Sun Jianfan, Fu Yundi, Hu Wenjie, Bo Yanwen, Nawaz Mohsin, Javed Qaiser, Khattak Wajid Ali, Akbar Rasheed, Xiaoyan Wang, Liu Wei, Du Daolin
Institute of Environment and Ecology, School of the Environment and Safety Engineering, Jiangsu University, Zhenjiang, China.
Jiangsu Collaborative Innovation Center of Technology and Material of Water Treatment, Suzhou University of Science and Technology, Suzhou, China.
Front Plant Sci. 2024 Dec 19;15:1503203. doi: 10.3389/fpls.2024.1503203. eCollection 2024.
Litter decomposition is essential for nutrient and chemical cycling in terrestrial ecosystems. Previous research on litter decomposition has often underestimated its impact on soil nutrient dynamics and allelopathy. To address this gap, we conducted a comprehensive study involving both field and greenhouse experiments to examine the decomposition and allelopathic effects of the invasive L. in comparison with the native L. In the field, a 6-month litter bag experiment using leaf litter from and was conducted across three community types: invasive, native, and mixed. Seed germination tests were also performed to investigate the allelopathic effects of decomposing litter. In the greenhouse, a pot experiment with lettuce as a bioindicator was performed to examine the allelochemical inputs from litter decomposition over various time intervals (0, 30, 60, 120, and 180 days). Subsequently, a soil-plant feedback experiment was carried out to further evaluate the effects of decomposing litter on soil biochemistry and plant dynamics. The findings of this study revealed that litter decomposed more rapidly and exhibited greater nitrogen (N) remaining mass compared with in both single and mixed communities. After 180 days, the values for litter mass remaining for and were 36% and 43%, respectively, when grown separately and were 32% and 44%, respectively, in mixed communities. At the invasive site, the soil ammonia and nitrate for increased gradually, reaching 0.89 and 14.93 mg/kg by day 120, compared with the native site with . The soil organic carbon for at the invasive site also increased from 10.6 mg/kg on day 0 to 15.82 mg/kg on day 120, showing a higher increase than that at the native site with . During the initial decomposition stages, all litters released almost all of their allelochemicals. However, at the later stages, litters continued to input nutrients into the soil, but had no significant impact on the soil carbon (C) and N cycling. Notably, litter-mediated plant-soil feedback facilitated the invasion of . In conclusion, this study highlights the significance of litter decomposition as a driver of transforming soil biochemistry, influencing the success of invasive .
凋落物分解对于陆地生态系统中的养分和化学物质循环至关重要。先前关于凋落物分解的研究往往低估了其对土壤养分动态和化感作用的影响。为了填补这一空白,我们进行了一项全面的研究,包括田间和温室实验,以比较入侵种L.与本地种L.的分解和化感作用。在田间,使用来自L.和L.的落叶进行了为期6个月的凋落物袋实验,实验跨越三种群落类型:入侵群落、本地群落和混合群落。还进行了种子萌发试验,以研究分解凋落物的化感作用。在温室中,以生菜作为生物指示剂进行了盆栽实验,以研究不同时间间隔(0、30、60、120和180天)内凋落物分解产生的化感物质输入。随后,进行了一项土壤-植物反馈实验,以进一步评估分解凋落物对土壤生物化学和植物动态的影响。本研究结果表明,与单独和混合群落中的L.相比,L.凋落物分解更快,氮(N)剩余质量更大。180天后,单独生长时L.和L.的凋落物剩余质量值分别为36%和43%,在混合群落中分别为32%和44%。在入侵地点,L.的土壤氨和硝酸盐逐渐增加,到第120天分别达到0.89和14.93 mg/kg,而本地种L.所在的本地地点则较低。入侵地点L.的土壤有机碳也从第0天的10.6 mg/kg增加到第120天的15.82 mg/kg,增幅高于本地种L.所在的本地地点。在初始分解阶段,所有凋落物几乎释放了其所有化感物质。然而,在后期阶段,凋落物继续向土壤中输入养分,但对土壤碳(C)和氮循环没有显著影响。值得注意的是,凋落物介导的植物-土壤反馈促进了L.的入侵。总之,本研究强调了凋落物分解作为改变土壤生物化学的驱动力、影响入侵种L.成功入侵的重要性。