在原始和受干扰泥炭地中,与藻相关的甲烷氧化菌是一种有弹性的甲烷生物过滤器

A. Putkinen
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引用次数: 1

摘要

北方泥炭地是非常重要的碳汇。这一功能主要是由一种形成泥炭的植物——泥炭藓实现的。除了通过逐渐创造共生条件来减缓分解外,它还为生物提供了一个庇护所,减少了甲烷(CH4)的排放——甲烷是一种在水下缺氧泥炭层中形成的有效温室气体。这些生物,甲烷氧化细菌(甲烷氧化菌,MOB),栖息在死的,充满水的透明细胞的Sphagnum和提供植物二氧化碳(CO2)从CH4氧化。虽然一些研究已经证实了sphagum -associated methanotrophs (SAM)的存在,但它们对苔藓的依赖程度以及环境条件如何影响其群落组成和活动仍不清楚。本文对原始和受干扰地区泥炭地不同发展阶段的SAM动态进行了评价。研究主要基于分子方法,针对mob特异性pmoA基因,以及实验室培养,包括稳定同位素探测。在第一项研究中,通过测试SAM是否会通过水相分散来评估SAM与苔藓之间的联系。这种被认为代表兼性共生的特性在两个实验中得到了证明。在田间,将无CH4氧化活性的苔藓移栽在有CH4氧化活性的苔藓旁边。在一个月内,邻近苔藓的SAM群落变得更加相似。通过将不活跃的苔藓浸泡在具有高CH4氧化活性的扁平孔隙水中,进一步证实了水基定植。在11 h内,活性被诱导,SAM丰度显著增加。另外两项研究显示,在原始时间序列和复植过的泥炭地梯度上,SAM群落组成模式相似。一般环境条件似乎并不是控制泥鳅群落组成的因素,而是控制泥鳅群落组成的因素。不同类型的SAM似乎有其偏好的环境生态位,其中Ia型MOB在年轻演替阶段较为活跃,而II型MOB在较老的、水文较为稳定的演替阶段较为活跃。尽管群落存在差异,但CH4氧化电位在梯度上没有差异,提示功能冗余。只有一些较干燥的沼泽样品未显示任何可检测的CH4氧化,表明地下水位对SAM活性的调节作用。过渡梯度泥炭层的MOB群落格局相似,但CH4氧化潜力随演替而增加。通过水分散的能力提供了一种从干旱等干扰中恢复的机制,预计干旱会随着气候变暖而增加。此外,SAM群落的多样性和功能冗余性增强了由活的Sphagnum苔藓形成的重要CH4生物过滤器的弹性。最年轻割草点苔藓中潜在的SAM活性促进了泥炭地移植实践作为一种工具,不仅可以促进植被恢复过程,还可以减轻受干扰泥炭地再湿润和恢复过程中形成的CH4排放。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Sphagnum-associated methanotrophs : a resilient CH4 biofilter in pristine and disturbed peatlands
Boreal peatlands are highly important sinks for carbon (C). This function is enabled largely by one peat-forming plant, the Sphagnum moss. In addition to slowing the decomposition by gradually creating ombrotrophic conditions, it gives a shelter for the organisms mitigating the emissions of methane (CH4) – an effective greenhouse gas formed in submerged, anoxic peat layers. These organisms, methane oxidizing bacteria (methanotrophs, MOB), inhabit the dead, water-filled hyaline cells of the Sphagnum and provide the plant carbon dioxide (CO2) derived from the CH4 oxidation. While several studies have confirmed the presence of Sphagnum-associated methanotrophs (SAM), it is still unclear how dependent they are on the mosses and how environmental conditions affect their community composition and activity. This thesis evaluated SAM dynamics in the different stages of peatland development on both pristine and disturbed areas. Studies were based mainly on molecular methods, targeting the MOB-specific pmoA gene, and laboratory incubations, including stable isotope probing. In the first study, the connection between the SAM and the mosses was assessed by testing whether the SAM will disperse through the water phase. This trait, considered to represent a facultative symbiosis, was demonstrated in two experiments. In the field, mosses inactive in CH4 oxidation were transplanted next to active ones. Within a month, SAM communities of the neighboring mosses become more similar. The water-based colonization was further confirmed by bathing inactive mosses in flark pore water that showed high CH4 oxidation activity. Within just 11 h, activity was induced and the SAM abundance significantly increased in the treated mosses. The other two studies revealed similar SAM community composition patterns on a pristine chronosequence and on a gradient of re-vegetating cutover peatlands. Instead of the Sphagnum species, the general environmental conditions seemed to control the SAM community composition. Different types of SAM seemed to have their preferred environmental niches, with the type Ia MOB present and active especially in the young succession stages and the type II MOB in the older, hydrologically more stable stages. Despite the community differences, the potential CH4 oxidation did not differ along the gradients, suggesting functional redundancy. Only some drier bog samples did not show any detectable CH4 oxidation, demonstrating the regulatory role of the water table level on the SAM activity. The peat layers of the cutover gradient showed similar MOB community patterns but the potential CH4 oxidation increased with succession. The ability to disperse through the water provides a recovery mechanism from disturbances such as droughts, which are predicted to increase with climate warming. In addition, the diversity and functional redundancy of the SAM communities enhance the resilience of this important CH4 biofilter formed by the living Sphagnum mosses. The potential SAM activity in the mosses of the youngest cutover site promotes the Sphagnum transplantation practice as a tool to not only enhance the re-vegetation process, but also to mitigate the CH4 emissions formed in the rewetting and restoration of disturbed peatlands.
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