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Buffer zones for biodiversity of plants and arthropods: is there a compromise on width?
Appendix F: Statistical models
A number of different models have been applied and a list of these is given in the following table:
|
|
|
No |
Type of data |
Where used |
1 |
Continuous
normally
distributed
measurements |
|
2 |
Shannons index and species for transect data
Shannons index and species from pitfalls
Shannons index and species from sweep nets |
3 |
Bird feed from sweep nets |
4 |
Bird feed in hedgerow |
5 |
Shannons index for plants |
6 |
Counts |
Plants in hedge |
7 |
Counts |
Arthropods in hedgerow |
8 |
Counts |
Plants in field |
8a* |
Counts |
Arthropods in pitfalls
Arthropods from sweep nets |
9 |
Relative counts |
Percentage of flowering plants |
10 |
Counts |
Arthropods in transects |
11 |
Counts |
Arthropods in transects |
12 |
Counts |
Plants in field |
13 |
Continuous
normally
distributed
measurements |
Accumulated number of plant species
Accumulated number of bugs in transects
Accumulated number of ground beetles in pitfalls
Accumulated number of butterflies in transects
Percent flowering plants in hedge-bottom |
14 |
Shannons index and species for plants |
15 |
Accumulated number of species |
16 |
Counts |
Relation between number of species of arthropods and plants |
*) The model does not include residual effect as the data are aggregated within each plot
Many of the analyses were carried out for different groups, such as sampling period, Type/class, order, family and specie. However, in order to be able to trust the analyses groups with very sparse occurrence were not analysed. Generally it was required that at least one plant/arthropod should be present in at least 25% of the replicates (when including each replicate in the analyses) or that at least one plant/arthropod should be present in at least 50% of the plots (when using sum of replicates in the analyses). In addition a few groups that fulfilled those requirements were left out because the occurrence of the plants/arthropods made it impossible to do the analyses properly.
All models were either linear mixed models, generalised linear mixed models or non-linear mixed model. The theory of linear mixed models and generalised linear mixed models may be found in books such as McCulloch and Searle (2001) and West et al. (2007). All statistical analyses were performed using the procedures MIXED, GLIMMIX and NLMIXED of SAS (SAS, 2008). Some of the data were visualised using the graphical procedures of SAS (SAS, 2009a and SAS, 2009b)
In all models it was assumed that the fields could be regarded blocks in the same experiment. Therefore analyses that included effects of both buffer width and distance to hedge were analyses at split-block design. Each combination of buffer width and distance from hedge is in the following called a plot.
In all analyses the denummerator degree of freedom were calculated using an extension of the Satterthwaites principle as described by Kenward and Roger (1997).
Pair wise comparisons of buffer widths and distances from hedge were carried out using the method of Tukey and Kramer, which were set up to control the comparison wise error rate at each level of buffer width when comparing distances from hedge and the comparison wise error rate at each level of distance from hedge when comparing buffer width. The method is based on the distribution of Studentized range (for more details see e.g. Miller, 1981).
Click here to see: Model 1
Click here to see: Model 2
Click here to see: Model 3
Click here to see: Model 4
Click here to see: Model 5
Click here to see: Model 6
Click here to see: Model 7
Click here to see: Model 8
Click here to see: Model 8a
Click here to see: Model 9
Click here to see: Model 10
Click here to see: Model 11
Click here to see: Model 12
Click here to see: Model 13
Click here to see: Model 14
Click here to see: Model 15
Click here to see: Model 16
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Version 1.0 November 2009, © Danish Environmental Protection Agency
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