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Optimal design of butterfly occupancy surveys and testing if occupancy converts to abundance for sparse populations

机译:蝴蝶占用率调查和测试的优化设计,以解决稀疏种群的占用率转化问题

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Occupancy has several important advantages over abundance methods and may be the best choice for monitoring sparse populations. Here we use simulations to evaluate competing designs (number of sites vs. number of surveys) for occupancy monitoring, with emphasis on sparse populations of the endangered Karner blue butterfly (Lycaeides melissa samuelis Nabokov). Because conservation planning is usually abundance-based, we also ask whether detectionon-detection data may reliably convert to abundance, hypothesizing that occupancy provides a more dependable shortcut when populations are sparse. Count-index and distance sampling were conducted across 50 habitat patches containing variably sparse Karner blue populations. We used occupancy-detection model estimates as simulation inputs to evaluate primary replication tradeoffs, and used peak counts and population densities to evaluate the occupancy-abundance relationship. Detection probability and therefore optimal design of occupancy monitoring was strongly temperature dependent. Assuming a quality threshold of 0.075 root-mean square error for the occupancy estimator, the minimum allowable effort was 360 (40 sites x 9 surveys) for spring generation and 200 (20 sites x 10 surveys) for summer generation. A mixture model abundance estimator for repeated detectionon-detection data was biased low for high-density and low-density populations, suggesting that occupancy may not provide a reliable shortcut in abundance-based conservation planning for sparse butterfly populations.
机译:与丰度方法相比,占用率具有几个重要优势,并且可能是监视稀疏人口的最佳选择。在这里,我们使用模拟来评估竞争性设计(站点数量与调查数量)以进行占用监测,重点是濒临灭绝的Karner蓝蝴蝶(Lycaeides melissa samuelis Nabokov)的稀疏种群。由于保护规划通常是基于丰度的,因此我们还询问检测/未检测数据是否可以可靠地转换为丰度,并假设在人口稀少时占用率提供了更可靠的捷径。在50个栖息地斑块上进行了计数指标和距离采样,这些斑块包含稀疏的Karner蓝色种群。我们使用占用检测模型估计作为模拟输入来评估主要复制权衡,并使用峰值计数和种群密度来评估占用-丰度关系。检测概率以及因此占用监测的最佳设计在很大程度上取决于温度。假设占用量估算器的质量阈值为0.075均方根误差,则春季的最小允许工作量为360(40个站点​​x 9个调查),夏季的最小允许工作量为200(20个站点x 10个调查)。对于高密度和低密度种群,用于重复检测/未检测数据的混合模型丰度估计值偏低,这表明,对于稀疏蝴蝶种群,基于丰度的保护规划中的占用可能无法提供可靠的捷径。

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