United States Environmental Protection Agency Robert S. Kerr Environmental Research Laboratory Ada, OK 74820 Bft Research and Development EPA-600/S2-82-073 Nov. 1982 Project Summary Minimizing Salt in Return Flow Through Irrigation Management Because irrigation is the largest user of water, irrigation management can have a significant impact on water quality. This report describes a research project designed to demon- strate that, through improved irrigation water management, it often is possible to reduce the salt load in irrigation return flow and, thereby, the concentration of dissolved solids in downstream reaches of a river system. The study was undertaken with a view to reducing the salinity of the Colorado River and, more specifically to address alternative means of meeting the U.S. obligation to deliver to Mexico Colorado River water of specified quality and quantity. Other concurrent studies are underway in Arizona by the U.S. Bureau of Reclamation, the Agricultural Research Service and the University of Arizona; an extensive program of planning and technical assistance is being conducted by the Soil Conservation Service. These studies complemented similar studies by various entities in the Upper Colorado Basin. Together, these studies highlight the potential of enhancing water resource use by stressing measures to increase on-farm water management. Two field experiments were conducted in the Wellton-Mohawk Irrigation and Drainage District of southwest Arizona to investigate the potential of reducing the salt load in irrigation return flow by decreased leaching. Three leaching treatments of 5, 10, and 20 percent, replicated nine times for citrus and five times for alfalfa, were established and compared with conventional flood irrigation management. The annual evapotranspiration of mature Valencia orange trees was found to be about 1470 mm. The leaching fractions, determined indirectly by several techniques, were close to those intended. The leaching fraction computed for the border flood check was 0.47. The leaching fractions in the alfalfa experiment were not exactly as planned. Based on several independent measurement techniques, the actual leaching fractions achieved were 0.06, 0.10, and 0.14; near 0.11 for the flood check. Annual evapotranspiration was estimated to be 1930 mm. After reducing the frequency and increasing the amount of water applied with each irrigation, no differences in alfalfa yield were noted among treatments or with the flood check. Both the citrus and the alfalfa experiments verified that Water applications could be reduced substantially below average commercial practice without loss of crop yield. Thus, irrigation return flow and its inherent salt load can be reduced consistent with the leaching requirement for the crop and irrigation water in question. This Project Summary was devel- oped by EPA's Robert S. Kerr Environ- mental Research Laboratory, Ada, OK. to announce key findings of the research project that is fully docu- mented in a separate report of the same title (see Project Report ordering information at back). ------- Figure 1. Location of citrus and alfalfa minimum leaching experiments in southwestern Arizona. Introduction The salt load of the Colorado River constitutes a major problem. Unless corrective actions are taken, the current average salt concentration of about 850 mg L-' in the lower reaches of the river is expected to increase substa ntial- ly as further water development takes place. Such an increase would have serious economic consequences for the seven states adjoining the river and for the Republic of Mexico. Return flow from irrigated lands has been identified by the U.S. Environmental Protection Agency (1971) as a major contributor of salts. Research at the U.S. Salinity Laboratory lead to the conclusion that often the amount of salt in drainage water from irrigated agriculture can be reduced substantially by modifying irrigation management. This project was initiated to evaluate the pertinence of this conclusion with particular reference to the Wellton-Mohawk Irrigation and Drainage District in southwestern Arizona, a district where improved irrigation management is a potential alternative to construction of a desalting complex to alleviate the adverse effects of returning brackish drainage water to the river. The primary objective of these field studies was to determine the feasibility of reducing the salt load in drainage water by reduced leaching while maintaining crop yield. Achieving this objective implied increasing irrigation efficiency, using uniform and frequent irrigations with minimal leaching consistent with crop needs; and taking advantage of the reductions in mineral dissolution or increases in salt precipi- tation as the leaching fraction is reduced. Additional objectives were to determine the components of the water and salt balance under the improved irrigation regimes and to determine the requirements of an irrigation system for these purposes. One experiment was installed in December 1973 with citrus on coarse- textured mesa soil and continued through fruit harvest in the spring 1979; the second was started in September 1974 with alfalfa on medium-textured valley soil and discontinued in October 1978. Concurrent research, by other groups and by the U.S. Salinity Laboratory, in the same district and in Colorado, addressed corollary issues or parallel questions under different cli- matic and geological circumstances. Thus, a concerted effort was mour during the 1970s to address the rela between agricultural water mana ment and the salinity of the Color River. The final report describes the experiments mentioned, reports results and interprets the findings. all objectives were fully attained, but project succeeded in verifying the bŁ premise. It also provided use estimates of the potential changes the water and salt balances that co realistically be achieved. Results and Conclusions To investigate the potential reducing the salt load in return fl from irrigated areas by redut leaching, two field projects w< established near Tacna, Arizona, in 1 Wellton-Mohawk Irrigation and Dra age District (Figure 1). Colorado Ri< water with about 944 mg L"1 total d solved solids (determined analytica equivalent to 859 mg L"1 TDS by residi was used for irrigation. Citrus In one project, trickle irrigation w used to control the amount of wai applied to each tree in a matt ------- Valencia orange orchard located on Dateland fine sandy loam soil. Three treatments replicated nine times, intended to result in leaching fractions of 0.05, 0.10, and 0.20, were established and compared with conventional borderflood irrigation. The trickle irrigated plots were irrigated several times a day with a depth of 1.7 mm per irrigation. The irrigation regime was imposed in December 1973 and maintained until fruit harvest in April 1979. The annual evapotranspiration of the mature citrus trees was found to be close to 1470 mm, a value somewhat higher than indicated in earlier reports. The actual leaching fractions obtained, in contrast to those planned, could not be measured directly. They were estimated from soil salinity, soil water chloride concentration, the salinity of the percolate in buried extractors, and from water balance data. A rather wide range of estimates resulted, but they were consistent with the conclusions that the leaching fractions obtained, averaged over time, were very nearly those planned. In the first four years, no effect of irrigation treatment was observed on fruit yield or quality. In the last year, a low yield year for all treatments, the yield of the five percent leaching treatment was substantially lower than that of the others. Unfortunately, an unambiguous conclusion on the effect of low leaching levels on citrus yield would have required continuing the experiment for additional years. The data at hand suggest that the fifth year yield depression at low leaching was a real treatment effect. It is possible, but not at all certain, that the capacity of the tree trunks to store chloride delays the negative effect on fruit yield several years after the roots are exposed to higher salinity levels. With some uncertainty, we conclude that the leaching requirement for Valencia oranges irrigated with Colorado River water exceeds five percent and is less than 20 percent. Foliar analysis indicated that nitrogen applications, in the form of foliar urea sprays of 690 g per tree per year, somewhat exceeded the nutritional requirement. Compared with University of Arizona results in an adjacent orchard that 340 g was borderline, a reasonable conclusion would be that 0.5 kg per tree is an adequate level for nitrogen fertilization. The spatial heterogeneity, the multidimensional nature of both the root- and flow-systems, and the temporal cycling prevented the quantitative use of soil salinity data in determining a clear partitioning of the salt in depth and time. However, the data in general were not at variance with expectations. It can be concluded unequivocally that insufficient time elapsed to establish chemical equilibrium in the soil solution with respect to Na, Ca, and Mg, and thus the sodium-adsorption-ratio. A detailed study of water and salt transport through the root zone was made for one set of nine trees by interruption of the high frequency irrigation for extended periods. Of the water uptake below the surface area wet by the irrigation system (less than half the total surface area), about 80 percent took place above a depth of 0.60 m. Significant uptake was noted outside the wetted area, with water provided by lateral flow. In summer, serious stress developed in the trees when irrigation was suspended more than 30 days; in winter, interruption up to 60 days showed no ill effects. These results indicate that even in extremely hot climates, citrus under frequent irrigation is not particularly vulnerable to temporary breakdowns of the irrigation system. They also suggest that, if water supplies are limited, it may be practical to practice deficit irrigation in the season of peak evaporative demand, depending on water stored in the soil profile that is replenished in the cool season; adequate fruit yield data were not obtained to verify this suggestion. Root length distribution data showed a similar pattern to that obtained from water, hydraulic head and salt measurements, with substantially more roots at shallow depths (<0.3 m) under the wetted area, and with 75 percent of the roots above 0.6 m. In the flood irrigated area, root distribution was more uniform with depth and also with distance from the trunk. Alfalfa The second project dealt with irrigation of alfalfa on Indio fine sandy loam soil. About 2 ha of an 8-ha field was divided into 15 plots, providing five replications of three treatments. The treatments imposed were expected to yield leaching fractions of 0.05, 0.10, and 0.20. Irrigations were applied with a moving-boom spray system that originally applied a depth of 6 mm of water per pass; after modification, it applied 70 mm per pass. The remainder of the field was irrigated by level basin flooding, applying about 150 mm per irrigation. Alfalfa was seeded early in October 1974 and replanted in October 1976. The experiment ended in October 1978. The original high frequency irrigation schedule proved incompatible with the other cultural practices. It resulted in excessive compaction and weediness and consequently, in reduced crop yields and poor infiltration. After the irrigation system was modified to accommodate less frequent irrigation, useful results were obtained. As with the citrus, evapotranspira- tion was estimated by a number of computational procedures. The best estimate is 1930 mm yr1. The leaching fractions actually obtained were not exactly as planned. A reasonable estimate of the actual leaching fractions is 0.06, 0.10, and 0.14; for the flood check, it probably was near 0.11. Drainage from the nearby mesa caused relatively high water tables in the alfalfa field part of the time. Hydraulic head data showed that, in the 0.05- and 0.10-leaching fraction treatments, the plants used some water from the water table. No such evidence was found for the 0.20-leaching fraction plots. After replanting, no dif- ferences in alfalfa yield were noted among treatments or between the sprinkler irrigated and the flood irrigated alfalfa. The annual yield was about 22 Mg ha-1. Thus, the leaching requirement, using Colorado River water, is less than five percent. Soil samples showed that the field had been well leached prior to the experiment. After establishing the new regimes, the salinity near the surface face was lower in the flood check than in the sprinkled plots. Soil water chloride data indicated that, in the sprinkled plots, 90 percent of the water was taken up above a depth of 0.6 m. Only 66 percent of the uptake took place above that depth for the flood check. Root density measurements gave a very similar pattern for the sprinkled plots, but we could not distinguish a different pattern for the flood check; this could have been due to the small number of root samples analyzed. The management of the farmer- irrigated flood check with a leaching ------- fraction of slightly over 0.10 illustrates clearly that high irrigation efficiencies can be obtained and are being obtained commercially. In fact, no advantage can be claimed for the sprinkler system for use on alfalfa. The average efficiency for alfalfa estimated by action agency personnel, however, is substantially lower than the 89 percent found here. Thus, even if the controlled leaching plots did not use significantly less water than the flood check, the conclusion still is that, especially with the locally well adapted level basin irrigation system, there is ample opportunity for reductions in water use in the Wellton-Mohawk District. Both the citrus and the alfalfa experi- ments verified that water applications could be reduced substantially below average commercial practice without crop yield reductions. Presumably, the same conclusion could be applied to other crops grown in the area. The consequences of such a reduction, if widely effected, would be several. Reduced water applications would result in reduced deep percolation and thus, in a reduced drainage flow. In the short run, this reduced flow would have the same salt concentration as at present. At steady state, the reduced flow would have a higher salt concentration than the current drainage flow, because of the salt stored in the aquifer. The concentration would be substantially higher than that expected ultimately were the current water bal- ance maintained. Given a set of assumptions, calculations can be made of the changes in salt and water balances per ha for each crop. Suffice it to point out that reducing the drainage flow consistent with the leaching requirement reduces the volume of water required to remove the necessary salt from the system and thus reduces the cost of disposal. By the same amount that the drainage volume is reduced, the amount of water retained in the river for later use is increased. We propose that the results obtained in these experiments provide evidence to support the assertion that Colorado River diversions into the Wellton- Mohawk District and, consequently, average drainage flow, can be reduced sufficiently, without damaging agricultural production, to make questionable the efficiency of alterna- tive means of salvaging the drainage flows. This Project Summary was authored by the U.S. Salinity Laboratory Staff of the U.S. Department of Agriculture, Riverside, CA 92501. James P. Law, Jr., is the EPA Project Officer (see below). The complete report, entitled "Minimizing Salt in Return Flow Through Irrigation Management," (Order No. PB 82-257 445; Cost: $ 16.50, subject to change) will be available only from: National Technical Information Service 5285 Port Royal Road Springfield, VA 22161 Telephone: 703-487-4650 The EPA Project Officer can be contacted at: Robert S. Kerr Environmental Research Laboratory U.S. Environmental Protection Agency P.O. 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