Waste Disposal Technologies for Polychlorinated Biphenyls
Improper practices in the disposal of polychlorinated biphenyl (PCB) wastes by land burial, chemical means and incineration distribute these chemicals and related compounds such as polychlorinated dibenzofurans (PCDFs) and polychlorinated dibenzodioxins (PCDDs) throughout the environment. The comple...
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Veröffentlicht in: | Environ. Health Perspect.; (United States) 1985-02, Vol.59, p.163-177 |
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description | Improper practices in the disposal of polychlorinated biphenyl (PCB) wastes by land burial, chemical means and incineration distribute these chemicals and related compounds such as polychlorinated dibenzofurans (PCDFs) and polychlorinated dibenzodioxins (PCDDs) throughout the environment. The complete range of methods for disposal that have been proposed and are in use are examined and analyzed, with emphasis given to the two most commonly used methods: land burial and incineration. The understanding of aquifer contamination caused by migration of PCBs from subsurface burial sites requires a description of the physical, chemical and biological processes governing transport in unsaturated and saturated soils. For this purpose, a model is developed and solved for different soil conditions and external driving functions. The model couples together the fundamental transport phenomena for heat, mass, and moisture flow within the soil. To rehabilitate a contaminated aquifer, contaminated groundwaters are withdrawn through drainage wells, PCBs are extracted with solvents or activated carbon and treated by chemical, photochemical or thermal methods. The chemical and photochemical methods are reviewed, but primary emphasis is devoted to the use of incineration as the preferred method of disposal. After discussing the formation of PCDFs and PCDDs during combustion from chloroaromatic, chloroaliphatic, as well as organic and inorganic chloride precursors, performance characteristics of different thermal destructors are presented and analyzed. To understand how this information can be used, basic design equations are developed from governing heat and mass balances that can be applied to the construction of incinerators capable of more than 99.99% destruction with minimal to nondetectable levels of PCDFs and PCDDs. |
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Thomas</creator><creatorcontrib>Piver, Warren T. ; Lindstrom, F. Thomas ; NIEHS, Research Triangle Park, NC</creatorcontrib><description>Improper practices in the disposal of polychlorinated biphenyl (PCB) wastes by land burial, chemical means and incineration distribute these chemicals and related compounds such as polychlorinated dibenzofurans (PCDFs) and polychlorinated dibenzodioxins (PCDDs) throughout the environment. The complete range of methods for disposal that have been proposed and are in use are examined and analyzed, with emphasis given to the two most commonly used methods: land burial and incineration. The understanding of aquifer contamination caused by migration of PCBs from subsurface burial sites requires a description of the physical, chemical and biological processes governing transport in unsaturated and saturated soils. For this purpose, a model is developed and solved for different soil conditions and external driving functions. The model couples together the fundamental transport phenomena for heat, mass, and moisture flow within the soil. To rehabilitate a contaminated aquifer, contaminated groundwaters are withdrawn through drainage wells, PCBs are extracted with solvents or activated carbon and treated by chemical, photochemical or thermal methods. The chemical and photochemical methods are reviewed, but primary emphasis is devoted to the use of incineration as the preferred method of disposal. After discussing the formation of PCDFs and PCDDs during combustion from chloroaromatic, chloroaliphatic, as well as organic and inorganic chloride precursors, performance characteristics of different thermal destructors are presented and analyzed. To understand how this information can be used, basic design equations are developed from governing heat and mass balances that can be applied to the construction of incinerators capable of more than 99.99% destruction with minimal to nondetectable levels of PCDFs and PCDDs.</description><identifier>ISSN: 0091-6765</identifier><identifier>DOI: 10.2307/3429889</identifier><identifier>PMID: 3921358</identifier><language>eng</language><publisher>United States: National Institute of Environmental Health Sciences. National Institutes of Health. 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Thomas</creatorcontrib><creatorcontrib>NIEHS, Research Triangle Park, NC</creatorcontrib><title>Waste Disposal Technologies for Polychlorinated Biphenyls</title><title>Environ. Health Perspect.; (United States)</title><addtitle>Environ Health Perspect</addtitle><description>Improper practices in the disposal of polychlorinated biphenyl (PCB) wastes by land burial, chemical means and incineration distribute these chemicals and related compounds such as polychlorinated dibenzofurans (PCDFs) and polychlorinated dibenzodioxins (PCDDs) throughout the environment. The complete range of methods for disposal that have been proposed and are in use are examined and analyzed, with emphasis given to the two most commonly used methods: land burial and incineration. The understanding of aquifer contamination caused by migration of PCBs from subsurface burial sites requires a description of the physical, chemical and biological processes governing transport in unsaturated and saturated soils. For this purpose, a model is developed and solved for different soil conditions and external driving functions. The model couples together the fundamental transport phenomena for heat, mass, and moisture flow within the soil. To rehabilitate a contaminated aquifer, contaminated groundwaters are withdrawn through drainage wells, PCBs are extracted with solvents or activated carbon and treated by chemical, photochemical or thermal methods. The chemical and photochemical methods are reviewed, but primary emphasis is devoted to the use of incineration as the preferred method of disposal. After discussing the formation of PCDFs and PCDDs during combustion from chloroaromatic, chloroaliphatic, as well as organic and inorganic chloride precursors, performance characteristics of different thermal destructors are presented and analyzed. To understand how this information can be used, basic design equations are developed from governing heat and mass balances that can be applied to the construction of incinerators capable of more than 99.99% destruction with minimal to nondetectable levels of PCDFs and PCDDs.</description><subject>500200 - Environment, Atmospheric- Chemicals Monitoring & Transport- (-1989)</subject><subject>510200 - Environment, Terrestrial- Chemicals Monitoring & Transport- (-1989)</subject><subject>520200 - Environment, Aquatic- Chemicals Monitoring & Transport- (-1989)</subject><subject>AROMATICS</subject><subject>BENZOFURANS</subject><subject>Chemical Phenomena</subject><subject>Chemistry</subject><subject>CHLORINATED AROMATIC HYDROCARBONS</subject><subject>CONTAMINATION</subject><subject>Dibenzofurans, Polychlorinated</subject><subject>Dioxins</subject><subject>ENERGY</subject><subject>ENVIRONMENTAL SCIENCES</subject><subject>ENVIRONMENTAL TRANSPORT</subject><subject>Formation and Decomposition and Environmental Pollution</subject><subject>FURANS</subject><subject>GROUND WATER</subject><subject>Groundwater</subject><subject>HALOGENATED AROMATIC HYDROCARBONS</subject><subject>HEAT</subject><subject>HETEROCYCLIC COMPOUNDS</subject><subject>Hot Temperature</subject><subject>HYDROGEN COMPOUNDS</subject><subject>INCINERATORS</subject><subject>Liquids</subject><subject>MANAGEMENT</subject><subject>MASS TRANSFER</subject><subject>MATHEMATICAL MODELS</subject><subject>Models, Theoretical</subject><subject>ORGANIC CHLORINE COMPOUNDS</subject><subject>ORGANIC COMPOUNDS</subject><subject>ORGANIC HALOGEN COMPOUNDS</subject><subject>ORGANIC OXYGEN COMPOUNDS</subject><subject>OXYGEN COMPOUNDS</subject><subject>Polychlorinated biphenyls</subject><subject>Polychlorinated Biphenyls - standards</subject><subject>Refuse Disposal - methods</subject><subject>Soil - analysis</subject><subject>Soil biochemistry</subject><subject>Soil chemistry</subject><subject>Soil Pollutants - analysis</subject><subject>Soil pollution</subject><subject>Soil water</subject><subject>Soil water movement</subject><subject>SOILS</subject><subject>WASTE DISPOSAL</subject><subject>WASTE MANAGEMENT</subject><subject>WATER</subject><subject>Water Pollutants, Chemical - analysis</subject><issn>0091-6765</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>1985</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNqNkUtLAzEUhbNQfOMvEAYRXVVzJ3MzyUbwrSDoQnEZ0kzGRtJJTVKh_96RlqIL0dVdnI9zOPcQsgv0uGS0PmFVKYWQK2SDUgkDXnNcJ5spvVFKQXC-RtaYLIGh2CDyRadsi0uXJiFpXzxZM-qCD6_OpqINsXgMfmZGPkTX6Wyb4txNRrab-bRNVlvtk91Z3C3yfH31dHE7uH-4ubs4ux8YBJYH3DCEkgrgQlusG62x4ZqzFkU5tMZUuhUNmCHUkqKFChkDYTRixdq6KTnbIqdz38l0OLaNsV2O2qtJdGMdZypop34qnRup1_ChALmggvYG-3ODkLJTybjcdzSh66zJCksuEb9SDhcpMbxPbcpq7JKx3uvOhmlSUDFgFbB_gCAlR_wbZILRqoYePJqDJoaUom2X3YCqr0HVYtCe3Pv-iiW3WLPXD-b6W8oh_mrzCetdp0I</recordid><startdate>19850201</startdate><enddate>19850201</enddate><creator>Piver, Warren T.</creator><creator>Lindstrom, F. 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Thomas</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c513t-6c351208168ae57daa5d6a63f582becc4af8d1cb17905e1453318ca5543f7d263</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>1985</creationdate><topic>500200 - Environment, Atmospheric- Chemicals Monitoring & Transport- (-1989)</topic><topic>510200 - Environment, Terrestrial- Chemicals Monitoring & Transport- (-1989)</topic><topic>520200 - Environment, Aquatic- Chemicals Monitoring & Transport- (-1989)</topic><topic>AROMATICS</topic><topic>BENZOFURANS</topic><topic>Chemical Phenomena</topic><topic>Chemistry</topic><topic>CHLORINATED AROMATIC HYDROCARBONS</topic><topic>CONTAMINATION</topic><topic>Dibenzofurans, Polychlorinated</topic><topic>Dioxins</topic><topic>ENERGY</topic><topic>ENVIRONMENTAL SCIENCES</topic><topic>ENVIRONMENTAL TRANSPORT</topic><topic>Formation and Decomposition and Environmental Pollution</topic><topic>FURANS</topic><topic>GROUND WATER</topic><topic>Groundwater</topic><topic>HALOGENATED AROMATIC HYDROCARBONS</topic><topic>HEAT</topic><topic>HETEROCYCLIC COMPOUNDS</topic><topic>Hot Temperature</topic><topic>HYDROGEN COMPOUNDS</topic><topic>INCINERATORS</topic><topic>Liquids</topic><topic>MANAGEMENT</topic><topic>MASS TRANSFER</topic><topic>MATHEMATICAL MODELS</topic><topic>Models, Theoretical</topic><topic>ORGANIC CHLORINE COMPOUNDS</topic><topic>ORGANIC COMPOUNDS</topic><topic>ORGANIC HALOGEN COMPOUNDS</topic><topic>ORGANIC OXYGEN COMPOUNDS</topic><topic>OXYGEN COMPOUNDS</topic><topic>Polychlorinated biphenyls</topic><topic>Polychlorinated Biphenyls - standards</topic><topic>Refuse Disposal - methods</topic><topic>Soil - analysis</topic><topic>Soil biochemistry</topic><topic>Soil chemistry</topic><topic>Soil Pollutants - analysis</topic><topic>Soil pollution</topic><topic>Soil water</topic><topic>Soil water movement</topic><topic>SOILS</topic><topic>WASTE DISPOSAL</topic><topic>WASTE MANAGEMENT</topic><topic>WATER</topic><topic>Water Pollutants, Chemical - analysis</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Piver, Warren T.</creatorcontrib><creatorcontrib>Lindstrom, F. Thomas</creatorcontrib><creatorcontrib>NIEHS, Research Triangle Park, NC</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Aqualine</collection><collection>Environment Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Environment Abstracts</collection><collection>Pollution Abstracts</collection><collection>OSTI.GOV</collection><collection>PubMed Central (Full Participant titles)</collection><jtitle>Environ. Health Perspect.; (United States)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Piver, Warren T.</au><au>Lindstrom, F. Thomas</au><aucorp>NIEHS, Research Triangle Park, NC</aucorp><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Waste Disposal Technologies for Polychlorinated Biphenyls</atitle><jtitle>Environ. Health Perspect.; (United States)</jtitle><addtitle>Environ Health Perspect</addtitle><date>1985-02-01</date><risdate>1985</risdate><volume>59</volume><spage>163</spage><epage>177</epage><pages>163-177</pages><issn>0091-6765</issn><abstract>Improper practices in the disposal of polychlorinated biphenyl (PCB) wastes by land burial, chemical means and incineration distribute these chemicals and related compounds such as polychlorinated dibenzofurans (PCDFs) and polychlorinated dibenzodioxins (PCDDs) throughout the environment. The complete range of methods for disposal that have been proposed and are in use are examined and analyzed, with emphasis given to the two most commonly used methods: land burial and incineration. The understanding of aquifer contamination caused by migration of PCBs from subsurface burial sites requires a description of the physical, chemical and biological processes governing transport in unsaturated and saturated soils. For this purpose, a model is developed and solved for different soil conditions and external driving functions. The model couples together the fundamental transport phenomena for heat, mass, and moisture flow within the soil. To rehabilitate a contaminated aquifer, contaminated groundwaters are withdrawn through drainage wells, PCBs are extracted with solvents or activated carbon and treated by chemical, photochemical or thermal methods. The chemical and photochemical methods are reviewed, but primary emphasis is devoted to the use of incineration as the preferred method of disposal. After discussing the formation of PCDFs and PCDDs during combustion from chloroaromatic, chloroaliphatic, as well as organic and inorganic chloride precursors, performance characteristics of different thermal destructors are presented and analyzed. To understand how this information can be used, basic design equations are developed from governing heat and mass balances that can be applied to the construction of incinerators capable of more than 99.99% destruction with minimal to nondetectable levels of PCDFs and PCDDs.</abstract><cop>United States</cop><pub>National Institute of Environmental Health Sciences. National Institutes of Health. Department of Health, Education and Welfare</pub><pmid>3921358</pmid><doi>10.2307/3429889</doi><tpages>15</tpages><oa>free_for_read</oa></addata></record> |
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subjects | 500200 - Environment, Atmospheric- Chemicals Monitoring & Transport- (-1989) 510200 - Environment, Terrestrial- Chemicals Monitoring & Transport- (-1989) 520200 - Environment, Aquatic- Chemicals Monitoring & Transport- (-1989) AROMATICS BENZOFURANS Chemical Phenomena Chemistry CHLORINATED AROMATIC HYDROCARBONS CONTAMINATION Dibenzofurans, Polychlorinated Dioxins ENERGY ENVIRONMENTAL SCIENCES ENVIRONMENTAL TRANSPORT Formation and Decomposition and Environmental Pollution FURANS GROUND WATER Groundwater HALOGENATED AROMATIC HYDROCARBONS HEAT HETEROCYCLIC COMPOUNDS Hot Temperature HYDROGEN COMPOUNDS INCINERATORS Liquids MANAGEMENT MASS TRANSFER MATHEMATICAL MODELS Models, Theoretical ORGANIC CHLORINE COMPOUNDS ORGANIC COMPOUNDS ORGANIC HALOGEN COMPOUNDS ORGANIC OXYGEN COMPOUNDS OXYGEN COMPOUNDS Polychlorinated biphenyls Polychlorinated Biphenyls - standards Refuse Disposal - methods Soil - analysis Soil biochemistry Soil chemistry Soil Pollutants - analysis Soil pollution Soil water Soil water movement SOILS WASTE DISPOSAL WASTE MANAGEMENT WATER Water Pollutants, Chemical - analysis |
title | Waste Disposal Technologies for Polychlorinated Biphenyls |
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