Faculty of Science, University of South Bohemia, Ceske Budejovice, Czech Republic.
PLoS One. 2011;6(6):e21345. doi: 10.1371/journal.pone.0021345. Epub 2011 Jun 30.
The Rosalia longicorn or Alpine longhorn (Coleoptera: Cerambycidae) is an endangered and strictly protected icon of European saproxylic biodiversity. Despite its popularity, lack of information on its demography and mobility may compromise adoption of suitable conservation strategies. The beetle experienced marked retreat from NW part of its range; its single population survives N of the Alps and W of the Carpathians. The population inhabits several small patches of old beech forest on hill-tops of the Ralska Upland, Czech Republic. We performed mark-recapture study of the population and assessed its distribution pattern. Our results demonstrate the high mobility of the beetle, including dispersal between hills (up to 1.6 km). The system is thus interconnected; it contained ∼2000 adult beetles in 2008. Estimated population densities were high, ranging between 42 and 84 adult beetles/hectare a year. The population survives at a former military-training ground despite long-term isolation and low cover of mature beech forest (∼1%). Its survival could be attributed to lack of forestry activities between the 1950s and 1990s, slow succession preventing canopy closure and undergrowth expansion, and probably also to the distribution of habitat patches on conspicuous hill-tops. In order to increase chances of the population for long term survival, we propose to stop clear-cuts of old beech forests, increase semi-open beech woodlands in areas currently covered by conifer plantations and active habitat management at inhabited sites and their wider environs.
罗氏角长蠹或高山长角牛(鞘翅目:天牛科)是欧洲腐木生物多样性的濒危和严格保护的标志性物种。尽管它很受欢迎,但缺乏关于其种群动态和流动性的信息可能会影响到合适的保护策略的采用。该甲虫从其分布范围的西北部显著退缩;其唯一的种群存活于阿尔卑斯山以北和喀尔巴阡山脉以西。该种群栖息于捷克共和国 Ralska 高原山顶的几片古老山毛榉林中。我们对该种群进行了标记重捕研究,并评估了其分布模式。我们的研究结果表明,甲虫的移动性很高,包括在山丘之间的扩散(最高可达 1.6 公里)。该系统是相互关联的;2008 年,它包含了约 2000 只成年甲虫。估计的种群密度很高,每年每公顷有 42 到 84 只成年甲虫。尽管长期隔离和成熟山毛榉林(约 1%)覆盖率低,但该种群仍在一个前军事训练场上生存。其生存可能归因于 20 世纪 50 年代至 90 年代之间缺乏林业活动、防止树冠关闭和林下植被扩张的缓慢演替,以及可能还有栖息地斑块分布在显眼的山顶上。为了增加该种群长期生存的机会,我们建议停止砍伐古老的山毛榉林,增加当前以针叶林种植为主的地区的半开放山毛榉林地,并在居住点及其周边地区进行积极的栖息地管理。