Bol. Soc. Argent. Bot. 59 (3) 2024
introduction
(most common 20 ℃, 5 ℃, -20 ℃ or -196 ℃ in
liquid nitrogen) (Pence, 2002, 2008; Quintanilla
Ferns are one of the oldest lineages of vascular et al., 2002; Aragón & Pangua, 2004; Ballesteros
plants, highly sensitive to environmental changes. et al., 2006, 2012; Gabriel y Galán & Prada, 2011;
They usually inhabit ecosystems susceptible to Mikula et al., 2009, 2015; Vargas & Droste, 2014;
degradation, so their protection and conservation Tomiczak et al., 2023). Usually, the viability of fern
contribute to ensuring the maintenance of these spores is retained when they are stored in dry and
ecosystems and the biodiversity therein (Ballesteros cold conditions (Pence, 2008; Gabriel y Galán &
et al., 2006; Arcand & Ranker, 2008; Mehltreter, Prada, 2010).
2
010). Ferns have diverse ecological roles and many
As part of a project that aims to investigate
species are of economic interest as ornamental, the optimal methods for ex situ conservation
food or medicinal plants (Mannan et al., 2008; of ferns that inhabit Argentina, we began our
Lee & Shin, 2010; Sharpe et al., 2010; Liu et al., studies in the central region of this country, one
2
012; Goswami et al., 2016; Huang et al., 2019). of the four centres of fern diversity in Southern
Furthermore, various fern taxa are considered as Cone (Arana et al., 2013). In this area, fern
indicators of environment disturbance, climate populations are concentrated in the mountain
changes and pollution (Della & Falkenberg, 2019).
systems (called “Sierras Pampeanas centrales”),
Procedures for biodiversity plant conservation which act as islands immersed in pampean plains
can be in situ (protection of natural habitats), or (Arana & Ponce, 2004; Oggero & Arana, 2012;
ex situ (botanic gardens, germplasm banks, in Arana et al., 2021). Despite habitat heterogeneity,
vitro culture), both not mutually exclusive but the biota inhabiting isolated mountain systems is
complementary (Dyer, 1994; Ibars & Estrelles, less likely to survive catastrophic events (Taylor &
2
012; Breman et al., 2021). Fern spore banks Kumar, 2016). In central Argentina, the mountain
(
analogous to seed banks for angiosperms) are systems are frequently disturbed by fires which
an ex-situ conservation tool that allows storing cause strong impacts on species composition,
large quantities of germplasm with high genetic vegetation structure, and biogeochemical and
variation in a small space (Dyer, 1994; Pence, hydrological cycles (Whelan, 1995; Morgan et al.,
2
008; Ibars & Estrelles, 2012; Ballesteros & 2001; Argarañaz et al., 2020).
Pence, 2018). Ballesteros et al. (2006) claimed The objective of the present work was to test
that the spores of ferns that inhabit threatened the ability of the spores to germinate after being
ecosystems should be included in germplasm stored in a freezer and to develop gametophytes
banks for experimental purposes and for long-term and sporophytes, in native fern species of genera
biodiversity conservation.
Amauropelta, Blechnum, and Physematium
The sporophytes of most ferns produce large from central Argentina with different ecological
quantities of spores that are readily available every requirements.
year, and their viability plays an important role for
the successful establishment of individuals and
populations in new habitats (Dyer, 1994; Sheffield, materialS and methodS
1
996). Due to their desiccation tolerance, spores
can be stored for long periods of time at low
temperatures maintaining their viability (Dyer, (Hieron.)Salino&T.E.Almeida(Thelypteridaceae),
979; Ballesteros, 2010). The reduction in spore Blechnum auriculatum Cav. (Blechnaceae), and
Three taxa were studied: Amauropelta argentina
1
viability can be measured by the decrease in Physematium montevidensis (Spreng.) Shmakov
germination percentage over time (Gabriel y Galán (Woodsiaceae). Materials were collected in four
&
Prada, 2010). localities of the Chaco serrano district, Chaco
Various works address the analysis of the optimal biogeographic province, Neotropical region: Las
conditions to preserve the viability of the spores Jarillas (31° 32´ 03.16´´ S, 64° 32´ 14.98´´ W), Atos
over time, using variables as wet or dry storage Pampa (31° 57´ 49.34´´ S, 64°40´13.19´´ W), Las
(i.e. spores stored in capsules with mineral agar vs. Albahacas (32° 53´ 59.02´´ S, 64° 50´´ 17.97´´ W),
kept in Eppendorf tubes), or different temperatures and Achiras (33° 09´ 07.38´´ S, 64° 59´ 32.78´´W).
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