Seasonality and the bet-hedging strategy
Seed dormancy (i.e. delayed germination even when conditions are favourable) is a key plant characteristic that occurs among many species worldwide. But, what selective pressures led to seed dormancy? A recent study provides a major analysis of the factors driving this trait at the global scale (Zhang et al., 2022). Using c. 12 000 species and 10 million records across the globe, they conclude that dormancy is a strategy for plants living under ‘seasonal/unpredictable’ environments; and suggest that bet-hedging could be the major mechanism behind the pattern. To reach their conclusions the authors relate the proportion of species with dormant seeds in a grid-cell global map against climate variables related to annual precipitation, temperature and seasonality. Then they showed that the most significant variables were those related to climate seasonality that they equate with unpredictable climates (although seasonal climates usually are highly predictable in their seasonal cycles).
The mechanism by which an unpredictable environment selects for seed dormancy is via the bet-hedging strategy, that is, spreading germination over a number of years to reduce year-to-year variation in fitness but taking advantage of exceptionally good years for establishment (Cohen, 1966; Philippi, 1993). However, actual unpredictability (i.e. interannual variability; Cowling et al., 2005) was not tested by Zhang et al. (2022). Furthermore, it is difficult to think of a mechanism for the selection of dormancy as an adaptive response to seasonality as such (i.e. predictable intra-annual variation); here nondormancy would appear to be equally adaptive if the same seasonal conditions suitable for germination are repeated every year. There may be some correlation between seasonality and unpredictability but, from a biological point of view, they are quite different constraints and select for different plant strategies. Note that in all of these studies (and here as well, unless otherwise stated), seed dormancy refers to inherent (also called primary or organic) dormancy, which is dormancy driven by seed characteristics, and includes physical, physiological and morphological dormancy (Baskin & Baskin, 2014). Once this dormancy is broken (or if the seeds produced are nondormant), seeds still do not germinate until the hydrothermal conditions are suitable. Overcoming this additional, environmentally imposed dormancy is controlled by when the wet season actually starts or local temperatures reaching certain thresholds, but this imposed dormancy is not considered in current broad-scale studies.
The importance of climatic variables, including seasonality, as correlates of (inherent) dormancy aligns well with other recent global studies focused on Fabaceae (Rubio de Casas et al., 2017; Wyse & Dickie, 2018) and on germination responses at the European scale (Carta et al., 2022). Another recent analysis of seedbank data for 2000 species across the globe (Gioria et al., 2020) considered binary variables related to habitat type, habitat openness (yes/no) and disturbance (yes/no) in addition to climate, and came up with a different conclusion. They concluded that habitat-related variables (disturbance and canopy openness), but not climate, affected the ability of seed plants to form persistent seed banks, and concluded that dormancy, the prerequisite for seedbanks, is a bet-hedging strategy in unpredictable environments.
Overall, these studies suggest that the mechanism selecting for seed dormancy is the bet-hedging strategy for dealing with unpredictable environments. Although this is notable in some ecosystems (especially arid regions; Cohen, 1966, Philippi, 1993, Venable, 2007), here we draw attention to the fact that there are other selective pressures unrelated to climate-associated bet-hedging that have shaped seed dormancy in many species across the globe but are not recognized in these recent studies. Our own contributions have been centred on seed germination in fire-prone environments, and hence have an emphasis on fire vs climate.
The best-bet strategy
A large part of the world has a seasonal climate with a dry season during which the vegetation is highly flammable (mediterranean, savanna, warm temperate, and dry boreal ecosystems). In these ecosystems, wildfires are frequent. Fire intervals are usually shorter than lifespan of the dominant species; thus, they act as a selective force shaping survival and reproductive traits of plants (Keeley et al., 2012). Among the adaptive traits is fire-released seed dormancy (see reviews in Keeley, 1991, Pausas & Lamont, 2022). Fires provide both a mechanism for dormancy release (proximate cause) and conditions (postfire) optimal for germination and establishment (low competition, high resource availability, low predation, low pathogen load) that increase fitness and allow maintenance of the population (ultimate cause). Thus, fires create a unique window of opportunity for recruitment, especially among weakly competitive, shade-intolerant plants. That is, fire is worth waiting for!
In order to benefit from postfire conditions, seeds of many species have acquired the ability to survive the passage of fire and detect presence of the fire gap to initiate germination. Seeds possess two means of detecting a fire event in order to break dormancy and prime the seeds for germination: they are sensitive either to heat or chemicals produced during the combustion of organic matter (collectively called ‘smoke’, although it may include ash and charcoal). Species with these mechanisms exhibit two syndromes: heat-released dormancy and smoke-released dormancy (Pausas & Lamont, 2022). The first is associated mainly with physical dormancy and the latter with physiological dormancy, although some seeds may respond to both fire cues (heat may increase permeability to by-products of combustion).
There are 100s of articles that provide experimental evidence among many species of the fitness benefits (enhanced germination and seedling establishment) when their seeds are subjected to smoke or heat intensities compatible with fire (reviewed in Pausas & Lamont, 2022). In most cases, these species accumulate seeds in the soil during their entire lifespan, and recruitment occurs in a single cohort after fire (postfire seeder species; Figs 1, 2, Supporting Information Fig. S1). That is, postfire recruitment occurs in a single pulse after fire. Here selection does not favour spreading the risk of recruitment failure over many years (bet-hedging) but, instead, maximizes germination in a single year when conditions are optimal, thus following the first substantial rains after fire. We call this strategy the best-bet strategy (Table 1) or environmental matching (sensu Pausas & Lamont, 2022). Although this strategy entails risks, it has adaptive advantages when fires are sufficiently frequent and predictable to occur within the interval between plant maturation and senescence (Pausas & Keeley, 2014). In these ecosystems, seed-dormancy release is not just a fail-safe response to unpredictable seasonal climates but also a routine response following a stochastic disturbance expected within the lifespan of most species in the plant community.
|Nondormant||Strategies that shape dormancy|
|(Temporal) bet-hedging||Best-bet||Spatial bet-hedging|
|Seed bank||None||Soil||Soil or canopy||None|
|Germination event*||Annual||Annual||Postfire only||Annual|
|Level of germination*||High (all of annual crop)||Low (small fraction of interannual crops)||Very high (most of interannual crops)||Med-high (most of annual crop)|
|Interannual fitness variation*||Low||Low||High||Low|
|Predictability of germination||High||Low||High||High|
|Recruitment and establishment||Continuous||Continuous||Single year cohort||Continuous|
|Fruit type||Variable||Dry||Dry (sometimes fleshy elaiosome)||Fleshy|
|Disturbance-prone||None||Small/light, unpredictable||Large/intense, predictable||None|
|Benefits||Low granivory||Spread mortality risk||Optimal establishment conditions||Transport to novel microsites|
|Climate (where dominant)||Ever-wet, tropical, cold temperate||Arid, alpine||Mediterranean, warm temperate||Tropical forests|
- * Given the appropriate hydrothermal conditions.
Fire-released dormancy is prominent in ecosystems that are seasonal and have dense, woody vegetation that limits recruitment of nondormant seeds. Under such conditions, fires are intense (crown-fire ecosystems) and create extensive gaps for recruitment. Prime examples include mediterranean, warm temperate and subtropical shrublands distributed all over the world (Menges & Kohfeldt, 1995; Bradstock et al., 2012; Keeley et al., 2012; Pausas et al., 2021). Fire-released dormancy also is present, but less important, in grassy ecosystems with scattered woody shrubs and trees (surface-fire regimes) such as Brazilian savannas (Zirondi et al., 2019). Fire-released dormancy is almost absent in deserts, extremely cold environments and rainforests; in some of these ecosystems, seed dormancy may be common but unlinked to fire (nonfire-released dormancy), and thus is more aligned to the bet-hedging strategy. For Helianthemum, a large genus in Cistaceae, loss of hard-seededness and heat-released dormancy are notable only among a few recently evolved species that now occupy fire-free habitats, such as gypsum outcrops, deserts and saline wetlands (Pausas & Lamont, 2022).
Serotiny (delayed seed release and dispersal) also is a strategy to accumulate seeds over the years, in this case held in closed cones or fruits stored in the plant crown (Lamont et al., 2020). It occurs mainly among conifers (in the Northern Hemisphere), and in a range of families in the Southern Hemisphere (Proteaceae, Myrtaceae, Casuarinaceae, Bruniaceae, and more rarely among Asteraceae, Anacardiaceae and Ericaceae). Fire again is the mechanism for cone/fruit opening and for creating the appropriate environment for dispersal and for suitable recruitment conditions of the dispersed seeds. Consequently, serotinous species recruit mostly after fire and not during the interfire period. Thus, serotiny (via pyriscence, fire-induced seed release) may also be viewed as an example of accumulating a seed bank as best-bet strategy.
The importance of fire does not mean that climate is unimportant in shaping seed dormancy in fire-prone ecosystems. For instance, summer temperatures determine the heat thresholds for dormancy release to ensure seed bank persistence – by avoiding germination before a fire (Zomer et al., 2022). Under a warming climate, summer temperatures may cross thresholds for dormancy release and stimulate germination under suboptimal conditions, thus depleting the seedbank and jeopardizing the postfire recruitment. In that sense, species with heat-released dormancy may be more sensitive to climate change than species with smoke-released dormancy. In addition, final germination not only depends on (inherent) dormancy release, but also on the hydrothermal conditions for germination (imposed-dormancy release), and this makes seed-bank species sensitive to climatic change. For instance, higher temperatures may maintain imposed dormancy for longer, resulting in reduced postfire germination, despite receiving the appropriate stimulus for dormancy release (e.g. fire; Arnolds et al., 2015). Furthermore, many species with seed dormancy that form the seed bank have dry fruits that are dispersed at relatively short distances (myrmecochory, autochory) and thus their potential migration in a rapidly warming planet is limited.
Long-distance seed dispersal
‘Bet-hedging’ and ‘best-bet’ are two strategies that select for seed dormancy in order to accumulate a seed bank and thus delay germination until conditions become more suitable. There is a further driver that selects for seed dormancy that does not imply the formation of seed banks. Many seeds have acquired seed dormancy to facilitate long-distance dispersal and thus spread germination across the landscape. The clearest example is dispersal by vertebrate frugivores (endozoochory by birds, bats, mammals and reptiles; Levey et al., 2002, Traveset et al., 2007). Frugivores consume the fruit pulp and defaecate or regurgitate the seeds far from the mother plant. This means that seeds need to resist passage through the gut and remain intact until arriving at a new microsite for germination. In such a way, plants benefit from long-distance dispersal to a potentially optimal microsite, often including the faecal material acting as fertilizer (Dinerstein & Wemmer, 1988; Traveset et al., 2007). Thus, seeds of fleshy fruited species typically are dormant, and scarification through the gut releases their dormancy (chemical and/or mechanical scarification, and more rarely removal of inhibitors in the pulp; Traveset et al., 2007). Although bet-hedging spreads germination of seeds accumulated in the seed bank over time, this strategy spreads the annual seed crop across space and thus it could be viewed as a spatial bet-hedging strategy (Table 1).
Climate is by no means the only driver of seed dormancy, nor is bet-hedging the only mechanism that shapes dormancy. Correlative studies based on climate datasets are unlikely to capture the diversity of adaptive strategies plants acquired to maximize their fitness; disturbances and species interactions also need to be considered. Despite the ubiquitous presence of fire across the globe (Archibald et al., 2013) and through geological time (Scott, 2018), recent seed dormancy reviews (noted above) fail to consider fire as drivers for the evolution of seed dormancy. However, fire-prone ecosystems are hotspots of seed dormancy that allow seed banks to accumulate in both the soil and the canopy (Keeley, 1991; Lamont et al., 2020; Pausas & Lamont, 2022). We need to overcome the ‘fire blindness’ syndrome (sensu Pausas & Lamont, 2018) that still seems to prevail in much ecological research. Further studies are needed to understand and quantify the relative importance of the different strategies in various ecosystems across the globe. An interesting test of climate vs disturbance as selective factors would be to compare dormancy in closed forests that seldom burn with species in adjacent regularly burnt shrublands under the same climate. We predict that dormancy and seedbanks would be largely restricted to the fire-prone ecosystems. More research also is needed to understand the environmental conditions that maintain and release imposed dormancy (once inherent dormancy is released or does not apply) as changes in climate cues could be the key to plant success under a changing climate.
This research was performed under the framework of projects FIROTIC (PGC2018-096569-B-I00; Spanish government, MCIN/AEI/10.13039/501100011033 and FEDER) and FocScales (Promteo/2021/040, Generalitat Valenciana).
JGP had the idea and wrote the first draft with the help of BBL; JEK and WJB contributed to the final version.
|nph18436-sup-0001-SupInfo.pdfPDF document, 3 MB||
Fig. S1 Examples of massive postfire recruitment from seed bank.
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- 2013. Defining pyromes and global syndromes of fire regimes. Proceedings of the National Academy of Sciences, USA 110: 6442–6447.
- 2015. Experimental climate warming enforces seed dormancy in South African Proteaceae but seedling drought resilience exceeds summer drought periods. Oecologia 177: 1103–1116.
- 2014. Seeds: ecology, biogeography, and evolution of dormancy and germination. San Diego, CA, USA: Elsevier.
- 2012. Flammable Australia. Clayton, Victoria, Australia: CSIRO.
- 2022. Climate shapes the seed germination niche of temperate flowering plants: a meta-analysis of European seed conservation data. Annals of Botany 129: 775–786.
- 1966. Optimizing reproduction in a randomly varying environment. Journal of Theoretical Biology 12: 119–129.
- 2005. Rainfall reliability, a neglected factor in explaining convergence and divergence of plant traits in fire-prone mediterranean-climate ecosystems. Global Ecology and Biogeography 14: 509–519.
- 1988. Fruits Rhinoceros eat: dispersal of Trewia nudiflora (Euphorbiaceae) in lowland Nepal. Ecology 69: 1768–1774.
- 2020. Phylogenetic relatedness mediates persistence and density of soil seed banks. Journal of Ecology 108: 2121–2131.
- 1991. Seed germination and life history syndromes in the California chaparral. The Botanical Review 57: 81–116.
- 2012. Fire in Mediterranean ecosystems: ecology, evolution and management. Cambridge, UK: Cambridge University Press.
- 2020. Fire as a selective agent for both serotiny and nonserotiny over space and time. Critical Reviews in Plant Sciences 39: 140–172.
- 2002. Seed dispersal and frugivory: ecology, evolution and conservation. Wallingford, UK: CAB International.
- 1995. Life history strategies of Florida scrub plants in relation to fire. Bulletin of the Torrey Botanical Club 122: 282–297.
- 2014. Evolutionary ecology of resprouting and seeding in fire-prone ecosystems. New Phytologist 204: 55–65.
- 2018. Ecology and biogeography in 3D: the case of the Australian Proteaceae. Journal of Biogeography 45: 1469–1477.
- 2022. Fire-released seed dormancy – a global synthesis. Biological Reviews 97: 1612–1639.
- 2021. A shrubby resprouting pine with serotinous cones endemic to Southwest China. Ecology 102: e03282.
- 1993. Bet-hedging germination of desert annuals: beyond the first year. American Naturalist 142: 474–487.
- 2017. Global biogeography of seed dormancy is determined by seasonality and seed size: a case study in the legumes. New Phytologist 214: 1527–1536.
- 2018. Burning planet: the story of fire through time. Oxford, UK: Oxford University Press.
- 2007. A review on the role of endozoochory in seed germination. In: AJ Dennis, EW Schupp, RA Green, DA Westcott, eds. Seed dispersal: theory and its application in a changing world. Wallingford, UK: CAB International, 78–103.
- 2007. Bet hedging in a guild of desert annuals. Ecology 88: 1086–1090.
- 2018. Ecological correlates of seed dormancy differ among dormancy types: a case study in the legumes. New Phytologist 217: 477–479.
- 2022. Seed dormancy in space and time: global distribution, paleo- and present climatic drivers and evolutionary adaptations. New Phytologist 234: 1770–1781.
- 2019. Fire effects on seed germination: heat shock and smoke on permeable vs impermeable seed coats. Flora 253: 98–106.
- 2022. Fire and summer temperatures interact to shape seed dormancy thresholds. Annals of Botany 129: 809–816.