Can liming change root anatomy, biomass allocation and trace element distribution among plant parts of Salix × smithiana in trace element-polluted soils?
Language English Country Germany Media print-electronic
Document type Journal Article
Grant support
CIGA 20142005
Česká Zemědělská Univerzita v Praze
20172016
Česká Zemědělská Univerzita v Praze
PubMed
28664494
DOI
10.1007/s11356-017-9510-7
PII: 10.1007/s11356-017-9510-7
Knihovny.cz E-resources
- Keywords
- Below-ground and above-ground biomass, Dolomite, Image analyses, Quick lime, Root morphology, Silky-leaf osier,
- MeSH
- Biodegradation, Environmental MeSH
- Biomass MeSH
- Plant Roots anatomy & histology drug effects MeSH
- Soil Pollutants analysis metabolism MeSH
- Oxides chemistry MeSH
- Soil chemistry MeSH
- Salix drug effects growth & development metabolism MeSH
- Calcium Compounds chemistry MeSH
- Trace Elements analysis metabolism MeSH
- Metals, Heavy analysis metabolism MeSH
- Publication type
- Journal Article MeSH
- Names of Substances
- Soil Pollutants MeSH
- lime MeSH Browser
- Oxides MeSH
- Soil MeSH
- Calcium Compounds MeSH
- Trace Elements MeSH
- Metals, Heavy MeSH
Willows (Salix spp.) are considered to be effective for the phytoremediation of trace elements from contaminated soils, but their efficiency is limited in heavily polluted soils because of poor growth. Liming can be a desirable measure to decrease the plant availability of elements, resulting in improved plant development. Notably, large root area and maximum soil penetration are basic parameters that improve the efficiency of phytoremediation. The impact of soil chemical properties on willow root anatomy and the distribution of trace elements below-ground have rarely been studied. The effect of liming on root parameters, biomass allocation and trace element distribution in non-harvestable (coarse roots, fine roots, stumps) and harvestable plant parts (twigs and leaves) of Salix × smithiana was assessed at the end of a 4-year pot experiment with two trace element-polluted soils that differed in terms of soil pH. Stump biomass predominated in weakly acidic soil. In neutral soil, the majority of biomass was located in fine roots and stumps; the difference from other plant parts was minor. Trace elements were the most concentrated in fine roots. Translocation to above-ground biomass increased as follows: Pb < As < Zn~Cd. In contrast to Cd and Zn, great differences in As and Pb mobility in plants were recorded after measurements of individual below-ground biomass (stumps < coarse roots < fine roots). Lime application decreased the concentrations of mobile Cd and Zn and related levels in plants, improved biomass production and root parameters and increased the removal of all trace elements in weakly acidic soil. None or minimum differences in the monitored parameters were recorded for dolomite treatments in both soils. The dose and source of liming had crucial effects on root anatomy. Growing willows in limed trace element-polluted soils is a suitable measure for combination of two remediation strategies, i.e. phytoextraction of Cd and Zn and assisted phytostabilization of As and Pb.
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