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000054326 0247_ $$2DOI$$a10.1080/15226510600846723
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000054326 084__ $$2WoS$$aEnvironmental Sciences
000054326 1001_ $$0P:(DE-HGF)0$$aAzaizeh, H.$$b0
000054326 245__ $$aPhytoremediation of selenium using subsurface-flow constructed wetland
000054326 260__ $$aPhiladelphia, Pa.$$bTaylor & Francis$$c2006
000054326 300__ $$a187 - 198
000054326 3367_ $$0PUB:(DE-HGF)16$$2PUB:(DE-HGF)$$aJournal Article
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000054326 440_0 $$016082$$aInternational Journal of Phytoremediation$$v1$$x1522-6514$$y8
000054326 500__ $$aRecord converted from VDB: 12.11.2012
000054326 520__ $$aThe potential of two plant species, Phragmites australis (common reed) and Typha latifolia (cattail), in the phytoremediation process of selenium (Se) was studied in subsurface-flow constructed wetland (SSF). Se was supplemented continuously at a concentration of 100 microg Se L(-1) in the inlet of the cultivation beds of the SSF. Water samples collected from the outlet of the Phragmites bed after 1, 3, 6, 9, and 12 wk of treatments showed that Se content was under detectable limits. Water samples collected from the Typha bed at the same five periods showed that Se concentrations in the outlet were 55, 47, 65, 76, and 25 microg/L, respectively. The results of bioaccumulation in the biomass of both species after 12 wk of treatment indicated that Typha plants accumulated Se mainly in fine roots. Phragmites accumulated Se mainly in leaves and rhizomes, and moderate levels were found in stems and fine organic materials. The results indicate that common reed is a very good species for Se phytoextraction and phytostabilization (immobilization) and that cattail is only a phytostabilization species. The use of common reed and cattail for Se phytoremediation in a SSF system and in constructed wetland models are discussed.
000054326 536__ $$0G:(DE-Juel1)FUEK407$$2G:(DE-HGF)$$aTerrestrische Umwelt$$cP24$$x0
000054326 588__ $$aDataset connected to Web of Science, Pubmed
000054326 650_2 $$2MeSH$$aBiodegradation, Environmental
000054326 650_2 $$2MeSH$$aBiomass
000054326 650_2 $$2MeSH$$aPlant Leaves: metabolism
000054326 650_2 $$2MeSH$$aPlant Roots: metabolism
000054326 650_2 $$2MeSH$$aPlant Stems: metabolism
000054326 650_2 $$2MeSH$$aPoaceae: metabolism
000054326 650_2 $$2MeSH$$aRhizome: metabolism
000054326 650_2 $$2MeSH$$aSelenium: metabolism
000054326 650_2 $$2MeSH$$aTyphaceae: metabolism
000054326 650_2 $$2MeSH$$aWater Movements
000054326 650_2 $$2MeSH$$aWetlands
000054326 650_7 $$07782-49-2$$2NLM Chemicals$$aSelenium
000054326 650_7 $$2WoSType$$aJ
000054326 65320 $$2Author$$asubsurface-flow constructed wetland (SSF)
000054326 65320 $$2Author$$aphytoremediation
000054326 65320 $$2Author$$awetland plants
000054326 65320 $$2Author$$aTypha
000054326 65320 $$2Author$$aPhragmites
000054326 7001_ $$0P:(DE-Juel1)VDB1374$$aSalhani, N.$$b1$$uFZJ
000054326 7001_ $$0P:(DE-HGF)0$$aSebesvari, Z.$$b2
000054326 7001_ $$0P:(DE-HGF)0$$aShardendu, S.$$b3
000054326 7001_ $$0P:(DE-HGF)0$$aEmons, H.$$b4
000054326 773__ $$0PERI:(DE-600)2094255-2$$a10.1080/15226510600846723$$gVol. 8, p. 187 - 198$$p187 - 198$$q8<187 - 198$$tInternational journal of phytoremediation$$v8$$x1522-6514$$y2006
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000054326 9131_ $$0G:(DE-Juel1)FUEK407$$bErde und Umwelt$$kP24$$lTerrestrische Umwelt$$vTerrestrische Umwelt$$x0
000054326 9141_ $$y2006
000054326 915__ $$0StatID:(DE-HGF)0010$$aJCR/ISI refereed
000054326 9201_ $$0I:(DE-Juel1)VDB49$$d31.12.2006$$gICG$$kICG-III$$lPhytosphäre$$x0
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