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Although soil reduction often results in P release to soil solutions, many researchers have observed an increased maximum P adsorption ( S max ) following soil reduction. We hypothesized that this result is an experimental artifact caused by exposure of the reduced soils to aerobic conditions and by the use of high P additions, which may result in precipitation. Four semiarid altered wetland soils were incubated under reduced conditions, followed by reoxidation, and their P‐adsorption characteristics were measured under atmospheric and N 2 –atmosphere conditions. During the reductive incubation, soluble P and Fe concentrations increased. In one of the soils, P and Fe were monitored after reoxidation and both were found to decrease. The reduction–reoxidation cycle has led to increased S max values. Under an N 2 atmosphere, the equilibrium P concentrations at zero adsorption (EPC 0 ) of all soils were higher than those determined under atmospheric conditions, whereas no significant changes were observed in S max values. Oversaturation of the equilibrating solutions with respect to P minerals suggested P precipitation and overestimation of S max at high added P concentrations under both aerobic and N 2 –atmosphere conditions. We conclude that aerobic batch experiments of reduced soils are affected by P adsorption to newly in‐tube‐formed ferric oxides. In accordance, we stress the importance of the EPC 0 rather than the S max as an informative measure of P adsorption, and the need for using low‐P experiments and maintaining anaerobic conditions in evaluating P adsorption of reduced soils.
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Brand-Klibanski et al. (2007) studied this question.
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