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RESEARCH ARTICLE

Shift in C and N humification during legume litter decomposition in an acid tropical Ferralsol

Jorge Sierra A C and Natacha Motisi B
+ Author Affiliations
- Author Affiliations

A INRA, UR1321 ASTRO Agrosystèmes Tropicaux, Petit-Bourg, F-97170, Guadeloupe, France.

B CIRAD, UPR URSIA Systèmes et Ingénierie Agronomique, Montpellier, F-34398, France; and Délégation du Cirad, Yaoundé, Cameroon.

C Corresponding author. Email: jorge.sierra@antilles.inra.fr

Soil Research 50(5) 380-389 https://doi.org/10.1071/SR12101
Submitted: 17 April 2012  Accepted: 18 June 2012   Published: 6 July 2012

Abstract

Several long-term studies on tropical soils have shown that legume residue incorporation increases soil nitrogen (N) sequestration more than that of carbon (C), resulting in a fall in the C/N ratio. This study was designed to assess the short-term effect of legume litter addition on N supply and the long-term effect on soil organic matter (SOM) formation and soil C/N decrease. The long-term effect was evaluated in a 2-year mesocosm experiment with high and frequent organic inputs from two types of legume litter with different C/N ratios, using stable isotope techniques. The short-term effect of litter was analysed using four different litters in 3-month laboratory incubations. A model of litter decomposition was used to describe C and N kinetics in the laboratory experiment and to verify whether the long-term effect of litter may be predicted from short-term incubations. The results of the mesocosm experiment confirmed that legume inputs increased soil organic N (mean +21%) more than organic C (mean +15%) (P = 0.05). Although no differences between litters were observed for C dynamics, N sequestration (14% and 28%) and the final soil C/N (12.0 and 10.8) varied with litter C/N (34.4 and 16.1, respectively). The laboratory experiment and model outputs confirmed these findings and indicated that the higher N sequestration was due to a change in the parameters describing humification of C and N coming from litter. This change depended on litter quality and was greater for litters with low C/N—C humification 0.66 g C g–1 C and N humification 0.76 g N g–1 N for litter C/N 16.1. Carbon and N sequestration were greater in the laboratory experiment, due to a higher mineralisation of the new SOM derived from litter in the mesocosm experiment—32% and 15% for the mesocosm and the laboratory experiments, respectively. Our results indicated that the decrease in soil C/N and the rapid mineralisation of new SOM should be considered in models of litter decomposition to respond correctly to the long- and the short-term effects of legume litter inputs in tropical soils.

Additional keywords: Canavalia ensiformis, C/N ratio, decomposition model, Gliricidia sepium, soil organic matter.


References

Abiven S, Recous S, Reyes V, Oliver R (2005) Mineralisation of C and N from root, stem and leaf residues in soil and role of their biochemical quality. Biology and Fertility of Soils 42, 119–128.
Mineralisation of C and N from root, stem and leaf residues in soil and role of their biochemical quality.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2MXhtFCrtLvP&md5=6f60940d069dd7b2132bb50fcf38452fCAS |

Allison SD, Wallesntein MD, Bradford MA (2010) Soil-carbon response to warming dependent on microbial physiology. Nature Geoscience 3, 336–340.
Soil-carbon response to warming dependent on microbial physiology.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC3cXlsFSksLY%3D&md5=408107746a60647f82161ab6921368e9CAS |

Baggie I, Zapata F, Sanginga N, Danso SKA (2000) Ameliorating acid infertile rice soil with organic residue from nitrogen fixing trees. Nutrient Cycling in Agroecosystems 57, 183–190.
Ameliorating acid infertile rice soil with organic residue from nitrogen fixing trees.Crossref | GoogleScholarGoogle Scholar |

Bjørnlund L, Christensen S (2005) How does litter quality and site heterogeneity interact on decomposer food webs of a semi-natural forest? Soil Biology & Biochemistry 37, 203–213.
How does litter quality and site heterogeneity interact on decomposer food webs of a semi-natural forest?Crossref | GoogleScholarGoogle Scholar |

Brisson N, Gary C, Justes E, Roche R, Mary B, Ripoche D, Zimmer D, Sierra J, Bertuzzi P, Burger P, Bussière F, Cabidoche YM, Cellier P, Debaeke P, Gaudillère JP, Maraux F, Seguin B, Sinoquet H (2003) An overview of the crop model STICS. European Journal of Agronomy 18, 309–332.
An overview of the crop model STICS.Crossref | GoogleScholarGoogle Scholar |

Chintu R, Zaharah AR, Wan Rasidah AK (2004) Decomposition and nitrogen release patterns of Paraserianthes falcataria tree residues under controlled incubation. Agroforestry Systems 63, 45–52.
Decomposition and nitrogen release patterns of Paraserianthes falcataria tree residues under controlled incubation.Crossref | GoogleScholarGoogle Scholar |

Corbeels M, McMurtrie RE, Pepper DA, O’Connell AM (2005) A process-based model of nitrogen cycling in forest plantations. Part I. Structure, calibration and analysis of the decomposition model. Ecological Modelling 187, 426–448.
A process-based model of nitrogen cycling in forest plantations. Part I. Structure, calibration and analysis of the decomposition model.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2MXhtVCnt7vM&md5=e68b07e299f3626d30c560acb25ef4f3CAS |

De Graaff MA, van Kessel C, Six J (2008) The impact of long-term elevated CO2 on C and N retention in stable SOM pools. Plant and Soil 303, 311–321.
The impact of long-term elevated CO2 on C and N retention in stable SOM pools.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1cXht1ShurY%3D&md5=d85f2664be64bef5b1b523075216124aCAS |

Diekow J, Mielniczuck J, Knicker H, Bayer C, Dick DP, Kögel-Knabner I (2005) Soil C and N stocks as affected by cropping systems and nitrogen fertilisation in a southern Brazil Acrisol managed under no-tillage for 17 years. Soil & Tillage Research 81, 87–95.
Soil C and N stocks as affected by cropping systems and nitrogen fertilisation in a southern Brazil Acrisol managed under no-tillage for 17 years.Crossref | GoogleScholarGoogle Scholar |

Dinesh R, Suryanarayana MA, Ghoshal Chaudhuri S, Sheeja TE (2004) Long-term influence of leguminous cover crops on the biochemical properties of a sandy clay loam Fluventic Sulfaquent in a humid tropical region of India. Soil & Tillage Research 77, 69–77.
Long-term influence of leguminous cover crops on the biochemical properties of a sandy clay loam Fluventic Sulfaquent in a humid tropical region of India.Crossref | GoogleScholarGoogle Scholar |

FAO (1988) ‘FAO/Unesco Soil Map of the World.’ World Soil Resources Report 60. (FAO: Rome)

Gijsman AJ, Hoogenboom G, Parton WJ, Kerridge PC (2002) Modifying DSSAT crop models for low-input agricultural systems using a soil organic matter-residue module from Century. Agronomy Journal 94, 462–474.
Modifying DSSAT crop models for low-input agricultural systems using a soil organic matter-residue module from Century.Crossref | GoogleScholarGoogle Scholar |

Hadas A, Kautsky L, Goek M, Kara EE (2004) Rates of decomposition of plant residues and available nitrogen in soil, related to residue composition through simulation of carbon and nitrogen turnover. Soil Biology & Biochemistry 36, 255–266.
Rates of decomposition of plant residues and available nitrogen in soil, related to residue composition through simulation of carbon and nitrogen turnover.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2cXmvFGrsA%3D%3D&md5=e35579fcf4f095062236e899fdef3477CAS |

Hartemink AE, O’Sullivan JN (2001) Leaf litter decomposition of Piper aduncum, Gliricidia sepium and Imperata cylindrical in the humid lowlands of Papua New Guinea. Plant and Soil 230, 115–124.
Leaf litter decomposition of Piper aduncum, Gliricidia sepium and Imperata cylindrical in the humid lowlands of Papua New Guinea.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3MXivFKjtLs%3D&md5=13d60ddcbf3838047b3e21d0d57e400fCAS |

Jensen LS, Salo T, Palmason F, Breland TA, Henriksen TM, Stenberg B, Pedersen A, Lundström C, Esala M (2005) Influence of biochemical quality on C and N mineralisation from a broad variety of plant materials in soil. Plant and Soil 273, 307–326.
Influence of biochemical quality on C and N mineralisation from a broad variety of plant materials in soil.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2MXks1Ojsbk%3D&md5=0da87cb8f0f61496f2ead8acbec58284CAS |

Lal R (2009) Challenges and opportunities in soil organic matter research. European Journal of Soil Science 60, 158–169.
Challenges and opportunities in soil organic matter research.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1MXkvVWntLo%3D&md5=203d95405069fe51e3f4ca6fc7d539ffCAS |

Lehmann J, Schroth G, Zech W (1995) Decomposition and nutrient release from leaves, twigs and roots of three alley-cropped tree legumes in central Togo. Agroforestry Systems 29, 21–36.
Decomposition and nutrient release from leaves, twigs and roots of three alley-cropped tree legumes in central Togo.Crossref | GoogleScholarGoogle Scholar |

Macdonald AJ, Murphy DV, Mahieu N, Fillery IRP (2007) Labile soil organic matter pools under a mixed grass/lucerne pasture and adjacent native bush in Western Australia. Australian Journal of Soil Research 45, 333–343.
Labile soil organic matter pools under a mixed grass/lucerne pasture and adjacent native bush in Western Australia.Crossref | GoogleScholarGoogle Scholar |

Manzoni S, Jackson RB, Trofymow JA, Porporato A (2008) The global stoichiometry of litter nitrogen mineralisation. Science 321, 684–686.
The global stoichiometry of litter nitrogen mineralisation.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1cXptVKnurk%3D&md5=622901c28b5920557e3d9f56e919637dCAS |

Nicolardot B, Recous S, Mary B (2001) Simulation of C and N mineralisation during crop residue decomposition: a simple dynamic model based on the C:N ratio of the residues. Plant and Soil 228, 83–103.
Simulation of C and N mineralisation during crop residue decomposition: a simple dynamic model based on the C:N ratio of the residues.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3MXhtlWkurs%3D&md5=714fef7179e9324937aee573f0e837a8CAS |

Nygren P, Cruz P, Domenach AM, Vaillant V, Sierra J (2000) Influence of forage harvesting regimes on dynamics of biological dinitrogen fixation of a tropical woody legume. Tree Physiology 20, 41–48.
Influence of forage harvesting regimes on dynamics of biological dinitrogen fixation of a tropical woody legume.Crossref | GoogleScholarGoogle Scholar |

Palm CA, Gachengo CN, Delve RJ, Cadisch G, Giller KE (2001) Organic inputs for soil fertility management in tropical agroecosystems: application of an organic resource database. Agriculture, Ecosystems & Environment 83, 27–42.
Organic inputs for soil fertility management in tropical agroecosystems: application of an organic resource database.Crossref | GoogleScholarGoogle Scholar |

Payne WJ (1970) Energy yields and growth of heterotrophs. Annual Review of Microbiology 24, 17–52.
Energy yields and growth of heterotrophs.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaE3MXjvFCmtw%3D%3D&md5=0853cd92e9815d5ccc6dfdc993b2ca6dCAS |

Recous S, Robin D, Darwis D, Mary B (1995) Soil inorganic availability: effect on maize residue decomposition. Soil Biology & Biochemistry 27, 1529–1538.
Soil inorganic availability: effect on maize residue decomposition.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK2MXhtVSntrbO&md5=fb2e3a02fd01ad095ad41d3ed290cc31CAS |

Resh SC, Binkley D, Parrotta JA (2002) Greater soil carbon sequestration under nitrogen-fixing trees compared with Eucalyptus species. Ecosystems 5, 217–231.
Greater soil carbon sequestration under nitrogen-fixing trees compared with Eucalyptus species.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD38Xks1Omu7c%3D&md5=836bbbd6dc641dd9e178730f710218d0CAS |

Sall S, Bertrand I, Chotte JL, Recous S (2007) Separate effects of the biochemical quality and N content of crop residues on C and N dynamics in soil. Biology and Fertility of Soils 43, 797–804.
Separate effects of the biochemical quality and N content of crop residues on C and N dynamics in soil.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2sXntlajs7g%3D&md5=70856fa1b129f08d94f7a488d7a06f69CAS |

Sierra J (2006) A hot-spot approach applied to nitrification in tropical acid soils. Soil Biology & Biochemistry 38, 644–652.
A hot-spot approach applied to nitrification in tropical acid soils.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD28XivVaqsb8%3D&md5=b26cecb1fb84d8bf3981647ef9728f2eCAS |

Sierra J, Desfontaines L (2011) Factors affecting apparent 15N fractionation during N mineralization in soils with different root litter inputs. Soil Research 49, 34–43.
Factors affecting apparent 15N fractionation during N mineralization in soils with different root litter inputs.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC3MXit1Wgu7w%3D&md5=51e5687cb5a2383a2d1609dc72f6aa44CAS |

Sierra J, Marbán L (2000) Nitrogen mineralization pattern of an Oxisol of Guadeloupe, French West Indies. Soil Science Society of America Journal 64, 2002–2010.
Nitrogen mineralization pattern of an Oxisol of Guadeloupe, French West Indies.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3MXhsFSlsQ%3D%3D&md5=e30b8ab19be0946f128148e017b8fc0cCAS |

Sierra J, Nygren P (2005) Role of root inputs from a dinitrogen-fixing tree in soil carbon and nitrogen sequestration in a tropical agroforestry system. Australian Journal of Soil Research 43, 667–675.
Role of root inputs from a dinitrogen-fixing tree in soil carbon and nitrogen sequestration in a tropical agroforestry system.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2MXntVWjsrg%3D&md5=bb902d5d1414c81af2b7d8e21547ceabCAS |

Sierra J, Brisson N, Ripoche D, Noël C (2003) Application of the STICS crop model to predict nitrogen availability and nitrate transport in a tropical acid soil cropped with maize. Plant and Soil 256, 333–345.
Application of the STICS crop model to predict nitrogen availability and nitrate transport in a tropical acid soil cropped with maize.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3sXotV2jtrg%3D&md5=225a84e7cd1b37ca437b9f3b15ed2f33CAS |

Sierra J, Brisson N, Ripoche D, Déqué M (2010) Modelling the impact of thermal adaptation of soil microorganisms and crop system on the dynamics of organic matter in a tropical soil under a climate change scenario. Ecological Modelling 221, 2850–2858.
Modelling the impact of thermal adaptation of soil microorganisms and crop system on the dynamics of organic matter in a tropical soil under a climate change scenario.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC3cXht1ems7zL&md5=dcd650d4c63447824546d704ac7a24c1CAS |

Tian G, Brussaard L, Kang BT (1995) An index for assessing the quality of plant residues and evaluating their effects on soil and crop in the subhumid tropics. Applied Soil Ecology 2, 25–32.
An index for assessing the quality of plant residues and evaluating their effects on soil and crop in the subhumid tropics.Crossref | GoogleScholarGoogle Scholar |

Trinsoutrot I, Recous S, Bentz B, Linères M, Chèneby D, Nicolardot B (2000) Biochemical quality of crop residues and carbon and nitrogen mineralization kinetics under nonlimiting nitrogen conditions. Soil Science Society of America Journal 64, 918–926.
Biochemical quality of crop residues and carbon and nitrogen mineralization kinetics under nonlimiting nitrogen conditions.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3cXms1equ7w%3D&md5=b6df52611c4324cc66cc25f77da3fd08CAS |

van Oort F (1988) Présence et évolution des minéraux argileux accessoires de type 2 : 1 dans les sols ferrallitiques d’origine volcanique de la Guadeloupe. Comptes Rendus de l’Académie des Sciences 307, 1297–1302.

Van Soest PJ (1963) Use of detergents in the analyses of fibrous feeds. I: preparation of fiber residues of low nitrogen content. Journal - Association of Official Analytical Chemists 46, 825–835.

Wang WJ, Baldock JA, Dalal RC, Moody PW (2004) Decomposition dynamics of plant materials in relation to nitrogen availability and biochemistry determined by NMR and wet-chemical analysis. Soil Biology & Biochemistry 36, 2045–2058.
Decomposition dynamics of plant materials in relation to nitrogen availability and biochemistry determined by NMR and wet-chemical analysis.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD2cXos1ejsbk%3D&md5=03b3f8e7d8bec555dc1745f6b4ea287fCAS |

Whitmore AP (2007) Describing the transformation of organic carbon and nitrogen in soil using the MOTOR system. Computers and Electronics in Agriculture 55, 71–88.
Describing the transformation of organic carbon and nitrogen in soil using the MOTOR system.Crossref | GoogleScholarGoogle Scholar |

Zaharah AR, Bah AR (1999) Patterns of decomposition and nutrient release by fresh Gliricidia (Gliricidia sepium) leaves in an ultisol. Nutrient Cycling in Agroecosystems 55, 269–277.
Patterns of decomposition and nutrient release by fresh Gliricidia (Gliricidia sepium) leaves in an ultisol.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD3cXisVCjsA%3D%3D&md5=bdb958aecacd5e6b7d4b1e282ebd6eb7CAS |

Zaharah AR, Bah AR, Mwange NK, Kathuli P, Juma P (1999) Management of Gliricidia (Gliricidia sepium) residues for improved sweet corn yield in an ultisol. Nutrient Cycling in Agroecosystems 54, 31–39.
Management of Gliricidia (Gliricidia sepium) residues for improved sweet corn yield in an ultisol.Crossref | GoogleScholarGoogle Scholar |

Zheng DW, Ågren GI, Bengtsson J (1999) How do soil organisms affect total organic nitrogen storage and substrate nitrogen to carbon ratio in soils? Oikos 86, 430–442.
How do soil organisms affect total organic nitrogen storage and substrate nitrogen to carbon ratio in soils?Crossref | GoogleScholarGoogle Scholar |