Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia
Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgr...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Hiller, Edgar [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2014 |
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| Schlagwörter: |
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| Anmerkung: |
© Springer-Verlag Berlin Heidelberg 2014 |
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| Übergeordnetes Werk: |
Enthalten in: Environmental earth sciences - Berlin : Springer, 2009, 73(2014), 11 vom: 23. Nov., Seite 7147-7156 |
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| Übergeordnetes Werk: |
volume:73 ; year:2014 ; number:11 ; day:23 ; month:11 ; pages:7147-7156 |
| Links: |
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| DOI / URN: |
10.1007/s12665-014-3894-1 |
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SPR026701774 |
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| 245 | 1 | 0 | |a Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia |
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| 520 | |a Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils. | ||
| 650 | 4 | |a Polycyclic aromatic hydrocarbons |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Urban soil |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Contamination |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Risk assessment |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Slovakia |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Lachká, Lucia |4 aut | |
| 700 | 1 | |a Jurkovič, Ľubomír |4 aut | |
| 700 | 1 | |a Vozár, Jaroslav |4 aut | |
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10.1007/s12665-014-3894-1 doi (DE-627)SPR026701774 (SPR)s12665-014-3894-1-e DE-627 ger DE-627 rakwb eng Hiller, Edgar verfasserin aut Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils. Polycyclic aromatic hydrocarbons (dpeaa)DE-He213 Urban soil (dpeaa)DE-He213 Contamination (dpeaa)DE-He213 Risk assessment (dpeaa)DE-He213 Slovakia (dpeaa)DE-He213 Lachká, Lucia aut Jurkovič, Ľubomír aut Vozár, Jaroslav aut Enthalten in Environmental earth sciences Berlin : Springer, 2009 73(2014), 11 vom: 23. Nov., Seite 7147-7156 (DE-627)599673451 (DE-600)2493699-6 1866-6299 nnns volume:73 year:2014 number:11 day:23 month:11 pages:7147-7156 https://dx.doi.org/10.1007/s12665-014-3894-1 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 73 2014 11 23 11 7147-7156 |
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10.1007/s12665-014-3894-1 doi (DE-627)SPR026701774 (SPR)s12665-014-3894-1-e DE-627 ger DE-627 rakwb eng Hiller, Edgar verfasserin aut Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils. Polycyclic aromatic hydrocarbons (dpeaa)DE-He213 Urban soil (dpeaa)DE-He213 Contamination (dpeaa)DE-He213 Risk assessment (dpeaa)DE-He213 Slovakia (dpeaa)DE-He213 Lachká, Lucia aut Jurkovič, Ľubomír aut Vozár, Jaroslav aut Enthalten in Environmental earth sciences Berlin : Springer, 2009 73(2014), 11 vom: 23. Nov., Seite 7147-7156 (DE-627)599673451 (DE-600)2493699-6 1866-6299 nnns volume:73 year:2014 number:11 day:23 month:11 pages:7147-7156 https://dx.doi.org/10.1007/s12665-014-3894-1 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 73 2014 11 23 11 7147-7156 |
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10.1007/s12665-014-3894-1 doi (DE-627)SPR026701774 (SPR)s12665-014-3894-1-e DE-627 ger DE-627 rakwb eng Hiller, Edgar verfasserin aut Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils. Polycyclic aromatic hydrocarbons (dpeaa)DE-He213 Urban soil (dpeaa)DE-He213 Contamination (dpeaa)DE-He213 Risk assessment (dpeaa)DE-He213 Slovakia (dpeaa)DE-He213 Lachká, Lucia aut Jurkovič, Ľubomír aut Vozár, Jaroslav aut Enthalten in Environmental earth sciences Berlin : Springer, 2009 73(2014), 11 vom: 23. Nov., Seite 7147-7156 (DE-627)599673451 (DE-600)2493699-6 1866-6299 nnns volume:73 year:2014 number:11 day:23 month:11 pages:7147-7156 https://dx.doi.org/10.1007/s12665-014-3894-1 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 73 2014 11 23 11 7147-7156 |
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10.1007/s12665-014-3894-1 doi (DE-627)SPR026701774 (SPR)s12665-014-3894-1-e DE-627 ger DE-627 rakwb eng Hiller, Edgar verfasserin aut Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils. Polycyclic aromatic hydrocarbons (dpeaa)DE-He213 Urban soil (dpeaa)DE-He213 Contamination (dpeaa)DE-He213 Risk assessment (dpeaa)DE-He213 Slovakia (dpeaa)DE-He213 Lachká, Lucia aut Jurkovič, Ľubomír aut Vozár, Jaroslav aut Enthalten in Environmental earth sciences Berlin : Springer, 2009 73(2014), 11 vom: 23. Nov., Seite 7147-7156 (DE-627)599673451 (DE-600)2493699-6 1866-6299 nnns volume:73 year:2014 number:11 day:23 month:11 pages:7147-7156 https://dx.doi.org/10.1007/s12665-014-3894-1 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 73 2014 11 23 11 7147-7156 |
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10.1007/s12665-014-3894-1 doi (DE-627)SPR026701774 (SPR)s12665-014-3894-1-e DE-627 ger DE-627 rakwb eng Hiller, Edgar verfasserin aut Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia 2014 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag Berlin Heidelberg 2014 Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils. Polycyclic aromatic hydrocarbons (dpeaa)DE-He213 Urban soil (dpeaa)DE-He213 Contamination (dpeaa)DE-He213 Risk assessment (dpeaa)DE-He213 Slovakia (dpeaa)DE-He213 Lachká, Lucia aut Jurkovič, Ľubomír aut Vozár, Jaroslav aut Enthalten in Environmental earth sciences Berlin : Springer, 2009 73(2014), 11 vom: 23. Nov., Seite 7147-7156 (DE-627)599673451 (DE-600)2493699-6 1866-6299 nnns volume:73 year:2014 number:11 day:23 month:11 pages:7147-7156 https://dx.doi.org/10.1007/s12665-014-3894-1 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 73 2014 11 23 11 7147-7156 |
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Enthalten in Environmental earth sciences 73(2014), 11 vom: 23. Nov., Seite 7147-7156 volume:73 year:2014 number:11 day:23 month:11 pages:7147-7156 |
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Hiller, Edgar @@aut@@ Lachká, Lucia @@aut@@ Jurkovič, Ľubomír @@aut@@ Vozár, Jaroslav @@aut@@ |
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<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">SPR026701774</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230401015905.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">201007s2014 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s12665-014-3894-1</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR026701774</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s12665-014-3894-1-e</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Hiller, Edgar</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2014</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="500" ind1=" " ind2=" "><subfield code="a">© Springer-Verlag Berlin Heidelberg 2014</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Polycyclic aromatic hydrocarbons</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Urban soil</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Contamination</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Risk assessment</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Slovakia</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Lachká, Lucia</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Jurkovič, Ľubomír</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Vozár, Jaroslav</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">Environmental earth sciences</subfield><subfield code="d">Berlin : Springer, 2009</subfield><subfield code="g">73(2014), 11 vom: 23. 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Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia Polycyclic aromatic hydrocarbons (dpeaa)DE-He213 Urban soil (dpeaa)DE-He213 Contamination (dpeaa)DE-He213 Risk assessment (dpeaa)DE-He213 Slovakia (dpeaa)DE-He213 |
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polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in bratislava, the capital city of slovakia |
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Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia |
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Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils. © Springer-Verlag Berlin Heidelberg 2014 |
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Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils. © Springer-Verlag Berlin Heidelberg 2014 |
| abstract_unstemmed |
Abstract One of the most urgent environmental problems in the world is contamination of soils by a variety of chemical pollutants in urban regions. The main goal in this study was to determine concentrations of 16 polycyclic aromatic hydrocarbons ($ Σ_{16} $PAHs) in soils in kindergartens and playgrounds because children are most often exposed to the soil surface. Totally, 61 surface soil samples (0–10 cm) were collected from the city of Bratislava and analyzed for basic soil properties and PAHs. The concentrations of $ Σ_{16} $PAHs ranged from 45 to 12,151 μg/kg with a mean concentration of 2,064.8 μg/kg and correlated positively with total organic carbon contents of the soils (Spearman r = 0.272, p < 0.034). There were significant differences in PAH concentrations between the old inner part of the city and the younger outer part. Kindergartens and playgrounds with more contaminated soils are located in the oldest part of the city (i.e., city center). Source apportionment using PAH diagnostic ratios indicated that traffic was likely the primary source of PAHs in soils, but wood or coal combustion from domestic heating as an additional contamination source could not be excluded. The benzo(a)pyrene equivalent concentrations for carcinogenic PAHs ($ BaP_{tpe} $) in 21 % of the soil samples were higher than the Canadian risk-based soil criterion. Nevertheless, total incremental lifetime cancer risks of PAHs ranged from 7.39 × $ 10^{−9} $ to 2.79 × $ 10^{−6} $, indicating negligible risk for the health of children even in the most contaminated soils. © Springer-Verlag Berlin Heidelberg 2014 |
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Polycyclic aromatic hydrocarbons in urban soils from kindergartens and playgrounds in Bratislava, the capital city of Slovakia |
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Lachká, Lucia Jurkovič, Ľubomír Vozár, Jaroslav |
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| score |
7.4000263 |