Abstract

Soil has the nature of acidity and alkalinity, mostly indicated by soil pH that could greatly affect soil ecological processes and functions. With exogenous inputs of acidic materials (such as acid rain), soils may more or less resist to maintain their pH levels within specific thresholds by various buffering processes. It has been well established that soil properties such as cation exchange capacity (CEC), soil organic matter (SOM), and clay content play important roles in mitigating the effects of acid inputs, but the factors varied across soils. This microcosm experiment was conducted to investigate changes in the soil pH and quantitatively estimate the critical pH threshold of simulated acid rain for three highly weathered soils (red soil, lateritic red soil, and latosol) that are typical soil types widely distributed across the world’s subtropical and tropical climatic zones, as well as important influential factors, after continuously adding different levels of simulated acid rain on the surface of soil cores. The results showed that the change in the soil pH was not significantly different among the three soils, although it was exponentially related to soil CEC and clay content. Resultantly, the latosol that had high soil CEC and clay content was more resistant to simulated acid rain, especially when relatively weak simulated acid rain treatments were applied. The lateritic red soil that contained the lowest soil CEC and clay content showed the greatest decline in the soil pH under the strongest simulated acid rain treatment of pH being 2.5. Furthermore, we estimated the critical pH threshold of simulated acid rain for the three soils and observed that it was considerably different among the soils. Surprisingly, the pH threshold of simulated acid rain was also positively related to the soil CEC and clay content, therefore making the highest pH threshold in the latosol. Our results imply that soil CEC and clay content may play critical roles in the soil acid-buffering processes from two aspects; it could not only contribute to the soil acid-buffering capacity, but also affect the threshold of acidity of acid rain below which abrupt soil acidification may occur.

Highlights

  • Soil acidity is an important aspect of soil chemical properties and can influence ecosystem processes and functions to a great extent, e.g., by altering nutrient supplies via regulating the soil sorption/desorption reactions and properties of the soil microbial community [1,2,3]

  • The abbreviation of EC stands for soil electrical conductivity, CEC for soil cation exchange capacity, and SOM is soil organic matter. † Statistical F values are calculated by one-way analysis of variances, with *** indicating significance level at p < 0.001

  • The results showed that changes in the soil pH under the simulated acid rain treatments were not significantly different among the soils, with significantly lower magnitude of soil pH change at relatively weak simulated acid rain treatments in the latosol, but significantly highest response to the strongest simulated acid rain treatment in the lateritic red soil

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Summary

Introduction

Soil acidity is an important aspect of soil chemical properties and can influence ecosystem processes and functions to a great extent, e.g., by altering nutrient supplies via regulating the soil sorption/desorption reactions and properties of the soil microbial community [1,2,3]. In several types of strongly acidic soils that distribute widely across those low latitude regions of the earth, the hydrolysis reaction of aluminum bound to organic materials could be the major source of soil acid-buffering capacity [16]. This context dependence highlights the necessity to widely investigate the soil acid-buffering capacity in diverse ecosystems under the changing scenarios such as agricultural managements and global changes

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