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Climate and wildfire area burned in western U. S. ecoprovinces, 1916-2003

机译:1916-2003年,美国西部生态省的气候和野火区域被烧毁

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The purpose of this paper is to quantify climatic controls on the area burned by. re in different vegetation types in the western United States. We demonstrate that wild. re area burned (WFAB) in the American West was controlled by climate during the 20th century (1916-2003). Persistent ecosystem-specific correlations between climate and WFAB are grouped by vegetation type (ecoprovinces). Most mountainous ecoprovinces exhibit strong year-of-fire relationships with low precipitation, low Palmer drought severity index (PDSI), and high temperature. Grass-and shrub-dominated ecoprovinces had positive relationships with antecedent precipitation or PDSI. For 1977-2003, a few climate variables explain 33-87% (mean = 64%) of WFAB, indicating strong linkages between climate and area burned. For 1916-2003, the relationships are weaker, but climate explained 25-57% (mean = 39%) of the variability. The variance in WFAB is proportional to the mean squared for different data sets at different spatial scales. The importance of antecedent climate (summer drought in forested ecosystems and antecedent winter precipitation in shrub and grassland ecosystems) indicates that the mechanism behind the observed. re-climate relationships is climatic preconditioning of large areas of low fuel moisture via drying of existing fuels or fuel production and drying. The impacts of climate change on. re regimes will therefore vary with the relative energy or water limitations of ecosystems. Ecoprovinces proved a useful compromise between ecologically imprecise state-level and localized gridded fire data. The differences in climate . re relationships among the ecoprovinces underscore the need to consider ecological context (vegetation, fuels, and seasonal climate) to identify specific climate drivers of WFAB. Despite the possible influence of. re suppression, exclusion, and fuel treatment, WFAB is still substantially controlled by climate. The implications for planning and management are that future WFAB and adaptation to climate change will likely depend on ecosystem-specific, seasonal variation in climate. In fuel-limited ecosystems, fuel treatments can probably mitigate. re vulnerability and increase resilience more readily than in climate-limited ecosystems, in which large severe. res under extreme weather conditions will continue to account for most area burned.
机译:本文的目的是量化燃烧区域的气候控制。在美国西部有不同的植被类型。我们证明那很野。在20世纪(1916-2003年),美国西部的区域烧毁(WFAB)受气候影响。气候和WFAB之间持久的特定于生态系统的相关性按植被类型(生态省)分组。大多数山区的生态省都有很强的火年关系,降水量低,帕尔默干旱严重度指数(PDSI)低,温度高。以草和灌木为主的生态省与先前的降水或PDSI呈正相关。在1977-2003年间,一些气候变量解释了WFAB的33-87%(平均= 64%),表明气候与燃烧面积之间有很强的联系。在1916-2003年间,这种关系较弱,但气候解释了变异性的25-57%(平均值= 39%)。 WFAB的方差与不同空间范围内不同数据集的均方成正比。前期气候的重要性(森林生态系统中的夏季干旱,灌木和草地生态系统中的冬季前期降水)表明了这一现象背后的机制。重新气候关系是通过干燥现有燃料或燃料生产和干燥对大面积的低燃料水分进行气候预处理。气候变化的影响。因此,生态系统将随生态系统相对能量或水的限制而变化。生态省证明了在生态上不精确的州级数据和局部网格化火数据之间的有益折衷。气候差异。生态省之间的关系强调需要考虑生态环境(植被,燃料和季节性气候)以识别WFAB的特定气候驱动因素。尽管有可能的影响。在抑制,排除和燃料处理方面,WFAB仍基本上受气候控制。规划和管理的意义在于,未来的WFAB和对气候变化的适应可能将取决于特定于生态系统的季节性气候变化。在燃料有限的生态系统中,燃料处理可能会缓解。与气候严重的大型气候限制型生态系统相比,它更容易遭受破坏,并更容易提高抵御能力。在极端天气条件下的水力发电将继续占烧毁面积的大部分。

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