Virtual water refers both to water consumed during the process of production and water remaining as the constituent of the product. Apart from its quantity, easily calculated, it can also be determined in qualitative terms, through the water footprint, which describes the amount of water used by any biological entity. It can be presented as three-portion system, comprised of blue, green and gray water. The attempts to solve agricultural problems in the countries suffering from water shortage, the importance of green water has been emphasized, pointing to adequate water management. Virtual water concept enabled understanding of the international water trading ways, as it remains within the products traded. Adjusting export oriented food production any country can save significant amounts of domestic water, thus implementing its water sustainability that is important for all the countries. Since large quantities of good quality water for agricultural irrigation are the utmost requirement, it is often a limiting factor, implying that new methodology of water-food transformation should be developed

Bošković, Jelena

Galonja Coghill, Tamara

Kostadinović, Ljiljana

Suturović, Edita

Bošković Jelena

Galonja Coghill Tamara

Kostadinović Ljiljana

Suturović Edita

University of Szeged

 Review on Agriculture and Rural Development 2013. vol. 2. (1) ISSN 2063-4803 224  VIRTUAL WATER IN AGRICULTURAL PRODUCTION  TAMARA GALONJA COGHILL1, JELENA BOŠKOVIĆ1, LJILJANA KOSTADINOVIĆ2, EDITA SUTUROVIĆ1  1Faculty for Biofarming, Bačka Topola, Megatrend University, Belgrade 2Institute for Food Technology, Novi Sad tamaragc@neobee.net   ABSTRACT Virtual water refers both to water consumed during the process of production and water remaining as the constituent of the product. Apart from its quantity, easily calculated, it can also be determined in qualitative terms, through the water footprint, which describes the amount of water used by any biological entity. It can be presented as three-portion system, comprised of blue, green and gray water. The attempts to solve agricultural problems in the countries suffering from water shortage, the importance of green water has been emphasized, pointing to adequate water management. Virtual water concept enabled understanding of the international water trading ways, as it remains within the products traded. Adjusting export oriented food production any country can save significant amounts of domestic water, thus implementing its water sustainability that is important for all the countries. Since large quantities of good quality water for agricultural irrigation are the utmost requirement, it is often a limiting factor, implying that new methodology of water-food transformation should be developed.  Keywords: virtual water, agriculture, water footprints   THE WATER USED IN AGRICULTURAL PRODUCTION  The water that is used during the production of any product, including agricultural products and remains a constituent of the product is called "virtual water" (ALLAN, 1998). Although this idea was firstly developed to analyze water scarcity-caused agricultural problems in the Middle East, it was widely recognized as the means of interconnecting trading, food and water, both freshwater and soil water. It takes into the account all the water consumed during the production process, regardless of the nature of the product. For example, for the production of 1000 g of beef, a total amount of over fifteen thousand litres of water must be used. Some grains (e.g. wheat) need an input of thirteen hundred litres of water, for the production of 1000 g of final product (MERRETT ET AL., 2003). Obviously, such situation raises questions regarding the international trade of water contained in traded products. If any country imports 1000 kg soybeans, it also imports all the water used in their production, e.g. 2752 m3 (Table 1). Some countries stopped exporting water demanding crops, hence reducing virtual water export. Indeed, those countries import such products, and some significant amounts of water contained within them. For example, 13805 m3 virtual water was imported by some Middle East countries during every single year between 1995 and 2000, as opposed to only 642 m3 water exported (COSGROVE AND RIJSBERMAN, 2000; HOEKSTRA, 2003). Adjusting export oriented food production, any country can save significant amounts of domestic water thus implementing its water sustainability that is important for all countries. Specific amounts of water needed for the production of some vegetal products are given in the Table 1.    Review on Agriculture and Rural Development 2013. vol. 2. (1) ISSN 2063-4803 225  Table 1. Specific Water Demands of some primary vegetal products   Products Specific Water Demand (m3/T) Products Specific Water Demand (m3/T) Wheat, millet, rye  1159 Groundnuts 2547 Barley  1910 Sunflower  3283 Oats  2374 Tomatoes  130 Sorghum  542 Onions  168 Rice  1408 Vegetable, others  195 Maize  710 Grapefruit  286 Cereals, others   1159 Lemons, limes  344 Potatoes   105 Oranges and other citrus  378 Sugar beet  193 Bananas  499 Sugar Cane  318 Apples  387 Pulses  1754 Pineapples  418 Tree nuts  4936 Dates  1660 Rape and Mustard seed  1521 Grapes  455 Soybeans  2752 Fruit, others  455 Olives  2500   (http://www.igd.com )  The analysis of virtual water flow includes any additional water consuming product or service, used for the production of a certain product. The amount of water incorporated into some of the products is given in Table 2.  Table 2. Estimates of the volume of water incorporated into different products   Item Liters Item Liters Item Liters Hamburger, 150g 2400 Cup of coffee, 125ml 140 Glass of orange juice, 200ml 170 Glass of milk, 200ml 200 Apple, 1 kg 700 Glass of apple juice, 200ml 190 Cup of tea, 250ml 35 Glass of wine, 125ml 120 Egg, 40g 135 Slice of bread, 30g 135 Tomato, 70g 13 Bovine leather shoes 8000 (http://www.igd.com )  Surprisingly, one pair of bovine leather shoes carry the load of about 8000 litres of incorporated water, while ordinary hamburger "contains" 2400 litres of  water used during its production (Table 2).  The international virtual water trade may be the way of preserving world water, although it would be realistic only if water rich countries should export products "containing" large   Review on Agriculture and Rural Development 2013. vol. 2. (1) ISSN 2063-4803 226  amounts of embedded water. There are also suggestions that monetary value of embedded water should be incorporated into the product price.   BLUE, GREEN AND GREY WATER FOOTPRINT  The idea of the ecological footprint was initially developed in 1996 (WAKEMAGEL AND REES, 1996) and quickly adopted by the UNESCO-IHE as water use indicator (HOEKSTRA, 2003). It defines the amount of water used by any biological entity, from an individual to the entire nation.  Water footprint comprises three components: blue, green and grey water (AHLENIUS, 2012). The blue water footprint is the amount of freshwater irreversibly used from surface and ground water. The green water footprint is the amount of consumed rainwater stored as soil moisture, evaporating from global green water resources. The grey water footprint is the amount of water polluted during the production of goods and services (water needed for the assimilation of pollutants). Provided that green water management is efficient, even some countries with water shortage could be able to produce enough food for their populations.  A particular blue-green-gray water footprint distribution can be assigned to each agricultural product, determining the dominant water source type and its polluting impact on the entire environment. In animal husbandry it is known that an average beef production consumes 93% green, 4% blue, 3% grey water, mainly using surface and ground freshwater sources. The portion of virtual water needed to carry the load of the pollutants created during the production process is 3%, while wheat production includes 11% grey water (KIRBY ET AL., 2003).   HEALTHY AGRICULTURAL FOOD PRODUCTION  Since large quantities of good quality water for agricultural irrigation are the utmost requirement, it often presents a limiting factor (KIRBY ET AL., 2003). The water used for the irrigation is classified by its trophic level, type and quantity of dissolved matter (salts and suspended solids), all of which can have negative impact not only on plants but also on other important organisms that maintain soil fertility and viability. Assessments of global water availability predict that seven out of ten people in the world will experience some water-related stress, by the year 2050.  In many areas water supply is limited and the cost of irrigation system construction is high. That implies that the new methodology of water-food transformation should be developed (RENAULT AND WALLENDER, 2000; ROSEGRANT AND RINGLER, 1999). There was a five-fold increase in water use for the agricultural production during the last decade of 20th century (500 to 2500 km3 per year). It is estimated that agriculture uses 70% of available water resources (NITTI, 2011). Water is essential in assuring the food hygiene, hence it is used not only in primary food production, but also for food processing, washing, cleaning, blanching, peeling, cutting, mixing, steaming, freezing, heating, boiling etc.  There may be crucial vital difference between the agricultural strategies that had focused on blue water irrigation (e.g. irrigation) and new strategies that rely on green water   Review on Agriculture and Rural Development 2013. vol. 2. (1) ISSN 2063-4803 227  (SABMILLER PLC., 2009). As illustrated in Figure 1, crops for beer production require 85% green and only 6% blue (irrigation) water. The pollution output is 9% (gray water, assimilating the resultant production pollutants).      Figure 1. Proportion of blue, green and gray water in beer production  Greatest water consumers amongst crops are rice, (more than 20% total water used in global crop production) and wheat (12% of global crop water use). All those should be taken into account when determining the national water footprint (NITTI, 2011).    CONCLUSIONS  The concept of virtual water interconnects freshwater (surface and ground) and soil water, used in the production of agricultural goods, considering it incorporated into the product or service. Any trade also implies trading embedded water. The total volume of virtual water can be presented through the water footprint that shows the amounts of fresh or rainwater used for the production, and the amount of water needed for the assimilation of production-born pollutants. Adjusting the three portions of national water footprint enables adequate water resources management. At this time, Serbia does not have virtual water strategy and needs to account for all its agricultural production inputs and outputs as well as export and import balance.   ACKNOWLEDGEMENT  This research was supported by the Ministry of Education and Science of the Republic of Serbia, as a part of the project TR31031, entitled "Promotion of sustainability and competitiveness in organic plant and stock production using new technologies and inputs".   REFERENCES  AHLENIUS, H. (2012): UNEP/GRID-Arendal, http://www.oecdbookshop.org, 17 April 2012 ALLAN, J.A., (1998): Virtual water: a strategic resource. Global solutions to regional deficits. Groundwater, 36(4):545-546. COSGROVE, W.J., RIJSBERMAN, F. (2000): World Water Vision, Making water everybody’s business. World Water Council, Earthscan, 108pp.   Review on Agriculture and Rural Development 2013. vol. 2. (1) ISSN 2063-4803 228  HOEKSTRA, A.Y. (2003): (ed) Virtual water trade: Proceedings of the International Expert Meeting on Virtual Water Trade, IHE Delft, the Netherlands HTTP://WWW.IGD.COM/index.asp?id=1&fid=1&sid=5&tid=157&foid=85&cid=326 KIRBY, R.M., BARTRAM, J., CARR, R. (2003): Water in food production and processing: quantity and quality concerns, Food Control, Volume 14, Issue 5, Pages 283–299 MERRETT, S., ALLAN, J.A. AND LANT, C. (2003): Virtual Water - the Water, Food, and Trade Nexus Useful Concept or Misleading Metaphor? IWRA, Water International, Volume 28, Number 1 NITTI, G. (2011): Water Is Not an Infinite Resource and the World is Thirsty. The Italian Insider (Rome): p. 8 RENAULT D., WALLENDER, W.W. (2000): Nutritional Water Productivity and Diets : From  "Crop per drop" towards "Nutrition per drop". Agricultural Water Management, 45:275-296. ROSEGRANT M. AND RINGLER, C. (1999): Impact on food security and rural development of reallocating water from agriculture. IFPRI. Washington DC. SABMILLER PLC. (2009): Water footprinting, Identifying and Addressing Water Risks in the Value Chain, WWF, UK, Panda House, England WAKEMAGEL, M., REES, W. (1996): Our Ecological Footprint: Reducing Human Impact on the Earth. Gabriola Island, BC, Canada: New Society Publishers    

Virtual water in agricultural production

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Virtual water in agricultural production

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