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Spatial pattern analysis for monitoring protected areas

机译:用于监测保护区的空间格局分析

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The management of diverse biota within protected areas is affected by both land cover change within a protected area and habitat loss and fragmentation in the surrounding landscape. Satellite images provide a synoptic view of land cover patterns, but the use of such imagery requires careful consideration of sensor type, resolution, extent, and the metrics used to quantify ecologically significant change. We examined these factors for landscape monitoring applications in four small National Parks near Washington, DC: Antietam National Battlefield, Catoctin Mountain Park, Prince William Forest Park and Rock Creek Park. Using 4 m Ikonos, 10 m SPOT, 15 m pan-sharpened Landsat ETM+ and 30 m Landsat ETM+ imagery, the parks and surrounding areas were mapped to National Land Cover system classes. For each park, we examined four methods for defining map extent, including park administrative boundaries, two variable buffer widths, and watershed boundaries, and then analyzed patterns of forest habitat for the maps using a graph theoretic approach (critical dispersal threshold distance) and common landscape metrics (number of patches, percent forest, forest edge density, and forest area-weighted mean patch size). As expected, landscape metrics for maps derived at differing resolutions varied significantly, but map extent often yielded even larger differences. We found that for most applications, coarser scale data (e.g., 30 m Landsat) are adequate for characterizing landscape pattern, although ultimately data from multiple sensors may be appropriate or necessary based on different objectives of landscape monitoring (e.g., mapping single trees vs. forest stands) and the scale at which a resource of interest interacts with the larger landscape (e.g., birds vs. herptiles). Our results provide a strong caution regarding the practical issues associated with combining data sources from multiple satellite sensors for monitoring applications.
机译:保护区内各种生物群落的管理受到保护区内土地覆盖变化以及周围景观中栖息地的丧失和破碎的影响。卫星图像提供了土地覆盖格局的概要视图,但是使用此类图像需要仔细考虑传感器的类型,分辨率,范围以及用于量化生态上重要变化的度量。我们在华盛顿特区附近的四个小型国家公园中研究了这些因素在景观监测中的应用:安提坦国家战场,卡特丁山公园,威廉王子森林公园和罗克克里克公园。使用4 m Ikonos,10 m SPOT,15 m泛锐化的Landsat ETM +图像和30 m Landsat ETM +图像,将公园和周边地区映射到国家土地覆被系统类别。对于每个公园,我们研究了四种定义地图范围的方法,包括公园管理边界,两个可变缓冲区宽度和分水岭边界,然后使用图形理论方法(临界扩散阈值距离)和常见的方法分析了森林栖息地的格局景观指标(斑块数量,森林百分比,森林边缘密度和森林面积加权平均斑块大小)。不出所料,以不同分辨率导出的地图的景观度量差异很大,但地图范围经常产生更大的差异。我们发现,对于大多数应用而言,粗略的尺度数据(例如30 m Landsat)足以表征景观格局,尽管最终根据景观监测的不同目标,来自多个传感器的数据可能是适当的或必要的(例如,绘制单棵树与树的对比)。森林林分)以及感兴趣的资源与更大的景观(例如鸟类与牧羊人)相互作用的规模。我们的结果对与合并来自多个卫星传感器的数据源进行监视的应用相关的实际问题提供了强烈的警告。

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