Abstract

AbstractA computer program for simulating cation‐exchange reactions in soil was developed and used for simulating the determination of exchangeable acidity with 1 M KCl and of hydrolytic acidity with 1 M NaOAc. The acidification process resulting from extraction of an initially base‐saturated soil with a dilute solution of an acid having various dissociation constant may also be simulated. From the calculated pH‐base saturation relationships for assumed K‐H exchange coefficent (KK‐H) varying from 1 × 101 to 1 × 10−6, it is noted that for KK‐H values of 1 × 10−n, the inflection point of the pH‐base saturation curve is at the pH value of n. Thus, the permanent charge sites of mineral soils appeared to have a KK‐H value of 1 × 10−1 and greater, while for the pH‐dependent charge sites the KK‐H values are smaller than 1 × 10−2. The acidity extracted by 1 M KCl solution corresponded to the H+ on the permanent charge sites, with KK‐H values of 1 × 10−2 and greater, but it may also include some portions of H+ bound on exchange sites with KK‐H values smaller than 1 × 10−2. Exchangeable H+ from sites with KK‐H smaller than 1 × 10−5 were practically not displaced by 1 M KCl solution. The use of 1 M NaOAc instead of Kcl could quantitatively displace the H+ held on the sites with KNa‐H values >1 × 10−3 by a single extraction, while those of 1 × 10−6 and greater may be displaced by repeated extractions. Calculations with KNa‐H values of 1 × 10−7 did not converge, but available soil data indicate that the pH‐dependent sites of soils have KNa‐H values in the order of 1 × 10−7. Use of a dilute acid solution in place of KCl or NaOAc solution simulates the acidification process of acid precipitations.

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