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. 2024 Jul 1;14(7):e11671. doi: 10.1002/ece3.11671

Seed dormancy types and germination response of 15 plant species in temperate montane peatlands

Jian‐Yi Wang 1,2,3, Zhao‐Jun Bu 1,2,3,, Peter Poschlod 4, Shuayib Yusup 1,2,3, Jia‐Qi Zhang 1,2,3, Zheng‐Xiang Zhang 1,2,3,
PMCID: PMC11216845  PMID: 38952654

Abstract

Despite their crucial role in determining the fate of seeds, the type and breaking mode of seed dormancy in peatland plants in temperate Asia with a continental monsoon climate are rarely known. Fifteen common peatland plant species were used to test their seed germination response to various dormancy‐breaking treatments, including dry storage (D), gibberellin acid soaking (GA), cold stratification (CS), warm followed cold stratification (WCS), GA soaking + cold stratification (GA + CS) and GA soaking + warm followed cold stratification (GA + WCS). Germination experiment, viability and imbibition test, and morphological observation of embryos were conducted. Of the 15 species, nine showed physiological dormancy (PD), with non‐deep PD being the dominant type. Four species, Angelica pubescens, Cicuta virosa, Iris laevigata, and Iris setosa exhibited morphophysiological dormancy. Two species, Lycopus uniflorus and Spiraea salicifolia, demonstrated nondormancy. Overall, the effect hierarchy of dormancy‐breaking is: CS > GA > WCS > GA + CS > D > GA + WCS. Principal component analysis demonstrated that seed traits, including embryo length: seed length ratio, seed size, and monocot/eudicot divergence, are more likely to influence seed dormancy than environmental factors. Our study suggests that nearly 90% of the tested peatland plant species in the Changbai Mountains demonstrated seed dormancy, and seed traits (e.g. embryo‐to‐seed ratio and seed size) and abiotic environmental factors (e.g. pH and temperature seasonality) are related to germination behavior, suggesting seed dormancy being a common adaptation strategy for the peatland plants in the temperate montane environment.

Keywords: Changbai Mountains, cold stratification, germination response, peatlands, physiological dormancy


Nearly, 90% of the tested peatland plant species demonstrate seed dormancy, mainly physiological dormancy.Seed traits, are more likely to influence seed dormancy than environmental factors.

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1. INTRODUCTION

Seed dormancy is an important adaptation strategy for numerous plant species to coordinate germination and establishment with the environment (Baskin & Baskin, 2014; Thompson & Grime, 1979). Generally, dormancy is controlled by both internal and external factors, and is one of the important life history features of plants, enabling them to cope with the cyclic and fluctuating environmental conditions (Finch‐Savage & Leubner‐Metzger, 2006). In harsh environment, to reduce the probability of sexual regeneration failure, plants tend to employ seed dormancy to prevent simultaneous germination of all seeds (Long et al., 2015). This delay in germination may ensure the persistence of seed banks and continuous regeneration of the plant community (Saatkamp et al., 2014). In the region of temperate Asia with continental monsoon climate, seasonality (namely, seasonal fluctuation) is rather strong and the frigid weather in early and growing seasons is more harsh than in other temperate, subtropical, and tropical regions (Cheng et al., 2017). However, the type and breaking mode of seed dormancy in the region are rarely known.

The means of dormancy releasing can vary depending on the type of seed dormancy. For seeds with PY, scarification, or high‐temperature treatments are required to break the dormancy (Lamont & Pausas, 2023). For PD, under the dual control of germination accelerator (GA) and germination inhibitor (ABA), seeds present a dormancy continuum, that is, states between dormancy and nondormancy (Footitt et al., 2011). Environment factors (temperature, light, oxygen, water, and chemicals) can cause changes in dormant states, and dormancy (non‐deep PD) can be broken by gibberellic acid soaking or environmental signals, such as cold and wet, or warm and wet weather (Baskin & Baskin, 2004). Seeds with MD have an undeveloped or undifferentiated embryo at seed maturity, and the dormancy can be released without pretreatment or with dry storage as the embryo grows (Baskin & Baskin, 2004). Seeds with MPD, which has both morphological and physiological dormancy characteristics and is sensitive to environmental change, can be broken by stratification (warm, cold, or alternating temperature) or GA. Seeds with combinational dormancy (PY + PD), exhibiting both physical and physiological dormancy, can be broken by scarification followed by stratification (Baskin & Baskin, 2014).

The effectiveness of dormancy releasing is means‐dependent. Dry storage, as a means to break seed PY (Gama‐Arachchige et al., 2012; Jayasuriya et al., 2008), is an effective way to break intermediate PD and MPD of seeds (Baskin & Baskin, 2020; Finch‐Savage & Leubner‐Metzger, 2006). Compared with dry storage, cold stratification (CS), in which seeds are exposed to moist and cold conditions (0–10°C) for at least 4–6 weeks (Merritt et al., 2007), is considered to be the much more practical way to break PD of the seeds. In temperate regions, CS is usually required for seeds to break PD in spring (Baskin & Baskin, 2014). A lot of studies show that GA can partially replace CS in breaking PD/MPD (e.g. Baskin & Baskin, 2014; Hao et al., 2014; Herranz et al., 2010; Zhang et al., 2019), but it cannot break deep PD (Baskin et al., 2005) and deep complex MPD (Phartyal et al., 2009; Walck & Hidayati, 2004). Therefore, the effectiveness of GA is generally lower than that of CS (Chien et al., 2011; Li et al., 2022; Wang et al., 2017). In temperate and boreal regions, warm stratification (WS) is usually required for the seeds with PD/MPD to geminate in autumn and WS followed by CS (hereafter called WCS) is needed for the seeds to break PD/MPD in spring (Baskin & Baskin, 2014). It has been reported that WCS greatly enhances seed germination by well‐breaking PD/MPD compared with WS or CS alone (Baskin & Baskin, 1989; Liu et al., 2023) and WS followed GA is effective in breaking PD (Chen et al., 2008, 2022). A combined treatment of GA and CS has been found to result in a greater seed germination than either treatment alone (Hashemirad et al., 2023; Li et al., 2022).

Seed size/mass (Gioria et al., 2020; Hashemirad et al., 2023; Rees, 1993; Shipley & Parent, 1991; Thompson & Grime, 1979), phylogeny (Rosbakh et al., 2019; Rubio de Casas et al., 2017; Scholten et al., 2009) and environmental factors especially climate factors (Carta et al., 2022; Rosbakh et al., 2023) were proved to jointly determine seed dormancy. Seed size/mass is a crucial seed trait. Numerous studies indicate that small‐seeded species have a higher proportion of dormancy than large‐seeded counterparts (Gioria et al., 2020; Rees, 1993, 1996; Thompson & Grime, 1979). Large‐seeded species possess an advantage in seedling establishment due to more nutrient supply in resource‐limited conditions. This exempts them from dormancy maintenance and maximizing their growth before adverse conditions occur (Rees, 1996). Conversely, small‐seeded species are less competitive and often require a vegetation gap after disturbance to accomplish seedling establishment. Considering plant phylogeny, PD is very common in some families, such as Cyperaceae (Rosbakh et al., 2019;  Schütz, 1997) and Poaceae (Fernández‐Pascual et al., 2022). Morphological dormancy (MD) and/or morphophysiological dormancy (MPD) are prevalent in Apiaceae, and MPD was also observed in various Iris and Lobelia species (Baskin & Baskin, 2014). Physical dormancy (PY) predominates in Fabaceae (Rubio de Casas et al., 2017). At a large scale, climatic factors such as seasonality, average annual temperature, and annual precipitation are associated with seed dormancy types (Rosbakh et al., 2023; Zhang, Liu, et al., 2022). For example, PY is more common in the area with strong seasonality in both temperature and precipitation; PD is predominated in relatively dry area with high‐emperature seasonality; and nondormancy is associated with stable, warm and humid climates (Baskin & Baskin, 2014; Jurado & Flores, 2005; Rosbakh et al., 2023). Seeds of many peatland plants can exhibit dormancy, predominantly PD (Fernández‐Pascual, 2016; Fernández‐Pascual et al., 2013; Jensen, 2004; Poschlod, 1990;  2019 Rosbakh et al., 2020; Schütz, 1997). For example, from 20 peatland species (13 raised bog or facultatively raised bog species, 15 fen or facultatively fen species) in Southeast‐Germany, 13 species showed a physiological dormancy (Poschlod, 1990). Six Carex species in northern Germany showed a seasonal dormancy cycle (Schütz, 1997). Fen plants were found to commonly show PD of seeds and CS and even WS effectively increased seed germination in 15 tested species in Spain (Fernández‐Pascual et al., 2013). A further study on 34 peatland species showed that the seeds of all species exhibited PD at dispersal, and 28 of the 34 species showed conditional type 2 non‐deep PD (Fernández‐Pascual, 2016).

Northern peatlands are rich in ecological gradients, such as water table depth and pH (Rydin & Jeglum, 2013; Wheeler & Proctor, 2000). Along the gradient of water table depth and pH, peatlands differentiated as hummocks and hollows and bogs and fens, respectively. The characterized ecological gradients affect ecological processes in peatlands (Rydin & Jeglum, 2013). For example, the germination of seeds (Fernández‐Pascual, 2016; Liu et al., 2005) and spores (Fan et al., 2023; Feng et al., 2018; Sundberg & Rydin, 2000) is strongly depressed by hypoxia in hollows with low water table depth. In Sphagnum dwelling peatlands, the strong acidity due to cation exchange by Sphagnum is believed as the main mechanism to suppress seed germination and then vascular plant colonization (van Breemen, 1995) even though spore germinability (represented by germination percentage) decreases with pH in Sphagnum (Feng et al., 2018). We, however, know rather less about seed dormancy type and even germination characteristics of peatland plants in temperate Asia with terrestrial monsoon climate, one of the main distribution areas for peatlands in the world.

To address the knowledge gap, we selected 15 vascular plant species collected from five peatlands in the Changbai Mountains of northeastern China, and tried to test the hypotheses through various means of dormancy breaking. Specifically, we hypothesized that: (1) most of the tested peatland plants would exhibit PD in seeds, with non‐deep PD being predominant; (2) for the effectiveness of dormancy breaking, combined treatments would be better than single treatments, while CS would be better than GA and dry storage; (3) seed size would negatively be correlated with germination percentage; and (4) The germinability would be related with maternal environmental characteristics, namely, positively correlated with water table depth and negatively correlated with pH.

2. MATERIALS AND METHODS

2.1. Study area

The Changbai Mountains is one of the main distribution regions of peatlands in China, covering a geographical span of 38°46′–47°30′ N and 121°08′–130°20′ E. The highest elevation in the area is 2691 m, and the lowest elevation is 410 m. Under the control of the East Asian monsoon, the study area is characterized by a mid‐temperate continental monsoon‐type mountain climate with four distinct seasons. In our study area (Figure 1), the mean annual temperature ranges from −4 to 9°C, and the annual precipitation ranges from 679 to 862 mm (data sources: WorldClim database). The growing season is from May to September, and the freezing period is from October to April. In peatlands, the vegetation is plant species rich and usually include diverse bryophytes, herbs, dwarf shrubs, and sparse trees. Among them, Sphagnum spp., Carex spp., Betula ovalifolia Rupr., Vaccinium uliginosum L., and Larix olgensis A. Henry are common (Bu et al., 2011).

FIGURE 1.

FIGURE 1

Maps showing the location of the study region in China (a) and study sites in the Changbai Mountains, northeastern China (b) and landscape photographs of Hani (c), Sandaohu (d), Anbei (e), Yueliangwan (f), and Dongfanghong (g) peatlands.

2.2. Seed collection

Fifteen species including three woody species and 12 herbaceous species from four habitats (Table 1) were chosen as the study species since they are common in the peatlands in the Changbai Mountains and their seed amounts are great enough for experiment use. During middle August–late September, 2020–2021, their seeds were collected from five peatlands (Figure 1). The collected seeds were air‐dried at laboratory conditions of RH 46% and 22°C until they reached a constant weight and were mixed thoroughly to ensure uniform seed quality (De Vitis et al., 2019). Only intact seeds without empty shells or mildew were used in the experiment. The collected fresh seeds for each species were air‐dried for 1 week and then were divided into eight groups, with 100 seeds in each group. Each group of seeds was weighed using a Sartorius analytical balance (BS224S, 0.0001 g).

TABLE 1.

Information on the study species, seed mass, seed collection sites and habitats.

Species Abbr. Life form Seed mass/g Site Habitat WTD/cm pH
Angelica pubescens A. pub Forb 2.231 (0.000) H F‐Hu 12.7 (3.37) 6.13 (0.160)
Betula ovalifolia B. ova Dwarf shrub 0.628 (0.000) H F‐Hu 12.7 (3.37) 6.13 (0.160)
Carex limosa C. lim Graminoid 1.161 (0.001) S O‐Ho 5.0 (3.27) 6.08 (0.052)
Cicuta virosa C. vir Forb 0.788 (0.000) A F‐Hu 9.0 (5.97) 5.35 (0.093)
Hypericum longistylum H. lon Forb 0.131 (0.001) A F‐Hu 9.0 (5.97) 5.35 (0.093)
Iris laevigata I. lae Forb 20.908 (0.000) H O‐Ho 19.1 (3.65) 6.03 (0.072)
Iris setosa I. set Forb 6.923 (0.000) H O‐Ho 19.1 (3.65) 6.03 (0.072)
Lobelia sessilifolia L. ses Forb 0.190 (0.000) H O‐Hu 19.1 (3.65) 6.03 (0.072)
Lycopus uniflorus L. uni Forb 0.171 (0.001) S F‐Hu 5.0 (0.82) 5.85 (0.081)
Lysimachia thyrsiflora L. thy Forb 0.326 (0.000) S O‐Hu 5.0 (3.27) 6.08 (0.052)
Lythrum salicaria L. sal Forb 0.035 (0.000) S O‐Ho 5.0 (3.27) 6.08 (0.052)
Pedicularis grandiflora P. gra Forb 0.968 (0.000) S O‐Ho 5.0 (3.27) 6.08 (0.052)
Scheuchzeria palustris S. pal Graminoid 5.231 (0.000) Y O‐Ho 15.9 (3.66) 5.50 (0.130)
Spiraea salicifolia S. sal Dwarf shrub 0.062 (0.000) H F‐Hu 12.7 (3.37) 6.13 (0.160)
Vaccinium uliginosum V. uli Dwarf shrub 0.228 (0.000) D F‐Hu 14.8 (3.23) 5.81 (0.123)

Note: Data are presented as mean (SD). Habitats: F, Forest margin; Ho, Hollow; Hu, Hummock; O, Open expanse. Peatland sites (elevation): A, Anbei (730 m); D, Dongfanghong (1114 m); H, Hani (900 m); S, Sandaohu (597 m); Y, Yueliangwan (1000 m).

Abbreviation: WTD, water table depth.

2.3. Experiment design

Given the various possibilities of dormancy type in the study species, we conducted four tests and one dormancy‐breaking treatment. Firstly, to test the viability of seeds, we carried out a viability test with tetrazolium. Secondly, based on the viability test, we further cut the seeds to observe embryo morphology, to determine whether MD was present. Thirdly, we conducted an imbibition test to determine if the seed coat could not absorb water and hence limit germination, to determine the presence or absence of PY. Fourthly, before and after stratification, we carried out a germination test to determine whether PD or MPD was present in the seeds. Fifthly, combining the imbibition test, stratification treatment, and then germination test, we tried to determine the presence of PY + PD.

2.4. Viability test

The protocol adapted from Bourgeois et al. (2019) was used to assess viability, and 2,3,5 triphenyl tetrazolium chloride (TTC) solution was prepared with phosphate buffer. Before being dyed, seeds were soaked at 30°C for 8 h to allow complete uptake of the deionized water. Seed embryos were then exposed by a longitudinal cut and dyed with TTC at a concentration of 1% for 12 h at 30°C in darkness (20 seeds per dish). Seeds were deemed viable if their embryos were firm, red, and showed no signs of necrosis. Otherwise, they were regarded as nonviable. For Scheuchzeria palustris seeds, a simple visual inspection was used (Bourgeois et al., 2019). Specifically, a seed is deemed as viable if the internal color, upon cutting, appears as emerald green or dark green. Conversely, if the color is brown or black, the seed is considered as nonviable.

2.5. Morphological observation of embryos

Seeds were soaked in deionized water for 24 h and then cut longitudinally with a scalpel. The morphology of seed embryos was observed using stereomicroscopes (SMZ1270, Nikon, Japan). The embryo‐to‐seed ratio (E:S ratio) was calculated by dividing the embryo length by the seed length after measuring. We followed the criteria of Baskin and Baskin (2014) to tell the status of embryo, namely, differentiated, undifferentiated, and differentiated but underdeveloped. If a radicle and cotyledon(s) can be distinguished, the seed embryo was regarded as differentiated. Otherwise, it was regarded as undifferentiated. If a radicle and cotyledon(s) can be distinguished but the volume proportion of embryo‐to‐seed was no more than 0.1%, the seed embryo was considered as differentiated but underdeveloped. For the seed with embryo development and differentiation, if germination happens within 4 weeks in a germination test, it was determined as morphological dormancy; if gemination cannot happens within 4 weeks, it was determined as morphophysiological dormancy.

2.6. Imbibition test

To determine whether the seed coat is permeable, that is, whether there is PY, we conducted an imbibition test (Baskin & Baskin, 2004). For seeds of species weighing more than 1 mg, we used three replicates containing 20 seeds for each species, while for seeds with weight less than 1 mg, we used 50 seeds per replicate. The seeds were placed in a Petri dish with two layers of Cytiva filter paper and incubated in a growth chamber (PRX‐450C, Ningbo Saifu, China) under white light at 25°C for 72 h, seed mass was measured after 0, 24, 48, and 72 h (ISTA, 2007). During the measurement, the seeds were removed from the wet filter paper and weighed again after being wiped dry. A significant increase in seed mass indicates the presence of permeable seed coat, while little or no increase in mass indicates the presence of impermeable seed coat. To account for the different seed mass, we converted the number of seeds to 20 during data analysis. In addition, for seeds of H. longistylum and V. uliginosum with weak water permeability, we took scanning electron microscope (SU8010, Hitachi, Japan) photos to further observe seed coat thickness and the presence of an impermeable layer.

2.7. Dormancy breaking and germination test

A two‐way factorial experiment was employed with two factors: seven levels of dormancy breaking and 15 levels of species, with four replicates each (420 samples in total). The seven levels of dormancy breaking included: control (CK, germination percentage before stratification), dry storage (D), GA soaking (GA), cold stratification (CS), warm + cold stratification (WCS), GA soaking + cold stratification (GA + CS), GA soaking + warm + cold stratification (GA + WCS).

Dry storage involved storing the seeds in a 4°C refrigerator for 5 months. For the GA treatment, the seeds were soaked in 500 mg/L GA3 for 12 h after pretreatment with 4 mol/L H2SO4 for 15 min which was demonstrated to well facilitate seed absorption of GA in a pre‐experiment. CS was carried out by storing the seeds at 1°C and relative humidity (RH) 50% in darkness for 12 weeks. Variable‐temperature stratification was conducted over a total of 18 weeks to simulate the late summer and early autumn climate in the Changbai Mountains. During weeks 1–6 (warm stratification), the incubator temperature was set at 25/15°C with a 14/10 h (light/dark) and RH 50%, photoperiod was the same as above. During 7–18 weeks (cold stratification), the growth chamber temperature was set at 1°C and RH 50% to simulate the winter climate in the region. Given the snow cover in winter and early spring, 24 h in darkness was used. To ensure that the seeds remained moist, a weekly flip check was performed during stratification under weak green light.

Preliminary experiments showed that seeds of many species exhibit low or no germination percentage at a constant temperature, but the germination percentage increases with the number and range of alternating temperature (Fenner & Thompson, 2005). Pre‐experiments have also demonstrated that seeds tend to germinate much better in an alternating temperature environment (25/15°C) than in constant temperature environment (20°C). Therefore, the thermoperiod of seed incubation in this study was set at 25/15°C. After cold, warm, or variable‐temperature stratification, the seeds were incubated for 4 weeks in 12/12 h light/dark photoperiod at 25/15°C, and germination percentages were recorded. Observations were carried out on day 1, 3, 5, 7, 14, 21, and 28 after incubation, with germination determined by the emergence of the embryo through the seed coat.

2.8. Data acquisition for maternal environment

We used the WorldClim database (https://www.worldclim.org/data/worldclim21.html), to obtain data on annual precipitation, annual mean temperature, temperature seasonality, and precipitation seasonality for each peatland. Water table depth (WTD) for the typical habitat of each species was determined by measuring the vertical distance from peatland surface to water table level using a tape measure (Yi et al., 2024). Water pH was determined by averaging values of three repeated measurements ~20 cm apart with the portable multi‐parameter analyzer (HQ30D, Hach, USA) in the nearest surface water within the typical habitat. Both WTD and pH measurements were collected from five typical habitats for each species more than 5 m apart in the peatlands.

2.9. Data processing and analysis

2.9.1. Data processing

The dyeing percentage of seeds was used to represent the viability of seeds, proportion of imbibed seed weight to initial seed weight was used to represent their permeability. Germination percentage was calculated as the proportion of germinated seeds to the total number of seeds in the Petri dish.

In the stratification experiment, there were 25 seeds per dish and four replicates were conducted. Although light availability was low, some seeds germinated during warm stratification in this experiment. Therefore, when counting germinated seeds, those germinated during stratification were also included.

2.9.2. Statistical analysis

All statistical analyses were conducted in R v 4.2.3. Generalized linear models (GLMs) were used to analyze the effect of dormancy‐breaking treatments (explained factor) on germination (germination percentage on the 28th day as dependent factor). The significance of factors for each experiment was assessed by Wald Chi‐square statistics to the model. Duncan's test was used for multiple comparisons. The difference between germination percentage of control and initial viability was determined by Mann–Whitney U‐tests to determine whether the seeds were dormant or not. Principal components analysis (PCA) was used to reduce and visualize the variability in the species' seed germination response, and to determine intercorrelations among seed traits or environmental factors. The PCA was carried out with the package ‘FactoMineR’ using the variance–covariance matrix. The significance level was set to α = .05.

3. RESULTS

3.1. Initial seed viability

The initial seed viability of the 15 tested species ranged from 76.1% to 100% with an average of 89.2 ± 3.74% (mean ± SEM). Betula ovalifolia (Figure 2) seeds had the lowest initial viability of 76.1 ± 4.73%. The average viability of C. limosa, C. virosa and Lyc. uniflorus seeds ranged between 76.3% and 81.5%. All other species had viability greater than 90% (the dashed line shown in Figure 2).

FIGURE 2.

FIGURE 2

Germination percentage of study species' seeds in peatlands of the Changbai Mountains under six dormancy‐breaking treatments. CK, control; D, dry storage; GA, gibberellic acid soaking; CS, cold stratification for 12 weeks; WCS, warm stratification for 6 weeks followed by cold stratification for 12 weeks; GA + CS, gibberellic acid soaking followed by cold stratification for 12 weeks; GA + WCS, gibberellin acid soaking followed by warm stratification for 6 weeks and then cold stratification for 12 weeks (mean ± SEM, n = 4). The blue dashed line represents the initial seed viability (n = 4). Full names of the 15 species are shown in Table 1.

3.2. Seed morphological observation of the embryo and imbibition

The seeds of A. pubescens, C. virosa, I. laevigata, and I. setosa were with linear underdeveloped embryos surrounded by endosperm (with a short hypocotyl and low E:S ratio of 0.08–0.55), but the seeds of all the other tested plants (11 species) were well differentiated and fully developed at the time of collection (Figure 3).

FIGURE 3.

FIGURE 3

Morphological structure of seeds of study species in the Changbai Mountain peatlands. Bars, 1 mm. The dashed line indicates the outline of the embryo; for exalbuminous seeds, the embryo is not drawn separately with a dashed line.

After imbibition for 24 h, all species showed a clear increase in seed weight and then no further increase was observed thereafter (see Appendix S1). The proportion of fresh weight increase varied among the tested species, with 50%–100% for C. virosa, I. laevigata, I. setosa and P. grandiflora, over 100% for A. pubescens, C. limosa and S. palustris, and 0–50% for the other species. Notably, H. longistylum showed the lowest water imbibition capacity among the tested species. In addition, no impermeable layer was found under the observation with a scanning electron microscope (Appendix S4).

3.3. Effect of dormancy‐breaking treatment on seed germination

Under the control treatment, except for the two non‐dormant species (S. salicifolia and Lyc. uniflorus), the initial germination percentage of the other 13 species was low, ranging from 0 to 37.5%, with an average of 16.39 ± 2.95%, suggesting the presence of dormancy in these species. Compared with the control, dry storage improved seed germination percentage of the tested species (χ 2 = 540.2, p < .001), except C. virosa and Lyc. uniflorus. It even resulted in Lyt. salicaria seeds achieving the highest germination percentage of 85 ± 3.79% (Figure 2). Gibberellic acid (GA) soaking increased the germination of A. pubescens, H. longistylum, Lyc. sessilifolia, Lys. thyriflora, S. palustris and V. uliginosum seeds (χ 2 = 928.1, p < .001), with germination percentage greater than 85% (Figure 2). CS significantly increased germination percentage of all species (χ 2 = 2041.6, p < .001). Cold stratified seeds of Lob. sessilifolia, Lys. thyriflora and S. salicifolia species showed germination percentage greater than 90% while B. ovalifolia, C. virosa, Lob. sessilifolia, S. salicifolia, and P. grandiflora seeds achieved their highest germination percentage (Table 2, Figure 2). Varied‐temperature stratification (WCS) (χ 2 = 117.4, p < .001) enhanced seed germination percentage of most species, but it inhibited the germination of some species, such as H. longistylum, Lyc. uniflorus, Lys. Thyriflora, and S. salicifolia. The GA + CS treatment resulted in the highest germination percentage in I. laevigata, I. setosa, and S. palustris seeds (χ 2 = 724.2, p < .001), but it inhibited seed germination in A. pubescens, C. virosa, Lyc. uniflorus, Lyt. salicaria, and S. salicifolia. Surprisingly, the GA + WCS treatment had the best effect on dormancy breaking of I. laevigata seeds (χ 2 = 74.5, p < .001), with germination percentage of 100%. The effect of dormancy breaking treatment on mean germination time (MGT) is species‐specific (see Appendices S2 and S3). On average, namely, species difference being neglected, GA, CS, WCS, and GA + CS all increased seed MGT.

TABLE 2.

Generalized linear mixed model (GLMM) fitted to the results of the effect of different dormancy‐breaking treatments on the 28th day germination percentage (GP) of 15 peatland plant species.

Species D GA CS WS GA + CS GA + WS
Angelica pubescens 474.2 568.8 552.4 260.5 0.12 <0.001
Betula ovalifolia 7.2 2.8 138.2 43.1 2.2 <0.001
Carex limosa <0.001 0.48 15.0 59.8 35.3 13.9
Cicuta virosa 14.6 10.7 40.6 8.1 16.8 25.0
Hypericum longistylum 44.4 423.6 363.0 0.78 5.5 7.0
Iris laevigata 1.3 0.72 243.1 661.2 710.2 799.5
Iris setosa 2.4 5.8 28.4 55.4 101.4 45.9
Lobelia sessilifolia 74.9 144.9 152.4 0.018 23.1 77.5
Lycopus uniflorus 0.27 6.2 4.5 4.5 93.4 96.5
Lysimachia thyrsiflora 7.0 762.4 658.8 5.4 266.8 224.6
Lythrum salicaria 77.1 72.2 36.9 7.9 0.9 0.12
Pedicularis grandiflora <0.001 <0.001 181.0 0.51 0.056 <0.001
Scheuchzeria palustris 112.8 225.4 214.5 189.1 245.0 217.1
Spiraea salicifolia 3.8 0.019 7.8 2.7 48.6 31.1
Vaccinium uliginosum <0.001 440.6 284.9 254.7 338.3 167.2

Note: The significance level of experimental treatment effects on GP of the species was assessed by Wald's χ 2 statistics of generalized linear model. Significant parameters (p < .05) are bolded.

3.4. PCA analysis on seed germination response to the dormancy‐breaking treatments

In Figure 4, the first three PCA axes explain 63.25% of the variance. Axis 1 (28.17% of variance) was positively correlated with the seed traits, including seed size, E:S ratio and monocot/eudicot divergence. This indicated that there was a differentiation in seed germination between large and small‐seeded species, long‐ and short‐embryo species, and monocotyledonous and eudicotyledonous species. Seeds of monocotyledonous, embryo‐short/embryo‐underdeveloped, and large‐seeded species (e.g. S. palustris, I. laevigata, I. setosa and C. limosa) required more complex and special treatments to germinate, whereas those of eudicotyledonous, endosperm‐less/embryo fully developed and small‐seeded species seemed to easily germinate under natural conditions. On the other hand, axis 2 (21.34% of variance) was mainly positively correlated with annual precipitation, annual mean temperature, temperature seasonality, precipitation seasonality, and pH, but negatively correlated with WTD, indicating that germination percentage of the tested plants was closely related to these ecological/environmental factors. Specifically, deeper water table, less mean annual precipitation, strong seasonality, lower mean annual temperature, and lower pH were all associated with high seed germinability.

FIGURE 4.

FIGURE 4

PCA analysis of study species in the peatlands of the Changbai Mountains was based on environmental factors, seed traits and germination response. The environmental factors are annual precipitation (AP), mean annual mean temperature (AMT), temperature seasonality (TS), precipitation seasonality (PS), water table depth (WTD) and pH, represented by blue arrows and fonts. Seed traits include embryo‐to‐seed ratio (E:S ratio), seed mass and monocot/eudicot divergence, and represented by red arrows and fonts. Axis 1 corresponded to seed traits, explained 28.2%; axis 2 corresponds to environmental factors with 21.3% explanation. CK, control; D, dry storage; GA, gibberellin acid soaking; CS, cold stratification for 12 weeks; WCS, warm stratification for 6 weeks followed by cold stratification for 12 weeks; GA + CS: gibberellin acid soaking followed by cold stratification for 12 weeks; GA + WCS, gibberellin acid soaking followed by warm stratification for 6 weeks and then cold stratification for 12 weeks (mean ± SEM, n = 4). Full names of the 15 species are given in Table 1.

4. DISCUSSION

The purpose of this study was to investigate seed dormancy type and germination characteristics of peatland plants in temperate Asia with terrestrial monsoon climate. In the experiment, we systematically used a series of dormancy‐breaking means. We expected that PD was the primary dormancy type for the tested species from continental monsoon climate with strong seasonality of temperature and precipitation. Our results demonstrated that nearly 90% of species had dormancy; 60% of dormant showed PD; CS, the most efficient way to break seed dormancy, and both seed traits (e.g. embryo‐to‐seed ratio and seed size) and abiotic environmental factors (e.g. pH and temperature seasonality) affected seed germination.

4.1. Dormancy types of peatland plant seeds in the Changbai Mountains

A non‐parametric significance test including both initial viability and initial germination percentage showed that dormancy was present in 13 out of 15 plant seeds, except Lyc. uniflorus and S. salicifolia seeds. Notwithstanding this, we contend that both species showed germination percentage of 58.75% and 67.5% in CK. However, after dormancy‐breaking treatment, the germination percentage and mean germination time increased.

The species with dormancy in this study can be classified into two dormancy types, MPD and PD, according to the classification system of Baskin and Baskin (2004). All the tested species showed permeable seed coat, indicating no physical dormancy (PY). The embryos of seeds in A. pubescens, C. virosa, I. setosa, and I. laevigata were underdeveloped. Treatment with GA, CS, and WCS for breaking dormancy resulted in the germination of seeds from A. pubescens, C. virosa, and I. setosa. These findings indicate that these three species exhibit non‐deep simple MPD. Furthermore, variable‐temperature stratification, but not GA soaking, successfully broke the dormancy of I. laevigata, indicating that this species has deep simple MPD. Although CS was less effective than GA treatment, it uniquely increased seed germination percentage in P. grandiflora, clearly indicating that this species has intermediate PD. Dry storage and GA treatment was effective in breaking the dormancy of the remaining eight species, demonstrating that these species have non‐deep PD. Therefore, the findings support our first hypothesis.

4.2. Effect of dormancy‐breaking treatment and seed traits on seed germination

Contrary to our second hypothesis, a strength hierarchy of dormancy breaking: CS > GA > WCS > GA + CS > D > GA + WCS was found in the study (by comparing the average germination percentage on the 28th day of 15 species among different treatments). Compared with the control, both single treatments including GA, CS, and WCS and combined treatments including GA + CS and GA + WCS, increased seed germination percentage. However, GA + WCS treatment also increased the possibility of fungal growth A. pubescens seeds, indicating a negative effect of the combined treatment. Varied‐temperature stratification is commonly used for the species with MPD, as it can promote morphologically and physiologically the after‐ripening of seeds to fully developed embryos (Baskin & Baskin, 2014). The mechanism behind may be that CS in varied‐temperature stratification breaks epicotyl dormancy, while warm stratification breaks radicle dormancy (Zhang, Pan, et al., 2022). However, in our experiment, this treatment inhibited seed germination in H. longistylum, Lyc. uniflorus, Lys. thyriflora and S. salicifolia, probably because of the absence of MPD or the presence of conditional dormancy (the transitional state between dormancy and nondormancy). CS treatment significantly increased germination percentage and reduced the mean germination time for all species, similar to the findings by Poschlod (1990) and Fernández‐Pascual et al. (2021). This phenomenon occurs because low temperature during winter can break dormancy, and subsequent soil warming functions as a cue to stimulate germination (Finch‐Savage & Footitt, 2017). Additionally, in this study, the GA treatment applied included sulfuric acid pretreatment, which caused some mechanical damage to the seed coat, resulting in increased permeability and removal of potential PD. Although all studied species had permeable seed coat, there were variations in their response to GA across species. This treatment reduced germination percentages of the seeds with thin seed coat such as S. salicifolia and Lyt. salicaria, but increased germination percentage of the seeds whose coat is thick and with poor permeability like H. longistylum and V. uliginosum.

4.3. Effect of monocot/eudicot divergence, seed size, and E: S ratio on seed germination

The results revealed that the seed size, monocot/eudicot divergence, and E:S ratio had significant effects on seed germination behavior. In particular, seed size was negatively correlated with germination percentage, which confirmed hypothesis 3. The monocotyledonous species with no embryos or undeveloped embryos in seeds, such as I. laevigata, I. setosa, C. limosa, and S. palustris. These species all producing big seeds, showed increased seed germination percentage after WCS, GA + CS, or GA + WCS. Conversely, the eudicotyledonous species with fully developed embryo or no endosperm, such as Lob. sessilifolia, Lyc. uniflorus, Lyt. Salicaria, and S. salicifolia, all producing small seeds, could germinate without dry storage or CS.

In our study, compared with the seeds of some eudicotyledonous species without endosperm, monocotyledonous seeds with endosperm require a longer time to provide nutrients to the growth of the embryo, resulting in a faster germination percentage of eudicotyledonous seeds than monocotyledonous seeds (Zhao et al., 2021). Similarly, in a study of 570 species of alpine meadows in the eastern Qinghai‐Tibet Plateau, a negative correlation between seed germination percentage and seed mass was also observed (Bu et al., 2007). This is because the seedlings produced by small seeds are smaller, and the rapid germination strategy allows them to enter the seedling growth stage earlier, giving them a shorter time to survive the fragile seedling period, which provides them with the temporal and spatial advantage over competing with seedlings produced by large seeds (Grime, 2002). Large seeds, however, have thicker seed coats, which are physically difficult for radicles to penetrate through, and their larger endosperm provides them with enough nutrients to survive adverse environmental conditions, so they germinate less and more slowly.

4.4. Seed germination and environmental factors

Dormancy status is strongly influenced by environmental factors such as temperature (e. g. Fernández‐Pascual et al., 2013; Finch‐Savage & Footitt, 2017; Zhang, Liu, et al., 2022), precipitation (Rosbakh et al., 2023; Zhang, Liu, et al., 2022), elevation (Chen et al., 2023; Ooi et al., 2012; Rosbakh et al., 2022), latitude (Rosbakh et al., 2023; Rubio de Casas et al., 2017; Zhang, Liu, et al., 2022), etc. Our analysis revealed that seed germination percentage was positively correlated with WTD but negatively correlated with habitat pH, annual precipitation, annual mean temperature, temperature seasonality, and precipitation seasonality, this confirms our hypothesis 4. These findings suggest that differences in dormancy are also associated with environmental change. For example, water table fluctuation may affect spore germinationability (Feng et al., 2017; Bu et al., 2017) and increase spore dormancy in Sphagnum (Fan et al., 2023). In our study, both WTD and pH are with small span, 5–19 cm for the former and 5.3–6.1 for the latter. Hence, we speculate that this trend would be more pronounced if more types of peatlands such as bogs and rich fens were included since the spans of both WTD and pH would be highly expanded.

Seed dormancy is an effective way to delay germination until environmental conditions become benign (Pausas et al., 2022; Zhang, Liu, et al., 2022). Rosbakh et al. (2023) showed that the annual range of temperature and precipitation seasonality had a significant effect on PD. Our study showed that seasonality seemed to lead the seeds to wait for suitable hydrothermal conditions to break dormancy and then germinate. However, in several species, release from dormancy is completed only after the seeds have been exposed to fluctuating temperatures (Chia et al., 2016). Similar to the finding of a recent study (Jiménez‐Alfaro et al., 2018), our study also demonstrated that annual mean temperature was less important than annual precipitation, and the areas with low precipitation and a deeper WTD were more suitable for seed germination.

4.5. Seed dormancy types and phylogeny of plants

Baskin and Baskin (2014) indicated that many species of Apiaceae have underdeveloped linear embryos surrounded by endosperm and their seeds therefore demonstrate typical MD. Morphophysiological dormancy (MPD) exists in most plants of the genus Angelica and the dormancy can be broken by CS (Baskin & Baskin, 2014), consistent with the results of A. pubescens in this study.

Mechanical resistance of the seed coat is the main cause of dormancy in Iris spp. (Blumenthal et al., 1986), and that dormancy in I. setosa is closely related to the presence of germination inhibitors in the endosperm (Lu et al., 2008). A study by Holloway (1987) on I. setosa showed that the seed germination percentage was the highest when GA3 and CS were combined used. Diao and Gao (2006) observed that GA treatment did not, but CS significantly did increase the germination percentages of Iris seeds, fully demonstrating the better effect of natural stratification than GA, which is supported by the results of our study.

Among the species with seed PD in this study, Lyt. salicaria, whose seeds were found to germinate rapidly at all six treatments, had the highest seed germination percentage after dry storage, indicating that this species has low environmental requirements for germination. High seed production, great dispersal ability due to small mass and high growth rate of seedlings (Shipley & Parent, 1991) and extremely long‐term persistent soil seed bank (>50 years) (Poschlod, 1993) are important reasons why this species has flourished in many habitats and even becomes an invasive species (Goodell & Parker, 2017). In addition, Lobelia seeds may exhibit MPD, MD (Baskin et al., 2020) or PD (Ronnenberg et al., 2008). This diversity of dormancy types may reflect the diverse selection pressures the plants of the genus has faced during evolution.

5. CONCLUSIONS

In summary, out of the 15 tested peatland species in the study, 13 species clearly showed dormancy. Among them, eight species exhibited non‐deep PD, one species showed intermediate PD, and four species demonstrated MPD, suggesting that non‐deep PD of seeds is common in the temperate Asian montane peatland ecosystem. Overall the effect hierarchy of breaking dormancy is CS > GA > WCS > GA + CS > D > GA + WCS, in which CS and GA are time‐saving treatments in breaking seed dormancy of peatland plants in the Changbai Mountains. Our study suggests that physiological dormancy of seeds is a common adaptation strategy for the temperate montane peatland plants, allowing them to cope with the strong seasonality. Both seed traits (e.g. E:S ratio and seed size) and abiotic environmental factors (e.g. WTD, pH, annual precipitation, annual mean temperature, temperature seasonality and precipitation seasonality) are related to germination behavior. Therefore, once seed dormancy being broken by low temperature in winter, the peatland plants can realize effective recruitment by seed germination and consequently seedling establishment in spring or early summer.

AUTHOR CONTRIBUTIONS

Jian‐Yi Wang: Conceptualization (equal); data curation (lead); formal analysis (lead); investigation (equal); methodology (lead); visualization (lead); writing – original draft (equal); writing – review and editing (equal). Zhao‐Jun Bu: Conceptualization (equal); funding acquisition (lead); investigation (equal); methodology (equal); project administration (lead); writing – original draft (equal); writing – review and editing (supporting). Peter Poschlod: Writing – review and editing (supporting). Shuayib Yusup: Formal analysis (equal); writing – original draft (supporting). Jia‐Qi Zhang: Formal analysis (equal). Zheng‐Xiang Zhang: Conceptualization (equal); writing – review and editing (supporting).

FUNDING INFORMATION

The National Nature Science Foundation of China (Nos. U23A2003, 42,371,050 and 41,871,046) and Jilin Provincial Science and Technology Development Project (Nos. 20210402032GH and 20230203002SF).

CONFLICT OF INTEREST STATEMENT

The authors declare no conflict of interest.

Supporting information

Appendix S1

Appendix S2

ECE3-14-e11671-s002.tif (11.2MB, tif)

Appendix S3

ECE3-14-e11671-s001.docx (17.6KB, docx)

Appendix S4

ECE3-14-e11671-s003.tif (15.1MB, tif)

ACKNOWLEDGEMENTS

We are appreciated for Sha‐Sha Liu's assistance in the lab work. We sincerely thank the anonymous reviewers who gave their helpful comments to greatly improve our former manuscript.

Wang, J.‐Y. , Bu, Z.‐J. , Poschlod, P. , Yusup, S. , Zhang, J.‐Q. , & Zhang, Z.‐X. (2024). Seed dormancy types and germination response of 15 plant species in temperate montane peatlands. Ecology and Evolution, 14, e11671. 10.1002/ece3.11671

Contributor Information

Zhao‐Jun Bu, Email: buzhaojun@nenu.edu.cn.

Zheng‐Xiang Zhang, Email: zhangzx040@nenu.edu.cn.

DATA AVAILABILITY STATEMENT

The data that support the findings of this study are available in Dryad at: https://doi.org/10.5061/dryad.dz08kps4x.

REFERENCES

  1. Baskin, C. C. , & Baskin, J. M. (2014). Seeds: Ecology, biogeography and evolution of dormancy and germination (2nd ed.). Academic Press. [Google Scholar]
  2. Baskin, C. C. , & Baskin, J. M. (2020). Breaking seed dormancy during dry storage: A useful tool or major problem for successful restoration via direct seeding? Plants, 9(5), 636. [DOI] [PMC free article] [PubMed] [Google Scholar]
  3. Baskin, C. C. , Baskin, J. M. , Yoshinaga, A. , & Thompson, K. (2005). Germination of drupelets in multi‐seeded drupes of the shrub Leptecophylla tameiameiae (Ericaceae) from Hawaii: A case for deep physiological dormancy broken by high temperatures. Seed Science Research, 15(4), 349–356. [Google Scholar]
  4. Baskin, C. C. , Baskin, J. M. , Yoshinaga, A. , & Wolkis, D. (2020). Seed dormancy in Campanulaceae: Morphological and morphophysiological dormancy in six species of Hawaiian lobelioids . Botany, 98(6), 327–332. [Google Scholar]
  5. Baskin, J. M. , & Baskin, C. C. (1989). Seed germination ecophysiology of Jeffersonia diphylla, a perennial herb of mesic deciduous forests. American Journal of Botany, 76(7), 1073–1080. [Google Scholar]
  6. Baskin, J. M. , & Baskin, C. C. (2004). A classification system for seed dormancy. Seed Science Research, 14(1), 1–16. [Google Scholar]
  7. Blumenthal, A. , Lerner, H. R. , Werker, E. , & Poljakoff‐Mayber, A. (1986). Germination preventing mechanisms in Iris seeds. Annals of Botany, 58(4), 551–561. [Google Scholar]
  8. Bourgeois, B. , Lemay, M. A. , Landry, T. , Rochefort, L. , & Poulin, M. (2019). Seed storage behaviour of eight peatland pool specialists: Implications for restoration. Aquatic Botany, 152, 59–63. [Google Scholar]
  9. Bu, H. Y. , Chen, X. L. , Xu, X. L. , Liu, K. , Jia, P. , & Du, G. Z. (2007). Seed mass and germination in an alpine meadow on the eastern Tsinghai–Tibet plateau. Plant Ecology, 191(1), 127–149. [Google Scholar]
  10. Bu, Z. J. , Rydin, H. , & Chen, X. (2011). Direct and interaction‐mediated effects of environmental changes on peatland bryophytes. Oecologia, 166, 555–563. [DOI] [PubMed] [Google Scholar]
  11. Bu, Z. J. , Sundberg, S. , Feng, L. , Li, H. K. , Zhao, H. Y. , & Li, H. C. (2017). The methuselah of plant diaspores: Sphagnum spores can survive in nature for centuries. New Phytologist, 214(4), 1398–1402. [DOI] [PubMed] [Google Scholar]
  12. Carta, A. , Fernández‐Pascual, E. , Gioria, M. , Müller, J. V. , Rivière, S. , Rosbakh, S. , Saatkamp, A. , Vandelook, F. , & Mattana, E. (2022). Climate shapes the seed germination niche of temperate flowering plants: A meta‐analysis of European seed conservation data. Annals of Botany, 129(7), 775–786. [DOI] [PMC free article] [PubMed] [Google Scholar]
  13. Chen, J. Z. , Huang, X. L. , Xiao, X. F. , Liu, J. M. , Liao, X. F. , Sun, Q. W. , Peng, L. , & Zhang, L. (2022). Seed dormancy release and germination requirements of Cinnamomum migao, an endangered and rare woody plant in southwest China. Frontiers in Plant Science, 13, 770940. [DOI] [PMC free article] [PubMed] [Google Scholar]
  14. Chen, K. , Chen, Z. H. , Huang, Y. Y. , & Jiang, Z. H. (2023). Elevation and phylogeny shape herbaceous seed dormancy in a biodiversity hotspot of southwest China. Ecology and Evolution, 13(4), e9986. [DOI] [PMC free article] [PubMed] [Google Scholar]
  15. Chen, S. Y. , Kuo, S. R. , & Chien, C. T. (2008). Roles of gibberellins and abscisic acid in dormancy and germination of red bayberry (Myrica rubra) seeds. Tree Physiology, 28(9), 1431–1439. [DOI] [PubMed] [Google Scholar]
  16. Cheng, Y. , Liu, H. , Wang, H. , Piao, S. , Yin, Y. , Ciais, P. , Wu, X. , Luo, Y. , Zhang, C. , Song, Y. , Gao, Y. , & Qiu, A. (2017). Contrasting effects of winter and summer climate on alpine timberline evolution in monsoon‐dominated East Asia. Quaternary Science Reviews, 169(1), 278–287. [Google Scholar]
  17. Chia, K. A. , Sadler, R. , Turner, S. R. , & Baskin, C. C. (2016). Identification of the seasonal conditions required for dormancy break of Persoonia longifolia (Proteaceae), a species with a woody indehiscent endocarp. Annals of Botany, 118(2), 331–346. [DOI] [PMC free article] [PubMed] [Google Scholar]
  18. Chien, C. T. , Chen, S. Y. , Tsai, C. C. , Baskin, J. M. , Baskin, C. C. , & Kuo‐Huang, L. L. (2011). Deep simple epicotyl morphophysiological dormancy in seeds of two Viburnum species, with special reference to shoot growth and development inside the seed. Annals of Botany, 108(1), 13–22. [DOI] [PMC free article] [PubMed] [Google Scholar]
  19. De Vitis, M. , Mondoni, A. , Pritchard, H. W. , Laverack, G. , & Bonomi, C. (2019). Native seed ecology, production & policy—Advancing knowledge and technology in Europe. MUSE, Museo delle Scienze di Trento. [Google Scholar]
  20. Diao, X. H. , & Gao, Y. K. (2006). Study on dormancy and germination of four Iris species seeds. Seed, 25(4), 41–44. [Google Scholar]
  21. Fan, B. B. , Yusup, S. , Sundberg, S. , Chen, Y. D. , Qiao, H. X. , Liu, S.‐S. , & Bu, Z. J. (2023). Dry/wet cycling reduces spore germination and viability in six peatland bryophytes. Plant Biology, 25(3), 440–447. [DOI] [PubMed] [Google Scholar]
  22. Feng, L. , Sundberg, S. , Ooi, M. K. , Wu, Y. H. , Wang, M. , & Bu, Z. J. (2018). Oxygen‐deficiency and allelochemicals affect Sphagnum spore persistence in peatlands. Plant and Soil, 432, 403–413. [Google Scholar]
  23. Feng, L. , Bu, Z. J. , Mallik, A. , Wang, Z. C. , Liu, S. S. , & Wu, Y. H. (2017). Continuous waterlogging may not facilitate germinability maintenance of Sphagnum spores. Wetlands, 37, 1015–1022. [Google Scholar]
  24. Fenner, M. , & Thompson, K. (2005). The ecology of seeds. Cambridge University Press. [Google Scholar]
  25. Fernández‐Pascual, E. (2016). Comparative seed germination traits in bog and fen mire wetlands. Aquatic Botany, 130, 21–26. [Google Scholar]
  26. Fernández‐Pascual, E. , Jiménez‐Alfaro, B. , & Díaz, T. E. (2013). The temperature dimension of the seed germination niche in fen wetlands. Plant Ecology, 214, 489–499. [Google Scholar]
  27. Fernández‐Pascual, E. , Carta, A. , Mondoni, A. , Cavieres, L. A. , Rosbakh, S. , Venn, S. , Satyanti, A. , Guja, L. , Briceño, V. F. , Vandelook, F. , Mattana, E. , Saatkamp, A. , Bu, H. , Sommerville, K. , Poschlod, P. , Liu, K. , Nicotra, A. , & Jiménez‐Alfaro, B. (2021). The seed germination spectrum of alpine plants: A global meta‐analysis. New Phytologist, 229(6), 3573–3586. [DOI] [PubMed] [Google Scholar]
  28. Fernández‐Pascual, E. , Vaz, M. , Morais, B. , Reiné, R. , Ascaso, J. , Afif Khouri, E. , & Carta, A. (2022). Seed ecology of European mesic meadows. Annals of Botany, 129(2), 121–134. [DOI] [PMC free article] [PubMed] [Google Scholar]
  29. Finch‐Savage, W. E. , & Footitt, S. (2017). Seed dormancy cycling and the regulation of dormancy mechanisms to time germination in variable field environments. Journal of Experimental Botany, 68(4), 843–856. [DOI] [PubMed] [Google Scholar]
  30. Finch‐Savage, W. E. , & Leubner‐Metzger, G. (2006). Seed dormancy and the control of germination. New Phytologist, 171(3), 501–523. [DOI] [PubMed] [Google Scholar]
  31. Footitt, S. , Douterelo‐Soler, I. , Clay, H. , & Finch‐Savage, W. E. (2011). Dormancy cycling in Arabidopsis seeds is controlled by seasonally distinct hormone‐signaling pathways. Proceedings of the National Academy of Sciences of the United States of America, 108(50), 20236–20241. [DOI] [PMC free article] [PubMed] [Google Scholar]
  32. Gama‐Arachchige, N. S. , Baskin, J. M. , Geneve, R. L. , & Baskin, C. C. (2012). The autumn effect: Timing of physical dormancy break in seeds of two winter annual species of Geraniaceae by a stepwise process. Annals of Botany, 110(3), 637–651. [DOI] [PMC free article] [PubMed] [Google Scholar]
  33. Gioria, M. , Pyšek, P. , Baskin, C. C. , & Carta, A. (2020). Phylogenetic relatedness mediates persistence and density of soil seed banks. Journal of Ecology, 108(5), 2121–2131. [Google Scholar]
  34. Goodell, K. , & Parker, I. M. (2017). Invasion of a dominant floral resource: Effects on the floral community and pollination of native plants. Ecology, 98(1), 57–69. [DOI] [PubMed] [Google Scholar]
  35. Grime, J. P. (2002). Plant strategies, vegetation processes, and ecosystem properties. John Wiley & Sons. [Google Scholar]
  36. Hao, H. P. , He, Z. , Li, H. , Shi, L. , & Tang, Y. D. (2014). Effect of root length on epicotyl dormancy release in seeds of Paeonia ludlowii, Tibetan peony. Annals of Botany, 113(3), 443–452. [DOI] [PMC free article] [PubMed] [Google Scholar]
  37. Hashemirad, S. , Soltani, E. , Darbandi, A. I. , & Alahdadi, I. (2023). Cold stratification requirement to break morphophysiological dormancy of fennel (Foeniculum vulgare Mill.) seeds varies with seed length. Journal of Applied Research on Medicinal and Aromatic Plants, 35, 100465. [Google Scholar]
  38. Herranz, J. M. , Copete, M. A. , Ferrandis, P. , & Copete, E. (2010). Intermediate complex morphophysiological dormancy in the endemic Iberian Aconitum napellus subsp. castellanum (Ranunculaceae). Seed Science Research, 20(2), 109–121. [Google Scholar]
  39. Holloway, P. S. (1987). Seed germination of Alaska Iris, Iris setosa ssp. interior. HortScience, 22(5), 898–899. [Google Scholar]
  40. ISTA . (2007). International rules for seed testing (Vol. 133, pp. 1–65). ISTA News Bulletin. [Google Scholar]
  41. Jayasuriya, K. G. , Baskin, J. M. , Geneve, R. L. , Baskin, C. C. , & Chien, C. T. (2008). Physical dormancy in seeds of the holoparasitic angiosperm Cuscuta australis (Convolvulaceae, Cuscuteae): Dormancy‐breaking requirements, anatomy of the water gap and sensitivity cycling. Annals of Botany, 102(1), 39–48. [DOI] [PMC free article] [PubMed] [Google Scholar]
  42. Jensen, K. (2004). Dormancy patterns, germination ecology, and seed‐bank types of twenty temperate fen grassland species. Wetlands, 24(2), 152–166. [Google Scholar]
  43. Jiménez‐Alfaro, B. , Suárez‐Seoane, S. , Chytrý, M. , Hennekens, S. M. , Willner, W. , Hájek, M. , Agrillo, E. , Álvarez‐Martínez, J. M. , Bergamini, A. , Brisse, H. , Brunet, J. , Casella, L. , Dítě, D. , Font, X. , Gillet, F. , Hájková, P. , Jansen, F. , Jandt, U. , Kącki, Z. , … Tsiripidis, I. (2018). Modelling the distribution and compositional variation of plant communities at the continental scale. Diversity and Distributions, 24(7), 978–990. [Google Scholar]
  44. Jurado, E. , & Flores, J. (2005). Is seed dormancy under environmental control or bound to plant traits? Journal of Vegetation Science, 16(5), 559–564. [Google Scholar]
  45. Lamont, B. B. , & Pausas, J. G. (2023). Seed dormancy revisited: Dormancy‐release pathways and environmental interactions. Functional Ecology, 37(4), 1106–1125. [Google Scholar]
  46. Li, L. , Yu, P. , Li, Q. , & Gu, M. (2022). Gibberellic acid and cold stratification improve sparkleberry (Vaccinium arboreum) germination under different collection times. Scientia Horticulturae, 291, 110606. [Google Scholar]
  47. Liu, C. P. , Chen, S. Y. , Baskin, C. C. , & Chien, C. T. (2023). Non‐deep simple and deep simple morphophysiological dormancy in seeds of three species of Ilex from subtropical and tropical regions of Taiwan. Seed Science Research, 33(1), 50–57. [Google Scholar]
  48. Liu, G.‐h. , Zhou, J. , Li, W. , & Cheng, Y. (2005). The seed bank in a subtropical freshwater marsh: Implications for wetland restoration. Aquatic Botany, 81(1), 1–11. [Google Scholar]
  49. Long, R. L. , Gorecki, M. J. , Renton, M. , Scott, J. K. , Colville, L. , Goggin, D. E. , Commander, L. E. , Westcott, D. A. , Cherry, H. , & Finch‐Savage, W. E. (2015). The ecophysiology of seed persistence: A mechanistic view of the journey to germination or demise. Biological Reviews, 90(1), 31–59. [DOI] [PubMed] [Google Scholar]
  50. Lu, T. T. , Zhang, J. Z. , Sun, G. F. , Li, X. D. , Jiang, C. D. , & Yu, X. B. (2008). Dormancy causes of the seeds of four species of wild apogons Iris in China. Acta Horticulturae Sinica, 35(2), 1497–1504. [Google Scholar]
  51. Merritt, D. J. , Turner, S. R. , Clarke, S. , & Dixon, K. W. (2007). Seed dormancy and germination stimulation syndromes for Australian temperate species. Australian Journal of Botany, 55(3), 336–344. [Google Scholar]
  52. Ooi, M. K. , Auld, T. D. , & Denham, A. J. (2012). Projected soil temperature increase and seed dormancy response along an altitudinal gradient: Implications for seed bank persistence under climate change. Plant and Soil, 353(1), 289–303. [Google Scholar]
  53. Pausas, J. G. , Lamont, B. B. , Keeley, J. E. , & Bond, W. J. (2022). Bet‐hedging and best‐bet strategies shape seed dormancy. New Phytologist, 236(4), 1232–1236. [DOI] [PMC free article] [PubMed] [Google Scholar]
  54. Phartyal, S. S. , Kondo, T. , Baskin, J. M. , & Baskin, C. C. (2009). Temperature requirements differ for the two stages of seed dormancy break in Aegopodium podagraria (Apiaceae), a species with deep complex morphophysiological dormancy. American Journal of Botany, 96(6), 1086–1095. [DOI] [PubMed] [Google Scholar]
  55. Poschlod, P. (1990). Vegetationsentwicklung in abgetorften Hochmooren des bayerischen Alpenvorlandes unter besonderer Berücksichtigung standortskundlicher und populationsbiologischer Faktoren. In Dissertationes botanicae (Vol. 152, p. 331). Bornträger. [Google Scholar]
  56. Poschlod, P. (1993). Untersuchungen zur Dynamik und Dauerhaftigkeit der Diasporenbank gefährdeter Lebensräume und deren Bedeutung für den Arten‐ und Biotopschutz am Beispiel von Kalkmagerrasen und Ufer‐ und Schlammbodenfluren [Habilitation thesis]. University of Hohenheim, Germany.
  57. Rees, M. (1993). Trade‐offs among dispersal strategies in British plants. Nature, 366(6451), 150–152. [Google Scholar]
  58. Rees, M. (1996). Evolutionary ecology of seed dormancy and seed size. Philosophical Transactions of the Royal Society of London. Series B: Biological Sciences, 351(1345), 1299–1308. [Google Scholar]
  59. Ronnenberg, K. , Wesche, K. , & Hensen, I. (2008). Germination ecology of central Asian Stipa spp.: Differences among species, seed provenances, and the importance of field studies. Plant Ecology, 196, 269–280. [Google Scholar]
  60. Rosbakh, S. , Carta, A. , Fernández‐Pascual, E. , Phartyal, S. S. , Dayrell, R. L. , Mattana, E. , Saatkamp, A. , Vandelook, F. , Baskin, J. , & Baskin, C. (2023). Global seed dormancy patterns are driven by macroclimate but not fire regime. New Phytologist, 240(2), 555–564. [DOI] [PubMed] [Google Scholar]
  61. Rosbakh, S. , Chalmandrier, L. , Phartyal, S. , & Poschlod, P. (2022). Inferring community assembly processes from functional seed trait variation along elevation gradient. Journal of Ecology, 110(10), 2374–2387. [Google Scholar]
  62. Rosbakh, S. , Hülsmann, L. , Weinberger, I. , Bleicher, M. , & Poschlod, P. (2019). Bleaching and cold stratification can break dormancy and improve seed germination in Cyperaceae. Aquatic Botany, 158, 103128. [Google Scholar]
  63. Rosbakh, S. , Phartyal, S. S. , & Poschlod, P. (2020). Seed germination traits shape community assembly along a hydroperiod gradient. Annals of Botany, 125(1), 67–78. [DOI] [PMC free article] [PubMed] [Google Scholar]
  64. Rubio de Casas, R. , Willis, C. G. , Pearse, W. D. , Baskin, C. C. , Baskin, J. M. , & Cavender‐Bares, J. (2017). Global biogeography of seed dormancy is determined by seasonality and seed size: A case study in the legumes. New Phytologist, 214(4), 1527–1536. [DOI] [PubMed] [Google Scholar]
  65. Rydin, H. , & Jeglum, J. K. (2013). The biology of peatlands (2nd ed.). Oxford University Press. [Google Scholar]
  66. Saatkamp, A. , Poschlod, P. , & Venable, D. L. (2014). The functional role of soil seed banks in natural communities. In Gallagher R. S. (Ed.), Seeds: The ecology of regeneration in plant communities (pp. 263–295). CABI. [Google Scholar]
  67. Schütz, W. (1997). Primary dormancy and annual dormancy cycles in seeds of six temperate wetland sedges. Aquatic Botany, 59, 75–85. [Google Scholar]
  68. Scholten, M. , Donahue, J. , Shaw, N. L. , & Serpe, M. D. (2009). Environmental regulation of dormancy loss in seeds of Lomatium dissectum (Apiaceae). Annals of Botany, 103(7), 1091–1101. [DOI] [PMC free article] [PubMed] [Google Scholar]
  69. Shipley, B. , & Parent, M. (1991). Germination responses of 64 wetland species in relation to seed size, minimum time to reproduction and seedling relative growth rate. Functional Ecology, 5(1), 111–118. [Google Scholar]
  70. Sundberg, S. , & Rydin, H. (2000). Experimental evidence for a persistent spore bank in Sphagnum. New Phytologist, 148(1), 105–116. [DOI] [PubMed] [Google Scholar]
  71. Thompson, K. , & Grime, J. P. (1979). Seasonal variation in the seed banks of herbaceous species in ten contrasting habitats. Journal of Ecology, 67(3), 893–921. [Google Scholar]
  72. van Breemen, N. (1995). How Sphagnum bogs down other plants. Trends in Ecology & Evolution, 10(7), 270–275. [DOI] [PubMed] [Google Scholar]
  73. Walck, J. L. , & Hidayati, S. N. (2004). Germination ecophysiology of the western North American species Osmorhiza depauperata (Apiaceae): Implications of preadaptation and phylogenetic niche conservatism in seed dormancy evolution. Seed Science Research, 14(4), 387–394. [Google Scholar]
  74. Wang, J. , Baskin, J. M. , Baskin, C. C. , Liu, G. , Yang, X. , & Huang, Z. (2017). Seed dormancy and germination of the medicinal holoparasitic plant Cistanche deserticola from the cold desert of northwest China. Plant Physiology and Biochemistry, 115, 279–285. [DOI] [PubMed] [Google Scholar]
  75. Wheeler, B. D. , & Proctor, M. C. F. (2000). Ecological gradients, subdivisions and terminology of north‐west European mires. Journal of Ecology, 88(2), 187–203. [Google Scholar]
  76. Yi, B. , Lu, F. , Sundberg, S. , Wu, J. , Yu, Z. , Wu, Z. , Wang, M. , & Bu, Z. J. (2024). Effects of nitrogen and phosphorus additions on nitrous oxide fluxes in a peatland in NE China. Plant and Soil, 1–16. [Google Scholar]
  77. Zhang, K. , Pan, H. , Baskin, C. C. , Baskin, J. M. , Xiong, Z. , Cao, W. , Yao, L. J. , Tang, B. , Zhang, C. N. , & Tao, J. (2022). Epicotyl morphophysiological dormancy in seeds of Paeonia ostii (Paeoniaceae): Seasonal temperature regulation of germination phenology. Environmental and Experimental Botany, 194, 104742. [Google Scholar]
  78. Zhang, K. , Zhang, Y. , Walck, J. L. , & Tao, J. (2019). Non‐deep simple morphophysiological dormancy in seeds of Angelica keiskei (Apiaceae). Scientia Horticulturae, 255, 202–208. [Google Scholar]
  79. Zhang, Y. Z. , Liu, Y. , Sun, L. , Baskin, C. C. , Baskin, J. M. , Cao, M. , & Yang, J. (2022). Seed dormancy in space and time: Global distribution, paleoclimatic and present climatic drivers, and evolutionary adaptations. New Phytologist, 234(5), 1770–1781. [DOI] [PubMed] [Google Scholar]
  80. Zhao, M. , Liu, Z. , Zhang, H. , Wang, Y. , & Yan, H. (2021). Germination characteristics is more associated with phylogeny‐related traits of species in a salinized grassland of northeastern China. Frontiers in Ecology and Evolution, 9, 748038. [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Appendix S1

Appendix S2

ECE3-14-e11671-s002.tif (11.2MB, tif)

Appendix S3

ECE3-14-e11671-s001.docx (17.6KB, docx)

Appendix S4

ECE3-14-e11671-s003.tif (15.1MB, tif)

Data Availability Statement

The data that support the findings of this study are available in Dryad at: https://doi.org/10.5061/dryad.dz08kps4x.


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