Seasonal Variation in Water Quality of River Subin in Kumasi
Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotomete...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Apau, Joseph [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2023 |
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| Anmerkung: |
© The Tunisian Chemical Society and Springer Nature Switzerland AG 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
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| Übergeordnetes Werk: |
Enthalten in: Chemistry Africa - Cham : Springer International Publishing, 2018, 6(2023), 4 vom: 15. März, Seite 2175-2185 |
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| Übergeordnetes Werk: |
volume:6 ; year:2023 ; number:4 ; day:15 ; month:03 ; pages:2175-2185 |
| Links: |
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| DOI / URN: |
10.1007/s42250-023-00637-z |
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SPR052621286 |
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| 520 | |a Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. During the wet season, concentrations in mg/L of metals present were Fe = 8.014 ± 0.225, Zn = 0.441 ± 7.00 × $ 10^{− 4} $, Pb = 0.461 ± 0.028, and Mn = 0.165 ± 3.05 × $ 10^{− 3} $. Metal concentrations were higher during the dry season than in the wet season probably due to dilution during the rainy season. The research also looked at some surface water’s physicochemical qualities. The other metrics are typically above or below the WHO criteria for drinkable water, with the exception of pH, which falls between 6.5 and 8.5, the WHO suggested limit for potable water. Principal component analysis indicated that anthropogenic activities and natural sources are responsible for the metals present. Surface water has been polluted by the metals discovered. The water quality of the river Subin in Kumasi may be classified as poor based on the measured elements and physicochemical characteristics. | ||
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| 650 | 4 | |a Anthropogenic activities |7 (dpeaa)DE-He213 | |
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| 700 | 1 | |a Coffie, David Osei Tutu |4 aut | |
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| 700 | 1 | |a Gyamfi, Opoku |4 aut | |
| 700 | 1 | |a Boateng, Godfred Owusu |4 aut | |
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10.1007/s42250-023-00637-z doi (DE-627)SPR052621286 (SPR)s42250-023-00637-z-e DE-627 ger DE-627 rakwb eng Apau, Joseph verfasserin aut Seasonal Variation in Water Quality of River Subin in Kumasi 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Tunisian Chemical Society and Springer Nature Switzerland AG 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. During the wet season, concentrations in mg/L of metals present were Fe = 8.014 ± 0.225, Zn = 0.441 ± 7.00 × $ 10^{− 4} $, Pb = 0.461 ± 0.028, and Mn = 0.165 ± 3.05 × $ 10^{− 3} $. Metal concentrations were higher during the dry season than in the wet season probably due to dilution during the rainy season. The research also looked at some surface water’s physicochemical qualities. The other metrics are typically above or below the WHO criteria for drinkable water, with the exception of pH, which falls between 6.5 and 8.5, the WHO suggested limit for potable water. Principal component analysis indicated that anthropogenic activities and natural sources are responsible for the metals present. Surface water has been polluted by the metals discovered. The water quality of the river Subin in Kumasi may be classified as poor based on the measured elements and physicochemical characteristics. Water pollution (dpeaa)DE-He213 Anthropogenic activities (dpeaa)DE-He213 Urban water supply (dpeaa)DE-He213 Coffie, David Osei Tutu aut Akoto, Osei aut Osei-Owusu, Jonathan aut Gyamfi, Opoku aut Boateng, Godfred Owusu aut Enthalten in Chemistry Africa Cham : Springer International Publishing, 2018 6(2023), 4 vom: 15. März, Seite 2175-2185 (DE-627)1028896840 (DE-600)2939117-9 2522-5766 nnns volume:6 year:2023 number:4 day:15 month:03 pages:2175-2185 https://dx.doi.org/10.1007/s42250-023-00637-z 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_138 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 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_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_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 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 AR 6 2023 4 15 03 2175-2185 |
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10.1007/s42250-023-00637-z doi (DE-627)SPR052621286 (SPR)s42250-023-00637-z-e DE-627 ger DE-627 rakwb eng Apau, Joseph verfasserin aut Seasonal Variation in Water Quality of River Subin in Kumasi 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Tunisian Chemical Society and Springer Nature Switzerland AG 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. During the wet season, concentrations in mg/L of metals present were Fe = 8.014 ± 0.225, Zn = 0.441 ± 7.00 × $ 10^{− 4} $, Pb = 0.461 ± 0.028, and Mn = 0.165 ± 3.05 × $ 10^{− 3} $. Metal concentrations were higher during the dry season than in the wet season probably due to dilution during the rainy season. The research also looked at some surface water’s physicochemical qualities. The other metrics are typically above or below the WHO criteria for drinkable water, with the exception of pH, which falls between 6.5 and 8.5, the WHO suggested limit for potable water. Principal component analysis indicated that anthropogenic activities and natural sources are responsible for the metals present. Surface water has been polluted by the metals discovered. The water quality of the river Subin in Kumasi may be classified as poor based on the measured elements and physicochemical characteristics. Water pollution (dpeaa)DE-He213 Anthropogenic activities (dpeaa)DE-He213 Urban water supply (dpeaa)DE-He213 Coffie, David Osei Tutu aut Akoto, Osei aut Osei-Owusu, Jonathan aut Gyamfi, Opoku aut Boateng, Godfred Owusu aut Enthalten in Chemistry Africa Cham : Springer International Publishing, 2018 6(2023), 4 vom: 15. März, Seite 2175-2185 (DE-627)1028896840 (DE-600)2939117-9 2522-5766 nnns volume:6 year:2023 number:4 day:15 month:03 pages:2175-2185 https://dx.doi.org/10.1007/s42250-023-00637-z 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_138 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 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_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_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 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 AR 6 2023 4 15 03 2175-2185 |
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10.1007/s42250-023-00637-z doi (DE-627)SPR052621286 (SPR)s42250-023-00637-z-e DE-627 ger DE-627 rakwb eng Apau, Joseph verfasserin aut Seasonal Variation in Water Quality of River Subin in Kumasi 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Tunisian Chemical Society and Springer Nature Switzerland AG 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. During the wet season, concentrations in mg/L of metals present were Fe = 8.014 ± 0.225, Zn = 0.441 ± 7.00 × $ 10^{− 4} $, Pb = 0.461 ± 0.028, and Mn = 0.165 ± 3.05 × $ 10^{− 3} $. Metal concentrations were higher during the dry season than in the wet season probably due to dilution during the rainy season. The research also looked at some surface water’s physicochemical qualities. The other metrics are typically above or below the WHO criteria for drinkable water, with the exception of pH, which falls between 6.5 and 8.5, the WHO suggested limit for potable water. Principal component analysis indicated that anthropogenic activities and natural sources are responsible for the metals present. Surface water has been polluted by the metals discovered. The water quality of the river Subin in Kumasi may be classified as poor based on the measured elements and physicochemical characteristics. Water pollution (dpeaa)DE-He213 Anthropogenic activities (dpeaa)DE-He213 Urban water supply (dpeaa)DE-He213 Coffie, David Osei Tutu aut Akoto, Osei aut Osei-Owusu, Jonathan aut Gyamfi, Opoku aut Boateng, Godfred Owusu aut Enthalten in Chemistry Africa Cham : Springer International Publishing, 2018 6(2023), 4 vom: 15. März, Seite 2175-2185 (DE-627)1028896840 (DE-600)2939117-9 2522-5766 nnns volume:6 year:2023 number:4 day:15 month:03 pages:2175-2185 https://dx.doi.org/10.1007/s42250-023-00637-z 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_138 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 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_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_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 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 AR 6 2023 4 15 03 2175-2185 |
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10.1007/s42250-023-00637-z doi (DE-627)SPR052621286 (SPR)s42250-023-00637-z-e DE-627 ger DE-627 rakwb eng Apau, Joseph verfasserin aut Seasonal Variation in Water Quality of River Subin in Kumasi 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Tunisian Chemical Society and Springer Nature Switzerland AG 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. During the wet season, concentrations in mg/L of metals present were Fe = 8.014 ± 0.225, Zn = 0.441 ± 7.00 × $ 10^{− 4} $, Pb = 0.461 ± 0.028, and Mn = 0.165 ± 3.05 × $ 10^{− 3} $. Metal concentrations were higher during the dry season than in the wet season probably due to dilution during the rainy season. The research also looked at some surface water’s physicochemical qualities. The other metrics are typically above or below the WHO criteria for drinkable water, with the exception of pH, which falls between 6.5 and 8.5, the WHO suggested limit for potable water. Principal component analysis indicated that anthropogenic activities and natural sources are responsible for the metals present. Surface water has been polluted by the metals discovered. The water quality of the river Subin in Kumasi may be classified as poor based on the measured elements and physicochemical characteristics. Water pollution (dpeaa)DE-He213 Anthropogenic activities (dpeaa)DE-He213 Urban water supply (dpeaa)DE-He213 Coffie, David Osei Tutu aut Akoto, Osei aut Osei-Owusu, Jonathan aut Gyamfi, Opoku aut Boateng, Godfred Owusu aut Enthalten in Chemistry Africa Cham : Springer International Publishing, 2018 6(2023), 4 vom: 15. März, Seite 2175-2185 (DE-627)1028896840 (DE-600)2939117-9 2522-5766 nnns volume:6 year:2023 number:4 day:15 month:03 pages:2175-2185 https://dx.doi.org/10.1007/s42250-023-00637-z 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_138 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 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_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_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 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 AR 6 2023 4 15 03 2175-2185 |
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10.1007/s42250-023-00637-z doi (DE-627)SPR052621286 (SPR)s42250-023-00637-z-e DE-627 ger DE-627 rakwb eng Apau, Joseph verfasserin aut Seasonal Variation in Water Quality of River Subin in Kumasi 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Tunisian Chemical Society and Springer Nature Switzerland AG 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. During the wet season, concentrations in mg/L of metals present were Fe = 8.014 ± 0.225, Zn = 0.441 ± 7.00 × $ 10^{− 4} $, Pb = 0.461 ± 0.028, and Mn = 0.165 ± 3.05 × $ 10^{− 3} $. Metal concentrations were higher during the dry season than in the wet season probably due to dilution during the rainy season. The research also looked at some surface water’s physicochemical qualities. The other metrics are typically above or below the WHO criteria for drinkable water, with the exception of pH, which falls between 6.5 and 8.5, the WHO suggested limit for potable water. Principal component analysis indicated that anthropogenic activities and natural sources are responsible for the metals present. Surface water has been polluted by the metals discovered. The water quality of the river Subin in Kumasi may be classified as poor based on the measured elements and physicochemical characteristics. Water pollution (dpeaa)DE-He213 Anthropogenic activities (dpeaa)DE-He213 Urban water supply (dpeaa)DE-He213 Coffie, David Osei Tutu aut Akoto, Osei aut Osei-Owusu, Jonathan aut Gyamfi, Opoku aut Boateng, Godfred Owusu aut Enthalten in Chemistry Africa Cham : Springer International Publishing, 2018 6(2023), 4 vom: 15. März, Seite 2175-2185 (DE-627)1028896840 (DE-600)2939117-9 2522-5766 nnns volume:6 year:2023 number:4 day:15 month:03 pages:2175-2185 https://dx.doi.org/10.1007/s42250-023-00637-z 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_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_138 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 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_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_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 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 AR 6 2023 4 15 03 2175-2185 |
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Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. 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seasonal variation in water quality of river subin in kumasi |
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Seasonal Variation in Water Quality of River Subin in Kumasi |
| abstract |
Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. During the wet season, concentrations in mg/L of metals present were Fe = 8.014 ± 0.225, Zn = 0.441 ± 7.00 × $ 10^{− 4} $, Pb = 0.461 ± 0.028, and Mn = 0.165 ± 3.05 × $ 10^{− 3} $. Metal concentrations were higher during the dry season than in the wet season probably due to dilution during the rainy season. The research also looked at some surface water’s physicochemical qualities. The other metrics are typically above or below the WHO criteria for drinkable water, with the exception of pH, which falls between 6.5 and 8.5, the WHO suggested limit for potable water. Principal component analysis indicated that anthropogenic activities and natural sources are responsible for the metals present. Surface water has been polluted by the metals discovered. The water quality of the river Subin in Kumasi may be classified as poor based on the measured elements and physicochemical characteristics. © The Tunisian Chemical Society and Springer Nature Switzerland AG 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
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Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. During the wet season, concentrations in mg/L of metals present were Fe = 8.014 ± 0.225, Zn = 0.441 ± 7.00 × $ 10^{− 4} $, Pb = 0.461 ± 0.028, and Mn = 0.165 ± 3.05 × $ 10^{− 3} $. Metal concentrations were higher during the dry season than in the wet season probably due to dilution during the rainy season. The research also looked at some surface water’s physicochemical qualities. The other metrics are typically above or below the WHO criteria for drinkable water, with the exception of pH, which falls between 6.5 and 8.5, the WHO suggested limit for potable water. Principal component analysis indicated that anthropogenic activities and natural sources are responsible for the metals present. Surface water has been polluted by the metals discovered. The water quality of the river Subin in Kumasi may be classified as poor based on the measured elements and physicochemical characteristics. © The Tunisian Chemical Society and Springer Nature Switzerland AG 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
| abstract_unstemmed |
Abstract Concentrations of iron, zinc, copper, silver, magnesium, nickel, chromium, cadmium and lead were analysed in water of river Subin in Kumasi during the dry and wet seasons. Water sample was digested and toxic heavy metal concentrations were determined using atomic absorption spectrophotometer. Maximum metal concentrations in mg/L during the dry season were Fe = 12.987 ± 0.220, Ni = 0.733 ± 0.028, Zn = 0.536 ± 4.40 × $ 10^{− 4} $, Cd = 0.737 ± 0.023, Pb = 1.244 ± 0.036, Mn = 0.225 ± 0.020, and Cr = 7.079 ± 2.00 × $ 10^{− 3} $. During the wet season, concentrations in mg/L of metals present were Fe = 8.014 ± 0.225, Zn = 0.441 ± 7.00 × $ 10^{− 4} $, Pb = 0.461 ± 0.028, and Mn = 0.165 ± 3.05 × $ 10^{− 3} $. Metal concentrations were higher during the dry season than in the wet season probably due to dilution during the rainy season. The research also looked at some surface water’s physicochemical qualities. The other metrics are typically above or below the WHO criteria for drinkable water, with the exception of pH, which falls between 6.5 and 8.5, the WHO suggested limit for potable water. Principal component analysis indicated that anthropogenic activities and natural sources are responsible for the metals present. Surface water has been polluted by the metals discovered. The water quality of the river Subin in Kumasi may be classified as poor based on the measured elements and physicochemical characteristics. © The Tunisian Chemical Society and Springer Nature Switzerland AG 2023. Springer Nature or its licensor (e.g. a society or other partner) holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law. |
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Seasonal Variation in Water Quality of River Subin in Kumasi |
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Coffie, David Osei Tutu Akoto, Osei Osei-Owusu, Jonathan Gyamfi, Opoku Boateng, Godfred Owusu |
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| score |
7.402337 |