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Crop and Pasture Science Crop and Pasture Science Society
Plant sciences, sustainable farming systems and food quality
RESEARCH ARTICLE

Chemical composition of cover plants and its effect on maize yield in no-tillage systems in the Brazilian savanna

A. M. de Carvalho A , M. C. Coelho B , R. A. Dantas B , O. P. Fonseca B , R. Guimarães Júnior A and C. C. Figueiredo B C
+ Author Affiliations
- Author Affiliations

A Embrapa, Cerrados Agricultural Research Center, 73310970 Planaltina, DF, Brazil.

B University of Brasília, Campus Universitário Darcy Ribeiro, 70910-900 Brasília, DF, Brazil.

C Corresponding author. Email: cicerocf@unb.br

Crop and Pasture Science 63(12) 1075-1081 https://doi.org/10.1071/CP12272
Submitted: 25 July 2012  Accepted: 9 December 2012   Published: 8 February 2013

Abstract

The use of cover plants is an important agricultural practice in no-tillage systems. Soil cover and nutrient recycling depend on the dynamics of plant residue decomposition. The objective of this study was to evaluate the effect of the chemical composition and decomposition rates of cover plants on maize yield in no-tillage systems in the savannah, central Brazil. Levels of hemicellulose, cellulose, and lignin, along with decomposition rates of the following plant species were determined at flowering and maturation: Urochloa ruziziensis, Cajanus cajan, Canavalia brasiliensis, Crotalaria juncea, Mucuna aterrima, Pennisetum glaucum, Raphanus sativus, Sorghum bicolor, and Triticum aestivum. Spontaneous vegetation growth in the fallow was used as a control. The highest dry matter yields were obtained from Sorghum bicolor, followed by P. glaucum, when harvested at maturation. Canavalia brasiliensis and U. ruziziensis, the species with lowest lignin levels, presented faster decomposition and lower half-life values compared with the residues of C. cajan and S. bicolor. Cover plants with the lowest lignin concentrations, and thus the fastest residue decomposition rates, such as C. brasiliensis, U. ruziziensis, and P. glaucum, resulted in higher maize yields. Urochloa ruziziensis and C. brasiliensis contributed to nutrient recycling due to their faster decomposition, while C. cajan aids in the formation of soil cover due to slower decomposition of its residues.

Additional keywords: decomposition, lignin, nutrient cycling, organic matter.


References

Addinsoft (2011) ‘XLSTAT 2011: statistical software to MS Excel.’ (Addinsoft: New York)

Aita C, Giacomini SJ (2003) Crop residue decomposition and nitrogen release in single and mixed cover crops. Brazilian Journal of Soil Science 27, 601–612 [In Portuguese with English abstract].

Correia MEF, Andrade AG (2008) Formação de serapilheira e ciclagem de nutrientes. In ‘Fundamentos da matéria orgânica do solo: ecossistemas tropicais e subtropicais’. (Ed. GA Santos) pp. 137–158. (Metrópole: Porto Alegre, Brazil)

Coulter JA, Nafziger ED, Wander M (2009) Soil organic matter response to cropping system and nitrogen fertilization. Agronomy Journal 101, 592–599.
Soil organic matter response to cropping system and nitrogen fertilization.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1MXmt1Wgsbc%3D&md5=ebda2602a74cb244ea52a61acca7f826CAS |

de Carvalho AM, Amabile RF (2006) Plantas condicionadoras de solo: interações edafoclimáticas, uso e manejo. In ‘Cerrado: adubação verde’. (Eds AM de Carvalho, RF Amabile) pp. 143–170. (Embrapa Cerrados: Planaltina, Brazil)

de Carvalho AM, Bustamante MMC, de Alcântara FA, Resck IS, Lemos SS (2009) Characterization by solid-state CPMAS 13C NMR spectroscopy of decomposing plant residues in conventional and no-tillage systems in Central Brazil. Soil & Tillage Research 101, 100–107.

de Carvalho AM, Souza LLP, Guimarães R, Alves PCAC, Vivaldi JL (2011) Cover plants with potential use for crop-livestock integrated systems in the Cerrado region. Brazilian Journal of Agricultural Research 26, 1200–1205.

Embrapa (2006) ‘Brazilian System of Soil Classification.’ (National Research Center for Soils: Rio de Janeiro, Brazil)

Fox RH, Myers RJK, Vallis I (1990) The nitrogen mineralization rate of legume in soil as influenced by their polyphenol, lignin and nitrogen contents. Plant and Soil 129, 251–259.

Gunnarsson S, Marstop H, Dahlin AS, Witter E (2008) Influence of non-cellulose structural carbohydrate composition on plant material decomposition in soil. Biology and Fertility of Soils 45, 27–36.
Influence of non-cellulose structural carbohydrate composition on plant material decomposition in soil.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BD1cXhtF2gs7bF&md5=58752e1f6cb9e4cc4e87f9d7b5b51f3fCAS |

Hollinger SE, Bernacchi CJ, Meyers TP (2005) Carbon budget of mature no-till ecosystem in North Central Region of the United States. Agricultural and Forest Meteorology 130, 59–69.
Carbon budget of mature no-till ecosystem in North Central Region of the United States.Crossref | GoogleScholarGoogle Scholar |

Isbell RF (2002) ‘The Australian Soil Classification.’ Revised edn. (CSIRO Publishing: Melbourne)

Johnson JMF, Barbour NW, Weyers SL (2007) Chemical composition of crop biomass impacts its decomposition. Soil Biology & Biochemistry 71, 155–162.

Leite LFC (2009) Plantio direto é o mais eficaz no sequestro de carbono. Meio ambiente Monsanto em campo Newsletter September 2009. Monsanto Company, São Paulo, Brazil. Available at: www.monsanto.com.br/monsanto/brasil/newsletter/geral/06_2009Setembro/meioambiente.asp

Machado LAZ, Assis PGG (2010) Straw and forage production of annual and perennial species in succession to soybean. Brazilian Journal of Agricultural Research 45, 415–442 [In Portuguese with English abstract].

Machado PLOA, Silva CA (2001) Soil management under no-tillage systems in the tropics with special reference to Brazil. Nutrient Cycling in Agroecosystems 61, 119–130.
Soil management under no-tillage systems in the tropics with special reference to Brazil.Crossref | GoogleScholarGoogle Scholar |

Marchão RL, Lavelle P, Celini L, Balbino LC, Vilela L, Becquer T (2009) Soil macrofauna under integrated crop–livestock systems in a Brazilian Cerrado Ferralsol. Brazilian Journal of Agricultural Research 44, 1011–1020.

Muhr L, Tarawali SA, Peters M, Schultzekraft R (1999) Forage legumes for improved fallows in agropastoral systems of subhumid West Africa. I. Establishment, herbage yield and nutritive value of legumes as dry season forage. Tropical Grasslands 33, 222–233.

Reinertsen AS, Elliott LF, Cochran VL, Campbell GS (1984) The role of available C and N in determining the rate of wheat straw decomposition. Soil Biology & Biochemistry 16, 459–464.
The role of available C and N in determining the rate of wheat straw decomposition.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaL2MXksFSisA%3D%3D&md5=7ad8263aa370d154389758f8232c3717CAS |

Rheinheimer DS, Anghinoni I, Conte E (2000) Phosphorus in the microbial biomass in soils under different management systems. Brazilian Journal of Soil Science 24, 589–597 [In Portuguese with English abstract].

Robertson JB, Van Soest PJ (1981) The detergent system of analysis and its application to human’s foods. In ‘The analysis of dietary fiber in food’. (Eds HPT James, O Theander) pp. 123–158. (Marcel Dekker: New York)

Sano EE, Rosa R, Brito JLS, Ferreira JR (2010) Land cover mapping of the tropical savanna region in Brazil. Environmental Monitoring and Assessment 166, 113–124.
Land cover mapping of the tropical savanna region in Brazil.Crossref | GoogleScholarGoogle Scholar |

Santos PF, Whitford WG (1981) The effects of microarthropods on litter decomposition in a Chihuazhuan ecosystem. Ecology 62, 654–663.
The effects of microarthropods on litter decomposition in a Chihuazhuan ecosystem.Crossref | GoogleScholarGoogle Scholar |

SAS Institute (2000) ‘SAS/STAT: User’s guide, version 8.1’. p. 943. (SAS Institute: Cary, NC)

Sodré Filho J, Cardoso NA, Carmona R, Carvalho AM (2004) Phytomass and soil cover of sequential crops after maize in Cerrado region. Brazilian Journal of Agricultural Research 39, 327–334 [In Portuguese with English abstract].

Soil Survey Staff (2006) ‘Keys to Soil Taxonomy’. p. 332. (USDA-SCS: Washington, DC)

Talbot JM, Yelle DJ, Nowick J, Treseder KK (2012) Litter decay rates are determined by lignin chemistry. Biogeochemistry 108, 279–295.
Litter decay rates are determined by lignin chemistry.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC38XivFOnsbk%3D&md5=e65be24ec3b421b016c16b4ee63f8f5eCAS |

Tian G, Kang BT, Brussaard L (1992) Biological effects of plant residues with contrasting chemical compositions under humid tropical conditions – decomposition and nutrient release. Soil Biology & Biochemistry 24, 1051–1060.
Biological effects of plant residues with contrasting chemical compositions under humid tropical conditions – decomposition and nutrient release.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK3sXmtF2k&md5=386cceb05ac7fbb75f613a7afa1bfe25CAS |

Vanlauwe B, Nwoke OC, Saginga N, Merckx R (1996) Impact of residue quality on the C and N mineralization of leaf and root residues of three agroforestry species. Plant and Soil 183, 221–231.
Impact of residue quality on the C and N mineralization of leaf and root residues of three agroforestry species.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK2sXlsValtg%3D%3D&md5=8042f36862e4d2d33c311fcf872155adCAS |

Wagner GH, Wolf DC (1999) Carbon transformations and soil organic matter formation. In ‘Principles and applications of soil microbiology’. (Eds DM Sylvia, JJ Fuhrmann, PG Hartel, DA Zuberer) pp. 218–256. (Prentice Hall: Upper Saddle River, NJ)