Effect of major cations (Ca2+, Mg2+, Na+, K+) and anions (SO42-, Cl-, NO3-) on Ni accumulation and toxicity in aquatic plant (Lemna minor L.): Implications For Ni risk assessment

被引:19
作者
Gopalapillai, Yamini [1 ,2 ]
Hale, Beverley [1 ]
Vigneault, Bernard [3 ]
机构
[1] Univ Guelph, Sch Environm Sci, Guelph, ON N1G 2W1, Canada
[2] Nat Resources Canada, CANMET Min, Ottawa, ON, Canada
[3] Nat Resources Canada, Geol Survey Canada, Ottawa, ON, Canada
基金
加拿大自然科学与工程研究理事会;
关键词
Ni toxicity; Ni accumulation; Lemna minor; Biotic ligand model; Ni risk assessment; BIOTIC LIGAND MODEL; RAINBOW-TROUT; DAPHNIA-MAGNA; SWISS-CHARD; FRESH-WATER; NICKEL; BIOAVAILABILITY; CALCIUM; COMPLEXATION; ALLEVIATION;
D O I
10.1002/etc.2116
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The effect of major cation activity (Ca2+, Mg2+, Na+, K+) on Ni toxicity, with dose expressed as exposure (total dissolved Ni concentration NiTot) or free Ni ion activity (in solution Ni2+), or as tissue residue (Ni concentration in plant tissue NiTiss) to the aquatic plant Lemna minor L. was examined. In addition, Ni accumulation kinetics was explored to provide mechanistic insight into current approaches of toxicity modeling, such as the tissue residue approach and the biotic ligand model (BLM), and the implications for plant Ni risk assessment. Major cations did not inhibit Ni accumulation via competitive inhibition as expected by the BLM framework. For example, Ca2+ and Mg2+ (sulfate as counter-anion) had an anticompetitive effect on Ni accumulation, suggesting that Ca or Mg forms a ternary complex with Nibiotic ligand. The counter-anion of the added Ca (sulfate, chloride, or nitrate) affected plant response (percentage of root growth inhibition) to Ni. Generally, sulfate and chloride influenced plant response while nitrate did not, even when compared within the same range of Ca2+, which suggests that the anion dominated the observed plant response. Overall, although an effect of major cations on Ni toxicity to L. minor L. was observed at a physiological level, Ni2+ or NiTot alone modeled plant response, generally within a span of twofold, over a wide range of water chemistry. Thus, consideration of major cation competition for improving Ni toxicity predictions in risk assessment for aquatic plants may not be necessary. Environ. Toxicol. Chem. 2013;32:810821. (c) 2013 SETAC
引用
收藏
页码:810 / 821
页数:12
相关论文
共 36 条
[1]  
Adams William J., 2011, Integrated Environmental Assessment and Management, V7, P75, DOI 10.1002/ieam.108
[2]   Kinetic analysis of zinc accumulation in the gills of juvenile rainbow trout: Effects of zinc acclimation and implications for biotic ligand modeling [J].
Alsop, DH ;
Wood, CM .
ENVIRONMENTAL TOXICOLOGY AND CHEMISTRY, 2000, 19 (07) :1911-1918
[3]  
[Anonymous], 1985, STANDARD METHODS EXA, V16th
[4]  
[Anonymous], 2002, Canada Gazette, P1412
[5]   The effect of metal diffusion and supply limitations on conditional stability constants determined for durum wheat roots [J].
Antunes, P. M. C. ;
Hale, B. A. .
PLANT AND SOIL, 2006, 284 (1-2) :229-241
[6]   Use of freshwater algae and duckweeds for phytotoxicity testing [J].
Blinova, I .
ENVIRONMENTAL TOXICOLOGY, 2004, 19 (04) :425-428
[7]   Modelling bioaccumulation and toxicity of metal mixtures [J].
Borgmann, U. ;
Norwood, W. P. ;
Dixon, D. G. .
HUMAN AND ECOLOGICAL RISK ASSESSMENT, 2008, 14 (02) :266-289
[8]   NICKEL IN PLANTS .1. UPTAKE KINETICS USING INTACT SOYBEAN SEEDLINGS [J].
CATALDO, DA ;
GARLAND, TR ;
WILDUNG, RE .
PLANT PHYSIOLOGY, 1978, 62 (04) :563-565
[9]   Measurement and computation of zinc binding to natural dissolved organic matter in European surface waters [J].
Cheng, T ;
De Schamphelaere, K ;
Lofts, S ;
Janssen, C ;
Allen, HE .
ANALYTICA CHIMICA ACTA, 2005, 542 (02) :230-239
[10]   A biotic ligand model predicting acute copper toxicity for Daphnia magna:: The effects of calcium, magnesium, sodium, potassium, and pH [J].
De Schamphelaere, KAC ;
Janssen, CR .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2002, 36 (01) :48-54