Sisikiyou Chipmunk Predicted Habitat - CWHR M058 [ds2516]

CWHR Predicted Habitat Models represent areas of predicted suitable habitat for each species within its range. These models are built from the following principal inputs: 1) a statewide, best-available vegetation map (FVEG); 2) GIS data representing a species’ range; 3) the CWHR database of habitat suitability values for over 700 terrestrial vertebrate species. Habitat suitability ranks of Low (non-zero values less than 0.34), Medium (0.34-0.66), and High (greater than 0.66) are based on the maximum suitability value across the 3 species life requisites: reproduction, feeding, and cover. Note that previous versions of these Predicted Habitat Models used an average across the 3 life requisites in order to obtain an overall suitability score for each habitat type and stage class. Habitat suitability scores were developed based on habitat patch sizes greater than 40 acres in size and are best interpreted for habitat patches greater than 200 acres in size. The FVEG landcover dataset is an aggregation of multiple statewide landcover and regional vegetation mapping efforts, conducted at different points in time (approximately 1990 up to time of publishing) and at various resolutions, compiled by the California Department of Forestry and Fire Protection (CALFIRE). FVEG uses the most current and consistent data available for each region of the state. Decision rules were developed that controlled which layers were given priority in areas of overlap. Crosswalks were used to attribute the various data sources according to the CWHR habitat-type classification system. Attributing FVEG with CWHR habitat types allows for the extraction of areas with non-zero suitability values for each species within the bounds of its range, creating a series of maps of predicted suitable habitat which are species-specific. Because FVEG is an amalgam of disparate landcover assessment efforts across the state, the predictive power for determining suitable habitat will vary between species, and possibly even regionally for species which are widely distributed. While these maps represent CDFW’s best estimate of the presence of suitable habitat for any given species in the CWHR system, these maps are also limited by several factors: 1) the accuracy and resolution of vegetation maps in a given region; 2) the dynamic nature of the landscape in which fire and other disturbance events alter conditions at a greater frequency than mapping efforts can track; 3) the currency of expert knowledge, particularly as species adapt to changing land and climate conditions and the shifting of other species’ ranges; 4) the frequency of species-specific surveys across a representative sample of a species’ entire range; 5) metapopulation dynamics, which describes the shifting of populations within their environment as result of numerous types of interactions and responses. CWHR GIS data representing predicted suitable habitat should not be used to indicate the presence or absence of a particular species at any specific site. CWHR predicted habitat models are named according to the 4-character alpha-numeric CWHR ID assigned to each species (5 characters in the case of subspecies or other sub-taxa). There is also a “CWHR Revision Tracking Table” containing a record for each species, its CWHR ID, scientific name, common name, and range and habitat model data revision history. CWHR species range models, predicted habitat models, and GIS data of the statewide distribution of all CWHR habitat types, along with the CWHR revision tracking table, are available for download at https://www.wildlife.ca.gov/Data/CWHR.CWHR预测栖息地模型（CWHR Predicted Habitat Models）指各物种在其分布范围内的潜在适宜栖息地区域。此类模型基于以下核心输入构建：1）全州最优可用植被地图（FVEG）；2）表征物种分布范围的地理信息系统（Geographic Information System，简称GIS）数据；3）涵盖700余种陆生脊椎动物栖息地适宜性分值的CWHR数据库。 栖息地适宜性等级分为低（非零分值小于0.34）、中（0.34~0.66）及高（大于0.66），其划分依据为物种3类生存必需条件——繁殖、觅食与隐蔽——对应的最大适宜性分值。需注意，此前版本的预测栖息地模型采用3类生存必需条件的平均分值，以生成各栖息地类型与阶段类的综合适宜性评分。 本数据集的栖息地适宜性分值基于面积大于40英亩的栖息地斑块生成，其最优解读场景为面积大于200英亩的栖息地斑块。 FVEG土地覆盖数据集整合了多项全州土地覆盖与区域植被测绘成果，这些测绘工作于不同时期（大致为1990年至发布之时）以不同分辨率开展，由加州森林与火灾防护部（California Department of Forestry and Fire Protection，简称CALFIRE）汇编而成。FVEG采用加州各区域当前可得的最一致、最新数据，并制定了决策规则以处理重叠区域的图层优先级问题，同时通过交叉对照表将各类数据源按照CWHR栖息地类型分类系统进行属性赋值。 将CWHR栖息地类型属性赋予FVEG后，即可提取物种分布范围内具有非零适宜性分值的区域，进而生成一系列针对单个物种的预测适宜栖息地图。 由于FVEG整合了全州范围内多种不同的土地覆盖评估成果，其预测适宜栖息地的能力因物种而异，对于分布广泛的物种，甚至可能因区域不同而存在差异。尽管此类地图为加州鱼类与野生动物部（California Department of Fish and Wildlife，简称CDFW）针对CWHR系统内任一物种的适宜栖息地存在情况所给出的最优评估结果，但仍受以下多项因素限制：1）特定区域植被地图的精度与分辨率；2）景观的动态性：火灾与其他干扰事件改变栖息地条件的频率高于测绘工作的更新频率；3）专家知识的时效性：尤其当物种适应不断变化的土地与气候条件，以及其他物种的分布范围发生偏移时；4）物种全分布范围代表性样本的专项调查频次；5）集合种群动态：即种群在环境中因多种交互作用与响应而发生的迁移变化。 CWHR表征预测适宜栖息地的GIS数据，不得用于判定特定物种在任一具体点位的存在与否。 CWHR预测栖息地模型以分配给各物种的4位字母数字组合CWHR ID命名（亚种或其他亚类群的物种则使用5位ID）。此外，还有一份“CWHR修订跟踪表”，其中包含各物种的CWHR ID、学名、通用名、分布范围及栖息地模型数据的修订历史记录。 CWHR物种分布模型、预测栖息地模型、所有CWHR栖息地类型的全州分布GIS数据，以及CWHR修订跟踪表，均可从https://www.wildlife.ca.gov/Data/CWHR下载获取。