Use of the15N natural abundance technique for the quantification of the contribution of N2 fixation to sugar cane and other grasses

2001 ◽  
Vol 28 (9) ◽  
pp. 889 ◽  
Author(s):  
Robert M. Boddey ◽  
José Carlos Polidoro ◽  
Alexander S. Resende ◽  
Bruno J. R. Alves ◽  
Segundo Urquiaga

This paper originates from an address at the 8th International Symposium on Nitrogen Fixation with Non-Legumes, Sydney, NSW, December 2000 The use of the 15N natural abundance technique to quantify contribution of biological nitrogen fixation (BNF) to any plant is based on the observation that N derived from soil is generally slightly different [usually higher in 15N abundance (δ15N‰)] than that of the air. Plants or micro-organisms growing solely on BNF generally accumulate N with 15N isotopic abundance lower than that of the air (i.e. δ15N‰ is negative), while plants obtaining all N from the soil generally show a positive δ15N‰ signal. The technique is applied by estimating the 15N abundance of the putative ‘N2-fixing’ crop and analysing the 15N abundance of neighbouring non-N2-fixing reference plants. However, often there are such large variations in the N derived from the soil by different non-N2-fixing plants that in natural ecosystems it is often impossible to even distinguish plants that are benefiting form BNF, let alone quantity this contribution. The reasons why soil derived N can vary so widely, especially in natural ecosystems, are briefly discussed and a sampling strategy is described to assess possible BNF inputs to sugar cane plants in commercial plantations in Brazil. The results suggest that in nine of the 11 sites studied, BNF inputs were significant ranging from 25 to 60% of N assimilated.

2015 ◽  
Vol 8 ◽  
pp. 585
Author(s):  
Ana Dolores Santiago de Freitas ◽  
Everardo Sampaio ◽  
Carolina Santos ◽  
Aleksandro Silva ◽  
Renata Carvalho

A fixação biológica de nitrogênio (FBN) é a principal forma de entrada de N em ecossistemas naturais e em sistemas agrícolas de subsistência, como os praticados predominantemente no Semiárido brasileiro. Estimativas dos aportes de N na Caatinga e em cultivos de importância para a região ainda são escassas, em parte pela dificuldade de medir simultaneamente as proporções de N derivadas da atmosfera (%Ndda) e as produções de biomassa no mesmo sistema. Estudos pioneiros indicam que diversas espécies de leguminosas, herbáceas e arbóreas, nativas e/ou cultivadas, podem fixar elevadas proporções de seu N. Em Caatinga bem preservada, os aportes de N em leguminosas arbóreas foram estimados em 11 kg ha-1 ano-1, um valor relativamente baixo devido à baixa densidade de plantas fixadoras. Entretanto, a densidade de leguminosas fixadoras na vegetação não é o único fator definindo o aporte de N, pois há observações de ausência de FBN em áreas de Caatinga em regeneração, dominadas por espécies fixadoras. No estrato herbáceo, os aportes de N podem chegar a 6 kg ha-1 ano-1, nas áreas com menor cobertura de arbóreas. As quantidades de N fixadas nos diferentes sistemas de cultivo são pouco conhecidas. Para o feijão-caupi, a FBN pode se aproximar dos 30 kg ha-1, em cultivos consorciados com milho, chegando a 45 kg ha-1, em cultivos solteiros. Em cultivos irrigados, adubos verdes podem adicionar 185 kg ha-1, superando a quantidade exportada nas colheitas. Em sistemas agroflorestais, a adição anual de N pode chegar a 40 kg ha-1. Não existem estimativas do N fixado em gramíneas na região, mas algumas espécies apresentem potencial de FBN. Biological nitrogen fixation (BNF) is the main N input in natural ecosystems and in subsistence agricultural systems, such as those commonly practiced in the Brazilian semiarid region. Estimates of N inputs in Caatinga and the main regional crops are still scarce, partly due to the difficulty in measuring concomitantly the proportion of plant N derived from the atmosphere (%Ndfa) and the amount of biomass produced in the same system. Pioneer studies indicate that several legume species, herbs and trees, native and/or cultivated, can fix large proportions of their N. In mature Caatinga, N inputs in tree legumes were estimated at 11 kg ha-1 year-1, a relatively low value due to the low plant density of the legume species. However, plant density is not the only factor defining N input, since absence of fixation has been reported in regenerating Caatinga, even in those dominated by potentially fixing species. In the herb stratum, N input up to 6 kg ha-1 year-1 has been reported in areas with lower tree cover. Inputs in crop systems are largely unknown. Fixation in cowpea can reach 30 kg ha-1, in plants consortiated with corn, and 45 kg ha-1, in single crop. Under irrigation, green manure crops can add 185 kg ha-1 of fixed N, more than the amounts exported by the main crop. In agroforest systems, the annual input may reach 40 kg ha-1. There are no publish reports on N biologically fixed by Poaceae species growing in the semiarid region but it is known that some species have the potential to fix. Keywords: N-15 natural abundance, slash and burn agriculture, diazotrophic microorganism, rhizobia, symbiosis.   


1995 ◽  
Vol 174 (1-2) ◽  
pp. 195-209 ◽  
Author(s):  
R. M. Boddey ◽  
O. C. de Oliveira ◽  
S. Urquiaga ◽  
V. M. Reis ◽  
F. L. de Olivares ◽  
...  

2020 ◽  
Vol 454 (1-2) ◽  
pp. 327-341
Author(s):  
Rafael Sanches Pacheco ◽  
Robert Michael Boddey ◽  
Bruno José Rodrigues Alves ◽  
Enderson Petrônio de Brito Ferreira ◽  
Rosângela Straliotto ◽  
...  

1969 ◽  
Vol 172 (1029) ◽  
pp. 367-388 ◽  

Biological nitrogen fixation is a characteristic of certain micro-organisms, which may be free-living or occur in symbiotic association with higher plants. The purpose of this paper is to summarize some of the biological and ecological aspects of nitrogen-fixation by free-living forms. Biochemical aspects have been reviewed in other contributions to this discussion by Drs Wilson, Burris, and Cox & Fay. Nitrogen fixation by heterotrophic micro-organisms has been considered by Jensen (1965); nitrogen fixation by blue-green algae by Fogg & Stewart (1965), and by Stewart (1966, 1969), while Moore (1966) has evaluated the contribution of nitrogen-fixing micro-organisms to soil fertility.


2011 ◽  
Vol 4 (2-3) ◽  
pp. 131-140 ◽  
Author(s):  
Mitchell Andrews ◽  
Euan K. James ◽  
Janet I. Sprent ◽  
Robert M. Boddey ◽  
Eduardo Gross ◽  
...  

1991 ◽  
pp. 105-111 ◽  
Author(s):  
R. M. Boddey ◽  
S. Urquiaga ◽  
V. Reis ◽  
J. Döbereiner

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