Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils
Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Liu, Zhaobing [verfasserIn] Huang, Ying [verfasserIn] Ji, Xionghui [verfasserIn] Xie, Yunhe [verfasserIn] Peng, Jianwei [verfasserIn] Eissa, Mamdouh A. [verfasserIn] Fahmy, Ahmed E. [verfasserIn] Abou-Elwafa, Salah F. [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2020 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Journal of soil science and plant nutrition - [Cham] : Springer International Publishing, 2010, 20(2020), 4 vom: 16. Juli, Seite 2316-2328 |
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| Übergeordnetes Werk: |
volume:20 ; year:2020 ; number:4 ; day:16 ; month:07 ; pages:2316-2328 |
| Links: |
|---|
| DOI / URN: |
10.1007/s42729-020-00297-9 |
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| Katalog-ID: |
SPR041888359 |
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| 520 | |a Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. Therefore, acid Cd-contaminated paddy fields can realize the safe production of rice by the continuous application of an appropriate amount of lime. | ||
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| 650 | 4 | |a Cadmium |7 (dpeaa)DE-He213 | |
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| 700 | 1 | |a Abou-Elwafa, Salah F. |e verfasserin |4 aut | |
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10.1007/s42729-020-00297-9 doi (DE-627)SPR041888359 (SPR)s42729-020-00297-9-e DE-627 ger DE-627 rakwb eng 630 570 ASE 580 630 ASE 48.30 bkl 58.52 bkl Liu, Zhaobing verfasserin aut Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. Therefore, acid Cd-contaminated paddy fields can realize the safe production of rice by the continuous application of an appropriate amount of lime. Rice (dpeaa)DE-He213 Lime application (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Paddy soils (dpeaa)DE-He213 Huang, Ying verfasserin aut Ji, Xionghui verfasserin aut Xie, Yunhe verfasserin aut Peng, Jianwei verfasserin aut Eissa, Mamdouh A. verfasserin aut Fahmy, Ahmed E. verfasserin aut Abou-Elwafa, Salah F. verfasserin aut Enthalten in Journal of soil science and plant nutrition [Cham] : Springer International Publishing, 2010 20(2020), 4 vom: 16. Juli, Seite 2316-2328 (DE-627)661265102 (DE-600)2611093-3 0718-9516 nnns volume:20 year:2020 number:4 day:16 month:07 pages:2316-2328 https://dx.doi.org/10.1007/s42729-020-00297-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-FOR SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 48.30 ASE 58.52 ASE AR 20 2020 4 16 07 2316-2328 |
| spelling |
10.1007/s42729-020-00297-9 doi (DE-627)SPR041888359 (SPR)s42729-020-00297-9-e DE-627 ger DE-627 rakwb eng 630 570 ASE 580 630 ASE 48.30 bkl 58.52 bkl Liu, Zhaobing verfasserin aut Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. Therefore, acid Cd-contaminated paddy fields can realize the safe production of rice by the continuous application of an appropriate amount of lime. Rice (dpeaa)DE-He213 Lime application (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Paddy soils (dpeaa)DE-He213 Huang, Ying verfasserin aut Ji, Xionghui verfasserin aut Xie, Yunhe verfasserin aut Peng, Jianwei verfasserin aut Eissa, Mamdouh A. verfasserin aut Fahmy, Ahmed E. verfasserin aut Abou-Elwafa, Salah F. verfasserin aut Enthalten in Journal of soil science and plant nutrition [Cham] : Springer International Publishing, 2010 20(2020), 4 vom: 16. Juli, Seite 2316-2328 (DE-627)661265102 (DE-600)2611093-3 0718-9516 nnns volume:20 year:2020 number:4 day:16 month:07 pages:2316-2328 https://dx.doi.org/10.1007/s42729-020-00297-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-FOR SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 48.30 ASE 58.52 ASE AR 20 2020 4 16 07 2316-2328 |
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10.1007/s42729-020-00297-9 doi (DE-627)SPR041888359 (SPR)s42729-020-00297-9-e DE-627 ger DE-627 rakwb eng 630 570 ASE 580 630 ASE 48.30 bkl 58.52 bkl Liu, Zhaobing verfasserin aut Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. Therefore, acid Cd-contaminated paddy fields can realize the safe production of rice by the continuous application of an appropriate amount of lime. Rice (dpeaa)DE-He213 Lime application (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Paddy soils (dpeaa)DE-He213 Huang, Ying verfasserin aut Ji, Xionghui verfasserin aut Xie, Yunhe verfasserin aut Peng, Jianwei verfasserin aut Eissa, Mamdouh A. verfasserin aut Fahmy, Ahmed E. verfasserin aut Abou-Elwafa, Salah F. verfasserin aut Enthalten in Journal of soil science and plant nutrition [Cham] : Springer International Publishing, 2010 20(2020), 4 vom: 16. Juli, Seite 2316-2328 (DE-627)661265102 (DE-600)2611093-3 0718-9516 nnns volume:20 year:2020 number:4 day:16 month:07 pages:2316-2328 https://dx.doi.org/10.1007/s42729-020-00297-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-FOR SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 48.30 ASE 58.52 ASE AR 20 2020 4 16 07 2316-2328 |
| allfieldsGer |
10.1007/s42729-020-00297-9 doi (DE-627)SPR041888359 (SPR)s42729-020-00297-9-e DE-627 ger DE-627 rakwb eng 630 570 ASE 580 630 ASE 48.30 bkl 58.52 bkl Liu, Zhaobing verfasserin aut Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. Therefore, acid Cd-contaminated paddy fields can realize the safe production of rice by the continuous application of an appropriate amount of lime. Rice (dpeaa)DE-He213 Lime application (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Paddy soils (dpeaa)DE-He213 Huang, Ying verfasserin aut Ji, Xionghui verfasserin aut Xie, Yunhe verfasserin aut Peng, Jianwei verfasserin aut Eissa, Mamdouh A. verfasserin aut Fahmy, Ahmed E. verfasserin aut Abou-Elwafa, Salah F. verfasserin aut Enthalten in Journal of soil science and plant nutrition [Cham] : Springer International Publishing, 2010 20(2020), 4 vom: 16. Juli, Seite 2316-2328 (DE-627)661265102 (DE-600)2611093-3 0718-9516 nnns volume:20 year:2020 number:4 day:16 month:07 pages:2316-2328 https://dx.doi.org/10.1007/s42729-020-00297-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-FOR SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 48.30 ASE 58.52 ASE AR 20 2020 4 16 07 2316-2328 |
| allfieldsSound |
10.1007/s42729-020-00297-9 doi (DE-627)SPR041888359 (SPR)s42729-020-00297-9-e DE-627 ger DE-627 rakwb eng 630 570 ASE 580 630 ASE 48.30 bkl 58.52 bkl Liu, Zhaobing verfasserin aut Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. Therefore, acid Cd-contaminated paddy fields can realize the safe production of rice by the continuous application of an appropriate amount of lime. Rice (dpeaa)DE-He213 Lime application (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Paddy soils (dpeaa)DE-He213 Huang, Ying verfasserin aut Ji, Xionghui verfasserin aut Xie, Yunhe verfasserin aut Peng, Jianwei verfasserin aut Eissa, Mamdouh A. verfasserin aut Fahmy, Ahmed E. verfasserin aut Abou-Elwafa, Salah F. verfasserin aut Enthalten in Journal of soil science and plant nutrition [Cham] : Springer International Publishing, 2010 20(2020), 4 vom: 16. Juli, Seite 2316-2328 (DE-627)661265102 (DE-600)2611093-3 0718-9516 nnns volume:20 year:2020 number:4 day:16 month:07 pages:2316-2328 https://dx.doi.org/10.1007/s42729-020-00297-9 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-FOR SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 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_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_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4367 GBV_ILN_4393 GBV_ILN_4700 48.30 ASE 58.52 ASE AR 20 2020 4 16 07 2316-2328 |
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English |
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Enthalten in Journal of soil science and plant nutrition 20(2020), 4 vom: 16. Juli, Seite 2316-2328 volume:20 year:2020 number:4 day:16 month:07 pages:2316-2328 |
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Enthalten in Journal of soil science and plant nutrition 20(2020), 4 vom: 16. Juli, Seite 2316-2328 volume:20 year:2020 number:4 day:16 month:07 pages:2316-2328 |
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Rice Lime application Cadmium Heavy metals Paddy soils |
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Journal of soil science and plant nutrition |
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Liu, Zhaobing @@aut@@ Huang, Ying @@aut@@ Ji, Xionghui @@aut@@ Xie, Yunhe @@aut@@ Peng, Jianwei @@aut@@ Eissa, Mamdouh A. @@aut@@ Fahmy, Ahmed E. @@aut@@ Abou-Elwafa, Salah F. @@aut@@ |
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2020-07-16T00:00:00Z |
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This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. 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Liu, Zhaobing |
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Liu, Zhaobing ddc 630 ddc 580 bkl 48.30 bkl 58.52 misc Rice misc Lime application misc Cadmium misc Heavy metals misc Paddy soils Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils |
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630 570 ASE 580 630 ASE 48.30 bkl 58.52 bkl Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils Rice (dpeaa)DE-He213 Lime application (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Heavy metals (dpeaa)DE-He213 Paddy soils (dpeaa)DE-He213 |
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ddc 630 ddc 580 bkl 48.30 bkl 58.52 misc Rice misc Lime application misc Cadmium misc Heavy metals misc Paddy soils |
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ddc 630 ddc 580 bkl 48.30 bkl 58.52 misc Rice misc Lime application misc Cadmium misc Heavy metals misc Paddy soils |
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ddc 630 ddc 580 bkl 48.30 bkl 58.52 misc Rice misc Lime application misc Cadmium misc Heavy metals misc Paddy soils |
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Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils |
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Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils |
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Liu, Zhaobing Huang, Ying Ji, Xionghui Xie, Yunhe Peng, Jianwei Eissa, Mamdouh A. Fahmy, Ahmed E. Abou-Elwafa, Salah F. |
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effects and mechanism of continuous liming on cadmium immobilization and uptake by rice grown on acid paddy soils |
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Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils |
| abstract |
Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. Therefore, acid Cd-contaminated paddy fields can realize the safe production of rice by the continuous application of an appropriate amount of lime. |
| abstractGer |
Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. Therefore, acid Cd-contaminated paddy fields can realize the safe production of rice by the continuous application of an appropriate amount of lime. |
| abstract_unstemmed |
Abstract Lime application is the most effective agricultural practice for the reduction of cadmium (Cd) bioavailability in acid soils. This study was conducted to investigate the impact of continuous liming across five consecutive growing seasons on the remediation of Cd in acid paddy soils, as well as rice yield. Two rice cultivars, i.e., Zhuliangyou 819 and Xiangwanxian 12, were cultivated in Cd-contaminated paddy soil for five consecutive growing seasons from 2014 to 2018. The investigated lime levels were 0, 450, 900, 1350, 1800, 2250, 3000, and 3750 kg $ ha^{−1} $. Lime application significantly increased rice yield, soil pH, exchangeable soil $ Ca^{2+} $, and rice calcium (Ca) contents; besides, it reduced soil and rice Cd contents. The application of lime at the rate of 1350–2250 kg $ ha^{−1} $ significantly increased rice yield. Under continuous liming, rice yield obviously increased first and then decreased with the cumulative application of lime. The application of a cumulative lime amount of 18,000 kg $ ha^{−1} $ was identified as the critical transition point of soil pH, soil Cd, and rice Cd content. Application of lime up to or above 3000 kg $ ha^{−1} $ per season reduced Cd content in brown rice below 0.20 mg $ kg^{−1} $. The results suggest that the reduction in effective Cd content might be a result of the combined action of exchangeable soil $ Ca^{2+} $ and soil pH rather than being a direct effect of $ Ca^{2+} $. Therefore, acid Cd-contaminated paddy fields can realize the safe production of rice by the continuous application of an appropriate amount of lime. |
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Effects and Mechanism of Continuous Liming on Cadmium Immobilization and Uptake by Rice Grown on Acid Paddy Soils |
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| score |
7.399417 |