Influence of pH and metal/carbon ratios on soluble organic complexation of Fe(II), Fe(III) and Al(III) in soil solutions determined by diffusive gradients in thin films

被引:54
作者
Jansen, B [1 ]
Nierop, KGJ [1 ]
Verstraten, JM [1 ]
机构
[1] Univ Amsterdam, Ctr Geoecol Res, IBED Phys Geog & Soil Sci, NL-1018 WV Amsterdam, Netherlands
关键词
DGT; DOM; complexation; Al(III); Fe(II); Fe(III);
D O I
10.1016/S0003-2670(01)01551-3
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
Soluble complexation of Al(II), Fe(II) and Fe(III) with dissolved organic matter (DOM) greatly influences the bioavailability and mobility of the metals as well as the DOM itself in acidic forest soils. A scarcity of analytical tools to distinguish between 'free' Al(III), Fe(II) and Fe(III) and soluble organic complexes in acidic soil solutions has limited research in this area. We further tested diffusive gradients in thin films (DGT) for this purpose and used it to assess the influence of pH, redox potential and metal/organic carbon (M/C) ratios on soluble organic complexation of AI(III), Fe(II) and Fe(III). We used water extracts of an organic soil (H) horizon from a Fimic Anthrosol at pH 3.5, 4.0 and 4.5 to which we sequentially added the three metal species. DGT worked well for all but Fe(II) at pH 3.5 where a correction for proton competition was needed. For all three metal species, the 'free' fraction increased with increasing M/C ratios. The order of soluble complexation strength was Fe(III) > Al(III) > Fe(II). At low M/C ratios the 'free' fraction was highest at the lowest pH value due to more deprotonated functional groups, at high M/C ratios increased (organic) precipitation at higher pH reversed this effect. Both reduction of Fe(III) and oxidation of Fe(II) were found. Selective precipitation of Fe(III) complexes led to predominantly soluble Fe(II)-DOM complexes at higher M/C ratios. Therefore, in studies of the mobility and bioavailability of Fe and Al in acidic forest soils, both M/C ratios and Fe(II)/Fe(III) speciation in solution must be determined. (C) 2002 Elsevier Science B.V. All rights reserved.
引用
收藏
页码:259 / 270
页数:12
相关论文
共 38 条
[1]  
Alfaro-De la Torre MC, 2000, ANAL CHIM ACTA, V418, P53, DOI 10.1016/S0003-2670(00)00946-6
[2]   DETERMINATION OF IRON(II) IN ROCK, SOIL AND CLAY [J].
BEGHEIJN, LT .
ANALYST, 1979, 104 (1244) :1055-1061
[3]   PH-DEPENDENT BINDING OF ALUMINUM BY A FULVIC-ACID [J].
BROWNE, BA ;
DRISCOLL, CT .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1993, 27 (05) :915-922
[4]   THE SIMULTANEOUS SPECIATION OF ALUMINUM AND IRON IN A FLOW-INJECTION SYSTEM [J].
CLARKE, N ;
DANIELSSON, LG .
ANALYTICA CHIMICA ACTA, 1995, 306 (01) :5-20
[5]   Study of the interaction of Al(III) with a soil fulvic acid in the acid pH range by self-modeling mixture analysis of synchronous fluorescence spectral data [J].
daSilva, JCGE ;
Machado, AASC ;
Oliveira, CJS .
ANALYTICA CHIMICA ACTA, 1997, 349 (1-3) :23-31
[6]   IN-SITU SPECIATION MEASUREMENTS OF TRACE COMPONENTS IN NATURAL-WATERS USING THIN-FILM GELS [J].
DAVISON, W ;
ZHANG, H .
NATURE, 1994, 367 (6463) :546-548
[7]   Sorption coefficients of polycyclic aromatic hydrocarbons for two lake sediments: Influence of the bactericide sodium azide [J].
de Maagd, PGJ ;
Sinnige, TL ;
Schrap, SM ;
Opperhuizen, A ;
Sijm, DTHM .
ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY, 1998, 17 (10) :1899-1907
[8]   In situ measurements of labile Cu, Cd and Mn in river waters using DGT [J].
Denney, S ;
Sherwood, J ;
Leyden, J .
SCIENCE OF THE TOTAL ENVIRONMENT, 1999, 239 (1-3) :71-80
[9]  
FAO, 1988, FAO UNESCO SOIL MAP
[10]   ALUMINUM COMPLEXATION BY HUMIC SUBSTANCES AND ALUMINUM SPECIES IN THE SOIL SOLUTION [J].
GERKE, J .
GEODERMA, 1994, 63 (02) :165-175