Three aspects of the paramo vegetation's response to fires were invest
igated: the measurement of fire temperatures, general observations of
changes in plant communities following fires, and monitoring the fate
of individual plants after burning. Fire temperatures were strongly in
fluenced by the physiognomy of the vegetation, dominated by tussocks o
f Calamagrostis spp. Temperatures were highest amongst the upper leave
s of the tussock (sometimes > 500 degrees C). The middle levels of the
tussock experienced temperatures in excess of 400 degrees C, but in t
he dense leaf bases temperatures were often below 65 degrees C. On the
ground between tussocks, temperatures were variable, whereas 2 cm bel
ow ground temperatures failed to reach 65 degrees C. Plant survival de
pended on the intensity of the fire and the plant's position within th
e tussock structure. Survival was often the result of high temperature
avoidance (with buds shielded by other plant parts or buried beneath
the soil surface). Post-fire Calamagrostis tiller mortality rates were
high and tussock regrowth was slow. Some other species appear to main
tain their populations by exploiting this recovery phase for seedling
establishment on tussocks. Between tussocks, changes of occupancy at t
he level of the individual plants were greater after fire than in cont
rol vegetation. Most transitions were random. Those which departed fro
m random often involved gaps and were related to post-fire mortality,
regrowth from below-ground parts, colonisation or, in the case of a cl
onal mat-forming species, to spatial rearrangement of rosettes. Recove
ry was slower at higher altitude. Recovery was much slower in burned p
lots when the upper 2 cm of soil was removed (along with buried plant
parts) compared with burned plots. Qualitative observations suggest th
at recovery may consist of a cyclical process, mediated by the serial
dominance of several species that are physiognomically important. The
frequency of fires determines the amount of fuel accumulated within gr
ass tussocks and some plants may be unable to survive repeated burning
. Chance survival of species in unburned patches of vegetation and ran
dom colonisation of gaps may be important determinants of subsequent c
ommunity structure.