This response in different eucalypt species is the result of adaptation to changes in their natural Australian habitat during millenia, and particularly to different degrees of natural selection pressure caused by relatively frequent forestry fire events. After the loss of their aerial part by fire, only the most vigorous coppicer specimens become dominant trees and, if free from further fire damage in the short term, are able to produce flowers, cross pollinate and produce seed for a next generation. They compete among themselves, with other quick growing surrounding vegetation and also, if reproductively mature before being charred, with a new cohort of seedlings rapidly growing on short-term fertile soils rich in nutrients from ash.


In Eucalyptus forestry plantations overseas those species, provenances and races introduced from areas where evolution favoured vigorous coppicers show a similar behaviour. Even if the aerial part is totally killed, some months later new regrowth shows up in Eucalyptus trees and proves casualty rate is relatively low. Other types of tree covers, especially conifers, are a total loss instead. Intact eucalypt root systems are able to hold denuded soil from the adverse effect of erosion, which in areas of noticeable slope is the major catastrophic risk after a fire.

But managed plantations are normally grown in short rotation cycles and at quite close spacings, so peak seed production is not yet achieved even if reproductive maturity is reached, and tree crowns are small. Only overgrown trees and extramature stands do release seed in sufficient amounts for a noticeable colonisation of bare soils after fires but in most cases where coppice is vigorous enough these are quickly dominated by the fastest growing survivors, able to use available resources more efficiently with their already formed root systems, the same that can offer the only noticeable protection to soil.

However even these hard to kill plants have limits. Repeated fire events affecting young regrowth can greatly diminish their resilience and the number of survivor stumps declines some months later. With ability to coppice more than a dozen times, species like E. globulus cannot be erradicated by fire. But their weakening can reduce their ability to retain soil considerably. Repeated fire events anihilate other quick colonising vegetation and destroy the fertile layers of top soil, impoverishing the diversity of a subsequent vegetation cover, in case all soil is not removed earlier along the natural drainage lines and makes restoration impossible.