Guidelines “On - Farm Water Management For Horticulture Crops” FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS This Guide was prepared in the framework of the project “Good Agriculture Practices For Sustainable Intensification Of The Small Holder Horticulture Sector In Egypt” Within the framework of cooperation between “Agriculture Research Center (ARC) Arab Republic of Egypt” and “Food and Agriculture Organization (FAO)” 2 Irrigation water use efficiency The Irrigation water efficiency (WUE) is defined to: 1- Water use efficiency 2- Distribution efficiency 3- Field application efficiency 1- Water use efficiency Water use efficiency = volume of product ÷ unit of water applied This represents a combination of the irrigation system and agronomic efficiencies for a crop. 2- Distribution efficiency Distribution efficiency is the comparison between the amount of water at the supply point and the amount of water that is delivered onto the field. The distribution efficiency is defines as: water delivered to irrigated field Distribution efficiency = -----------------------------------------------------total inflow to supply system 3- Field application efficiency Field application efficiency is the comparison between the amount of water delivered to the field and the amount of water that is used by the crop. Field application efficiency is defines as: crop water use Field application efficiency = --------------------------------------------water delivered to irrigated field Using water more efficiently can result in significant cost savings and environmental benefits. Therefore, water use efficiency is a term commonly used to describe the relationship between water (input) and agriculture product (output). Thus, water productivity might be measured by the volume of water taken into a plant to produce a unit of the output. In general, the lower the resource input requirement per unit, the higher the efficiency. 3 Water use efficiency is also often used to express the effectiveness of irrigation water delivery and use. Therefore we can defined irrigation efficiency as the ratio between the water stored in the soil depth inhabited with active plant roots to the water applied by the irrigation system (Table, 28). Thus, water applied by the irrigation system and not being made available to be taken up by plant roots is wasted and reduces irrigation efficiency. The major causes for reduced irrigation efficiency are drainage of excess irrigation water to soil layers deeper than the depth of active roots. Leakage of irrigation water to deep soil layers could result in pollution of the water table. The cases of irrigation efficiency of 100 % are practically none existent even in the most modern irrigation systems. Major difficulties in obtaining high irrigation efficiency stems from the inability to obtain an accurate estimate of the quantity of water needed to recharge the soil root zone depth and the lack of valid, real time information concerning the actual soil depth of active roots. Table (28): Irrigation efficiency under different methods of irrigation Methods of Irrigation Irrigation efficiencies Surface Sprinkler Drip Conveyance efficiency 40-50 100 100 (canal) 60-70 (well) Application efficiency 60-70 70-80 90 Surface water moisture 30-40 30-40 20-25 evaporation Overall efficiency 30-45 50-60 80-90 However, these efficiencies can be misleading and depend on soil type, moisture conditions before irrigation, depth to groundwater, the crop being grown, management practices, and quality of irrigation water. A technology that can lead to potentially high efficiencies, such as drip irrigation, still has to be managed to take full advantage of that potential. Generally, improving water use efficiency or a crop water use index will require the amount of water a crop transpires to be maximized and the losses that occur as the water moves to the plant to be minimized. Factors affecting water-use efficiency 1- Water delivery systems Open canals, lined ditches and pipelines (Plate, 42) vary in their ability to convey water and in the losses made. At macro level, the water conveyance system is a major factor in determining water-use efficiency. 4 Open canals lined ditches pipelines Plate (42): Water delivery systems 2- Irrigation systems. There are various methods for increasing water availability for transpiration. Factors to be considered for maximizing the availability of water are improvement of water movement in the soils, absorption by the roots and movement through the plant. The amount of water required for irrigation can be estimated by sampling the soil at several places in the field and estimating the moisture deficit. The water application is then calculated allowing for the possible losses. 3- Crop shape and morphology. When soil evaporation is low, crops with closed-leaf canopies (depending mainly on genetic factors) have better water use efficiency. 4- Climatic factors. The climate affects the physical processes controlling crop evapotranspiration and is key to the management and minimization of water loss. 5 5- Management. Appropriate decisions aim to increase the amount of water available for crop production and to improve crop growth characteristics in order to increase economic yield. Irrigation water management can be significantly enhanced by the agricultural practices that increase the soil's moisture-holding capacity or decrease evaporation, such as: A- Conservation tillage B- Cover crops C- Conservation crop rotations D- Field windbreaks E- Using mulching F- Using organic fertilizer A- conservation tillage Conservation tillage method (Plate, 43) is Improved soil and water quality by adding organic matter as crop residue decomposes; this creates an open soil structure that lead to the following: Lets water in more easily -Reducing runoff Conserves water by reducing evaporation at the soil surface Optimizes soil moisture Enhancing crop growth in dry periods or on droughty soils Plate (43) : Conservation tillage method B- Cover crops Cover crops are grasses, legumes or forbs planted to provide seasonal soil cover on cropland when the soil would otherwise be bare i.e., before the crop emerges in spring or after fall harvest. The advantages of cover crops to the efficient irrigation Improves water and soil quality by adding soil organic matter. This creates an open soil structure which allows water in more easily, reducing runoff. Protects groundwater quality by preventing nitrogen from leaching into the water table. Helps soil retain moisture for use by primary crops. Cover crops on the soil surface lead to reduce evaporation. C- Conservation crop rotations Conservation crop rotation (Plate, 44) is a system for growing several different crops in planned succession on the same field, including at least one soil-conserving crop such as perennial hay. Including a soil-conserving crop in the rotation reduces the risk of soil erosion and runoff to nearby waters. 6 D- Field windbreaks Field windbreaks are linear plantings of trees/shrubs designed to reduce wind speed in open fields, preventing soil erosion and protecting adjacent crops from wind damage. The advantages of field windbreaks to the efficient irrigation: -Reduces soil erosion from wind and protects water -Increase water use efficiency due to micro-climate changes in temperature and humidity Improves irrigation efficiency. Plate (44): Using of cover crops for planting cabbage to increase water-use efficiency E- Using mulching The use of mulches in agriculture should be standard practice. Researchers from many agricultural experiment stations and private sector of Agriculture have shown striking benefits from mulch applications on irrigation efficiency. The uses of mulches have benefits as follow: •Mulches conserve moisture by reducing the amount of soil water lost through evaporation. Therefore, mulching can reduce the irrigation requirements of plants by up to 70%, mainly by reducing evaporation of water from exposed soil surfaces (Abu-Awwad, A.M. ,1998 and 1999). •Mulches help maintain a uniform soil temperature. They act as insulators, keeping the soil warmer during cool weather and cooler during the warm months of the year which reduces water loss and reduces plant stress. •Mulches minimize soil erosion and compaction from heavy rains and aid in water penetration. 7 •Mulches help with weed problems that lead to not seed weed germination and will not compete the plants on water irrigation. •Mulching helps hold water and reduce leaching loss, and improves the drought resistance of plants. This is a significant benefit in non-irrigated areas. Organic mulch materials 1) Buckwheat hulls: This material is fine textured and may blow around if used in windy places. 2) Compost: An excellent mulch and soil conditioner that you can make at home by composting various types of yard wastes such as grass clippings leaves, and plant tops from vegetables and flowers. 3) Hay (leguminous): Used mostly in farm gardens since the material is more likely to be available. No additional nitrogen is required. 4) Manure: Makes excellent mulch for use if partially decomposed. Aerate this mulch before using to reduce the heat of decomposition. 5) Peanut hulls: Excellent attractive mulch that can be obtained in garden centers located near peanut processing areas. 6) Sawdust: A very common mulch in areas where readily available. Its decomposition will cause a nitrogen deficiency unless fertilizer is applied regularly. When available, aged sawdust is preferable to fresh sawdust. 7) Straw: Used for winter protection and as a summer mulch in vegetable gardens. It is highly inflammable and should not be used in high traffic areas. F- Using organic fertilizer Using composted soil conditioners improves soil structure, water infiltration, and water holding capacity of the soil. Turf grown with the application of composted soil conditioner can require up to 30% less water. This can increase root penetration, resulting in deeper root systems that explore a larger soil area for moisture and nutrients, reducing deep drainage and irrigation requirements (US Composting Council, 1996). - In sandy soils, composted soil conditioners improve water retention and lateral root distribution in the soil, improving plant access to soil water, and reducing deep drainage and irrigation requirements. Composted soil conditioners are incorporated into the topsoil, commonly before planting, to Improve soil structure and water holding capacity. 5- Economic considerations. The cash return per unit of yield is central to improving efficiency. Therefore, the economic component of the crop must be considered. Crop productivity per unit area of land and water consumption per unit of yield must be taken into account. Maximum cash return per unit volume of water in a given area is important in crop selection. 6- Social and political factors. They condition whether or not to give priority to increasing water-use efficiency in crop production in a given area. 8 Improving water-use efficiency To maximize crop water-use efficiency, it is necessary both to conserve water and to promote maximal growth as follow: Conservation of water Reduce conveyance losses by lining channels or, preferably, by using closed conduits. Reduce direct evaporation during irrigation by avoiding midday sprinkling. Minimize foliar interception by under-canopy, rather than by overhead sprinkling. Reduce runoff and percolation losses due to over irrigation. Reduce evaporation from bare soil by mulching and by keeping the inter-row strips dry. Reduce transpiration by weeds, keeping the inter-row strips dry and applying weed control measures where needed. Use of organic fertilizers such as composted and soil conditioners. These have been shown to improve the efficiency of water use by reducing evaporation, improving water infiltration and storage, and reducing deep drainage. Use of mulching that increases the water-use efficiency. Enhancement of crop growth • Select most suitable and high-yielding crops for the region which well adapted to the local soil and climate. • Use optimal timing for planting and harvesting. • Use optimal tillage (avoid excessive cultivation). • Use appropriate insect, parasite and disease control. • Apply manures and green manures where possible and fertilize effectively (preferably by injecting the necessary nutrients into the irrigation water). Practice soil conservation for long-term sustainability. Avoid progressive salinization by monitoring water-table elevation and early signs of salt accumulation, and by appropriate drainage. Irrigate at high frequency and in the exact amounts needed to prevent water deficits, taking account of weather conditions and crop growth stage. Poor irrigation efficiency can be caused by several things: Low irrigation efficiency can be attributed to water mismanagement, in addition to technical problems of conveyance, distribution or on-farm application, as well as poor maintenance of irrigation structures as detailed in the following points: • Not stopping the flow of water to the field when the amount of water needed has been delivered • Not knowing the exact quantity of water (head) flowing from the water source to the field. • Not knowing the soil moisture level at the time of irrigation • Not knowing the water holding capacity of the soils being irrigated • Not applying water based on the intake characteristics of the soil 9 • Not knowing the daily water use requirements of the crops being grown • Not using the proper set sizes for the available head of water • Non-uniform slopes which cause poor water distribution across the field • Excessive slopes which creates high runoff losses Water-use efficiency of greenhouse crops in Egypt Greenhouses can easily double the water-use efficiency of vegetable crops as crop water requirements are easily managed under protected cultivation systems. Therefore, Water-use efficiency values of greenhouse crops are generally much higher than for open field crops in Egypt, due to the low water use and particularly to the high economic value of vegetable crops grown out of season. Water-use efficiency will vary due to crop season (autumn, winter, spring and summer) grown in greenhouse. In greenhouse vegetable crops, the irrigation water-use efficiency (kg m-3, Water-use efficiency), expressed as the ratio between marketable crop production and total crop irrigation supply, is higher than in open field crops due to the low evaporative demand inside the greenhouse that reduces water requirements and the higher productivity of greenhouse-grown crops. Water-use efficiency of greenhouse crops was increased under the following conditions: • improved greenhouse structure • increased length of growing season • Recirculation of nutrients in substrate-grown crops • Use the environment control (Heating, cooling, ventilation) inside the greenhouse. GAP recommendations 10 Using water more efficiently can result in significant cost savings and environmental benefits. Thus, water productivity might be measured by the volume of water taken into a plant to produce a unit of the output. The major causes for reduced irrigation efficiency are drainage of excess irrigation water to soil layers deeper than the depth of active roots. Leakage of irrigation water to deep soil layers could result in pollution of the water table. water efficiently is depend on soil type, moisture conditions before irrigation, depth to groundwater, the crop being grown, management practices, and quality of irrigation water. Water delivery systems, irrigation systems, crop shape and morphology, climatic factors and management are the major factors in determining water-use efficiency. To maximize crop water-use efficiency, it is necessary both to conserve water and to promote maximal growth. • Water-use efficiency of greenhouse crops can be increased by improving greenhouse structure, increasing length of growing season, recirculation of nutrients in substrate-grown crops and using the environment control (Heating, cooling, ventilation) inside the greenhouse. References Abu-Awwad, A.M. (1998). Effect of mulch and irrigation water amounts on soil evaporation and transportation. J. Agron. Crop Sci. 181:55-59.1. Abu-Awwad, A.M. (1999). Irrigation water management for efficient use in mulched onion. J. Agron. Crop Sci. 183:1-7. Abu-Zeid, M.(1979). On-farm water management improvement programs; in: Water management for arid lands in developing countries, edited by Biswas, A. e. a.; Pergamon Press, Oxford, UK. Allen R.G., Pereira L.S., Raes D. and Smith M. (1998). Crop evapotranspiration: guidelines for computing crop water requirements. FAO Irrigation and Drainage paper No. 56. Rome. British Columbia (2006). Water Conservation Fact Sheet. Ministry of Agriculture and Lands. Order No. 577.100-2 Revised: May 2006 Campbell-Clause, J., (1994). Irrigating table grapes in Carnarvon. Farmnote No. 48/94, Agriculture Western Australia. Castilla, N. and Hernández, J. 2005. The plastic greenhouse industry of Spain. Chron. Hort., 45(3): 15–20. Colorado State University Cooperative Extension (1994). Best Management Practices For Irrigation Management (Bulletin). DACOM, the Soil Company (2008). Pilot Project On-Farm Irrigation Management Improvement Egypt. WaterWatch company – Generaal Foulkesweg 28 – 6703 BS – Wageningen – the Netherlands – www.waterwatch.nl Doorenbos, J., and Pruitt, W. O. (1977). Crop water requirements. Irrigation and Drainage Paper No. 24, (rev.) FAO, Rome. Dukes, M.D.; L. Zotarelli, G.D. Liu, and E.H. Simonne (2012). Principles and Practices of Irrigation Management for Vegetables. UF/IFAS Extension, University of Florida. Fernández, M.D., Bonachela, S., Orgaz F., Thompson, R.B., López, J.C., Granados, M.R., Gallardo, M. & Fereres, E. (2011). Erratum to: Measurement and estimation of plastic greenhouse reference evapotranspiration in a Mediterranean climate. Irrig. Sci., 29: 91–92. Fernández, M.D., Bonachela, S., Orgaz, F., Thompson, R.B., López, J.C., Granados, M.R., Gallardo, M. & Fereres, E. (2010). Measurement and estimation of plastic greenhouse reference evapotranspiration in a Mediterranean climate. Irrig. Sci., 28: 497–509. 11 FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS (FAO), (1998). Guide to efficient plant nutrition management. Land and water development division, FAO, Rome. FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS (FAO), (1988). Irrigation water management, Training manuals, Book. FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS (FAO), 2011. Country pasture/forage resource profiles. Egypt. FAO, Rome, Italy. FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS (2013). Good Agricultural Practices for greenhouse vegetable crops. Principles for Mediterranean climate areas. Food and Agriculture Organization of the United Nations (FAO),/Unesco, 1973 Irrigation, Drainage and Salinity. An International Sourcebook. Paris, Unesco/Hutchinson (Publishers), London. 510 p. Gratton, S.R. and J. Oster (1992). Water quality guidelines for trees and vines. Drought Tip 9238, California Department of Water Resources, LAWR Department-University of California, USDA Drought Response Office, and USDA Soil Conservation Service. ICARDA (2011). Water and Agriculture in Egypt, Technical paper based on the EgyptAustralia-ICARDA Workshop on “On-farm Water-use Efficiency” Cairo-Egypt. Izuno, F (1997). Principles of on-farm water management; Agricultural and Biological Engineering Department, Florida Cooperative Extension Service, University of Florida, Institute of Food and Agricultural Sciences (UF/IFAS); http://edis.ifas.ufl.edu/AE099. Jenny Jobling, J, G. Rogers, A. Anderson, A. Vicic (2008). Managing Water for Yield and Profit “A training guide for Irrigators in the Australian Vegetable Industry”. HAL project VG06136 “Water Use Efficiency Maas E.V. 1984 Salt tolerance of plants. In: The Handbook of Plant Science in Agriculture. B.R. Christie (ed). CRC Press, Boca Raton, Florida. McDonald RC, Isbell RF, Speight JG, Walker J, Hopkins MS (1998) Australian Soil and Land Survey Field Handbook. (Australian Collaborative Land Evaluation Program: Canberra). Michigan State University’s (1999). Fruit Crop Advisory Team Alert Vol. 14, No. 5, May 11, Möller, M. & Assouline, S. 2007. Effects of a shading screen on microclimate and crop water requirements. Irrig. Sci., 25: 171–181. 12 Orgaz, F., Fernández, M.D., Bonachela, S., Gallardo, M. & Fereres, E. (2005). Evapotranspiration of horticultural crops in an unheated plastic greenhouse. Agric. Water Manage., 72: 81–96. Pire C., R., E. Tortolero, Y. de Fréitez, and M.L. de Pire, 1988. El riego de la vid (Vitis vinifera L.) en el Tocuyo, estado Lara. I. Relaciones sueloagua. Agronomía Tropical. 38(1-3): 135-154 Ramsey, H. (2007). Calculating readily available water. Farm Note 198. Dept. of Agriculture and Food. Government of Western Australia. p. 1-3. Sanders, D.C., (1997). Vegetable crop irrigation. Horticulture Information Leaflet 33-E, North Carolina Cooperative Extension Service, North Carolina Sate University. South Australian Research and Development Apricots. SARDI, Adelaide, South Australia. Institute (1996). SARDI Horticulture- US Composting Council (1996). Benefits of Compost. The Field Guide to Compost Use. 13
© Copyright 2026 Paperzz