Tian Kai, Wang Xin, Ye Rumeng, Wang Yingqi, Chen Zhicheng, Liu Xiaojing, Wang Wenxia, Yao Lunguang
Henan Field Observation and Research Station of Headwork Wetland Ecosystem of the Central Route of South-to-North Water Diversion Project, School of Life Sciences and Agricultural Engineering Nanyang Normal University Nanyang China.
Henan International Joint Laboratory of Watershed Ecological Security in the Water Source Area of the Middle Route of South-to-North Water Diversion Project Nanyang China.
Ecol Evol. 2025 Jan 28;15(2):e70918. doi: 10.1002/ece3.70918. eCollection 2025 Feb.
Photodegradation-photochemical mineralization of standing litters-often exerts a legacy effect aiding biodegradation in soil (PLE), which is overlooked in deciduous forests containing marcescent leaves. Meanwhile, increasing anthropogenic microplastics have deposited in forests, how they would affect the PLE on subsequent litter bio-decomposition is currently unknown. Here, we employed an ultraviolet-accelerated aging chamber to replicate the abiotic photodegradation process of a naturally marcescent tree, , then manipulated mesocosm bio-incubations to quantify how decomposers (microbial alone or with soil animals) and microplastic contamination would interactively affect the PLE. We found abiotic photodegradation significantly decreased litter lignin content before and after the bio-incubation. During an early phase decomposition, lignin lost greatly and displayed a crucial role in determining the ways that soil animal and photodegradation affect the bio-decomposition. Microbial decomposer alone led to a positive PLE universally. Soil animals depressed microbial biomass and inhibited the microbial-mediated PLE in unpolluted mesocosms but intensified the PLE in contaminated soils. We conclude that decomposer interactions can attenuate PLE, but microplastics will disrupt the established equilibrium, making contaminated soil more susceptible to photodegradation-induced litter chemical changes. This promotes integration of radiation and emerging pollution to further our understanding of biogeochemical cycle in forest ecology.
凋落物的光降解 - 光化学矿化作用通常会产生遗留效应,有助于土壤中的生物降解(PLE),而在含有枯叶的落叶林中这一效应被忽视了。与此同时,越来越多的人为微塑料沉积在森林中,它们如何影响后续凋落物生物分解中的PLE目前尚不清楚。在这里,我们使用紫外线加速老化箱来模拟天然枯叶树的非生物光降解过程,然后通过中宇宙生物培养来量化分解者(单独的微生物或与土壤动物一起)和微塑料污染如何相互作用影响PLE。我们发现非生物光降解在生物培养前后显著降低了凋落物木质素含量。在早期分解过程中,木质素大量损失,并且在决定土壤动物和光降解影响生物分解的方式中起着关键作用。仅微生物分解者普遍导致正的PLE。土壤动物降低了微生物生物量,并在未受污染的中宇宙中抑制了微生物介导的PLE,但在受污染的土壤中增强了PLE。我们得出结论,分解者之间的相互作用可以减弱PLE,但微塑料会破坏已建立的平衡,使受污染的土壤更容易受到光降解引起的凋落物化学变化的影响。这促进了辐射和新出现的污染的整合,以进一步加深我们对森林生态系统中生物地球化学循环的理解。