2018
DOI: 10.4996/fireecology.140165084
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Cryptogam Recolonization after Wildfire: Leaders and Laggards in Assemblages?

Abstract: Cryptogams (restricted here to mosses, liverworts, and lichens) have no particular fire-adapted survival strategies and rely on airborne spores or propagules

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Cited by 13 publications
(13 citation statements)
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“…Additionally, diseased or dead ash trees can still keep typical epiphytic lichens for some years, increasing the availability of their propagules and allowing them to spread. In such cases the persistence of lichen propagules in the environment increases the probability of their survival (Eaton et al 2017;Ronnås et al 2017;Wills et al, 2018). The extent and number of possible epiphytic lichen propagule sources within the landscape scale can prevent the species loss in the biota and facilitate their colonization on other microhabitats (Bouchard and Boudreault 2015).…”
Section: Discussionmentioning
confidence: 99%
“…Additionally, diseased or dead ash trees can still keep typical epiphytic lichens for some years, increasing the availability of their propagules and allowing them to spread. In such cases the persistence of lichen propagules in the environment increases the probability of their survival (Eaton et al 2017;Ronnås et al 2017;Wills et al, 2018). The extent and number of possible epiphytic lichen propagule sources within the landscape scale can prevent the species loss in the biota and facilitate their colonization on other microhabitats (Bouchard and Boudreault 2015).…”
Section: Discussionmentioning
confidence: 99%
“…Our analysis focused on discontinuities, composition, and loading of dead or cured understory fuels at distances of centimeters to meters, the scale hypothesized to be most relevant to our study system given the size of the focal organism. Observations from ecosystems characterized by standreplacing fire regimes have generally stressed the importance of unburned vegetation patches within much larger wildfire perimeters or outside of the burn area as potential sources for recolonization during relatively long firefree intervals (e.g., 50 to >100 yr; Maikawa and Kershaw 1976, Zouaoui et al 2014, Wills et al 2018. While postdisturbance dispersal from adjacent areas likely plays some role in Cladonia dynamics on inland dunes of the Delmarva Peninsula, it is unclear to what extent it may help explain their historical densities in the context of a frequent low-severity fire regime, assuming slow colonization and growth rates (e.g., Heinken 1999).…”
Section: Fire Refugiamentioning
confidence: 99%
“…Viewed broadly, the responses of this group to burning are highly variable, exhibiting negative, neutral, or positive responses depending on an array of interacting factors (see the extensive literature review available at Fire Effects Information System, FEIS, https://www.feis-crs.org/feis/). This range of responses has been attributed to differences in aspects of fire regimes including intensity and return interval (Johansson and Reich 2005;O'Bryan et al 2009;Zouaoui et al 2014;Wills et al 2018), selective effects of fire on competing vegetation and habitat structure (Hawkes and Menges 1996;O'Bryan et al 2009), and the existence of unburned patches or other refugia (Holt and Severns 2005;Johansson et al 2006;Ray et al 2015).…”
Section: Introductionmentioning
confidence: 99%
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“…The 66 islands highly varied in area size, together with variation in dispersal capacity among different bryophyte species, which were possibly another reason accounting for a high level of nestedness for bryophytes in the Zhoushan Archipelago [17]. Besides, although bryophytes have a long-distance dispersal capacity, such capacity would vary among different species and categories [25]. Because taxa with a comparatively higher level of nestedness had stronger dispersal ability [17], the variation in their dispersal capacity, coupled with a range of isolation degrees of islands, would result in different levels of nestedness.…”
Section: Nestedness Level Of Bryophyte Distributionmentioning
confidence: 99%