Advances in the application of biochar in sandy soil remediation

doi:10.7522/j.issn.1000-694X.2024.00104

Journal of Desert Research ›› 2024, Vol. 44 ›› Issue (4): 315-326.DOI: 10.7522/j.issn.1000-694X.2024.00104

Advances in the application of biochar in sandy soil remediation

Yu Xiang¹^,²^,³(), Yuqiang Li¹^,²^,³, Chengzhuo Zheng¹^,²^,³, Mengqi Yuan³^,⁴, Weiyuan Liu⁵

^1.Key Laboratory of Ecological Safety and Sustainable Development in Arid Lands /, Northwest Institute of Eco-Environment and Resources，Chinese Academy of Sciences，Lanzhou 730000，China
^2.Naiman Desertification Research Station, Northwest Institute of Eco-Environment and Resources，Chinese Academy of Sciences，Lanzhou 730000，China
^3.University of Chinese Academy of Sciences，Beijing 100049，China
^4.Xinjiang Institute of Ecology and Geography，Chinese Academy of Sciences，Urumqi 830011，China
^5.Daliushu State Owned Sand Control Forest Farm in Naiman Banner，Naiman Banner 028300，Inner Mongolia，China

Received:2024-06-09 Revised:2024-07-09 Online:2024-07-20 Published:2024-08-29

Abstract

Abstract:

China is confronted with severe challenges of desertification， sandy land expansion， and soil degradation， which urgently necessitate ecological restoration and soil conservation efforts. Biochar is a carbon-rich material derived from the pyrolysis of various feedstocks， which is commonly used as an amendment for soil improvement and remediation， and is of significant importance for improving sandy soils in arid regions. This study examines the effects of biochar on soil physical and chemical properties， carbon sequestration capacity，and crop growth in sandy soils. This review is conducive to understanding the current status of biochar application in sandy soils and enhancing the understanding and comprehension of the mechanisms underlying biochar-mediated soil improvement. It provides a reference for both practical applications and theoretical research on the use of biochar in sandy soils.

Key words: biochar, sand restoration, soil improvement, soil carbon sequestration, soil amendment

CLC Number:

S156.2

Yu Xiang, Yuqiang Li, Chengzhuo Zheng, Mengqi Yuan, Weiyuan Liu. Advances in the application of biochar in sandy soil remediation[J]. Journal of Desert Research, 2024, 44(4): 315-326.

Figures/Tables 1

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原料类型	热解温度/℃	施加量	效果	实验条件	参考文献
黄松木	400	0~100% wt.	提升	实验室	[58]
柳树、纤维污泥和谷物壳	550、520	1% wt.	提升	实验室	[43]
老芒果树	600	2.5%和5% wt.	提升	实验室	[47]
约80%硬木和20%挪威云杉木材的混合物	380~430	10%、20%、30% wt.	提升	实验室	[46]
葡萄茎	—	0、2%、5% wt.	提升	实验室	[59]
棉壳、猪粪、桉树锯木厂残渣、甘蔗滤饼	400 500 600	5% wt.	提升	实验室	[60]
松木、杂交杨木、松树皮	350、600	20 g·kg^-1	提升	实验室	[61]
牧豆树	400	2% wt.	提升	实验室	[33]
松木片、硬木片、硬木颗粒、燕麦壳	500	1%、2%、5% wt.	提升	实验室	[62]
松树、杨树或污泥	500~550	18 g·kg^-1	提升	实验室	[63]
玉米秸秆和柳枝稷	650	40 g·kg^-1	提升	实验室	[53]
油茶壳树	550	0、1%、5%	提升	实验室	[38]
粪便	500	2% wt.	提升	实验室	[26]
木兰叶、苹果屑、玉米秸秆	300、400、500、600、700	0、2%、5%、7% wt.	提升	实验室	[55]
木屑	500~600	50、100 g·kg^-1	提升	实验室	[64]
混合木片小麦秸秆葡萄园修剪物	525 400	3% wt.	提升	实验室	[65]
消化渣（主要由玉米组成）和木屑（由柳树和杨树组成）	750	2%wt.	提升	实验室	[57]
牧豆树木材	400	10% wt.	提升	实验室	[66]
柳枝稷	375~475	1% wt.	提升	实验室	[67]
红橡木	500	0、3%、6% wt.	提升	实验室	[68]
玉米和橡树	450	0.5% wt.	提升	实验室与田间	[69]
玉米	750	1%、2.5%、5% wt.	提升	实验室与田间	[70]
软木、核桃壳	600~700 900	0、0.5%、1% wt.	提升	实验室与田间	[71]
谷壳和纸纤维污泥	450~500	0、3、15、30 t·hm^-2	提升	田间	[72]
玉米芯	500~550	10、20、20 t·hm^-2	提升	田间	[73]
玉米芯	350	0、0.8%、2.5% wt. 0、1.7%、3.4% wt.	提升	田间	[13]
草本原料	400~600	1、5、10、20、50 t·hm^-2	无明显影响	田间	[29]
桉木	400~500	0.4%、0.7%、1.5% wt.	提升	田间	[74]
金合欢	550	15 kg	无明显影响	田间	[52]
玉米芯	350	0、2、6 t·hm^-2	提升	田间	[37]
去皮云杉木片	550~600	0、5、10、20、30 t·hm^-2	提升	田间	[75]

原料类型	热解温度/℃	施加量	效果	实验条件	参考文献
黄松木	400	0~100% wt.	提升	实验室	[58]
柳树、纤维污泥和谷物壳	550、520	1% wt.	提升	实验室	[43]
老芒果树	600	2.5%和5% wt.	提升	实验室	[47]
约80%硬木和20%挪威云杉木材的混合物	380~430	10%、20%、30% wt.	提升	实验室	[46]
葡萄茎	—	0、2%、5% wt.	提升	实验室	[59]
棉壳、猪粪、桉树锯木厂残渣、甘蔗滤饼	400 500 600	5% wt.	提升	实验室	[60]
松木、杂交杨木、松树皮	350、600	20 g·kg^-1	提升	实验室	[61]
牧豆树	400	2% wt.	提升	实验室	[33]
松木片、硬木片、硬木颗粒、燕麦壳	500	1%、2%、5% wt.	提升	实验室	[62]
松树、杨树或污泥	500~550	18 g·kg^-1	提升	实验室	[63]
玉米秸秆和柳枝稷	650	40 g·kg^-1	提升	实验室	[53]
油茶壳树	550	0、1%、5%	提升	实验室	[38]
粪便	500	2% wt.	提升	实验室	[26]
木兰叶、苹果屑、玉米秸秆	300、400、500、600、700	0、2%、5%、7% wt.	提升	实验室	[55]
木屑	500~600	50、100 g·kg^-1	提升	实验室	[64]
混合木片小麦秸秆葡萄园修剪物	525 400	3% wt.	提升	实验室	[65]
消化渣（主要由玉米组成）和木屑（由柳树和杨树组成）	750	2%wt.	提升	实验室	[57]
牧豆树木材	400	10% wt.	提升	实验室	[66]
柳枝稷	375~475	1% wt.	提升	实验室	[67]
红橡木	500	0、3%、6% wt.	提升	实验室	[68]
玉米和橡树	450	0.5% wt.	提升	实验室与田间	[69]
玉米	750	1%、2.5%、5% wt.	提升	实验室与田间	[70]
软木、核桃壳	600~700 900	0、0.5%、1% wt.	提升	实验室与田间	[71]
谷壳和纸纤维污泥	450~500	0、3、15、30 t·hm^-2	提升	田间	[72]
玉米芯	500~550	10、20、20 t·hm^-2	提升	田间	[73]
玉米芯	350	0、0.8%、2.5% wt. 0、1.7%、3.4% wt.	提升	田间	[13]
草本原料	400~600	1、5、10、20、50 t·hm^-2	无明显影响	田间	[29]
桉木	400~500	0.4%、0.7%、1.5% wt.	提升	田间	[74]
金合欢	550	15 kg	无明显影响	田间	[52]
玉米芯	350	0、2、6 t·hm^-2	提升	田间	[37]
去皮云杉木片	550~600	0、5、10、20、30 t·hm^-2	提升	田间	[75]

[1]	Zhou Lijing, Wang Yajun, Xie Zhongkui, Zhang Yubao, Guo Zhihong, Qiu Yang, Hua Cuiping, Zhao Chengzheng. Improvement Effect of Biochar on the Degraded Soil of Lanzhou Lily Field [J]. Journal of Desert Research, 2019, 39(2): 134-143.
[2]	LI Yu-qiang;ZHAO Xue-yong;LIU Xin-ping;SHANG Wen;FENG Jing;SU Na. Soil Carbon Sequestration in Sand-fixation Plantation of Pinus sylvestris var. Mongolica and Response of Soil Respiration to Drought and Wet Conditions [J]. JOURNAL OF DESERT RESEARCH, 2011, 31(2): 282-287.

Advances in the application of biochar in sandy soil remediation

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