Spring, 1992 (v4n3)

Citrus Herbicides & Groundwater Quality

By Chuck Ingles, SAREP

(Editor's Note: This is the second part of a two-part series on citrus production and groundwater contamination. Part 1 appeared in Sustainable Agriculture News, Vol.4, No.2, Winter 1992. Information from this series will be included in a SAREP citrus publication due out at the end of 1992.)

For citrus growers, prevention of nitrate leaching can be a far more difficult task than that of herbicide leaching: farmers cannot simply stop applying nitrogen (N). The problem is a concern to both conventional and organic growers, since nitrate can leach below the root zone from organic and synthetic fertilizers. Several management practices exist to reduce the potential for nitrate leaching.

Determine N supply and demand. Citrus trees typically require about 100 to 150 pounds of N/acre/year, however lemons can require up to double this amount. Annual leaf analyses can indicate the need for less N; fertilizing on the basis of leaf analysis can result in less nitrate leaching while maintaining fruit quality and yield. Equally important, and often overlooked, is the need to sample irrigation water to determine nitrate content, and to reduce N fertilizer use accordingly.

Time of application. The time of maximum N uptake is during the summer. Because flowering and fruit set require high levels of N in the tree, however, N must be made available to the trees shortly before flowering. Fertilizer is usually applied in late winter and early spring, with split soil applications frequently made in February, March, and April. Some growers, however, apply N fertilizer in the fall. This practice stems from the tradition of applying raw manure in the fall so that winter rains can move nitrate into the root zone. A substantial portion of fall-applied N will leach beyond the root zone as a result of winter rainfall, water applied during frosts to warm the orchard, and reduced root N uptake during the winter.

Choice of materials. The choice of N fertilizer can affect the accumulation and leaching of nitrate. Synthetic nitrogen fertilizers supply N in the form of nitrate, ammonium, and/or urea (which is rapidly converted to ammonium in the soil). Some ammonium is taken up by the plants directly and some is adsorbed onto soil particles, thus delaying N loss through leaching. However, most of the ammonium is converted to nitrate within a relatively short period of time. How much nitrate leaches below the root zone depends on the rate and frequency of application as well as the depth to which irrigation water percolates.

Bulky organic materials such as manure and compost release N more slowly as the organic matter decomposes. However, excessive applications of manure can also result in leaching losses. Finished compost supplies a more stable and slow-release form of N than conventional fertilizers or manure. Compost applications can therefore be made at any time of the year without significant loss to leaching. Compost also provides the soil with humus, a stable form of organic matter, which is invaluable in nutrient cycling. Because of low N content and expense, most growers who use compost also use supplements of chemical fertilizers and/or cover crops. Slow-release synthetic fertilizers are also available; these can reduce the nitrate pollution potential. A significant problem with slow-release fertilizers, including organic materials, is that a continuous N supply can cause fruit quality problems such as regreening. A moderate application of compost, together with spring applications of soluble materials, may strike a balance between maintaining fruit quality and yields, reducing nitrate leaching, and improving soil quality.

Cover crops can be useful in converting mobile soil nitrate into immobile plant organic N. Winter annual cover crops can utilize rainfall for growth and remove excess soil nitrate during winter, when nitrate leaching potential is the greatest. (For more information on cover cropping in citrus, see UC SAREP's Components, Vol.2, No.3, Summer 199].)

Foliar applications of urea result in vastly reduced nitrate pollution potential compared to soil-applied N, and yield and fruit quality can be maintained or enhanced. A practical fertilization strategy might be to supply half the N to the foliage (two to four sprays) and half through soil applications. Foliar sprays may be applied in the winter and early spring, but researchers at UC Riverside have recently shown that January and February applications may lead to the highest yields. Organic materials such as fish emulsion may be useful as foliar sprays, although they contain less N and are far more expensive than urea. The practice of applying N to the foliage is not universally accepted. Some growers believe that the nutrient pathway is and should be through the roots.

"Fertigation." The application of water-soluble fertilizers through the irrigation system is called "fertigation." If the depth of wetting can be limited as well, fertigation can provide a "steady state" of N availability only when N is needed by the tree, with greatly reduced potential for nitrate leaching. Fertigation can be used in small amounts up to 15 times through the spring. (Often only three to five applications are made.)

Growers of all crops are being challenged to produce safe, inexpensive food without damaging the soil, the air, or the water. They must also maintain their economic stability. In the long term, however, economic stability is dependent on environmental and social well-being. Citrus growers are confronted with numerous obstacles to sustainability. Yet many practices have been developed to reduce the environmental impacts. Should we wait until regulations force us to be nonpolluting?

Thanks go to John Freeman, Jim Gorden, Ralph Jurgens, Rob McGill, Neil O'Connell, John Pehrson and others for information used in these articles.

References

Embleton, T.W., W.W. Jones, and R.G. Platt. 1983. Leaf analysis as a guide to citrus fertilization. Soil and Plant Tissue Testing in California. Univ. of Calif., Division of Agric. Sci., Bull. 1879, pp.8-13.

Embleton, T.W, M. Matsumura, L.H. Stolzy, D.A. Devitt, W.W Jones, R. ElMotaium, and L.L. Summers. 1986. Citrus nitrogen fertilizer management, groundwater pollution, soil salinity and nitrogen balance. Applied Agric. Res., 1(1):57-64.

Lovatt, C. 1991. Maximizing the "growth regulator" properties of foliar-applied urea to increase flowering, fruit set and yield (without a reduction in fruit size) in the "Washington" navel orange. Progress Report to the Citrus Research Board and UC Citrus Research Advisory Commirtee.

Pehrson, J. 1985. Irrigation scheduling in San Joaquin citrus. Citrog. 70:183-84,188.

Pehrson, J. 1988. Vegetation management in citrus groves. Citrog. 74:15-18,20.

Pickett, C.R., L.S. Hawkins, J.E. Pehrson, and N.V. O'Connell. 1990. Herbicide use in citrus production and ground water contamination in Tulare County. Calif. Dept. of Food & Agric. pub. no. PM 90-1.


 
    

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