Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions
Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transport...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Yuan, Zaijian [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: |
© The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2022 |
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| Übergeordnetes Werk: |
Enthalten in: Environmental science and pollution research - Berlin : Springer, 1994, 29(2022), 55 vom: 01. Juli, Seite 83969-83980 |
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| Übergeordnetes Werk: |
volume:29 ; year:2022 ; number:55 ; day:01 ; month:07 ; pages:83969-83980 |
| Links: |
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| DOI / URN: |
10.1007/s11356-022-21623-x |
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| Katalog-ID: |
SPR048572608 |
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| 520 | |a Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. Excessively high level (7%) of biochar application may aggravate soil erosion and result in more Cd loss. | ||
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| 650 | 4 | |a Simulated rainfall |7 (dpeaa)DE-He213 | |
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| 650 | 4 | |a Aggregate stability |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Cadmium |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Acidic red soil |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Song, Yueyan |4 aut | |
| 700 | 1 | |a Li, Dingqiang |4 aut | |
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| 700 | 1 | |a Chen, Yunhui |4 aut | |
| 700 | 1 | |a Ge, Xiaojun |4 aut | |
| 700 | 1 | |a Zheng, Mingguo |4 aut | |
| 700 | 1 | |a Liao, Yishan |4 aut | |
| 700 | 1 | |a Xie, Zhenyue |4 aut | |
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10.1007/s11356-022-21623-x doi (DE-627)SPR048572608 (SPR)s11356-022-21623-x-e DE-627 ger DE-627 rakwb eng Yuan, Zaijian verfasserin aut Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2022 Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. Excessively high level (7%) of biochar application may aggravate soil erosion and result in more Cd loss. Biochar (dpeaa)DE-He213 Simulated rainfall (dpeaa)DE-He213 Water erosion (dpeaa)DE-He213 Aggregate stability (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Acidic red soil (dpeaa)DE-He213 Song, Yueyan aut Li, Dingqiang aut Huang, Bin (orcid)0000-0003-0875-0722 aut Chen, Yunhui aut Ge, Xiaojun aut Zheng, Mingguo aut Liao, Yishan aut Xie, Zhenyue aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 29(2022), 55 vom: 01. Juli, Seite 83969-83980 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:29 year:2022 number:55 day:01 month:07 pages:83969-83980 https://dx.doi.org/10.1007/s11356-022-21623-x 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_381 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 29 2022 55 01 07 83969-83980 |
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10.1007/s11356-022-21623-x doi (DE-627)SPR048572608 (SPR)s11356-022-21623-x-e DE-627 ger DE-627 rakwb eng Yuan, Zaijian verfasserin aut Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2022 Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. Excessively high level (7%) of biochar application may aggravate soil erosion and result in more Cd loss. Biochar (dpeaa)DE-He213 Simulated rainfall (dpeaa)DE-He213 Water erosion (dpeaa)DE-He213 Aggregate stability (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Acidic red soil (dpeaa)DE-He213 Song, Yueyan aut Li, Dingqiang aut Huang, Bin (orcid)0000-0003-0875-0722 aut Chen, Yunhui aut Ge, Xiaojun aut Zheng, Mingguo aut Liao, Yishan aut Xie, Zhenyue aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 29(2022), 55 vom: 01. Juli, Seite 83969-83980 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:29 year:2022 number:55 day:01 month:07 pages:83969-83980 https://dx.doi.org/10.1007/s11356-022-21623-x 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_381 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 29 2022 55 01 07 83969-83980 |
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10.1007/s11356-022-21623-x doi (DE-627)SPR048572608 (SPR)s11356-022-21623-x-e DE-627 ger DE-627 rakwb eng Yuan, Zaijian verfasserin aut Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2022 Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. Excessively high level (7%) of biochar application may aggravate soil erosion and result in more Cd loss. Biochar (dpeaa)DE-He213 Simulated rainfall (dpeaa)DE-He213 Water erosion (dpeaa)DE-He213 Aggregate stability (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Acidic red soil (dpeaa)DE-He213 Song, Yueyan aut Li, Dingqiang aut Huang, Bin (orcid)0000-0003-0875-0722 aut Chen, Yunhui aut Ge, Xiaojun aut Zheng, Mingguo aut Liao, Yishan aut Xie, Zhenyue aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 29(2022), 55 vom: 01. Juli, Seite 83969-83980 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:29 year:2022 number:55 day:01 month:07 pages:83969-83980 https://dx.doi.org/10.1007/s11356-022-21623-x 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_381 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 29 2022 55 01 07 83969-83980 |
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10.1007/s11356-022-21623-x doi (DE-627)SPR048572608 (SPR)s11356-022-21623-x-e DE-627 ger DE-627 rakwb eng Yuan, Zaijian verfasserin aut Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2022 Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. Excessively high level (7%) of biochar application may aggravate soil erosion and result in more Cd loss. Biochar (dpeaa)DE-He213 Simulated rainfall (dpeaa)DE-He213 Water erosion (dpeaa)DE-He213 Aggregate stability (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Acidic red soil (dpeaa)DE-He213 Song, Yueyan aut Li, Dingqiang aut Huang, Bin (orcid)0000-0003-0875-0722 aut Chen, Yunhui aut Ge, Xiaojun aut Zheng, Mingguo aut Liao, Yishan aut Xie, Zhenyue aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 29(2022), 55 vom: 01. Juli, Seite 83969-83980 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:29 year:2022 number:55 day:01 month:07 pages:83969-83980 https://dx.doi.org/10.1007/s11356-022-21623-x 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_381 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 29 2022 55 01 07 83969-83980 |
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10.1007/s11356-022-21623-x doi (DE-627)SPR048572608 (SPR)s11356-022-21623-x-e DE-627 ger DE-627 rakwb eng Yuan, Zaijian verfasserin aut Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions 2022 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2022 Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. Excessively high level (7%) of biochar application may aggravate soil erosion and result in more Cd loss. Biochar (dpeaa)DE-He213 Simulated rainfall (dpeaa)DE-He213 Water erosion (dpeaa)DE-He213 Aggregate stability (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Acidic red soil (dpeaa)DE-He213 Song, Yueyan aut Li, Dingqiang aut Huang, Bin (orcid)0000-0003-0875-0722 aut Chen, Yunhui aut Ge, Xiaojun aut Zheng, Mingguo aut Liao, Yishan aut Xie, Zhenyue aut Enthalten in Environmental science and pollution research Berlin : Springer, 1994 29(2022), 55 vom: 01. Juli, Seite 83969-83980 (DE-627)320517926 (DE-600)2014192-0 1614-7499 nnns volume:29 year:2022 number:55 day:01 month:07 pages:83969-83980 https://dx.doi.org/10.1007/s11356-022-21623-x 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_381 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 29 2022 55 01 07 83969-83980 |
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Enthalten in Environmental science and pollution research 29(2022), 55 vom: 01. Juli, Seite 83969-83980 volume:29 year:2022 number:55 day:01 month:07 pages:83969-83980 |
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Enthalten in Environmental science and pollution research 29(2022), 55 vom: 01. Juli, Seite 83969-83980 volume:29 year:2022 number:55 day:01 month:07 pages:83969-83980 |
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Yuan, Zaijian @@aut@@ Song, Yueyan @@aut@@ Li, Dingqiang @@aut@@ Huang, Bin @@aut@@ Chen, Yunhui @@aut@@ Ge, Xiaojun @@aut@@ Zheng, Mingguo @@aut@@ Liao, Yishan @@aut@@ Xie, Zhenyue @@aut@@ |
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This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. 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Yuan, Zaijian |
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Yuan, Zaijian misc Biochar misc Simulated rainfall misc Water erosion misc Aggregate stability misc Cadmium misc Acidic red soil Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions |
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Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions Biochar (dpeaa)DE-He213 Simulated rainfall (dpeaa)DE-He213 Water erosion (dpeaa)DE-He213 Aggregate stability (dpeaa)DE-He213 Cadmium (dpeaa)DE-He213 Acidic red soil (dpeaa)DE-He213 |
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Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions |
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Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions |
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effects of biochar application on the loss characteristics of cd from acidic soil under simulated rainfall conditions |
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Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions |
| abstract |
Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. Excessively high level (7%) of biochar application may aggravate soil erosion and result in more Cd loss. © The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2022 |
| abstractGer |
Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. Excessively high level (7%) of biochar application may aggravate soil erosion and result in more Cd loss. © The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2022 |
| abstract_unstemmed |
Abstract Biochar is widely used for immobilizing heavy metals in soil as a kind of high-effective passivator. This research conducted incubation and simulated rainfall experiments to study the effects of biochar application on the loss characteristics of runoff and sediment, as well as the transportation of the Cd during the water erosion process. Two rainfall intensities (60 and 120 mm $ h^{−1} $) and five biochar application rates (0%, 1%, 3%, 5%, and 7%) were considered in the experiment. The result showed that slaking had a greater effect than mechanical stirring in aggregate breakdown of the soil, and the addition of biochar generally increased the sensitivity of the soil to wet stirring, while had no obvious influence on the resistance to slaking. The $ H_{2} $O and $ CaCl_{2} $ extractable Cd in soil significantly decreased with the increase of biochar application rate. The runoff yields decreased with the increase of biochar application rate at both the two rainfall intensities, while the eroded sediment generally decreased at the 120 mm $ h^{−1} $ rainfall intensity. The addition of biochar tended to increase the loss of the middle-sized (1–0.05 mm) aggregates at the 60 mm $ h^{−1} $ rainfall intensity, whereas reduced their loss at the 120 mm $ h^{−1} $ rainfall intensity. Biochar application could significantly reduce the concentration of Cd in the runoff and decreased the total loss amount of Cd (sediment+runoff) in most of the cases. Excessively high level (7%) of biochar application may aggravate soil erosion and result in more Cd loss. © The Author(s), under exclusive licence to Springer-Verlag GmbH Germany, part of Springer Nature 2022 |
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Effects of biochar application on the loss characteristics of Cd from acidic soil under simulated rainfall conditions |
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https://dx.doi.org/10.1007/s11356-022-21623-x |
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Song, Yueyan Li, Dingqiang Huang, Bin Chen, Yunhui Ge, Xiaojun Zheng, Mingguo Liao, Yishan Xie, Zhenyue |
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Song, Yueyan Li, Dingqiang Huang, Bin Chen, Yunhui Ge, Xiaojun Zheng, Mingguo Liao, Yishan Xie, Zhenyue |
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2024-07-03T20:05:34.214Z |
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| score |
7.398978 |