Soil K forms and K budget in integrated crop-livestock systems in subtropical paddy fields
Introduction
Rice (Oryza sativa L.) is considered one of the most important grain crops in developing countries and it is responsible for feeding over 4 billion people in the world, with the prospect of increasing rice consumption by 25 % until 2030 (International Rice Research Institute IRRI, 2019). Rice is grown in an area of 161 million hectares worldwide (USDA, 2020), mainly in monocropping systems of flooded rice under conventional tillage (CT), with annual soil mobilization by plowing and harrowing combined with fallow in the off-season (Chauhan et al., 2017).
Soil disturbance has been pointed out as the main cause of soil degradation (Lal, 2015), leading to a decline in flooded rice yield over time (Bado et al., 2010). On the other hand, although still scarcely used by farmers, no-till (NT) has proved efficient in improving soil quality and flooded rice yield (Denardin et al., 2019). In this scenario, the crop diversification with paddy-upland crops rotation is sustainable way to increase soil fertility and rice yields (Hou et al., 2018; Yu et al., 2014). Moreover, alternating the grain crops (rice, soybeans and maize) with pastures for animal grazing in integrated crop-livestock system (ICLS) (Moraes et al., 2014), has been pointed out as a management strategy to booster soil fertility and nutrient use efficiency in subtropical paddy fields (Carlos et al., 2020).
It is well known that NT (Firmano et al., 2019) and crop rotations (Tiecher et al., 2017) increase the availability of potassium (K) in the soil. Although the dynamics of K in the soil in crop production systems has been widely explored (Vieira et al., 2016; Mortele et al., 2016, 2019; Gatiboni et al., 2019), there is still a lack of knowledge about the soil K dynamics in ICLS, especially considering paddy fields under different soil tillage systems and crop rotations.
Potassium in soil can be broadly divided into three main forms: (i) in small concentrations in the soil solution as a free ion (K+) (Rawat et al., 2016), (ii) as part of primary minerals highly resistant to weathering (structural form), and (iii) adsorbed to soil functional groups forming surface complexes with varying degrees of energy and availability for plants (Weil and Brady, 2017). The most available soil K form to plants can be extracted with chemical solutions such as Mehlich-1 and ammonium acetate, and it is generically called "exchangeable K" (Warncke and Brown, 1998). In the medium-long term, there is a continuous process of depletion of K retained with less energy by the soil, forcing the release of K adsorbed with greater energy, often present in the mineral structure (Fraga et al., 2009; Mortele et al., 2019). It means that part of the K present in the 2:1 claymineral interlayer can be released by diffusion into the soil solution. In order to estimate the quantity of K retained in this form, other extractors can be used, such as sodium tetraphenylborate. The amount of K extracted by this method is generically called “non-exchangeable K”.
The main soil type used for flooded rice cultivation in subtropical paddy fields is the Planosol derived from granite-gnaissitic and sedimentary rocks (Silva et al., 2019). These soils have high natural K reserves, mainly associated with the presence of K-feldspar and mica in the silt fraction, and the presence of 2:1 clayminerals (smectite, vermiculite and illite) in the clay fraction (Britzke et al., 2012). The non-exchangeable and total K content in Planosols can reach up to 1,750 and 39,500 mg kg−1 respectively (Nachtigall and Vahl, 1991; Britzke et al., 2012). In these soils, when the amount of K supplied by fertilizers is lower than the uptake by plants, there is a release of K adsorbed in the siloxane cavities of 2:1 clayminerals (Golestanifard et al., 2020). On the other hand, when the addition of K is higher than the plant need, 2:1 clayminerals, such as vermiculite, can act as a K sink, adsorbing the excess K in their interlayer spaces (Mortele et al., 2019).
The combined use of crop rotation, ICLS and NT enhances K cycling, increasing K use efficiency (Assmann et al., 2017; Ferreira et al., 2009). In addition, in paddy fields, wetting and drying cycles (Weil and Brady, 2017) may result in fixation or release of K in soils with excess or deficiency of K, respectively (Scott and Smith, 1968; Olk et al., 1995; Golestanifard et al., 2020). Thus, the K sink or source behavior of the soil will be affected by the cultivation frequency of flooded rice and rainfed crops in summer (soybean, maize and pasture). Therefore, our hypothesis is that the K will accumulate differently in the soil with a traditional system based on flooded rice monocropping in summer and winter fallow with CT compared to a more diversified and conservationist system, such as ICLS under NT, especially when associated with paddy-upland crop rotation in summer season.
This study aimed to evaluate the forms of K in the soil and to quantify the K budget after 66 months of cultivation with different production systems of flooded rice, involving different soil tillage, animal grazing and crop rotation in a Brazilian subtropical paddy field.
Section snippets
History of the experimental area
The study was carried out in the edaphoclimatic region of the Internal Coastal Plain of the State of Rio Grande do Sul, Southern Brazil (Fig. 1). The climate is humid subtropical (Cfa) according to Köppen-Geiger classification (Alvares et al., 2013), with no defined dry season and with annual rainfall ranging from 1200 to 2000 mm. Geology is characterized by sandy pleistocene deposits of lagoon plain with influence of coluvionar sediments of precambrian granitic-gnaissic rocks of the
Soil K forms
Most of the K in the soil (98.4 %) was found in the structural form in the 0–30 cm soil layer. These values are compatible with the mineralogy of the soil and the material of colluvial granitic-gneissic origin of the region, which has K bearing minerals such as micas and feldspars (Fig. 3) that are considered as a potential source of K in the soil (Britzke et al., 2012). The non-exchangeable K represented about 1.4 %, whereas the exchangeable form was only 0.2 % of the total K in the soil.
Conclusion
The present study investigated the soil K forms and the K budget after 66 months of cultivation with different flooded rice production systems. The results show that the non-exchangeable, structural and total K were more sensitive than exchangeable K to detect the variation resulting from the inputs of K added via fertilization and the output of K via grains and meat. The Mehlich-1 and ammonium acetate extractors were not suitable for understanding the dynamics of K in lowland soils with
Funding
This work was funded by a grant from the Agrisus foundation (Grant number PA 2926/20) and the Coordination for the Improvement of Higher Education Personnel (CAPES) for financial and scholarship support, respectively.
Ethics approval
This study follows the rules of the ethics committee on the use of animals of the Federal University of Rio Grande do Sul.
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
We would like to thank the technician of the Laboratory of Soil Chemistry and Soil Fertility of the Federal University of Rio Grande do Sul, Adão Luiz Ramos dos Santos for his assistance in the analysis and the under-graduation students of the Interdisciplinary Research Group of Environmental Biogeochemistry (IRGEB). We also thank the Fundação Agrisus for the approval of the project (Grant number 2926/20) and the Coordination for the Improvement of Higher Education Personnel (CAPES) for
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