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Organic matter (OM) in loess-paleosol sequences is used for paleoenvironmental reconstructions, based e.g. on stable carbon isotope composition. Loess OM (
The aims of this study were to investigate the effect of nitrogen (N) fertilisation on the below‐ground carbon (C) translocation by lettuce and the CO 2 efflux from its rhizosphere. Two N fertilisation levels (80 and 160 kg N ha −1 ) and two growth stages (43 and 60 days) were tested. 14 C pulse labelling of shoots followed by 14 C monitoring in the soil, roots, microbial biomass and CO 2 efflux from the soil was used to distinguish between root‐derived and soil organic matter‐derived C. The 14 C allocation in the below‐ground plant parts was 1.5–4.6 times lower than in the leaves. The total quantity of C translocated into the soil was much lower than in the case of cereals and grasses, amounting to 120 and 160 kg C ha −1 for low and high N respectively. N fertilisation diminished the proportion of assimilated C translocated below ground. About 5–8% of the assimilated C was respired into the rhizosphere. Root‐derived CO 2 (the sum of root respiration and rhizomicrobial respiration) represented about 15–60% of the total CO 2 efflux from the planted soil. Two peaks were measured in the 14 CO 2 efflux: the first peak (4–5 h after labelling) was attributed to root respiration, whilst the second peak (12 h after labelling) was attributed to microbial respiration of exudates. Twelve days after labelling, 0.15–0.25% of the assimilated C was found in the microbial biomass. The higher microbial activity in the lettuce rhizosphere doubled the soil organic matter decomposition rate compared with unplanted soil. © 2002 Society of Chemical Industry
No abstract is provided for this article.
No abstract is provided for this article.
Land-use change from forest to agriculture, which is driven by the demands of sustaining the growing global population, affects nutrient dynamics and availability in soil. Although phosphorus (P) is one of the main limiting nutrients in agricultural production, little is known about the influence of soil microorganisms on the dynamics of P cycling in subtropical land use systems. The objective was to assess the impacts of land use (organic farming, conventional farming and forest) on forms and distribution of P in soil. After conversion of forest, the P stock significantly increased by 373% and 170% in soil under organic farming at 0–10 and 10–20 cm depth, respectively. In conventional farming, the P stock increased by 64% and 36% at 0–10 cm and 10–20 cm depth, respectively compared to forest. The larger (up to 4 times) fraction of organic P (Po) than inorganic P (Pi) implies that total P is regulated by organic P. Easily-available P fractions (microbial biomass P, NaHCO3-Pi and Po), moderately available P (NaOH-Po) and non-available P (HCl-Pi and Po) were much higher in organic farming than conventional farming and forest, especially at the 0–10 cm depth. Compared to organic farming, the higher (>100) Corg: Po ratio that soils under conventional farming and forest are P limited which correspond with higher (2–8 times) activity of acid phosphatase in conventional farming and forest. Concluding, land use and management practices i.e. crop rotation, residue input and farmyard manure application significantly increase different fractions of P in organic farming.
Soil is a hierarchical, self-organizing, and emergent system that supports plant and microbial growth, enables carbon sequestration, facilitates water fluxes, and provide habitat for microorganisms, all of which depend on soil structure. Recent debates have generally reduced soil functioning to geometry and topology of soil solids and pores and denied the existence and role of soil aggregates and hierarchy of solids. Here we argue that soil structure has a dual nature that essentially boils down to the interlocking of pores and solids in groupings of specific complexity and dynamics called aggregates. By comparing their architectural, chemical, and energetic parameters, we conclude that aggregates have a much higher information density than pores. Therefore, aggregates (as unity of solids and pores) perform much broader range of functions compared to pores alone, especially in long-term. A set of soil functions corresponding to each level of the soil structure hierarchy depends on aggregate type (macroaggregates, water-stable aggregates, microaggregates, and elementary soil particles) determined by their specific binding energy, dynamics, and lifetime. The introduced here energy-based concept justifies the hierarchy of soil structure, and is the base for the soil structuring and carbon stabilization processes in their most general form. We understand the soil structure implying the energy-based approach: each hierarchy level corresponds to specific bonding strength of mineral and organic particles forming aggregates. Aggregate formation is a bottom-up process because the energy binding elementary soil particles and microaggregates is orders of magnitude higher than that gluing macroaggregates. The duality of soil structure is manifested not only in the relationship between pores and solids in aggregates, but also in the interactions and competition between the biological and non-biological processes that aggregate and disaggregate the structure. The view of the pore space as a transport pathway and habitat for soil living phase and plant roots, the solid-pore interface as a setting for physico-chemical and biological transformations, and aggregates as a result of these phenomena, provides a context for mechanistic understanding and process-based modeling of soil functions and health.