Abstract

Lead (Pb) is recognized as one of the most pervasive environmental health concerns in the industrialized world. While there has been a substantial reduction in the use of Pb in gasoline, water pipes, and Pb-based residential paint, residual Pb from their use is still in the environment and constitutes an important source of Pb in the atmosphere, water, and soil. Soil acts as a sink for these anthropogenic sources of Pb, accumulating the deposits over time in the upper 2 - 5 cm of undisturbed soil. Generally, Pb binds strongly to soil particles and renders a significant soil-metal fraction insoluble and largely unavailable for phytoremediation or plant uptake. A major objective of current phytoremediation research, therefore, is to induce desorption of Pb from the soil matrix into solution and increase the propensity for plant uptake. We hypothesized that the bioavailability of Pb for plant uptake can be increased through chelate amendments. To test this hypothesis, we mixed delta top soil and peat (2:1) and added lead nitrate [Pb (NO3)2[ to generate a Pb-contaminated soil concentration of 2000 mg Pb/kg dry soil. After incubating the Pb-spiked soil in a greenhouse for 6 weeks, Sesbania plants were grown in the soil and harvested at 6, 8, and 10 weeks after emergence. Six days before each harvest, a chelating agent, ethylenediaminetetraacetic acid (EDTA) was applied to the root zone as an aqueous solution in a 1:1 ratio with the Pb concentration in the soil. Sequential extraction procedures were used to assess selective chemical fractions of Pb in the soil. Our results showed that a higher exchangeable fraction of Pb was available for plant uptake after chelate amendment compared to pre-chelate amendment. We also saw higher root and shoot Pb uptake after chelate amendment compared to pre-chelate amendment, especially at 10 weeks after emergence. Together, these results suggest that chelate amendments can promote the bioavailability of Pb in the soil and increased the propensity for uptake by plants into roots and shoots. Further, these results indicate that Sesbania exaltata can be grown under elevated Pb conditions and may be suitable as a potential crop rotation species for phytoextraction.

Highlights

  • Geochemical forms of heavy metals in contaminated soils affect their solubility, which directly influence their availability to plants [1,2,3]

  • We have found in previous studies [10], using delta top soil and humus peat (2:1), that Ethylenediaminetetraacetic acid (EDTA) was the most effective in solubilizing soil bound Pb and that Pb concentrations in soil solution increased with extraction

  • In a sequential extraction procedure for the speciation of particulate trace metals, Tessier et al [11] found that the exchangeable fraction of Pb (Fraction 1) is readily available for sorption-desorption processes, Fraction 2 is more likely to be susceptible to changes of pH, Fraction 3, and Fraction 4, have a scavenging action for trace metals that is far out of proportion to their (Fe, Mn and organic matter) own concentrations, and should be considered when estimating the bio-availability of a particular metal

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Summary

Introduction

Geochemical forms of heavy metals in contaminated soils affect their solubility, which directly influence their availability to plants [1,2,3]. The total Pb concentration in many contaminated soils may be high, the bioavailable Pb fraction (water soluble and exchangeable) is usually very low due to the strong association of Pb with organic matter, Fe-Mn oxides, and clays, and precipitation as carbonates, hydroxides, and phosphates

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