Research Article |
Corresponding author: Matti Landvik ( matti.landvik@gmail.com ) Academic editor: Alessandro Campanaro
© 2017 Matti Landvik, Andreia Miraldo, Pekka Niemelä, Uldis Valainis, Raimonds Cibuļskis, Tomas Roslin.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Landvik M, Miraldo A, Niemelä P, Valainis U, Cibuļskis R, Roslin T (2017) Evidence for geographic substructuring of mtDNA variation in the East European Hermit beetle (Osmoderma barnabita). In: Campanaro A, Hardersen S, Sabbatini Peverieri G, Carpaneto GM (Eds) Monitoring of saproxylic beetles and other insects protected in the European Union. Nature Conservation 19: 171-189. https://doi.org/10.3897/natureconservation.19.12877
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The genus Osmoderma is a flagship taxon of invertebrate conservation in Europe and encompasses a complex of four accepted species. While species limits amongst Osmoderma have been intensively studied, patterns of intraspecific variation are poorly known. In this paper, the authors focus on clarifying the phylogeographic structure of the East European Osmoderma barnabita using samples from Croatia to Finland. Samples of hind legs were collected from populations in Latvia and Finland (n=186) and combined with previously-published sequences from GenBank and museum specimens (n=10). In a partial sequence of the mitochondrial COI gene (759 bp), 26 closely related haplotypes were found. Beetle samples from different parts of Europe were distinct and showed no overlap in haplotype composition. The solitary population of Finland proved to be monomorphic and all 97 individuals sampled here belonged to a single haplotype unique to this region. The results suggest the Northern parts of Eastern Europe to be dominated by a single COI haplotype to which most of the other haplotypes are linked by one or two mutations. The pattern seems to reflect a founder effect or a strong bottleneck event. While O. barnabita is widely distributed over Eastern Europe, current patterns of mitochondrial genetic diversity appear influenced by population history and little homogenisation by ongoing gene flow. From a conservation perspective, the patterns suggest that regional populations might need to be managed as subunits and that the population of Finland may be affected by low genetic diversity.
Osmoderma, population expansion, demographic history, phylogeography, sub-populations, threatened species
Genetic diversity within a single species is a fundamental aspect of biodiversity and can be used in species conservation and management (
A wealth of molecular methods is now available for detecting the level of intraspecific diversity or divergence amongst sub-populations (
In Europe, the migration of organisms after the Pleistocene glacial period has significantly influenced patterns of genetic variation within species (
In Europe, one example of a taxon presumptively expanding from South to North after the glacial period is the genus Osmoderma LePeletier & Audinet-Serville, 1828 (
The hermit beetles were previously thought to be a single species, Osmoderma eremita. However, following the revisions by
In this paper, the authors focus on Osmoderma barnabita within the Eastern clade of the hermit beetle, occurring from Northern Greece across Eastern parts of Europe and Western Russia to South West Finland (see
To obtain comprehensive material from the full range of O. barnabita, three sources were used: samples of hind leg tarsus or tibia from live beetles sampled in Latvia and Finland (n=186), previously published sequences from GenBank (n=3) and new sequences from dry-mounted and ethanol-stored museum specimens (n=7). In total, material was obtained from 196 individuals collected in 9 countries (Figure
Non-destructive sampling was achieved by pheromone trapping (in Finland and Latvia); for a trap description see
Museum specimens (total n=7), from single locations, were obtained on request from Central and Eastern European museums (Figure
Sampling sites of Osmoderma barnabita and of CO1 haplotypes within regions. The regional sub-populations defined in the text are indicated by hatched areas. Sampling sites are identified by open circles.
Origin of sequence data used in this study (*reared individual). Sequenced specimens were collected from Central, Eastern and Northern Europe. The main part of the dataset (N=193) consists of new sequences (GenBank accession codes: KY362552-KY362744), with additional material obtained from
Country | Location | Collecting dates | Coordinates | No. individuals | Reference |
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Croatia | Plitvice Lakes Nat. Park | 30.7.2002 | 44°52'N, 15°34'E | 1 |
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Estonia | Koiva woodland | n.a. | 57°40'N, 26°15'E | 1 | current study |
Finland | Turku region | 18.7–1.8.2011 and 4–30.7.2012 | 60°25'N, 22°09'E | 97 | current study |
Germany | Saxony, Hagberg | 12.6.2005 | 51°32'N, 14°38'E | 1 |
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Hungary | Győr, Győr-Moson-Sopron | 20.1.2011* | 47°42'N, 17°36'E | 1* | current study |
Hungary | Sárvár, Vas county | 28.7.2008 | 47°17'N, 16°57'E | 1 | current study |
Latvia | Pededze Valley | 5–26.7.2011 | 57°30'N, 26°53'E | 89 | current study |
Slovakia | Zvolen, Dobrá Niva | 7.2006 | 48°28'N, 19°06'E | 1 |
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Romania | Roades, Brasov | 12.7.2012 | 46°04'N, 25°03'E | 1 | current study |
Russia | Tolmachevo | 23.6.2011 | 58°51'N, 29°52'E | 3 | current study |
Total DNA was extracted from leg samples using the Macherey-Nagel NucleoSpin Tissue kit following the manufacturer’s instructions. To amplify a more diverse fragment (approx. 800 base pairs) than the most commonly used ‘barcoding region’ (
Estimation of haplotype relationships and genetic population structure
MtDNA sequences were edited with Geneious v8.1.7 (
Changes in historical population size
Historical signatures of population growth were assessed for the entire dataset by comparing the observed distribution of pairwise differences between haplotypes and the expected results under a constant population size model, a sudden-demographic expansion model and a spatial-demographic expansion model. Statistically significant differences between observed and simulated expected distributions were evaluated with the sum of the square deviations (SSD) and Harpending’s raggedness index (hg) (
This dataset of 196 mtDNA COI sequences included a total of 26 unique haplotypes. All haplotypes were closely related to each other and separated by only one to four mutations from the central COI haplotype (H5; Figure
Minimum spanning networks presenting 26 haplotypes in O. barnabita. The size of each circle corresponds to its relative frequency in the total sample. The number in each circle offers a unique identifier for each haplotype (H1-H26). Haplotype samples collected from the Baltic region and Russia (BRR: Estonia, N= 1, H5; Latvia, N= 89, H5, H10-26; Russia, N= 3, H5, H8) are coloured in orange, from Central and Eastern Europe (CEE: Croatia, N= 1, H1; Germany, N= 1, H2; Hungary, N= 2, H6, H7; Slovakia, N= 1, H3; Romania, N= 1, H9) in light green and Finnish samples from the Turku region (FIN, H4: Artukainen, N= 3; Jänessaari, N= 4; Muhkuri, N= 7; Pansio, N= 1; Ruissalo, N= 81; Runeberg Park, N= 1) in dark blue, with haplotype numbers in white. Smaller black dots on lines between individual haplotypes indicate the number of mutation steps separating them.
Mitochondrial DNA CO1 sequences variation in Osmoderma barnabita. Estimates of genetic diversity amongst regions, with the following metrics identified: N= regional sample size (number of individuals), hn= number of distinct haplotypes, h= haplotype diversity, P= polymorphic sites, ī= mean pairwise genetic differences (uncorrected p distances), π= nucleotide diversity. Calculations are based on a sequence length of 759 bp.
Area | N | hn | h (mean ± s.d.) | P | ī (mean ± s.d.) | π (mean ± s.d.) |
FIN (Turku region, Finland) | 97 | 1 | 0 | 0 | 0 | 0 |
BRR (Baltic region and Russia) | 93 | 19 | 0.771 ± 0.0019 | 17 | 1.3478 ± 0.8428 | 0.0018 ± 0.0012 |
CEE (Central and Eastern Europe) | 6 | 6 | 1.000 ± 0.0093 | 10 | 3.3300 ± 1.9861 | 0.0044 ± 0.0030 |
BRR and CEE combined | 99 | 25 | 0.798 ± 0.0400 | 25 | 1.5811 ± 0.9490 | 0.0021 ± 0.0014 |
Pooled sample | 196 | 26 | 0.705 ± 0.0300 | 26 | 1.3201 ± 0.8262 | 0.0017 ± 0.0012 |
All tests applied suggested that either population expansion or pronounced selection had occurred. Values of both Tajima’s D (D=-1.9575, P=0.002) and Fu’s FS (FS=-22.2775, P>0.001) were negative and statistically significant, thus indicating either an expansion or strong selection within the overall population of O. barnabita. Population expansion was further confirmed by significant values of Ramos-Onsis’ and Rozas’ statistics (R2=0.0257, P=0.029). This analysis of mismatch distributions revealed significant Harpending’s raggedness (hg=0.0275, P=0.025), again implying that the null hypothesis of constant population size can be rejected. Turning to the two models of sudden demographic expansion versus spatial expansion model, neither could be rejected (SDD=0.0011, P=0.770; hg=0.02747, P=0.79; SDD=0.0006, P=0.820; hg=0.02747, P=0.90). Thus, the patterns seem compatible with either model.
The current distribution of haplotype diversity in O. barnabita seems consistent with a recent expansion through Eastern Europe. As a result of these historic processes, haplotype diversity decreased from the South northwards to a single haplotype present in the northernmost population. Distinct haplotype clades were found within different parts of Europe, suggesting strong phylogeographic structuring amongst regions. Each of these findings has implications for the conservation and management of this flagship species, as will be further discussed below.
The current distribution of mtDNA haplotypes in O. barnabita seems highly indicative of demographic expansion. Overall, the haplotype network showed a star-shaped topology as characteristic of population expansion after a bottleneck, wherein newer mutations form groups of (mostly) lower-frequency haplotypes budding from a central haplotype (Figure
Given the geological history of Europe (
Given the imprints of post-glacial history described above, the distribution of mtDNA variation within the current range of O. barnabita is characterised by two patterns: distinct differences in the haplotype composition of different regions and a marked decrease of genetic diversity towards the North. Both patterns attest to the fact that, following the colonisation of regions, later gene flow may have been much too weak to homogenise genetic composition.
In terms of genetic diversity, all metrics of diversity decreased northwards. The highest levels of mtDNA COI diversity were encountered in Central and Eastern Europe (Figure
Beetles in the genus Osmoderma specialise in old deciduous trees (
From an applied perspective, two key implications of the reported patterns for the conservation and management of O. barnabita have been proposed. First, there might be a need to manage some isolated populations as independent genetic units in different parts of the species range, as they may be on different demographic and evolutionary trajectories. Second, the solitary northernmost population seems genetically impoverished, suggesting a possible risk of limited evolutionary potential.
With regard to local management units, it has been suggested that regionally adapted small populations are sensitive to changes in the environment (
When it comes to the genetic diversity of the northernmost population, the current low level of diversity suggests that increased attention should be given to genetic aspects in managing this unit. Persistent isolation, lack of gene flow, increased rate of inbreeding and influence of genetic drift may result in detrimental genetic changes which can elevate the regional extinction risk (
What creates a particular challenge to O. barnabita is the combination of longer-term, climatically-driven forces with current anthropogenic impact on the environment. The former process has eroded diversity over time, during the expansion phase and the latter is now causing additional isolation for the remaining populations: given its specialisation for old deciduous trees, the Osmoderma species complex is currently faced with a highly fragmented landscape all over its European range (cf.
Importantly, the situation of O. barnabita is likely shared by many saproxylic species associated with scarce, diminishing and fragmented habitats (
We thank Niklas Wahlberg and Meri Lindqvist for organising research in the Center of Evolutionary Applications, University of Turku, Finland. Financial support by the Societas Pro Fauna et Flora Fennica is gratefully acknowledged. Jolanta Bara coordinated and organised studies within the Latvian European Union LIFE+ programme project EREMITA MEADOWS, LIFE09/NAT/LV/000240. The following personnel at Natural History Museums and entomologists over Europe kindly provided sample specimens: Ilmar Süda (Estonia), Ottó Merkl (Hungary), Dmitry Telnov (Latvia), Arvids Barsevskis (Latvia), Vytautas Tamutis (Lithuania), Petru V. Istrate (Romania) and Andrey Frolov (Russia). We are grateful for laboratory work by Katja Salminen from the Center of Evolutionary Applications, University of Turku, Finland. We thank the subject editor and reviewers for their constructive comments and evalution of our manuscript. Legal permissions for this project were granted by city of Turku and the Centre of Economic Development, Transport and the Environment with diar.nr VARELY/919/07.01/2010, VARELY403/07.01/2011 and VARELY/52/07.01/2012.
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