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UC navies Vegetable Research and Information Center Fertility Management of Dni lrrigated Vegetahbles <br /> v <br /> soils in Florida, an overall irrigation cycle of 45 min (young crop) up to 1.5 h (mature crop) <br /> would be sufficient (assuming today's typical drip tube flow rates) to apply the amount of water <br /> ` required by a tomato crop during any one irrigation cycle (Clark et al., 1990; Smajstrla et al., <br /> 1985). Irrigation cycles>1.5 h for a mature crop on sandy soils run the risk of leaching nutrients <br /> and moving water below the root zone. Longer irrigation cycles can be used effectively on soils <br /> ` with high water-holding capacity. More detail on injection calculations and periods is available <br /> (Clark et al. 1990; Hochmuth and Clark, 1991). It is very important to design the system and <br /> fertilizer injector so that injection and flushing can be achieved in a reasonable amount of time <br /> without running the risk of overwatering the crop simply to apply the fertilizer. <br /> In some systems, fertilizer is injected continuously (concentration injection) so that all irrigation <br /> water applied contains nutrients. This is acceptable as long as no irrigation cycle is so long that <br /> nutrients are leached below the root zone. During rainy periods, a bulk injection of a larger <br /> amount of fertilizer might be needed to fertilize a crop when no water is required. <br /> Water management is integrally linked to fertigation management. Water that moves below the <br /> active crop root zone can carry NO3-N (and, in very sandy soils, K) in substantial quantities. One <br /> cm of leachate at 100 mg NO3-N•liter 1 would contain 10 kg N•ha". Indeed, one of the major <br /> advantages of polyethylene bed mulch (frequently used in conjunction with drip irrigation) is the <br /> reduction of NO3-N leaching with precipitation, but that advantage can be negated by excessive <br /> drip irrigation. Conversely, in some areas well water used for drip irrigation contains a significant <br /> concentration of NO3-N; in regions such as the Salinas Valley of California NO3-N levels of 10-20 <br /> mg•liter 1 are common. Irrigating a crop with a total of 30 cm of water at 15 mg NO3-N•fiter 1 <br /> would add approximately 45 kg N•ha'1. <br /> Nutrient monitoring: <br /> The fertigation scheduling approach outlined above should, in most situations, supply adequate <br /> nutrition; however, monitoring soil and/or plant nutrient status is the essential safeguard to ensure <br /> maximum crop productivity. In conventional production, soil NO3-N testing usually has been <br /> +- limited to preplant sampling; since drip irrigation provides the ability to add N at will, more <br /> extensive NO3-N monitoring is justified. Traditional soil sampling and laboratory analysis offer <br /> the most complete, accurate information, but growers are not likely to go to the effort and <br /> expense of this technique on an ongoing basis through a cropping cycle. <br /> There are several alternative techniques to aid on-farm nitrogen measurement. One approach is <br /> the use of soil solution access tubes, also called suction lysimeters. These devices are simply <br /> porous ceramic cups, similar to tensiometer cups, attached to hollow access tubes. The units are <br /> installed in the field with the ceramic tips in the active root zone. To collect a sample, a vacuum <br /> is applied which draws water from the surrounding soil into the tube. This soil water sample is <br /> collected and analyzed for NO3-N content; the vast majority of mineral N is usually in the nitrate <br /> form <br /> The use of suction lysimetry has serious limitations. There can be large spatial variability; one <br /> portion of a field may vary from another and, since NO3-N moves with the wetting front, there <br /> can be stratification of NO3-N within the bed. This problem can be minimized by using multiple <br /> �„ Page 5 <br />