Depollution potential of three macrophytes: Exudated, wall-bound and intracellular peroxidase activities plus intracellular phenol concentrations

被引:28
作者
Larue, Camille [1 ,2 ]
Korboulewsky, Nathalie [1 ]
Wang, Runying [1 ]
Mevy, Jean-Philippe [1 ]
机构
[1] Univ Aix Marseille 1, Ctr St Charles, Equipe Diversite Fonct Communautes Vegetales, IMEP,UMR CNRS 6116, F-13331 Marseille, France
[2] CEA, IRAMIS, SIS2M, Lab Struct & Dynam Resonance Magnet, F-91191 Gif Sur Yvette, France
关键词
Constructed wetland; Macrophytes; Peroxidase; Phenols; Metal detoxication; PHRAGMITES-AUSTRALIS; CONSTRUCTED WETLAND; WASTE-WATER; AZO-DYE; PHYTOREMEDIATION; L; DEGRADATION; ENZYMES; ACCUMULATION; PHENANTHRENE;
D O I
10.1016/j.biortech.2010.05.010
中图分类号
S2 [农业工程];
学科分类号
0828 ;
摘要
The aim of this study was to investigate the potential role of three macrophyte species (Iris pseudacorus, Typha latifolia and Phragmites australis) for detoxication of xenobiotics, and to study their variations with seasons or concentrations of sewage sludge from the food industry. For this purpose, some aspects of the green liver concept were explored through peroxidase measurements in three compartments in roots: intracellular, cell wall and extracellular. In addition, phenol concentrations were also measured in order to assess heavy metal detoxication potential. Enzyme activities and phenol concentrations were overall lower in winter according to the phenological stages and some sludge effects occurred. Results show that P. australis roots exuded and contained more peroxidase in all seasons: 17 U/g (1373 U/g protein), 0.8 U/g (613 U/g protein) and 4.8 U/g (1329 U/g protein) in intracellular compartments, cell wall and exudates, respectively. In contrast, the highest phenol concentration was found in I. pseudacorus roots: 143.3 mg eq. gallic acid/g. Hence, in constructed wetlands, P. australis is suitable for organic waste water treatment, while I. pseudacorus should be used in the case of waters highly charged with heavy metals. (c) 2010 Elsevier Ltd. All rights reserved.
引用
收藏
页码:7951 / 7957
页数:7
相关论文
共 44 条
[1]   Class III peroxidases in plant defence reactions [J].
Almagro, L. ;
Ros, L. V. Gomez ;
Belchi-Navarro, S. ;
Bru, R. ;
Barcelo, A. Ros ;
Pedreno, M. A. .
JOURNAL OF EXPERIMENTAL BOTANY, 2009, 60 (02) :377-390
[2]   Methyl parathion toxicity to and removal efficiency by Typha latifolia in water and artificial sediments [J].
Amaya-Chavez, A. ;
Martinez-Tabche, L. ;
Lopez-Lopez, E. ;
Galar-Martinez, M. .
CHEMOSPHERE, 2006, 63 (07) :1124-1129
[3]  
Bergmeyer HU, 1974, METHOD ENZYMAT AN, V1, P495
[4]  
BRADFORD MM, 1976, ANAL BIOCHEM, V72, P248, DOI 10.1016/0003-2697(76)90527-3
[5]   Accumulation of nutrients and heavy metals in Phragmites australis (Cav.) Trin. ex Steudel and Bolboschoenus maritimus (L.) Palla in a constructed wetland of the Venice lagoon watershed [J].
Bragato, Claudia ;
Brix, Hans ;
Malagoli, Mario .
ENVIRONMENTAL POLLUTION, 2006, 144 (03) :967-975
[6]  
Brix H., 1993, P9
[7]   The effects of tannery wastewater on the development of different plant species and chromium accumulation in Phragmites australis [J].
Calheiros, Cristina S. C. ;
Rangel, Antonio O. S. S. ;
Castro, Paula M. L. .
ARCHIVES OF ENVIRONMENTAL CONTAMINATION AND TOXICOLOGY, 2008, 55 (03) :404-414
[8]   Constructed wetland systems vegetated with different plants applied to the treatment of tannery wastewater [J].
Calheiros, Cristina S. C. ;
Rangel, Antonio O. S. S. ;
Castro, Paula M. L. .
WATER RESEARCH, 2007, 41 (08) :1790-1798
[9]   Are Phragmites australis enzymes involved in the degradation of the textile azo dye acid orange 7? [J].
Carias, Catia C. ;
Novais, Julio M. ;
Martins-Dias, Susete .
BIORESOURCE TECHNOLOGY, 2008, 99 (02) :243-251
[10]   Enhancement of phenanthrene and pyrene degradation in rhizosphere of tall fescue (Festuca arundinacea) [J].
Cheema, Sardar Alam ;
Khan, Muhammad Imran ;
Tang, Xianjin ;
Zhang, Congkai ;
Shen, Chaofeng ;
Malik, Zaffar ;
Ali, Shafaqat ;
Yang, Jianjun ;
Shen, Kaili ;
Chen, Xincai ;
Chen, Yingxu .
JOURNAL OF HAZARDOUS MATERIALS, 2009, 166 (2-3) :1226-1231