An Interpretation of Sustainable 
Development and Urban Sustainability 
in Low-Cost Housing and Settlements 
in South Africa
Daniel K. Irurah and Brian Boshoff

Introduction: Sustainable development and sustainable urban form

The sustainable development paradigm can be viewed as a convergence of two paradigms 

that initially evolved in an antagonistic manner, possibly as far back as the industrial 

revolution. The first one is the growth and development paradigm, which was strongly 

rooted in economic growth based on the economic output of an economy as measured 

by GDP (gross domestic product). Until the late 1900s, governments and communities 

had committed themselves to a vision of improved standards of living through increasing 

the GDP of their respective economies, while paying minimal attention to environmental 

and resource impacts.

Then in the 1950s to 1970s the environmental movement coalesced after almost a 

century of isolated pronouncements on resource and environmental degradation 

arising from exponen tial population growth as well as increasing levels of production 

and consumption. The movement argued that unless humanity voluntarily controlled 

population and economic growth, environmental and resource degradation would put 

a limit on human survival. The strongest substantiation of the argument was presented 

in the Club of Rome Report, Limits to Growth (Meadows et al., 1972).

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The challenge of reconciling the concerns of the two movements or paradigms 

emerged as a global imperative in the 1970s in an effort to prepare for action in the 

twenty-first century. The United Nations Conference on Environment and Develop-

ment held in Stockholm in 1972 laid the foundation for this process. Through this 

conference, it became clear that the two issues could no longer be addressed separately 

or through the antagonistic approach that had been applied until then. Similarly, the 

need for a global framework of action became evident.

A United Nations-led initiative was launched under the World Commission on 

Environment and Development (WCED) in 1984. In 1987, the commission released 

its final report (Our Common Future), which has now become a primary reference  

on sustainable development. It is in this report that a globally derived definition of 

sustainable development was first presented, and it is the definition that has become 

most commonly used. The report defines sustainable development as:

… development that meets the needs of the present without compromising the ability of 
future generations to meet their own needs (WCED, 1987:43).

The important point to note about this definition is that it retained the development 

vision but with a condition that it should not be pursued at the expense of future 

generations. Several variations of the definition have emerged out of the intense 

debates over the relevance and implications of the paradigm (see for example the 

review of definitions in Mawhinney, 2002:2–24).

The elaboration of the paradigm during both the Earth Summit in Rio de Janeiro 

in 1992 (see Agenda 21 (UN, 1992)) and the World Summit for Sustainable Develop-

ment (WSSD) in Johannesburg in 2002 (see Johannesburg Plan of Implementation 

(UN, 2002)) has gone a long way towards establishing the roadmap for humanity in 

the twenty-first century and beyond.

The key implication of the paradigm is that for the wealthy developed countries, 

the challenge to be addressed is the stabilisation of economic growth through a shift 

away from over-production and over-consumption, as well as towards the redistribution 

of resources to the minority poor within these economies (and the majority poor in 

developing countries). For the poorer developing countries, the challenge is to stabilise 

population growth and fast-track growth responsibly in order to meet the basic needs 

of the majority now living in squalor, and to stabilise over-consumption by the 

wealthy elite.

These differentiated requirements of sustainable development for developed 

versus developing countries have been the root of intense debate and negotiation 

during the two earth summits (Earth Summit – Rio de Janeiro, 1992, and World 

Summit for Sustainable Development (WSSD) – Johannesburg, 2002). For example, 

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during the WSSD in Johannesburg, no firm targets could be agreed upon on the issue 

of over-production and over-consumption, especially in developed countries. Instead 

a ten-year framework was established within which to formulate appropriate 

programmes.

The redistribution of resources from developed to developing countries received 

much attention during the WSSD. For example, facilitation for the establishment of 

partnerships between the developed and developing countries’ stakeholders (through 

Type II partnerships) has opened an opportunity for both public- and private-sector 

resources to be channeled to developmental programmes in developing countries. Key 

Type II partnerships launched during the WSSD cover programmes in a variety of 

areas like water and sanitation, energy, health, agriculture and biodiversity.

In spite of the frustrations expressed by stakeholders with regard to the WSSD 

outcomes (for example, slow progress in implementation to date, refusal of the US to 

sign the Kyoto Protocol, inability to set targets for renewable energy and over-

production/over-consumption for developed countries), the summit provided a plan 

for increased momentum in the realisation of sustainable development.

This articulation of a new development paradigm for human civilisation in the 

twenty-first century has meant a re-examination of all facets of human activities and 

lifestyles with a view towards re-alignment for sustainability. This chapter provides a 

review of the implications of the paradigm for cities and human settlements, as well 

as the local interpretations of the paradigm in South Africa’s settlement policy and 

practice. However, the main focus of the chapter is on sustainable low-cost housing in 

South Africa in terms of policy and practice.

Sustainable cities and human settlements

Cities and human settlements constitute one of the most powerful tools of human 

civilisation and development. Lozano (1990:5) argues that:

Cities are civilization; the word ‘civilization’ – related to the Latin civilitas, civis, and civitas – 
refers to culture of cities, places where a heterogenous mixture of people are concentrated 
in clusters of meaningful size to exchange – exchange goods, services, and ideas.

When seen as systems of habitation, production and consumption, human settle-

ments, and especially contemporary cities, can be treated as macro-scale systems that 

require inputs for their metabolism. These inputs in turn generate by-products that 

often lead to waste and pollution. These two aspects of inputs and by-products of 

urban metabolism translate into major impacts on resources and the environment  

in general.

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The concept ‘ecological footprint’ of a city or settlement has been applied as a 

measure of the ecological impacts of individuals. The Redefining Progress Organisa-

tion in the USA estimates that the average American’s footprint on the planet is 24 

acres (the requirement to sustain current lifestyles) compared to 17 acres for the 

average Canadian and nine acres for the average Italian (Redefining Progress: www.

progress.org/programs/sustainability/ef/).

Under this concept, one tries to capture and quantify in one indicator the flow of 

key resources and the waste of a system or subsystem through various networks of 

channels. Beyond the ecological footprint, which captures only the environmental 

impacts, urban sustainability calls for development of human settlements guided by 

three additional pillars of sustainable development: economic growth, socio-cultural 

responsiveness and institutional capacity (Irurah et al., 2002:6–16).

Under environmental conservation, sustainable settlements and buildings envisage 

the emergence of cities and buildings that are responsive to the resource and sink 

limits of the planet. The resource limits entail the finite resource base especially for 

some of the key inputs in sustenance of cities and buildings. These include land and 

natural habitats, energy, water, construction materials and other raw materials for 

inputs to manufacturing and service industries. The sink limits focus on the finite 

capacity of air, land and water systems to receive and process waste generated as 

by-products of human production and consumption patterns. Greenhouse gases such 

as CO2, wastewater and solid waste are some of the examples.

Economic sustainability arises out of the need to ensure sustained functioning of 

the economic system, which sustains the flow of goods and services essential for 

human consumption and further production of wealth. Employment and job creation 

is one of the key goals of economic sustainability. However, the key sustainability 

challenge is the equitable distribution of benefits generated through economic 

activities as well as the mitigation of externalities generated by such activities and their 

impacts on those who do not necessarily benefit from the respective activities. Poverty 

alleviation is therefore a major component of economic sustainability.

Socio-cultural sustainability addresses the impacts of buildings and settlements on 

the social system and the related cultural values of households, communities and 

nations. The need for an enabling, equitable, non-discriminatory and just social 

system has emerged as the most pressing one in modern times. In this regard, the 

rights of vulnerable groups such as women, children, the aged and those with 

disabilities require special attention in the context of sustainable cities and buildings 

(both in production and habitation processes). In countries like South Africa, where 

an HIV/Aids epidemic is prevalent, a spatial and built environment response to the 

needs of the affected people is emerging as a critical challenge to sustainability.

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Institutional sustainability addresses the need for appropriate policy, legislation 

and implementation frameworks or structures in the public, private and civic sectors 

of society. Participatory processes in decision making, democratic and transparent 

governance, as well as public accountability in all the three sector-entities, are the key 

requirements for sustainability under this pillar.

The four pillars above (environmental, economic, socio-cultural and institutional) 

indicate that the concept of urban sustainability implies the need for assessment of the 

threat to continuity of a harmonious and vitalised inter-relationship between the 

inhabitants of the city and their social, economic and environmental subsystems. This 

perspective constitutes the motivation for sustainable development and urban 

sustainability indicators that are regularly derived and reported in order to track the 

state of, and changes in sustainability levels.

This in turn constitutes a framework for responsive action and strategies by the 

inhabitants to address the threats using the capacity and resources at their disposal. It 

is in this context that sustainable development and urban sustainability are considered 

to be a human-centred rather than an ecology-oriented paradigm. It is also in this 

context that the institutional component of urban sustainability emerges as it 

emphasises the need for both individual and collective responsibility and the 

appropriate strategies in addressing such threats.

Urban sustainability and urban form

The challenge of urban sustainability has generated intense debate on the appropriate 

urban form that can ensure the realisation of the respective sustainability objectives. 

Consequently, a variety of contrasting characterisations of urban forms have been 

regularly applied in the debate. Key characterisations include:

■ The compact versus the sprawl city

■ The integrated versus the segregated city

■ The ecological versus the non-ecological city

■ The just versus the unjust city

The compact versus the sprawl city

One of the primary resources consumed by cities is land, which is required for siting 

and development of the different urban functions such as commercial, industrial, 

residential and socio-cultural activities. Being a scarce resource, land-take for such 

urban functions means an opportunity cost with regard to alternative uses such as 

agriculture, nature conservation, mining and quarrying, among others.

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In the context of rapidly growing cities and settlements, the distribution of urban 

functions as well as the typologies used in the development of specific sites can 

translate into low- or high-density urban form and land utilisation. Low-density 

urban form is characterised by the suburban approach to development of housing 

and commercial facilities, as well as socio-cultural amenities in the form of pavilions 

or objects within a garden or park. The office park, suburban house and mall are 

typical examples of this approach. This in turn requires the development of long runs 

of bulk and connector infrastructure for various properties.

The main disadvantage of this approach is the high cost of infrastructure and 

services per property, as well as the need for commuting (which is mainly motorised) 

over long distances between the different functional zones of the city. Increasing 

segregation, loss of urbanism and weakening of socio-cultural practices (loss of 

cohesion) are often cited as additional shortcomings of this approach (Lozano, 

1990:6).

The compact city is frequently viewed as the more desirable urban form with 

regard to sustainability. Besides a higher density (mainly supported by low-rise 

buildings), compact cities exhibit high levels of mixed use in different zones or 

neighbourhoods, as well as enhanced quality of urban space, socio-cultural cohesion, 

safety and security (arising out of passive surveillance and social cohesion). Such cities 

therefore demonstrate high levels of environmental and socio-cultural sustainability 

and their ecological footprint is relatively low.

It is highly unlikely that any city can be considered to be totally sprawled or 

entirely compact. In most cases, examples of compact city neighbourhoods and 

sprawling suburban areas co-exist in a single city. A city can then be characterised on 

the basis of the predominant pattern of urban form. It is on this basis that American 

cities are on average considered to be sprawled cities while most European cities are 

considered to be compact.

Other contrasts in city form

The integrated versus the segregated city: When functional zoning of cities was the main 

planning and development control tool, the approach was to differentiate and 

segregate key urban functions based on their perceived levels of incompatibility. The 

non-compatible functions were zoned far apart with clear buffer zones of more 

compatible functions in-between. The sprawl city is one of the legacies of extreme 

functional zoning among other factors. The integrated city facilitates higher levels of 

mixed use in neighbourhoods and only zones off highly incompatible functions as 

well as those which require a large reservoir of land for their future growth (airports, 

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major industries and harbours, for example). South Africa’s cities are segregated and 

sprawled primarily as a result of racial zoning applied in the apartheid era (Gelderblom 

and Kok, 1994:101–105).

The non-ecological versus the ecological city (green or eco-cities): This characterisa-

tion of urban form is based on the ecological footprint of a city. Cities that make 

special efforts to tap into renewable resources (renewable energy, for example) or 

those which minimise resource and waste throughput in their metabolism (through 

conservation interventions or re-use/recycle, for instance) are viewed to be ecological. 

Most contemporary cities are considered to be non-ecological because of their heavy 

dependence on motorised transport, grid electricity (fossil-fuel, nuclear- or hydro-

generated power), virgin raw materials, low levels of re-use/recycle and sprawl over 

large tracts of land.

The socio-cultural dimensions of the debate about city form are often captured in 

the just versus the unjust city contrast. Besides ensuring environmental health and 

economic sustenance for all, a just city form exhibits interventions in response to 

threats to human rights and marginalisation of certain population groups. Key among 

such groups are the disabled, women and children. For countries such as South Africa, 

poverty reduction and narrowing of the income differential are major challenges in 

the just city context.

Before ending this section, it is important to note that all the urban characterisations 

above are at times inclusive of one another and conflicting in other instances. For 

example, the ecological city form has requirements that contradict with those of the 

compact city form (for example, emphasis on ample space for independent and 

organic food production based on permaculture and recycled waste or compost). 

Such contradictions between the ecological city and other sustainability requirements 

are comprehensively reviewed in Wortmann (1999:8–18).

This overview of the general sustainable development and sustainable city debates 

provides the framework used in reviewing the translation of the paradigm in the 

sustainable city and low-cost housing or settlement practices in South Africa.

Sustainable low-cost housing, urban sustainability and the  
sustainable development debate in South Africa

Although South Africa is a signatory to most of the international protocols on 

environmental conservation and sustainable development, their influence on the local 

development agenda is still minimal. For example, although Agenda 21 for Sustainable 

Development (including Local Agenda 21) and Habitat Agenda are well recognised in 

most policy frameworks of different government departments and local 

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authorities, there is no overall sustainable development framework to guide 

development policy in various sectors of the economy. Attempts at formulating a 

National Strategy for Sustainable Development (NSSD) under the Department of 

Environmental Affairs and Tourism (DEAT) have not delivered the required 

framework, even after several years in the process. Similarly, ad hoc sustainability 

initiatives now evident in the private sector have not converged to a coherent or 

systematic approach as yet. In contrast, the NGO and CBO sectors have managed to 

attract significant resources (financial, technical and managerial skills) from local and 

international donor agencies with the objective of addressing environmental and 

socio-economic sustainability issues such as energy efficiency, water conservation and 

poverty alleviation.

Since homelessness and poverty are the most glaring sustainability issues in 

South Africa (especially because of the ‘human face’ component and the impacts on 

the environment), a number of such NGOs and CBOs have focused on housing, 

social services, job creation and the related environmental challenges which can be 

addressed through housing delivery and habitat management. However, most of 

these initiatives are implemented on a project-by-project basis without significant 

synergy or impact on the broader housing delivery programme and urban development 

agenda.

It is the activities of such NGOs, CBOs and their related projects that have raised 

the sustainability debate around low-cost housing to heights well above the minor role 

of this sub-sector in the building construction sector and urban development in 

general. In so doing, two contradictory scenarios are emerging. The first scenario 

(business as usual) is one where such initiatives are confronted by immense challenges 

as they attempt to mainstream the practice of sustainable housing and human 

settlement. Consequently, they are ignored by government and/or the private sector, 

and none of the emerging lessons percolate into the construction sector and urban 

development or mainstream policy in general. If such challenges prove to be 

overwhelming to a point where diffusion of lessons learned from specific projects to 

general practice gets inhibited, momentum will be lost and the debate will dwindle.

The second scenario is where the initiatives as well as the related advocacy among 

different stakeholders translate into the adoption of such responses into policy, 

legislation and urban development frameworks at various levels of government. This 

could even translate into appropriate responses by the private sector, as the business 

case of such practice starts to emerge. Such a scenario would boost the momentum 

and could even see the low-cost housing sub-sector being the driver of sustainability 

in the building construction sector, urban development and the rest of the economy 

in general.

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The question at this point is: Which of the two scenarios is likely to prevail? A 

response to the question will be attempted in the concluding part of this chapter. The 

subsequent sections will map out the minor role of the low-cost housing sub-sector 

in building construction and the economy in general. This will be followed by 

examples of sustainability initiatives in housing by NGOs and CBOs in the context of 

South Africa’s housing subsidy programme. The final section before the conclusion 

will deal with indications of recent government response in terms of policies and 

guidelines in sustainable housing and the implication for urban sustainability.

Low-cost housing in the context of the building construction sector

Building construction is one of the 90 sectors of the South African economy, as 

applied in the input-output tables compiled by Statistics South Africa (see Statistics 

South Africa, 1995). The sector is also used as a data-capture category with regards to 

plans passed and buildings completed under different local authorities, employment 

opportunities and fixed capital formation, among others. Although there is no regular 

data capture of the environmental impacts of settlements and buildings, isolated 

studies on energy impact through production (embodied energy) and operation cycle 

of buildings have been undertaken (Irurah, 1997, 1998; Irurah and Holm, 1999). 

Irurah (1998) provided a preliminary overview on some of the environmental impacts 

of the cradle-to-grave cycle of building production, habitation, demolition and 

disposal of construction waste.

Although data on the low-cost housing sub-sector is not regularly captured under 

the above categories, there are indicative pieces of information showing that low-cost 

housing plays only a minor role in terms of economic and environmental impacts of 

the larger building sector. With regard to GDP and fixed capital formation, BIFSA 

(2000a:31) shows that in 1999, building construction contributed 3.3% and 20.4% 

respectively compared to 2.4% of GDP by civil construction. With regard to overall 

formal employment in 1999, civil construction absorbed 67 000 employees compared 

to 222 000 in building construction (BIFSA, 2000a:24). This clearly indicates that 

within the construction industry, the building construction sector dominates over 

civil construction.

Data from the Reserve Bank (2002:S-120) and BIFSA (2000b:13) indicates that 

although the residential sub-sector contributes almost the same ratio as the non-residential 

with regard to fixed capital formation, formal low-cost housing contributes only 10% of 

the sector’s turnover and capital formation. Equally, its consumption of inputs in 

production (construction materials, labour and services) and habitation (energy, water, 

waste disposal, etc.) can be assumed to be relatively low compared to 

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the other two sub-sectors (middle- to high-income residential and non-residential). 

However, in terms of absolute land take for settlements and impacts such as pollution 

(water, air and solid waste) from informal settlements without adequate levels of 

infrastructure and services, low-cost housing might entail significantly higher impacts 

compared to the other sub-sectors.

Total residential consumption of electricity accounts for less than 20%, while 

industrial and mining consumption shows the highest consumption of 63% 

(Doppegieter et al., 2001:49–50). On materials consumption, Statistics South Africa 

(1997:83) indicates that construction of homes contributed a mere 25% to the 

purchase value of cement in 1994, 15% for ready-made concrete and 40% for bricks 

and blocks. It is likely that in each case, low-cost housing contributes less than a 

quarter of these percentages (6.25%, 2% and 10% for cement, ready-made concrete 

and brick or blocks respectively). Similar patterns can be expected for water 

consumption and wastewater, solid waste generation and other such impacts.

In view of this minor role of the sub-sector, it is surprising that it has received 

some of the most intense sustainability attention especially from NGOs and CBOs. 

On the other hand, the attention can be justified in terms of numbers of people and 

households affected (the backlog in housing and services like water, sanitation and 

waste disposal, and expensive and inadequate public transport, among others). Any 

attempts to address such a large backlog in total disregard of sustainability issues 

would entail major impacts on the sustainability of the other urban subsystems. The 

subsequent section provides an overview of such initiatives. It demonstrates the 

spectrum of issues addressed and how this influences housing policy at the national, 

provincial and municipal levels, as well as the interests of the private sector.

Sustainable housing and settlement initiatives: Overview of  
case studies

Since 1994, housing delivery for low-income households has been one of the key 

programmes of the South African government. The estimated backlog of three 

million houses set the government’s focus on mass delivery at the highest possible 

rate with an emphasis on so-called greenfield development. Targets of about 300 000 

houses per year were set for the ten-year period from 1994. Given the limited 

budgetary resources, delivery focused on the lowest possible investment per 

household (in the form of a subsidy) and the widest coverage in terms of 

beneficiaries.

Key subsidy categories of the housing programme are the project-linked, 

relocation, consolidation, institutional and rural subsidies (Department of Housing, 

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2000). Since April 2002, there was a change of policy on the subsidy programme. In 

particular, subsidies for different categories were increased to match price increases 

and inflation, a minimum contribution by beneficiary households was set and 

emphasis was shifted to institutional subsidies and projects through the People’s 

Housing Process.

Even though several subsidy categories were defined, the largest proportion of 

resources has been spent on the project-linked subsidies. This is the category of 

‘greenfield’ development with minimum stand size of 250 m2 and a minimum house 

size of 30 m2. Minimum standards for services are also stipulated (Department of 

Housing, 2000). Through this programme, hundreds of thousands of houses have 

been developed on cheap land located on urban peripheries and with minimal levels 

of shelter or services. The typical product of the programme is the so-called matchbox 

typology replicated over tens or hundreds of hectares in a single project with minimal 

regard to sense of identity, pedestrian circulation, urban design and density, open 

spaces, integration of social services (police stations, schools, libraries, clinics, etc.). 

Even though minimum service standards are set for sanitation, electricity and water, 

the overall shelter performance and standards of design and construction are only 

marginally better than the ‘shack’, which the so-called matchbox seeks to replace. Loss 

of community coherence and social networks creates further deficiencies in such 

settlements when compared to informal settlements.

The above factors, coupled with others such as the absence of urban integration 

(contributing to sprawl), the poor market value of the properties developed and the 

implications of high life-cycle costs (for households, municipalities, provincial and 

national government), contribute to the perpetuation of poverty, segregation and 

environmental degradation. In response, several NGO and CBO initiatives have 

emerged in an attempt to demonstrate alternative housing delivery, which aims at 

alleviating the above shortcomings. Details of most of the project examples and cases 

mentioned in this section can be found in Irurah et al. (2002), which constitutes the 

first attempt at consolidating cases on good practice in sustainable housing and 

settlement since 1994.

The relationship between poverty and environment in this housing scenario has 

become a major opportunity for NGOs and CBOs to attract donor funding to 

supplement the government subsidy in pilot projects. Shelter-performance has 

emerged as the most strongly supported component, especially because it is linked to 

energy and water efficiency or conservation. Energy efficiency in turn is linked to the 

mitigation of greenhouse gas emission (a key contributing factor to global warming 

and climate change, which has now become a key global environmental challenge). 

The link to the Kyoto Protocol and emergent finance mechanisms for mitigation 

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projects has generated enthusiasm among housing stakeholders on the potential for 

meeting the additional costs incurred by making housing sustainable.

Consequently, technologies and capacity building in energy-efficient housing have 

been piloted by a variety of NGOs in partnership with CBOs and beneficiaries. 

Kutlwanong in Kimberley, Tlholego near Rustenburg, Midrand Eco-city and the 

Soweto energy-efficient house are some of the project examples. The All Africa Games 

Village near Alexandra in Johannesburg is one example where a conventional 

‘greenfield’ project has been enhanced for energy and water efficiency without NGO 

and CBO participation. Unfortunately, most of the interventions have not been 

adequately sustained, because owners and community in general were not empowered 

for the task of appropriate habitat management from the perspective of sustainable 

settlement.

With regard to capacity building, NGOs such as Planact, IIEC (International 

Institute for Energy Conservation) and SEED (Sustainable Energy, Environment and 

Economic Development), as well as private-sector consultancies such as PEER Africa 

Pty Ltd., have partnered with communities, municipalities and provincial and national 

government for both advocacy and capacity facilitation at the decision-making level.

Since urban integration is a major requirement for poverty alleviation and 

resource efficiency at the urban scale, well-located projects such as the various 

settlements of Cator Manor in Durban and the Johannesburg Housing Company 

projects (Douglas Rooms, Carr Gardens, etc.) demonstrate sustainable housing with 

regard to urban integration.

Turning to the socio-economic dimension, job creation, skills development, 

support for entrepreneurial opportunities and empowerment of women are some of 

the key responses demonstrated in some projects. Kutlwanong in Kimberley was 

developed through the People’s Housing Process of the national housing programme 

and has therefore demonstrated how socio-economic needs could be addressed even 

through an energy-efficient housing focus. The Tlholego project constitutes a strong 

rural example of integrated housing delivery that addresses both environmental 

requirements (energy, water and materials efficiency) and socio-economic needs 

(skills development, organic agriculture based on permaculture, empowerment of 

rural women, affirming social structures and cultural values, etc.). Enhancement of 

access especially through pedestrian circulation and for disabled people has been 

demonstrated in several projects. A demonstration house in Kutlwanong has been 

enhanced for access by disabled persons. In Cato Manor (Durban), the Riverdene 

settlement demonstrated prioritisation of pedestrian rather than vehicular circulation 

as well as enhancement for access and use by disabled persons.

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The management of waste in human settlements is a crucial environmental 

sustainability requirement, especially with regard to environmental health and 

resource recovery. Communities and municipalities have also realised that this 

component has major potential for socio-economic benefits. In this regard, 

partnerships between municipalities, NGOs, CBOs and the private sector have 

ensured that community-based enterprises are generating economic value out of 

collection, sorting and recycling of waste. The Iteke and Mitchell’s Plain projects, as 

well as the Durban Solid Waste Management Programme, are some of several 

examples in this regard.

Regarding institutional sustainability, one of the common features of all the 

projects that aim at piloting and demonstrating sustainable housing alternatives is 

that they involve partnerships between different stakeholders. Besides the NGOs and 

CBOs, public-sector resources or contributions in terms of land and subsidies or 

other forms of facilitation have been essential. In some rare cases, private-sector 

participation and contribution has been achieved. The Abahlali project (Irurah et al., 

2002:48) is a unique example where a private-sector entity was directly involved in 

bridge financing of the project.

One critical requirement for institutional sustainability is continuity and evolution 

of policy frameworks that facilitate the initiatives. Continuity of contribution and 

facilitation by other stakeholders, especially NGOs and CBOs, is also critical. 

Consequently, appropriate funding, management skills and transparent and 

accountable governance are essential ingredients. This is particularly critical for 

NGOs and CBOs, which mainly rely on external funding for survival. The Kutlwanong 

Civic Integrated Housing Trust (KCIHT) and the Cato Manor Development 

Association (CMDA) provide examples of how to tackle this sustainability component 

while also spreading the benefits and lessons learned to several projects (Irurah et al., 

2002:15–16, 99–100).

Sustainable housing and settlement: Policy initiatives

The emergence of South Africa as a democratic state in the mid-90s has gone hand in 

hand with the rapid adoption of international frameworks and protocols related to 

sustainable development and sustainable settlement. Key among these are Agenda 21 

(United Nations, 1992 and its derivatives, such as Local Agenda 21) and Habitat 

Agenda (UNCHS (Habitat), 1996). The translation of such frameworks into national 

and local legislation or policy has also been systematically undertaken.

However, the translation from policy and legislation to implementation of 

programmes by national, provincial and local governments has not been systematic. 

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This section reviews the related policies and legislation that are currently in place and 

how they relate to sustainable settlement and housing. The section also reviews the 

sustainable housing policy of the City of Johannesburg as an illustrative example of an 

approach towards mainstreaming the lessons learned from demonstration projects 

into the practice of implementing sustainable housing and settlements in South 

Africa.

Policy and legislation with reference to sustainable housing and settlement

The process towards a national strategy for sustainable development (NSSD) for 

South Africa commenced almost two years ago under the Department of 

Environmental Affairs and Tourism (DEAT). There was a high expectation that the 

process would yield the draft or final version of the NSSD by the time of the Earth 

Summit in Johannesburg (August 2002). This has not happened and no clear 

timeframes have been set for this outcome. On the other hand, the country has in 

place several pieces of legislation and policies, that directly relate to sustainable 

housing and settlement.

The constitution (RSA, 1996) entrenches the right of access to housing opportunities, 

an environment that is not harmful to one’s wellbeing, and protection of the 

environment for present and future generations. The Reconstruction and Development 

Programme (RDP (ANC, 1994)) and its successor (Growth, Employ ment and 

Redistribution Strategy (GEAR (ANC, 1996)) have identified housing and economic 

growth with employment and economic empowerment (poverty reduction) as the key 

development challenges which the country must address.

The Urban Development Strategy (RSA, 1995a) and the Urban Development 

Framework (UDF) (see Department of Housing, 2000, Chapter 3, section 3.7)) have 

more specific relationships to sustainable housing and settlement. Both policy 

documents envision South African settlements that are:

■ Spatially, racially and socio-economically integrated;

■ Economically sustainable;

■ Democratically governed with participatory planning as a key ingredient;

■ Environmentally sustainable; and

■ Adequately financed through public sector budgets and public-private sector 

partnerships.

The UDF identifies four key programmes for the realisation of this vision. These are:

■ Integrating the city (undoing the legacy of apartheid planning);

■ Improving housing and infrastructure with a view towards sustainable 

communities;

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■ Promoting housing and infrastructure with a view towards sustainable 

communities;

■ Promoting urban economic development; and

■ Creating institutions for delivery.

The local level institutional requirements for urban development have been provided 

for through the Local Government: Municipal Systems Act (RSA, 2000). It is this piece 

of legislation, above all others, which attempts to facilitate the realisation of integrated 

urban planning and development. The act makes the formulation of integrated 

development plans (IDPs) a mandatory requirement for all municipalities in the 

country. However, inadequate capacity in local authorities (especially financial 

capacity and skills) has meant an extremely slow start to the process of formulation 

and implementation of such IDPs.

The most recent policy framework in this line is being articulated through the 

White Paper on Spatial Planning and Land Use Management (Department of 

Agriculture, 2002). The paper is part of the process towards drafting a Land Use Bill, 

which is aimed at replacing apartheid-legacy legislation currently impairing the 

systematic implementation of the Development Facilitation Act (DFA (RSA, 1995b)). 

The paper aims to facilitate:

■ A holistic approach to urban development;

■ A reduction in the range of existing policies and legislation on this issue; and

■ Integration with related legislation or policies in governance, environmental and 

resource management (including environmental impact assessment require-

ments).

One of the key features of the DFA (RSA, 1995b), which will be reinforced by the 

anticipated land-use bill, are the general principles for land development, which 

discourage low-density, segregated, fragmented and mono-functional urban 

development in favour of compact, integrated and mixed-use settlements.

Other policies and legislation which impact on settlements at another level include 

the White Paper on National Transport and Moving South Africa (Department of 

Transport, 1998), the National Environmental Management Act – NEMA (RSA, 1998), 

the White Paper on Energy Policy (Department of Minerals and Energy, 1998) and the 

Water Services Act (RSA, 1997). Similarly, extensive legislation and policies with regard 

to socio-cultural challenges have been formulated by respective national and 

provincial governments.

Although the examples of legislation and policy papers highlighted above indicate 

that strong facilitation towards sustainable housing and settlement in the country is 

already in place, their translation into the implementation of programmes and 

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projects has not been consistent. Hence, the set vision and goals have not been 

achieved in any significant manner. Instead, urban sprawl, desegregated settlements, 

inadequate shelter in low-cost housing, inadequate responses to resource and 

environmental degradation, as well as continued disregard of the rights of vulnerable 

groups, continue to dominate housing practice and habitat management in South 

Africa. It is in this context that the City of Johannesburg initiated its sustainable 

housing policy, which is reviewed in the section below.

Sustainable housing policy of the city of Johannesburg

From the point of view of housing and settlements, the lessons derived from the 

diverse demonstration projects by NGOs and CBOs have not yet percolated upwards 

into policy revisions and enhancement to facilitate mainstreaming of related 

principles and practices at national, provincial and local governments. However, 

continued advocacy and lobbying by various stakeholders and interest groups have 

managed to convince the City of Johannesburg to pioneer the road to a sustainable 

housing policy in spite of an absence of a comprehensive policy at provincial and 

national levels.

Through a stakeholder consultation process in 2000 on the Metropolitan Housing 

Strategy 2010, feedback (especially from NGOs and CBOs working on various 

challenges of sustainable housing) identified a total absence of sustainability 

considerations in the strategy. The outcome of the consultation process was that the 

City of Johannesburg undertook to amend the strategy to reflect such considerations. 

This was implemented in 2001 when the Sustainable Housing Policy for Johannesburg 

was formulated, followed by capacity building (implementation guidelines, training 

and project assessment tools) for implementation by 2004 (City of Johannesburg and 

Syn-Consult Africa, 2001).

The mainstreaming of sustainable housing and settlement practice would thus 

assist the City of Johannesburg in the realisation of its housing vision of:

Healthier, wealthier and secure households and communities in environmentally responsive, 
spatially, socio-culturally and economically integrated housing and habitats within a 
resource- and environment-conserving city, for the benefit of current and future generations 
of Johannesburg and South Africa (City of Johannesburg Council and Syn-Consult Africa, 
2001:22).

Through integration of several sustainability components (energy and water 

efficiency, land-use optimisation, alternative or green finance, job creation and 

response to rights of vulnerable groups, among others) and the key stages of a 

housing-project cycle (from conceptualisation through to monitoring and 

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evaluation), the policy commits the Council to progressively play a leadership and 

facilitation role for the realisation of sustainable housing and settlement for the 

city. The formulation of implementation guidelines, training of officials and 

councilors and institutional arrangement are now being implemented as part of 

the capacity-building process for policy implementation. This policy process 

marks a turning point in sustainable housing and settlement in South Africa as it 

shows a commitment by a public sector stakeholder to mainstream lessons derived 

from the various projects implemented by NGOs and CBOs at grassroots level.

Conclusion

The emergence of the sustainable development paradigm has kindled debate on 

urban sustainability and sustainable urban form. Characterising and contrasting cities 

through concepts such as compact versus sprawl, ecological versus non-ecological and 

just versus unjust cities serve as clear indications of the evolution of this debate which 

in turn feeds into the re-definition and understanding of sustainable development.

Although South Africa has adopted key international protocols and agreements on 

sustainable development (including Agenda 21 and Habitat Agenda) into its 

development policies and legislation, this has not been systematically followed 

through in implementation. Even in the absence of an explicit national strategy for 

sustainable development, there exist several pieces of legislation and policy frameworks 

that could significantly contribute to sustainable development and urban sustainability 

if effectively implemented. Inadequate capacity (especially skills and financial 

resources) has been the key contributing factor to this outcome.

On the other hand, the country has enjoyed intensive piloting and demonstration 

of sustainable housing or settlement projects by NGOs and CBOs mainly with donor 

funding. Lobbying and advocacy by such NGOs and CBOs has convinced the City of 

Johannesburg Council to pioneer the process of formulating a sustainable housing 

policy and the necessary capacity building for its implementation. In the other 

sub-sectors in construction and the economy in general, there have been no significant 

initiatives towards coherent sustainability programmes.

In view of the above scenario, it is now an appropriate moment in which to 

attempt an answer to the question of whether sustainable low-cost housing initiatives 

can influence the transformation towards sustainable urban development and 

construction in South Africa. In view of the tremendous international commitment 

to sustainable development and South Africa’s political will to align itself with this 

movement, the search for sustainable housing and urban development will continue 

to attract political attention in the foreseeable future. Equally, lessons on 

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implementation strategies will be systematically sought as the implementation 

agencies endeavour to ensure coherence and reliability in their programmes.

It is also clear that, given its current momentum, the low-cost housing or settlement 

sub-sector will continue in the search for sustainable urban development and 

construction. When this is coupled with the sustainability-oriented pieces of policy 

and legislation, one can reach the conclusion that there will be a convergence, which 

will allow the mainstreaming of lessons from sustainable housing projects into 

sustainable urban development and sustainable development in South Africa. 

However, the timeframes and exact process for this convergence would be difficult to 

predict at this stage.

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	Chapter 15: An Interpretation of Sustainable Development and Urban Sustainability in Low-Cost Housing and Settlements in South Africa
	Introduction: Sustainable development and sustainable urban form
	Sustainable cities and human settlements
	Urban sustainability and urban form
	The compact versus the sprawl city
	Other contrasts in city form

	Sustainable low-cost housing, urban sustainability and the sustainable development debate in South Africa
	Low-cost housing in the context of the building construction sector
	Sustainable housing and settlement initiatives: Overview of case studies
	Sustainable housing and settlement: Policy initiatives
	Policy and legislation with reference to sustainable housing and settlement
	Sustainable housing policy of the city of Johannesburg

	Conclusion
	References