Arsenic accumulation in the roots of Helianthus annuus and Zea mays by irrigation with arsenic-rich groundwater: Insights from synchrotron X-ray fluorescence imaging

被引:29
作者
Neidhardt, H. [1 ,2 ]
Kramar, U. [2 ]
Tang, X. [2 ]
Guo, H. [3 ]
Norra, S. [2 ]
机构
[1] Univ Tubingen, Dept Geosci, D-72070 Tubingen, Germany
[2] Karlsruhe Inst Technol, Inst Mineral & Geochem, D-76131 Karlsruhe, Germany
[3] China Univ Geosci, Sch Water Resources & Environm, Beijing 100083, Peoples R China
基金
中国国家自然科学基金;
关键词
Arsenic plant uptake; Zea mays; Helianthus annuus; mu-XRF; Soil-plant-transfer; Iron plaque; IRON PLAQUE; TEMPORAL VARIABILITY; SPATIAL-DISTRIBUTION; SOIL; SPECIATION; IMPACT; CHEMISTRY; BEHAVIOR; FIELDS; CROPS;
D O I
10.1016/j.chemer.2015.04.001
中图分类号
P3 [地球物理学]; P59 [地球化学];
学科分类号
0708 ; 070902 ;
摘要
The aim of this study was to investigate the accumulation of arsenic (As) in and on roots of Zea mays (maize) and Helianthus annuus (sunflower) by means of synchrotron-based micro-focused X-ray fluorescence imaging (mu-XRF). Plant and soil samples were collected from two field sites in the Hetao Plain (Inner Mongolia, China) which have been regularly irrigated with As-rich groundwater. Detailed mu-XRF element distribution maps were generated at the Fluo-beamline of the Anka synchrotron facility (Karlsruhe Institute of Technology) to assess the spatial distribution of As in thin sections of plant roots and soil particles. The results showed that average As concentrations in the roots (14.5-27.4 mg kg(-1)) covered a similar range as in the surrounding soil, but local maximum root As concentrations reached up to 424 mg kg(-1) (H. annuus) and 1280 mg kg(-1) (Z. mays), respectively. Importantly, the results revealed that As had mainly accumulated at the outer rhizodermis along with iron (Fe). We therefore conclude that thin crusts of Fe-(hydr)oxides cover the roots and act as an effective barrier to As, similar to the formation of Fe plague in rice roots. In contrast to permanently flooded rice paddy fields, regular flood irrigation results in variable redox conditions within the silty and loamy soils at our study site and fosters the formation of Fe-(hydr)oxide plague on the root surfaces. (C) 2015 Elsevier GmbH. All rights reserved.
引用
收藏
页码:261 / 270
页数:10
相关论文
共 77 条
[1]  
[Anonymous], 2006, World Reference Base for Soil Resources 2006, V103
[2]  
[Anonymous], 2012, ARSENIC CONTAMINATIO, DOI DOI 10.1002/JSFA.4663
[3]  
[Anonymous], 2005, Electron Microprobe Analysis and Scanning Electron Microscopy in Geology
[4]  
Armstrong M., 1998, BASIC LINEAR GEOSTAT, DOI DOI 10.1007/S12020-008-9041-6
[5]   CHARACTERISTICS OF COATINGS FORMED ON RICE ROOTS AS AFFECTED BY IRON AND MANGANESE ADDITIONS [J].
BACHA, RE ;
HOSSNER, LR .
SOIL SCIENCE SOCIETY OF AMERICA JOURNAL, 1977, 41 (05) :931-935
[6]   Mass balance modeling of arsenic processes in cropland soils [J].
Bar-Yosef, B ;
Chang, AC ;
Page, AL .
ENVIRONMENTAL GEOCHEMISTRY AND HEALTH, 2005, 27 (02) :177-184
[7]   Rhizosphere pH dynamics in trace-metal-contaminated soils, monitored with planar pH optodes [J].
Blossfeld, Stephan ;
Perriguey, Jerome ;
Sterckeman, Thibault ;
Morel, Jean-Louis ;
Loesch, Rainer .
PLANT AND SOIL, 2010, 330 (1-2) :173-184
[8]   Aqueous and solid phase arsenic speciation in the sediments of a contaminated wetland and riverbed [J].
Blute, N. K. ;
Jay, J. A. ;
Swartz, C. H. ;
Brabander, D. J. ;
Hemond, H. F. .
APPLIED GEOCHEMISTRY, 2009, 24 (02) :346-358
[9]   Arsenic sequestration by ferric iron plaque on cattail roots [J].
Blute, NK ;
Brabander, DJ ;
Hemond, HF ;
Sutton, SR ;
Newville, MG ;
Rivers, ML .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2004, 38 (22) :6074-6077
[10]   Biogeochemical Redox Processes and their Impact on Contaminant Dynamics [J].
Borch, Thomas ;
Kretzschmar, Ruben ;
Kappler, Andreas ;
Van Cappellen, Philippe ;
Ginder-Vogel, Matthew ;
Voegelin, Andreas ;
Campbell, Kate .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2010, 44 (01) :15-23