Tight metal binding by humic acids and its role in biomineralization

被引:153
作者
Davies, G
Fataftah, A
Cherkasskiy, A
Ghabbour, EA
Radwan, A
Jansen, SA
Kolla, S
Paciolla, MD
Sein, LT
Buermann, W
Balasubramanian, M
Budnick, J
Xing, BS
机构
[1] NORTHEASTERN UNIV,BARNETT INST,BOSTON,MA 02115
[2] AGR RES CTR,SOIL SALIN LAB,ALEXANDRIA 21616,EGYPT
[3] UNIV ALEXANDRIA,DEPT CHEM ENGN,ALEXANDRIA,EGYPT
[4] TEMPLE UNIV,DEPT CHEM,PHILADELPHIA,PA 19122
[5] UNIV CONNECTICUT,DEPT PHYS,STORRS,CT 06269
[6] UNIV MASSACHUSETTS,DEPT PLANT & SOIL SCI,AMHERST,MA 01003
来源
JOURNAL OF THE CHEMICAL SOCIETY-DALTON TRANSACTIONS | 1997年 / 21期
关键词
D O I
10.1039/a703145i
中图分类号
O61 [无机化学];
学科分类号
070301 ; 081704 ;
摘要
Analytical and thermodynamic data, EPR, FTIR, solution H-1 and solid-state C-13 cross polarization magic angle spinning NMR and solid-state extended X-ray absorption fine structure (EXAFS) and X-ray absorption near-edge structure (XANES) spectra have been recorded for purified humic acids (HAs) isolated from a German peat (GHA), an Irish peat (IHA), an unpolluted New Hampshire bog soil (NHA) and their tightly bound copper(II), iron(III) and manganese(II) forms. Brief water washing of partly or fully metal-loaded HAs leaves 'tightly' bound metal in the isolated freeze-dried solids. Mo:rt of this metal is removed by washing with 0.1 M HCl, indicating acidic HA functional groups as principal metal binding sites. The number of nearest-neighbour atoms coordinated to tightly bound Cu-II (four), Fe-III (six, probably with distorted geometry) and Mn-II (six, undistorted) in solid GHA, IHA and NHA were determined by XANES and EXAFS spectroscopy with reference standards. Isotherms measured at 20.0 degrees C and pH 2.4-3.2 with [M](total) = 0.18-25.8 mM for tight, reversible Cu2+(aq), Fe3+(aq), and Mn2+(aq) binding by solid IHA and NHA fit the Langmuir model and give the pH-independent stoichiometric site capacities nu(1) and equilibrium constants K-i for metal binding at specific HA sites i = A, B and C. Tight binding sites A, B and C of IHA are occupied by Cu-II, sites A and B by Fe-III and site A by Mn-II, while only identical metal binding site A in NHA is tight enough to resist metal removal by brief water washing. A new helical HA molecular model based on the empirical formula C36H30N2O15. xH(2)O visualizes metal binding and the likely roles of HAs in biomineralization. Site A is suggested to be carboxylate, mixed ligands probably constitute site B, and site C is tentatively assigned as the interior of the HA helix. Binding free energies and EPR evidence suggest that Cu2+(aq), Fe3+(aq) and Mn2+(aq) rapidly transfer between specific HA binding sites. This affects rates of metal release and transfer to minerals.
引用
收藏
页码:4047 / 4060
页数:14
相关论文
共 81 条
[11]   SORPTION OF N2 AND EGME VAPORS ON SOME SOILS, CLAYS, AND MINERAL OXIDES AND DETERMINATION OF SAMPLE SURFACE-AREAS BY USE OF SORPTION DATA [J].
CHIOU, CT ;
RUTHERFORD, DW ;
MANES, M .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1993, 27 (08) :1587-1594
[12]   THE SURFACE-AREA OF SOIL ORGANIC-MATTER [J].
CHIOU, CT ;
LEE, JF ;
BOYD, SA .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1990, 24 (08) :1164-1166
[13]   A modified cross-polarization magic angle spinning C-13 NMR procedure for the study of humic materials [J].
Cook, RL ;
Langford, CH ;
Yamdagni, R ;
Preston, CM .
ANALYTICAL CHEMISTRY, 1996, 68 (22) :3979-3986
[14]  
DAVIES G, 1995, ADV NEW MAT EMERGING, P677
[15]  
DAVIES G, 1997, J PHYS CHEM B, V101, P3328
[16]  
DAVIES G, IN PRESS P 8 IHSS M
[17]  
EPHARIM J, 1986, ENVIRON SCI TECHNOL, V20, P367
[18]  
FATAFTAH A, 1997, THESIS NE U
[19]  
FRIMMEL FH, 1989, HUMIC SUBSTANCES ENV
[20]   ISOLATION OF HUMIC-ACID FROM THE BROWN ALGA PILAYELLA-LITTORALIS [J].
GHABBOUR, EA ;
KHAIRY, AH ;
CHENEY, DP ;
GROSS, V ;
DAVIES, G ;
GILBERT, TR ;
ZHANG, XY .
JOURNAL OF APPLIED PHYCOLOGY, 1994, 6 (5-6) :459-468