This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. Fire in Southwestern Riparian Habitats: Functional and Community Responses D.E. Busch 1 FIRE OCCURRENCE There was little difference between the structural classification of burned vegetation and the genernl population of riparian vegetation that had not burned. Comparisons of burned areas within each dominance type indicated that significantly less cottonwood/willow (Populus fremontii/Salix gooddingii) and mesquite (Prosopis glandulosa and P. pubescens) dominated habitat- burned than would be expected based on the representation of these taxa in the riparian community. Fires in habitats dominated by saltcedar (Tamarix ramosissima) appeared to be disproportionately latge, but this relationship was not statistically significant presumably due to the small subsample of stands that could be evaluated using GIS. Assuming that the period evaluated is representative, fire could be expected to burn approximately 25% of the riparian vegetation, and 40% of the saltcedar-dominated habitat, each decade. This implies a distmbance interval shorter than that from fire in most forest associations, and one that is insufficient for full maturation of historically dominant cottonwood, willow, and mesquite. It appears that shrubby species that are less valuable from a wildlife habitat standpoint may benefit from riparian zone fires. Hydrogeological perturbations and exotic species introductions are among the factors indirectly contributing to shifts in riparian ecosystem processes. Among these altered processes is the incidence of :Qre, which appears to occur at greatly elevated frequencies in pertw:bed low-elevation riparian ecosystems and may be a novel fonn of disturbance in these systems. - Between 1981 and 1992, 166 fires burned 11,846 ha (27%) of the riparian vegetation in the lower Colorado and Bill Williams River floodplains (Fig. 1). The area burned annually and fire frequency were correlated between 1981 and 1988 (r = 0.85, P < 0.01). 40 3000 --AREA 2500 -----__ • NUMBER 30 cu 2000 .c: - <C ~ 1500 <C w a:: u: FUNCTIONAL RESPONSES a:: 20 w m :E => Z W a:: u: 1000 10 500 o 1980 1982 1984 1986 1988 1990 1992 YEAR Figure 1. - Area and number of fires occurring between 1981 and 1991 in the lower Colorado and Bill Williams River riparian zones. 1Bureau of Reclamation, Division of Environment, Boulder City, Nevada, USA. 304 There is evidence for mechanisms which would facilitate increased community dominance of saltcedar and arrowweed (Tessaria sericea) following riparian zone fires. Rapid recovery in these taxa appears to be attributable to salinity tolerance and to mechanisms pennitting efficient water uptake and use (Busch and Smith 1993). Soil elemental analyses indicated that concentrations of nearly all soil constituents increased following fire. This contributed to a potential nutrient abundance, but also was a manifestation of elevated alluvium salinity. Boron was elevated in riparian soils following fire and lower leaf tissue concentrations suggest that saltcedar may derive tolerance to this element by an effective elimination mechanism. Based on leaf sodium concentrations, a dichotomy between halophytic (saltcedar and arrowweed) and glycophytic (cottonwood and willow) taxa was detectable, but no clear fire-related differences were apparent. There was little interspecific variation in leaf nitrogen concentration, but burned arrowweed had elevated concentrations of this element. This may contribute to the higher water use efficiency following fire that was observed in recovering burned arrowweed relative to unburned controls. Higher leaf stomatal conductance in all taxa and in both ecosystems was an indication of vigorous post-fIre recovety. This may, in part, be attributable to increased rndiation loads associated with the reduction of plant canopy cover following fire. However, decreases in water potential accompanying an increased transpiration load may signify water stress as a result of fire injury or inefficient recovery. Examination of trnnspiration-water potential regression parameters provided evidence for reduced post-fire hydraulic efficiency in burned Colorado River willows. saltcedar. Marked increases in arrowweed abundance accompanied cottonwood declines in the cottonwood/willow dominance type. Willow maintained its importance in burned cottonwoodlwillow vegetation, but did not become established in other dominance types in the manner of arrowweed. Similarly, mesquite and other shrubs were present in burned riparian stands, but did not dominate even those areas that were classified as mesquite-<iominated prior to fire. As was expected of plants that recover from fIre via resprouting, multiple linear regression analysis of burned riparian comnmnity ordination data revealed that the species that were dominant prior I to burning were strongly associated with post-fire community composition. Subtle evidence of a successional trend was shown by the positive relationship of community structure with fire year, and the tendency of younger tree demographic classes and ruderal taxa to be found near the opposite extremes of Detrended Correspondence Analysis axis 3 from older demographic classes and slower growing species. COMMUNITY RESPONSES In agreement with functional, analyses of fIre recovety efficiency, the community importance of saltcedar and arrowweed was high following fire in all pre-fire dominance types. Fire also appears to contribute to the catastrophic declines in cottonwood populations that are in evidence in pertUJbed desert riparian ecosystems. Relative cover and frequency of saltcedar was high in three burned riparian vegetation dominance types while arrowweed importance in burned riparian vegetation approached that of REFERENCE Busch, D.E. and S.D. Smith. 1993. Effects of fire on water and salinity relations of riparian woody taxa. Oecologia 94:186-194. 305