Wang Zixuan, Chen Shuai, Yang Lingxiao, Wang Qiquan, Hou Ning, Zhang Jiahe, Tong Yi, Li Xianyue
College of Resources and Environment, Northeast Agricultural University, Harbin, Heilongjiang 150030, PR China.
College of Resources and Environment, Northeast Agricultural University, Harbin, Heilongjiang 150030, PR China.
J Hazard Mater. 2025 Jun 15;490:137854. doi: 10.1016/j.jhazmat.2025.137854. Epub 2025 Mar 4.
The pyrolysis of straw for biochar production offers significant advantages in resource recycling and soil improvement. However, the concurrent effects of biochar on contaminant degradation and biogeochemical cycles in polycyclic aromatic hydrocarbons (PAHs)-contaminated soil remain unclear. This study aims to integrate the roles of functional microorganisms, PAHs degradation pathways, and soil element cycles to elucidate the remediation characteristics of PAHs-contaminated soil. The results demonstrated that the addition of biochar increased the removal rate of phenanthrene (PHE) of PAHs in soil by 75.7 %, and microbial inoculum enhanced this rate to 93.4 %. Both treatments simultaneously improved soil physicochemical properties. Additionally, these amendments influenced the composition of the microbial community, increasing microbial diversity as evidenced by a rise in the Chao1 index by 2.75 % and 4.50 %, and the Shannon index by 8.73 % and 7.60 %, respectively. Moreover, the addition of biochar and microbial inoculum enabled quorum sensing and key microbial species to play a significant role in PHE degradation and ecological restoration. Specifically, these amendments have altered the degradation pathways of soil PHE: biochar promoted PHE degradation via the phthalate pathway, whereas microbial inoculum favored the salicylic acid pathway. Furthermore, both amendments expedited nutrient element cycling in soils. Biochar stimulated nitrate assimilation and the degradation of labile organic carbon compounds, while microbial inoculum enhanced the biodegradation of refractory organic carbon, carbon and nitrogen fixation, and concurrently reduced greenhouse gas emissions. This study presents an innovative strategy for ecologically rehabilitating PHE-contaminated soils by integrating microbial interactions with soil element circulation.
秸秆热解制备生物炭在资源循环利用和土壤改良方面具有显著优势。然而,生物炭对多环芳烃(PAHs)污染土壤中污染物降解和生物地球化学循环的协同影响仍不明确。本研究旨在综合功能微生物、PAHs降解途径和土壤元素循环的作用,以阐明PAHs污染土壤的修复特性。结果表明,添加生物炭使土壤中PAHs的菲(PHE)去除率提高了75.7%,而接种微生物使该去除率提高到93.4%。两种处理均同时改善了土壤理化性质。此外,这些改良措施影响了微生物群落的组成,增加了微生物多样性,Chao1指数分别提高了2.75%和4.50%,Shannon指数分别提高了8.73%和7.60%。此外,添加生物炭和接种微生物使群体感应和关键微生物物种在PHE降解和生态恢复中发挥了重要作用。具体而言,这些改良措施改变了土壤PHE的降解途径:生物炭通过邻苯二甲酸途径促进PHE降解,而接种微生物则有利于水杨酸途径。此外,两种改良措施均加快了土壤中营养元素的循环。生物炭促进了硝酸盐同化和不稳定有机碳化合物的降解,而接种微生物则增强了难降解有机碳的生物降解、碳和氮的固定,同时减少了温室气体排放。本研究提出了一种通过整合微生物相互作用与土壤元素循环来生态修复PHE污染土壤的创新策略。