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024 7 _ |2 DOI
|a 10.1007/s11104-009-0190-z
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|a WOS:000276234200015
024 7 _ |2 ISSN
|a 0032-079X
024 7 _ |2 uri
|a 10.1007/s11104-009-0190-z
024 7 _ |2 Handle
|a 2128/4398
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037 _ _ |a PreJuSER-4582
041 _ _ |a eng
082 _ _ |a 570
082 _ _ |a 500
084 _ _ |2 WoS
|a Agronomy
084 _ _ |2 WoS
|a Plant Sciences
084 _ _ |2 WoS
|a Soil Science
100 1 _ |0 P:(DE-Juel1)129286
|a Blossfeld, S.
|b 0
|u FZJ
245 _ _ |a Rhizosphere pH dynamics in trace-metal-contaminated soils, monitored with planar ph optodes
260 _ _ |a Dordrecht [u.a.]
|b Springer Science + Business Media B.V
|c 2010
295 1 0 |a Plant and Soil Volume 330, Numbers 1-2, 173-184
336 7 _ |a Journal Article
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440 _ 0 |0 9161
|a Plant and Soil
|v 330
|x 0032-079X
|y 1
500 _ _ |a This work was supported by the "Deutscher Akademischer Austausch Dienst" (DAAD) and the "Ministere de l'Education Nationale, de l'Enseignement Superieur et de la Recherche" within the framework of the PROCOPE programme in 2008.
500 _ _ |a The final publication is available at: http://www.springerlink.com/content/55431383x86127k2/
500 _ _ |a Record converted from JUWEL: 18.07.2013
520 _ _ |a The present study presents new insights into pH dynamics in the rhizosphere of alpine pennycress (Noccaea caerulescens (J. Presl & C. Presl) F.K. Mey), maize (Zea mays L.) and ryegrass (Lolium perenne L.), when growing on three soils contaminated by trace metals with initial pH values varying from 5.6 to 7.4. The pH dynamics were recorded, using a recently developed 2D imaging technique based on planar pH optodes. This showed that alpine pennycress and ryegrass alkalinized their rhizosphere by up to 1.7 and 1.5 pH units, respectively, whereas maize acidified its rhizosphere by up to -0.7 pH units. The alkalinization by the roots of alpine pennycress and ryegrass was permanent and not restricted to specific root zones, whereas the acidification along the maize roots was restricted to the elongation zone and thus only temporary. Calculations showed that such pH changes should have noticeable effects on the solubility of the trace metal in the rhizosphere, and therefore on their uptake by the plants. As a result, it is suggested that models for trace metal uptake should include precise knowledge of rhizospheric pH conditions.
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650 _ 7 |a Alpine pennycress
650 _ 7 |a Acidification
650 _ 7 |a Maize
650 _ 7 |a Alkalinization
650 _ 7 |a Cadmium
650 _ 7 |a Ryegrass
653 2 0 |2 Author
|a Maize
653 2 0 |2 Author
|a Alpine pennycress
653 2 0 |2 Author
|a Ryegrass
653 2 0 |2 Author
|a Cadmium
653 2 0 |2 Author
|a Alkalinization
653 2 0 |2 Author
|a Acidification
700 1 _ |0 P:(DE-HGF)0
|a Perriguey, J.
|b 1
700 1 _ |0 P:(DE-HGF)0
|a Sterckeman, T.
|b 2
700 1 _ |0 P:(DE-HGF)0
|a Morel, J.-L.
|b 3
700 1 _ |0 P:(DE-HGF)0
|a Lösch, R.
|b 4
773 _ _ |0 PERI:(DE-600)1478535-3
|a 10.1007/s11104-009-0190-z
|g Vol. 330
|q 330
|t Plant and soil
|v 330
|x 0032-079X
|y 2010
856 7 _ |u http://dx.doi.org/10.1007/s11104-009-0190-z
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