Lessons from four decades of monitoring vegetation and fire: maintaining diversity and resilience in Florida’s uplands

Abstract

Worldwide, humans are altering the fire regimes (fire-return intervals, severity, seasonality) of fire-prone ecosystems, fragmenting natural landscapes, and altering climates. Efforts to restore fire regimes in natural areas are usually guided by fire management plans (FMP) that rely on prescribed burning. Despite the common use of FMPs, limited efforts have gone to assessing vegetative and faunal responses. While some insights into responses to fire from short-term studies are available, there is less knowledge about FMP outcomes applied over multiple decades. Peninsular Florida hosts many fire-prone communities including globally threatened Florida scrub. We repeatedly sampled species composition and abundance during a 38-yr period at 11 upland stands including wet prairies, flatwoods, and Florida scrub (i.e., oak scrub, rosemary scrub, hickory scrub). A total of 22 fires impacted the stands with individual stands experiencing as few as 2 and up to 11 fires. There was no invasion of non-native plants following fires and stands showed remarkable ecological resilience with limited change in species composition and modest abundance shifts due to differential recovery rates. Importantly, ecological resilience was not eroded with repeated fire. Species richness, evenness, and diversity were significantly higher at the end vs. beginning of our study, suggesting that current fire regimes are within the range of those with which species evolved. While resprouting shrubs and trees persevered under a range of fire-return intervals, an obligate-seeding shrub was adversely impacted by fires more frequent than FMP-recommended intervals. Several lessons are apparent from our findings. Best practice should: use the full range of firereturn variation at evolutionarily appropriate intervals; utilize natural fire seasons to the extent possible; compare outcomes and modify prescriptions as necessary to meet FMP goals; give special consideration to burn units with embedded associations of widely differing fire regimes than principal associations in order to maintain diversity of both associations; and account for climate change in FMPs since fire behavior, frequency, and community responses to fire will likely change in the coming decades. Outcomes of FMPs must be carefully evaluated to ensure prescriptions are evolutionarily appropriate and to ameliorate the impacts of altered climates.

Territory and population attributes affect Florida scrub‐jay fecundity in fire‐adapted ecosystems

“…Once degraded by long periods without fire, scrub burns poorly under controlled conditions and requires mechanical cutting to prepare fuels; mechanical cutting is expensive and produces ecological effects different than fire by itself (Menges & Gordon, 2010 ; Schmalzer & Boyle, 1998 ). Restoration and maintenance of scrub produces heterogenous and uncertain responses because of annual rainfall, edge effects, fire history, and variability (Abrahamson et al, 2021 ; Breininger et al, 2018 ; Johnson et al, 2011 ). We use territory habitat quality state and not time‐since‐fire as a covariate because fires do not always kill all above‐ground oak stems and regrowth rates after fire are influenced by stored underground biomass and repeated fire frequency (Schmalzer & Foster, 2022 ).…”

What kills the virtually immortal palms of the Florida scrub?

“…The vegetation is described in Abrahamson et al (1984, 2021), Myers (1990), and Menges (1999); here we offer an overview. Plant names follow Wunderlin et al (2023).…”