University of Idaho, Environmental Science Program, 810 West 7th Street, McClure Hall 203, Moscow, Idaho 83844-3021, USA.
Ecol Appl. 2012 Oct;22(7):1876-91. doi: 10.1890/11-1785.1.
Outbreaks of aggressive bark beetle species cause widespread tree mortality, affecting timber production, wildlife habitat, wildfire, forest composition and structure, biogeochemical cycling, and biogeophysical processes. As a result, agencies responsible for forest management in the United States and British Columbia conduct aerial surveys to map these forest disturbances. Here we combined aerial surveys from British Columbia (2001 2010) and the western conterminous United States (1997-2010), produced 1-km2 grids of the area of crown mortality from bark beetle attack, and analyzed spatial and temporal patterns. We converted aerial-survey polygon data for each combination of host type and bark beetle species available in the western United States, and for each bark beetle species available in British Columbia. We converted affected area (which includes live and killed trees) to mortality area (crown area of killed trees) using species-specific crown diameters and the number (U.S.) or percentage (British Columbia) of killed trees. In the United States we also produced an upper estimate of mortality area by forcing the mortality area to match that from high-resolution imagery in Idaho, Colorado, and New Mexico. Resulting adjustment factors of 3.7-20.9 illustrate the underestimate of mortality by the U.S. aerial surveys. The upper estimate, which we suggest is more realistic, better matched the spatial patterns and severity of the British Columbia mortality area. Cumulative mortality area from all bark beetles was 5.46 Mha in British Columbia in 2001-2010 and 0.47-5.37 Mha (lower and upper estimate) in the western conterminous United States during 1997-2010. We note that we report year of detection here; studies that consider year of tree mortality should shift the time series back one year. We conclude by discussing uses and limitations of these data in ecological studies, including uncertainties associated with assumptions in the methods, lack of complete coverage by surveys, and the subjective nature of the survey databases.
攻击性树皮甲虫物种的爆发导致广泛的树木死亡,影响木材生产、野生动物栖息地、野火、森林组成和结构、生物地球化学循环和生物地球物理过程。因此,负责美国和不列颠哥伦比亚森林管理的机构进行航空调查,以绘制这些森林干扰图。在这里,我们结合了不列颠哥伦比亚省(2001-2010 年)和美国西部大陆(1997-2010 年)的航空调查结果,制作了 1 平方公里的树皮甲虫攻击导致树冠死亡率网格,并分析了空间和时间模式。我们转换了美国西部每个可用的宿主类型和树皮甲虫物种的航空调查多边形数据,以及不列颠哥伦比亚省每个可用的树皮甲虫物种的航空调查多边形数据。我们使用特定物种的树冠直径和死亡树木的数量(美国)或百分比(不列颠哥伦比亚省),将航空调查的受影响面积(包括活树和死树)转换为死亡率面积(死树的树冠面积)。在美国,我们还通过迫使死亡率面积与爱达荷州、科罗拉多州和新墨西哥州的高分辨率图像相匹配,生成了死亡率面积的上限估计。由此产生的调整系数 3.7-20.9 说明了美国航空调查对死亡率的低估。我们建议使用的上限估计更符合实际情况,更好地匹配了不列颠哥伦比亚省死亡率面积的空间模式和严重程度。2001-2010 年,不列颠哥伦比亚省所有树皮甲虫造成的累积死亡率面积为 546 万公顷,1997-2010 年美国西部大陆的死亡率面积为 0.47-5.37 万公顷(下限和上限估计)。我们注意到,我们在这里报告的是检测年份;考虑树木死亡年份的研究应该将时间序列向后推一年。最后,我们讨论了这些数据在生态研究中的用途和局限性,包括方法假设的不确定性、调查的不完全覆盖以及调查数据库的主观性。