Skip to main content
Passa alla visualizzazione normale.

LUCIANO GRISTINA

Particle-size distribution and associated organic matter under different cropping systems and tillage practices in a semi arid environment.

  • Authors: BARBERA, V; POMA, I; GRISTINA, L
  • Publication year: 2008
  • Type: Articolo in rivista (Articolo in rivista)
  • Key words: SOC, particle size distribution, tillage, crop rotation
  • OA Link: http://hdl.handle.net/10447/58656

Abstract

The aim of this study was to evaluate the long-term impact of different management practice and tillage tools on :1) changes in soil carbon stock with different cropping systems and soil tillage managements; 2) aggregate size distribution and organic carbon concentration of each fraction; 3) organic matter composition and stability Methodology The research was carried out at the Pietranera farm, located in southern part of central Sicily (Italy) (37°32’74” N / 13°31’53” E; elevation 236 m; mean annual precipitation 481 mm; mean air temperature 19 °C) on a soil of a long term experiment. The soil is classified as a fine-clayey, calcareous, mixed, xeric Chromic Pelloxerert with a slope of 4%. The soil were sampled before the start of the experiment and had 471 g kg-1 clay, 225 g kg-1 silt, 304 g kg-1 sand, 18,1 g kg-1 SOC (soil organic carbon), 1,29 g kg-1 N, and a pH of 8,1. The twelve plots (twenty years long term trial) used in this test area follow two crops rotations, wheat-wheat (W) and wheat-bean (WB), with three different soil managements: 1) traditional (CT = conventional tillage) consisting of a ploughing at 30-35 cm depth; 2) dual layers tillage (DL) with a chisel at 40 cm and 15 cm depth; 3) no tillage (NT). Soil sample were taken at 0-20 cm depth, air dried and sieved at 2 mm. Wet aggregate-size fractions, with no chemical dispersion were isolated by mechanic shaking of 50 g air-dry 2 mm sieved sample of soil on a column of 2000, 1000, 500, 250, 75 and 25 μm sieves. After the physical fractionation, we distinguished three main fractions: 75-250 μm (large microggregates), 25-75 μm (small microaggregates), < 25 μm (silt and clay fraction). The relative distribution of nitrogen and organic carbon content as well as the 13C natural abundance were measured for these fractions. Cumulative carbon input of the cropping systems were calculated according to Kong et al. (2005). Results The carbon content in the different experimental plots does not vary greatly, ranging from 18,3 g kg-1 up to 21,2 g kg-1. The highest carbon content values were found under the wheat monocropping system with no-tillage (WNT) (21,2 g kg-1) and conventional tillage management (WCT) (20,8 g kg-1), respectively. Comparing the three different soil management techniques, NT shows a higher influence on organic carbon accumulation (20,4 g kg-1), than the CT and dual layer (DL) (19,7 g kg-1 and 18,3 g kg-1). The estimated cumulative C input, ranged from 6,5 Mg C ha-1 in WBDL to 7,0 Mg C ha-1 in WCT. Annual SOC sequestered is higher for W than WB (0,16 Mg C ha-1 yr-1 vs. 0,05 Mg C ha-1 yr-1, p<0,05). Among the different soil managements techniques the DL seems to be less effective in soil organic carbon protection. Regarding the different soil aggregates, the <25 μm fraction was the most abundant one (mean 688 g kg-1). Conversion from continuous wheat to wheat-bean rotation resulted in no real differences in the large microaggregates percentage (102 g kg-1). Long-term NT systems does not produce a better aggregation state. Comparing the C contribution of different aggregates to the total organic C amount, the following order was discerned: 0-25 μm > 25-75 μm > 75-250 μm > 250-2000 μm. The higher resistance to mineralisation processes of silt-clay associated organic matter is also explained by the higher concentration of N in this fraction (cf. Kleber et al., 2007) than in the bulk soil (average N = 1,30 g kg-1 and 1,17 g kg-1, respectively; p<0,05). Taking, however, the average C concentration in each fraction into the consideration, the 75-250 μm aggregate size show a C enrichment (23,9 g kg-1), while the corresponding values of the 25-75 μm and 0-25 μm fractions do not differ greatly from the bulk soil concentration (19,3 g kg-1 and 19,8 g kg-1 respectively). According to Gerzabek et. al. (2001), we compared C and mass distributions between size fractions and found that large microaggregates (7