Predicting As, Cd, Cu, Pb and Zn levels in grasses (Agrostis sp and Poa sp.) and stinging nettle (Urtica dioica) applying soil-plant transfer models

被引:50
作者
Boshoff, Magdalena [1 ]
De Jonge, Maarten [1 ]
Scheifler, Renaud [2 ]
Bervoets, Lieven [1 ]
机构
[1] Univ Antwerp, Lab Syst Physiol & Ecotoxicol Res, Dept Biol, B-2020 Antwerp, Belgium
[2] Univ Franche Comte, CNRS Usc INRA, UMR 6249, F-25030 Besancon, France
关键词
Trace metals; Soil contamination; Vegetation; Soil properties; CaCl2; Aqua-regia; HEAVY-METAL CONCENTRATIONS; CADMIUM CONCENTRATION; CONTAMINATED SOILS; EXTRACTION METHODS; CALCIUM-CHLORIDE; LOLIUM-PERENNE; TRACE-METALS; BIOAVAILABILITY; ACCUMULATION; POLLUTION;
D O I
10.1016/j.scitotenv.2014.06.076
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The aim of this study was to derive regression-based soil plant models to predict and compare metal(loid) (i.e. As, Cd, Cu, Pb and Zn) concentrations in plants (grass Agrostis sp./Poa sp. and nettle Urtica dioica L.) among sites with a wide range of metal pollution and a wide variation in soil properties. Regression models were based on the pseudo total (aqua-regia) and exchangeable (0.01 M CaCl2) soil metal concentrations. Plant metal concentrations were best explained by the pseudo total soil metal concentrations in combination with soil properties. The most important soil property that influenced U. dioica metal concentrations was the clay content, while for grass organic matter (OM) and pH affected the As (OM) and Cu and Zn (pH). In this study multiple linear regression models proved functional in predicting metal accumulation in plants on a regional scale. With the proposed models based on the pseudo total metal concentration, the percentage of variation explained for the metals As, Cd, Cu, Pb and Zn were 0.56%, 0.47%, 0.59%, 0.61%, 030% in nettle and 0.46%, 038%, 027%, 0.50%, 028% in grass. (C) 2014 Elsevier B.V. All rights reserved.
引用
收藏
页码:862 / 871
页数:10
相关论文
共 81 条
  • [1] [Anonymous], 2008, URBAN ECOLOGY INT PE
  • [2] [Anonymous], 2002, OFFICIAL J EUROPEAN, V140, P10
  • [3] [Anonymous], 2008, OVAMSAMENVATTING S B
  • [4] Baker A. J. M., 1990, Heavy metal tolerance in plants: evolutionary aspects., P155
  • [5] Comparison of Extraction Procedures for Assessing Soil Metal Bioavailability of to Wheat Grains
    Bakircioglu, Dilek
    Kurtulus, Yasemin Bakircioglu
    Ibar, Hilmi
    [J]. CLEAN-SOIL AIR WATER, 2011, 39 (08) : 728 - 734
  • [6] Bioavailability of heavy metals in strongly acidic soils treated with exceptional quality biosolids
    Basta, NT
    Sloan, JJ
    [J]. JOURNAL OF ENVIRONMENTAL QUALITY, 1999, 28 (02) : 633 - 638
  • [7] Field-flow fractionation characterization and binding properties of particulate and colloidal organic matter from the Rio Amazon and Rio Negro
    Benedetti, M
    Ranville, JF
    Ponthieu, M
    Pinheiro, JP
    [J]. ORGANIC GEOCHEMISTRY, 2002, 33 (03) : 269 - 279
  • [8] Prediction of cadmium concentration in selected home-produced vegetables
    Bester, Petra Karo
    Lobnik, Franc
    Erzen, Ivan
    Kastelec, Damijana
    Zupan, Marko
    [J]. ECOTOXICOLOGY AND ENVIRONMENTAL SAFETY, 2013, 96 : 182 - 190
  • [9] Behavior of Trifolium repens and Lolium perenne growing in a heavy metal contaminated field:: Plant metal concentration and phytotoxicity
    Bidar, G.
    Garcon, G.
    Pruvot, C.
    Dewaele, D.
    Cazier, F.
    Douay, F.
    Shirali, P.
    [J]. ENVIRONMENTAL POLLUTION, 2007, 147 (03) : 546 - 553
  • [10] Bitton G, 2005, SMALL SCALE FRESHWATER TOXICITY INVESTIGATIONS, VOL 2: HAZARD ASSESSMENT SCHEMES, P215, DOI 10.1007/1-4020-3553-5_7