Chickpea and white lupin rhizosphere carboxylates vary with soil properties and enhance phosphorus uptake

Author(s):  
Erik J. Veneklaas ◽  
Jason Stevens ◽  
Gregory R. Cawthray ◽  
Stephen Turner ◽  
Alasdair M. Grigg ◽  
...  
2003 ◽  
Vol 248 (1/2) ◽  
pp. 187-197 ◽  
Author(s):  
Erik J. Veneklaas ◽  
Jason Stevens ◽  
Gregory R. Cawthray ◽  
Stephen Turner ◽  
Alasdair M. Grigg ◽  
...  

2006 ◽  
Vol 55 (1) ◽  
pp. 117-126 ◽  
Author(s):  
György Füleky

The new hot water percolation (HWP) method was introduced to determine the phosphorus supply of soils from the Soil Bank of 36 Hungarian soils. The present work aimed to explain the availability of phosphorus by determining the inorganic phosphate fractions and using ryegrass test plants. Four inorganic phosphate fractions were distinguished: Fraction I, the sorbed phosphates; Fraction II, the easily soluble Ca phosphates and the Al bound phosphates; Fraction III, the Fe phosphates; and Fraction IV, the hardly soluble Ca phosphates. Fraction II, in which the easily soluble Ca phosphates and Al phosphates accumulate, was the main phosphorus source for the test plants on both calcareous and non-calcareous soils. Fraction III (the iron phosphates) plays a greater role in non-calcareous soils, while Fraction IV (the hardly soluble Ca phosphates) in calcareous soils. Both fractions are closely connected with soil development, and with soil properties such as pH and CaCO 3 content. The hot water percolation method reflects the phosphorus supply of soil as well as that measured with ryegrass plants and with the AL method. This new HWP method is in good correlation with the main source of phosphate, with fraction II. For routine purposes the first collected HWP fraction can possibly be used to determine the phosphorus supply of soil correlating well with the phosphorus uptake of test plants.


2009 ◽  
Vol 55 (1) ◽  
pp. 107-113 ◽  
Author(s):  
Jun Wasaki ◽  
Hayato Maruyama ◽  
Miho Tanaka ◽  
Takuya Yamamura ◽  
Hiraki Dateki ◽  
...  

2009 ◽  
Vol 46 (2) ◽  
pp. 79-91 ◽  
Author(s):  
Haigang Li ◽  
Jianbo Shen ◽  
Fusuo Zhang ◽  
Petra Marschner ◽  
Greg Cawthray ◽  
...  

Soil Research ◽  
2013 ◽  
Vol 51 (6) ◽  
pp. 484 ◽  
Author(s):  
Md Alamgir ◽  
Petra Marschner

Previously we showed that addition of legume residues affected the size of different soil phosphorus (P) pools in an alkaline loamy sand soil. Here, we tested whether the changes in soil P pools induced by residue addition are generally applicable or whether they are dependent on certain soil properties. Three legume residues differing in P concentration, faba bean (Vicia faba L.) (high P), chickpea (Cicer arietinum L.) (medium P), and white lupin (Lupinus albus L.) (low P), were added at a rate of 20 g residue kg–1 soil to three different soils with low Colwell-P concentration: Mt Bold (sandy clay loam, high organic carbon (C) content, pH 5.1), Monarto (loamy sand, low organic C content, pH 7.5), and Langhorne Creek (sandy loam, low organic C content, pH 8.1). Soil P pools were assessed by sequential P fractionation on days 0 and 42. In residue-amended soils from day 0 to day 42, the concentrations of water-soluble and microbial P decreased, whereas the concentrations of NaHCO3-Pi (inorganic P) and NaOH-Po (organic P) increased. The magnitude of these changes differed among soils, being greatest in the Mt Bold soil. Residue addition had little or no effect on the concentrations of NaOH-Pi and residual P, which also did not change significantly over time. Principal component analysis of the data showed that the size of the P pools was related to soil properties; high concentrations of HCl-P were associated with high pH and calcium concentrations, high concentrations of NaOH-P and residual P were correlated with high aluminium, silt, organic C, and total nitrogen and P. In the unamended soil on day 0, the concentration of NaHCO3-Pi was correlated with the clay content, whereas on day 42, the concentrations of the labile P pools were related to amount of P added with the residues. It can be concluded that most effects of residue addition to soils on microbial activity and growth and soil P pools can be generalised across the three soil used in this study, but that the size of the P pools is affected by soil properties such as organic C content, pH, and texture.


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