Phosphorus-arsenic interactions in variable-charge soils in relation to arsenic mobility and bioavailability

被引:134
作者
Bolan, Nanthi [1 ,2 ]
Mahimairaja, Santiago [3 ]
Kunhikrishnan, Anitha [4 ]
Choppala, Girish [1 ,2 ,5 ]
机构
[1] Univ S Australia, CERAR, Mawson Lakes, SA 5095, Australia
[2] Univ S Australia, CRC Contaminat Assessment & Remediat Environm, Mawson Lakes, SA 5095, Australia
[3] Tamil Nadu Agr Univ, Dept Environm Sci, Coimbatore 641003, Tamil Nadu, India
[4] Natl Acad Agr Sci, Dept Agrofood Safety, Chem Safety Div, Suwon 441707, Gyeonggi Do, South Korea
[5] Cent Queensland Univ, Ctr Plant & Water Sci, Rockhampton, Qld 4702, Australia
关键词
Arsenic; Adsorption; Phosphorus; Variable-charge soil; Bioavailability; PTERIS-VITTATA; CONTAMINATED SOILS; HOLCUS-LANATUS; PHOSPHATE; ACCUMULATION; HYPERACCUMULATOR; REMEDIATION; RICE; LEAD; L;
D O I
10.1016/j.scitotenv.2013.04.016
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Phosphorus (P) influences arsenic (As) mobility and bioavailability which depends on the charge components of soil. The objective of this study was to examine P-As interaction in variable-charge allophanic soils in relation to P-induced As mobilization and bioavailability. In this work, the effect of P on arsenate [As(V)] adsorption and desorption was examined using a number of allophanic and non-allophanic soils which vary in their anion adsorption capacity. The effect of P on As uptake by Indian mustard (Brassica juncea L.) plants was examined using a solution culture, and a soil plant growth experiment involving two As-spiked allophanic and non-allophanic soils which vary in their anion adsorption capacity, and a field As-contaminated sheep dip soil. Arsenate adsorption increased with an increase in the anion adsorption capacity of soils. The addition of P resulted in an increase in As desorption, and the effect was more pronounced in the case of allophanic soil. In the case of both As-spiked soils and field contaminated sheep-dip soil, application of P increased the desorption of As, thereby increasing its bioavailability. The effect of P on As uptake was more pronounced in the high anion adsorbing allophanic than low adsorbing non-allophanic soil. In the case of solution culture, As phytoavailability decreased with increasing concentration of P which is attributed to the competition of P for As uptake by roots. While increasing P concentration in solution decreased the uptake of As, it facilitated the translocation of As from root to shoot. The net effect of P on As phytoavailability in soils depends on the extent of P-induced As mobilization in soils and P-induced competition for As uptake by roots. The P-induced mobilization of As could be employed in the phytoremediation of As-contaminated sites. However, care must be taken to minimize the leaching of As mobilized through the P-induced desorption, thereby resulting in groundwater and off site contamination. (C) 2013 Elsevier B.V. All rights reserved.
引用
收藏
页码:1154 / 1162
页数:9
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