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Kinetics of diatrizoate degradation by ozone and the formation of disinfection by-products in the sequential chlorination
In this study, we studied the degradation kinetics of a common iodine contrast agent, diatrizoate, by ozone and the formation of disinfection by-products (DBPs) in the sequential chlorination. Effects of ozone concentration, solution pH, and bromide concentration on diatrizoate degradation were eval...
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Published in: | Journal of water reuse and desalination 2021-12, Vol.11 (4), p.560-571 |
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description | In this study, we studied the degradation kinetics of a common iodine contrast agent, diatrizoate, by ozone and the formation of disinfection by-products (DBPs) in the sequential chlorination. Effects of ozone concentration, solution pH, and bromide concentration on diatrizoate degradation were evaluated. The results indicate that diatrizoate can be effectively degraded (over 80% within 1 h) by ozone, and the degradation kinetics can be well described using the pseudo-first-order kinetic model. The pseudo-first-order rate constant (kobs) of diatrizoate degradation significantly increased with increasing ozone concentration and decreasing bromide concentration. The kobs kept increasing with the increase of pH value and reached a maximum of 6.5 (±0.05) × 10−2 min−1 at pH 9. As the ozone concentration gradually increased from 0.342 to 1.316 mg/L, the corresponding kobs of diatrizoate degradation increased from 1.76 (±0.20) × 10−3 to 4.22 (±0.3) × 10−2 min−1. The bromide concentration exhibited a strong inhibitory effect on diatrizoate degradation because of the competition for ozone with diatrizoate. Trichloromethane was the only detected DBP in the subsequent chlorination in the absence of bromide. However, in the presence of bromide, six other DBPs were detected, and bromochloroiodomethane and tribromomethane became the major products with concentrations 1–2 orders higher than those of the other DBPs. In order to provide safe drinking water to the public, water should be maintained at circumneutral pH values and low bromine concentrations ( |
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Effects of ozone concentration, solution pH, and bromide concentration on diatrizoate degradation were evaluated. The results indicate that diatrizoate can be effectively degraded (over 80% within 1 h) by ozone, and the degradation kinetics can be well described using the pseudo-first-order kinetic model. The pseudo-first-order rate constant (kobs) of diatrizoate degradation significantly increased with increasing ozone concentration and decreasing bromide concentration. The kobs kept increasing with the increase of pH value and reached a maximum of 6.5 (±0.05) × 10−2 min−1 at pH 9. As the ozone concentration gradually increased from 0.342 to 1.316 mg/L, the corresponding kobs of diatrizoate degradation increased from 1.76 (±0.20) × 10−3 to 4.22 (±0.3) × 10−2 min−1. The bromide concentration exhibited a strong inhibitory effect on diatrizoate degradation because of the competition for ozone with diatrizoate. Trichloromethane was the only detected DBP in the subsequent chlorination in the absence of bromide. However, in the presence of bromide, six other DBPs were detected, and bromochloroiodomethane and tribromomethane became the major products with concentrations 1–2 orders higher than those of the other DBPs. In order to provide safe drinking water to the public, water should be maintained at circumneutral pH values and low bromine concentrations (<5 μM) before reaching the chlorine disinfection process to effectively control the formation of DBPs.</description><identifier>ISSN: 2220-1319</identifier><identifier>ISSN: 2709-6092</identifier><identifier>EISSN: 2408-9370</identifier><identifier>EISSN: 2709-6106</identifier><identifier>DOI: 10.2166/wrd.2021.053</identifier><language>eng</language><publisher>London: IWA Publishing</publisher><subject>bromide ; Bromine ; Byproducts ; Chlorination ; Chlorine ; Chloroform ; Contrast agents ; Degradation ; Disinfection ; disinfection by-product (dbp) ; Drinking water ; Experiments ; Gas absorption ; iodinated x-ray contrast media (icm) ; Iodine ; Kinetics ; Medical research ; Oxidation ; Ozone ; pH effects ; Potassium ; Public health ; Radiation ; Sodium ; Water treatment</subject><ispartof>Journal of water reuse and desalination, 2021-12, Vol.11 (4), p.560-571</ispartof><rights>Copyright IWA Publishing Dec 2021</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c367t-47ff1ae90a70c9623da7a1e6fd3e8b87f728b711f36b457b38543465351059533</citedby><cites>FETCH-LOGICAL-c367t-47ff1ae90a70c9623da7a1e6fd3e8b87f728b711f36b457b38543465351059533</cites><orcidid>0000-0002-1930-8174 ; 0000-0003-3426-3565</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,777,781,27905,27906</link.rule.ids></links><search><creatorcontrib>Hu, Chen-Yan</creatorcontrib><creatorcontrib>Ren, Si-Cheng</creatorcontrib><creatorcontrib>Lin, Yi-Li</creatorcontrib><creatorcontrib>Zhang, Ji-Chen</creatorcontrib><creatorcontrib>Zhu, Ye-Ye</creatorcontrib><creatorcontrib>Xiong, Cun</creatorcontrib><creatorcontrib>Wang, Qiang-Bin</creatorcontrib><title>Kinetics of diatrizoate degradation by ozone and the formation of disinfection by-products in the sequential chlorination</title><title>Journal of water reuse and desalination</title><description>In this study, we studied the degradation kinetics of a common iodine contrast agent, diatrizoate, by ozone and the formation of disinfection by-products (DBPs) in the sequential chlorination. Effects of ozone concentration, solution pH, and bromide concentration on diatrizoate degradation were evaluated. The results indicate that diatrizoate can be effectively degraded (over 80% within 1 h) by ozone, and the degradation kinetics can be well described using the pseudo-first-order kinetic model. The pseudo-first-order rate constant (kobs) of diatrizoate degradation significantly increased with increasing ozone concentration and decreasing bromide concentration. The kobs kept increasing with the increase of pH value and reached a maximum of 6.5 (±0.05) × 10−2 min−1 at pH 9. As the ozone concentration gradually increased from 0.342 to 1.316 mg/L, the corresponding kobs of diatrizoate degradation increased from 1.76 (±0.20) × 10−3 to 4.22 (±0.3) × 10−2 min−1. The bromide concentration exhibited a strong inhibitory effect on diatrizoate degradation because of the competition for ozone with diatrizoate. Trichloromethane was the only detected DBP in the subsequent chlorination in the absence of bromide. However, in the presence of bromide, six other DBPs were detected, and bromochloroiodomethane and tribromomethane became the major products with concentrations 1–2 orders higher than those of the other DBPs. In order to provide safe drinking water to the public, water should be maintained at circumneutral pH values and low bromine concentrations (<5 μM) before reaching the chlorine disinfection process to effectively control the formation of DBPs.</description><subject>bromide</subject><subject>Bromine</subject><subject>Byproducts</subject><subject>Chlorination</subject><subject>Chlorine</subject><subject>Chloroform</subject><subject>Contrast agents</subject><subject>Degradation</subject><subject>Disinfection</subject><subject>disinfection by-product (dbp)</subject><subject>Drinking water</subject><subject>Experiments</subject><subject>Gas absorption</subject><subject>iodinated x-ray contrast media (icm)</subject><subject>Iodine</subject><subject>Kinetics</subject><subject>Medical research</subject><subject>Oxidation</subject><subject>Ozone</subject><subject>pH effects</subject><subject>Potassium</subject><subject>Public health</subject><subject>Radiation</subject><subject>Sodium</subject><subject>Water treatment</subject><issn>2220-1319</issn><issn>2709-6092</issn><issn>2408-9370</issn><issn>2709-6106</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2021</creationdate><recordtype>article</recordtype><sourceid>DOA</sourceid><recordid>eNo9UU1vGyEQXVWJ1MjxLT8Aqdeuy8ACy7GK2jSKpVzaM5pdIMFyIAWsyv71xR_KXGY08-bNx-u6O6ArBlJ--5ftilEGKyr4p-6GDXTsNVf0qsWM0R446M_dspQNbSaE5gA33f4pRFfDXEjyxAasORwSVkese8losYYUybQn6ZCiIxgtqa-O-JTfzqVTVwnRu_kC7d9zsru5FhLiCVzc352LNeCWzK_blEM8td521x63xS0vftH9-fnj9_2vfv388Hj_fd3PXKraD8p7QKcpKjprybhFheCkt9yN06i8YuOkADyX0yDUxEcx8EEKLoAKLThfdI9nXptwY95zeMO8NwmDOSVSfjGY2we2zjgukU1SD0zDYFFMIHBwavbtv22WbVxfzlztxnZUqWaTdjm29Q2TIGHUIxcN9fWMmnMqJTv_MRWoOWplmlbmqJVpWvH_c5qIAg</recordid><startdate>20211201</startdate><enddate>20211201</enddate><creator>Hu, Chen-Yan</creator><creator>Ren, Si-Cheng</creator><creator>Lin, Yi-Li</creator><creator>Zhang, Ji-Chen</creator><creator>Zhu, Ye-Ye</creator><creator>Xiong, Cun</creator><creator>Wang, Qiang-Bin</creator><general>IWA Publishing</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7TN</scope><scope>7UA</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>BKSAR</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>F1W</scope><scope>GNUQQ</scope><scope>H97</scope><scope>HCIFZ</scope><scope>L.G</scope><scope>PATMY</scope><scope>PCBAR</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>DOA</scope><orcidid>https://orcid.org/0000-0002-1930-8174</orcidid><orcidid>https://orcid.org/0000-0003-3426-3565</orcidid></search><sort><creationdate>20211201</creationdate><title>Kinetics of diatrizoate degradation by ozone and the formation of disinfection by-products in the sequential chlorination</title><author>Hu, Chen-Yan ; Ren, Si-Cheng ; Lin, Yi-Li ; Zhang, Ji-Chen ; Zhu, Ye-Ye ; Xiong, Cun ; Wang, Qiang-Bin</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c367t-47ff1ae90a70c9623da7a1e6fd3e8b87f728b711f36b457b38543465351059533</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2021</creationdate><topic>bromide</topic><topic>Bromine</topic><topic>Byproducts</topic><topic>Chlorination</topic><topic>Chlorine</topic><topic>Chloroform</topic><topic>Contrast agents</topic><topic>Degradation</topic><topic>Disinfection</topic><topic>disinfection by-product (dbp)</topic><topic>Drinking water</topic><topic>Experiments</topic><topic>Gas absorption</topic><topic>iodinated x-ray contrast media (icm)</topic><topic>Iodine</topic><topic>Kinetics</topic><topic>Medical research</topic><topic>Oxidation</topic><topic>Ozone</topic><topic>pH effects</topic><topic>Potassium</topic><topic>Public health</topic><topic>Radiation</topic><topic>Sodium</topic><topic>Water treatment</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Hu, Chen-Yan</creatorcontrib><creatorcontrib>Ren, Si-Cheng</creatorcontrib><creatorcontrib>Lin, Yi-Li</creatorcontrib><creatorcontrib>Zhang, Ji-Chen</creatorcontrib><creatorcontrib>Zhu, Ye-Ye</creatorcontrib><creatorcontrib>Xiong, Cun</creatorcontrib><creatorcontrib>Wang, Qiang-Bin</creatorcontrib><collection>CrossRef</collection><collection>Aqualine</collection><collection>Oceanic Abstracts</collection><collection>Water Resources Abstracts</collection><collection>ProQuest One Sustainability</collection><collection>ProQuest Central</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>ProQuest Central</collection><collection>Natural Science Collection</collection><collection>Earth, Atmospheric & Aquatic Science Collection</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central Korea</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>ProQuest Central Student</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>SciTech Premium Collection</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Environmental Science Database</collection><collection>Earth, Atmospheric & Aquatic Science Database</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>Environmental Science Collection</collection><collection>DOAJ Directory of Open Access Journals</collection><jtitle>Journal of water reuse and desalination</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Hu, Chen-Yan</au><au>Ren, Si-Cheng</au><au>Lin, Yi-Li</au><au>Zhang, Ji-Chen</au><au>Zhu, Ye-Ye</au><au>Xiong, Cun</au><au>Wang, Qiang-Bin</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Kinetics of diatrizoate degradation by ozone and the formation of disinfection by-products in the sequential chlorination</atitle><jtitle>Journal of water reuse and desalination</jtitle><date>2021-12-01</date><risdate>2021</risdate><volume>11</volume><issue>4</issue><spage>560</spage><epage>571</epage><pages>560-571</pages><issn>2220-1319</issn><issn>2709-6092</issn><eissn>2408-9370</eissn><eissn>2709-6106</eissn><abstract>In this study, we studied the degradation kinetics of a common iodine contrast agent, diatrizoate, by ozone and the formation of disinfection by-products (DBPs) in the sequential chlorination. Effects of ozone concentration, solution pH, and bromide concentration on diatrizoate degradation were evaluated. The results indicate that diatrizoate can be effectively degraded (over 80% within 1 h) by ozone, and the degradation kinetics can be well described using the pseudo-first-order kinetic model. The pseudo-first-order rate constant (kobs) of diatrizoate degradation significantly increased with increasing ozone concentration and decreasing bromide concentration. The kobs kept increasing with the increase of pH value and reached a maximum of 6.5 (±0.05) × 10−2 min−1 at pH 9. As the ozone concentration gradually increased from 0.342 to 1.316 mg/L, the corresponding kobs of diatrizoate degradation increased from 1.76 (±0.20) × 10−3 to 4.22 (±0.3) × 10−2 min−1. The bromide concentration exhibited a strong inhibitory effect on diatrizoate degradation because of the competition for ozone with diatrizoate. Trichloromethane was the only detected DBP in the subsequent chlorination in the absence of bromide. However, in the presence of bromide, six other DBPs were detected, and bromochloroiodomethane and tribromomethane became the major products with concentrations 1–2 orders higher than those of the other DBPs. In order to provide safe drinking water to the public, water should be maintained at circumneutral pH values and low bromine concentrations (<5 μM) before reaching the chlorine disinfection process to effectively control the formation of DBPs.</abstract><cop>London</cop><pub>IWA Publishing</pub><doi>10.2166/wrd.2021.053</doi><tpages>12</tpages><orcidid>https://orcid.org/0000-0002-1930-8174</orcidid><orcidid>https://orcid.org/0000-0003-3426-3565</orcidid><oa>free_for_read</oa></addata></record> |
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subjects | bromide Bromine Byproducts Chlorination Chlorine Chloroform Contrast agents Degradation Disinfection disinfection by-product (dbp) Drinking water Experiments Gas absorption iodinated x-ray contrast media (icm) Iodine Kinetics Medical research Oxidation Ozone pH effects Potassium Public health Radiation Sodium Water treatment |
title | Kinetics of diatrizoate degradation by ozone and the formation of disinfection by-products in the sequential chlorination |
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