Sorption of halogenated phenols and pharmaceuticals to biochar: affecting factors and mechanisms

The feasibility of using biochar as a sorbent to remove nine halogenated phenols (2,4-dichlorophenol, 2,4-dibromophenol, 2,4-difluorophenol, 2-chlorophenol, 4-chlorophenol, 2-bromophenol, 4-bromophenol, 2-fluorophenol, and 4-fluorophenol) and two pharmaceuticals (triclosan and ibuprofen) from water...

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Veröffentlicht in:Environmental science and pollution research international 2016-01, Vol.23 (2), p.951-961
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description The feasibility of using biochar as a sorbent to remove nine halogenated phenols (2,4-dichlorophenol, 2,4-dibromophenol, 2,4-difluorophenol, 2-chlorophenol, 4-chlorophenol, 2-bromophenol, 4-bromophenol, 2-fluorophenol, and 4-fluorophenol) and two pharmaceuticals (triclosan and ibuprofen) from water was examined through a series of batch experiments. Types of biochar, synthesized using various biomasses including fallen leaves, rice straw, corn stalk, used coffee grounds, and biosolids, were evaluated. Compared to granular activated carbon (GAC), most of the biochar samples did not effectively remove halogenated phenols or pharmaceuticals from water. The increase in pH and deprotonation of phenols in biochar systems may be responsible for its ineffectiveness at this task. When pH was maintained at 4 or 7, the sorption capacity of biochar was markedly increased. Considering maximum sorption capacity and properties of sorbents and sorbates, it appears that the sorption capacity of biochar for halogenated phenols is related to the surface area and carbon content of the biochar and the hydrophobicity of halogenated phenols. In the cases of triclosan and ibuprofen, the sorptive capacities of GAC, graphite, and biochars were also significantly affected by pH, according to the point of zero charge (PZC) of sorbents and deprotonation of the pharmaceuticals. Pyrolysis temperature did not affect the sorption capacity of halogenated phenols or pharmaceuticals. Based on the experimental observations, some biochars are good candidates for removal of halogenated phenols, triclosan, and ibuprofen from water and soil.
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Types of biochar, synthesized using various biomasses including fallen leaves, rice straw, corn stalk, used coffee grounds, and biosolids, were evaluated. Compared to granular activated carbon (GAC), most of the biochar samples did not effectively remove halogenated phenols or pharmaceuticals from water. The increase in pH and deprotonation of phenols in biochar systems may be responsible for its ineffectiveness at this task. When pH was maintained at 4 or 7, the sorption capacity of biochar was markedly increased. Considering maximum sorption capacity and properties of sorbents and sorbates, it appears that the sorption capacity of biochar for halogenated phenols is related to the surface area and carbon content of the biochar and the hydrophobicity of halogenated phenols. In the cases of triclosan and ibuprofen, the sorptive capacities of GAC, graphite, and biochars were also significantly affected by pH, according to the point of zero charge (PZC) of sorbents and deprotonation of the pharmaceuticals. Pyrolysis temperature did not affect the sorption capacity of halogenated phenols or pharmaceuticals. 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In the cases of triclosan and ibuprofen, the sorptive capacities of GAC, graphite, and biochars were also significantly affected by pH, according to the point of zero charge (PZC) of sorbents and deprotonation of the pharmaceuticals. Pyrolysis temperature did not affect the sorption capacity of halogenated phenols or pharmaceuticals. Based on the experimental observations, some biochars are good candidates for removal of halogenated phenols, triclosan, and ibuprofen from water and soil.</description><subject>2,4-dichlorophenol</subject><subject>2-chlorophenol</subject><subject>Activated carbon</subject><subject>adsorbents</subject><subject>Adsorption</subject><subject>Aquatic Pollution</subject><subject>Atmospheric Protection/Air Quality Control/Air Pollution</subject><subject>biochar</subject><subject>Biomass</subject><subject>Biosolids</subject><subject>Carbon</subject><subject>Carbon fibers</subject><subject>Charcoal</subject><subject>Charcoal - chemistry</subject><subject>Chlorophenol</subject><subject>Chlorophenols - chemistry</subject><subject>Coffee</subject><subject>corn stover</subject><subject>Drugs</subject><subject>Earth and Environmental Science</subject><subject>Ecological Assessment and Remediation (CLEAR 2014) Conference: Environmental Pollution and Remediation</subject><subject>Ecotoxicology</subject><subject>Environment</subject><subject>Environmental Chemistry</subject><subject>Environmental Health</subject><subject>Explosives</subject><subject>graphene</subject><subject>Heavy metals</subject><subject>Hydrogen</subject><subject>Hydrophobicity</subject><subject>Ibuprofen</subject><subject>Ibuprofen - chemistry</subject><subject>Land pollution</subject><subject>leaves</subject><subject>Metals</subject><subject>Nonsteroidal anti-inflammatory drugs</subject><subject>Organic contaminants</subject><subject>p-Chlorophenol</subject><subject>pH effects</subject><subject>Pharmaceuticals</subject><subject>Phenols</subject><subject>Phenols - chemistry</subject><subject>Pyrolysis</subject><subject>Remediation</subject><subject>Rice straw</subject><subject>Selected Papers from the 2nd Contaminated Land</subject><subject>Soil</subject><subject>Soil Pollutants - chemistry</subject><subject>Soil temperature</subject><subject>sorbates</subject><subject>Sorbents</subject><subject>Sorption</subject><subject>surface area</subject><subject>temperature</subject><subject>Triclosan</subject><subject>Triclosan - chemistry</subject><subject>Waste Water Technology</subject><subject>Water Management</subject><subject>Water Pollution Control</subject><subject>Water Purification - methods</subject><issn>0944-1344</issn><issn>1614-7499</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2016</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNqNkU9v1DAQxS1ERZfCB-ACkbhwSTtjO7bDrar4J1XqofRsvM54m2pjL3Zy4NvjVQpCHBAnW_N-743sx9grhHME0BcFUXSqBexayQFb84RtUKFstez7p2wDvZQtCilP2fNSHgA49Fw_Y6e8U0Yr6Dfs223Kh3lMsUmhuXf7tKPoZhqawz3FtC-Ni8e7y5PztMyjd3U2p2Y7Jl-n7xsXAvl5jLsmOD-nvDomqmocy1ResJNQPfTy8Txjdx8_fL363F7ffPpydXnd-k6ouRVm0KREL2EbvA-oveZmMNyDGgLoAOgDKG-QQgUlR72FgTSFoDo5KC7O2Ls195DT94XKbKexeNrvXaS0FItamU71AsT_oPWfTAd9Rd_-hT6kJcf6kEoZo2qaOFK4Uj6nUjIFe8jj5PIPi2CPTdm1KVubssemrKme14_Jy3ai4bfjVzUV4CtQqhR3lP9Y_Y_UN6spuGTdLo_F3t1WSQGgQNMZ8RNDOKd9</recordid><startdate>20160101</startdate><enddate>20160101</enddate><creator>Oh, Seok-Young</creator><creator>Seo, Yong-Deuk</creator><general>Springer Berlin Heidelberg</general><general>Springer Nature B.V</general><scope>FBQ</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>3V.</scope><scope>7QL</scope><scope>7SN</scope><scope>7T7</scope><scope>7TV</scope><scope>7U7</scope><scope>7WY</scope><scope>7WZ</scope><scope>7X7</scope><scope>7XB</scope><scope>87Z</scope><scope>88E</scope><scope>88I</scope><scope>8AO</scope><scope>8C1</scope><scope>8FD</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>8FL</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BEZIV</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>FRNLG</scope><scope>FYUFA</scope><scope>F~G</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>HCIFZ</scope><scope>K60</scope><scope>K6~</scope><scope>K9.</scope><scope>L.-</scope><scope>M0C</scope><scope>M0S</scope><scope>M1P</scope><scope>M2P</scope><scope>M7N</scope><scope>P64</scope><scope>PATMY</scope><scope>PQBIZ</scope><scope>PQBZA</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>7X8</scope><scope>7ST</scope><scope>7TG</scope><scope>KL.</scope><scope>SOI</scope></search><sort><creationdate>20160101</creationdate><title>Sorption of halogenated phenols and pharmaceuticals to biochar: affecting factors and mechanisms</title><author>Oh, Seok-Young ; 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Types of biochar, synthesized using various biomasses including fallen leaves, rice straw, corn stalk, used coffee grounds, and biosolids, were evaluated. Compared to granular activated carbon (GAC), most of the biochar samples did not effectively remove halogenated phenols or pharmaceuticals from water. The increase in pH and deprotonation of phenols in biochar systems may be responsible for its ineffectiveness at this task. When pH was maintained at 4 or 7, the sorption capacity of biochar was markedly increased. Considering maximum sorption capacity and properties of sorbents and sorbates, it appears that the sorption capacity of biochar for halogenated phenols is related to the surface area and carbon content of the biochar and the hydrophobicity of halogenated phenols. In the cases of triclosan and ibuprofen, the sorptive capacities of GAC, graphite, and biochars were also significantly affected by pH, according to the point of zero charge (PZC) of sorbents and deprotonation of the pharmaceuticals. Pyrolysis temperature did not affect the sorption capacity of halogenated phenols or pharmaceuticals. Based on the experimental observations, some biochars are good candidates for removal of halogenated phenols, triclosan, and ibuprofen from water and soil.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><pmid>25687609</pmid><doi>10.1007/s11356-015-4201-8</doi><tpages>11</tpages></addata></record>
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subjects 2,4-dichlorophenol
2-chlorophenol
Activated carbon
adsorbents
Adsorption
Aquatic Pollution
Atmospheric Protection/Air Quality Control/Air Pollution
biochar
Biomass
Biosolids
Carbon
Carbon fibers
Charcoal
Charcoal - chemistry
Chlorophenol
Chlorophenols - chemistry
Coffee
corn stover
Drugs
Earth and Environmental Science
Ecological Assessment and Remediation (CLEAR 2014) Conference: Environmental Pollution and Remediation
Ecotoxicology
Environment
Environmental Chemistry
Environmental Health
Explosives
graphene
Heavy metals
Hydrogen
Hydrophobicity
Ibuprofen
Ibuprofen - chemistry
Land pollution
leaves
Metals
Nonsteroidal anti-inflammatory drugs
Organic contaminants
p-Chlorophenol
pH effects
Pharmaceuticals
Phenols
Phenols - chemistry
Pyrolysis
Remediation
Rice straw
Selected Papers from the 2nd Contaminated Land
Soil
Soil Pollutants - chemistry
Soil temperature
sorbates
Sorbents
Sorption
surface area
temperature
Triclosan
Triclosan - chemistry
Waste Water Technology
Water Management
Water Pollution Control
Water Purification - methods
title Sorption of halogenated phenols and pharmaceuticals to biochar: affecting factors and mechanisms
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