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
. 2017:2017:6201048.
doi: 10.1155/2017/6201048. Epub 2017 Jun 22.

Removal of Cu, Zn, Pb, and Cr from Yangtze Estuary Using the Phragmites australis Artificial Floating Wetlands

Affiliations

Removal of Cu, Zn, Pb, and Cr from Yangtze Estuary Using the Phragmites australis Artificial Floating Wetlands

Xiaofeng Huang et al. Biomed Res Int. 2017.

Abstract

Contamination of heavy metals would threaten the water and soil resources; phytoremediation can be potentially used to remediate metal contaminated sites. We constructed the Phragmites australis artificial floating wetlands outside the Qingcaosha Reservoir in the Yangtze Estuary. Water characteristic variables were measured in situ by using YSI Professional Pro Meter. Four heavy metals (copper, zinc, lead, and chromium) in both water and plant tissues were determined. Four heavy metals in estuary water were as follows: 0.03 mg/Kg, 0.016 mg/Kg, 0.0015 mg/Kg, and 0.004 mg/Kg. These heavy metals were largely retained in the belowground tissues of P. australis. The bioaccumulation (BAF) and translation factor (TF) value of four heavy metals were affected by the salinity, temperature, and dissolved oxygen. The highest BAF of each metal calculated was as follows: Cr (0.091 in winter) > Cu (0.054 in autumn) > Pb (0.016 in summer) > Zn (0.011 in summer). Highest root-rhizome TF values were recorded for four metals: 6.450 for Cu in autumn, 2.895 for Zn in summer, 7.031 for Pb in autumn, and 2.012 for Cr in autumn. This indicates that the P. australis AFW has potential to be used to protect the water of Qingcaosha Reservoir from heavy metal contamination.

PubMed Disclaimer

Figures

Figure 1
Figure 1
Location of the study area and the model of the P. australis AFW (AFW, artificial floating wetland; (a) the study site; (b) the P. australis AFW site; (c) the P. australis AFW photo; (d) the P. australis AFW model).
Figure 2
Figure 2
Dry weight of the P. australis aboveground tissues in four seasons.
Figure 3
Figure 3
Metal concentration of Cu, Pb, Zn, and Cr in the P. australis shoots, roots, and rhizomes in four seasons (values are the means of six replicates ± standard deviation; significant difference between sites (within the same season) is showed by small letter; significant difference between seasons (within the same tissue) is showed by capital letter).

Similar articles

Cited by

References

    1. Klavins M., Briede A. Heavy metals in aquatic macrophytes in lakes of Latvia. Proceedings of the Latvian Academy of Sciences Section B Natural Exact and Applied Sciences; 1999; pp. 80–86.
    1. Chen Z., Saito Y., Kanai Y., et al. Low concentration of heavy metals in the Yangtze estuarine sediments, China: A diluting setting. Estuarine, Coastal and Shelf Science. 2004;60(1):91–100. doi: 10.1016/j.ecss.2003.11.021. - DOI
    1. Kumar P. B. A. N., Dushenkov V., Motto H., Raskin I. Phytoextraction: the use of plants to remove heavy metals from soils. Environmental Science & Technology. 1995;29(5):1232–1238. doi: 10.1021/es00005a014. - DOI - PubMed
    1. Hunt A. J., Anderson C. W. N., Bruce N., et al. Phytoextraction as a tool for green chemistry. Green Processing and Synthesis. 2014;3(1):3–22. doi: 10.14315/evth-2014-0205. - DOI
    1. Heaton A. C. P., Rugh C. L., Wang N.-J., Meagher R. B. Phytoremediation of mercury- and methylmercury-polluted soils using genetically engineered plants. Soil and Sediment Contamination. 1998;7(4):497–509. doi: 10.1080/10588339891334384. - DOI

LinkOut - more resources