Crop residue management and oxalate‐extractable iron and aluminium explain long‐term soil organic carbon sequestration and dynamics

The management of crop residues affects carbon (C)-sequestration. This study aimed to identify the interaction between residue management and soil properties on C-sequestration. The hypothesis was that larger silt and clay contents and larger residue inputs enhance C-sequestration. The soil was sampled in Belgium in long-term (≥ 15 years) cropping systems with grain maize, Zea mays L. (all stover (leaves and stalks) returned), silage maize (all stover removed) or permanent grass. The fields sampled were distributed over two adjacent regions; one with sandy soil (33% silt + clay) and one with silty loam soil (71% silt + clay). The 13C abundance of the soil organic carbon (SOC) revealed that topsoil (0–30 cm) under grain maize contained more maize-derived SOC than that under silage maize (14 ± 1 and 9 ± 1 Mg C ha−1, respectively, P < 0.001, in sand, and 17 ± 1 and 14 ± 1 Mg C ha−1, respectively, P < 0.001, in silty loam). Total SOC stocks were unaffected by crop management, however, which suggests substitution of native SOC by fresh SOC derived from residues, especially in sandy soil where the silt and clay fraction is saturated with SOC. The maize-derived SOC stocks of the silty loam soil are 3.5–5.5 Mg C ha−1 larger than those of the sandy soil, which confirms the larger potential of the former to sequester C. Surprisingly, the native C3-SOC stocks in the sandy soil were 25–30 Mg C ha−1 larger than those of the silty loam soil. The concentration of SOC in the silt and clay fraction was on average three times larger for the sandy than for the silty loam soil. The concentration of oxalate-extractable Al and Fe in the same fraction was on average 2.5 times larger for sandy than for silty loam soil. Silt and clay-associated SOC correlated with the Fe + Al concentration across all regions and treatments (R2 = 0.62). This suggests that organo-mineral associations and the formation of organo-metal complexes promote C-sequestration in this temperate region. Highlights Different factors affect carbon stocks under two contrasting soils and four cropping systems. Returning maize residues promotes substitution of native soil organic carbon by maize-derived carbon. Organo-mineral interactions in the silt and clay fraction enhance carbon sequestration. The legacy of historical plaggen manuring has a strong effect on native soil carbon stocks.

[1]  Richard Webster,et al.  Regression and functional relations , 1997 .

[2]  C. Mörth,et al.  Characterization of iron(III) in organic soils using extended X-ray absorption fine structure spectroscopy. , 2008, Environmental science & technology.

[3]  D. R. Linden,et al.  Corn-Residue Transformations into Root and Soil Carbon as Related to Nitrogen, Tillage, and Stover Management , 2004 .

[4]  E. Ranst,et al.  The soil map of the Flemish region converted to the 3rd edition of the World Reference Base for soil resources , 2014 .

[5]  C. Campbell,et al.  Influence of fertilizer and straw baling on soil organic matter in a thin black chernozem in western Canada , 1991 .

[6]  P. M. Driessen,et al.  The major soils of the world , 1991 .

[7]  K. Paustian,et al.  Stabilization mechanisms of soil organic matter: Implications for C-saturation of soils , 2002, Plant and Soil.

[8]  Michael Zimmermann,et al.  Measured soil organic matter fractions can be related to pools in the RothC model , 2007 .

[9]  W. A. Adams,et al.  Iron oxyhydroxides in soils developed from lower palaeozoic sedimentary rocks in mid-wales and implications for some pedogenetic processes , 1984 .

[10]  H. Kirchmann,et al.  C-rich sandy Ap horizons of specific historical land-use contain large fractions of refractory organic matter , 2002 .

[11]  C. Clapp,et al.  Effects of Increasing Amounts of Organic Residues on Continuous Corn: II. Organic Carbon, Nitrogen, Phosphorus, and Sulfur1 , 1972 .

[12]  D. Reicosky,et al.  Long-Term Corn Residue Effects: Harvest Alternatives, Soil Carbon Turnover, and Root-Derived Carbon , 2004 .

[13]  Jones Arwyn,et al.  World reference base for soil resources 2014International soil classification system for naming soils and creating legends for soil maps , 2015 .

[14]  J. Neidhardt,et al.  Biodegradation of ferrihydrite-associated organic matter , 2014, Biogeochemistry.

[15]  R. Mendes R: The R Project for Statistical Computing , 2016 .

[16]  D. Reicosky,et al.  Continuous corn with moldboard tillage: Residue and fertility effects on soil carbon , 2002 .

[17]  R. Mikutta,et al.  Sorptive stabilization of organic matter by amorphous Al hydroxide , 2010 .

[18]  André Mariotti,et al.  Natural 13C abundance as a tracer for studies of soil organic matter dynamics , 1987 .

[19]  W. Wilson,et al.  EXTRACTABLE Fe, Al, Si AND C IN B HORIZONS OF PODZOLIC AND BRUNISOLIC SOILS FROM ONTARIO , 1985 .

[20]  Jean-Marc Jossart,et al.  Energy and CO2 balance of maize and grass as energy crops for anaerobic digestion. , 2008, Bioresource technology.

[21]  Deutsche Ausgabe World Reference Base for Soil Resources 2006 , 2007 .

[22]  P. E. Rasmussen,et al.  Crop Residue Influences on Soil Carbon and Nitrogen in a Wheat‐Fallow System , 1980 .

[23]  L. Giani,et al.  Properties of soil organic matter of Plaggic Anthrosols from Northwest Germany, Northwest and North Russia , 2009 .

[24]  Larry G. Bundy,et al.  Soil organic C in the tallgrass prairie-derived region of the corn belt: effects of long-term crop management , 1998 .

[25]  R. Cruse,et al.  Cropping System and Nitrogen Effects on Mollisol Organic Carbon , 1996 .

[26]  S. W. Melsted,et al.  CHANGES IN ORGANIC CARBON AND NITROGEN OF MORROW PLOT SOILS UNDER DIFFERENT TREATMENTS, 1904–1973 , 1984 .

[27]  D. R. Linden,et al.  Crop and Soil Productivity Response to Corn Residue Removal: A Literature Review , 2004 .

[28]  N. Breemen,et al.  Cryptopodzolic Soils in Switzerland , 1997 .

[29]  R. R. Allmaras,et al.  Long‐Term Corn Residue Effects , 2004 .

[30]  H. L. Kristensena,et al.  Mineralization and immobilization of nitrogen in heath soil under intact Calluna , after heather beetle infestation and nitrogen fertilization , 1999 .

[31]  R. H. Dowdy,et al.  Soil organic carbon and 13C abundance as related to tillage, crop residue, and nitrogen fertilization under continuous corn management in Minnesota. , 2000 .

[32]  F. J. Pierce,et al.  Impacts of agricultural management practices on C sequestration in forest-derived soils of the eastern Corn Belt , 1998 .

[33]  U. Schwertmann Differenzierung der Eisenoxide des Bodens durch Extraktion mit Ammoniumoxalat‐Lösung , 1964 .

[34]  J. Hassink,et al.  The capacity of soils to preserve organic C and N by their association with clay and silt particles , 1997, Plant and Soil.

[35]  T. F. Morris,et al.  Long-term effects of tillage and corn stalk return on soil carbon dynamics , 2005 .

[36]  R. Wagai,et al.  Sorptive stabilization of organic matter in soils by hydrous iron oxides , 2007 .

[37]  W. B. Voorhees,et al.  Crop and Soil Productivity Response to Corn Residue Removal: A Literature Review , 2004 .

[38]  Jürgen K. Friedel,et al.  Review of mechanisms and quantification of priming effects. , 2000 .