A species' persistence is related to its ability to survive in a given environment. Persistence is generally defined as a species's continued presence in a given geographic area. Locally, it can be measured in units of time, where a species' persistence time is defined as the time between local colonization and extinction in a given geographic area.
To predict a species' persistence in a given area, one must consider the species' colonization potential and the species' chance of extinction.
To persist, a species must either be a primary producer without strong predators or competitors, or the species must be a consumer with strong mutualistic partners or prey in sufficient abundance
Read on for some thoughts on why this can be a difficult subject for teachers and students, five suggestions for changing it, and the many benefits of using our virtual lab.
Figure 1: Laboratory demonstration showing patient reception for this class. The landscape ecology simulation is provided by Labster and available for University / College classes.
Why Landscape Ecology Can Be Challenging For Students
There are three reasons in particular why students find this course to be difficult.
1. Missing basic concept
If the basic knowledge is not well understood by the students, the practical application of the course becomes very scary for them. Studying how different species disappear from year to year can be demoralizing because it indicates that human activities are threatening these species.
2. Inadequate teaching tools or materials.
Many ecological phenomena are difficult to study because ecosystems are highly integrated sites with many actors having diverse relationships with one another. This complexity implies that it is often difficult to know the actual consequences of an event or action
The lack of training tools makes this a challenge, as modeling one landscape ecology lab within another to determine sustainability in a spatially heterogeneous setting is not always feasible.
3. Subject complexity
Figure 2: Laboratory demonstration from the landscape ecology simulation, which is provided by Labster and available for University / College classes.
In ecology, colonization refers to the formation of organisms, populations, or species in a new area. Successful colonization takes many generations and results in an expansion of the species' population distribution. Many factors influence the colonization potential of a species, including dispersal and specialization.
Barriers can prevent the spread of species or resources between patches and reduce landscape connectivity. In response, a corridor is a patch that physically connects two larger areas of a similar type of patch. Similarly, stages are patches that support dispersal between two patches by maintaining a small population of species between two large patches.
5 Pathways To Make Landscape Ecology Class More Understandable
With those points in mind, here are five things you might consider incorporating into your landscape ecology class to make it more engaging, accessible, and fun to teach for you and your students.
1. How it all started
A central theory of landscape ecology goes back to "The Theory of Island Biogeography" by MacArthur & Wilson. This work considers island biodiversity as a result of competing colonization forces by continental stocks and stochastic extinctions. The concept of island biogeography has been generalized from physical islands to abstract habitat patches by Levins' metapopulation model (which can be applied, for example, to forest islands in agricultural landscapes). This generalization stimulates the growth of landscape ecology by providing conservationists with a new tool to assess how habitat fragmentation affects population survival. Recent growth in landscape ecology has been largely driven by the development of geographic information systems (GIS) and the availability of large-scale habitat data (e.g. remote sensing data sets) is promoted.
2. Relate it to the real world
Extinction is defined as the cessation of the existence of a species within an area. This reduces biodiversity within that area and can affect the health, population size, and persistence of other species due to direct and indirect effects of the species' disappearance.
Extinction rates refer to the number of species that will become extinct per unit of time, unit of reduced area, or unit of species present in that area. Two methods of estimating the number of extinct species due to landscape area reduction are using the Species-Area Relationship (SAR) and the Endemics-Area Relationship (EAR).
The Species-Area Relationship (SAR) describes the relationship between the area of a landscape, or part of a landscape, and the number of species found within that area. The area must be contained and is often depicted as islands or patches inside a large landscape. From the SAR curve shown in Figure 3, you can see that the number of species within an area tends to increase with the size of the area. In smaller areas, the increase in species is due mainly to colonization, while in larger areas, the increase in species is caused by speciation. When constructing a SAR curve, often only a sub-category of species is selected to analyze. The popular power-law model for SAR is:
SA = cAz ;
where S is the number of species, c is a constant, A is the area and z is the slope of the curve. The reverse SAR curve can also be used to estimate the extinction rate linked with a given reduction in the size of the habitat.
3. Use graphics to create more impact
Making learning more practical by using graphical representations can interest your students and make your lessons easier to understand.
For example, explaining the relationship between endemic areas and range. Compared to the Species-Area Relationship (SAR), which measures the number of ALL species in a given habitat area, Endemic Species-Area Relationship (EAR) only measures the number of endemic species in habitats of different sizes. The slope of this curve can also be used to estimate species decline due to habitat loss using the model:
Sloss = cAz - c(A - a)z ; where S is the number of species, c is a constant, A is the original area, a is the new area, and z is the slope of the EAR curve.
Using the EAR rather than the SAR respects the fact that a non-endemic species that become extinct within one area, may still have a healthy population within a different area, and therefore, only the loss of endemic species is important for estimating extinction rates due to loss of habitat size.
4. Explain unfamiliar terms
As a teacher, explaining foreign terms to students will further increase their motivation in the subject.
Dispersal refers to the distribution of a species' population in the environment. Different modes of dispersal (e.g., seed dispersal, migration, or foraging) can be measured by measuring the species' dispersal radius, which represents the distance from the place of birth to the site of reproduction during the organism's lifetime. In general, species with a larger distribution radius have a higher probability of colonization.
Species specialization refers to its ability to survive in diverse environments and utilize various resources. It depends on evolutionary trade-offs that lead to the species' preferred diet, habitat, and climate. Species can be described as specialists or non-specialists. Specialists have a population distribution limited to a small landscape area because they need specific, unique, and/or scarce resources. Generalists are found in various environments due to their ability to adapt to a wide variety of foods, habitats, and climates. Generalists often have higher colonization rates because of their greater likelihood of surviving in new environments.
Patch: In landscape ecology, it is recognized that the features of large landscapes are often not evenly distributed and that the landscape is instead made up of many distinct sub-areas, called patches. Spatial heterogeneous landscapes consist of different types of patches. The patch in each landscape is not self-evident, and the specific identity of the patch must be determined with the phenomenon under consideration.
Patch identity: Patches can have different identities based on their characteristics and importance to the landscape as a whole. For example, the landscape matrix can be defined as the patch type, which is the most extensive and cohesive and therefore exerts a dominant influence on the area's flora, fauna, and ecological processes. The connectivity matrix is the extent to which the landscape facilitates the movement of species between patches. Not all landscapes have a clear matrix. An isolated patch is a patch that is located at a significant distance from other similar patches. Isolation may result in decreased colonization rates in this patch.
5. Help them enjoy using Labster's virtual lab simulations
A unique way to teach landscape ecology is through a virtual laboratory simulation. At Labster, we’re dedicated to delivering fully interactive advanced laboratory simulations that utilize gamification elements like storytelling and scoring systems, inside an immersive and engaging 3D universe.
Check out the Labster Landscape ecology simulation that allows students to learn through active, inquiry-based learning. In the simulation, students will learn to identify and compare unique patch types on the exoplanet Astakos IV and use their specific characteristics to help understand local population dynamics.
Learn more about Labster's landscape ecology simulation here or get in touch to find out how you can start using virtual labs with your students.