Equilibrium: $x_e = \gamma/\delta$, $y_e = \alpha/\beta$
Conservation: $V = \delta x - \gamma\ln x + \beta y - \alpha\ln y$
Tune α, β, γ, δ and watch how oscillation period changes. The closed orbits in the phase portrait reveal the conservative nature of classic Lotka-Volterra dynamics. Switch to logistic or Holling Type II to see how ecological realism changes the picture.
Equilibrium: $x_e = \gamma/\delta$, $y_e = \alpha/\beta$
Conservation: $V = \delta x - \gamma\ln x + \beta y - \alpha\ln y$
x₀ and y₀ sliders, puts the system into a permanent, closed orbit around that point. In practice, real ecosystems have stabilizing factors, which is why we added parameters like Carrying Capacity (K). Set K to a low value and watch the oscillations dampen.h means each meal occupies a predator longer, reducing its total consumption rate. This limits predator growth and can stabilize the system. For instance, a lion after a big kill rests for hours. Slide the handling time up and see how it smooths out the violent predator peaks.The core engine of the simulation is a pair of coupled, nonlinear ordinary differential equations (ODEs). The first describes the rate of change of the prey population (x), which grows on its own but is reduced by encounters with predators (y).
$$\frac{dx}{dt}= \alpha x - \beta x y$$$\alpha$ : Prey intrinsic growth rate (1/time). $\beta$ : Predation rate coefficient, representing the efficiency of capture. The term $\beta x y$ assumes encounters are proportional to the product of both populations (the "mass action" law).
The second equation governs the predator population, which dies off naturally but grows by converting consumed prey into new predators.
$$\frac{dy}{dt} = \delta \beta x y - \gamma y$$$\gamma$ : Predator mortality rate (1/time). $\delta$ : Conversion efficiency (how many new predators result from one consumed prey). Note that $\delta \beta$ is often grouped as a single parameter in the classic form. The equilibrium populations, where both rates are zero, are $x_e = \gamma / \delta \beta$ and $y_e = \alpha / \beta$.
Fisheries Management: The model is used to understand the dynamics of commercially fished species (prey) and their predators. For instance, overfishing cod can cause an explosion in their prey, like shrimp, destabilizing the entire North Atlantic ecosystem. Managers simulate different harvest rates to find sustainable yields.
Pest Control & Agriculture: Introducing a natural predator (like ladybugs for aphids) is a classic biocontrol strategy. The Lotka-Volterra model helps predict whether the introduced predator will establish a stable balance with the pest or cause harmful population crashes and resurgences.
Epidemiology: The same mathematical structure models the spread of diseases, where "prey" are susceptible individuals and "predators" are infected individuals. The contact rate ($\beta$) and recovery/death rate ($\gamma$) are key parameters in basic SIR models, crucial for predicting epidemic waves.
Chemical Kinetics & CAE: In chemical engineering, these equations describe autocatalytic reactions where one species promotes the production of another. The numerical methods (like Runge-Kutta) used to solve these ODEs in our simulator are identical to those in CAE software for simulating structural vibrations, heat transfer, or fluid flow over time.
When you start using this simulator, there are a few points you should be aware of. First, keep in mind that "the parameters are not the actual real-world values themselves". For example, setting the growth rate α=0.1 does not necessarily mean "a 10% increase per day". Since the simulation implicitly decides the unit of time (day, month, year), the relative magnitude is what's important. When applying this in practice, you'll need a separate process of identifying parameters by back-calculating from field data.
Next, you should experience firsthand how the results change significantly based on the initial values. In the basic model, slightly shifting from the equilibrium point yields beautiful periodic solutions. However, if you set the rabbits to 0, for instance, the foxes go extinct and no oscillation occurs. This represents the obvious yet crucial principle that "predators cannot survive without prey". Conversely, in the model with the logistic term, setting the environmental carrying capacity K to an extremely small value (e.g., smaller than the initial population) causes the prey population itself to decline rapidly before any oscillation can occur. When adjusting parameters, get into the habit of changing them one at a time and observing the results while considering their physical meaning.
Finally, note that this model does not account for "stochastic events". In real ecosystems, chance events like disease, abnormal weather, and the randomness of individual encounters have a major impact. This simulator uses a deterministic model, so the same parameters and initial values will always reproduce the same results. This is excellent for learning the basics, but to handle real-world uncertainty, more advanced models like "stochastic differential equations" are required.
Lynx-hare system with alpha=0.6/year (hare growth), beta=0.015 (lynx predation efficiency), gamma=0.8/year (lynx mortality), delta=0.08 (biomass conversion). Simulation shows hare equilibrium xₑ≈53 individuals and lynx yₑ≈8, with hare populations peaking at 180 before predator lag causes collapse to 15, while lynx peak follows 6–8 months later at 22 individuals. Phase portrait traces counterclockwise ellipse, confirming classic 2–3 year cycle observed in Hudson Bay fur trade records (1821–1940).