The Use of Bark in Biomonitoring Heavy Metal Pollution of Forest Areas on the Example of Selected Areas in Poland
In the year 2016, passive biomonitoring studies were conducted in the forest areas of southern and north-eastern Poland: the Karkonosze Mountains (Kark), the Beskidy Mountains (Beskid), Borecka Forest (P. Bor), Knyszynska Forest (P. Kny), and Białowieza Forest (P. Bia). This study used bark from the...
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description | In the year 2016, passive biomonitoring studies were conducted in the forest areas of southern and north-eastern Poland: the Karkonosze Mountains (Kark), the Beskidy Mountains (Beskid), Borecka Forest (P. Bor), Knyszynska Forest (P. Kny), and Białowieza Forest (P. Bia). This study used bark from the tree,
Roth. Samples were collected in spring (Sp), summer (Su), and autumn (Au). Concentrations of Mn, Fe, Ni, Cu, Zn, Cd, and Pb were determined for the samples using the atomic absorption spectrometry method with flame excitation (F-AAS). Based on the obtained results, the studied areas were ranked according to level of heavy-metal deposition: forests of southern Poland > forests of north-eastern Poland. Some seasonal changes in the concentrations of metals accumulated in bark were also indicated, which is directly related to their changing concentrations in the air during the calendar year, for instance, the winter heating season produces higher concentrations of heavy metals in the bark samples taken in spring. When deciding to do biomonitoring studies using bark, but also other biological materials, it is necessary to take into account the period in which the conducted research is done and the time when the samples are taken for analysis, because this will have a significant impact on the obtained results. |
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Roth. Samples were collected in spring (Sp), summer (Su), and autumn (Au). Concentrations of Mn, Fe, Ni, Cu, Zn, Cd, and Pb were determined for the samples using the atomic absorption spectrometry method with flame excitation (F-AAS). Based on the obtained results, the studied areas were ranked according to level of heavy-metal deposition: forests of southern Poland > forests of north-eastern Poland. Some seasonal changes in the concentrations of metals accumulated in bark were also indicated, which is directly related to their changing concentrations in the air during the calendar year, for instance, the winter heating season produces higher concentrations of heavy metals in the bark samples taken in spring. When deciding to do biomonitoring studies using bark, but also other biological materials, it is necessary to take into account the period in which the conducted research is done and the time when the samples are taken for analysis, because this will have a significant impact on the obtained results.</description><identifier>ISSN: 1898-6196</identifier><identifier>EISSN: 2084-4549</identifier><identifier>EISSN: 1898-6196</identifier><identifier>DOI: 10.2478/eces-2020-0013</identifier><language>eng</language><publisher>Opole: Sciendo</publisher><subject>Absorption spectroscopy ; Air pollution ; Atmospheric aerosols ; Atomic absorption analysis ; atomic absorption spectrometry ; Atomic absorption spectroscopy ; Autumn ; Bark ; Biological materials ; Biomonitoring ; Cadmium ; Copper ; Forests ; Gold ; Heavy metals ; Lead ; Leaves ; Manganese ; Metal concentrations ; Metals ; Mosses ; Mountains ; Nickel ; Pollutant deposition ; Pollutants ; Pollution ; Scientific imaging ; Seasonal variation ; Seasonal variations ; Spectral analysis ; Spectrometry ; Spring ; Spring (season) ; Trees ; Zinc</subject><ispartof>Ecological Chemistry and Engineering S, 2020-06, Vol.27 (2), p.195-210</ispartof><rights>2020. This work is published under http://creativecommons.org/licenses/by-nc-nd/3.0 (the “License”). Notwithstanding the ProQuest Terms and Conditions, you may use this content in accordance with the terms of the License.</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c413t-c92574b879e9f1efaa95c46c589ffc6ff1faa9b5050e1ccdcb688a33f1ab228d3</citedby><cites>FETCH-LOGICAL-c413t-c92574b879e9f1efaa95c46c589ffc6ff1faa9b5050e1ccdcb688a33f1ab228d3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://sciendo.com/pdf/10.2478/eces-2020-0013$$EPDF$$P50$$Gwalterdegruyter$$Hfree_for_read</linktopdf><linktohtml>$$Uhttps://sciendo.com/article/10.2478/eces-2020-0013$$EHTML$$P50$$Gwalterdegruyter$$Hfree_for_read</linktohtml><link.rule.ids>314,780,784,27924,27925,76164,76165</link.rule.ids></links><search><creatorcontrib>Świsłowski, Paweł</creatorcontrib><creatorcontrib>Kříž, Jan</creatorcontrib><creatorcontrib>Rajfur, Małgorzata</creatorcontrib><title>The Use of Bark in Biomonitoring Heavy Metal Pollution of Forest Areas on the Example of Selected Areas in Poland</title><title>Ecological Chemistry and Engineering S</title><description>In the year 2016, passive biomonitoring studies were conducted in the forest areas of southern and north-eastern Poland: the Karkonosze Mountains (Kark), the Beskidy Mountains (Beskid), Borecka Forest (P. Bor), Knyszynska Forest (P. Kny), and Białowieza Forest (P. Bia). This study used bark from the tree,
Roth. Samples were collected in spring (Sp), summer (Su), and autumn (Au). Concentrations of Mn, Fe, Ni, Cu, Zn, Cd, and Pb were determined for the samples using the atomic absorption spectrometry method with flame excitation (F-AAS). Based on the obtained results, the studied areas were ranked according to level of heavy-metal deposition: forests of southern Poland > forests of north-eastern Poland. Some seasonal changes in the concentrations of metals accumulated in bark were also indicated, which is directly related to their changing concentrations in the air during the calendar year, for instance, the winter heating season produces higher concentrations of heavy metals in the bark samples taken in spring. When deciding to do biomonitoring studies using bark, but also other biological materials, it is necessary to take into account the period in which the conducted research is done and the time when the samples are taken for analysis, because this will have a significant impact on the obtained results.</description><subject>Absorption spectroscopy</subject><subject>Air pollution</subject><subject>Atmospheric aerosols</subject><subject>Atomic absorption analysis</subject><subject>atomic absorption spectrometry</subject><subject>Atomic absorption spectroscopy</subject><subject>Autumn</subject><subject>Bark</subject><subject>Biological materials</subject><subject>Biomonitoring</subject><subject>Cadmium</subject><subject>Copper</subject><subject>Forests</subject><subject>Gold</subject><subject>Heavy metals</subject><subject>Lead</subject><subject>Leaves</subject><subject>Manganese</subject><subject>Metal concentrations</subject><subject>Metals</subject><subject>Mosses</subject><subject>Mountains</subject><subject>Nickel</subject><subject>Pollutant deposition</subject><subject>Pollutants</subject><subject>Pollution</subject><subject>Scientific imaging</subject><subject>Seasonal variation</subject><subject>Seasonal variations</subject><subject>Spectral analysis</subject><subject>Spectrometry</subject><subject>Spring</subject><subject>Spring (season)</subject><subject>Trees</subject><subject>Zinc</subject><issn>1898-6196</issn><issn>2084-4549</issn><issn>1898-6196</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2020</creationdate><recordtype>article</recordtype><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNptkMFPwjAUhxujiQS5em7iedh23dYmXoCAmGA0Ec5L173icKzQDpX_3k5IvHh6zcv3-17zQ-iWkiHjmbgHDT5ihJGIEBpfoB4jgkc84fIS9aiQIkqpTK_RwPsNCUjCZJyyHtov3wGvPGBr8Fi5D1w1eFzZrW2q1rqqWeM5qM8jfoZW1fjV1vWhrWzT4TPrwLd45EB5HFZtME2_1XZX_9reoAbdQnkGgjekVVPeoCujag-D8-yj1Wy6nMyjxcvj02S0iDSncRtpyZKMFyKTIA0Fo5RMNE91IqQxOjWGdqsiIQkBqnWpi1QIFceGqoIxUcZ9dHfy7pzdH8JP8409uCaczBlnaZYyyVmghidKO-u9A5PvXLVV7phTknfN5l2zedds3jUbAg-nwJeqW3AlrN3hGB5_9v-DLGNUJvEPTzKATg</recordid><startdate>20200601</startdate><enddate>20200601</enddate><creator>Świsłowski, Paweł</creator><creator>Kříž, Jan</creator><creator>Rajfur, Małgorzata</creator><general>Sciendo</general><general>De Gruyter Poland</general><scope>AAYXX</scope><scope>CITATION</scope><scope>7QH</scope><scope>7SN</scope><scope>7ST</scope><scope>7UA</scope><scope>8FE</scope><scope>8FG</scope><scope>8FH</scope><scope>ABJCF</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BBNVY</scope><scope>BENPR</scope><scope>BGLVJ</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>D1I</scope><scope>DWQXO</scope><scope>F1W</scope><scope>GNUQQ</scope><scope>H97</scope><scope>HCIFZ</scope><scope>KB.</scope><scope>L.G</scope><scope>L6V</scope><scope>LK8</scope><scope>M7P</scope><scope>M7S</scope><scope>PATMY</scope><scope>PDBOC</scope><scope>PIMPY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PTHSS</scope><scope>PYCSY</scope><scope>SOI</scope></search><sort><creationdate>20200601</creationdate><title>The Use of Bark in Biomonitoring Heavy Metal Pollution of Forest Areas on the Example of Selected Areas in Poland</title><author>Świsłowski, Paweł ; Kříž, Jan ; Rajfur, Małgorzata</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c413t-c92574b879e9f1efaa95c46c589ffc6ff1faa9b5050e1ccdcb688a33f1ab228d3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2020</creationdate><topic>Absorption spectroscopy</topic><topic>Air pollution</topic><topic>Atmospheric aerosols</topic><topic>Atomic absorption analysis</topic><topic>atomic absorption spectrometry</topic><topic>Atomic absorption spectroscopy</topic><topic>Autumn</topic><topic>Bark</topic><topic>Biological materials</topic><topic>Biomonitoring</topic><topic>Cadmium</topic><topic>Copper</topic><topic>Forests</topic><topic>Gold</topic><topic>Heavy metals</topic><topic>Lead</topic><topic>Leaves</topic><topic>Manganese</topic><topic>Metal concentrations</topic><topic>Metals</topic><topic>Mosses</topic><topic>Mountains</topic><topic>Nickel</topic><topic>Pollutant deposition</topic><topic>Pollutants</topic><topic>Pollution</topic><topic>Scientific imaging</topic><topic>Seasonal variation</topic><topic>Seasonal variations</topic><topic>Spectral analysis</topic><topic>Spectrometry</topic><topic>Spring</topic><topic>Spring (season)</topic><topic>Trees</topic><topic>Zinc</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Świsłowski, Paweł</creatorcontrib><creatorcontrib>Kříž, Jan</creatorcontrib><creatorcontrib>Rajfur, Małgorzata</creatorcontrib><collection>CrossRef</collection><collection>Aqualine</collection><collection>Ecology Abstracts</collection><collection>Environment Abstracts</collection><collection>Water Resources Abstracts</collection><collection>ProQuest SciTech Collection</collection><collection>ProQuest Technology Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>Materials Science & Engineering Collection</collection><collection>ProQuest Central (Alumni Edition)</collection><collection>ProQuest Central UK/Ireland</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>Biological Science Collection</collection><collection>ProQuest Central</collection><collection>Technology Collection</collection><collection>Natural Science Collection</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ProQuest One Community College</collection><collection>ProQuest Materials Science Collection</collection><collection>ProQuest Central Korea</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>ProQuest Central Student</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>SciTech Premium Collection</collection><collection>Materials Science Database</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>ProQuest Engineering Collection</collection><collection>ProQuest Biological Science Collection</collection><collection>Biological Science Database</collection><collection>Engineering Database</collection><collection>Environmental Science Database</collection><collection>Materials Science Collection</collection><collection>Publicly Available Content Database</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>Engineering Collection</collection><collection>Environmental Science Collection</collection><collection>Environment Abstracts</collection><jtitle>Ecological Chemistry and Engineering S</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Świsłowski, Paweł</au><au>Kříž, Jan</au><au>Rajfur, Małgorzata</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>The Use of Bark in Biomonitoring Heavy Metal Pollution of Forest Areas on the Example of Selected Areas in Poland</atitle><jtitle>Ecological Chemistry and Engineering S</jtitle><date>2020-06-01</date><risdate>2020</risdate><volume>27</volume><issue>2</issue><spage>195</spage><epage>210</epage><pages>195-210</pages><issn>1898-6196</issn><eissn>2084-4549</eissn><eissn>1898-6196</eissn><abstract>In the year 2016, passive biomonitoring studies were conducted in the forest areas of southern and north-eastern Poland: the Karkonosze Mountains (Kark), the Beskidy Mountains (Beskid), Borecka Forest (P. Bor), Knyszynska Forest (P. Kny), and Białowieza Forest (P. Bia). This study used bark from the tree,
Roth. Samples were collected in spring (Sp), summer (Su), and autumn (Au). Concentrations of Mn, Fe, Ni, Cu, Zn, Cd, and Pb were determined for the samples using the atomic absorption spectrometry method with flame excitation (F-AAS). Based on the obtained results, the studied areas were ranked according to level of heavy-metal deposition: forests of southern Poland > forests of north-eastern Poland. Some seasonal changes in the concentrations of metals accumulated in bark were also indicated, which is directly related to their changing concentrations in the air during the calendar year, for instance, the winter heating season produces higher concentrations of heavy metals in the bark samples taken in spring. When deciding to do biomonitoring studies using bark, but also other biological materials, it is necessary to take into account the period in which the conducted research is done and the time when the samples are taken for analysis, because this will have a significant impact on the obtained results.</abstract><cop>Opole</cop><pub>Sciendo</pub><doi>10.2478/eces-2020-0013</doi><tpages>16</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Absorption spectroscopy Air pollution Atmospheric aerosols Atomic absorption analysis atomic absorption spectrometry Atomic absorption spectroscopy Autumn Bark Biological materials Biomonitoring Cadmium Copper Forests Gold Heavy metals Lead Leaves Manganese Metal concentrations Metals Mosses Mountains Nickel Pollutant deposition Pollutants Pollution Scientific imaging Seasonal variation Seasonal variations Spectral analysis Spectrometry Spring Spring (season) Trees Zinc |
title | The Use of Bark in Biomonitoring Heavy Metal Pollution of Forest Areas on the Example of Selected Areas in Poland |
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