Reciprocal effects of copper and zinc in plants
Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu...
Ausführliche Beschreibung
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| Autor*in: |
Liščáková, P. [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2022 |
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| Schlagwörter: |
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| Anmerkung: |
© Islamic Azad University (IAU) 2021 |
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| Übergeordnetes Werk: |
Enthalten in: International journal of environmental science and technology - Tehran : Islamic Azad University, 2004, 19(2022), 9 vom: 25. Jan., Seite 9297-9312 |
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| Übergeordnetes Werk: |
volume:19 ; year:2022 ; number:9 ; day:25 ; month:01 ; pages:9297-9312 |
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| DOI / URN: |
10.1007/s13762-021-03854-6 |
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| Katalog-ID: |
SPR047798823 |
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| 245 | 1 | 0 | |a Reciprocal effects of copper and zinc in plants |
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| 520 | |a Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. This study can help with future investigations dealing with a similar issue and with the selection of suitable plants to be planted in Cu and Zn contaminated sites. | ||
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| 650 | 4 | |a Zinc |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Antagonistic effect |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Bioaccumulation |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Oxidation stress |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Reciprocal effect |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Heavy metals |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Nawaz, A. |4 aut | |
| 700 | 1 | |a Molnárová, M. |4 aut | |
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10.1007/s13762-021-03854-6 doi (DE-627)SPR047798823 (SPR)s13762-021-03854-6-e DE-627 ger DE-627 rakwb eng Liščáková, P. verfasserin aut Reciprocal effects of copper and zinc in plants 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Islamic Azad University (IAU) 2021 Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. This study can help with future investigations dealing with a similar issue and with the selection of suitable plants to be planted in Cu and Zn contaminated sites. Copper (dpeaa)DE-He213 Zinc (dpeaa)DE-He213 Antagonistic effect (dpeaa)DE-He213 Bioaccumulation (dpeaa)DE-He213 Oxidation stress (dpeaa)DE-He213 Reciprocal effect (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Nawaz, A. aut Molnárová, M. aut Enthalten in International journal of environmental science and technology Tehran : Islamic Azad University, 2004 19(2022), 9 vom: 25. Jan., Seite 9297-9312 (DE-627)510463398 (DE-600)2230399-6 1735-2630 nnns volume:19 year:2022 number:9 day:25 month:01 pages:9297-9312 https://dx.doi.org/10.1007/s13762-021-03854-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_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_2232 GBV_ILN_2336 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 AR 19 2022 9 25 01 9297-9312 |
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10.1007/s13762-021-03854-6 doi (DE-627)SPR047798823 (SPR)s13762-021-03854-6-e DE-627 ger DE-627 rakwb eng Liščáková, P. verfasserin aut Reciprocal effects of copper and zinc in plants 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Islamic Azad University (IAU) 2021 Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. This study can help with future investigations dealing with a similar issue and with the selection of suitable plants to be planted in Cu and Zn contaminated sites. Copper (dpeaa)DE-He213 Zinc (dpeaa)DE-He213 Antagonistic effect (dpeaa)DE-He213 Bioaccumulation (dpeaa)DE-He213 Oxidation stress (dpeaa)DE-He213 Reciprocal effect (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Nawaz, A. aut Molnárová, M. aut Enthalten in International journal of environmental science and technology Tehran : Islamic Azad University, 2004 19(2022), 9 vom: 25. Jan., Seite 9297-9312 (DE-627)510463398 (DE-600)2230399-6 1735-2630 nnns volume:19 year:2022 number:9 day:25 month:01 pages:9297-9312 https://dx.doi.org/10.1007/s13762-021-03854-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_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_2232 GBV_ILN_2336 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 AR 19 2022 9 25 01 9297-9312 |
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10.1007/s13762-021-03854-6 doi (DE-627)SPR047798823 (SPR)s13762-021-03854-6-e DE-627 ger DE-627 rakwb eng Liščáková, P. verfasserin aut Reciprocal effects of copper and zinc in plants 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Islamic Azad University (IAU) 2021 Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. This study can help with future investigations dealing with a similar issue and with the selection of suitable plants to be planted in Cu and Zn contaminated sites. Copper (dpeaa)DE-He213 Zinc (dpeaa)DE-He213 Antagonistic effect (dpeaa)DE-He213 Bioaccumulation (dpeaa)DE-He213 Oxidation stress (dpeaa)DE-He213 Reciprocal effect (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Nawaz, A. aut Molnárová, M. aut Enthalten in International journal of environmental science and technology Tehran : Islamic Azad University, 2004 19(2022), 9 vom: 25. Jan., Seite 9297-9312 (DE-627)510463398 (DE-600)2230399-6 1735-2630 nnns volume:19 year:2022 number:9 day:25 month:01 pages:9297-9312 https://dx.doi.org/10.1007/s13762-021-03854-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_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_2232 GBV_ILN_2336 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 AR 19 2022 9 25 01 9297-9312 |
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10.1007/s13762-021-03854-6 doi (DE-627)SPR047798823 (SPR)s13762-021-03854-6-e DE-627 ger DE-627 rakwb eng Liščáková, P. verfasserin aut Reciprocal effects of copper and zinc in plants 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Islamic Azad University (IAU) 2021 Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. This study can help with future investigations dealing with a similar issue and with the selection of suitable plants to be planted in Cu and Zn contaminated sites. Copper (dpeaa)DE-He213 Zinc (dpeaa)DE-He213 Antagonistic effect (dpeaa)DE-He213 Bioaccumulation (dpeaa)DE-He213 Oxidation stress (dpeaa)DE-He213 Reciprocal effect (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Nawaz, A. aut Molnárová, M. aut Enthalten in International journal of environmental science and technology Tehran : Islamic Azad University, 2004 19(2022), 9 vom: 25. Jan., Seite 9297-9312 (DE-627)510463398 (DE-600)2230399-6 1735-2630 nnns volume:19 year:2022 number:9 day:25 month:01 pages:9297-9312 https://dx.doi.org/10.1007/s13762-021-03854-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_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_2232 GBV_ILN_2336 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 AR 19 2022 9 25 01 9297-9312 |
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10.1007/s13762-021-03854-6 doi (DE-627)SPR047798823 (SPR)s13762-021-03854-6-e DE-627 ger DE-627 rakwb eng Liščáková, P. verfasserin aut Reciprocal effects of copper and zinc in plants 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Islamic Azad University (IAU) 2021 Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. This study can help with future investigations dealing with a similar issue and with the selection of suitable plants to be planted in Cu and Zn contaminated sites. Copper (dpeaa)DE-He213 Zinc (dpeaa)DE-He213 Antagonistic effect (dpeaa)DE-He213 Bioaccumulation (dpeaa)DE-He213 Oxidation stress (dpeaa)DE-He213 Reciprocal effect (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Nawaz, A. aut Molnárová, M. aut Enthalten in International journal of environmental science and technology Tehran : Islamic Azad University, 2004 19(2022), 9 vom: 25. Jan., Seite 9297-9312 (DE-627)510463398 (DE-600)2230399-6 1735-2630 nnns volume:19 year:2022 number:9 day:25 month:01 pages:9297-9312 https://dx.doi.org/10.1007/s13762-021-03854-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_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_2232 GBV_ILN_2336 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 AR 19 2022 9 25 01 9297-9312 |
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Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. 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Liščáková, P. |
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Liščáková, P. misc Copper misc Zinc misc Antagonistic effect misc Bioaccumulation misc Oxidation stress misc Reciprocal effect misc Heavy metals Reciprocal effects of copper and zinc in plants |
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Reciprocal effects of copper and zinc in plants Copper (dpeaa)DE-He213 Zinc (dpeaa)DE-He213 Antagonistic effect (dpeaa)DE-He213 Bioaccumulation (dpeaa)DE-He213 Oxidation stress (dpeaa)DE-He213 Reciprocal effect (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 |
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Reciprocal effects of copper and zinc in plants |
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Reciprocal effects of copper and zinc in plants |
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Liščáková, P. |
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International journal of environmental science and technology |
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Liščáková, P. |
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10.1007/s13762-021-03854-6 |
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reciprocal effects of copper and zinc in plants |
| title_auth |
Reciprocal effects of copper and zinc in plants |
| abstract |
Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. This study can help with future investigations dealing with a similar issue and with the selection of suitable plants to be planted in Cu and Zn contaminated sites. © Islamic Azad University (IAU) 2021 |
| abstractGer |
Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. This study can help with future investigations dealing with a similar issue and with the selection of suitable plants to be planted in Cu and Zn contaminated sites. © Islamic Azad University (IAU) 2021 |
| abstract_unstemmed |
Abstract Copper and zinc are, together with other metals, highly occurring in the environment. Cu enters the environment artificially mainly through biocides or fungicides, which were applied, for example, to vineyards but also elsewhere in agriculture in recent years. Due to the toxic effects of Cu on flora and fauna, various studies have begun to examine the suitability of replacing Cu with Zn, which is more tolerable for plants. This review is a research about published articles focused on reciprocal effects of copper and zinc in plants. Comparison of the Cu and Zn effects in the mixture and as individual metals revealed that most of the interactions were antagonistic. Reciprocal effects between Cu and Zn can affect also other metals. In combination with Fe, they can reduce its translocation to above-ground parts of plants. The presence of Pb can enhance Zn uptake and their overall relation might be synergic. Increasing toxicity in plants caused by synergic effects can lead for example to leaf chlorosis, growth inhibition, decreasing of chlorophyll a and b and total carotenoids, oxidation stress, which have been observed for Pisum sativum, Phaseolus vulgaris, Glycine max and others. This study can help with future investigations dealing with a similar issue and with the selection of suitable plants to be planted in Cu and Zn contaminated sites. © Islamic Azad University (IAU) 2021 |
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Reciprocal effects of copper and zinc in plants |
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https://dx.doi.org/10.1007/s13762-021-03854-6 |
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Nawaz, A. Molnárová, M. |
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10.1007/s13762-021-03854-6 |
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2024-07-03T15:03:08.445Z |
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|
| score |
7.399583 |