|
| Species |
|
Seeds
of the same species |
|
Seeds
of congeneric species |
|
Seeds
of species that are assumed to share common predators |
| |
r |
n |
P |
|
r |
n |
P |
|
r |
n |
P |
|
| Acer mono |
|
-0.25 |
9 |
0.508 |
|
|
-0.25 |
9 |
0.519 |
|
-0.30 |
7 |
0.519 |
|
|
|
|
|
| Acer amoenum |
|
-0.68 |
7 |
0.090 |
|
| Carpinus cordata |
|
-0.98 |
6 |
0.001*** |
|
|
-0.98 |
6 |
0.001** |
-0.96 |
5 |
0.009* |
| -0.98 |
6 |
0.001** |
|
-0.77 |
6 |
0.071 |
|
|
|
-0.97 |
6 |
0.001** |
|
-0.96 |
5 |
0.009* |
|
-0.94 |
6 |
0.006* |
|
-0.87 |
6 |
0.026 |
|
-0.90 |
7 |
0.006* |
|
| Carpinus japonica |
|
-0.99 |
5 |
0.011* |
|
|
| Carpinus laxiflora |
|
-0.99 |
6 |
0.0003*** |
|
|
| Carpinus tschonoskii |
|
-0.76 |
6 |
0.079 |
|
|
| Ostrya japonica |
|
-0.85 |
7 |
0.016* |
|
|
|
|
|
| Swida controversa |
|
-0.99 |
6 |
0.0003*** |
| Styrax obassia |
|
-0.29 |
6 |
0.581 |
| Fagus crenata |
|
-0.84 |
5 |
0.074 |
|
|
-0.86 |
5 |
0.066 |
| -0.89 |
6 |
0.016* |
|
| Fagus japonica |
|
-0.93 |
6 |
0.007** |
|
| Quercus crispula |
|
-0.39 |
7 |
0.392 |
|
|
-0.80 |
7 |
0.029 |
| -0.85 |
9 |
0.004** |
|
|
|
-0.80 |
7 |
0.030 |
| -0.84 |
9 |
0.004* |
| -0.30 |
6 |
0.565 |
|
| Quercus serrata |
|
-0.85 |
9 |
0.004** |
|
| Castanea crenata |
|
-0.69 |
6 |
0.126 |
|
|
|
|
|
|
Notes:
The results of correlation between the sum of the number of sound and holed
seeds (log transformed) and the percentage of insect predation are shown. We
tested three types of the number of seeds: seeds of the same species (left);
seeds of congeneric species are combined (center); seeds of species that are
assumed to share common seed predators are combined (right). When species are
correlated by the same seed production value, those are enclosed with a square,
and Bonferroni correction is carried out in each square. Correlation whose family-wise
significant probability level is kept under 0.05, 0.01, and 0.001 is shown by
*, **, and *** for each.