1✉ Department of Animal Taxonomy and Ecology, Adam Mickiewicz University in Poznań, Uniwersytetu Poznańskiego 6, PL- 61-714 Poznań, Poland. 2Department of Animal Morphology, Adam Mickiewicz University in Poznań, Uniwersytetu Poznańskiego 6, PL- 61-714 Poznań, Poland. 3Department of Invertebrate Systematics and Ecology, Wrocław University of Environmental and Life Sciences, Kożuchowska 5b, PL- 51-631 Wrocław, Poland. 4Department of Animal Morphology, Adam Mickiewicz University in Poznań, Uniwersytetu Poznańskiego 6, PL- 61-714 Poznań, Poland. 5Department of Animal Taxonomy and Ecology, Adam Mickiewicz University in Poznań, Uniwersytetu Poznańskiego 6, PL- 61-714 Poznań, Poland.
The study provides the list of soil mites from suborder Prostigmata in selected habitats of Morasko Campus of Adam Mickiewicz University in Poznań. Representatives of 21 families belonging to 58 genera and 139 species were found in 20 collected samples. One family, 11 genera and 26 species are new to the fauna of Poland and two species new to the fauna of Europe.
Introduction
Although the history of the study of prostigmatic and endeostigmatic mites extends over more than two hundred years (Krantz and Walter 2009), the knowledge about these arthropods is still poor. The number of known species represents only a small fraction of their real richness and even less is known about their ecology and behavior. Moreover, when comparing mites (excluding ticks) with spiders, the former seems to have a much higher diversity, than the latter, despite having similar number of described species. Furthermore, scientific literature devoted to all mites and available through the internet is much poorer, than that related to spiders (Walter and Proctor 2010). There are several reasons for this situation, e.g. mites, with special reference to Prostigmata, are numerous and highly diverse, and their identification is not easy. The literature is still scanty and spotty among the members of the suborder. The identification keys, or comprehensive revisions and monographs on many (if not most) groups of Prostigmata are still relatively scarce. Descriptions of many species are often curt and lacking vital diagnostic features, indicating a vast demand for redescriptions. Additionally, the number of competent specialists is limited and their regard in wide academic and scientific communities is meager (Walter and Proctor 2010).
Mites and particularly Prostigmata however, have great potential as model organisms in various research areas of modern biology. For instance, they can serve as models in variety of studies, including ecology (Walter and Proctor 2010) or experimental evolution (Belliure et al. 2010). Thus, the aim of this study was not only to contribute to the checklist of prostigmatic mites in Poland, but also to create a list of species accessible in our immediate vicinity, i.e. surroundings of the university facilities, and make them available for those interested in carrying out the research on these arachnids.
Material and methods
A total of 20 samples of soil litter and plant debris were collected from 10 localities representing 10 different habitats (see Table 1) in western part of Morasko Campus of Adam Mickiewicz University in Poznań (Figure 1). The first sampling was carried out in winter, whereas the second one in spring 2019.
Table 1. Habitats with coordinates and date of sampling.
Figure 1. Study area with 10 sampling localities (nos. 1-10) and its border marked by black line.
The sampling area is located in lowland in central-western Poland, whose landforms originated during glacial (Pleistocene), and postglacial (Holocene) periods. Most of the Morasko Campus are actually covered by buildings. Except for secondary plant community with Pinus sylvestris and Padus serotina as well as an alder forest, there are mostly regularly mowed lawns with sparsely distributed trees (mainly P. sylvestris and Betula pendula) and separated small tree stands.
Mites were extracted from samples using Berlese-Tullgren funnels (photo-eclectors) for 7-10 days and stored in 75% ethanol. Specimens of the family Nanorchestidae were additionally placed in 10% KOH to dissolve crystals of uric acid accumulated in the body, and then rinsed with distilled water. After that, specimens were mounted in Hoyer's medium on microscopic slides and heated for several days at 55 °C. They were studied with phase-contrast (Olympus BX 41) and interference-contrast (Olympus BX 51) microscopes supplied with a digital photographic camera Olympus E-5, and also with a phase-contrast microscope Nikon Eclipse 80i, equipped with DIC and DS-Fi3 camera system. Mite species were identified using keys and other taxonomic references by following authors: Bizarro et al. (2020), Booth et al. (1985), Fan Q.-H. (2004), Gabryś (2016), Gilyarov et al. (1978), Haitlinger (1986, 2002), Jesionowska (2010), Kaliszewski (1987, 1993), Kaźmierski (1998), Khaustov (2014), Krantz and Walter (2009), Łaydanowicz and Mąkol (2010), Magowski (1997), Mąkol (2010), Mąkol and Wohltmann (2012), Michocka (1987), Rack (1981), Smiley (1992), Stålstedt et al. (2016), Strandtmann (1971), Thor and Willmann (1941), Uusitalo (2010), Wohltmann et al. (2007), and Zacharda (1980).
The species found are divided into three categories, namely: (a) fully identified species, (b) those resembling known species but its identity uncertain (hence marked ''cf.''), and (c) those whose identity could not be ascertained for technical reasons (bad position, missing diagnostic features) but not closely resembling known species (hence marked ''sp. 1'', ''sp. 2'', etc.). Species omitted from the count are individuals damaged beyond species recognition. Only fully named species are counted as new for Polish or European faunas. Genera Echinoeupodes, Neoprotereunetes, Archidispus, and Pygmodispus are also listed as new for respective faunas (for Poland or Europe) even though their representing species were not identified and therefore only indicated as ''sp.'' (thus in abovementioned category c). In the list hereunder of recorded taxa the abbreviations ''NP'' and ''NE'' refer to taxa new to Polish and European faunas, respectively. Localities and seasons of sampling (W – winter, S – spring) following the number of the locality are marked according to the Table 1. The following symbols refer to the instars: female – ♀, male – ♂, tritonymph – tn, deutonymph – dn, protonymph – pn, larva – lv, unidentified nymph – n, unidentified instar – ?.
The collection of samples and specimens is deposited in the Department of Animal Taxonomy and Ecology, Adam Mickiewicz University in Poznań, except for Erythraeidae, which are deposited at the Department of Invertebrate Systematics and Ecology, Wrocław University of Environmental and Life Sciences.
Results
In the course of our study 868 individuals of 21 families belonging to 58 genera and 139 species were found. Selected representatives of the suborder Prostigmata are shown in Figure 2. The list of family level taxa is provided in systematic order following Krantz and Walter (2009); the list of genera and species within particular family – in alphabetical order.
Figure 2. Representatives of Prostigmata found in Morasko Campus: A – Cunaxidae: Armascirus bakeri larva; B – Eupodidae: Caleupodes reticulatus adult female; C – Tydeidae: Lorryia reticuloinsignia adult female; D – Erythraeidae: Abrolophus rudaensis larva; E – Eupalopsellidae: Eupalopsellus trudis adult female; F – Stigmaeidae: Agistemus gratus adult female. Scale bars are 100 μm.
Terpnacarus subterraneus Weis-Fogh, 1948 NP. Locality: 6W: 1 ♀
Discussion
With reference to previous data summarized in Bogdanowicz et al. (2008), Kaźmierski et al. (2018), and Mąkol and Wohltmann (2012), one family, 11 genera and 27 species recorded during present study are new to the fauna of Poland and two species are also new to the fauna of Europe (André 2004; Baker 2004; Silva et al. 2016; Magowski 2004; Uusitalo, and Judson 2004).
Majority of recorded species were found in one habitat only, whereas the most frequently occurring species were Cunaxa setirostris, Eupodes voxencollinus, Microtydeus beltrani and Nanorchestes cf. antarcticus, each found in more than five habitats. The latter may indicate that these four species display relatively low habitat selectivity.
A comparison of our results with those of other similar studies is difficult due to the scarcity of surveys on Prostigmata soil faunas carried out in limited spatial areas. Such studies usually deal with highly distinct habitats (e.g. subterranean in Skubała et al. 2013, marches in Dogan et al. 2015) or refer to narrower taxonomic scope. One of the few similar projects to ours, though covering a larger area, was carried out by Niedbała et al. (1982). During our investigation, 139 species were found with 868 examined individuals, whereas Niedbała et al. (1982) recorded 321 species represented by 8169 individuals. The latter work involved also Oribatida (Acariformes) and Gamasida (Parasitiformes), which were not included in our research. This means that in our study the no. of species per no. of specimens is four times higher than in Niedbała et al. (1982), despite involving narrower spectrum of systematic groups. The disproportion can be tentatively explained by a wider variety of habitats examined in our survey. Moreover, in our study only 20 samples were collected, while as many as 400 were examined by Niedbała et al. (1982). Thus, the species no./sample index amounts to 7.0 in our study, while it is 0.8 in Niedbała et al. (1982). Unfortunately, no exact number of samples per each particular mite group is given in the latter paper, rendering such comparisons hardly informative. When compiling the comparable aspects of these two datasets, the cohort Heterostigmatina is represented by 71 species in Niedbała et al. (1982) and by 36 in our study. The remaining Prostigmata, however, are represented by 50 species in Niedbała et al. (1982) and 99 in this study, testifying to nearly a twice higher diagnostic resolution in our approach, despite ca. 20 times lower number of samples examined. The number of species of the suborder Endeostigmata recorded in both studies was comparable and rather low.
No doubts, the regular sampling, even limited in space contributes to species richness. Łaydanowicz and Mąkol (2010) recorded as many as 13 species, representing four families and constituting almost nine percent of the Polish fauna of terrestrial Parasitengona mites, within a studied area of ca. 200 m2, located in the vicinity of the university campus in Wrocław.
Some semi-aquatic or aquatic taxa i.e., representatives of the Hydrachnidia (water mites), as well as plant-associated mites, i.e., Tetranychidae (spider mites) were recorded in our material. Presence of the former can be explained by the proximity of the pond to the locality no. 2, whereas the latter finding is regarded accidental. Nevertheless, both should be considered as accidental in the typically soil habitats.
As mentioned before, our aim was not only to provide a local checklist of Prostigmata and Endeostigmata, but also to make the data on the presence of those mites in AMU Campus accessible to other biologists, who need material for their laboratory studies. This objective has been already met, since some of our early results were recently used for a molecular phylogenetic assay on Eupodoidea by Szudarek-Trepto et al. (2020). Further studies based on our findings are underway.
Systematic evaluation and comments on the mite material presented herewith will be a subject of a separate study.
Acknowledgements
We would like to thank the staff members of the Department of Plant Ecology and Conservation Biology, Adam Mickiewicz University in Poznań for identification of plant communities in sampling areas. We are grateful to the reviewers for their valuable comments.
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