Mechanistic insights into the degradation of trichloroethylene by controlled release nano calcium peroxide activated by iron species coupled with nano iron sulfide

被引:55
作者
Ali, Meesam [1 ,2 ]
Danish, Muhammad [3 ]
Tariq, Muhammad [1 ]
Ahmad, Ayyaz [2 ]
Ayub, Khurram Shahzad [1 ,4 ]
Lyu, Shuguang [1 ,5 ]
机构
[1] East China Univ Sci & Technol, State Environm Protect Key Lab Environm Risk Asse, Shanghai 200237, Peoples R China
[2] Muhammad Nawaz Sharif Univ Engn & Technol, Dept Chem Engn, Multan 60000, Pakistan
[3] Univ Engn & Technol UET, Chem Engn Dept, Lahore Faisalabad Campus,GT Rd, Lahore, Pakistan
[4] Univ Gujrat, Dept Chem Engn, Gujrat, Pakistan
[5] Shanghai Inst Pollut Control & Ecol Secur, Shanghai 200092, Peoples R China
基金
中国国家自然科学基金;
关键词
PVA@nCP; Iron species; nFeS; Surface mechanism; TCE remediation; ALPHA-TOLUIC ACID; MACKINAWITE FES; HYDROGEN-PEROXIDE; AQUEOUS-SOLUTION; RATE CONSTANTS; PERSULFATE; REMOVAL; FENTON; NANOPARTICLES; OXIDATION;
D O I
10.1016/j.cej.2020.125754
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
This study demonstrated a novel approach for prolonged benefits in groundwater remediation schemes utilizing PVA coated nano calcium peroxide (PVA@nCP) activated by Fe(II)/nFeS or Fe(III)/nFeS. Various techniques (SEM, TEM, XRD, EDS, FTIR, and BET) were used to characterize the synthesized nFeS and the prepared PVA@ nCP. Trichloroethylene (TCE) was chosen as the target pollutant and its degradation performance was assessed in both Fe(II)/nFeS and Fe(III)/nFeS activated PVA@nCP systems, and the second-order reaction kinetics were determined. The effect of nFeS dose revealed its dominant role in Fe(III)/nFeS system by providing a surface platform, and at the same time, it also enhanced TCE removal in Fe(II)/nFeS system center dot H2O2 release behavior, the participation of Fe(II) in both solution and surface, and the generated (free and surface-bound) active species (HO center dot, O-2(-)center dot & O-1(2)) determined the insights of synergistic mechanisms. Electron spin resonance (ESR) identified the active species initially, which correspondingly confirmed by quenching tests. Moreover, X-ray photoelectron spectroscopy (XPS) investigated the surface reaction mechanism, showing the dominant role of S(-II) as an efficient converter of iron species as Fe(II) increased from 35% to 45% and 45.5% and Fe(III) decreased from 65% to 55% and 54.5% in Fe(II)/nFeS and Fe(III)/nFeS systems respectively. The effects of initial solution pH and common anions (Cl-, HCO3-, NO3-, & SO42-) on TCE removal were further examined, and recycling use of nFeS was investigated for its reusability in both systems. The findings of this work suggest that both systems, i.e., PVA@nCP/Fe(II)/nFeS and PVA@nCP/Fe(III)/nFeS, are novel processes and possessing potential applicability in TCE contaminated groundwater remediation.
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页数:12
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