With very high grazing pressure, animals may harm vegetation points by removing too much biomass,
especially from preferred plant species. This happens more easily by animals being able to remove biomass close to the soil, such as horses, sheep or goats rather than cattle (Animut and Goetsch 2008; Benavides et al. 2009; Menard et al. 2002). With high grazing intensity, Dibutyryl-cAMP clinical trial effects due to treading and gap creation will also be more serious. In contrast to selective grazing, gap creation and compaction will not be maximal at low grazing pressures, but increase with increasing intensity. However, colonisation of new gaps will be retarded with high grazing intensity due to frequent disturbances of newly emerging propagules. Excreta patches will affect larger pasture areas (White et al. 2001) and more nutrients can be lost by run-off, leaching or gaseous losses. However, increased grazing pressure decreases the size of dung pats as the animals tend to feed closer to and sooner after an excretion event. The grazing system may have large effects on diversity, even if the annual Acadesine stocking density is the same for different systems. Most important in selleck chemicals this respect are rotational grazing and permanently stocked pasture. Permanently stocked pasture requires less work from the farmer, as the animals are put on the pasture in
spring and removed at the end of the grazing season. In rotational grazing, animals have less space per unit of time, but are transferred to a new paddock at regular time intervals. Thus, at a given time, the stocking density is higher with rotational grazing, but the vegetation is then allowed time to recover until the animals rotate back to the same paddock. Therefore, the pressure on preferred species is less intense than in permanently stocked pastures (Pavlu et al. 2003). It has been found that grazing at intermediate intensity may allow more plants to get to the flowering stage (Correll et al. 2003; Sahin Demirbag et al. 2009) and may thus have positive effects on the vegetation, but also on the abundance of insects (Dumont et al. 2009; Kruess and
Tscharntke 2002). As permanently stocked pastures can only be grazed with relatively few animals to allow them to find enough fodder even ADP ribosylation factor in times of little vegetation growth, different areas develop with very different frequency of use. The seasonal vegetation development of a continuously grazed pasture (set stocking) in temperate areas can be divided into three parts, namely the spring/early summer period, the summer, and the late summer/autumn period based on the development of herbage mass (Jacob 1987). Figure 1 gives an overview of the interactions of grazing cattle and sward structure during a grazing period. The spring/early summer period is characterized by a surplus of herbage mass of good quality allowing a high performance of livestock.