Low tolerance of N ew C aledonian secondary forest species to savanna fires

Questions How do early secondary successional forest species that grow in savannas differ in their tolerance to surface fires? What are the consequences of these fire tolerances for savanna–forest dynamics and landscape management? Location Anthropogenic savannas in the N ew C aledonian biodiversity hotspot ( SW P acific). Methods We estimated the range of fire intensity in N ew C aledonian savannas using field survey of fuels and the B ehave P lus fire behaviour model. Within the predicted range of fire line intensity, we assessed theoretical fire injury to the cambium and crown for 11 species: the dominant tree of N ew C aledonian savannas ( M elaleuca quinquenervia ) and early secondary successional forest species. Using empirical models, for each species we estimated cambium damage from depth of necrosis (as a function of fire line intensity and fire residence time) and bark thickness, and crown damage from scorch height (as a function of fire line intensity) and tree height. We compared bark thickness and tree height increment patterns among species as well as species potential fire tolerance. Results The 11 species had very contrasting capacity to avoid fire injury to the bole cambium due to differences in bark investment patterns, but were all very exposed to scorching and crown injury. Overall, most of sampled individuals are likely top‐killed by low intensity fires (<1000 kW·m −1 ), which are frequent according to our simulations. Conclusions The early secondary successional forest species growing in N ew C aledonian savannas are poorly adapted to fire, in comparison with literature on worldwide trees in savannas. As a result, their juveniles are unlikely to reach adult size in fire‐prone areas. Restoration using the most fire‐tolerant species and fire prevention may be complementary strategies to manage such tropical landscapes in order to conserve biodiversity and ecosystem services.