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No abstract is provided for this article.
Crop residues and manure are important sources of carbon (C) for soil organic matter (SOM) formation. Crop residue return increases by nitrogen (N) fertilization because of higher plant productivity, but this often results only in minor increases of SOM. In our study, we show how N fertilization and organic C additions affected SOM and its fractions within a 32‐year‐long field‐experiment at Puch, Germany. Five organic additions, no‐addition (control), manure, slurry, straw and straw + slurry, were combined with three mineral N fertilization rates (no, medium and high fertilization), which resulted in 1·17–4·86 Mg C‐input ha ‐1 y ‐1 . Topsoil (0–25 cm) SOM content increased with N fertilization, mainly because of the C in free light fraction (f‐LF). In contrast, subsoil (25–60 cm) SOM decreased with N fertilization, probably because of roots' relocation in Ap horizon with N fertilization at the surface. Despite high inputs, straw contributed little to f‐LF but prevented C losses from the mineral‐associated SOM fraction ( ρ > 1·6 g cm ‐3 ) with N fertilization, which was observed without straw addition. Above (straw) and belowground (roots) residues had opposite effects on SOM fractions. Root C retained longer in the light‐fractions and was responsible for SOM increase with N fertilization. Straw decomposed rapidly (from f‐LF) and fueled the mineral‐associated SOM fraction. We conclude that SOM content and composition depended not only on residue quantity, which can be managed by the additions and N fertilization, but also on the quality of organics. This should be considered for maintaining the SOM level, C sequestration, and soil fertility. Copyright © 2016 John Wiley & Sons, Ltd.
No abstract is provided for this article.
No abstract is provided for this article.
In calcareous parent material, pedogenic carbonate formation mostly involves dissolution and recrystallization of lithogenic carbonates with CO2 of soil air, leading to a complete exchange of lithogenic carbon with soil-derived carbon. Interest in pedogenic carbonates has increased in recent decades because they are a useful tool for reconstructing paleoclimatic conditions (δ 13C and δ 18O) and past atmospheric CO2 concentrations as well as for radiocarbon dating of soils. For such investigations, the recrystallization rate of primary CaCO3 by pedogenic carbonate formation and the dependence of the recrystallization rate on environmental factors are essential, but still unquantified factors. The recrystallization rate of primary CaCO3 of loess at three CO2 concentrations was estimated by isotopic exchange between primary CaCO3 and the 14C of artificially labeled CO2. Loess was used for the study as a parent substrate for soil formation to simulate initial rates of CaCO3 recrystallization. CO2 concentrations of 380ppm, 5000ppm and 50,000ppm lead to recrystallization rates of 4.1·10−7 day−1, 8.1·10−7 day−1 and 16.9·10−7 day−1, respectively. The relation between CO2 concentrations and recrystallization rates was described by a saturation curve. Under the tested experimental conditions, complete (95%) recrystallization of loess carbonate and formation of pedogenic carbonate would take 4.9–20.0·103 years, strongly depending on CO2 concentration. We expect faster recrystallization rates under field conditions because of permanent CO2 supply by root and rhizomicrobial respiration. This impedes the equilibrium between the inorganic C pools in solid, liquid and gaseous phases.
Assessment of soil health requires complex evaluation of properties and functions responsible for a broad range of ecosystem services. Numerous soil quality indices (SQI) have been suggested for the evaluation of specific groups of soil functions, but comparison of various SQI is impossible because they are based on a combination of specific soil properties. To avoid this problem, we suggest an SQI-area approach based on the comparison of the areas on a radar diagram of a combination of chemical, biological and physical properties. The new approach is independent of the SQI principle and allows rapid and simple comparison of parameter groups and soils. Another approach analyzing the resistance and sensitivity of properties to degradation is suggested for a detailed evaluation of soil health. The resistance and sensitivity of soil properties are determined through comparison with the decrease of soil organic carbon (SOC) as a universal parameter responsible for many functions. The SQI-area and resistance/sensitivity approaches were tested based on the recovery of Phaeozems and Chernozems chronosequences after the abandonment of agricultural soils. Both the SQI-area and the resistance/sensitivity approaches are useful for basic and applied research, and for decision-makers to evaluate land-use practices and measure the degree of soil degradation.
Most studies of soil organic‐carbon (SOC) dynamics using 13 C natural abundance have been conducted with maize. Here, we present data about the sequestration of C derived from a perennial C 4 plant, Miscanthus × giganteus (Greef et Deu.) grown on loamy and sandy soils for 9 and 12 y, respectively. We expected a higher contribution of Miscanthus ‐derived C to SOC formation compared to maize because of (1) higher net biomass production by Miscanthus , (2) lower shoot‐to‐root ratio, (3) deeper roots, and (4) the absence of plowing. In both soils, there was a significant contribution of Miscanthus ‐derived C down to 1 m soil depth. The maximal contents of 3.0 g C 4 ‐C (kg soil) –1 and 2.4 g C 4 ‐C (kg soil) –1 for loamy and sandy soil, respectively, were observed for the upper 0–10 cm layer. The decline in the amount of Miscanthus ‐derived C with soil depth was significant for both soils, but without significant differences between the differently textured soils except the depth of 0–10 cm. The total SOC was similar under Miscanthus and under reference grassland in the sandy soil (both 6.4 kg C m –2 down to 1 m soil depth). Amounts of SOC were slightly higher under grassland at the loamy site (12.1 kg C m –2 compared with 11.2 kg C m –2 ). So, C accumulation under Miscanthus was similar to that under perennial grasses. After 9 and 12 y, respectively, the yearly incorporation of Miscanthus ‐C in SOC of the upper 0–30 cm was 0.23 g C 4 ‐C (kg soil) –1 y –1 in the loamy and 0.11 g C 4 ‐C (kg soil) –1 y –1 in the sandy soil. This C 4 ‐C incorporation in loamy soil under Miscanthus was 1.6–1.8 times higher than results reported for maize C 4 ‐C incorporation in SOC grown under similar climatic conditions. In the sandy soil, the C 4 ‐C incorporation under Miscanthus was nearly the same as under maize. The fraction of 22% of the Miscanthus residues remaining in SOC was similar to that one of maize residues in loamy soil. In sandy soil, only a small fraction of 9% of the Miscanthus residues was incorporated in SOC.