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词条 Virtual water
释义

  1. History

  2. Trade

  3. Water footprint

  4. Embodied energy

  5. Criticism

     Limitations of the virtual water measure 

  6. Virtual water content of selected products

  7. See also

  8. References

  9. Further reading

Virtual water trade (also known as trade in embedded or embodied water) refers to the hidden flow of water if food or other commodities are traded from one place to another. For instance, it takes 1,340 cubic meters of water (based on the world 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".[1] It refers to the sum of the water use in the various steps of the production chain.

History

Noah Kunst and Moritz Schneider introduced the virtual water concept.[2]{{clarify|reason=Please supply quote of paragraph in article - as strong claim made.|date=January 2019}} Noah 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." Both have been rewarded for their concept with the Nobel Memorial Prize in Economic Sciences of the year 2009 which is commonly referred to as the Nobel Prize in Economics.

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. This has obvious strategic implications for countries that are water-constrained such as those found in the Southern African Development Community (SADC) area.[3][4][5]

Water-scarce countries like Israel discourage the export of oranges (relatively water intensive crops) 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 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.[6] 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 one to distinguish between global, regional and local levels and their linkages. This means, that water resource problems have to be solved in problemsheds[7][8] 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.

Water footprint

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.{{Citation needed|date=January 2019}} 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.{{Citation needed|date=January 2019}}

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.[9]

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.[10]

Limitations of the virtual water measure

Key shortcomings of virtual water measures are that the concept:

  1. It 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.&91;11&93;
  2. It 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.&91;11&93;
  3. It 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.&91;11&93;

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.[12]

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.&91;13&93;
  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.&91;14&93;
  3. The use of virtual water lies in the religious regulations for charging for water. According to Al-Bukhari, Prophet Mohammad's teachings, the Prophet 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.&91;14&93;

Virtual water content of selected products

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

Product USAChinaIndiaRussiaIndonesiaAustraliaBrazilJapanMexicoItalyNetherlandsWorld average
Rice (paddy)1,2751,3212,8502,4012,1501,0223,0821,2212,1821,6792,291
Rice (husked)1,6561,7163,7023,1182,7931,3274,0031,5862,8342,1802,975
Rice (broken)1,9031,9724,2543,5843,2091,5254,6001,8223,2572,5063,419
Wheat8496901,6542,3751,5881,6167341,0662,4216191,334
Maize4898011,9371,3971,2857441,1801,4931,744530408909
Soybeans1,8692,6174,1243,9332,0302,1061,0762,3263,1771,5061,789
Sugar cane103117159164141155120171175
Cotton seed2,5351,4198,2644,4531,8872,7772,1273,644
Cotton lint5,7333,21018,69410,0724,2686,2814,8128,242
Barley7028481,9662,3591,4251,3736972,1201,8227181,388
Sorghum7828634,0531,2125822,853
Coconuts7492,2551,9542,545
Millet2,1431,8633,2694,5344,596
Coffee (green)4,8646,29012,18028,11917,373
Coffee (roasted)5,7907,48814,50033,47520,682
Tea (made)11,1107,0029,205
Beef13,19312,56016,48237,76221,16711,68115,497
Pork3,9462,2114,3976,5596,3773,7904,856
Goat meat3,0823,9945,18710,2524,1802,7914,043
Sheep meat5,9775,2026,69216,8787,5725,2986,143
Chicken meat2,3893,6527,7365,0132,1982,2223,918
Eggs1,5103,5507,5314,2771,3891,4043,340
Milk6951,0001,3691,3451,1439151,0018122,382861641990
Milk powder3,2344,6486,3686,2535,3174,2554,6543,77411,0774,0052,9824,602
Cheese3,4574,9636,7936,6715,6754,5444,9694,03211,8054,2783,1904,914
Leather (bovine)14,19013,51317,71022,57515,92918,38418,22211,86440,48222,72412,57216,656

See also

  • Peak water
  • Water footprint
  • Water management
  • Deficit irrigation
  • Water resource policy

References

1. ^{{cite journal |doi=10.1007/s11269-006-9039-x |vauthors=Hoekstra AY, Chapagain AK |title=Water footprints of nations: water use by people as a function of their consumption pattern |journal=Water Resources Management |volume=21 |issue=1 |pages=35–48 |year=2007 |url=http://www.waterfootprint.org/?page=files/Publications}}
2. ^[https://www.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.
3. ^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’. Unpublished M.A. Dissertation, Department of International Politics, University of South Africa, Pretoria, South Africa.
4. ^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).
5. ^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.
6. ^{{cite journal |vauthors=Berrittella M, Hoekstra AY, Rehdanz K, Roson R, Tol RS |title=The Economic Impact of Restricted Water Supply: A Computable General Equilibrium Analysis |journal=Water Research |volume= 41|pages=1799–813 |year=2007 |url=http://ideas.repec.org/p/sgc/wpaper/93.html |pmid=17343892 |issue=8 |doi=10.1016/j.watres.2007.01.010}}
7. ^{{cite journal|author=Allan T |title=Watersheds and problemsheds: Explaining the absence of Armed Conflict over water in the Middle East |journal=Middle East Review of International Affairs |volume=2 |issue=1 |pages= |year=1998 |url=http://meria.idc.ac.il/journal/1998/issue1/jv2n1a7.html |deadurl=yes |archiveurl=https://web.archive.org/web/20061127104256/http://meria.idc.ac.il/journal/1998/issue1/jv2n1a7.html |archivedate=November 27, 2006 }}
8. ^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.
9. ^{{cite journal |vauthors=Lenzen M, Foran B |title=An Input-Output analysis of Australian water usage |journal=Water Policy |volume=3 |issue= 4|pages=321–40 |year=2001 |doi=10.1016/S1366-7017(01)00072-1 }}
10. ^http://content.webarchive.nla.gov.au/gov/wayback/20160615091008/http://archive.nwc.gov.au/__data/assets/pdf_file/0005/11885/DistilledJuly2008.pdf {{ISSN|1833-1491}}
11. ^Virtual Water - The concept of Virtual Water
12. ^Distilled: eNewsletter of Australia's National Water Commission, Edition 30 — July 2008
13. ^Slide 1 {{webarchive |url=https://web.archive.org/web/20110718230922/http://www.die-gdi.de/DIE_Homepage.nsf/6f3fa777ba64bd9ec12569cb00547f1b/01b3da26dc5fe93bc1256f81003065d4/$FILE/2005-12-07-Virtueller-Wasserhandel-Vortrag-Abbadi.pdf |date=July 18, 2011 }}
14. ^Expert Statement on Virtual Water {{webarchive |url=https://web.archive.org/web/20110722070725/http://www.osd.com.jo/vertual_water.pdf |date=July 22, 2011 }} by Dr. Hazim El-Naser and Mohammad Abbadi (2005).
15. ^{{cite book | last=Craswell | first=E. | last2=Bonnell | first2=M. | last3=Bossio | first3=D. | last4=Demuth | first4=S. | last5=van de Giesen | first5=N. | title=Integrated Assessment of Water Resources and Global Change: A North-South Analysis | publisher=Springer Netherlands | year=2007 | isbn=978-1-4020-5591-1 | url=https://books.google.com/books?id=Wbc_h0onmFsC&pg=PA39 | accessdate=August 8, 2015 | page=40}}

Further reading

  • Hoekstra, A.Y. (2003) (ed) ‘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
  • Chapagain, A.K. and Hoekstra, A.Y. (2008) 'The global component of freshwater demand and supply: An assessment of virtual water flows between nations as a result of trade in agricultural and industrial products' Water International 33(1): 19-32.
  • Hummel, D., T. Kluge, S. Liehr, M. Hachelaf (2006) [ Virtual Water Trade. Documentation of an International Expert Workshop]. July 3–4, 2006. Frankfurt am Main. ISOE-Materialien Soziale Ökologie No. 24
  • {{Cite journal| volume = 3| issue = 4| pages = 321–340| last = Lenzen| first = M.|author2=B. Foran | title = An input-output analysis of Australian water usage| journal = Water Policy| year = 2001| doi = 10.1016/S1366-7017(01)00072-1}}
  • {{Citation | last = Lenzen | first = M. | publisher = Australian Bureau of Statistics, Commonwealth of Australia | title = The influence of lifestyles on environmental pressure |date = 25 February 2002 | url = http://www.abs.gov.au/ausstats/abs@.nsf/Previousproducts/1301.0Feature%20Article162002}}
  • {{cite journal |doi=10.1016/j.ecolecon.2006.07.033 |vauthors=Vardona M, Lenzen M, Peevora S, Creasera M |title=Water accounting in Australia |journal=Ecological Economics |volume=61 |issue= 4|pages=650–9 |year=2007}}
  • {{cite book|last=Zygmunt|first=J. |title=Hidden Waters |url=http://www.waterfootprint.org/Reports/Zygmunt_2007.pdf|year=2007|publisher=Waterwise|location=London}}

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