery of Modern Art in Mumbai, as well as in a book (Das, 2012). This was during the period when the MCGM was developing the current Mumbai Development Plan, which will be in force from 2014 to 2034 (MCGM, 2013)—the development of this plan was a requirement under the Jawaharlal Nehru National Urban Renewal Mission (Mahadevia et al., 2009). Open Mumbai has been able to clearly point out and make the living conditions of the urban poor widely visible: It concludes that more than 50% of Mumbai’s population, close to 6.5 million people (as per the 2011 census), live in slums; furthermore, it has developed a number of maps that clearly point out the locations of informal housing in Mumbai.
These maps have become known as the “Mumbai Slum Maps.” Intriguingly, they illustrate that not only is there a need for a comprehensive master plan for slum redevelopment but that it is also possible to house the urban poor in affordable housing and in an environmentally sustainable manner (Das, 2011). One of the major achievements of Open Mumbai is that, through the maps, “for the first time [the bureaucrats see] Mumbai the way we [the people involved in Open Mumbai] see it” (Nair, 2012, p. 8). The Slum Maps were the central aspect of the 2012 exhibition and attracted much media attention. This resulted in a counter media offensive by the MCGM. A top bureaucrat of the Municipal Corporation, accompanied by 75 of his staff, attended the exhibition, an event that was well covered by the media, at which he publicly stated: “The study [Open Mumbai] is useful for all the stakeholders in the development of Mumbai, especially the Municipal Corporation, to alert them about where urgent attention is required” (Gurav, 2012, p. 10). The current Mumbai Development Plan was notably influenced by the Mumbai Slum Maps, and it now includes the city’s various slum areas. The Municipal Corporation has further entered into dialogue with the people involved in Open Mumbai to discuss the various solutions that they have in mind to improve the housing conditions of the urban poor, as well as improve the environmental sustainability of the city as a whole (Rangwale, 2013).
Discussion
This concluding section discusses the details of the relevant similarities and differences and lessons learnt across the six new urban governance practices. It assesses, in more depth, the newness of this new urban governance, its major opportunities for low-carbon building and city development and transformation in India, and its main risks.
What Is New About the New Urban Governance in India?
Any concept coined with the term new ultimately loses its newness. Particularly in the global North, where most of the theorizing on the new urban governance has emerged, this approach to urban governance appears to be the rule rather than the exception (Bulkeley & Betsill, 2013; van der Heijden, 2014). This appears to be less the case in India, where the type of new urban governance practices discussed in this article is still seeing only marginal application (see also Boyd & Ghosh, 2013). Particularly new about this approach to urban governance in the Indian context is that it seeks and helps to overcome the shortfalls of the formal institutional setting for environmentally sustainable urban governance—currently a complex patchwork of tasks and responsibilities that are allocated to governments at all levels.
Another novelty with respect to the examples discussed is that they are, often, driven by more than environmental sustainability at the building and city level. The certification instruments are built on market forces—buildings that are certified under these instruments are expected to yield higher sales or rental prices. PEARL seeks to align a wide range of city development goals—including environmental sustainability, housing and infrastructure development, and modernized public service delivery. Mumbai First combines market forces—the personal interests of participating firms—with the overall development of Mumbai. Finally, Open Mumbai links urban environmental sustainability with informal housing in the city. This breaks away from the tradition in Indian policy making of developing environmental sustainability policies in isolation from other policy areas and interests (Boyd & Ghosh, 2013; Jayal & Mehta, 2010).
That being said, the six new urban governance practices studied appear to operate in isolation from each other. For example, while TERI is involved in both GRIHA and Eco-Housing, the certification instruments themselves do not overlap. Or, while Mumbai First and Open Mumbai aim to achieve broadly similar aims, there is no evidence—from the interviews and additional data—that the two work together.
Opportunities: A Repertoire of Actors, Innovative Collaborations, and Complementary Instruments
Following the literature on new urban governance, one of the main strengths of this approach to urban governance in India is that it allows for a broad repertoire of actors in the governing of urban environmental sustainability. LEED India is almost fully driven by private sector actors and has resulted in a voluntary governance instrument for environmentally sustainable building design and development that reaches well beyond the ambitions of mandatory building regulation in India. The inclusion of private sector actors in Mumbai First and private and civil society actors in Open Mumbai has allowed for the inclusion of valuable tacit knowledge in the Mumbai Development Plan—knowledge that the MCGM would otherwise not have obtained.
Second, innovative and sometimes unexpected collaborations have emerged. The collaboration between Open Mumbai and the National Gallery of Modern Art turned out to be an extremely strong way to reach out to the citizens of Mumbai, the local press, and, finally, the Municipal Corporation. More conventional collaborations are those that include international organizations such as USAID, the World Bank, and Cities Alliances. These organizations may have more interest in supporting new governance practices than traditional policy and governance practices in India. Such processes resonate well with these organizations’ (normative) vision of contemporary governance, which are often inspired by governance innovations that have proved to be successful in the global North (Hughes & Hutchings, 2011).
Third and finally, different governance instruments have developed under these new governance practices as complements to the existing ones. Most illustrative are the various voluntary certification instruments—a national private instrument, a national public instrument, and a local public instrument—that complement the building codes in India. But the city network PEARL has also provided some insight into novel instruments—such as city twinning and a publicly accessible website with city performance data—that provide promising complements to more traditional governance instruments for low-carbon building and city development and transformation in India.
Risks: No Shadow of Hierarchy, Weak Institutional Capital, and Potential Inequalities
While providing some potential to improve low-carbon building and city development and transformation in India, the new urban governance should not be relied on to an excessive degree. The six practices point out a number of related risks.
The first of these risks seems somewhat paradoxical: While the new urban governance has emerged to overcome the weakness of formal urban governance in this area, it is exactly this weakness that limits the performance of the new governance practices studied. The literature on new governance often discusses the role of formal and mandatory regulation and governance as a necessary backbone for new governance practices to be effective; this is often referred to as “the shadow of hierarchy” (Héritier & Eckert, 2008). The idea is that formal and mandatory regulation and governance act as a benchmark that the new governance seeks to improve or that they can come into play when the new governance fails. In the global North, certification instruments often require limited improvement over the benchmark set by mandatory building regulation (van der Heijden, 2015), yet in India, instruments such as LEED India and GRIHA ask for major improvements, compared with the virtually absent building codes. Also, it is often argued that, in the global North, voluntary certification instruments are introduced and committed, particularly by firms, to prevent the introduction of mandatory governmental regulation (Borck & Coglianese, 2009). Yet, in India, with its complex governance patchwork for urban environmental sustainability, it is unlikely that any mandatory governmental regulation will be implemented in the short or medium term.
Second, the new urban governance practices hardly address the problem of the weak institutional capital in the area of urban development in India. The interviewees were generally critical of a lack of compliance with mandatory building regulation and planning legislation—often due to a lack of staff at government agencies—and a culture of corruption in the construction and property sectors (see also Vittal, 2012). New urban governance practices rely strongly on self-regulation by the regulated actors and introduce incentives that may result in deviant behavior—in particular, financial incentives may be accompanied by this risk. Such practices provide a poor patch up for the situation of weak institutional capital (cf. Short, 2013). It remains, of course, a question as to whether other forms of governance are capable of overcoming these problems of corruption, capture of regulators, and weak institutional capital (cf. Mitnick, 2011).
Third and finally, new urban governance practices may result in (unintended) inequalities. The example of Eco-Housing is telling—Eco-Housing-certified homes are unaffordable for the average citizen of Pune—but Mumbai First also points to this risk. The firms that make up Mumbai First have strong personal interests in seeing specific urban development realized. Through Mumbai First, they actively lobby for such development. Others citizens of and firms in Mumbai do not have such direct access to policy makers. This may result in situations in which the interests of the firms that make up Mumbai First are served over those of others—the “Indian Tsunami” provides a tragic illustration.
Concluding Remarks
The new urban governance provides some solutions for governing the rapid urbanization of India, particularly in the area of urban environmental sustainability. The opening up of governance processes to nonstate actors allows for the usage of their tacit knowledge and expertise; furthermore, the shift to less traditional and noncoercive governance instruments has allowed for a relatively speedy implementation of instruments that respond to local urban conditions. The new urban governance also comes, however, with considerable risks. Particularly, the lack of a mandatory urban sustainable development and transformation legislation and regulation to fall back on when the new urban governance fails to achieve its goals, as well as the persistent problem of corruption, makes this approach to governing urban development and transformation play out differently in India than in the countries in the global North, where it originated. While the new urban governance has global appeal—politically and theoretically—it should not be expected to act as a global panacea for the problems in urban environmental governance. This is not a novel insight. The new urban governance is being critiqued more and more for not living up to its normative promises (Holley et al., 2012; van der Heijden, 2014).
The six examples from India add to this growing critique of the new urban governance. At first glance, all of the examples hold much promise in terms of reducing the carbon intensities of the cities, but in practice, they do not reveal a large number of participants who are interested in joining the new urban governance practices, or they face complications in changing the behavior of their participants. The six examples also provide novel insights into the (critical) literature on the new urban governance. They indicate that specific contextual conditions have a strong impact on how new urban governance practices play out in real-world settings. Specifically in contexts in which there is a lack of institutional capital and mandatory regulation and legislation (the “shadow of the law”), there is a culture of noncompliance with building codes and planning legislation, and corruption is rife, the problems of the new urban governance that have been identified in the global North will likely be amplified. This raises questions about the desirability of the new urban governance in countries in the global South, including India. Future scholarship may wish to focus more on the conditions that explain the successes and failures of the new urban governance, and specifically, the critical differences in contextual conditions between countries in the global North and global South. International nongovernmental organizations such as the World Bank and Cities Alliance may, in turn, wish to reconsider their strong support and promotion of new urban governance practices in India and other rapidly developing economies. The six examples studied in this article indicate that simply because a governance innovation achieves promising results in the global North, it should by no means be expected that it will also achieve promising results in the global South. Policy makers, finally, may wish to call for strong democratic accountability processes when entering in new urban governance practices.
Footnotes
Acknowledgments
Many thanks to four anonymous reviewers for suggested changes to an earlier version of the article. All usual disclaimers apply.
Declaration of Conflicting Interests
The author declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.
Funding
The author disclosed receipt of the following financial support for the research, authorship, and/or publication of this article: This article was supported by a VENI grant from the Netherlands Organisation for Scientific Research (grant number 45111015) and a DECRA grant from the Australian Research Council (grant number DE15100511).
