Literature DB >> 28311564

Fluctuations of density and survival of carabid populations.

P J den Boer1.   

Abstract

Standardized and all-year pitfall-sampling during a number of years gives reliable estimates of the yearly changes in size (year-catches) of the local breeding populations (interaction groups) of carabid species. From sampling runs at 89 sites, 2,893 estimates of coefficients of net reproduction (R) of 64 carabid species were obtained. The R-values of all species appeared to be lognormally distributed (LND). For each species realistic fluctuations of density could thus be simulated after estimation of mean and standard deviation of the fitted LND (Appendix). Simulation results were compared with field data in two ways: 1. The range between highest and lowest density (logarithmic range: LR), only for those sampling runs of 4-12 years that are not interrupted by zero year-catches. These LR-values were compared with those from simulated runs at similar catch-levels (n), i.e. runs with the highest catch between 1/2·3 n and 1/2·3 n+1, if n=1, 2,..., 7. As the number of uninterrupted (by zero year-catches) time series of catches decreases at lower catch-levels, by which the distribution of LR-values becomes skewed, each sampling run from the field could only be compared with simulations at the same catch-level. It thus appeared, that in the field density usually fluctuated within wider ranges than could be expected from the concerning simulations (where density fluctuated according to R-values drawn at random from the fitted LND). This means, that in the field the succession of R-values generally is less favourable than at random. This was especially evident for species with high powers of dispersal (T-species; glossary). In species with low powers of dispersal (L-species) the density range (LR) of field populations only at higher catch-levels agreed well with the expected values from the simulations. 2. The number of zero year-catches in sampling runs of 4-12 years taking into account the catch-level. In the field very low densities as a cause of zero year-catches cannot be distinguished from extinction and/or (re) founding (turnover). In the simulations the density level (start density) can be chosen such that only very low densities can still be a cause of zero year-catches (pseudo-turnover), the chance of which is higher the lower the catch-level. Correcting the field data for pseudo-turnover for each species gives estimates of the actual turnover. Local populations of carabid species thus appear to survive for only restricted periods, in T-species around 10 years, in L-species around 40 years. This fits in well with previous findings on differences in the Distribution of Population Sizes (DPS; glossary) between species (Den Boer 1977). The survival times of local populations are not so much determined by the instability of the habitat, but more by the instability of the populations themselves. The low survival times of local populations of T-species seem directly to result from the high level of dispersal.

Entities:  

Year:  1985        PMID: 28311564     DOI: 10.1007/BF00384936

Source DB:  PubMed          Journal:  Oecologia        ISSN: 0029-8549            Impact factor:   3.225


  4 in total

1.  EXPLICIT ESTIMATES FROM CAPTURE-RECAPTURE DATA WITH BOTH DEATH AND IMMIGRATION-STOCHASTIC MODEL.

Authors:  G M JOLLY
Journal:  Biometrika       Date:  1965-06       Impact factor: 2.445

2.  On the survival of populations in a heterogeneous and variable environment.

Authors:  P J den Boer
Journal:  Oecologia       Date:  1981-08       Impact factor: 3.225

3.  Simulation experiments illustrating stabilization of animal numbers by spreading of risk.

Authors:  Joannes Reddingius; P J den Boer
Journal:  Oecologia       Date:  1970-09       Impact factor: 3.225

4.  Catches in pitfall traps in relation to mean densities of carabid beetles.

Authors:  M A Baars
Journal:  Oecologia       Date:  1979-07       Impact factor: 3.225

  4 in total
  10 in total

1.  On the stabilizing effect of density-dependent mortality factors.

Authors:  H J Pocthke; M Kirchberg
Journal:  Oecologia       Date:  1987-11       Impact factor: 3.225

2.  Density dependence and the stabilization of animal numbers : 1. The winter moth.

Authors:  P J den Boer
Journal:  Oecologia       Date:  1986-07       Impact factor: 3.225

3.  On the stabilization of animal numbers. Problems of testing : 3. What do we conclude from significant test results?

Authors:  P J Den Boer
Journal:  Oecologia       Date:  1990-05       Impact factor: 3.225

4.  Geographic patterns in the flight ability of a monophagous beetle.

Authors:  Mark A Davis
Journal:  Oecologia       Date:  1986-06       Impact factor: 3.225

5.  Density dependence and the stabilization of animal numbers : 3. The winter moth reconsidered.

Authors:  P J den Boer
Journal:  Oecologia       Date:  1988-03       Impact factor: 3.225

6.  Seeing the trees for the wood: random walks or bounded fluctuations of population size?

Authors:  P J den Boer
Journal:  Oecologia       Date:  1991-05       Impact factor: 3.225

7.  Long-distance dispersal by a parasitoid (Anagrus delicatus, Mymaridae) and its host.

Authors:  M F Antolin; D R Strong
Journal:  Oecologia       Date:  1987-09       Impact factor: 3.225

8.  Possibilities for flight in the carabid beetle Nebria brevicollis (F.) : The importance of food during larval growth.

Authors:  M N E Nelemans
Journal:  Oecologia       Date:  1987-07       Impact factor: 3.225

9.  Social organization of the bank vole (Clethrionomys glareolus, Schreber 1780) and its demographic consequences: a model.

Authors:  G Bujalska; L Grüm
Journal:  Oecologia       Date:  2013-03-13       Impact factor: 3.225

10.  Species traits modify the species-area relationship in ground-beetle (Coleoptera: Carabidae) assemblages on islands in a boreal lake.

Authors:  Aaron J Bell; Iain D Phillips; Scott E Nielsen; John R Spence
Journal:  PLoS One       Date:  2017-12-20       Impact factor: 3.240

  10 in total

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