Fate of coagulant species and conformational effects during the aggregation of a model of a humic substance with Al13 polycations

A model of a humic substance (MHS) obtained from auto-oxidation of catechol and glycine, was aggregated at pH 6 and 8 with Al(13) polycations. The fate of Al(13) coagulant species upon association with MHS functional groups was studied using solid state (27)Al Magic-angle spinning (MAS) NMR and CP-M...

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Veröffentlicht in:Water research (Oxford) 2006-06, Vol.40 (10), p.1965-1974
Hauptverfasser: Kazpard, V, Lartiges, B.S, Frochot, C, d'Espinose de la Caillerie, J.B, Viriot, M.L, Portal, J.M, Gorner, T, Bersillon, J.L
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container_end_page 1974
container_issue 10
container_start_page 1965
container_title Water research (Oxford)
container_volume 40
creator Kazpard, V
Lartiges, B.S
Frochot, C
d'Espinose de la Caillerie, J.B
Viriot, M.L
Portal, J.M
Gorner, T
Bersillon, J.L
description A model of a humic substance (MHS) obtained from auto-oxidation of catechol and glycine, was aggregated at pH 6 and 8 with Al(13) polycations. The fate of Al(13) coagulant species upon association with MHS functional groups was studied using solid state (27)Al Magic-angle spinning (MAS) NMR and CP-MAS (13)C NMR. Electrophoretic measurements and steady-state fluorescence spectroscopy with pyrene as a fluoroprobe, were combined to investigate structural re-organization of humic material with aluminum concentration. MAS (27)Al NMR revealed that the coagulant species are Al(13) polycations or oligomers of Al(13) units at both pHs. CP MAS (13)C spectra indicated that, at low Al concentration, hydrolyzed aluminum species bind selectively to carboxylic groups at pH 6 and to phenolic moieties at pH 8. At higher coagulant concentrations, the remaining functional groups also interact with hydrolyzed Al to yield similar CP MAS (13)C spectra in the optimum concentration range. Negative values of electrophoretic mobility were obtained at optimum coagulant concentrations even though an overall charge balance was achieved between MHS anionic charge and Al(13) cationic charge at pH 6. The polarity-sensitive fluorescence of pyrene revealed that the interaction of Al(13) coagulant species with MHS functional groups induces the formation of intramolecular hydrophobic microenvironments. Such structural changes were reversed upon further addition of Al(13) polycations.
doi_str_mv 10.1016/j.watres.2006.03.014
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The fate of Al(13) coagulant species upon association with MHS functional groups was studied using solid state (27)Al Magic-angle spinning (MAS) NMR and CP-MAS (13)C NMR. Electrophoretic measurements and steady-state fluorescence spectroscopy with pyrene as a fluoroprobe, were combined to investigate structural re-organization of humic material with aluminum concentration. MAS (27)Al NMR revealed that the coagulant species are Al(13) polycations or oligomers of Al(13) units at both pHs. CP MAS (13)C spectra indicated that, at low Al concentration, hydrolyzed aluminum species bind selectively to carboxylic groups at pH 6 and to phenolic moieties at pH 8. At higher coagulant concentrations, the remaining functional groups also interact with hydrolyzed Al to yield similar CP MAS (13)C spectra in the optimum concentration range. Negative values of electrophoretic mobility were obtained at optimum coagulant concentrations even though an overall charge balance was achieved between MHS anionic charge and Al(13) cationic charge at pH 6. The polarity-sensitive fluorescence of pyrene revealed that the interaction of Al(13) coagulant species with MHS functional groups induces the formation of intramolecular hydrophobic microenvironments. 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The fate of Al(13) coagulant species upon association with MHS functional groups was studied using solid state (27)Al Magic-angle spinning (MAS) NMR and CP-MAS (13)C NMR. Electrophoretic measurements and steady-state fluorescence spectroscopy with pyrene as a fluoroprobe, were combined to investigate structural re-organization of humic material with aluminum concentration. MAS (27)Al NMR revealed that the coagulant species are Al(13) polycations or oligomers of Al(13) units at both pHs. CP MAS (13)C spectra indicated that, at low Al concentration, hydrolyzed aluminum species bind selectively to carboxylic groups at pH 6 and to phenolic moieties at pH 8. At higher coagulant concentrations, the remaining functional groups also interact with hydrolyzed Al to yield similar CP MAS (13)C spectra in the optimum concentration range. Negative values of electrophoretic mobility were obtained at optimum coagulant concentrations even though an overall charge balance was achieved between MHS anionic charge and Al(13) cationic charge at pH 6. The polarity-sensitive fluorescence of pyrene revealed that the interaction of Al(13) coagulant species with MHS functional groups induces the formation of intramolecular hydrophobic microenvironments. Such structural changes were reversed upon further addition of Al(13) polycations.</description><subject>aluminum</subject><subject>Aluminum Compounds - chemistry</subject><subject>Applied sciences</subject><subject>catechol</subject><subject>cations</subject><subject>coagulants</subject><subject>coagulation</subject><subject>drinking water</subject><subject>Electrophoresis</subject><subject>Environmental Engineering</subject><subject>Environmental Sciences</subject><subject>Exact sciences and technology</subject><subject>fluorescence</subject><subject>glycine (amino acid)</subject><subject>humic substances</subject><subject>Humic Substances - analysis</subject><subject>Hydrogen-Ion Concentration</subject><subject>hydrolysis</subject><subject>hydrophobicity</subject><subject>Magnetic Resonance Spectroscopy</subject><subject>nuclear magnetic resonance spectroscopy</subject><subject>organic matter</subject><subject>Other industrial wastes. Sewage sludge</subject><subject>Pollution</subject><subject>Polyamines - chemistry</subject><subject>provenance</subject><subject>river water</subject><subject>simulation models</subject><subject>soil aggregates</subject><subject>spectroscopy</subject><subject>Wastes</subject><subject>Water Pollutants, Chemical - analysis</subject><subject>Water Purification - methods</subject><subject>water treatment</subject><subject>Water treatment and pollution</subject><issn>0043-1354</issn><issn>1879-2448</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2006</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNpFkE1v1DAQQC0EokvhHyDwhQOHhPFHHOe4qlqKtBIH6NmaOHY2q3ys7ISqR_45TrOiJ1uj90aaR8hHBjkDpr6d8kecg4s5B1A5iByYfEV2TJdVxqXUr8kOQIqMiUJekXcxngCAc1G9JVdMqVJzwXfk7x3Ojk6e2gnbpcdxpvHsbOcixbFJ09FPYcC5m0bsqfPe2TnSZgnd2NL56Ci2bXDtM7CuQTpMjeu373EZOkvjUscZR-voYzcf6b5ngp6n_sk-S_E9eeOxj-7D5b0mD3e3v2_us8PP7z9u9ofMpgNkhspVGspScaElKzizIGuOCuqKc2QsXeMdKMV5zaRqtC98UYi65lUaN4yJa_J123vE3pxDN2B4MhN25n5_MOssxVFF8v-srNxYG6YYg_P_BQZmrW9OZqtv1voGhEn1k_Zp085LPbjmRbrkTsCXC4DRYu9DytLFF64stQYtEvd54zxOBtuQmIdfHJgABroAJcU_h3mX_Q</recordid><startdate>200606</startdate><enddate>200606</enddate><creator>Kazpard, V</creator><creator>Lartiges, B.S</creator><creator>Frochot, C</creator><creator>d'Espinose de la Caillerie, J.B</creator><creator>Viriot, M.L</creator><creator>Portal, J.M</creator><creator>Gorner, T</creator><creator>Bersillon, J.L</creator><general>Elsevier Science</general><general>IWA Publishing/Elsevier</general><scope>FBQ</scope><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>1XC</scope><scope>VOOES</scope><orcidid>https://orcid.org/0000-0002-7659-3864</orcidid><orcidid>https://orcid.org/0000-0002-6722-053X</orcidid><orcidid>https://orcid.org/0000-0002-2463-6877</orcidid></search><sort><creationdate>200606</creationdate><title>Fate of coagulant species and conformational effects during the aggregation of a model of a humic substance with Al13 polycations</title><author>Kazpard, V ; Lartiges, B.S ; Frochot, C ; d'Espinose de la Caillerie, J.B ; Viriot, M.L ; Portal, J.M ; Gorner, T ; Bersillon, J.L</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c3544-a6e98077623841521c04b2a60b922a11232fe06622b146d8f5f553bb29fe0d113</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2006</creationdate><topic>aluminum</topic><topic>Aluminum Compounds - chemistry</topic><topic>Applied sciences</topic><topic>catechol</topic><topic>cations</topic><topic>coagulants</topic><topic>coagulation</topic><topic>drinking water</topic><topic>Electrophoresis</topic><topic>Environmental Engineering</topic><topic>Environmental Sciences</topic><topic>Exact sciences and technology</topic><topic>fluorescence</topic><topic>glycine (amino acid)</topic><topic>humic substances</topic><topic>Humic Substances - analysis</topic><topic>Hydrogen-Ion Concentration</topic><topic>hydrolysis</topic><topic>hydrophobicity</topic><topic>Magnetic Resonance Spectroscopy</topic><topic>nuclear magnetic resonance spectroscopy</topic><topic>organic matter</topic><topic>Other industrial wastes. Sewage sludge</topic><topic>Pollution</topic><topic>Polyamines - chemistry</topic><topic>provenance</topic><topic>river water</topic><topic>simulation models</topic><topic>soil aggregates</topic><topic>spectroscopy</topic><topic>Wastes</topic><topic>Water Pollutants, Chemical - analysis</topic><topic>Water Purification - methods</topic><topic>water treatment</topic><topic>Water treatment and pollution</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Kazpard, V</creatorcontrib><creatorcontrib>Lartiges, B.S</creatorcontrib><creatorcontrib>Frochot, C</creatorcontrib><creatorcontrib>d'Espinose de la Caillerie, J.B</creatorcontrib><creatorcontrib>Viriot, M.L</creatorcontrib><creatorcontrib>Portal, J.M</creatorcontrib><creatorcontrib>Gorner, T</creatorcontrib><creatorcontrib>Bersillon, J.L</creatorcontrib><collection>AGRIS</collection><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>Hyper Article en Ligne (HAL)</collection><collection>Hyper Article en Ligne (HAL) (Open Access)</collection><jtitle>Water research (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Kazpard, V</au><au>Lartiges, B.S</au><au>Frochot, C</au><au>d'Espinose de la Caillerie, J.B</au><au>Viriot, M.L</au><au>Portal, J.M</au><au>Gorner, T</au><au>Bersillon, J.L</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Fate of coagulant species and conformational effects during the aggregation of a model of a humic substance with Al13 polycations</atitle><jtitle>Water research (Oxford)</jtitle><addtitle>Water Res</addtitle><date>2006-06</date><risdate>2006</risdate><volume>40</volume><issue>10</issue><spage>1965</spage><epage>1974</epage><pages>1965-1974</pages><issn>0043-1354</issn><eissn>1879-2448</eissn><coden>WATRAG</coden><abstract>A model of a humic substance (MHS) obtained from auto-oxidation of catechol and glycine, was aggregated at pH 6 and 8 with Al(13) polycations. The fate of Al(13) coagulant species upon association with MHS functional groups was studied using solid state (27)Al Magic-angle spinning (MAS) NMR and CP-MAS (13)C NMR. Electrophoretic measurements and steady-state fluorescence spectroscopy with pyrene as a fluoroprobe, were combined to investigate structural re-organization of humic material with aluminum concentration. MAS (27)Al NMR revealed that the coagulant species are Al(13) polycations or oligomers of Al(13) units at both pHs. CP MAS (13)C spectra indicated that, at low Al concentration, hydrolyzed aluminum species bind selectively to carboxylic groups at pH 6 and to phenolic moieties at pH 8. At higher coagulant concentrations, the remaining functional groups also interact with hydrolyzed Al to yield similar CP MAS (13)C spectra in the optimum concentration range. Negative values of electrophoretic mobility were obtained at optimum coagulant concentrations even though an overall charge balance was achieved between MHS anionic charge and Al(13) cationic charge at pH 6. The polarity-sensitive fluorescence of pyrene revealed that the interaction of Al(13) coagulant species with MHS functional groups induces the formation of intramolecular hydrophobic microenvironments. Such structural changes were reversed upon further addition of Al(13) polycations.</abstract><cop>Oxford</cop><pub>Elsevier Science</pub><pmid>16678232</pmid><doi>10.1016/j.watres.2006.03.014</doi><tpages>10</tpages><orcidid>https://orcid.org/0000-0002-7659-3864</orcidid><orcidid>https://orcid.org/0000-0002-6722-053X</orcidid><orcidid>https://orcid.org/0000-0002-2463-6877</orcidid><oa>free_for_read</oa></addata></record>
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source MEDLINE; Elsevier ScienceDirect Journals Complete
subjects aluminum
Aluminum Compounds - chemistry
Applied sciences
catechol
cations
coagulants
coagulation
drinking water
Electrophoresis
Environmental Engineering
Environmental Sciences
Exact sciences and technology
fluorescence
glycine (amino acid)
humic substances
Humic Substances - analysis
Hydrogen-Ion Concentration
hydrolysis
hydrophobicity
Magnetic Resonance Spectroscopy
nuclear magnetic resonance spectroscopy
organic matter
Other industrial wastes. Sewage sludge
Pollution
Polyamines - chemistry
provenance
river water
simulation models
soil aggregates
spectroscopy
Wastes
Water Pollutants, Chemical - analysis
Water Purification - methods
water treatment
Water treatment and pollution
title Fate of coagulant species and conformational effects during the aggregation of a model of a humic substance with Al13 polycations
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