P. W. Cheung, Daryl R. Williams, D. Kirk, P. Murphy, S. Barton, James Barker
{"title":"过氧二硫酸钠对废水中金属偶氮染料的脱色:一个实验研究模板","authors":"P. W. Cheung, Daryl R. Williams, D. Kirk, P. Murphy, S. Barton, James Barker","doi":"10.2174/25902776-v16-e230201-2022-2","DOIUrl":null,"url":null,"abstract":"\n \n It has long been recognized that the presence of azo metal complex dyes and their non-complexed counterparts in wastewaters, which arise from their manufacturing and their use in the textile industries, renders natural waterways intensely coloured, and is therefore aesthetically unacceptable. Azo dye moieties are also known to be precursors of human carcinogenicity.\n \n \n \n This work aimed at the decolourisation of metal-azo dyes present in wastewaters so that pollution of natural bodies of water can be prevented. Decolourisation is indicative of the destruction of the metal-ligand complex, allowing the retrieval of transition metal ions, which are also water contaminants. Fracturing of the azo bond itself minimizes the potential for carcinogenicity of these dyes.\n \n \n \n Decolourisation is achieved by the oxidative action of free radicals furnished by Na2S2O8, the sodium salt of peroxodisulphuric acid (Marshall’s acid). Raman spectroscopy characterizes the dye (ligand) known as “Eriochrome Black T (EBT)” by a peak at 1425 cm-1. Dismantling of its molecular structure by peroxodisulphate will lead to decolourisation accompanied by the collapse of the peak. Concomitantly, as EBT ligands fracture and cease to chelate, metallic ions are released, oxidized to a higher oxidation state, and precipitated as insoluble compounds in alkaline media.\n \n \n \n The concentration of metallic ions in the aqueous phase has been found to be substantially reduced. The successfully treated dye solutions are mostly clear and colourless; their Beer-Lambert absorbances are in the range of 0.02 ≤ absorbance ≤ 0.05. The treatment of Ni(II), Co(II) and Fe(II)-EBT solutions is straightforward; the Cu(II) and Cr(III)-EBT solutions require additional treatment to be included in the above absorbance range. The Cr(III)-EBT is the least responsive to treatment. Fracturing of the azo bond is evinced by Raman Spectroscopy.\n \n \n \n A template to investigate the feasibility of decolourisation of metal-complex dye solutions is pioneered and recommended.\n","PeriodicalId":110993,"journal":{"name":"The Open Environmental Research Journal","volume":"43 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2023-02-02","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Decolourisation of Metal-Azo Dyes in Wastewaters by Sodium Peroxodisulphate: A Template for Experimental Investigations\",\"authors\":\"P. W. Cheung, Daryl R. Williams, D. Kirk, P. Murphy, S. Barton, James Barker\",\"doi\":\"10.2174/25902776-v16-e230201-2022-2\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"\\n \\n It has long been recognized that the presence of azo metal complex dyes and their non-complexed counterparts in wastewaters, which arise from their manufacturing and their use in the textile industries, renders natural waterways intensely coloured, and is therefore aesthetically unacceptable. Azo dye moieties are also known to be precursors of human carcinogenicity.\\n \\n \\n \\n This work aimed at the decolourisation of metal-azo dyes present in wastewaters so that pollution of natural bodies of water can be prevented. Decolourisation is indicative of the destruction of the metal-ligand complex, allowing the retrieval of transition metal ions, which are also water contaminants. Fracturing of the azo bond itself minimizes the potential for carcinogenicity of these dyes.\\n \\n \\n \\n Decolourisation is achieved by the oxidative action of free radicals furnished by Na2S2O8, the sodium salt of peroxodisulphuric acid (Marshall’s acid). Raman spectroscopy characterizes the dye (ligand) known as “Eriochrome Black T (EBT)” by a peak at 1425 cm-1. Dismantling of its molecular structure by peroxodisulphate will lead to decolourisation accompanied by the collapse of the peak. Concomitantly, as EBT ligands fracture and cease to chelate, metallic ions are released, oxidized to a higher oxidation state, and precipitated as insoluble compounds in alkaline media.\\n \\n \\n \\n The concentration of metallic ions in the aqueous phase has been found to be substantially reduced. The successfully treated dye solutions are mostly clear and colourless; their Beer-Lambert absorbances are in the range of 0.02 ≤ absorbance ≤ 0.05. The treatment of Ni(II), Co(II) and Fe(II)-EBT solutions is straightforward; the Cu(II) and Cr(III)-EBT solutions require additional treatment to be included in the above absorbance range. The Cr(III)-EBT is the least responsive to treatment. Fracturing of the azo bond is evinced by Raman Spectroscopy.\\n \\n \\n \\n A template to investigate the feasibility of decolourisation of metal-complex dye solutions is pioneered and recommended.\\n\",\"PeriodicalId\":110993,\"journal\":{\"name\":\"The Open Environmental Research Journal\",\"volume\":\"43 1\",\"pages\":\"0\"},\"PeriodicalIF\":0.0000,\"publicationDate\":\"2023-02-02\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"The Open Environmental Research Journal\",\"FirstCategoryId\":\"1085\",\"ListUrlMain\":\"https://doi.org/10.2174/25902776-v16-e230201-2022-2\",\"RegionNum\":0,\"RegionCategory\":null,\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"\",\"JCRName\":\"\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"The Open Environmental Research Journal","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.2174/25902776-v16-e230201-2022-2","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 0
摘要
人们早就认识到,偶氮金属络合染料及其非络合染料在废水中的存在,这是由于偶氮金属络合染料的制造和纺织工业的使用而产生的,使自然水道呈现强烈的颜色,因此在美学上是不可接受的。偶氮染料也被认为是人类致癌性的前体。这项工作的目的是脱色金属偶氮染料存在于废水中,从而可以防止自然水体的污染。脱色表明金属配体复合物的破坏,允许过渡金属离子的回收,这也是水污染物。偶氮键本身的断裂使这些染料致癌性的可能性降到最低。脱色是通过过氧化二硫酸(马歇尔酸)的钠盐Na2S2O8提供的自由基的氧化作用实现的。拉曼光谱表征染料(配体)称为“Eriochrome Black T (EBT)”的峰值在1425厘米-1。过二硫酸盐破坏其分子结构将导致脱色并伴有峰的崩塌。同时,随着EBT配体断裂并停止螯合,金属离子被释放,氧化到更高的氧化态,并在碱性介质中沉淀为不溶化合物。发现水相中金属离子的浓度大大降低了。成功处理的染料溶液大多是透明无色的;其比尔-朗伯吸光度范围为0.02≤吸光度≤0.05。Ni(II), Co(II)和Fe(II)-EBT溶液的处理很简单;Cu(II)和Cr(III)-EBT溶液需要额外处理才能包含在上述吸光度范围内。Cr(III)-EBT对治疗反应最差。用拉曼光谱证实了偶氮键的断裂。研究金属络合染料溶液脱色可行性的模板是首创和推荐的。
Decolourisation of Metal-Azo Dyes in Wastewaters by Sodium Peroxodisulphate: A Template for Experimental Investigations
It has long been recognized that the presence of azo metal complex dyes and their non-complexed counterparts in wastewaters, which arise from their manufacturing and their use in the textile industries, renders natural waterways intensely coloured, and is therefore aesthetically unacceptable. Azo dye moieties are also known to be precursors of human carcinogenicity.
This work aimed at the decolourisation of metal-azo dyes present in wastewaters so that pollution of natural bodies of water can be prevented. Decolourisation is indicative of the destruction of the metal-ligand complex, allowing the retrieval of transition metal ions, which are also water contaminants. Fracturing of the azo bond itself minimizes the potential for carcinogenicity of these dyes.
Decolourisation is achieved by the oxidative action of free radicals furnished by Na2S2O8, the sodium salt of peroxodisulphuric acid (Marshall’s acid). Raman spectroscopy characterizes the dye (ligand) known as “Eriochrome Black T (EBT)” by a peak at 1425 cm-1. Dismantling of its molecular structure by peroxodisulphate will lead to decolourisation accompanied by the collapse of the peak. Concomitantly, as EBT ligands fracture and cease to chelate, metallic ions are released, oxidized to a higher oxidation state, and precipitated as insoluble compounds in alkaline media.
The concentration of metallic ions in the aqueous phase has been found to be substantially reduced. The successfully treated dye solutions are mostly clear and colourless; their Beer-Lambert absorbances are in the range of 0.02 ≤ absorbance ≤ 0.05. The treatment of Ni(II), Co(II) and Fe(II)-EBT solutions is straightforward; the Cu(II) and Cr(III)-EBT solutions require additional treatment to be included in the above absorbance range. The Cr(III)-EBT is the least responsive to treatment. Fracturing of the azo bond is evinced by Raman Spectroscopy.
A template to investigate the feasibility of decolourisation of metal-complex dye solutions is pioneered and recommended.