Elsevier

Geoderma

Volume 409, 1 March 2022, 115592
Geoderma

Role of clay minerals in controlling phosphorus availability in a subtropical Alfisol

https://doi.org/10.1016/j.geoderma.2021.115592Get rights and content

Highlights

  • The fate of P fertilizers in Alfisol is controlled by chemical adsorption reactions.

  • P is primarily immobilized by goethite, kaolinite, and illite in Alfisol.

  • P adsorbed by illite may serve as an indicator of P availability in Alfisol.

Abstract

Inorganic P is adsorbed by a variety of soil minerals. For acidic subtropical Alfisols with high contents of both (hydr)oxides and clay minerals, there is an underappreciated understanding of the importance of clay minerals to P species and availability varying with soil pH and P concentration. In this study, the rate and equilibrium of P adsorption in a subtropical Alfisol were investigated by combining soil incubation with three types of P fertilizer with multi-surface modelling. Phosphorus species analysis revealed that most of the P was present in the forms of Al-P and Fe-P in the subtropical Alfisol. The multi-surface model calculation showed that goethite, kaolinite, and illite were the most important soil constituents responsible for the immobilization of P. Clay minerals were as important as Al/Fe (hydr)oxides for P adsorption in the subtropical Alfisol. In addition, there was a highly positive linear correlation between P adsorbed by illite and Olsen P, with a slope of approximately to 1. The model analysis also showed that >99% of the P adsorbed by illite was in the form of -SO2PO22-. These results suggest the important role of illite in controlling P availability and that P adsorption by illite may serve as an indicator of P availability in the subtropical Alfisol.

Introduction

Phosphorus is an essential macronutrient for plant growth in both terrestrial and aquatic ecosystems and is often a primary limiting factor in agricultural production (Hinsinger, 2001, Raghothama and Karthikeyan, 2005). However, long-term nutrient fertilization in intensive farming systems has led to high accumulation of P in soils, which can lead to serious environmental problems such as eutrophication of surface waters (Jiao et al., 2012, Kier and Kirkland, 2013). In soils, P is directly taken up by crops in the form of orthophosphate anions (PO43-). Phosphorus availability is strongly affected by the adsorption of P onto the positively charged sites of Fe and Al (hydr)oxides and clay minerals and the formation of P-containing minerals (Barrow, 2017, Hiemstra et al., 2013, Holford, 1997, Meyer et al., 2021, Weng et al., 2011). Fe/Al (hydr)oxides have been generally recognized as important agents in controlling P availability in the subtropical Alfisol because of their high positive charge and P adsorption capacity (Antelo et al., 2005; Xu et al., 2019), whereas the role of clay mineral has been largely ignored (Cui and Weng, 2013, Weng et al., 2011, Weng et al., 2012). In actual agricultural production, crops can only utilize a very small fraction (10–20%) of the fertilized P, which is largely determined by the soil properties and fertiliztion strategies (Liu et al., 2017, Meyer et al., 2021). The relationship between individual soil constituents and P availability is still poorly understood and difficult to predict in soils.

It is generally accepted that P availability is highly correlated with P species. The role of P adsorbed by clay minerals in controlling P availability is generally neglected compared with that of Fe/Al oxides (Gérard, 2016, Hinsinger, 2001). A review of experimental studies over a 70 years periods revealed that in most soils, clay minerals should be considered as important P-binding constituents that can possibly outcompete Fe/Al (hydr)oxides P adsorption (Gérard, 2016). Our recent study also demonstrated that myo-inositol hexakisphosphate a common type of organic P in soils, can form inner-sphere complexes and surface precipitates on the surface of kaolinite (Hu et al., 2020). These findings indicate that although the P adsorption capacity of clay minerals is much lower than that of Fe/Al (hydr)oxides, they may also provide a potentially important interface for P adsorption owing to their higher contents in soils, especially in the subtropical Alfisol, the clay minerals content of which is over six times that of Fe/Al (hydr)oxides. The P adsorbed by clay minerals is more easily desorbed than that adsorbed by Fe/Al (hydr)oxides, thereby indicating that the stability of P adsorption to clay minerals is weaker than that of Fe/Al (hydr)oxides; thus P is more readily available to plants (Al-Kanani and MacKenzie, 1991). It has also been demonstrated that there is a high linear correlation between available P and the clay mineral content in soils (Herlihy and McGrath, 2007). These facts indicate that in soil such as the subtropical Alfisol the potential importance of clay minerals to P availability may be greatly underestimated compared with that of Fe/Al (hydr)oxides.

To evaluate the contribution of clay minerals to P availability in the subtropical Alfisol, it is critical to use a reasonable method to identify the P species regarding the soil constituents. In practice, Olsen P is a convenient measure of available P in soil; P species can be classified into Al-P, Fe-P, Ca-P, and occluded P (O-P) by Jackson-Chang’s method (Chang and Jackson, 1957). Such P species can be easily measured by different chemical extractions using acids and bases. A ‘family’ of P is adsorbed by active sites with similar affinities on different soil constituents. It is impossible to accurately reflect the contribution of clay minerals to P availability (Olsen P). However, the shortcomings of chemical methods for the determination of P species can be complemented by the multi-surface model. The model considers that the soil is composed of a series of independent soil constituents, and the amount of P adsorbed by soil is a linear sum of the P adsorbed by each individual soil constituent. Phosphorus species based on the types of soil constituents and dissolved inorganic P can be accurately predicted by the multi-surface model under certain pH levels and P concentrations (Devau et al., 2011, Devau et al., 2010, Weng et al., 2001). Therefore, it is an effective and convenient approach to determine the P species, which can be used to link P adsorption to clay minerals with the available P in the subtropical Alfisol.

In this study, to examine the role of clay minerals in controlling P availability in the subtropical Alfisol, the kinetics and isotherms of P adsorption were investigated by combining soil incubation with three types of P fertilizer with multi-surface modelling. The pH, dissolved organic carbon (DOC) concentration and Olsen P concentration were monitored during incubation. The P species in the subtropical Alfisol depending on the incubation time and P concentration were analyzed first by Jackson-Chang’s method, and then calculated using the multi-surface model. The contributions of different soil constituents to P availability were also compared. The hypotheses of this study are as follows: (1) clay minerals are important for P adsorption and P species in the subtropical Alfisol; (2) the multi-surface model is an effective and convenient method to determine P adsorption by clay minerals, and (3) clay minerals play a key role in controlling the P availability in the subtropical Alfisol.

Section snippets

Soil samples

Topsoil (0–20 mm depth) was sampled in the summer of 2018 from farmland in Qiyang City, Hunan Province, China (E111°52′32″, N26°45′12″), which belongs to the subtropical monsoon climate zone. The sampling point was a control group of a long-term monitoring experiment. The soil type was Alfisol derived from Quaternary red clay. Soil samples were air-dried, sieved to 2 mm, loaded in a closed plastic bag, and stored in the dark before analysis.

Physicochemical properties of soil

The soil pH was measured using a pH meter after

Outline of the multi-surface model

The multi-surface model was established to calculate the P species, which were classified by the type of soil constituents in the subtropical Alfisol. The model parameters are summarized in Table 2. The definitions of individual soil constituents and their corresponding sub-models for ion adsorption and ion exchange were introduced briefly as follows.

Kinetics of P adsorption in the subtropical Alfisol

All three types of P fertilizer treatments resulted in similar trends of changes in pH, DOC, and Olsen P for the kinetics of P adsorption in the subtropical Alfisol, thereby reflecting the typical variations in the redistribution of PO43- at the soil particle-water interface (Fig. 1). The pH, DOC, and Olsen P changed significantly in the first 14 d of incubation and then stabilized in most soil samples after 42 d, thereby indicating that the fate of P fertilizer in the subtropical Alfisol was

Importance of clay minerals for P adsorption in the subtropical Alfisol

In Fig. 5a, b and c, the contributions of individual soil constituents to P adsorption in the subtropical Alfisol can be evaluated by comparing the percentage of each P species. For all three types of P fertilizer treatments, the percentage of P adsorbed by kaolinite and illite ranged of 44% to 52%, whereas that adsorbed by Al/Fe (hydr)oxides ranged from 48% to 56% depending on the pH and P concentration. These results indicate that clay minerals play an equally important role as Al/Fe

Conclusions

In this study, the rate and equilibrium of P adsorption in a subtropical Alfisol were investigated by combining soil incubation with three P fertilizers with multi-surface modelling. The calculated P species indicated that P was mainly adsorbed by goethite, kaolinite, and illite, and the dissolved P in the soil solution could be ignored. Approximately 50% of the active P was adsorbed by clay minerals under the experimental conditions, which suggested that the role of clay minerals is as

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

Acknowledgements

This research was supported by the National Natural Science Foundation of China (42030709 and 32061123007), the national key research and development programs of China (2017YFD0200200) and the Cooperation Foundation from CAS Key Laboratory of Mineralogy and Metallogeny (KLMM20190103).

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