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Strong observer effect on tree micro habitats inventories: A case study in a French lowland forest

机译:观察者对树木微生境清单的强烈影响:以法国低地森林为例

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Validating biodiversity indicators requires an analysis of their applicability, their range of validity and their degree of correlation with the biodiversity they are supposed to represent. In this process, assessing the magnitude of observer effect is an essential step, especially if non-specialist observers are involved. Tree microhabitats - woodpecker cavities, cracks and bark characteristics - are reputed to be easily detected by non-specialists as microhabitat observation does not require prior forestry or ecology knowledge. We therefore quantified the probabilities of true and false positive detections made by observers during inventories. Within two 0.5 ha plots in a forest reserve that has not been harvested for at least 150 years, 14 observers with various backgrounds visually inventoried microhabitats on 106 oak (Quercus petraea and Quercus robur) and beech (Fagus sylvatica) trees. We used parametric and Bayesian statistics to compare these observers' recorded observations with results from an independent census. The mean number of microhabitats per tree varied widely among observers - from 1.4 to over 3. Only five observers reported a mean number of microhabitats per tree that was statistically equivalent to the reference census. The probability of true detection also varied among observers for each microhabitat (from to 0 to 1) as did the probability of false positive detection (from 0 to 0.7). These results show that microhabitat inventories are particularly prone to observer effects. Such strong observer effects weaken the usefulness of microhabitats as biodiversity indicators. If microhabitat inventories are to be developed, we recommend controlling for observer effects by (ⅰ) defining standard operating procedures and multiplying the number of observer training sessions and of consensual standardization censuses; (ⅱ) using pairs of observers to record microhabitats whenever possible (though the efficiency of this method remains to be tested); (ⅲ) planning fieldwork so that the factors of interest are not confused with observer effects; and (ⅳ) integrating observer profiles into the statistical models used to analyze the data.
机译:验证生物多样性指标需要分析其适用性,有效性范围以及与它们应代表的生物多样性的相关程度。在此过程中,评估观察员效果的幅度是必不可少的步骤,尤其是在涉及非专业观察员的情况下。树木微生境-啄木鸟的蛀牙,裂缝和树皮特征-被认为非专业人员很容易检测到,因为对微生境的观察不需要事先的林业或生态知识。因此,我们量化了清单中观察员进行正确和错误阳性检测的概率。在至少有150年没有被采伐的森林保护区的两个0.5公顷土地中,有14位具有不同背景的观察员目视调查了106棵橡树(栎属栎和栎栎)和山毛榉(山毛榉)树上的微生境。我们使用参数统计和贝叶斯统计将这些观察者的记录观察结果与独立普查结果进行比较。在观察者中,每棵树的平均微生境数量差异很大,从1.4到3个以上。只有五位观察员报告,每棵树的平均微生境数量在统计学上与参考普查相当。观察者之间对于每个微栖息地的真实检测概率也有所不同(从0到0:1),而假阳性检测的概率(从0到0.7)也有所不同。这些结果表明,微栖息地的清单特别容易受到观察者的影响。这种强烈的观察者效应削弱了微生境作为生物多样性指标的作用。如果要开发微栖息地清单,我们建议通过以下方法控制观察者的影响:(operating)定义标准操作程序,并增加观察者培训课程和自愿性标准化普查的次数; (ⅱ)尽可能使用成对的观察者记录微生境(尽管该方法的有效性尚待测试); (ⅲ)计划野外工作,以使感兴趣的因素不会与观察者的影响相混淆; (ⅳ)将观察者资料整合到用于分析数据的统计模型中。

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