000172188 001__ 172188
000172188 005__ 20210129214403.0
000172188 0247_ $$2doi$$a10.1016/j.agee.2014.04.023
000172188 0247_ $$2ISSN$$a0167-8809
000172188 0247_ $$2ISSN$$a1873-2305
000172188 0247_ $$2WOS$$aWOS:000338618400008
000172188 037__ $$aFZJ-2014-05685
000172188 082__ $$a330
000172188 1001_ $$0P:(DE-HGF)0$$aAgnelli, A.$$b0$$eCorresponding Author
000172188 245__ $$aCarbon and nitrogen in soil and vine roots in harrowed and grass-covered vineyards
000172188 260__ $$aAmsterdam [u.a.]$$bElsevier$$c2014
000172188 3367_ $$0PUB:(DE-HGF)16$$2PUB:(DE-HGF)$$aJournal Article$$bjournal$$mjournal$$s1415607186_16503
000172188 3367_ $$2DataCite$$aOutput Types/Journal article
000172188 3367_ $$00$$2EndNote$$aJournal Article
000172188 3367_ $$2BibTeX$$aARTICLE
000172188 3367_ $$2ORCID$$aJOURNAL_ARTICLE
000172188 3367_ $$2DRIVER$$aarticle
000172188 520__ $$aTo examine the effects of vineyard soil management on soil C and N content and quality, we studied harrowed and grass-covered vineyards on a soil developed on plio-pleistocene, marine sediments. A soil naturally covered by grasses adjacent to the vineyards served as control. To reach this goal, we assessed (1) the distribution of C and N and their 13C and 15N signatures in different soil organic matter pools, (2) the amount of C and N as live and dead vine fine roots and their 13C, 15N and 14C signatures, and (3) the stocks of C and N forms accumulated at two soil-depth intervals (0–50 and 50–100 cm).Independent of the soil management, the vines increased the total organic C and total N content in the deeper soil horizons because of root turnover and rhizodeposition processes. In the upper horizons, a greater organic matter accumulation was fostered by the presence of the grass cover and the absence of tillage. The grass cover favoured the organic C storage mainly in the form of particulate and highly stabilised organic matter (humic acids and humin), and reduced the soil N content by plant uptake, whereas the harrowing produced a greater abundance of fulvic acids, which were mainly ascribed to oxidative processes enhanced by the soil tillage. In both vineyard soils, decaying vine roots represented an important source of organic C and N, especially in the deepest horizons. Indeed, isotope analyses revealed a more intense degradation of the dead vine roots in the deeper soil portion, where they likely constituted the main substrate for soil microorganisms. In the deepest horizons of the grass-covered vineyard, the greater mean residence time of the decaying vine roots and the lower root production were attributed to the easily available energetic substrates supplied by grass root turnover and rhizodeposition, which were preferentially used by microorganisms. This fact fostered a larger C accumulation in the grass-covered than in the harrowed vineyard.
000172188 536__ $$0G:(DE-HGF)POF2-246$$a246 - Modelling and Monitoring Terrestrial Systems: Methods and Technologies (POF2-246)$$cPOF2-246$$fPOF II$$x0
000172188 536__ $$0G:(DE-HGF)POF3-255$$a255 - Terrestrial Systems: From Observation to Prediction (POF3-255)$$cPOF3-255$$fPOF III$$x1
000172188 588__ $$aDataset connected to CrossRef, juser.fz-juelich.de
000172188 7001_ $$0P:(DE-Juel1)145865$$aBol, R.$$b1$$ufzj
000172188 7001_ $$0P:(DE-HGF)0$$aTrumbore, S. E.$$b2
000172188 7001_ $$0P:(DE-HGF)0$$aDixon, L.$$b3
000172188 7001_ $$0P:(DE-HGF)0$$aCocco, S.$$b4
000172188 7001_ $$0P:(DE-HGF)0$$aCorti, G.$$b5
000172188 773__ $$0PERI:(DE-600)2013743-6$$a10.1016/j.agee.2014.04.023$$gVol. 193, p. 70 - 82$$p70 - 82$$tAgriculture, ecosystems & environment$$v193$$x0167-8809$$y2014
000172188 8564_ $$uhttps://juser.fz-juelich.de/record/172188/files/FZJ-2014-05685.pdf$$yRestricted
000172188 909CO $$ooai:juser.fz-juelich.de:172188$$pVDB:Earth_Environment$$pVDB
000172188 9101_ $$0I:(DE-588b)5008462-8$$6P:(DE-Juel1)145865$$aForschungszentrum Jülich GmbH$$b1$$kFZJ
000172188 9132_ $$0G:(DE-HGF)POF3-255$$1G:(DE-HGF)POF3-250$$2G:(DE-HGF)POF3-200$$aDE-HGF$$bPOF III$$lMarine, Küsten- und Polare Systeme$$vTerrestrische Umwelt$$x0
000172188 9131_ $$0G:(DE-HGF)POF2-246$$1G:(DE-HGF)POF2-240$$2G:(DE-HGF)POF2-200$$3G:(DE-HGF)POF2$$4G:(DE-HGF)POF$$aDE-HGF$$bErde und Umwelt$$lTerrestrische Umwelt$$vModelling and Monitoring Terrestrial Systems: Methods and Technologies$$x0
000172188 9131_ $$0G:(DE-HGF)POF3-255$$1G:(DE-HGF)POF3-250$$2G:(DE-HGF)POF3-200$$3G:(DE-HGF)POF3$$4G:(DE-HGF)POF$$9G:(DE-HGF)POF3-255$$aDE-HGF$$bErde und Umwelt$$lTerrestrische Umwelt$$vTerrestrial Systems: From Observation to Prediction$$x1
000172188 9141_ $$y2014
000172188 915__ $$0StatID:(DE-HGF)0100$$2StatID$$aJCR
000172188 915__ $$0StatID:(DE-HGF)0110$$2StatID$$aWoS$$bScience Citation Index
000172188 915__ $$0StatID:(DE-HGF)0111$$2StatID$$aWoS$$bScience Citation Index Expanded
000172188 915__ $$0StatID:(DE-HGF)0150$$2StatID$$aDBCoverage$$bWeb of Science Core Collection
000172188 915__ $$0StatID:(DE-HGF)0199$$2StatID$$aDBCoverage$$bThomson Reuters Master Journal List
000172188 915__ $$0StatID:(DE-HGF)0200$$2StatID$$aDBCoverage$$bSCOPUS
000172188 915__ $$0StatID:(DE-HGF)0300$$2StatID$$aDBCoverage$$bMedline
000172188 915__ $$0StatID:(DE-HGF)0310$$2StatID$$aDBCoverage$$bNCBI Molecular Biology Database
000172188 915__ $$0StatID:(DE-HGF)0420$$2StatID$$aNationallizenz
000172188 915__ $$0StatID:(DE-HGF)1040$$2StatID$$aDBCoverage$$bZoological Record
000172188 915__ $$0StatID:(DE-HGF)1050$$2StatID$$aDBCoverage$$bBIOSIS Previews
000172188 915__ $$0StatID:(DE-HGF)1060$$2StatID$$aDBCoverage$$bCurrent Contents - Agriculture, Biology and Environmental Sciences
000172188 915__ $$0StatID:(DE-HGF)9900$$2StatID$$aIF < 5
000172188 9201_ $$0I:(DE-Juel1)IBG-3-20101118$$kIBG-3$$lAgrosphäre$$x0
000172188 980__ $$ajournal
000172188 980__ $$aVDB
000172188 980__ $$aI:(DE-Juel1)IBG-3-20101118
000172188 980__ $$aUNRESTRICTED