den Boer P J
Biological Station of Agricultural, University Wageningen, Kampsweg 27, NL-9418 PD, Wijster (Drenthe), The Netherlands.
Oecologia. 1985 Oct;67(3):322-330. doi: 10.1007/BF00384936.
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 and 1/2·3 , 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.
多年来进行标准化的全年陷阱采样,可以可靠地估计步甲物种当地繁殖种群(相互作用群体)的年数量变化(年捕获量)。通过在89个地点的采样,获得了64种步甲物种净繁殖系数(R)的2893个估计值。所有物种的R值似乎呈对数正态分布(LND)。因此,在估计拟合LND的均值和标准差后,可以模拟每个物种密度的实际波动情况(附录)。模拟结果与实地数据通过两种方式进行比较:1. 最高密度和最低密度之间的范围(对数范围:LR),仅针对那些4至12年的采样,且这些采样没有被零年捕获量打断。将这些LR值与类似捕获水平(n)下模拟运行的LR值进行比较,即如果n = 1、2、...、7,捕获量最高在1/2·3和1/2·3之间的运行。由于在较低捕获水平下,未被零年捕获量打断的捕获时间序列数量减少,导致LR值的分布变得偏斜,因此实地的每个采样只能与相同捕获水平下的模拟进行比较。结果表明,实地的密度波动范围通常比相应模拟预期的要宽(在模拟中,密度根据从拟合LND中随机抽取的R值波动)。这意味着,实地R值的序列总体上不如随机情况有利。这在具有高扩散能力的物种(T物种;术语表)中尤为明显。在扩散能力低的物种(L物种)中,只有在较高捕获水平下,实地种群的密度范围(LR)才与模拟的预期值吻合良好。2. 考虑捕获水平的4至12年采样中零年捕获量的数量。在实地,作为零年捕获量原因的极低密度无法与灭绝和/或(重新)建立(周转)区分开来。在模拟中,可以选择密度水平(起始密度),使得只有极低密度仍可能是零年捕获量的原因(伪周转),捕获水平越低,这种情况的可能性越高。对每个物种的实地数据进行伪周转校正后,可以得到实际周转的估计值。步甲物种的当地种群似乎只能在有限的时期内存活,T物种约为10年,L物种约为40年。这与之前关于物种间种群大小分布差异(DPS;术语表)的研究结果非常吻合。当地种群的存活时间与其说是由栖息地的不稳定性决定的,不如说是由种群自身的不稳定性决定的。T物种当地种群的低存活时间似乎直接源于其高水平的扩散。