2 research outputs found
Hydrothermal Carbon-Mediated Fenton-Like Reaction Mechanism in the Degradation of Alachlor: Direct Electron Transfer from Hydrothermal Carbon to Fe(III)
As
Fenton systems suffer from the undesirable FeÂ(III)/FeÂ(II) cycle, great
efforts were made to realize the effective reduction of FeÂ(III) to
FeÂ(II). The effects of hydrothermal carbon (HTC) on the FeÂ(III)/H<sub>2</sub>O<sub>2</sub> Fenton-like reaction and the subsequent degradation
of alachlor in water was systematically investigated, and the results
indicated that HTC could enhance alachlor degradation in FeÂ(III)/H<sub>2</sub>O<sub>2</sub> by promoting the FeÂ(III)/FeÂ(II) cycle via electron
transfer from HTC to FeÂ(III) ions. The apparent alachlor degradation
rate constant in the HTC-G/FeÂ(III)/H<sub>2</sub>O<sub>2</sub> system
(7.02 × 10<sup>–2</sup> min<sup>–1</sup>) was about
3 times higher than that in the FeÂ(III)/H<sub>2</sub>O<sub>2</sub> system (2.25 × 10<sup>–2</sup> min<sup>–1</sup>). The electron spin resonance spectra analysis revealed that HTC
consists of abundant carbon-centered persistent free radicals to act
as the electron donor. Meanwhile, the hydroxyl groups on the surface
of HTC also played an important role in the enhanced alachlor degradation
because the decrease in the surface hydroxyl groups on HTC significantly
decreased the degradation of alachlor. On the basis of these results,
an FeÂ(III) complex with surface hydroxyl groups on HTC was proposed
to favor the electron transfer from the hydroxyl groups to FeÂ(III),
and then, the simultaneously produced FeÂ(II) could accelerate the
catalytic decomposition of H<sub>2</sub>O<sub>2</sub> to facilitate
alachlor degradation. These findings shed new light on the possible
roles of carbon materials in a natural aquatic environment and provide
a new pathway for environmental pollutant control and remediation
of organic contaminants by HTC
Protocatechuic Acid Promoted Alachlor Degradation in Fe(III)/H<sub>2</sub>O<sub>2</sub> Fenton System
In this study, we demonstrate that
protocatechuic acid (PCA) can
significantly promote the alachlor degradation in the FeÂ(III)/H<sub>2</sub>O<sub>2</sub> Fenton oxidation system. It was found that the
addition of protocatechuic acid could increase the alachlor degradation
rate by 10 000 times in this Fenton oxidation system at pH
= 3.6. This dramatic enhancement of alachlor degradation was attributed
to the complexing and reduction abilities of protocatechuic ligand,
which could form stable complexes with ferric ions to prevent their
precipitation and also accelerate the FeÂ(III)/FeÂ(II) cycle to enhance
the ·OH generation. Meanwhile, the FeÂ(III)/PCA/H<sub>2</sub>O<sub>2</sub> system could also work well at near natural pH even in the
case of PCA concentration as low as 0.1 mmol/L. More importantly,
both alachlor and PCA could be effectively mineralized in this Fenton
system, suggesting the environmental benignity of PCA/FeÂ(III)/H<sub>2</sub>O<sub>2</sub> Fenton system. We employed gas chromatography–mass
spectrometry to identify the degradation intermediates of alachlor
and then proposed a possible alachlor degradation mechanism in this
novel Fenton oxidation system. This study provides an efficient way
to remove chloroacetanilide herbicides, and also shed new insight
into the possible roles of widely existed phenolic acids in the conversion
and the mineralization of organic contaminants in natural aquatic
environment