Abstract

The regeneration of alien and indigenous vegetation in various post-fire environments, following the extensive January 2000 wildfires on the Cape Peninsula, South Africa, is described. The effects of dry season wildfire burning of standing alien plants and stacks of mechanically cleared, alien plant material, on post-fire seed banks and vegetation recovery, are presented. These are compared to the effects of wildfire burning on adjacent stands of un-invaded Sandstone Fynbos (previously known as Mountain Fynbos) vegetation and to that on cleared areas surrounding wildfire burnt stacks. The effects of stacking and controlled burning of slash of cleared alien plant material on regeneration potential, under cool weather conditions, are also reported. Seed banks and regeneration were linked to pre-fire vegetation characteristics, fire intensity and, in particular, to the management of alien plants. Large volumes of either standing or stacked alien woody plant biomass impact negatively upon post-wildfire seed banks and upon the recruitment of indigenous fynbos vegetation. Heat damage, associated with stacks of woody alien biomass, kills all seeds to a soil depth of at least 0.15m. In contrast, the controlled winter burning of stacks of alien material results in large scale localised germination of alien seeds. Both persistent indigenous seed banks and the seed of alien invasive species are present in the burnt disturbed areas surrounding stacks of alien slash burnt in wildfires. It is concluded that the current practice of stacking slash resulting from the control of alien plants requires urgent review.

Highlights

  • In South Africa, the control of alien plant species poses ecosystem managers with their biggest problem in terms of manpower, money and time spent (Marais 1998)

  • Alien vegetation management in the greater Cape Peninsula National Park, a reserve situated in the South African fynbos shrublands, currently requires that felled alien vegetation be stacked, leaving the piles scattered through the landscape (Milton and Hall 1981, Holmes et al 1987, Macdonald et al 1989, Euston-Brown 2001)

  • In order to monitor regeneration patterns and to infer viable seed-bank and propagule sizes (Roberts 1981), adjacent field plots were selected in the Silvermine Valley, Cape Peninsula National Park, during February 2000

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Summary

Introduction

In South Africa, the control of alien plant species poses ecosystem managers with their biggest problem in terms of manpower, money and time spent (Marais 1998). It has been suggested that fires burn stacks at highly elevated temperatures, killing soil-stored indigenous and alien seeds. This results in the formation of so-called heat scars on the landscape (Richardson and Van Wilgen 1986, Breytenbach 1989, Macdonald et al 1989, Holmes et al 2000, Euston-Brown 2001)

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