Fractionation of polycyclic aromatic hydrocarbon residues in soils
Understanding the forms and availabilities of polycylic aromatic hydrocarbons (PAHs) would have considerable benefits for their risk assessment, and is of crucial importance for food security and remediation strategies in contaminated sites. In this work, the forms of six PAHs (fluorene, phenanthren...
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description | Understanding the forms and availabilities of polycylic aromatic hydrocarbons (PAHs) would have considerable benefits for their risk assessment, and is of crucial importance for food security and remediation strategies in contaminated sites. In this work, the forms of six PAHs (fluorene, phenanthrene, fluoranthene, pyrene, benzo[a]anthracene, and benzo[a]pyrene) in soils were separated into three fractions including a desorbing fraction, a non-desorbing fraction, and a bound residual fraction using a sequential extraction mass balance approach. The desorbing and non-desorbing fractions were extracted with hydroxypropyl-beta-cyclodextrin (HPCD) and dichloromethane:acetone (1:1, vol/vol), respectively. The desorbing and non-desorbing fractions always dominated the total PAH content in soils. The proportion of bound PAH residue in nonsterilized soils was small ( |
doi_str_mv | 10.1016/j.jhazmat.2009.07.084 |
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In this work, the forms of six PAHs (fluorene, phenanthrene, fluoranthene, pyrene, benzo[a]anthracene, and benzo[a]pyrene) in soils were separated into three fractions including a desorbing fraction, a non-desorbing fraction, and a bound residual fraction using a sequential extraction mass balance approach. The desorbing and non-desorbing fractions were extracted with hydroxypropyl-beta-cyclodextrin (HPCD) and dichloromethane:acetone (1:1, vol/vol), respectively. The desorbing and non-desorbing fractions always dominated the total PAH content in soils. The proportion of bound PAH residue in nonsterilized soils was small (<16%), and even smaller (4.5%) in sterilized soils. The concentrations of the desorbing fraction of PAHs as well as the percentage of this fraction to the total PAH content in soils clearly decreased in 0–16 weeks, which may be due to microbial biodegradation and its transfer to other fractions in soils. The concentrations of the non-desorbing PAH fractions increased in sterilized soils, while remaining nearly constant or decreasing to some extent in nonsterilized soils after 16 weeks. The proportion of non-desorbing PAH fractions significantly increased in 16 week-incubation, and this proportion was positively correlated with the molecular weights of the PAHs tested, indicating that larger PAHs are more likely to be present in non-desorbing fractions. The bound PAH residue tended to increase at first and decrease thereafter over the 0–16-week period, and microbes played an important role in the formation of bound residue.</description><identifier>ISSN: 0304-3894</identifier><identifier>EISSN: 1873-3336</identifier><identifier>DOI: 10.1016/j.jhazmat.2009.07.084</identifier><identifier>PMID: 19692170</identifier><identifier>CODEN: JHMAD9</identifier><language>eng</language><publisher>Kidlington: Elsevier B.V</publisher><subject><![CDATA[Applied sciences ; Benz(a)Anthracenes - analysis ; Benz(a)Anthracenes - isolation & purification ; Benzo(a)pyrene - analysis ; Benzo(a)pyrene - isolation & purification ; Bioavailability ; Biodegradation, Environmental ; Biological and medical sciences ; Chemical engineering ; Chemical Fractionation ; Cyclodextrins ; Exact sciences and technology ; Extraction ; Fluorenes - analysis ; Fluorenes - isolation & purification ; Food engineering ; Food industries ; Form ; Fractionation ; Fundamental and applied biological sciences. Psychology ; General aspects ; Microorganisms ; Phenanthrene ; Phenanthrenes - analysis ; Phenanthrenes - isolation & purification ; Pollution ; Polyallylamine hydrochloride ; Polycyclic aromatic hydrocarbons (PAHs) ; Polycyclic Aromatic Hydrocarbons - analysis ; Polycyclic Aromatic Hydrocarbons - isolation & purification ; Pyrenes - analysis ; Pyrenes - isolation & purification ; Remediation ; Residue ; Residues ; Safety ; Security ; Soil ; Soil Pollutants - analysis ; Soil Pollutants - isolation & purification ; Soils]]></subject><ispartof>Journal of hazardous materials, 2009-12, Vol.172 (2), p.897-903</ispartof><rights>2009 Elsevier B.V.</rights><rights>2015 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c530t-de85c0b4101bf21721378bb27c1157cf083cd7a7a3b84f4e16f92260cbe04cd23</citedby><cites>FETCH-LOGICAL-c530t-de85c0b4101bf21721378bb27c1157cf083cd7a7a3b84f4e16f92260cbe04cd23</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://dx.doi.org/10.1016/j.jhazmat.2009.07.084$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,777,781,3537,27905,27906,45976</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=22585644$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/19692170$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Gao, Yanzheng</creatorcontrib><creatorcontrib>Zeng, Yuechun</creatorcontrib><creatorcontrib>Shen, Qing</creatorcontrib><creatorcontrib>Ling, Wanting</creatorcontrib><creatorcontrib>Han, Jin</creatorcontrib><title>Fractionation of polycyclic aromatic hydrocarbon residues in soils</title><title>Journal of hazardous materials</title><addtitle>J Hazard Mater</addtitle><description>Understanding the forms and availabilities of polycylic aromatic hydrocarbons (PAHs) would have considerable benefits for their risk assessment, and is of crucial importance for food security and remediation strategies in contaminated sites. In this work, the forms of six PAHs (fluorene, phenanthrene, fluoranthene, pyrene, benzo[a]anthracene, and benzo[a]pyrene) in soils were separated into three fractions including a desorbing fraction, a non-desorbing fraction, and a bound residual fraction using a sequential extraction mass balance approach. The desorbing and non-desorbing fractions were extracted with hydroxypropyl-beta-cyclodextrin (HPCD) and dichloromethane:acetone (1:1, vol/vol), respectively. The desorbing and non-desorbing fractions always dominated the total PAH content in soils. The proportion of bound PAH residue in nonsterilized soils was small (<16%), and even smaller (4.5%) in sterilized soils. The concentrations of the desorbing fraction of PAHs as well as the percentage of this fraction to the total PAH content in soils clearly decreased in 0–16 weeks, which may be due to microbial biodegradation and its transfer to other fractions in soils. The concentrations of the non-desorbing PAH fractions increased in sterilized soils, while remaining nearly constant or decreasing to some extent in nonsterilized soils after 16 weeks. The proportion of non-desorbing PAH fractions significantly increased in 16 week-incubation, and this proportion was positively correlated with the molecular weights of the PAHs tested, indicating that larger PAHs are more likely to be present in non-desorbing fractions. The bound PAH residue tended to increase at first and decrease thereafter over the 0–16-week period, and microbes played an important role in the formation of bound residue.</description><subject>Applied sciences</subject><subject>Benz(a)Anthracenes - analysis</subject><subject>Benz(a)Anthracenes - isolation & purification</subject><subject>Benzo(a)pyrene - analysis</subject><subject>Benzo(a)pyrene - isolation & purification</subject><subject>Bioavailability</subject><subject>Biodegradation, Environmental</subject><subject>Biological and medical sciences</subject><subject>Chemical engineering</subject><subject>Chemical Fractionation</subject><subject>Cyclodextrins</subject><subject>Exact sciences and technology</subject><subject>Extraction</subject><subject>Fluorenes - analysis</subject><subject>Fluorenes - isolation & purification</subject><subject>Food engineering</subject><subject>Food industries</subject><subject>Form</subject><subject>Fractionation</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General aspects</subject><subject>Microorganisms</subject><subject>Phenanthrene</subject><subject>Phenanthrenes - analysis</subject><subject>Phenanthrenes - isolation & purification</subject><subject>Pollution</subject><subject>Polyallylamine hydrochloride</subject><subject>Polycyclic aromatic hydrocarbons (PAHs)</subject><subject>Polycyclic Aromatic Hydrocarbons - analysis</subject><subject>Polycyclic Aromatic Hydrocarbons - isolation & purification</subject><subject>Pyrenes - analysis</subject><subject>Pyrenes - isolation & purification</subject><subject>Remediation</subject><subject>Residue</subject><subject>Residues</subject><subject>Safety</subject><subject>Security</subject><subject>Soil</subject><subject>Soil Pollutants - analysis</subject><subject>Soil Pollutants - isolation & purification</subject><subject>Soils</subject><issn>0304-3894</issn><issn>1873-3336</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2009</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqF0ctO3DAUBmALUcGU8ghU2dB2k_T4FjurqkVAKyGxgbXlnDjCo0w8tTNIw9PX0UR0BxsfL75zkX5CLihUFGj9fV2tn-zLxk4VA2gqUBVocURWVCtecs7rY7ICDqLkuhGn5GNKawCgSooTckqbumFUwYr8uokWJx9GOz9F6IttGPa4x8FjYWPIC_Lnad_FgDa2mUSXfLdzqfBjkYIf0ifyobdDcudLPSOPN9cPV7_Lu_vbP1c_70qUHKayc1oitCJf3_Z5OaNc6bZlCimVCnvQHDtlleWtFr1wtO4bxmrA1oHAjvEz8vUwdxvD33zAZDY-oRsGO7qwS0ZxQalSTGX55U3JRaOlUM27kFE2j5QZfnsTZgSskYrqTOWBYgwpRdebbfQbG_eGgpmjM2uzRGfm6Awok6PLfZ-XFbt247r_XUtWGVwuwCa0Qx_tiD69OsaklrWYB_04OJfDePYumoTejeg6Hx1Opgv-nVP-AcHTuQE</recordid><startdate>20091230</startdate><enddate>20091230</enddate><creator>Gao, Yanzheng</creator><creator>Zeng, Yuechun</creator><creator>Shen, Qing</creator><creator>Ling, Wanting</creator><creator>Han, Jin</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>7QQ</scope><scope>7SR</scope><scope>7SU</scope><scope>8BQ</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>JG9</scope><scope>KR7</scope><scope>7QO</scope><scope>7ST</scope><scope>7T7</scope><scope>7TV</scope><scope>7U1</scope><scope>7U2</scope><scope>7U7</scope><scope>P64</scope><scope>SOI</scope><scope>7X8</scope></search><sort><creationdate>20091230</creationdate><title>Fractionation of polycyclic aromatic hydrocarbon residues in soils</title><author>Gao, Yanzheng ; Zeng, Yuechun ; Shen, Qing ; Ling, Wanting ; Han, Jin</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c530t-de85c0b4101bf21721378bb27c1157cf083cd7a7a3b84f4e16f92260cbe04cd23</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2009</creationdate><topic>Applied sciences</topic><topic>Benz(a)Anthracenes - analysis</topic><topic>Benz(a)Anthracenes - isolation & purification</topic><topic>Benzo(a)pyrene - analysis</topic><topic>Benzo(a)pyrene - isolation & purification</topic><topic>Bioavailability</topic><topic>Biodegradation, Environmental</topic><topic>Biological and medical sciences</topic><topic>Chemical engineering</topic><topic>Chemical Fractionation</topic><topic>Cyclodextrins</topic><topic>Exact sciences and technology</topic><topic>Extraction</topic><topic>Fluorenes - analysis</topic><topic>Fluorenes - isolation & purification</topic><topic>Food engineering</topic><topic>Food industries</topic><topic>Form</topic><topic>Fractionation</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General aspects</topic><topic>Microorganisms</topic><topic>Phenanthrene</topic><topic>Phenanthrenes - analysis</topic><topic>Phenanthrenes - isolation & purification</topic><topic>Pollution</topic><topic>Polyallylamine hydrochloride</topic><topic>Polycyclic aromatic hydrocarbons (PAHs)</topic><topic>Polycyclic Aromatic Hydrocarbons - analysis</topic><topic>Polycyclic Aromatic Hydrocarbons - isolation & purification</topic><topic>Pyrenes - analysis</topic><topic>Pyrenes - isolation & purification</topic><topic>Remediation</topic><topic>Residue</topic><topic>Residues</topic><topic>Safety</topic><topic>Security</topic><topic>Soil</topic><topic>Soil Pollutants - analysis</topic><topic>Soil Pollutants - isolation & purification</topic><topic>Soils</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Gao, Yanzheng</creatorcontrib><creatorcontrib>Zeng, Yuechun</creatorcontrib><creatorcontrib>Shen, Qing</creatorcontrib><creatorcontrib>Ling, Wanting</creatorcontrib><creatorcontrib>Han, Jin</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>Ceramic Abstracts</collection><collection>Engineered Materials Abstracts</collection><collection>Environmental Engineering Abstracts</collection><collection>METADEX</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Materials Research Database</collection><collection>Civil Engineering Abstracts</collection><collection>Biotechnology Research Abstracts</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution Abstracts</collection><collection>Risk Abstracts</collection><collection>Safety Science and Risk</collection><collection>Toxicology Abstracts</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environment Abstracts</collection><collection>MEDLINE - Academic</collection><jtitle>Journal of hazardous materials</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Gao, Yanzheng</au><au>Zeng, Yuechun</au><au>Shen, Qing</au><au>Ling, Wanting</au><au>Han, Jin</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Fractionation of polycyclic aromatic hydrocarbon residues in soils</atitle><jtitle>Journal of hazardous materials</jtitle><addtitle>J Hazard Mater</addtitle><date>2009-12-30</date><risdate>2009</risdate><volume>172</volume><issue>2</issue><spage>897</spage><epage>903</epage><pages>897-903</pages><issn>0304-3894</issn><eissn>1873-3336</eissn><coden>JHMAD9</coden><abstract>Understanding the forms and availabilities of polycylic aromatic hydrocarbons (PAHs) would have considerable benefits for their risk assessment, and is of crucial importance for food security and remediation strategies in contaminated sites. In this work, the forms of six PAHs (fluorene, phenanthrene, fluoranthene, pyrene, benzo[a]anthracene, and benzo[a]pyrene) in soils were separated into three fractions including a desorbing fraction, a non-desorbing fraction, and a bound residual fraction using a sequential extraction mass balance approach. The desorbing and non-desorbing fractions were extracted with hydroxypropyl-beta-cyclodextrin (HPCD) and dichloromethane:acetone (1:1, vol/vol), respectively. The desorbing and non-desorbing fractions always dominated the total PAH content in soils. The proportion of bound PAH residue in nonsterilized soils was small (<16%), and even smaller (4.5%) in sterilized soils. The concentrations of the desorbing fraction of PAHs as well as the percentage of this fraction to the total PAH content in soils clearly decreased in 0–16 weeks, which may be due to microbial biodegradation and its transfer to other fractions in soils. The concentrations of the non-desorbing PAH fractions increased in sterilized soils, while remaining nearly constant or decreasing to some extent in nonsterilized soils after 16 weeks. The proportion of non-desorbing PAH fractions significantly increased in 16 week-incubation, and this proportion was positively correlated with the molecular weights of the PAHs tested, indicating that larger PAHs are more likely to be present in non-desorbing fractions. The bound PAH residue tended to increase at first and decrease thereafter over the 0–16-week period, and microbes played an important role in the formation of bound residue.</abstract><cop>Kidlington</cop><pub>Elsevier B.V</pub><pmid>19692170</pmid><doi>10.1016/j.jhazmat.2009.07.084</doi><tpages>7</tpages></addata></record> |
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subjects | Applied sciences Benz(a)Anthracenes - analysis Benz(a)Anthracenes - isolation & purification Benzo(a)pyrene - analysis Benzo(a)pyrene - isolation & purification Bioavailability Biodegradation, Environmental Biological and medical sciences Chemical engineering Chemical Fractionation Cyclodextrins Exact sciences and technology Extraction Fluorenes - analysis Fluorenes - isolation & purification Food engineering Food industries Form Fractionation Fundamental and applied biological sciences. Psychology General aspects Microorganisms Phenanthrene Phenanthrenes - analysis Phenanthrenes - isolation & purification Pollution Polyallylamine hydrochloride Polycyclic aromatic hydrocarbons (PAHs) Polycyclic Aromatic Hydrocarbons - analysis Polycyclic Aromatic Hydrocarbons - isolation & purification Pyrenes - analysis Pyrenes - isolation & purification Remediation Residue Residues Safety Security Soil Soil Pollutants - analysis Soil Pollutants - isolation & purification Soils |
title | Fractionation of polycyclic aromatic hydrocarbon residues in soils |
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