Franzén Markus, Nilsson Sven G
Department of Animal Ecology, Ecology Building, Lund University, SE-223 62 Lund, Sweden.
J Anim Ecol. 2007 Nov;76(6):1224-30. doi: 10.1111/j.1365-2656.2007.01285.x.
Among small animals dispersal parameters are mainly obtained by traditional methods using population studies of marked individuals. Dispersal studies may underestimate the rate and distance of dispersal, and be biased because of aggregated habitat patches and a small study area. The probability of observing long distance dispersal events decreases with distance travelled by the organisms. In this study a new approach is presented to solve this methodological problem. An extensive mark-release-recapture programme was performed in an area of 81 km(2) in southern Sweden. To estimate the required size of the study area for adequate dispersal measures we examined the effect of study area size on dispersal distance using empirical data and a repeated subsampling procedure. In 2003 and 2004, two species of diurnal burnet moths (Zygaenidae) were studied to explore dispersal patterns. The longest confirmed dispersal distance was 5600 m and in total 100 dispersal events were found between habitat patches for the two species. The estimated dispersal distance was strongly affected by the size of the study area and the number of marked individuals. For areas less than 10 km(2) most of the dispersal events were undetected. Realistic estimates of dispersal distance require a study area of at least 50 km(2). To obtain adequate measures of dispersal, the marked population should be large, preferably over 500 recaptured individuals. This result was evident for the mean moved distance, mean dispersal distance and maximum dispersal distance. In general, traditional dispersal studies are performed in small study areas and based on few individuals and should therefore be interpreted with care. Adequate dispersal measures for insects obtained by radio-tracking and genetic estimates (gene flow) is still a challenge for the future.
在小型动物中,扩散参数主要通过对有标记个体进行种群研究的传统方法来获取。扩散研究可能会低估扩散的速率和距离,并且由于栖息地斑块的聚集和研究区域较小而存在偏差。观察到远距离扩散事件的概率会随着生物移动的距离而降低。在本研究中,提出了一种新方法来解决这一方法学问题。在瑞典南部一个81平方公里的区域内进行了一项广泛的标记重捕计划。为了估计获得充分扩散测量所需的研究区域大小,我们使用经验数据和重复抽样程序研究了研究区域大小对扩散距离的影响。在2003年和2004年,对两种昼行性斑蛾(Zygaenidae)进行了研究,以探索扩散模式。确认的最长扩散距离为5600米,这两个物种在栖息地斑块之间总共发现了100次扩散事件。估计的扩散距离受到研究区域大小和标记个体数量的强烈影响。对于面积小于10平方公里的区域,大多数扩散事件未被检测到。对扩散距离进行实际估计需要至少50平方公里的研究区域。为了获得充分的扩散测量,标记种群应该很大,最好有超过500个被重新捕获的个体。这一结果在平均移动距离、平均扩散距离和最大扩散距离方面都很明显。一般来说,传统的扩散研究是在小研究区域内基于少数个体进行的,因此应该谨慎解释。通过无线电追踪和遗传估计(基因流动)获得昆虫的充分扩散测量仍然是未来的一个挑战。