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Determination of Benzo[a]pyrene, Benz[a]anthracene and Dibenz[a,h]anthracene in Creosotes and Creosote-Treated Woods
The amount of benzo[a]pyrene (BaP), benz[a]anthracene (BaA), and dibenz[a,h]anthracene (DBA) has been restricted to a concentration of 10 μg/g each in creosotes, and 3 μg/g each in creosote-treated woods, respectively, because of the possibility of the risk of skin cancer in consumers, and creosotes...
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Published in: | Journal of Health Science 2005, Vol.51(5), pp.597-606 |
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description | The amount of benzo[a]pyrene (BaP), benz[a]anthracene (BaA), and dibenz[a,h]anthracene (DBA) has been restricted to a concentration of 10 μg/g each in creosotes, and 3 μg/g each in creosote-treated woods, respectively, because of the possibility of the risk of skin cancer in consumers, and creosotes can otherwise contain high concentrations of each chemical. We already reported the content of 16 polycyclic aromatic hydrocarbons (PAHs) and phenols in creosotes and creosote-treated wood as determined by gas chromatography-mass spectrometry (GC-MS) and absorptiometry [Chemosphere, 60, 1279-1287 (2005)]. However, the limit of determination of each PAH per sample was > 40 μg/g according to that method, the sensitivity of which was insufficient for determining the allowable levels of these 3 compounds. Moreover, a substantial amount of time was needed for GC-MS analysis. In the present study, we improved upon our previous analytical method in order to increase the sensitivity of the test and to reduce the duration of GC-MS analysis. Creosote was extracted from treated wood samples by dichloromethane-soak incubation, and was placed on a Sep-Pak silica cartridge and eluted with dichloromethane. The eluates were evaporated and dissolved in dichloromethane. The sample solution spiked with the internal standard solution was injected into the GC-MS system. The limit of determination of each chemical in the test solution was approximately 0.2 μg/ml, which corresponded to 1-2 μg/g in each sample. The duration of GC-MS analysis was approximately 17 min. A collaborative study was also carried out in order to evaluate the reproducibility of the method for determining low levels of BaP and related compounds in creosotes. The present method was applied for the analysis of certain commercially available creosotes and creosote-treated wood samples in Japan. It was confirmed that some creosotes and railway sleepers contained these compounds in high concentrations, thus exceeding the allowed control value. |
doi_str_mv | 10.1248/jhs.51.597 |
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We already reported the content of 16 polycyclic aromatic hydrocarbons (PAHs) and phenols in creosotes and creosote-treated wood as determined by gas chromatography-mass spectrometry (GC-MS) and absorptiometry [Chemosphere, 60, 1279-1287 (2005)]. However, the limit of determination of each PAH per sample was > 40 μg/g according to that method, the sensitivity of which was insufficient for determining the allowable levels of these 3 compounds. Moreover, a substantial amount of time was needed for GC-MS analysis. In the present study, we improved upon our previous analytical method in order to increase the sensitivity of the test and to reduce the duration of GC-MS analysis. Creosote was extracted from treated wood samples by dichloromethane-soak incubation, and was placed on a Sep-Pak silica cartridge and eluted with dichloromethane. The eluates were evaporated and dissolved in dichloromethane. The sample solution spiked with the internal standard solution was injected into the GC-MS system. The limit of determination of each chemical in the test solution was approximately 0.2 μg/ml, which corresponded to 1-2 μg/g in each sample. The duration of GC-MS analysis was approximately 17 min. A collaborative study was also carried out in order to evaluate the reproducibility of the method for determining low levels of BaP and related compounds in creosotes. The present method was applied for the analysis of certain commercially available creosotes and creosote-treated wood samples in Japan. 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We already reported the content of 16 polycyclic aromatic hydrocarbons (PAHs) and phenols in creosotes and creosote-treated wood as determined by gas chromatography-mass spectrometry (GC-MS) and absorptiometry [Chemosphere, 60, 1279-1287 (2005)]. However, the limit of determination of each PAH per sample was > 40 μg/g according to that method, the sensitivity of which was insufficient for determining the allowable levels of these 3 compounds. Moreover, a substantial amount of time was needed for GC-MS analysis. In the present study, we improved upon our previous analytical method in order to increase the sensitivity of the test and to reduce the duration of GC-MS analysis. Creosote was extracted from treated wood samples by dichloromethane-soak incubation, and was placed on a Sep-Pak silica cartridge and eluted with dichloromethane. The eluates were evaporated and dissolved in dichloromethane. The sample solution spiked with the internal standard solution was injected into the GC-MS system. The limit of determination of each chemical in the test solution was approximately 0.2 μg/ml, which corresponded to 1-2 μg/g in each sample. The duration of GC-MS analysis was approximately 17 min. A collaborative study was also carried out in order to evaluate the reproducibility of the method for determining low levels of BaP and related compounds in creosotes. The present method was applied for the analysis of certain commercially available creosotes and creosote-treated wood samples in Japan. It was confirmed that some creosotes and railway sleepers contained these compounds in high concentrations, thus exceeding the allowed control value.</description><subject>benzo[a]pyrene</subject><subject>creosote</subject><subject>GC-MS</subject><subject>polycyclic aromatic hydrocarbon</subject><subject>wood preservative</subject><issn>1344-9702</issn><issn>1347-5207</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2005</creationdate><recordtype>article</recordtype><recordid>eNpdkE1v1DAQhiNEJUrhwi-IhMQBNcuMY8fJCdHtB0iVemnFASHLcSbEq6y92N5D-fV4d9uCerDHM_O871hTFO8QFsh4-2k1xYXAhejki-IYay4rwUC-3L951Ulgr4rXMa4AWActHhfpnBKFtXU6We9KP5Zn5P74H_rn5j6Qo9N9nlPt0hS0yaVSu6E8t_2-fjr937GuXAby0SeKe-wxq24D6URD-d37Ib4pjkY9R3r7EE-Ku8uL2-XX6vrm6tvyy3VlGmxTNZihaXjdjmyse94zBjS2DRIg07JH02NuD5mqheg7LYcODIFkTSe17rLopPhw8N0E_3tLMam1jYbmWTvy26hQcikajhl8_wxc-W1w-W8KOa95J1DsqI8HygQfY6BRbYJd63CvENRu_SqvXwlUef0ZvjrAaxqs0bN3s3X0z9dEOZGek2IAQuWDu4CoIKsVNNAgyBYQstPng9MqJv2LnobqkKyZ6Wnow5XVjx0z6aDI1X8Blqym4A</recordid><startdate>2005</startdate><enddate>2005</enddate><creator>Ikarashi, Yoshiaki</creator><creator>Kaniwa, Masa-aki</creator><creator>Tsuchiya, Toshie</creator><general>The Pharmaceutical Society of Japan</general><general>Pharmaceutical Society of Japan</general><general>Pharmaceutical Society of Japan, Nihon Yakugakkai</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7TV</scope><scope>7U7</scope><scope>C1K</scope></search><sort><creationdate>2005</creationdate><title>Determination of Benzo[a]pyrene, Benz[a]anthracene and Dibenz[a,h]anthracene in Creosotes and Creosote-Treated Woods</title><author>Ikarashi, Yoshiaki ; Kaniwa, Masa-aki ; Tsuchiya, Toshie</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c618t-dcd66438f2f3b4b220ef861e012a7b1cb1664ddcd355b9a7d90ce072697aa92f3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2005</creationdate><topic>benzo[a]pyrene</topic><topic>creosote</topic><topic>GC-MS</topic><topic>polycyclic aromatic hydrocarbon</topic><topic>wood preservative</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Ikarashi, Yoshiaki</creatorcontrib><creatorcontrib>Kaniwa, Masa-aki</creatorcontrib><creatorcontrib>Tsuchiya, Toshie</creatorcontrib><creatorcontrib>National Institute of Health Sciences</creatorcontrib><creatorcontrib>Division of Medical Devices</creatorcontrib><collection>CrossRef</collection><collection>Pollution Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><jtitle>Journal of Health Science</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Ikarashi, Yoshiaki</au><au>Kaniwa, Masa-aki</au><au>Tsuchiya, Toshie</au><aucorp>National Institute of Health Sciences</aucorp><aucorp>Division of Medical Devices</aucorp><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Determination of Benzo[a]pyrene, Benz[a]anthracene and Dibenz[a,h]anthracene in Creosotes and Creosote-Treated Woods</atitle><jtitle>Journal of Health Science</jtitle><date>2005</date><risdate>2005</risdate><volume>51</volume><issue>5</issue><spage>597</spage><epage>606</epage><pages>597-606</pages><issn>1344-9702</issn><eissn>1347-5207</eissn><abstract>The amount of benzo[a]pyrene (BaP), benz[a]anthracene (BaA), and dibenz[a,h]anthracene (DBA) has been restricted to a concentration of 10 μg/g each in creosotes, and 3 μg/g each in creosote-treated woods, respectively, because of the possibility of the risk of skin cancer in consumers, and creosotes can otherwise contain high concentrations of each chemical. We already reported the content of 16 polycyclic aromatic hydrocarbons (PAHs) and phenols in creosotes and creosote-treated wood as determined by gas chromatography-mass spectrometry (GC-MS) and absorptiometry [Chemosphere, 60, 1279-1287 (2005)]. However, the limit of determination of each PAH per sample was > 40 μg/g according to that method, the sensitivity of which was insufficient for determining the allowable levels of these 3 compounds. Moreover, a substantial amount of time was needed for GC-MS analysis. In the present study, we improved upon our previous analytical method in order to increase the sensitivity of the test and to reduce the duration of GC-MS analysis. Creosote was extracted from treated wood samples by dichloromethane-soak incubation, and was placed on a Sep-Pak silica cartridge and eluted with dichloromethane. The eluates were evaporated and dissolved in dichloromethane. The sample solution spiked with the internal standard solution was injected into the GC-MS system. The limit of determination of each chemical in the test solution was approximately 0.2 μg/ml, which corresponded to 1-2 μg/g in each sample. The duration of GC-MS analysis was approximately 17 min. A collaborative study was also carried out in order to evaluate the reproducibility of the method for determining low levels of BaP and related compounds in creosotes. The present method was applied for the analysis of certain commercially available creosotes and creosote-treated wood samples in Japan. It was confirmed that some creosotes and railway sleepers contained these compounds in high concentrations, thus exceeding the allowed control value.</abstract><cop>Tokyo</cop><pub>The Pharmaceutical Society of Japan</pub><doi>10.1248/jhs.51.597</doi><tpages>10</tpages><oa>free_for_read</oa></addata></record> |
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subjects | benzo[a]pyrene creosote GC-MS polycyclic aromatic hydrocarbon wood preservative |
title | Determination of Benzo[a]pyrene, Benz[a]anthracene and Dibenz[a,h]anthracene in Creosotes and Creosote-Treated Woods |
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