Daehler C C, Strong Donald R
Center for Population Biology, University of California Davis, Davis, CA 94923, USA, , , , , , US.
Oecologia. 1997 Mar;110(1):99-108. doi: 10.1007/s004420050138.
We compared resistance to insect herbivory in two introduced populations of smooth cordgrass (Spartina alterniflora) differing in their history of herbivory. One population in Willapa Bay, Washington, has spread in the absence of herbivory for more than a century, while another population in San Francisco, California, was introduced 20 years ago and is fed upon by the Spartina-specialist planthopper, Prokelisia marginata. The planthopper is a sap-feeder common on the Atlantic and Gulf coasts of North America, where smooth cordgrass is native. Smooth cordgrass plants from Willapa Bay (WB), San Francisco Bay (SFB), and Maryland (the source of the SFB introduction) were exposed to P. marginata herbivory over two consecutive summers in a common greenhouse environment, and their growth was compared with that of control plants that were grown herbivore-free. The planthoppers had relatively little effect on the growth of SFB plants, with plants exposed to herbivores averaging 77% and 83% of the aboveground biomass of herbivore-free controls after the first and second season of herbivory, respectively. The growth of plants from Maryland was similarly little-affected by the planthoppers, with the plants exposed to herbivores averaging near 100% of the biomass of herbivore-free controls after two seasons. In contrast, the growth of the WB plants was greatly reduced by the planthopper, with the plants exposed to planthopper herbivory averaging only 30% and 12% of the aboveground biomass of herbivore-free controls after the first and second seasons of herbivory, respectively. By the end of the second season of herbivory, 37% of the WB plants exposed to herbivory had died, while none of the SFB plants exposed to herbivores had died. Among WB clones, there was variation in resistance; one WB clone suffered 0% mortality while another suffered 100% mortality when exposed to herbivores. Short-term herbivory experiments with the putative founder clone for the WB population suggested that the WB founder was similar to the more resistant WB clones in its susceptibility to planthopper herbivory. Nitrogen analyses of green leaf tissue indicated that WB plants, including the WB founder clone, averaged 70% more total leaf nitrogen than SFB and Maryland plants. In a planthopper choice experiment, more planthoppers were observed on WB plants than SFB plants after 95 days of exposure to herbivory. Planthopper preference for WB plants may have contributed to the lower resistance of WB plants to herbivory; however, even before planthoppers had become more abundant on the WB plants, the proportion of leaves with 50% or more dead tissue averaged significantly greater on the WB plants, suggesting a difference between populations in tolerance to herbivory as well. Multiple factors, including a founder effect, further loss of herbivore tolerance, and herbivore preference for WB plants, appear to account for the reduced planthopper resistance in the WB population.
我们比较了互花米草(Spartina alterniflora)两个引入种群对昆虫食草作用的抗性,这两个种群的食草历史不同。华盛顿州威拉帕湾的一个种群在没有食草动物的情况下已经扩散了一个多世纪,而加利福尼亚州旧金山的另一个种群是20年前引入的,以专食互花米草的飞虱Prokelisia marginata为食。这种飞虱是一种吸食汁液的昆虫,在互花米草的原生地北美大西洋和墨西哥湾沿岸很常见。来自威拉帕湾(WB)、旧金山湾(SFB)和马里兰州(SFB引入种群的来源地)的互花米草植株,在一个普通温室环境中连续两个夏天遭受P. marginata的食草作用,并将它们的生长情况与未遭受食草动物侵害的对照植株进行比较。飞虱对SFB植株的生长影响相对较小,在遭受食草作用的第一个季节和第二个季节后,遭受食草动物侵害的植株地上生物量分别平均为未遭受食草动物侵害的对照植株的77%和83%。来自马里兰州的植株生长同样受飞虱影响较小,在两个季节后,遭受食草动物侵害的植株生物量平均接近未遭受食草动物侵害的对照植株的100%。相比之下,飞虱使WB植株的生长大幅降低,在遭受食草作用的第一个季节和第二个季节后,遭受飞虱食草作用的植株地上生物量分别平均仅为未遭受食草动物侵害的对照植株的30%和12%。到食草作用的第二个季节结束时,遭受食草动物侵害的WB植株中有37%死亡,而遭受食草动物侵害的SFB植株无一死亡。在WB克隆中,存在抗性差异;一个WB克隆在遭受食草动物侵害时死亡率为0%,而另一个则为100%。对WB种群假定的奠基克隆进行的短期食草实验表明,WB奠基克隆在对飞虱食草作用的易感性方面与抗性更强的WB克隆相似。绿叶组织的氮分析表明,包括WB奠基克隆在内的WB植株总叶氮平均比SFB和马里兰州的植株多70%。在一个飞虱选择实验中,在遭受食草作用暴露95天后,观察到WB植株上的飞虱比SFB植株上的更多。飞虱对WB植株的偏好可能导致了WB植株对食草作用的抗性较低;然而,即使在飞虱在WB植株上变得更加丰富之前,WB植株上有50%或更多死亡组织的叶片比例平均显著更高,这也表明种群之间在对食草作用的耐受性方面也存在差异。包括奠基者效应、对食草动物耐受性的进一步丧失以及飞虱对WB植株的偏好在内的多种因素,似乎可以解释WB种群对飞虱抗性的降低。