Molecular size distribution characteristics of the metal-DOM complexes in stream waters by high-performance size-exclusion chromatography (HPSEC) and high-resolution inductively coupled plasma mass spectrometry (ICP-MS)

被引:54
作者
Wu, FC [1 ]
Evans, D
Dillon, P
Schiff, S
机构
[1] Acad Sinica, Inst Geochem, State Key Lab Environm Geochem, Guiyang 550002, Guizhou, Peoples R China
[2] Trent Univ, Dept Chem, Peterborough, ON K9J 7B8, Canada
[3] Univ Waterloo, Dept Earth Sci, Waterloo, ON N2L 3G1, Canada
关键词
D O I
10.1039/b402819h
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
In this work, the complexation of the metals Fe, V, Ce, Th, U, Mo, Cu, Ni, Co, Cr, Zn, Pb and Cd with different molecular size ( MS) fractions of dissolved organic matter (DOM) in natural waters was investigated. In order to assess the MS distribution of the metal-DOM complexes, DOM samples from stream waters were concentrated by reverse osmosis, and were then analyzed by high-performance size-exclusion chromatography (HPSEC) coupled with on-line UV-Vis absorbance and high-resolution inductively coupled plasma mass spectrometry (ICPMS). The MS distribution of overall DOM and its metal-bound complexes was evaluated. The results indicate the following order of decreasing number-averaged molecular weight: Cu > Ni > (Co, Zn, Cr) > Pb > Cd for the DOM-bound complexes of transitional metals, which is consistent with Irving-Williams series, and (Fe, V, Ce) > Th > U > Mo for the DOM-bound complexes of the other metals. The results suggest that the metal distribution among the different MS fractions was closely related to metal binding strength; metals with high binding strength were distributed more in the larger MS fractions, and metals with low strength were distributed more in the smaller MS fractions. Possible mechanisms for these observations were discussed. This study is significant to the understanding of metal complexation with DOM in natural waters.
引用
收藏
页码:979 / 983
页数:5
相关论文
共 49 条
[1]   Trace elemental distribution in soil and compost-derived humic acid molecular fractions and colloidal organic matter in municipal wastewater by flow field-flow fractionation-inductively coupled plasma mass spectrometry (flow FFF-ICP-MS) [J].
Amarasiriwardena, D ;
Siripinyanond, A ;
Barnes, RM .
JOURNAL OF ANALYTICAL ATOMIC SPECTROMETRY, 2001, 16 (09) :978-986
[2]  
ANDRE JS, 2002, NATURWISSENSCHAFTEN, V89, P84
[3]   Determination of metal-humic complexes, free metal ions and total concentrations in natural waters [J].
Appelblad, PK ;
Baxter, DC ;
Thunberg, JO .
JOURNAL OF ENVIRONMENTAL MONITORING, 1999, 1 (03) :211-217
[4]   Copper speciation and binding by organic matter in copper-contaminated streamwater [J].
Breault, RF ;
Colman, JA ;
Aiken, GR ;
McKnight, D .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1996, 30 (12) :3477-3486
[5]   Characterization of aquatic humic substances and their metal complexes by immobilized metal-chelate affinity chromatography on iron(III)-loaded ion exchangers [J].
Burba, P ;
Jakubowski, B ;
Kuckuk, R ;
Küllmer, K ;
Heumann, KG .
FRESENIUS JOURNAL OF ANALYTICAL CHEMISTRY, 2000, 368 (07) :689-696
[6]   Determination of thorium and light rare-earth elements in soil water and its high molecular mass organic fractions by inductively coupled plasma mass spectrometry and on-line-coupled size-exclusion chromatography [J].
Casartelli, EA ;
Miekeley, N .
ANALYTICAL AND BIOANALYTICAL CHEMISTRY, 2003, 377 (01) :58-64
[7]  
CHARLES MS, 1999, ENVIRON SCI TECHNOL, V33, P3264
[8]  
CHEN Y, 1986, ROLE ORGANIC MATTER, P7
[9]   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
[10]   NMR spectroscopy with spectral editing for the analysis of complex mixtures [J].
Dixon, AM ;
Larive, CK .
APPLIED SPECTROSCOPY, 1999, 53 (11) :426A-440A