Soil organic matter dynamics and land-use change on Oxisols in the Cerrado, Brazil
Introduction
The Cerrado biome is a complex of plant formations that occupies approximately 2 million km2 in the Brazilian territory (Brazil, 2018). It occurs in several regions of the country; its phytophysiognomy is highly diverse, depending on edaphic-climatic conditions (Ribeiro and Walter, 1998). The Cerrado in Piauí State is part of a region called MATOPIBA (because occupies part of the Maranhão, Tocantins, Piauí and Bahia States) and occupies about 11% (8.2 Mha) of the state territory (Embrapa, 2014) and accounts for a considerable percentage of the Brazilian grain (2% - rice, maize and soybean), fiber (1% - cotton) and livestock (1% - beef cattle) production (IBGE, 2018). Because of soil and climate characteristics favorable to the development of agricultural produce with high economic values, attracts new investors, has placed this region in the focus of potential ecosystem changes to expansion of feedstocks production areas.
Land use change (LUC) is the transformation of large parts of a landscape, directly altering its capacity to maintain its ecosystem services (Foley et al., 2005). Such changes are generally associated with the production of feedstock (food, fiber, bioenergy). Nevertheless, within the current LUC standards, the conversion of natural vegetation into agricultural areas is still the main factor of deforestation, especially in the tropics (Karp et al., 2015). Within a relatively short-time, LUC may significantly change the physical and biogeochemical properties of Cerrado soils (Hunke et al., 2015), through a reduction in organic material inputs to the soil (Lal, 2004; Saidy et al., 2013), consequently, reducing soil organic matter (SOM) (Ashagrie et al., 2007; Don et al., 2011; Corbeels et al., 2016; Matias et al., 2009; Siqueira-Neto et al., 2010).
SOM is the largest C stock in the biosphere (Lal, 2004) and formed by a complex and heterogeneous mixture of organic composts in different degrees of biochemical transformation, which more stable forms are generally associated with mineral soil fraction (Zinn et al., 2005). To maintain soil C stocks, the SOM needs to be in chemically more stable fractions (recalcitrant-C pools), such as humic substances (HS), which are formed by resynthesis processes and are relatively inert in the soils (Silva and Mendonça, 2007) and with longer response time to land-use and management changes (Rumpel and Kögel-knabner, 2011). On the other hand, a minor amount of SOM it's formed by less complexed C compounds (labile-C pools), which are characterized by their rapid turnover and are therefore more sensitive to management changes or variations in environmental conditions than total C stocks (Duxbury et al., 1989). In this sense, the particulate organic matter (POM) fraction plays an important role in soil nutrient availability, even as energy source for microorganisms; and it is influenced by residue quality, C:N ratio, climate, land-use and management (Bayer et al., 2004).
Agricultural systems in the Piauí Cerrado are characterized by intensive and frequent soil revolving (Pragana et al., 2012). In this context, the high rate of agricultural expansion, in which large areas are subjected to intensive mechanization, has raised concern about the potential impacts of LUC on ecosystem services provided by soils, mainly in terms of regulation and support (e.g. soil C stocks in SOM, retention and conservation of water resources, sources and cycling of nutrients) (Fu et al., 2015).
Several researchers have shown that LUC causes considerable SOM losses (Corbeels et al., 2016; Coser et al., 2018; Marchão et al., 2009; Salton et al., 2014; Sant-Anna et al., 2017; Siqueira-Neto et al., 2010; Zotarelli et al., 2012). Thus, it is assumed that in the MATOPIBA, where, predominantly, climatic conditions (high temperature and short-time rain season), soil characteristics (high sand content, clay fraction formed by low activity materials - Fe and Al oxide, low structuration with presence of cohesive horizon), besides soil revolving facilitates the organic material decomposition and SOM mineralization. This study tested the hypothesis that after SOM decline due to LUC, conservationist land-uses (e.g. no-till, well-managed pasture and Eucalyptus afforestation) can recover SOM levels through the organic material inputs (crop/grasses - above and belowground - residues) and sustainable management practices. Thus, we conducted a field study to evaluated different land-uses, common in this region of the Cerrado and recognized for their potential to increase SOM, to quantify their effects on soil C stocks, as well as SOM chemical and physical fractions.
Section snippets
Study site and treatment
The study was conducted in the municipality of Uruçuí (Piauí State, Northeast region of Brazil). The climate of the region is humid tropical of savannah type (Aw - Köppen's classification) with a high average annual temperature of 25 °C and a distinct rainy season from November to April; average annual rainfall ranges from 800 to 1200 mm (Aguiar and Gomes, 2004). The hydrological conditions favor a sub-deciduous character, drastically reducing the size and density of native vegetation (Jacomine
Results
Soil bulk density (BD) significantly differed between land-uses for all depths (Table 2), with the lowest values for NV (p < .05). The top soil (0.1 m) of EU showed similar values than NV, although BD values increased with depth. Bulk density was highest for PA and NT throughout all depths (p < .05).
Soil carbon contents differed significantly between land-uses (p < .05; Table 2) and presented higher values in the top soil decreasing with depth. In the top (0.1 m), higher C values were found for
Effect of different land-uses on soil C stocks
We evaluated the effects of current land-uses on SOM in this specific region of the Cerrado, called MATOPIBA, and we tried to show which theses land-uses have the potential to recover soil C contents over time after losses due the LUC.
We know that the operations that comprise LUC are main causes of SOM loss (Rabbi et al., 2014). Generally, LUC (in this study - LUC 1; Table 1) starts with the conversion of native vegetation. After slashing and burning of the plant biomass, the soil is ploughed
Conclusions
Our study assessed SOM changes due to land-uses in a specific region of the Cerrado, the so-called “MATOPIBA”, currently, subject to LUC intensification. In this region, SOM levels are generally low due to low natural occurrence, high intemperism, sandy texture, physical restrictions due to the presence of a cohesive horizon, in addition the climatic characteristics approaching the Semiarid Northeast of Brazil, consequently, the natural vegetation consists of sparse shrub formations with low
Acknowledgements
MRG thanks the Foundation of Support to Research of Piauí (FAPEPI) for providing her scholarship. We would like to thank the PROCAD-CAPES for providing the interaction between Federal University of Piauí (UFPI) and Federal University of Lavras (UFLA) and to perform the laboratory analysis in Soil Science Departments (DCS-UFLA). We thank the Postgraduate Program in Soil and Plant Nutrition (PPGSNP) and the farm in Uruçuí, PI, for allowing us to soil sampling in their areas. MSN thank the
References (66)
- et al.
Soil aggregation, and total and particulate organic matter following conversion of native forests to continuous cultivation in Ethiopia
Soil Tillage Res.
(2007) - et al.
Methods for physical separation and characterization of soil organic matter fractions
Geoderma
(1993) - et al.
Soil C and N stocks as affected by cropping systems and nitrogen fertilisation in a southern Brazil Acrisol managed under no-tillage for 17 years
Soil Till. Res.
(2005) Soil organic matter stratification ratio as an indicator of soil quality
Soil Till. Res.
(2002)- et al.
Soil organic matter pools and carbon fractions in soil under different land uses
Soil Till. Res.
(2013) - et al.
Soil changes under different land-uses in the Cerrado of Mato Grosso
Brazil Geoderma Reg
(2015) - et al.
National indicators for observing ecosystem service change
Glob. Environ. Chang.
(2015) - et al.
Short-term temporal changes of soil carbon losses after tillage described by a first-order decay model
Soil Till. Res.
(2008) - et al.
Effect of grassland management on soil carbon sequestration in Rondônia and Mato Grosso states, Brazil
Geoderma
(2009) - et al.
Changes in soil organic carbon storage under different agricultural management systems in the Southwest Amazon Region of Brazil
Soil Till. Res.
(2010)