Evaluation of Two Density Estimators of Small Mammal Population Size

1985 ◽  
Vol 66 (1) ◽  
pp. 13-21 ◽  
Author(s):  
K. R. Wilson ◽  
D. R. Anderson
2015 ◽  
Vol 42 (2) ◽  
pp. 108 ◽  
Author(s):  
S. Hein ◽  
J. Jacob

In this review we summarise published knowledge regarding small mammal population recovery following sudden population collapse, regardless as to whether the collapse is caused by natural or man-made events. We determine recovery mechanisms, recovery time and recovery rate, and suggest how to adapt and optimise current methods to regulate small mammal population size, for pest management and/or conservation. It is vital that the principles underlying the recovery mechanisms are known for both pest control and conservation to align management methods to either maintain animal numbers at a permanent minimum level or increase population size. Collapses can be caused naturally, as in the declining phase of multi-annual fluctuations and after natural disasters, or by man-made events, such as pesticide application. In general, there are three ways population recovery can occur: (1) in situ survival and multiplication of a small remaining fraction of the population; (2) immigration; or (3) a combination of the two. The recovery mechanism strongly depends on life history strategy, social behaviour and density-dependent processes in population dynamics of the species in question. In addition, the kind of disturbance, its intensity and spatial scale, as well as environmental circumstances (e.g. the presence and distance of refuge areas) have to be taken into account. Recovery time can vary from a couple of days to several years depending on the reproductive potential of the species and the type of disturbances, regardless of whether the collapse is man made or natural. Ultimately, most populations rebound to levels equal to numbers before the collapse. Based on current knowledge, case-by-case decisions seem appropriate for small-scale conservation. For pest control, a large-scale approach seems necessary. Further investigations are required to make sound, species-specific recommendations.


Ecology ◽  
1988 ◽  
Vol 69 (6) ◽  
pp. 1952-1959 ◽  
Author(s):  
George E. Menkens ◽  
Stanley H. Anderson

Ecology ◽  
1972 ◽  
Vol 53 (2) ◽  
pp. 310-313 ◽  
Author(s):  
James H. Brown ◽  
Gerald A. Lieberman ◽  
William F. Dengler

1998 ◽  
Vol 62 (4) ◽  
pp. 1196 ◽  
Author(s):  
Thomas P. Sullivan ◽  
Christopher Nowotny ◽  
R. A. Lautenschlager ◽  
Robert G. Wagner

2015 ◽  
Vol 75 (1) ◽  
pp. 208-215 ◽  
Author(s):  
JHF Mello ◽  
TP Moulton ◽  
DSL Raíces ◽  
HG Bergallo

We carried out a six-year study aimed at evaluating if and how a Brazilian Atlantic Forest small mammal community responded to the presence of the invasive exotic species Artocarpus heterophyllus, the jackfruit tree. In the surroundings of Vila Dois Rios, Ilha Grande, RJ, 18 grids were established, 10 where the jackfruit tree was present and eight were it was absent. Previous results indicated that the composition and abundance of this small mammal community were altered by the presence and density of A. heterophyllus. One observed effect was the increased population size of the spiny-rat Trinomys dimidiatus within the grids where the jackfruit trees were present. Therefore we decided to create a mathematical model for this species, based on the Verhulst-Pearl logistic equation. Our objectives were i) to calculate the carrying capacity K based on real data of the involved species and the environment; ii) propose and evaluate a mathematical model to estimate the population size of T. dimidiatus based on the monthly seed production of jackfruit tree, Artocarpus heterophyllus and iii) determinate the minimum jackfruit tree seed production to maintain at least two T. dimidiatus individuals in one study grid. Our results indicated that the predicted values by the model for the carrying capacity K were significantly correlated with real data. The best fit was found considering 20~35% energy transfer efficiency between trophic levels. Within the scope of assumed premises, our model showed itself to be an adequate simulator for Trinomys dimidiatus populations where the invasive jackfruit tree is present.


1950 ◽  
Vol 31 (1) ◽  
pp. 17 ◽  
Author(s):  
Glen C. Sanderson

2018 ◽  
Vol 99 (2) ◽  
pp. 478-485
Author(s):  
François Chiron ◽  
Susanne Hein ◽  
Rémi Chargé ◽  
Romain Julliard ◽  
Léo Martin ◽  
...  

1959 ◽  
Vol 40 (3) ◽  
pp. 425 ◽  
Author(s):  
Joseph LoBue ◽  
Rezneat M. Darnell

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