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Degradation of azo dye active brilliant red X-3B by composite ferrate solution
Composite ferrate(VI) solution (CFS) with improved stability was successfully prepared in this study. The stability of Fe(VI) increased from hours for potassium ferrate at pH 9–10 to 16 d for 1 mmol L −1 Fe(VI) in CFS at 25 °C, decomposing 24%. The Fe(VI) was more stable at low concentration (1 mmol...
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Published in: | Journal of hazardous materials 2009-01, Vol.161 (2), p.1299-1305 |
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description | Composite ferrate(VI) solution (CFS) with improved stability was successfully prepared in this study. The stability of Fe(VI) increased from hours for potassium ferrate at pH 9–10 to 16
d for 1
mmol
L
−1 Fe(VI) in CFS at 25
°C, decomposing 24%. The Fe(VI) was more stable at low concentration (1
mmol
L
−1) than that at high concentration (10
mmol
L
−1). The degradation of the azo dye reactive brilliant red X-3B (X-3B) by CFS was investigated. The results showed that pH, initial dye concentration and CFS dosage affected the degradation efficiency. For 0.08
mmol
L
−1 X-3B simulate wastewater, the optimal pH and CFS dosage were 8.4 and 25
mg
L
−1 (as K
2FeO
4), and about 99% X-3B was decolorized after 20
min under this conditions. The color decay was considerably faster than the decrease in COD and TOC, which was attributed to the ease of chromophore destruction. Compared with the decolorization, the removal percentage of COD and TOC were 42% and 9% after 60
min, respectively. The Fe(VI) and ClO
− were contained in CFS, which have synergetic effect for the degradation of X-3B. Additionally, phthalic acid and muconic acid were identified as intermediates by GC/MS, which was in accordance with the lowered pH with the reaction time. The complete mineralization of X-3B cannot be achieved under the oxidation by CFS. And a tentative pathway for the oxidative degradation of X-3B was postulated. |
doi_str_mv | 10.1016/j.jhazmat.2008.04.090 |
format | article |
fullrecord | <record><control><sourceid>proquest_cross</sourceid><recordid>TN_cdi_proquest_miscellaneous_35335029</recordid><sourceformat>XML</sourceformat><sourcesystem>PC</sourcesystem><els_id>S0304389408006456</els_id><sourcerecordid>19694158</sourcerecordid><originalsourceid>FETCH-LOGICAL-c496t-ba1f5c6dc06f4e7189451eb58338ccbe2fcc057eb9fbd3858b123d4c5a377fd03</originalsourceid><addsrcrecordid>eNqFkEtv1DAURi1ERYeBnwDyBnYJ17GdOCsE5SlV7aZI7CzHvgaPkniwM5Wmvx6PJoJl7-bbnPs6hLxiUDNg7btdvfttHiaz1A2AqkHU0MMTsmGq4xXnvH1KNsBBVFz14pI8z3kHAKyT4hm5ZEqW6tWG3HzCX8k4s4Q40-ipeYjUHZEau4R7pEMK4xjMvNCEjv6s-Ec6HKmN0z7msCD1mJIpmeN4OI14QS68GTO-XHNLfnz5fHf1rbq-_fr96sN1ZUXfLtVgmJe2dRZaL7Bj5UTJcJCKc2XtgI23FmSHQ-8Hx5VUA2u4E1Ya3nXeAd-St-e5-xT_HDAvegrZ4jiaGeMhay45l9D0j4Ksb3vByuItkWfQpphzQq_3KUwmHTUDfTKud3o1rk_GNQhdjJe-1-uCwzCh-9-1Ki7AmxUw2ZrRJzPbkP9xTflMqkYU7v2Zw-LtPmDS2QacLbqQ0C7axfDIKX8BNiKhvQ</addsrcrecordid><sourcetype>Aggregation Database</sourcetype><iscdi>true</iscdi><recordtype>article</recordtype><pqid>19694158</pqid></control><display><type>article</type><title>Degradation of azo dye active brilliant red X-3B by composite ferrate solution</title><source>ScienceDirect Journals</source><creator>Xu, G.R. ; Zhang, Y.P. ; Li, G.B.</creator><creatorcontrib>Xu, G.R. ; Zhang, Y.P. ; Li, G.B.</creatorcontrib><description>Composite ferrate(VI) solution (CFS) with improved stability was successfully prepared in this study. The stability of Fe(VI) increased from hours for potassium ferrate at pH 9–10 to 16
d for 1
mmol
L
−1 Fe(VI) in CFS at 25
°C, decomposing 24%. The Fe(VI) was more stable at low concentration (1
mmol
L
−1) than that at high concentration (10
mmol
L
−1). The degradation of the azo dye reactive brilliant red X-3B (X-3B) by CFS was investigated. The results showed that pH, initial dye concentration and CFS dosage affected the degradation efficiency. For 0.08
mmol
L
−1 X-3B simulate wastewater, the optimal pH and CFS dosage were 8.4 and 25
mg
L
−1 (as K
2FeO
4), and about 99% X-3B was decolorized after 20
min under this conditions. The color decay was considerably faster than the decrease in COD and TOC, which was attributed to the ease of chromophore destruction. Compared with the decolorization, the removal percentage of COD and TOC were 42% and 9% after 60
min, respectively. The Fe(VI) and ClO
− were contained in CFS, which have synergetic effect for the degradation of X-3B. Additionally, phthalic acid and muconic acid were identified as intermediates by GC/MS, which was in accordance with the lowered pH with the reaction time. The complete mineralization of X-3B cannot be achieved under the oxidation by CFS. And a tentative pathway for the oxidative degradation of X-3B was postulated.</description><identifier>ISSN: 0304-3894</identifier><identifier>EISSN: 1873-3336</identifier><identifier>DOI: 10.1016/j.jhazmat.2008.04.090</identifier><identifier>PMID: 18555598</identifier><identifier>CODEN: JHMAD9</identifier><language>eng</language><publisher>Kidlington: Elsevier B.V</publisher><subject>Active brilliant red X-3B ; Applied sciences ; Azo Compounds - analysis ; Azo Compounds - chemistry ; Azo dye ; Chemical engineering ; Chemistry Techniques, Analytical - methods ; Coloring Agents - analysis ; Composite ferrate solution ; Exact sciences and technology ; General purification processes ; Hydrogen-Ion Concentration ; Iron - chemistry ; Iron Compounds - chemistry ; Models, Chemical ; Naphthalenesulfonates - analysis ; Oxidation ; Pharmaceutical Solutions ; Pollution ; Potassium Compounds - chemistry ; Reactors ; Solutions ; Temperature ; Time Factors ; Waste Disposal, Fluid - methods ; Wastewaters ; Water Pollutants, Chemical - chemistry ; Water Purification - methods ; Water treatment and pollution</subject><ispartof>Journal of hazardous materials, 2009-01, Vol.161 (2), p.1299-1305</ispartof><rights>2008 Elsevier B.V.</rights><rights>2009 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c496t-ba1f5c6dc06f4e7189451eb58338ccbe2fcc057eb9fbd3858b123d4c5a377fd03</citedby><cites>FETCH-LOGICAL-c496t-ba1f5c6dc06f4e7189451eb58338ccbe2fcc057eb9fbd3858b123d4c5a377fd03</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=21235824$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/18555598$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Xu, G.R.</creatorcontrib><creatorcontrib>Zhang, Y.P.</creatorcontrib><creatorcontrib>Li, G.B.</creatorcontrib><title>Degradation of azo dye active brilliant red X-3B by composite ferrate solution</title><title>Journal of hazardous materials</title><addtitle>J Hazard Mater</addtitle><description>Composite ferrate(VI) solution (CFS) with improved stability was successfully prepared in this study. The stability of Fe(VI) increased from hours for potassium ferrate at pH 9–10 to 16
d for 1
mmol
L
−1 Fe(VI) in CFS at 25
°C, decomposing 24%. The Fe(VI) was more stable at low concentration (1
mmol
L
−1) than that at high concentration (10
mmol
L
−1). The degradation of the azo dye reactive brilliant red X-3B (X-3B) by CFS was investigated. The results showed that pH, initial dye concentration and CFS dosage affected the degradation efficiency. For 0.08
mmol
L
−1 X-3B simulate wastewater, the optimal pH and CFS dosage were 8.4 and 25
mg
L
−1 (as K
2FeO
4), and about 99% X-3B was decolorized after 20
min under this conditions. The color decay was considerably faster than the decrease in COD and TOC, which was attributed to the ease of chromophore destruction. Compared with the decolorization, the removal percentage of COD and TOC were 42% and 9% after 60
min, respectively. The Fe(VI) and ClO
− were contained in CFS, which have synergetic effect for the degradation of X-3B. Additionally, phthalic acid and muconic acid were identified as intermediates by GC/MS, which was in accordance with the lowered pH with the reaction time. The complete mineralization of X-3B cannot be achieved under the oxidation by CFS. And a tentative pathway for the oxidative degradation of X-3B was postulated.</description><subject>Active brilliant red X-3B</subject><subject>Applied sciences</subject><subject>Azo Compounds - analysis</subject><subject>Azo Compounds - chemistry</subject><subject>Azo dye</subject><subject>Chemical engineering</subject><subject>Chemistry Techniques, Analytical - methods</subject><subject>Coloring Agents - analysis</subject><subject>Composite ferrate solution</subject><subject>Exact sciences and technology</subject><subject>General purification processes</subject><subject>Hydrogen-Ion Concentration</subject><subject>Iron - chemistry</subject><subject>Iron Compounds - chemistry</subject><subject>Models, Chemical</subject><subject>Naphthalenesulfonates - analysis</subject><subject>Oxidation</subject><subject>Pharmaceutical Solutions</subject><subject>Pollution</subject><subject>Potassium Compounds - chemistry</subject><subject>Reactors</subject><subject>Solutions</subject><subject>Temperature</subject><subject>Time Factors</subject><subject>Waste Disposal, Fluid - methods</subject><subject>Wastewaters</subject><subject>Water Pollutants, Chemical - chemistry</subject><subject>Water Purification - methods</subject><subject>Water treatment and pollution</subject><issn>0304-3894</issn><issn>1873-3336</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2009</creationdate><recordtype>article</recordtype><recordid>eNqFkEtv1DAURi1ERYeBnwDyBnYJ17GdOCsE5SlV7aZI7CzHvgaPkniwM5Wmvx6PJoJl7-bbnPs6hLxiUDNg7btdvfttHiaz1A2AqkHU0MMTsmGq4xXnvH1KNsBBVFz14pI8z3kHAKyT4hm5ZEqW6tWG3HzCX8k4s4Q40-ipeYjUHZEau4R7pEMK4xjMvNCEjv6s-Ec6HKmN0z7msCD1mJIpmeN4OI14QS68GTO-XHNLfnz5fHf1rbq-_fr96sN1ZUXfLtVgmJe2dRZaL7Bj5UTJcJCKc2XtgI23FmSHQ-8Hx5VUA2u4E1Ya3nXeAd-St-e5-xT_HDAvegrZ4jiaGeMhay45l9D0j4Ksb3vByuItkWfQpphzQq_3KUwmHTUDfTKud3o1rk_GNQhdjJe-1-uCwzCh-9-1Ki7AmxUw2ZrRJzPbkP9xTflMqkYU7v2Zw-LtPmDS2QacLbqQ0C7axfDIKX8BNiKhvQ</recordid><startdate>20090130</startdate><enddate>20090130</enddate><creator>Xu, G.R.</creator><creator>Zhang, Y.P.</creator><creator>Li, G.B.</creator><general>Elsevier B.V</general><general>Elsevier</general><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7TV</scope><scope>7U7</scope><scope>C1K</scope><scope>8FD</scope><scope>FR3</scope><scope>KR7</scope></search><sort><creationdate>20090130</creationdate><title>Degradation of azo dye active brilliant red X-3B by composite ferrate solution</title><author>Xu, G.R. ; Zhang, Y.P. ; Li, G.B.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c496t-ba1f5c6dc06f4e7189451eb58338ccbe2fcc057eb9fbd3858b123d4c5a377fd03</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2009</creationdate><topic>Active brilliant red X-3B</topic><topic>Applied sciences</topic><topic>Azo Compounds - analysis</topic><topic>Azo Compounds - chemistry</topic><topic>Azo dye</topic><topic>Chemical engineering</topic><topic>Chemistry Techniques, Analytical - methods</topic><topic>Coloring Agents - analysis</topic><topic>Composite ferrate solution</topic><topic>Exact sciences and technology</topic><topic>General purification processes</topic><topic>Hydrogen-Ion Concentration</topic><topic>Iron - chemistry</topic><topic>Iron Compounds - chemistry</topic><topic>Models, Chemical</topic><topic>Naphthalenesulfonates - analysis</topic><topic>Oxidation</topic><topic>Pharmaceutical Solutions</topic><topic>Pollution</topic><topic>Potassium Compounds - chemistry</topic><topic>Reactors</topic><topic>Solutions</topic><topic>Temperature</topic><topic>Time Factors</topic><topic>Waste Disposal, Fluid - methods</topic><topic>Wastewaters</topic><topic>Water Pollutants, Chemical - chemistry</topic><topic>Water Purification - methods</topic><topic>Water treatment and pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Xu, G.R.</creatorcontrib><creatorcontrib>Zhang, Y.P.</creatorcontrib><creatorcontrib>Li, G.B.</creatorcontrib><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Pollution Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Technology Research Database</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><jtitle>Journal of hazardous materials</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Xu, G.R.</au><au>Zhang, Y.P.</au><au>Li, G.B.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Degradation of azo dye active brilliant red X-3B by composite ferrate solution</atitle><jtitle>Journal of hazardous materials</jtitle><addtitle>J Hazard Mater</addtitle><date>2009-01-30</date><risdate>2009</risdate><volume>161</volume><issue>2</issue><spage>1299</spage><epage>1305</epage><pages>1299-1305</pages><issn>0304-3894</issn><eissn>1873-3336</eissn><coden>JHMAD9</coden><abstract>Composite ferrate(VI) solution (CFS) with improved stability was successfully prepared in this study. The stability of Fe(VI) increased from hours for potassium ferrate at pH 9–10 to 16
d for 1
mmol
L
−1 Fe(VI) in CFS at 25
°C, decomposing 24%. The Fe(VI) was more stable at low concentration (1
mmol
L
−1) than that at high concentration (10
mmol
L
−1). The degradation of the azo dye reactive brilliant red X-3B (X-3B) by CFS was investigated. The results showed that pH, initial dye concentration and CFS dosage affected the degradation efficiency. For 0.08
mmol
L
−1 X-3B simulate wastewater, the optimal pH and CFS dosage were 8.4 and 25
mg
L
−1 (as K
2FeO
4), and about 99% X-3B was decolorized after 20
min under this conditions. The color decay was considerably faster than the decrease in COD and TOC, which was attributed to the ease of chromophore destruction. Compared with the decolorization, the removal percentage of COD and TOC were 42% and 9% after 60
min, respectively. The Fe(VI) and ClO
− were contained in CFS, which have synergetic effect for the degradation of X-3B. Additionally, phthalic acid and muconic acid were identified as intermediates by GC/MS, which was in accordance with the lowered pH with the reaction time. The complete mineralization of X-3B cannot be achieved under the oxidation by CFS. And a tentative pathway for the oxidative degradation of X-3B was postulated.</abstract><cop>Kidlington</cop><pub>Elsevier B.V</pub><pmid>18555598</pmid><doi>10.1016/j.jhazmat.2008.04.090</doi><tpages>7</tpages></addata></record> |
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language | eng |
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source | ScienceDirect Journals |
subjects | Active brilliant red X-3B Applied sciences Azo Compounds - analysis Azo Compounds - chemistry Azo dye Chemical engineering Chemistry Techniques, Analytical - methods Coloring Agents - analysis Composite ferrate solution Exact sciences and technology General purification processes Hydrogen-Ion Concentration Iron - chemistry Iron Compounds - chemistry Models, Chemical Naphthalenesulfonates - analysis Oxidation Pharmaceutical Solutions Pollution Potassium Compounds - chemistry Reactors Solutions Temperature Time Factors Waste Disposal, Fluid - methods Wastewaters Water Pollutants, Chemical - chemistry Water Purification - methods Water treatment and pollution |
title | Degradation of azo dye active brilliant red X-3B by composite ferrate solution |
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