Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration
Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effect...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Zhang, Yaling [verfasserIn] Menke, Carl [verfasserIn] Drigo, Barbara [verfasserIn] Bai, Shahla Hosseini [verfasserIn] Anderson, Ian [verfasserIn] Xu, Zhihong [verfasserIn] Chen, Hong [verfasserIn] Zhang, Manyun [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2017 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Journal of soils and sediments - Berlin : Springer, 2001, 17(2017), 10 vom: 01. Juli, Seite 2410-2419 |
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| Übergeordnetes Werk: |
volume:17 ; year:2017 ; number:10 ; day:01 ; month:07 ; pages:2410-2419 |
| Links: |
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| DOI / URN: |
10.1007/s11368-017-1765-6 |
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| Katalog-ID: |
SPR018962246 |
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| 100 | 1 | |a Zhang, Yaling |e verfasserin |4 aut | |
| 245 | 1 | 0 | |a Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration |
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| 520 | |a Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. However, it would be more difficulty to rehabilitate mine spoils in future with the rising atmospheric $ CO_{2} $ concentration. | ||
| 650 | 4 | |a Biochar |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Elevated CO |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Mine rehabilitation |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a δ |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a C and δ |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a N |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a C and N nutrient cycles |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Menke, Carl |e verfasserin |4 aut | |
| 700 | 1 | |a Drigo, Barbara |e verfasserin |4 aut | |
| 700 | 1 | |a Bai, Shahla Hosseini |e verfasserin |4 aut | |
| 700 | 1 | |a Anderson, Ian |e verfasserin |4 aut | |
| 700 | 1 | |a Xu, Zhihong |e verfasserin |4 aut | |
| 700 | 1 | |a Chen, Hong |e verfasserin |4 aut | |
| 700 | 1 | |a Zhang, Manyun |e verfasserin |4 aut | |
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10.1007/s11368-017-1765-6 doi (DE-627)SPR018962246 (SPR)s11368-017-1765-6-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Zhang, Yaling verfasserin aut Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. However, it would be more difficulty to rehabilitate mine spoils in future with the rising atmospheric $ CO_{2} $ concentration. Biochar (dpeaa)DE-He213 Elevated CO (dpeaa)DE-He213 Mine rehabilitation (dpeaa)DE-He213 δ (dpeaa)DE-He213 C and δ (dpeaa)DE-He213 N (dpeaa)DE-He213 C and N nutrient cycles (dpeaa)DE-He213 Menke, Carl verfasserin aut Drigo, Barbara verfasserin aut Bai, Shahla Hosseini verfasserin aut Anderson, Ian verfasserin aut Xu, Zhihong verfasserin aut Chen, Hong verfasserin aut Zhang, Manyun verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 17(2017), 10 vom: 01. Juli, Seite 2410-2419 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:17 year:2017 number:10 day:01 month:07 pages:2410-2419 https://dx.doi.org/10.1007/s11368-017-1765-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_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_183 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 17 2017 10 01 07 2410-2419 |
| spelling |
10.1007/s11368-017-1765-6 doi (DE-627)SPR018962246 (SPR)s11368-017-1765-6-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Zhang, Yaling verfasserin aut Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. However, it would be more difficulty to rehabilitate mine spoils in future with the rising atmospheric $ CO_{2} $ concentration. Biochar (dpeaa)DE-He213 Elevated CO (dpeaa)DE-He213 Mine rehabilitation (dpeaa)DE-He213 δ (dpeaa)DE-He213 C and δ (dpeaa)DE-He213 N (dpeaa)DE-He213 C and N nutrient cycles (dpeaa)DE-He213 Menke, Carl verfasserin aut Drigo, Barbara verfasserin aut Bai, Shahla Hosseini verfasserin aut Anderson, Ian verfasserin aut Xu, Zhihong verfasserin aut Chen, Hong verfasserin aut Zhang, Manyun verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 17(2017), 10 vom: 01. Juli, Seite 2410-2419 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:17 year:2017 number:10 day:01 month:07 pages:2410-2419 https://dx.doi.org/10.1007/s11368-017-1765-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_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_183 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 17 2017 10 01 07 2410-2419 |
| allfields_unstemmed |
10.1007/s11368-017-1765-6 doi (DE-627)SPR018962246 (SPR)s11368-017-1765-6-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Zhang, Yaling verfasserin aut Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. However, it would be more difficulty to rehabilitate mine spoils in future with the rising atmospheric $ CO_{2} $ concentration. Biochar (dpeaa)DE-He213 Elevated CO (dpeaa)DE-He213 Mine rehabilitation (dpeaa)DE-He213 δ (dpeaa)DE-He213 C and δ (dpeaa)DE-He213 N (dpeaa)DE-He213 C and N nutrient cycles (dpeaa)DE-He213 Menke, Carl verfasserin aut Drigo, Barbara verfasserin aut Bai, Shahla Hosseini verfasserin aut Anderson, Ian verfasserin aut Xu, Zhihong verfasserin aut Chen, Hong verfasserin aut Zhang, Manyun verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 17(2017), 10 vom: 01. Juli, Seite 2410-2419 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:17 year:2017 number:10 day:01 month:07 pages:2410-2419 https://dx.doi.org/10.1007/s11368-017-1765-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_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_183 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 17 2017 10 01 07 2410-2419 |
| allfieldsGer |
10.1007/s11368-017-1765-6 doi (DE-627)SPR018962246 (SPR)s11368-017-1765-6-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Zhang, Yaling verfasserin aut Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. However, it would be more difficulty to rehabilitate mine spoils in future with the rising atmospheric $ CO_{2} $ concentration. Biochar (dpeaa)DE-He213 Elevated CO (dpeaa)DE-He213 Mine rehabilitation (dpeaa)DE-He213 δ (dpeaa)DE-He213 C and δ (dpeaa)DE-He213 N (dpeaa)DE-He213 C and N nutrient cycles (dpeaa)DE-He213 Menke, Carl verfasserin aut Drigo, Barbara verfasserin aut Bai, Shahla Hosseini verfasserin aut Anderson, Ian verfasserin aut Xu, Zhihong verfasserin aut Chen, Hong verfasserin aut Zhang, Manyun verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 17(2017), 10 vom: 01. Juli, Seite 2410-2419 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:17 year:2017 number:10 day:01 month:07 pages:2410-2419 https://dx.doi.org/10.1007/s11368-017-1765-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_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_183 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 17 2017 10 01 07 2410-2419 |
| allfieldsSound |
10.1007/s11368-017-1765-6 doi (DE-627)SPR018962246 (SPR)s11368-017-1765-6-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl Zhang, Yaling verfasserin aut Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. However, it would be more difficulty to rehabilitate mine spoils in future with the rising atmospheric $ CO_{2} $ concentration. Biochar (dpeaa)DE-He213 Elevated CO (dpeaa)DE-He213 Mine rehabilitation (dpeaa)DE-He213 δ (dpeaa)DE-He213 C and δ (dpeaa)DE-He213 N (dpeaa)DE-He213 C and N nutrient cycles (dpeaa)DE-He213 Menke, Carl verfasserin aut Drigo, Barbara verfasserin aut Bai, Shahla Hosseini verfasserin aut Anderson, Ian verfasserin aut Xu, Zhihong verfasserin aut Chen, Hong verfasserin aut Zhang, Manyun verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 17(2017), 10 vom: 01. Juli, Seite 2410-2419 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:17 year:2017 number:10 day:01 month:07 pages:2410-2419 https://dx.doi.org/10.1007/s11368-017-1765-6 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_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_183 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 58.52 ASE AR 17 2017 10 01 07 2410-2419 |
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Enthalten in Journal of soils and sediments 17(2017), 10 vom: 01. Juli, Seite 2410-2419 volume:17 year:2017 number:10 day:01 month:07 pages:2410-2419 |
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Biochar Elevated CO Mine rehabilitation δ C and δ N C and N nutrient cycles |
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Zhang, Yaling @@aut@@ Menke, Carl @@aut@@ Drigo, Barbara @@aut@@ Bai, Shahla Hosseini @@aut@@ Anderson, Ian @@aut@@ Xu, Zhihong @@aut@@ Chen, Hong @@aut@@ Zhang, Manyun @@aut@@ |
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2017-07-01T00:00:00Z |
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We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. 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Zhang, Yaling |
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Zhang, Yaling ddc 550 bkl 58.52 misc Biochar misc Elevated CO misc Mine rehabilitation misc δ misc C and δ misc N misc C and N nutrient cycles Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration |
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550 ASE 58.52 bkl Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration Biochar (dpeaa)DE-He213 Elevated CO (dpeaa)DE-He213 Mine rehabilitation (dpeaa)DE-He213 δ (dpeaa)DE-He213 C and δ (dpeaa)DE-He213 N (dpeaa)DE-He213 C and N nutrient cycles (dpeaa)DE-He213 |
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ddc 550 bkl 58.52 misc Biochar misc Elevated CO misc Mine rehabilitation misc δ misc C and δ misc N misc C and N nutrient cycles |
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ddc 550 bkl 58.52 misc Biochar misc Elevated CO misc Mine rehabilitation misc δ misc C and δ misc N misc C and N nutrient cycles |
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ddc 550 bkl 58.52 misc Biochar misc Elevated CO misc Mine rehabilitation misc δ misc C and δ misc N misc C and N nutrient cycles |
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Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration |
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Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration |
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Journal of soils and sediments |
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Zhang, Yaling Menke, Carl Drigo, Barbara Bai, Shahla Hosseini Anderson, Ian Xu, Zhihong Chen, Hong Zhang, Manyun |
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assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ co_{2} $ concentration |
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Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration |
| abstract |
Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. However, it would be more difficulty to rehabilitate mine spoils in future with the rising atmospheric $ CO_{2} $ concentration. |
| abstractGer |
Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. However, it would be more difficulty to rehabilitate mine spoils in future with the rising atmospheric $ CO_{2} $ concentration. |
| abstract_unstemmed |
Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. However, it would be more difficulty to rehabilitate mine spoils in future with the rising atmospheric $ CO_{2} $ concentration. |
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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">SPR018962246</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20220111064115.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">201006s2017 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s11368-017-1765-6</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR018962246</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s11368-017-1765-6-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="082" ind1="0" ind2="4"><subfield code="a">550</subfield><subfield code="q">ASE</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">58.52</subfield><subfield code="2">bkl</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Zhang, Yaling</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Assessing the potential of using biochar in mine rehabilitation under elevated atmospheric $ CO_{2} $ concentration</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2017</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="520" ind1=" " ind2=" "><subfield code="a">Purpose Re-establishment of soil nitrogen (N) capital is a priority in mine rehabilitation. We aimed to evaluate the effects of biochar addition on improving mine spoil N pools and the influence of elevated $ CO_{2} $ concentration on mine rehabilitation. Materials and methods We assessed the effects of pinewood biochar, produced at three temperatures (650, 750 and 850 °C, referred as $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively), on mine spoil total N concentrations with five different plant species, including a tree species (Eucalyptus crebra), N-fixing shrubs (Acacia floribunda and Allocasuarina littoralis) and $ C_{3} $ and $ C_{4} $ grasses (Austrodanthonia tenuior and Themeda australis) incubated at ambient (400 μL $ L^{−1} $) and elevated (700 μL $ L^{−1} $) atmospheric $ CO_{2} $ concentrations, as well as the effects of elevated $ CO_{2} $ on mine rehabilitation. Results and discussion Soil total N significantly improved following biochar incorporation under all plant species (P < 0.05) except for T. Australis. E. crebra had the highest soil total N (0.197%, 0.198% and 0.212% for $ B_{650} $, $ B_{750} $ and $ B_{850} $, respectively). Different from the negligible influence of elevated $ CO_{2} $ on soil properties under the grasses and the N-fixing shrubs, elevated $ CO_{2} $ significantly increased soil water and hot water extractable organic C (WEOC and HWEOC, respectively) and decreased total C under E. crebra, indicating that the nutrient demands were not met. Conclusions Biochar addition showed the potential in mine rehabilitation in terms of improving soil N pool, especially with E. crebra. 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