Sumerford D V, Abrahamson W G, Weis A E
Department of Biology, Bucknell University, Lewisburg, PA 17837, USA, , , , , , US.
Oecologia. 2000 Feb;122(2):240-248. doi: 10.1007/PL00008852.
Environmental catastrophes, such as severe drought, can reduce host-plant quality and/or abundance, which in turn decrease levels of herbivore populations. Such changes in herbivore populations affect populations of their natural enemies. As part of a long-term field experiment (1983-1991), galls of Eurosta solidaginis from 16 fields in central Pennsylvania were systematically collected from goldenrod ramets. Galls were dissected to compare the occurrence of E. solidaginis mortality caused by its natural enemies in 2 drought years (1988, 1991) with 5 pre-drought years (1983-1987) and 2 post-drought years (1989-1990). Gall diameters were significantly smaller in both drought years and early larval death significantly decreased E. solidaginis survivorship in the first drought year. Of the natural enemies, the parasitoid wasp Eurytoma gigantea caused significant selection for larger gall size in all pre-drought years, the 1991 drought, and both post-drought years, due to its differential attack of smaller galls. In spite of drought-induced small gall size in 1988, there was negligible selection on gall size by natural enemies. However, populations of E. solidaginis did suffer local extirpations at nine of the 16 fields during the first drought year and population recoveries of the gall inducer and natural enemies varied among fields in the post-drought years. As a consequence of reduced herbivore abundance in drought and post-drought years, some natural-enemy populations were absent. Drought therefore drastically reduced the abundance of E. solidaginis and natural enemies resulting in slow recoveries to pre-drought numbers.
环境灾难,如严重干旱,会降低寄主植物的质量和/或数量,进而减少食草动物的种群数量。食草动物种群的这种变化会影响其天敌的种群数量。作为一项长期田间试验(1983 - 1991年)的一部分,从宾夕法尼亚州中部16块田地的一枝黄花分株上系统收集了金蝇瘿。解剖瘿以比较在2个干旱年份(1988年、1991年)中,由其天敌导致的金蝇死亡情况与5个干旱前年份(1983 - 1987年)和2个干旱后年份(1989 - 1990年)的差异。在两个干旱年份,瘿的直径都显著更小,并且在第一个干旱年份,幼虫早期死亡显著降低了金蝇的存活率。在天敌中,寄生蜂巨瘤姬蜂在所有干旱前年份、1991年干旱年份以及两个干旱后年份,都会对更大的瘿进行显著选择,因为它对较小的瘿有不同程度的攻击。尽管1988年干旱导致瘿变小,但天敌对瘿大小的选择可以忽略不计。然而,在第一个干旱年份,16块田地中有9块的金蝇种群遭受了局部灭绝,并且在干旱后年份,瘿诱导者和天敌的种群恢复情况在不同田地间各不相同。由于干旱年份和干旱后年份食草动物数量减少,一些天敌种群消失了。因此,干旱极大地减少了金蝇和天敌的数量,导致恢复到干旱前数量的速度缓慢。