Domestic rainwater harvesting to improve water supply in rural South Africa

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Abstract

Halving the proportion of people without sustainable access to safe drinking water and basic sanitation, is one of the targets of the 7th Millennium Development Goals (MDGs). In South Africa, with its mix of developed and developing regions, 9.7 million (20%) of the people do not have access to adequate water supply and 16 million (33%) lack proper sanitation services. Domestic Rainwater Harvesting (DRWH), which provides water directly to households enables a number of small-scale productive activities, has the potential to supply water even in rural and peri-urban areas that conventional technologies cannot supply. As part of the effort to achieve the MDGs, the South African government has committed itself to provide financial assistance to poor households for the capital cost of rainwater storage tanks and related works in the rural areas. Despite this financial assistance, the legal status of DRWH remains unclear and DRWH is in fact illegal by strict application of the water legislations. Beyond the cost of installation, maintenance and proper use of the DRWH system to ensure its sustainability, there is risk of waterborne diseases. This paper explores challenges to sustainable implementation of DRWH and proposes some interventions which the South African government could implement to overcome them.

Introduction

South Africa is one of the signatories of the Millennium Development Goals. With its mix of both developed and developing regions, 3.7 million people have no access to any form of water supply infrastructure and an additional 5.4 million people who have some access have to be brought up to a basic level of service (Info, 2006). Domestic rainwater harvesting (DRWH) is an alternative for South Africa to meet the Millennium Development Goals of halving, by 2015, the proportion of people without sustainable access to safe drinking water and basic sanitation (MDG 7, Target 1), and provide free the first six kilolitres of water consumed monthly to poor households (households with less than USD 112 income/month). Rainwater harvesting (RWH) describes the small-scale concentration, collection, storage, and use of rainwater runoff for productive purposes. DRWH is one of the broad categories of RWH where water is collected from rooftops, courtyards and similar compacted or treated surfaces, stored in underground tanks (UGTs) or aboveground tanks (AGTs) and used for domestic purposes, garden watering and small-scale productive activities. DRWH is not new in the region, rooftop RWH is a major source of drinking water in the rainy season especially in KwaZulu-Natal and the Eastern Cape (Duncker, 2000). The practice is currently spreading in rural South Africa, especially with the financial assistance provided by the Department of Water Affairs and Forestry (DWAF) to resource poor households for the capital cost of rainwater storage tanks and related works. There is a direct link between the provision of clean water, adequate sanitation and improved health (Gleick, 1996), and often inadequate water supply is pointed as a factor contributing to poor sanitation. Improving the quantity and quality of water supply improves the level of sanitation. Sanitation is an important public health measure which is essential for the prevention of diseases. With regard to sanitation services, in South Africa, 16 million people (3.9 million households) are without adequate sanitation services (Info, 2006). Water plays a major role in laying the foundation for economic growth, not only by increasing the assurance of supply, but also by improving water quality and therefore human health (Phillips et al., 2006). There are two categories of storage reservoirs for DRWH, surface or aboveground tanks (common for roof collection) and sub-surface or underground tanks (common for ground catchment systems). As the level of adoption increases some critical aspect of DRWH such as the health implication, the sizing of the storage tank and the management strategy need consideration. Apart from the most spoken advantage of enabling small-scale productive activities (brewing, small-scale food production, household construction, etc.); DRWH also has the adverse potential impact to spread a number of water related diseases if proper measures are not taken. The immune systems of HIV-positive people are susceptible to a wider range of common illnesses and diseases than individuals whose immune systems are not compromised by HIV and AIDS (Ashton and Ramasar, 2002). As funds are made available for the widespread of DRWH, there is a need to explore its potential to improve the rural water supply. This paper presents the current state of DRWH in South Africa and seeks to highlight the challenges to overcome for its sustainable implementation.

Section snippets

The RWH Pilot programme

As part of the efforts of the South African government to halve the number of food insecure households, financial assistance is provided for the implementation of storage tanks. During the Demonstration Phase of its Pilot Programme, DWAF has constructed, through implementing agents, 64 underground tanks (UGTs) (Fig. 1) in 26 villages distributes in 4 provinces, namely Eastern Cape, Limpopo, KwaZulu-Natal and Free State. (De Lange, 2006).

Results of the DWAF RWH Demonstration Phase, November

Literature review of the potential impact of DRWH on water-related diseases

The main advantage of DRWH is to provide water right at the household, suppressing the burden of having to walk long distances to fetch water. The quantity of water delivered and used for households is an important aspect of domestic water supplies, which influences hygiene and therefore public health (Howard and Bartram, 2003). In the South African context, the quality of the water takes another dimension when one considers the HIV/AIDS epidemic (one of the worst in the world) that shows no

Sizing the DRWH storage tank

For a given size and location of DRWH system and operating strategy, there will be a limit on the water it can supply per day, per week or per year (DTU, 2001). The storage tank accounts for a large fraction of the cost of the DRWH system (Table 1). It is therefore critical to size it appropriately, and to get the maximum benefit out of it. Often the storage tank is either oversized or undersized. To find the optimum storage tank size, which will help reaching a certain reliability of supply,

Legal aspect of DRWH

A review by Kahinda et al. (2005) of the National Water Act (Act No. 36 of 1998) and the Water Services Act (Act No. 108 of 1997) indicates that the current water legislations do not give a clear legal framework for the adoption of DRWH, making DRWH illegal by strict application of the law. If under the National Water Act, Section 22 (1) (c), DRWH is a permissible water use which does not require a license (Schedule 1), the Water Services Act, Section 6 (1) states that it will require an

Discussion and conclusion

The review performed on this study shows that although DRWH appears to be one of the most promising alternatives for supplying freshwater in the face of increasing water scarcity and escalating demand (Sazakli et al., 2007), it should not be looked upon as the panacea for water supply.

The sustainability of the DRWH requires close cooperation between the government, the private sector (NGOs and Scientists) and the rural households (Fig. 5) but also an integrated system approach where the

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