Mutual relations between PAHs derived from atmospheric deposition, enzymatic activity, and humic substances in soils of differently urbanized areas

Purpose The aim of this study was to determine the mutual relations between polycyclic aromatic hydrocarbons (PAHs) originated from atmospheric emissions and enzymatic activity and humic substances in soils at differently urbanized area, on an example of the Lublin city, east Poland. Materials and m...

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Veröffentlicht in:Journal of soils and sediments 2018-08, Vol.18 (8), p.2682-2691
Hauptverfasser: Bielińska, Elżbieta J., Futa, Barbara, Ukalska-Jaruga, Aleksandra, Weber, Jerzy, Chmielewski, Szymon, Wesołowska, Sylwia, Mocek-Płóciniak, Agnieszka, Patkowski, Krzysztof, Mielnik, Lilla
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container_end_page 2691
container_issue 8
container_start_page 2682
container_title Journal of soils and sediments
container_volume 18
creator Bielińska, Elżbieta J.
Futa, Barbara
Ukalska-Jaruga, Aleksandra
Weber, Jerzy
Chmielewski, Szymon
Wesołowska, Sylwia
Mocek-Płóciniak, Agnieszka
Patkowski, Krzysztof
Mielnik, Lilla
description Purpose The aim of this study was to determine the mutual relations between polycyclic aromatic hydrocarbons (PAHs) originated from atmospheric emissions and enzymatic activity and humic substances in soils at differently urbanized area, on an example of the Lublin city, east Poland. Materials and methods The chosen areas represented three differently urbanized environments: old tenement houses and modern residential blocks, mixture of different building and rural landscape, and typical rural environment with smallholding farms, respectively. On each of the urban, suburban, and rural areas, one representative plot was chosen on fallow lands classified as luvisol derived from loess. The soil samples were collected from the top 25 cm layer. The following properties were determined: pH, organic carbon, total nitrogen, humic and fulvic acids, PAHs content (14 PAHs from US EPA list), and the activities of the following enzymes: dehydrogenases, acid phosphatase, alkane phosphatase, protease, and urease. Results and discussion Higher contents of organic C and total N were found in the rural soil samples. The share of humic acid was similar in all soils investigated, ranging from 19.38 to 25.27%, while fulvic acid values differ significantly between urban and rural areas. The urban soils indicated much lower share of fulvic acids (9.78–10.99%) than those of rural (29.02–29.32%). Consequently, the values of the C HA :C FA ratio of the urban soil were approximately two times higher than those of the rural soil. The results showed that both the rate of humification and the activity of dehydrogenases, acid phosphatase, alkaline phosphatase, and proteases in the soils increased in the following sequence: urban < suburban < rural. Conclusions The results showed that an increase of PAHs in the urbanized areas affect other soil properties. The phenanthrene/anthracene and fluoranthene/pyrene ratios pointed to coal combustion as the principal source of PAHs in the investigated soils. The PAH content in the urbanized area inhibit humification processes in the soil and the activity of dehydrogenases, acid phosphatase, alkaline phosphatase, and proteases.
doi_str_mv 10.1007/s11368-018-1937-z
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Materials and methods The chosen areas represented three differently urbanized environments: old tenement houses and modern residential blocks, mixture of different building and rural landscape, and typical rural environment with smallholding farms, respectively. On each of the urban, suburban, and rural areas, one representative plot was chosen on fallow lands classified as luvisol derived from loess. The soil samples were collected from the top 25 cm layer. The following properties were determined: pH, organic carbon, total nitrogen, humic and fulvic acids, PAHs content (14 PAHs from US EPA list), and the activities of the following enzymes: dehydrogenases, acid phosphatase, alkane phosphatase, protease, and urease. Results and discussion Higher contents of organic C and total N were found in the rural soil samples. The share of humic acid was similar in all soils investigated, ranging from 19.38 to 25.27%, while fulvic acid values differ significantly between urban and rural areas. The urban soils indicated much lower share of fulvic acids (9.78–10.99%) than those of rural (29.02–29.32%). Consequently, the values of the C HA :C FA ratio of the urban soil were approximately two times higher than those of the rural soil. The results showed that both the rate of humification and the activity of dehydrogenases, acid phosphatase, alkaline phosphatase, and proteases in the soils increased in the following sequence: urban &lt; suburban &lt; rural. Conclusions The results showed that an increase of PAHs in the urbanized areas affect other soil properties. The phenanthrene/anthracene and fluoranthene/pyrene ratios pointed to coal combustion as the principal source of PAHs in the investigated soils. The PAH content in the urbanized area inhibit humification processes in the soil and the activity of dehydrogenases, acid phosphatase, alkaline phosphatase, and proteases.</description><identifier>ISSN: 1439-0108</identifier><identifier>EISSN: 1614-7480</identifier><identifier>DOI: 10.1007/s11368-018-1937-z</identifier><language>eng</language><publisher>Berlin/Heidelberg: Springer Berlin Heidelberg</publisher><subject>Acid phosphatase ; Acids ; Alkaline phosphatase ; Alkanes ; Anthracene ; Aromatic compounds ; Aromatic hydrocarbons ; Atmospheric pollution deposition ; Dehydrogenases ; Earth and Environmental Science ; Environment ; Environmental Physics ; Enzymatic activity ; Enzyme activity ; Farms ; Fluoranthene ; Fulvic acids ; Houses ; Humic acids ; Humic substances ; Humic Substances in the Environment ; Humification ; Loess ; Nitrogen ; Organic carbon ; Phenanthrene ; Phosphatase ; Polycyclic aromatic hydrocarbons ; Pyrene ; Ratios ; Residential areas ; Residential buildings ; Rural areas ; Rural environments ; Soil ; Soil investigations ; Soil properties ; Soil Science &amp; Conservation ; Urease</subject><ispartof>Journal of soils and sediments, 2018-08, Vol.18 (8), p.2682-2691</ispartof><rights>Springer 2018</rights><rights>Journal of Soils and Sediments is a copyright of Springer, (2018). All Rights Reserved.</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c359t-dcafa8c0f9b23ccac6dccac82361df7c06ec5f784380ec3b304faf5492693be73</citedby><cites>FETCH-LOGICAL-c359t-dcafa8c0f9b23ccac6dccac82361df7c06ec5f784380ec3b304faf5492693be73</cites><orcidid>0000-0002-3606-6453</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://link.springer.com/content/pdf/10.1007/s11368-018-1937-z$$EPDF$$P50$$Gspringer$$Hfree_for_read</linktopdf><linktohtml>$$Uhttps://link.springer.com/10.1007/s11368-018-1937-z$$EHTML$$P50$$Gspringer$$Hfree_for_read</linktohtml><link.rule.ids>315,781,785,27928,27929,41492,42561,51323</link.rule.ids></links><search><creatorcontrib>Bielińska, Elżbieta J.</creatorcontrib><creatorcontrib>Futa, Barbara</creatorcontrib><creatorcontrib>Ukalska-Jaruga, Aleksandra</creatorcontrib><creatorcontrib>Weber, Jerzy</creatorcontrib><creatorcontrib>Chmielewski, Szymon</creatorcontrib><creatorcontrib>Wesołowska, Sylwia</creatorcontrib><creatorcontrib>Mocek-Płóciniak, Agnieszka</creatorcontrib><creatorcontrib>Patkowski, Krzysztof</creatorcontrib><creatorcontrib>Mielnik, Lilla</creatorcontrib><title>Mutual relations between PAHs derived from atmospheric deposition, enzymatic activity, and humic substances in soils of differently urbanized areas</title><title>Journal of soils and sediments</title><addtitle>J Soils Sediments</addtitle><description>Purpose The aim of this study was to determine the mutual relations between polycyclic aromatic hydrocarbons (PAHs) originated from atmospheric emissions and enzymatic activity and humic substances in soils at differently urbanized area, on an example of the Lublin city, east Poland. Materials and methods The chosen areas represented three differently urbanized environments: old tenement houses and modern residential blocks, mixture of different building and rural landscape, and typical rural environment with smallholding farms, respectively. On each of the urban, suburban, and rural areas, one representative plot was chosen on fallow lands classified as luvisol derived from loess. The soil samples were collected from the top 25 cm layer. The following properties were determined: pH, organic carbon, total nitrogen, humic and fulvic acids, PAHs content (14 PAHs from US EPA list), and the activities of the following enzymes: dehydrogenases, acid phosphatase, alkane phosphatase, protease, and urease. Results and discussion Higher contents of organic C and total N were found in the rural soil samples. The share of humic acid was similar in all soils investigated, ranging from 19.38 to 25.27%, while fulvic acid values differ significantly between urban and rural areas. The urban soils indicated much lower share of fulvic acids (9.78–10.99%) than those of rural (29.02–29.32%). Consequently, the values of the C HA :C FA ratio of the urban soil were approximately two times higher than those of the rural soil. The results showed that both the rate of humification and the activity of dehydrogenases, acid phosphatase, alkaline phosphatase, and proteases in the soils increased in the following sequence: urban &lt; suburban &lt; rural. Conclusions The results showed that an increase of PAHs in the urbanized areas affect other soil properties. The phenanthrene/anthracene and fluoranthene/pyrene ratios pointed to coal combustion as the principal source of PAHs in the investigated soils. The PAH content in the urbanized area inhibit humification processes in the soil and the activity of dehydrogenases, acid phosphatase, alkaline phosphatase, and proteases.</description><subject>Acid phosphatase</subject><subject>Acids</subject><subject>Alkaline phosphatase</subject><subject>Alkanes</subject><subject>Anthracene</subject><subject>Aromatic compounds</subject><subject>Aromatic hydrocarbons</subject><subject>Atmospheric pollution deposition</subject><subject>Dehydrogenases</subject><subject>Earth and Environmental Science</subject><subject>Environment</subject><subject>Environmental Physics</subject><subject>Enzymatic activity</subject><subject>Enzyme activity</subject><subject>Farms</subject><subject>Fluoranthene</subject><subject>Fulvic acids</subject><subject>Houses</subject><subject>Humic acids</subject><subject>Humic substances</subject><subject>Humic Substances in the Environment</subject><subject>Humification</subject><subject>Loess</subject><subject>Nitrogen</subject><subject>Organic carbon</subject><subject>Phenanthrene</subject><subject>Phosphatase</subject><subject>Polycyclic aromatic hydrocarbons</subject><subject>Pyrene</subject><subject>Ratios</subject><subject>Residential areas</subject><subject>Residential buildings</subject><subject>Rural areas</subject><subject>Rural environments</subject><subject>Soil</subject><subject>Soil investigations</subject><subject>Soil properties</subject><subject>Soil Science &amp; 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Futa, Barbara ; Ukalska-Jaruga, Aleksandra ; Weber, Jerzy ; Chmielewski, Szymon ; Wesołowska, Sylwia ; Mocek-Płóciniak, Agnieszka ; Patkowski, Krzysztof ; Mielnik, Lilla</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c359t-dcafa8c0f9b23ccac6dccac82361df7c06ec5f784380ec3b304faf5492693be73</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2018</creationdate><topic>Acid phosphatase</topic><topic>Acids</topic><topic>Alkaline phosphatase</topic><topic>Alkanes</topic><topic>Anthracene</topic><topic>Aromatic compounds</topic><topic>Aromatic hydrocarbons</topic><topic>Atmospheric pollution deposition</topic><topic>Dehydrogenases</topic><topic>Earth and Environmental Science</topic><topic>Environment</topic><topic>Environmental Physics</topic><topic>Enzymatic activity</topic><topic>Enzyme activity</topic><topic>Farms</topic><topic>Fluoranthene</topic><topic>Fulvic acids</topic><topic>Houses</topic><topic>Humic acids</topic><topic>Humic substances</topic><topic>Humic Substances in the Environment</topic><topic>Humification</topic><topic>Loess</topic><topic>Nitrogen</topic><topic>Organic carbon</topic><topic>Phenanthrene</topic><topic>Phosphatase</topic><topic>Polycyclic aromatic hydrocarbons</topic><topic>Pyrene</topic><topic>Ratios</topic><topic>Residential areas</topic><topic>Residential buildings</topic><topic>Rural areas</topic><topic>Rural environments</topic><topic>Soil</topic><topic>Soil investigations</topic><topic>Soil properties</topic><topic>Soil Science &amp; 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Materials and methods The chosen areas represented three differently urbanized environments: old tenement houses and modern residential blocks, mixture of different building and rural landscape, and typical rural environment with smallholding farms, respectively. On each of the urban, suburban, and rural areas, one representative plot was chosen on fallow lands classified as luvisol derived from loess. The soil samples were collected from the top 25 cm layer. The following properties were determined: pH, organic carbon, total nitrogen, humic and fulvic acids, PAHs content (14 PAHs from US EPA list), and the activities of the following enzymes: dehydrogenases, acid phosphatase, alkane phosphatase, protease, and urease. Results and discussion Higher contents of organic C and total N were found in the rural soil samples. The share of humic acid was similar in all soils investigated, ranging from 19.38 to 25.27%, while fulvic acid values differ significantly between urban and rural areas. The urban soils indicated much lower share of fulvic acids (9.78–10.99%) than those of rural (29.02–29.32%). Consequently, the values of the C HA :C FA ratio of the urban soil were approximately two times higher than those of the rural soil. The results showed that both the rate of humification and the activity of dehydrogenases, acid phosphatase, alkaline phosphatase, and proteases in the soils increased in the following sequence: urban &lt; suburban &lt; rural. Conclusions The results showed that an increase of PAHs in the urbanized areas affect other soil properties. The phenanthrene/anthracene and fluoranthene/pyrene ratios pointed to coal combustion as the principal source of PAHs in the investigated soils. The PAH content in the urbanized area inhibit humification processes in the soil and the activity of dehydrogenases, acid phosphatase, alkaline phosphatase, and proteases.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><doi>10.1007/s11368-018-1937-z</doi><tpages>10</tpages><orcidid>https://orcid.org/0000-0002-3606-6453</orcidid><oa>free_for_read</oa></addata></record>
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subjects Acid phosphatase
Acids
Alkaline phosphatase
Alkanes
Anthracene
Aromatic compounds
Aromatic hydrocarbons
Atmospheric pollution deposition
Dehydrogenases
Earth and Environmental Science
Environment
Environmental Physics
Enzymatic activity
Enzyme activity
Farms
Fluoranthene
Fulvic acids
Houses
Humic acids
Humic substances
Humic Substances in the Environment
Humification
Loess
Nitrogen
Organic carbon
Phenanthrene
Phosphatase
Polycyclic aromatic hydrocarbons
Pyrene
Ratios
Residential areas
Residential buildings
Rural areas
Rural environments
Soil
Soil investigations
Soil properties
Soil Science & Conservation
Urease
title Mutual relations between PAHs derived from atmospheric deposition, enzymatic activity, and humic substances in soils of differently urbanized areas
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