Abstract

Silicon (Si) speciation and availability in soils is highly important for ecosystem functioning, because Si is a beneficial element for plant growth. Si chemistry is highly complex compared to other elements in soils, because Si reaction rates are relatively slow and dependent on Si species. Consequently, we review the occurrence of different Si species in soil solution and their changes by polymerization, depolymerization, and condensation in relation to important soil processes. We show that an argumentation based on thermodynamic endmembers of Si dependent processes, as currently done, is often difficult, because some reactions such as mineral crystallization require months to years (sometimes even centuries or millennia). Furthermore, we give an overview of Si reactions in soil solution and the predominance of certain solid compounds, which is a neglected but important parameter controlling the availability, reactivity, and function of Si in soils. We further discuss the drivers of soil Si cycling and how humans interfere with these processes. The soil Si cycle is of major importance for ecosystem functioning; therefore, a deeper understanding of drivers of Si cycling (e.g., predominant speciation), human disturbances and the implication for important soil properties (water storage, nutrient availability, and micro aggregate stability) is of fundamental relevance.

Highlights

  • As well as biogenic silica, can act as a source for silicic acid, i.e., the dissolved form of Si [2,3,4,5]

  • About 35% of total phytogenic biogenic amorphous silica (bASi) has accumulated in field crops on a global scale, and this proportion is going to increase with increased agricultural production within the decades [101]

  • In contrast to natural ecosystems, where bASi is recycled in great amounts, agricultural sites are subject to high Si exports by harvest year by year with implications for Si bioavailability in agricultural soils, and Si cycling in agricultural soil–plant systems (Struyf et al [93], Vandevenne et al [94], Vandevenne et al [95]; see Section 7)

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Summary

Introduction

Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations. For example: (i) monosilicic acid requires several months for polymerization under low pH (pH ~4) and is much faster polymerized under higher pH, changing binding affinity to soil minerals [32]; (ii) silica-rich precipitations in soil solution are mostly considered as clay minerals despite the fact that mineral crystallization is a process that requires months to millennia, depending on the specific mineral [33,34]. Another reason for differences in the interpretation of study results seems to be the differing use of definitions. The review ends with an outlook, where recommendations for future research are given (Section 8)

Si Extraction Methods
Silicic Acid and Soluble Silica Species in Soils and Sediments
Biogenic Silica Pools in Soils and Their Relevance for Si Cycling
Further Organisms and Corresponding bASi Pools
The Phytogenic Si Continuum in Soils
Si Fertilization
Importance of Si for Crop Production
The Need of Crops for Si
The Importance of Si for Mitigating Abiotic Stress
The Importance of Si for Mitigating Biotic Stress
Findings
Outlook
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