This course presents the principles of evolution and ecology for citizens and students interested in studying biology and environmental sciences. It discusses major ideas and results. Recent advances have energised these fields with evidence that has implications beyond their boundaries: ideas, mechanisms, and processes that should form part of the toolkit of all biologists and educated citizens.
Major topics covered by the course include fundamental principles of ecology, how organisms interact with each other and their environment, evolutionary processes, population dynamics, communities, energy flow and ecosystems, human influences on ecosystems, and the integration and scaling of ecological processes through systems ecology.
This course will also review major ecological concepts, identify the techniques used by ecologists, provide an overview of local and global environmental issues, and examine individual, group and governmental activities important for protecting natural ecosystems. The course has been designed to provide information, to direct the student toward pertinent literature, to identify problems and issues, to utilise research methodology for the study of ecology and evolution, and to consider appropriate solutions and analytical techniques.
Needed Learner Background: general biology and a good understanding of English.
This course has the following expectations and results:
1) covers the theoretical and practical issues involved in ecology and evolution,
2) conducting surveys and inventories in ecology,
3) analyzing the information gathered,
4) and applying their analysis to ecological and conservation problems.
From the lesson
Module 2. The Ecosystem
In this module, we will talk about agonistic and foraging interactions between species (such as predation, herbivory and parasitism) and mutualistic interactions (such as symbiosis, commensalism, endosymbiosis, etc.). Then we will see how these interactions influence the evolutionary ecology of species and their diversity. In the last lesson of this module we will analyse the energy flux and biogeochemical cycles that keep alive Earth’s ecosystems and the whole biosphere (e.g. Gaia).
Ph.D., Associate Professor in Ecology and Biodiversity Biological Diversity and Ecology Laboratory, Bio-Clim-Land Centre of Excellence, Biological Institute
Hi learners, welcome to my eighth lesson of the course Ecology: From Cells to Gaia.
Today we will talk about evolutionary ecology.
To understand the factors responsible for
the population dynamics of even a single species in a single location,
it is necessary to have knowledge of physical chemical conditions, available resources,
the organism life cycle,
and the influence of competitors,
predators and parasites or rate of birth,
death, immigration and emigration.
There are contrasting theories to explain the abundance of populations.
At one extreme, researchers emphasized the apparent stability of
population and point to the importance of forces that stabilize,
such as the density-dependent factors.
At the other extreme those who place more emphasis
on density fluctuation may look at external,
often density independent factors,
to explain the changes.
K factors analysis is a technique that can be applied to
life table studies to draw light both on determination and regulation of abundance.
Movement can be a vital factor in determining and/or regulating the abundances.
A radical change in the way ecologists think about population has
involved focusing attention less on process occuring within population,
and more patchiness: the colonization and extinction of subpopulation,
within an overall metapopulation and dispersal between subpopulations.
Disturbances that open up gaps - patches - are common in all kinds of community.
Founder controlled communities are those in which
all species are approximately equivalent in their ability to evade gaps,
and there are equal competitors that can hold
the gaps against all comers during their lifetime.
Dominance controlled communities are inside those in
which some species are competitively superior to others,
so that an initial colonizer of a patch cannot necessarily maintain its presence there.
The phenomenon of dominance control is
responsible for many example of community succession.
Primary succession as I told you before,
occur in habitats were no seeds or spores remained from previous occupants of the site.
All colonization must be from the outside the patch.
Secondary succession instead occur when existing communities are disarmed,
but some, at least of their seed, remain there.
It can be very difficult to identify when
a succession reaches a stable climate's community,
since this way takes centuries to achieve and in the meantime,
further disturbances are likely to occur.
The exact nature of
the colonization process in an empty patch depends on the size and location of that.
No predator-prey, parasite-host or grazer-plant pair exist in isolation.
Each is part of a complex food web involving other predators, parasite,
food sources and competitors within the various throphic level of a community.
The effect on one species on another,
its herbivorous prey, maybe direct and straightforward.
But indirect effect may also be felt by any of
the myriad species linked more remotely in the food web.
One of the most common is a trophic cascade;
in which a predator reduces the abundance
of a herbivore thus increasing the abundance of plants.
Top-down control of a food web occurs in situation in which the structure, the abundance,
the species number of lower trophic levels
depends on the effect of consumers from higher trophic levels.
Bottom-up control, instead, in a community structure depend on factors such as
nutrient concentration and prey availability that influence the trophic level from below.
The relative importance of these forces varies according to
the trophic level under investigation and the number of trophic levels present.
Some species are more tightly woven in the food web than others.
This species removal would produce a significant effect such as extinction,
or a larger change in density in at least one other species,
may be thought of as a strong interactor.
Removal of some strong interactors leads
to significant changes that spread throughout the food web.
We refer to these as keystone species.
The relationship between food web complexity and stability is uncertain.
Anchor is needed in deciding what is meant by stability.
Mathematical and empirical studies agree in suggesting that if anything,
population stability decreases with complexity whereas the stability of
aggregate properties or work communities
increases with complexity in particular species richness.
So at the end of this lesson I have some question for you.
The first is: what are mean by bottom-up and top-down control?
The second is: how would you expect communities to differ
if they were dominated by founder or dominance control?
So thank you for your attention and see you at the next lecture.