Abstract

In this article several economic studies undertaken to assist with the implementation of the National Water Act (NWA) No. 36 of 1998 are reviewed. In these studies the following procedures were applied to model water use: operational research, econometric analysis, input/output analysis, willingness to pay and the conceptual framework of water markets. Main use sectors are agriculture, forestry, municipalities (domestic consumption) and the environment. Water values estimated in the studies differ significantly between sectors, as well as between and within catchment areas. Most of the studies focused on irrigated agriculture as an important use sector in terms of water volumes, food production and capital investment. Input/output analysis indicates that South African agriculture is a less productive user of water in terms of gross income generated per unit of water. Evidence suggests that industrial and domestic use place a high value on assurance of supply of current water consumption levels. In contrast, agriculture requires large volumes of water for food production in response to market demand. The average value product of water is much higher for industry than agriculture, but the marginal value products appear similar in both sectors. From this it is concluded that water-use rights will in future be transferred from agriculture to industry but there is no urgency at present. As water is transferred in future from agriculture to domestic use and industrial use, the value (rents) now attached to land will transfer to water and real water prices will accordingly increase. The transfer of rents from land to water should not affect the value of farms. The expected significant increase in real water prices in a water market will provide further incentives for its conservation. The purpose in this review paper that covers a wide range of topics is to provide information to policy decision-makers on the economics of water management in South Africa. Keywords: use sectors, modelling research, water values, market transactions, water prices

Highlights

  • Several studies have been undertaken to assist with the implementation of the National Water Act (NWA), Act No 36 of 1998 (RSA, 1998), and the National Water Resource Strategy (NWRS) of 2004 (RSA, 2004), by the Department of Water Affairs (DWA)

  • The water price is the economic price as revealed by the catchment using econometric techniques demand schedules at the given level of supply, i.e. the price which would be current if there were a market for water

  • Component (PC1) shows positive loadings amongst the following variables: buyers of water entitlements (TYPE = 1 for buyer and = 0 for seller); percentage of cropped area planted to export table grapes (EXP); percentage planted to horticultural crops (HOR), percentage of advanced irrigation technology used (DRIP); income per cubic meter of water applied (IN)

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Summary

Introduction

In this paper some of the economic studies are reviewed with the purpose of documenting the lessons learnt. Water resources should be allocated in a way that will ensure its ‘best possible use’. The ‘best possible use’ entails more than the productive use of water since in addition social, economic and environmental factors must be included to achieve the objectives of equity, efficiency and sustainability of water use. Findings in several economic studies are reviewed with the focus on economic efficiency using a modelling approach. Sustainability is given attention in this article in several studies on the environmental use of water and pollution.

Economic principles
Water as a consumption good estimated by econometric models
Modelling the value of water use in nonagricultural sectors
Municipal value of water estimated by econometric techniques
Predicted values
Modelling the value of water use in agriculture
Studying water right markets in the Crocodile River catchment
Bare land
Great Letaba River Catchment
Studying water right markets in the Orange River
Modelling policy risk in water markets
Assurance of supply
Water quality and economic models of pollution trading offsets
Findings
Conclusion
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