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Population Growth – Chapter 11 Growth With Discrete Generations • Species with a single annual breeding season and a life span of one year (ex. annual plants). • Population growth can then be described by the following equation: Nt+1 = R0Nt • Where – Nt = population size of females at generation t – Nt+1 = population size of females at generation t + 1 – R0 = net reproductive rate, or number of female offspring produced per female generation • Population growth is very dependent on R0 Multiplication Rate (R0) Constant • If R0 > 1, the population increases geometrically without limit. If R0 < 1 then the population decreases to extinction. • The greater R0 is the faster the population Geometric Growth increases: Multiplication Rate (R0) Dependent on Population Size • Carrying Capacity – the maximum population size that a particular environment is able to maintain for a given period. – At population sizes greater than the carrying capacity, the population decreases – At population sizes less than the carrying capacity, the population increases – At population sizes = the carrying capacity, the population is stable • Equilibrium Point – the population density that = the carrying capacity. Net Reproductive rate (R0) as a function of population density: Y = mX + b Y = b – m(X) N = 100, then R0 = 1.0 population stable N > 100, then R0 < 1.0 population decreases Intercept N < 100, then R0 > 1.0 population increases Remember, at R0 = 1.0 birth rates = death rates • We can measure population size in terms of deviation from the equilibrium density: z = N – Neq Where: z = deviation from equilibrium density N = observed population size Neq = equilibrium population size (R0 = 1.0) • R0 = 1.0 – B(N – Neq) ( When N = Neq then R0 = 1.0) Where: R0 = net reproductive rate y-intercept (b) will always = 1.0; population is stable (-)B = slope of line (m; the B comes from a regression coefficient. With these equations: z = N – Neq R0 = 1.0 – B(N – Neq) We can substitute R0 in Nt+1 = R0Nt to get: Nt+1 = [1.0 – B(zt)]Nt How much the population will change (R0) Start with an initial population (Nt) of 10, a slope (B) = 0.009, and Neq = 100, and the population gradually reaches 100 and stays there. Nt+1 = [1.0 – B(z)]Nt 10.00 2 18.10 3 31.44 4 50.84 120 5 73.34 100 6 90.93 7 98.35 8 99.81 9 99.98 10 100.00 11 100.00 12 100.00 Population Size 1 The population reaches stabilization with a smooth approach. 80 60 40 20 0 1 2 3 4 5 6 7 Generation 8 9 10 11 12 10.00 2 26.20 3 61.00 4 103.82 5 96.68 6 102.46 7 97.92 8 101.58 9 98.69 10 101.02 11 99.17 12 100.65 13 99.47 14 100.42 15 99.66 16 100.27 17 99.78 18 100.17 19 99.86 20 100.11 Start with an initial population (Nt) of 10, a slope (B) = 0.018, and Neq = 100, and the population oscillates a little bit but eventually (64 generations) stabilizes at 100 and stays there. This is called convergent oscillation. Nt+1 = [1.0 – B(z)]Nt Population Size 1 120 100 80 60 40 20 0 1 3 5 7 9 11 13 Generation 15 17 19 10.00 2 32.50 3 87.34 4 114.98 5 71.92 6 122.41 7 53.84 8 115.97 9 69.67 10 122.50 11 53.60 12 115.78 13 70.11 14 122.50 15 53.59 16 115.77 17 70.12 18 122.50 19 53.59 20 115.77 Start with an initial population (Nt) of 10, a slope (B) = 0.025, and Neq = 100, and the population oscillates with a stable limit cycle that continues indefinitely. Nt+1 = [1.0 – B(z)]Nt 150 Population 1 100 50 0 1 3 5 7 9 11 13 Generation 15 17 19 10.00 2 36.10 3 103.00 4 94.05 5 110.29 6 77.39 7 128.13 8 23.59 9 75.87 10 128.96 11 20.64 12 68.14 13 131.10 14 12.87 15 45.40 16 117.28 17 58.51 18 128.91 19 20.84 20 68.68 Start with an initial population (Nt) of 10, a slope (B) = 0.029, and Neq = 100, and the population fluctuates chaotically. Nt+1 = [1.0 – B(z)]Nt 150 Population 1 100 50 0 1 3 5 7 9 11 13 Generation 15 17 19 B 0.009 0.018 Population Gradually approaches equilibrium Convergent oscillation 0.025 0.029 Stable limit cycles Chaotic fluctuation As the slope increases, the population fluctuates more. A high B causes an ‘overshoot’ towards stabilization. Remember: B is the slope of the line and represents how much Y changes for each change in X. • Define L as B(Neq): The response of the population at equilibrium – L between 0 and 1 Population approaches equilibrium without oscillations – L between 1and 2 Population undergoes convergent oscillations – L between 2 and 2.57 Population exhibits stable limit cycles – L above 2.57 Population fluctuates chaotically Growth With Overlapping Generations • Previous examples were for species that live for a year, reproduce then die. • For populations that have a continuous breeding season, or prolonged reproductive period, we can describe population growth more easily with differential equations. Multiplication Rate Constant • In a given population, suppose the probability of reproducing (b) is equal to the probability of dying (d). – r=b–d Nt rt – Then rN = (b – d)N = e N0 – Where: Nt = population at time t t = time r = per-capita rate of population growth b = instantaneous birth rate d = instantaneous death rate – Population grows geometrically Nt+1 = R0Nt We can determine how long it will take for a population to double: Nt rt = 2 = e N0 Loge(2) = rt Loge(2) / r = t; r = realized rate of population growth per capita For example: r t 0.01 69.3 0.02 34.7 0.03 23.1 0.04 17.3 0.05 13.9 0.06 11.6 Multiplication Rate Dependent on Population Size dN K-N = rN dt K Where: N = population size t = time r = intrinsic capacity for increase K = maximal value of N (‘carrying capacity’) K r Pop. Size (K-N/K) Growth Rate 1 1 99/100 0.99 1 25 25/100 6.25 1 50 50/100 25 1 75 25/100 18.75 1 95 5/100 4.75 1 99 1/100 0.99 1 100 0/100 0 Logistic population growth has been demonstrated in the lab. Year-to-year environmental fluctuations are one reason that population growth can not be described by the simple logistic equation. Time-Lag Models • Animals and plants do not respond immediately to environmental conditions. • Change our assumptions so that a population responds to t-1 population size, not the t population size. L=Bneq If 0<L<0.25, then stable equilibrium with no oscillation If 0.25<L<1.0, then convergent oscillation If L > 1.0, then stable limit cycles or divergent oscillation to extinction Ex. Daphnia Stochastic Models • Models discussed so far are deterministic: given certain conditions, each model predicts one exact condition. • However, biological systems are probabilistic: – what is the probability that a female will have a litter in the next unit of time? – What is the probability that a female will have a litter of three instead of four? • Natural population trends are the joint outcome of many individual probabilities • These probabilistic models are called stochastic models. Basic Nature of Stochastic Models • Nt+1 = R0Nt • If R0 = 2, then a population size of 6 will yield a population of 12 in one generation according to a deterministic model: Nt+1 = 2(6) = 12 • Suppose our stochastic model says that a female has an equal probability of having 1 or 3 offspring (average = 2; so R0 = 2): Probability One female offspring Three female offspring 0.5 0.5 • Since the number of offspring is random, we can flip a coin and heads = 1 offspring, tails = 3 offspring to determine the total number of offspring produced: Outcome Parent Trial 1 Trial 2 Trial 3 Trial 4 1 (h)1 (t)3 (h)1 (t)3 2 (t)3 (h)1 (t)3 (h)1 3 (h)1 (t)3 (h)1 (h)1 4 (t)3 (t)3 (t)3 (t)3 5 (t)3 (t)3 (t)3 (h)1 6 (t)3 (t)3 (h)1 (h)1 14 16 12 10 Total population in next generation: Frequency Distribution After Several Trials • Although the most common population size is twelve as expected, the population could be any size from 6 to 18. Population Projection Matrices • Used to calculate population changes from agespecific (or stage specific) birth and survival rates. – Can estimate how population growth will respond to changes in only one specific age class. F = fecundity P = probability of surviving and moving to next age class F = fecundity Age Based P = probability of surviving and staying in same stage G = probability of moving to next stage Stage Based Stage-based life table and fecundity table for the loggerhead sea turtle. #’s assume a 3% population decline / year. Class Size Approx. Age 1 Eggs, hatchlings <10 <1 0.6747 0 2 Small Juv. 10.1 – 58.0 1-7 0.7857 0 3 Large Juv. 58.1 – 80.0 8-15 0.6758 0 4 Subadults 80.1 – 87.0 16-21 0.7425 0 5 Novice Breeders >87.0 22 0.8091 127 6 1st year remigrants >87.0 23 0.8091 4 7 Mature breeder >87.0 24-54 0.8091 80 Stage # Annual survivorship Fecundity (eggs/yr) Matrix Model P1 F2 F3 F4 F5 F6 F7 G1 P2 0 0 0 0 0 0 G2 P3 0 0 0 0 0 0 G3 P4 0 0 0 0 0 0 G4 P5 0 0 0 0 0 0 G5 P6 0 0 0 0 0 0 G6 P7 Pi = proportion of that stage that remains in that stage Gi = proportion of that stage that moves to the next stage Fi = specific fecundity for that stage Stage # Approx. Annual Fecundity Age survivorship (eggs/yr) 1 <1 0.6747 0 2 1-7 0.7857 0 3 8-15 0.6758 0 4 16-21 0.7425 0 5 22 0.8091 127 6 23 0.8091 4 7 24-54 0.8091 80 0.7370 = P2 0.0487 = G2 0.7857 = P2 + G2 1 2 3 4 5 6 7 0 0 0 0 127 4 80 0 0 0 0 0 0 0 0 0 0 0 0 0.6747 0.7370 0 0.0487 0.6610 0 0 0.0147 0.6907 0 0 0 0.0518 0 0 0 0 0 0 0 0.8091 0 0 0 0 0 0 0 0.8091 0.8089 = Stage # P1 F2 F3 F4 F5 F6 F7 N1 G1 P2 0 0 0 0 0 N2 0 G2 P3 0 0 0 0 N3 0 0 G3 P4 0 0 0 0 0 0 G4 P5 0 0 N5 0 0 0 0 G5 P6 0 N6 0 0 0 0 0 G6 P7 N7 X N4 = N1 = (P1*N1) + (F2*N2) + (F3*N3) + (F4*N4) + (F5*N5) + (F6*N6) + (F7*N7) N2 = (G1*N1) + (P2*N2) + (0*N3) + (0*N4) + (0*N5) + (0*N6) + (0*N7) N3 = (0*N1) + (G2*N2) + (P3*N3) + (0*N4) + (0*N5) + (0*N6) + (0*N7) N4 = (0*N1) + (0*N2) + (G3*N3) + (P4*N4) + (0*N5) + (0*N6) + (0*N7) N5 = (0*N1) + (0*N2) + (0*N3) + (G4*N4) + (P5*N5) + (0*N6) + (0*N7) N6 = (0*N1) + (0*N2) + (0*N3) + (0*N4) + (G5*N5) + (P6*N6) + (0*N7) N7 = (0*N1) + (0*N2) + (0*N3) + (0*N4) + (0*N5) + (G6*N6) + (P7*N7) • With matrix models, we can simulate an increase or decrease in survival or fecundity and then determine what effect that will have on population growth. • So what? Well, we can determine what age class or stage is most important to population growth for an endangered species. By either increasing fecundity by 50% or survival to 100%, we can see that large juvenile survival is most important to population growth, so put your management efforts towards protecting large juveniles.