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SOAC 2017 Auckland’s Urban Sprawl, Planning Frameworks and Peri-Urbanisation to Pukekohe. Cristian Silva School of Architecture and Planning, University of Auckland, Auckland, New Zealand Abstract: Although urban sprawl has been largely discussed, the range of determinants for the incorporation of rural lands remain less systematised and mainly framed by transport improvements, housing shortage and land- market constraints. Because of that, measures to tackle impacts of sprawl are lacking considering that its determinants operate as interlinked and somehow embedded within planning policies and regulations. Additionally, some of them rely on rural forces, landowners’ interests and rural plans outside urban boundaries that influence land-use changes of peri-urban areas. This paper discusses these interlinked determinants placed in planning regulations to demonstrate that many of them are indeed supported by, finally stimulating further suburbanisation. This is contextualised in Auckland and illustrated through the case of Pukekohe – a recently incorporated rural village for housing intensification – in which key regulations of control provide enough flexibility to incorporate agriculturally productive lands. The paper concludes that planning tools for controlling sprawl in Auckland are still partial in their capability to manage dispersed suburbanisation and to integrate the complex spectrum of rural forces and environmental values that define the character of peri- urban lands. Key words: Urban Sprawl; Planning Policies; Peri-Urbanisation; Auckland; Pukekohe 1 Introduction Urban sprawl has been widely discussed from different perspectives but mainly driven by the housing debate (Phelps, 2012; Charmes and Keil, 2015) and transformation of peri-urban areas (Gallent and Shaw, 2007; Ravetz and Loibl, 2011). In this light, there is a persistent focus on understanding sprawl as an uncontrolled phenomenon – barely addressed by regulatory frameworks – that illustrates a dislocation between ‘the planned city’ and ‘the real one’ defined by random additions of peri-urban lands (Qian and Wong, 2012). Nevertheless, urban sprawl occurs in the scope of planning regulations suggesting that missed determinants are still pending to be included or simply that planning rationales deliberately contribute to urban sprawl (Bruegmann, 2005; Couch and Karecha, 2006; Kombe, 2005). This paradoxical condition of ‘controlling and enabling’ is less explicit in the planning literature – apart from contradictions of neoliberal planning schemes – but is clearly illustrated from the literature on political ecology, ecosystem services, natural capital and green- infrastructure, in which planning mechanisms appear as ignoring environmental and rural forces (Tacoli, 1998; Zhang et al., 2013; Heynen et al., 2006). This partly explains the large number of uncompleted projects driven by urban design frameworks as substantial transformations of peri-

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Page 1: apo.org.au · Web viewIn the Australasian context, for instance, although mechanisms to control extended peri-urbanisation it is nevertheless the most persistent trend (Hamel and

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Auckland’s Urban Sprawl, Planning Frameworks and Peri-Urbanisation to Pukekohe.

Cristian SilvaSchool of Architecture and Planning, University of Auckland, Auckland, New Zealand

Abstract: Although urban sprawl has been largely discussed, the range of determinants for the incorporation of rural lands remain less systematised and mainly framed by transport improvements, housing shortage and land-market constraints. Because of that, measures to tackle impacts of sprawl are lacking considering that its determinants operate as interlinked and somehow embedded within planning policies and regulations. Additionally, some of them rely on rural forces, landowners’ interests and rural plans outside urban boundaries that influence land-use changes of peri-urban areas. This paper discusses these interlinked determinants placed in planning regulations to demonstrate that many of them are indeed supported by, finally stimulating further suburbanisation. This is contextualised in Auckland and illustrated through the case of Pukekohe – a recently incorporated rural village for housing intensification – in which key regulations of control provide enough flexibility to incorporate agriculturally productive lands. The paper concludes that planning tools for controlling sprawl in Auckland are still partial in their capability to manage dispersed suburbanisation and to integrate the complex spectrum of rural forces and environmental values that define the character of peri-urban lands.

Key words: Urban Sprawl; Planning Policies; Peri-Urbanisation; Auckland; Pukekohe

1 Introduction Urban sprawl has been widely discussed from different perspectives but mainly driven by the housing debate (Phelps, 2012; Charmes and Keil, 2015) and transformation of peri-urban areas (Gallent and Shaw, 2007; Ravetz and Loibl, 2011). In this light, there is a persistent focus on understanding sprawl as an uncontrolled phenomenon – barely addressed by regulatory frameworks – that illustrates a dislocation between ‘the planned city’ and ‘the real one’ defined by random additions of peri-urban lands (Qian and Wong, 2012). Nevertheless, urban sprawl occurs in the scope of planning regulations suggesting that missed determinants are still pending to be included or simply that planning rationales deliberately contribute to urban sprawl (Bruegmann, 2005; Couch and Karecha, 2006; Kombe, 2005).

This paradoxical condition of ‘controlling and enabling’ is less explicit in the planning literature – apart from contradictions of neoliberal planning schemes – but is clearly illustrated from the literature on political ecology, ecosystem services, natural capital and green-infrastructure, in which planning mechanisms appear as ignoring environmental and rural forces (Tacoli, 1998; Zhang et al., 2013; Heynen et al., 2006). This partly explains the large number of uncompleted projects driven by urban design frameworks as substantial transformations of peri-urban lands often follow differing directions or ‘out of plan’ contingencies (Keil and Macdonald, 2016; Vallance, 2014; Carrion-Flores, 2004; Keeble, 1995). In the Australasian context, for instance, although mechanisms to control extended peri-urbanisation it is nevertheless the most persistent trend (Hamel and Keil, 2015) driven by finally ambiguous regulations and norms (Forster, 2006; Willing and Pojani, 2017).

In the case of Auckland, controlling sprawl relies on a metropolitan plan that incorporates peri-urban lands under two figures: the ‘Rural Urban Boundary’ (RUB) and ‘satellite towns’. One of those satellites is the southern rural village of Pukekohe – distanced 50km from central Auckland – consolidated as a rural service town (Auckland Council, 2012, Pukekohe Area Plan, 2014). Apart from its inclusion for housing intensification, the plan does not disclose the arguments to set up specific agricultural properties between Pukekohe and Auckland, or the interests of rural landowners in changing peri-urban land-uses. This is particularly relevant as Pukekohe’s surroundings are agriculturally productive and reputed by a series of well-known environmental services (Powell and Lambert, 2013; Curran-Cournane et al., 2014; Curran-Cournane et al., 2016). Several authors have highlighted this issue describing consolidation of urban sprawl from non-urban goals, opening a more regional understanding of suburbanisation (Keil and Macdonald, 2016; Vallance, 2014; Carrion-Flores, 2004).

The aim of this paper is to discuss planning policies as the scope of interlinked determinants of urban sprawl to then inspect the presence (and absences) of rural dimensions on peri-urbanisation in Auckland. It would demonstrate that Auckland’s sprawl is driven by planning schemes and rural dynamics although clear aims for controlling the expansion. This is empirically exemplified by the

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incorporation of Pukekohe, to finally conclude that Auckland’s regulations contribute to traditional sprawl. It is suggested that more sustainable planning should include urban-rural dynamics based on the understanding of peri-urban boundaries as a different geography that deserves its own planning approach.

2 MethodologyThe analysis presented in this paper is part of a larger study aimed to inspect the different determinants of Auckland’s urban sprawl linked to the role of rural landowners in transforming peri-urban lands. In this paper, a fraction of collected data is discussed mainly based on analysis of key planning policies and regulations. This research is particularly relevant considering multidimensional efforts for controlling Auckland’s extended suburbanisation through different instruments, including intensifying suburban zones and improvements on transportation.

The research adopted a qualitative approach to examine policy conflicts to understand the extent to which planning policies give effect to urban sprawl it employs a document analysis approach (Bowen, 2009) collated to empirical data from official statistical databases. Key planning documents analysed are The Auckland Plan, The Auckland Unitary Plan (Operative in Part 2016), the Rural Urban Boundary Report, Transport Issues Report (The Auckland Unitary Plan), Rural Production (Greenfield Study Areas), the Addendum for The Rural Urban Boundary (Auckland Unitary Plan), the Capacity for Growth Study (2006), the Pukekohe Area Plan (2014) and The Auckland Council District Plan (Operative Franklin Section 2000). Documentary review also includes secondary research, government reports, masterplans and urban design proposal, statistical databases, and relevant journalistic reports related to the Pukekohe and Auckland’s urban growth.

Site visits are still being undertaken and aimed to observe the peri-urban space subject to housing intensification. Among limitations, considering that this is an ongoing research, methods are predominantly focused on document analysis and will be complemented with semi-structured interviews with central and local planners, policy-makers, developers and rural landowners of relevant peri-urban areas. The research is also limited by the lack of secondary research on Pukekohe from an urban planning perspective. However, this is complemented by environmental studies on the Pukekohe area and its agricultural attributes. What is still unpacked, are the interests of peri-urban landowners in transforming Auckland’s urban-rural boundary.

3 The ambiguous nature of urban sprawl Urban sprawl is generalised to describe most of patterns of urban growth in almost all cities, assuming that sprawl is the expression of uncontrolled determinants although planning regulations of control (Oueslati et al., 2015; Pirotte and Madre, 2011). There are different constraints in disclosing its determinants, but they are mainly related to the understanding of sprawl as such, the nature of planning policies, and the inclusion of a wider range of factors placed on the rural scope.

Regarding conceptual understandings, there is a consensus in indicating that not all patterns of urban growth can be properly identified as an instance of ‘urban sprawl’ and thus, determinants of urban growth not necessarily explain urban sprawl as such. There is still an open debate regarding the elements that define a sprawling pattern and the boundaries of a sprawling area (Barnes et al., 2001; Ewing et al., 2002; Wolman et al., 2005). At any case, ‘urban growth’ as ‘urban sprawl’ follows two streams of arguments. First, the idea of dispersed suburbanisation driven by the increasing use of private cars driven by construction of motorway systems (Gillham, 2002; Soule, 2006), and second, the increasing demand for living near the countryside signalised as ‘suburbanisation’ (Hamel and Keil, 2015; Hess, et al., 2001). A morphological consensus describes sprawl as largely characterised by low-density residential neighbourhoods, regional transport infrastructure, car-dependency, single land-uses and lack of physical continuity (Torrens, 2006; Barnes, et al., 2001; Jaret, et al., 2009). As such, it is highly criticised for its environmental, social and economic impacts (Gallent and Shaw, 2007; Thomas, 2001).

Although critics, morphological descriptions are insufficient to indicate any form of urban growth as ‘sprawl’ and thus, more policy-based factors are considered. Nelson (1999) asserts that land-use conversion, population change, traffic and vehicle miles travelled, energy consumption and fiscal measures are relevant in defining sprawl (Nelson, 1999). Also, technical studies suggest that a set of indicators are crucial to determine ‘the sprawl index’ and thus, identify an urban area as in sprawling condition (Galster, et al., 2001; Wolman et al., 2005; Jaret et al., 2009)

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Another conceptual constraint pertains to the assumption that urban sprawl is an ‘urban’ issue, not possible to be explained from different categories of suburbanisation (Peiser, 2001; Gillham, 2002; Harvey and Works, 2002; Irwin and Bockstael, 2007; Leontidou and Couch, 2007). However, emerging literature links urban sprawl with transformation of fringe-belt areas not purely driven by urban forces. It appears as a non-exclusive dimension of the urban realm that embraces urban-rural interactions, depicted by mixed landscapes composed by urbanised fragments interspersed with rural lands. So, the idea of ‘urbanized countryside’ proposed by Sieverts (2003) arises to better describe this ambiguous urban-rural territory, understood as a new geography which is neither urban nor rural at all but that embraces characteristic of both (Sieverts, 2003). Tacoli (1998) argues that urban sprawl and peri-urban areas are conceptually problematic because urban and rural activities take place in the same geographical space, a hybrid zone in which agricultural and non-agricultural activities spatially and functionally coexist (Tacoli, 1998). It suggests that peri-urban areas are not simply unintended encroachments of the rural space for the city, but a spatial category in its own right in which different institutional representations shape distinctive modes of suburban governance (Hamel and Keil, 2015) and define a spatial category that deserves particular attention and alternative policy approaches (Wandl and Magoni, 2017). So, urban sprawl is complex, ambiguous and multifaceted, and not only determined by urban but also rural fluctuations. This clarification is relevant because urban sprawl is nevertheless a continuous incorporation of peri-urban lands and thus, a process that should be assessed more by its dynamics rather than its static and transitional fragmentation (Hess, et al., 2001).

4 The urban-rural boundary and planning implications As a dynamic process, urban sprawl defines different configurations over time. It could be heterogeneous in its degree of land fragmentation and functional complexity, even within the same urban region and thus, could not show a homogeneous urban-rural interface (Ravetz and Loibl, 2011; Qian and Wong, 2012).Advanced stages of suburbanisation define new complexities of urban-rural boundaries characterised by increasing functional self-sufficiency, concentration of employment and a certain degree of disconnection from traditional urban centres (Charmes and Keil, 2015; Phelps and Wood, 2011; Calthorpe and Fulton, 2001). Similarly, contemporary peri-urban boundaries appear as scenarios of emerging patterns of ‘polycentricity’ in which different sub-centres attract population and employment growth (Van Oort, et al., 2010; Kloosterman, and Lambregts, 2001). From a regional viewpoint, ‘multi-functionality’ describes peri-urban boundaries where different functions coexist linking urban and rural activities (Gallent and Shaw, 2007; Faludi et al., 1996; Fazal et al., 2012). These spaces are more multifaceted and complete suburbanisation processes – beyond residential land-use – such as conurbations zones or satellite towns that as part of wider urban-regional systems (Burger and Meijers, 2011; Van Oort et al., 2010; Roe and Saglie, 2011).

For some, the varied character of peri-urban boundaries appears as expression of advanced capitalist processes in which market trends and asymmetric institutional relations delay planning reactions and leave instruments of control behind de facto situations. In this context, successful land management relies on individuals’ leadership capacities and clearly exceed the supremacy of technical solutions or macro-scale plans (Kombe, 2005; Phelps, 2012). It reinforces the idea that planning orthodoxies should be reinterpreted in the light of emerging realities and acceptation of peri-urban boundaries as independent territorial categories (Wandl, 2017; Gallent and Shaw, 2007). There is a view that planning rationales leave crucial determinants of suburbanisation aside – including those placed in the rural realm – or simply that they implicitly arrange the uncontrolled transformation of peri-urban lands by omission. Indeed, anti-growth narratives assumes sprawl as ‘unplanned’, evincing its unintended nature driven by unforeseen determinants (Hebbert, 1986). Therefore, a closer inspection of planning policies is needed as it could provide a wider understanding of the extent to which urban sprawl is implicitly triggered by the same instruments that aim to control it.

5 Planning policies, urban sprawl and peri-urbanisation Empirical studies identify determinants of urban sprawl as causal factors linked to housing policies, land market constraints and infrastructure (Oueslati.et al., 2015). Nevertheless, there are some limitations as they are based on European realities and monocentric city models characterised by clear relations between land fragmentation, land prices and income growth triggering suburbanisation (Oueslati.et al., 2015; Pirotte and Madre, 2010; Hamel and Keil, 2015). Social factors such as rates of crime in central areas also encourage suburbanisation along with land-use changes of agricultural lands closer to urban markets (Qian and Wong, 2012; Van Leeuwen and Nijkamp, 2006). In this light, it is recognised that closer inspection on the different planning dimensions and policies is needed for a wider understanding of rationales that enhance suburbanisation at different levels (Pirotte and Madre, 2010; Oueslati et al., 2015).

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5.1. Transport infrastructureA well-discussed determinant that operates upon peri-urbanisation pertains to the inclusion of rural lands near transport infrastructure. This is also criticised because although planned, these areas are not always consolidated and define strong pressure on land-use changes (Weber and Puissant, 2003; Camagni, et al., 2002; Zhang et al., 2013). Transport is a strong indicator of land competitiveness that encourage developers and public authorities to obtain parcels well served by roads or early information on future political decisions related to transport investments (Gillham, 2002; Soule, 2006; Cervero, 2003; Keil and Young, 2011; Batten, 1995).

5.2 The ‘suburban dream’ It is also clear that middle-class population demand available lands to fulfil the long-standing desire of living near the countryside according to income increments and access to private cars (Ekers et al., 2012). This is complemented by the fact that rural lands outside urban limits tend to be cheaper, affordable for new families led by the ‘suburban dream’ (Hess et al., 2001; Beauregard, 2005; Phelps, 2012).

5.3 Cheaper outer lands Cheaper outer lands also lead suburbanisation beyond consolidated areas. It defines different levels of land fragmentation as developers build new neighbourhoods at some distance from existing urban areas creating a series of vacant parcels in-between that contribute to fragmentation of urban boundaries (Holcombe, 1999). It supposes affordability and advantages related to the open space and thus, residents accept longer commutes in exchange of lower-priced houses (ibid, 1999).

5.4 The ‘urban limit’ The presence of the so-called ‘urban limit’ to control the expansion also contributes to urban sprawl and peri-urbanisation. Depending on the region, it could take the form of a virtual line in a map or a concrete zone around the city (such as the ‘Green Belts’) in which construction is restricted or simply prohibited (Gallent and Shaw, 2007; Kühn, 2003; Morrison, 2010). At any case, the ‘urban limit’ appears as an unsuccessful tool as it does not stop the expansion at all and even works in an opposite way (Grimes and Liang, 2009; Petermann, 2006; Evans, 2006; Schulze, 2010). According to López (1981) this is a disturbing tool as the division of a land in ‘urban’ and ‘rural’ by an arbitrary line increases its value without any condition or extra-cost for the owner. Additionally, land division encourages landowners to change functions of those portions outside the limit as their profitability increases with a real estate development. So, the ‘urban limit’ has a paradoxical effect: while it tries to prevent uncontrolled growth, it creates a perverse incentive for incorporating the countryside trying to modify norms and functions (López, 1981). As a side-effect, low-income families use to be relocated further away on cheaper lands – increasing distances to work places – or on rural villages that define local pressures for services triggered by unplanned demographic increments.

5.5 The absence of an ‘urban limit’ Detractors of the ‘urban limit’ consider its abolition for increasing the land-stock and thus, affordability (Petermann, 2006; Gross, 1991; Pavez, 2011). However, if this measure is not linked to market regulations what is seen is that peri-urban landowners keep their lands undeveloped to gain value over time. Therefore, the peri-urban area can enter into a fast land-price increment that creates expensive and unaffordable rings around the city. Thus, new families should be relocated on remote areas or rural villages many times without proportional responses on transport and services (Ducci, 1998; Rodriguez y Sugranyes, 2004).

5.6 Conurbation zonesAnother determinant that shapes peri-urbanisation are conurbation zones. Mainly linked to transport infrastructure these areas are increasingly complex due to unregulated coexistences of rural and urban functions (Kassa, 2013). On the one hand, several rural plots still keep animals and factories that increasingly disturb new residents who decided living near clean and quiet environments (Ducci and Gonzalez, 2006; Banerjee et al., 2012; Zhang et al., 2013). On the other hand, encroachment of agricultural lands diminishes their performances and quality of impervious surfaces triggering environmental deregulations. As a consequence, along with relocating industrial facilities unexpected superficial water flood local and external areas and diminishes agricultural fertility (Curran-Cournane et al., 2016; Barkasi et al., 2012)

5.7 Regeneration policies The absence of regeneration policies to recover underused spaces also contributes to sprawling expansion. Implementation of revamping processes of inner lands appears as expensive and without

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political support to address brownfields, landfills and other infrastructural lands (Silva, 2017; Frantál et al., 2015). Additionally, clusters of private landowners that form larger suburban vacant lands not always coincide in development interests and thus, leave their lands undeveloped contributing to relocation of new developments on peri-urban areas (Gilly and Wallet., 2001; Adams et al., 1994)

5.8 Taxation on empty lands Weak taxation (or any form of impact fee) on undeveloped inner lands contributes to peri-urbanisation as landowners leave properties empty for catching value over time (Song and Zenou, 2006; Clawson, 1962). In some cases, it derives to physical land’s erosions due to the lack of security and maintenance that finally affects the overall suburban landscape. So, lack of taxation on undeveloped, derelict, abandoned, vacant, underused or even inner lands trigger further peri-urbanisation and reinforce detriments of internal areas by lack of maintenance, cleaning or security ( Ige and Atanda, 2013; Foo et al., 2013).

5.9 Institutional asymmetriesThe encroachment of the peri-urban boundary is also determined by institutional asymmetries between rural and urban representations. Unbalanced power between ministries of agriculture, food, environment, infrastructure, housing, and others define the extent to which urbanisation will take place on peri-urban boundaries. These processes are highly sensitive to political and technical capacities for managing land development beyond urban limits, relying on actors’ support conferred by legal attributions (De Zeeuw et al., 2000; La Greca et al., 2011). Specifically, agricultural authorities use to be in a political position in which rejecting urbanisation on rural lands are unpopular, and have very limited influence in defining the urban limit and other conditions for preserving rural areas (De Zeeuw et al., 2000; Pothukuchi and Kaufman, 1999).

6 Auckland’s urban sprawl, the urban-rural boundary and PukekoheAuckland is the largest city of New Zealand, recognised as one of the most important urbanised areas in the whole Pacific Rim (Statistic New Zealand, 2014; Memon et al., 2007). It is home to one third of New Zealand’s population (Chambers & Walters, 2013) and over the next 30 years is going to accommodate 60% of population growth – increasing from 1.5 million to 2.3 million people – mainly fuelled by natural growth and both internal and overseas migrations (Statistic New Zealand, 2014). It is also known that the city is currently facing substantial environmental pressures linked to the rapid population growth, urban expansion, suburban intensification and increasing needs of infrastructure and services (Mattingly and Morrisey, 2014; Eason et al., 2003b).

Considering that Auckland is often commented as an instance of traditional suburbanisation (McArthur, 2017; Gu, 2010; Mouat and Dodson, 2013; Latham, 2000), determinants that explain this condition are less discussed and still perceived as somehow failed efforts from planning instruments for controlling peri-urbanisation (Gunder, 2002; Bradbury and Bogunovich, 2013; Memon et al., 2007). It is worth noticing that planning instruments in New Zealand operates at national and regional levels and give special relevance to urban growth strategies, housing and urban design regulations, most of them matched with contemporary narratives of urban sustainability (Mattingly and Morrissey, 2014; Ghosh and Vale, 2009; Dupuis and Dixon, 2002).

Although seen as an example of a developed-world city, Auckland is nevertheless characterised by implications associated to urban sprawl (Memon et al., 2007). During the last 20 years, Auckland has evolved from a traditional agglomeration of suburban districts towards an amalgamated metropolitan entity regulated by a general framework plan: ‘The Auckland Unitary Plan’. This contemplates current Auckland’s growth but also expansion on urban boundaries and rural areas, and simultaneously advocates for a ‘compact city model’ indicating that a 70% of future urban developments will be placed within the urban boundaries and a 30% outside the consolidated area (Auckland Council, 2102). Bradbuty and Bogunovich (2013), however, indicates that future urban growth in Auckland could describe a more detailed geographical expansion that somehow vanish the abrupt urban-rural opposition opening at least four zones – urban, suburban, peri-urban and ex-urban – that would configure its character as city-region (Bradbuty and Bogunovich, 2013).

In the light of a more complex peri-urban geography, Auckland’s suburbanisation emerges as relatively homogeneous as it still follows traditional low-density residential patterns (Ghosh and Vale, 2009) and thus, the plan advocates for a more compact city model associated to benefits of residential densification/intensification (Allen, 2015; Carroll et al., 2011). Although the plan aims to consolidate ‘the world’s most liveable city’ (The Auckland Plan, 2012, pp. 18), it also states the need for expansive

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growth, peri-urban and ex-urban extensions that contribute to urban sprawl and associated detriments. To control this apparently paradoxical figure, urban development outside boundaries would be limited with exception of the selected locations of Warksworth in the North and Pukekekohe in the South, both small villages surrounded by agricultural and environmental assets (Bradbuty and Bogunovich, 2013). Aside from differing positions, expansion areas are necessary considering current housing shortage, but their inclusion is criticised due to the environmental impacts of urbanisation on a series of well-reputed ecosystem services (Curran-Cournane et al., 2014). This countered view is partly explained from consolidation of a neoliberal agenda that still cannot harmonise economic growth with environmental protection, and thus, leads to more unregulated and flexible approaches that emphasise managing impacts of activities rather than prescribing to support economic efficiency and growth (Memon et al., 2007; Berke et al., 2006; Gunder, 2104).

Supposedly and under this rationale, suburbanisation beyond the limits would improve housing affordability. However, Grimes and Liang (2008) argue that Auckland does not describe a typical economic geography to assume that outer lands become cheaper. That argue that Auckland will be more polycentric, surrounded by natural amenities that increment land prices and additionally distorted urban limits and other restrictions that do not have methods for land-value capture (Grimes and Liang, 2008). This is more critical considering that ‘affordability’ is still debatable and undefined in current New Zealand legislation (Brebner, 2014). The Auckland Plan states that ‘there is no agreed definition or measure of “affordable” or “unaffordable” housing’ (The Auckland Plan, 2012, pp. 269) but indicates that housing affordability is still a priority considering ‘the housing crisis’ (ibid: 269), and because Auckland is recognised as the highest price-to-rent ratio and the second highest price-to-income ratio of countries that belong to OECD (OECD, 2014). To address this issue, the Plan indicates the release of land in the ‘Rural Urban Boundary’ (RUB) to ensure sufficient development capacity (The Auckland Plan, 2012) considering that value of land within the limit is around nine times higher that prices just outside (Brebner, 2014).

6.1 The Rural Urban Boundary (RUB) and PukekoheThe RUB is a key tool for the general control of Auckland’s extended suburbanisation. It replaced the ‘Metropolitan Urban Limit’ (MUL) in 2010 and defined a geographical zone formed by rural and urban areas complemented by infrastructure and services (Auckland Council, 2012). The Auckland Plan clearly indicates that – although proposed growth zones – the RUB would provide flexible conditions that allow up to 40% of new homes can be built outside the urban limit in well-planned Greenfields, necessary to ensure land availability for the next 30 years to meet housing needs (ibid, 2012). This approach is to provide certainty for communities, landowners, infrastructure providers and developers on where Auckland will experience the most significant changes. The RUB is based on land availability and states that natural features (rather than environmental or ecological properties) will be considered to provide well-defined physical boundaries (ibid, 2012). For the Auckland Unitary Plan, the RUB is a geographical space ‘that will define the maximum extent of urban development to 2040 in the form of permanent rural-urban interface’ (Addendum, 2013a, pp. 07), and embraces part of the metropolitan area, rural-coastal villages, and the satellite towns of Warkworth in the North and Pukekohe in the South. It indicates that the RUB encourages further growth in existing urban areas to protect the rural space. Nevertheless, it also states that Greenfield areas for investigation will be delineated by the RUB and thus, urban boundaries can be reshaped (ibid, 2013).

Although the plan also states that urban expansion on rural villages must ‘avoid urbanisation of highly productive farmland and versatile soils where possible…’ (The Auckland Plan, 2012, pp. 230), it simultaneously considers re-zoning rural lands for future urbanisation as a ‘zone intended to allow rural activities to continue until urban development can take place’ (ibid, 2013b, pp. 4), explicitly determining their temporary character. Once transformed into urban, it indicates that their value increase with the concurrent transference of wealth to the landowner (windfall gain as outcome of rezoning decisions) and thus, the plan proposes that the Council receives a proportion of this land-value capture to re-investing on infrastructure, public goods, affordable housing or further growth. However, this mechanism is still pending as the Local Government Act should be first changed to ensure proper power to levy it (ibid: 2013b). Overall, peri-urban and rural lands that surround Auckland are subject to urbanisation as part of the RUB that defines a fragmented landscape of still agriculturally productive agricultural lands and satellite towns.

Pukekohe – one of these satellites located at the Franklin district – and its rural surrounding illustrate how extended suburbanisation operates from metropolitan regulations on highly productive rural lands. It includes the areas of Paerata and Drury located between Pukekohe and Auckland, all intended for housing intensification and well served by transport infrastructure (Auckland Council, 2017) (Figure 01). This area is recognised as one of the most fertile lands of the Auckland region, known for its frost-

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free climate and highly productive rural soils largely used for vegetable production (Curran-Cournane et al., 2016; Moran, 1979). It embraces around the 86% of Class 1 land – considered a powerhouse in terms of outdoor vegetable production (Statistics NZ, 2011) – and source of a significant economic activity and employment in the whole Auckland region and the highest amongst all other regions in New Zealand (Curran-Cournane et al., 2016).

This area is also identified in rural studies as one of the main sources of relevant Greenfield sites to be protected from urban encroachment, highlighted for food provision for the entire region (Powell and Lambert, 2013). Only the southern space composed by Karaka, Paerata and Pukekohe contributes with around a 60 % of the whole turnover per hectare dominated by dairying, livestock grazing, vegetable growing and cropping. They have soils labelled as Class I, II and III that define the Franklin district as the most competitive in terms of exports to other regions and local supply (ibid, 2013). The Pukekohe area ‘…has some of the most productive soils in New Zealand and has long been associated with market gardening’ (Franklin District Plan, 2000, pp. 1) predominantly located in future urban development zones that can clearly diminishes their productivity and impacts on the overall economy as – along with northern Greenfields – contributes with 10.6% of the Auckland region’s GDP (ibid, 2013).

01. Auckland region and expansion areas.

Auckland Region’s Rural Soils, Auckland Plan and Pukekohe Expansion Areas (Author’s image based on Auckland Unitary Plan, 2012 and Pukekohe Area Plan, 2104).

In terms of urbanisation rate, the plan states that 400,000 additional households should be completed by 2040, and that 40% – including employment growth – will be located outside metropolitan boundaries including Pukekohe, rural coastal towns, greenfield areas for investigation and rural villages (Addendum, 2013a). Here, Pukekohe area is intended to host around 50,000 people, up to 55,000 dwellings and 35,000 jobs (Arbury, 2012). The areas for urbanisation around Pukekohe are the ‘core’ areas of Paerata North, Pukekohe North East, Pukekohe West, Pukekohe South and Drury, all for housing intensification (ibid, 2012). Prioritised scenarios have been defined around transportation corridors and hubs – highly considered in comparison to other Greenfields – as they have significant implications in public expenditure. This would significantly extent Auckland’s urban area and the size of Pukekohe.

Following the adoption of the Auckland Plan, Pukekohe was zoned ‘future urban’ in the Unitary Plan. Subsequently, the Future Urban Land Supply Strategy, adopted to sequence the development of future urban areas across the Auckland Region, determined that part of Pukekohe be available for urban development now with remaining areas coming on stream from 2023 (Auckland Council, 2017). An area is considered ‘development ready’ if bulk infrastructure is available and if quality urban outcomes, as outlined in the Auckland Plan and the Unitary Plan, can be achieved (ibid, 2017). The

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anticipated dwelling capacity for Pukekohe is approximately 7,920 (ibid, 2017). Within the bounds of the RUB, and as enabled in the Unitary Plan, the Future Urban Land Supply Strategy identifies when urban development can begin to expand into the previously rural area between the existing urban area and the RUB.

Although economic and environmental contributions, maintaining rural properties is becoming increasingly expensive, partly because of high-costs associated with land ownership. High land-values mean that rural producers may need to produce goods more efficiently, sell into high-value market niches or increase productivity per hectare to become competitive. As alternative, cross-subsidise rural production costs with off-farm income emerges for supplying commercial rate of return. Nevertheless, it also triggers strong incentives for land subdivisions following urban purposes, finally, translated into various environmental impacts related to land fragmentation (Powell and Lambert, 2013). It is expected that the area finally becomes a desirable place to live partly stimulated by planned transport improvements and its definition in the Auckland Unitary Plan for housing intensification (Auckland Council, 2012).

7 Conclusions Urban sprawl is mainly seen as an unexpected outcome of planning policies and regulations. However, they also enhance extended suburbanisation as simultaneously provide contradictory definitions and flexible interpretations on land restrictions. This is partly explained by the understanding of urban sprawl as an ‘urban’ phenomenon led by centralised policies – rather than a regional one – that does not include rural forces and environmental values that operate upon peri-urban lands. The understanding of this rural-regional dimension of sprawl suggests alternative approaches for planning the urban-rural interface. The ‘urbanized countryside’ could shift the way of traditional functions – based on exclusive farming productivity or purely housing intensification – to activities that decrease natural processes and incorporate the rural character as part of the urban environment, finally challenging planning for ecological modernisation.

In the case of Auckland and its extension to Pukekohe, several studies highlight the ecological dimension of this peri-urban boundary. However, suburban growth cannot be restrained and is indeed prospected by planning instruments to enhance traditional suburbanisation. In this vein, it is expected that planning and building practices to consolidate Auckland’s boundaries consider their highly efficient agricultural performance – including rural landowners’ interests – to harmonise urban and environmental values. To do so, it worth exploring different figures to regulate peri-urban boundaries as they emerge as a different geography that deserves a planning approach in its own right.

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