Abstract:Sandy cropland soils in NW Europe were found to contain unusually high organic-carbon (OC) levels, and a link with their land-use history has been suggested. This study's aim was to assess the discriminating power of physical and chemical fractionation procedures to yield information on soil-organic-matter (OM) stability for these soils. In relict-and cultivated-heathland soils, much higher proportions of 6% NaOCl treatment-resistant but 10% HF-soluble OC (MOC) and N (32.2% and 29.9%) were measured compared to… Show more
“…These differences were also confirmed for a larger soil set studied by Sleutel et al (2010). Differences in N content ofthe physical fractions were smaller and insignificant.…”
Section: Organic Carbon and Nitrogen Distribution Over Isolated Size supporting
confidence: 71%
“…Both were commonly practiced over centuries in Northwest Europe from Schleswig-Holstein to Belgium (Blume and Leinweber, 2004). Studies employing incubation experiments, physical and chemical fractionation methods (Springob and Kirchmann, 2002;Sleutel et al, 2010) and detailed spectroscopic characterizations (Sleutel et al, 2008) have confirmed both the similarity in soil OM stability of relict and cultivated heathlands on the one hand, and the lower stability of soil OM in sandy cropland soils without this historical land use on the other. Specifically, lipids, sterols and to a lesser extent N-containing compounds were selectively preserved from previous heathland land-use (Sleutel et al, 2008).…”
mentioning
confidence: 68%
“…Specifically, lipids, sterols and to a lesser extent N-containing compounds were selectively preserved from previous heathland land-use (Sleutel et al, 2008). In addition, the high OM loadings of the claysized fraction (Sleutel et al, 2010) suggested more than 'mono-OM-layer-equivalent' covering of soil particles, that is, an OM loading equivalent to what would be expected for a single layer of moderately sized organic molecules. Because variation in organicmineral particle density may reflect variations in the thickness of organic accumulations (SoUins et al, 2006) we hypothesize that such thick OM layered particles are preferentially fractionated in lower density clay fractions.…”
Land-use history is often overlooked when assessing soil fertility of intensive cropland production systems. The unusually high organic carbon (OC) content of many sandy cropland soils in Northwestern Europe is unexpected given their general low clay content (3-8%) and organic matter (OM) input typical of cropland, but appears to be related to historical heathland land-use. Clay fraction OM composition was compared between two groups of sandy cropland soils with (HC) or without (CC) a history of heathland/forest land-use. Light ( 1.6-2.2 gem"') and heavy (>2.2 gem"') clay fractions in HC soils were nearly twice as rich in OC (on average 199 g kg"') compared with those of CC soils (on average 109 g kg" '). The hypothesized preferential presence of stable heathland derived OM in hght soil fractions, was not supported by our data. Pyrolysis-field ionization mass spectrometty of the clay fractions revealed a more decomposed character of OM in the CC soils and lasting long-term influence of land-use history on SOM composition. This could be concluded from higher proportions of lipids and sterols, a lower thermostability in the HC compared with the CC soils, and enrichment of alkylaromatics and heterocyclic N-containing compounds in the latter. The density fractionation methodology separated organic-mineral particles with similar OM loadings but lower proportions of sterols and medium to long-chained lipids in the heavy compared with the light clay fraction. Given the very high clay OC loadings (6-1 é mg C m"') and low binding capacity ofthe quartz/kaolinite/mica dominated clays, we hypothesize that OM-OM interactions are involved as an OM stabilization mechanism. However, contrary to our hypothesis high clay OC loading (and hence thick OM layering) were found in all sandy croplands regardless of land-use history or density fraction.
“…These differences were also confirmed for a larger soil set studied by Sleutel et al (2010). Differences in N content ofthe physical fractions were smaller and insignificant.…”
Section: Organic Carbon and Nitrogen Distribution Over Isolated Size supporting
confidence: 71%
“…Both were commonly practiced over centuries in Northwest Europe from Schleswig-Holstein to Belgium (Blume and Leinweber, 2004). Studies employing incubation experiments, physical and chemical fractionation methods (Springob and Kirchmann, 2002;Sleutel et al, 2010) and detailed spectroscopic characterizations (Sleutel et al, 2008) have confirmed both the similarity in soil OM stability of relict and cultivated heathlands on the one hand, and the lower stability of soil OM in sandy cropland soils without this historical land use on the other. Specifically, lipids, sterols and to a lesser extent N-containing compounds were selectively preserved from previous heathland land-use (Sleutel et al, 2008).…”
mentioning
confidence: 68%
“…Specifically, lipids, sterols and to a lesser extent N-containing compounds were selectively preserved from previous heathland land-use (Sleutel et al, 2008). In addition, the high OM loadings of the claysized fraction (Sleutel et al, 2010) suggested more than 'mono-OM-layer-equivalent' covering of soil particles, that is, an OM loading equivalent to what would be expected for a single layer of moderately sized organic molecules. Because variation in organicmineral particle density may reflect variations in the thickness of organic accumulations (SoUins et al, 2006) we hypothesize that such thick OM layered particles are preferentially fractionated in lower density clay fractions.…”
Land-use history is often overlooked when assessing soil fertility of intensive cropland production systems. The unusually high organic carbon (OC) content of many sandy cropland soils in Northwestern Europe is unexpected given their general low clay content (3-8%) and organic matter (OM) input typical of cropland, but appears to be related to historical heathland land-use. Clay fraction OM composition was compared between two groups of sandy cropland soils with (HC) or without (CC) a history of heathland/forest land-use. Light ( 1.6-2.2 gem"') and heavy (>2.2 gem"') clay fractions in HC soils were nearly twice as rich in OC (on average 199 g kg"') compared with those of CC soils (on average 109 g kg" '). The hypothesized preferential presence of stable heathland derived OM in hght soil fractions, was not supported by our data. Pyrolysis-field ionization mass spectrometty of the clay fractions revealed a more decomposed character of OM in the CC soils and lasting long-term influence of land-use history on SOM composition. This could be concluded from higher proportions of lipids and sterols, a lower thermostability in the HC compared with the CC soils, and enrichment of alkylaromatics and heterocyclic N-containing compounds in the latter. The density fractionation methodology separated organic-mineral particles with similar OM loadings but lower proportions of sterols and medium to long-chained lipids in the heavy compared with the light clay fraction. Given the very high clay OC loadings (6-1 é mg C m"') and low binding capacity ofthe quartz/kaolinite/mica dominated clays, we hypothesize that OM-OM interactions are involved as an OM stabilization mechanism. However, contrary to our hypothesis high clay OC loading (and hence thick OM layering) were found in all sandy croplands regardless of land-use history or density fraction.
“…Within the here studied loess soils, humus class became as important as the clay contents. This did not apply to sandy soils, probably due to relatively high amounts of relatively stable SOM in podzolized sandy arable soils with very low clay contents (Sleutel et al 2010;Springob and Kirchmann 2002).…”
Avoiding surplus N fertilization without reducing crop yields could be accomplished by accounting for current net N mineralization in N fertilizer recommendations. N simulation models would allow a quantitative consideration of important factors and could be based upon digitally mapped data. Soil-specific temperature and water functions that were derived in part I of the paper needed a differentiation between only three soil groups and the two allocating criteria were taken from digital soil maps. Here, the objectives were to experimentally determine pedotransfer functions (PTFs) for the pool sizes of two organic N pools (N fast , N slow ) that could be calculated via digitally available data and need a minimum set of easily accessible management data. Interestingly, most important input data for the PTFs of both pool sizes were mean clay contents of the texture class (German soil classification system). However, the underlying mechanisms might be different, as N slow could be positively influenced by clay-associated mineralizable SOM, whereas N fast could be positively related to clay content due to higher yield potential and thus more residues on finertextured soils. For N slow including the humus class improved the accuracy of the PTF (r 2 = 0.60; P \ 0.050). For N fast it was important to include a negative influence of the mean fall temperature of the preceding year (r 2 = 0.42; P \ 0.010), probably due to its influence on residue degradation before winter. Surprisingly, easily accessible management data, e.g. previous crop, did not improve the predictions in this study. Field studies with plant cover will have to further prove the applicability of the derived PTFs.
“…Corroborating our findings, in the Cerrado region, a 49 % difference in the clay content between two soils was responsible for a 46 % reduction in soil organic carbon (SOC) losses when the native vegetation was converted to conventional tillage systems (Dieckow et al, 2009). The lower aggregation capacity, specific surface, and charge density in sandy soils make soil C biochemistry properties of fundamental importance to SOC preservation over time (Sleutel et al, 2010). Remarkably, after three years of residue removal, δ 13 C-POM was less negative than initially recorded in the West region (Table 2), indicating a selective preservation of C derived from C 4 plants.…”
Eucalyptus forests in southern Bahia (BA) are planted in soils with a sandy surface layer and humid tropical climate, conditions that lead to soil carbon (C) decomposition. Recent studies have shown that nitrogen (N) may be important for soil C stabilization. The aim of this study was to evaluate the contribution of Eucalyptus harvest residues and nitrogen fertilization to C stabilization in Ultisols of southern BA. The experiment was conducted in Eucalyptus clonal plantations cultivated in two regions of Eunápolis, BA, Brazil, with different clay content: southern region (140 g kg -1 of clay) and western region (310 g kg -1 of clay). Five treatments were evaluated: one control (CTR), without Eucalyptus harvest residues and N fertilization, and four treatments with harvest residues combined with four rates of N fertilization: 0, 25, 50, and 100 kg ha N) of particulate organic matter (POM) and mineral-associated organic matter (MAOM) were determined. In the southern region after 36 months, the C-MAOM stocks in the 0.00-0.10 m layer of the CTR decreased by 33 %. The addition of harvest residue followed by 100 kg ha -1 N increased C-POM and N-POM stocks (0.00-0.10 m) compared to the CTR, and the final N-POM stocks and residue-C recovery in the surface soil layer were positively correlated with the increase in N fertilization rates. In the western region, residue maintenance resulted in increased C-MAOM stocks (0.00-0.10 m) compared to the CTR, but an increase in N availability reduced this increment. The increase in N fertilization rates did not alter C stocks, but reduced N stocks of POM and MAOM in the upper soil layer. At the end of the experiment, N fertilizer recovery (0.00-0.60 m) was similar among the regions evaluated. In soil with lower clay content, higher N availability led to higher C and N stocks in the particulate fraction. In soils with high clay content, physical and chemical protections are more important than N fertilization for soil C stabilization, and just maintaining harvest residues may suffice to increase C and N in the more stable SOM fraction.
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