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Effect of moisture regime on the redistribution of heavy metals in paddy soil 被引量:29

Effect of moisture regime on the redistribution of heavy metals in paddy soil
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摘要 Sequential extraction procedure was applied to assess the dynamics of solid-phase transformation of added Cu, Pb, Cd, and Hg in a typical Chinese paddy soil incubated under three moisture regimes (75% field capacity, wetting-drying cycle, and flooding). The heavy metals spiked in the soil were time-dependently transferred from the easily extractable fraction (the exchangeable fraction) into less labile fractions (Fe-Mn oxide- and organic matter-bound fractions), and thus reduced lability of the metals. No significant changes were found for the carbonate-bound and residual fractions of the heavy metals in the soil during the whole incubation. Change rate of the mobility factor (MF), a proportion of weakly bound fractions (exchangeable and carbonate-bound) in the total metal of soil, reflected the transformation rate of metal speciation from the labile fractions toward stable fractions. It was found that soil moisture regime did not change the direction and pathways of transformation of metal speciation, but it significantly affected the transformation rate. In general, the paddy soil under flooding regime had higher metal reactivity compared with 75% field capacity and wetting-drying cycle regimes, resulting in the more complete movement of metals toward stable fractions. This might be related to the increased pH, precipitation of the metals with sulfides and higher concentration of amorphous Fe oxides under submerged condition. Sequential extraction procedure was applied to assess the dynamics of solid-phase transformation of added Cu, Pb, Cd, and Hg in a typical Chinese paddy soil incubated under three moisture regimes (75% field capacity, wetting-drying cycle, and flooding). The heavy metals spiked in the soil were time-dependently transferred from the easily extractable fraction (the exchangeable fraction) into less labile fractions (Fe-Mn oxide- and organic matter-bound fractions), and thus reduced lability of the metals. No significant changes were found for the carbonate-bound and residual fractions of the heavy metals in the soil during the whole incubation. Change rate of the mobility factor (MF), a proportion of weakly bound fractions (exchangeable and carbonate-bound) in the total metal of soil, reflected the transformation rate of metal speciation from the labile fractions toward stable fractions. It was found that soil moisture regime did not change the direction and pathways of transformation of metal speciation, but it significantly affected the transformation rate. In general, the paddy soil under flooding regime had higher metal reactivity compared with 75% field capacity and wetting-drying cycle regimes, resulting in the more complete movement of metals toward stable fractions. This might be related to the increased pH, precipitation of the metals with sulfides and higher concentration of amorphous Fe oxides under submerged condition.
出处 《Journal of Environmental Sciences》 SCIE EI CAS CSCD 2011年第3期434-443,共10页 环境科学学报(英文版)
基金 supported by the National Basic Research Program (973) of China (No. 2005CB121104) the National Natural Science Foundation of China (No.41071145)
关键词 heavy metal SPECIATION moisture regime REDISTRIBUTION paddy soil heavy metal speciation moisture regime redistribution paddy soil
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参考文献25

  • 1Kashem M A, Singh B R, 2001a. Metal availability in contaminated soils: I. Effects of floodingand organic matter on changes in Eh, pH and solubility of Cd, Ni and Zn. Nutrient Cycling in Agroecosystems, 61 (3): 247-255.
  • 2Chuan M C, Shu G Y, Liu J C, 1996. Solubility of heavy metals in a contaminated soil: effects of redox potential and pH. Water, Air, and Soil Pollution, 90(3): 543-556.
  • 3Ettler V, Vaněk A, Mihaljevi M, Bezdi Ka P, 2005. Contrasting lead speciation in forest and tilled soils heavily polluted by lead metallurgy. Chemosphere, 58(10): 1449-1459.
  • 4Kabra K, Chaudhary R, Sawhney R L, 2007. Effect of pH on solar photocatalytic reduction and deposition of cu(Ⅱ), Ni(Ⅱ), Pb(Ⅱ) and Zn(Ⅱ): Speciation modeling and reaction kinetics. Journal of Hazardous Materials, 149(3): 680-685.
  • 5Jalali M, Khanlari Z V, 2008. Effect of aging process on the fractionation of heavy metals in some calcareous soils of Iran. Geoderma, 143(1-2): 26-40.
  • 6Narteh L T, Sahrawat K L, 1999. Influence of flooding on electrochemical and chemical properties of West African soils. Geoderma, 87(3-4): 179-207.
  • 7McBride M B, 1994. Environmental Chemistry of Soils. Oxford University Press, London. 127-333.
  • 8Martínez C E, McBride M B, 2001. Cd, Cu, Pb, and Zn coprecipitates in Fe oxide formed at different pH: Aging effects on metal solubility and extractability by citrate. Environmental Toxicology and Chemistry, 20(1): 122-126.
  • 9Jenne E A, 1968. Controls on Mn, Fe, Co, Ni, Cu, and Zn concentrations in soils and water: the significant role of hydrous Mn and Fe oxides. Advances in Chemistry Series, 73: 337-387.
  • 10Phillips I R, 1999. Copper, lead, cadmium, and zinc sorption by waterlogged and air-dry soil. Soil and Sediment Contamination, 8(3): 343-364.

二级参考文献29

  • 1Fitz W J, Wenzel W W, Zhang H, Nurmi J, Stipek K, Fischerova Z et al., 2003. Rhizosphere characteristics of the arsenic hyperaccumulator Pteris vittata L. and monitoring of phytoremoval efficiency. Environmental Science and Technology, 37(21): 5008-5014.
  • 2Holm P E, Christensen T H, Lorenz S E, Hamon R E, Domingues H C, Sequeira E M, McGrath S P, 1998. Measured soil water concentrations of cadmium and zinc in plant pots and estimated leaching outflows from contaminated soils. Water, Air and Soil Pollution, 102(1-2): 105-115.
  • 3Holm P E, Christensen T H, Tjell J C, McGrath S P, 1995. Speciation of cadmium and zinc with application to soil solutions. Journal of Environ Quality, 24:183-190.
  • 4Kim K R, Owens G, Naidu R, 200-9. Heavy metal distribution, bioaccessibility and phytoavailability in long-term contaminated soils from Lake Macuqarie. Australian Journal of Soil Research, 47(2): 166-176.
  • 5Knight B, Zhao F J, McGrath S P, Shen Z G, 1997. Zinc and cadmium uptake by the hyperaccumulator Thlaspi caerulescens in contaminated soils and its effects on the concentration and chemical speciation of metals in soil solution. Plant and Soil, 197: 71-78.
  • 6Krishnamurti G S R, Naidu R, 2000. Speciation and phytoavailability of cadmium in selected surface soils of south Australia. Australian Journal of Soil Research, 38: 991- 1004.
  • 7Maskall J E, Thornton I, 1998. Chemical partitioning of heavy metals in soils, clays and rocks at historical lead smelting sites. Water, Air and Soil Pollution, 108(3-4): 391-409.
  • 8McBride M, Sauve S, Hendershot W, 1997. Solubility control of Cu, Zn, Cd and Pb in contaminated soils. European Journal of Soil Science, 48: 337-346.
  • 9Miller W P, Miller D M, 1987. A micro pipette method for soil mechanical analysis. Communication of Soil Science and Plant Analysis, 18: 1-15.
  • 10Morrison A L, i003. An assessment of the effectiveness of lead pollution reduction strategies in North Lake Macquarie, NSW, Australia. Science of the Total Environment, 303(1- 2): 125-138.

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