Mapping of urban environmentally sensitive areas in Bratislava city
Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area,...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Sobocká, Jaroslava [verfasserIn] Saksa, Martin [verfasserIn] Feranec, Ján [verfasserIn] Szatmári, Daniel [verfasserIn] Holec, Juraj [verfasserIn] Bobáľová, Hana [verfasserIn] Rášová, Andrea [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2020 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Journal of soils and sediments - Berlin : Springer, 2001, 21(2020), 5 vom: 18. Juni, Seite 2059-2070 |
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| Übergeordnetes Werk: |
volume:21 ; year:2020 ; number:5 ; day:18 ; month:06 ; pages:2059-2070 |
| Links: |
|---|
| DOI / URN: |
10.1007/s11368-020-02682-4 |
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| Katalog-ID: |
SPR043847250 |
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| 520 | |a Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. The identification of the U-ESA can be used for solving of housing comfort and quality of living standards in the frame of urban development and balanced spatial urban planning. | ||
| 650 | 4 | |a Environmentally sensitive areas |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Urban soils |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Pedo-urban complex |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Urban heat island |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Bratislava |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Saksa, Martin |e verfasserin |4 aut | |
| 700 | 1 | |a Feranec, Ján |e verfasserin |4 aut | |
| 700 | 1 | |a Szatmári, Daniel |e verfasserin |4 aut | |
| 700 | 1 | |a Holec, Juraj |e verfasserin |4 aut | |
| 700 | 1 | |a Bobáľová, Hana |e verfasserin |4 aut | |
| 700 | 1 | |a Rášová, Andrea |e verfasserin |4 aut | |
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10.1007/s11368-020-02682-4 doi (DE-627)SPR043847250 (DE-599)SPRs11368-020-02682-4-e (SPR)s11368-020-02682-4-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Sobocká, Jaroslava verfasserin aut Mapping of urban environmentally sensitive areas in Bratislava city 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. The identification of the U-ESA can be used for solving of housing comfort and quality of living standards in the frame of urban development and balanced spatial urban planning. Environmentally sensitive areas (dpeaa)DE-He213 Urban soils (dpeaa)DE-He213 Pedo-urban complex (dpeaa)DE-He213 Urban heat island (dpeaa)DE-He213 Bratislava (dpeaa)DE-He213 Saksa, Martin verfasserin aut Feranec, Ján verfasserin aut Szatmári, Daniel verfasserin aut Holec, Juraj verfasserin aut Bobáľová, Hana verfasserin aut Rášová, Andrea verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 21(2020), 5 vom: 18. Juni, Seite 2059-2070 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:21 year:2020 number:5 day:18 month:06 pages:2059-2070 https://dx.doi.org/10.1007/s11368-020-02682-4 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_183 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_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 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_2118 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 21 2020 5 18 06 2059-2070 |
| spelling |
10.1007/s11368-020-02682-4 doi (DE-627)SPR043847250 (DE-599)SPRs11368-020-02682-4-e (SPR)s11368-020-02682-4-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Sobocká, Jaroslava verfasserin aut Mapping of urban environmentally sensitive areas in Bratislava city 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. The identification of the U-ESA can be used for solving of housing comfort and quality of living standards in the frame of urban development and balanced spatial urban planning. Environmentally sensitive areas (dpeaa)DE-He213 Urban soils (dpeaa)DE-He213 Pedo-urban complex (dpeaa)DE-He213 Urban heat island (dpeaa)DE-He213 Bratislava (dpeaa)DE-He213 Saksa, Martin verfasserin aut Feranec, Ján verfasserin aut Szatmári, Daniel verfasserin aut Holec, Juraj verfasserin aut Bobáľová, Hana verfasserin aut Rášová, Andrea verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 21(2020), 5 vom: 18. Juni, Seite 2059-2070 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:21 year:2020 number:5 day:18 month:06 pages:2059-2070 https://dx.doi.org/10.1007/s11368-020-02682-4 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_183 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_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 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_2118 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 21 2020 5 18 06 2059-2070 |
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10.1007/s11368-020-02682-4 doi (DE-627)SPR043847250 (DE-599)SPRs11368-020-02682-4-e (SPR)s11368-020-02682-4-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Sobocká, Jaroslava verfasserin aut Mapping of urban environmentally sensitive areas in Bratislava city 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. The identification of the U-ESA can be used for solving of housing comfort and quality of living standards in the frame of urban development and balanced spatial urban planning. Environmentally sensitive areas (dpeaa)DE-He213 Urban soils (dpeaa)DE-He213 Pedo-urban complex (dpeaa)DE-He213 Urban heat island (dpeaa)DE-He213 Bratislava (dpeaa)DE-He213 Saksa, Martin verfasserin aut Feranec, Ján verfasserin aut Szatmári, Daniel verfasserin aut Holec, Juraj verfasserin aut Bobáľová, Hana verfasserin aut Rášová, Andrea verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 21(2020), 5 vom: 18. Juni, Seite 2059-2070 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:21 year:2020 number:5 day:18 month:06 pages:2059-2070 https://dx.doi.org/10.1007/s11368-020-02682-4 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_183 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_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 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_2118 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 21 2020 5 18 06 2059-2070 |
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10.1007/s11368-020-02682-4 doi (DE-627)SPR043847250 (DE-599)SPRs11368-020-02682-4-e (SPR)s11368-020-02682-4-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Sobocká, Jaroslava verfasserin aut Mapping of urban environmentally sensitive areas in Bratislava city 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. The identification of the U-ESA can be used for solving of housing comfort and quality of living standards in the frame of urban development and balanced spatial urban planning. Environmentally sensitive areas (dpeaa)DE-He213 Urban soils (dpeaa)DE-He213 Pedo-urban complex (dpeaa)DE-He213 Urban heat island (dpeaa)DE-He213 Bratislava (dpeaa)DE-He213 Saksa, Martin verfasserin aut Feranec, Ján verfasserin aut Szatmári, Daniel verfasserin aut Holec, Juraj verfasserin aut Bobáľová, Hana verfasserin aut Rášová, Andrea verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 21(2020), 5 vom: 18. Juni, Seite 2059-2070 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:21 year:2020 number:5 day:18 month:06 pages:2059-2070 https://dx.doi.org/10.1007/s11368-020-02682-4 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_183 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_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 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_2118 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 21 2020 5 18 06 2059-2070 |
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10.1007/s11368-020-02682-4 doi (DE-627)SPR043847250 (DE-599)SPRs11368-020-02682-4-e (SPR)s11368-020-02682-4-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Sobocká, Jaroslava verfasserin aut Mapping of urban environmentally sensitive areas in Bratislava city 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. The identification of the U-ESA can be used for solving of housing comfort and quality of living standards in the frame of urban development and balanced spatial urban planning. Environmentally sensitive areas (dpeaa)DE-He213 Urban soils (dpeaa)DE-He213 Pedo-urban complex (dpeaa)DE-He213 Urban heat island (dpeaa)DE-He213 Bratislava (dpeaa)DE-He213 Saksa, Martin verfasserin aut Feranec, Ján verfasserin aut Szatmári, Daniel verfasserin aut Holec, Juraj verfasserin aut Bobáľová, Hana verfasserin aut Rášová, Andrea verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 21(2020), 5 vom: 18. Juni, Seite 2059-2070 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:21 year:2020 number:5 day:18 month:06 pages:2059-2070 https://dx.doi.org/10.1007/s11368-020-02682-4 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_183 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_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 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_2118 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 21 2020 5 18 06 2059-2070 |
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Enthalten in Journal of soils and sediments 21(2020), 5 vom: 18. Juni, Seite 2059-2070 volume:21 year:2020 number:5 day:18 month:06 pages:2059-2070 |
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Sobocká, Jaroslava @@aut@@ Saksa, Martin @@aut@@ Feranec, Ján @@aut@@ Szatmári, Daniel @@aut@@ Holec, Juraj @@aut@@ Bobáľová, Hana @@aut@@ Rášová, Andrea @@aut@@ |
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The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. 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Sobocká, Jaroslava |
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Sobocká, Jaroslava ddc 550 bkl 58.52 misc Environmentally sensitive areas misc Urban soils misc Pedo-urban complex misc Urban heat island misc Bratislava Mapping of urban environmentally sensitive areas in Bratislava city |
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550 ASE 58.52 bkl Mapping of urban environmentally sensitive areas in Bratislava city Environmentally sensitive areas (dpeaa)DE-He213 Urban soils (dpeaa)DE-He213 Pedo-urban complex (dpeaa)DE-He213 Urban heat island (dpeaa)DE-He213 Bratislava (dpeaa)DE-He213 |
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Sobocká, Jaroslava Saksa, Martin Feranec, Ján Szatmári, Daniel Holec, Juraj Bobáľová, Hana Rášová, Andrea |
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mapping of urban environmentally sensitive areas in bratislava city |
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Mapping of urban environmentally sensitive areas in Bratislava city |
| abstract |
Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. The identification of the U-ESA can be used for solving of housing comfort and quality of living standards in the frame of urban development and balanced spatial urban planning. |
| abstractGer |
Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. The identification of the U-ESA can be used for solving of housing comfort and quality of living standards in the frame of urban development and balanced spatial urban planning. |
| abstract_unstemmed |
Purpose Environmentally sensitive areas within urban environment (U-ESA) play an essential role in maintaining urban ecological balance and ecological safety. The aims of our study were to analyse and evaluate the U-ESA spatial distribution in Bratislava city, in terms of the impact of sealed area, soil quality and urban green areas infrastructure as well as the occurrence of urban heat island in the summer months. These phenomena significantly reduce the ecological functions and ecosystem services of urban soils and can result in negative affect of the living standard and health condition of urban population. Methods The methodology for assessing U-ESA is based on a multi-criteria process in which the following parameters have been identified and synthesized: pedo-urban complexes and their quality, urban heat island (UHI) areas and spatial distribution of urban vegetation types. Pedo-urban complexes (soil units including sealing areas, land use and soil degradation forms) were classified according to WRB. Results Georeferenced databases and maps became the basis for the identification of parameters involved within identification of U-ESA. Several partial products were compiled: vectorized land cover/land use categorized according to the Extended Nomenclature Urban Atlas 2012, database of pedo-urban complexes, modelled urban heat island map and map of urban vegetation types. Overlaying and synthesis of these partial results confirm thesis that sealed surfaces are one of the main causes of the increased incidence urban heat islands, but not entirely. The resulting U-ESA, designed areas in Bratislava, which are under increased risk in terms of quality of living standards. Conclusion The key point of the research in the future is to find assessment of the soil quality in urbanized areas. We assume that the assessment should be based on ecosystem functions of pedo-urban complexes, i.e. anthropogenic soils. The identification of the U-ESA can be used for solving of housing comfort and quality of living standards in the frame of urban development and balanced spatial urban planning. |
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| score |
7.399684 |