Q2. What is the protocol for grazing experiments?
Research protocol requires that grazing experiments be structured in a manner that minimizes both ecological and managerial variability to effectively test hypotheses that enhance their understanding of critical ecological processes operating in grazed ecosystems.
Q3. Why does intensive grazing reduce the energy of raindrop impact?
This occurs because the removal of large amounts of plant cover and biomass by intensive grazing reduces the potential to dissipate the energy of raindrop impact and overland flow.
Q4. What is the important factor in the response of soil hydrological characteristics to grazing?
These hydrological responses to grazing are strongly contingent on community composition, with communities that provide greater cover and obstruction to overland flow such as midgrass-dominated communities having greater hydrological function, including infiltration rate, than short grass–dominated communities (Wood and Blackburn 1981; Thurow 1991).
Q5. What are the objectives of this synthesis?
The specific objectives of this synthesis are to 1) reevaluate the complexity, underlying assumptions, and ecological processes governing the response of grazed ecosystems, 2) summarize plant and animal production responses to rotational and continuous grazing, 3) characterize the prevailing perceptions influencing the assessment of rotational and continuous grazing, and 4) attempt to direct the profession toward a reconciliation of perceptions advocating support for rotational grazing systems with that of the experimental evidence.
Q6. What is the main reason why rotational grazing is not supported by empirical evidence?
A fundamental ecological explanation for why the unifying principles of vegetation responses to grazing do not support greater effectiveness of rotational grazing is that grazing management must optimize several competing ecological processes to attain production goals sustainably.
Q7. What is the primary misconception underlying continued advocacy for rotational grazing on rangelands?
An overestimation of the presumed benefits of rest from grazing, within the framework of rotational grazing systems (e.g., several weeks rest between brief and often intensive grazing periods), may represent the primary misconception underlying continued advocacy for rotational grazing on rangelands (e.g., Taylor et al.
Q8. What is the critical interpretation of continuous grazing?
The critical interpretation of continuous grazing, prompted by excessive stocking rates that werecommon prior to the implementation of proper grazing management, may still be promulgated today.
Q9. What percentage of the experiments reported no differences for plant production/standing crop?
Eighty-nine percent of the experiments (17 of 19) reported no differences for plant production/standing crop between rotational and continuous grazing with similar stocking rates (Fig. 1A).
Q10. What are the main conservation goals of grazing systems?
Conservation goals often emerge at large scales, and even though the flexibility associated with rotational grazing systems can provide managers with opportunities to manipulate grazing frequency, intensity, and seasonality to pursue specific conservation goals (e.g., bird nesting success, periodic plant establishment or reproduction, fuel accumulation or suppression), there has not yet been a comprehensive accounting of the conservation effects associated with the large-scale adoption of grazing systems.
Q11. What is the main argument for rotational grazing?
The experimental evidence indicates that rotational grazing is a viable grazing strategy on rangelands, but the perception that it is superior to continuous grazing is not supported by the vast majority of experimental investigations.