Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil
Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Li, Ying [verfasserIn] Wen, Jiaqi [verfasserIn] Shen, Pengfei [verfasserIn] Zhou, Yu [verfasserIn] Shen, Jianxiang [verfasserIn] Jiang, Jinlin [verfasserIn] Kong, Xiangji [verfasserIn] Gu, Xueyuan [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: Bulletin of environmental contamination and toxicology - New York, NY : Springer, 1966, 105(2020), 4 vom: 21. Sept., Seite 639-644 |
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| Übergeordnetes Werk: |
volume:105 ; year:2020 ; number:4 ; day:21 ; month:09 ; pages:639-644 |
| Links: |
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| DOI / URN: |
10.1007/s00128-020-02995-7 |
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| Katalog-ID: |
SPR041224477 |
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| 520 | |a Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. Therefore, ZVI/biochar and $ MnO_{2} $/ZVI mixtures may offer effective solutions to the remediation of farmland soil contaminated with both As and Cd. | ||
| 650 | 4 | |a As–Cd |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Combined pollution |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Stabilization |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Immobilization |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Soil remediation |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Wen, Jiaqi |e verfasserin |4 aut | |
| 700 | 1 | |a Shen, Pengfei |e verfasserin |4 aut | |
| 700 | 1 | |a Zhou, Yu |e verfasserin |4 aut | |
| 700 | 1 | |a Shen, Jianxiang |e verfasserin |4 aut | |
| 700 | 1 | |a Jiang, Jinlin |e verfasserin |4 aut | |
| 700 | 1 | |a Kong, Xiangji |e verfasserin |4 aut | |
| 700 | 1 | |a Gu, Xueyuan |e verfasserin |4 aut | |
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10.1007/s00128-020-02995-7 doi (DE-627)SPR041224477 (SPR)s00128-020-02995-7-e DE-627 ger DE-627 rakwb eng 570 ASE 333.7 610 ASE 43.13 bkl 44.39 bkl 44.13 bkl Li, Ying verfasserin aut Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. Therefore, ZVI/biochar and $ MnO_{2} $/ZVI mixtures may offer effective solutions to the remediation of farmland soil contaminated with both As and Cd. As–Cd (dpeaa)DE-He213 Combined pollution (dpeaa)DE-He213 Stabilization (dpeaa)DE-He213 Immobilization (dpeaa)DE-He213 Soil remediation (dpeaa)DE-He213 Wen, Jiaqi verfasserin aut Shen, Pengfei verfasserin aut Zhou, Yu verfasserin aut Shen, Jianxiang verfasserin aut Jiang, Jinlin verfasserin aut Kong, Xiangji verfasserin aut Gu, Xueyuan verfasserin aut Enthalten in Bulletin of environmental contamination and toxicology New York, NY : Springer, 1966 105(2020), 4 vom: 21. Sept., Seite 639-644 (DE-627)253390362 (DE-600)1458480-3 1432-0800 nnns volume:105 year:2020 number:4 day:21 month:09 pages:639-644 https://dx.doi.org/10.1007/s00128-020-02995-7 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-PHA 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_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_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_267 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 43.13 ASE 44.39 ASE 44.13 ASE AR 105 2020 4 21 09 639-644 |
| spelling |
10.1007/s00128-020-02995-7 doi (DE-627)SPR041224477 (SPR)s00128-020-02995-7-e DE-627 ger DE-627 rakwb eng 570 ASE 333.7 610 ASE 43.13 bkl 44.39 bkl 44.13 bkl Li, Ying verfasserin aut Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. Therefore, ZVI/biochar and $ MnO_{2} $/ZVI mixtures may offer effective solutions to the remediation of farmland soil contaminated with both As and Cd. As–Cd (dpeaa)DE-He213 Combined pollution (dpeaa)DE-He213 Stabilization (dpeaa)DE-He213 Immobilization (dpeaa)DE-He213 Soil remediation (dpeaa)DE-He213 Wen, Jiaqi verfasserin aut Shen, Pengfei verfasserin aut Zhou, Yu verfasserin aut Shen, Jianxiang verfasserin aut Jiang, Jinlin verfasserin aut Kong, Xiangji verfasserin aut Gu, Xueyuan verfasserin aut Enthalten in Bulletin of environmental contamination and toxicology New York, NY : Springer, 1966 105(2020), 4 vom: 21. Sept., Seite 639-644 (DE-627)253390362 (DE-600)1458480-3 1432-0800 nnns volume:105 year:2020 number:4 day:21 month:09 pages:639-644 https://dx.doi.org/10.1007/s00128-020-02995-7 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-PHA 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_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_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_267 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 43.13 ASE 44.39 ASE 44.13 ASE AR 105 2020 4 21 09 639-644 |
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10.1007/s00128-020-02995-7 doi (DE-627)SPR041224477 (SPR)s00128-020-02995-7-e DE-627 ger DE-627 rakwb eng 570 ASE 333.7 610 ASE 43.13 bkl 44.39 bkl 44.13 bkl Li, Ying verfasserin aut Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. Therefore, ZVI/biochar and $ MnO_{2} $/ZVI mixtures may offer effective solutions to the remediation of farmland soil contaminated with both As and Cd. As–Cd (dpeaa)DE-He213 Combined pollution (dpeaa)DE-He213 Stabilization (dpeaa)DE-He213 Immobilization (dpeaa)DE-He213 Soil remediation (dpeaa)DE-He213 Wen, Jiaqi verfasserin aut Shen, Pengfei verfasserin aut Zhou, Yu verfasserin aut Shen, Jianxiang verfasserin aut Jiang, Jinlin verfasserin aut Kong, Xiangji verfasserin aut Gu, Xueyuan verfasserin aut Enthalten in Bulletin of environmental contamination and toxicology New York, NY : Springer, 1966 105(2020), 4 vom: 21. Sept., Seite 639-644 (DE-627)253390362 (DE-600)1458480-3 1432-0800 nnns volume:105 year:2020 number:4 day:21 month:09 pages:639-644 https://dx.doi.org/10.1007/s00128-020-02995-7 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-PHA 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_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_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_267 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 43.13 ASE 44.39 ASE 44.13 ASE AR 105 2020 4 21 09 639-644 |
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10.1007/s00128-020-02995-7 doi (DE-627)SPR041224477 (SPR)s00128-020-02995-7-e DE-627 ger DE-627 rakwb eng 570 ASE 333.7 610 ASE 43.13 bkl 44.39 bkl 44.13 bkl Li, Ying verfasserin aut Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. Therefore, ZVI/biochar and $ MnO_{2} $/ZVI mixtures may offer effective solutions to the remediation of farmland soil contaminated with both As and Cd. As–Cd (dpeaa)DE-He213 Combined pollution (dpeaa)DE-He213 Stabilization (dpeaa)DE-He213 Immobilization (dpeaa)DE-He213 Soil remediation (dpeaa)DE-He213 Wen, Jiaqi verfasserin aut Shen, Pengfei verfasserin aut Zhou, Yu verfasserin aut Shen, Jianxiang verfasserin aut Jiang, Jinlin verfasserin aut Kong, Xiangji verfasserin aut Gu, Xueyuan verfasserin aut Enthalten in Bulletin of environmental contamination and toxicology New York, NY : Springer, 1966 105(2020), 4 vom: 21. Sept., Seite 639-644 (DE-627)253390362 (DE-600)1458480-3 1432-0800 nnns volume:105 year:2020 number:4 day:21 month:09 pages:639-644 https://dx.doi.org/10.1007/s00128-020-02995-7 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-PHA 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_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_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_267 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 43.13 ASE 44.39 ASE 44.13 ASE AR 105 2020 4 21 09 639-644 |
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10.1007/s00128-020-02995-7 doi (DE-627)SPR041224477 (SPR)s00128-020-02995-7-e DE-627 ger DE-627 rakwb eng 570 ASE 333.7 610 ASE 43.13 bkl 44.39 bkl 44.13 bkl Li, Ying verfasserin aut Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. Therefore, ZVI/biochar and $ MnO_{2} $/ZVI mixtures may offer effective solutions to the remediation of farmland soil contaminated with both As and Cd. As–Cd (dpeaa)DE-He213 Combined pollution (dpeaa)DE-He213 Stabilization (dpeaa)DE-He213 Immobilization (dpeaa)DE-He213 Soil remediation (dpeaa)DE-He213 Wen, Jiaqi verfasserin aut Shen, Pengfei verfasserin aut Zhou, Yu verfasserin aut Shen, Jianxiang verfasserin aut Jiang, Jinlin verfasserin aut Kong, Xiangji verfasserin aut Gu, Xueyuan verfasserin aut Enthalten in Bulletin of environmental contamination and toxicology New York, NY : Springer, 1966 105(2020), 4 vom: 21. Sept., Seite 639-644 (DE-627)253390362 (DE-600)1458480-3 1432-0800 nnns volume:105 year:2020 number:4 day:21 month:09 pages:639-644 https://dx.doi.org/10.1007/s00128-020-02995-7 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA SSG-OPC-GGO SSG-OPC-PHA 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_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_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_267 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 43.13 ASE 44.39 ASE 44.13 ASE AR 105 2020 4 21 09 639-644 |
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Enthalten in Bulletin of environmental contamination and toxicology 105(2020), 4 vom: 21. Sept., Seite 639-644 volume:105 year:2020 number:4 day:21 month:09 pages:639-644 |
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As–Cd Combined pollution Stabilization Immobilization Soil remediation |
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Li, Ying @@aut@@ Wen, Jiaqi @@aut@@ Shen, Pengfei @@aut@@ Zhou, Yu @@aut@@ Shen, Jianxiang @@aut@@ Jiang, Jinlin @@aut@@ Kong, Xiangji @@aut@@ Gu, Xueyuan @@aut@@ |
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In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. 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Li, Ying |
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Li, Ying ddc 570 ddc 333.7 bkl 43.13 bkl 44.39 bkl 44.13 misc As–Cd misc Combined pollution misc Stabilization misc Immobilization misc Soil remediation Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil |
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570 - Life sciences; biology 333 - Economics of land & energy 610 - Medicine & health |
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570 ASE 333.7 610 ASE 43.13 bkl 44.39 bkl 44.13 bkl Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil As–Cd (dpeaa)DE-He213 Combined pollution (dpeaa)DE-He213 Stabilization (dpeaa)DE-He213 Immobilization (dpeaa)DE-He213 Soil remediation (dpeaa)DE-He213 |
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ddc 570 ddc 333.7 bkl 43.13 bkl 44.39 bkl 44.13 misc As–Cd misc Combined pollution misc Stabilization misc Immobilization misc Soil remediation |
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ddc 570 ddc 333.7 bkl 43.13 bkl 44.39 bkl 44.13 misc As–Cd misc Combined pollution misc Stabilization misc Immobilization misc Soil remediation |
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ddc 570 ddc 333.7 bkl 43.13 bkl 44.39 bkl 44.13 misc As–Cd misc Combined pollution misc Stabilization misc Immobilization misc Soil remediation |
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Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil |
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Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil |
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Li, Ying |
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Bulletin of environmental contamination and toxicology |
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Bulletin of environmental contamination and toxicology |
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eng |
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Li, Ying Wen, Jiaqi Shen, Pengfei Zhou, Yu Shen, Jianxiang Jiang, Jinlin Kong, Xiangji Gu, Xueyuan |
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Li, Ying |
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10.1007/s00128-020-02995-7 |
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verfasserin |
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comparison of four amendments for arsenic and cadmium combined contaminated soil |
| title_auth |
Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil |
| abstract |
Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. Therefore, ZVI/biochar and $ MnO_{2} $/ZVI mixtures may offer effective solutions to the remediation of farmland soil contaminated with both As and Cd. |
| abstractGer |
Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. Therefore, ZVI/biochar and $ MnO_{2} $/ZVI mixtures may offer effective solutions to the remediation of farmland soil contaminated with both As and Cd. |
| abstract_unstemmed |
Abstract Arsenic (As) and cadmium (Cd) are common soil pollutants whose opposing geochemical behaviors must be taken into account in the development of cost-effective, environmentally friendly remediation strategies. In this study, a pot experiment with lettuce and a field experiment with wheat were performed to examine the impacts of zeolite, biochar, $ MnO_{2} $, zero-valent iron (ZVI) individually and in binary combinations thereof on As–Cd pollution. The results of the pot experiment showed that biochar, $ MnO_{2} $ and ZVI had good passivation effects on As and Cd when provided individually, but the effects of a combination of 0.2% ZVI/0.5% biochar or 0.2% $ MnO_{2} $/0.5% ZVI were even better. These amendments were further investigated in a field experiment, which confirmed the positive effect of 0.2% $ MnO_{2} $/0.5% ZVI. Therefore, ZVI/biochar and $ MnO_{2} $/ZVI mixtures may offer effective solutions to the remediation of farmland soil contaminated with both As and Cd. |
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Comparison of Four Amendments for Arsenic and Cadmium Combined Contaminated Soil |
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Wen, Jiaqi Shen, Pengfei Zhou, Yu Shen, Jianxiang Jiang, Jinlin Kong, Xiangji Gu, Xueyuan |
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| score |
7.4019604 |