Arsenic mobility and toxicity on soil acid phosphatase activity increased with added phosphorus in contaminated mine soils

Soil phosphatase activity is identified as sensitive to arsenic (As) pollution and therefore, often used as an indicator to estimate As toxicity in soil. Nevertheless, the effect of As on soil phosphatase activity after its desorption by P is not adequately studied. This study employed sequential extraction procedure and ecological dose parameters to show As mobility and its toxicity to acid phosphatase (AcP). Results indicated that P application significantly increased As desorption ratio in the As ageing process. In S1 (As 2895 mg kg(-1)) soil, after P addition, the water-soluble (F-WS) fraction had the highest proportion of As, while for S2 (As 645 mg kg(-1)) and S3 (As 39 mg kg(-1)) it was residual (F-RES) fraction. Additionally, P addition increased the As bioavailability in all soils. Generally, P addition significantly reduced soil AcP activity under all P concentrations and increased in the soil with minimum As content. The variation partitioning analysis indicated that for S1, P concentration was the major factor, for S2 and S3 soils, it was As desorption and ageing time, respectively, that influenced the AcP activity in soils. The calculated ecological dose (ED50) showed that in most cases, As toxicity increased at the end of ageing. Thus, it is essential to control the phosphorus fertilizer applications in silty soils with acid and neutral pH, since it can lead to increased As mobility and toxicity to soil AcP.