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A review on the scope of remediating chlorinated paraffin contaminated water bodies and soils/sediments

Journal

SCIENCE OF THE TOTAL ENVIRONMENT
Volume 885, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.scitotenv.2023.163941

Keywords

Polychlorinated n -alkane; CPs; Thermal degradation; Photocatalytic degradation; Bioremediation; Phytoremediation

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Chlorinated paraffins, a wide range of complex mixtures of chlorinated alkanes, are ubiquitous materials due to their versatile physicochemical properties and wide range of use. This review covers various remediation techniques for CP-contaminated water bodies and soil/sediments, including thermal, photolytic, photocatalytic, nanoscale zero-valent iron (NZVI), microbial, and plant-based methods. Thermal treatment can achieve almost 100% degradation of CPs, but high operational and maintenance costs are required. Photocatalysis and NZVI also show efficient CP removal, while bioremediation and phytoremediation have shown promising results. Further research should focus on analytical techniques, toxicity assessment, and environmental evaluation of different remediation approaches.
Chlorinated paraffins (CPs) involve a wide range of complex mixtures of chlorinated alkanes. The versatility of their physicochemical properties and their wide range of use has turned them into ubiquitous materials. This review covers the scope of remediating CP-contaminated water bodies and soil/sediments via thermal, photolytic, photocatalytic, nanoscale zero-valent iron (NZVI), microbial and plant-based remediation techniques. Thermal treatments above 800 & DEG;C can lead to almost 100 % degradation of CPs by forming chlorinated polyaromatic hydrocarbons and thus should be supported with appropriate pollution control measures leading to high operational and maintenance costs. The hydrophobic nature of CPs lowers their water solubility and reduces their subsequent photolytic degrada-tion. However, photocatalysis can have considerably higher degradation efficiency and generates mineralized end products. The NZVI also showed promising CP removal efficiency, especially at lower pH, which is challenging to achieve during field application. CPs can also be bioremediated by introducing both naturally occurring bacteria and also by engineered bacterial strains which are capable of producing specific enzymes (like LinA2 and LinB) to cat-alyze CP degradation. Depending on the type of CP, bioremediation can even achieve a dechlorination efficiency of >90 %. Moreover, enhanced degradation rates can be achieved through biostimulation. Phytoremediation has also exhibited CP bioaccumulation and transformation tendencies, both at lab-scale and in field-scale studies. The future research scope can include developing more definitive analytical techniques, toxicity and risk assessment studies of CPs and their degradation products, and technoeconomic and environmental assessment of different remediation approaches.

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