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Uranium (U) source, speciation, uptake, toxicity and bioremediation strategies in soil-plant system: A review

Journal

JOURNAL OF HAZARDOUS MATERIALS
Volume 413, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.jhazmat.2021.125319

Keywords

Uranium; Bioavailability; Accumulation; Phytotoxicity; Tolerance; Bioremediation

Funding

  1. Key R&D Program of Gansu Province, China [17YF1NA065]
  2. Gansu Special Project for Guiding Innovation and Development of Science and Technology, China [2018ZX-09]
  3. Fonds National de la Recherche Scientifique
  4. Charge de recherches of Belgium

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This review focuses on the sources, geochemical behavior, uptake, toxicity, detoxification, and bioremediation strategies of Uranium in soil-plant systems. It highlights mining activities as the main source of soil Uranium contamination, with Uranium mainly accumulating in plant roots but being translocated to aerial parts in some species. Plants tolerate Uranium toxicity through various defense mechanisms.
Uranium(U), a highly toxic radionuclide, is becoming a great threat to soil health development, as returning nuclear waste containing U into the soil systems is increased. Numerous studies have focused on: i) tracing the source in U contaminated soils; ii) exploring U geochemistry; and iii) assessing U phyto-uptake and its toxicity to plants. Yet, there are few literature reviews that systematically summarized the U in soil-plant system in past decade. Thus, we present its source, geochemical behavior, uptake, toxicity, detoxification, and bioremediation strategies based on available data, especially published from 2018 to 2021. In this review, we examine processes that can lead to the soil U contamination, indicating that mining activities are currently the main sources. We discuss the relationship between U bioavailability in the soil-plant system and soil conditions including redox potential, soil pH, organic matter, and microorganisms. We then review the soil-plant transfer of U, finding that U mainly accumulates in roots with a quite limited translocation. However, plants such as willow, water lily, and sesban are reported to translocate high U levels from roots to aerial parts. Indeed, U does not possess any identified biological role, but provokes numerous deleterious effects such as reducing seed germination, inhibiting plant growth, depressing photosynthesis, interfering with nutrient uptake, as well as oxidative damage and genotoxicity. Yet, plants tolerate U toxicity via various defense strategies including antioxidant enzymes, compartmentalization, and phytochelatin. Moreover, we review two biological remediation strategies for Ucontaminated soil: (i) phytoremediation and (ii) microbial remediation. They are quite low-cost and eco-friendly compared with traditional physical or chemical remediation technologies. Finally, we conclude some promising research challenges regarding U biogeochemical behavior in soil-plant systems. This review, thus, further indicates that the combined application of U low accumulators and microbial inoculants may be an effective strategy for the bioremediation of U-contaminated soils.

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