University of Missouri, 203 Natural Resources Building, Columbia, MO 65211, USA.
USDA Forest Service, Northern Research Station, University of Missouri, 202 Natural Resources Building, Columbia, MO 65211, USA.
Sci Total Environ. 2014 Apr 1;476-477:591-600. doi: 10.1016/j.scitotenv.2014.01.048. Epub 2014 Feb 1.
Regionally-distinctive open oak forest ecosystems have been replaced either by intensive agriculture and grazing fields or by denser forests throughout eastern North America and Europe. To quantify changes in tree communities and density in the Missouri Plains, a grassland-forest landscape, we used historical surveys from 1815 to 1864 and current surveys from 2004 to 2008. To estimate density for historical communities, we used the Morisita plotless density estimator and applied corrections for surveyor bias. To estimate density for current forests, we used Random Forests, an ensemble regression tree method, to predict densities from known values at plots using terrain and soil predictors. Oak species decreased from 62% of historical composition to 30% of current composition and black and white oaks historically were dominant species across 93% of the landscape and currently were dominant species across 42% of the landscape. Current forest density was approximately two times greater than historical densities, demonstrating loss of savanna and woodlands and transition to dense forest structure. Average tree diameters were smaller than in the past, but mean basal area and stocking remained similar over time because of the increase in density in current forests. Nevertheless, there were spatial differences; basal area and stocking decreased along rivers and increased away from rivers. Oak species are being replaced by other species in the Missouri Plains, similar to replacement throughout the range of Quercus. Long-term commitment to combinations of prescribed burning and silvicultural prescriptions in more xeric sites may be necessary for oak recruitment. Restoration of open oak ecosystems is a time-sensitive issue because restoration will become increasingly costly as oaks are lost from the overstory and the surrounding matrix becomes dominated by non-oak species.
在北美东部和欧洲,具有地域特色的开阔栎树林生态系统要么被集约化农业和放牧地取代,要么被更密集的森林所取代。为了量化密苏里平原(一个草原-森林景观)中树木群落和密度的变化,我们利用了 1815 年至 1864 年的历史调查数据和 2004 年至 2008 年的当前调查数据。为了估计历史群落的密度,我们使用了无样方 Morisita 密度估计器,并对调查员偏差进行了修正。为了估计当前森林的密度,我们使用了随机森林(一种集成回归树方法),从已知的地形和土壤预测因子来预测斑块上的密度值。栎属物种从历史组成的 62%减少到当前组成的 30%,黑栎和白栎在过去 93%的景观中是优势物种,而在当前的 42%的景观中是优势物种。当前森林的密度大约是历史密度的两倍,这表明了热带稀树草原和林地的丧失,以及向密集森林结构的转变。平均树木直径比过去小,但由于当前森林密度的增加,平均基面积和林分保持相似。尽管如此,还是存在空间差异;基面积和林分密度沿河流减少,远离河流则增加。密苏里平原上的栎属物种正在被其他物种所取代,这与栎属在其分布范围内的替代过程相似。在更干旱的地方,长期承诺采用规定的燃烧和造林处方的组合,可能是栎属植物重新生长所必需的。开阔栎树林生态系统的恢复是一个时间敏感的问题,因为随着栎属树木从林冠层中消失,周围的基质由非栎属物种主导,恢复的成本将会越来越高。