Effect of long-term conservation tillage on soil biochemical properties in Mediterranean Spanish areas
Introduction
Benefits from conservation tillage, including improvement of soil properties, savings of time, energy and water, and wind erosion control, have been reported in many studies carried out under different environment conditions (Griffith et al., 1986, Lal, 1989). Thus, traditional, intensive inversion tillage (TT) is being replaced by conservation tillage systems. Conservation tillage systems reduce labour, fuel, and machinery expenses and also have some agronomic and environmental implications. Conservation tillage protects the soil against water and wind erosion and reduces soil evaporation by leaving crop residues on the soil surface, thus promoting greater soil moisture content (Lafond, 1994).
To be considered conservation tillage (CT), any tillage and planting system must maintain at least 30% of the soil surface covered by residue after planting to reduce soil erosion by water. Where soil erosion by wind is a primary concern, the system must maintain a 1.1 Mg ha−1 flat small grain residue equivalent on the surface during the critical wind erosion period (Gajri et al., 2002). Some times, there is no distinction between CT, MT (minimum tillage) or reduced tillage (RT) (Bradford and Peterson, 2000). Types of CT include no-tillage (NT), ridge tillage, mulch tillage and zone tillage (Hill, 1996).
Under semi-arid climate, CT is one of the best options to store and conserve soil water (Rawitz and Hadas, 1994). Many short-term studies and a few long-term studies have evaluated the effect of tillage systems on plant productivity (Cantero-Martinez et al., 2003, Moreno et al., 1997). In general, the lack of negative effect on yield, make conservation tillage attractive attending the reduction in operating costs and soil quality increase (Franzluebbers, 2004). Soil quality can be defined as its capacity to work properly within ecosystem boundaries maintaining biological productivity, environment quality and also to promote plant and animal health (Doran and Safley, 1997). The definition of soil quality has focused on some properties that affect soil health and quality (Doran and Safley, 1997). Soil microbial biomass and enzymes have been suggested as potential indicators of soil quality because of their relationship to soil biology, ease of measurement (i.e., potential to be adopted by commercial laboratories for routine soil testing), rapid response to changes in soil management and high sensitivity to temporary soil changes originated by management and environment factors (Nannipieri, 1994). Conservation tillage increases organic matter levels in superficial layers of the soil (Franzluebbers, 2004). Thus, biological activity has been found to be higher in soils under CT than under TT (Bolinder et al., 1999). Also, under CT, an increase of the activity of some enzymes (acid phosphomonoesterase, arylsulphatase, dehydrogenase, urease and β-glucosidase) has been found (Angers et al., 1993, Eivazi et al., 2003).
During the past 20 years, conservation tillage practices, as RT or NT, have been introduced in the Mediterranean areas with different success (Cantero-Martinez et al., 2003, Lopez et al., 1996, Lopez et al., 2005, Moreno et al., 1997). In these areas, studies of the performance of conservation tillage systems have demonstrated advantages in yield, water profitability (water storage, water use by crops) and protection of the soil against erosion by water and wind (Álvaro-Fuentes et al., 2008a, Cantero-Martinez et al., 2003, Mrabet, 2002, Muñoz et al., 2007). Reduction of CO2 fluxes to the atmosphere derived from conservation tillage adoption has also been reported (Álvaro-Fuentes et al., 2008b). Despite some disadvantages such as the increase of the use of herbicides, CT appears to be the most important sustainable alternative system to traditional agriculture to cope with negative agro-environmental problems derived from TT, including the diminution in soil biodiversity. However, comparatively little attention has been given to soil biochemical properties under different tillage systems (Madejón et al., 2007).
The aims of the study were to determine the effects of long-term conservation tillage on soil chemical properties and microbial function in three sites of Spain under semi-arid Mediterranean conditions. We hypothesized that conservation tillage would have a positive effect by increasing soil organic matter and fertility, and, enhancing soil microbial functionality.
Section snippets
Materials and methods
The study was carried out in three different experimental sites of the semi-arid Spain located specifically in the provinces of Lleida (LLE), Zaragoza (ZAR) and Sevilla (SEV) (Fig. 1). All the sites have a long history of experimentation of conservation tillage (12–18 years).
Soil total organic carbon and water soluble carbon
As a rule, TOC and WSC values were higher in the soils under RT and NT that under TT at the superficial layer (0–5 cm) (Fig. 2a and b). For both parameters, differences among treatments were only significant at LLE, where the increase of TOC and WSC with conservation tillage was noticeable even at intermediate layers (5–10 cm) (Fig. 2c and d). In the three experimental sites, soil organic matter content decreased with depth and at the deepest layer (10–25 cm) the values of TOC and WSC were similar
Conclusion
Long-term use of conservation tillage has become a proven strategy to increase soil organic matter, especially surface soil biochemical quality in Mediterranean areas of Spain. Changes in soil biochemical properties with tillage and in their stratification ratios should provide practical tools to complement physical and chemical test and, thus, evaluate the effect of tillage in Mediterranean semi-arid conditions. As the climatic conditions of the semi-arid Mediterranean areas are an important
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2021, Soil and Tillage ResearchCitation Excerpt :Instead of continuously cultivating one crop species, crop rotation introduces several crop species and increases soil organic carbon conservation (Tiemann et al., 2015; West and Post, 2002). Conservation tillage, which is defined as leaving at least 30 % of the soil surface covered by crop residues, reduces physical disturbances to soil and can restore soil fertility (Liu et al., 2014; Madejón et al., 2009). How crop rotation and conservation tillage alter soil properties has been examined in both field and incubation studies (Bünemann et al., 2004; Jacinthe and Lal, 2005; Madari et al., 2005; Salvo et al., 2010; Xu et al., 2013).