4.7 Article

Degradation of tris(1-chloro-2-propanyl) phosphate by the synergistic effect of persulfate and zero-valent iron during a mechanochemical process

期刊

ENVIRONMENTAL SCIENCE AND POLLUTION RESEARCH
卷 29, 期 23, 页码 34349-34359

出版社

SPRINGER HEIDELBERG
DOI: 10.1007/s11356-022-18665-6

关键词

Tris(1-chloro-2-propanyl) phosphate; Persulfate; Mechanochemical; Zero-valent iron; Dechlorination; Degradation

资金

  1. Natural Science Foundation of Jiangsu Province [BK20201388]
  2. Industry Prospect and Common Key Technologies in Jiangsu Province [BE2018015]
  3. Priority Academic Program Development of Jiangsu Higher Education Institutions (PAPD)

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This study revealed a dual pathway for the degradation of tris(1-chloro-2-propanyl) phosphate (TCPP) by zero-valent iron (ZVI) and persulfate as co-milling agents in a mechanochemical process. The method was also effective in degrading TCPP in soil.
This study revealed a dual pathway for the degradation of tris(1-chloro-2-propanyl) phosphate (TCPP) by zero-valent iron (ZVI) and persulfate as co-milling agents in a mechanochemical (MC) process. Persulfate was activated with ZVI to degrade TCPP in a planetary ball mill. After milling for 2 h, 96.5% of the TCPP was degraded with the release of 63.16, 50.39, and 42.01% of the Cl-, SO42-, and PO43-, respectively. In the first degradation pathway, persulfate was activated with ZVI to produce hydroxyl (center dot OH) radicals, and ZVI is oxidized to Fe(II) and Fe(III). A substitution reaction occurred as a result of the attack of center dot OH on the P-O-C bonds, leading to the successive breakage of the three P-O-C bonds in TCPP to produce PO43-. In the second pathway, a C-Cl bond in part of the TCPP molecule was oxidized by SO4 center dot(-) to carbonyl and carboxyl groups. The P-O-C bonds continued to react with center dot OH to produce PO43-. Finally, the intermediate organochloride products were further reductively dechlorinated by ZVI. However, the synergistic effect of the oxidation (center dot OH and SO4 center dot(-)) and the reduction reaction (ZVI) did not completely degrade TCPP to CO2, resulting in a low mineralization rate (35.87%). Moreover, the intermediate products still showed the toxicities in LD50 and developmental toxicant. In addition, the method was applied for the degradation of TCPP in soil, and high degradations (> 83.83%) were achieved in different types of soils.

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