estimate lambda
project future growth, e.g., Nt = N0 (lambda)t
follow cohort through time or approximate with time-specific techniques
calculate the population's rate of change (~ r, Ro, lambda)
rate of change x population size = future population size
Nt = N0 (lambda)t
Nt = r Nt-1 or Nt = No ert
assumptions?
Age-specific vital rates x data on population size and structure
based on the multiplication of 2 matrices: Leslie Matrix × Population Vector
Contains age-specific fecundity and survival rates.
where Fx = age-specific fecundity x survivalSx = age-specific survival rate
The equation for Fx depends on where sampling occurs relative to the breeding season:
Pre-birth pulse sampling (young-of-year not present): Fx = S0 mx
Post-birth pulse sampling: Fx = Sx mx+1
Birth-flow fertility: more complicated situation (we will not discuss)
Fx is used to calculate the number of recruits (young) in the next generation
Contains the number of individuals in the population in each age class (or stage) at time t
For 3 age classes (females only):
n1 = A x no and N1 = sum of ni's in population vector n1
n2 = A x n1 and N2 = sum of ni's in population vector n2
nt+1 = A x nt and Nt = sum of ni's in population vector nt
theoretically: nt = At x n0 and lambda = Nt+1 / Nt
Remember that Fx = Sx mx+1 in post-birth pulse sampling.
Age-specific vital rates for female component of population:
x | nx | Sx | mx | Fx |
0 | 20 | 0.5 | 0 | 0.5 x 1 = 0.5 |
1 | 10 | 0.8 | 1 | . |
2 | 40 | 0.5 | 3 | . |
3 | 30 | 0.0 | 2 | 0.0 |
N0 = | 100 | --- | --- | ---- |
mx = average female offspring per female of a given age in the population
Leslie matrix (A):
Population vector (nt=0 ):
where 20 = young-of-year, 10 = one-yr olds, ...
n1 = Leslie matrix (A) x population vector (n0 )
nt=1 = x
nt=1 = =
Calculate population size and finite rate of change
N1 = 74 + 10 + 8 + 20 = 112
Lambda = Nt+1 / Nt = 112 / 100 = 1.12
Projecting population growth of both female and male segments of the population
We can make similar projections using both female and male components of the population if we have age-specific data for both sexes. The Leslie matrix becomes slightly more complicated when you include males (i.e., it incorporates sex-specific survival as well as information on sex ratio at birth).
Alternatively, we can double the population projection for females to estimate total population size (females + males). The later estimate is valid only if we assume a 50:50 sex ratio at birth and equal age-specific survival for females and males.
It is appropriate to classify individuals by age, i.e., properties other than age, such as size or developmental stage, are irrelevant to an individual's demographic fate.
The discrete nature of the model discards all information on age dependency of vital rates within age classes.
Fertility and survival rates remain constant, i.e., the environment is constant and density effects are unimportant. Note: stochastic Leslie models are possible -- we will use a stochastic-based Leslie model in a few weeks.
Most demographic models are based on one sex, usually the female. The implicit assumption is that life cycles of the sexes are identical or the dynamics of the population are determined by one sex independent of the relative abundance of the other (e.g., there will always be enough males to fertilize the females).
Stable-age distribution is not required for valid population projections.
Can conduct sensitivity analysis to see how changing certain age-specific vital rates affects population size and age structure.
Can incorporate density-dependence, i.e., can dampen values in the matrix to account for density-dependent factors limiting population growth.
Can derive useful mathematical properties from the matrix formulas, including stable-age distribution and finite rate of population change (i.e., lambda).
Requires a large amount of data (i.e., age-specific data on survival, fecundity, and population structure).
In practice, the estimation of Fx is difficult at best (Taylor and Carley 1988).
Program LESLIE - instructions will be given in lab.
Kareiva et al (2000), used Leslie matrices in an innovative way to evaluate whether eliminating downstream mortality of smolts passing down the Snake and Columbia Rivers as well as eliminating upstream mortality of spawners would lead to recovery of these populations. You can download a PowerPoint presentation on this paper by clicking on the title above which is a link to the PowerPoint file.
Begon M., and M. Mortimer. 1986. Population ecology: A unified study of animals and plants. Blackwell Scientific Publ., Boston. 220pp.
Caswell, H. 1989. Matrix population models. Sinauer Assoc., Inc., Sunderland, Mass. 328pp.
Elseth, G. D., and K. D. Baumgardner. 1981. Population biology. D. Van Nostrand Co., New York. 623pp.
Kareiva, P., M. Marvier and M. McClure. 2000. Recovery and management options for Spring/SummerChinook Salmon in the Columbia River Basin. Science 290:977-979.
Krebs, C. J. 1972. Ecology: The experimental analysis of distribution and abundance. Harper & Row, Publ., New York. 694pp.
Ricklefs, R. E. 1979. Ecology, second edition. Chiron Press, New York. 966pp.
Taylor, M. and J. S. Carley. 1988. Life table analysis of age structured populations in seasonal environments. J. Wildl. Manage. 52:366-373.
Revised: 19 August 2002