Transformation of aminopyrine in the presence of free available chlorine: Kinetics, products, and reaction pathways

Aminopyrine (AMP) has been frequently detected in the aquatic environment. In this study, the transformation mechanism of AMP by free available chlorine (FAC) oxidation was investigated. The results showed that FAC reacted with AMP rapidly, and a 74% elimination was achieved for 1.30 μM AMP after 2 ...

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Veröffentlicht in:Chemosphere (Oxford) 2017-03, Vol.171, p.625-634
Hauptverfasser: Cai, Mei-Quan, Feng, Li, Zhang, Li-Qiu
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description Aminopyrine (AMP) has been frequently detected in the aquatic environment. In this study, the transformation mechanism of AMP by free available chlorine (FAC) oxidation was investigated. The results showed that FAC reacted with AMP rapidly, and a 74% elimination was achieved for 1.30 μM AMP after 2 min at 14.08 μM FAC dose. AMP chlorination was strongly pH-dependent, and its reaction included second- and third-order kinetic processes. Three active FAC species, including chlorine monoxide (Cl2O), molecular chlorine (Cl2), and hypochlorous acid (HOCl), were observed to contribute to AMP degradation. The intrinsic rate constants of each FAC species with neutral (AMP0) and cation (AMP+) species were obtained by kinetic fitting. Cl2O exhibited the highest reactivity with AMP0 (kAMP0, Cl2O = (4.33 ± 1.4) × 109 M−1s−1). In addition, Cl2 showed high reactivity (106–107 M−1s−1) in the presence of chloride, compared with HOCl (kAMP+, HOCl = (5.73 ± 0.23) × 102 M−1s−1, kAMP0, HOCl = (9.68 ± 0.96) × 102 M−1s−1). At pH 6.15 and 14.08 μM FAC dose without chloride addition, the contribution of Cl2O reached to the maximum (33.3%), but in the whole pH range, HOCl was the main contributor (>66.6%) for AMP degradation. The significance of Cl2 was noticeable in water containing chloride. Moreover, 11 transformation products were identified, and the main transformation pathways included pyrazole ring breakage, hydroxylation, dehydrogenation, and halogenation. •Aminopyrine (AMP) chlorination included the reactions of AMP with HOCl, Cl2, and Cl2O.•The reactivity of each FAC species toward AMP: HOCl  Cl2.•The role Cl2 became significant in the presence of Cl− at acidic pH.•AMP underwent pyrazole ring opening, hydroxylation, dehydrogenation, and halogenation.
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In this study, the transformation mechanism of AMP by free available chlorine (FAC) oxidation was investigated. The results showed that FAC reacted with AMP rapidly, and a 74% elimination was achieved for 1.30 μM AMP after 2 min at 14.08 μM FAC dose. AMP chlorination was strongly pH-dependent, and its reaction included second- and third-order kinetic processes. Three active FAC species, including chlorine monoxide (Cl2O), molecular chlorine (Cl2), and hypochlorous acid (HOCl), were observed to contribute to AMP degradation. The intrinsic rate constants of each FAC species with neutral (AMP0) and cation (AMP+) species were obtained by kinetic fitting. Cl2O exhibited the highest reactivity with AMP0 (kAMP0, Cl2O = (4.33 ± 1.4) × 109 M−1s−1). In addition, Cl2 showed high reactivity (106–107 M−1s−1) in the presence of chloride, compared with HOCl (kAMP+, HOCl = (5.73 ± 0.23) × 102 M−1s−1, kAMP0, HOCl = (9.68 ± 0.96) × 102 M−1s−1). At pH 6.15 and 14.08 μM FAC dose without chloride addition, the contribution of Cl2O reached to the maximum (33.3%), but in the whole pH range, HOCl was the main contributor (&gt;66.6%) for AMP degradation. The significance of Cl2 was noticeable in water containing chloride. Moreover, 11 transformation products were identified, and the main transformation pathways included pyrazole ring breakage, hydroxylation, dehydrogenation, and halogenation. •Aminopyrine (AMP) chlorination included the reactions of AMP with HOCl, Cl2, and Cl2O.•The reactivity of each FAC species toward AMP: HOCl &lt; Cl2 &lt; Cl2O.•The contribution of each FAC species at neutral pH (no Cl− added): HOCl &gt; Cl2O &gt; Cl2.•The role Cl2 became significant in the presence of Cl− at acidic pH.•AMP underwent pyrazole ring opening, hydroxylation, dehydrogenation, and halogenation.</description><identifier>ISSN: 0045-6535</identifier><identifier>EISSN: 1879-1298</identifier><identifier>DOI: 10.1016/j.chemosphere.2016.12.033</identifier><identifier>PMID: 28056449</identifier><language>eng</language><publisher>England: Elsevier Ltd</publisher><subject>Aminopyrine - chemistry ; Aminopyrine chlorination ; By-products ; Chlorine - chemistry ; Chlorine Compounds - chemistry ; Chlorine monoxide ; Halogenation ; Hydrogen-Ion Concentration ; Hydroxylation ; Hypochlorous Acid - chemistry ; Kinetics ; Molecular chlorine ; Oxidation-Reduction ; Water Pollutants, Chemical - chemistry ; Water Purification - methods</subject><ispartof>Chemosphere (Oxford), 2017-03, Vol.171, p.625-634</ispartof><rights>2016 Elsevier Ltd</rights><rights>Copyright © 2016 Elsevier Ltd. 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In this study, the transformation mechanism of AMP by free available chlorine (FAC) oxidation was investigated. The results showed that FAC reacted with AMP rapidly, and a 74% elimination was achieved for 1.30 μM AMP after 2 min at 14.08 μM FAC dose. AMP chlorination was strongly pH-dependent, and its reaction included second- and third-order kinetic processes. Three active FAC species, including chlorine monoxide (Cl2O), molecular chlorine (Cl2), and hypochlorous acid (HOCl), were observed to contribute to AMP degradation. The intrinsic rate constants of each FAC species with neutral (AMP0) and cation (AMP+) species were obtained by kinetic fitting. Cl2O exhibited the highest reactivity with AMP0 (kAMP0, Cl2O = (4.33 ± 1.4) × 109 M−1s−1). In addition, Cl2 showed high reactivity (106–107 M−1s−1) in the presence of chloride, compared with HOCl (kAMP+, HOCl = (5.73 ± 0.23) × 102 M−1s−1, kAMP0, HOCl = (9.68 ± 0.96) × 102 M−1s−1). At pH 6.15 and 14.08 μM FAC dose without chloride addition, the contribution of Cl2O reached to the maximum (33.3%), but in the whole pH range, HOCl was the main contributor (&gt;66.6%) for AMP degradation. The significance of Cl2 was noticeable in water containing chloride. Moreover, 11 transformation products were identified, and the main transformation pathways included pyrazole ring breakage, hydroxylation, dehydrogenation, and halogenation. •Aminopyrine (AMP) chlorination included the reactions of AMP with HOCl, Cl2, and Cl2O.•The reactivity of each FAC species toward AMP: HOCl &lt; Cl2 &lt; Cl2O.•The contribution of each FAC species at neutral pH (no Cl− added): HOCl &gt; Cl2O &gt; Cl2.•The role Cl2 became significant in the presence of Cl− at acidic pH.•AMP underwent pyrazole ring opening, hydroxylation, dehydrogenation, and halogenation.</description><subject>Aminopyrine - chemistry</subject><subject>Aminopyrine chlorination</subject><subject>By-products</subject><subject>Chlorine - chemistry</subject><subject>Chlorine Compounds - chemistry</subject><subject>Chlorine monoxide</subject><subject>Halogenation</subject><subject>Hydrogen-Ion Concentration</subject><subject>Hydroxylation</subject><subject>Hypochlorous Acid - chemistry</subject><subject>Kinetics</subject><subject>Molecular chlorine</subject><subject>Oxidation-Reduction</subject><subject>Water Pollutants, Chemical - chemistry</subject><subject>Water Purification - methods</subject><issn>0045-6535</issn><issn>1879-1298</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2017</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqNkMtu1DAUQC0EokPLLyCzY9EEP2InZodGlCIqsWnXlmNfKx4lcbAzRfP3OExBLLuxretzXweh95TUlFD58VDbAaaYlwES1KyEaspqwvkLtKNdqyrKVPcS7QhpRCUFFxfoTc4HQgop1Gt0wToiZNOoHcr3yczZxzSZNcQZR4_NFOa4nFKYAYcZrwPgJUGG2cL27RMANo8mjKYfAdthjBv6CX8v5xpsvi54dEe7lpeZHU5g7J_ai1mHX-aUr9Arb8YMb5_uS_Rw8-V-f1vd_fj6bf_5rrK8bddKeiEZ41x56Yjse2KV6I11Tcuccdx3oKBRSpAOrFRcKqkskV76tmfEAeWX6MO5bpnn5xHyqqeQLYyjmSEes6adKDqkZG1B1Rm1KeacwOslhcmkk6ZEb871Qf_nXG_ONWW6OC-5757aHPsJ3L_Mv5ILsD8DUJZ9DJB0tmHT6UICu2oXwzPa_AauY5sQ</recordid><startdate>20170301</startdate><enddate>20170301</enddate><creator>Cai, Mei-Quan</creator><creator>Feng, Li</creator><creator>Zhang, Li-Qiu</creator><general>Elsevier Ltd</general><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>7X8</scope></search><sort><creationdate>20170301</creationdate><title>Transformation of aminopyrine in the presence of free available chlorine: Kinetics, products, and reaction pathways</title><author>Cai, Mei-Quan ; Feng, Li ; Zhang, Li-Qiu</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c377t-6f5622339f6d06bb0c95bacd472dad3f8e9e499508ec6936969c06f6f7b20de13</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2017</creationdate><topic>Aminopyrine - chemistry</topic><topic>Aminopyrine chlorination</topic><topic>By-products</topic><topic>Chlorine - chemistry</topic><topic>Chlorine Compounds - chemistry</topic><topic>Chlorine monoxide</topic><topic>Halogenation</topic><topic>Hydrogen-Ion Concentration</topic><topic>Hydroxylation</topic><topic>Hypochlorous Acid - chemistry</topic><topic>Kinetics</topic><topic>Molecular chlorine</topic><topic>Oxidation-Reduction</topic><topic>Water Pollutants, Chemical - chemistry</topic><topic>Water Purification - methods</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Cai, Mei-Quan</creatorcontrib><creatorcontrib>Feng, Li</creatorcontrib><creatorcontrib>Zhang, Li-Qiu</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>MEDLINE - Academic</collection><jtitle>Chemosphere (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Cai, Mei-Quan</au><au>Feng, Li</au><au>Zhang, Li-Qiu</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Transformation of aminopyrine in the presence of free available chlorine: Kinetics, products, and reaction pathways</atitle><jtitle>Chemosphere (Oxford)</jtitle><addtitle>Chemosphere</addtitle><date>2017-03-01</date><risdate>2017</risdate><volume>171</volume><spage>625</spage><epage>634</epage><pages>625-634</pages><issn>0045-6535</issn><eissn>1879-1298</eissn><abstract>Aminopyrine (AMP) has been frequently detected in the aquatic environment. In this study, the transformation mechanism of AMP by free available chlorine (FAC) oxidation was investigated. The results showed that FAC reacted with AMP rapidly, and a 74% elimination was achieved for 1.30 μM AMP after 2 min at 14.08 μM FAC dose. AMP chlorination was strongly pH-dependent, and its reaction included second- and third-order kinetic processes. Three active FAC species, including chlorine monoxide (Cl2O), molecular chlorine (Cl2), and hypochlorous acid (HOCl), were observed to contribute to AMP degradation. The intrinsic rate constants of each FAC species with neutral (AMP0) and cation (AMP+) species were obtained by kinetic fitting. Cl2O exhibited the highest reactivity with AMP0 (kAMP0, Cl2O = (4.33 ± 1.4) × 109 M−1s−1). In addition, Cl2 showed high reactivity (106–107 M−1s−1) in the presence of chloride, compared with HOCl (kAMP+, HOCl = (5.73 ± 0.23) × 102 M−1s−1, kAMP0, HOCl = (9.68 ± 0.96) × 102 M−1s−1). At pH 6.15 and 14.08 μM FAC dose without chloride addition, the contribution of Cl2O reached to the maximum (33.3%), but in the whole pH range, HOCl was the main contributor (&gt;66.6%) for AMP degradation. The significance of Cl2 was noticeable in water containing chloride. Moreover, 11 transformation products were identified, and the main transformation pathways included pyrazole ring breakage, hydroxylation, dehydrogenation, and halogenation. •Aminopyrine (AMP) chlorination included the reactions of AMP with HOCl, Cl2, and Cl2O.•The reactivity of each FAC species toward AMP: HOCl &lt; Cl2 &lt; Cl2O.•The contribution of each FAC species at neutral pH (no Cl− added): HOCl &gt; Cl2O &gt; Cl2.•The role Cl2 became significant in the presence of Cl− at acidic pH.•AMP underwent pyrazole ring opening, hydroxylation, dehydrogenation, and halogenation.</abstract><cop>England</cop><pub>Elsevier Ltd</pub><pmid>28056449</pmid><doi>10.1016/j.chemosphere.2016.12.033</doi><tpages>10</tpages></addata></record>
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subjects Aminopyrine - chemistry
Aminopyrine chlorination
By-products
Chlorine - chemistry
Chlorine Compounds - chemistry
Chlorine monoxide
Halogenation
Hydrogen-Ion Concentration
Hydroxylation
Hypochlorous Acid - chemistry
Kinetics
Molecular chlorine
Oxidation-Reduction
Water Pollutants, Chemical - chemistry
Water Purification - methods
title Transformation of aminopyrine in the presence of free available chlorine: Kinetics, products, and reaction pathways
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