Branch Lyn C, Villarreal Diego, Hierro Jose Luis, Portier Kenneth M
Department of Wildlife Ecology and Conservation, University of Florida, 32611, Gainesville, FL, USA.
Program for Studies in Tropical Conservation, University of Florida, 32611, Gainesville, FL, USA.
Oecologia. 1996 May;106(3):389-399. doi: 10.1007/BF00334567.
We studied spatial and temporal effects of local extinction of the plains vizcacha (Lagostomus maximus) on plant communities following widespread, natural extinctions of vizcachas in semi-arid scrub of Argentina. Spatial patterns in vegetation were examined along transects extending outward from active and extinct vizcacha burrow systems. Responses of vegetation to removal of vizcachas were assessed experimentally with exclosures and by documenting vegetation dynamics for 6 years following extinctions. Transect data demonstrated clear spatial patterns in plant cover, particularly an increase in perennial grasses, outward from active vizcacha burrows. These patterns were consistent with predictions based on foraging theory and studies that document grasses as the preferred food of vizcachas. Removal of vizcachas, experimentally and with extinctions, resulted in an immediate increase in perennial and annual forbs indicating that intense herbivory can depress forb cover, as well as grasses. After a 1-year lag following cessation of herbivory, cover of grasses increased. Forbs declined as grasses increased. The long-term effect of extinction of vizcachas was a conversion of colony sites from open patches dominated by forbs to dense bunch grass characteristic of the matrix. Major changes in vegetation occurred within 2-3 years after extinction, resulting in a large pulse of landscape change. However, some species of grasses were uncommon until 5-6 years after the vizcacha extinction. With extinction and colonization, vizcachas generate a dynamic mosaic of patches on the landscape and create temporal, as well as spatial, heterogeneity in semi-arid scrub.
我们研究了阿根廷半干旱灌木丛中草原豚鼠(Lagostomus maximus)局部灭绝后对植物群落的时空影响,这些灭绝是广泛的自然现象。沿着从活跃和已灭绝的草原豚鼠洞穴系统向外延伸的样带,研究了植被的空间格局。通过设置围栏实验以及记录灭绝后6年的植被动态,评估了植被对草原豚鼠消失的反应。样带数据显示出植物覆盖的明显空间格局,特别是从活跃的草原豚鼠洞穴向外,多年生草本植物有所增加。这些格局与基于觅食理论的预测以及将草作为草原豚鼠首选食物的研究结果一致。通过实验和实际灭绝去除草原豚鼠后,多年生和一年生杂类草立即增加,这表明强烈的食草作用会抑制杂类草以及草本植物的覆盖。在食草作用停止1年后,草本植物的覆盖增加。随着草本植物增加,杂类草减少。草原豚鼠灭绝的长期影响是群落地点从以杂类草为主的开阔斑块转变为基质特有的密集丛生草。灭绝后2 - 3年内植被发生了重大变化,导致景观变化出现大幅波动。然而,直到草原豚鼠灭绝5 - 6年后,一些草本植物种类才变得常见。随着灭绝和重新定居,草原豚鼠在景观上形成了动态的斑块镶嵌,并在半干旱灌木丛中创造了时间和空间上的异质性。