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Microbial and biogeochemical responses to changing precipitation patterns in grassland ecosystems.

机译:微生物和生物地球化学对草原生态系统中降水变化的响应。

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摘要

Global circulation models predict that precipitation patterns in grasslands will both intensify and be characterized by more severe drought in the future. In these systems, the availability of water strongly controls ecosystem function, so changes in precipitation are likely to significantly alter biological communities and biogeochemical dynamics. Since these biogeochemical changes could feed back on climate drivers by influencing regional to global scale energy and water balance, predicted changes in grassland precipitation call for a better understanding of relationships between water availability and grassland biogeochemical dynamics.;My dissertation aimed to address how changing rainfall patterns affect biogeochemical cycling and soil microbial communities in grasslands. I first tested the generality of controls over soil organic matter storage in temperate grasslands by studying existing spatial gradients in soil carbon and nitrogen, as they relate to the spatial variation in average precipitation and temperature, and soil texture. I found that statistical models developed in US grasslands overestimated soil organic carbon and underestimated soil organic nitrogen in Chinese grasslands. However, when I incorporated nitrogen deposition and historical land use using a simulation model, it resulted in more accurate model estimates for this region. This work suggests that nitrogen deposition and historical land use legacies may need to be considered to accurately describe biogeochemical dynamics in Chinese grasslands and better predict the vulnerability of global carbon stocks to loss.;Responses of ecosystems to changes through time are often somewhat different than relationships gleaned from large-scale spatial gradients. At the local scale, I found that an 11-year drought can significantly alter biogeochemical and ecosystem dynamics in the highly drought-resistant shortgrass steppe. Here, soil inorganic nitrogen availability increased up to 4-fold in plots receiving 25% of summer precipitation. This accumulation of nitrogen under drought may explain the higher plant tissue nitrogen and N2O flux observed under recovery. A more "open" nitrogen cycle that I observed following severe drought could affect the impact of drought on grassland ecosystems, as well as the timescale of recovery.;Soil microbial community composition was also altered by this 11-year drought manipulation in the shortgrass steppe, and these differences persisted even after communities were subject to the same moisture conditions for 36 hours in the lab. In this lab experiment, I also identified specific microbial groups that grew under a certain moisture levels, presenting evidence of moisture niche partitioning in microbial communities. However, this niche differentiation wasn't realized in the field; communities that grew under dry conditions in the lab were not similar to those that emerged under long-term drought plots. Overall, this work suggests that contrary to previous assumptions, microbial communities display legacies from long-term field treatments, and that although soil moisture has the potential to drive microbial community composition through niche partitioning, this factor may not always be the primary driver of long-term community composition.;Microbial communities were also sensitive to altered precipitation timing in the tallgrass prairie. In addition, communities that were subject to intensified precipitation patterns in the field respired less than control soils after laboratory rewetting events, but respiration rates of the different field treatments converged after 100 days under the same conditions. Surprisingly, species composition of these communities was more sensitive to drying and rewetting pulses in the lab than those from the control. Together, these results show that microbial communities display legacies to altered precipitation timing, in addition to drought, but community composition is not necessarily tightly linked to respiration.;Overall, my dissertation work suggests that grasslands will be sensitive to extreme shifts in precipitation, and that biogeochemical and microbial responses could influence how grasslands are altered under future precipitation regimes. However, my work also shows that precipitation is not the only factor controlling biogeochemical and microbial community dynamics in grasslands, even under rainfall manipulations and across precipitation gradients. Therefore, the response of grasslands to other environmental factors -- that shift with precipitation changes or are predicted to change independently -- should not be overlooked.
机译:全球环流模型预测,未来草原的降水模式将加剧,并以更严重的干旱为特征。在这些系统中,水的可利用性强烈地控制着生态系统的功能,因此降水的变化可能会显着改变生物群落和生物地球化学动力学。由于这些生物地球化学变化可以通过影响区域乃至全球规模的能源和水平衡而反馈给气候驱动因素,因此预测的草地降水变化需要更好地了解水的可利用性与草地生物地球化学动力学之间的关系。格局影响草原的生物地球化学循环和土壤微生物群落。我首先通过研究土壤碳和氮的现有空间梯度来检验温带草原土壤有机质存储控制的一般性,因为它们与平均降水和温度以及土壤质地的空间变化有关。我发现,美国草原开发的统计模型高估了中国草原的土壤有机碳,而低估了中国草原的土壤有机氮。但是,当我使用模拟模型将氮沉降和历史土地利用结合起来时,就可以对该区域进行更准确的模型估算。这项工作表明可能需要考虑氮的沉积和土地的历史遗留特征,以准确地描述中国草原的生物地球化学动态,并更好地预测全球碳储量对损失的脆弱性。生态系统对时间变化的响应通常与关系有所不同。从大规模的空间梯度收集。在当地范围内,我发现11年的干旱会大大改变高度抗旱的短草草原的生物地球化学和生态系统动态。在这里,土壤无机氮的利用率在接受夏季降水25%的土地上增加了4倍。干旱下氮的这种积累可能解释了在恢复下观察到的较高的植物组织氮和N2O通量。我在严重干旱后观察到一个更“开放”的氮循环,这可能会影响干旱对草原生态系统的影响以及恢复的时间尺度。;在短草草原上进行了11年的干旱处理,土壤微生物群落组成也发生了变化。 ,即使在实验室中使社区在相同的湿度条件下放置36个小时,这些差异仍然存在。在此实验室实验中,我还确定了在一定湿度下生长的特定微生物群,从而提供了微生物群落中水分生态位分配的证据。但是,这种利基差异在该领域并未实现。在实验室中,在干旱条件下生长的群落与在长期干旱地区出现的群落不同。总体而言,这项工作表明,与以前的假设相反,微生物群落显示出长期田间处理的遗留物,并且尽管土壤水分有潜力通过生态位分配来驱动微生物群落组成,但这一因素可能并不总是导致长期微生物生长的主要动力。群落组成。;微生物群落对高草草原的降雨时间变化也很敏感。此外,在实验室再湿润事件后,田间降雨模式加剧的社区的呼吸少于对照土壤,但是在相同条件下100天后,不同田间处理的呼吸速率趋于一致。出乎意料的是,这些群落的物种组成对实验室中的干燥和再润湿脉冲比对对照更敏感。总之,这些结果表明,除干旱外,微生物群落还显示出降雨时间变化的遗留物,但群落组成不一定与呼吸紧密相关。总的来说,我的论文工作表明草原将对降雨的极端变化敏感,并且生物地球化学和微生物反应可能会影响未来降雨制度下草地的变化方式。但是,我的工作还表明,即使在降雨操纵和整个降水梯度下,降水也不是控制草原生物地球化学和微生物群落动态的唯一因素。因此,草原对其他环境因素的响应(随降水变化而变化或预计会独立变化)的响应不应忽视。

著录项

  • 作者

    Evans, Sarah E.;

  • 作者单位

    Colorado State University.;

  • 授予单位 Colorado State University.;
  • 学科 Biology Ecology.;Biology Microbiology.;Biogeochemistry.
  • 学位 Ph.D.
  • 年度 2012
  • 页码 147 p.
  • 总页数 147
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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