Bouranis John A, McGivern Bridget B, Makke Ghiwa, Jurgensen Sophie K, Bosman Samantha H, Stemple Brooke, Chanton Jeffrey P, Wrighton Kelly C, Tfaily Malak M
Department of Environmental Science, University of Arizona, Tucson, Arizona, USA.
Department of Soil and Crop Sciences, Colorado State University, Fort Collins, Colorado, USA.
Glob Chang Biol. 2025 Aug;31(8):e70390. doi: 10.1111/gcb.70390.
Permafrost thaw represents one of Earth's largest climate feedback risks, potentially releasing vast carbon (C) stores as greenhouse gases (GHG). However, our ability to predict emissions remains limited by poor understanding of how changing organic matter (OM) composition affects microbial carbon processing. We test a metabolism-centered redox framework, which views microbial processes as coupled oxidative-reductive reactions, to mechanistically explain how organic matter metabolite quality controls greenhouse gas production in permafrost-affected peatland ecosystems. Rather than relying solely on geochemical redox measurements, our approach examines how microbes balance electron flow through metabolic pathways. Using active layer peat (9-19 cm) from contrasting environments (bog and fen), we employed multi-omics approaches, including metabolomics, metagenomics, and metatranscriptomics, to link OM chemistry to microbial function. Our results reveal distinct dissolved organic matter metabolite composition, with fen systems enriched in compounds with higher substrate quality (low molecular weight (MW) sugars with high H:C ratios and low aromaticity) and bog systems dominated by compounds with lower substrate quality (high MW phenols with lower H:C ratios and higher aromaticity). In fen samples, these sugar-like compounds correlated with higher oxidative metabolism and methanogenesis, supported by increased glycolysis gene expression. Initially, electrons from increased oxidative metabolism were balanced through nitrate and sulfate reduction, but as these electron acceptors were depleted, methanogenesis increased to maintain redox balance. Fen samples showed rapid degradation of both high- and low-substrate-quality compounds, suggesting sufficient energy for efficient C cycling. Conversely, bog samples exhibited more polyphenolic compounds, lower glycolysis activity, and higher stress-related gene expression, suggesting energy was diverted towards cell maintenance under acidic conditions rather than C processing. This approach suggests that predicting greenhouse gas emissions requires an understanding of how organic matter quality shapes microbial energy allocation strategies, providing a mechanistic framework for improving emission predictions from permafrost-affected peatlands and similar ecosystems.
永久冻土融化是地球面临的最大气候反馈风险之一,有可能将大量碳(C)储存以温室气体(GHG)的形式释放出来。然而,由于我们对不断变化的有机物质(OM)组成如何影响微生物碳处理的了解不足,我们预测排放的能力仍然有限。我们测试了一个以代谢为中心的氧化还原框架,该框架将微生物过程视为耦合的氧化还原反应,以机械地解释有机物质代谢物质量如何控制受永久冻土影响的泥炭地生态系统中的温室气体产生。我们的方法不是仅仅依赖地球化学氧化还原测量,而是研究微生物如何通过代谢途径平衡电子流。利用来自不同环境(沼泽和湿地)的活动层泥炭(9 - 19厘米),我们采用了多组学方法,包括代谢组学、宏基因组学和宏转录组学,将OM化学与微生物功能联系起来。我们的结果揭示了不同的溶解有机物质代谢物组成,湿地系统富含底物质量较高的化合物(具有高H:C比和低芳香性的低分子量(MW)糖),而沼泽系统则以底物质量较低的化合物为主(具有较低H:C比和较高芳香性的高MW酚类)。在湿地样本中,这些类似糖的化合物与较高的氧化代谢和甲烷生成相关,糖酵解基因表达增加支持了这一点。最初,来自增加的氧化代谢的电子通过硝酸盐和硫酸盐还原得到平衡,但随着这些电子受体的耗尽,甲烷生成增加以维持氧化还原平衡。湿地样本显示高底物质量和低底物质量化合物都快速降解,表明有足够的能量进行有效的碳循环。相反,沼泽样本表现出更多的多酚类化合物、较低的糖酵解活性和较高的应激相关基因表达,表明在酸性条件下能量被转移用于细胞维持而非碳处理。这种方法表明,预测温室气体排放需要了解有机物质质量如何塑造微生物能量分配策略,为改进受永久冻土影响的泥炭地和类似生态系统的排放预测提供了一个机械框架。