Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay
Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Res...
Ausführliche Beschreibung
Autor*in: |
Mikulic, N. [verfasserIn] |
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E-Artikel |
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Sprache: |
Englisch |
Erschienen: |
2004 |
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Anmerkung: |
© Springer-Verlag 2004 |
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Übergeordnetes Werk: |
Enthalten in: Environmental geology - Berlin : Springer, 1975, 46(2004), 1 vom: 24. März, Seite 62-70 |
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Übergeordnetes Werk: |
volume:46 ; year:2004 ; number:1 ; day:24 ; month:03 ; pages:62-70 |
Links: |
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DOI / URN: |
10.1007/s00254-004-1015-2 |
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Katalog-ID: |
SPR003045951 |
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520 | |a Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments. | ||
650 | 4 | |a Cu, Pb, Zn pollution |7 (dpeaa)DE-He213 | |
650 | 4 | |a Long-range transport |7 (dpeaa)DE-He213 | |
650 | 4 | |a Traffic |7 (dpeaa)DE-He213 | |
650 | 4 | |a Antifouling paints |7 (dpeaa)DE-He213 | |
650 | 4 | |a Croatia |7 (dpeaa)DE-He213 | |
650 | 4 | |a Punat Bay sediments |7 (dpeaa)DE-He213 | |
700 | 1 | |a Orescanin, V. |4 aut | |
700 | 1 | |a Legovic, T. |4 aut | |
700 | 1 | |a Zugaj, R. |4 aut | |
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10.1007/s00254-004-1015-2 doi (DE-627)SPR003045951 (SPR)s00254-004-1015-2-e DE-627 ger DE-627 rakwb eng Mikulic, N. verfasserin aut Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2004 Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments. Cu, Pb, Zn pollution (dpeaa)DE-He213 Long-range transport (dpeaa)DE-He213 Traffic (dpeaa)DE-He213 Antifouling paints (dpeaa)DE-He213 Croatia (dpeaa)DE-He213 Punat Bay sediments (dpeaa)DE-He213 Orescanin, V. aut Legovic, T. aut Zugaj, R. aut Enthalten in Environmental geology Berlin : Springer, 1975 46(2004), 1 vom: 24. März, Seite 62-70 (DE-627)253722586 (DE-600)1459034-7 1432-0495 nnns volume:46 year:2004 number:1 day:24 month:03 pages:62-70 https://dx.doi.org/10.1007/s00254-004-1015-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_20 GBV_ILN_24 GBV_ILN_31 GBV_ILN_40 GBV_ILN_63 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_110 GBV_ILN_120 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_267 GBV_ILN_285 GBV_ILN_293 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2055 GBV_ILN_2059 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2106 GBV_ILN_2108 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_4012 GBV_ILN_4035 GBV_ILN_4037 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_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4338 AR 46 2004 1 24 03 62-70 |
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10.1007/s00254-004-1015-2 doi (DE-627)SPR003045951 (SPR)s00254-004-1015-2-e DE-627 ger DE-627 rakwb eng Mikulic, N. verfasserin aut Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2004 Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments. Cu, Pb, Zn pollution (dpeaa)DE-He213 Long-range transport (dpeaa)DE-He213 Traffic (dpeaa)DE-He213 Antifouling paints (dpeaa)DE-He213 Croatia (dpeaa)DE-He213 Punat Bay sediments (dpeaa)DE-He213 Orescanin, V. aut Legovic, T. aut Zugaj, R. aut Enthalten in Environmental geology Berlin : Springer, 1975 46(2004), 1 vom: 24. März, Seite 62-70 (DE-627)253722586 (DE-600)1459034-7 1432-0495 nnns volume:46 year:2004 number:1 day:24 month:03 pages:62-70 https://dx.doi.org/10.1007/s00254-004-1015-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_20 GBV_ILN_24 GBV_ILN_31 GBV_ILN_40 GBV_ILN_63 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_110 GBV_ILN_120 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_267 GBV_ILN_285 GBV_ILN_293 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2055 GBV_ILN_2059 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2106 GBV_ILN_2108 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_4012 GBV_ILN_4035 GBV_ILN_4037 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_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4338 AR 46 2004 1 24 03 62-70 |
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10.1007/s00254-004-1015-2 doi (DE-627)SPR003045951 (SPR)s00254-004-1015-2-e DE-627 ger DE-627 rakwb eng Mikulic, N. verfasserin aut Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2004 Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments. Cu, Pb, Zn pollution (dpeaa)DE-He213 Long-range transport (dpeaa)DE-He213 Traffic (dpeaa)DE-He213 Antifouling paints (dpeaa)DE-He213 Croatia (dpeaa)DE-He213 Punat Bay sediments (dpeaa)DE-He213 Orescanin, V. aut Legovic, T. aut Zugaj, R. aut Enthalten in Environmental geology Berlin : Springer, 1975 46(2004), 1 vom: 24. März, Seite 62-70 (DE-627)253722586 (DE-600)1459034-7 1432-0495 nnns volume:46 year:2004 number:1 day:24 month:03 pages:62-70 https://dx.doi.org/10.1007/s00254-004-1015-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_20 GBV_ILN_24 GBV_ILN_31 GBV_ILN_40 GBV_ILN_63 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_110 GBV_ILN_120 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_267 GBV_ILN_285 GBV_ILN_293 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2055 GBV_ILN_2059 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2106 GBV_ILN_2108 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_4012 GBV_ILN_4035 GBV_ILN_4037 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_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4338 AR 46 2004 1 24 03 62-70 |
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10.1007/s00254-004-1015-2 doi (DE-627)SPR003045951 (SPR)s00254-004-1015-2-e DE-627 ger DE-627 rakwb eng Mikulic, N. verfasserin aut Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2004 Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments. Cu, Pb, Zn pollution (dpeaa)DE-He213 Long-range transport (dpeaa)DE-He213 Traffic (dpeaa)DE-He213 Antifouling paints (dpeaa)DE-He213 Croatia (dpeaa)DE-He213 Punat Bay sediments (dpeaa)DE-He213 Orescanin, V. aut Legovic, T. aut Zugaj, R. aut Enthalten in Environmental geology Berlin : Springer, 1975 46(2004), 1 vom: 24. März, Seite 62-70 (DE-627)253722586 (DE-600)1459034-7 1432-0495 nnns volume:46 year:2004 number:1 day:24 month:03 pages:62-70 https://dx.doi.org/10.1007/s00254-004-1015-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_20 GBV_ILN_24 GBV_ILN_31 GBV_ILN_40 GBV_ILN_63 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_110 GBV_ILN_120 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_267 GBV_ILN_285 GBV_ILN_293 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2055 GBV_ILN_2059 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2106 GBV_ILN_2108 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_4012 GBV_ILN_4035 GBV_ILN_4037 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_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4338 AR 46 2004 1 24 03 62-70 |
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10.1007/s00254-004-1015-2 doi (DE-627)SPR003045951 (SPR)s00254-004-1015-2-e DE-627 ger DE-627 rakwb eng Mikulic, N. verfasserin aut Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay 2004 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2004 Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments. Cu, Pb, Zn pollution (dpeaa)DE-He213 Long-range transport (dpeaa)DE-He213 Traffic (dpeaa)DE-He213 Antifouling paints (dpeaa)DE-He213 Croatia (dpeaa)DE-He213 Punat Bay sediments (dpeaa)DE-He213 Orescanin, V. aut Legovic, T. aut Zugaj, R. aut Enthalten in Environmental geology Berlin : Springer, 1975 46(2004), 1 vom: 24. März, Seite 62-70 (DE-627)253722586 (DE-600)1459034-7 1432-0495 nnns volume:46 year:2004 number:1 day:24 month:03 pages:62-70 https://dx.doi.org/10.1007/s00254-004-1015-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_20 GBV_ILN_24 GBV_ILN_31 GBV_ILN_40 GBV_ILN_63 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_110 GBV_ILN_120 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_267 GBV_ILN_285 GBV_ILN_293 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2007 GBV_ILN_2009 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2018 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2055 GBV_ILN_2059 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2106 GBV_ILN_2108 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_4012 GBV_ILN_4035 GBV_ILN_4037 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_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4338 AR 46 2004 1 24 03 62-70 |
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Mikulic, N. misc Cu, Pb, Zn pollution misc Long-range transport misc Traffic misc Antifouling paints misc Croatia misc Punat Bay sediments Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay |
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Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay Cu, Pb, Zn pollution (dpeaa)DE-He213 Long-range transport (dpeaa)DE-He213 Traffic (dpeaa)DE-He213 Antifouling paints (dpeaa)DE-He213 Croatia (dpeaa)DE-He213 Punat Bay sediments (dpeaa)DE-He213 |
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misc Cu, Pb, Zn pollution misc Long-range transport misc Traffic misc Antifouling paints misc Croatia misc Punat Bay sediments |
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Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay |
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estimation of heavy metals (cu, zn, pb) input into punat bay |
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Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay |
abstract |
Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments. © Springer-Verlag 2004 |
abstractGer |
Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments. © Springer-Verlag 2004 |
abstract_unstemmed |
Abstract The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments. © Springer-Verlag 2004 |
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Estimation of heavy metals (Cu, Zn, Pb) input into Punat Bay |
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