Abstract

In order to determine the effect of acid precipitation on the movement of Cd and Zn in metal-contaminated systems, Cd- and Zn-amended soil systems, with and without eastern white pine seedlings, were treated with solution at pH levels of 2, 3, 4, and 5.3 for a 10-week period. While the soil parameters measured were not significantly altered by the higher pH treatments, treatment at pH 2 decreased soil pH, base saturation, and leachate pH, and increased leachate metal content. The presence of the seedlings moderated the effects of the pH 2 treatment by a probable combination of root cation exchange capacity and plant uptake. Seedlings receiving the higher pH treatments exhibited the expected metal distribution pattern (roots ≫ stems = leaves), while the pH 2 seedlings exhibited a different pattern (roots = stems = leaves). Cadmium and Zn levels in the stems and needles of the pH 2 plants were significantly higher than levels in those of the higher pH seedlings, while levels in the roots treated with pH 2 solution were significantly lower. This unusual distribution pattern may be the result of root injury due to the highly acidic solution. Although metal distribution was clearly affected by the acid treatments, increased toxicity symptoms were not observed in seedlings subjected to soil applications of acidified solutions.

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