A scanned copy of a photograph of the garden of Di Madgin's former home in the Red Zone, taken before the earthquakes. She describes the scene in the photograph as, "This is the courtyard that we made, to have an eating place at the back of the house. The tree in the neighbours' was a tree that Pete's brother stole on a school trip up in the mountains from a national park. They planted this red beech in the garden. It became the neighbourhood bird tree and the sound was fantastic in the evenings."
Tree mortality is a fundamental process governing forest dynamics, but understanding tree mortality patterns is challenging
because large, long-term datasets are required. Describing size-specific mortality patterns can be especially difficult, due to
few trees in larger size classes. We used permanent plot data from Nothofagus solandri var. cliffortioides (mountain beech)
forest on the eastern slopes of the Southern Alps, New Zealand, where the fates of trees on 250 plots of 0.04 ha were
followed, to examine: (1) patterns of size-specific mortality over three consecutive periods spanning 30 years, each
characterised by different disturbance, and (2) the strength and direction of neighbourhood crowding effects on sizespecific
mortality rates. We found that the size-specific mortality function was U-shaped over the 30-year period as well as
within two shorter periods characterised by small-scale pinhole beetle and windthrow disturbance. During a third period,
characterised by earthquake disturbance, tree mortality was less size dependent. Small trees (,20 cm in diameter) were
more likely to die, in all three periods, if surrounded by a high basal area of larger neighbours, suggesting that sizeasymmetric
competition for light was a major cause of mortality. In contrast, large trees ($20 cm in diameter) were more
likely to die in the first period if they had few neighbours, indicating that positive crowding effects were sometimes
important for survival of large trees. Overall our results suggest that temporal variability in size-specific mortality patterns,
and positive interactions between large trees, may sometimes need to be incorporated into models of forest dynamics.
