Journal of Vegetation Science && (2012) Frost as a limiting factor for recruitment and establishment of early development stages in an alpine glacier foreland? Silvia Marcante, Angela Sierra-Almeida, Joachim P. Spindelböck, Brigitta Erschbamer & Gilbert Neuner Keywords adults; alpine plant species; chronosequence; freezing stress; juveniles; plantlets; primary succession; seeds and seedlings Nomenclature Fischer et al. (2005). Abstract Questions: How frost resistant are the early development stages (seeds, seedlings, plantlets and juveniles) of alpine plant species? Do summer frosts impair establishment of plant species typical of different successional stages on a central alpine glacier foreland? Location: Rotmoos glacier foreland, Austrian Central Alps (Obergurgl, Tyrol, Received 20 December 2010 Accepted 7 February 2012 Co-ordinating Editor: Francesco de Bello Marcante, S. (corresponding author, [email protected]), Erschbamer, B. ([email protected]) & Neuner, G. ([email protected]): lnstitute of Botany, University of Innsbruck, Sternwartestrasse 15, 6020, Innsbruck, Austria Sierra-Almeida A. ([email protected]): ECOBIOSIS, Departamento de Botânica, Universidad de Concepcion, Concepcion, Chile Spindelböck, J.P. (Joachim.Spindelbock@ hisf.no): Faculty of Science, Sogn og Fjordane University College, PO Box 133, N-6851, Sogndal, Norway Austria). Methods: Seeds of 12 species typical of different successional stages were collected in the glacier foreland and either sown directly in the field or in a growth chamber (25/10 °C, 16/8 h) and grown to the investigated development stages. Frost resistance of the early development and adult stages was determined by exposing them to a set of freezing temperatures and assessing viability with the tetrazolium test (LT50, i.e. 50% of samples being lethally frost damaged). Results: Dry seeds had the highest frost resistance (LT50: 19 °C), followed by wet seeds after imbibition (LT50: 8 °C). With the onset of germination, frost resistance decreased rapidly. While germinated seeds tolerated a mean of 3.2 ° C, seedlings and juveniles were less frost resistant (LT50: 2.5 °C). Along the primary succession, seedlings of pioneer species were significantly less frost resistant than early- and late-successional species. However, field grown seedlings, mainly of pioneer species, showed higher frost resistance (mean: 5 °C) than the growth chamber seedlings (mean: 3 °C), indicating that frost hardening (transition from a lower to a higher level of frost resistance) is already possible during these early stages of development. Conclusions: The low frost resistance during and after germination may not suffice to survive summer frosts and may at least in certain years explain the high seedling mortality rates recognized in the glacier foreland. Introduction Establishment of plants in the glacier forelands proceeds slowly and is often fragmentary. Although a considerable number of seeds germinate (Niederfriniger Schlag & Erschbamer 2000; Marcante et al. 2009a), species establish only at low rates due to high seedling mortality (Welling et al. 2005; Erschbamer et al. 2008; Marcante et al. 2009b). These high seedling mortality rates supposedly depend on extreme low temperatures and water shortage caused by rapid drainage of water through the undeveloped soils (Körner 2003). Freezing temperatures during the growing season could be the dominant factor, particularly if frost resistance in the early development stages of plants is insufficient. On recently deglaciated terrain, germination takes place on the surface of the bare ground. The surface is particularly prone to low temperature extremes during the night, and additionally, this area is also exposed to cooling winds coming from the glacier and from the side slopes (Hoinkes 1955; Tackenberg & Stöcklin 2008). At the elevation of glacier forelands in the Austrian Central Alps long-term bioclimatic temperature records indicate that freezing temperatures down to 5 °C can occur throughout the Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science 1 Does frost limit recruitment and establishment on a glacier foreland? whole growing period (Larcher et al. 2010). Field observations indicate that summer frost events damage adult alpine plants at temperatures between 3.0 and 10.8 °C in summer (Taschler & Neuner 2004). A substantial fraction of their above-ground tissues can be lost during such freezing events, although the plants can survive if undamaged below-ground organs have developed (Körner 2003; Taschler & Neuner 2004; Neuner & Hacker 2010). However, to the best of our knowledge, there is a lack of information on the frost resistance of early development stages of alpine plants, such as germinating seeds, seedlings, juveniles and of vegetative dispersal units such as plantlets. As far as we know, only one preliminary study has addressed this point. This study, investigating four alpine plants, suggests that frost resistance of early development stages (Maria Wildner-Eccher and Walter Larcher, unpublished data) is lower than for adults, leading to a higher risk of being damaged by frosts. Additionally, restoration after frost damage of above-ground plant parts is less likely to occur during early development stages as such plants lack a sufficiently large below-ground biomass. Growing plant tissues are known to be particularly frost susceptible, and their frost hardening potential, i.e. the reversible transition from a lower to a higher level of frost resistance upon exposure to triggering environmental conditions, is also limited (Taschler et al. 2004; Neuner & Beikircher 2010; Hacker et al. 2011). Tissue growth processes are dominant during early plant development and might affect frost hardening. Moreover, we hypothesized that field-grown seedlings may possess a higher frost resistance than seedlings cultivated in a growth chamber, as the natural environmental conditions may force them to become frost hardened. As far as we know, little if anything, is known about the frost hardening potential during early stages of plant development. As for seedlings, plantlets and bulbils from viviparous and pseudo-viviparous species such as Poa alpina and Persicaria vivipara are released from the mother plants at a very sensitive stage. It is recognized that the production of P. alpina plantlets is governed by temperature (Heide 1989): they are produced under harsh conditions, whereas propagation by seed seems to prevail under more benign conditions. As plantlets are largely responsible for maintaining plant populations in the pioneer stages (Marcante et al. 2009b; Winkler et al. 2010), we hypothesized that they may also have a higher frost resistance than seedlings. Our general hypothesis is that frost could be a limiting factor for the colonization of open areas in alpine glacier forelands due to frost damage that can affect imbibed seeds, seedlings, juveniles or plantlets. Along the successional gradient of a glacier foreland, a temperature gradient exists, with soil surface temperatures during the growing 2 S. Marcante et al. season of 7.5–9.0 °C at the 35-yr ice-free sites to 10.5– 12.0 °C at the oldest ice-free sites (Schwienbacher et al. 2012). Freezing may occur at any time during the growing season on the recently ice-free sites. Thus, early colonizing species should be adapted to lower temperatures and should have higher frost resistance at all development stages compared to species occurring at older successional stages. Hence, we investigated frost resistance of glacier foreland species, from pioneer to late-successional species, to test to what extent frost affects plant population dynamics and plant survival along the primary succession. Our experimental approach was designed to answer the following questions: 1. Do early development stages of glacier foreland species differ in their frost resistance? 2. Does frost resistance of pioneer species differ to earlyand late-successional species? 3. Are adult alpine plants more frost resistant than their seedlings? 4. Do plantlets of P. alpina acquire a higher frost resistance than seedlings? 5. Are there differences in frost resistance between seedlings cultivated in the field and in the growth chamber, i.e. do seedlings possess a frost hardening capacity? Methods Research area The research area is situated in the Austrian Central Alps on the pioneer stage (1971 moraine) of the glacier foreland of the Rotmoos Valley (Obergurgl, Ötztal, Tyrol, Austria, 46°52′N, 11°02′E) at 2400 m a.s.l. The valley is almost flat and ascends only slightly near the glacier tongue. Over the last 150 yr the glacier has retreated by more than 2 km. The largely well-preserved chronosequence exhibits a series of glacier moraines (e.g. 1971, 1923, 1870), delimitated by a terminal moraine ridge dated to 1858 (G. Patzelt, University of Innsbruck, unpublished data). The chronosequence proceeds from a pioneer stage (1971) via an early(1923) to a late-successional stage (1858; Raffl & Erschbamer 2004; Raffl et al. 2006a). Soil development shows slow progressive development from Syrozems on the youngest moraines to Pararendzinas on the oldest sites (Erschbamer et al. 1999). Microclimate To assess the severity and frequency of low temperature extremes at the pioneer stage in the glacier foreland, a microclimate station was installed at the research area and temperature data were collected throughout three successive summer periods (2008–2010). Air (at 15 cm above the soil surface) and soil surface temperatures were Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science Does frost limit recruitment and establishment on a glacier foreland? S. Marcante et al. determined with thermocouple sensors (Type T; solder junction diameter: 0.2 mm; Thermo-Est, Vienna, Austria). Soil temperatures (2-, 3-, 5- and 10-cm depth) were measured with thermistors (107; Campbell Scientific, Logan, UT, USA). All sensor types were connected to a data logger (CR10X; Campbell Scientific), collecting data every 10 min from each sensor and recording mean values at 30-min intervals. have sufficient field-grown seedlings for the laboratory experiments in 2009. Bulbils of P. vivipara were regarded as seeds, given that they also occur in the seed banks of the Rotmoos glacier foreland (Marcante et al. 2009a). The experimental field was regularly watered during the 2009 growing season to prevent drought stress to seedlings. Adults and plantlets were collected in the glacier foreland during the 2009 growing season. Plant material Determination of frost resistance Frost resistance of seeds and early development stages was studied in 12 alpine plant species, all of which occur along the primary succession of the Rotmoos glacier foreland (Raffl & Erschbamer 2004; Table 1). The nomenclature follows Fischer et al. (2005). Almost 500 seeds per species were collected at the research site. For the laboratory experiments, seeds of all species were sown into Petri dishes and exposed in a growth chamber (Sanyo, E&E Europe BV, Leicestershire, UK; MLR-350H; 25/10 ° C, 16/8 h light/dark, 400 lmol photons m 2·s 1) and further cultivated to the respective development stages. The following development stages were investigated: dry seeds (G0, after field collection), imbibed seeds (G1, wet seeds), germinated seeds (G2, emerged radicle at least 2mm long), seedlings (G3S, cotyledons completely extended), plantlets (G3P, two leaves completely extended, no roots), juveniles (G4, first pair of true leaves completely extended), and adults (A, more than two leaves). To test frost-hardening capacity, seedlings were cultivated at the research area on a flat site at the 1971 moraine (pioneer stage) and then the frost resistance experiments were performed in the laboratory. The seeds were sown into the substrate in autumn 2008 in order to In the laboratory, frost resistance of seeds, seedlings, plantlets, juveniles and adult plants was determined by exposing samples in a temperature-controlled, convective freezing chamber. In the freezing chamber, temperatures were lowered at a moderate cooling rate of 2 K·h 1. Target temperatures identical for all the species and ranging from 0 to 10 °C in 2 °C steps, were maintained for 4 h, i.e. a frost treatment protocol generally used in frost resistance studies (Sakai & Larcher 1987). The target temperatures were identical for all the species and were selected after preparatory experiments on the experimental species. The highest temperature was chosen to cause no frost damage and the lowest to cause 100% frost damage to the sample. Thawing took place at a rate of 4 K·h 1. Sample temperature was recorded with fine-wire thermocouples connected to a data logger (CR10X; Campbell Scientific). Thermocouple sensors were placed at the surface of the analysed organs and attached with a special adhesive (Transpore; BM-Austria GmbH, Vienna, Austria). After a latency period of 5 d, viability of the samples as a whole and of single organs was tested with the topographic tetrazolium (TTC) test (Ruf & Brunner 2003; Larcher et al. 2010). Dehydrogenase activity reduces the colourless tetrazolium salt to red-coloured triphenyl formazan; so that red-coloured cells and organs can be rated as viable (Larcher 1969). The percentage of frost damage to the samples was calculated with image analysis software (OPTIMAS) and then plotted against the treatment temperature. A classic logistic function was fitted to the data with P-Fit software (Biosoft, Durham, NC, USA): Y = Min + (Max Min)/(1 + e k(X X50)), where X is the input variable (target temperature), Y is the output variable (injury as a percentage), Min and Max are asymptotic upper and lower limits of the curve (0%, 100%), X50 is the input variable at the inflection point (Min Max)/2 and k is a slope factor. Values of X50 were read directly from the fitted curve and used as a measure of frost resistance [i.e. taken as LT50, the lethal temperature (°C) for half of the samples]. For each development stage and each species values of at least five measurements were included. Table 1. Occurrence of the 12 investigated species at three successional stages (pioneer, early and late) deglaciated since 1971, 1923 and 1858, respectively, and their seed appendages. Species Abbreviations Successional stage Seed appendage Saxifraga aizoides Artemisia genipi Oxyria digyna Trifolium pallescens Persicaria vivipara Poa alpina Leontodon hispidus Anthyllis vulneraria subsp. alpicola Achillea moschata Erigeron uniflorus Silene acaulis subsp. exscapa Trifolium badium SAXAIZ ARTGEN OXYDIG TRIPAL PERVIV POAALP LEOHIS ANTALP Pioneer Pioneer Pioneer Early Early Early Late Late No Pappus Wings No No No Pappus No ACHMOS ERIUNI SILACA Late Late Late No Pappus No TRIBAD Late No Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science 3 Does frost limit recruitment and establishment on a glacier foreland? S. Marcante et al. occurred at a low frequency of up to 1.3% of days during the snow-free growing season (Table 2, Fig. 1). The 2008 growing season was particularly prone to freezing with severe temperatures down to 5.6 °C at the soil surface, mainly at the beginning of autumn. At a depth of 5 cm, the mean minimum temperatures were much less extreme ( 0.8 °C). During the 2008 growing season, freezing temperatures occurred only at a frequency of 4% of snow-free days. Air temperature records at 15 cm above the ground showed a higher frequency of significant freezing temperatures than soil temperatures. During the 2008 growing season almost 4% of the daily temperatures were below 2.5 °C. Statistical analysis The LT50 was used to compare frost resistance of the investigated development stages, species and successional stages. Differences between species and development stages, our first hypotheses, were tested with a generalized linear mixed model after log transformation of the data. Development stages were used as a fixed factor and species as a random factor. To test our second hypothesis on the effect of successional stages to the development stages; another model was run with development stages as fixed factor and the species categorized by successional stages as random factor. The frost resistance of adult individuals compared to the frost resistance of their seedlings and the frost hardening capacity of seedlings were tested with the Mann-Whitney U-test. Median, 25th and 75th percentile and minimum and maximum values are shown in box plots. Statistics were performed using STATISTICA 6.1 (Stat. Soft Inc., Tulsa, OK, USA). Frost resistance along the primary succession Significant differences (P < 0.001) in frost resistance (LT50) between different development stages were observed (Fig. 2a). Frost resistance (median) decreased from dry seeds ( 19.8 °C) to imbibed seeds ( 8.0 °C). There was a considerable variability in frost resistance within both dry seeds (range: 22 to 8 °C, median: 19.8 °C) and imbibed seeds (range: 25 to 2 °C, median: 7.8 °C). During germination, frost resistance decreased further to 3.2 °C for G2 and to 2.4 °C for G3. Interspecific variability of frost resistance was still high in germinated seeds Results Microclimate During the 2008–2010 growing seasons about 10% of daily soil surface temperature minima were lower than 0 °C. However, significant freezing temperatures below 2.5 °C Table 2. Mean minimum temperatures (MIN) and standard deviations (SD) recorded during three growing seasons (1 June–1 Oct; 2008–2010) and in autumn winter–spring (1 Oct–1 June; 2008–2010) at 15 cm above the soil surface (air; two sensors), on the soil surface (28 sensors) and in the soil at a depth of 5 cm, and frequency (%) of the records lower than 0, 2.5 and 5 °C. 2010 Air MIN all year, °C MIN growing season, °C MIN autumn–winter–spring, °C Frequency < 0 °C growing season, % Frequency < 2.5 °C growing season, % Frequency < 5 °C growing season, % Soil Surface MIN all year, °C MIN growing season, °C MIN autumn–winter–spring, °C Frequency < 0 °C growing season, % Frequency < 2.5 °C growing season, % Frequency < 5 °C growing season, % Soil (5 cm) MIN all year, °C MIN growing season, °C MIN autumn–winter–spring, °C Frequency < 0 °C growing season, % Frequency < 2.5 °C growing season, % Frequency < 5 °C growing season, % 4 2009 2008 Mean SD Mean SD Mean SD 2.8 2.8 1.2 17.3 0.1 0.0 0.1 0.1 0.02 9.3 2.9 4.9 11.8 0.1 0.0 2.4 0.1 1.3 7.6 7.6 3.6 12.6 3.7 0.5 1.1 1.1 0.6 2.9 2.9 0.9 10.7 0.1 0.03 2.1 2.1 0.7 5.4 1.2 2.9 5.6 5.3 2.8 5.9 1.3 0.2 2.5 2.9 1.2 0.8 0.2 0.8 9.9 0.0 0.0 7.2 2.3 3.6 8.3 0.05 0.0 2.8 0.2 1.6 10.3 0.0 0.0 2.8 0.8 2.04 3.8 0.1 0.0 Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science Does frost limit recruitment and establishment on a glacier foreland? S. Marcante et al. Fig. 1. Daily minimum temperatures over 2009 (Jan–Dec) collected at the pioneer stage of the Rotmoos glacier foreland (2400 m a.s.l.). Air temperatures were collected at 15 cm above the soil surface. Soil temperatures were collected at the surface, and at depths of 5 and 10 cm. Imbibed seeds Germinated seeds a b Seedlings c Juveniles Adults c bc LT50 (°C) (a) (b) Germinated seeds Imbibed seeds a b a b a Juveniles Seedlings a b b a b Adults c a b a LT50 (°C) a Developmental stages Fig. 2. Frost resistance (LT50) of all investigated alpine species (a) and categorized by successional stage (b). Determined are the following development stages: imbibed seeds (n = 96), germinated seeds (n = 76), seedlings (n = 97), juveniles (n = 72) and adult individuals (n = 55). Different letters (a, b, c) represent multiple comparisons of P -values performed with the GLMM (n = 396). ( 14.7 to 0.7 °C) but was low in seedlings and juveniles. From G3 to G4 ( 2.5 °C) it remained unchanged. Multiple comparisons showed a significant difference (P < 0.001) between the frost resistance of dry and imbibed seeds (G0 and G1), germinated seeds (G2) and seedlings (G3). Adults differed (P < 0.001) in their frost resistance from the dry and imbibed seeds but not from germinated seeds (G2), seedlings (G3) and juveniles (G4). Along the primary succession (Fig. 2b), germinated seeds and seedlings of pioneer species possessed a lower frost resistance ( 3.3, 1.8 °C, respectively), than germinated seeds and seedlings of early-successional species ( 7.3, 3.3 °C, respectively) and of late-successional species, even if not always significant ( 3.1, 2.6 °C, respectively). The juveniles of pioneer and early-successional species differed significantly (P < 0.001). Frost resistance of adult individuals differed significantly (P < 0.01) between pioneer, early- and late-successional species ( 2.2, 4.8 and 3.6 °C, respectively). Significant differences in frost resistance during development among the investigated species were observed (P < 0.001; Fig. 3a–e). Imbibed seeds (G1) were characterized by a high variability in frost resistance (Fig. 3a). Among the pioneer species, Oxyria digyna seeds showed a higher frost resistance than Saxifraga aizoides and Artemisia genipi seeds. Imbibed seeds of the early-successional species Trifolium pallescens showed an extremely high frost resistance (LT50: 25 °C). Among the late-successional species Leontodon hispidus and Achillea moschata exhibited a frost resistance lower than 20 °C, while other species could only tolerate freezing temperatures between 4 and 8 °C. With the onset of germination frost resistance decreased rapidly (Fig. 3b). The highest frost resistance was found for Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science 5 Does frost limit recruitment and establishment on a glacier foreland? S. Marcante et al. (a) (b) (c) (d) (e) Fig. 3. Frost resistance (LT50) of the investigated species sorted by development stages (a–e). Boxes indicate the range of LT50 lethal temperatures ( °C) of half of the samples. Within development stages, differences between species were tested with GLMM (P < 0.001). Different letters (a, b, abc and c) represent multiple comparisons of P-values. Species abbreviations follow Table 1. Insufficient replicates caused the missing values of species within the juveniles and adult individuals. T. pallescens (LT50: 13 °C), the lowest for O. digyna (LT50: 0.7 ° C). With the elongation of hypocotyls and cotyledons, the frost resistance further decreased (Fig. 3c,d). Seedlings (G3) and juveniles (G4) showed a similar trend: the frost resistance ranged from 5.6 to 0.7 °C for G3 and from 3.7 to 1.5 °C for G4. The most frost-resistant species in G3 and G4 was P. vivipara. 6 Frost resistance of different organs (root, hypocotyl and cotyledons) was assessed at the seedling stage. Roots were generally the most frost susceptible parts, followed by cotyledons, first leaves and the hypocotyl (data not shown). Frost resistance of adult plants was compared with that of seedlings grown in the field (Fig. 4). Taking all species Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science S. Marcante et al. Fig. 4. Frost resistance (LT50) comparison between adult individuals and seedlings grown in the field (G3 field). Differences are among species and between development stages (n.s., not significant; *P < 0.05; **P < 0.01; ***P < 0.001). Species abbreviations follow Table 1. together, no significant difference was detected [P > 0.05, KW-H (1, 101) = 0.4]. However, some species-specific differences between adult individuals and seedlings were observed (Fig 4). Adult individuals of A. genipi and T. pallescens showed a significantly higher frost resistance than seedlings. In contrast, adult individuals of the pioneer species S. aizoides and O. digyna had a lower frost resistance than their seedlings. There was little difference in frost resistance between adults and seedlings of the late-successional species L. hispidus and Anthyllis alpicola. The frost resistance of plantlets of P. alpina was similar to that of adult individuals ( 10.3 ± 0.2 and 9.8 ± 2.7 °C, respectively), whereas seedlings showed a significantly (P < 0.001) lower frost resistance ( 2.4 ± 0.5 °C). Frost resistance between seedlings grown in the field and growth chamber varied markedly across species (Fig. 5). In some pioneer species the frost resistance was higher when grown in the field, even if not always significant (S. aizoides P < 0.05; O. digyna P < 0.05; A. genipi P > 0.05). In contrast, the frost resistance of the earlysuccessional species T. pallescens and of the latesuccessional species L. hispidus (P < 0.01) and A. alpicola (P = 0.05) was higher when grown in the growth chamber. The seedlings of P. alpina and P. vivipara were not affected by the environmental conditions during cultivation (P > 0.05). Discussion Establishment and growth of alpine plants along the primary successions in glacier forelands have frequently been shown to be under abiotic control (Bliss 1971; Körner 2003; Dolezal et al. 2008). Our results demonstrate that Does frost limit recruitment and establishment on a glacier foreland? Fig. 5. Comparison between frost resistance (LT50) of seedlings grown in the growth chamber (G3) and seedlings grown in the field (G3 field). Differences are among species and between development stages. (n.s., not significant; *P < 0.05; **P < 0.01; ***P < 0.001). Species abbreviations follow Table 1. freezing temperatures during the growing season are only sporadic events in the alpine glacier foreland, but they are potentially severe enough to kill early development stages. This can significantly affect the recruitment and speed of establishment of species, as well as their ability to maintain populations. Each of the early development stages investigated was affected by freezing temperatures in a different manner. Dehydrated seeds were not endangered during the growing season because their frost resistance (LT50 – 20 °C) is sufficient to survive the lowest freezing temperatures that occurred at the research site. Although air temperatures can drop below 20 °C, soil is usually covered by snow, which moderates temperatures significantly (Körner et al. 2003; Fig. 1). Absolute soil temperature minima at the research area were between 4.9 and 1.0 °C during the study years 2008–2010 (data shown only for 2009). Liquid water content of snowpack in the Central European Alps is mostly highest at the soil surface throughout winter and steadily increases until snowmelt (Kuhn 2012). In the glacier foreland, the water from snowmelt imbibes seeds when they are still covered by snow at the beginning of June (Niederfriniger Schlag & Erschbamer 2000), thus seed imbibition and seed germination start when freezing temperatures are still a possibility. The dehydrated seeds are stored either in transient seed banks (0–5-cm deep; Marcante et al. 2009a), which could still be affected by freezing temperatures at the beginning of the growing season, or in permanent seed banks (5–10-cm deep) where freezing events should be prevented unless unpredictable frost events occur before a snow cover develops (Körner et al. 2003). Our results demonstrate that imbibed seeds (LT50: 8 °C) may still be relatively unaffected by the Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science 7 Does frost limit recruitment and establishment on a glacier foreland? freezing temperatures occurring in the field. In contrast, germinated seeds are highly frost susceptible and frost damage may still occur in transient seed banks. However, at our research area, numerous seedlings can be counted in the field after snowmelt but, in most cases, up to 90% of these seedlings subsequently die (Niederfriniger Schlag & Erschbamer 2000; Marcante et al. 2009b). Our results indicate that this high seedling mortality, also found elsewhere in alpine plant communities (Chambers 1995; Kiviniemi & Eriksson 1999; Forbis 2003), could be caused by frost damage and especially by night freezing with temperature minima lower than frost resistance of these development stages. The high frost susceptibility of these stages may be connected to the onset of active metabolism that results in tissue growth processes leading to the appearance of the radicle. Growing tissues as also found in sprouting shoots (Taschler et al. 2004), in roots (Sakai & Larcher 1987) or during flower development (Hacker et al. 2011) and are generally known to be the most frost susceptible plant parts, with only limited frost hardening potential. The primary succession along the glacier foreland is characterized by a shift in species composition, where pioneers are replaced by early-successional colonizers, which are followed by species of late-successional stages (Matthews & Whittaker 1987). As pioneers have to cope with stronger constraints during establishment than late-successional species and that colonization on bare ground areas is also limited by lack of safe sites, we expected pioneer species to be more frost resistant than early- and latesuccessional species. The results only partially supported this hypothesis, e.g. dry and imbibed seeds of O. digyna were among the most frost resistant, whereas germinated seeds and seedlings were highly susceptible to freezing temperatures. Even if differences between the species groups remained relatively weak, pioneer species more often proved to have a lower frost resistance than earlyand late-successional species. As Caccianiga et al. (2006) demonstrated, several pioneer glacier foreland species share ruderal traits, although Grime (2001) suggested that primary successions should be dominated by stress-tolerant species. Our results regarding the lower frost resistance of the pioneer species seem to confirm that these species are adapted to disturbance and less so to abiotic stress. Along the primary succession, some differences in frost resistance among species could be explained with seed morphological traits. Seed mass and seed shape, tested against seed frost resistance in previous experiments (unpublished data), did not clarify our results; however, some outcomes could be explained by the presence or absence of seed appendages. O. digyna has flattened and winged seeds. These appendages ensure that the seeds remain at the soil surface and have to survive freezing temperatures in autumn and winter. Within the early-successional species, the dry and 8 S. Marcante et al. imbibed seeds of T. pallescens exhibit high frost resistance. Seeds of this species can frequently be found unburied on the soil surface after snowmelt, making high frost resistance essential for survival. Among the late-successional species, dry and imbibed seeds of L. hispidus were also among the most frost resistant. The seeds of L. hispidus carry an elongated pappus that also prevents burial of seeds and thus they remain exposed to temperature extremes (Peart 1984). The intraspecific differences in frost resistance between adults and seedlings were very divergent in the Rotmoos glacier foreland. The seedlings of the most important pioneer species in the study site, S. aizoides, exhibited a higher significant frost resistance in the field than their adult individuals. In contrast, adult individuals of the pioneer species A. genipi and of the early-successional species T. pallescens and P. alpina showed a significantly higher frost resistance than their seedlings, which supports earlier results on tree seedlings (Larcher 1969; Meza-Basso et al. 1986; Rios et al. 1988; Neuner et al. 1997). In the late-successional species group, seedlings in the field were less frost resistant than adults. Our results illustrated that early development stages of P. alpina, growing and establishing all across the glacier foreland (Raffl & Erschbamer 2004), do not possess a significant frost hardening capacity, even if the adult individuals are highly frost resistant (Taschler & Neuner 2004): the leaves of this species freeze independently of each other due to anatomical ice barriers in their shoots, some leaves can even supercool down to 11.6 °C (Hacker et al. 2008). As an example, we compared the response to frost events of the sexual and asexual offspring of P. alpina. At the pioneer stage, this species propagates mainly through plantlets, successfully enhancing its establishment (Marcante et al. 2009b; Winkler et al. 2010). This may be due to the significantly higher frost resistance of the plantlets than the seedlings. The lower frost resistance of seedlings could hinder successful establishment in the pioneer stage and lead to enforced asexual reproduction, as found in other alpine species (Lee & Harmer 1980; Stöcklin 1992; Pluess & Stöcklin 2005; Weppler et al. 2006). Despite the apparent reliance on clonal regeneration of some alpine plants, there is evidence that many alpine species produce hundreds of viable seeds (Sayers & Ward 1966; Chambers et al. 1987; S. Marcante unpublished data) that contribute to extensive soil seed banks (Freedman et al. 1982; Cooper et al. 2004; Marcante et al. 2009a). Most of them are able to germinate easily (Kibe & Masuzava 1994; Forbis 2003; Welling et al. 2005), ensuring an increase in plant population size (Marcante et al. 2009b) and maintaining a high genetic diversity (Raffl et al. 2006b, 2008). The high frost susceptibility of the early development stages implies that establishment will depend on microsites protected from Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science S. Marcante et al. low temperature extremes (Harper et al. 1961; Matthews & Whittaker 1987; Svoboda & Henry 1987; Whittaker 1991; Frenot et al. 1998; Jumpponen et al. 1999). Concave soil surfaces, coarse substrate and small stones provide favourable microclimate conditions, avoiding temperature extremes and desiccation. Temperature extremes moderated by only 1–2 °C would already be sufficient for seeds and seedlings to survive in our research area. In this initial stage of primary succession seedlings with insufficient frost hardening capacity rely on suitable microsites to resist climate extremes. Conclusions In alpine areas freezing temperatures have always been considered to be one of the main abiotic factors, besides drought and heat, that contribute to high seedling mortality rates (Billings & Mooney 1968; Bell & Bliss 1980; Chapin & Bliss 1989; Niederfriniger Schlag & Erschbamer 2000; Forbis 2003; Körner 2003). Our results show that at the glacier foreland of the Rotmoos Valley, due to its relatively low elevation, frost events critical for survival are relatively rare in summer and may not fully explain the high seedling mortality (Marcante et al. 2009b) in all years. A better understanding of the susceptibility of seeds and seedlings to critical soil surface heating and frequent drought in the undeveloped soils will further help to explain mortality rates at the pioneer stage. Freezing temperatures during the growing season can cause frost damage in early development stages of alpine plants. They are, in contrast to adult plants, unable to recuperate via undamaged below-ground organs. Nevertheless, adult plants showed some frost hardening capacity. Nevertheless, the risk of frost damage to early development stages remains a potential threat that can retard plant colonization in the glacier foreland. Acknowledgements We thank Othmar Buchner for constructing the microclimate station in the field and for assistance in data collection, Jürgen Hacker for the laboratory assistance during the experiments and Erich Schwienbacher for field assistance. We are particularly grateful to four anonymous reviewers and the Co-ordinating Editor Francesco de Bello for many constructive comments on previous versions of the manuscript. This project was financed by the Austrian Science Fund (FWF 19090-B16). References Bell, K. & Bliss, L.C. 1980. Plant reproduction in a High arctic environment. Arctic and Alpine Research 12: 1–10. Does frost limit recruitment and establishment on a glacier foreland? Billings, W.D. & Mooney, H.A. 1968. Ecology of Arctic and Alpine plants. Biological Reviews of the Cambridge Philosophical Society 43: 481–529. Bliss, L.C. 1971. Arctic and alpine life cycles. Annual Review of Ecology and Systematics 2: 405–438. Caccianiga, M., Luzzaro, A., Pierce, S., Cerini, R.M. & Cerabolini, B. 2006. The functional basis of a primary succession resolved by CSR classification. Oikos 112: 10–10. Chambers, J.C. 1995. Disturbance, life-history strategies, and seed fates in alpine herbfield communities. American Journal of Botany 82: 421–433. Chambers, J.C., MacMahon, J.A. & Brown, R.W. 1987. Germination characteristics of alpine grasses and forbs: a comparison of early and late seral dominants with reclamation potential. Reclamation and Revegetation Research 6: 235–249. Chapin, D.M. & Bliss, L.C. 1989. Seedling growth, physiology, and survivorship in a subalpine, volcanic environment. Ecology 70: 1325–1334. Cooper, E.J., Alsos, I.G., Hagen, D., Smith, F.M., Coulson, S.J. & Hodkinson, I.D. 2004. Plant recruitment in the High Arctic: seed bank and seedling emergence on Svalbard. Journal of Vegetation Science 15: 115–124. Dolezal, J., Homma, K., Vyatkina, M.P., Yakubov, V., Vetrova, V. P. & Hara, T. 2008. Primary succession following deglaciation at Koryto Glacier Valley, Kamchatka. Arctic Antarctic and Alpine Research 40: 309–322. Erschbamer, B., Bitterlich, W. & Raffl, C. 1999. Die Vegetation als Indikator für die Bodenbildung im Gletschervorfeld des Rotmoosferners (Obergurgl, Ötztal, Tirol). Berichte Des Naturwissenschaftlich-Medizinischen Vereins in Innsbruck. 86: 107–122. Erschbamer, B., Niederfriniger Schlag, R. & Winkler, E. 2008. Colonization processes on a central Alpine glacier foreland. Journal of Vegetation Science 19: 855–862. Fischer, M.A., Adler, W. & Oswald, K. 2005. Exkursionsflora für Österreich, Liechtenstein und Südtirol, 2nd edn. Oberösterreichisches Landesmuseen, Linz, AT. Forbis, T.A. 2003. Seedling demography in an alpine ecosystem. American Journal of Botany 90: 1197–1206. Freedman, B., Hill, N., Svoboda, J. & Henry, G. 1982. Seed banks and seedling occurrence in a High Arctic oasis at Alexandra Fjord, Ellesmere Island, Canada. Canadian Journal of BotanyRevue Canadienne de Botanique 60: 2112–2118. Frenot, Y., Gloaguen, J.C., Cannavacciuolo, M. & Bellido, A. 1998. Primary succession on glacier forelands in the Subantarctic Kerguelen Islands. Journal of Vegetation Science 9: 75–84. Grime, J.P. 2001. Plant strategies and vegetation processes. Wiley, Chichester, UK. Hacker, J., Spindelböck, J.P. & Neuner, G. 2008. Mesophyll freezing and effects of freeze dehydration visualized by simultaneous measurement of IDTA and differential imaging chlorophyll fluorescence. Plant, Cell and Environment 31: 1725–1733. Hacker, J., Ladinig, U., Wagner, J. & Neuner, G. 2011. Inflorescences of alpine cushion plants freeze autonomously and Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science 9 Does frost limit recruitment and establishment on a glacier foreland? may survive subzero temperatures by supercooling. Plant Science 180: 149–156. Harper, J., Clatworthy, J., Mc Naughton, I. & Sagar, G. 1961. The evolution of closely related species living in the same area. Evolution 15: 209–227. Heide, O. 1989. Environmental control of flowering and viviparous proliferation in seminiferous and viviparous arctic populations of two Poa species. Arctic and Alpine Research 21: 305–315. Hoinkes, H.. 1955. Beitrage zur Kenntnis des Gletscherwindes. In: Mörikofer, W. & Steinhauser, F. (eds.) Archiv für Meteorologie, Geophysik und Bioklimatologie, Band 6, pp. 36–53. Springer, Vienna, AT. Jumpponen, A., Vare, H., Mattson, K., Ohtonen, R. & Trappe, J. 1999. Characterization of ’’safe sites“ for pioneers in primary succession on recently deglaciated terrain. Journal of Ecology 87: 98–105. Kibe, T. & Masuzawa, T. 1994. Seed germination and seedling growth of Carex doenitzii growing on alpine zone of Mt Fuji. Journal of Plant Research 107: 23–27. Kiviniemi, K. & Eriksson, O. 1999. Dispersal, recruitment and site occupancy of grassland plants in fragmented habitats. Oikos 86: 241–253. Körner, Ch. 2003. Alpine plant life: functional plant ecology of high mountain ecosystems, 2nd edn. Springer, Heidelberg, DE. Körner, Ch., Paulsen, J. & Pelaez-Riedl, S.. 2003. A bioclimatic characterisation of Europe’s alpine areas. In: Nagy, L., Grabherr, G., Körner, Ch. & Thompson, D.B.A. (eds.) Alpine biodiversity in Europe. Ecological studies 167, pp. 13–28. Springer, Berlin, DE. Kuhn, M.. 2012. Rain and snow at high elevation. In: Lütz, C. (ed.) Plants in Alpine regions. pp. 1–10. Springer, New York, NY, US. Larcher, W. 1969. Increase in ability to become frost resistant during ageing in Quercus ilex. Planta 88: 130–135. Larcher, W., Kainmüller, C. & Wagner, L. 2010. Survival types of high mountain plants under extreme temperatures. Flora – Morphology, Distribution, Functional Ecology of Plants 205: 3–18. Lee, J.A. & Harmer, R. 1980. Viviparity, a reproductive strategy in response to environmental stress? Oikos 35: 254–265. Marcante, S., Schwienbacher, E. & Erschbamer, B. 2009a. Genesis of a soil seed bank on a primary succession in the Central Alps (Ötztal, Austria). Flora – Morphology, Distribution, Functional Ecology of Plants 204: 434–444. Marcante, S., Winkler, E. & Erschbamer, B. 2009b. Population dynamics along a primary succession gradient: do alpine species fit into demographic succession theory? Annals of Botany 103: 1129–1143. Matthews, J.A. & Whittaker, R.J. 1987. Vegetation succession on the Storbreen glacier foreland. Arctic and Alpine Research 19: 385–395. Meza-Basso, L., Guarda, P., Rios, D. & Alberdi, M. 1986. Changes in free amino acid and frost resistance in Nothofagus dombeyi leaves. Phytochemistry 25: 1843–1846. 10 S. Marcante et al. Neuner, G. & Beikircher, B. 2010. Critically reduced frost resistance of Picea abies during sprouting could be linked to cytological changes. Protoplasma 243: 145–152. Neuner, G. & Hacker, J. 2010. Ice formation and propagation in alpine plants. In: Lütz, C. (ed.) Plants in Alpine regions: cell physiology of adaptation and survival strategies, pp. 163–174. Springer, Berlin, DE. Neuner, G., Bannister, P. & Larcher, W. 1997. Ice formation and foliar frost resistance in attached and excised shoots from seedlings and adult trees of Nothofagus menziesii. New Zealand Journal of Botany 35: 221–227. Niederfriniger Schlag, R. & Erschbamer, B. 2000. Germination and establishment of seedlings on a glacier foreland in the Central Alps, Austria. Arctic, Antarctic and Alpine Research 32: 270–277. Peart, M.H. 1984. The effect of morphology, orientation and position of grass diaspores on seedling survival. Journal of Ecology 72: 437–453. Pluess, A.R. & Stöcklin, J. 2005. The importance of population origin and environment on clonal and sexual reproduction in the alpine plant Geum reptans. Functional Ecology 19: 228–237. Raffl, C. & Erschbamer, B. 2004. Comparative vegetation analyses of two transects crossing a characteristic glacier valley in the Central Alps. Phytocoenologia 34: 225–240. Raffl, C., Mallaun, M., Mayer, R. & Erschbamer, B. 2006a. Vegetation succession pattern and diversity changes in a glacier valley, Central Alps, Austria. Arctic, Antarctic and Alpine Research 38: 421–428. Raffl, C., Schönswetter, P. & Erschbamer, B. 2006b. ‘Sax-Sess’ – Genetics of primary succession in a pioneer species on two parallel glacier forelands. Molecular Ecology 15: 2433–2440. Raffl, C., Holderegger, R., Parson, W. & Erschbamer, B. 2008. Patterns in genetic diversity of Trifolium pallescens populations do not reflect chronosequence on alpine glacier forelands. Heredity 100 (5): 526–532. Rios, D., Meza-Basso, L., Guarda, P., Peruzzo, G. & Alberdi, M. 1988. Frost hardiness and carbohydrate changes in leaves of Nothofagus dombeyi (Mirb.) Oerst. at various ontogenetic stages. Acta Oecologica 9: 135–144. Ruf, M. & Brunner, I. 2003. Vitality of tree fine roots: reevaluation of the tetrazolium test. Tree Physiology 23: 257–263. Sakai, A. & Larcher, W. 1987. Frost survival of plants. Responses and adaptation to freezing stress. In: Billings, W.D., Golloy, F., Large, D.L., Olsen, J.S. & Rammnet, S. (eds.) Ecological studies, Vol. 62, pp. 1–321. Springer, Berlin, DE. Sayers, R. & Ward, R. 1966. Germination responses in alpine species. Botanical Gazette 127: 11–16. Schwienbacher, E., Navarro-Cano, J.A., Neuner, G. & Erschbamer, B. 2012. Correspondence of seed traits with niche position in glacier foreland succession. Plant Ecology 213 (3): 371–382. Stöcklin, J. 1992. Umwelt, Morphologie und Wachstumsmuster klonaler Pflanzen – eine Übersicht. Botanica Helvetica 102: 3–21. Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science S. Marcante et al. Svoboda, J. & Henry, G.H.R. 1987. Succession in marginal arctic environments. Arctic and Alpine Research 19: 373–384. Tackenberg, O. & Stöcklin, J. 2008. Wind dispersal of alpine plant species: a comparison with lowland species. Journal of Vegetation Science 19: 109–118. Taschler, D. & Neuner, G. 2004. Summer frost resistance and freezing patterns measured in situ in leaves of major alpine plant growth forms in relation to their upper distribution boundary. Plant, Cell and Environment 27: 737–746. Taschler, D., Beikircher, B. & Neuner, G. 2004. Frost resistance and ice nucleation in leaves of five woody timberline species measured in situ during shoot expansion. Tree Physiology. 24: 331–337. Welling, P., Tolvanen, A. & Laine, K. 2005. Plant traits: their role in the regeneration of alpine plant communities in sub-arctic Finland. Journal of Vegetation Science 16: 183–190. Does frost limit recruitment and establishment on a glacier foreland? Weppler, T., Stoll, P. & Stöcklin, J. 2006. The relative importance of sexual and clonal reproduction for population growth in the long-lived alpine plant Geum reptans. Journal of Ecology 94: 869–879. Whittaker, R.J. 1991. The vegetation of the Storbreen gletschervorfeld Jotunheimen, Norway. IV. Short-term vegetation change. Journal of Biogeography 18: 41–52. Winkler, E., Marcante, S. & Erschbamer, B. 2010. Demographic consequences of the two reproductive modes in Poa alpina l. along a primary succession gradient in the Central Alps. Arctic, Antarctic, and Alpine Research 42: 227–235. Journal of Vegetation Science Doi: 10.1111/j.1654-1103.2012.01411.x © 2012 International Association for Vegetation Science 11
© Copyright 2026 Paperzz