Gervasi Vincenzo, Aragno Paola, Salvatori Valeria, Caniglia Romolo, De Angelis Daniele, Fabbri Elena, La Morgia Valentina, Marucco Francesca, Velli Edoardo, Genovesi Piero
Istituto Superiore per la Protezione e la Ricerca Ambientale Roma Italy.
Federparchi-Italian Federation of Parks and Natural Reserves Roma Italy.
Ecol Evol. 2024 May 13;14(5):e11285. doi: 10.1002/ece3.11285. eCollection 2024 May.
Estimating demographic parameters for wide-ranging and elusive species living at low density is challenging, especially at the scale of an entire country. To produce wolf distribution and abundance estimates for the whole south-central portion of the Italian wolf population, we developed an integrated spatial model, based on the data collected during a 7-month sampling campaign in 2020-2021. Data collection comprised an extensive survey of wolf presence signs, and an intensive survey in 13 sampling areas, aimed at collecting non-invasive genetic samples (NGS). The model comprised (i) a single-season, multiple data-source, multi-event occupancy model and (ii) a spatially explicit capture-recapture model. The information about species' absence was used to inform local density estimates. We also performed a simulation-based assessment, to estimate the best conditions for optimizing sub-sampling and population modelling in the future. The integrated spatial model estimated that 74.2% of the study area in south-central Italy (95% CIs = 70.5% to 77.9%) was occupied by wolves, for a total extent of the wolf distribution of 108,534 km (95% CIs = 103,200 to 114,000). The estimate of total population size for the Apennine wolf population was of 2557 individuals (SD = 171.5; 95% CIs = 2127 to 2844). Simulations suggested that the integrated spatial model was associated with an average tendency to slightly underestimate population size. Also, the main contribution of the integrated approach was to increase precision in the abundance estimates, whereas it did not affect accuracy significantly. In the future, the area subject to NGS should be increased to at least 30%, while at least a similar proportion should be sampled for presence-absence data, to further improve the accuracy of population size estimates and avoid the risk of underestimation. This approach could be applied to other wide-ranging species and in other geographical areas, but specific a priori evaluations of model requirements and expected performance should be made.
估算低密度生存的广泛分布且难以捉摸的物种的种群参数具有挑战性,尤其是在整个国家的尺度上。为了得出意大利狼种群整个中南部地区的狼分布和数量估计,我们基于2020 - 2021年为期7个月的采样活动收集的数据,开发了一个综合空间模型。数据收集包括对狼存在迹象的广泛调查,以及在13个采样区域的密集调查,旨在收集非侵入性基因样本(NGS)。该模型包括(i)一个单季、多数据源、多事件占有模型和(ii)一个空间明确的捕获 - 再捕获模型。关于物种不存在的信息被用于为局部密度估计提供依据。我们还进行了基于模拟的评估,以估计未来优化子采样和种群建模的最佳条件。综合空间模型估计,意大利中南部74.2%的研究区域(95%置信区间 = 70.5%至77.9%)有狼占据,狼分布的总面积为108,534平方千米(95%置信区间 = 103,200至114,000)。亚平宁狼种群的总数量估计为2557只个体(标准差 = 171.5;95%置信区间 = 2127至2844)。模拟表明,综合空间模型平均有略微低估种群数量的倾向。此外,综合方法的主要贡献是提高了数量估计的精度,而对准确性没有显著影响。未来,应将进行NGS的区域至少增加到30%,同时至少以类似比例采样存在 - 不存在数据,以进一步提高种群数量估计的准确性并避免低估风险。这种方法可应用于其他广泛分布的物种和其他地理区域,但应进行模型要求和预期性能的具体先验评估。