Botanical Journal of the Linnean Society (1996), 122: 301-313. With 1 figure Reproduction of the rare monocarpic species Saxifraga mutata L. ROLF HOLDEREGGER Institute of Systmatic Botqy, Universi@of Zurich, Zolldmstr. 107, CH-8008 Zurich, Switzerland Received May 1996, acceptedfw publication Aupust 1996 The aim of the study is to investigate the impact of reproduction and genetic variation on the persistence of populations of the prealpine, monocarpic SmJfugu mututu L. The species grows on erosion slopes or rocks, and its local populations are often small and isolated. Crossing experiments resulted in better seedset than selfing, but both yielded viable seeds. Agamospermy did not occur. In an early-successional species like S. mututu, successful selfing is important in the colonization of new habitats. Flowers of S. mututu were visited by Syrphidae and unspecialized Hymenoptera. A germination rate of 40% was reached in cultivation after 20 weeks but germination continued until the end of the experiment after 92 weeks. Seeds stored dry for 30 months at room temperature mostly lost their germinability. In natural habitats, seedlings were found almost throughout the year with a peak in spring. Suitable safe sites were small patches of open soil, bare marl on erosion slopes, and rock crevices. AU individuals investigated were diploid with 2n = 26. AUozyme electrophoresis showed a lack of segregation within the populations. Intra- and interpopulation genetic variation was low. These results were in partial disagreement with theoretical expectations in a mixed mating species. It is concluded that demographic rather than genetic processes are the main cause of extinction of populations of S. mututu, at least in the short-term. Bl996 The Linnean Society of London ADDITIONAL KEY WORDS: -allozymes - conservation biology - genetic variation - germination - pollination - population dynamics. CONTENTS Introduction . . . . . . . . . . . . . . . . . . . . . . . . . . Material and methods . . . . . . . . . . . . . . . . . . . . . . . The species . . . . . . . . . . . . . . . . . . . . . . . . . Study sites . . . . . . . . . . . . . . . . . . . . . . . . . Pollination experiments . . . . . . . . . . . . . . . . . . . . . Flower visitors . . . . . . . . . . . . . . . . . . . . . . . . Seed sizes and germination experiments . . . . . . . . . . . . . . . Enzyme electrophoresis . . . . . . . . . . . . . . . . . . . . . Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . Pollination experiments . . . . . . . . . . . . . . . . . . . . . Flower visitors . . . . . . . . . . . . . . . . . . . . . . . . Seed sizes and germination experiments . . . . . . . . . . . . . . . Enzyme electrophoresis . . . . . . . . . . . . . . . . . . . . . 00244074/96/012301+13 $25.00/0 30 1 302 302 302 303 303 304 304 304 305 305 306 306 307 01996 The Linnean Society of London 302 R. HOLDEREGGER Discussion . . . . . . . . Breeding system and pollination Genetic variation . . Germination Conservation biology . Acknowledgements References . . . . . 308 308 309 31 0 310 311 311 INTRODUCTION A long standing question in conservation biology is whether genetic or demographic processes are more important as critical factors affecting the extinction or persistence of small populations (Lande, 1988). In rare or endangered plant species, knowledge of demography, in terms of the number of individuals per population, and knowledge of intrapopulational genetic variation are therefore of fundamental importance (Harvey, 1985; Gilpin & Soule, 1986). Existing data imply that demographic processes including environmental stochasticity are more important as causes of extinction of local populations than are genetic processes (Lande, 1988; Barrett & Kohn, 1991; Ellstrand & Elan, 1993). Knowledge of the reproductive biology of a species is a key for the understanding of intrapopulational processes of both types, demographic and genetic (Loveless & Hamrick, 1984). In species with formerly large but recently small and isolated populations like Salvia pratensis L., Scabiosa columbari.a L. and Gentiana pneumonanthe L., genetic erosion may cause extinction due to inbreeding effects resulting in low genetic variation (van Treuren et al., 1993; Ouborg & van Treuren, 1994; Oostermeijer et al., 1995). In species that are naturally rare and have always occupied isolated habitat patches deleterious genetic processes due to inbreeding may be of minor importance or totally absent. This was shown in several rock-inhabiting fern species (Holderegger & Schneller, 1994; Schneller & Holderegger, 1996). Nevertheless, the importance of genetic variation within populations of rare perennial plant species that exhibit marked changes in population size and structure due to naturally occurring environmental stochasticity is still insufficiently known. A study of the demography of the rare, prealpine Saxi.ftaga mutata L. has indicated that size structure (in terms of rosette diameters), recruitment, and timing of reproduction are connected with the course of succession (Holderegger, in press), and that stochastic erosion events strongly influence the persistence of local populations. The present paper deals with the reproductive biology and the intrapopulational genetic variation of S. mutata in order to assess their potential impact on its conservation biology. Pollination experiments and germination experiments were undertaken, field observations on flower visitors were made, and allozyme diversity was determined to evaluate the importance of genetic factors for the survival of the species' local populations. MATERIAL AND METHODS The species Saxifraga mutata L. (Saxifragaceae) is characterized by widely scattered and often transient populations in the European prealps and Carpathian mountains (Webb & REPRODUCTION OF SAXZFRAGA MUIATA 303 Gornall, 1989). Most of its sometimes very small populations are found at altitudes between 800 and 1200 m a.s.1. (Kaplan, 1995). In river valleys or ravines it inhabits calcareous rocks and debris or gravel on erosion slopes. Its dark green, basal rosettes with lime-secretinghydathodes can reach diameters of 20 cm. The flowering panicles usually bear about 60 flowers with linear, yellow to faint-red petals. The flowering season is from July to late August. Single rosettes of S. mututu are normally strictly monocarpic, requiring several years from seed to flowering, but genets may sometimes behave as true perennials by means of vegetative offsets (Webb & Gornall, 1989). In Switzerland, S. mutata is a rare plant species (Landolt, 1991). Populations are usually isolated from each other, but in a river valley or ravine the species may occupy several small habitat patches. study sites The study was made in the Canton of Zurich in a mountainous region of northeastern Switzerland. Three populations of S. mututu were investigated: (T) Tosstal; coordinates of the Swiss national grid 715.100/241.250. A population of about ten thousand individuals of S. mututu inhabits steep erosion slopes and rocks of calcareous conglomerate in a deep river valley at altitudes of about 800 m a.s.1. (FJ Falatsche near Zurich; coordinates: 680.500/243.250. A population of S. mututu with about three thousand individuals is found at altitudes between 700 m and 780 m a d . on a steep slope of marl or calcareous sandstone in the shape of a semicircular funnel. Erosion is frequent at this study site. (K) Kusnacht; coordinates: 687.800/241.500. A small population of S. mututu of about 200 rosettes occupies slopes of marl in a small ravine at an altitude of 500m a.s.1. in the vicinity of Zurich (Holderegger, 1994). Pollination expmimts Experiments were performed in summer 1990 in all three populations in order to investigate the breeding system of S. mutab. Flower buds were bagged in synthetic, water-resistant silk with a mesh-width of 12 pm (Nybolt Gaze, Schweizer Seidenfabrik AG) one week before the onset of flowering. Only flowers of second order within the panicle were taken because flower size depends on the position within the panicle. One flower bud from each of 70 plants was used per treatment, 140 flowers were marked as controls. Substantial losses of marked and experimentally treated flowers occurred because they were damaged by deer and chamois, land slides, or hail (see sample sizes). Five different treatments were carried out. (1) Artificial crossings: stamens of the pollen-receiving flowers removed before bagging; pollen for crossing was collected from individuals within a distance of 5 m from the experimental plant and mixed; n = 33. (2) Spontaneous selfing: flower buds were bagged without hrther treatment; n = 65. (3) Artificial selfing: stamens of the experimental flowers were removed before bagging; selfing was performed with pollen from another flower of the same individual ( = geitonogamy); n = 67. (4) Agamospermy: flower buds were bagged 304 R. HOLDEREGGER after stamen-removal; no further treatment; n = 42. (5) Open pollination: control; no treatment; n = 139. Ripe fruits were harvested before dehiscence, and the number of ripe seeds per fruit was determined. Viability of these seeds was tested in a germination experiment (for experimental design see below). Flower Uzritors Insects visiting flowers of S. mutata were caught in July and August 1990 during four hours in the afternoon of two days with changing weather conditions in population T, three days in population F, and one day in population K. Each species was collected and recorded only once, and no attempt was made to count flower visitors. Flower visitors were identified at least to the level of genera. Seed sizes and germination expm'ments Differences in seed sizes among populations could have an effect on germination rates. Therefore, ripe seeds were sampled in all three populations. Length and width of five seeds per plant were measured under a dissecting microscope. Seeds of 30 individuals were analysed in population T, 29 in F, and 28 in K. Seeds used in the germination experiments A 4 were collected in late August and September 1990. Fifty ripe seeds from a single individual of S. mutata were scattered on wet filter paper in a petri dish. Since no fungicide was applied, some seeds were infected, but their germination was usually not inhibited or delayed when compared with the germination of uninfected seeds. Nevertheless, some losses occurred. The petri dishes were exposed to a constant temperature of 2OoC and to a 16h light/8 h darkness regime. Tap water was added once a week. Germination rate was checked every two weeks. Experiment A: this experiment was started immediately after sampling and lasted for 20 weeks. Seeds from 26 individuals were harvested from population T, 30 from F, and 23 from K. A total of 3907 seeds was used for analysis. Experiment B: seeds were stored dry for 10 months at room temperature before the experiment started (T: n = 40 individuals; F n = 40; K: n = 6). Additionally, capsules of five individuals of S. mutata of the previous season were sampled from population F in spring 1991. These seeds were also incorporated in this experiment. Germination was checked for 92 weeks starting in June 1991. A total of 450 1 seeds was taken into account. Experiment C: seeds were tested after a dry storage of 30 months at room temperature (T: n = 10 individuals; F: n = 10; K: n = 5). The experiment was carried on for 96 weeks; 1250 seeds were used. Enzyme electrophoresis The chromosome number of S. mututu has been debated several times (Kupfer & Rais, 1983). Therefore, in populations T , F, and K the meiosis of 13 individuals in REPRODUCTION OF SAXIFRAGA M U A T A 305 total was examined using the classical acetocarmine squash method (Darlington & LaCour, 1976). Genetic variation within populations was investigated with allozyme electrophoresis. Both starch-gel electrophoresis and agarose-gel electrophoresis were used (Wendel & Weeden, 1989; Schneller & Scheffrahn, 1989). Modifications of the loading technique enabled the analysis of 52 individuals per agarose gel. Best results were obtained with agarose-gel electrophoresis (Schneller & Scheffrahn, 1989),but a second run was usually done using starch-gel electrophoresis in order to confirm the banding patterns. The grinding buffer of Schneller & Scheffrahn (1989: 199) with 20% w/v PVP 40000 was used. PGM and GPI were best scored with buffer system No 5 of Soltis et al. (1983)adjusted to pH 7.0 with citric acid and gel buffer No 5 of Schneller & Scheffrahn (1989). For IDH the electrode buffer No 5 had a pH 7.2. MDH and SKD were analysed with electrode and gel buffers No 1 of Schneller & Scheffrahn (1989). Problems with the material during grinding and loading the gels (withering) resulted in bad resolution of bands after staining. This is the reason for the different sample sizes per enzyme system and per population (Table 3). Only fresh plant material could be used. Five enzyme systems with a total of seven loci were interpreted at the allelic level, namely Qi-2, Idh, Mdh-1, Mdh-2, Mdh-3, Pp-2, and Skd (Weeden & Wendel, 1989). Results are presented as genotypes per loci. RESULTS Pollination experimts Mean seed-set per capsule decreased in the following order: open pollination (161.92) > artificial crossing (45.39) > spontaneous selfing (24.75) > artificial selfing (5.03) > agamospermy (0.00). The large standard errors in Table 1 show that there was high variation in seed-set within each treatment. According to a Kruskal-Wallis analysis (d.f. = 3, P < 0.001) with subsequent Nemenyi pairwise comparisons (2' = 0.05; Sachs, 1992) open pollination had significantly higher seed-set than all other treatments, and artificial crossing resulted in a significantlyhigher seed number compared with the agamospermy experiment. Neither of the other comparisons exhibited significant differences. Mean germination rates after 92 weeks were 90.4% in open pollinated flowers (number of sampled plants n = 86, total number of seeds n = 4300), 73.3% in artificially crossed flowers (n = 8, seeds n = 400), 96.0% in spontaneously selfed TABLE1. Mean number of ripe seeds per capsule (K), standard error (SE), and number of replicates ( n ) , i.e. the number of flowers per treatment in the pollination experiments of Saxapaga mutata Open pollination X SE n 161.92 10.47 139 Artificial crossing 45.39 13.31 33 Spontaneous selfing ArtifiCal selfing Agamospermy 24.75 5.72 65 5.03 1.88 67 0.00 42 R. HOLDEREGGER 306 flowers (n = 2, seeds n = loo), and 65.8% in artificially selfed flowers (n = 10, seeds n = 500). Flower uisitors Only Hymenoptera and syrphids were caught in all three populations; Hymenoptera were: Andrm bicolor (Fabricius, 1775), Apis mellfera (Linnaeus, 1758), Bombus patorum (hnaeus, 176l), B. pascuorum (Scopoli, 1763), hioglossum calceatum (Scopoli, 1763), L.JiLlviCom (IGrby, 1802), L. morio (Fabricius, 1793), and L. ?.lsfitarse (Zetterstedt, 1838); Syrphidae were: EpZrtrophe sp., Plapckrus sp., Scaeva sp., Sphwophoria sp., and Sy-hus sp. Seed sizes and gemination experiments Seeds of S. mututa are spindle-shaped with a mean length of about 0.8 mm and a mean width of about 0.3 mm (Table 2). Seed sizes were only significantly different between populations T and F (ANOVA, d.f. = 83, length: P = 0.003, width: P < 0.001; 95% LSD pairwise comparison). Nevertheless, the differences in seed sizes were $0small among populations that they were assumed not to have significant effects on germination. All populations showed essentially the same course of germination in experiment A (Fig. 1A-C). Germination started slowly, and germination rate of all three populations averaged about 4o0/o after 20 weeks. In experiment B, populations reached germination rates between 40% and 80% after 20 weeks (Fig. 1D-F).Substantial differences occurred between the populations. In populations T and K germination was higher after stratification (experiment B) than without stratification (experiment A). Only a few seeds germinated after 24 weeks in populations T and K. In population F (Fig. 1E) germination after 24 weeks took an almost linear course. At the end of the experiment after 92 weeks, germination rates were between 83% and 96%. Seeds that had overwintered in capsules in the field germinated very quickly reaching 60% after four weeks. After 92 weeks, their germination rate was 88% (Fig. 1G). After dry storage at room temperature for 30 months, the germination of seeds was drastically decreased (experimentC; Fig. 1H-K). In populations T and K almost no germination occurred, while a germination rate of 22% was still observed in population F. TABLE 2. Seed length and seed width (pm) of Smj-ugu mututa in the populations TGsstal (T), FalHtsche (F), and KGsnacht (K). Mean (3,standard error (SE), and the number of replicates (mean of five seeds per individual; n) T Seed length X SE Seed width X SE n 854.4 11.2 327.4 4.1 30 F 793.0 9.9 302.6 4.1 29 K 827.2 12.6 322.3 4.4 28 REPRODUCTION OF U Z F R A G A MUTATA 307 Enzyme elecpophoresti AU cytologically investigated individuals of S. mutata from the three populations showed regular chromosome pairing in meiosis. The chromosome number was 2n = 26. B 0 4 8 12 16 20 0 12 24 36 48 60 72 84 - 0 tc 4 8 12 16 20 0 12 24 36 48 60 72 84 0 4 8 12 16 20 0 12 24 36 48 60 72 84 0 0 12 24 36 48 60 72 84 100 s '1 0 '5 H K I 80 60 40 20 0 0 12 24 36 48 60 72 84 96 0 12 24 36 4g 60 72 84 96 0 12 24 36 48 60 72 84 96 week week week Figure 1. Germination rates of seeds of Smzuga mutata (mean f SD). A-C, germination experiment A (no stratification). D-G, germination experiment B (I-F, seeds stored dry at room temperature for 10 months. G, seeds averwinteredin capsules in the field). H-K,germinationexperiment C (seedsstored dry at room temperature for 30 months). A,D,H, Population Tosstal, B,E,G,I, population Falltrche; C,F,K, population Kiisnacht. Sample sizes are given in the text. R. HOLDEREGGER 308 Enzyme loci Gpi-2,Mdh-1, Mdh-2, Mdh-3 were completely uniform. All individuals were heterozygous at the three Mdh loci and homozygous for Gpi-2.In population F all investigated individuals exhibited exactly the same multilocus genotype (Table 3). Only low variation was detected at the loci Idh and Skd in population K. The greatest variation, though still low, was detected in population T in Idh, P p - 2 and Skd. A strange Idh-enzyme phenotype, which occurred in two individuals, was interpreted as a combination of two heterozygote loci ‘ac’ and ‘bc’ (Table 3). Heterozygotes at the polymorphic loci Pgm-2 and Skd were rare in the investigated populations. DISCUSSION Breeding system and pollination Outbreeding is the dominant mating system in several Saxzjagu species, but selfing usually also yields seed (Stenstrom & Molau, 1992; Molau & Prentice, 1992; Lindgaard Hansen & Molau, 1994). In S. mutata, open pollinated individuals (assumed to receive mainly foreign pollen), and artificially crossed flowers had greater seed-set than spontaneously selfed or artificially selfed flowers (Table 1). In all pollination experiments viable seeds were obtained. Smajiaga mutata is thus expected to be mainly outbred but selfing is possible. The dominant mating system in its populations may be mixed. Artificially treated flowers yielded fewer seeds than flowers in spontaneous pollination treatments. This indicates that artificial pollination was not very successful (for possible reasons see Young & Young, 1992). Experiments showed no agamospermy in the studied populations. TABLE3. Genotype frequencies at 7 loci in the populations T6sstal (T), Falgtsche (F), and Kiisnacht (K) of Saxzpugu mututa (enzyme abbreviations according to Weeden & Wendel, 1989; number of individuals in parenthesis);a,b,c denote different alleles (e.g. ‘ab’ is a heterozygote and ‘aa’a homozygote) Locus Genotype T F K (3-2 aa 1.oo Idh aa ac (80) 0.80 1.oo (53) 1.00 (39) 0.14 0.86 ~~ bc 0.12 =/bc 0.08 (25) 1 .oo (73) Mdh-1 ab Mdh-2 ab Mdh-3 ab Pgm-2 aa ab bb Skd aa ab bb 1.oo (73) 1 .oo (73) 0.02 0.03 0.95 (66) 0.12 0.88 (25) - 1 .oo - - (11) 1 .oo (37) 1 .oo (37) 1 .oo (37) (14) 1 .oo (41) 1.00 (41) 1.oo (41) 1.00 1.00 (36) - - (22) - 1.00 (6) - - 0.03 0.97 (30) ~ REPRODUCTION OF SAXIFRAGA MULATA 309 Selfing may be supported by the kind of dichogamy in the protandrous flowers of S. mutata. At dehiscence, stamens bend towards the gynoecium one after the other. After this movement, they return to their original position. Stigmas reach receptivity at this time. After this female phase, just before the petals begin to wither, all the stamens again bend inwards and the remaining pollen may be deposited on the stigma surfaces (Holderegger, pers. observ.). Sax$iaga mutata has actinomorphic flowers, which are visited by Syrphidae and polylectic Hymenoptera, which unspecifically collect pollen (Kugler, 1970; Westrich, 1989). Both insect groups are frequently found in substantial numbers on flowering panicles of S. mutata. This spectrum of flower visitors is in accordance with other studies on SUX&~Uspecies (McGuire & Armbruster, 1991;Warncke & Olesen, 1991; Warncke et al., 1993; Lindgaard Hansen & Molau, 1994). Bees seldom fly on cloudy or cold days (Westrich, 1989), while Syrphidae are not so strongly influenced by adverse weather (Faegri & van der Pijl, 1971). On relatively cold, cloudy days in summer 1990 only Syrphidae were caught. They may ensure pollination of S. mutata flowers even in weather unfavourable for bees. The high seed-set in open pollinated flowers combined with self-compatibility and autodeposition indicate no pollen limitation in S. mutata. A pollen limited reproductive success was found in a subarctic tundra population of the almost obligate outcrosser S. opposit@liu L. (Stenstrom & Molau, 1992). Genetic vanation Hamel (1950, 1953) reported a chromosome number of 2n = 28 for S. mututa, but Kupfer & Rais (1983) tested some individuals near the sites where Hamel had sampled and found only plants with 26 chromosomes. From the Carpathians there is a report indicating a different chromosome number of 2n = 32 (Tarnavschi, 1981). In the present study all individuals had a chromosome number of 2n = 26. My counts thus agree with those of Kiipfer & Rais (1983), and it seems most probable that S. mutata is a diploid with a basic number of x = 13, which is found in many other Smtj?aga species (Webb & Gornall, 1989). Genetic variation within and among the three populations of S. mututa was very low. It was impossible to calculate meaningful genetic diversities using the methods of Nei (1972). In view of the small number of investigated loci and the differing sample sizes, the results on allozymes should be interpreted with caution. Low genetic variation is somewhat unexpected in an at least partially outbreeding species. They are often characterized by high levels of variation within populations (Schoen & Brown, 1991; Hamrick et aL, 1991). In addition, monocarpic species have been found to exhibit high genetic variation among populations (Hamrick, 1989). The presented allozyme data on S. mutata, therefore, are not in agreement with those that might have been predicted from the results of the breeding experiments. At the Mdh-loci, all plants showed the same heterozygous genotypes. At these Mdhloci, the diploid S. mutata had banding patterns similar to tetraploid species with fixed heterozygosity. Most plants were heterozygous at the Idh-locus; only very few homozygous plants were found. There were two individuals in population T with an Idh-banding pattern that looked like a combination of two heterozygous patterns (Table 3). Whether this was the result of a single gene duplication cannot be analysed without analysis of progeny. In P p - 2 and Skd most plants were homozygous. 310 R. HOLDEREGGER It seems unlikely that inbreeding could be the sole cause of the low genetic variation found in S. mutata, especially in view of the lack of differentiation between widely separated populations. Apomixis or vegetative reproduction could in principle lead to genetic uniformity in populations of Saxzzaga species (Bauert, 1994), but the former did not occur (Table l), and the latter is too rare to influence strongly the intrapopulational genetic variation; less than 8% of flowering individuals produced offsets (Holderegger, in press). A reason for the apparent genetic uniformity may be that the three populations were founded by diaspores with similar genotypes despite the great distances between the populations. Another possible explanation is that allozyme electrophoresis may have provided an inadequate representation of the extent of genetic variation in S. mutata. Germination Germination rates of Saxtj?aga species vary substantially. Reports show quick and high germination in S. hirculus L. (Ohlson, 1989; Dahlgaard & Warncke, 1995) or slow and low germination in S. paniculata Miller (Sapzhenkova, Syenchyna & Druchas, 1986). Germination rates of S. mutata reached about 40% after 20 weeks. After dry storage for more than 30 months, germination rates drastically decreased. Germination experiments are usually carried on for 2 or 3 months. Such experiments would not have detected the unusual course of germination in S. mutata. After 3 months only a moderate germination rate would have been detected (Fig. 1). Nevertheless, rates between 83% and 96% were reached after 92 weeks in experiment B. Successful establishment of many monocarpic species is only possible in vegetation-free gaps (Silvertown, 1983). Field observations showed that on sparsely colonized erosion-slopes seedling of S. mutata often grew in the shade of other plants, especially mature plants of S. mutata, Campanula cochleari$olia Lam., or Leontodon hzipidus ssp. hyoseroides (Welwitsch)J. Murr. Inflorescences of S. mutata are bent downwards during winter. If there are still viable seeds in the capsules, they will be released near to the mother plant. Many seedlings were found just below dead rosettes of S. mutata. In more closed vegetation, seeding occurred only on small patches of open soil. On rocks and cliffs, seedlings grew in crevices or on small ledges. Seedlings also grew in cushions of mosses like Barbula crocea (Brid.) Web. & Mohr, but not in stands of taller bryophytes like DitrichumJIexicaule (Schwaegr.) Hampe (Holderegger, pers. observ.). Suitable safe sites for S. mutata exist at any time during the year. A life history strategy, including seeds that either germinate immediately or else germinate in low numbers throughout the year, would increase the chance of successful establishment in an unpredictable habitat. In the field, seedling abundance of S. mutata was highest in spring (April, May, and earlyJune), but germination occurred almost throughout the year (Holderegger,pers. observ.). These field observations are in accordance with the results of the germination experiments. Conservation biology Populations of S. mutata are often small and isolated from each other (Webb & Gornall, 1989). In a river-valley or along a steep mountain slope, the species usually REPRODUCTION OF SAXZFMGA M W A T A 311 occupies several suitable sites, forming a set of local populations or a metapopulation (Hanski, 1991). Unfortunately, nothing is known about the potential dispersal abilities of S. mutata. Earlier authors (e.g. Daniker, 1939) have stated that S. mutata colonizes open erosion slopes but that ongoing succession excludes it from these sites. At the local scale S. mutatu will only survive if it is able to disperse and re-locate to another, perhaps recently eroded slope. Extinction and colonization events are inherent in the dynamics of local populations or metapopulations of S. mututu. Selfing may be of great importance for the successful colonization of hitherto unoccupied patches in the above mentioned population dynamics (Baker, 1955). In respect to the allozyme data and the large set of viable seeds of selfed flowers, one may conclude that selfing has had no deleterious effects in populations of S. mutata. Lande (1988) concludes that demographic processes are more important for the maintenance of local plant populations than are genetic processes. Frankham (1 995) stresses that the responses of populations to demographic and environmental stochasticity are affected by inbreeding or loss of genetic variation as well. In this case, extinctions can be incorrectly attributed to nongenetic factors rather than to interactions between genetic and nongenetic factors. Lande & Schannon (1996)show that in the short-term genetic variation is theoretically less critical than other determinants of population persistence, but that in the long-run it plays a decisive role in population persistence and adaptation to a changing environment. In S. mutata, succession and erosion are most important in determining the size of local populations (Holderegger, in press). Size structure, timing of reproduction, and recruitment within the populations are strongly related to the course of succession. Loss of landscape erosive processes due to protective measures like river embankments is thus the major threat to populations of S. mutata. ACKNOWLEDGEMENTS Elena Conti, C.D.K. Cook, F. Gugerli, and JJ. Schneller made valuable comments on earlier versions of the manuscript and improved my English. A. Muller helped in the determination of Hymenoptera. Special thanks go to Q.O.N. Kay for very carefully reviewing the paper, and greatly enhancing its contents and strength. REFERENCES Baker HG. 1955. Self-compatibility and establishment after “long-distance” dispersal. Evolution 9: 347-349. Barrett SCH, Kohn JR.1991. Genetic and evolutionary consequences of small population sue in plants: implications for conservation. In: Falk DA, Holsinger KE, eds. Gmetics and consmabn of rure plants. New York Oxford University Press, 3-30. Bauert MR. 1994. Voruntersuchungen der genetkchen Variabilitat eiszeitlicher Relitpopulationen von Sunzuga cmua. Botanka Helvelka 104: 2 15-220. Dahlpard J, Warncke E. 1995. Seed set and germination in crosses within and between two geographically isolated small populations of Smzuga hirculuc in Denmark. NordicJounalofBofany 15: 337-341. Diiniker AU. 1939. Die Wanzengesellschaft, ihre Stn&tur und ihr Standort. B&ht h SchWeiZeischm Botankchm Gsellschnz 49: 522-5443, Darlington CD, LaCour LF. 1976. Ihe handling $chromosomes, 6 ed. London: M e n and Unwin. Ellstrand NC, Elan DR. 1993. Population genetic consequences of small population sizes: implications for conservation.Annual Reuierv OfEcoloQ and $sternatics 24: 217-242. 312 R. HOLDEREGGER Faegri K, van der Pijl L. 1971. 7heprinciples ofpollination e c o l o ~ .Oxford: Pergamon Press. Frankham R. 1995. Conservation genetics. Annual Rpoiew ofGwtiLs 29: 305-327. Gilpia ME, Sod6 ME. 1986. Minimum viable populations: processes of species extinction. In: Soult ME, ed. Conservation b w h . : the science OJscardy and dim+. Sunderland: Sinauer, 19-34. HamelJL. 1950. Notes prtliinaires a I'itude caryologiques des Saxifragactes. V. Les chromosomes somatiques de six saxifrages appartenant a la section Euaizoonia (Schott) Engler. Bulktin du Murie de 1'HiStoire Natureh 22: 7 8 5 ~789. ~ HamelJL. 1953. Contribution a I'ttude cyto-taxinomiquedes Saxifragactes. Rarue de Cytoh,gie et de Biolo& figitales 14: 113-313. HamrickJL. 1989. Isozymes and the analysis of genetic structure in plant populations. In: Soltis DE, Soltis PS, eds. Isozpnes in plant bwhgy. Portland: Dioscorides, 87--105. Hamrick JL, Godt MJW, Murawski DA, Loveless MD. 1991. Correlations between species traits and allozyme diversity: implications for consenration biology. In: Falk DA, Holsinger KE, eds. Gemtics and conrervation ofrare plants. New York Oxford University Press, 75-86. Hanski I. 1991. Single-species metapopulation dynamics: concepts, models, and observations. Biohgi~alJoumalof the Lannean &ci& 42: 17-38. Harvey HJ. 1985. Population biology and consenration of rare species. In: White J, ed. Studies on plant demograph. d fiestschnflfmJohn L. Harper. London: Academic Press, 11 1-123. Holderegger R. 1994. Zur Flora und Vegetation des Kiisnachtertobels:Veranderungen innerhalb der letzten 50 Jahre. Botanica Hehetka 104: 55-68. Holderegger R. Intrapopulational size structure of the monocarpic species Samzaga mutata and its relationship to succession. Flora, in press. Holderegger R, Schneller JJ.1994. Are s m d isolated populations of A s p h i u m septenhionale variable? Biological Journal ofthe Linnean So&p 51: 377-385. Kaplan K. 1995. Saxifragaceae. In: Weber HE, ed. Hegi G. Ill~~tri&Flnra uon Mittehuropa, IV2A, 3.ed. Berlin: Blackwell, 130-229. Kugler H. 1970. Bliitmoblogk. Stuttgart: Gustav Fischer. Kiipfer P, Rais JR. 1983. Index des nombres chromosomatiques des spermatophytes de la Suisse. I. Saxifragaceae. Botanica Helwtica 93: 11-26. Lande R. 1988. Genetics and demography in biological consemation. Science 241: 1455-1460. Lande R, Shannon S. 1996. The role of genetic variation in adaptation and population persistence in a changing environment. Evolution 50: 434-437. Laadolt E. 1991. Gfdrdung der Fam- und BlifenpJanzm in der &hu& mitgesamtschweiraischm und r q i o n a b rotm htm. Bern: BCWAL. Lindgaard HansenJE, Molau U. 1994. Pollination biology, mating system, and seed set in a Danish population of S m j a g a granulata. .Vordu Journal of Botany 14: 257-268. Loveless MD, Hamrick JL. 1984. Ecological determinants of genetic structure in plant populations. Annual Ranmi ofEcohgy and .$sternatics 15: 65-95. McGuire AD, Armbruster WS. 1991. An experimental test for reproductive interactions between two sequentially blooming Saxzzaga species (Saxifragaceae).AmeriGan Joumal ofBotany 78: 2 14-219. Molau U, Prentice HC. 1992. Reproductive system and pollination structure in three Samjaga species. Joumal of ECO~OQ 80: 149- 161. Nei M. 1972. Genetic distance between populations. American Naatralirt 106: 283-292. Ohlson M. 1989. Ecotypic differentiation and phenotypic plasticity in h j a g a hirculur populations in central and northern Sweden. HolarctiL Ecology 12: 4 6 5 3 . OostermeijerJGB, Eijck M W ,vaa h e u w e n NC, den NijsJCM. 1995. Analysis of the relationship between allozyme heterozygosity and fitness in the rare Cenhhna pneumonanthe L. Joumal of Evolutionary Biologv 8: 739-759. Ouborg NJ, van Treuren RV. 1994. The significance of genetic erosion in the process of extinction. IV. Inbreeding load and heterosis in relation to population size in the mint Saluia pmtennsir. ~~r!,ohtioion48: 9961008. Saebs L. 1992. Angewandte Statistik, 2.ed. Berlin: Springer. Sapzhenkova W , Syenehyna BV, Druchas IV. 1986. Seed germination in some species of Carpathian mountain plants in culture conditions. Ukraine BotanicalJoumal43(5): 28-31. (In Russian.) SchnellerJJ, &he&& W. 1989. Agarose gel electrophoresisof fern extracts to detect enzyme polymorphisms. An alternative method to starch " eel electroDhoresis. Botanica Helvetica 9% 197-202. Schneller JJ,Holderegger R. 1996. Genetic variation in small, isolated fern populations. Joumal of Vegetatzon S&re 7: 1 13- 120. Schoen DJ, Brown AHD. 1991. Intraspeciiic variation in population gene diversity and effective population size correlates with the mating system in plants. Proceedings 0ftheNational Academy ofSciences 88: 4494-4497. SilvertownJW. 1983. Why are biennials sometimes not so few? American Naturalist 121: 448-453. Soltis DE, Haufler CH, Darrow DC, Gastony GJ. 1983. Starch gel electrophoresisof ferns: a compilation of grinding buffers, gel and electrode buffers, and staining schedules. Ammcan FmJoumal73: 9-27. Stenstdm My Molau U. 1992. Reproductive ecology of Samzaga opposttifolta: phenology, mating system and reproductive success. A r c h and Alpine Research 24: 337-343. REPRODUCTION OF SAXIFRAGA Mu7ATA 313 Tarnavschi IT. 1981. Die Chromosomenzahlen der Arten Sux$aga demissa Schott et Kotschy und Sanfiaga mutata L. aus Rumanien. Revue Roumaine de Biolopie, Eiolopie Egitale 26: 79-81. van Treuren R, Bijlsma R, Ouborg NJ, v m Delden W. 1993. The significance of genetic erosion in the process of extinction. TV.Inbreeding depression and heterosis effects caused by selfing and outcrossing in Scabiosa columbaria. Evolution 47: 1669-1680. Warncke E, OlesenJM. 1991. Smj?aga hirculur L. Patch size and seed set. Acta Horticulturae 288: 326-328. Warncke E, T e m p U, Michelsen V, Erhardt A. 1993. Flower visitors to Smzuga hirculur in Switzerland and Denmark, a comparative study. Botanica Helvetica 103: 141-147. Webb DA, Gornall RJ. 1989. Smzages OfEurope. London: Christopher Helm. Weeden NF, WendelJF. 1989. Genetics of plant isozymes. In: Soltis DE, Soltis PS, eds. Isoqmes in plant biology. Portland Dioscorides, 46-72. WendelJF, Weeden NF. 1989. Visualization and interpretation of plant isozymes. In: Soltis DE, Soltis PS, eds. Isoqmes in plant biology. Portland: Dioscorides, 5545. Westrich P. 1989. Die Wild6ima Baden-Wirhbergs. Stuttgart: Eugen Ulmer. Young HJ,Young TP. 1992. Alternative outcomes of natural and experimental high pollen loads. Ecology 73: 639447.
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