THEEWATERSKLOOF GREEN ECONOMY - Theewaterskloof Municipality
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THEEWATERSKLOOF GREEN ECONOMY A renewable energy and green business opportunities scoping study anton@econologic.co.za 1 1 Anton Cartwright is an independent economist and a researcher with the African Centre for Cities. Jacqui Boule and Joanna Dibden of Theewaterskloof provided invaluable support to this scoping study and comments on early drafts. Lisa Constable from ERM (Pty) Ltd provided valuable comments on an earlier draft of this strategy. 1
CONTENTS 1. INTRODUCTION 3 2. THE NATURE OF THE THEEWATERSKLOOF ECONOMY 6 3. THEEWATERSKLOOF GREEN ECONOMY OPTIONS 10 3.1 Carbon 10 3.2 Water 16 3.3 Built environment and the space economy 20 3.4 Industry and energy security 25 3.5 Innovative farming and biodiversity 30 3.6 Innovation and the knowledge economy 34 4. WHAT ROLE FOR THE MUNICIPALITY? 37 5. BUSINESS OPPORTUNITIES, AND EMPLOYMENT POTENTIAL 45 6. CONCLUSION 46 REFERENCE LIST 48 APPENDIX A: PRINCIPLES OF THE GREEN ECONOMY 52 APPENDIX B: INNOVATORS AND PIONEERS IN THEEWATERSKLOOF GREEN ECONOMY 58 APPENDIX C: CARBON TAX 65 APPENDIX D: LIST OF CONSULTED PEOPLE AND COMPANIES AND PRESENTATIONS 65 2
1. INTRODUCTION Theewaterskloof Municipality is busy with the remarkable process of formulating a “2030 Strategy”. The strategy aims to guide development planning over the next 19 years, and has identified making Theewaterskloof (1) a great place to live, (2) a visitor destination of choice, (3) a centre of learning, (4) a vibrant economy and (5) a green and low carbon economy, as among its ambitions. The exercise is remarkable in that local governments in South Africa, loaded with a raft of novel and at times unfunded socio-economic development responsibilities when municipal boundaries were redrafted in 2000 (RSA, 1996; dplg, 2002), have generally struggled to perform their day-to-day tasks let alone plan for their future or strategise around their development responsibilities. In the course of developing its 2030 Strategy Theewaterskloof has identified “sustainability” as being central to the pursuit of all other goals (TWK, 2010b) and the municipality is looking to attract investment and create employment through a “green economy”. In so doing Theewaterskloof is aligning itself with a global trend. The “green economy” re-entered the global economic discourse in the wake of the 2007 financial crisis when 6 per cent (US$188 billion) of the fiscal support package was reserved for “green stimuli” (Bloomberg, 2009). Understanding of what is meant by the “green economy” has remained fluid. UNEP initially proposed a sector-based understanding2, but has subsequently developed a more encompassing definition: “A green economy is one that results in improved human well-being and social equity, while significantly reducing environmental risks and ecological scarcities. In its simplest expression, a green economy can be thought of as one which is low carbon, resource efficient and socially inclusive” (UNEP, 2010).3 In a signal of intent, the United Nations indicated that the Earth Summit in 2012 (called Rio+20 to mark the 20 th anniversary of the founding summit at which the United Nation‟s Agenda 21 was adopted) will be exclusively focussed on the green economy and in February 2011 UNEP released its most recent and most detailed articulation of the green economy, Towards a Green Economy: Pathways to Sustainable Development and Poverty Eradication (UNEP, 2011) which expounds seven key statements: A green economy recognises the value of and invests in natural capital (especially “living capital”) The green economy is necessary for poverty alleviation The green economy creates jobs and promotes social equity 2 Agricultural, manufacturing, research and development (R&D), administrative, and service activities that contribute substantially to preserving or restoring environmental quality. 3 http://www.unep.org/greeneconomy/AboutGEI/FrequentlyAskedQuestions/tabid/29678/Default.aspx 3
In the green economy, renewable energy and low carbon technologies substitute fossil fuels. A green economy makes better use of resources The green economy involves more sustainable urban living and low carbon mobility A green economy grows faster than a brown economy (over time) while maintaining the value of natural capital. Behind these statements is the assertion that, “The green economy is not only the best economy of the future, but the only economy” on the grounds that developing economies no longer have the option of pursuing the extractive and resource intensive industrial development pathways used by current-day OECD countries in the 20th Century (see Figure 1). Figure 1: Over the past 30 years growth in global GDP has outpaced population growth and a $ of global GDP has become less material intensive. Resource extraction, however, has grown at a similar pace as global GDP and contributed to growing pollution, environmental degradation and growing resource constraints (UNEP, 2011) South Africa has picked up on the emerging green economy discourse, most notably in recent State of the Nation addresses (Presidency, February 2010 & February 2011) and via the newly formed Ministry of Economic Development.4 For South Africa the green economy offers the hope of redressing the capital-labour ratios and spatial forms that constrain the prevailing 4 At the opening of the Green Economy Summit in Sandton 2010, Minister Ibrahim Patel said, “Government is working on a new growth path that seeks to be more labour absorbing, less carbon intensive and that connects the significant scientific and technological capacities of the society with the challenges of jobs and economic growth,” 4
economy. South Africa certainly has the legislative instruments to participate in such an economy. Post 1994, South Africa‟s policy makers drew eclectically on international best practice to craft the National Water Act (NWA) (1998), the National Environmental Management Act (2008), the White Paper on Energy (1998) and hastily signed United Nation‟s conventions to fight desertification (UNCCD), biodiversity loss (UNCBD), atmospheric pollution (Montreal Protocol), wetland destruction (Ramsar Convention) and climate change (UNFCCC). Implicit in much of this legislation was the understanding that a functional environment was necessary for economic growth and poverty alleviation and that a reform of environmental rights was a component of the reform of human and economic rights. Good policies on their own, however, do not ensure change. At a national level the difficult structural decisions that would have ensured a departure from the business as usual and particularly the “mineral-energy complex” (Fine, 1999) have never been confronted in South Africa. Instead of a green economy, South Africa has pursued a series of projects and programmes with distinct economic, social and environmental objectives. The result has been a collection of economic contradictions: The National Water Act (1998) is internationally acclaimed but is undermined by a series of perverse incentives for the water misallocation, not the least of which is price protection for the sugar industry that absorbs disproportionate volumes of water relative to the income and employment that it creates. Employment hope is placed in eco-tourism, but pristine habitats are repeatedly compromised by the extension of mining rights. The President has proposed strident cuts in greenhouse gas emissions and Cabinet has approved a “carbon tax”, but State Owned Companies continue to be amongst the most greenhouse gas intensive in the world and are expanded in the interests of developmental government. The natural environment provides valuable services, especially to the most poor, but many of these services are compromised by the manner in which infrastructure and houses are built. A carbon tax has been levied on all new vehicles, but the statutory guidelines on diesel and petrol quality are outdated and do not permit the type of fuel quality that would allow fuel-efficient vehicles to be introduced onto South Africa‟s roads. The “minerals energy complex” that defines so much of South Africa‟s economic structure, has remained in-tact, in spite of its negative implications for the environment, employment creation, energy security and economic diversification. A certain level of contradiction is perhaps inevitable. Resources are limited, the legacy of past decisions endures, needs are varied and trade-offs are an unavoidable part of development. But 5
the extent of the contradiction in the national economy is testament to the danger of pursuing projects without principles. In South Africa‟s national discourse the green economy is seen as an add-on, an annex to the real economy with the potential to create a few additional jobs5 and revenue streams if it succeeds. In this way the green economy is seen much like Local Economic Development (LED) as something distinct from the mainstream economy. If the green economy is to fulfil its potential for job creation, investment attraction and the enhancement of economic competiveness in Theewaterskloof then the green economy needs to be seen not as a distinct sector, but as a way of taking economic decisions that acknowledges the principle that all economic activity is dependent on natural resources, the flow of economic services and environmental stability. The green economy theory and principles that inform this scoping of programmes and projects in Theewaterskoof align closely with UNEP‟s latest position (UNEP, 2011) and are presented in more detail in Appendix A of this report. 2. THE NATURE OF THE THEEWATERSKLOOF ECONOMY Theewaterskloof is a diverse municipality: humid in the west, arid in the east; accommodating both intensive-irrigated and extensive-dryland agriculture; it is a centre of excellence for the country‟s fruit industry and home to a number of leading enterprises while also containing a growing level of informal business and housing. Urbanisation into rural towns has increased, but much of the municipality remains rural, agricultural and sparsely populated. It is ironic for a rural, hinterland municipality such as Theewaterskloof that its sustainability success is likely to be determined by its towns. The agricultural sector will continue to provide the mainstay of the Theewaterskloof economy until 2030, but the key changes and arising challenges will be result of migration to the municipality‟s towns from farms, from Cape Town‟s peri-urban settlements and from elsewhere in the sub-Continent. The ability to accommodate and service up to 240,000 people (a more-than-doubling of the 2010 population) by 2030 in a manner that supports local markets, facilitates the extension of services so as to improve living standards and does not destroy the environmental resource base that supports all economic activity in Theewaterskloof, will ultimately determine how sustainable Theewaterskloof is in 2030. The municipality‟s towns are faced with the challenge of extending accommodation and services, maintaining existing infrastructure and simultaneously re- inventing themselves as economic hubs and places to live, rather than agricultural service depots. 55 South Africa’s governing party believes the green economy can create 300,000 new employment opportunities by 2020. The green economy in National Government’s analysis is depicted as a sector, and the anticipated employment creation is greater than any other single sector. 6
Figure 2a: TWK Gross Value Added (2000-2008) Figure 2b:Sectoral contributions to TWK economy 2008 Economic growth in Theewaterskloof has been above the national average over the past decade. The economy relies heavily on the agricultural sector which, although growing, is unable to generate sufficient employment to address the unskilled labour surplus. The rate of economic diversification into construction, agri-processing and manufacturing accelerated between 2000 and 2008, but even if this trend is extrapolated these sectors are unlikely to meet the extent of the demand for employment, services, housing and infrastructure. What the trends do reveal is that supplying sufficient water, housing, refuse removal and employment, while still supporting local markets, will require a structural break from “business as usual” in terms of service delivery (TWK, 2010). Outlining how to achieve this without destroying the existing economy or the natural resources that provide the bedrock of the municipality‟s economy is central to Theewaterskloof‟s 2030 Strategy. 7
Figure 3: Aerial photograph showing most of Theewaterskloof Municipality, the major towns and roads. The water catchment in the west and the drier grainlands of the east. That the Theewaterskloof economy is undergoing rapid flux is undeniable. The rate of change requires difficult decisions, especially if it is acknowledged that a simple replication of past development is neither possible nor capable of delivering on the socio-economic need. The proposed Caledon Casino and golf estate development, for example, will bring an estimated R6 million worth of rates to the Municipality every year and enhance the purchasing power in the region, but the associated housing estate and petrol station is in many ways inconsistent with the notion of densifying and investing in the centre of Theewaterskloof‟s towns so as to create mixed-use public spaces, while the private sector investment in water infrastructure that forms part of the development will complicate water governance for the Catchment Management Agency. To its great advantage, the municipality is home to a large number of established and innovative agri-processing businesses and business leaders and is the target location for aspirant renewable energy and energy technology companies. It is also pioneering a number of sustainable development initiatives and programmes through the Municipality, the Development Bank of South Africa, the Worldwide Fund for Nature and local NGOs. Understanding the operations, needs and strategies of local companies and their people is essential in understanding and supporting the emergence of a green economy in Theewaterskloof. Based on interviews conducted as part of this study, Appendix B contains a description of some of the pioneering and innovative companies and programmes that are underway or being considered within Theewaterskloof. From Annex B it is clear that: 8
i. The extent of existing capacity (management, innovation and industrial) and activity in Theewaterskloof is remarkable. This provides the foundation for future green economy activity and permits a level of ambition that is not justified in many other municipalities. It is important that the ideas proposed in this study succeed or fail on their intrinsic merit, and not simply due to poor implementation. In the words of the Municipal Manager6, “Theewaterskloof seeks to be a reliable guinea-pig”. Certainly Theewaterskloof has the capacity to pilot programmes and innovations that could find application elsewhere. ii. Existing practise in Theewaterskloof contains both good and problematic precedents, both of which are able to inform future decisions so as to allow for the consistent management of existing and imminent trade-offs. iii. There is potential for symbiotic relationships between Theewaterskloof‟s innovators, so as to enhance the flow of materials, energy and benefits throughout the local economy. For example (based on Appendix B) WWF‟s existing “water neutral” programme could include the Palmiet River; combustible solid waste from the Municipality‟s landfills could be transported to energy co-generators instead of Overstrand; energy intensive industries could purchase “green” wind energy from the wind farm in wheeling agreements; the Caledon Casino and large farming enterprises could benefit from the broad-based BEE participation of the Community Trust; the Elgin Learning Foundation and the GSDI could partner with Electricall in establishing mini-grids; eco-estates could procure renewable energy from the proposed “green” business park; local industry could collaborate to address the common problem of increasingly expensive road freight; Appletiser and the Melsetter Group could share ideas on re-using “waste” water; the findings of Colors biochar experiment could be used to benefit the entire industry; in general there are a multitude of learning opportunities if the Theewaterskloof innovators were to share ideas in the interests of a local knowledge economy. That Theewaterskloof has a number of Municipal, civil society, business leaders and companies that are already active in their pursuit of the green economy, does not negate the need for principles and guidelines that reduce uncertainty and manage expectations. Some of the existing policy uncertainty is a function of national policies and it would be wrong to assume that a local municipality such as Theewaterskloof could, on its own, create the definitive enabling environment for a green economy; but it can be expected to play its part. A green economy strategy, in conjunction with the 2030 Strategy, provides the framework required to manage social, ecological and economic trade-offs in a consistent manner. 6 Mr Stanley Wallace, addressing the Stellenbosch University Council 31 March 2011. 9
Central to the approach adopted in this document is the understanding that investments in ecological capital have multiple positive spin-offs for the economy and for people. This notion is supported by a form of Endogenous Growth Theory (Romer, 1986; Romer and Rivera-Batiz, 1990) in which investments in ecological capital create self-perpetuating spirals of growth driven by improved human capital, greater resource efficiency and fewer market failures and associated poverty traps. An Endogenous Growth model involving ecological capital depends on the effective management (or governance) of the “commons” (the atmosphere, biodiversity, water resources, soil fertility) so as to prevent productivity collapse and ensure more efficient and equitable access to resources (Ostrom, 1990 & 1994; Williamson, 2000). Ostrom cautions against a reliance on global institutions to solve the problem of coordinating and marshalling work against environmental destruction, and points out that key management decisions should be made at the local level and based on local conditions. This formed part of an idea that saw Ostrom win the Nobel Prize for Economics, and one that fits neatly with the idea of a Theewaterskloof green economy. Identifying and selecting the type of investment opportunities that will lead to better governance of the “commons” and support endogenous growth is the focus of this scoping study. It is useful to assess opportunities within central themes. The ideas discussed below are presented under the headings (i) carbon, (ii) water, (iii) the built environment and space economy, (iv) industrialisation and energy security, (v) biodiversity and sustainable agriculture and (vi) the knowledge economy. 3. THEEWATERSKLOOF GREEN ECONOMY OPTIONS 3.1 CARBON Key programmes and targets ACTION OUTCOME PROCESS & RATIONALE Measure Greenhouse gas inventory Identification of key greenhouse gas sources and planned reduction Tourism Carbon Voluntary off-set market TWK tourism reduces its carbon footprint functioning in TWK and revenue invested in RE &EE projects Soil Carbon Soil carbon:nitrogen Less GHG emissions and greater soil restored to pre-degradation fertility and water absorption. levels SWH and energy Installation of SWH on Demand side management as the cheapest efficient every house in TWK. source of “energy creation”. Carbon technologies Energy efficient lighting liabilities reduced. 10
and insulation as standard in all houses. Gloally, the burning of fossil fuel currently emits 9 billion tons of carbon dioxide equivalent (CO2e) greenhouse gas per annum and atmospheric concentrations of CO2 have increased from 280ppm in 1850 to 390 ppm. As a result, mean atmospheric temperatures have increased 0.74°C over the past century and an increase of 2.2°C by the end of this century is now unavoidable (Parry, 2009)7. The real danger is that the 9 billion tons emitted annually catalyses much greater emissions as warming climates release greenhouse gases from vaults in the permafrost, tundra and oceans - a scenario referred to as “run-away climate change”. Figure 4: Temperature increases by continent. Source IPCC Fourth Assessment Report, 2007. South Africa‟s is a greenhouse gas intensive economy. Each megawatt hour (MWh) of electricity produced in South Africa results in just over one ton of CO2 equivalent being released into the atmosphere, and for every $1,000 of GDP produced in South Africa almost 1.4 tons of CO2 equivalent greenhouse gas is released (Cloete, 2010). Theewaterskloof is no different. Half the 7 Martin Parry heads the IPCC’s Working Group 2 and was addressing a group at SwissRe’s Centre for Global Dialogue in Switzerland, July 2009. 11
electricity consumed in Theewaterskloof is purchased by the Municipality from Eskom for forward sales to urban consumers. The balance is purchased by industry and rural consumers directly from Eskom. In both cases the low grade of coal used as a feedstock, transmission losses as the electricity is transported from the East Rand to Theewaterskloof and energy intensive applications and activities in Theewaterskloof combine with land use practices to release an estimated 877,000 tCO2 in the municipality annually (based on 2010). Unchecked this could increase three-fold by 2030 as population and the economy grow (TWK, 2010). There is mounting international pressure, however, to curtail emissions and although South Africa (as an “Annex 2” developing country signatory to the Kyoto Protocol) does not currently face a legally binding emissions reduction target, the Presidency has provisionally committed the country to a 34 per cent reduction in emissions relative to “business as usual” by 2020 and 42 per cent by 2025. Many municipalities and cities, seeking a presence in international markets, are forging their own climate change mitigation strategies (see Amman, Vancouver, Curitiba, Cape Town, Durban, New York, London). Figure 5: Carbon intensity of economies with GDP greater than US$ 200 billion (2008). Source: Cloete (2010) In late 2010 National Treasury published a discussion paper exploring options for implementing a carbon tax in South Africa (National Treasury, 2010). The proposed carbon taxes were approved by Cabinet in December 2010. Treasury considers a carbon tax of R75 per ton of carbon dioxide (tCO2), increasing to R200/tCO2 over time to be “feasible and appropriate” to induce behavioural changes and achieve reduction targets. A domestically raised carbon tax would avoid the alternative of this levy accruing to South Africa‟s export markets in the form of “border adjustment taxes” levied by countries seeking to manage their 12
own emissions. As a phenomenally carbon intensive economy (see Figure 3), South Africa‟s commitment to the global need to reduce emissions will have a disproportionately negative impact on the country‟s economy, relative to many of our competitors. The production and export of a kilogram of fruit from Theewaterskloof, for example, results in 2.0 kilograms of CO2 being emitted on average.8 A carbon tax of R100 per ton of CO2 would add R 0.20 to the cost of each kilogram of export fruit. Significantly the same tax levied on Chilean fruit would add only R0.06 – R0.11 per kilogram of fruit. A carbon-constrained world will affect the competitiveness of all Theewaterskloof sectors. The solution lies in better managing the municipality‟s greenhouse gas emissions, and using this process as a means of introducing a suite of production efficiencies so as to gain an economic advantage over other South African municipalities and competitor regions outside of South Africa. The planned installation of utility-scale wind turbines is unlikely to reduce the carbon intensity of the municipal economy, given that the carbon credits from these projects have already been sold. There are, however, a number of potential actions listed below that Theewaterskloof could readily pursue in preparing its economy for carbon constraints. Measure: The chief greenhouse gas, CO2, is for the most part, colourless and odourless and invisible. Yet the Stern Review (2007) estimated that each ton of CO2-equivalent costs society ZAR 770.9 This is a cost worth managing, but management is only possible if a clear indication of the volume and source of emissions is available. As a signatory to the UNFCCC South Africa is required to submit a national greenhouse inventory, but this is a compliance measure not a management tool and it provides little information at the local scale. A regularly updated Theewaterskloof greenhouse gas inventory would enable local awareness and management of emissions. A local inventory, compiled to international standards, would give Theewaterskloof credibility in its efforts to reduce its emissions and allow the municipality to promote its carbon management efforts with credibility on the national and international stage. Tourism Carbon: The global carbon market attempts to channel investment in renewable energy and energy efficiency to regions and technologies with the lowest “marginal abatement cost” 8Citrus: 1,22 kg CO2e/kg, Topfruit: 1,70 kg CO2e/kg, Stonefruit: 2,58 kg CO2e/kg, Grapes: 2,33 kg CO2e/kg, Easy Peelers: 1,33 kg CO2e/kg fruit, Oranges: 1,17 kg CO2e/kg 9 TruCost, the UK NGO put the “marginal social damage cost” at US$ 31 per ton. 13
– those which achieve the greatest reduction in emissions for the least money. The market, which operates through the Clean Development Mechanism and various voluntary market standards, has become hampered by high transaction costs and an inability to accommodate small developmental projects, most notably in Africa. It is, however, possible for regions and sectors within regions to operate their own carbon markets. A precedent for this has been established by the “Kruger2Canyons Community Carbon Trading Project” in the South African Lowveld, and a similar programme is proposed for Theewaterskloof‟s tourism sector. The Lowveld project operates on a voluntary basis. Tourists are given the option of off- setting the emissions associated with a typical bednight and during game drives. The required payment amounts to just under R15 per person per bednight (based on typical consumption of Eskom energy during a bednight) and the revenue gathered is used to support local development projects to introduce renewable energy and energy efficient technologies and forestry and agricultural projects that sequestrate carbon. All transactions are recorded in a central registry and off-setters are issued which credit certificates when they check out of their accommodation. Such a programme would allow Theewaterskloof to market itself as a “low carbon” tourism destination, but also position it for a time when mandatory restrictions are required of the municipality or the tourism industry. In addition money would be generated for use in renewable energy and energy efficient projects. Where effectively managed, this money can be used to supplement the Municipality‟s indigent energy budget and create community development projects that tourists themselves may visit. Soil Carbon: Theewaterskloof‟s commercially successful agricultural sector has, in conjunction with the local forestry sector, depleted much of the municipality‟s soil carbon reserves over many years. Soil carbon represents a sink for atmospheric carbon. When depleted, soil carbon contributes to global warming – globally roughly 25 per cent of the increase in atmospheric CO2 since the industrial revolution is the result of land use changes and the associated depletion of soil carbon (IPCC, 1998). Soil carbon is further important in controlling the impact of erosion and enhancing water infiltration. We know that in semi-arid climates, rainfall events exceeding 10 mm tend to result in run-off, some erosion and soil carbon losses (Boardman et al., 2010). The extent of erosion increases dramatically as rainfall increases and where soil has been predisposed to erosion by overgrazing, compaction or organic material depletion. 14
A Theewaterskloof programme that committed farmers to periodically restoring and maintaining pre-degradation soil carbon:nitrogen ratios would sequestrate greenhouse gases, improve water infiltration and nutrient cycling and reduce erosion thereby contributing to a more sustainable agricultural sector. It would also secure considerable acclaim for the municipal agricultural sector. The Melsetter Group is, in conjunction with Stellenbosch University, already undertaking such a programme. Soil carbon is relatively easy to measure and soil carbon levels can be restored through judicious crop rotation and the addition of either biochar, nitrogen fertilisers, treated municipal sludge or the ploughing-in of alley crops and weeds. The proposed concept would be similar to maintaining what the water sector refers to as the “ecological reserve” – a critical minimum amount of water in each catchment so as to maintain hydrological functions. A soil carbon reserve would maintain the long term fertility of the region‟s land. The recording and managing of soil organic carbon within the municipality is compatible with the ongoing effort to identify the region‟s “terroir” locations for the production of quality wines (see below) and the compatibility is itself symptomatic of the type of value-addition that the green economy frequently yields. In discussion the University of Stellenbosch‟s has committed its Department of Soil Sciences to conduct an experiment involving the use of biochar, alley cropping and inorganic nitrogen fertilisers to gauge the relative merits of each approach to improving soil carbon:nitrogen ratios. Solar water heaters and energy efficiency technologies: Solarwater heater (SWH) roll-outs are already a component of the national energy strategy. The national programme offers (at best) a 90 per cent rebate on the cost of installation (Worthman, pers comms)10 and the most successful programmes are those supported by their local municipalities in order to cover the balance of funding and maintenance. The cost of SWHs is coming down, the quality is improving, the cost of Eskom electricity is increasing. The trends combine to give a current pay-back on a solarwater heater installation to private houses of between 2 and 4 years. The payback is quicker if the Eskom rebate is accessed. A 150 litre SWH heater saves roughly 2 tons of CO2 per annum per household of four people. Trading this carbon could contribute roughly R160 per annum per unit to the revenue streams available for installation and maintenance, provided suitable voluntary carbon market outlets can be secured. Regardless of carbon revenue, a SWH saves domestic users up to 25 per cent of their monthly electricity bill. 10 Cedric Worthman is in charge of the low cost solarwater heater roll-out at Eskom 15
The same increasingly favourable cost-benefit trends apply to a suite of demand-side management technologies such as Low Emission Diode (LED) building and public lighting, geyser insulation sleeves, ceilings in houses and solar passive design of buildings. These technologies are set to become a feature of all South African municipalities regardless of how the national grid sources its energy. Supporting the establishment of industrial capacity to either manufacture or install these technologies within Theewaterskloof will ensure Theewaterskloof businesses a stake in a local growth sector. The Municipality is not responsible for housing budgets but does have a say in where and how these projects are developed. By enforcing the use of energy efficient and renewable energy technologies on houses at both ends of the market, the Municipality would not only reduce the local greenhouse gas emissions, but support better quality, more sustainable, residential development. Demand side management technologies do reduce the amount of money that the Municipality can make by forward selling bulk electricity from Eskom to private users. This budget short-fall would have to be managed and should prove negligible relative to the rates and levies secured by the Municipality once Theewaterskloof is recognised as a prosperous, sustainable and well- managed municipality. Crucially, demand side management technologies can be financed by banks or mezzanine finance instruments, where the savings on Eskom electricity are used to pay- back the costs incurred in the installation of the technologies. IDC, commercial banks, UNEP Finance Initiative, DBSA and even some installers such as Teljoy have explored this model with success. 3.2 WATER Key programmes and targets ACTION OUTCOME PROCESS & RATIONALE Water governance CMA functional and NWA Water governance is closely linked to rolled out returns on water and avoiding crises. The NWA is an acclaimed piece of legislation that requires local implementation. Water Different qualities of water Not all uses requires the same quality. differentiation applied for different uses Differentiating can save money and see better utilisation of resource. Plug leaks More efficient municipal Existing leaks are extensive and the cost water use benefit of plugging leaks is favourable. 16
Promote efficient Less water used for higher Agriculture is the greatest consumer of irrigation yields, less soil erosion. Gap water. Current wide range in gap technology between best and worst between best and worst irrigation irrigation practice narrowed. practice can be easily closed. Prevent Municipal Less sewerage and Water quality reduces the available and agricultural agricultural discharge. Better resource. contamination water quality in natural resources. Expand links with Rehabilitation of the Palmiet Expanding existing links with WWF‟s WWF‟s Water River and investment in water neutral programmes attracts neutral programme hydrological infrastructure investment, creates employment and rehabilitates existing water resources, freeing up water. South Africa is a water scarce country.11 Theewaterskloof is fortunate to be part of the Breede Overberg Catchment, a basin that was reported to have a small water surplus in DWAF‟s internal strategic perspective study (DWAF, 2000). This surplus is under extreme pressure as demand in Cape Town and locally grows, and much of Theewaterskloof is socio-economically constrained by water shortages. The origins and economic implications of this scarcity are not always understood. South Africa captures 79 per cent of its available water resource in large dams – the highest proportion of capture in the world (Turton, 2010) – a status that precludes the construction of new bulk water storage infrastructure. Accordingly, the national policy focus has shifted to making better use of existing water. Technology has a role to play. Grey water recycling, more efficient industrial users and agri-processors, the adoption of more water efficient irrigation technology, residential water storage tanks, judicious use of ground water reserves and small off-stream farm-dams could contribute to greater economic returns on the available water resource. But technology on its own will not suffice; globally the efficiency gain in industrial and agricultural water use between 1990 and 2004 was only 1 per cent per annum (McKinsey, 2009). The overarching need is for better water governance. Water governance is complicated in that water is simultaneously a social, economic and environmental asset, but South Africa‟s National Water Act (1998) and National Water Resource Strategy (NWRS) (2003) provide a comprehensive framework for managing the country‟s water in the face of competing development needs. The legislation acknowledges catchments as the unit of water governance, prohibits any private water ownership, safeguards an “ecological reserve” for the maintenance of hydrological systems and provides structured and progressive means of allocating the remaining water in line with both economic and social interests (DWAF, 2003). Both the Act and NWRS have received international acclaim, but have also proven extremely difficult to implement against 11 The country receives an average of 470 mm per annum, while the global average is 857mm per annum. 17
the backdrop of vested interests in historical water allocation patterns and an under-capacitated Department of Water Affairs. Water governance: Water catchment boundaries do not align with municipal boundaries, but given that the bulk of Theewaterskloof falls within the Breede-Overberg Water Management Area and the Municipality has a vested interest in ensuring good water governance, the influence of the Municipality on the Catchment Management Agency (CMA) is critical. The Municipality is represented on the CMA‟s board, and should use this influence to ensure that national water legislation gains local traction and serves local needs. Crucial in this regard is the inter-basin transfer of water out of the Breede-Overberg catchment to meet growing demands in the City of Cape Town - over 37 per cent of the surface water resource in the Breede Basin in transferred in this way (DWAF, 2009). The CMA is the key to managing these transfers and in ensuring that Theewaterskloof is suitably compensated for the constraints that Cape Town‟s expansion is placing on its sustainability and development. A robust and proactive CMA would serve Theewaterskloof‟s green economy aspirations in others ways too. It would, for example, become possible under the NWA to allocate water that is realised by alien clearing and the introduction of grey-water recycling to poor female headed households under the Act‟s Compulsory Licensing arrangement or through General Authorisations. Such allocations would require commercial users seeking additional water to purchase or rent water from these women, and render the local water resource an instrument for social inclusion and equity. Similarly a local application of the NWA would permit the marshalling of water in support of employment creation or other mandated programmes, as opposed to locking historical water allocations into the Theewaterskloof economy regardless of their merit. Water differentiation: Irrigation and stock-watering does not require residential drinking water quality. South Africa‟s water is considered a “unitary resource” (NWA, 1998). Water can, however, be differentiated at the local level in terms of its quality and reliability. Since different users require different levels of quality and reliability of supply, differentiating at the local level, can save purification costs, realise new water sources (such as grey water and industrial effluent) and make more efficient use of existing water. 18
Plug leaks: The cheapest source of water available to Theewaterskloof‟s expanding towns is, “The water that is already supplied to [them]” (Turton, 2009). The figures are difficult to establish but nationally up to 30 per cent of available water is “lost” between reservoir and tap (IWA, 2008). Not all of this loss is leakage, some of it is due to administrative and measurement errors, and in many instances managers already lower water pressure during off-peak periods so as to reduce leakage. However preventing leaks through pipeline maintenance in bulk and private infrastructure offers potential for significant gains and is cheaper than constructing new supply side infrastructure. A programme aimed at plugging leaks can, as with demand side management, generate some of its own finance as water that is recovered is resold. Promote efficient irrigation technology: Agriculture and forestry account for roughly 95 per cent of Theewaterskloof‟s water use (DWAF, 2009), but the gap between the best available irrigation and stock-watering technologies and those used by most farmers in Theewaterskloof is wide, and widening in the absence of technical demonstration days organised by the Department of Agriculture. Uptake of more efficient irrigation technology represents a relatively easy water demand management gain. By facilitating show-days in which farmers get to see and learn about new technologies that are operating in Theewaterskloof, the rate of technology absorption would be advanced and irrigation efficiency improved. The Fruitways packshed, for example, makes use of a closed loop water system that saves water costs and prevents the release of contaminated effluent. Prevent contamination, especially from municipal systems and agriculture: Contamination of Theewaterskloof‟s water resources reduces the amount of available water, increases the cost of using water (see South African Breweries‟ efforts to purify water from Theewaterskloof Dam in Appendix B), threatens the phytosanitary compliance of fruit and vegetables produced in the area and causes disease and illness for people and livestock. Water quality in certain Theewaterskloof rivers is known to be compromised. Agricultural run-off, packshed and industrial effluent and towns that fail to maintain patent bulk water and sewerage systems are the chief culprits. Measurement using the Department of Water and Environmental Affairs‟ “Blue Drop” programme is a start. Improving the impacts of Theewaterskloof‟s municipal water quality provides a cost-effective means of reducing the economic burden of scarce water. 19
3.3 BUILT ENVIRONMENT AND THE SPACE ECONOMY Key programmes and targets ACTION OUTCOME PROCESS & RATIONALE Densification More people living in Greater purchasing power in tows, TWK‟s towns in mixed use shorter commuting distances, less habitat buildings destruction for residential sprawl Rural residential Up-market eco-villages New residential opportunities to create clusters living off-grid and purchasing power. Affluent market for independently of bulk clean technologies supports these sectors. services. Sustainable low cost SWHs, ceilings and gutters Ease financial and environmental burden housing to be mandatory on low on poorest residents by building better cost housing. houses, saves money in the medium term. Greening low cost Less money spent on Locals paid if they are able to sustain housing establishing trees and trees and shrubs provided with public shrubs in low-cost funds. neighbourhoods. Green MIG for MIG used to maintain and Ecological goods and services provided ecological restore ecological goods to all TWK residents, and functionality of infrastructure and services. services retained. The spatial the mis-alignment between people and markets – a direct legacy of the apartheid space economy – continues to provide one of the defining structural constraints on the South African economy. In Theewaterskloof this manifests as low residential densities in the rural towns of Grabouw, Villiersdorp and Caledon, people living a long way from their place of work and spending disproportionate amounts of time and money getting to their place of work, high transaction costs for producers in getting their goods to markets and a lack of purchasing power concentrated in the municipality‟s rural towns. Theewaterskloof‟s low urban densities are linked to weak “agglomeration forces” (World Bank, 2009) and insufficient local market size to support local businesses and industries or to attract new industries and investment. The result is that Theewaterskloof‟s towns remain stuck in an “agricultural service-town” mode, and fail to fulfil their economic and social potential. The same spatial form means that South African towns are inefficient in their use of energy, materials and land. Public transport, including rail, bus and taxi services are part of the solution (agglomeration economies only work if people can access the opportunities), but transport is not within the Municipality‟s powers or remit.12 The 12 Local industries such as SAB, KROMCO and Appletizer in partnership with the municipality might enter into collaborative partnerships with TRANSNET rail and port facility to ensure greater and easier mobility of their goods and people, but this is at best a partial solution for the municipality. 20
Municipality can, however, control the built environment. The built environment defines the relationship between people and the natural environment, and is central to the creation of sustainable markets, the management of environmental impact and the nature of economic development. The apartheid state used spatial planning in towns and cities extremely effectively in the 1960s to support its socio-economic ideology. The challenge for Theewaterskloof is to use space as effectively to reverse the apartheid legacy and support a more inclusive socio-economic system. Densification: The Municipality controls the allocation of development rights, building designs and spatial planning and could use this control to influence the nature and density of residential developments, so as to create a critical purchasing power and financially sustainable local businesses within Theewaterskloof‟s towns. Certainly, the main roads and central business districts of towns such as Grabouw, Villersdorp and Caledon offer considerably more economic, real-estate and social potential than is currently utilised. Very few people live in the town centres and development is restricted to low-density ribbon expansion of commercial property along the major roads, and retail at the respective taxi termini. The flow of traffic and people in these towns is controlled by the location of petrol stations, a casino (in Caledon) and franchised retail outlets. The towns cater for “passers through” rather than seeking to attract permanent residents and their money. They do not have public recreation space and do not have easily recognised town squares that combine recreation, retail and residential property. The result is that many people who work in Theewaterskloof live and shop outside of the region, and businesses in the major towns often struggle to attain critical scale. A town planning approach that creates residential space in the municipality‟s town centres in multi-storey mixed purpose buildings is to be piloted in Grabouw by the Grabouw Sustainable Development Initiative. The potential is to reduce transport costs, generate a critical mass of local residents for local businesses, reduce the sprawl and associated habitat destruction of existing residential developments and lower the unit cost of service delivery. Rural residential eco-clusters: Theewaterskloof offers an attractive location for middle and high income households who either work in Somerset West or Strand or are not required to be in the City of Cape Town for their work. Such households represent purchasing power and investment potential, but are restricted by the lack of suitable accommodation in the municipality. 21
They are unlikely to be attracted to the region‟s towns, even if they do embrace denser, mixed-use property development, and struggle to find land and housing outside of the towns without purchasing a farm. Whilst some Public Works and State forestry land is available, the process of alienating this land from State entities for private development is protracted. Similarly the process of using private agricultural land for residential development is restricted by the Subdivision of Agricultural Land Act (70 of 1970) and its attempts to protect food security. It is proposed that the concept of food security promoted by the Act has its origins in apartheid-era isolationist thinking, is outdated and incorrect.13 As one farmer pointed out, he has a 12 hectare piece of land on his farm that has no agricultural potential, is currently occupied by water thirsty pine trees but could serve as a home for 6-8 houses with a mountain and dam view, fynbos gardens and clean technology. Challenging this Act and its implications represents a long-term process, but the Municipality has the role of interpretation and application. It is proposed that clustered developments on pockets of low-potential agricultural land be used for up-market developments, with the intention of increasing investment and purchasing power in the municipality. Such eco-clusters would only be possible with strong guidelines from the Municipality. Necessarily these estates would have to exist without access to the national electricity grid or the bulk water system, but the technologies to enable this are available, proven, and falling rapidly in price. A combination of gas, photovoltaic energy panels, solarwater heaters, rainwater harvesting, grey water systems and composting toilets, can currently be installed in an upmarket house for a total of R150,000- R250,000 without any noticeable impact on services (Cohen, 2010)14. The type of houses envisaged should be able to pay this premium. In addition to enhancing purchasing power and facilitating investment, such developments would generate ideas, showcase opportunities and attract the type of industries and skills to the region that would see the formation of businesses that will prosper when these approaches become the norm. Sustainable low cost housing: Making better use of existing commercial and residential property in the rural towns is a component of the solution to Theewaterskloof‟s housing challenge, but even where this 13 While retaining food and fibre production is an important component of the Theewaterskloof economy, food security is equally supported by the creation of viable markets and a wide number of options for accessing food. 14 http://www.mg.co.za/article/2010-12-23-unplugged-life-off-the-grid 22
is successful, the Provincial Government, in partnership with the Theewaterskloof Municipality, will be required to build new low cost housing. The current approach to building government housing requires a rethink – especially in rural areas where houses tend to be poorly constructed from inferior products without consideration of the natural environment or the socio-economic consequences of the lay-out or location of these houses. More sustainable low cost housing offers multiple benefits: (i) adding gutters would facilitate rainwater harvesting and reduce soil erosion and localised flooding; (ii) solarwater heaters tend to last longer than electric geysers, reduce the residents energy costs, save green house gas emissions and create a market for the local industry; (iii) ceilings regulate internal temperature, reduce energy costs and make for a healthier living environment; (iv) biodigesters collect sewerage from the neighbourhood and convert this to energy and clean water, saving bulk infrastructure construction, providing an energy source, saving water purification energy and providing a local source of irrigation water; (v) magnesium (as opposed to calcium) carbonate cement products save CO2 emissions in construction; (vi) designing settlements with public spaces that are observed from the respective houses makes neighbourhoods safer. Low-cost housing is not the place to experiment with unproven technologies, but many of the well-proven technologies have the potential to save households money, save the Municipality money over the long-term and deliver better services. It is incumbent on the municipality to insist that contractors install these products. The MFMA requirement to install “lowers cost” options in all instances need not be an impediment if the life- cycle cost, and external costs are considered (De Visser, 2010). Greening low cost settlements: The need for greenery – trees, shrubs and groundcover – is a much cited need in low cost developments. The reality is that greenery is often used as fodder, fuelwood or building material and is expensive to irrigate and maintain. A municipal system in which households are paid if trees that are planted by the Municipality or Province are kept alive is more likely to succeed. Experience in Durban15 shows that where incentivised in this way households find a variety of innovative ways to protect and nurture greenery in their environment and that the approach is both more successful and less costly than Municipal approaches involving water trucks and periodic replanting. 15 Durban has run a “Tree-preneur” Programme 23
Green MIG and ecological infrastructure: The Municipal Infrastructure Grant (MIG) is the largest conditional grant from National Treasury to local governments. In 2011/12 Theewaterskloof will receive a R21.5 million MIG allocation and will spend this on a range of water and sewerage projects. The role of infrastructure and the services that they deliver are understood to be central to the functioning of “developmental local government”. The reality is that municipalities are struggling with the “triple challenge” of building new infrastructure, maintaining existing infrastructure and using new infrastructure to contribute to poverty eradication (Brown-Luthango, 2010), and whilst MIG allocation and expenditure has improved considerably over the past decade, much of the infrastructure delivered has not been well maintained or provided adequate services. At the same time, the environment, and the value of services and goods provided by functional environments, has been a key oversight in the roll-out of MIG (MXA, 2003). In a rural municipality such as Theewaterskloof, the value of services provided by the environment – pollination, water purification, provision of food and fibre to wild harvesters, soil nutrient recycling, carbon sequestration, emotional well-being and tourism support – is probably greater than the value of services provided by the municipality. Just as municipal service delivery faces a number of pressures, so too is the value of ecological services under pressure. Balancing the roll-out of traditional municipal services such infrastructure and solid waste disposal, with the services provided by the natural environment represents a key challenge for the green economy. The Development Bank of South Africa (DBSA) with support from the South African National Botanical Institute (SANBI) has made the case for permitting the maintenance and restoration of “ecological infrastructure” with MIG grants, particularly where this infrastructure contributes to municipal services and can provide these services more cheaply than infrastructure projects creating more jobs in the process. It is a compelling argument, and one in which National Treasury has expressed interest.16 Grabouw already has a sustainability initiative operating with DBSA and has the institutional capacity to run a trial project around this “Green MIG”. The soil carbon project mentioned above, wetland restoration programmes, the tree-preneur programme used for greening, solid waste recycling programmes, rainwater harvesting, composting toilets and the clearing of alien vegetation from water catchments are all examples of the type of activity that might be funded by the Green MIG. Where such a trial was launched it would further distinguish Theewaterskloof as a place of significance and innovation in the global green economy. 16 Ian Palmer, Anthony Black and Dave Savage are three Treasury consultants that would be useful in advancing this idea. 24
3.4 INDUSTRY AND ENERGY SECURITY Key programmes and targets ACTION OUTCOME PROCESS & RATIONALE Wind farmers Bulk wind energy produced TWK has an excellent wind resource. assisted in securing and consumed in TWK Localisation of a national industry. TWK PPA & RODs gains international profile and benefit5s form a new clean industry. Local businesses have access to clean energy. Co-generation of Industrial plants using waste energy at industrial to generate electricity and plants avoid landfill methane Local manufacturing New labour intensive Local markets for technologies supported manufacturing and by local manufacturing and expertise that maintenance of strategic RE will be exported when the industry and EE technologies grows. Green business hub Cluster development of green Critical mass of green economy players economy players running developing markets and providing an business off renewable energy attractive location for businesses and and material recycling. industries requiring a green profile. Includes a logistics hub linked Cement or glass depot to reduce road to rail service freight, particularly on Sir Lowry‟s Pass. Differentiate tariffs Cheaper electricity and more Charging lower prices for off-peak between peak and efficient use of available electricity and higher prices for peak non-peak electricity, most notably electricity is permitted by NERSA and renewable energy would encourage companies and households to run non-essential items during off-peak, thereby smoothing the demand curve. Net metering Allow industrial and Incentivise local electricity users to install residential electricity meters to localised energy generating devices so a run in two directions to reduce their energy consumption Waste to energy Landfill content used in Theewaterskloof has 4 landfill sites all of combustion. “Excess” solid which pose problems for the waste transported to Municipality. South Africa‟s waste has a cogeneration sites instead of high energy content and burning it in a Overstrand landfill. Later controlled environment can provide landfill methane used as an energy and reduce the solid waste energy feedstock. Avoid burden. transport of solid waste to Overstrand. 25
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