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Related Experiment Video

Updated: Nov 8, 2025

Two-Dimensional Visualization and Quantification of Labile, Inorganic Plant Nutrients and Contaminants in Soil
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Soil selenium uptake and root system development in plant taxa differing in Se-accumulating capability.

Christopher C Goodson1, David R Parker1, Christopher Amrhein1

  • 1Soil and Water Sciences Section, Department of Environmental Sciences, University of California, Riverside CA 92521, USA.

The New Phytologist
|April 20, 2021
PubMed
Summary

Identifying selenium-accumulating plants is key for phytoremediation. This study found that plants, including hyperaccumulators, access the same labile selenium pools in soil, suggesting broader applicability for selenium removal strategies.

Keywords:
hyperaccumulatorisotopic dilutionlabile Sephytoremediationroot architectureselenium (Se)

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Area of Science:

  • Environmental Science
  • Soil Science
  • Plant Biology

Background:

  • Phytoremediation offers a sustainable approach for removing selenium (Se) from contaminated environments.
  • Identifying plant taxa capable of extracting recalcitrant soil Se is crucial for enhancing phytoremediation efficiency.

Purpose of the Study:

  • To evaluate the Se uptake capacity of six plant genotypes from labile and non-labile soil pools.
  • To compare the biologically labile pool (L-value) with the chemically labile pool (E-value) of soil Se for different plant species.

Main Methods:

  • A glasshouse study utilized five high-Se soils amended with 75Se, cropped with selected plant genotypes (Astragalus bisulcatus, Astragalus canadensis, Brassica juncea, Sporobolus airoides, and Stanleya pinnata).
  • Biologically labile Se (L-value) was determined using isotopic signatures of harvested shoots.
  • Chemically labile Se (E-value) was measured through 0.1 M KCl extraction.
  • Rhizobox experiments assessed root growth in Se-enriched soils.

Main Results:

  • The biologically labile pool (L-value) ranged from 2-37% of total soil Se, while the chemically labile pool (E-value) ranged from 4-73%.
  • No tested plant consistently showed L-values exceeding E-values, indicating all plants access similar labile Se fractions.
  • Some Se-accumulating plants exhibited root proliferation in Se-present soils, warranting further investigation.

Conclusions:

  • All evaluated plants, including Se hyperaccumulators, appear to utilize the same labile soil Se fractions.
  • The findings suggest that phytoremediation strategies may not need to exclusively target hyperaccumulators for labile Se extraction.
  • Further research into root responses of Se-accumulators in contaminated soils is recommended.