Jia Xiaohui, Zhang Baiyu, Han Yonghe, Guan Jiunian, Gao Hongjie, Guo Ping
Key Laboratory of Groundwater Resources and Environment Ministry of Education, College of New Energy and Environment, Jilin University, Changchun 130012, PR China; Jilin Provincial Key Laboratory of Water Resources and Environment, Jilin University, Changchun 130012, PR China.
Department of Civil Engineering, Faculty of Engineering and Applied Science, Memorial University, St. John' s, NL A1B 3X5, Canada.
Environ Int. 2025 May;199:109471. doi: 10.1016/j.envint.2025.109471. Epub 2025 Apr 30.
Biochar, as an amendment to enhance phytoremediation of heavy metal contamination, can mediate reactive oxygen species (ROS) generation. However, the role of biochar-mediated ROS (BMR) during soil-plant phytoremediation remains inadequately understood. In this study, a combination of pot experiments, chemical extraction, and partial least squares path modeling (PLS-PM) was employed to investigate BMR dynamics and their influence on chromium (Cr) accumulation and detoxification in plants. Biochar addition promoted Cr removal efficiency and decreased ROS concentrations in soil, notably reaching the largest removal efficiency of 80.60 % and the lowest ROS concentration of 37.53 μmol/kg in BC-3 group at 90d. Decreased ROS concentrations in soil facilitated the plant absorbing water-soluble Cr (VI), adsorbed Cr (VI), and chromate-precipitated Cr (VI) in soil, and enhanced Cr accumulation in metabolically inactive compartments (cell walls and vacuoles). When biochar was added at concentrations of 2 % and 3 % (w/w), ROS concentrations in plant tissues decreased to signaling molecule thresholds. This reduction further stimulated antioxidant enzyme activity, promoted the reduction of Cr (VI) within subcellular organelles, and enhanced Cr cell wall fixation and vacuolar compartmentation, ultimately achieving their synergistic integration with Cr detoxification with accumulation. This study provides an in-depth understanding of BMR-related mechanisms during phytoremediation and valuable insights into strategies for enhancing mitigation of variable valence heavy metals in soils.
生物炭作为一种用于增强重金属污染植物修复的改良剂,可介导活性氧(ROS)的产生。然而,生物炭介导的ROS(BMR)在土壤-植物修复过程中的作用仍未得到充分理解。在本研究中,采用盆栽试验、化学提取和偏最小二乘路径建模(PLS-PM)相结合的方法,研究BMR动态及其对植物中铬(Cr)积累和解毒的影响。添加生物炭提高了Cr去除效率,并降低了土壤中的ROS浓度,在90天时,BC-3组的去除效率最高达到80.60%,ROS浓度最低达到37.53μmol/kg。土壤中ROS浓度的降低促进了植物吸收土壤中水溶性Cr(VI)、吸附态Cr(VI)和铬酸盐沉淀态Cr(VI),并增强了代谢非活性区室(细胞壁和液泡)中的Cr积累。当以2%和3%(w/w)的浓度添加生物炭时,植物组织中的ROS浓度降低到信号分子阈值。这种降低进一步刺激了抗氧化酶活性,促进了亚细胞器内Cr(VI)的还原,并增强了Cr在细胞壁的固定和液泡分隔,最终实现了它们与Cr解毒和积累的协同整合。本研究深入了解了植物修复过程中与BMR相关的机制,并为增强土壤中可变价重金属缓解策略提供了有价值的见解。