Manier Daniel J, Hobbs N Thompson
Natural Resource Ecology Laboratory, Colorado State University, Fort Collins, CO 80523-1499, USA.
Oecologia. 2007 Jul;152(4):739-50. doi: 10.1007/s00442-007-0689-z. Epub 2007 Mar 21.
Improving understanding of the connections between vegetation, herbivory, and ecosystem function offers a fundamental challenge in contemporary terrestrial ecology. Using exclosures constructed during the late 1950s, we examined effects of grazing by wild and domestic herbivores on plant community structure, aboveground herbaceous primary production, and nutrient cycling at six sites in semi-arid, sagebrush rangelands during 2001-2002 in Colorado, USA. Enclosures provided three treatments: no grazing, grazing by wild ungulates only, and grazing by wild and domestic ungulates. Excluding all grazing caused an increase in shrub cover (F = 4.97, P = 0.033) and decrease in bare ground (F = 4.74, P = 0.037), but also a decrease in plant species richness (F = 6.19, P = 0.018) and plant diversity (F = 7.93, P = 0.008). Effects of wild ungulate grazing on plant cover and diversity were intermediate to the effects of combined domestic and wild grazing. Aboveground net primary production was higher in both grazed treatments than in the ungrazed one (F(wild + domestic) = 2.98, P = 0.0936 and F(wild only) = 3.55, P = 0.0684). We were unable to detect significant effects of grazing on other ecosystem states and processes including C:N ratios of standing crops, N mineralization potential, or nitrification potential. Best approximating models revealed positive correlation between N availability and herbaceous cover and a negative correlation between herbaceous primary production and the ratio of shrub-herb cover and plant diversity. We conclude that ungulate herbivory, including both wild and domestic ungulates, had significant effects on plant community structure and ecosystem function during this 42-year span. Responses to the wild ungulate treatment were consistently intermediate to responses to the no grazing and wild + domestic grazing treatments. However, we were unable to detect statistical difference between effects of wild ungulates alone and wild ungulates in combination with livestock.
增进对植被、食草动物与生态系统功能之间联系的理解,是当代陆地生态学面临的一项根本性挑战。利用20世纪50年代末建造的围栏,我们于2001年至2002年在美国科罗拉多州半干旱的蒿属植物牧场的六个地点,研究了野生和家养食草动物的放牧对植物群落结构、地上草本植物初级生产力以及养分循环的影响。围栏设置了三种处理方式:不放牧、仅由野生有蹄类动物放牧以及由野生和家养有蹄类动物放牧。排除所有放牧导致灌木覆盖度增加(F = 4.97,P = 0.033)和裸地减少(F = 4.74,P = 0.037),但植物物种丰富度(F = 6.19,P = 0.018)和植物多样性(F = 7.93,P = 0.008)也有所下降。野生有蹄类动物放牧对植物覆盖度和多样性的影响介于家养和野生联合放牧与不放牧的影响之间。两种放牧处理下的地上净初级生产力均高于不放牧处理(F(野生 + 家养)= 2.98,P = 0.0936;F(仅野生)= 3.55,P = 0.0684)。我们未能检测到放牧对其他生态系统状态和过程的显著影响,包括现存作物的碳氮比、氮矿化潜力或硝化潜力。最佳近似模型显示,氮有效性与草本植物覆盖度呈正相关,草本植物初级生产力与灌木 - 草本植物覆盖度之比和植物多样性呈负相关。我们得出结论,在这42年期间,有蹄类动物的啃食,包括野生和家养有蹄类动物,对植物群落结构和生态系统功能产生了显著影响。对野生有蹄类动物处理的响应始终介于对不放牧和野生 + 家养放牧处理的响应之间。然而,我们未能检测到仅野生有蹄类动物与野生有蹄类动物和家畜联合作用之间影响的统计学差异。