© Entomologica Fennica. 28 November 2019

Five (Collembola) species inhabiting heathlands in Poland

Micha³ Furgo³, Agata Piwnik & Konrad Wiœniewski

Furgo³, M., Piwnik, A. & Wiœniewski, K. 2019: Five springtail (Collembola) species inhabiting heathlands in Poland. — Entomol. Fennica 30: 186–195. doi: https://doi.org/10.33338/ef.87176 We report the presence of five Collembola species from western Poland, three of which were recorded in this country for the first time – pistillum Gisin, 1964 (), tellecheae Arbea & Jordana 1990 () and caerulea Bourlet, 1839 (). doll- fusi Carl, 1899 (Entomobryidae) was earlier known solely from a single, old re- port. Pachyotoma topsenti (Denis, 1948) (Isotomidae) is generally considered a rare species in the region. Though generally infrequently encountered, all five species occur in very high numbers in our plots and they are among the dominant . The habitats surveyed in the study, i.e. dry Calluna-heathlands and their accompanying habitats are endangered in Central Europe and require active management. In one of the studied plots, a prescribed burn was applied to rejuve- nate the heather. We discuss the distribution and habitat preferences of the five species in the European context and their possible significance as indicators of different habitat types. M. Furgo³ (ORCID: 0000-0001-8723-6363) & A. Piwnik (ORCID: 0000-0002- 2407-5037), Department of Invertebrate Biology, Evolution and Conservation, Institute of Environmental Biology, Faculty of Biological Sciences, University of Wroc³aw, Przybyszewskiego 65, 51-148 Wroc³aw, Poland; E-mails: [email protected] & [email protected] K. Wiœniewski (ORCID: 0000-0002-6780-3292), Department of Zoology, Insti- tute of Biology and Environmental Protection, Faculty of Mathematics and Nat- ural Sciences, Pomeranian University in S³upsk, Arciszewskiego 22b, 76-200 S³upsk, Poland; E-mail: [email protected] Received 1 February 2019, accepted 18 June 2019

1. Introduction of the most interesting and diverse groups, were largely neglected as far as research Calluna-heathlands and their associated habitats in heathlands are considered, although some data may host highly diverse, specific and endangered have already been published (Petersen 1995, invertebrate fauna (Usher 1992), which has been Shaw 1997). Dry heathlands are associated with observed in some different groups, such as cara- sandy areas, such as dunes and pioneer grass- bids (Schirmel 2010, Buchholz et al. 2013), some lands. The springtail fauna of these habitats other insect taxa (Swengel 2001) and spiders seems to be equally interesting (S³awska 1996, (Krause & Assmann 2016). The springtails, one Russell 2008, Piwnik & Skar¿yñski 2011, 2015). ENTOMOL. FENNICA Vol. 30 • Five springtail species in heathlands 187

Collembola are abundant in a variety of habi- shrubs, a plot where heather was rejuvenated with tats, their assemblages are often rich in species, a controlled burn on 15.III.2015 and a plot, in and therefore they may be used as indicators of which Molinia caerulea (L.) Moench grass al- habitats or change of habitat quality (Ponge et al. most totally dominates. The invertebrate fauna is 2008, Dunger & Voigtländer 2009). In addition, surveyed by use of pitfall traps (7 independent the composition of their assemblages may reflect traps per plot in a transect with 20 m spacing, one the intensity of some disturbances, e.g. fire transect per plot). The traps are exposed all year (Huebner et al. 2012). Little is known about the round and checked every 3 weeks in the growing biology of many springtail species, which im- season, in winter the interval is slightly longer, pairs further analysis of their plausible role as in- i.e. about 1 month. Additionally, we sampled col- dicator organisms. lembolans from vegetation onto a metal bowl in Dry heathlands in Poland with compact the same three plots as above and in their nearest Calluna vulgaris (L.) hull thicket that cover large surroundings. areas persist almost exclusively in former mili- Some records of Lepidocyrtus tellecheae tary areas due to human activity (Adamska et al. Arbea & Jordana, 1990 and Isotoma caerulea 2015). The main factors responsible for that are Bourlet, 1839 come from another project, in trampling and the occurrence of accidental fires. which interstitial Collembola of sand dunes, After having been abandoned, this type of habi- heath and pine forest were compared. This pro- tats quickly undergoes natural succession. As ject was carried out in a nearby area heathlands highly contribute to local diversity, (N 51°25’34”, E 15°39’16”; UTM: WS49). We they are actively protected and some manage- collected soil-litter samples from the micro- ment methods are applied to prevent their disap- habitats mentioned above and extracted spring- pearance (Webb 1998). However, the outcomes tails in Tullgren (Barlese) funnels. In this part of of using these methods are different (Sedláková our study, there were a total of 312 samples, col- & Chytrý 1999). One of the management activi- lected during 8 field sessions between April 2015 ties is prescribed burn (Webb 1998, Ascolti et al. and March 2017. 2009). In the course of our study, it was applied Besides the two projects above, we list all the for the first time in Poland and we undertook a historic data of Seira dollfusi Carl, 1899 from the successive fauna survey that encompasses sev- contemporary territory of Poland (they come eral invertebrate groups. from the former Prussia). The aim of this article is to present and docu- For close inspections, the springtails were ment our findings of Collembola, supplement cleared in Nesbitt’s fluid and mounted on slides in data on the distribution of the five recorded a Barlese-Swan’s medium (Swan 1936). We took springtail species, summarize their habitat prefer- multi-layer pictures of their diagnostic features, ences and evaluate their prospective significance stacked them using the Helicon Focus 6.7.1. and as indicator species for heath or associated habi- prepared in Adobe Photoshop CS6. The spring- tats. tails were identified using a set of keys (Gisin 1960, Bretfeld 1999, Potapov 2001, Fjellberg 2. Materials and methods 2007, Mateos 2008, Cipola et al. 2018). All the records were compared with the current Polish We present data from two independent projects checklist of Collembola (Sterzyñska et al. 2007). carried out in closely situated heath areas. The ul- timate scope of the first of them – which is still in progress – is to examine the influence of pre- 3. The records scribed burn on invertebrate fauna of the heath. The plot is situated in the former training military 3.1. Bourletiella pistillum Gisin, 1964 area in the northern part of Lower Silesia (W Po- (Bourletiellidae) land; N 51°28’01”, E 15°42’02”; UTM: WT40). Three habitats were included in our study: a plot We recorded 82 specimens of B. pistillum only in of an old and compact thicket of Calluna vulgaris pitfall traps. It solely inhabits the plot where the 188 Furgo³ et al. • ENTOMOL. FENNICA Vol. 30

Fig. 1. Bourletiella pistillum. – a. Dorsal male organ on abdomen VI. – b. Female circumanal setae. Lepidocyrtus tellecheae. – c. Macrochaetae (chaetopores) in anterodorsal part of head. – d. Simple apical labral setae and papillae of labral edge. – e. Acuminate unguiculus. – f. Chaetotaxy of abdomen II (ps: pseudopore, tr: trichobothria). – g. Macrochaetae (chaetopores) on abdomen IV (left side). Isotoma caerulea. – h. Bispinose manubrial teeth. – i. Macrochaetae on dorsal side of manubrium and basal part of dens. Pachyotoma topsenti. – j. Ventral side of dens and mucro. – k. Integument granulation (abdomen IV). Setal symbols a, c and i after Fjellberg (2007); f and g after Mateos (2008). ENTOMOL. FENNICA Vol. 30 • Five springtail species in heathlands 189

Fig. 2. Pachyotoma topsenti. – a, b. Aggregations on sand. Seira dollfusi. – c. Colour pattern, dorsal view. prescribed burn was applied. The majority of the per trap in a single sampling period (i.e. three specimens occurred in a period between May and weeks). Lepidocyrtus tellecheae appeared in all October, however we have observed a male in a of the studied plots in the first of our projects, trap, which was exposed from mid-December to with the highest numbers in the burnt plot and the late January. area dominated by M. caerulea. In the other study The species is distinguished from the conge- it was present in a pine forest and in a heath on a ners by characteristic arrangement of setae on sand dune. Our data suggest that it might have a dorsal male organ on the sixth segment of abdo- winter activity peak – the majority of the speci- men (Fig. 1a) and the presence of differentiated mens in pitfall traps were recorded between No- circumanal setae in females (Fig. 1b). vember and March – nevertheless we observed it This species is new to the fauna of Poland. throughout the year. The species can be distinguished from the congeners by a pattern of macrochaetae on head 3.2. Lepidocyrtus tellecheae (R0, R1, R2; Fig. 1c), and simple labral setae Arbea & Jordana, 1990 (Entomobryidae) (Fig. 1d), macrochaeta m3 on the second segment of the abdomen (Fig. 1f), macrochaeta C1 on the Almost 7,000 specimens of L. tellecheae were fourth segment of the abdomen (Fig. 1g), and collected in pitfall traps and 34 specimens were acuminate unguiculus (Fig. 1e). found in soil-litter samples. The species is gregar- This is the first record of this species in Po- ious with a maximum of about 700 individuals land. 190 Furgo³ et al. • ENTOMOL. FENNICA Vol. 30

Table 1. Historic records (ordered westwards) of Seira dollfusi by Schubert (1933) in contemporary Poland and northeastern Czech Republic (Opawskie Mts).

Country Mountain name Approx. GPS Habitat (contemporary) (Polish or Czech / orig. German) coordinates

PolandGóra Parkowa, Przednia Kopa /N50°18’, E17°21’ Quartzite rocks Holzberg, Vorderkoppe D³ugota / Langer Berg N50°16’, E17°31’ Walls, solitary M³yñska Góra / Mühlberg N50°17’, E17°28’ rocks, scree in Olszak / Birkberg N50°17’, E17°27’ former quarries

The Czech Špièák (?) by Supíkovice / N50°17’, E17°15’ A marble quarry, Republic Spitzstein by Saubsdorf among stones and rock blocks

3.3. Isotoma caerulea Bourlet, 1839 (Fig. 1j) with integument granulation of body sur- (Isotomidae) face specific for the (Fig. 1k).

We recorded 205 specimens of I. caerulea in pit- fall traps of all studied plots. There were 47 speci- 3.5. Seira dollfusi Carl, 1899 mens in soil-litter samples from a heath and litter (Entomobryidae) of a small group of Pinus sylvestris L. trees grow- ing on a semi-open sand dune. We observed 153 specimens of S. dollfusi in pit- The species can be distinguished from the fall traps. The species is common in the area, congeners, and especially Isotoma anglicana which was confirmed by some additional samp- Lubbock, 1862 by the bispinose manubrial teeth ling onto a metal bowl from lower parts of vegeta- (Fig. 1h), two dorsobasal macrochaetae on dens tion (mainly C. vulgaris and M. caerulea). and manubrial dorsal macrochaetae A

4. Discussion tain and some characters overlap with the features of the closely related S. pallidipes. Based on the During the study, we recorded five notable spe- latest key proposed by Cipola et al. (2018) and cies of springtails. They are rarely encountered the general appearance of the investigated ani- and three of them – Bourletiella pistillum Gisin, mals, we conclude that the specimens we ana- 1964 (Bourletiellidae), Isotoma caerulea Bour- lysed belong to S. dollfusi. Nevertheless, not all let, 1839 (Isotomidae) and Lepidocyrtus telle- features perfectly fit those suggested by Cipola et cheae Arbea & Jordana 1990 (Entomobryidae) – al. (2018). As mentioned above the number of are recorded in Poland for the first time. The macrochaetae on Abd IV was higher than sug- fourth species, Seira dollfusi Carl, 1899 (Ento- gested, i.e. instead of 7 we observed 8 or 9. The mobryidae) is known in the region only from his- variability in this feature may be too high to use it toric data. The fifth species, Pachyotoma topsenti for identifying species. (Denis, 1948) (Isotomidae), was known form Po- land already prior to the present study, but the re- cords were very infrequent. Occurrences of these 4.2. Distributions five species may be of importance concerning conservation issues. Many records of B. pistillum come either from the North of Europe or from mountains (Fjellberg 2007), which could suggest that it is a boreo- 4.1. Recognizing species and their identity montane species. However, there are a few re- cords from Central European lowlands and their Two of the analyzed species were described re- common feature seems to be that they come from cently, so they require special care during identi- open and xerothermic habitats (see below). fication. Isotoma caerulea was confused with Isotoma caerulea has probably a wide range, I. anglicana until the revision by Fjellberg although older records are uncertain due to confu- (2003), the result being supported shortly thereaf- sion with I. anglicana. Fjellberg (2003) mentions ter by a molecular-based research (Burkhardt & its presence in Scandinavia and most of Western Filser 2005). Europe. It was also noted in Moldavia (Buºma- The identity of L. tellecheae might be prob- chiu & Weiner 2013) and Hungary (Winkler & lematic, because this is a recently described spe- Tóth 2012). Moreover, there are records from the cies from Spain, assigned to the lignorum-group USA and Greenland (Fjellberg 2003). based on its colouration, size, chaetotactic pattern The records of P. topsenti in Europe are and smooth labral setae (Arbea & Jordana 1990, scarce. The species has been noted only in few Mateos 2011). The species identity has recently countries, i.e. Germany, France, Poland and been verified by the molecular data. The authors Switzerland (Denis 1948, Dunger 1987, Potapov suggested that there exist several further cryptic 2001, Sterzyñska et al. 2007), and in each of species (Mateos et al. 2018). Therefore, based on those there are just single localities of the species. previous data and the huge geographical distance, Lepidocyrtus tellecheae has only been re- we suggest that populations from Poland should corded in the North and North-East of the Iberian undergo taxonomic analysis in the future, pre- Peninsula (Arbea & Jordana 1990, Mateos et al. sumably using molecular methods. The species 2018) and was thought to be endemic to the re- group in question has not yet been sufficiently an- gion (Mateos 2008). The huge gap in its range is alyzed and there are some data on its occurrence striking and provokes taxonomical questions. (L.cf.tellecheae) from Hungary (Traser & Hor- However, the reasons for this untypical distribu- vàth-Szovàti 2006, Dányi & Traser 2007). tion may also have its source in insufficient Seira dollfusi is another species, which may knowledge on collembolan fauna generally. As require more detailed analysis. The genus has mentioned before, this is not the first report on the been lately revised (Cipola et al. 2018), but due to species from Central Europe (Traser & Horvàth- problems with obtaining the type specimens Szovàti 2006, as Lepidocyrtus cf. tellecheae). much information concerning S. dollfusi is uncer- Seira dollfusi reaches its northern range in 192 Furgo³ et al. • ENTOMOL. FENNICA Vol. 30

Central Europe and its known populations are Dunger (1987) in Eastern Germany from very scattered in the region. The northernmost data similar habitats as in the case of our study, i.e. come from the Eastern Sudetes in Southern Po- pine and spruce plantation, with sparsely growing land by Schubert (1933). Our data expand this trees. The author also observed a mass occurrence range in the country further to the North. The of the species, the phenomenon mentioned al- presence of S. dollfusi in this part of Europe has ready by the author of the species name, Denis been questionable to date (Sterzyñska et al. (1948). The species seems to prefer open habitats 2007). and it disappears with the succession of pine fo- rests (S³awska & S³awski 2016). 4.3. Habitats Isotoma caerulea inhabits xerothermic envi- ronments, predominately with dry and sandy The five species in question seem to prefer soils, as opposed to its near relative, I. anglicana, slightly different habitat types. In the heathland which prefers humid soils, rich in organic matter studied by us, B. pistillum inhabited solely the (Fjellberg 2003, 2007). The author recorded this burnt area, which suggests that it is a pioneer spe- species on seashore meadows in Norway. cies. Indeed, it has been previously reported from Slightly contradictory information on the two mining dumps in Eastern Germany, where it Isotoma species is presented, however, by Burk- dominated. The species colonized the plots as one hardt and Filser (2005). Buºmachiu and Weiner of the first (Dunger et al. 2002, Wanner (2013) report its presence in Dniester river banks & Dunger 2002). In Spain, the species was pres- in Moldavia. It has been noted in grasslands on ent in pine forests that underwent fires while it Iceland (Gudleifsson & Bjarnadottir 2008), was not found in control (unburned) plots or in meadows, pastures and road verges in Finland other forest types (Mateos & Selga 1991). On the (Komonen & Kotaja-aho 2017) and steppe mead- other hand, in a burnt montane forest with dwarf ows in Hungary (Winkler & Tóth 2012). Franken pine shrubs it clearly preferred an undisturbed and Berg (2018) noted it also on Dutch sand plot (Querner et al. 2010). The record, however, dunes. It was one of the dominant species in moss comes from high altitudes in the Alps, thus the in calcareous grasslands in Sweden (Cronberg et species habitat preferences might be different al. 2008). there. Some authors indicate that the species is Open warm and dry habitats seem to provide characteristic for dry habitats (Wanner et al. suitable conditions for I. caerulea,makingita 1999). good indicator of such environments. It may be Apart from this, the species seems to prefer cautiously assumed that some I. anglicana found northern parts of Europe and mountains (Ellis so far in environments like sand dunes, heath- 1975, Fjellberg 2007), inhabiting dry slopes or lands or dry pine forests may have been I. caeru- rocks in lowlands (Fjellberg 2007), subalpine and lea. alpine meadows (Gisin 1960, Fjellberg 1976) or Seira dollfusi is considered a South European montane heaths (Ellis 1975, Fjellberg 1976, springtail (Stach 1928), which in Central Europe 2007). Large numbers of B. pistillum were re- lives in habitats affording proper thermal condi- ported from the canopy of pine trees in Norway tions, usually on sun exposed walls of quarries or (Thunes et al. 2004). Pine forests are also preva- rocks (Schubert 1933). Dry heathlands in Central lent in our study area. Summing up, the species is Europe seem to afford proper thermal conditions known from numerous localities in the North and to sustain numerous populations of the species. It mountains and it can be found also in other alti- is not the only example of arthropod species, tudes and latitudes, where it is known to colonise which inhabits both exposed rocky habitats in the disturbed areas. mountains and lowland heathlands or sandy habi- Data on L. tellecheae are very scarce. The tats in Central Europe. The spider species above-mentioned specimens of uncertain identity Philaeus chrysops Poda, 1791 may serve as an from Hungary (Traser & Horvàth-Szovàti 2006) example for this type of habitat preference in Po- came from a region with sandy calcareous soils. land, although it has a slightly broader habitat Pachyotoma topsenti was recorded by range. ENTOMOL. FENNICA Vol. 30 • Five springtail species in heathlands 193

4.4. Significance Vol. 2: . — Staatliches Museum für Naturkunde Görlitz, Görlitz. 318 pp. Buchholz, S., Hannig, K. & Schirmel J. 2013: Losing uni- Among springtails, there is a number of rarely queness – shifts in carabid species composition during found species, which often inhabit some unique dry grassland and heathland succession. — habitats or habitat types. Understanding their bio- Conservation 16(6): 661–670. doi: https://doi.org/ logy, including the preferred habitats, may facili- 10.1111/acv.12046 tate further analysis of their assemblages. In the Burkhardt, U. & Filser, J. 2005: Molecular evidence for a fourth species within the group (Insecta, Central European heathlands we report five spe- Collembola). — Zoologica Scripta 34(2): 177–185. doi: cies of interest, because of their rarity, new taxo- https://doi.org/10.1111/j.1463-6409.2005.00181.x nomic status or potential indicator value. Bour- Buºmachiu, G. & Weiner, M. W. 2013: Collembola from letiella pistillum may be regarded as a facultative the Moldavian banks of Dniester River. New records. pioneer species of disturbed areas, I. caerulea and — Annales Zoologici 63(4): 529–535. doi: https:// doi.org/10.3161/000345413X676759 S. dollfusi may serve as an indicator species of Cipola, N. G., Arbea, J., Baquero, E., Jordana, J., de Mo- xerothermic habitats in Central Europe. Lepi- rais, J. W. & Bellini, B. C. 2018: The survey of Seira docyrtus tellecheae has a rather unusual distribu- Lubbock, 1870 (Collembola, Entomobryidae, Seiri- tion pattern and the systematics of this species nae) from Iberian Peninsula and Canary Islands, inclu- should be reconsidered. Pachyotoma topsenti is ding three new species. — Zootaxa 4458(1): 1–66. doi: https://doi.org/10.11646/zootaxa.4458.1.1 characteristic for its aggregations and indicates Cronberg, N., Natcheva, R. & Berggren, H. 2008: Obser- dry, open habitats, which may easily undergo vations regarding the life cycle of silvermoss Bryum succession by a forest. argenteum.—In:Mohamed,H.,Baki,B.B.,Nasrul- haq-Boyce, A. & Lee, P. K. Y. (eds), Bryology in the Acknowledgements. The inventory of springtails is a part New Millennium: 347–352. University of Malaya, of the project “Establishing the fire protection rules for the Kuala Lumpur. 513 pp. protected areas and objects, and use of prescribed burn as Denis, J. R. 1948: Sur la faune francaise des Apterygotes an active nature conservation method” led by the Institute (XXIII). — Bulletin scientifique de Bourgogne: 45– of Forestry Research in Sêkocin and financed by the Gen- 51. [In French.] eral Directory of the National Forests. We would like to Dányi, L. & Traser, G. 2007: An annotated checklist of the thank Angelika Dawidowicz, Adam Malkiewicz, Dariusz springtail fauna of Hungary (: Collembola). Skar¿yñski and Ewa Szczêœniak from the University of — Opuscula Zoologica Budapest 38: 3–82. Wroc³aw, and the staff of the Forest District in Przemków Dunger, W. 1987: Proisotoma topsenti Denis, 1948, eine and the Regional Department of the National Forests in seltene, zu Übervermehrung neigende Art der Collem- Wroc³aw. We would like to express our sincere thanks to bola (Insecta). — Abhandlungen und Berichte des Na- the two anonymous reviewers for their valuable sugges- turkundemuseums Görlitz 60(12): 53–60. tions. Dunger, W., Schulz, H.-J. & Zimdars, B. 2002: Coloniza- tion behaviour of Collembola under different condi- tions of dispersal. — Pedobiologia 46: 316–327. Dunger, W. & Voigtländer, K. 2009: Soil fauna (Lumbrici- References dae, Collembola, Diplopoda and Chilopoda) as indica- tors of soil eco-subsystem development in post-mi- Adamska, E., Deptu³a, M., Filbrandt-Czaja, A., Kamiñski, ning sites of eastern Germany – a review. — Soil Or- D., Lewandowska-Czarnecka, A., Nienartowicz, A. & ganisms 81(1): 1–51. https://doi.org/10.1078/0031- Sewerniak, P. 2015: Heathlands and associated com- 4056-00139 munities in Kujawy and Pomerania: management, Ellis, W. N. 1975: On Bourletiella (Cassagnaudiella) treatment and conservation. — Towarzystwo Nauko- pruinosa (Tullberg, 1871) and its allies (Collembola: we w Toruniu, Toruñ. 236 pp. ). — Bulletin Zoölogisch Museum, Uni- Arbea, J. I. & Jordana, R. 1990: New species of Pseudosi- versiteit van Amsterdam 4(9): 69–81. nella and Lepidocyrtus from Navarra (Northern Iberi- Fjellberg, A. 1976: Collembola from mountains in South an Peninsula). — Spixiana 13(1): 25–31. Norway. — Norwegian Journal of Entomology 23: Ascolti, D., Beghin, R., Ceccato, R., Gorlier, A., Lombar- 127–137. di, G., Lonati, M., Marzano, R., Bovio, G. & Cavalle- Fjellberg, A. 2003: Revision of six northern species of the ro, A. 2009: Developing an adaptive management Isotoma viridis Bourlet, 1839 complex (Collembola, approach to prescribed burning: a long-term heathland Isotomidae). — Norwegian Journal of Entomology conservation experiment in north-west Italy. — Inter- 50: 91–98. national Journal of Wildland Fire 18 (6): 727–735. Fjellberg, A. 2007: The Collembola of Fennoscandia and doi: https://doi.org/10.1071/WF07114 Denmark, part II: and Symphy- Bretfeld, G. 1999: Synopses on Palaearctic Collembola. pleona. — Fauna Entomologica Scandinavica 42. 194 Furgo³ et al. • ENTOMOL. FENNICA Vol. 30

Brill, Leiden, Boston. 264 pp. doi: https://doi.org/ Potapov, M. B. 2001: Synopses on Palaearctic Collembo- 10.1163/ej.9789004157705.i-265 la. Vol. 3. Isotomidae. — Staatliches Museum für Na- Franken, O. & Berg, M. P. 2018: Entomofauna van de turkunde Görlitz, Görlitz. 603 pp. Noord-Hollandse duinen. Verslag van de 171e NEV- Russell, D. J. 2008. Collembolan community structures in zomerbijeenkomst. — Entomologische Berichten a continental psammic habitat of south-west Germany. 78(2): 42–69. [In Dutch with English summary.] — Soil Organisms 80(1): 117–131. Gisin, H. 1960: Collembolenfauna Europas. — Museum Querner, P., Bruckner, A., Weigand, E. & Prötsch, M. d’histoire naturelle, Geneve. 312 pp. [In German.] 2010: Short- and long-term effects of fire on the Col- Gudleifsson, B. E. & Bjarnadottir, B. 2008: Springtail lembola communities of a sub-alpine dwarf pine eco- (Collembola) populations in hayfields and pastures in system in the Austrian Alps. — Eco.mont – Journal of northern Iceland. — Icelandic Agricultural Sciences protected mountain areas research and management 21: 49–59. 2(2): 29–36. doi: https://doi.org/10.1553/eco.mont-2- Huebner, K., Lindo, Z. & Lechowicz, M. J. 2012: Post-fire 2s29 succession of collembolan communities in a northern Schirmel, J. 2010: Short-term effects of modern heathland hardwood forest. — European Journal of Soil Biology management measures on carabid beetles (Coleop- 48: 59–65. doi: https://doi.org/10.1016/j.ejsobi. tera: Carabidae). — Applied Ecology and Environ- 2011.10.004 mental Research 8(3): 165–175. Komonen, A. & Kataja-aho, S. 2017: Springtails (Collem- Schubert, K. 1933: Ökologische Studien an schlesischen bola) in meadows, pastures and road verges in Central Apterygoten. — Deutsche Entomologische Zeitschrift Finland. — Entomologica Fennica 28: 157–163. 2–3: 177–272. doi: https://doi.org/10.1002/mmnd. Krause, R. H. & Assmann, T. 2016: Impact of prescribed 193419330203 burning on a heathland inhabiting spider community. Sedláková, I. & Chytrý, M. 1999: Regeneration patterns in — Arachnologische Mitteilungen / Arachnology Let- a Central European dry heathland: effects of burning, ters 51: 57–63. doi: https://doi.org/10.5431/aramit sod-cutting and cutting. — Plant Ecology 143: 77–87. 5108 doi: https://doi.org/10.1023/A:1009807411654 Mateos, E. 2008: The European Lepidocyrtus Bourlet, Shaw, P. J. A. 1997: Post-fire successions of Collembola in 1839 (Collembola: Entomobryidae). — Zootaxa lowland heaths in South-Eastern UK. — Pedobiologia 1769: 35–59. doi: https://doi.org/10.11646/zootaxa. 41: 80–87. 1769.1.2 S³awska, M. 1996: Succession of Collembola in an active Mateos, E. 2011: New Lepidocyrtus Bourlet, 1839 taxa deflation hollow in S³owiñski National Park. — Pedo- from Greece (Collembola: Entomobryidae). — Zoo- biologia 41(1–3): 139–144. taxa 3108: 25–40. doi: https://doi.org/10.11646/zoo- S³awska, M. & S³awski, M. 2016: Powrót lasu na zanie- taxa.3108.1.2 chane rolniczo sandrowe gleby Równiny Charzykow- Mateos, E., Escuer, P., Buºmachiu, G., Riutort, M. & Ál- skiej. — Studia i Materia³y CEPL w Rogowie 46(1): varez-Presas, M. 2018: Untangling Lepidocyrtus 147–162. [In Polish.] (Collembola, Entomobryidae): new molecular data Stach, J. 1928: Verzeichnis der Apterygogenea Ungarns. shed light on the relationships of the European groups. — Annales Musei Nationalis Hungarici 26: 269–312. — Invertebrate Systematics 32: 639–651. doi: https:// Sterzyñska, M., Pomorski, R.J., S³awska, M., Skar¿yski, doi.org/10.1071/IS17056 D., Smolis, A. & Weiner, W.M. 2007: Skoczogonki Mateos, E. & Selga. D. 1991: Efecto de los incendios fo- (Collembola). — In: Bogdanowicz, W., Chudzicka, restales sobre las problaciones de colémbolos edáficos E., Pilipiuk, I. & Skibiñska, E. (eds), Fauna of Poland en bosque mediterráneo. — Revue d’Ecologie et de – characteristics and checklist of species: 401–415. Biologie du Sol 28(1): 19–30. [In Spanish.] Museum and Institute of Zoology PAS, Warsaw. Petersen, H. 1995: Temporal and spatial dynamics of soil 505 pp. Collembola during secondary succession in Danish Swan, D. A. 1936: Barlese’s fluid: remarks upon its prepa- heathland. — Acta Zoologica Fennica 196: 190–194. ration and use a mounting medium. — Bulletin of En- Piwnik, A. & Skar¿yñski, D. 2011: Skoczogonki (Collem- tomological Research 27(3): 389–391. doi: https:// bola) wydm œródl¹dowych specjalnego obszaru och- doi.org/10.1017/S0007485300058259 rony Wrzosowisko Przemkowskie. — Parki Narodo- Swengel, A. B. 2001: A literature review of insect respon- we i Rezerwaty Przyrody, 30(3–4): 122–128. [In Po- ses to fire, compared to other conservation manage- lish with English summary.] ments of open habitat. — Biodiversity and Conserva- Piwnik, A. & Skar¿yñski, D. 2015: Psammophilic spring- tion 10: 1141–1169. doi: https://doi.org/10.1023/ tails (Collembola) new to Polish fauna. — Wiado- A:1016683807033 moœci Entomologiczne 34(1): 5–11. [In Polish with Thunes, K. H., Skartveit, J., Gjerde, I., Starý, J., Solhøy, T., English summary.] Fjellberg, A., Kobro, S., Nakahara, S., zur Strassen, Ponge, J.-F., Tully, T. & Gins, A. 2008: Short-term respon- R., Vierbergen, G., Szadziewski, R., Hagan, D.V., ses of two collembolan communities after abrupt envi- Grogan Jr., W. L., Jonassen, T., Aakra, K., Anonby, J., ronmental perturbation: A field experimental app- Greve, L., Aukema, B., Heller, K., Michelsen, V., Ha- roach. — Pedobiologia 52: 19–28. doi: https:// enni, J.-P., Emeljanov, A. F., Douwes, P., Berggren, doi.org/10.1016/j.pedobi.2008.01.005 K.,Franzen,J.,Disney,R.H.L.,Prescher,S.,Johan- ENTOMOL. FENNICA Vol. 30 • Five springtail species in heathlands 195

son, K. A., Mamaev, B., Podenas, S., Andersen, S., Wanner, M. & Dunger, W. 2002: Primary immigration and Gaimari, S. D., Nartshuk, E., Søli, G. E. E., Papp, L., succession of soil organisms on reclaimed opencast Midtgaard, F., Andersen, A., von Tschirnhaus, M., coal mining areas in eastern Germany. — European Bächli,G.,Olsen,K.M.,Olsvik,H.,Földvári,M., Journal of Soil Biology 38: 137–143. doi: https:// Raastad, J. E., Hansen, L. O. & Djursvoll, P. 2004: The doi.org/10.1016/S1164-5563(02)01135-4 arthropod community of Scots pine (Pinus sylvestris Wanner, M., Hauser, H., Zimdars, B. & Dunger, W. 1999: L.) canopies in Norway. — Entomologica Fennica 15: Einwanderungswege der Bodenfauna auf Kippen des 65–90. Tagebaues Berzdorf. — Berichte der Naturforschen- Traser, G. & Horvàth-Szovàti, E. 2006: Land–use intensity den Gesellschaft der Oberlausitz 7/8: 101–104. and diversity parameters: Collembola (Insecta) com- munities in Csévharaszt (Hungary). — In: Csóka, Gy., Webb, N. R. 1998: The traditional management of Europe- Hirka, A. & Koltay, A. (eds.), Biotic damage in fo- an heathlands. — Journal of Applied Ecology 35: rests: 329–339. Proceedings of the IUFRO (WP7. 987–990. doi: https://doi.org/10.1111/j.1365-2664. 03.10) Symposium held in Mátrafüred, Hungary, Sep- 1998.tb00020.x tember 12–16, 2004. 360 pp. Winkler, D. & Tóth, V. 2012: Effects of afforestation with Usher, M. B. 1992: Management and diversity of arthro- pines on Collembola Diversity in the limestone hills of pods in Calluna heathland. — Biodiversity and Con- Szárhalom (West Hungary). — Acta Silvatica et Lig- servation 1: 63–79. doi: https://doi.org/10.1007/ naria Hungarica 8: 9–20. doi: https://doi.org/10.2478/ BF00731035 v10303-012-0001-8