- Volumes 84-95 (2024)
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Volumes 72-83 (2023)
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Volume 83
Pages 1-258 (December 2023)
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Volume 82
Pages 1-204 (November 2023)
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Volume 81
Pages 1-188 (October 2023)
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Volume 80
Pages 1-202 (September 2023)
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Volume 79
Pages 1-172 (August 2023)
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Volume 78
Pages 1-146 (July 2023)
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Volume 77
Pages 1-152 (June 2023)
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Volume 76
Pages 1-176 (May 2023)
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Volume 75
Pages 1-228 (April 2023)
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Volume 74
Pages 1-200 (March 2023)
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Volume 73
Pages 1-138 (February 2023)
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Volume 72
Pages 1-144 (January 2023)
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Volume 83
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Volumes 60-71 (2022)
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Volume 71
Pages 1-108 (December 2022)
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Volume 70
Pages 1-106 (November 2022)
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Volume 69
Pages 1-122 (October 2022)
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Volume 68
Pages 1-124 (September 2022)
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Volume 67
Pages 1-102 (August 2022)
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Volume 66
Pages 1-112 (July 2022)
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Volume 65
Pages 1-138 (June 2022)
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Volume 64
Pages 1-186 (May 2022)
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Volume 63
Pages 1-124 (April 2022)
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Volume 62
Pages 1-104 (March 2022)
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Volume 61
Pages 1-120 (February 2022)
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Volume 60
Pages 1-124 (January 2022)
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Volume 71
- Volumes 54-59 (2021)
- Volumes 48-53 (2020)
- Volumes 42-47 (2019)
- Volumes 36-41 (2018)
- Volumes 30-35 (2017)
- Volumes 24-29 (2016)
- Volumes 18-23 (2015)
- Volumes 12-17 (2014)
- Volume 11 (2013)
- Volume 10 (2012)
- Volume 9 (2011)
- Volume 8 (2010)
- Volume 7 (2009)
- Volume 6 (2008)
- Volume 5 (2007)
- Volume 4 (2006)
- Volume 3 (2005)
- Volume 2 (2004)
- Volume 1 (2003)
• Preparation of carbon based oil absorbing materials from agricultural solid waste walnut shells.
• Modification of biochar surface groups, pore structure and magnetic properties using simple co-modification methods.
• Co-modified adsorbents exhibit good oil absorption and reuse properties.
• Solid-phase partitioning, hydrogen bonding, electrostatic interaction, and π-π bonding synergize the adsorption of oil.
A magnetic biochar adsorbent (BM–OH–BC) was prepared through NaOH–ball milling co-modification with walnut shells as the raw material, and its oil adsorption characteristics were investigated. The adsorption properties of oil pollutants were compared before and after the NaOH-ball-milling co-modification, and the mechanism of NaOH-ball-milling on oil pollutants was investigated by scanning electron microscope-energy dispersive X-ray spectroscopy, BET, X-ray photoelectron spectroscopy and Fourier transform infrared spectroscopy. The experimental results showed that the oil adsorption capacity of BM–OH–BC can reach 2.75 g/g, which is 129% higher than that of unmodified biochar. Moreover, after five adsorption and desorption cycles, the adsorption rate of BM–OH–BC only decreased by 5.9%, which was because the oil adsorption of BM–OH–BC is mainly chemical adsorption. The adsorption processes involving single layer, heterogeneous phase and multilayer made BM–OH–BC have excellent adsorption properties. After biochar co-modification, the specific surface area of BM–OH–BC increased to 466 m2/g, the total pore volume increased to 0.245 cm3/g, the average pore size decreased to1.90 nm, and the number of hydrophobic non-polar functional groups increased, leading to the enhancement of its oil absorption capacity. This study provides a reference for the treatment of oil-contaminated water bodies.