Journal
CHEMICAL ENGINEERING JOURNAL
Volume 426, Issue -, Pages -Publisher
ELSEVIER SCIENCE SA
DOI: 10.1016/j.cej.2021.131679
Keywords
Cu(0)/peroxymonosulfate system; Fe(III); Acetaminophen; Fe(IV); Cu(III) and center dot OH
Categories
Funding
- Natural Science Foun-dation of Hunan Province [2018JJ3060]
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The Fe(III)/Cu(0)/PMS system significantly enhances the degradation of acetaminophen and removal of total organic carbon by generating multiple reactive oxidants such as Fe(IV), Cu(III), and hydroxyl radical (center dot OH). Fe(IV) and center dot OH play a major role in the degradation of acetaminophen, while Fe(IV), Cu(III), and center dot OH are responsible for the degradation of orange II. Adjusting the final reaction solution to pH 8.0 and subsiding can ensure compliance with environmental standards for total copper discharge.
Zero valent copper activated peroxymonosulfate (Cu(0)/PMS) system had widely studied for degrading contaminant due to being highly efficient. However, the weak reactivity and easy dismutation of Cu(I) in acid condition restrained its efficiency. In our study, ferric ion (Fe(III)) significantly enhanced Cu(0)/PMS system for acetaminophen degradation and total organic carbon removal. Multiple reactive oxidants including Fe(IV), Cu (III) and hydroxyl radical (center dot OH) were generated in the Fe(III)/Cu(0)/PMS system. In the Fe(III)/Cu(0)/PMS system, Cu(0) generated Cu(I) by hydrogen corrosion and PMS oxidation, and then Fe(III) reacted with Cu(I) and Cu(0) producing Fe(II). At the same time, PMS reduced Cu(II) to Cu(I), and Cu(I) reacted with oxygen with forming hydrogen peroxide (H2O2). Finally, both Cu(I) and Fe(II) induced H2O2 and PMS producing reactive oxidants, and meanwhile H2O2 was formed by the reaction of Fe(IV) and center dot OH. Thereinto, Fe(IV) and center dot OH made main contribution on the degradation of acetaminophen, while Fe(IV), Cu(III) and center dot OH were responsible for orange II degradation. Common water matrix including sulfate ion, nitrate ion and carbonate ion had inapparent impact on acetaminophen degradation, but chloride ion and humic acid limited slightly the degradation of acetaminophen. There had a good degradation of acetaminophen in tap water, lake water and well water with the Fe(III)/Cu(0)/PMS system. Adjusting the final reaction solution to pH 8.0 and subsiding, the discharge of total copper was within the II-level environmental quality standards for surface water in China (1 mg/L). The study might provide a new and promising idea based on Cu(0) activated PMS system for enhanced degradation of contaminants.
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