2002
DOI: 10.1016/s0038-0717(01)00175-4
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Soil amino acid turnover dominates the nitrogen flux in permafrost-dominated taiga forest soils

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Cited by 259 publications
(181 citation statements)
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“…This new ( 15 N-14 C) approach to quantify the significance of organic N uptake by plants offers greater sensitivity than commonly applied 15 N-13 C techniques, since the detection of 14 C as opposed to 13 C is not hindered by the large background of 12 C (Nä sholm and Persson 2001). Moreover, the slow-release kinetics of soluble organic N from macromolecular N (algae, isolated protein) enable the assessment of organic N nutrition over extended periods as opposed to the inherent problems when injecting double-labelled amino acids that turnover within minutes to hours (Jones 1999;Jones and Kielland 2002). Two points should be considered that potentially interfere with the technique.…”
Section: Discussionmentioning
confidence: 99%
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“…This new ( 15 N-14 C) approach to quantify the significance of organic N uptake by plants offers greater sensitivity than commonly applied 15 N-13 C techniques, since the detection of 14 C as opposed to 13 C is not hindered by the large background of 12 C (Nä sholm and Persson 2001). Moreover, the slow-release kinetics of soluble organic N from macromolecular N (algae, isolated protein) enable the assessment of organic N nutrition over extended periods as opposed to the inherent problems when injecting double-labelled amino acids that turnover within minutes to hours (Jones 1999;Jones and Kielland 2002). Two points should be considered that potentially interfere with the technique.…”
Section: Discussionmentioning
confidence: 99%
“…In this regard, however, there still exists an obvious shortcoming that the amino acids were injected into the soil only once and in the form of aqueous solutions of one amino acid (Nä sholm et al 2000;Nordin et al 2001;Taylor et al 2004;Weigelt et al 2005) or a mixture of several amino acids (Chapin et al 1993;Persson and Nä sholm 2003) while in soils free amino acids are continuously produced by microbial decomposition as a mixture of amino acids and therefore continuously contribute to plant organic N acquisition. Single injections of amino acids into soils in short-term studies are problematic because of fast decomposition and immobilization of free amino acids in soils (Schmidt et al 1960;Kassim et al 1981;Jones 1999;Jones and Kielland 2002).…”
Section: Introductionmentioning
confidence: 99%
“…After a wildfire, both a decrease in quality and amount of soil C are likely. Under these conditions, DON may represent a preferential labile C source for soil microbes, decreasing its soil concentration on a long-term basis (Jones and Kielland, 2002). On shorter time scales, losses by volatilization and pyrolysis or plant uptake, may explain a decline in soil DON (Raison, 1979;Smithwick, 2005).…”
Section: Discussionmentioning
confidence: 99%
“…It has been shown that the turnover of free amino acids in soil through microbial mineralization is very fast (within a few hours) (Jones and Kielland, 2002). The mineralization of the colloidal sized organic Se might be slower than the free amino acids.…”
Section: Mass Balance Estimationmentioning
confidence: 99%
“…It has been estimated that the total amount of Se taken up by plants in both pot experiment using the potato field soils and field experiment using the grassland soils is in similar range, i.e. 0.8 to 14 times and 1.3 to 11 times, respectively, of the shown that the turnover of free amino acids in soil is in the magnitude of hours (Jones and Kielland, 2002), whereas the turnover of up to 40% of DOM in soil solution is in the order of days to months (Kalbitz et al, 2000). Our study has…”
Section: Thementioning
confidence: 99%