Duncan Golicher
This is a rather old (Potvin and Huot 1983), but interesting study.
White tailed deer
The carrying capacity of a white-tailed deer (Odocoileus virginianus) wintering area was detremined based on food availability and biological characteristics of the animals.
Estimated carrying capacity could vary between 0 and 18 deer/\(km^2\) depending on sinking depth of deer in a severe winter
The desirable population in the area studied should be maintained between 15 and 28 deer/\(km^2\).
The sensitivity of the model to variations in the original values was tested and the possible strategies for management discussed.
Looked at
What might a low reproductive rate be due to?
Read the paper for more details of how these challenges were addressed.
Cheetah life cycle that can be divided into three stages.
(Doherty and Ritchie 2016)
http://r.bournemouth.ac.uk:82/Ecosystems/papers/Doherty_Ritchie_2017_Stop_Jumping_the_Gun.pdf
(Miller and Schmitz 2019)
http://r.bournemouth.ac.uk:82/Ecosystems/papers/Miller_Schmitz_2019_Landscape_of_fear.pdf
“In recent decades the ‘landscape of fear’ has grown in popularity to become a central consideration in wildlife management, and has even been reconceptualised as the’landscape of coexistence’for understanding human-wildlife conflicts such as predator attacks on livestock. Yet fear effects are not always the predominant driver of predator-prey interactions. Thus, guiding ecological principles have not been assembled to explain the broader food web interactions that shape the context dependency of carnivore-livestock conflict. We address this gap by developing a conceptual framework as a way to think about the contingencies under which inducing non-consumptive ‘fear effects’ on predators would be effective to mitigate carnivore-livestock conflict. The frame-work specifically considers interactions among wildlife (carnivore predators, wild ungulate prey) and humans(people and livestock) in terms of spatial predator-prey assemblages in which the nature of wildlife human interactions,as either a carnivore-livestock conflict or a coexistence food web, is contingent on the nature of spatial movement and overlap of humans and wildlife across landscapes. Considering human-wildlife interactions within such a spatial food web context can assist in enabling people and wildlife, especially imperiled carnivores, to coexist in human-modified landscapes. The framework offers predictions that should be tested via adaptive management experiments that evaluate whether conflict mitigation solutions aligned with particular spatial human-livestock-carnivore contexts do indeed resolve conflict.”
(Jones et al. 2017)
(Gilpin 1973)
http://r.bournemouth.ac.uk:82/Ecosystems/papers/Gilpin%20-%201973%20-%20Do%20Hares%20Eat%20Lynx.pdf
(Deng 2018)
(May 1999)
(Alan A. Berryman 1992)