Evaluation of the Bioavailability and Translocation of Selected Heavy Metals by Brassica juncea and Spinacea oleracea L for a South African Power Utility Coal Fly Ash

This study evaluated the physicochemical and mineralogical properties, mobile chemical species bioavailability and translocation in and L. plants of a South African coal-fired power utility. Coal-fly-ash (CFA) disposal is associated with various environmental and health risks, including air, soil, s...

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Veröffentlicht in:International journal of environmental research and public health 2018-12, Vol.15 (12), p.2841
Hauptverfasser: Mashau, Aluwani Shiridor, Gitari, Mugera Wilson, Akinyemi, Segun Ajayi
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Gitari, Mugera Wilson
Akinyemi, Segun Ajayi
description This study evaluated the physicochemical and mineralogical properties, mobile chemical species bioavailability and translocation in and L. plants of a South African coal-fired power utility. Coal-fly-ash (CFA) disposal is associated with various environmental and health risks, including air, soil, surface, and groundwater pollution due to the leaching of toxic heavy metals; these ends up in food webs affecting human health, while repeated inhalation causes bronchitis, silicosis, hair loss, and lung cancer. The morphology and chemical and mineralogical composition of CFA were determined using Scanning Electron Microscopy (SEM), X-ray fluorescence (XRF), and X-ray diffraction, respectively. In pot-culture experiments, L. and plants were grown in three sets of pots containing CFA (Set 1), soil (Set 2), and a mixture of CFA plus soil at a ratio of 1:1 (50% CFA: 50% soil, Set 3), while no plants were grown in Set 4 as a control for the leachate samples. SEM showed that the surface morphology of CFA has a lower degree of sphericity with the irregular agglomerations of many particles. XRF results revealed that CFA contains 43.65%, 22.68%, and 10.89% of SiO₂, Al₂O and Fe₂O respectively, which indicates that CFA is an aluminosilicate material. X-ray diffraction (XRD) showed that CFA contains mullite as a major phase, followed by quartz mineral phases. Chemical species such as B, Ba, Mo, and Cr were occurring at higher concentrations in the leachates for most weeks in the pot-culture experiments, especially for CFA and soil + CFA growth media. However, there was a common trend for all growth media of chemical-species concentrations declining with time, which might have been caused by plant uptake or wash-off with water during irrigation; even for the growth media as well, where no plants were grown. Chemical species, such as Fe, Mn, B, Ba, and Zn, accumulated highly in most parts of the plant species. However, showed higher potential to accumulate chemical species as compared to L. Bioconcentration and translocation factors (BF and TF) showed that was the most effective in terms of bioconcentration and translocation of most of the chemical species. This indicates that has potential in application for the phytoremediation of CFA dumps, and could contribute to the remediation of CFA dumps and the reduction of potential health and environmental impact associated with CFA.
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Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (http://creativecommons.org/licenses/by/4.0/). 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Coal-fly-ash (CFA) disposal is associated with various environmental and health risks, including air, soil, surface, and groundwater pollution due to the leaching of toxic heavy metals; these ends up in food webs affecting human health, while repeated inhalation causes bronchitis, silicosis, hair loss, and lung cancer. The morphology and chemical and mineralogical composition of CFA were determined using Scanning Electron Microscopy (SEM), X-ray fluorescence (XRF), and X-ray diffraction, respectively. In pot-culture experiments, L. and plants were grown in three sets of pots containing CFA (Set 1), soil (Set 2), and a mixture of CFA plus soil at a ratio of 1:1 (50% CFA: 50% soil, Set 3), while no plants were grown in Set 4 as a control for the leachate samples. SEM showed that the surface morphology of CFA has a lower degree of sphericity with the irregular agglomerations of many particles. 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Bioconcentration and translocation factors (BF and TF) showed that was the most effective in terms of bioconcentration and translocation of most of the chemical species. This indicates that has potential in application for the phytoremediation of CFA dumps, and could contribute to the remediation of CFA dumps and the reduction of potential health and environmental impact associated with CFA.</description><subject>Aluminosilicates</subject><subject>Aluminum oxide</subject><subject>Aluminum silicates</subject><subject>Bioaccumulation</subject><subject>Bioavailability</subject><subject>Biodegradation, Environmental</subject><subject>Biological Availability</subject><subject>Biological magnification</subject><subject>Biological Transport</subject><subject>Biomass</subject><subject>Brassica juncea</subject><subject>Bronchitis</subject><subject>Chemical composition</subject><subject>Chemical speciation</subject><subject>Chlorophyll</subject><subject>Chromium</subject><subject>Coal</subject><subject>Coal Ash - chemistry</subject><subject>Coal Ash - metabolism</subject><subject>Coal-fired power plants</subject><subject>Culture</subject><subject>Culture media</subject><subject>Environmental health</subject><subject>Environmental Pollutants - chemistry</subject><subject>Environmental Pollutants - metabolism</subject><subject>Experiments</subject><subject>Ferric oxide</subject><subject>Flowers &amp; plants</subject><subject>Fluorescence</subject><subject>Fly ash</subject><subject>Food contamination &amp; poisoning</subject><subject>Food webs</subject><subject>Groundwater pollution</subject><subject>Growth media</subject><subject>Harvest</subject><subject>Health risks</subject><subject>Heavy metals</subject><subject>Industrial plant emissions</subject><subject>Inhalation</subject><subject>Irrigation water</subject><subject>Leachates</subject><subject>Leaching</subject><subject>Lung cancer</subject><subject>Manganese</subject><subject>Metals, Heavy - metabolism</subject><subject>Molybdenum</subject><subject>Morphology</subject><subject>Mullite</subject><subject>Mustard Plant - metabolism</subject><subject>Phytoremediation</subject><subject>Power Plants</subject><subject>Respiration</subject><subject>Scanning electron microscopy</subject><subject>Sediment pollution</subject><subject>Seeds</subject><subject>Silicon dioxide</subject><subject>Silicosis</subject><subject>Soil - chemistry</subject><subject>Soil contamination</subject><subject>Soil pollution</subject><subject>Soils</subject><subject>South Africa</subject><subject>Spinacia oleracea - metabolism</subject><subject>Translocation</subject><subject>X-ray diffraction</subject><issn>1660-4601</issn><issn>1661-7827</issn><issn>1660-4601</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2018</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><recordid>eNpdkk1vEzEQhlcIREvhyhFZ4tJLij_WXueClEYtRQoCKe3ZmvXOso4cO9i7QfuH-J1smxK1nGZGft53ZuQpiveMXggxp5_cBtOuY5Jxrkv2ojhlStFZqSh7-SQ_Kd7kvKFU6FLNXxcngkrJpJ6fFn-u9uAH6F0MJLak75Bcugh7cB5q510_EggNuU0Qso_2CK7Ro-2xITcI-5F8wx58JvVILhPk7CyQzRAswoN6vXMB7ovoMT0kK9LGRICs49B3ZNGmSRHIj_gbE7nrD32XETy59iNZ5O5t8aqdGuC7x3hW3F1f3S5vZqvvX74uF6uZLZnuZ7apq9LWWmigmlpZVWWppNSNanXdYEVrWclS1MCUbBhUHBVXVggoG-RYgzgrPh98d0O9xcZi6BN4s0tuC2k0EZx5_hJcZ37GvVGCiclrMjh_NEjx14C5N1uXLXoPAeOQDWeyUorPq2pCP_6HbuKQwrSe4VJzTRXjeqIuDpRNMeeE7XEYRs39CZjnJzAJPjxd4Yj_-3PxF8SOsCI</recordid><startdate>20181213</startdate><enddate>20181213</enddate><creator>Mashau, Aluwani Shiridor</creator><creator>Gitari, Mugera Wilson</creator><creator>Akinyemi, Segun Ajayi</creator><general>MDPI AG</general><general>MDPI</general><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>7X7</scope><scope>7XB</scope><scope>88E</scope><scope>8C1</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FYUFA</scope><scope>GHDGH</scope><scope>K9.</scope><scope>M0S</scope><scope>M1P</scope><scope>PIMPY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PRINS</scope><scope>7X8</scope><scope>5PM</scope><orcidid>https://orcid.org/0000-0002-4286-6318</orcidid><orcidid>https://orcid.org/0000-0001-6363-3698</orcidid><orcidid>https://orcid.org/0000-0002-6387-0682</orcidid></search><sort><creationdate>20181213</creationdate><title>Evaluation of the Bioavailability and Translocation of Selected Heavy Metals by Brassica juncea and Spinacea oleracea L for a South African Power Utility Coal Fly Ash</title><author>Mashau, Aluwani Shiridor ; Gitari, Mugera Wilson ; Akinyemi, Segun Ajayi</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c418t-cdb74cb838a080c577446558d6f8bde70b57543ba165d1a72e626c33a4de2eba3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2018</creationdate><topic>Aluminosilicates</topic><topic>Aluminum oxide</topic><topic>Aluminum silicates</topic><topic>Bioaccumulation</topic><topic>Bioavailability</topic><topic>Biodegradation, Environmental</topic><topic>Biological Availability</topic><topic>Biological magnification</topic><topic>Biological Transport</topic><topic>Biomass</topic><topic>Brassica juncea</topic><topic>Bronchitis</topic><topic>Chemical composition</topic><topic>Chemical speciation</topic><topic>Chlorophyll</topic><topic>Chromium</topic><topic>Coal</topic><topic>Coal Ash - chemistry</topic><topic>Coal Ash - metabolism</topic><topic>Coal-fired power plants</topic><topic>Culture</topic><topic>Culture media</topic><topic>Environmental health</topic><topic>Environmental Pollutants - chemistry</topic><topic>Environmental Pollutants - metabolism</topic><topic>Experiments</topic><topic>Ferric oxide</topic><topic>Flowers &amp; 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Coal-fly-ash (CFA) disposal is associated with various environmental and health risks, including air, soil, surface, and groundwater pollution due to the leaching of toxic heavy metals; these ends up in food webs affecting human health, while repeated inhalation causes bronchitis, silicosis, hair loss, and lung cancer. The morphology and chemical and mineralogical composition of CFA were determined using Scanning Electron Microscopy (SEM), X-ray fluorescence (XRF), and X-ray diffraction, respectively. In pot-culture experiments, L. and plants were grown in three sets of pots containing CFA (Set 1), soil (Set 2), and a mixture of CFA plus soil at a ratio of 1:1 (50% CFA: 50% soil, Set 3), while no plants were grown in Set 4 as a control for the leachate samples. SEM showed that the surface morphology of CFA has a lower degree of sphericity with the irregular agglomerations of many particles. XRF results revealed that CFA contains 43.65%, 22.68%, and 10.89% of SiO₂, Al₂O and Fe₂O respectively, which indicates that CFA is an aluminosilicate material. X-ray diffraction (XRD) showed that CFA contains mullite as a major phase, followed by quartz mineral phases. Chemical species such as B, Ba, Mo, and Cr were occurring at higher concentrations in the leachates for most weeks in the pot-culture experiments, especially for CFA and soil + CFA growth media. However, there was a common trend for all growth media of chemical-species concentrations declining with time, which might have been caused by plant uptake or wash-off with water during irrigation; even for the growth media as well, where no plants were grown. Chemical species, such as Fe, Mn, B, Ba, and Zn, accumulated highly in most parts of the plant species. However, showed higher potential to accumulate chemical species as compared to L. Bioconcentration and translocation factors (BF and TF) showed that was the most effective in terms of bioconcentration and translocation of most of the chemical species. This indicates that has potential in application for the phytoremediation of CFA dumps, and could contribute to the remediation of CFA dumps and the reduction of potential health and environmental impact associated with CFA.</abstract><cop>Switzerland</cop><pub>MDPI AG</pub><pmid>30551589</pmid><doi>10.3390/ijerph15122841</doi><orcidid>https://orcid.org/0000-0002-4286-6318</orcidid><orcidid>https://orcid.org/0000-0001-6363-3698</orcidid><orcidid>https://orcid.org/0000-0002-6387-0682</orcidid><oa>free_for_read</oa></addata></record>
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source MDPI - Multidisciplinary Digital Publishing Institute; MEDLINE; PubMed Central; Free Full-Text Journals in Chemistry; EZB Electronic Journals Library; PubMed Central Open Access
subjects Aluminosilicates
Aluminum oxide
Aluminum silicates
Bioaccumulation
Bioavailability
Biodegradation, Environmental
Biological Availability
Biological magnification
Biological Transport
Biomass
Brassica juncea
Bronchitis
Chemical composition
Chemical speciation
Chlorophyll
Chromium
Coal
Coal Ash - chemistry
Coal Ash - metabolism
Coal-fired power plants
Culture
Culture media
Environmental health
Environmental Pollutants - chemistry
Environmental Pollutants - metabolism
Experiments
Ferric oxide
Flowers & plants
Fluorescence
Fly ash
Food contamination & poisoning
Food webs
Groundwater pollution
Growth media
Harvest
Health risks
Heavy metals
Industrial plant emissions
Inhalation
Irrigation water
Leachates
Leaching
Lung cancer
Manganese
Metals, Heavy - metabolism
Molybdenum
Morphology
Mullite
Mustard Plant - metabolism
Phytoremediation
Power Plants
Respiration
Scanning electron microscopy
Sediment pollution
Seeds
Silicon dioxide
Silicosis
Soil - chemistry
Soil contamination
Soil pollution
Soils
South Africa
Spinacia oleracea - metabolism
Translocation
X-ray diffraction
title Evaluation of the Bioavailability and Translocation of Selected Heavy Metals by Brassica juncea and Spinacea oleracea L for a South African Power Utility Coal Fly Ash
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