Virtual water

Virtual water (also known as embedded water, embodied water, or hidden water) refers, in the context of trade, to the water used in the production of a good or service. For instance, it takes 1,300 cubic meters of water on average to produce one metric tonne of wheat. The precise volume can be more or less depending on climatic conditions and agricultural practice. Hoekstra and Chapagain have defined the virtual-water content of a product (a commodity, good or service) as "the volume of freshwater used to produce the product, measured at the place where the product was actually produced". [Hoekstra, A.Y. and Chapagain, A.K. (2007) [http://www.waterfootprint.org/?page=files/Publications Water footprints of nations: water use by people as a function of their consumption pattern, Water Resources Management 21(1): 35-48 ] ] It refers to the sum of the water use in the various steps of the production chain.

Professor John Anthony Allan from King’s College London and the School of Oriental and African Studies was the creator of the virtual water concept, [ [http://environment.newscientist.com/channel/earth/mg19926700.100-looming-water-crisis-simply-a-management-problem.html "Looming water crisis simply a management problem"] by Jonathan Chenoweth, New Scientist 28 Aug., 2008, pp. 28-32.] which measures how water is embedded in the production and trade of food and consumer products. For his contributions he was awarded the 2008 Stockholm Water Prize [http://www.siwi.org/sa/node.asp?node=25] . In his awarding, the Stockholm International Water Institute (SIWI) stated that "Virtual water has major impacts on global trade policy and research, especially in water-scarce regions, and has redefined discourse in water policy and management. By explaining how and why nations such as the US, Argentina and Brazil ‘export’ billions of litres of water each year, while others like Japan, Egypt and Italy ‘import’ billions, the virtual water concept has opened the door to more productive water use."

As professor John Anthony Allan (2005) stated: "The water is said to be virtual because once the wheat is grown, the real water used to grow it is no longer actually contained in the wheat. The concept of virtual water helps us realize how much water is needed to produce different goods and services. In semi-arid and arid areas, knowing the virtual water value of a good or service can be useful towards determining how best to use the scarce water available."

There are, however, significant deficiencies with the concept of virtual water that mean there is a significant risk in relying on these measures to guide policy conclusions. Accordingly, Australia's National Water Commission considers that the measurement of virtual water has little practical value in decision making regarding the best allocation of scarce water resources.

Virtual water in various products

It is essential to recognize that virtual water adds up. To produce 1 kilogram of wheat about 1000 liters of water are needed, but for beef about 15 times as much is required. The majority of the water that we consume is embedded in our food. Below there is a listing of the various average amounts of virtual water in food. This data was published through UNESCO-IHE "Institute for Water Education": [Chapagain, A.K. and Hoekstra, A.Y. (2004) [http://www.waterfootprint.org/Reports/Report16Vol1.pdf Water footprints of nations] Value of Water Research Report Series, No.6, UNESCO-IHE]

Agricultural products

* the production of 1 kg wheat costs 1,300 L water
* the production of 1 kg broken rice costs 3,400 L water
* the production of 1 kg eggs costs 3,300 L water
* the production of 1 kg beef costs 15,000 L water
* the production of 1 cotton shirt of 300 gram costs 2,500 L water

Household products

Not only is there virtual water in food, but it is located in various other products that the everyday person uses. The figures below were taken from another report published through UNESCO-IHE titled The Water Footprint of Cotton Consumption. [Chapagain, A.K., Hoekstra, A.Y., Savenije, H.H.G. and Gautam, R. (2006) [http://www.waterfootprint.org/?page=files/Publications The water footprint of cotton consumption: An assessment of the impact of worldwide consumption of cotton products on the water resources in the cotton producing countries] Ecological Economics. 60(1): 186-203.]
*Jeans (1000g) there is 10,850 liters of embedded water
*Diaper (75g) there is 810 liters of embedded water
*Bed Sheet (900g) there is 9,750 Liters of embedded water

Industrial products

Industrial goods also contain embodied water. One needs to understand how internal water resources are being used to produce cars, bicycles, teacups, and the like - particularly because industry usually uses only blue water for production (though rainwater harvesting is becoming more common). On average, a 1.1 tonne passenger car has about 400,000 liters of water embedded in it. This fact is compiled from several different resources including the UNESCO-IHE study [ [http://www.waterfootprint.org/?page=files/Research%20data Virtual water and water footprint database] ] and the Australian Food & Grocery 2003. [ [http://www.afgc.org.au Australian Food and Grocery Council. 2003. Environment Report 2003.] ] Another source suggests Australian cars require one million litres of water, though this is from using a different method.Lenzen, M., Foran, B. (2001) , "Water Policy", 3, 321-340.] The construction of house, using a combination of methods, requires about 6 million litres of water. [McCormack, M.S., Treloar, G.J., Palmowski, L. and Crawford, R.H. (2007) [http://www.informaworld.com/index/M66582J06590K467.pdf Modelling direct and indirect water consumption associated with construction] , Building Research and Information, 35 [2] , 156-162.]

The three colours of a product’s virtual-water content

The virtual-water content of a product consists of three components, called green, blue and grey components. [ [http://www.waterfootprint.org/?page=files/Concept_VirtualWater Water footprint and virtual water ] ]

The ‘green’ virtual-water content of a product is the volume of rainwater that evaporated during the production process. This is mainly relevant for agricultural products, where it refers to the total rainwater evaporation from the field during the growing period of the crop (including transpiration by the plants and other forms of evaporation).

The ‘blue’ virtual-water content of a product is the volume of surface water or groundwater that evaporated as a result of the production of the product. In the case of crop production, the blue water content of a crop is defined as the sum of the evaporation of irrigation water from the field and the evaporation of water from irrigation canals and artificial storagereservoirs (although for practical reasons the latter component has been left out from our studies). In the cases of industrial production and domestic water supply, the blue water content of the product or service is equal to the part of the water withdrawn from ground or surface water that evaporates and thus does not return to the system where it came from.

The ‘grey’ virtual-water content of a product is the volume of water that becomes polluted during its production. This can be quantified by calculating the volume of water required to dilute pollutants emitted to the natural water system during its production process to such an extent that the quality of the ambient water remains beyond agreed water quality standards.

The distinction between green and blue water originates from Falkenmark (2003). [Falkenmark, M. (2003) , Philosophical Transaction of the Royal Society of London B 358(1440): 2037-2049. PMCID PMC1693285.] It is relevant to know the ratio of green to blue water use, because the impacts on the hydrological cycle are different. Both the green and blue components in the total virtual-water content of a product refer to evaporation. The grey component in the total virtual-water content of a product refers to the volume of polluted water. Evaporated water and polluted water have in common that they are both ‘lost’, i.e. in first instance unavailable for other uses. It is said ‘in first instance’ because evaporated water may come back as rainfall above land somewhere else and polluted water may become clean in the longer term, but these are considered here as secondary effects that will never take away the primary effects.

Impact of virtual water

Once you add up all the virtual water you eat and in the products that you buy along with the daily use of water out of the tap, you will have a better idea of what your water footprint is. Water footprints are used to give nations a better consumption-based indicator of water use.

Trade

Virtual water trade refers to the idea that when goods and services are exchanged, so is virtual water. When a country imports one tonne of wheat instead of producing it domestically, it is saving about 1,300 cubic meters of real indigenous water. If this country is water-scarce, the water that is 'saved' can be used towards other ends. If the exporting country is water-scarce, however, it has exported 1,300 cubic meters of virtual water since the real water used to grow the wheat will no longer be available for other purposes.

Daniel Zimmer, Director of the World Water Council, in his presentation at the session on "virtual water trade and geopolitics" at the 2003 World Water Forum in Kyoto::"The contrast in water use can be noticed between continents. In Asia, people consume an average of 1,400 litres of virtual water a day, while in Europe and North America, people consume about 4,000 litres. About 70 per cent of all water used by humans goes into food production. [...] ":"Among the biggest net exporter countries of virtual water are the U.S., Canada, Thailand, Argentina, India, Vietnam, France and Brazil. Some of the largest net import countries are Sri Lanka, Japan, the Netherlands, South Korea, China, Spain, Egypt, Germany and Italy."

Water-scarce countries like Israel discourage the export of oranges (relatively heavy water guzzlers) precisely to prevent large quantities of water being exported to different parts of the world.

In recent years, the concept of virtual water trade has gained weight both in the scientific as well as in the political debate. The notion of the concept is ambiguous. It changes between an analytical, descriptive concept and a political induced strategy. As an analytical concept, virtual water trade represents an instrument which allows the identification and assessment of policy options not only in the scientific but also in the political discourse. As a politically induced strategy the question is, whether virtual water trade can be implemented in a sustainable way, whether the implementation can be managed in a socially, economically and ecologically fashion, and for what countries the concept offers a meaningful option.

The data that underlie the concept of virtual water can readily be used to construct water satellite accounts, and brought into economic models of international trade such as the GTAP Computable General Equilibrium Model. [Berrittella, M., A.Y. Hoekstra, K. Rehdanz, R. Roson and R.S.J. Tol (2007), [http://ideas.repec.org/p/sgc/wpaper/93.html The Economic Impact of Restricted Water Supply: A Computable General Equilibrium Analysis] , Water Research, 42, 1799-1813.] Such a model can be used to study the economic implications of changes in water supply or water policy, as well as the water resource implications of economic development and trade liberalisation.

In sum, virtual water trade allows a new, amplified perspective on water problems: In the framework of recent developments from a supply-oriented to a demand-oriented management of water resources it opens up new fields of governance and facilitates a differentiation and balancing of different perspectives, basic conditions and interests. Analytically the concept enables to distinguish between global, regional and local levels and their linkages. This means, that water resource problems have to be solved in "problemsheds" [Allan, T. (1998) [http://meria.idc.ac.il/journal/1998/issue1/jv2n1a7.html Watersheds and problemsheds] ] if they cannot be successfully addressed in the local or regional watershed. Virtual water trade can thus overcome the hydro-centricity of a narrow watershed view. According to the proceedings of a 2006 conference in Frankfurt, Germany, it seems reasonable to link the new concept with the approach of Integrated water resources management.

Limitations of the virtual water measure

Key shortcomings of ‘virtual water’ measures are that the concept:

1. Relies on an assumption that all sources of water, whether in the form of rainfall or provided through an irrigation system, are of equal value. [http://www.dpi.vic.gov.au/DPI/nrenfa.nsf/LinkView/A1F945CE4D56F40ACA257412002310642B72296A5108C4FFCA25734F0009F96F/$file/Virtual%20Water%20-%20for%20release%20-%20STC%2008-03-07.pdf Virtual Water - for release - STC ] ]

2. Implicitly assumes that water that would be released by reducing a high water use activity would necessarily be available for use in a less water-intensive activity. For example, the implicit assumption is that water used in rangeland beef production would be available to be used to produce an alternative, less water-intensive activity. As a practical matter this may not be the case, nor might the alternatives be economic.

3. Fails as an indicator of environmental harm nor does it provide any indication of whether water resources are being used within sustainable extraction limits. The use of virtual water estimates therefore offer no guidance for policy makers seeking to ensure that environmental objectives are being met.

The deficiencies with the concept of virtual water mean that there is a significant risk in relying on these measures to guide policy conclusions. Accordingly, Australia's National Water Commission considers that the measurement of virtual water has little practical value in decision making regarding the best allocation of scarce water resources. [http://www.nwc.gov.au/resources/documents/DistilledJuly2008.pdf Distilled] ]

Other limitations more specific to the MENA (Middle East & North Africa) region include:

1. In MENA rural societies, farmers are by tradition politically influential and would prohibit new policies for water allocation. Reallocating the water resources adds a huge burden on the farmers especially when a large portion of those farmers use their land for their own food consumption which happens to be their only source of food supply. [ [http://www.die-gdi.de/DIE_Homepage.nsf/6f3fa777ba64bd9ec12569cb00547f1b/01b3da26dc5fe93bc1256f81003065d4/$FILE/2005-12-07-Virtueller-Wasserhandel-Vortrag-Abbadi.pdf Slide 1 ] ]

2. Importing food could pose the risk of further political dependence. The notion of "Self Sufficiency" has always been the pride of the MENA region. [http://www.osd.com.jo/vertual_water.pdf Expert Statement on Virtual Water] by Dr. Hazim El-Naser and Mohammad Abbadi (2005).]

3. The use of virtual water lies in the religious regulations for charging for water. According to Al-Bukhari, Prophet Mohammad’s teachings, The Profit said: “People are partners in three: Water,Herbs and Fire” (referring to basic energy resources). Therefore, and because farmers are generally poor and rain water, rivers and lakes are like a gift from God,the MENA countries might find it difficult to charge the farmers the full cost for water.

Embodied energy

Some researchers have attempted to use the methods of energy analysis, which aim to produce embodied energy estimates, to derive virtual, or embodied water estimates.

References

See also

* Water management
* Water footprint

External links

* [http://environment.newscientist.com/data/images/archive/2670/26700101.jpgGraph] showing virtual water imports and exports world-wide, from [http://environment.newscientist.com/channel/earth/mg19926700.100-looming-water-crisis-simply-a-management-problem.html "Looming water crisis simply a management problem"] by Jonathan Chenoweth, New Scientist 28 Aug., 2008, pp. 28-32.
* Hoekstra, A.Y. (2003) (ed) ‘ [http://www.waterfootprint.org/Reports/Report12.pdf Virtual water trade: Proceedings of the International Expert Meeting on Virtual Water Trade] ’ Value of Water Research Report Series No.12, UNESCO-IHE, Delft, the Netherlands
* Hummel, D., T. Kluge, S. Liehr, M. Hachelaf (2006) [http://www.isoe.de/ftp/vwt-documentation.pdf Virtual Water Trade. Documentation of an International Expert Workshop] . July 3-4, 2006. Frankfurt am Main. ISOE-Materialien Soziale Ökologie No. 24
* [http://www.wateryear2003.org/en/ev.php-URL_ID=5868&URL_DO=DO_TOPIC&URL_SECTION=201.html UN International year of fresh water - virtual water]
* Vardona,M, Lenzen,M. Peevora, S., Creasera, M. 2007. Water accounting in Australia, "Ecological Economics", 61, 650 – 659.
* [http://www.traumkrieger.de/virtualwater Virtual Water poster] . Typographic poster series on Virtual Water and Water Footprints of Nations, based on the research data of UNESCO-IHE.
* Zygmunt, J. (2007) [http://www.waterwise.org.uk Hidden Waters, A Waterwise briefing on embedded water and water footprints] .
* [http://www.abs.gov.au/ausstats/abs@.nsf/Previousproducts/1301.0Feature%20Article162002?opendocument&tabname=Summary&prodno=1301.0&issue=2002&num=&view= Australian Bureau of Statistics Article on Embodied Water]
* [http://www.fao.org/nr/water/promotional.html Virtual Water poster] . Educational poster on Virtual Water by the Food and Agriculture Organization of the United Nations (FAO Water Unit)