Organic acid enhanced soil risk element (Cd, Pb and Zn) leaching and secondary bioconcentration in water lettuce (Pistia stratiotes L.) in the rhizofiltration process
Language English Country United States Media print
Document type Journal Article, Research Support, Non-U.S. Gov't
- MeSH
- Araceae growth & development metabolism MeSH
- Biodegradation, Environmental MeSH
- Biological Transport MeSH
- Biomass MeSH
- Time Factors MeSH
- Water Pollutants, Chemical metabolism MeSH
- Cadmium metabolism MeSH
- Plant Roots growth & development metabolism MeSH
- Citric Acid metabolism MeSH
- Carboxylic Acids metabolism MeSH
- Soil Pollutants metabolism MeSH
- Plant Leaves growth & development metabolism MeSH
- Lead metabolism MeSH
- Soil chemistry MeSH
- Tartrates metabolism MeSH
- Metals, Heavy metabolism MeSH
- Zinc metabolism MeSH
- Publication type
- Journal Article MeSH
- Research Support, Non-U.S. Gov't MeSH
- Geographicals
- Czech Republic MeSH
- Names of Substances
- Water Pollutants, Chemical MeSH
- Cadmium MeSH
- Citric Acid MeSH
- Carboxylic Acids MeSH
- Soil Pollutants MeSH
- Lead MeSH
- Soil MeSH
- Tartrates MeSH
- tartaric acid MeSH Browser
- Metals, Heavy MeSH
- Zinc MeSH
The use of natural chelates to enhance risk element mobility combined with rhizofiltration by free floating macrophytes have not been thoroughly studied in recent years. The aim of this study was to investigate the efficiency of organic acids in soil by conducting flushing experiments to enhance the mobility of Cd, Pb, and Zn from soil to solution. In addition, the bioaccumulation of Cd, Pb, and Zn, in water lettuce (Pistia stratiotes L.) will be studied as they affect the biomass in the rhizofiltration process. The results revealed that citric and tartaric acids mobilised the highest amount of all risk elements. In comparison to control, citric acid mobilised 71%, 181%, and 112% of Cd, Pb, and Zn while tartaric acid mobilised 70%, 155%, and 135% of Cd, Pb, and Zn respectively. The bioconcentration factor was approximately 2-5 times higher for juvenile plants than mature plants for all treatments as well as for both parts (leaves and roots). The risk element translocation into aerial parts decreased with increased time. Juvenile and mature plants proved a high accumulation potential and a 3 week growth period was observed as a sufficient time period to remove more than 80% of Cd, Pb, and Zn.
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