James Hutton Institute, Craigiebuckler, Aberdeen AB15 8QH, UK.
Ann Bot. 2013 Aug;112(4):731-9. doi: 10.1093/aob/mct126. Epub 2013 Jun 24.
Large herbivores are often removed or reduced as part of vegetation restoration programmes, but the resultant increase in vegetation biomass and changes in vegetation structure may favour small mammals. Small mammals may have large impacts on plant community composition via granivory and sapling herbivory, and increased small mammal populations may reduce any benefits of large herbivore removal for highly preferred species. This study tested the impacts of small mammal herbivory, microsite characteristics and their interaction on growth and survival of three montane willow species with differing chemical compositions, Salix lapponum, S. myrsinifolia and S. arbuscula.
In two separate years, 1-year-old saplings were planted within a 180 ha, large-mammal scrub regeneration exclosure, and either experimentally protected from or exposed to small mammals (bank voles). Saplings were planted in one of two microsite treatments, vegetation mown (to mimic a grazed sward) or disturbed (all above- and below-ground competition removed), and monitored throughout the first year of growth.
Approximately 40 % of saplings planted out in each year were damaged by bank voles, but direct mortality due to damage was very low (<2 %). There were no strong species differences in susceptibility to vole damage. Microsite treatment had no impact on the proportion of saplings attacked, but in 2004 saplings in mown microsites were more severely damaged and had smaller increases in size than those in disturbed microsites. In 2003, saplings in mown microsites had smaller increases in stem diameter following attack than those in disturbed microsites.
Planting 1-year-old willow saplings into disturbed microsites may aid growth, reduce the severity of small mammal damage and improve recovery following sub-lethal small mammal damage. Restoration management of montane willow scrub should therefore consider manipulating the planting site to provide disturbed areas of soil.
大型食草动物通常作为植被恢复计划的一部分被移除或减少,但随之而来的植被生物量增加和植被结构变化可能有利于小型哺乳动物。小型哺乳动物可能通过食果和幼树食草对植物群落组成产生重大影响,而增加的小型哺乳动物种群可能会减少大型食草动物移除对高度偏好物种的任何益处。本研究测试了小型哺乳动物食草、微生境特征及其相互作用对三种具有不同化学成分的高山柳树物种(Salix lapponum、S. myrsinifolia 和 S. arbuscula)生长和存活的影响。
在两个独立的年份中,在一个 180 公顷的大型哺乳动物灌丛再生围栏内种植了 1 年生的幼树,并对其进行了实验性的保护或暴露于小型哺乳动物(田鼠)之下。幼树种植在两种微生境处理之一中,一种是植被修剪(模拟放牧草地),另一种是干扰(所有地上和地下竞争物都被移除),并在整个生长的第一年进行监测。
每年种植的幼树约有 40%受到田鼠的损害,但由于损害导致的直接死亡率非常低(<2%)。在易受田鼠损害方面,没有明显的物种差异。微生境处理对受攻击的幼树比例没有影响,但在 2004 年,修剪微生境中的幼树受到的损害更严重,且比干扰微生境中的幼树生长得更小。在 2003 年,修剪微生境中的幼树在受到攻击后,茎直径的增长比干扰微生境中的幼树小。
将 1 年生柳树幼树种植到干扰微生境中可能有助于生长,减少小型哺乳动物损害的严重程度,并改善小型哺乳动物亚致死损害后的恢复。因此,高山柳树灌丛的恢复管理应考虑操纵种植地点,提供干扰土壤的区域。