School of Resource and Environmental Management, Simon Fraser University, 8888 University Drive, Burnaby, British Columbia V5A 1S6 Canada.
Conserv Biol. 2012 Oct;26(5):894-904. doi: 10.1111/j.1523-1739.2012.01882.x. Epub 2012 Jun 28.
Although there are many indicators of endangerment (i.e., whether populations or species meet criteria that justify conservation action), their reliability has rarely been tested. Such indicators may fail to identify that a population or species meets criteria for conservation action (false negative) or may incorrectly show that such criteria have been met (false positive). To quantify the rate of both types of error for 20 commonly used indicators of declining abundance (threat indicators), we used receiver operating characteristic curves derived from historical (1938-2007) data for 18 sockeye salmon (Oncorhynchus nerka) populations in the Fraser River, British Columbia, Canada. We retrospectively determined each population's yearly status (reflected by change in abundance over time) on the basis of each indicator. We then compared that population's status in a given year with the status in subsequent years (determined by the magnitude of decline in abundance across those years). For each sockeye population, we calculated how often each indicator of past status matched subsequent status. No single threat indicator provided error-free estimates of status, but indicators that reflected the extent (i.e., magnitude) of past decline in abundance (through comparison of current abundance with some historical baseline abundance) tended to better reflect status in subsequent years than the rate of decline over the previous 3 generations (a widely used indicator). We recommend that when possible, the reliability of various threat indicators be evaluated with empirical analyses before such indicators are used to determine the need for conservation action. These indicators should include estimates from the entire data set to take into account a historical baseline.
尽管有许多濒危指标(即种群或物种是否符合需要采取保护行动的标准),但这些指标的可靠性很少得到检验。这些指标可能无法识别一个种群或物种是否符合保护行动的标准(假阴性),或者可能错误地显示已经符合这些标准(假阳性)。为了量化 20 种常用的数量减少指标(威胁指标)的这两种错误类型的比率,我们使用来自加拿大不列颠哥伦比亚省弗雷泽河 18 个红大麻哈鱼(Oncorhynchus nerka)种群的历史(1938-2007 年)数据得出的接收者操作特征曲线来计算。我们根据每个指标回溯性地确定每个种群的年度状况(通过时间上的数量变化反映)。然后,我们将当年的种群状况与随后几年的状况进行比较(通过这些年份的数量下降幅度来确定)。对于每个红大麻哈鱼种群,我们计算了过去状况的每个指标与随后状况匹配的频率。没有单一的威胁指标能提供无错误的状况估计,但反映过去数量下降幅度的指标(通过当前数量与某些历史基线数量进行比较)往往比过去 3 代的下降速度(一种广泛使用的指标)更能反映随后几年的状况。我们建议,在使用这些指标来确定是否需要采取保护行动之前,应尽可能使用实证分析来评估各种威胁指标的可靠性。这些指标应包括整个数据集的估计值,以考虑到历史基线。