Sorption of Zn(II), Pb(II), and Co(II) using natural sorbents: Equilibrium and kinetic studies

Natural Jordanian sorbent (consisting of primary minerals, i.e., quartz and aluminosilicates and secondary minerals, i.e., calcite and dolomite) was shown to be effective for removing Zn(II), Pb(II) and Co(II) from aqueous solution. The major mineral constitutions of the sorbent are calcite and quar...

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Veröffentlicht in:Water research (Oxford) 2006-08, Vol.40 (14), p.2645-2658
Hauptverfasser: Al-Degs, Yahya S., El-Barghouthi, Musa I., Issa, Ayman A., Khraisheh, Majeda A., Walker, Gavin M.
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container_title Water research (Oxford)
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creator Al-Degs, Yahya S.
El-Barghouthi, Musa I.
Issa, Ayman A.
Khraisheh, Majeda A.
Walker, Gavin M.
description Natural Jordanian sorbent (consisting of primary minerals, i.e., quartz and aluminosilicates and secondary minerals, i.e., calcite and dolomite) was shown to be effective for removing Zn(II), Pb(II) and Co(II) from aqueous solution. The major mineral constitutions of the sorbent are calcite and quartz. Dolomite was present as minor mineral and palygorskite was present as trace mineral. The sorbent has microporous structure with a modest surface area of 14.4 m 2 g −1. pH zpc (pH of zero point charge) of the sorbent was estimated by alkaline–titration methods and a value of 9.5 was obtained. The sorption capacities of the metals were: 2.860, 0.320, 0.076 mmol cation g −1 for Zn(II), Pb(II) and Co(II) at pH 6.5, 4.5 and 7.0, respectively. The shape of the experimental isotherm of Zn(II) was of a “L2” type, while that of Pb(II) and Co(II) was of a “L1” type according to Giles classification for isotherms. Sorption data of metals were described by Langmuir and Freundlich models over the entire concentration range. It was found that the mechanism of metal sorption was mainly due to precipitation of metal carbonate complexes. The overall sorption capacity decreased after acid treatment, as this decreased the extent of precipitation on calcite and dolomite. The effect of Zn(II) ions concentration on sorption kinetics was investigated. Kinetic data were accurately fitted to pseudo-first order and external diffusion models which indicated that sorption of Zn(II) occurred on the exterior surface of the sorbent and the contribution of internal diffusion mechanism was insignificant. Furthermore, the sorption rate of Zn(II) was found to be slow, where only 10–20% of the maximum capacity was utilized in the first 30 min of interaction.
doi_str_mv 10.1016/j.watres.2006.05.018
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The major mineral constitutions of the sorbent are calcite and quartz. Dolomite was present as minor mineral and palygorskite was present as trace mineral. The sorbent has microporous structure with a modest surface area of 14.4 m 2 g −1. pH zpc (pH of zero point charge) of the sorbent was estimated by alkaline–titration methods and a value of 9.5 was obtained. The sorption capacities of the metals were: 2.860, 0.320, 0.076 mmol cation g −1 for Zn(II), Pb(II) and Co(II) at pH 6.5, 4.5 and 7.0, respectively. The shape of the experimental isotherm of Zn(II) was of a “L2” type, while that of Pb(II) and Co(II) was of a “L1” type according to Giles classification for isotherms. Sorption data of metals were described by Langmuir and Freundlich models over the entire concentration range. It was found that the mechanism of metal sorption was mainly due to precipitation of metal carbonate complexes. The overall sorption capacity decreased after acid treatment, as this decreased the extent of precipitation on calcite and dolomite. The effect of Zn(II) ions concentration on sorption kinetics was investigated. Kinetic data were accurately fitted to pseudo-first order and external diffusion models which indicated that sorption of Zn(II) occurred on the exterior surface of the sorbent and the contribution of internal diffusion mechanism was insignificant. 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The major mineral constitutions of the sorbent are calcite and quartz. Dolomite was present as minor mineral and palygorskite was present as trace mineral. The sorbent has microporous structure with a modest surface area of 14.4 m 2 g −1. pH zpc (pH of zero point charge) of the sorbent was estimated by alkaline–titration methods and a value of 9.5 was obtained. The sorption capacities of the metals were: 2.860, 0.320, 0.076 mmol cation g −1 for Zn(II), Pb(II) and Co(II) at pH 6.5, 4.5 and 7.0, respectively. The shape of the experimental isotherm of Zn(II) was of a “L2” type, while that of Pb(II) and Co(II) was of a “L1” type according to Giles classification for isotherms. Sorption data of metals were described by Langmuir and Freundlich models over the entire concentration range. It was found that the mechanism of metal sorption was mainly due to precipitation of metal carbonate complexes. The overall sorption capacity decreased after acid treatment, as this decreased the extent of precipitation on calcite and dolomite. The effect of Zn(II) ions concentration on sorption kinetics was investigated. Kinetic data were accurately fitted to pseudo-first order and external diffusion models which indicated that sorption of Zn(II) occurred on the exterior surface of the sorbent and the contribution of internal diffusion mechanism was insignificant. 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Sewage sludge</subject><subject>palygorskite</subject><subject>Pollution</subject><subject>pollution control</subject><subject>porosity</subject><subject>quartz</subject><subject>Solubility</subject><subject>sorption</subject><subject>sorption capacity</subject><subject>sorption isotherms</subject><subject>sorption rate</subject><subject>Spectrophotometry, Infrared</subject><subject>Thermodynamics</subject><subject>Waste Disposal, Fluid</subject><subject>Wastes</subject><subject>Water Pollutants, Chemical - chemistry</subject><subject>Water Pollutants, Chemical - isolation &amp; purification</subject><subject>water pollution</subject><subject>Water treatment and pollution</subject><subject>X-Ray Diffraction</subject><subject>zinc</subject><subject>Zinc - chemistry</subject><subject>Zinc - isolation &amp; purification</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>eNqF0d9rFDEQB_Agir1W_wPRfWlRcNfJz018EOSoelBQqH3xwZBNsiXnXnJNdhX_e_fcg77p00zgM0OYL0LPMDQYsHizbX6ZMfvSEADRAG8AywdohWWrasKYfIhWAIzWmHJ2gk5L2QIAIVQ9RidYSKq4JCv0_Trl_RhSrFJffYsvN5tXr6sv3VJNdNU6HfpqKiHeVtGMUzZDVVLufBzL2-rybgpD6HKYdn_5jxD9GGxVxskFX56gR70Zin96rGfo5sPl1_Wn-urzx836_VVtOSNjLSkhQHphPLZScSUVAwrWSCq4Mlji1tFOOCdEz1vSza-29dQ757xxVCp6hi6Wvfuc7iZfRr0LxfphMNGnqWgCHHPWwn8hZq2kVJAZsgXanErJvtf7HHYm_9YY9CEAvdVLAPoQgAau5wDmsefH_VO38-5-6HjxGZwfgSnWDH020YZy71qlMFMH92JxvUna3ObZ3FwTwBQwzIsEm8W7Rfj5sD-Dz7rY4KP1LmRvR-1S-Pdf_wCaiKyB</recordid><startdate>20060801</startdate><enddate>20060801</enddate><creator>Al-Degs, Yahya S.</creator><creator>El-Barghouthi, Musa I.</creator><creator>Issa, Ayman A.</creator><creator>Khraisheh, Majeda A.</creator><creator>Walker, Gavin M.</creator><general>Elsevier Ltd</general><general>Elsevier Science</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>7ST</scope><scope>C1K</scope><scope>SOI</scope><scope>7QH</scope><scope>7UA</scope><scope>F1W</scope><scope>H96</scope><scope>L.G</scope></search><sort><creationdate>20060801</creationdate><title>Sorption of Zn(II), Pb(II), and Co(II) using natural sorbents: Equilibrium and kinetic studies</title><author>Al-Degs, Yahya S. ; El-Barghouthi, Musa I. ; Issa, Ayman A. ; Khraisheh, Majeda A. ; Walker, Gavin M.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c542t-832202f6ae1c8959894030ca83659a1817d3b6dd66f572b7d377e3edddead3893</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2006</creationdate><topic>acid treatment</topic><topic>adsorbents</topic><topic>Adsorption</topic><topic>Applied sciences</topic><topic>Biological Products - chemistry</topic><topic>Calcite</topic><topic>Calcium Carbonate - chemistry</topic><topic>chemical concentration</topic><topic>chemical precipitation</topic><topic>Clay minerals</topic><topic>cobalt</topic><topic>Cobalt - chemistry</topic><topic>Cobalt - isolation &amp; purification</topic><topic>diffusion</topic><topic>dolomite</topic><topic>Exact sciences and technology</topic><topic>Heavy metals</topic><topic>Hydrogen-Ion Concentration</topic><topic>Kinetics</topic><topic>lead</topic><topic>Lead - chemistry</topic><topic>Lead - isolation &amp; purification</topic><topic>mathematical models</topic><topic>metal ions</topic><topic>Natural adsorbent</topic><topic>Nitrogen - chemistry</topic><topic>Osmolar Concentration</topic><topic>Other industrial wastes. Sewage sludge</topic><topic>palygorskite</topic><topic>Pollution</topic><topic>pollution control</topic><topic>porosity</topic><topic>quartz</topic><topic>Solubility</topic><topic>sorption</topic><topic>sorption capacity</topic><topic>sorption isotherms</topic><topic>sorption rate</topic><topic>Spectrophotometry, Infrared</topic><topic>Thermodynamics</topic><topic>Waste Disposal, Fluid</topic><topic>Wastes</topic><topic>Water Pollutants, Chemical - chemistry</topic><topic>Water Pollutants, Chemical - isolation &amp; purification</topic><topic>water pollution</topic><topic>Water treatment and pollution</topic><topic>X-Ray Diffraction</topic><topic>zinc</topic><topic>Zinc - chemistry</topic><topic>Zinc - isolation &amp; purification</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Al-Degs, Yahya S.</creatorcontrib><creatorcontrib>El-Barghouthi, Musa I.</creatorcontrib><creatorcontrib>Issa, Ayman A.</creatorcontrib><creatorcontrib>Khraisheh, Majeda A.</creatorcontrib><creatorcontrib>Walker, Gavin M.</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>Environment Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Environment Abstracts</collection><collection>Aqualine</collection><collection>Water Resources Abstracts</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science &amp; Fisheries Abstracts (ASFA) 2: Ocean Technology, Policy &amp; Non-Living Resources</collection><collection>Aquatic Science &amp; Fisheries Abstracts (ASFA) Professional</collection><jtitle>Water research (Oxford)</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Al-Degs, Yahya S.</au><au>El-Barghouthi, Musa I.</au><au>Issa, Ayman A.</au><au>Khraisheh, Majeda A.</au><au>Walker, Gavin M.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Sorption of Zn(II), Pb(II), and Co(II) using natural sorbents: Equilibrium and kinetic studies</atitle><jtitle>Water research (Oxford)</jtitle><addtitle>Water Res</addtitle><date>2006-08-01</date><risdate>2006</risdate><volume>40</volume><issue>14</issue><spage>2645</spage><epage>2658</epage><pages>2645-2658</pages><issn>0043-1354</issn><eissn>1879-2448</eissn><coden>WATRAG</coden><abstract>Natural Jordanian sorbent (consisting of primary minerals, i.e., quartz and aluminosilicates and secondary minerals, i.e., calcite and dolomite) was shown to be effective for removing Zn(II), Pb(II) and Co(II) from aqueous solution. The major mineral constitutions of the sorbent are calcite and quartz. Dolomite was present as minor mineral and palygorskite was present as trace mineral. The sorbent has microporous structure with a modest surface area of 14.4 m 2 g −1. pH zpc (pH of zero point charge) of the sorbent was estimated by alkaline–titration methods and a value of 9.5 was obtained. The sorption capacities of the metals were: 2.860, 0.320, 0.076 mmol cation g −1 for Zn(II), Pb(II) and Co(II) at pH 6.5, 4.5 and 7.0, respectively. The shape of the experimental isotherm of Zn(II) was of a “L2” type, while that of Pb(II) and Co(II) was of a “L1” type according to Giles classification for isotherms. Sorption data of metals were described by Langmuir and Freundlich models over the entire concentration range. It was found that the mechanism of metal sorption was mainly due to precipitation of metal carbonate complexes. The overall sorption capacity decreased after acid treatment, as this decreased the extent of precipitation on calcite and dolomite. The effect of Zn(II) ions concentration on sorption kinetics was investigated. Kinetic data were accurately fitted to pseudo-first order and external diffusion models which indicated that sorption of Zn(II) occurred on the exterior surface of the sorbent and the contribution of internal diffusion mechanism was insignificant. Furthermore, the sorption rate of Zn(II) was found to be slow, where only 10–20% of the maximum capacity was utilized in the first 30 min of interaction.</abstract><cop>Oxford</cop><pub>Elsevier Ltd</pub><pmid>16839582</pmid><doi>10.1016/j.watres.2006.05.018</doi><tpages>14</tpages></addata></record>
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source MEDLINE; Elsevier ScienceDirect Journals
subjects acid treatment
adsorbents
Adsorption
Applied sciences
Biological Products - chemistry
Calcite
Calcium Carbonate - chemistry
chemical concentration
chemical precipitation
Clay minerals
cobalt
Cobalt - chemistry
Cobalt - isolation & purification
diffusion
dolomite
Exact sciences and technology
Heavy metals
Hydrogen-Ion Concentration
Kinetics
lead
Lead - chemistry
Lead - isolation & purification
mathematical models
metal ions
Natural adsorbent
Nitrogen - chemistry
Osmolar Concentration
Other industrial wastes. Sewage sludge
palygorskite
Pollution
pollution control
porosity
quartz
Solubility
sorption
sorption capacity
sorption isotherms
sorption rate
Spectrophotometry, Infrared
Thermodynamics
Waste Disposal, Fluid
Wastes
Water Pollutants, Chemical - chemistry
Water Pollutants, Chemical - isolation & purification
water pollution
Water treatment and pollution
X-Ray Diffraction
zinc
Zinc - chemistry
Zinc - isolation & purification
title Sorption of Zn(II), Pb(II), and Co(II) using natural sorbents: Equilibrium and kinetic studies
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