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Distinguishing Boron Desorption from Mineral Dissolution in Arid‐Zone Soils
Author(s) -
Goldberg Sabine,
Suarez Donald L.
Publication year - 2011
Publication title -
soil science society of america journal
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.836
H-Index - 168
eISSN - 1435-0661
pISSN - 0361-5995
DOI - 10.2136/sssaj2010.0439
Subject(s) - dissolution , chemistry , desorption , sorption , soil water , adsorption , extraction (chemistry) , mineral , boron , silicate minerals , silicate , mineralogy , environmental chemistry , chromatography , geology , soil science , organic chemistry
Boron release from six arid‐zone soil samples from the San Joaquin Valley of California was investigated as a function of reaction time, solution pH, and suspension density. A multiple batch extraction experiment was performed for 362 d to distinguish B desorption from B released from mineral dissolution. Amounts of B released decreased rapidly and reached a low constant value after about 6 mo of reaction time. Slopes of the B release curves for the last eight extractions approached zero (constant release rate), indicating that this B release was from mineral dissolution. We also did a shorter term experiment that contained added Mg and silicate in solution. These experiments were conducted to evaluate the contribution of B release from dissolution of B‐containing Mg silicate minerals. We determined that most of the B released from the soils can be attributed to release from sorption sites rather than resulting from dissolution of B‐containing Mg silicates. Various B soil tests were evaluated for their ability to measure native extractable adsorbed B. The diethylenetriaminepentaacetic acid (DTPA)–sorbitol extract was the best measure of available adsorbed B but still only extracted 48% of the amount of B released in the long‐term experiment. The greatest amount of B was extracted at the lowest suspension density for DTPA–sorbitol (92%) and phosphate buffer pH 6.6 (95%). These extractants are recommended for quantifying native extractable adsorbed B, which must be considered in application of chemical speciation transport models to describe B movement in soils. Incorporation of our results will allow improved predictions of soil solution B concentrations under diverse agricultural and environmental conditions.