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A Holarctic Biogeographical Analysis of the Collembola (Arthropoda, Hexapoda) Unravels Recent Post-Glacial Colonization Patterns

Department Arctic Biology, University Centre in Svalbard, P.O. box 156. 9171, Longyearbyen, Norway
Ecological and Environmental Change Research Group (EECRG), Department of Biology, University of Bergen, p.b. 7800, N-5200 Bergen, Norway
Department Arctic Biology, University Centre in Svalbard, P.O. box 156. 9171, Longyearbyen, Norway
Author to whom correspondence should be addressed.
Insects 2011, 2(3), 273-296;
Received: 15 May 2011 / Revised: 1 June 2011 / Accepted: 20 June 2011 / Published: 29 June 2011


We aimed to describe the main Arctic biogeographical patterns of the Collembola, and analyze historical factors and current climatic regimes determining Arctic collembolan species distribution. Furthermore, we aimed to identify possible dispersal routes, colonization sources and glacial refugia for Arctic collembola. We implemented a Gaussian Mixture Clustering method on species distribution ranges and applied a distance-based parametric bootstrap test on presence-absence collembolan species distribution data. Additionally, multivariate analysis was performed considering species distributions, biodiversity, cluster distribution and environmental factors (temperature and precipitation). No clear relation was found between current climatic regimes and species distribution in the Arctic. Gaussian Mixture Clustering found common elements within Siberian areas, Atlantic areas, the Canadian Arctic, a mid-Siberian cluster and specific Beringian elements, following the same pattern previously described, using a variety of molecular methods, for Arctic plants. Species distribution hence indicate the influence of recent glacial history, as LGM glacial refugia (mid-Siberia, and Beringia) and major dispersal routes to high Arctic island groups can be identified. Endemic species are found in the high Arctic, but no specific biogeographical pattern can be clearly identified as a sign of high Arctic glacial refugia. Ocean currents patterns are suggested as being an important factor shaping the distribution of Arctic Collembola, which is consistent with Antarctic studies in collembolan biogeography. The clear relations between cluster distribution and geographical areas considering their recent glacial history, lack of relationship of species distribution with current climatic regimes, and consistency with previously described Arctic patterns in a series of organisms inferred using a variety of methods, suggest that historical phenomena shaping contemporary collembolan distribution can be inferred through biogeographical analysis.
Keywords: dispersal; colonization; distribution range; glacial refugia; Gaussian mixture clustering; Arctic dispersal; colonization; distribution range; glacial refugia; Gaussian mixture clustering; Arctic

1. Introduction

The historical frame in which contemporary biogeographical patterns in the Arctic have been shaped is as yet a mystery for most species of invertebrates. Furthermore, for most species, whether any overall pattern defines their Arctic distribution has never been clarified, although it is clear that not all species are found everywhere. Environment and physiological limitations, together with dispersal abilities, are frequently highlighted as major factors determining the ranges of species in different taxa [1], but more recently it has been highlighted that historical influences can contribute to contemporary patterns of biodiversity to a similar or greater extent than contemporary climatic regimes [2]. The current geographical distribution of species reflects not only the ability of given species to survive the environmental conditions, compete and successfully reproduce in a particular location, but also their ability to have successfully colonized the area once the appropriate niche became available. The Arctic thus arises as an ideal platform for studying the large scale dispersal abilities of terrestrial invertebrates as, for much of the area, a relatively accurate date estimate can be given to the “opening of the niche” event.

Ice ages have been repeatedly shown to have a measurable impact on current Arctic diversity patterns through species range reduction (bottlenecks) and expansion episodes [38]. Most of the high Arctic was covered by permanent ice during the Wisconsinan/Weischelian glacial episode, although the exact area and timing of the Last Glacial Maximum (LGM) extension of ice varied between regions [9]. Outlet glaciers of the Laurentide ice sheet in the Canadian Arctic retreated rapidly approximately 12- 10 Ka B.P. [10], while late glacial nunataks showing pioneer dwarf- shrub vegetation were present in southern central Scandinavia 16 Ka B.P. [11]. Recent analysis however points at a Last Scandinavian Ice Sheet deglaciation mostly due to surface thinning rather than marginal retreat [12]. Areas such as Beringia and most of Siberia as far as the Taymyr peninsula were ice-free for most if not all of the glacial period [1315], leaving a broad area in the eastern Palaearctic that could have potentially provided glacial refugia. The Kara Ice Sheet could have left ice-free ground available along its western sector as early as 15 Ka B.P. [14]. Knowledge of patterns of the LGM ice sheet extension and thickness are in general based on large scale reconstructions, often with doubtful boundaries and low resolving power in the context of identifying small islands of ice-free ground (see [14,10,11]). This has led to the concept of cryptic refugia [16], which are areas, probably scattered and in low densities, where organisms could have persisted during major glacial episodes. In the instance of the Svalbard archipelago, it has been suggested that some ice-free areas could have remained in Murchinsonfjorden [1719] and Danskøya [20], but the currently available reconstructions cannot accurately assess whether those areas were ice-free or covered by a thin cold-based ice sheet [17,19]. In most of the possible ice-free areas in the high Arctic, the environment is thought to have been harsh enough that no soil mesofauna could have survived in situ. Genetic data suggest that no Arctic plants were present in high Arctic regions prior to the abrupt end of the LGM 10 Ka. B.P. [5], when large periglacial areas opened for colonization. Several authors nonetheless, point to survival of a number of invertebrate groups in the arguably more severe conditions of continental Antarctica [2123], thereby challenging current reconstructions of the glacial history of the Antarctic continent [21]. Furthermore, different collembolan ecotypes show different adaptations to harsh environments, and even cryophilic glacial dweller collembolan species have been described [24,25]. This challenges the often unquestioned concept that nothing could have survived in the high Arctic, and replaces it with the question of what could have survived and where?

How past colonization patterns shaped the current spatial distribution of species is of special interest in determining the historical forces driving species biogeography. For many species, the chance of winning the battle against global extinction depends on their ability to both live in a range of environments and the ability to track them [26]. Even though this is commonly assumed, few studies have applied large-scale biogeographical analyses as a tool to evaluate present biodiversity in the Arctic, even though macroecological approaches are increasingly applied elsewhere [1,2,2731]. In the case of Arctic soil invertebrates, diversity and distribution patterns are often poorly described or understood [32].

Soil invertebrates play an important role in ecosystem functioning, for example having an impact on nitrogen fixation [33] and carbon availability [34], modifying soil structure and properties [35], indirectly enhancing seedbank persistence [36] or acting as fungal spore vectors [37]. Decomposer communities are essential for ecosystem function, also accounting for the major energy and nutrient pathways in polar terrestrial ecosystems, and the soil microarthropod community fulfils an important role accelerating microbial and fungal uptake, immobilization and mineralization of nutrients required by the autotrophic community [38]. Large scale alterations in distribution patterns of soil invertebrates could thus have significant effects on ecosystem change and development over time.

In most cases, the distribution records of Arctic species are confusing or incomplete, thus data on aspects such as biogeography, dispersal, expansion or reduction of species ranges is difficult, often impossible, to extract. Collembola are an abundant and widespread element of the soil fauna about which there is considerable information available for the polar regions, from molecular biology to ecophysiology [22,3941], making it an ideal group for macroecological analysis. Early studies showed how collembolan distribution can be determined both by broad zoogeographical factors and short-range ecological determinants. At a global level evidence for a pre- Gondwanaland origin for the Collembola can be inferred through group biogeography [42]. More recent studies suggest present day patterns in collembolan distribution in Antarctica to be the result of the interaction between historical and environmental drivers [43]. In the case of Arctic springtails, the taxonomy has recently been subject to comprehensive revision, and diversity and distribution are well described regionally [32,4449].

Recently, efforts have been made to standardize the existing knowledge into a homogeneous dataset, not only at the regional level [32,50], but for the entire Arctic area [44]. Nonetheless, these data are yet to be used in a comprehensive biogeographical analysis. Arctic springtails possess several attributes which make them particularly suitable to large-scale biogeographical analysis, for example, many species are highly flexible in regard to dietary requirements, and possessing long and flexible life cycles that permit advantage to be taken of short periods of favorable conditions [5153].

In a rapidly changing Arctic, with temperatures expected to rise up to 5 °C by the end of 21st Century [54], current biogeographic patterns may well soon belong to the past. Our study focuses on deciphering historical patterns underlining the existing biogeography in Arctic areas and determining whether, in areas of recent colonization, historical influences on these distribution patterns are more strongly visible than ecophysiological constraints. Distance-based test statistics have been developed to test for the existence of clusters of species according to their ranges [55]. By implementing a multivariate statistical approach on species presence/absence data, in combination with ten years' (1996–2005) environmental data from 15 Arctic areas as indicative of contemporary climatic regimes, we aimed to address the following questions concerning the Collembola: (1) Does any biogeographical pattern exist in the Arctic? (2) Can this pattern be explained solely by contemporary climatic regimes? (3) Do biogeographical patterns in the Arctic relate to historical geographical events? We additionally attempt to provide evidence or interpretation as to (4) Could any terrestrial biota have survived in the Arctic in situ throughout the LGM?

2. Experimental Section

1.1. Diversity Data Collection

A presence/absence (1/0) matrix was created from the data compiled at the Arctic collembolan catalogue by Babenko and Fjellberg [44], considering 16 geographical areas also as defined by Babenko and Fjellberg [44] (Figure 1), Area C (Urals), although indicated in the main description table (Table 1), was excluded from the statistical analyses as this region has been considerably under-sampled in comparison with the remaining areas and the diversity index is unrealistically low [56]. Additionally, and to avoid bias in the dataset, species with dubious records (marked as a ‘?’ in Babenko and Fjellberg [44]), likely recent introductions into Arctic regions (for example Orchesella), recently described species (species described from 2005 onwards, as they may have been overlooked in other regions) and species with unresolved status were not included in the current study. Thus 358 species were considered in the study from a total of 390 species described from Arctic areas.

1.2. Environmental Data

Information on contemporary climatic regimes from each mainland area was gathered, including factors previously identified as affecting collembolan species distribution: temperature [39,57] and precipitation [58]. Available meteorological data from the Arctic island archipelagos is in most cases scattered and often biased towards summer measurements. Therefore environmental data from the Arctic islands were not included.

1.2.1. Temperature

Temperature data for the period 1996–2005 were retrieved from the US National Oceanic and Atmospheric Administration (NOAA) [59], available through the World Meteorological Organization (WMO) [60]. A representative weather station was selected for each Arctic area (A: Tromsø airport; B: Arkhangelsk; D: Ostrov Dikson; E: Tiksi; F: Shmidta; G: Cape Lisburne; H: Cambridge Bay; I: Illulisat), All temperature stations are within an altitude range of 0 to 40 m.a.s.l.

1.2.2. Precipitation

Precipitation data were obtained as yearly averages from the WMO data centre [60], where possible sourced from the same weather stations as the temperature data (A: Tromsø airport; B: Arahngelsk; D: Dudinka; E: Tiksi; F: Anadyr'; G: Fairbanks; H: Inivuk; I: Nuuk.) All precipitation stations are located in an altitude range from 0 to 80 m.a.s.l. with the exceptions of Dudinka (200 m.a.s.l.) and Fairbanks (140 m.a.s.l.).

1.3. Statistical Analyses

1.3.1. Gaussian Mixture Clustering

Cluster analysis was carried out using R-Package MCLUST [6163] to perform a distance-based parametric bootstrap test for clustering. This will reveal background biogeographical patterns based on presence-absence data (clustering of species ranges). MCLUST uses Kulczynski distance measures, which approximates to 1 when ranges do not overlap, 0 for complete overlap, and to 0.5 when one range is a subset of the other. The procedure provides a number of meaningful clusters (K), defining each cluster as a series of biotic factors (species) [64]; MCLUST requires previous identification of those points that do not fit in any cluster. These are considered as noise by the software NNclean included in the package [65,66]. This analysis assumes two main characteristics for taxon ranges: (1) the occurrence of a taxon in one geographical unit increases the probability of occurrence in neighboring units and (2) different geographical units vary in their potential to contain species diversity [55]. MCLUST thus computes a Multidimensional Scaling (MDS) based on Kulczynski distances and applies maximum likelihood Gaussian mixture clustering with noise to the MDS points, considering normal components as stable patterns in the data [67]. A parametric bootstrap test was performed on the Kulczynski distance matrix using statistics test distratio with 1000 bootstrap simulations. Clusters were plotted on each geographical location using ESRI ArcMap.

1.3.2. Polynomial Models and Analysis of Variance

Polynomial regression was performed, as it does not assumes a priori linearity in the response, between biodiversity and cluster distribution and the environmental variables using SigmaPlot (V. 11, Systat Software Inc.). Analysis of variance in ranks was applied to the presence/absence data among areas, and weather data among areas, using the same software, to establish pairwise significant differences between areas due to temperature and diversity data.

3. Results

3.1. Clustering

Gaussian mixture clustering was significant for K = 9 (statistics value for original data = 0.26; mean for null data = 0.335; p < 0.05). From the 358 species included in the study, 169 were considered noise by NNclean, while the remaining 189 were allocated to any of the 9 clusters. Cluster 1 was composed mainly by Palaearctic/Atlantic species, clusters 2, 5 and 7 by mainly Nearctic species, clusters 3, 4, 6 and 8 mainly by Palaearctic species and cluster 9 by Holarctic species (Table 2).

Common elements were present within Siberian areas, Atlantic areas and the Canadian Arctic (Figure 2), with some wide-ranging species shared among all them. Just one cluster (cluster 9) was found throughout the Arctic, comprising exclusively cosmopolitan and holarctic, species: Agrenia bidenticulata (Tullberg, 1876), Folsomia bisetosa Gisin, 1953, Folsomia quadrioculata (Tullberg, 1871), Pseudoisotoma sensibilis (Tullberg, 1876), Megalothorax minimus (Willem 1900), Oligaphorura groenlandica (Tullberg, 1876) and Sminthurides malmgreni (Tullberg, 1876). This is in contrast to the Beringian area (F, G) which showed a high number of species characteristic from that area (22 species from cluster 2 exclusive from G, and the 13 species from cluster 4, which are mainly found in F), although some species characteristic of area F also appear in area E: Tetracanthella martynovae Potapov, 1997, Psyllaphorura sensillifera (Martynova, 1981), Protaphorura neriensis (Martynova, 1976), Anurida bondarenkoae Tshelnokov, 1988) (Table 2).

Three clusters appear uniquely in one mainland area and are absent from their respective Arctic island groups: Cluster 2 in the American side of Beringia, comprising species present in Western America (G); Cluster 3 in mid-Siberia including species present in west and mid-Siberia (D); and Cluster 5 in the Canadian Arctic. The American-Beringian cluster (Cluster 2) appears as unique and different to the main Asian-Beringian cluster (Cluster 4) (Figure 2). Most of the species that colonize Atlantic areas have European-Western Palaearctic distributions, while species colonizing Eastern Siberia have mostly Asiatic distributions and species found in the Canadian Arctic are mainly Nearctic (Table 2). Species distributed throughout the Arctic are mostly not exclusively known from Arctic areas, while limited-range or endemic species appear in Beringia, mid-Siberia, the Canadian Arctic and Greenland (Table 3).

High Arctic islands seem to be colonized primarily by wide-ranging species, although that is not the case for the Svalbard archipelago which comprises elements from the common holarctic cluster (9) and the Atlantic and East European clusters. There is just one species currently thought to be specific to the high Arctic islands not present elsewhere in the Arctic, Folsomia altamontana Yosii, 1971, described from Severnaya Zemlya and New Siberian Islands.

3.2. Polynomial Models and Analysis of Variance

Geographical areas were found to be clearly different whether considering species composition (analysis of variance on ranks, H = 84.80, df = 7, p < 0.05) or daily temperature (period 1996–2005) (analysis of variance on ranks, H = 5091.93, df = 7, p < 0.05). The post-hoc Dunn's test for pairwise differences between areas revealed that pairwise differences between areas due to temperature were not the same as the pairwise differences between areas due to species distribution (Table 4).

For 8 out of the 9 clusters found by Gaussian mixture clustering, no clear relation was found between the geographical distribution of the species present in each cluster and the environmental variables accounted. Species belonging to each different cluster shows a geographical distribution (Figure 3) which does not relate to the curved representing average temperature (Figure 4A), temperature of the warmest month (July) (Figure 4B), or precipitation (Figure 4B). The distribution of cluster 1 shows a linear relation with both precipitation (r2 = 0.830, F = 29.255, p < 0.005) and mean annual temperature (r2 = 0.593, F = 8.725, p < 0.05).The distribution of cluster 6 shows a second grade relation with mean temperature of the warmest month (r2 = 0.59, F = 11.40, p < 0.05). The distribution of species considered as noise by Gaussian Mixture Clustering does not show a relationship neither with mean annual temperature (r2 = 0.210, F = 1.591, p >0.05), nor with precipitation (r2 = 0.172, F = 1.244, p > 0.05)

4. Discussion

If the biogeography of Arctic Collembola is determined by current climatic regimes, distribution patterns would follow climatic features rather than defined geographical features. The pattern identified by our analyses, however, appears to be more strongly determined by recent historical events such LGM ice extent and glacial refugia, and colonization patterns.

4.1. Biogeographical Pattern for Arctic Collembola

The geographical distribution of clusters (Figure 2) showed the existence of a relationship within different Atlantic areas (A, a, I, as far as area B in East Europe), western Siberia (B, c, D), eastern Siberia (E, F, D), Asian-Beringia (E,F), Alaskan-Beringia (G) and the Canadian Arctic (H). Greenland appears as more closely related to the European Arctic than to the Canadian Arctic. The western and eastern Palaearctic showed a different cluster structure, sharing just the common Holarctic element. Specific clusters, exclusive to a particular region were found in mid-Siberia, Asian-Beringia, Alaskan-Beringia and the Canadian Arctic, while the high Arctic islands possessed mainly components from the most widespread cluster composed of wide-ranging species. Only a small number of cosmopolitan species were present throughout the Arctic (Table 2).

Species colonizing each defined Arctic area also tended to share specific regional distributions: species colonizing the Canadian Arctic were mainly Nearctic, those colonizing Scandinavia had mainly a western Palaearctic distribution and species colonizing the eastern Palaearctic had mostly Asiatic-Beringian distributions. Endemic species were present in mid- and western Siberia (D), particularly in the Taimyr Peninsula, in Beringia (F and G) and only a single endemic species occurred in eastern North America (H) and Greenland (I) (Table 3).

4.2. Effect of Contemporary Climatic Regimes on Arctic Collembolan Distribution

Factors as precipitation and temperature have been previously indicated as limiting the distribution of collembolan [39,57,58]. Differences found in climate between areas also do not match closely those found in species distribution (Table 4). Clustering do not follow environmental parameters either—for instance areas more distantly related in terms of climatic regimes (e.g., Scandinavia (A) and mid-Siberia (D)) share a cluster which is not share by Greenland (I), which has an intermediate temperature and precipitation regime. Each cluster shows a defined distribution, often sharply skewed towards certain geographic locations (Figure 3), showing no consistency with temperature and precipitation gradients (Figure 4A and 4B). Additionally, species considered as noise do not show a relationship with environmental parameters. Although contemporary climatic regimes may play a role in species distribution, this is not capable of explaining the geographical variation found. Additionally, adjacent areas are more likely to be influenced by similar climatic regimes, for instance the western Palaearctic, Svalbard Archipelago and Greenland are under the influence of the North Atlantic Oscillation [68]. Therefore, there is a possibility that these environmental parameters are in effect autocorrelated with the distribution clusters.

4.3. Relationship between Biogeographical Pattern and Recent Historical Events

Northbound colonization patterns as the Arctic deglaciated would explain why most species colonizing Atlantic areas have European-western Palaearctic distributions, species colonizing eastern Siberia have mostly Asiatic distributions and species found in the Canadian Arctic are mainly Nearctic (Table 1). The strong Atlantic influence on distribution clusters of the Greenland area disagrees with previous Holarctic studies both in Tardigrada [69] and in Cladocera [70] where a Nearctic origin of the Greenland fauna was suggested. Nevertheless, Cladocera and Tardigrada, aquatic groups presenting drought resistance stages, have been highlighted as good airborne dispersers [70]. On the other hand for the non-anhydrobiotic springtails, long distance aerial dispersal in polar areas is unlikely [71] due to mortality following rapid desiccation [72], In spite of collembolan being considered truly soil dwellers, some surface active species can show higher dispersal potential and resistance to desiccation, and aerial dispersal should not to be underestimated for short distance dispersal in moist conditions. Springtails have, however, been shown to survive long periods on sea- water [73], and ocean currents, together with glacial refugia, may have an important role in delineating Antarctic distributions [74]. Collembola has been described to been passively disperse by water [75,76]. Should species of Collembola be effective sea water dispersers, it raises the question of why there is no obvious connection between the Palaearctic and Nearctic areas even though ocean currents and ice flow patterns show a level of physical connection between the Palaearctic and Nearctic across the Arctic Ocean [77] and given that springtails have also been shown to survive extended periods below zero [7880]. Plant molecular studies have also failed to support the traditional hypothesis that considers the north Atlantic an important dispersal barrier between Palaearctic and Nearctic areas [7,81,82]. Abbott et al [83], applying RFLP techniques in chloroplast DNA of the Arctic plant species Saxifraga oppositifolia L., obtained a general Arctic structure showing a series of similarities with the pattern obtained in the current study (Figure 2). A Beringian component was shared among eastern Siberia areas as far as Taymyr, a mid-Siberian component was shared as far as Scandinavia and the Svalbard archipelago and an Atlantic component was present from Scandinavia to western Greenland. These patterns were associated with glacial refugia and post-glacial colonization phenomena. In both cases, either gaussian mixture clustering in the distribution of the Arctic springtails or cp DNA haplotype distribution of S. oppositifolia, the eastern boundaries of the Atlantic component occur west of the Taimyr Peninsula, while the Taimyr forms the western boundary of the Beringian cluster. The link between Atlantic and west and mid-Siberia shown by cluster 8 suggest a link between these areas and could be indicative of post-glacial colonization from LGM ice-free areas in mid-Siberia.

Beringia refugia as determining factor on biogeographical structure of terrestrial fauna and flora have been repeatedly emphasized [4,5,84]. Insights into the colonization of Siberia from Beringia, as described for Arctic plants [83], are provided from the extension of cluster 6 from Beringia (F) to mid-Siberia (D) as well as cluster 4 into eastern Siberia (E). The low number of species colonizing the high Arctic islands could suggest recent colonization. Nonetheless, the high Arctic islands, although colonized by a lower number of species, appear to have a higher species diversity than that which would be expected by island biogeography theory [85]. In the case of high Arctic Canada and many Siberian Arctic islands, only wide-ranging species colonize them rather than species commonly found on the closer mainland (Figure 2). This suggests that mostly wide-ranging and competent dispersers have had the ability to reach these areas. Wrangel island and the New Siberian islands could be also colonized from eastern Siberia and Beringia, their closest mainland with which they share cluster 6 as has been previously suggested based on local fauna descriptions [50], Novaya Zemlya could have been colonized from either or both Eastern Europe and Mid Siberia, while the Svalbard archipelago seems to have been colonized both from distant (mid-Siberia) and close (Atlantic), mainland sources.

The disjunct distribution of the high Arctic species Folsomia altamontana Yosii, 1971, which is present not only in Severnaya Zemlya and the New Siberian islands but also the Himalaya and Putorana Plateau, could suggest either a magnificent ability for long distance dispersal, relict populations for what during glaciation was a more widespread species, or a cryptic speciation event, as has recently been suggested for the Antarctic Friesea grisea (Shaffer 1891) [41]. Folsomia altamontana is thus an interesting target for further phylogeographical analysis.

4.4. Could Collembola Have Survived in Situ in the Arctic during LGM?

Endemic collembolan species (narrow range endemism) occur in north and mid-Siberia (D), Beringia (F and G), the Canadian Arctic (H) and Greenland (I), all of which have been previously indicated as including possible refugia during LGM by a number of authors and for a series of taxa [81,82,8688]. The two possible glacial refugia that could be identified in mid-Siberia, east of Ural Mountains (D), and Beringia (F and G), defined by cluster characteristics (Figure 2) and inferred from the raw data through presence of endemic species (Table 3), agree with glacial refugia described for Arctic plants [82,6]. In contrast, the exclusive cluster in the Canadian Arctic seems to be composed mainly by species widespread (5) in North America, suggesting a main dispersal route to the Arctic rather than a possible refugium, as discussed in the case of Arctic Tardigrada [69]. Additionally, no indication of glacial survival in the high Arctic islands can be found in the current analysis of Arctic Collembola, although occurrence of endemism in other invertebrate groups could indicate otherwise [89]. A particularly interesting case is provided by the high Arctic islands in the Canadian Archipelago, including Ellesmere island and Baffin island. This region was suggested by Hultén [81] as a possible glacial refugium as it remained largely unglaciated throughout LGM and was postulated as a source for post-glacial Arctic recolonization for plant species such as Dryas integrifolia [88] or the collared lemming Dicrostonyx groenlandicus [86]. However, this area does not show other patterns which might be expected in an area of recent colonization, for example no endemic or limited range species, rather being colonized by a low number of species, and possessing mostly cosmopolitan or Holarctic species. Species-level biogeographical analysis however overlooks obscure regional endemism due to cryptic speciation, a phenomenon that is not unknown in the Collembola [41] and not unexpected in Arctic areas as high levels of intra-specific genetic variation have been found in widespread groups genera as Folsomia [90]. Furthermore, species-specific and individual responses to climate fluctuations, as well as differences in environmental, climatic conditions, geographical extension and duration of the occupation of the different glacial refugia, would determine post- glacial characteristics of the species and communities in the area [91] making some refugia more readily identifiable than others. Cryptic glacial refugia can nonetheless be detected applying the appropriate method, as repeatedly shown by phylogeographical studies [22,23,41].

Exclusive clusters could be an indicator of either glacial refugia or early post-glacial recolonization, although the high number of species restricted to Beringia would support the glacial refugium hypothesis in line with the accumulating additional evidence of the Beringian glacial refugia [83,86,87]. Abbott et al. [83] used haplotype diversity analysis to define Beringia as the major refugium for Saxifraga oppositifolia during the LGM, although the high haplotype diversity in Taimyr area was also suggested as being the result of dispersal to the area from different sources rather than resulting from differentiation in glacial refugia. Later studies on the colonization patterns of high Arctic plants [7] have pointed to drifting ice and wood as important high Arctic dispersal vectors, creating patterns such as the link between mid-Siberia and the Svalbard Archipelago, the latter mainly colonized from a refugium east of the Ural Mountains [6]. This agrees with the link shown in Figure 2 between Atlantic and mid-Siberia through cluster 8. The exclusive cluster from the west and mid-Siberian area (D) might therefore reflect the invertebrate community of the glacial refugium described for Arctic plants [6], a hypothesis strengthened by the existence of endemic springtail species in mid-Siberia (D) (Table 3).

Figure 1. Area nomenclature and location as defined by Babenko and Fjellberg [44], including indication of weather stations used in the study indicating type of data obtained as t: temperature and p: precipitation (1: Tromsø (t&p), 2: Arkhangelsk(t&p), 3: Ostrov Dikson, (t), 4: Dudinka (p), 5: Tiski (t&p), 6: Shmidta (t), 7: Anadyr' (p), 8: Cape Lisburne (t), 9: Fairbanks (p), 10: Cambridge Bay (t), 11: Inuvik (p), 12: Illulisat (t), 13: Nuuk (p)). Capital letters define continental areas and lower case indicate Arctic islands (A: western Europe, B: eastern Europe, C: Urals, D: west and mid-Siberia, E: east Siberia, F: North- East Asia, G: western America, H: eastern America, I: Greenland, a: Svalbard, b: Franz Josef Land, c: Novaya Zemlya, d: Severnaya Zemlya, e: New Siberian Islands, f: Wrangel island, h: Queen Elisabeth Islands and Ellesmere island).
Figure 1. Area nomenclature and location as defined by Babenko and Fjellberg [44], including indication of weather stations used in the study indicating type of data obtained as t: temperature and p: precipitation (1: Tromsø (t&p), 2: Arkhangelsk(t&p), 3: Ostrov Dikson, (t), 4: Dudinka (p), 5: Tiski (t&p), 6: Shmidta (t), 7: Anadyr' (p), 8: Cape Lisburne (t), 9: Fairbanks (p), 10: Cambridge Bay (t), 11: Inuvik (p), 12: Illulisat (t), 13: Nuuk (p)). Capital letters define continental areas and lower case indicate Arctic islands (A: western Europe, B: eastern Europe, C: Urals, D: west and mid-Siberia, E: east Siberia, F: North- East Asia, G: western America, H: eastern America, I: Greenland, a: Svalbard, b: Franz Josef Land, c: Novaya Zemlya, d: Severnaya Zemlya, e: New Siberian Islands, f: Wrangel island, h: Queen Elisabeth Islands and Ellesmere island).
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Figure 2. Gaussian mixture clustering geographically represented as number of species allocated to each cluster at each Arctic area. Arrows represent suggested dispersal routes to (thick arrows) and within (thin arrows) Arctic areas. Dashed arrows indicate areas of unresolved main dispersal routes.
Figure 2. Gaussian mixture clustering geographically represented as number of species allocated to each cluster at each Arctic area. Arrows represent suggested dispersal routes to (thick arrows) and within (thin arrows) Arctic areas. Dashed arrows indicate areas of unresolved main dispersal routes.
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Figure 3. Main distribution of the species in a longitude and latitude axis system for each species cluster, as number of species of the cluster present at each longitude/latitude coordinate.
Figure 3. Main distribution of the species in a longitude and latitude axis system for each species cluster, as number of species of the cluster present at each longitude/latitude coordinate.
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Figure 4. Main distribution of average temperature (A), precipitation (B), and mean temperature of the warmest month (July) (C) data in longitude and latitude axis system, as average temperature for the period 1996– 2005 (A) and average yearly precipitation (B) recorded at each longitude/ latitude coordinate.
Figure 4. Main distribution of average temperature (A), precipitation (B), and mean temperature of the warmest month (July) (C) data in longitude and latitude axis system, as average temperature for the period 1996– 2005 (A) and average yearly precipitation (B) recorded at each longitude/ latitude coordinate.
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Table 1. Number of species described from each area and the number of species showing each main type of distribution. Dubious records, as defined in the text, are not included.
Table 1. Number of species described from each area and the number of species showing each main type of distribution. Dubious records, as defined in the text, are not included.
Number of speciesABCDEFGHIabcdefH
Exclusive from the area*52201849221350000000

*Absent from other Arctic areas.

Table 2. Number of species per cluster showing different general distribution patterns.
Table 2. Number of species per cluster showing different general distribution patterns.
Number of species123456789
In the cluster8722191313111077
Table 3. List of restricted or endemic species and the area where they occur (*described as Palaearctic but has only been described from the Yenisey river basin).
Table 3. List of restricted or endemic species and the area where they occur (*described as Palaearctic but has only been described from the Yenisey river basin).
Folsomia cryptophila Potapov and Babenko, 2000D
Willemia fjellbergi Potapov, 1994D
Anurida dynkendga Babenko, 1998D
Anurida zenokhae Babenko, 1998*D
Sminthurus sylvestris Banks, 1899D
Lepidocyrtus tundriensis Tshelnokov & Bondarenko, 1978F
Anurida parapapillosa Tshelnokov, 1998F
Sminthurinus henshawi (Folsom, 1896)F
Micranurida valiana Fjellberg, 1985G
Protaphorura churchulliana (Hammer, 1953)H
Proisotoma roberti Fjellberg, 1991I
Table 4. Dunn's test pairwise comparisons between areas. Upper right table: pairwise comparisons based on species distribution; Lower left table: pairwise comparisons based on daily temperature recorded between 1996–2005. X: the areas are significantly different (p < 0.05). O: differences are not significant (p > 0.05).
Table 4. Dunn's test pairwise comparisons between areas. Upper right table: pairwise comparisons based on species distribution; Lower left table: pairwise comparisons based on daily temperature recorded between 1996–2005. X: the areas are significantly different (p < 0.05). O: differences are not significant (p > 0.05).
Pairwise Comparisons on Presence/Absence of Collembola Species between Areas

Pairwise comparisons on monthly aver. temperature measured for the period 1996–2005 between areas.

Hymenaphorura nearctica000111000000000N
Hymenaphorura palaearctica Pomorski, 2001000110000000010N
Hymenaphorura polonica Pomorski 19901000000000000001
Hymenaphorura sensitiva Pomorski 20010000010000000002
Hymenaphorura sibirica (Tullberg, 1876)011000000000000N
Hymenaphorura similis (Folsom, 1917)000110000000010N
Hypogastrura actandria Fjellberg, 1988100011100000001N
Hypogastrura concolor (Carpenter, 1900)011111111111111N
Hypogastrura fjellbergi Babenko & Bulavintsev, 1993001111000011000N
Hypogastrura helena Christiansen & Bellinger, 19800000010000000002
Hypogastrura lapponica (Axelson, 1902)101010000000000N
Hypogastrura macrotuberculata (Hammer, 1953)0000011000000007
Hypogastrura nivicola (Fitch, 1846)0000011000000007
Hypogastrura oregonensis Yosii, 1960000011100000000N
Hypogastrura perplexa Christiansen & Bellinger, 19800000011000000007
Hypogastrura purpurescens (Lubbock, 1867)|1000000100000001
Hypogastrura rangkuli Martynova, 1975001101000000000N
Hypogastrura sahlbergi (Reuter, 1895)1000000000000001
Hypogastrura sensilis (Folsom 1919)001111101101111N
Hypogastrura spei Babenki 19940010100000000006
Hypogastrura tooliki Fjellberg, 19850000010000000002
Hypogastrura trybomi (Schött, 1893)001100000111100N
Hypogastrura vernalis (Carl, 1901)1000000000000001
Hypohastrura socialis (Uzel, 1891)1000000000000001
Isotoma anglicana Lubbock, 1862110010011010000N
Isotoma arctica Schött, 1893000011000000000N
Isotoma caerulea Bourlet, 1839000001010000000N
Isotoma gorodkovi Martynova, 19700011100000000106
Isotoma riparia (Nicolet, 1842)011110000010000N
Isotomiella minor (Schäffer, 1896)110000111000000N
Isotomodella pusilla Martynova, 19671000000000000001
Isotomodes bisetosus Cassagnau, 19591000000000000001
Isotomurus balteatus (Reuter, 1876)1000000000000001
Isotomurus plumosus Bagnall, 1940011010000001000N
Kalaphorura bermani (Martynova, 1976)000011000000000N
Karlstejnia norvegica Fjellberg, 19741000000100000001
Lepidocyrtus tundriensis Tshelnokov & Bondarenko, 19780000100000000004
Mackenziella psocoides100000100000000N
Marisotoma tenuicornis (Axelson, 1903)1000000000000001
Megalothorax minimus (Willem 1900)1111111110011119
Megaphorura arctica (Tullberg, 1876)1100000110100001
Mesaphorura arbeai Simón, Ruiz, Martin et Luciáñez, 1994000000010000000N
Mesaphorura critica Ellis, 19761000000100000001
Mesaphorura hylophila Rusek, 19821000000100000001
Mesaphorura italica (Rusek, 1971)1000000100000001
Mesaphorura jarmilae Rusek, 19821000000000000001
Mesaphorura jirii Rusek 19821100000110000001
Mesaphorura krausbaueri Börner, 19011000000100000001
Mesaphorura macrochaeta Rusek, 1976110110011000011N
Mesaphorura petterdassi (Fjellberg, 1988)1000000100000001
Mesaphorura sylvatica (Rusek, 1971)1000000000000001
Mesaphorura tenuisensillata Rusek, 1974111000011000000N
Mesaphorura yosii (Rusek, 1967)1000000000000001
Metaphorura affinis (Börner, 1902)1000000000000001
Metisotoma grandiceps (Reuter, 1891)001011100000010N
Micranurida forsslundi Gisin, 19491000000000000001
Micranurida pygmaea Börner, 1901111011111000001N
Micranurida spirillifera Hammer, 19530000011000000007
Micranurida valiana Fjellberg, 19850000010000000002
Micranurophorus musci Bernard, 19771000000000000001
Micraphorura absoloni (Börner, 1901)110011110000000N
Micraphorura alnus (Fjellberg, 1987)000010000000010N
Micraphorura interrupta (Fjellberg, 1987)000100000000000N
Micraphorura nataliae (Fjellberg, 1987)000010000000100N
Mitchellania gibbomucronata (Hammer, 1953)0000001000000005
Mitchellania horrida (Yossi, 1960)0000010000000002
Mitchellaria loricata (Yosii, 1960)0000010000000002
Morulina mackenziana Hammer, 1953000001100000001N
Morulina theeli Babenko & fjellberg, 20010010000000000003
Morulina thulensis Hammer, 1953000011100000010N
Morulodes serratus (Folsom, 1916)0000010000000002
Mucrella denali (Fjellberg, 1985)000011000000000N
Mucrella navicularis (Schött, 1893)001100000000000N
Multivesicula dolomitica Rusek, 1982001010100000010N
Oligaphorura groenlandica (Tullberg, 1876)1111111111111119
Oligaphorura nuda (Fjellberg, 1987)000101000000000N
Oligaphorura pingicola (Fjellberg, 1987)0000010000000002
Oligaphorura reversa (Fjellberg, 1987)0000010000000002
Oligaphorura schoetti (Lie- Pettersen, 1896)1000000000000001
Oligaphorura ursi (Fjellberg, 1984)111011011010000N
Pachyotoma crassicauda (Tullberg, 1871)011001000010000N
Paranura quadrilobata Hammer, 1953000011100000000N
Paranura sexpunctata Axelson, 19021000000000000001
Parisotoma agrelli (Delamare Debuotteville, 1950)1000000000000001
Parisotoma ekmani (Fjellberg, 1977)111011110000001N
Parisotoma longa (Potapov, 1991)0010100000000006
Parisotoma notabilis (Schäffer, 1896)111011111010000N
Parisotoma reducta (Rusek, 1984)011110000000100N
Parisotoma trichaetosa (Martynova, 1977)0000100000000004
Podura aquatica Linnaeus, 1758111111100001111N
Pogonognathellus lividus (Tullberg, 1876)0010100000000006
Proisotoma ananevae Babenko & Bulavintsev, 1993001010000010010N
Proisotoma buddenbrocki strenzke, 19541000000000000001
Proisotoma clavipila (Axelson, 1903)1000000000000001
Proisotoma ladaki Denis, 19360010000000000003
Proisotoma minima (Absolon, 1901)1000000000000001
Proisotoma minuta (Tullberg, 1871)1000000000000001
Proisotoma roberti000000010000000N
Proisotoma subarctica Gisin, 1950101000000010000N
Protaphorura armata (Tullberg, 1986)1000000000000001
Protaphorura bicampata (Gisin, 1956)101000000000000N
Protaphorura boedvarssoni Pomorski, 19931110000000000008
Protaphorura borealis (Martynova, 1973)001111000000010N
Protaphorura campata000000010000000N
Protaphorura cancellata (Gisin, 1956)101000000011000N
Protaphorura churchulliana (Hammer, 1953)0000001000000005
Protaphorura duodecimopunctata (Folsom, 1919)0000011000000007
Protaphorura islandica (Bödvarsson, 1959)1000000000000001
Protaphorura jacutica (Martynova, 1976011100000000000N
Protaphorura macfadyeni (Gisin, 1953)1000000110000001
Protaphorura madrodentata (Hammer, 1953)000000100000001N
Protaphorura neriensis (Martynova, 1976)0001100000000004
Protaphorura paucisetosa (Hammer, 1953)0000001000000005
Protaphorura pjasinae (Martynova, 1976)001010000011110N
Protaphorura procampata (Gisin, 1956)1100000100000001
Protaphorura pseudoarmata (Folsom, 1917)000001110000000N
Protaphorura pseudovanderdrifti (Gisin, 1957)1000000100000001
Protaphorura pulvinata (Gisin, 1954)011000000000000N
Protaphorura subartica (Martynova, 1976)011100000010100N
Protaphorura subuliginata Gisin, 19561100000100000001
Protaphorura taimiryca (Martynova, 1976)001000000010000N
Protaphorura tricampata (Gisin, 1956)1000000000000001
Protaphorura tschernovi (Martynova, 1976)0010000000000003
Protaphorura tundricola (Martynova, 1976)0010000000000003
Protaphorura vanderdrifti (Gisin, 1952)010000000000000N
Pseudachorutella asigillata (Börner, 1901)1100000000000001
Pseudachorutes corticicolus (Schäffer, 1896)1000000000000001
Pseudachorutes dubius Krausbauer, 18981100000000000001
Pseudachorutes sibiricus Rusek, 1991011111000000000N
Pseudachorutes subcrassus Tullberg, 18711000000000000001
Pseudanurophorus alticolus Bagnall, 1949101010011001000N
Pseudanurophorus arcticus Christiansen, 1951001011100000000N
Pseudanurophorus binoculatus Kseneman 1934111011011000001N
Pseudoisotoma sensibilis (Tullberg, 1876)1111111110100119
Pseudonychiurus dentatus (Folsom, 1902)0000010000000002
Psyllaphorura sensillifera (Martynova, 1981)0001100000000004
Psyllaphorura uenoi (Yosii, 1954)0000010000000002
Ptenothrix palmatus (Folsom, 1902)0000010000000002
Schaefferia oculea Babenko, 1999000100000000000N
Schoettella ununguiculata (Tullberg, 1869)000000110000000N
Secotomodes sibiricus Potapov, 19880010000000000003
Sminthurides malmgreni (Tullberg, 1876)1111111110101119
Sminthurides occultus Mills, 19340000001000000005
Sminthurides parvulus (Krausbauer, 1898)111110000000000N
Sminthurides pseudassimilis Stach, 19561000000000000001
Sminthurides schoetti Axelson, 1903101110010010010N
Sminthurinus albifrons (Tullberg, 1871)1000000000000001
Sminthurinus bimaculatus Axelson, 19021100000000000001
Sminthurinus elegans (Fitch, 1863)100001000000000N
Sminthurinus henshawi (Folsom, 1896)0000100000000004
Sminthurinus quadrimaculatus (Ryder, 1879)0000011000000007
Sminthurus incisus Snider, 19780000010000000002
Sminthurus multipunctatus Schäffer, 1896001100000000000N
Sminthurus nigromaculatus Tullberg, 1871001000010000000N
Sminthurus orientalis Bretfeld, 2000000110000000010N
Sminthurus sylvestris Banks, 18990010000000000003
Sminthurus variegatus Tullberg, 18760010100000000006
Sphaeridia leutrensis Dunger & Bretfeld, 19890010000000000003
Sphaeridia pumilis (Krausbauer, 1898)111111111000001N
Stachanorema tolerans Babenko, 1994000000100000001N
Stenacidia violacea (Reuter, 1881)101010000001010N
Stenaphorurella quadrispina (Börner, 1901)010000000000000N
Supraphorura furcifera (Börner, 1901)011000000010000N
Tantulonychiurus volinensis (Szeptycki, 1964)0011100000000006
Tetracanthella arctica Cassagnau 1959100000001000001N
Tetracanthella martynovae Potapov, 19970001100000000004
Tetracanthella orientalis Martynova, 19770000100000000004
Tetracanthella pilosa Schött, 18911000000000000001
Tetracanthella sibirica Deharveng, 1987000111110000110N
Tetracanthella wahlgreni Axelson, 19071110000000100008
Thalassaphorura debilis (Moniez, 1890)100001010000101N
Thalassaphorura duplopunctata (Strenzke, 1954)100001010000101N
Tomocerus minutus Tullberg, 1876111011000000000N
Tomocerus sibiricus Reuter, 1891011000000000000N
Tomocerus vulgaris (Tullberg, 1871)0010000000000003
Uralaphorura schilovi (Martynova, 1976)101100000010000N
Uzellia hansoni Mills & Richards, 19530000011000000007
Vertagopus arcticus Martynova, 1969101110011001110N
Vertagopus brevicaudatus (Carpenter, 1900)001000000101001N
Vertagopus cinereus (Nicolet, 1842)1000000100000001
Vertagopus reuteri (Schött, 1893)0000100000000004
Vertagopus Sarekensis (Whalgren, 1906)1000000000000001
Vertagopus westerlundi (Reuter, 1897)1000000000000001
Wankeliella intermedia Potapov & Stebaeva, 1997001000001000000N
Wankeliella medialis Simón & Jordana, 19941000000000000001
Weberacantha octa Christiansen, 1951000011110000000N
Willemia anophthalma Börner 1901101111111000001N
Willemia arida Fjellberg, 19910000010000000002
Willemia denisi Mills, 1932111011110000010N
Willemia fjellbergi Potapov, 19940010000000000003
Willemia multilobata Gers & Deharveng, 1985001000000000001N
Willemia scandinavica Stach, 1949101001111101011N
Willemia similis Mills, 1934011111111001111N
Willowsia nigromaculata (Lubbock, 1873)101010100000000N
Xenylla boernery Axelson, 19031000000000000001
Xenylla brevicaudata Tullberg, 18691100000000000001
Xenylla canadensis Hammer, 19530000001000000005
Xenylla corticales Börner 19011000000000000001
Xenylla grisea Axelson, 19001000000100000001
Xenylla humicola (Fabricius, 1780)111010111010000N
Xenylla maritima Tullberg 18691100000000000001
Xenylla martynovae Dunger, 19830010000000000003
Xenylla xavieri Gama, 19591000000000000001
Xenyllodes armatus Axelson 1903111111101010000N
Xenyllodes wapti fjellberg, 19850000010000000002


We would like to express our gratitude to Arne Fjellberg for highly valuable comments and corrections on species distributions. We would also like to thank Peter Convey and two anonymous reviewers for valuable and enriching comments to the manuscript.

References and Notes

  1. Woodward, F.I.; Kelly, C.K. Why are species not more widely distributed? In Macroecology: Concepts and Consequences. 43rd Annual Symposium of the British Ecological Society, University of Birmingham; Cambridge University Press: Cambridge, UK, 2002. [Google Scholar]
  2. Stevens, R.D. Historical processes enhance patterns of diversity along latitudinal gradients. Proc. R. Soc. B 2006, 273, 2283–2289. [Google Scholar]
  3. Hewitt, G.M. Some genetic consequences of ice ages, and their role in divergence and speciation. Biol. J. Linn. Soc. 1996, 58, 247–276. [Google Scholar]
  4. Hewitt, G.M. The genetic legacy of the Quaternary ice ages. Nature 2000, 405, 907–913. [Google Scholar]
  5. Brochmann, C.; Gabrielsen, T.M.; Nordal, I.; Landvik, J.Y.; Elven, R. Glacial survival or tabula rasa? The history of the North Atlantic biota revisited. Taxon 2003, 52, 417–450. [Google Scholar]
  6. Skrede, I.; Eidensen, P.; Piñeiro Portela, R.; Brochman, C. Refugia, differentiation and postglacial migration in arctic– alpine Eurasia, exemplified by the mountain avens (Dryas octopetala L.). Mol. Ecol. 2006, 15, 1827–1840. [Google Scholar]
  7. Alsos, I.G.; Eidesen, P.B.; Ehrich, D.; Skrede, I.; Westergaard, K.; Jacobsen, G.H.; Landvik, J.Y.; Taberlet, P.; Brochmann, C. Frequent long- distance plant colonization in the changing Arctic. Science 2007, 316, 1601–1608. [Google Scholar]
  8. Bennett, K.D.; Provan, J. What do we mean by ‘refugia’? Quat. Sci. Rev. 2008, 27, 2449–2455. [Google Scholar]
  9. Gataullin, V.; Mangerud, J.; Svendsen, J.I. The extent of the Late Weichselian ice sheet in the southeastern Barents Sea. Global Planet. Change 2001, 31, 453–474. [Google Scholar]
  10. Briner, J.P.; Davis, P.T.; Miller, G.H. Latest pleistocene and holocene glaciation of baffin island, arctic canada: key patterns and chronologies. Quat. Sci. Rev. 2009, 28, 2075–2087. [Google Scholar]
  11. Paus, A.; Velle, G.; Larsen, J.; Nesje, A.; Lie, Ø. Lateglacial nunataks in central Scandinavia: Biostratigraphical evidence for ice thickness from Lake Flåfattjønn, Tynset, Norway. Quat. Sci. Rev. 2006, 25, 1228–1246. [Google Scholar]
  12. Bitinas, A. New insights into the last deglaciation of the south-eastern flank of the Scandinavian Ice Sheet. Quat. Sci. Rev. 2011. [Google Scholar] [CrossRef]
  13. Elias, S.A.; Short, S.K.; Birks, H.H. Late Wisconsin environments of the Bering Land Bridge. Palaeogeogr. Palaeoclimatol. Palaeoecol. 1997, 136, 293–308. [Google Scholar]
  14. Astakhov, V. The last ice sheet of the Kara Sea: Terrestrial constraints on its age. Quat. Int. 1998, 45–46, 19–28. [Google Scholar]
  15. Mangerud, J.; Astakhov, V.; Svendsen, J.I. The extent of the Barents-Kara ice sheet during the Last Glacial Maximum. Quat. Sci. Rev. 2002, 21, 111–119. [Google Scholar]
  16. Provan, J.; Bennett, K.D. Phylogeographic insights into cryptic glacial refugia. Trends Ecol. Evol. 2008, 23, 564–571. [Google Scholar]
  17. Kaakinen, A.N.U.; Salonen, V.P.; Kubischta, F.; Eskola, K.O.; Oinonen, M. Weichselian glacial stage in Murchisonfjorden, Nordaustlandet, Svalbard. Boreas 2009, 38, 718–729. [Google Scholar]
  18. Kubischta, F.; Knudsen, K.L.; Kaakinen, A.; Saloonen, V.P. Late quaternary foraminiferal record in Murchisonfjorden, Nordaustlandet, Svalbard. Polar Res. 2010, 29, 283–297. [Google Scholar]
  19. Hormes, A.; Akçar, N.; Kubik, P. Cosmogenic radionuclide dating indicates ice-sheet configuration during MIS 2 on Nordaustlandet, Svalbard. Boreas 2011. [Google Scholar] [CrossRef]
  20. Landvik, J.Y.; Brook, E.J.; Gualtieri, L.; Raisbeck, G.; Salvigsen, O.; Yiou, F. Northwest Svalbard during the last glaciation: ice-free areas existed. Geology 2003, 31, 905–908. [Google Scholar]
  21. Convey, P.; Gibson, J.A. E.; Hillenbrand, C.D.; Hodgson, D.A.; Pugh, P.J. A.; Smellie, J.L.; Stevens, M.I. Antarctic terrestrial life- challenging the history of the frozen continent? Biol. Rev. 2008, 83, 103–117. [Google Scholar]
  22. McGaughran, A.; Torricelli, G.; Carapelli, A.; Frati, F.; Stevens, M.I.; Convey, P.; Hogg, I.D. Contrasting phylogeographical patterns for springtails reflect different evolutionary histories between the Antarctic Peninsula and continental Antarctica. J. Biogeogr. 2010, 37, 103–119. [Google Scholar]
  23. Mortimer, E.; van Vuuren, B.J.; Lee, J.E.; Marshall, D.J.; Convey, P.; Chown, S. L. Mite dispersal among the Southern Ocean Islands and Antarctica before the last glacial maximum. Proc. R. Soc. B 2011, 278, 1247–1255. [Google Scholar]
  24. Zettel, J. Alpine Collembola-adaptations and strategies for survival in harsh environments. Zoology 2000, 102, 73–89. [Google Scholar]
  25. Fjellberg, A. Cryophilic Isotomidae (Collembola) of the Northwestern Rocky Mountains, U.S.A. Zootaxa 2010, 2513, 27–49. [Google Scholar]
  26. Pease, C.M.; Lande, R.; Bull, J.J. A Model of population growth, dispersal and evolution in a changing environment. Ecology 1989, 70, 1657–1664. [Google Scholar]
  27. Blackburn, T.M.; Gaston, K.J. Scale in macroecology. Global Ecol. Biogeogr. 2002, 11, 185–189. [Google Scholar]
  28. Clarke, A.; Griffiths, H.J.; Linse, K.; Barnes, D.K.A.; Crame, J.A. How well do we know the Antarctic marine fauna? A preliminary study of macroecological and biogeographical patterns in Southern Ocean gastropod and bivalve molluscs. Diversity Distrib. 2007, 13, 620–632. [Google Scholar]
  29. Kent, M. Biogeography and macroecology: now a significant component of physical geography. Progr. Phys. Geogr. 2007, 31, 643–657. [Google Scholar]
  30. Calosi, P.; Bilton, D.T.; Spicer, J.I.; Votier, S.C.; Atfield, A. What determines a species' geographical range? Thermal biology and latitudinal range size relationships in European diving beetles (Coleoptera: Dytiscidae). J. Anim. Ecol. 2010, 79, 194–204. [Google Scholar]
  31. Chown, S.L.; Gaston, K. J. Body size variation in insects: A macroecological perspective. Biol. Rev. 2010, 85, 139–169. [Google Scholar]
  32. Coulson, S.J. Terrestrial and freshwater invertebrate fauna of the high Arctic archipelago of Svalbard. Zootaxa 2007, 1448, 41–58. [Google Scholar]
  33. Birkemoe, T.; Liengen, T. Does collembolan grazing influence nitrogen fixation by cyanobacteria in the high Arctic? Polar Biol. 2000, 23, 589–592. [Google Scholar]
  34. Cole, L.; Bardgett, R.D.; Ineson, P. Enchytraeid worms (Oligochaeta). enhance mineralization of carbon in organic upland soils. Eur. J. Soil Sci. 2000, 51, 185–192. [Google Scholar]
  35. Schrader, S.; Langmaack, M.; Helming, K. Impact of Collembola and Enchytraeidae on soil surface roughness and properties. Biol. Fertil. Soils 1997, 25, 396–400. [Google Scholar]
  36. Mitschunas, N.; Wagner, M.; Filser, J. Evidence for a positive influence of fungivorous soil invertebrates on the seed bank persistence of grassland species. J. Ecol. 2006, 94, 791–800. [Google Scholar]
  37. Renker, C.; Otto, P.; Schneider, K.; Zimdars, B.; Maraun, M.; Buscot, F. Oribatid mites as potential vectors for soil microfungi: Study of mite- associated fungal species. Microb. Ecol. 2005, 50, 518–528. [Google Scholar]
  38. Bardgett, R.D.; Wardle, D.A.; Yeates, G.W. Linking above-ground and below-ground interactions: How plant responses to foliar herbivory influence soil organisms. Soil Biol. Biochem. 1998, 30, 1867–1878. [Google Scholar]
  39. Hodkinson, I.D.; Webb, N.R.; Bale, J.S.; Block, W.; Coulson, S.J.; Strathdee, A.T. Global change and Arctic ecosystems: conclusions and predictions from experiments with terrestrial invertebrates on Spitsbergen. Arct. Alp. Res. 1998, 30, 306–313. [Google Scholar]
  40. Holmstrup, M.; Sømme, L. Dehydration and cold hardiness in the Arctic Collembolan Onychiurus arcticus Tullberg 1876. J. Comp. Physiol. B 1998, 168, 197–203. [Google Scholar]
  41. Torricelli, G.; Carapelli, A.; Convey, P.; Nardi, F.; Boore, J.L.; Frati, F. High divergence across the whole mitochondrial genome in the “pan-Antarctic” springtail Friesea grisea: Evidence for cryptic species? Gene 2010, 449, 30–40. [Google Scholar]
  42. Blackith, R.E.; Blackith, R.M. Zoogeographical and ecological determinants of collembolan distribution. Proc. R. Ir. Acad., Sect. B 1975, 75, 345–368. [Google Scholar]
  43. Caruso, T.; Hogg, I.D.; Carapelli, A.; Frati, F.; Bargagli, R. Large-scale spatial patterns in the distribution of Collembola (Hexapoda) species in Antarctic terrestrial ecosystems. J. Biogeogr. 2009, 36, 879–886. [Google Scholar]
  44. Babenko, A.; Fjellberg, A. Collembola septentrionale. A catalogue of springtails of the Arctic Regions; KMK Scientific Press Ltd.: Moscow, Russia, 2006. [Google Scholar]
  45. Fjellberg, A. Collembola from Nordaustlandet, Svalbard. Fauna Norvegiva Series B 1997, 44, 71–75. [Google Scholar]
  46. Fjellberg, A. The collembola of the Norwegian Arctic islands; Norsk Polarinstitutt: Oslo, Norway, 1994. [Google Scholar]
  47. Fjellberg, A. The Collembola of Fennoscandia and Denmark; Brill: Leiden, The Netherlands, 2007. [Google Scholar]
  48. Mills, H.B.; Richards, W.R. Collembola from Arctic and Boreal Canada. J. Kans. Entomol. Soc. 1953, 26, 53–59. [Google Scholar]
  49. Potapov, M.B.; Babenko, A.B. Species of the genus Folsomia (Collembola: Isotomidae) of northern Asia. Eur. J. Entomol. 2000, 97, 51–74. [Google Scholar]
  50. Babenko, A. The springtail (Hexapoda, Collembola) fauna of Wrangel Island. Entomol. Rev. 2010, 90, 571–584. [Google Scholar]
  51. Addison, J.A. Biology of Hypogastrura tullbergi (Collembola) at a high Arctic site. Holoarctic Ecol. 1981, 4, 49–58. [Google Scholar]
  52. Convey, P. Life history adaptations to polar and alpine environments. In Low Temperature Biology of Insects; Denlinger, D.L., Lee, R.E., Jr., Eds.; Cambridge University Press: Cambridge, UK, 2010; pp. 297–321. [Google Scholar]
  53. Hawes, T.C.; Couldridge, C.E.; Bale, J.S.; Worland, M.R.; Convey, P. Habitat temperature and the temporal scaling of cold hardening in the high Arctic collembolan, Hypogastrura tullbergi (Schäffer). Ecol. Entomol. 2006, 31, 450–459. [Google Scholar]
  54. ACIA Scientific Report 2005. Available online: (accessed on 15 November 2010).
  55. Hennig, C.; Hausdorf, B. Distance-based parametric bootstrap tests for clustering of species ranges. Comput. Stat. Data Anal. 2004, 45, 875–895. [Google Scholar]
  56. Fjellberg. A. Tjømme, Norway. Personal Communication, 2010.
  57. Hodkinson, I.D.; Coulson, S.J.; Webb, N.R.; Block, W. Can high Arctic soil microarthropods survive elevated summer temperatures? Funct. Ecol. 1996, 10, 314–321. [Google Scholar]
  58. Detsis, V.; Diamantopoulos, J.; Kosmas, C. Collembolan assemblages in Lesvos, Greece. Effects of differences in vegetation and precipitation. Acta Oecol. 2000, 21, 149–159. [Google Scholar]
  59. National Climatic Data Center. US. Available online: (accessed on 15 July 2010).
  60. World Weather Information Centre. Available online: (accessed on 15 July 2010).
  61. R Development Core Team. R: A Language and Environment for Statistical Computing; R Foundation for Statistical Computing: Vienna, Austria, 2009. [Google Scholar]
  62. Fraley, C.; Raftery, A.E. Model-based clustering, discriminant analysis, and Density Estimation. J. Am. Stat. Assoc. 2002, 97, 611–631. [Google Scholar]
  63. Fraley, C.; Raftery, A.E. MCLUST for R: Normal Mixture Modeling and Model-based Clustering, version 3; Technical Report 504; Department of Statistics, University of Washington: Seattle, WA, USA, 2006; (revised December 2009). [Google Scholar]
  64. Hausdorf, B.; Hennig, C. Biotic element analysis in biogeography. Syst. Biol. 2003, 52, 717–723. [Google Scholar]
  65. Byers, S.; Raftery, A.E. Nearest-neighbor clutter removal for estimating features in spatial point processes. J. Am. Stat. Assoc. 1998, 93, 577–584. [Google Scholar]
  66. Hausdorf, B.; Hennig, C. Does vicariance shape biotas? Biogeographical tests of the vicariance model in the north-west European land snail fauna. J. Biogeogr. 2004, 31, 1751–1757. [Google Scholar]
  67. Hennig, C. Cluster-wise assessment of cluster stability. Comput. Stat. Data Anal. 2007, 52, 258–271. [Google Scholar]
  68. Dickson, R.R.; Osborn, T.J.; Hurrell, J.W.; Meincke, J.; Blindheim, J.; Adlandsvik, B.; Vinje, T.; Alekseev, G.; Maslowski, W. The Arctic ocean response to the North Atlantic oscillation. J. Clim. 2000, 13, 2671–2696. [Google Scholar]
  69. Pugh, P.J.A.; McInnes, S.J. The origin of Arctic terrestrial and freshwater tardigrades. Polar Biol. 1998, 19, 177–182. [Google Scholar]
  70. Gíslason, G.M. Origin of freshwater fauna of the North-Atlantic islands; present distribution in relation to climate and possible migration routes. Verh. Int. Ver. Limnol. 2005, 29, 198–203. [Google Scholar]
  71. Hawes, T.C.; Worland, M.R.; Convey, P.; Bale, J.S. Aerial dispersal of springtails on the Antarctic Peninsula: implications for local distribution and demography. Antarct. Sci. 2007, 19, 3–10. [Google Scholar]
  72. Hopkin, S.P. The Biology of the Collembola (springtails): The Most Abundant Insects in the World; Natural History Museum: London, UK, 1997. [Google Scholar]
  73. Coulson, S.J.; Hodkinson, I.D.; Webb, N.R.; Harrison, J.A. Survival of terrestrial soil- dwelling arthropods on and in seawater: implications for trans- oceanic dispersal. Funct. Ecol. 2002, 16, 353–356. [Google Scholar]
  74. McGaughran, A.; Stevens, M.I.; Holland, B.R. Biogeography of circum-Antarctic springtails. Mol. Phylogenet. Evol. 2010, 57, 48–58. [Google Scholar]
  75. Hawes, T.C. Rafting in the Antarctic springtail, gomphiocephalus hidgsoni. Antarc. Sci. 2011. in press. [Google Scholar] [CrossRef]
  76. Hawes, T.C.; Worland, M.R.; Bale, J.S.; Convey, P. Rafting in Antarctic Collembola. J. Zool. 2008, 274, 44–50. [Google Scholar]
  77. Smith, W.O. Polar Oceanography. Part A, Physical science; Academic Press: San Diego, CA, USA, 1990. [Google Scholar]
  78. Coulson, S.J.; Birkemoe, T. Long- term cold tolerance in Arctic invertebrates: Recovery after 4 years at below -20 deg.C. Can. J. Zool. 2000, 78, 2055–2058. [Google Scholar]
  79. Sinclair, B.J.; Sjursen, H. Cold tolerance of the Antarctic springtail Gomphiocephalus hodgsoni (Collembola, Hypogastruridae). Antarct. Sci. 2001, 13, 271–279. [Google Scholar]
  80. Worland, M.R.; Convey, P. Rapid cold hardening in Antarctic microarthropods. Funct. Ecol. 2001, 15, 515–524. [Google Scholar]
  81. Hultén, E. Outline of the History of Arctic and Boreal Biota during the Quarternary Period; Lehre J Cramer: New York, NY, USA, 1937. [Google Scholar]
  82. Abbott, R.J.; Brochmann, C. History and evolution of the arctic flora: in the footsteps of Eric Hultén. Mol. Ecol. 2003, 12, 299–313. [Google Scholar]
  83. Abbott, R.J.; Smith, L.C.; Milne, R.I.; Crawford, R.M.M.; Wolff, K.; Balfour, J. Molecular analysis of plant migration and refugia in the Arctic. Science 2000, 289, 1343–1346. [Google Scholar]
  84. Cook, J.A.; Hoberg, E.P.; Koehler, A.; Henttonen, H.; Wickström, L.; Haukisalmi, V.; Galbreath, K.; Chernyavski, F.; Dokuchaev, N.; Lahzuhtkin, A.; et al. Beringia: Intercontinental exchange and diversification of high latitude mammals and their parasites during the Pliocene and quaternary. Mammal Study 2005, 30, 33–44. [Google Scholar]
  85. Ulrich, W.; Fiera, C. Environmental correlates of species richness of European springtails (Hexapoda: Collembola). Acta Oecol. 2009, 35, 45–52. [Google Scholar]
  86. Fedorov, V.B.; Stenseth, N.C. Multiple glacial refugia in the North American Arctic: Inference from phylogeography of the collared lemming (Dicrostonyx groenlandicus). Proc. R Soc. London Ser. B 2002, 269, 2071–2077. [Google Scholar]
  87. Weider, L.J.; Hobæk, A. Glacial refugia, haplotype distributions, and clonal richness of the Daphnia pulex complex in arctic Canada. Mol. Ecol. 2003, 12, 463–473. [Google Scholar]
  88. Tremblay, N.O.; Schoen, D.J. Molecular phylogeography of Dryas integrifolia: Glacial refugia and postglacial recolonization. Mol.r Ecol. 1999, 8, 1187–1198. [Google Scholar]
  89. Strathdee, A.T.; Bale, J.S.; Hodkinson, I.D.; Block, W.C.; Webb, N.R.; Coulson, S.J. Identification of 3 previously unknown morphs of Acyrthosiphon svalbardicum Heikinheimo (Hemiptera, Aphididae) on Spitsbergen. Entomol. Scand. 1993, 24, 43–47. [Google Scholar]
  90. Hogg, I.D.; Hebert, P.D.N. Biological identification of springtails (Hexapoda: Collembola). From the Canadian Arctic, using mitochondrial DNA barcodes. Can. J. Zool. 2004, 82, 749–754. [Google Scholar]
  91. Stewart, J.R.; Lister, A.M.; Barnes, I.; Dalén, L. Refugia revisited: individualistic responses of species in space and time. Proc. R. Soc. B 2010, 277, 661–671. [Google Scholar]
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