Table 1.
Source | MGT |
FDS |
||||||
---|---|---|---|---|---|---|---|---|
d.f. | MS | F | P | d.f. | MS | F | P | |
Population | 5 | 97·57 | 9·76 | <0·01 | 5 | 0·27 | 8·83 | <0·01 |
TAS | 2 | 104·34 | 10·44 | <0·01 | 2 | 0·30 | 10·00 | <0·01 |
Population × TAS | 10 | 23·05 | 2·31 | 0·02 | 10 | 0·06 | 2·11 | 0·03 |
WA | 1 | 702·99 | 70·32 | <0·01 | 1 | 0·82 | 27·12 | <0·01 |
Population × WA | 5 | 9·53 | 0·95 | 0·45 | 5 | 0·02 | 0·56 | 0·73 |
WA × TAS | 2 | 5·08 | 0·51 | 0·60 | 2 | 0·01 | 0·31 | 0·73 |
Population × WA × TAS | 10 | 29·99 | 3·00 | 0·00 | 10 | 0·02 | 0·65 | 0·77 |
IL | 1 | 78·91 | 7·89 | 0·01 | 1 | 0·48 | 15·91 | 0·00 |
Population × IL | 5 | 0·47 | 0·05 | 1·00 | 5 | 0·08 | 2·61 | 0·03 |
WA × IL | 1 | 1·61 | 0·16 | 0·69 | 1 | 0·05 | 1·68 | 0·20 |
Population × WA × IL | 5 | 4·38 | 0·44 | 0·82 | 5 | 0·06 | 1·83 | 0·11 |
TAS × IL | 2 | 0·85 | 0·09 | 0·92 | 2 | 0·27 | 9·04 | 0·00 |
Population × TAS × IL | 10 | 10·03 | 1·00 | 0·45 | 10 | 0·07 | 2·27 | 0·02 |
WA × TAS × IL | 2 | 2·39 | 0·24 | 0·79 | 2 | 0·22 | 7·39 | 0·00 |
Population × WA × TAS × IL | 7 | 9·48 | 0·95 | 0·47 | 10 | 0·04 | 1·41 | 0·18 |
Seed weight | 1 | 0·23 | 0·02 | 0·88 | 1 | 0·00 | 0·05 | 0·83 |
Seed weight was included as a covariate to account for maternal effects. The overall model for each variable was statistically significant (MGT: d.f. = 69, MS = 38·68, F = 3·87, P = 0·01, R2 = 0·72; FDS: d.f. = 72, MS = 0·10, F = 3·36, P < 0·01, R2 = 0·72).
TAS, time of precipitation addition after summer treatment ended (three levels); WA, amount of water added at watering event (two levels); IL, inundation length following watering event (two levels).