Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates
Abstract This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, b...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Chen, Can [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2023 |
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| Anmerkung: |
© The Author(s), under exclusive licence to 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: Water, air & soil pollution - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971, 234(2023), 4 vom: Apr. |
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| Übergeordnetes Werk: |
volume:234 ; year:2023 ; number:4 ; month:04 |
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| DOI / URN: |
10.1007/s11270-023-06294-9 |
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| Katalog-ID: |
SPR050051679 |
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| 520 | |a Abstract This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. Biochar can promote Cd transformation to stable, less mobile forms, especially in < 0.053 mm, 0.053–0.25 mm, and 0.25–1 mm aggregates. | ||
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| 650 | 4 | |a Cd |7 (dpeaa)DE-He213 | |
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| 700 | 1 | |a Cai, Peng |4 aut | |
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10.1007/s11270-023-06294-9 doi (DE-627)SPR050051679 (SPR)s11270-023-06294-9-e DE-627 ger DE-627 rakwb eng Chen, Can verfasserin (orcid)0000-0003-3517-5567 aut Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to 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 This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. Biochar can promote Cd transformation to stable, less mobile forms, especially in < 0.053 mm, 0.053–0.25 mm, and 0.25–1 mm aggregates. Red paddy soil (dpeaa)DE-He213 Biochar addition (dpeaa)DE-He213 Soil aggregates (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Dai, Ziqiang aut Cai, Peng aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 234(2023), 4 vom: Apr. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:234 year:2023 number:4 month:04 https://dx.doi.org/10.1007/s11270-023-06294-9 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_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_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 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 234 2023 4 04 |
| spelling |
10.1007/s11270-023-06294-9 doi (DE-627)SPR050051679 (SPR)s11270-023-06294-9-e DE-627 ger DE-627 rakwb eng Chen, Can verfasserin (orcid)0000-0003-3517-5567 aut Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to 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 This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. Biochar can promote Cd transformation to stable, less mobile forms, especially in < 0.053 mm, 0.053–0.25 mm, and 0.25–1 mm aggregates. Red paddy soil (dpeaa)DE-He213 Biochar addition (dpeaa)DE-He213 Soil aggregates (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Dai, Ziqiang aut Cai, Peng aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 234(2023), 4 vom: Apr. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:234 year:2023 number:4 month:04 https://dx.doi.org/10.1007/s11270-023-06294-9 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_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_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 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 234 2023 4 04 |
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10.1007/s11270-023-06294-9 doi (DE-627)SPR050051679 (SPR)s11270-023-06294-9-e DE-627 ger DE-627 rakwb eng Chen, Can verfasserin (orcid)0000-0003-3517-5567 aut Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to 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 This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. Biochar can promote Cd transformation to stable, less mobile forms, especially in < 0.053 mm, 0.053–0.25 mm, and 0.25–1 mm aggregates. Red paddy soil (dpeaa)DE-He213 Biochar addition (dpeaa)DE-He213 Soil aggregates (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Dai, Ziqiang aut Cai, Peng aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 234(2023), 4 vom: Apr. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:234 year:2023 number:4 month:04 https://dx.doi.org/10.1007/s11270-023-06294-9 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_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_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 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 234 2023 4 04 |
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10.1007/s11270-023-06294-9 doi (DE-627)SPR050051679 (SPR)s11270-023-06294-9-e DE-627 ger DE-627 rakwb eng Chen, Can verfasserin (orcid)0000-0003-3517-5567 aut Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to 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 This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. Biochar can promote Cd transformation to stable, less mobile forms, especially in < 0.053 mm, 0.053–0.25 mm, and 0.25–1 mm aggregates. Red paddy soil (dpeaa)DE-He213 Biochar addition (dpeaa)DE-He213 Soil aggregates (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Dai, Ziqiang aut Cai, Peng aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 234(2023), 4 vom: Apr. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:234 year:2023 number:4 month:04 https://dx.doi.org/10.1007/s11270-023-06294-9 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_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_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 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 234 2023 4 04 |
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10.1007/s11270-023-06294-9 doi (DE-627)SPR050051679 (SPR)s11270-023-06294-9-e DE-627 ger DE-627 rakwb eng Chen, Can verfasserin (orcid)0000-0003-3517-5567 aut Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates 2023 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to 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 This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. Biochar can promote Cd transformation to stable, less mobile forms, especially in < 0.053 mm, 0.053–0.25 mm, and 0.25–1 mm aggregates. Red paddy soil (dpeaa)DE-He213 Biochar addition (dpeaa)DE-He213 Soil aggregates (dpeaa)DE-He213 Cd (dpeaa)DE-He213 Dai, Ziqiang aut Cai, Peng aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 234(2023), 4 vom: Apr. (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:234 year:2023 number:4 month:04 https://dx.doi.org/10.1007/s11270-023-06294-9 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_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_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 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 234 2023 4 04 |
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<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">SPR050051679</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230423064619.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">230417s2023 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s11270-023-06294-9</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR050051679</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s11270-023-06294-9-e</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Chen, Can</subfield><subfield code="e">verfasserin</subfield><subfield code="0">(orcid)0000-0003-3517-5567</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2023</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="500" ind1=" " ind2=" "><subfield code="a">© The Author(s), under exclusive licence to 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.</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. 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Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates Red paddy soil (dpeaa)DE-He213 Biochar addition (dpeaa)DE-He213 Soil aggregates (dpeaa)DE-He213 Cd (dpeaa)DE-He213 |
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impact of biochar addition on the extractable forms of cadmium in red paddy soil aggregates |
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Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates |
| abstract |
Abstract This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. Biochar can promote Cd transformation to stable, less mobile forms, especially in < 0.053 mm, 0.053–0.25 mm, and 0.25–1 mm aggregates. © The Author(s), under exclusive licence to 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 This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. Biochar can promote Cd transformation to stable, less mobile forms, especially in < 0.053 mm, 0.053–0.25 mm, and 0.25–1 mm aggregates. © The Author(s), under exclusive licence to 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 This study was conducted to understand the impact of biochar addition on the extractable forms of cadmium (Cd) in red paddy soil aggregates. Biochar was added once at five treatment rates (0, 10, 20, 30, and 40 t $ ha^{−1} $) in the soil surface (0–17 cm) and subsurface (17–29 cm) layers, before rice cultivation in March 2020. Soil samples were collected from both layers at rice maturity in October 2020. Soil physicochemical properties were measured according to Bao’s method. The various forms of cadmium were extracted by modified European Community Bureau of Reference (BCR) method, determined by ICP-MS. Soil aggregates were separated by wet sieving. The results showed that soil pH, soil organic matter (SOM), and cation exchange capacity (CEC) in both soil layers increased with the rate of biochar addition. Biochar applied at the high rate of 40 t $ ha^{−1} $ was the most effective in both soil layers. Biochar can promote the transformation of acid-soluble Cd forms into reducible and oxidizable forms in the soil. Correlation was analyzed between all fractions of Cd and soil physicochemical properties. The results showed that soil pH, SOM, and CEC were significantly correlated with different forms of Cd. Biochar can promote Cd transformation to stable, less mobile forms, especially in < 0.053 mm, 0.053–0.25 mm, and 0.25–1 mm aggregates. © The Author(s), under exclusive licence to 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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Impact of Biochar Addition on the Extractable Forms of Cadmium in Red Paddy Soil Aggregates |
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Dai, Ziqiang Cai, Peng |
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10.1007/s11270-023-06294-9 |
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2024-07-04T03:15:54.961Z |
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| score |
7.4002705 |