中国农业气象 ›› 2024, Vol. 45 ›› Issue (12): 1391-1404.doi: 10.3969/j.issn.1000-6362.2024.12.001

• 农业生态环境栏目 •    下一篇

镧改性生物炭对砷污染红壤的修复效应及酶活性的影响

谢金倪,李莲芳,吕鹏,王紫含,颜澳,康梦琦,周雪,叶婧   

  1. 中国农业科学院农业环境与可持续发展研究所/农业农村部农业环境重点实验室,北京 100081
  • 收稿日期:2023-12-23 出版日期:2024-12-20 发布日期:2024-12-20
  • 作者简介:谢金倪,E-mail:1936615761@qq.com
  • 基金资助:
    国家自然科学基金项目(42377257);国家重点研发计划课题(2020YFC1806401)

Immobiliaztion Effect of Arsenic in Contaminated Red Soils and Its Enzyme Activities after Application of Lanthanum-modified Biochar

XIE Jin-ni, LI Lian-fang, LV Peng, WANG Zi-han, YAN Ao, KANG Meng-qi, ZHOU Xue, YE Jing   

  1. Institute of Environment and Sustainable Development in Agriculture, Chinese Academy of Agricultural Sciences/Key Laboratory of Agro-Environment, Ministry of Agriculture and Rural Affairs, Beijing 100081, China
  • Received:2023-12-23 Online:2024-12-20 Published:2024-12-20

摘要:

高温限氧裂解制备而成的生物炭作为农业废弃物资源化利用及固碳减排的重要抓手,在环境污染修复领域发挥了重要作用,市场前景较好。作为土壤修复的功能材料,生物炭对重金属吸附固定能力不足,限制了其应用推广,而生物炭经改性设计后制备的工程材料已成为修复土壤重金属污染的重要发展方向。本研究以木屑为原料制备生物炭(BC),辅以镧改性设计制得镧改性生物炭(LBC),开展为期30d的土壤培养试验,以施用镧改性生物炭(LBC)、生物炭(BC)、不施炭材料(CK)的砷污染红壤为研究对象,设置30%70%100%田间持水量共3种土壤含水量条件,探讨生物炭在镧改性前后对不同水分条件下的砷污染红壤修复效应。结果表明:(1)施用镧改性生物炭有利于缓解南方红壤的酸化现象。当土壤培养试验结束时,在30%70%100%田间持水量下,LBC处理的土壤pH值较CK处理升高0.861.20个单位,较BC处理提升0.090.44个单位。(2)施用镧改性生物炭有助于固定污染红壤中的砷。LBC应用于不同土壤含水量条件下的砷污染红壤,全周期固定效率达54.7%~90.0%,培养末期(第30天)固定效率达81.0%85.8%BC施用后在全周期内土壤砷较CK处理活化135.4%895.9%3)镧改性生物炭对土壤砷的固定效应主要与施用后土壤砷形态的转化有关。LBC施用后土壤砷由非专性吸附态向残渣态等稳定的形态转化,而添加BC的土壤中非专性吸附态砷含量升高,促进了土壤砷活化。(4)镧改性生物炭修复砷污染红壤的同时,对土壤酶活性等微生态情况未构成明显不良影响。施用LBC可以提升土壤脲酶及过氧化氢酶活性,虽导致土壤磷酸酶及蔗糖酶活性略有降低,但土壤蔗糖酶活性较BC处理更高。综上所述,镧改性生物炭应用于砷污染红壤修复潜力较大

关键词: 生物炭, 红壤, 砷, 钝化, 酶活性

Abstract:

Biochar pyrolysis at high temperature with limited oxygen plays an important role in the resource utilization of agricultural waste, carbon sequestration and emission reduction, indicating the great potential of biochar for remediating contaminated environment. As a functional material for soil remediation, its ability of adsorption and fixation for heavy metals is still insufficient, which limits the large-scale promotion and application of biochar. Nowadays, it has been an increasingly important research area to enhance the adsorption and fixation capacity of biochar through modification design of engineered materials. In this study, wood chips were used as raw materials to prepare biochar (BC), and then lanthanum modified biochar (LBC) was manufactured. Aiming to remediate arsenic contaminated red soil and compare the immobilization difference, these two kinds of amendments (LBC, BC) were applied into the experimental soils separately, and the blank soil without material addition was used as control treatment. All these above treatments was cultivated for 30days under the soil moisture content with 30%, 70%, and 100% field water capacity respectively, and the corresponding remediation effects of arsenic contaminated red soil by using LBC and BC were investigated. The results were as following: (1) LBC addition was beneficial for alleviating the acidification of southern red soils. When the cultivation experiment was finished, soil pH treated by LBC was enhanced obviously and the increased pH ranged from 0.86 to 1.20 units under three kinds of soil moisture content with 30%, 70%, and 100% field water capacity. In comparison with BC treatment, the soil pH also increased by 0.090.44 units after LBC addtion. (2) LBC application led to the obvious immobilization effect of arsenic in red soils, and the related fixation efficiency under three kinds of soil water content was up to 54.7%90.0% during the whole soil cultivation period, and the immobilization efficiency reached 81.0%85.8% after 30days of cultivation. On the contrary, soil treated by BC resulted in the arsenic activation of soils with the increased percent 135.4%895.9% compared to the control. (3) The immobilization effect of LBC on soil arsenic is mainly related to the transformation of arsenic in various speciation, especially from non-specialized adsorption forms to more stable ones such as residue forms. In the meanwhile, BC resulted in the enhancement of non-specialized adsorption arsenic and promoted the activation of soil arsenic. (4) LBC was capable of immobilizing arsenic in red soils with high efficiency, and did not obviously excert negative influence on soil enzyme activity. The application of LBC was able to improve the activity of soil urease and catalase although it led to a slight decrease in soil phosphatase and sucrase activities. It is worth mention that LBC treatment remained higher soil sucrase activities than those for BC treatments. Overall, it manifest that LBC has great potential for remediating arsenic contaminated red soil.

Key words:

Bioch ar, Red soil, Arsenic, Passivation, Enzyme activity