Selected farmlands in southern Baja California, Mexico, were surveyed to determine the levels and the causes of salinization/sodication in irrigated agricultural soil. The salt dynamics observed in profiles differed from farm to farm. Low EC and high pH levels were observed in the profiles of sandy fields, because the salt composition of these soils can easily change when salts are leached by irrigation water that contains carbonates of sodium. On the other hand, high levels of salinity and sodicity were observed in the soils of clayey fields. Soil salinization/sodication is complexly interrelated with soil characteristics, the amount and composition of salts in the soil, the quantity and quality of irrigation water applied, and the irrigation methods used. Our findings indicate that irrigation water in Baja California should be supplied at a rate that is sufficient to meet crop requirements without exacerbating salt accumulation. 1. Introduction In arid regions, desertification is mainly caused by human activity [1, 2]. Attempts to grow crops in arid inadequate irrigated areas have mainly resulted in the salinization and/or sodication of the soil. Because the irrigation of agricultural lands in arid regions has not yet become a widespread practices a relatively small area has been degraded compared to the areas used for grazing or those in which rain-fed agriculture is carried out. However, irrigation tends to increase productivity in the short term, and the need to produce food for an increasing population might result in the conversion of grazed, rain-fed, and even virgin lands to irrigated fields [3]. Furthermore, the reclamation of salt-affected land that has been irrigated for agricultural purposes has become increasingly important. Reducing the severity and extent of soil salinity is primarily a matter of soil and water management. Good water management involves both preventing water received in the recharge areas from percolating into groundwater and maintaining the water table of the discharge areas at low, safe levels. The most common approach to salinity management is to maintain a prescribed leaching requirement. However, this approach is ineffective when the irrigation water contains significant levels of sodium, carbonates, and bicarbonates. In addition, the surface drainage capacity of these arid soils is usually poor. The Baja California peninsula was once a part of the North American Plate, of which mainland Mexico remains a part. In southern Baja California, Pliocene to early Quaternary sedimentary formations were deposited
References
[1]
UNEP, “Global Deserts Outlook,” p. 168, 2006.
[2]
J. F. Reynolds, D. M. Stafford Smith, E. F. Lambin et al., “Ecology: global desertification: building a science for dryland development,” Science, vol. 316, no. 5826, pp. 847–851, 2007.
[3]
S. Rost, D. Gerten, A. Bondeau, W. Lucht, J. Rohwer, and S. Schaphoff, “Agricultural green and blue water consumption and its influence on the global water system,” Water Resources Research, vol. 44, no. 9, Article ID W09405, 2008.
[4]
L. Geoffroy and J. Pronost, “Late pliocene to early quaternary extensional detachment in the La Paz-El Cabo area (Baja California Sur, Mexico): implications on the opening of the Gulf of California and the mechanics of oblique rifting,” Terra Nova, vol. 22, no. 1, pp. 64–69, 2010.
[5]
S. H. Bullock, “Seasonality, spatial coherence and history of precipitation in a desert region of the Baja California peninsula,” Journal of Arid Environments, vol. 53, no. 2, pp. 169–182, 2003.
[6]
Soil Survey Staff, Keys to Soil Taxonomy, USDA-NRCS. U.S. Gov. Print Office, Washington, DC, USA, 11th edition, 2010.
[7]
IUSS Working Group WRB, “Work reference base for soil resources 2006,” World Soil Resources Reports 103, FAO, Rome, Italy, 2006.
[8]
S. R. Vieira, D. R. Nielsen, and J. W. Biggar, “Spatial variability of field-measured infiltration rate,” Soil Science Society of America Journal, vol. 45, no. 6, pp. 1040–1048, 1981.
[9]
B. B. Trangmar, R. S. Yost, and G. Uehara, “Application of geostatistics to spatial studies of soil properties,” Advances in Agronomy, vol. 38, pp. 45–94, 1985.
[10]
G. Bourgault, A. G. Journel, J. D. Rhoades, D. L. Corwin, and S. M. Lesch, “Geostatistical analysis of a soil salinity data set,” Advances in Agronomy, vol. 58, pp. 241–292, 1996.
[11]
P. Goovaerts, “Geostatistics in soil science: state-of-the-art and perspectives,” Geoderma, vol. 89, no. 1-2, pp. 1–45, 1999.
[12]
G. W. Gee and J. W. Bauder, “Particle-size analysis,” in Methods of Soil Analysis—Part 1: Physical and Mineralogical Methods, A. Klute, Ed., pp. 383–411, American Society of Agronomy and Soil Science Society of America, Madison, Wis, USA, 1986.
[13]
G. W. Gee and D. Orr, Methods of Soil Analysis. Part 4 Physical Methods, vol. 5 of Soil Science Society of America Book Series, Soil Science Society of America, 2002.
[14]
S. R. Olsen, C. V. Cole, F. S. Watanabe, and L. A. Dean, Estimation of available phosphorus in soils by extraction with sodium carbonate, USDA Department circular 939. Government Printing Office, Washington, DC, USA, 1954.
[15]
W. L. Lindsay and W. A. Norvell, “Development of a DTPA soil test for zinc, iron, manganese, and copper,” Soil Science Society of American Journal, vol. 42, pp. 421–428, 1978.
[16]
US Salinity Laboratory Staff, “Diagnosis and improvement of saline and alkali soils,” in US Department of Agricultural Hand Book, vol. 60, p. 147, US Department of Agricultural, 1954.
[17]
H. L. Bohn, B. L. McNeal, and G. A. O'Connor, Soil Chemistry, Wiley Interscience, New York, NY, USA, 2nd edition, 1985.