Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey
Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotom...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Bakirdere, Sezgin [verfasserIn] Yaman, Mehmet [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2007 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Environmental monitoring and assessment - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1981, 136(2007), 1-3 vom: 23. März, Seite 401-410 |
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| Übergeordnetes Werk: |
volume:136 ; year:2007 ; number:1-3 ; day:23 ; month:03 ; pages:401-410 |
| Links: |
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| DOI / URN: |
10.1007/s10661-007-9695-1 |
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| Katalog-ID: |
SPR012211583 |
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| 245 | 1 | 0 | |a Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey |
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| 520 | |a Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. Standard reference material (SRM) was used to find the accuracy of the results of soil analyses. | ||
| 650 | 4 | |a Cadmium |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Copper |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Lead |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Plant leaves |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Roadside soil |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Traffic contamination |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Yaman, Mehmet |e verfasserin |4 aut | |
| 773 | 0 | 8 | |i Enthalten in |t Environmental monitoring and assessment |d Dordrecht [u.a.] : Springer Science + Business Media B.V, 1981 |g 136(2007), 1-3 vom: 23. März, Seite 401-410 |w (DE-627)31281738X |w (DE-600)2012242-1 |x 1573-2959 |7 nnns |
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10.1007/s10661-007-9695-1 doi (DE-627)SPR012211583 (SPR)s10661-007-9695-1-e DE-627 ger DE-627 rakwb eng 333.7 ASE 30.00 bkl 43.00 bkl Bakirdere, Sezgin verfasserin aut Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. Standard reference material (SRM) was used to find the accuracy of the results of soil analyses. Cadmium (dpeaa)DE-He213 Copper (dpeaa)DE-He213 Lead (dpeaa)DE-He213 Plant leaves (dpeaa)DE-He213 Roadside soil (dpeaa)DE-He213 Traffic contamination (dpeaa)DE-He213 Yaman, Mehmet verfasserin aut Enthalten in Environmental monitoring and assessment Dordrecht [u.a.] : Springer Science + Business Media B.V, 1981 136(2007), 1-3 vom: 23. März, Seite 401-410 (DE-627)31281738X (DE-600)2012242-1 1573-2959 nnns volume:136 year:2007 number:1-3 day:23 month:03 pages:401-410 https://dx.doi.org/10.1007/s10661-007-9695-1 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_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_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 30.00 ASE 43.00 ASE AR 136 2007 1-3 23 03 401-410 |
| spelling |
10.1007/s10661-007-9695-1 doi (DE-627)SPR012211583 (SPR)s10661-007-9695-1-e DE-627 ger DE-627 rakwb eng 333.7 ASE 30.00 bkl 43.00 bkl Bakirdere, Sezgin verfasserin aut Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. Standard reference material (SRM) was used to find the accuracy of the results of soil analyses. Cadmium (dpeaa)DE-He213 Copper (dpeaa)DE-He213 Lead (dpeaa)DE-He213 Plant leaves (dpeaa)DE-He213 Roadside soil (dpeaa)DE-He213 Traffic contamination (dpeaa)DE-He213 Yaman, Mehmet verfasserin aut Enthalten in Environmental monitoring and assessment Dordrecht [u.a.] : Springer Science + Business Media B.V, 1981 136(2007), 1-3 vom: 23. März, Seite 401-410 (DE-627)31281738X (DE-600)2012242-1 1573-2959 nnns volume:136 year:2007 number:1-3 day:23 month:03 pages:401-410 https://dx.doi.org/10.1007/s10661-007-9695-1 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_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_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 30.00 ASE 43.00 ASE AR 136 2007 1-3 23 03 401-410 |
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10.1007/s10661-007-9695-1 doi (DE-627)SPR012211583 (SPR)s10661-007-9695-1-e DE-627 ger DE-627 rakwb eng 333.7 ASE 30.00 bkl 43.00 bkl Bakirdere, Sezgin verfasserin aut Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. Standard reference material (SRM) was used to find the accuracy of the results of soil analyses. Cadmium (dpeaa)DE-He213 Copper (dpeaa)DE-He213 Lead (dpeaa)DE-He213 Plant leaves (dpeaa)DE-He213 Roadside soil (dpeaa)DE-He213 Traffic contamination (dpeaa)DE-He213 Yaman, Mehmet verfasserin aut Enthalten in Environmental monitoring and assessment Dordrecht [u.a.] : Springer Science + Business Media B.V, 1981 136(2007), 1-3 vom: 23. März, Seite 401-410 (DE-627)31281738X (DE-600)2012242-1 1573-2959 nnns volume:136 year:2007 number:1-3 day:23 month:03 pages:401-410 https://dx.doi.org/10.1007/s10661-007-9695-1 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_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_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 30.00 ASE 43.00 ASE AR 136 2007 1-3 23 03 401-410 |
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10.1007/s10661-007-9695-1 doi (DE-627)SPR012211583 (SPR)s10661-007-9695-1-e DE-627 ger DE-627 rakwb eng 333.7 ASE 30.00 bkl 43.00 bkl Bakirdere, Sezgin verfasserin aut Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. Standard reference material (SRM) was used to find the accuracy of the results of soil analyses. Cadmium (dpeaa)DE-He213 Copper (dpeaa)DE-He213 Lead (dpeaa)DE-He213 Plant leaves (dpeaa)DE-He213 Roadside soil (dpeaa)DE-He213 Traffic contamination (dpeaa)DE-He213 Yaman, Mehmet verfasserin aut Enthalten in Environmental monitoring and assessment Dordrecht [u.a.] : Springer Science + Business Media B.V, 1981 136(2007), 1-3 vom: 23. März, Seite 401-410 (DE-627)31281738X (DE-600)2012242-1 1573-2959 nnns volume:136 year:2007 number:1-3 day:23 month:03 pages:401-410 https://dx.doi.org/10.1007/s10661-007-9695-1 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_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_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 30.00 ASE 43.00 ASE AR 136 2007 1-3 23 03 401-410 |
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10.1007/s10661-007-9695-1 doi (DE-627)SPR012211583 (SPR)s10661-007-9695-1-e DE-627 ger DE-627 rakwb eng 333.7 ASE 30.00 bkl 43.00 bkl Bakirdere, Sezgin verfasserin aut Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. Standard reference material (SRM) was used to find the accuracy of the results of soil analyses. Cadmium (dpeaa)DE-He213 Copper (dpeaa)DE-He213 Lead (dpeaa)DE-He213 Plant leaves (dpeaa)DE-He213 Roadside soil (dpeaa)DE-He213 Traffic contamination (dpeaa)DE-He213 Yaman, Mehmet verfasserin aut Enthalten in Environmental monitoring and assessment Dordrecht [u.a.] : Springer Science + Business Media B.V, 1981 136(2007), 1-3 vom: 23. März, Seite 401-410 (DE-627)31281738X (DE-600)2012242-1 1573-2959 nnns volume:136 year:2007 number:1-3 day:23 month:03 pages:401-410 https://dx.doi.org/10.1007/s10661-007-9695-1 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_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_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 30.00 ASE 43.00 ASE AR 136 2007 1-3 23 03 401-410 |
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Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. 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Bakirdere, Sezgin |
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Bakirdere, Sezgin ddc 333.7 bkl 30.00 bkl 43.00 misc Cadmium misc Copper misc Lead misc Plant leaves misc Roadside soil misc Traffic contamination Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey |
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333.7 ASE 30.00 bkl 43.00 bkl Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey Cadmium (dpeaa)DE-He213 Copper (dpeaa)DE-He213 Lead (dpeaa)DE-He213 Plant leaves (dpeaa)DE-He213 Roadside soil (dpeaa)DE-He213 Traffic contamination (dpeaa)DE-He213 |
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ddc 333.7 bkl 30.00 bkl 43.00 misc Cadmium misc Copper misc Lead misc Plant leaves misc Roadside soil misc Traffic contamination |
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ddc 333.7 bkl 30.00 bkl 43.00 misc Cadmium misc Copper misc Lead misc Plant leaves misc Roadside soil misc Traffic contamination |
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Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey |
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Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey |
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determination of lead, cadmium and copper in roadside soil and plants in elazig, turkey |
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Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey |
| abstract |
Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. Standard reference material (SRM) was used to find the accuracy of the results of soil analyses. |
| abstractGer |
Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. Standard reference material (SRM) was used to find the accuracy of the results of soil analyses. |
| abstract_unstemmed |
Abstract The concentrations of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey were investigated. Soil samples were collected at distances of 0, 25 and 50 m from the roadside. The concentrations of lead, cadmium and copper were measured by Flame Atomic Absorption Spectrophotometry (FAAS). A slotted tube atom trap (STAT) was used to increase the sensitivity of lead and cadmium in FAAS. Lead concentrations in soil samples varied from 1.3 to 45 mg $ kg^{−1} $ while mean lead levels in plants ranged from120 ng $ g^{−1} $ for grape in point-4 to 866 ng $ g^{−1} $ for apple leaves in point-2. Lead analyses showed that there was a considerable contamination in both soil and plants affected from traffic intensity. Overall level of Cd in soil samples lies between 78 and 527 ng/g while cadmium concentration in different vegetations varied in the range of 0.8–98.0 ng $ g^{−1} $. Concentrations of copper in soil and plant samples were found in the range of 11.1–27.9 mg $ kg^{−1} $ for soil and 0.8–5.6 mg $ kg^{−1} $ for plants. Standard reference material (SRM) was used to find the accuracy of the results of soil analyses. |
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| container_issue |
1-3 |
| title_short |
Determination of lead, cadmium and copper in roadside soil and plants in Elazig, Turkey |
| url |
https://dx.doi.org/10.1007/s10661-007-9695-1 |
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| author2 |
Yaman, Mehmet |
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| doi_str |
10.1007/s10661-007-9695-1 |
| up_date |
2024-07-04T02:15:03.067Z |
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| score |
7.3985834 |