Molecular weight fractionation of humic substances by adsorption onto minerals

被引:158
作者
Hur, J
Schlautman, MA [1 ]
机构
[1] Clemson Univ, Dept Agr & Biol Engn, Clemson, SC 29634 USA
[2] Clemson Univ, Dept Environm Engn & Sci, Anderson, SC 29625 USA
[3] Clemson Univ, Dept Environm Toxicol, Pendleton, SC 29670 USA
[4] Clemson Univ, Clemson Inst Environm Toxicol, Pendleton, SC 29670 USA
基金
美国国家科学基金会;
关键词
humic substances; adsorption; fractionation; molecular weight; size exclusion chromatography; mineral surface;
D O I
10.1016/S0021-9797(03)00444-2
中图分类号
O64 [物理化学(理论化学)、化学物理学];
学科分类号
070304 ; 081704 ;
摘要
Molecular weight (MW) fractionation of Suwannee River fulvic acid (SRFA) and purified Aldrich humic acid (PAHA) by adsorption onto kaolinite and hematite was investigated in equilibrium and rate experiments with a size-exclusion chromatography system using ultraviolet (UV) light detection. The extent of adsorptive fractionation based on UV detection was positively correlated with the percent carbon adsorption for both humic substances (HS), although the specific fractionation pattern observed depended on the particular HS and mineral used. Higher MW fractions of SRFA, an aquatic HS, were preferentially adsorbed to both kaolinite and hematite whereas the fractionation trends for PAHA, a terrestrial peat HS, differed for the two minerals. The contrasting fractionation patterns for SRFA versus PAHA can be explained reasonably well by the different structural trends that occur in their respective MW fractions and the underlying adsorption processes. Rate studies of adsorptive fractionation revealed an initial rapid uptake of smaller HS molecules by the mineral surfaces, followed by their replacement at the surface by a much slower uptake of the larger HS molecules present in aqueous solution. (C) 2003 Elsevier Inc. All rights reserved.
引用
收藏
页码:313 / 321
页数:9
相关论文
共 43 条
[1]   Mechanisms of pore water organic matter adsorption to montmorillonite [J].
Arnarson, TS ;
Keil, RG .
MARINE CHEMISTRY, 2000, 71 (3-4) :309-320
[2]   Kinetics of humic acid adsorption at solid-water interfaces [J].
Avena, MJ ;
Koopal, LK .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1999, 33 (16) :2739-2744
[3]   THE ABUNDANCE, DISTRIBUTION, AND CONFIGURATION OF POREWATER ORGANIC COLLOIDS IN RECENT SEDIMENTS [J].
CHIN, YP ;
GSCHWEND, PM .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1991, 55 (05) :1309-1317
[4]   MOLECULAR-WEIGHT, POLYDISPERSITY, AND SPECTROSCOPIC PROPERTIES OF AQUATIC HUMIC SUBSTANCES [J].
CHIN, YP ;
AIKEN, G ;
OLOUGHLIN, E .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1994, 28 (11) :1853-1858
[5]   Reaction of forest floor organic matter at goethite, birnessite and smectite surfaces [J].
Chorover, J ;
Amistadi, MK .
GEOCHIMICA ET COSMOCHIMICA ACTA, 2001, 65 (01) :95-109
[6]  
Christl I, 2000, EUR J SOIL SCI, V51, P617, DOI 10.1046/j.1365-2389.2000.00352.x
[7]  
DAVIS JA, 1981, ENVIRON SCI TECHNOL, V26, P1388
[8]   Quantitative approach to humic acid associations [J].
Engebretson, RR ;
Amos, T ;
vonWandruszka, R .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1996, 30 (03) :990-997
[9]   Adsorption of small weak organic acids on goethite: Modeling of mechanisms [J].
Filius, JD ;
Hiemstra, T ;
Van Riemsdijk, WH .
JOURNAL OF COLLOID AND INTERFACE SCIENCE, 1997, 195 (02) :368-380
[10]  
Grimaldi G.O., 1999, THESIS TEXAS A M U