001     23478
005     20180210133403.0
024 7 _ |2 DOI
|a 10.1016/S0045-6535(02)00607-0
024 7 _ |2 WOS
|a WOS:000180580300002
037 _ _ |a PreJuSER-23478
041 _ _ |a eng
082 _ _ |a 333.7
084 _ _ |2 WoS
|a Environmental Sciences
100 1 _ |a Shardendu, S.
|b 0
|0 P:(DE-HGF)0
245 _ _ |a Phytoremediation of selenium by two helophyte species in subsurface flow constructed wetland
260 _ _ |a Amsterdam [u.a.]
|b Elsevier Science
|c 2003
300 _ _ |a 967 - 973
336 7 _ |a Journal Article
|0 PUB:(DE-HGF)16
|2 PUB:(DE-HGF)
336 7 _ |a Output Types/Journal article
|2 DataCite
336 7 _ |a Journal Article
|0 0
|2 EndNote
336 7 _ |a ARTICLE
|2 BibTeX
336 7 _ |a JOURNAL_ARTICLE
|2 ORCID
336 7 _ |a article
|2 DRIVER
440 _ 0 |a Chemosphere
|x 0045-6535
|0 1228
|v 50
500 _ _ |a Record converted from VDB: 12.11.2012
520 _ _ |a The phytoremediation of selenium by two different wetland species was investigated. Selenium (20.4 mug/l) was supplied continuously to subsurface flow constructed wetlands, one vegetated with Typha latifolia L. and the other with Phragmites australis (Cav.) Trin. ex Steud. The beds of both species had same hydraulic loading rate (0.079 m(3)/m(2)/d) and water retention time (24 h). However, the mass loading rate was 1.27 mg Se/m(2)/d for Phragmites and 1.35 mg Se/m(2)/d for Typha. In the Typha bed Se migrated faster than in the Phragmites bed. After 25 d of Se supplementation in the Typha bed about 54% of the Se inlet concentration remained in the outlet water. In the Phragmites bed Se was removed completely from the water after passing through 3/4 of the bed length. After 65 d of Se supplementation the highest amount of Se (2.8 mug/g dry matter) was determined in the organic material of the Typha bed. Roots and rhizomes accumulated 2,2 and 1.8 mug/g dry matter respectively. Phragmites accumulated Se in the leaves and stems, but not in the rhizomes. The accumulation in the leaves (1.8 mug Se/g dry matter) was three times higher than in the sterns (0.6 mug Se/g dry matter). (C) 2002 Elsevier Science Ltd. All rights reserved.
536 _ _ |a Chemie und Dynamik der Geo-Biosphäre
|c U01
|2 G:(DE-HGF)
|0 G:(DE-Juel1)FUEK257
|x 0
588 _ _ |a Dataset connected to Web of Science
650 _ 7 |a J
|2 WoSType
653 2 0 |2 Author
|a constructed wetlands
653 2 0 |2 Author
|a Phragmites
653 2 0 |2 Author
|a selenium
653 2 0 |2 Author
|a Typha
700 1 _ |a Salhani, N.
|b 1
|u FZJ
|0 P:(DE-Juel1)VDB1374
700 1 _ |a Boulyga, S. F.
|b 2
|0 P:(DE-HGF)0
700 1 _ |a Stengel, E.
|b 3
|0 P:(DE-HGF)0
773 _ _ |a 10.1016/S0045-6535(02)00607-0
|g Vol. 50, p. 967 - 973
|p 967 - 973
|q 50<967 - 973
|0 PERI:(DE-600)1496851-4
|t Chemosphere
|v 50
|y 2003
|x 0045-6535
856 7 _ |u http://dx.doi.org/10.1016/S0045-6535(02)00607-0
909 C O |o oai:juser.fz-juelich.de:23478
|p VDB
913 1 _ |k U01
|v Chemie und Dynamik der Geo-Biosphäre
|l Chemie und Dynamik der Geo-Biosphäre
|b Environment (Umwelt)
|0 G:(DE-Juel1)FUEK257
|x 0
914 1 _ |y 2003
915 _ _ |0 StatID:(DE-HGF)0010
|a JCR/ISI refereed
920 1 _ |k ICG-III
|l Phytosphäre
|d 31.12.2006
|g ICG
|0 I:(DE-Juel1)VDB49
|x 0
970 _ _ |a VDB:(DE-Juel1)14234
980 _ _ |a VDB
980 _ _ |a ConvertedRecord
980 _ _ |a journal
980 _ _ |a I:(DE-Juel1)IBG-2-20101118
980 _ _ |a UNRESTRICTED
981 _ _ |a I:(DE-Juel1)IBG-2-20101118
981 _ _ |a I:(DE-Juel1)ICG-3-20090406


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