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Virtual water

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(Redirected from Embodied water)

The virtual water trade is the hidden flow of water in food or other commodities that are traded from one place to another.[1] Other terms for it are embedded or embodied water. The virtual water trade is the idea that virtual water is exchanged along with goods and services. This idea provides a new, amplified perspective on water problems. It balances different perspectives, basic conditions, and interests. This concept makes it possible to distinguish between global, regional, and local levels and their linkages. However, the use of virtual water estimates may offer no guidance for policymakers seeking to ensure they are meeting environmental objectives.

For example, cereal grains have been major carriers of virtual water in countries where water resources are scarce. So cereal imports can compensate for local water deficits.[2] However, low-income countries may not be able to afford such imports in the future. This could lead to food insecurity and starvation.

Concept

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The virtual water concept, also known as embodied water, was coined by John Anthony Allan (Tony Allan) in 1993. He received the Stockholm Water Prize for the concept in 2008.[3][4]

The virtual water trade is 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. This has obvious strategic implications for countries that are water-constrained such as those found in the Southern African Development Community (SADC) area.[5][6][7]

Water-scarce countries like Israel discourage the export of oranges (relatively water intensive crops) precisely to prevent large quantities of water from being exported to different parts of the world.[8]

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 that 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 if virtual water trade can be implemented in a sustainable way, whether the implementation can be managed in a social, economical, and ecological fashion, and for which 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.[9] Such a model can be used to study the economic implications of changes in the water supply or water policy, as well as the water resource implications of economic development and trade liberalization.

In sum, virtual water trade allows a new, amplified perspective on water problems: In the framework of recent developments from a supply-oriented to demand-oriented management of water resources, it opens up new fields of governance and facilitates differentiation and balancing of different perspectives, basic conditions, and interests. Analytically, the concept enables one to distinguish between global, regional, and local levels and their linkages. This means, that water resource problems have to be solved in problems[10][11] 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.

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Water footprint

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The concept of virtual water trade was introduced to refer to the idea that countries can save domestic water by importing food. Imported food, however, comes from somewhere. In 2002, Arjen Y. Hoekstra, while working for UNESCO-IHE, introduced the concept of water footprint.[12] The water footprint shows the link between consumer goods or a consumption pattern and water use and pollution. Virtual water trade and water footprint can be seen as part of a bigger story: the globalization of water.

For instance, it takes 1,340 cubic meters of water (based on the world average) to produce one tonne of wheat. The precise volume can be more or less depending on climatic conditions and agricultural practice. Hoekstra has 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".[13] It refers to the sum of the water use in the various steps of the production chain.

Embodied energy

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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.[14]

Virtual water content of selected products

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The following table shows the average virtual water content of some selected products for a number of selected countries (m3/ton):[15]

Product USA China India Russia Indonesia Australia Brazil Japan Mexico Italy Netherlands World average
Rice (paddy) 1,275 1,321 2,850 2,401 2,150 1,022 3,082 1,221 2,182 1,679 2,291
Rice (husked) 1,656 1,716 3,702 3,118 2,793 1,327 4,003 1,586 2,834 2,180 2,975
Rice (broken) 1,903 1,972 4,254 3,584 3,209 1,525 4,600 1,822 3,257 2,506 3,419
Wheat 849 690 1,654 2,375 1,588 1,616 734 1,066 2,421 619 1,334
Maize 489 801 1,937 1,397 1,285 744 1,180 1,493 1,744 530 408 909
Soybeans 1,869 2,617 4,124 3,933 2,030 2,106 1,076 2,326 3,177 1,506 1,789
Sugar cane 103 117 159 164 141 155 120 171 175
Cotton seed 2,535 1,419 8,264 4,453 1,887 2,777 2,127 3,644
Cotton lint 5,733 3,210 18,694 10,072 4,268 6,281 4,812 8,242
Barley 702 848 1,966 2,359 1,425 1,373 697 2,120 1,822 718 1,388
Sorghum 782 863 4,053 1,212 582 2,853
Coconuts 749 2,255 1,954 2,545
Millet 2,143 1,863 3,269 4,534 4,596
Coffee (green) 4,864 6,290 12,180 28,119 17,373
Coffee (roasted) 5,790 7,488 14,500 33,475 20,682
Tea (made) 11,110 7,002 9,205
Beef 13,193 12,560 16,482 37,762 21,167 11,681 15,497
Pork 3,946 2,211 4,397 6,559 6,377 3,790 4,856
Goat meat 3,082 3,994 5,187 10,252 4,180 2,791 4,043
Sheep meat 5,977 5,202 6,692 16,878 7,572 5,298 6,143
Chicken meat 2,389 3,652 7,736 5,013 2,198 2,222 3,918
Eggs 1,510 3,550 7,531 4,277 1,389 1,404 3,340
Milk 695 1,000 1,369 1,345 1,143 915 1,001 812 2,382 861 641 990
Milk powder 3,234 4,648 6,368 6,253 5,317 4,255 4,654 3,774 11,077 4,005 2,982 4,602
Cheese 3,457 4,963 6,793 6,671 5,675 4,544 4,969 4,032 11,805 4,278 3,190 4,914
Leather (bovine) 14,190 13,513 17,710 22,575 15,929 18,384 18,222 11,864 40,482 22,724 12,572 16,656

Limitations

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The virtual water or the water footprint concepts have faced some criticism. 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.[16]

Other limitations more specific to the MENA (the Middle East & North Africa) region include the fact that importing food could pose the risk of further political dependence. The notion of "self-sufficiency" has always been the pride of the MENA region.[17]

See also

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References

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  1. ^ Hoekstra, A. Y. (2003). Virtual water trade : proceedings of the international expert meeting on virtual water trade. IHE. OCLC 66727970.
  2. ^ Yang, Hong; Reichert, Peter; Abbaspour, Karim C.; Zehnder, Alexander J. B. (2003). "A Water Resources Threshold and Its Implications for Food Security". Environmental Science & Technology. 37 (14): 3048–3054. doi:10.1021/es0263689. ISSN 0013-936X. PMID 12901649.
  3. ^ Kruzman, Diana (31 May 2021). "U.S. Southwest, Already Parched, Sees 'Virtual Water' Drain Abroad". Undark. Retrieved 10 June 2021.
  4. ^ Stack Whitney, Kaitlin; Whitney, Kristoffer (Spring 2018). "John Anthony Allan's 'Virtual Water': Natural Resources Management in the Wake of Neoliberalism". Environment & Society Portal, Arcadia (11). Rachel Carson Center for Environment and Society. doi:10.5282/rcc/8316. ISSN 2199-3408. S2CID 158594930. Retrieved 10 June 2021.
  5. ^ Turton, A.R. (1998). The Hydropolitics of Southern Africa: The Case of the Zambezi River Basin as an Area of Potential Co-operation Based on Allan's Concept of 'Virtual Water' (MA Thesis ed.). Pretoria: University of South Africa.
  6. ^ Turton, A.R., Moodley, S., Goldblatt, M. & Meissner, R. 2000. An Analysis of the Role of Virtual Water in Southern Africa in Meeting Water Scarcity: An Applied Research and Capacity Building Project. Johannesburg: Group for Environmental Monitoring (GEM).
  7. ^ Earle, A. & Turton, A.R. 2003. "The Virtual Water Trade amongst Countries of the SADC". In Hoekstra, A. (Ed.) Virtual Water Trade: Proceedings of the International Experts Meeting on Virtual Water Trade. Delft, the Netherlands, 12–13 December 2002. Research Report Series No. 12. Delft: IHE. pp. 183-200.
  8. ^ "The End of the Jaffa Orange Highlights Israel Economic Shift - Bloomberg". Bloomberg News. 2020-03-06. Archived from the original on 2020-03-06. Retrieved 2021-09-20.
  9. ^ Berrittella M, Hoekstra AY, Rehdanz K, Roson R, Tol RS (2007). "The Economic Impact of Restricted Water Supply: A Computable General Equilibrium Analysis". Water Research. 41 (8): 1799–813. doi:10.1016/j.watres.2007.01.010. PMID 17343892.
  10. ^ Allan, Tony (1998). "Watersheds and Problemsheds: Explaining the absence of Armed Conflict over water in the Middle East". Middle East Review of International Affairs. 2 (1). Archived from the original on November 27, 2006.
  11. ^ Earle, A. 2003. "Watersheds and Problemsheds: A Strategic Perspective on the Water/Food/Trade Nexus in Southern Africa". In Turton, A.R., Ashton, P.J. & Cloete, T.E. (Eds.) Transboundary Rivers, Sovereignty, and Development: Hydropolitical Drivers in the Okavango River Basin. Pretoria & Geneva: AWIRU & Green Cross International. pp. 229-249.
  12. ^ "Aims & History". Water Footprint Network. Retrieved 10 June 2020. In 2002, Arjen Hoekstra, whilst working at the UNESCO-IHE Institute for Water Education, created the water footprint as a metric to measure the amount of water consumed and polluted to produce goods and services along their full supply chain.
  13. ^ Hoekstra AY, Chapagain AK (2007). "Water footprints of nations: water use by people as a function of their consumption pattern". Water Resources Management. 21 (1): 35–48. doi:10.1007/s11269-006-9039-x. S2CID 154320617.
  14. ^ Lenzen M, Foran B (2001). "An Input-Output analysis of Australian water usage". Water Policy. 3 (4): 321–40. doi:10.1016/S1366-7017(01)00072-1.
  15. ^ Craswell, E.; Bonnell, M.; Bossio, D.; Demuth, S.; van de Giesen, N. (2007). Integrated Assessment of Water Resources and Global Change: A North-South Analysis. Springer Netherlands. p. 40. ISBN 978-1-4020-5591-1. Retrieved August 8, 2015.
  16. ^ WA WATER (2014) Western Australia Branch Newsletter, June 2014, p. 1
  17. ^ Expert Statement on Virtual Water Archived July 22, 2011, at the Wayback Machine by Dr. Hazim El-Naser and Mohammad Abbadi (2005).

Further reading

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