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. 2023 Jul 25;12(15):2753. doi: 10.3390/plants12152753

New Finds and Ecology of the Rare Liverworts Scapania apiculata, Scapania carinthiaca, and Scapania scapanioides in Austria

Michaela Kropik 1, Harald G Zechmeister 1,*
Editor: Marko Sabovljevic1
PMCID: PMC10421421  PMID: 37570907

Abstract

Scapania apiculata, Scapania carinthiaca, and Scapania scapanioides are rare deadwood-dwelling liverworts threatened across Europe. Scapania carinthiaca is thus listed in the Habitats Directive. However, their distribution data are scattered, and their ecologic demands are insufficiently studied. Here, we present new locations and data on the ecology of the species, which resulted from a targeted search in selected regions of Austria. We found ten new sites each for Scapania apiculata and Scapania scapanioides and twenty for Scapania carinthiaca. Reproduction was exclusively asexual. The macroclimates of all known locations in Austria did not differ significantly between the three species. It was consistently wet, with a mean annual precipitation of 1615.3 mm, a high evenness of rainfall, and a low desiccation risk. The mean temperature averaged 7.4 °C. The habitat was shaded dead wood of Picea abies, Abies alba, and Fagus sylvatica of all decay stages at a median distance of 2.5 m from streams or springy areas in semi-natural forests of montane and submontane regions. Thus, high deadwood volumes under a suitable climate are a prerequisite for the occurrences of the species. The number of locations of new finds has more than doubled in Austria and thus in Europe.

Keywords: bryophytes, epixylic, deadwood, climate, Habitats Directive, IUCN Red List of Threatened Species, conservation

1. Introduction

Scapania apiculata Spruce, Scapania carinthiaca J.B.Jack ex Lindb., and Scapania scapanioides (C. massal.) Grolle are three rare deadwood-dwelling liverworts of exceptional smallness within the species-rich genus Scapania (Scapaniaceae, Jungermanniales), which still raises taxonomic questions [1,2]. With a size of only a few millimetres, the three species are easy to overlook, and a targeted search is like looking for a needle in a haystack.

These are north-temperate species, but their range is still insufficiently known [3]. Reports to date have come mainly from the mountains of Central Europe, Scandinavia, and North America [4,5]. In Austria, there are 16 published records of S. carinthiaca—many of which are in the south of Austria, in Carinthia—ten for S. apiculata, and five for S. scapanioides [6]. In the neighbouring countries Germany and Liechtenstein, S. apiculata is expected to occur but without endangerment classifications [7]; the Czech Republic classifies the species as critically endangered [8]; in Switzerland, it has the status endangered; Italy and Hungary state insufficient distribution data; in Slovenia, there are doubts about its occurrence [7,9]; and in Slovakia, it is classified as least concern [10]. S. carinthiaca is regionally extinct in Slovakia [10]; critically endangered in Germany [11], Italy, the Czech Republic, and Slovenia [7]; and endangered in Liechtenstein [12] and Switzerland [7]. S. scapanioides is known to occur only in Italy and Switzerland. There, it is classified as endangered [7]. The classifications for Europe [3,7] for S. apiculata (LC), S. carinthiaca (EN), and S. scapanioides (CR) might thus change due to an improved data situation in the future.

The reported habitat for the European sites is deadwood in humid, shady areas; the colonised logs are mostly near mountain streams, in ravines, or on deadwood in mountain forests influenced by slope pressure water [6,13,14,15]. Except for Scapania carinthiaca, there are also reports of the species on siliceous rocks near streams [6].

Overall, the data on this species group are incomplete and partly contradictory. Since S. carinthiaca is a species of Annex II of the Habitats Directive and thus subject to monitoring and reporting obligations, knowledge has improved the data situation for the entire species group to some extent, but studies on their ecology are lacking. Therefore, this study aimed to deepen the knowledge of the distribution and ecological requirements of the target species in Austria so that future surveys can be more targeted.

2. Results

2.1. Distribution and Ecology

In total, we found 17 colonised deadwood logs at ten study sites with S. apiculata (Figure 1), 29 deadwood logs at twenty study sites with S. carinthiaca (Figure 2), and 11 deadwood logs at ten study sites with S. scapanioides (Figure 3). In several cases, the three species co-occurred. According to the project regions, study sites were located in the Alpine region of Styria, Salzburg, Lower and Upper Austria (see Appendix A, Table A1 for details), with a distribution focus in the Northern Limestone Alps.

Figure 1.

Figure 1

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Location of ten previously published finds (yellow, see Appendix A, Table A2) and ten new finds (red) of S. apiculata in Austria.

Figure 2.

Figure 2

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Location of 16 previously published finds (yellow) and 20 new finds (red) of S. carinthiaca in Austria.

Figure 3.

Figure 3

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Location of 5 previously published finds (yellow) and 10 new finds (red) of S. scapanioides in Austria.

The macroclimates in the Austrian sites known so far did not differ significantly between the three species regarding the mean annual temperature (H(2) = 0.124; p = 0.54), mean annual precipitation sum (H(2) = 1.49; p = 0.47), desiccation risk (H(2) = 2.49; p = 0.29), or evenness of precipitation (H(2) = 0.62; p = 0.73). Therefore, in Figure 4, we present the climate indicators for all new and previously published sites in one boxplot. The macroclimate was consistently wet, with a mean annual precipitation of 1615.3 mm. The mean annual temperature averaged 7.4 °C. The precipitation distribution showed a high evenness, with at least one millimetre of rain falling on an average on more than 126 days per year. At the same time, the risk of desiccation in the growing sites was low; the maximum number of precipitation-free days with a temperature of more than 20 degrees averaged 5.9 days.

Figure 4.

Figure 4

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Climatic conditions at the Austrian locations of S. apiculata, S. carinthiaca, and S. scapanioides: boxplots of mean annual precipitation sum (prec_sum), mean annual temperature (temp_mean) in °C, evenness of precipitation (daysprec11), and desiccation risk (p0cont_gt_20) based on 71 finds (including previously published ones) across Austria.

Within this distinctly wet macroclimate, the microclimate was also humid and reduced the risk of desiccation. Growth sites were on lying deadwood shaded all day long directly adjacent to streams in headwaters (trout region) in ravines or north-exposed forests influenced by spring areas or slope water. The median distance to the water course was 2.5 m. Thus, the local risk of desiccation in the place of growth was low to unlikely.

Regarding altitude, the finds came from the montane to submontane region (Figure 5), with a few exceptions.

Figure 5.

Figure 5

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Boxplots showing the altitude of Austrian locations of S. apiculata, S. carinthiaca, and S. scapanioides.

The logs of the host trees had diameters of at least 30 cm, but most were significantly larger. Host trees showed decay stages from 2 to 5 except but did not show decay stage 1 with still-intact bark. Most finds of S. carinthiaca were from Picea abies, and some finds were from Fagus sylvatica and Abies alba. S. apiculata occurred relatively evenly on Picea abies, Abies alba, and Fagus sylvatica; S. scapanioides mainly occurred on Picea abies and rarely occurred on Abies alba.

2.2. Characteristics of the Target Species

As is characteristic of the genus, the leaves of the target species consist of a smaller dorsal and a larger ventral lobe. In the target species, the lobes enclose the stem in a sheathing manner and do not run down it. The leaf bases are not keeled. Characteristically, single- or two-celled gemmae, depending on the species, serve for vegetative reproduction. They are located either on the leaf margins or erect flagellar shoots. The perianth mouth is entire, but a perianth is rarely present. Usually, large parts of the stem are covered densely with long rhizoids.

A first delimitation of the three target species within the genus is allowed by the location: the tiny target species, of only a few millimetres in size, occur almost exclusively on lying deadwood at wet sites, except for S. carinthiaca, which was found sporadically on wet silicate rock. Gemmae are advantageous for reliable identification, especially for distinguishing the target species from the juvenile and vestigial forms of other species within the genus Scapania. All our finds had abundant gemmae. However, we never observed a perianth. S. scapanioides can be distinguished from the other two species by its two-celled, broadly oval gemmae of brown colour (Figure 6). However, S. carinthiaca and S. apiculata have unicellular gemmae. They are brown in S. carinthiaca (Figure 7) and reddish-brown to black in S. apiculata (Figure 8). The gemmae of S. apiculata often sit at the tip of erect small-leaved shoots or, as observed in S. carinthiaca, at the leaf margins A clear differentiation of S. apiculata from S. carinthiaca is made possible by the triangularly thickened cell corners of S. apiculata (Figure 8). Furthermore, S. carinthiaca has conspicuously pointed upper lobes, which are pronouncedly smaller than the lower lobes at the shoot tips and are oriented towards the shoot tip (Figure 7); by contrast, the rectangular upper and lower lobes in S. apiculata are nearly equal in size. Table 1 summarises the particularly well-differentiated characteristics of the target species.

Figure 6.

Figure 6

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Photographs of S. scapanioides in situ (top left), a single plant (top right), its cells (bottom left), and its bicellular, brown gemmae (bottom right).

Figure 7.

Figure 7

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Photographs of a characteristic location of S. carinthiaca on deadwood (top left); a single plant (top right); its cells, with characteristically unequal size and slightly bulging leaf margin (bottom left); and its unicellular brown gemmae (bottom right).

Figure 8.

Figure 8

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Photographs of S. apiculata in situ (top left); a single plant (top right); its characteristic cells, with strongly triangularly thickened cell corners (bottom left); and the unicellular gemmae (bottom right).

Table 1.

Well-differentiated characteristics of the deadwood-dwelling liverworts S. apiculata, S. carinthiaca, and S. scapanioides.

S. apiculata S. scapanioides S. carinthiaca
Cell corners Strikingly triangular thickened Not thickened Not thickened
Gemmae Unicellular
reddish to black		 Bicellular
brown		 Unicellular
brown
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3. Discussion

3.1. Distribution and Ecology

The present data improve the knowledge about the distribution of the three species in Austria by providing ten new records each for S. apiculata and S. scapanioides and twenty new records for S. carinthiaca. The S. carinthiaca finds known so far have mainly been in Carinthia [6], where the species was first described [4] and to which the epithet refers. However, the Northern Limestone Alps seem to be another centre of its distribution (Figure 1, Figure 2 and Figure 3), as the current surveys showed. S. apiculata and S. scapanioides seem to have a similar distribution. However, it is still not fully clarified. Targeted searches in individual provinces, such as Tyrol, lead us to expect further finds. The small species are easy to overlook in quadrant-based mappings and occurred only in small populations, as was observed by others [5]. Therefore, we recommend targeted searches.

Concerning habitat, the three target species in Austria occur predominantly in sub-montane to montane regions [6], as confirmed by this study (Figure 5). All our finds of the target species were on deadwood, as Müller [4] also stated. However, isolated records of S. carinthiaca from wet silicate rocks occur in Austria [6]. In general, the substrate was acidic, as observed by others [5], with flooding increasing the base content [6]. The species have been found on peat on rock walls in North America [5] and on softwood in Scandinavia [16], but they have not been found in these habitats in Austria. Apart from Fagus sylvatica, the three target species we found mainly on the coniferous wood of the host trees Picea abies and Abies alba in the upper reaches of streams. Lying deadwood of early decay stages at a median distance of 2.5 m from a stream seems ideal for colonization under the prevailing conditions in Austria. Regular flooding, which might increase the base content of the deadwood logs, seems to be a prerequisite for the target species [6]; however, very wet, permanently flooded deadwood seems unsuitable as a habitat. We observed microfilms under such conditions, which could hinder the establishment of the target species, as was also observed in deadwood communities [17].

The terpenoids observed in Scapania carinthiaca [18] might favour survival under these wet conditions. They are also known to occur on other bryophyte species [19] and serve in other biotic and pathogenic interactions, such as interactions with fungi, which presumably benefit from the extremely humid conditions. However, no studies in this regard are available for the target species. Likewise, the fungal growths visible in cross-section, as also described by Schuster [5], have not yet been studied in detail; such studies could provide further information on moss–fungus interactions.

There are probably also physiological reasons why excessively wet conditions have an unfavourable effect on the occurrence of the target species. In water, gas diffusion is decreased by a factor of about 104 compared with that in air, and thus the respiration and photosynthesis rates of poikilohydric moss plants are also reduced [20]. Many finds have originated from logs of decay stage two, on which competition from fast-growing pleurocarpous species is still low. Vigorous species might hinder the establishment of the target species on logs of later decay stages. Beyond that, however, the species persist to late decomposition stages.

In addition to an adequate substrate, however, a macroclimate with high precipitation is a prerequisite for the occurrence of the target species. High and evenly distributed rainfall reduces the risk of desiccation, which is limiting for moist-adapted deadwood liverworts [21]. In addition, the location of the microsites on shaded, permanently moist deadwood, predominantly along streams, further reduces the risk of desiccation. The average number of warm days (over 20 °C) in a row without precipitation was 5.9 days, and desiccation was thus low. These results were consistent with the findings on Buxbaumia viridis (Moug. ex Lam. & DC.) Brid. ex Moug. & Nestl. [22] and other forest bryophytes, for which, depending on the species, desiccation of four to ten days is limiting [22,23].

As a corollary, favourable conditions for occurrence include high deadwood volumes with a low desiccation risk and consistently high (air) humidity along streams, as well as all-day shading of the growing site, as is the case in narrow gorges, for example. Some finds have been from mountain forests with very high precipitation, where deadwood logs influenced by slope water may provide suitable habitats. According to current data, Austria is highly responsible for all three species.

3.2. Implications for Management and Conservation

According to current knowledge, the rarest of the three species is S. scapanioides, as assumed for Europe, where the IUCN [15] estimated no more than 50 individual equivalents, although it admitted that the distribution was poorly clarified. The threat categories for the Austrian provinces (Table 2) need to be adjusted according to the latest data from this study and supplemented by the new finding of S. scapanioides in Lower Austria.

Table 2.

Status of S. apiculata, S. carinthiaca, and S. scapanioides in the Red Data Lists of the Austrian provinces Carinthia [24], Lower Austria [25], Upper Austria [26], and Vorarlberg [27] and Red List Status for Austria and Europe [3] based on the IUCN categories: CR—Critically Endangered, EN—Endangered, NT—Near Threatened, VU—Vulnerable; °—Occurrence of the species confirmed (either least concern or no information about status).

Carinthia Lower Austria Upper Austria Vorarlberg Austria Europe
S. apiculata EN CR EN - VU NT
S. carinthiaca VU CR EN CR ° EN
S. scapanioides EN - EN - VU CR
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Most of the Austrian occurrences are in protected areas (see Annex), which is advantageous because the target species are strongly dependent on natural dynamics, which, outside protected areas, often collide with flood protection or power plants.

The three Scapania species are weak in competition and settle on deadwood in low to middle decomposition stages, where the competition from fast-growing mosses and vascular plants is negligible. Due to the decomposition process, succession to more vigorous species, especially mosses, can be observed [28,29], and these species often overgrow the tiny Scapania species, as observed by others [30].

Apart from the competition, a deadwood log has a finite lifespan and is subject to high site dynamics along streams. Flooding causes deadwood logs to be relocated or completely uprooted from favourable sites. A sufficient supply of potentially colonisable deadwood logs is, therefore, a prerequisite for the long-term survival of the target species. They must be able to compensate for local extinction on a single deadwood log by successfully colonising elsewhere. Currently known populations will thus disappear in the future, together with their habitat, while ideally, suitable growth sites will emerge elsewhere and be successfully colonised. These population dynamics require large amounts of deadwood of larger diameters; deadwood of smaller diameters was populated only in exceptional cases, as others have also reported [29,31]. An important factor is the continuous shading and thus low desiccation risk of the host tree logs, which is less of a problem in narrow ravines and under closed canopy covers in forests. The increase in beetle calamities or windthrows and the loss of old-growth forests and virgin forests throughout Europe [32] are thus threats to the three target species. Management should thus consist of maintaining or restoring semi-natural forests along mountain streams and leaving deadwood of larger diameters, especially along shady stream margins, preferably in narrow gorges. The same applies to deadwood bryophytes in general, for which 60 m3 of lying deadwood per hectare with a diameter over 30 cm was the critical threshold for species-rich communities [22]. This measure also fosters the biodiversity of other deadwood-related species groups [33,34,35,36]. Softwoods, such as willow observed in Norway [16], do not seem to be an adequate substrate under the conditions prevailing in Austria.

In addition, the persistence of a population depends highly on the successful formation of reproductive units. Gemmae were found at all sites, but no perianths were found. Vegetative reproduction thus appears to be the main form of reproduction in the three target species. Asexual reproduction is generally widespread in temperate liverworts, especially in harsh environments [37]. This has been considered a means of maintaining local populations [37], as gemmae have higher survival rates than spores due to their size, and they germinate faster than the latter [38]. However, asexual reproduction reduces the spatial scale of dispersal in terrestrial environments [38], but this should not adversely affect the target species, as their gemmae are most likely dispersed downstream by water. However, asexual reproduction may help the target species maintain well-adapted phenotypes in an ecologically stable habitat [39]. The factors that control the formation of reproductive units have not yet been studied in detail for the target species. Concerning metapopulation ecology, vital populations in the upper reaches could act as source populations to supply lower-lying growing sites with diaspores [40,41]. Water is most likely responsible for the dispersal of the gemmae of the target species. Compared with terrestrial habitats, where dispersal capacity is usually limited to a few centimetres [38,42,43], water overcomes long distances; however, dispersal remains confined further down the watercourse, and the contribution of a coincidence to finding an adequate deadwood log is very high. The extent to which animal vectors, as assumed in a few previous studies [44,45], are relevant for dispersal may also play a role in the target species’ colonisation of new stream systems, and concerning upstream dispersal, this requires a focused investigation. Dispersal by spores seems to occur only in exceptional cases, at least in the Austrian growing sites. Thus, dispersal limitation could be an influencing factor for the target species but requires further investigation.

As a corollary, it takes much deadwood under a suitable climate in the upper reaches of mountain streams, often removed outside protected areas due to the risk of clogging. To further improve data, targeted searches are advantageous. Monitoring should take into account natural population dynamics.

4. Materials and Methods

We collected data between 2012 and 2022 within several projects [46,47,48,49]. The study on deadwood bryophytes [49] represented Austria in terms of its climatic gradient and different available deadwood volumes of forest sites. It followed a standardized random method [17] and first brought baseline data on the distribution and ecological requirements of the target species. On the basis of these and knowledge from previous locations in Austria [6], targeted searches were carried out in further projects [46,47,48] focused on the occurrence of species listed in Annex II of the Habitats Directive, including S. carinthiaca. After selecting potential locations on the basis of our previous experiences, preliminary mapping, and terrain data, we specifically searched numerous deadwood logs for the occurrence of the target species in these areas. The target regions of the projects were the provinces of Lower Austria, Styria, and the Kalkalpen National Park in Upper Austria. Searches in previously published locations in Austria were not carried out for this study, as these locations are recent. We thus assumed that the species still occurred there.

M.K. and H.Z. performed the field surveys and microscopic identification of species. Specimens are in private herbaria. The nomenclature of the bryophytes followed the Austrian Checklist of Bryophytes [50]. Because of the comparably small number of finds, the target species still raise taxonomic questions that remain incompletely resolved, and species concepts are partly contradictory, e.g., [4,5,51,52]. Buch [53] placed Scapaniella as a separate genus of tiny Scapania species without distinct stem cortex differentiation, within which he distinguished S. apiculata as a separate section. Crandall-Stotler et al. [54] also placed Scapaniella as a genus. Müller, on the other hand, placed S. apiculata and S. carinthiaca in the group Scapaniella alongside S. massalongii and S. glaucocephala but did not consider a separate genus of Scapaniella to be justified because its characteristics correspond to the genus Scapania. Like Potemkin [55] and Köckinger [6], we synonymised C. carinthiaca and C. massalongii. Likewise, we considered S. glaucocephala to be synonymous with S. scapanioides, as others have proposed [2,6].

We extracted the climate data for historical and new sites from the SPARTACUS gridded dataset [56,57] of the Central Institute for Meteorology and Geodynamics (ZAMG). It has a spatial resolution of one square kilometre and a temporal resolution of one day between 2004 and 2018. On the basis of these data, we calculated the mean annual temperature (temp_mean) in °C and mean annual precipitation sum (prec_sum). We aimed to depict the evenness of precipitation (daysprec11) by calculating the number of days with at least one millimetre of precipitation and a mean temperature above 0 °C since bryophytes benefit more from regular (even light) rain than from isolated heavy rain events [58]. As an approximation of desiccation risk [21], we calculated the maximum number of consecutive days without precipitation whose mean daily temperature was more than 20 °C (p0cont_gt_20) since desiccation is a limiting factor for moisture-adapted forest bryophytes [23,59,60], the deadwood specialist Buxbaumia viridis [22], and species-rich deadwood communities in general [17]. We reported the decay stage of host tree logs in a five-part scale following the Swiss Forest Inventory [61,62]: Decay stage 1 describes sap-bearing fresh wood with the bark still intact; decay stage 2 stands for sapless, firm hardwood that is difficult to penetrate with a pocket knife in the direction of the grain. In rotten wood of decay stage 3, this is easily possible in the direction of the grain but not across it; in soft rotten wood of decay stage 4, this is possible regardless of grain direction with only a little pressure. Decay stage 5 describes mulch wood that is barely coherent and very loose. We generated statistics, including the boxplots, using R statistical software [63], version 4.0.3. If the locations of the three species differed regarding the given climate variables, we performed a Kruskal–Wallis test.

Acknowledgments

We thank Heribert Köckinger for confirming numerous specimens, Ingeborg Lang and Helmuth Goldammer for their support with microscope photography, Dietmar Moser for his help in preparing the climate data, and two anonymous reviewers for their constructive feedback. Open Access Funding by the University of Vienna.

Appendix A

Table A1.

New reports of S. apiculata, S. carinthiaca, and S. scapanioides in Austria.

Species Finder Site N P Quad Date
1 S. apiculata HZ Rothwald, Kleiner Urwald * 1 L 82562 6 August 2012
2 S. apiculata MK and HZ Hintere Saigerin * 1 U 82533 18 July 2017
3 S. apiculata MK and HZ Toplitzsee * 1 St 83492 28 July 2017
4 S. apiculata MK and HZ Rothwald, Großer Urwald * 4 L 82562 10 July 2019
5 S. apiculata MK and HZ Lahnsattel 2 L 82591 20 June 2019
6 S. apiculata MK and HZ Brutgern * 1 S 83452 7 July 2020
7 S. apiculata MK and HZ Grießbachkessel * 1 S 82453 8 July 2020
8 S. apiculata MK and HZ Zellerbrunnbach * 1 St 82562 16 July 2020
9 S. apiculata MK and HZ Zellerbrunn-Dürradmer * 2 St 82562 17 July 2020
10 S. apiculata MK and HZ Josefsgraben * 3 St 83534 4 July 2022
1 S. carinthiaca MK and HZ Rothwald, Großer Urwald * 3 L 82562 9 July 2019
2 S. carinthiaca MK and HZ Groißnalm, Kalkalpen * 1 U 82523 18 July 2016
3 S. carinthiaca MK and HZ Kulisse, Kalkalpen * 1 U 82521 17 August 2016
4 S. carinthiaca MK and HZ Rettenbachtal * 1 St 83482 3 June 2017
5 S. carinthiaca MK and HZ Mitterwand * 1 St 83482 5 June 2017
6 S. carinthiaca MK and HZ Koppentraun left bank 1 St 84481 23 July 2019
7 S. carinthiaca MK and HZ Kammersee * 1 St 83494 25 July 2017
8 S. carinthiaca MK and HZ Toplitzsee * 1 St 83492 28 July 2017
9 S. carinthiaca MK and HZ Krumme Steyerling * 2 U 82521 7 June 2019
10 S. carinthiaca MK and HZ Lahnsattel 1 L 82591 21 June 2019
11 S. carinthiaca MK and HZ Grimmingbach N Gnanitzalm * 1 St 84501 24 July 2019
12 S. carinthiaca MK and HZ Haselschlucht, Kalkalpen * 1 U 82522 7 June 2020
13 S. carinthiaca MK and HZ Brutgern * 1 S 83452 7 July 2020
14 S. carinthiaca MK and HZ Grießbachkessel * 3 S 82453 8 July 2020
15 S. carinthiaca MK and HZ Ufer des Schallerbachs * 3 St 82564 13 July 2020
16 S. carinthiaca MK and HZ Salza, Prescenyriegel * 1 St 83564 13 July 2020
17 S. carinthiaca MK and HZ Zellerbrunnbach * 3 St 82562 16 July 2020
18 S. carinthiaca MK and HZ Josefsgraben, S Kropfbründl, Gesäuse * 1 St 83534 4 July 2022
19 S. carinthiaca MK and HZ Wasserfallweg, Gesäuse * 1 St 84532 5 July 2022
20 S. carinthiaca MK and HZ Ebner-Klamm: Schlucht 1, Gesäuse * 1 St 84534 7 July 2022
1 S. scapanioides MK and HZ Groißnalm, Kalkalpen * 1 U 82523 16 July 2016
2 S. scapanioides MK and HZ Krumme Steyerling * 1 U 82521 7 June 2019
3 S. scapanioides MK and HZ Geißlucke, Kalkalpen * 1 U 82522 10 June 2019
4 S. scapanioides MK and HZ Lahnsattel 1 L 82591 21 June 2019
5 S. scapanioides MK and HZ Wasserlochklammm, Wildalpen * 1 St 82553 13 July 2019
6 S. scapanioides MK and HZ Ufer des Schallerbachs, Wildalpen * 1 St 82564 13 July 2020
7 S. scapanioides MK and HZ Zellerbrunnbach, Wildalpen * 1 St 82562 16 July 2020
8 S. scapanioides MK and HZ Ebner-Klamm: Schlucht 1, Gesäuse * 2 St 84534 7 July 2022
9 S. scapanioides MK and HZ Ebner-Klamm: Schlucht 2, Gesäuse * 1 St 84534 7 July 2022
10 S. scapanioides MK and HZ Rohr-Bach, Gesäuse * 1 St 84532 8 July 2022
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Abbreviations are as follows: Finder: MK = Michaela Kropik, HZ = Harald G. Zechmeister; Site: * = Protected area; N = Number of colonized logs; P = Austrian province, L = Lower Austria, S = Salzburg, St = Styria, U = Upper Austria; Quad = Quadrant of the Austrian Flora Mapping; Date = Date of discovery.

Table A2.

Previously published reports of S. apiculata, S. carinthiaca, and S. scapanioides in Austria.

Species Finder Site P Published in
1 S. apiculata GS Molln, Bodinggraben U [64]
2 S. apiculata HK and AS Stubalpe, Waldensteiner Graben C [6]
3 S. apiculata HK and AS Saualpe, Woisbachgraben C [6]
4 S. apiculata K and K Gailtaler Alpen, W Greifenburg C [6]
5 S. apiculata HK Karnische Alpen, Garnitzenklamm C [6]
6 S. apiculata HK and AS Karawanken, Strugarzagraben C [6]
7 S. apiculata K and K Zinkenbachgraben S [6]
8 S. apiculata CS Königsbachtal S Wolfgangsee S [6]
9 S. apiculata B Tannheim, Haldensee T [6]
10 S. apiculata MR Kleinwalsertal, Breitachtal V [6]
1 S. carinthiaca GS Haselschlucht U [64]
2 S. carinthiaca HK Ladritscher Tobel, V [65]
3 S. carinthiaca HK Vermielbach St. Gallenkirch V [65]
4 S. carinthiaca HK Hohe Tauern, Gößnitzfall C [6]
5 S. carinthiaca HK and HvM Kolmitzgraben bei Mörtschach C [6]
6 S. carinthiaca HK Lodronsteig im Maltatal C [6]
7 S. carinthiaca HKandHvM Lamnitzgraben C [6]
8 S. carinthiaca HK Fuggeralm, Flattnitz C [6]
9 S. carinthiaca HK Sommeraugraben, Reichenfels C [6]
10 S. carinthiaca HK Fraßgraben, Koralm C [6]
11 S. carinthiaca HK Kirchbachgraben N Kirchbach C [6]
12 S. carinthiaca HK and HvM Grießbachschlucht S Würmlach C [6]
13 S. carinthiaca HK and MS Kuplitzklamm SE Eisenkappl C [6]
14 S. carinthiaca CS Königsbachtal S Wolfgangsee S [6]
15 S. carinthiaca K and K Schwarzwand bei Hüttschlag S [6]
16 S. carinthiaca HK Gragger Schlucht SW Neumarkt St [6]
1 S. scapanioides GS Höllenleitenbachgraben/Großraming U [64]
2 S. scapanioides HK and HvM Marchgraben E Weißensee C [6]
3 S. scapanioides HK and AS Karawanken, Strugarzagraben C [6]
4 S. scapanioides HK and AS Eselgraben im Loibltal C [6]
5 S. scapanioides HK and MS Kuplitzklamm SE Eisenkappl C [6]
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Abbreviations are as follows: Finder: AS = Adi Schriebl, B = Biedermann, CS = Christian Schröck, GS = Gerhard Schlüsslmayr, HK = Heribert Köckinger, HvM = Hubert van Melik, K and K = Koppe and Koppe, MR = Markus Reimann, MS = Michael Suanjak; P = Austrian province, C = Carinthia, S = Salzburg, St = Styria, U = Upper Austria, V = Vorarlberg.

Author Contributions

Data acquisition and evaluation, photos, writing—original draft preparation, M.K.; funding acquisition, project administration, data acquisition, reviewing and editing the draft, H.G.Z. All authors have read and agreed to the published version of the manuscript.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

Funding Statement

Parts of this research were funded by the following projects: “Erfassung der Moose in NÖ”, sponsored by the Amt der NÖ Landesregierung (RU5-S-770/001-2009); “Kartierung von FFH-Moosen in der Steiermark”, sponsored by the Amt der Steiermärkischen Landesregierung (ABT13-56M-25); “Erhebung der Moosarten des Anhanges II der Fauna-Flora-Habitat-Richtlinie im Natura-2000-Gebiet Nationalpark Nördliche Kalkalpen”, sponsored by the Nationalkpark OÖ Kalkalpen GmbH; “Erfassung der FFH-Moose Mannia triandra und Scapania carinthiaca”, sponsored by the Nationalpark Gesäuse GmbH. The project on deadwood bryophytes was sponsored by the Österreichische Bundesforste AG (ÖBf, Purkersdorf, Austria) and supported by the Bundesforschungszentrum für Wald (BfW, Vienna, Austria).

Footnotes

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