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5.3.3.2 Population models

Overview

Population models use differential equations to describe how the size of a group of living organisms changes over time. Typical questions include:

In this chapter, we focus on simple but important models: exponential growth/decay, logistic growth, and a brief look at interacting populations. The emphasis is on formulating the differential equation, interpreting its terms, and understanding the qualitative behavior of solutions, not on advanced solution techniques.

Throughout, we usually let:

Exponential Growth and Decay

Basic idea and differential equation

The simplest assumption is that the rate of change of the population is proportional to the population itself:

$$
\frac{dP}{dt} = k P(t),
$$

where $k$ is a constant:

Interpretation: each individual has the same average chance per unit time of producing new individuals (or dying), so more individuals means a larger total rate of change.

Solution form and interpretation

Solving $\dfrac{dP}{dt} = k P$ with initial condition $P(0) = P_0$ gives

$$
P(t) = P_0 e^{kt}.
$$

Key features:

A useful quantity is the doubling time (for $k > 0$):

Similarly, for decay ($k < 0$), one often uses the half-life $T_{1/2}$, defined by $P(T_{1/2}) = \frac12 P_0$:

$$
T_{1/2} = \frac{\ln 2}{|k|}.
$$

When exponential models are reasonable

Exponential models can approximate population behavior when:

They are usually good over short time spans or for small populations in a very rich environment, but they become unrealistic in the long term because no real population can grow forever without limits.

Logistic Growth

Motivation: limited resources

Real populations usually face:

These factors tend to slow down growth as the population becomes large. A simple way to model this is to assume that:

This leads to the logistic model.

Logistic differential equation

The logistic model is usually written as

$$
\frac{dP}{dt} = r P\left(1 - \frac{P}{K}\right),
$$

where:

Interpretations:

Equilibria and stability

Equilibria are constant solutions where $\frac{dP}{dt} = 0$.

For the logistic equation:

$$
\frac{dP}{dt} = r P\left(1 - \frac{P}{K}\right) = 0
$$

This happens if:

Thus there are two equilibrium populations: $P = 0$ and $P = K$.

To understand stability qualitatively:

So:

Solution form and graph shape (logistic curve)

Solving the logistic equation with initial condition $P(0)=P_0$ gives a solution of the form

$$
P(t) = \frac{K}{1 + A e^{-rt}},
$$

where $A$ is a constant determined by $P_0$:

$$
A = \frac{K - P_0}{P_0}.
$$

Important qualitative features:

Population biologists often fit this kind of curve to data, estimating $r$ and $K$ from observed population sizes over time.

Comparing Exponential and Logistic Models

Choosing between them:

Harvesting and Other Modifications

Real populations may be affected by external actions, such as harvesting (fishing, hunting, logging) or restocking. These effects can be added to basic models.

Constant harvesting in a logistic model

A common modification is to introduce a constant harvest rate $h$, so the logistic model becomes

$$
\frac{dP}{dt} = rP\left(1 - \frac{P}{K}\right) - h,
$$

where $h \ge 0$ represents the number of individuals removed per unit time.

Key features:

To find equilibria, solve

$$
rP\left(1 - \frac{P}{K}\right) - h = 0.
$$

This is a quadratic equation in $P$; depending on $h$, it can have:

This kind of analysis is important in resource management (e.g., sustainable fishing quotas).

Other possible terms

More complicated models might include:

In each case, the added terms modify the differential equation, and we analyze how they affect equilibria and long-term behavior.

Interacting Populations (Brief Overview)

Beyond single populations, differential equations are used to model interactions between species or groups. Two classic examples:

Predator–prey (Lotka–Volterra type)

Let:

A simple model might be

$$
\begin{aligned}
\frac{dx}{dt} &= ax - bxy, \\
\frac{dy}{dt} &= -cy + dxy,
\end{aligned}
$$

with positive constants $a,b,c,d$.

Interpretation (at a basic level):

This system can produce oscillations: prey numbers rise, then predators increase and reduce prey, leading predators to fall, and so on.

Competing species

If two species compete for the same resources, both populations may be modeled with logistic-type terms that also depend on the other species. For instance, one can add terms that reduce each species’ growth in proportion to the size of the other.

The precise form depends on the situation and empirical data, but the general idea remains: the rate of change depends on both the species’ own population and its interactions with others.

Using Population Models in Practice

In applications, the steps are usually:

  1. Model formulation
    • Choose variables (e.g., $P(t)$).
    • Decide which factors to include (growth rate, carrying capacity, harvesting, interactions).
    • Write a differential equation that reflects these assumptions.
  2. Parameter estimation
    • Use data (population counts over time, birth/death rates, etc.) to estimate parameters like $k$, $r$, $K$, $h$.
    • Often done with statistical or numerical methods.
  3. Analysis
    • Identify equilibria.
    • Determine stability (qualitative behavior near equilibria).
    • Study long-term trends (extinction, stabilization at carrying capacity, unbounded growth, oscillations).
  4. Interpretation
    • Use results to inform decisions (e.g., setting harvest quotas, conservation strategies).
    • Check whether model predictions match further data; if not, refine the model.

Population models are simplifications, but even the basic differential equations discussed here capture important qualitative behaviors: exponential explosion, saturation at a carrying capacity, possible extinction under heavy harvesting, and complex dynamics when multiple species interact.

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