Mobility and recalcitrance of organo-chromium(III) complexes

被引:63
作者
Puzon, Geoffrey J. [1 ,2 ]
Tokala, Ranjeet K. [2 ,3 ]
Zhang, Hua [1 ]
Yonge, David [2 ,3 ]
Peyton, Brent M. [2 ,4 ]
Xun, Luying [1 ,2 ]
机构
[1] Washington State Univ, Sch Mol Biosci, Pullman, WA 99164 USA
[2] Washington State Univ, Ctr Multiphase Environm Res, Pullman, WA 99164 USA
[3] Washington State Univ, Dept Civil & Environm Engn, Pullman, WA 99164 USA
[4] Montana State Univ, Dept Chem & Biol Engn, Bozeman, MT 59717 USA
关键词
chromium; organo-Cr(III) complex; recalcitrant; mobility; soil;
D O I
10.1016/j.chemosphere.2007.09.010
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Hexavalent chromium [Cr(VI)l is a major industrial pollutant. Bioremediation of Cr(VI) to Cr(III) is a viable clean-up approach. However, Cr(VI) bioreduction also produces soluble organo-Cr(III) complexes, and little is known about their behavior in the environment. When tested with soil columns, citrate-Cr(III) showed little sorption to soil; malate-Cr(III) had limited partitioning with soil; and histidine-Cr(III) exhibited significant interaction with soil. It appears that the mobility varies depending on the organic ligand. Further, Ralstonia eutropha JMP 134 and Pseudomonas aeruginosa pAO1 readily degraded malate, citrate, and histidine, but not the corresponding organo-Cr(III) complexes. The recalcitrance is not due to toxicity, but the complexes are likely to cause hindrance to enzymes, as malate dehydrogenase and amino acid oxidase could not use malate-Cr(III) and bistidine-Cr(III), respectively. The data are in agreement with the reports of soluble organo-Cr(III) complexes in the environment. (c) 2007 Elsevier Ltd. All rights reserved.
引用
收藏
页码:2054 / 2059
页数:6
相关论文
共 36 条
[1]  
[Anonymous], MOL CLONING
[2]   INTRACELLULAR CHROMIUM REDUCTION [J].
ARSLAN, P ;
BELTRAME, M ;
TOMASI, A .
BIOCHIMICA ET BIOPHYSICA ACTA, 1987, 931 (01) :10-15
[3]   The metal reductase activity of some multiheme cytochromes c:: NMR structural characterization of the reduction of chromium(VI) to chromium(III) by cytochrome c7 [J].
Assfalg, M ;
Bertini, I ;
Bruschi, M ;
Michel, C ;
Turano, P .
PROCEEDINGS OF THE NATIONAL ACADEMY OF SCIENCES OF THE UNITED STATES OF AMERICA, 2002, 99 (15) :9750-9754
[4]  
Barnhart J, 1997, J SOIL CONTAM, V6, P561, DOI 10.1080/15320389709383589
[5]   BEHAVIOR OF CHROMIUM IN SOILS .3. OXIDATION [J].
BARTLETT, R ;
JAMES, B .
JOURNAL OF ENVIRONMENTAL QUALITY, 1979, 8 (01) :31-35
[6]  
BEATTIE JK, 1972, PROGR INORG CHEM, V17, P93
[7]   EVALUATION OF SOME NEW TRACERS FOR SOIL-WATER STUDIES [J].
BOWMAN, RS .
SOIL SCIENCE SOCIETY OF AMERICA JOURNAL, 1984, 48 (05) :987-993
[8]  
DRAGUN J, 1988, ELEMENT FIXATION SOI, P75
[9]   Chromium speciation and fractionation in ground and surface waters in the vicinity of chromite ore processing residue disposal sites [J].
Farmer, JG ;
Thomas, RP ;
Graham, MC ;
Geelhoed, JS ;
Lumsdon, DG ;
Paterson, E .
JOURNAL OF ENVIRONMENTAL MONITORING, 2002, 4 (02) :235-243
[10]   Cytotoxicity, apoptosis, and in vitro DNA damage induced by potassium chromate [J].
Flores, A ;
Pérez, JM .
TOXICOLOGY AND APPLIED PHARMACOLOGY, 1999, 161 (01) :75-81