|  |  | Test | |||
---|---|---|---|---|---|---|
Constraint | -ln L | Difference | AU | SH | WKH | WSH |
Tetanocera feeding group analysis (59-taxon data set) | ||||||
Unconstrained | −38932.126 | (Best) |  |  |  |  |
Aquatic snail predators1* | −39212.682 | 280.556 | p = 4e-06 | p < 1e-100 | p < 1e-100 | p < 1e-100 |
Aquatic snail predators2* | −39252.447 | 320.321 | p = 2e-41 | p < 1e-100 | p < 1e-100 | p < 1e-100 |
Shoreline snail predators1 | −38971.538 | 39.412 | p = 0.001 | p = 0.002 | p = 0.002 | p = 0.002 |
Shoreline snail predators2* | −39004.527 | 72.401 | p = 1e-07 | p = 0.005 | p < 1e-100 | p = 4e-05 |
Slug parasitoids | −38941.015 | 8.889 | p = 0.038 | p = 0.631 | p = 0.062 | p = 0.193 |
Terrestrial snail predators* | −39051.229 | 119.103 | p = 1e-08 | p < 1e-100 | p < 1e-100 | p < 1e-100 |
Renocerinae monophyly analysis (entire 115-taxon data set) | ||||||
Unconstrained | −73022.049 | (Best) |  |  |  |  |
Renocerinae | −73056.937 | 34.89 | p = 0.055 | p = 0.059 | p = 0.059 | p = 0.059 |
Comparison of Bayes MAP (Figure 1) and best ML (Additional file 1: Figure S1) trees (entire data set) | ||||||
ML tree | −72999.441 | (Best) |  |  |  |  |
Bayes MAP tree | −73005.315 | 5.875 | p = 0.377 | p = 0.388 | p = 0.388 | p = 0.388 |