Baltensweiler Werner
Institute of Plant Sciences, Phytomedicine/Applied Entomology, ETH Zürich/CLS, CH-8092, Zürich, Switzerland.
Oecologia. 1993 May;94(1):62-66. doi: 10.1007/BF00317302.
The larch bud-moth cycle has been observed in the sub-alpine larch-cembran pine forests 16 times since 1850. Infestation is easily recognized by the characteristic red-brown discoloration of the larch crowns due to the wasteful feeding of the bud moth larvae. The heaviest defoliation recurs at intervals of 8.47±0.27 (SE) years, and the larval density per kilogram of larch branches varies more than 10000-fold over four or five generations. The basic regulatory mechanism for this cycle is the induced change in food quality for the two or more subsequent larval generations. Defoliation functions as a negative feedback mechanism acting on larval density. In 1989 local discoloration in the Upper Engadine valley was observed in the usual first focus. In 1990 and 1991, however, instead of the expected widespread defoliation damage, larval densities decreased drastically. Based on extensive field data collected from 1961 to 1991 on the development and the survival of the bud moth (Zeiraphera diniana Gn.) and the phenology of the host, Larix decidua L., this paper shows the effect of weather on survival in the egg stage and on the coincidence of larval hatching with the sprouting of the larch. It is shown that the winter and spring weather conditions in 1989-1991 were conducive to unusually high egg mortality. Since these conditions occurred in three successive generations, population growth was effectively reduced and the cycle collapsed prematurely. Thus the rather persistent cyclicity of the larch-larch bud-moth system was disturbed by weather conditions with a very low probability of occurrence, but due to the inherent high resilience of the system, the next population peak with visible defoliation is expected to occur 1996/1997, provided that the weather conditions return to the climatic standard.
自1850年以来,落叶松芽蛾的生命周期已在亚高山落叶松-瑞士石松林中被观测到16次。由于芽蛾幼虫的过度取食,落叶松树冠呈现出特有的红棕色变色,虫害很容易被识别。最严重的落叶现象每隔8.47±0.27(标准误)年出现一次,每千克落叶松树枝上的幼虫密度在四到五代内变化超过10000倍。这个周期的基本调节机制是后续两代或更多代幼虫食物质量的诱导变化。落叶起到了对幼虫密度的负反馈机制作用。1989年,在上恩加丁山谷通常的首个发生地观察到了局部变色现象。然而,在1990年和1991年,并未出现预期的广泛落叶损害,幼虫密度却急剧下降。基于1961年至1991年收集的关于芽蛾(Zeiraphera diniana Gn.)发育和存活以及寄主欧洲落叶松(Larix decidua L.)物候的大量野外数据,本文展示了天气对卵期存活以及幼虫孵化与落叶松发芽同步性的影响。结果表明,1989 - 1991年的冬季和春季天气状况导致了异常高的卵死亡率。由于这些状况连续在三代中出现,种群增长被有效抑制,周期过早崩溃。因此,落叶松-落叶松芽蛾系统相当持久的周期性被发生概率极低的天气状况扰乱,但由于该系统固有的高恢复力,预计在天气状况恢复到气候标准的情况下,下一个可见落叶的种群高峰期将出现在1996/1997年。