| Literature DB >> 18047588 |
Abstract
I present a computational approach to calculate the population growth rate, its sensitivity to life-history parameters and associated statistics like the stable population distribution and the reproductive value for exponentially growing populations, in which individual life history is described as a continuous development through time. The method is generally applicable to analyse population growth and performance for a wide range of individual life-history models, including cases in which the population consists of different types of individuals or in which the environment is fluctuating periodically. It complements comparable methods developed for discrete-time dynamics modelled with matrix or integral projection models. The basic idea behind the method is to use Lotka's integral equation for the population growth rate and compute the integral occurring in that equation by integrating an ordinary differential equation, analogous to recently derived methods to compute steady-states of physiologically structured population models. I illustrate application of the method using a number of published life-history models.Entities:
Mesh:
Year: 2007 PMID: 18047588 PMCID: PMC2228373 DOI: 10.1111/j.1461-0248.2007.01121.x
Source DB: PubMed Journal: Ecol Lett ISSN: 1461-023X Impact factor: 9.492
Model equations, parameters with default value and interpretation, and population growth rate results for the Medfly example model (Carey 1993; Müller )
| Life-history equations | ||
|---|---|---|
| Fecundity: | if | |
| Mortality rate: | (20) | |
| β 0 | 47.0 day−1 | Maximum daily fecundity right after maturation |
| β 1 | 0.04 day−1 | Decay rate in fecundity with age |
| 11.0 day | Age at first reproduction | |
| μ 0 | 0.00095 day−1 | Daily mortality rate of newborn individuals |
| μ 1 | 0.0581 day−1 | Rate of increase of mortality with age |
| Population growth rate: | 0.41906 | (+4.0×10−5%) |
| Sensitivity to bgr 0: | 0.0016159 | (−9.3×10−4%) |
| Sensitivity to bgr 1: | −0.16460 | (+6.3×10−3%) |
| Sensitivity to | −0.031982 | (+7.6×10−4%) |
| Sensitivity to mgr 0: | −1.5264 | (+9.1×10−4%) |
| Sensitivity to mgr 1: | −0.011325 | (+7.6×10−4%) |
Percentages in parentheses represent the difference between the result computed with the integration method and the analytical values derived in Appendix 1.
Model variables, parameters with default value and interpretation, and equations describing the dynamic energy budget model, adapted from Klanjscek
| Variable | Dimension | Description | |
| Length3 | Volume of the structure compartment | ||
| Mass | Mass of damage-inducing compound | ||
| Probability/time | Hazard or mortality rate: probability of death per unit time | ||
| κ | – | 0.8 | Energy partitioning coefficient |
| κ | – | 0.001 | Fraction of reproduction energy realizedin a newborn |
| ν | Length/time | 0.075 m.year−1 | Energy conductance |
| Time−1 | 0.58 year−1 | Maintenance rate coefficient: cost ofmaintenance relative to cost of growth | |
| – | 1.286 | Energy investment ratio: cost of growthrelative to maximum available energyfor growth | |
| Length3 | 10−9 m3 | Structural volume at birth | |
| Length3 | 1.73 × 10−6 m3 | Structural volume at maturation | |
| [ | Energy/length3 | 0.7 | Maximum energy reserve density |
| Length/mass/time | Ageing acceleration – rate of increase of thehazard rate | ||
| – | Varied | Energy intake scaled to maximumenergy intake |
Value misprinted in original article (T. Klanjscek, personal communication).
The factor x converts a chosen measure for energy into Joules, which cancels out after parameterization (Fujiwara ; Klanjscek ).
Figure 1Population growth rate as a function of scaled food intake rate f for the dynamic energy budget model with continuous (solid line) and pulsed reproduction (dashed line).
Figure 2Left: Population growth rate of the Medfly life-history model when juveniles are exposed to strong, periodic pulses of mortality as a function of the period between these mortality pulses. Right: Pulses of mortality (thin dashed line), changes in population birth rate (top) and changes in relative density of juvenile (middle) and adult (bottom) medflies (all thick solid lines) in the exponentially growing population during the cycles of additional juvenile mortality. Period of mortality pulses: 15 days. All results were obtained assuming a peak juvenile mortality of khgr 0 = 20 day−1, which decays rapidly over time with a time constant of khgr 1 = 2 day−1, and a discretization of the phase in the environmental cycle into intervals with length Δ = 0.2 (halving or doubling the latter value does not noticeably change the results).