Department of Plant Sciences, University of Cambridge, Cambridge, UK.
Natural Resources Canada, Great Lakes Forestry Centre, Sault Ste. Marie, Ontario.
Glob Chang Biol. 2018 Nov;24(11):5110-5122. doi: 10.1111/gcb.14391. Epub 2018 Aug 26.
Boreal lakes are major components of the global carbon cycle, partly because of sediment-bound heterotrophic microorganisms that decompose within-lake and terrestrially derived organic matter (t-OM). The ability for sediment bacteria to break down and alter t-OM may depend on environmental characteristics and community composition. However, the connection between these two potential drivers of decomposition is poorly understood. We tested how bacterial activity changed along experimental gradients in the quality and quantity of t-OM inputs into littoral sediments of two small boreal lakes, a dark and a clear lake, and measured the abundance of operational taxonomic units and functional genes to identify mechanisms underlying bacterial responses. We found that bacterial production (BP) decreased across lakes with aromatic dissolved organic matter (DOM) in sediment pore water, but the process underlying this pattern differed between lakes. Bacteria in the dark lake invested in the energetically costly production of extracellular enzymes as aromatic DOM increased in availability in the sediments. By contrast, bacteria in the clear lake may have lacked the nutrients and/or genetic potential to degrade aromatic DOM and instead mineralized photo-degraded OM into CO . The two lakes differed in community composition, with concentrations of dissolved organic carbon and pH differentiating microbial assemblages. Furthermore, functional genes relating to t-OM degradation were relatively higher in the dark lake. Our results suggest that future changes in t-OM inputs to lake sediments will have different effects on carbon cycling depending on the potential for photo-degradation of OM and composition of resident bacterial communities.
北方湖泊是全球碳循环的主要组成部分,部分原因是由于沉积物结合的异养微生物分解了湖泊内和陆地衍生的有机物质(t-OM)。沉积物细菌分解和改变 t-OM 的能力可能取决于环境特征和群落组成。然而,这两个潜在分解驱动因素之间的联系尚未得到充分理解。我们通过实验测试了在两个小型北方湖泊的浅滩沉积物中,t-OM 输入的质量和数量沿实验梯度的变化如何影响细菌活性,并测量了操作分类单元和功能基因的丰度,以确定细菌响应的机制。我们发现,随着沉积物孔隙水中芳香族溶解有机物质(DOM)的增加,BP 在两个湖泊中均呈下降趋势,但湖泊之间的这种模式背后的过程不同。随着沉积物中芳香族 DOM 的可用性增加,深色湖泊中的细菌投入了能量昂贵的胞外酶的生产。相比之下,清澈湖泊中的细菌可能缺乏降解芳香族 DOM 的营养物质和/或遗传潜力,而是将光降解 OM 矿化为 CO 2 。两个湖泊的群落组成存在差异,溶解有机碳和 pH 值的浓度区分了微生物群落。此外,与 t-OM 降解相关的功能基因在深色湖中相对较高。我们的研究结果表明,未来湖泊沉积物中 t-OM 输入的变化将根据 OM 的光降解潜力和驻留细菌群落的组成,对碳循环产生不同的影响。