Atomically dispersed Fe boosting elimination performance of g-C3N4 towards refractory sulfonic azo compounds via catalyst-contaminant interaction

Puying Liang , Zhouping Wang , Shiyu Liao , Yang Lou , Jiawei Zhang , Chengsi Pan , Yongfa Zhu , Jing Xu
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Abstract

Herein, an oxygen-doped porous g-C3N4 photocatalyst modified with atomically dispersed Fe (Fe1/OPCN) is successfully prepared and exhibits significant superiority in removing refractory sulfonic azo contaminants from water via catalyst-contaminant interaction. The elimination performance of Fe1/OPCN towards acid red 9, acid red 13 and amaranth containing similar azonaphthalene structure and increasing sulfonic acid groups increases gradually. The amaranth degradation rate of Fe1/OPCN is 17.7 and 6.1 times as that of homogeneous Fenton and OPCN, respectively. In addition, Fe1/OPCN also has more outstanding removal activities towards other contaminants with sulfonic acid and azo groups alone. The considerable enhancement for removing sulfonic azo contaminants of Fe1/OPCN is mainly ascribed to the following aspects: (1) The modified Fe could enhance the adsorption towards sulfonic azo compounds to accelerate the mass transfer, act as e acceptor to promote interfacial charge separation, and trigger the self-Fenton reaction to convert in-situ generated H2O2 into •OH. (2) Fe(Ⅲ) could coordinate with N=N to form d-π conjugation, which could attract e transfer to attack N=N bond. Meanwhile, the inhibited charge recombination could release more free h+ to oxidize sulfonic acid groups into SO4•. (3) Under the cooperation of abundant multiple active species (O2, h+, e, OH, SO4•) formed during the degradation reaction, sulfonic azo compounds could be completely mineralized into harmless small molecules (CO2, H2O, etc.) by means of N=N cleavage, hydroxyl substitution, and aromatic ring opening. This work offers a novel approach for effectively eliminating refractory sulfonic azo compounds from wastewater.

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通过催化剂与污染物的相互作用,原子分散的铁元素提高了 g-C3N4 对难熔磺酰基偶氮化合物的消除性能
本文成功制备了一种用原子分散的 Fe(Fe1/OPCN)修饰的掺氧多孔 g-C3N4 光催化剂,并通过催化剂与污染物的相互作用,在去除水中难去除的磺酸偶氮污染物方面表现出显著的优势。Fe1/OPCN 对酸性红 9、酸性红 13 和含有类似偶氮萘结构且磺酸基团不断增加的苋菜的消除性能逐渐提高。Fe1/OPCN 对苋菜的降解率分别是均相 Fenton 和 OPCN 的 17.7 倍和 6.1 倍。此外,Fe1/OPCN 对其他单独带有磺酸和偶氮基团的污染物的去除活性也更为突出。Fe1/OPCN 对磺酸偶氮污染物的去除率显著提高主要归因于以下几个方面:(1)修饰的 Fe 可增强对磺酸偶氮化合物的吸附以加速传质,作为电子受体促进界面电荷分离,并引发自 Fenton 反应将原位生成的 H2O2 转化为 -OH。(2) Fe(Ⅲ)能与 -N=N- 配位形成 d-π 共轭,从而吸引 e- 转移攻击 -N=N- 键。同时,受抑制的电荷重组可以释放出更多的游离 h+,将磺酸基团氧化成 SO4--。(3) 在降解反应中形成的丰富的多种活性物种(-O2-、h+、e-、-OH、SO4--)的协同作用下,磺酰基偶氮化合物可通过-N=N-裂解、羟基取代和芳香环打开等方式完全矿化为无害的小分子(CO2、H2O 等)。这项研究为有效消除废水中的难溶性磺酰基偶氮化合物提供了一种新方法。
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