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Speciation of inorganic chromium in river water by graphite furnace-atomic absorption spectrometry after chromabond NH2 column based solid phase extraction
Chromium (Cr) can be either essential or carcinogenic depending on the chemical form. The aim of this study was to speciate Cr in water samples, collected from Blood and Mokolo Rivers, Limpopo Province. Water samples were collected from ten sampling sites from each river. The accuracy of the method...
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Published in: | International journal of environmental analytical chemistry 2022-12, Vol.102 (16), p.4042-4057 |
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creator | Mokgohloa, Conny P. Thomas, Mary S. Mokgalaka, Ntebogeng S. Ambushe, Abayneh A. |
description | Chromium (Cr) can be either essential or carcinogenic depending on the chemical form. The aim of this study was to speciate Cr in water samples, collected from Blood and Mokolo Rivers, Limpopo Province. Water samples were collected from ten sampling sites from each river. The accuracy of the method was evaluated by employing standard reference material of trace elements in water (SRM 1643 f) before sample analysis. Total Cr and Cr(VI) in water samples were quantified using graphite furnace-atomic absorption spectrometry (GF-AAS). The concentrations of Cr in water samples collected from Blood and Mokolo Rivers were found in the range of 1.56 μg/L to 6.11 μg/L and 1.34 µg/L to 3.53 µg/L, respectively. A solid phase extraction (SPE) method based on chromabond NH
2
column was used to determine Cr(VI) in water. In order to achieve separation of Cr(VI), the sample was pre-concentrated and passed through a conditioned chromabond NH
2
column at a flow rate of 3 mL/min. Hexavalent Cr was selectively adsorbed onto the column and the contents were dried under vacuum. The retained Cr(VI) was subsequently eluted with two column volumes of 2 M HNO
3
and diluted to a final volume of 10.0 mL. The limit of detection (LOD) was 0.105 µg/L and the percentage relative standard deviations were less than 10%. The validation of the procedure was performed by spiking standard solutions containing Cr(III) and Cr(VI) and the percentage recoveries were higher than 88%. The concentrations of Cr(VI) in Blood and Mokolo Rivers ranged from 0.13 µg/L to 1.99 µg/L and 0.13 µg/L to 0.55 µg/L, respectively. In Blood and Mokolo Rivers, although the concentrations of Cr(VI) are low, their values suggest a link with the industrial and agricultural activities in the area. |
doi_str_mv | 10.1080/03067319.2020.1779243 |
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2
column was used to determine Cr(VI) in water. In order to achieve separation of Cr(VI), the sample was pre-concentrated and passed through a conditioned chromabond NH
2
column at a flow rate of 3 mL/min. Hexavalent Cr was selectively adsorbed onto the column and the contents were dried under vacuum. The retained Cr(VI) was subsequently eluted with two column volumes of 2 M HNO
3
and diluted to a final volume of 10.0 mL. The limit of detection (LOD) was 0.105 µg/L and the percentage relative standard deviations were less than 10%. The validation of the procedure was performed by spiking standard solutions containing Cr(III) and Cr(VI) and the percentage recoveries were higher than 88%. The concentrations of Cr(VI) in Blood and Mokolo Rivers ranged from 0.13 µg/L to 1.99 µg/L and 0.13 µg/L to 0.55 µg/L, respectively. In Blood and Mokolo Rivers, although the concentrations of Cr(VI) are low, their values suggest a link with the industrial and agricultural activities in the area.</description><identifier>ISSN: 0306-7319</identifier><identifier>EISSN: 1029-0397</identifier><identifier>DOI: 10.1080/03067319.2020.1779243</identifier><language>eng</language><publisher>Abingdon: Taylor & Francis</publisher><subject>Absorption ; Absorption spectroscopy ; Analytical methods ; Atomic absorption analysis ; Atomic absorption spectroscopy ; Blood ; Carcinogens ; Chromium ; Flow velocity ; Graphite ; River water ; Rivers ; Scientific imaging ; solid phase extraction ; Solid phases ; Speciation ; Spectral analysis ; Spectrometry ; Trace elements ; water ; Water analysis ; Water sampling</subject><ispartof>International journal of environmental analytical chemistry, 2022-12, Vol.102 (16), p.4042-4057</ispartof><rights>2020 Informa UK Limited, trading as Taylor & Francis Group 2020</rights><rights>2020 Informa UK Limited, trading as Taylor & Francis Group</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,27924,27925</link.rule.ids></links><search><creatorcontrib>Mokgohloa, Conny P.</creatorcontrib><creatorcontrib>Thomas, Mary S.</creatorcontrib><creatorcontrib>Mokgalaka, Ntebogeng S.</creatorcontrib><creatorcontrib>Ambushe, Abayneh A.</creatorcontrib><title>Speciation of inorganic chromium in river water by graphite furnace-atomic absorption spectrometry after chromabond NH2 column based solid phase extraction</title><title>International journal of environmental analytical chemistry</title><description>Chromium (Cr) can be either essential or carcinogenic depending on the chemical form. The aim of this study was to speciate Cr in water samples, collected from Blood and Mokolo Rivers, Limpopo Province. Water samples were collected from ten sampling sites from each river. The accuracy of the method was evaluated by employing standard reference material of trace elements in water (SRM 1643 f) before sample analysis. Total Cr and Cr(VI) in water samples were quantified using graphite furnace-atomic absorption spectrometry (GF-AAS). The concentrations of Cr in water samples collected from Blood and Mokolo Rivers were found in the range of 1.56 μg/L to 6.11 μg/L and 1.34 µg/L to 3.53 µg/L, respectively. A solid phase extraction (SPE) method based on chromabond NH
2
column was used to determine Cr(VI) in water. In order to achieve separation of Cr(VI), the sample was pre-concentrated and passed through a conditioned chromabond NH
2
column at a flow rate of 3 mL/min. Hexavalent Cr was selectively adsorbed onto the column and the contents were dried under vacuum. The retained Cr(VI) was subsequently eluted with two column volumes of 2 M HNO
3
and diluted to a final volume of 10.0 mL. The limit of detection (LOD) was 0.105 µg/L and the percentage relative standard deviations were less than 10%. The validation of the procedure was performed by spiking standard solutions containing Cr(III) and Cr(VI) and the percentage recoveries were higher than 88%. The concentrations of Cr(VI) in Blood and Mokolo Rivers ranged from 0.13 µg/L to 1.99 µg/L and 0.13 µg/L to 0.55 µg/L, respectively. In Blood and Mokolo Rivers, although the concentrations of Cr(VI) are low, their values suggest a link with the industrial and agricultural activities in the area.</description><subject>Absorption</subject><subject>Absorption spectroscopy</subject><subject>Analytical methods</subject><subject>Atomic absorption analysis</subject><subject>Atomic absorption spectroscopy</subject><subject>Blood</subject><subject>Carcinogens</subject><subject>Chromium</subject><subject>Flow velocity</subject><subject>Graphite</subject><subject>River water</subject><subject>Rivers</subject><subject>Scientific imaging</subject><subject>solid phase extraction</subject><subject>Solid phases</subject><subject>Speciation</subject><subject>Spectral analysis</subject><subject>Spectrometry</subject><subject>Trace elements</subject><subject>water</subject><subject>Water analysis</subject><subject>Water sampling</subject><issn>0306-7319</issn><issn>1029-0397</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2022</creationdate><recordtype>article</recordtype><recordid>eNo1kVFLwzAQx4MoOKcfQQj43Jk07dK-KUOdMPRBfS7Xa7JldE1NMuc-i1_WdNOXHDl-94O7PyHXnE04K9gtE2wqBS8nKUtjS8oyzcQJGXGWlgkTpTwlo4FJBuicXHi_ZoyLvBAj8vPWKzQQjO2o1dR01i2hM0hx5ezGbDexRZ35Uo7uIMS33tOlg35lgqJ66zpAlUCIKFKovXX9QeWjNUSBCm5PQQ-DByHUtmvoyzylaNvtpqM1eNVQb1vT0H4VP1R9Bwc4WC7JmYbWq6u_OiYfjw_vs3myeH16nt0vEsPzPCSIdSkQC6xFIXlZZ3wquSy04HmmESQ0vMZpJlLNebyQagTG3QsusIBSNrkYk5ujt3f2c6t8qNZ22Kz1VSozJmVeFmmk7o6U6bR1G9hZ1zZVgH1rnXbQofGV4KwaIqn-I6mGSKq_SMQvoq-C3Q</recordid><startdate>20221216</startdate><enddate>20221216</enddate><creator>Mokgohloa, Conny P.</creator><creator>Thomas, Mary S.</creator><creator>Mokgalaka, Ntebogeng S.</creator><creator>Ambushe, Abayneh A.</creator><general>Taylor & Francis</general><general>Taylor & Francis LLC</general><scope>7QH</scope><scope>7SN</scope><scope>7ST</scope><scope>7TN</scope><scope>7U7</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope><scope>SOI</scope></search><sort><creationdate>20221216</creationdate><title>Speciation of inorganic chromium in river water by graphite furnace-atomic absorption spectrometry after chromabond NH2 column based solid phase extraction</title><author>Mokgohloa, Conny P. ; Thomas, Mary S. ; Mokgalaka, Ntebogeng S. ; Ambushe, Abayneh A.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-i155t-ccb93cc8cb38719b4167178f3154fca7ad1bc6432f11202ed3c358813c8a97d53</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2022</creationdate><topic>Absorption</topic><topic>Absorption spectroscopy</topic><topic>Analytical methods</topic><topic>Atomic absorption analysis</topic><topic>Atomic absorption spectroscopy</topic><topic>Blood</topic><topic>Carcinogens</topic><topic>Chromium</topic><topic>Flow velocity</topic><topic>Graphite</topic><topic>River water</topic><topic>Rivers</topic><topic>Scientific imaging</topic><topic>solid phase extraction</topic><topic>Solid phases</topic><topic>Speciation</topic><topic>Spectral analysis</topic><topic>Spectrometry</topic><topic>Trace elements</topic><topic>water</topic><topic>Water analysis</topic><topic>Water sampling</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Mokgohloa, Conny P.</creatorcontrib><creatorcontrib>Thomas, Mary S.</creatorcontrib><creatorcontrib>Mokgalaka, Ntebogeng S.</creatorcontrib><creatorcontrib>Ambushe, Abayneh A.</creatorcontrib><collection>Aqualine</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>Oceanic Abstracts</collection><collection>Toxicology Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Environment Abstracts</collection><jtitle>International journal of environmental analytical chemistry</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Mokgohloa, Conny P.</au><au>Thomas, Mary S.</au><au>Mokgalaka, Ntebogeng S.</au><au>Ambushe, Abayneh A.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Speciation of inorganic chromium in river water by graphite furnace-atomic absorption spectrometry after chromabond NH2 column based solid phase extraction</atitle><jtitle>International journal of environmental analytical chemistry</jtitle><date>2022-12-16</date><risdate>2022</risdate><volume>102</volume><issue>16</issue><spage>4042</spage><epage>4057</epage><pages>4042-4057</pages><issn>0306-7319</issn><eissn>1029-0397</eissn><abstract>Chromium (Cr) can be either essential or carcinogenic depending on the chemical form. The aim of this study was to speciate Cr in water samples, collected from Blood and Mokolo Rivers, Limpopo Province. Water samples were collected from ten sampling sites from each river. The accuracy of the method was evaluated by employing standard reference material of trace elements in water (SRM 1643 f) before sample analysis. Total Cr and Cr(VI) in water samples were quantified using graphite furnace-atomic absorption spectrometry (GF-AAS). The concentrations of Cr in water samples collected from Blood and Mokolo Rivers were found in the range of 1.56 μg/L to 6.11 μg/L and 1.34 µg/L to 3.53 µg/L, respectively. A solid phase extraction (SPE) method based on chromabond NH
2
column was used to determine Cr(VI) in water. In order to achieve separation of Cr(VI), the sample was pre-concentrated and passed through a conditioned chromabond NH
2
column at a flow rate of 3 mL/min. Hexavalent Cr was selectively adsorbed onto the column and the contents were dried under vacuum. The retained Cr(VI) was subsequently eluted with two column volumes of 2 M HNO
3
and diluted to a final volume of 10.0 mL. The limit of detection (LOD) was 0.105 µg/L and the percentage relative standard deviations were less than 10%. The validation of the procedure was performed by spiking standard solutions containing Cr(III) and Cr(VI) and the percentage recoveries were higher than 88%. The concentrations of Cr(VI) in Blood and Mokolo Rivers ranged from 0.13 µg/L to 1.99 µg/L and 0.13 µg/L to 0.55 µg/L, respectively. In Blood and Mokolo Rivers, although the concentrations of Cr(VI) are low, their values suggest a link with the industrial and agricultural activities in the area.</abstract><cop>Abingdon</cop><pub>Taylor & Francis</pub><doi>10.1080/03067319.2020.1779243</doi><tpages>16</tpages></addata></record> |
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subjects | Absorption Absorption spectroscopy Analytical methods Atomic absorption analysis Atomic absorption spectroscopy Blood Carcinogens Chromium Flow velocity Graphite River water Rivers Scientific imaging solid phase extraction Solid phases Speciation Spectral analysis Spectrometry Trace elements water Water analysis Water sampling |
title | Speciation of inorganic chromium in river water by graphite furnace-atomic absorption spectrometry after chromabond NH2 column based solid phase extraction |
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