Isothiazolone emissions from building products
Adding biocides to dispersion products is a well‐known practice to control microbial deterioration. Isothiazolones are among the most commonly used preservatives, in particular a mixture of 2‐methyl‐2H‐isothiazol‐3‐one (MIT) and 5‐chloro‐2‐methyl‐2H‐isothiazol‐3‐one (CIT). In recent years, for healt...
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Veröffentlicht in: | Indoor air 2015-02, Vol.25 (1), p.68-78 |
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description | Adding biocides to dispersion products is a well‐known practice to control microbial deterioration. Isothiazolones are among the most commonly used preservatives, in particular a mixture of 2‐methyl‐2H‐isothiazol‐3‐one (MIT) and 5‐chloro‐2‐methyl‐2H‐isothiazol‐3‐one (CIT). In recent years, for health reasons, due to its strong sensitizing effect, CIT has been replaced by 1,2‐benzisothiazol‐3‐one (BIT). Furthermore, numerous products are now available for interiors containing the fungicidal active substance 2‐octyl‐2H‐isothiazol‐3‐one (OIT). So far nearly nothing is known of the emission behavior of BIT and OIT. An analytical method was developed for these two isothiazolones and interior products containing BIT respectively OIT have been investigated in an emission chamber and in test rooms. The chamber tests revealed maximum concentrations of 6.7 μg OIT/m3, 1.9 μg BIT/m3, and 187 μg MIT/m3. Concentrations obtained in the test rooms were at levels up to 1.4 μg OIT/m3 and 29 μg MIT/m3. A noticeable finding was the very slight subsidence of OIT and BIT levels over several weeks. While MIT outgassed quickly, OIT in particular showed low concentrations, but prolonged evaporation. |
doi_str_mv | 10.1111/ina.12126 |
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Isothiazolones are among the most commonly used preservatives, in particular a mixture of 2‐methyl‐2H‐isothiazol‐3‐one (MIT) and 5‐chloro‐2‐methyl‐2H‐isothiazol‐3‐one (CIT). In recent years, for health reasons, due to its strong sensitizing effect, CIT has been replaced by 1,2‐benzisothiazol‐3‐one (BIT). Furthermore, numerous products are now available for interiors containing the fungicidal active substance 2‐octyl‐2H‐isothiazol‐3‐one (OIT). So far nearly nothing is known of the emission behavior of BIT and OIT. An analytical method was developed for these two isothiazolones and interior products containing BIT respectively OIT have been investigated in an emission chamber and in test rooms. The chamber tests revealed maximum concentrations of 6.7 μg OIT/m3, 1.9 μg BIT/m3, and 187 μg MIT/m3. Concentrations obtained in the test rooms were at levels up to 1.4 μg OIT/m3 and 29 μg MIT/m3. A noticeable finding was the very slight subsidence of OIT and BIT levels over several weeks. While MIT outgassed quickly, OIT in particular showed low concentrations, but prolonged evaporation.</description><identifier>ISSN: 0905-6947</identifier><identifier>EISSN: 1600-0668</identifier><identifier>DOI: 10.1111/ina.12126</identifier><identifier>PMID: 24810042</identifier><language>eng</language><publisher>England: Blackwell Publishing Ltd</publisher><subject>Adhesives - analysis ; Air Pollutants - analysis ; Air Pollution, Indoor - analysis ; Allergens ; Biocides ; Building materials ; Building products ; Chromatography, Liquid ; Construction Materials - analysis ; Disinfectants - analysis ; Emissions ; Environmental Monitoring - methods ; Fungicides, Industrial - analysis ; Germany ; Household Products - analysis ; Humans ; Indoor air quality ; Indoor spaces ; Isothiazolones ; Paint - analysis ; Pesticides ; Thiazoles - analysis</subject><ispartof>Indoor air, 2015-02, Vol.25 (1), p.68-78</ispartof><rights>2014 John Wiley & Sons A/S. Published by John Wiley & Sons Ltd</rights><rights>2014 John Wiley & Sons A/S. Published by John Wiley & Sons Ltd.</rights><rights>Copyright © 2015 John Wiley & Sons A/S. 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Isothiazolones are among the most commonly used preservatives, in particular a mixture of 2‐methyl‐2H‐isothiazol‐3‐one (MIT) and 5‐chloro‐2‐methyl‐2H‐isothiazol‐3‐one (CIT). In recent years, for health reasons, due to its strong sensitizing effect, CIT has been replaced by 1,2‐benzisothiazol‐3‐one (BIT). Furthermore, numerous products are now available for interiors containing the fungicidal active substance 2‐octyl‐2H‐isothiazol‐3‐one (OIT). So far nearly nothing is known of the emission behavior of BIT and OIT. An analytical method was developed for these two isothiazolones and interior products containing BIT respectively OIT have been investigated in an emission chamber and in test rooms. The chamber tests revealed maximum concentrations of 6.7 μg OIT/m3, 1.9 μg BIT/m3, and 187 μg MIT/m3. Concentrations obtained in the test rooms were at levels up to 1.4 μg OIT/m3 and 29 μg MIT/m3. A noticeable finding was the very slight subsidence of OIT and BIT levels over several weeks. While MIT outgassed quickly, OIT in particular showed low concentrations, but prolonged evaporation.</description><subject>Adhesives - analysis</subject><subject>Air Pollutants - analysis</subject><subject>Air Pollution, Indoor - analysis</subject><subject>Allergens</subject><subject>Biocides</subject><subject>Building materials</subject><subject>Building products</subject><subject>Chromatography, Liquid</subject><subject>Construction Materials - analysis</subject><subject>Disinfectants - analysis</subject><subject>Emissions</subject><subject>Environmental Monitoring - methods</subject><subject>Fungicides, Industrial - analysis</subject><subject>Germany</subject><subject>Household Products - analysis</subject><subject>Humans</subject><subject>Indoor air quality</subject><subject>Indoor spaces</subject><subject>Isothiazolones</subject><subject>Paint - analysis</subject><subject>Pesticides</subject><subject>Thiazoles - analysis</subject><issn>0905-6947</issn><issn>1600-0668</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2015</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp10LtOwzAUBmALgWgpDLwAqsQCQ1o7vo9VBaWoKgO30XJiF1zSuMSJoDw9hl4GJLx48Hd-H_0AnCLYQ_H0Xal7KEUp2wNtxCBMIGNiH7ShhDRhkvAWOAphDiHiWOJD0EqJQBCStA164-DrV6e_fOFL27ULF4LzZejOKr_oZo0rjCtfusvKmyavwzE4mOki2JPN3QGP11cPw5tkcjcaDweTJCeSsURYyrHNZ0wahCGXQktDspTInKfQ5JRkBov4bjilLMPYUIp1KpiGnGVWctwBF-vc-PF7Y0Ot4mK5LQpdWt8EhRhNsZCIokjP_9C5b6oybhcVoYIQQWFUl2uVVz6Eys7UsnILXa0UguqnRBVLVL8lRnu2SWyyhTU7uW0tgv4afLjCrv5PUuPpYBuZrCdcqO3nbkJXb4pxzKl6no4UuX9ChN9OlMDfRW2IQg</recordid><startdate>201502</startdate><enddate>201502</enddate><creator>Nagorka, R.</creator><creator>Gleue, C.</creator><creator>Scheller, C.</creator><creator>Moriske, H.-J.</creator><creator>Straff, W.</creator><general>Blackwell Publishing Ltd</general><general>Hindawi Limited</general><scope>BSCLL</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>7ST</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>KR7</scope><scope>SOI</scope><scope>7X8</scope></search><sort><creationdate>201502</creationdate><title>Isothiazolone emissions from building products</title><author>Nagorka, R. ; Gleue, C. ; Scheller, C. ; Moriske, H.-J. ; Straff, W.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c4966-8e573ecf69d130798a9d4b249c720dc54bd38ecfd7556b33d553a286a076be973</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2015</creationdate><topic>Adhesives - analysis</topic><topic>Air Pollutants - analysis</topic><topic>Air Pollution, Indoor - analysis</topic><topic>Allergens</topic><topic>Biocides</topic><topic>Building materials</topic><topic>Building products</topic><topic>Chromatography, Liquid</topic><topic>Construction Materials - analysis</topic><topic>Disinfectants - analysis</topic><topic>Emissions</topic><topic>Environmental Monitoring - methods</topic><topic>Fungicides, Industrial - analysis</topic><topic>Germany</topic><topic>Household Products - analysis</topic><topic>Humans</topic><topic>Indoor air quality</topic><topic>Indoor spaces</topic><topic>Isothiazolones</topic><topic>Paint - analysis</topic><topic>Pesticides</topic><topic>Thiazoles - analysis</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Nagorka, R.</creatorcontrib><creatorcontrib>Gleue, C.</creatorcontrib><creatorcontrib>Scheller, C.</creatorcontrib><creatorcontrib>Moriske, H.-J.</creatorcontrib><creatorcontrib>Straff, W.</creatorcontrib><collection>Istex</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Environment Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Civil Engineering Abstracts</collection><collection>Environment Abstracts</collection><collection>MEDLINE - Academic</collection><jtitle>Indoor air</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Nagorka, R.</au><au>Gleue, C.</au><au>Scheller, C.</au><au>Moriske, H.-J.</au><au>Straff, W.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Isothiazolone emissions from building products</atitle><jtitle>Indoor air</jtitle><addtitle>Indoor Air</addtitle><date>2015-02</date><risdate>2015</risdate><volume>25</volume><issue>1</issue><spage>68</spage><epage>78</epage><pages>68-78</pages><issn>0905-6947</issn><eissn>1600-0668</eissn><abstract>Adding biocides to dispersion products is a well‐known practice to control microbial deterioration. Isothiazolones are among the most commonly used preservatives, in particular a mixture of 2‐methyl‐2H‐isothiazol‐3‐one (MIT) and 5‐chloro‐2‐methyl‐2H‐isothiazol‐3‐one (CIT). In recent years, for health reasons, due to its strong sensitizing effect, CIT has been replaced by 1,2‐benzisothiazol‐3‐one (BIT). Furthermore, numerous products are now available for interiors containing the fungicidal active substance 2‐octyl‐2H‐isothiazol‐3‐one (OIT). So far nearly nothing is known of the emission behavior of BIT and OIT. An analytical method was developed for these two isothiazolones and interior products containing BIT respectively OIT have been investigated in an emission chamber and in test rooms. The chamber tests revealed maximum concentrations of 6.7 μg OIT/m3, 1.9 μg BIT/m3, and 187 μg MIT/m3. Concentrations obtained in the test rooms were at levels up to 1.4 μg OIT/m3 and 29 μg MIT/m3. A noticeable finding was the very slight subsidence of OIT and BIT levels over several weeks. While MIT outgassed quickly, OIT in particular showed low concentrations, but prolonged evaporation.</abstract><cop>England</cop><pub>Blackwell Publishing Ltd</pub><pmid>24810042</pmid><doi>10.1111/ina.12126</doi><tpages>11</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Adhesives - analysis Air Pollutants - analysis Air Pollution, Indoor - analysis Allergens Biocides Building materials Building products Chromatography, Liquid Construction Materials - analysis Disinfectants - analysis Emissions Environmental Monitoring - methods Fungicides, Industrial - analysis Germany Household Products - analysis Humans Indoor air quality Indoor spaces Isothiazolones Paint - analysis Pesticides Thiazoles - analysis |
title | Isothiazolone emissions from building products |
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