Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2007;173(3):509-516.
doi: 10.1111/j.1469-8137.2006.01952.x.

Do high-nickel leaves shed by the nickel hyperaccumulator Alyssum murale inhibit seed germination of competing plants?

Affiliations

Do high-nickel leaves shed by the nickel hyperaccumulator Alyssum murale inhibit seed germination of competing plants?

Lan Zhang et al. New Phytol. 2007.

Abstract

Elemental allelopathy suggests that nickel (Ni)-rich leaves shed by hyperaccumulators inhibit the germination and growth of nearby plant species. Here, the germination of eight herbaceous species following addition of Alyssum murale biomass or Ni(NO3)2, with the same Ni level added to soil, was assessed. The distribution of Ni in soil was tested by determining Ni phytoavailability and speciation over time. Phytoavailable Ni in soil amended with biomass declined rapidly over time due to Ni binding to iron (Fe)/manganese (Mn) oxides in the soil. No significant effects on seed germination were observed. Unlike the Ni complex in Alyssum biomass, more Ni remained soluble and phytoavailable in soil amended with Ni(NO3)2, thus significantly inhibiting seed germination. High-Ni leaves shed by hyperaccumulators did not appear to create a 'toxic zone' around the plants and inhibit germination or growth of competing plants. The lack of an allelopathic effect was probably related to low Ni availability.

PubMed Disclaimer

References

    1. AOAC. 1984. Official method 3.014(a). In: Official Methods of Analysis of Association of Official Analytical Chemists (AOAC), 14th edn. Gaithersberg, MD, USA: AOAC international, 38-40.
    1. Baker AJM, Walker PL. 1989. Physiological responses of plants to heavy metals and the quantification of tolerance and toxicity. Chemical Speciation Bioavailablity. 1: 7-17.
    1. Baker AJM, McGrath SP, Reeves RD, Smith JAC. 2000. Metal hyperaccumulator plants: a review of the ecology and physiology of a biological resource for phytoremediation of metal-polluted soils. In: Terry N, Bañuelos GS, eds. Phytoremediation of contaminated soil and water. Boca Raton, FL, USA: CRC Press, 85-107.
    1. Basta NT, Ryan JA, Chaney RL. 2005. Trace element chemistry in residual-treated soil: key concepts and metal bioavailability. Journal of Environmental Quality 34: 49-63.
    1. Bhatia NP, Walsh KB, Orlic I, Siegele R, Ashwath N, Baker AJM. 2004. Studies on spatial distribution of nickel in leaves and stems of the metal hyperaccumulator Stackhousia tryonii Bailey using nuclear microprobe (micro-PIXE) and EDXS techniques. Functional Plant Biology 31: 1061-1074.