Geochemical Fractions of the Agricultural Soils of Southern Poland and the Assessment of the Potentially Harmful Element Mobility

Surface samples (0−25 cm each) of agricultural soils were investigated in five Regions (voivodeships) of southern Poland. The mean Potentially Harmful Element (PHE) pseudototal content ranges were as follows (mg/kg): As 5.19−10.9, Cd 0.34−1.56, Co 1.92−6.70, C...

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Main Authors: Agnieszka Gruszecka-Kosowska, Agnieszka Baran, Katarzyna Mazur-Kajta, Tomasz Czech
Format: Article
Language:English
Published: MDPI AG 2019-10-01
Series:Minerals
Subjects:
Online Access:https://www.mdpi.com/2075-163X/9/11/674
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spelling doaj-790956e43be747849f07a7275d6573c82020-11-25T00:05:18ZengMDPI AGMinerals2075-163X2019-10-0191167410.3390/min9110674min9110674Geochemical Fractions of the Agricultural Soils of Southern Poland and the Assessment of the Potentially Harmful Element MobilityAgnieszka Gruszecka-Kosowska0Agnieszka Baran1Katarzyna Mazur-Kajta2Tomasz Czech3Faculty of Geology, Geophysics, and Environmental Protection, Department of Environmental Protection, AGH University of Science and Technology, Al. Mickiewicza 30, 30-059 Kraków, PolandFaculty of Agriculture and Economics, Department of Agricultural and Environmental Chemistry, University of Agriculture in Kraków, Al. A. Mickiewicza 21, 31-120 Kraków, PolandFaculty of Economics and Management, Department of International Economic Relations, Opole University of Technology, ul. Prószkowska 76, 45-758 Opole, PolandFaculty of Agriculture and Economics, Department of Agricultural and Environmental Chemistry, University of Agriculture in Kraków, Al. A. Mickiewicza 21, 31-120 Kraków, PolandSurface samples (0&#8722;25 cm each) of agricultural soils were investigated in five Regions (voivodeships) of southern Poland. The mean Potentially Harmful Element (PHE) pseudototal content ranges were as follows (mg/kg): As 5.19&#8722;10.9, Cd 0.34&#8722;1.56, Co 1.92&#8722;6.70, Cr 9.05&#8722;25.7, Cu 8.74&#8722;69.4, Hg 0.001&#8722;0.08, Ni 3.93&#8722;19.9, Pb 20.3&#8722;183, Sb 0.80&#8722;1.42, Tl 0.04&#8722;0.17, and Zn 61.3&#8722;422. The PHE availability depended on pH, the organic carbon (C<sub>org</sub>) content, and the pseudototal PHE content in soils. Exchangeable and acid soluble PHE contents (BCR<sub>F1</sub>) determined in the Community Bureau of Reference (BCR) three-step sequential extraction procedure decreased in this order: Cd &gt; Zn &gt; Co &gt; Ni = Sb &gt; Cu &gt; Tl &gt; As &gt; Cr = Pb. Actually available PHE contents in pore water (0.01 mol/dm<sup>3 </sup>CaCl<sub>2</sub>) ranged as follows: Cd 0.81&#8722;17%, Cr 0&#8722;0.25%, Cu 0.01&#8722;2.31%, Ni 0.16&#8722;2%, Pb 0.2&#8722;0.49%, and Zn 0.25&#8722;2.12%. The potential soluble total content of PHEs in pore water (0.05 mol/dm<sup>3</sup> Na<sub>2</sub>EDTA) ranged as follows: Cd 27&#8722;91%, Cr 0.7&#8722;7.1%, Cu 6.7&#8722;98%, Ni 3.6&#8722;41%, Pb 15&#8722;41%, and Zn 3&#8722;34%. The mobility factor (MF) values indicated Cd (31.6%) and Zn (21.0%) as the most mobile elements in soil. Other PHEs followed the order of Co &gt; Ni &gt; Tl &gt; As &gt; Sb &gt; Cu &gt; Cr &gt; Pb, with the MF values &lt;10%. The risk assessment code (RAC) values revealed a very high ecological risk of Cd and Zn in the Podkarpackie Region and a high ecological risk of Cd in the Regions of Opolskie, Śląskie, Małopolskie, and Podkarpackie, and the same of Zn in the Opolskie and Śląskie. The modified risk assessment code (mRAC) index pointed a very high potential of adverse effects in soils in the Podkarpackie and a medium potential in the Opolskie, Śląskie, Małopolskie, and Świętokrzyskie. The potential adverse effect risk, described by the individual contamination factor (ICF) factor, was the following in the Regions, in the decreasing order: Cd &gt; Pb &gt; Sb &gt; Zn &gt; Co &gt; Cu &gt; Ni &gt; Tl &gt; As &gt; Cr, and the same as described by the global contamination factor (GCF) values: Opolskie &gt; Podkarpackie &gt; Świętokrzyskie &gt; Śląskie &gt; Małopolskie.https://www.mdpi.com/2075-163X/9/11/674mobilityecological riskmf factormrac indexicf factorgcf factor
collection DOAJ
language English
format Article
sources DOAJ
author Agnieszka Gruszecka-Kosowska
Agnieszka Baran
Katarzyna Mazur-Kajta
Tomasz Czech
spellingShingle Agnieszka Gruszecka-Kosowska
Agnieszka Baran
Katarzyna Mazur-Kajta
Tomasz Czech
Geochemical Fractions of the Agricultural Soils of Southern Poland and the Assessment of the Potentially Harmful Element Mobility
Minerals
mobility
ecological risk
mf factor
mrac index
icf factor
gcf factor
author_facet Agnieszka Gruszecka-Kosowska
Agnieszka Baran
Katarzyna Mazur-Kajta
Tomasz Czech
author_sort Agnieszka Gruszecka-Kosowska
title Geochemical Fractions of the Agricultural Soils of Southern Poland and the Assessment of the Potentially Harmful Element Mobility
title_short Geochemical Fractions of the Agricultural Soils of Southern Poland and the Assessment of the Potentially Harmful Element Mobility
title_full Geochemical Fractions of the Agricultural Soils of Southern Poland and the Assessment of the Potentially Harmful Element Mobility
title_fullStr Geochemical Fractions of the Agricultural Soils of Southern Poland and the Assessment of the Potentially Harmful Element Mobility
title_full_unstemmed Geochemical Fractions of the Agricultural Soils of Southern Poland and the Assessment of the Potentially Harmful Element Mobility
title_sort geochemical fractions of the agricultural soils of southern poland and the assessment of the potentially harmful element mobility
publisher MDPI AG
series Minerals
issn 2075-163X
publishDate 2019-10-01
description Surface samples (0&#8722;25 cm each) of agricultural soils were investigated in five Regions (voivodeships) of southern Poland. The mean Potentially Harmful Element (PHE) pseudototal content ranges were as follows (mg/kg): As 5.19&#8722;10.9, Cd 0.34&#8722;1.56, Co 1.92&#8722;6.70, Cr 9.05&#8722;25.7, Cu 8.74&#8722;69.4, Hg 0.001&#8722;0.08, Ni 3.93&#8722;19.9, Pb 20.3&#8722;183, Sb 0.80&#8722;1.42, Tl 0.04&#8722;0.17, and Zn 61.3&#8722;422. The PHE availability depended on pH, the organic carbon (C<sub>org</sub>) content, and the pseudototal PHE content in soils. Exchangeable and acid soluble PHE contents (BCR<sub>F1</sub>) determined in the Community Bureau of Reference (BCR) three-step sequential extraction procedure decreased in this order: Cd &gt; Zn &gt; Co &gt; Ni = Sb &gt; Cu &gt; Tl &gt; As &gt; Cr = Pb. Actually available PHE contents in pore water (0.01 mol/dm<sup>3 </sup>CaCl<sub>2</sub>) ranged as follows: Cd 0.81&#8722;17%, Cr 0&#8722;0.25%, Cu 0.01&#8722;2.31%, Ni 0.16&#8722;2%, Pb 0.2&#8722;0.49%, and Zn 0.25&#8722;2.12%. The potential soluble total content of PHEs in pore water (0.05 mol/dm<sup>3</sup> Na<sub>2</sub>EDTA) ranged as follows: Cd 27&#8722;91%, Cr 0.7&#8722;7.1%, Cu 6.7&#8722;98%, Ni 3.6&#8722;41%, Pb 15&#8722;41%, and Zn 3&#8722;34%. The mobility factor (MF) values indicated Cd (31.6%) and Zn (21.0%) as the most mobile elements in soil. Other PHEs followed the order of Co &gt; Ni &gt; Tl &gt; As &gt; Sb &gt; Cu &gt; Cr &gt; Pb, with the MF values &lt;10%. The risk assessment code (RAC) values revealed a very high ecological risk of Cd and Zn in the Podkarpackie Region and a high ecological risk of Cd in the Regions of Opolskie, Śląskie, Małopolskie, and Podkarpackie, and the same of Zn in the Opolskie and Śląskie. The modified risk assessment code (mRAC) index pointed a very high potential of adverse effects in soils in the Podkarpackie and a medium potential in the Opolskie, Śląskie, Małopolskie, and Świętokrzyskie. The potential adverse effect risk, described by the individual contamination factor (ICF) factor, was the following in the Regions, in the decreasing order: Cd &gt; Pb &gt; Sb &gt; Zn &gt; Co &gt; Cu &gt; Ni &gt; Tl &gt; As &gt; Cr, and the same as described by the global contamination factor (GCF) values: Opolskie &gt; Podkarpackie &gt; Świętokrzyskie &gt; Śląskie &gt; Małopolskie.
topic mobility
ecological risk
mf factor
mrac index
icf factor
gcf factor
url https://www.mdpi.com/2075-163X/9/11/674
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