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The spring season of 2001 has seen several - usually minor - diseases in lettuce, causing some major crop losses. Apparently, the heavy rain that hit the Central Coast in early April provided ideal conditions for the development of these pathogens.
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![]() NITROGEN MANAGEMENTTim Hartz, Vegetable Crops Extension Specialist at UC Davis
Brassica crops are heavy feeders, on average taking up approximately 200-220 lbs. N per acre by first harvest. Average Salinas Valley N application levels for broccoli and cauliflower are somewhat higher than these amounts, but not radically so. It is tempting to think that fertilization rates and crop requirements are in rough balance, but that is not really so, for several reasons: a) fertilizer is only one source of available N for crop uptake, and b) only about 1/3 of total N uptake is removed from the field in the harvested product; the rest is returned to the soil in the form of crop residue. From a whole-farm nutrient balance standpoint, current levels of fertilization far exceed N removal in the harvest, suggesting that substantial loss of nutrients to the environment is possible. The following discussion will suggest some simple practices that can help reduce fertilizer usage in broccoli and cauliflower production. Crops draw N from several sources: a) fertilizer; b) residual soil nitrate-nitrogen (NO3-N); c) in-season mineralization of soil organic N; and d) NO3-N in irrigation water. Accounting for NO3-N in irrigation water is simple. To calculate how much N you are delivering in the water you apply, multiply the PPM NO3-N in the water by 0.23 to calculate pounds of N per acre inch of water; well water with a NO3-N concentration of 10 PPM contains 2.3 lbs. N/acre inch. Assuming an average irrigation efficiency of 70 percent, that means that 70 percent of this NO3-N could be counted as fertilizer equivalent. As a practical matter, the N contribution of water with NO3-N concentration less than 10 PPM can be ignored. However, wells that are at least 15 PPM make significant N contributions on a seasonal basis, and this contribution should be included in your fertilizer management. In-season mineralization of soil organic matter is also reasonably predictable. Tests we have run on dozens of coastal vegetable soils show that from the time of first side-dressing until harvest approximately 1-2 percent of organic N in the top foot of soil is likely to be mineralized (converted into NO4-N or NO3-N by soil microbes, available for plant uptake). For a sandy, low organic matter soil that may only amount to 30 lbs. N/acre; for a higher organic matter soil (like that common in the Blanco district) it may amount to twice that much. The rate of soil N mineralization can be much higher in the first weeks following the incorporation of vegetable crop residue, but it is typically a month or more before the next crop reaches the stage at which sidedressing is contemplated. Mineralization taking place between crops, as well as residual soil NO3-N carried over from the previous crop can easily be measured by soil testing before sidedressing. Soil testing allows you to estimate the amount of available N already in the root zone; this can help tailor your sidedress decisions to fit field-specific conditions. In sampling more than 100 coastal vegetable fields just prior to the first sidedressing, I have found that soil residual NO3-N varied from near zero to as high as 80 PPM in the top foot of soil; since an acre foot of soil weighs approximately 4,000,000 lbs., that range was equivalent to 0-320 lbs. available N/acre. Clearly, knowing how much residual NO3-N is present can help guide sidedress decisions. Through a series of more than 30 experiments conducted in commercial vegetable fields we have found that any time soil residual NO3-N is above 20 PPM, sidedressing can be delayed without affecting crop growth rate. Furthermore, when soil NO3-N was below the 20 PPM threshold, sidedressing only enough to bring the level up to that threshold worked well. Most growers sidedress broccoli and cauliflower at least twice. By employing pre-sidedress soil nitrate testing (PSNT) before all sidedressings, unnecessary N application can be minimized. PSNT is less useful early in the spring, when winter rains have usually leached most NO3-N from the root zone; chances of finding substantial residual NO3-N levels are slim. However, by May or June significant residual soil NO3-N levels are commonly found. If soil testing at all sidedressings is too labor-intensive for your operation, concentrate on testing prior to the first sidedressing. It is at that time that the biggest sidedress reductions can usually be achieved. Putting the pieces together, N use efficiency can be significantly improved by following these practices:
2. Adjust these general guidelines on a field by field basis, based on the contribution of N from irrigation water, and pre-sidedress soil NO3-N testing, particularly at the first sidedressing. Based on what we have seen with our field trials, the average reduction in fertilizer usage could reach 100 lbs. N/acre per crop for some growers. More detailed information on efficient N management for cool season vegetables is available on the Web site of the UC Vegetable Research and Information Center located at http://www.vric.ucdavis.edu. Source: Vegetables West/May 2001 issue. Reprinted by permission.
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