%0 Journal Article
%T Depletion of the heaviest stable N isotope is associated with NH4+/NH3 toxicity in NH4+-fed plants
%A Idoia Ariz
%A Cristina Cruz
%A Jose F Moran
%A Mar¨ªa B Gonz¨¢lez-Moro
%A Carmen Garc¨ªa-Olaverri
%A Carmen Gonz¨¢lez-Murua
%A Maria A Martins-Lou£¿£¿o
%A Pedro M Aparicio-Tejo
%J BMC Plant Biology
%D 2011
%I BioMed Central
%R 10.1186/1471-2229-11-83
%X Several NO3--fed plants were consistently enriched in 15N, whereas plants under NH4+ nutrition were depleted of 15N. It was shown that more sensitive plants to NH4+ toxicity were the most depleted in 15N. In parallel, N-deficient pea and spinach plants fed with 15NH4+ showed an increased level of NH3 uptake at alkaline pH that was related to the 15N depletion of the plant. Tolerant to NH4+ pea plants or sensitive spinach plants showed similar trend on 15N depletion while slight differences in the time kinetics were observed during the initial stages. The use of RbNO3 as control discarded that the differences observed arise from pH detrimental effects.This article proposes that the negative values of ¦Ä15N in NH4+-fed plants are originated from NH3 uptake by plants. Moreover, this depletion of the heavier N isotope is proportional to the NH4+/NH3 toxicity in plants species. Therefore, we hypothesise that the low affinity transport system for NH4+ may have two components: one that transports N in the molecular form and is associated with fractionation and another that transports N in the ionic form and is not associated with fractionation.Nitrogen (N) and carbon (C) are the main components of all living organisms and regulate the productivity of most ecosystems. In agriculture, N is by far the main nutrient in fertilisers, with nitrate (NO3-) and ammonium (NH4+) being the main N sources used by plants. However, relatively little is known about the isotopic fractionation during uptake of these ions. Assessment under natural conditions is difficult because, under most circumstances, NO3- and NH4+ are simultaneously present in the soil and their concentrations change both spatially and temporally over a wide range (e.g., 20 ¦ÌM to 20 mM) [1,2]. Furthermore, this situation becomes even more complex if the rhizosphere and its symbiotic interactions (N2-fixing organisms or mycorrhiza) are taken into account.The natural variation in stable N isotopes has been shown to be a pow
%K Low affinity ammonium transporters
%K Nitrogen isotopic signature
%K Ammonium/ammonia
%K Ammonium dissociation isotope factor
%K ammonia uptake
%U http://www.biomedcentral.com/1471-2229/11/83