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AN ECOLOGICAL AND PALEOECOLOGICAL STUDY OF THE VEGETATION IN THE BIG WOODS REGION OF MINNESOTA.

机译:明尼苏达州大森林地区的植被生态学和古生态学研究。

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摘要

The Big Woods was a large area of deciduous forest along the prairie-woodland border in south-central Minnesota. Records of the original land surveys were used to reconstruct the presettlement vegetation, and fossil-pollen analysis was used to reconstruct the vegetation for the past several thousand years.;Computer plots of bearing trees were used to map the vegetation of the Big Woods region. The characteristic trees of the Big Woods were elm, basswood, ironwood, sugar maple, ash, hickory, and butternut. Although the Big Woods has been described as a sugar maple-basswood forest, the most abundant tree was elm. Basswood and ironwood were widespread. Sugar maple had a more restricted distribution, occurring in the areas of lowest fire frequency. Oak scrub occurred on rolling, well-drained topography south and east of the Big Woods; while aspen-parkland occurred on level, poorly drained topography west of the Big Woods. The vegetation is poorly correlated with the regional climatic gradients. Fire frequency strongly controlled the overall pattern of the vegetation. The primary variables influencing fire frequency were water bodies, topography, and the existing vegetation. Firebreaks sharply formed the prairie-woodland border. Fire-tolerant oak and aspen woodlands formed a buffer zone between the Big Woods and prairie, except where very effective firebreaks formed sharp boundaries between them. The oak woodland along the prairie-woodland border has frequently been described as savanna; however, the oak-dominated vegetation in the Big Woods region was dense scrub. A review of the literature reveals that the interpretation of savanna in other areas is questionable.;The pollen and sediment stratigraphy of three sites was investigated--Wolsfeld Lake and Wolsfeld Woods Marsh in the northeastern Big Woods and French Lake near the western margin of the Big Woods. Most of the Big Woods was prairie during the mid-Holocene. Oak woodland began invading prairie about 5000 years ago in the eastern Big Woods, then expanded westward, becoming established at French Lake 2400 years ago. Oak woodland persisted until 300 years ago, when ironwood, elm, basswood, and eventually sugar maple expanded and became dominant. The changes from prairie to oak woodland and from oak woodland to "bigwoods" must have required reductions in fire frequency, probably caused by increased precipitation and decreased temperature. About 100 years before the expansion of bigwoods sediment influx increased at the coring site in Wolsfeld Lake and continuous peat began to accumulate in Wolsfeld Woods Marsh, supporting the hypothesis that increased precipitation triggered the expansion of bigwoods. A conceptual model is presented, in which climatic changes trigger vegetation changes, but interactions among the existing vegetational pattern, fire, and topography cause climatic thresholds for vegetational change to vary in space and time.;The bearing-tree data in the land-survey records have been widely used for reconstructing vegetation. Contrary to the assumption of many ecologists, however, the bearing trees were not necessarily the closest trees to the corner posts but, in fact, were a biased sample of the vegetation. The purpose of bearing trees was to facilitate relocation of the corners, and the surveyors chose the trees most likely to achieve this purpose. The most common misuses of the data have been purported statistical analyses of surveyor bias and calculations of absolute tree density. These require the unlikely and untestable assumption that trees were randomly arranged throughout the entire area from which the trees are a sample. Reliable calculations of absolute tree density also require the assumption of no surveyor bias. Despite these limitations, if used with a proper perspective towards their original purpose, the land-survey data are extremely valuable for reconstructing vegetation.
机译:大森林是在明尼苏达州中南部的草原-林地边界沿线的一片落叶林。使用原始土地调查的记录来重建预设植被,并使用化石花粉分析来重建过去几千年的植被。;用带轴承的计算机绘图来绘制大森林地区的植被。大树林的特色树是榆木,bass木,铁木,糖枫,白蜡木,山核桃木和胡桃木。尽管大树林曾被描述为糖枫-木森林,但最丰富的树是榆树。 ass木和铁木广泛存在。枫糖的分布更受限制,发生在火灾频率最低的地区。橡树灌木丛发生在大树林以南和东部的起伏,排水良好的地形上。而白杨公园地势平坦,大树林西部的地表排水不畅。植被与区域气候梯度的相关性很差。火灾频率强烈地控制了植被的总体格局。影响火灾发生频率的主要变量是水体,地形和现有植被。防火带迅速形成了草原与林地的边界。耐火的橡树和白杨林地在大树林和草原之间形成缓冲区,除非非常有效的防火带在两者之间形成清晰的边界。草原-林地边界沿线的橡树林常被称为大草原。然而,大森林地区以橡树为主的植被是茂密的灌木丛。文献回顾表明,其他地区对热带稀树草原的解释存在疑问。;对三个地点的花粉和沉积物地层进行了调查-东北大森林的沃尔斯费尔德湖和沃尔斯费尔德森林沼泽和西湖边缘附近的法国湖。大树林。全新世时期,大多数大树林都是草原。橡树林地大约在5000年前开始入侵大比格斯东部的草原,然后向西扩展,在2400年前在法国湖建立。橡树林一直持续到300年前,那时铁木,榆木,bass木和糖枫逐渐扩大并占主导地位。从草原到橡木林地,再到从橡木林地到“大树林”的变化,必须减少火灾发生的频率,这可能是由于降水增加和温度降低引起的。在沃尔夫斯费尔德湖取芯地的大林增长之前,沉积物的涌入量增加,并且连续的泥炭开始在沃尔斯费尔德森林沼泽中积累,大约100年之前,这支持了降水增加引发大森林扩张的假说。提出了一个概念模型,其中气候变化触发了植被变化,但是现有植被格局,火灾和地形之间的相互作用导致植被变化的气候阈值随时间和空间而变化。;土地测量中的方位树数据记录已被广泛用于重建植被。然而,与许多生态学家的假设相反,承压树木不一定是最靠近角柱的树木,而实际上是有偏差的植被样本。承栽树木的目的是为了方便角落的重新安置,测量师选择了最有可能达到此目的的树木。据称,最常见的数据滥用是对测量师偏见的统计分析和绝对树密度的计算。这些要求不太可能且不可测试的假设是,树木是在样本所在的整个区域中随机排列的。可靠的绝对树密度计算还需要假设没有验船师偏差。尽管存在这些限制,但如果以正确的眼光看待原始目的,土地调查数据对于重建植被非常有价值。

著录项

  • 作者

    GRIMM, ERIC CHRISTOPHER.;

  • 作者单位

    University of Minnesota.;

  • 授予单位 University of Minnesota.;
  • 学科 Ecology.;Geographic information science.
  • 学位 Ph.D.
  • 年度 1981
  • 页码 379 p.
  • 总页数 379
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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