Plant litter decomposition drives soil biogeochemical cycling, yet how warming alters interactions among litter quality, microbial communities, and soil C, N, and P transformations remains unclear. We conducted a 90-day soil microcosm incubation at 15, 25, and 35 °C using single and mixed litter of Calamagrostis angustifolia and Carex lasiocarpa from the Xingkai Lake wetland to assess warming effects on decomposition, microbial communities, and C, N, and P dynamics. Warming significantly accelerated decomposition, with the highest decomposition constant observed for mixed litter at 35 °C. Mixed litter showed greater temperature sensitivity at 25–35 °C, whereas decomposition rates were weakly correlated with initial litter C/N, C/P, and N/P ratios. Warming and decomposition time reshaped microbial communities, with bacterial diversity increasing over time and fungal diversity declining at 35 °C. Despite accelerated mass loss, C, N, and P dynamics remained asynchronous, with net C release in some treatments, net N accumulation, and litter-dependent P responses. Three-way ANOVA, RDA, and partial least squares structural equation modeling were used to examine associations among environmental factors, microbial attributes, litter decomposition, and soil C, N, and P status. Overall, warming modifies relationships among litter quality, microbial communities, and C, N, and P transformations, providing insights into freshwater wetland responses to climate warming.
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Wang et al. (2026) studied this question.
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