Soil Organic carbon

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Soils can be taken account as the largest pool of actively cycling carbon in terrestrial ecosystems (Jobbágy and Jackson, 2000; Janzen, 2004). In addition, the inventory of soil organic matter (SOM) and the evaluation of processes involving its transport are needed for greenhouse gas inventories and carbon mitigation (Ravindranath and Ostwald, 2008). The restoring soil carbon is indispensable to improving soil quality, sustaining food production, maintaining clean water, and decreasing rises in atmospheric CO2 (Lal, 2004). The magnitude and variation of soil organic carbon (OC) stocks is deeply connected to various factors, including temperature, moisture, organic carbon structure, texture, soil type and topography (natural factors) (Parton et al., 1987, Tan et al., 2004) , land use type, and management intensity ( human activities). (Tan et al., 2004; Mou et al., 2005; Somaratne et al., 2005; Von Lützow et al., 2006). Appropriate assessment of the spatial variability pattern and reserves of SOC, especially at national and sub-national scales, is an essential step when evaluating sequestration potentials (Liu et al., 2011). The world SOC reserves has been projected to be about 1400–1500 Pg Carbon at a depth of 100 cm soil layer (Post et al., 1982; Eswaren et al., 1993; Batjes, 1996), which is around twice the amount of C in the atmosphere and three times the amount stored in terrestrial vegetation (Smith, 2004). On the other hand, annual soil carbon sequestration is 0.4 to 1.2 Pg C year−1 in the world scale that these values is equivalent to 6% to 20% of the annual CO2 which release from the combustion of fossil fuel (Lal, 2004; Houghton, 2005). Therefore, control of spatial variability of SOC can be investigated as potentially pr...

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...spatial heterogeneity of surface soil properties has in ecosystem functioning, few studies have described the spatial heterogeneity of SOC in Golestan province and their relations with topography and different slope position loessial hillslope lands of northen Iran. However, just few studies on the spatial variability of soil organic carbon in farmland are available (Ayoubi et al, 2007).
In summary, accessibility to OC budget requires sustainable agricultural development, preservation and restoration of ecosystems. Despite little information is available at hillslope spatial scales and efficiency of different slope position is still unclear. The objectives of this paper were 1) to estimate soil organic carbon content and reveal the spatial heterogeneity of SOC at different parts of hillslope and 2) to compare the results of Geostatistical models in estimation of OC.

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