A Review on Remediation Technologies of PCBs from the Contaminated Soils or Sediments

Article Preview

Abstract:

Polychlorinated biphenyls, which are toxic, carcinogenic and mutagenic, are ubiquitous and persistent in environment. For PCBs are hydrophobic and lipophilic, soils or sediments are their final destinations in environment. Consequently, PCBs-contaminated soils or sediments are increasingly attracting more and more attention. In this paper, basic properties of PCBs and the situation of PCBs-contaminated soils or sediments were described. Remediation technologies of PCBs-contaminated soils or sediments inside and outside China were reviewed. This paper also presented the prospect of technology development.

You might also be interested in these eBooks

Info:

Periodical:

Advanced Materials Research (Volumes 955-959)

Pages:

2238-2242

Citation:

Online since:

June 2014

Export:

Price:

Permissions CCC:

Permissions PLS:

Сopyright:

© 2014 Trans Tech Publications Ltd. All Rights Reserved

Share:

Citation:

* - Corresponding Author

[1] The influence of soil composition on the leachability of selected hydrophobic organic compounds (HOCs)from soils using a batch leaching test[J]. Journal of Hazardous Materials, 2013, 254-255: 26-35.

DOI: 10.1016/j.jhazmat.2013.03.019

Google Scholar

[2] United Nations Industrial Development Organization. Destruction Technologies for Polychlorinated Biphenyls (PCBs)[R]. Italy: United Nations Industrial Development Organization, (2000).

DOI: 10.18356/a34ab52c-en-fr

Google Scholar

[3] U.S. Department of Health and Human Services. Toxicological Profile for Polychlorinated Biphenyls (PCBs)[R]. Atalanta: Public Health Service, (2000).

Google Scholar

[4] U.S. Naval Facilities Engineering Command Engineering Service Center. Application of a Bimetallic Treatment System (BTS) for PCB Removal from Older Structures on DoD Facilities[R]. California: NAVFAC Engineering Service Center, (2011).

Google Scholar

[5] Seija S, Jaakko P. Degradation half-lifetimes of PCDDs, PCDFs and PCBs for environmental fate modeling [J]. Chemosphere, 2000, 40(9-11): 943-949.

DOI: 10.1016/s0045-6535(99)00337-9

Google Scholar

[6] Dalla Valle M, Jurado M, Dachs J, et al. The maximum reservoir capacity of soils for persistent organic pollutants: implications for global cycling [J]. Environment Pollution, 2005, 134(1): 153-164.

DOI: 10.1016/j.envpol.2004.07.011

Google Scholar

[7] Meijer S N, Ockenden W A, Sweetman A, et al. Global distribution and budget of PCBs and HCB in background surface soils: implications for sources and environmental processes [J]. Environmental Science and Technology, 2003, 37(4): 667-672.

DOI: 10.1021/es025809l

Google Scholar

[8] Ahmed M, Focht D D. Degradation of polychlorinated biphenyls by two species of Achromobacter [J]. Canadian Journal of Microbiology, 1973, 19(1): 47-52.

DOI: 10.1139/m73-007

Google Scholar

[9] Groeger A G, Fletcher J S. The influence of increasing chlorine content on the accumulation and metabolism of polychlorinated biphenyls (PCBs) by Paul's Scarlet Rose Cells [J]. Plant Cell Report, 1988, 7(5): 329-332.

DOI: 10.1007/bf00269930

Google Scholar

[10] Liu Ya-yun, Sun Hong-bin, Chen Gui-zhu etc. Eco-physiological response of Kandelia candel seedlings to polychlorinated biphenyls (PCBs) treatment [J]. Acta Ecologica Sinica, 2007, 27(2): 746-750. (In Chinese).

Google Scholar

[11] Liu Ya-yun, Sun Hong-bin, Chen Gui-zhu etc. Effects of PCBs on the growth of mangrove specics, Kandelia candel [J]. Marine Environmental Science, 2007 , 26(1): 23-26. (In Chinese).

Google Scholar

[12] Magee K D. Dechlorination of PCB in the presence of plant nitratereductase [J]. Environmental Toxicology & Pharmacology, 2008(25): 144-147.

DOI: 10.1016/j.etap.2007.10.009

Google Scholar

[13] Teng Ying, Luo Yong-ming, Gao Jun etc. Combined remediation effects of arbuscular mycorrhizal fungi-legumes-rhizobium symbiosis on PCBs contaminated soils [J]. Environmental Sciences, 2008, 29(10): 2925-2930. (In Chinese).

Google Scholar