Abstract
Fire-related cues may enhance seed recruitment in flammable ecosystems and differences in fire-germination responses of invasive vs. native species can drive the invasion process. We evaluated the effects of heat shock and smoke water solution treatment on seed germination of invasive (Melinis minutiflora, Urochloa decumbens, U. brizantha) and native grasses (Axonopus pressus, Aristida setifolia, Gymnopogon foliosus) of the Cerrado. The effect of fire temperature was tested by exposing seeds to heat shock treatments of 60, 100, and 200 °C for one minute, comparing them to untreated seeds. The effect of smoke was tested by soaking seeds for 24-h in an aqueous smoke comparing them to seeds soaked in distilled water. Differences among treatments were evaluated by ANOVA and randomization tests. None of the tested species had germination stimulated by the temperature or smoke. Both species of Urochloa experienced decreased viability with increasing temperature, while seeds of native species and M. minutiflora tolerated heat shock up to 200 °C. The invasive grasses usually germinated faster than the native grasses. Germination time is therefore a crucial trait driving the invasion process, irrespective of fire-related cues. Other seed traits (e.g. dormancy) and higher resprouting capacity may help invasive species to persist in frequently burned savannas.
Highlights
Successful germination and seedling establishment are important regeneration traits that lead to effective processes of biological invasion (Pyšek & Richardson 2007; Gioria & Pyšek 2017)
In this study we aimed to evaluate the effects of heat shock and smoke on seed viability, germination percentage, and mean germination time (MGT) of three invasive (Melinis minutiflora, Urochloa decumbens and Urochloa brizantha), and three native (Axonopus pressus, Aristida setifolia and Gymnopogon foliosus) grass species frequently found in open Cerrado
Average MGT was of 4.7 days and it was not affected by heat shock treatments (Tab. 2)
Summary
Successful germination and seedling establishment are important regeneration traits that lead to effective processes of biological invasion (Pyšek & Richardson 2007; Gioria & Pyšek 2017). Potentially invasive species are often more adapted to disturbance regimes when compared to the native ones (Facon et al 2006). Fire is a principal disturbance in many ecosystems, and its effects depend on its origin (natural, by a lightning strike, or accidental, by human actions), season and intensity (Whelan 1995), as well as on the particular adaptations of the community species (Huston 2004; Lockwood et al 2007). Fire could affect plants by altering species richness, composition and structure (Whelan 1995; Fidelis et al 2012). Fire could affect the survival, viability and germination of seeds (Moreira et al 2010; Clarke & French 2005)
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