Title | Ecology Notes |
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Course | Ecology And Evolution |
Institution | University of North Carolina at Chapel Hill |
Pages | 33 |
File Size | 1.3 MB |
File Type | |
Total Downloads | 69 |
Total Views | 136 |
lecture notes for the semester...
Population Growth 11.07.18 ***Populations grow by multiplication*** Geometric Growth Equation: Nt+1 = 2 x N t. Geometric growth occurs when reproduction happens at discrete time intervals (ex. Annual plants, cicadas, etc.). Alternate Equation for Geometric Growth: Nt = t N 0 Population at time t = finite rate of increase (growth rate) x initial population size. This equation creates a J-shaped curve. If is 1, population is stable. If > 1, population is growing. If 0 < < 1, population is shrinking. Geometric growth assumes individuals reproduce in synchrony (generations do not overlap). Exponential growth occurs in populations with continuous reproduction and overlapping generations (ex. humans). Equation: Nt = ert x N0 where e is a constant raised to the finite rate of increase, r. Exponential growth creates a J-shaped curve. If r = 0, lambda is 1 and population is stable. If r > 0, lambda > 1 and population is growing. If r < 0, 0 < lambda < 1 and populations is shrinking. Geometric and exponential equations describe the same growth. Exponential shows a more cohesive J-shaped curve while geometric shows a set of points in a J-shaped curve. Short Answer Problem: - If population was 185 in one year and then 198 the following cycle, what is the geometric rate of increase? (Nt = t N 0) 1.07 - Assuming growth rate does not change, what will the population size be two cycles later? 227 - What is the net reproductive rate for this population of cicadas? 1.07 because with a geometric population, lambda is equal to the net reproductive rate There is a finite amount of resources in the universe, therefore there is only a certain number of individuals our planet can support. ● Ex. You are growing a bacteria in a closed jar. What will happen to the population?
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Population will start to grow. Resources and space will be depleted, aggression/competition will increase. Carrying capacity will be reached, population will start to level o and will continue at that same size.
Logistic Growth v. Exponential Growth: - [dN/dt = rN] is the exponential growth equation. [dN/dt = rN (1-N/K)] adds a discounting term to account for density. This discounting term explains the bend in the exponential curve as carrying capacity is approached (exponential growth is density-dependent). - N is current population size, r is finite rate of increase under ideal conditions, K is carrying capacity. - In exponential growth, r is constant. Logistic growth assumes K is constant. Population Regulation: - Leveling o suggests that extrinsic forces limit growth as population size (and density) increases. - Births, deaths, and dispersal (emigration and immigration) all contribute to change in population size. Density-Dependent Population Regulation: factors that might decrease births, increase deaths, or increase dispersal out of an area when population density increases. - Ex. availability of food, predation, disease and migration, parasites. Because density-dependent factors respond to population density, they can regulate populations. Density-Independent Factors do NOT regulate population size, but they do aect the population.
SimUText Assignment 18: Competition (Sec 1: 1-5, 11-12; Sec 3: 1-26) If resources are unlimited, populations grow exponentially and competition does not occur. When resources are limited, similar organisms compete for those resources. This impacts both individual organisms and whole populations. Resources are always limited over the long term so living organisms are almost always competing for something. All living organisms need certain resources to live and reproduce. Each organism needs energy (photosynthesis, consumption of other organisms, consumption of detritus). Each organism also needs nutrients like nitrogen/phosphorous and some require complex molecules like amino acids. Populations will grow rapidly if they have unlimited resources. Even if resources are temporarily abundant, the resulting population growth will eventually lead to resource depletion. When their life-sustaining resources are limited, organisms are forced to compete with each other. Sometimes those competitive interactions will be direct while other times they will be subtle. The competitive exclusion principle states that no two species can coexist in exactly the same ecological niche. As a result, if two species are using exactly the same resources, one of them is expected to win the competition and to drive the other species to extinction in that location. A species' fundamental niche is the complete set of environmental conditions in which the species can potentially survive and reproduce. This includes both abiotic factors like temperature and precipitation as well as biotic factors like food availability. However, unlike the realized niche, the fundamental niche is not restricted by interactions with other species. A species' realized niche is the set of environmental conditions in which the species is actually found in nature. It is a subset of the species' fundamental niche; the realized niche is further restricted by biotic interactions like competition, predation, and parasitism. Competition is the interaction between two organisms that use the same limited resource. Both organisms tend to be negatively aected by this interaction and can suer increased mortality and reduced reproductive capacity because of it.
Competition can also be an important driving force of adaptation, however, and may ultimately influence how species evolve. Competition can occur between members of the same species (intraspecific competition) or between members of dierent species (interspecific competition). Plants usually compete for physical space, water, light, and soil or water nutrients; animals often compete for food, territory, and mating partners. Parasitism is a form of symbiosis where one organism lives in close association with another and gains advantage from doing so. The parasite gains from this relationship whereas the host is harmed in some way. It is easy to find situation where competitive exclusion does not operate; there are also some theoretical problems with the definition of a niche but both concepts are very helpful in ecological research. Ecologists quantify the relative competitive strengths of dierent versus same species competitors with competition coecients. Competition coecients represent the per capita eect on the growth of one species (species 1) of another species (species 2) and are symbolized by the Greek letter alpha, α, and two subscripts. Thus, the competition coecient describing the eect on species 1 of species 2 would is written as α12 while the competition coecient describing the eect on species 2 of species 1 would be written as α 21 . By convention, the first subscript indicates which species' growth is being reduced while the second subscript represents its competitor. The logistic growth equation with N1 K1 )
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NO COMPETITION: dN 1 /dt = rN 1 (1
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EQUIVALENT COMPETITOR: dN 1 /dt = rN 1 (1
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ANY COMPETITOR: dN 1 /dt = rN 1 (1
N 1+N 2 K1 )
N 1+α 12N 2 ) K1
The equations for when any competitor is present is called the Lotka-Volterra competition equation. It predicts how the population size of two competing species will change over time (you can use K2 and N2 in the equation for the second population).
Ecologists use a phase plane graph to plot the population sizes of both species against each other. A single species has reached its equilibrium population size when its population is no longer growing or contracting. Mathematically, the equilibrium population size is reached when dN/dt = 0. For a species without competitors or predators, the equilibrium population is equal to the species' carrying capacity. In other words, for this single species, dN/dt = 0 when N = K. Technically, it is also true that dN/dt = 0 when the population has gone extinct, i.e., when N = 0, but this is usually a less interesting equilibrium. When two populations have reached their equilibrium size, they stop growing and all future points are plotted on top of each other. When no changes occur in population sizes over time, a steady state point has been reached. Sometimes a steady state is globally stable (there is one state the system will reach no matter where it starts). A phase portrait, plotted on a phase plane, is a type of two-dimensional graph that describes how a dynamic system will change over a short period of time, given dierent initial values for the graphed variables. It depicts (usually using arrows) trajectories of change for each combination of the two variables. The isocline of zero population growth line for a pathogen indicates the condition under which the pathogen population (N1) will not grow or shrink (N2 for N1 and K2 for K1 can be substituted to measure the zero population growth of the probiotic). N 1 = α12N 2 + K 1 When two isoclines intersect and all phase portrait arrows point toward the intersection, this indicates that the system has a stable equilibrium: no matter what the initial population sizes are, the two bacteria strains will ultimately coexist. Population sizes of both species will move toward the intersection of the isoclines and then remain at those sizes indefinitely. Increasing the carrying capacity (K2) of the probiotic shifts the location of the probiotic’s isocline farther and farther from the origin. When K2 is very large, the probiotic isocline lies entirely outside the pathogen’s isocline. All of the arrows of the phase portrait point to a steady state on the y-axis where the pathogen population size is zero. If the two isoclines don’t intersect coexistence is not possible and the species who isocline lies furthest from the origin will eliminate the other from the system.
Changing α12 alters the location of the pathogen’s isocline. As α12 is increased the y-intercept shifts further toward the origin. When α12 is large enough the pathogen’s isocline is so close to the origin that it no longer intersects the probiotic’s isocline. This indicates that the probiotic will outcompete the pathogen and eliminate it from the system. If a process or system is at an equilibrium, its overall behavior is not changing over time. If the system is at an unstable equilibrium, small perturbations (changes to the system) will upset the balance and the system will not likely return to the same state. A special case of equivalent competitors exists when α12 = α21 and K1 = K2. Stable coexistence results when intraspecific competition is stronger than interspecific competition (when K2 < K1/α12 and K1 < K2/α21). Smaller intraspecific competition leads to a smaller carrying capacity because individuals of the same species compete for the same resources. The strength of competition between species often reflects how similarly they use resources; species are less likely to coexist when their resources are more similar. When two species have strong competitive eects on each other, one of them will likely be driven to extinction. *Interspecific competition is stronger than intraspecific competition*
SimUText Assignment 19: Predation (Sec 1: 1-2; Sec 2: 1-14; Sec 3: 1-23) The organism that a pathogen or parasite lives in or feeds on is its host. A parasite may require several hosts of dierent species to complete its entire life cycle. The definitive host is the host in which the parasite reaches maturity and undergoes sexual reproduction. The other hosts are intermediate hosts, and often play an important role in dispersing the parasite to places where it can reinfect new definitive hosts. Predation, parasitism, and herbivory are forms of exploitation and can be represented as (+/-) interactions. One species gains (+) and the other loses (-). A species can also be neutral (0) in an interaction with another species. Types of Species Interactions - Competition (-/-) : both species do worse in the other’s presence than they do if the other species is absent. - Amensalism (0/-) : one species is unaected by the interaction while the other is harmed. - Exploitation (-/+) : one species benefits and one is harmed. - Neutral (0/0) : two species inhabit the same area but don’t have a positive or negative aect on one another. - Commensalism (0/+) : one species benefits from the interaction while the other is unaected. - Mutualism (+/+) : both species benefit from the interaction. Exponential Growth: N (t + 1) = λN(t) where N(t) is the size of the population at time t, λ is the number of ospring produced per individual each unit of time, and N(t + 1) is the size of the population one unit of time after the present time. If the unit of time is very small, the equation can be rewritten as dN/dt = rN (EXPONENTIAL GROWTH EQUATION). dN/dt is how fast the population size is changing and r represents the population’s intrinsic growth rate (growth rate per individual when resources are unlimited). The per capita growth rate is the rate at which additional individuals are being added to the population, per individual already in the population.
dN prey
Prey growth with predation: dt = r prey x N prey - aNpreyN predator Encounters with predators should cause the prey population to grow less rapidly. The more predators there are, the more encounters there will be and the slower the prey population should grow. The rate at which predators encounter prey also depends on how many prey are available. More prey available means more prey consumed. The encounter term (N preyNpredator) increases with more predators or more prey. Because this term is negative in the equation, as the number of predators/prey increases, prey growth will decrease and vice versa if the predators/prey decrease. The searching eciency parameter (a) represents the variation in how fast predators can find/attack/kill prey. Larger values of a reflect more ecient predators. aNpreyNpredator is the consumption rate. Predator growth (partial conversion) with death:
dN predator = dt
abN preyNpredator - mN predator
The prey consumption rate (aN preyNpredator) defines how quickly predators reduced prey. This term represents how much the predators are eating so it also determines how quickly the predator population will grow. The predator population should grow in proportion to how much they eat but it implies that consumption of one prey individual produces one predator individual which isn’t necessarily the case. A predator has to eat many prey before it accumulates enough resources to have ospring. A conversion factor (b) is used to convert the encounter rate into the number of new predators produced. Predators die and random death is modeled as a proportion of the predator population dying in each unit of time (negative m for mortality). Adjusting predation and prey growth rates cannot eliminate cycling and cannot cause prey to go extinct. If the prey population is large and the predator population is small, the predator population will increase. If the predator population is large, the prey population will decrease. If the prey population is small and the predator population is large, the predator population will decrease. If the predator population is small, the prey population will increase. Growth of the predator population lags behind growth of the prey population because the abundance of prey stimulates predator population growth. The relationships
between these growth are presented as continuous up and down cycles. These cycles are regular and even with predator cycles following prey cycles. The Lotka-Volterra equations all listed above are deterministic: the values of the parameters and the initial population sizes determine exactly what will happen. A stochastic model includes randomness and variation. Predators can reduce the number of prey directly by killing individuals. But predators can also aect prey indirectly, when prey respond to the risk of predation by altering their behavior. The concept of the ecology of fear integrates the behavioral changes that can result from predator-prey interactions with the numerical changes. An example of the ecology of fear is illustrated by behavioral cascades. Behavior cascades are a specific type of top-down eect in which the impacts of adding or removing a predator aects primary producers. They dier, however, in that the population size and/or biomass of the herbivore is not necessarily aected by the predator. Instead, when the predator is present, it alters the behavior of the herbivore to such a degree that the herbivore can no longer exert enough grazing pressure to limit plant growth. A two-dimensional space showing one state variable plotted against another state variable is called a Phase Plane. Each timestep, a point in the Phase Plane is plotted at the intersection of prey and predator population sizes (Nprey, Npredator). If the prey and predator populations are both small, a point will appear in the lower left part of the phase plane. If they are both large, a point will appear in the upper right, and so on. The trajectory of this graph shows how the two populations change relative to each other. Each cycle of prey v. predator can be characterized by two numbers. The amplitude of the cycle is the height dierence between the top and the bottom of each cycle. The period is the amount of time from one peak to the next in the cycle. If there were phase plane plots for 2 dierent predator-prey systems, you would be able to see the dierence if they had cycles with the same period (time required to experience one peak and one trough) but dierent amplitudes (population size dierence between peak and trough).
You would not be able to see the dierence between cycles of the same amplitude but with dierent periods. The location and the width/height of the phase plot circle corresponds to the amplitudes of the cycles on the time plot. When predator and prey populations are modeled using the Lotka-Volterra equations, the cycle through the same peaks and valleys in size, time after time. Because there is no dierence in the amplitude of the cycles, each cycle lies right on top of the previous one in the phase plane. The Lotka-Volterra predator-prey equations are neutrally stable. This means that changing the initial population sizes simply causes the population cycles to proportionally adjust, returning to their new sizes again and again. The arrows in the phase portrait indicate whether the predator and prey populations will increase or decrease in the next timestep given dierent starting positions in phase space. If the initial combination of predator and prey population sizes is at the arrow’s origin, the prey population will decrease and the predator population will stay exactly the same size in the next timestep.
There is one particular combination of initial predator and prey population sizes that generates such a small, tight trajectory that it plots as a single point. When the predator and prey populations start out at this combination of sizes, there will be no cycling because neither population will change in size over time. Assumptions of the Lotka-Volterra predator-prey model: - There are no eects of crowding for either the prey or predator (there is no density dependence in growth rate). - All predator and prey individuals are equally likely to meet any of the others (populations are evenly spread out and well mixed). - The prey species is the only food source for the predator. - The predator is the only significant cause of death for the prey. - Each predator individual can catch and eat prey individuals instantly (there is no handling time). - There is no immig...