Department of Physical Geography, Stockholm University, Stockholm, Sweden.
Bolin Centre for Climate Research, Stockholm University, Stockholm, Sweden.
Glob Chang Biol. 2024 Oct;30(10):e17522. doi: 10.1111/gcb.17522.
Climate change is causing an intensification of soil drying and rewetting events, altering microbial functioning and potentially destabilizing soil organic carbon. After rewetting, changes in microbial community carbon use efficiency (CUE), investment in life history strategies, and fungal to bacterial dominance co-occur. Still, we have yet to generalize what drives these dynamic responses. Here, we collated 123 time series of microbial community growth (G, sum of fungal and bacterial growth, evaluated by leucine and acetate incorporation, respectively) and respiration (R) after rewetting and calculated CUE = G/(G + R). First, we characterized CUE recovery by two metrics: maximum CUE and time to maximum CUE. Second, we translated microbial growth and respiration data into microbial investments in life history strategies (high yield (Y), resource acquisition (A), and stress tolerance (S)). Third, we characterized the temporal change in fungal to bacterial dominance. Finally, the metrics describing the CUE recovery, investment in life history strategies, and fungal to bacterial dominance after rewetting were explained by environmental factors and microbial properties. CUE increased after rewetting as fungal dominance declined, but the maximum CUE was explained by the CUE under moist conditions, rather than specific environmental factors. In contrast, higher soil pH and carbon availability accelerated the decline of microbial investment in stress tolerance and fungal dominance. We conclude that microbial CUE recovery is mostly driven by the shifting microbial community composition and the metabolic capacity of the community, whereas changes in microbial investment in life history strategies and fungal versus bacterial dominance depend on soil pH and carbon availability.
气候变化导致土壤干燥和再湿润事件加剧,改变了微生物的功能,可能使土壤有机碳不稳定。再湿润后,微生物群落碳利用效率(CUE)、生活史策略投资和真菌与细菌优势的变化同时发生。然而,我们还没有概括出是什么驱动了这些动态响应。在这里,我们整理了 123 个微生物群落生长(G,通过分别掺入亮氨酸和醋酸盐评估的真菌和细菌生长的总和)和再湿润后呼吸(R)的时间序列,并计算了 CUE=G/(G+R)。首先,我们通过两个指标来描述 CUE 的恢复:最大 CUE 和达到最大 CUE 的时间。其次,我们将微生物生长和呼吸数据转化为微生物在生活史策略中的投资(高产量(Y)、资源获取(A)和应激耐受(S))。第三,我们描述了真菌与细菌优势的时间变化。最后,描述再湿润后 CUE 恢复、生活史策略投资和真菌与细菌优势的指标由环境因素和微生物特性解释。再湿润后 CUE 增加,因为真菌优势下降,但最大 CUE是由湿润条件下的 CUE 解释的,而不是特定的环境因素。相比之下,较高的土壤 pH 值和碳可利用性加速了微生物应激耐受和真菌优势投资的下降。我们得出的结论是,微生物 CUE 的恢复主要是由微生物群落组成的变化和群落的代谢能力驱动的,而生活史策略投资和真菌与细菌优势的变化取决于土壤 pH 值和碳可利用性。