In-depth Analysis of the Roles and Mechanisms of Sulfate Radical and Hydroxyl Radical in the Degradation of Metal-Cyanide Complexes

IF 11.4 1区 环境科学与生态学 Q1 ENGINEERING, ENVIRONMENTAL Water Research Pub Date : 2024-10-19 DOI:10.1016/j.watres.2024.122656
Yunmei Wei, Peng Song, Yi Wen, Qin Liao, Xiaoqi Du, Lianying Chen, Jialiang Liang, Gang Long, Takayuki Shimaoka
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Abstract

Persulfate-based advanced oxidation processes (PS-based AOPs), characterized by the coexistence of SO₄•⁻ and HO•, have been proven effective in treating a series of cyanide-bearing pollutants. However, the mechanisms of these reactive species in the degradation of cyanides, especially metal-cyanide complexes, remain unclear or contradictory. The degradation behavior of representative cyanides (including potassium cyanide and potassium ferricyanide) at different pH conditions (2, 7 and 12) in thermally activated persulfate system (T = 60°C) was explored, and the roles of SO₄•⁻ and HO• in cyanide degradation were explored by leveraging the distinct characteristics of reactive species under different pH conditions. The study found that both HO• and SO₄•⁻ can react with free cyanide (CN⁻ and HCN). However, the reaction barrier between CN⁻ and HO• is lower than that between HCN and SO₄•⁻, resulting in a higher removal rate of free cyanide under alkaline conditions compared to acidic and neutral conditions. For complexed cyanide, the complex bonds in ferricyanide were completely broken within 24 hours by thermally activated persulfate at pH 2, releasing free cyanide, indicating the effectiveness of SO₄•⁻ in breaking the Fe-C bonds in ferricyanide. In contrast, ferricyanide was barely decomposed at pH 12, implying the inefficacy of HO• in breaking the Fe-C bonds. This study also innovatively found that SO₄•⁻ breaks the Fe-C bonds by oxidizing Fe(Ⅲ) in ferricyanide to Fe(Ⅳ) or Fe(Ⅴ), releasing CN⁻, which is then converted to CNO⁻ by SO₄•⁻ and HO•. CNO⁻ is further mineralized to NO₃⁻, NH₄⁺, and N₂ through hydrolysis or oxidation reactions. This research clarifies, for the first time, the activity of SO₄•⁻ and HO• toward cyanide degradation in PS-based AOPs.

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深入分析硫酸根自由基和羟基自由基在金属氰化物络合物降解过程中的作用和机理
基于过硫酸盐的高级氧化工艺(PS-based AOPs)以 SO₄-- 和 HO- 共存为特征,已被证明可有效处理一系列含氰化物的污染物。然而,这些反应物在降解氰化物(尤其是金属-氰化物复合物)过程中的作用机制仍不明确或相互矛盾。本研究探讨了具有代表性的氰化物(包括氰化钾和铁氰化钾)在不同 pH 值条件(2、7 和 12)下在热激活过硫酸盐体系(T = 60°C)中的降解行为,并利用不同 pH 值条件下活性物种的不同特性,探讨了 SO₄-- 和 HO- 在氰化物降解中的作用。研究发现,HO- 和 SO₄-- 都能与游离氰化物(CN- 和 HCN)发生反应。不过,CN- 和 HO- 之间的反应障碍低于 HCN 和 SO₄-之间的反应障碍,因此与酸性和中性条件相比,碱性条件下游离氰化物的去除率更高。对于络合氰化物,在 pH 值为 2 的条件下,铁氰化物中的络合物键在 24 小时内被热活化的过硫酸盐完全断裂,释放出游离氰化物,这表明 SO₄-- 能有效断裂铁氰化物中的 Fe-C 键。相反,在 pH 值为 12 时,铁氰化物几乎不被分解,这意味着 HO- 在断裂铁-C 键方面没有作用。这项研究还创新性地发现,SO₄-- 通过将铁氰化物中的铁(Ⅲ)氧化成铁(Ⅳ)或铁(Ⅴ),释放出 CN-,然后在 SO₄-- 和 HO- 的作用下转化成 CNO-,从而断裂铁-C 键。通过水解或氧化反应,CNO- 进一步矿化为 NO₃-、NH₄⁺ 和 N₂。这项研究首次阐明了 SO₄-- 和 HO- 在基于 PS 的 AOPs 中降解氰化物的活性。
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来源期刊
Water Research
Water Research 环境科学-工程:环境
CiteScore
20.80
自引率
9.40%
发文量
1307
审稿时长
38 days
期刊介绍: Water Research, along with its open access companion journal Water Research X, serves as a platform for publishing original research papers covering various aspects of the science and technology related to the anthropogenic water cycle, water quality, and its management worldwide. The audience targeted by the journal comprises biologists, chemical engineers, chemists, civil engineers, environmental engineers, limnologists, and microbiologists. The scope of the journal include: •Treatment processes for water and wastewaters (municipal, agricultural, industrial, and on-site treatment), including resource recovery and residuals management; •Urban hydrology including sewer systems, stormwater management, and green infrastructure; •Drinking water treatment and distribution; •Potable and non-potable water reuse; •Sanitation, public health, and risk assessment; •Anaerobic digestion, solid and hazardous waste management, including source characterization and the effects and control of leachates and gaseous emissions; •Contaminants (chemical, microbial, anthropogenic particles such as nanoparticles or microplastics) and related water quality sensing, monitoring, fate, and assessment; •Anthropogenic impacts on inland, tidal, coastal and urban waters, focusing on surface and ground waters, and point and non-point sources of pollution; •Environmental restoration, linked to surface water, groundwater and groundwater remediation; •Analysis of the interfaces between sediments and water, and between water and atmosphere, focusing specifically on anthropogenic impacts; •Mathematical modelling, systems analysis, machine learning, and beneficial use of big data related to the anthropogenic water cycle; •Socio-economic, policy, and regulations studies.
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