Capital Expenditure (CapEx)
Capital Expenditure is the costs of providing a water or sanitation service to users where there was no service before; or of substantially increasing the level of services received by users. It includes the capital invested in first time construction or purchase of fixed assets such as concrete structures, wells, pumps, pipes or toilets prior to implementation of the service and to improve or expand existing water or sanitation systems. Costs for rehabilitation or replacement of major parts of a water or sanitation system, such as replacing a pump, are considered expenditure on capital maintenance (CapManEx). Capital expenditure (CapEx) consists of expenses on hardware and software (see figure 1). Capital expenditure hardware (CapEx hrd) includes expenditure on fixed assets as pumps, pipes, etc. and required equipment such as vehicles or offices to support the construction of water and sanitation systems prior to implementation of the service. Capital Expenditure software (CapEx Sft) includes the costs of one-off work with stakeholders prior to construction or implementation or extension of the service such as one-off training of pump mechanics or caretakers, community mobilisation or hygiene education.
Source: Smits et.al, 2011, 7.
ExamplesAccording to the 2012 GLAAS report (WHO and UN-Water, 2012, 29), 69% of funds for water and sanitation expended in 11 respondent countries were directed towards Capital Expenditure (see figure 2). Figure 2 Capital expenditure versus operational and maintenance expenditure Capital expenditure water service deliveryBased on research from the #WASHCost project, Capital Expenditure (CapEx) to provide a basic level of water service with a borehole and handpump (at 2011 prices) range from US$ 20 per person to just over US$ 60 per person (see figure 3). For small schemes, including mechanised boreholes and piped supplies, the costs range from US$ 30 to just over US$ 130 per person. For intermediate and larger schemes benchmark capital costs vary widely from US$ 20 to US$ 152 per person. Key DocumentsBatchelor, C., Fonseca, C., and Smits, S., 2011. Life-cycle costs of rainwater harvesting systems. (Occasional paper series / IRC; 46). The Hague, The Netherlands: IRC International Water and Sanitation Centre. Available at: <http://www.irc.nl/page/66835> In partnership with IRC and the Rainwater Harvesting Implementation Network, WASHCost studied the historical trends and drivers of adopting Rain Water Harvesting (RWH). Detailed comparisons are made between life-cycle costs of RWH systems and the life-cycle costs of other water supply systems Burr, P. and Fonseca, C., 2011. Applying the life-cycle costs approach to sanitation : costs and service levels in Andhra Pradesh (India), Burkina Faso, Ghana and Mozambique. (WASHCost briefing note; 3). [online] The Hague, The Netherlands: IRC International Water and Sanitation Centre. Available at: <http://www.washcost.info/page/1626> This briefing note presents an application of the life-cycle costs (LCCA) approach to sanitation in rural and peri-urban areas in four different countries— Andhra Pradesh (India), Burkina Faso, Ghana, and Mozambique. The document compares the differences between the financial costs of traditional and improved latrines, and the quality of service delivered to users. Fonseca, C. et al., 2011. Life-cycle costs approach : costing sustainable services. (WASHCost briefing note; 1a). The Hague, The Netherlands: IRC International Water and Sanitation Centre. Available at: <http://www.washcost.info/page/1557> This briefing note describes the life-cycle costs approach and why it was developed. It explains the main cost components for water and sanitation in rural and peri-urban areas. IRC, 2012a. Providing a basic level of water and sanitation services that last : cost benchmarks . (WASHCost infosheet; 1). The Hague, The Netherlands: IRC International Water and Sanitation Centre. Available at: <http://www.washcost.info/page/2386> Information sheet provides an overview of the minimum benchmarks for costing sustainable basic services in developing countries. The benchmarks have been derived from the WASHCost project dataset and the best available cost data from other organisations all over the world. The benchmarks are useful for planning, assessing sustainability from a cost perspective and for monitoring value for money. IRC, 2012b. The cost of sustaining sanitation services for 20 years can be 5-20 times the cost of building a latrine. (WASHCost infosheet; 2). The Hague, The Netherlands: IRC International Water and Sanitation Centre. Available at: <http://www.washcost.info/page/2439> Smits, S. et al., 2011. Arrangements and cost of providing support to rural water service providers. (WASHCost working paper; 5). The Hague, The Netherlands: IRC International Water and Sanitation Centre. Available at: <http://www.washcost.info/page/1567> WHO and UN-Water, 2012. UN-Water global annual assessment of sanitation and drinking-water (GLAAS) 2012 report : the challenge of extending and sustaining services. (UN-water global annual assessment of sanitation and drinking-water (GLAAS) report; 2012). Geneva, Switzerland: World Health Organization (WHO). Available at: <http://washurl.net/6jo133> Links
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