A comparative study for the sorption of Cd(II) by K-feldspar and sepiolite as soil components, and the recovery of Cd(II) using rhamnolipid biosurfactant

被引:43
作者
Asci, Y. A. [1 ]
Nurbas, M. [1 ]
Acikel, Y. Sag [2 ]
机构
[1] Eskisehir Osmangazi Univ, Dept Chem Engn, TR-26480 Bati Meselik, Eskisehir, Turkey
[2] Hacettepe Univ, Dept Chem Engn, TR-06800 Ankara, Turkey
关键词
soil remediation; K-feldspar; sepiolite; Langmuir model; Freundlich model; desorption; rhamnolipid biosurfactant;
D O I
10.1016/j.jenvman.2007.03.006
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
This study investigated the sorption characteristics and recovery of selected heavy metal Cd(II) from K-feldspar and sepiolite, representative soil components, using rhamnolipid biosurfactant. Although the proposed technique was classified as a soil bioremediation process, it can also be applied to treatment of waste waters containing Cd(II) ions with minor modifications. The effect of initial Cd(II) concentration on sorption capacity was characterized by determining the sorption isotherms. Of the four models examined, the Freundlich model showed the best fit for the sorption of Cd(II) on K-feldspar, whereas the Langmuir-model was used succesfully to characterize the sorption of Cd(II) on sepiolite. Although a, high Cd(II) uptake of 7.49 mmol/kg by K-feldspar was obtained, sepiolite was a superior Cd(H) accumulater, with amaximum Cd(II) uptake of 24.66 mmol Cd(II)/kg. The presence of Cd(II) in the sepiolite or K-feldspar prior to addition of the rhamnolipid generally resulted in less rhamnolipid sorption to sepiolite or K-feldspar. The maximum Cd(II) desorption efficiency by rhamnolipid from K-feldspar was substantially higher than that of sepiolite and determined to be 96% of the sorbed Cd(II), whereas only 10.1% of the sorbed Cd(II) from sepiolite was recovered by rhamnolipid solution. (C) 2007 Elsevier Ltd. All rights reserved.
引用
收藏
页码:383 / 392
页数:10
相关论文
共 41 条
[1]  
Alumaa P., 2001, P EST ACAD SCI, V50, P104
[2]   Sorption of Cd(II) onto kaolin as a soil component and desorption of Cd(II) from kaolin using rhamnolipid biosurfactant [J].
Asci, Y. ;
Nurbas, M. ;
Acikel, Y. Sag .
JOURNAL OF HAZARDOUS MATERIALS, 2007, 139 (01) :50-56
[3]   Kinetics of heavy-metal removal and recovery in sepiolite [J].
Brigatti, MF ;
Lugli, C ;
Poppi, L .
APPLIED CLAY SCIENCE, 2000, 16 (1-2) :45-57
[4]   Microbial resistance to metals in the environment [J].
Bruins, MR ;
Kapil, S ;
Oehme, FW .
ECOTOXICOLOGY AND ENVIRONMENTAL SAFETY, 2000, 45 (03) :198-207
[5]   Microbial surfactants and their use in field studies of soil remediation [J].
Christofi, N ;
Ivshina, IB .
JOURNAL OF APPLIED MICROBIOLOGY, 2002, 93 (06) :915-929
[6]   Effects of bivalent salts on the flotation separation of Na-feldspar from K-feldspar [J].
Demir, C ;
Bentli, I ;
Gülgönül, I ;
Çelik, MS .
MINERALS ENGINEERING, 2003, 16 (06) :551-554
[7]   Experimental studies of the interaction of aqueous metal cations with mineral substrates: Lead, cadmium, and copper with perthitic feldspar, muscovite, and biotite [J].
Farquhar, ML ;
Vaughan, DJ ;
Hughes, CR ;
Charnock, JM ;
England, KER .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1997, 61 (15) :3051-3064
[8]   Lipid lather removes metals [J].
Frazer, L .
ENVIRONMENTAL HEALTH PERSPECTIVES, 2000, 108 (07) :A320-A323
[9]  
Freundlich H.M.F., 1907, J PHYS CHEM, V57, P385
[10]   Heavy metal adsorption by different minerals:: application to the remediation of polluted soils [J].
García-Sánchez, A ;
Alastuey, A ;
Querol, X .
SCIENCE OF THE TOTAL ENVIRONMENT, 1999, 242 (1-3) :179-188