Skip to main content
UKPMC Funders Author Manuscripts logoLink to UKPMC Funders Author Manuscripts
. Author manuscript; available in PMC: 2015 Mar 23.
Published in final edited form as: Arthropod Syst Phylogeny. 2014 Dec 19;72(3):309–329.

Cryptic diversity of caddisflies in the Balkans: the curious case of Ecclisopteryx species (Trichoptera: Limnephilidae)

Ana Previšić 1,*,#, Wolfram Graf 2,#, Simon Vitecek 3,#, Mladen Kučinić 1, Miklós Bálint 4, Lujza Keresztes 5, Steffen U Pauls 4, Johann Waringer 3
PMCID: PMC4370265  EMSID: EMS62607  PMID: 25810791

Abstract

Adults and larvae of two new cryptic, endemic caddisflies, Ecclisopteryx keroveci sp.n. and Ecclisopteryx ivkae sp.n., are described and illustrated from the Western Balkans. Phylogenetic analysis (Bayesian MCMCMC) and association of different life history stages in both cryptic species were achieved through comparison of morphological characters and mitochondrial (mtCOI and mtLSU) and nuclear (nuWG) gene sequence data. The new species form a sister clade to the widely distributed E. dalecarlica and E. guttulata, with which they were formerly misidentified. Adults differ from each other and other species in the genus by the uniquely shaped inferior appendages in males and segment X in females. The larvae differ from each other and their congeners in the shape of the pronotum, and presence and constitution of additional spines on the parietalia. Larvae of both species are grazers and prefer stony substrate. Ecclisopteryx keroveci sp.n. has a wide distribution in the Western Balkans, while E. ivkae sp.n. is endemic to Dalmatia. Our findings demonstrate the significance of the Western Balkans as a freshwater biodiversity hotspot, and accentuate the importance of research focused on freshwater biodiversity and biogeography in southern Europe.

Keywords: Biodiversity, Drusinae, larval morphology, adult morphology, phylogeny

1. Introduction

Cryptic species are typically defined as two or more distinct species that are classified as a single nominal species, mostly due to seemingly identical morphology (Bickford et al. 2007). A broader definition describes cryptic species as “those that cannot be identified by conventional means” (Ross 1974). “Conventional means” have changed historically, and numerous methods examining ecology, behaviour and genetics have been used to discover cryptic species (e.g. recognition of distinctive mating signals in various animals; review in Howard & Berlocher 1998, variability in allozyme markers; review in Avise 2004, etc.). However, the discovery of cryptic species has increased in recent years in different taxa, habitats, and regions, facilitated by the use of DNA barcoding among other methods (e.g. Pfenninger & Schwenk 2007; Zakšek et al. 2009; Pauls et al. 2010; Jackson et al. 2014; Weiss et al. 2014). Expectably, high cryptic diversity occurs in poorly surveyed and geographically isolated regions, such as the Balkan Peninsula (e.g. Francuski et al. 2011; Klobučar et al. 2013; Tsuomani et al. 2013). In fact, many cryptic species have been discovered recently in different freshwater taxa in the Balkans, including fishes (Tsuomani et al. 2013), crayfishes (Klobučar et al. 2013), amphipods (Weiss et al. 2014), and caddisflies (Oláh et al. 2012).

Within Europe, highest species diversity and endemism of Trichoptera (caddisflies) fauna are recorded in ecoregions (sensu Illies 1978) covering diverse mountain areas (e.g. Iberic-Macaronesian Region [ER1], Italy, Corsica and Malta [ER3], Hellenic Western Balkan [ER6], The Carpathians [ER10], Alps [ER4] etc.; Graf et al. 2008; Graf & Schmidt-Kloiber 2011). In particular, high numbers of endemic species are common in cold adapted montane groups, such as Drusinae (Limnephilidae) (Malicky 2005; Graf et al. 2008; Oláh 2010, 2011; Kučinić et al. 2011). Considering the remarkable distribution patterns of Drusinae (Graf et al. 2008) and their complex evolutionary history (Pauls et al. 2006; Previšić et al. 2009, 2014), more endemics and cryptic species are likely to be discovered, particularly in poorly explored areas, such as the Balkans.

The subfamily Drusinae comprises eight genera, including Ecclisopteryx Kolenati, 1848, with five species (Schmid 1956; Pauls et al. 2008). The genus is restricted to Europe. Three species have relatively wide and partially overlapping ranges: Ecclisopteryx dalecarlica Kolenati, 1848, Ecclisopteryx guttulata (Pictet, 1834) and Ecclisopteryx madida (McLachlan, 1867) (Graf et al. 2008; Graf & Schmidt-Kloiber 2011; Fig. 1A). Ecclisopteryx dalecarlica was previously reported from throughout the Western Balkans (e.g., Slovenia: Urbanič 2004; Croatia: Previšić & Popijač 2010; Vučković 2011; Vučković et al. 2011; Bosnia and Herzegovina: Stanić-Koštroman 2009; Kosovo: Ibrahimi 2011). In older literature, however, E. guttulata was listed from only part of the Western Balkan region (e.g., Bosnia: Radovanović 1935; Marinković-Gospodnetić 1970).

Fig. 1.

Fig. 1

Distribution of Ecclisopteryx species; A: widespread and B: endemic species (based on data from the Distribution Atlas of European Trichoptera [DAET; the BioFresh EU project–Biodiversity of Freshwater Ecosystems: Status, Trends, Pressures and Conservation Priorities]).

The remaining two Ecclisopteryx species are endemic to the Karawanken and Julian Alps (Ecclisopteryx asterix Malicky, 1979) and the Lessinian Alps (Ecclisopteryx malickyi Moretti, 1991) (Graf et al. 2008, 2011; Graf & Schmidt-Kloiber 2011; Fig. 1B). Monophyly of the genus Ecclisopteryx within Drusinae was rejected by a multigene phylogenetic study on the subfamily (Pauls et al. 2008). Ecclisopteryx species formed two distant lineages consisting of closely related species (E. madida + E. guttulata + E. dalecarlica and E. malickyi + E. asterix) that were corroborated by larval morphology and geographic distribution (Pauls et al. 2008; Graf et al. 2011).

Ecclisopteryx specimens similar to E. dalecarlica were collected in eastern Bosnia and Herzegovina and Dalmatia (southern Croatia). Comparison of morphological characters and molecular genetic sequence data [mitochondrial cytochrome oxidase c subunit I (mtCOI) and ribosomal large subunit (mtLSU = 16S) and nuclear wingless (nuWG)] with Ecclisopteryx specimens from other parts of the Western Balkan region and central Europe enabled us to distinguish two new Ecclisopteryx species that were previously overlooked and/or misidentified. Thus, in the current paper we describe the morphological features of males and females as well as the larvae of two new species. We also summarise the most important morphological characteristics enabling their identification and successful separation from each other and the other Drusinae. Moreover, we define distribution ranges of these cryptic species in the Western Balkans and discuss distribution patterns of the more widespread E. dalecarlica and E. guttulata.

2. Material and methods

2.1. Material

Specimens of Ecclisopteryx keroveci sp.n. were collected at the mouth of the Jabučica River where it joins the Sutjeska River (Table 1). Adults were collected using a UV light trap and larvae were collected by handpicking. Adults of Ecclisopteryx ivkae sp.n. were collected in the Glavaš spring and 2 sites in the upper reach of the Cetina River using a sweeping net (Table 1). Larvae were collected in the Glavaš spring by handpicking.

Table 1.

Information on specimens used in this study.

Locality (country, name) Longitude dec. Latitude dec. Altitude (m) No of specimens and stage/sex Specimen Code GenBank Accession Nos Collector Publication
Morphology Molecular genetic analyses mtCOI nuWG mtLSU
Ecdisopteryx dalecarlica Kolenati, 1848
AT, Bruck/Lafnitz N 47.4396 E 15.9138 560 1 IM/M Graf this study
AT, Ritterkamp, Kamp Aqem N 48.52887 E 15.10722 581 4 Lv Graf this study
SK, Vysoké Tatry (high Tatra Mts.), Podbanské, Béla river N 49.14017 E 19.90247 934 5 IM (3M + 2F) Graf this study
D, Spessart, Jossa below Sahlensee N 50.218548 E 9.484726 290 Lv ED001 EU215112 EU215165 EU215218 Lohse Pauls et al. 2008
D, Spessart, Jossa below Sahlensee N 50.218548 E 9.484726 290 Lv ED002 EU215113 EU215166 EU215219 Lohse Pauls et al. 2008
N, Hedmark, Folldal, Streitlie N 62.09520 E 9.96412 804 2 IM (1M + 1F) IM/M fEda0801M KM001830 KM001819 KM001825 Andersen this study
N, Hedmark, Folldal, Streitlie N 62.09520 E 9.96412 804 IM/F fEda0802F KM001829 KM001820 KM001826 Andersen this study
RO, Ţarcu Mts., Poiana Mărului N 45.403056 E 22.540556 638 IM/F Dsp023 EU215106 EU215159 EU215212 Balint Pauls et al. 2008
RO, Ţarcu Mts., Poiana Mărului N 45.403056 E 22.540556 638 IM/F Dsp031 EU215107 EU215160 EU215213 Balint Pauls et al. 2008
RO, Carlibaba, Tibau Valley N 47.464228 E 24.842512 980 IM/F IM/F fEda0701F KM001831 KM001818 KM001824 Neu this study
BG, Rhodope Mts., stream close to Teshel, Devin N 41.666389 E 24.365556 870 IM/F IM/F fEda0901F KM001828 KM001818 KM001827 Neu this study
RO, Făgăra Mts., Bâlea Valley N 45.665299 E 24.554063 800 IM/F fEda0601F Balint, Theissinger & Taubmann this study
RO, Fǎgǎra Mts., Bâlea Valley N 45.665299 E 24.554063 800 IM/F fEda0602F this study
RO, Sibiului Mts (Cindrel), Râu Sadu N 45.624 E 24.033 770 IM/M fEda0401M this study
RO, Sibiului Mts (Cindrel), Râu Sadu N 45.624 E 24.033 770 IM/F fEda0402F this study
RO, Muntii Ciucas, Sacele, stream close to Babarunca N 45.513889 E 25.848333 960 IM/M IM/M fEda0501M KM001833 KM001822 Neu this study
RO, Muntii Ciucas, Sacele, stream close to Babarunca N 45.513889 E 25.848333 960 IM/F IM/F fEda0502F KM001832 KM001823 Neu this study
Ecdisopteryx ivkae Previšić, Graf & Vitecek, sp.n.
HR, Cetina River, Crveni most N 43.960347 E 16.429489 370 12 IM (5M + 7F) IM/M fEda0101M KM001813 KM001799 KM001806 Previšić this study
HR, Cetina River, Crveni most N 43.960347 E 16.429489 370 IM/M fEda0102M KM001815 KM001801 KM001808 Previšić this study
HR, Cetina River, Crveni most N 43.960347 E 16.429489 370 IM/F fEdaO101F KM001812 KM001798 KM001805 Previšić this study
HR, Cetina River, Glavaš spring (LT) N 43.976697 E 16.430150 386 12 IM (6M + 6F) IM/F fEda0102F KM001814 KM001800 KM001807 Previšić this study
HR, Cetina River, Glavaš spring (LT) N 43.976697 E 16.430150 386 8 Lv Lv fDsp3301L KM001811 KM001797 KM001804 Kučinić & Previšić this study
HR, Cetina River, Glavaš spring (LT) N 43.976697 E 16.430150 386 Lv fEda1201L KM001816 KM001802 KM001809 this study
HR, Cetina River, Glavaš spring (LT) N 43.976697 E 16.430150 386 Lv fEda1202L KM001817 KM001803 KM001810 this study
HR, Cetina River, Vinalić N 43.936253 E 16.443441 375 1 IM/M Previšić this study
Ecclisopteryx keroveci Previšić, Graf & Vitecek, sp.n.
*BIH, Pazarić, SW of Sarajevo, valley of Krupa River N 43.786 E 18.166 630 1 IM/M Winneguth this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 40 IM (20M + 20F) IM/M fDs30101M KM001785 KM001761 KM001773 Ivković, Mihaljević, Miliša & Previšić this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 IM/M fDs30102M KM001786 KM001762 KM001774 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 IM/M fDs30103M KM001787 KM001763 KM001775 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 IM/M fDs30105M KM001788 KM001764 KM001776 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 IM/F fDs30106F KM001789 KM001765 KM001777 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 IM/F fDs30109F KM001790 KM001766 KM001778 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 IM/M fDs30113M KM001851 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 IM/M fDs30114M KM001852 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 IM/F fDs30115F KM001853 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 IM/F fDs30116F KM001854 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 10 Lv Lv E1JAL1 KM001847 KM001836 KM001842 Graf & Previšić this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 Lv E1JAL2 KM001848 KM001837 KM001843 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 Lv E2JAL1 KM001849 KM001838 KM001844 this study
BIH, Sutjeska NP, mouth of the Jabučica River (LT) N 43.29022 E 18.61733 765 Lv E2JAL2 KM001850 KM001839 KM001845 this study
BIH, Željeznica River, upper reach N 43.898666 E 17.952901 650 2 IM/M Stanić-Koštroman Stanić-Koštroman 2009
HR, Čabranka, spring reach N 45.60126 E 14.64043 589 4 IM (3M + 1F); 2 Lv IM/M EdIM1 FJ002686 FJ002818 Bokan, Kučinić, Popijač & Previšić Previšić et al. 2009; this study
Ecclisopteryx keroveci Previšić, Graf & Vitecek, sp.n.
HR, Kupa, bridge before Čabranka mouth N 45.524417 E 14.700383 292 2 IM (1M + 1F) Popijač Previšić & Popijač 2010
HR, Velika Belica, bridge at Kuželj N 45.475514 E 14.805144 242 1 IM/M fEda1001M KM001794 KM001770 KM001782 Popijač Previšić & Popijač 2010
KS, Pejë, Lumbardhi and Pejës rivers N 42.66128 E 20.25958 587 2 IM (1M + 1F) Ibrahimi Ibrahimi 2011
MK, Radika river, Monastery St. Jovan Bigorski NE of Debar N 41.623611 E 20.606111 694 2 IM/M Chvojka this study
MN, Brodavac, right tributary of Peručica N 42.68587 E 19.73636 960 2 IM (1M + 1F) IM/M fEda0201M KM001791 KM001767 KM001779 Miliša this study
MN, Brodavac, right tributary of Peručica N 42.68587 E 19.73636 960 IM/F fEda0202F KM001792 KM001768 KM001780 Miliša this study
MN, Grncar, Gusinje N 42.565944 E 19.833389 922 2 IM (1M + 1F) IM/F fEda1101F KM001795 KM001771 KM001783 Graf this study
MN, Grncar, Gusinje N 42.565944 E 19.833389 922 IM/M fEns0101M KM001796 KM001772 KM001784 Graf this study
MN, Peručica N 42.69472 E 19.75661 884 5 IM (4M + 1F) IM/M fEda0301 M KM001793 KM001769 KM001781 Previšić this study
Ecclisopteryx asterix Malicky, 1979
AT, Soboth, Krumbach tributary N 46.716667 E 15.066667 1130 Lv EastDDest002 EU215111 EU215164 EU215217 Graf & Pauls Pauls et al. 2008
AT, Karawanken, Babniakgraben N 46.5201 E 14.2345 683 Lv East003 EU215110 EU215163 EU215216 Graf Pauls et al. 2008
SLO, Julian Alps, Radovna stream N 46.4303 E 13.963 717 4 IM (3M + 1F) IM/M fEas0101M KM001760 KM001757 KM001754 Olah this study
SLO, Julian Alps, Radovna stream N 46.4303 E 13.963 717 IM/M fEas0102M KM001758 KM001755 Olah this study
SLO, Julian Alps, Radovna stream N 46.4303 E 13.963 717 IM/M fEas0103M KM001759 KM001756 Olah this study
Ecclisopteryx guttulata (Pictet, 1834)
AT, Ybbs at Lunz N 47.856 E 15.023 600 12 Lv Graf this study
AT, Jogland, Lafnitz tributary N 47.43 E 15.48 1170 IM/M Egut009 EU215114 EU215167 EU215220 Graf & Pauls Pauls et al. 2008
ES, Pyrenees, Val d’Aran, Salardu N 42.706361 E 0.896944 1220 4 IM (3M + 1F) IM/M fEgu0101M KM001750 KM001742 KM001746 Graf this study
ES, Pyrenees, Val d’Aran, Salardu N 42.706361 E 0.896944 1220 IM/F fEgu0102F KM001751 KM001743 KM001747 Graf this study
ES, Pyrenees, Val d’Aran, Salardu N 42.706361 E 0.896944 1220 IM/M fEgu0103M KM001752 KM001744 KM001748 Graf this study
ES, Pyrenees, Val d’Aran, Salardu N 42.706361 E 0.896944 1220 IM/M fEgu0104M KM001753 KM001745 KM001749 Graf this study
Ecclisopteryx madida (McLachlan, 1867)
RO, Bucegi Mts., Valea Dobresti, Cariera Lespezi, Pietrele Albe N 45.287451 E 25.405600 889 IM/M EM001 EU215115 EU215168 EU215221 Pauls & Ujvarosi Pauls et al. 2008
SVK, Hronec N 48.8 E 19.6 550 Lv EM002 KM001727 KM001733 Graf this study
SVK, Hronec N 48.8 E 19.6 550 Lv EM003 KM001728 KM001734 Graf this study
AT, Nockberge, St. Oswald stream N 46.864432 E 13.787671 1570 IM/M EM004 EU215116 KM001729 EU215222 Graf Pauls et al. 2008
AT, Nockberge, St. Oswald stream N 46.864432 E 13.787671 1570 IM/M EM005 KM001730 KM001735 Graf this study
AT, Nockberge, St. Oswald stream N 46.864432 E 13.787671 1570 IM/M EM006 KM001739 EU215169 KM001736 Graf Pauls et al. 2009
Ecclisopteryx madida (McLachlan, 1867)
AT, Bruck/Lafnitz N 47.4396 E 15.9138 560 IM/M fEma0101M KM001740 KM001731 KM001737 Graf this study
AT, Bruck/Lafnitz N 47.4396 E 15.9138 560 IM/M fEma0102M KM001741 KM001732 KM001738 Graf this study
Ecclisopteryx malickyi Moretti, 1991
IT, springbrook near Camposilvano SE of Rovereto, Monti Lessini, Trentino N 45.748231 E 11.151095 1171 IM/F Emal001 EU215223 EU215170 EU2015117 Graf Pauls et al. 2008
IT, springbrook near Camposilvano SE of Rovereto, Monti Lessini, Trentino N 45.748231 E 11.151095 1171 Lv Emal002 KM001726 KM001725 Graf this study
** Drusus discolor (Rambur, 1842)
HR, Čabranka, spring reach N 45.60126 E 14.64043 589 IM/M DdCAIM1 KC881331 KM001835 KM001841 Sivec Previšić et al. 2014, this study
** Allogamus uncatus (Brauer, 1857)
AT, Gampadelsbach, Vorarlberg N 47.03638 E 9.88972 1555 IM/M AUn003 KM001846 KM001834 KM001840 Graf this study
*

Historical collection, geographic reference is provided for the closest town, Pazarić, as the exact location is not known;

**

Outgroup taxa in phylogenetic analysis.

LT = locus typicus, IM = imagines, adults, M = male, F = female, Lv = larvae.

Collected specimens were stored in 70 and 96% EtOH for morphological and molecular analysis, respectively. All collected specimens are deposited in the Faculty of Science, University of Zagreb (Croatia), the Institute of Hydrobiology and Aquatic Ecosystem Management, University of Natural Resources and Applied Life Sciences, Vienna (Austria), and the Biology Centre, Oberösterreichisches Landesmuseum, Linz (Austria). Terminology for larval morphological features follows Wiggins (1998) and Waringer & Graf (2011). Nomenclature of primary setae and setal areas follows Wiggins (1998). Nomenclature of male terminalia follows Nielsen (1957).

To delineate the two new species from remaining Ecclisopteryx species and maximise geographic coverage, we compared Ecclisopteryx specimens from the entire Western Balkan region in the current study (Table 1). For both morphological characters and mtCOI, mtLSU and nuWG sequence data, we also compared E. dalecarlica specimens from Northern, Central and Eastern Europe and E. guttulata from Central Europe (Table 1). Sequence data were taken from Pauls et al. (2008) and Previšić et al. (2014); additional specimens used for comparative morphology were provided by the many colleagues listed in Table 1 and the Acknowledgements.

Adult male and female of E. dalecarlica were re-drawn based on material collected in Norway (Table 1). Illustrations were prepared as described by Thomson & Holzenthal (2010). Briefly, pencil drawings were produced using a camera lucida mounted on a compound microscope, and digitally edited and inked.

2.2. DNA extraction and PCR amplification

DNA extraction and amplification were performed as outlined by Pauls et al. (2008) and Previšić et al. (2009) for the 541-bp-long fragment of the mitochondrial cytochrome oxidase c subunit I (mtCOI) using primers S20 and Jerry (Simon et al. 1994; Pauls et al. 2006), a 346-bp-long fragment of the nuclear wingless gene (nuWG) using primers WGbDrrev (5′-ACCCTCTCCCGCARCACATTGAG) and WgbDrfwd 5′-CTTGCTGGATGCGTCTGCC), and a 362-bp-long fragment of the mitochondrial large ribosomal subunit gene (mtLSU) using primers LeptoF and LeptoR (Malm & Johanson 2008). Sequences were edited manually using the program Geneious R7 (Biomatters Ltd., New Zealand) and aligned using MAFFT v.7 (Katoh & Standley 2013). Sequences were deposited in GenBank under accession nos: KM001724 – KM001854. In addition, published sequences of all Ecclisopteryx species (Pauls et al. 2008; Table 1) were included in the alignment and intra- and interspecific uncorrected p-distances were calculated in Mega 4.0.1 (Tamura et al. 2007) based on the 541-bp-long fragment of the mtCOI. For p-distances a colour heat map was drawn using the package ‘pheatmap’ in R (version 3.0.2, R Core Team 2013).

2.3. Phylogenetic reconstruction

To examine Ecclisopteryx species delineation and association of specimens from the Western Balkans, we inferred a phylogeny using all available mtCOI, mtLSU and nuWG sequences of Ecclisopteryx species (Table 1). As outgroups taxa we used Drusus discolor (Limnephilidae: Drusinae) andAllogamus uncatus (Limenphilidae: Stenophylacini) (Table 1). According to the Akaike Information Criterion (AIC) test implemented in MrModeltest 2.2 (Nylander 2004) the following models of DNA substitution were identified as best-fit for particular data sets: mtCOI: Hasegawa – Kishino – Yano + Invariant + Gamma (HKY + I + G), mtLSU: General time reversible + Gamma (GTR+G), and nuWG; Hasegawa – Kishino – Yano + Gamma (HKY+G). The phylogeny was estimated using a Bayesian Metropolis-coupled Monte Carlo Markov Chain (MCMCMC) method with the program MrBayes 3.2. (Ronquist & Huelsenbeck 2003) using concatenated sequences of the three genes. The matrix contained 6.5% missing data with 9 individuals missing one and 4 individuals missing two gene regions, respectively (Table 1). Two parallel runs were performed with four chains each (10 million generations, sampling every 1000th generation). The likelihood scores were plotted against generation time using Tracer 1.4 (Drummond & Rambaut 2007) to determine the number of generations needed to reach the stationary phase. Consequently, the initial 3000 trees were discarded as burn-in and the remaining trees used to create a 50% majority rule consensus tree.

3. Results

3.1. Ecclisopteryx species delimitation

In a B/MCMCMC phylogeny based on concatenated partial sequences of mtCOI, mtLSU and nuWG, with the exception of E. ivkae sp.n., monophyly of each putative Ecclisopteryx species was highly supported (pp ≥ 0.95; Fig. 2). Ecclisopteryx dalecarlica specimens from different parts of its range (i.e., Norway, Germany, Bulgaria and Romania, Table 1) formed a highly supported clade, as did E. guttulata specimens (pp ≥ 0.98; Fig. 2). All specimens of E. keroveci sp.n. including the Ecclisopteryx larvae collected from the Jabučica River also formed a highly supported monophyletic clade (pp = 0.99; Fig. 2). Ecclisopteryx keroveci sp.n. and E. ivkae sp.n. formed a highly supported monophyletic clade (pp = 1; Fig. 2); however, E. ivkae sp.n. haplotypes occured in a basal polytomy, thus this species was not recovered as monophyletic (Fig. 2). Ecclisopteryx dalecarlica + E. guttulata were the sister clade to E. keroveci sp.n. + E. ivkae sp.n., and this relationship was also highly supported (p = 0.99; Fig. 2).

Fig. 2.

Fig. 2

Rooted Bayesian phylogenetic tree of seven Ecclisopteryx species based on the partial mitochondrial (mtCOI, mtLSU) and nuclear (nuWG) gene sequences. Drusus discolor and Allogamus uncatus were used as outgroup taxa. Bold lines bear nodes with posterior probabilities ≥ 0.95.

Mitochondrial COI haplotypes (fragment length 440 bp) of E. keroveci sp.n. adults and larvae sampled at the mouth of the Jabučica River were either identical or differed at a maximum of 5 nucleotide positions ( = 1.1%). Overall, mtCOI haplotypes of E. keroveci sp.n. differed across the whole region by at most 8 nucleotide positions (21 specimens); hence, intraspecific uncorrected p-distances ranged from 0 – 1.8% (Fig. 3). A similar case was observed in E. ivkae sp.n., as mtCOI haplotypes from the two sequenced sampling sites (both at the Cetina River) were found to differ by maximally 4 nucleotide positions (7 specimens), with intraspecific uncorrected p-distance ranging from 0 – 0.9% (Fig. 3). Overall, interspecific uncorrected p-distances of mtCOI haplotypes ranged from 1.6 – 2.7% between E. keroveci sp.n. and E. ivkae sp.n., 8.2 – 10.5% between E. dalecarlica and E. keroveci, and 7.7 – 9.5% between E. dalecarlica and E. ivkae sp.n. (Fig. 3). Uncorrected p-distances of the same mtCOI fragment between the other Ecclisopteryx species ranged from 6.1 – 13.2% (Fig. 3).

Fig. 3.

Fig. 3

Colour heat map showing inter- and intraspecific uncorrected p-distances of the partial mitochondrial COI gene sequence (440 bp) between seven Ecclisopteryx species. Intraspecific p-distances are outlined by the black line. For detailed information on haplotypes see Table 1.

3.2. Description of Ecclisopteryx keroveci Previšić, Graf & Vitecek sp.n.

Adults

General appearance: light brown; sternites and tergites brown; cephalic, thoracic and abdominal setal areas pale, yellowish; body setation light brown; legs light brown; haustellum and intersegmental teguments pale, whitish. Male maxillary palps 3-segmented. Spur formula (male and female): 1-2-3. Forewing length: male 9.8 – 12.1 mm (N = 20), female 10 – 12.5 mm (N = 20).

Male terminalia (Fig. 4A–E)
Fig. 4.

Fig. 4

Ecclisopteryx keroveci sp.n.; male genitalia, A: lateral view, B: ventral view, C: aedeagus and parameres, D: dorsal view and E: caudal view; female genitalia, F: lateral view, G: ventral view, H: dorsal view and variability in female genitalia, dorsal view and I: caudal view. — Abbreviations: tia=tip of inferior appendages, ia=inferior appendages, tsX=tip of segment X, sp=supragenital plate, lsp=lobes of supragenital plate.

Tergite VIII brown with lighter areas around alveoli and somewhat darker stripe medially lacking setae; setation concentrated posteriorly, around spinate area, anterior part of tergite VIII with few setae. Spinate area mushroom-shaped in dorsal view and flanked by membraneous areas.

Segment IX rhombus-shaped in lateral view, transversely dilated: in ventral view distance from lateral most point of segment IX to straight anteroposterior line originating from lateral most point of inferior appendages is approximately 10% of total width of segment IX on each side.

Superior appendages (cerci sensu Snodgrass 1935) in lateral view round, simple, without further modifications. Intermediate appendages (paraprocts sensu Snodgrass 1935) reduced as typical for genus, membraneous dorsal and ventral protuberances rounded. Inferior appendages (gonopods sensu Snodgrass 1935) in lateral view bipartite with well sclerotized dorsal part and less sclerotized, seemingly membranous, ventral part; dorsal part prolonged caudally with distinct dorsally turned tip: with broad and shallow lateral concavity, somewhat bifurcated with 2 rounded tips of unequal length (dorsal one shorter than ventral one), in dorsal view triangular and slender with tips separated by small indentation, caudal parts and median margins strongly sclerotized and covered with spines; setation of appendices inferiores concentrated laterally on dorsal part, forming setal brush.

Aedeagus slender with distinct terminal protuberance (in lateral view only) and parameres of equal length. Parameres fused at their bases, with 2 major concentrations of thorn-like spines on dorsal surface; several well developed distal thorn-like spines and medial group of smaller thorn-like spines, the latter with bulbous bases.

Female terminalia (Fig. 4F – I)

Lateral lobe of segment IX membraneous, triangular in lateral view with dorsal sclerotized setose part, the latter evenly rounded in dorsal and ventral view. Segment X wider proximally than distally, in dorsal view with 2 lateral lobes and median triangular excision of varying shape (Fig. 4H); lateral lobes laterally slightly concave, tips sharp and distinct in dorsal and ventral views, curved somewhat dorsally in lateral view; approximately as long as supragenital plate; ventrally unsclerotized. Supragenital plate in lateral view quadrangular with small dorsal process; in ventral view quadrangular; in caudal view quadrangular with 2 indistinct ventral lobes. Vulvar scale with 3 lobes in ventral view: 2 lateral lobes, roundly oval with converging tips; 1 median, well developed, about half as long as lateral lobes and of greater length than width.

Fifth instar larvae

Body length of larva 10 – 13.1 mm, head width 1.3 – 1.5 mm (N = 10). Case slightly curved, consisting of mineral particles (Fig. 7A), 10.2 – 13.7 mm long, slightly attenuating posteriorly (width at anterior opening 2.8 – 4.5 mm and at posterior opening 1.4 – 2.9 mm).

Fig. 7.

Fig. 7

Ecclisopteryx keroveci sp.n., larva; A: larva in its case, B: head and pronotum, left lateral view, C: thorax and first abdominal segment, dorsal view. Ecclisopteryx ivkae sp.n., larva; D: larva in its case, E: thorax, dorsal view and F: head and pronotum, left lateral view. Scale bar is 1 mm.

Head

Light to chestnut brown with dark muscle attachment spots, with yellowish-white rings around the eyes (Fig. 7B). 18 pairs of primary setae (# 1, 4, 10, 11 white; 13, 16 light brown, rest dark brown) and additional spines on parietalia present (i.e. between eyes and anterior head margin; N = 12 – 20, light brown, 100 – 300 μm length) (Figs. 7B, 8A). Frontoclypeus bell-shaped; carinae bearing antennae; ventral apotome bell-shaped, yellowish-brown. Mandibles typical for grazers, lacking teeth.

Fig. 8.

Fig. 8

Ecclisopteryx keroveci sp.n., larva; head and pronotum in A: frontal and B: lateral view. Ecclisopteryx ivkae sp.n., larva; head and pronotum in C: frontal and D: lateral view. Ecclisopteryx dalecarlica Kolenati, larva; head and pronotum in E: frontal and F: lateral view. Ecclisopteryx guttulata (Pictet), larva; head and pronotum in G: frontal and H: lateral view. I: Ecclisopteryx madida (McLachlan), larva; head and pronotum in frontal view. Arrows: median notch on pronotum.

Thorax

Pronotum light to chestnut brown, with dark muscle attachment spots, posterior margin thickened and darkly striped (Fig. 7B,C). Dorsal profile in lateral view lacking distinct ridge, in dorsal and lateral view medially with a delicate step (Figs. 7B, 8B). Two setal rows along anterior border of pronotum: (1) dense fringe of short, curved, fine, yellow setae; (2) widely-spaced, continuous row of long, straight, dark setae meeting at anterior pronotal midline; in total, 110 – 130 dark setae of varying lengths (100 – 300 μm) distributed over each pronotal half. Small, white recumbent setae present on pronotal surface. Prosternal horn present.

Mesonotal sclerites light brown, with dark muscle attachment spots and lateral and posterior margins darkly sclerotised (Fig. 7C). Anterior mesonotal setal group (sa1) consisting of 7 – 13 setae; posterior group, sa2 (26 – 41 setae) and lateral group, sa3 (30 – 40 setae) connected, not clearly separated.

Metanotum divided into 3 pairs of light brown sclerites. Anteromedian sclerites (sa1) ellipsoid, distance between them smaller than their length (Fig. 7C); 19 – 30 setae per sclerite. Posteromedian sclerites small (sa2), with 16 – 21 setae; lateral sclerites (sa3) with 30 – 40 setae. A row of setae present between posteromedian sclerites (sa2); a small setal group of 20 – 30 setae present between each lateral (sa3) and posteromedian sclerite.

Legs light brown to yellowish with numerous setae on coxae, trochanters and femora; tibiae and tarsi bearing less setae. Foreleg coxa, femur and tibia each wider than those of mid- and hind legs. Whole dorsal and ventral margins of all coxae and femora covered with setae. Forefemora each with 3 – 6 yellow and 2 – 5 dark setae on ventral-edge, midfemora each with 6 – 13 dark and hind femora each with 6 – 10 dark setae on ventral edge. Additional setae present at both anterior and posterior faces of all femora; ventral trochanteral brush present at distal section of foretrochanters. Setae present at ventral margin (proximal and distal sections) of all trochanters. Dorsal setae only at distal third of mid- and hind tibiae.

Abdomen

First abdominal segment with 1 dorsal and 2 lateral fleshy protuberances. Setal areas sa 1, sa2 and sa3 fused, resulting in continuous transverse row of setae anterior to the dorsal protuberance, reaching to the dorsal section of each lateral protuberance. Setal group posterior to dorsal protuberance lacking (Fig. 7C). Lateral protuberances lacking posterior sclerites; in front of each lateral protuberance lies continuous band of anterolateral setae, linking with each dorsal and ventral sa3 setal group. First abdominal sternum with fused setal areas sa1, sa2 and sa3, resulting in a continuous field of setae, with small sclerites at the base of individual setae.

Single filamentous gills present on segments II – VII. Dorsal pre- and post-segmental gills present on segments II – VII; ventral pre- and post-segmental gills present on segments II – VII. Lateral pre-segmental gills present on segments II and V and post-segmental gills on segments II – IV. Lateral fringe extends from anterior border of segment III to anterior border of segment VIII. Number of posterodorsal setae on segment VIII 2 – 6.

Etymology

The name of keroveci was given in honour of our colleague, Prof. Dr. Mladen Kerovec, who has enthusiastically supported our studies of Drusinae in the Balkans for many years.

Type material

Ecclisopteryx keroveci sp.n.: Holotype ♂: Bosnia and Hercegovina, mouth of Jabučica River, N 43.29022 E 18.61733, 765 m asl, 04.vii.2012, leg. Previšić A., Ivković M., Mihaljević Z., Miliša M.; deposited in the Biology Centre, Oberösterreichisches Landesmuseum, Linz, Austria. Paratypes: 30 ♂ and 49 ♀, same data; deposited in the first author’s collection at the Faculty of Science in Zagreb. 10 5th instar larvae, same location, 14.v.2008 and 02.vi.2009, leg. Previšić A., Graf W.

3.3. Description of Ecclisopteryx ivkae Previšić, Graf & Vitecek sp.n.

All morphological characters of adults and 5th-instar larvae identical to Ecclisopteryx keroveci sp.n. except:

Adults

General appearance: brown; cephalic, thoracic and abdominal setal areas pale, yellowish to light brown; body setation light brown to brown. Forewing length: male 10.4 – 12.5 mm (N=7), female 12.4 – 14.0 mm (N = 9).

Male terminalia (Fig. 5A–E)
Fig. 5.

Fig. 5

Ecclisopteryx ivkae sp.n.; male genitalia, A: lateral view, B: ventral view, C: aedeagus and parameres, D: dorsal view and E: caudal view; female genitalia, F: lateral view, G: ventral view, H: dorsal view and I: caudal view. — Abbreviations: tia=tip of inferior appendages, ia=inferior appendages, sp=supragenital plate, sX=segment X.

Tergite VIII brown, lacking a darker median stripe; setation evenly distributed over the whole surface of tergite VIII with larger setae posteriorly. Superior appendages (cerci sensu Snodgrass 1935) in lateral view somewhat elongated. Dorsal part of inferior appendages (gonopods sensu Snodgrass 1935) in lateral view not turned dorsally, with a deep and broad lateral concavity, faintly bifurcated with 2 tips of more or less equal length, in dorsal view broadly triangular with the tips separated by a distinct indentation. Parameres fused at their bases, with 3 major concentrations of thornlike spines on dorsal surface: several well developed distal thorn-like spines and medial group of smaller thornlike spines divided into 2 groups of thorn-like spines.

Female terminalia (Fig. 5F – I)

Segment X in dorsal view with 2 lateral lobes and a deep and round median excision leaving 2 distinct median protrusions in lateral, ventral and dorsal view; tips of lateral lobes rounded, not curved dorsally in lateral view, somewhat longer than the supragenital plate. Supragenital plate quadrangular in lateral and ventral view; in caudal view hourglass-shaped. Vulvar scale with 3 lobes in ventral view: 2 lateral lobes, quadrangular with converging tips; 1 median lobe, about half as long as the lateral lobes and triangular in shape.

Fifth instar larva

Body length of larva 8.0 – 9.5 mm, head width 1.5 – 1.7 mm (N = 8). Case slightly curved, consisting of mineral particles (Fig. 7D), 7.5 – 10.8 mm long, slightly attenuating (width at anterior opening 2.8 – 4.8 mm and at posterior opening 1.7 – 1.8 mm).

Head

Brown to brownish black with granular surface sculpturing. Primary setae # 1, 4, 10, 11 white; the remaining setae dark brown; 1 – 7 dark brown spines on parietalia (200 – 375 μm length) present (Figs. 7F, 8C,D).

Thorax

Pronotum brown to brownish black with granular surface sculpturing (Fig. 7E). Dorsal profile in lateral view with small but distinct ridge, in dorsal view medially with a delicate step-like structure (Figs. 7F, 8D). In total, 110 – 120 dark setae of varying lengths (100 – 300 μm) distributed over each pronotal half. Mesonotum sclerites chestnut brown, with dark muscle attachment spots and lateral and posterior margins darkly sclerotised (Fig. 7E,F). Anterior mesonotal setal group (sa1) consisting of 3 – 7 setae; posterior group, sa2 (20 – 32 setae) and lateral group, sa3 (28 – 40 setae) connected, not clearly separated. Anteromedian metanotum sclerites (sa1) quadrangular, distance between them smaller than their length (Fig. 7E); 16 – 28 setae per sclerite. Posteromedian metanotum sclerites small (sa2), with 15 – 19 setae; lateral sclerites (sa3) with 20 – 32 setae. A row of setae present between posteromedian sclerites (sa2); a small setal group of 16 – 22 setae present between each lateral (sa3) and posteromedian sclerite.

Legs chestnut brown with numerous setae on coxae, trochanters and femora; tibiae and tarsi with only small number of setae. Forefemora each with 3 – 4 yellow and 2 – 5 dark ventral-edge setae, midfemora each with 6 – 9 dark and hind femora each with 3 – 7 dark ventral edge setae. Number of posterodorsal setae on segment VIII 4 – 9.

Etymology

The name of ivkae was given in honour of Ivka Previšić, the first author’s grandmother.

Type material

Ecclisopteryx ivkae sp.n.: Holotype ♂: Cetina River, Glavaš spring N 43.976697 E 16.430150, 386 m asl, 02.vi.2011, leg. Previšić A.; deposited in the Biology Centre, Oberösterreichisches Landesmuseum, Linz, Austria. Paratypes: 4 ♂ and 2 ♀, same data; 1 ♂ and 1 ♀ 31.V.2005, leg. Previšić A.; 1 ♀ 07.vi.2007, leg. Graf W; 2 ♀ 02.vi.2012, leg. Previšić A.; deposited in the first author’s collection at the Faculty of Science in Zagreb. 8 5th instar larvae: same location, 04.x.2013 (N = 4, leg. Kučinić M.) and 07.xi.2013 (N = 4, leg. Previšić A.).

3.4. Differential diagnosis of Ecclisopteryx keroveci, E. ivkae, E. dalecarlica and other Drusinae species

Adult males

Ecclisopteryx keroveci and E. ivkae males are morphologically most similar to E. dalecarlica males, but differ distinctly in several features. They can be separated using the following key:

  • 1

    Tips of inferior appendages distinctly indented in lateral view (Fig. 6A; arrow tia), inferior appendages elongate and slender in ventral view (Fig. 6B; arrow ia): ....................................................... E. dalecarlica

  • 1′

    Tips of inferior appendages lacking a distinct indentation in lateral view, inferior appendages more or less triangular and broad in ventral view (Figs. 4A,B & 5A, B; arrows tia & ia): ........... 2, E. ivkae & E. keroveci

  • 2

    Posterior edge of tip of inferior appendages ventrally elongated and arched dorsally (Fig. 4A; arrow tia), tips in dorsal view lacking a distinct shoulder (Fig. 4D; arrow ia):...........................................E. keroveci

  • 2′

    Posterior edge of tip of inferior appendages more or less straight in lateral view, lacking a clear ventral elongation (Fig. 5A; arrow tia), tips in dorsal view with a distinct shoulder (Fig. 5D; arrow ia):..........E. ivkae

Fig. 6.

Fig. 6

Ecclisopteryx dalecarlica Kolenati, 1848; male genitalia, A: lateral view, B: ventral view, C: aedeagus and parameres, D: dorsal view and E: caudal view; female genitalia, F: lateral view, G: ventral view, H: dorsal view and I: caudal view. — Abbreviations: tia=tip of inferior appendages, ia=inferior appendages, sp=supragenital plate, tsX=tip of segment X, sX=segment X.

Adult females

Ecclisopteryx keroveci and E. ivkae females are morphologically most similar to E. dalecarlica females, but differ in several features. Species can be distinguished using the following key:

  • 1

    In lateral view, segment X with a distinct protuberance (Fig. 6F; arrow tsX) and supragenital plate with a sharp median incision (Fig. 6F; arrow sp); and in dorsal and ventral view segment X with 2 distinct median lobes, somewhat shorter than outer lobes (Fig. 6G,H; arrows sX): ............................. E. dalecarlica

  • 1′

    In lateral view, tips of segment X somewhat curved dorsadly (Fig. 4F; arrow tsX) and supragenital plate longer ventrally than dorsally (Fig. 4F; arrow sp), in caudal view with 2 distinct ventral lobes (Fig. 4I; arrow lsp):..................................................E. keroveci

  • 1”

    In lateral view, supragenital plate lacking an indentation (Fig. 5F; arrow sp); in dorsal and ventral view, segment X with distinct, round median incision, leaving 2 mediolateral lobes (Fig. 5G,H; arrows sX): ... E. ivkae

Larvae

A summary of morphological features for the identification of Limnephilidae and Drusinae larvae was given by Waringer (1985). Within the framework of the limnephilid key by Waringer & Graf (2011), E. keroveci is keyed together with E. dalecarlica and Drusus trifidus, whereas E. ivkae is keyed together with E. guttulata and E.madida.

  • (A)
    The fifth instar larva of E. keroveci can be separated from the larva of D. trifidus and E. dalecarlica using the following key:
    • 1
      Colouration of head capsule and body sclerites blackish brown; additional spines lacking on parietalia; additional spines on pronotum short and yellow; lateral fringe extending from anterior margin of abdominal segment III to first 1/3 of segment VIII: ................................................................. D. trifidus
    • 1′
      Colouration of head capsule and body sclerites yellow or brown (Figs. 7B,C, 8A,E); additional spines present on parietalia (Figs. 7B, 8A,E,F); additional spines on pronotum long and brown (Fig. 7B) or short and blackish brown (Fig. 8F); lateral fringe extending from anterior margin of abdominal segment III to end of segment VIII: ................................2, E. dalecarlica & E. keroveci
    • 2
      Colouration of head capsule and body sclerites yellow (Fig. 8E,F); additional spines on parietalia and pronotum blackish, stout and of roughly the same length (80 – 100 μm; Fig. 8E,F): ...... E. dalecarlica
    • 2′
      Colouration of head capsule and body sclerites light brown to chestnut brown (Figs. 7B, 8A); the additional spines on parietalia and pronotum light brown, pointed, varying in length (100 – 300 μm; Figs. 7B, 8A): .......................................................E. keroveci
  • (B)
    The fifth instar larva of E. ivkae can be separated from the larvae of E. guttulata and E. madida using the following key:
    • 1
      Colouration of head capsule and body sclerites brownish-red (Fig. 8G,H); pronotum with a pronounced median notch in anterior view (Fig. 8G): ...............................................................E. guttulata
    • 1′
      Colouration of head capsule and body sclerites blackish brown (Figs. 7D – F, 8C,D); pronotum without a pronounced median notch in anterior view (Fig. 8C,I): ................................2, E. ivkae & E. madida
    • 2
      Number of additional spines on each parietale is 1 – 7 (Figs. 7F, 8C,D); lateral fringe ending at the end of abdominal segment VIII:............................E. ivkae
    • 2′
      Number of additional spines on each parietale is > 20 (Fig. 8I); lateral fringe ending at the first 1/3 of abdominal segment VIII:............................ E. madida

The most important morphological features enabling separation of all Ecclisopteryx species (and D. trifidus) are summarised in Table 2 and Fig. 8. For reliable identification, distribution ranges of these species should also be kept in mind: D. trifidus does not occur in the Dinaric Western Balkan ecoregion (ER5; Graf et al. 2008; Graf & Schmidt-Kloiber 2011) (Table 2); Ecclisopteryx asterix and E. malickyi are very restricted in their distribution ranges and are not known from ecoregion ER5 (Graf et al. 2008, 2011; Graf & Schmidt-Kloiber 2011). Also, larvae of the two latter species differ from all other Ecclisopteryx species by lacking additional spines on the parietalia, and are easily differentiated from larvae of E. keroveci and E. ivkae by various features summarized in Table 2.

Table 2.

Synoptic key for the diagnosis of the larvae of the genus Ecclisopteryx and Drusus trifidus (Limnephilidae: Drusinae). Distribution of Ecclisopteryx species following Graf et al. 2008, 2011; Graf & Schmidt-Kloiber 2011, unpublished data;

Species Parietalia: presence and number of additional spines per parietale Lateral fringe extending on abdominal segments: Mesonotal sclerites, colour: Pronotum with Distribution
beginning at ending at sharp ridge (lateral view) pronounced median notch (anterior view)
E. keroveci yes (12–20) anterior margin of III end of VIII light brown to chestnut brown no (Fig. 8B) no (Fig. 8A) Western Balkan region
E. ivkae yes (1–7) anterior margin of III end of VIII brownish-black yes (Fig. 8D) no (Fig. 8C) Dalmatia
E. dalecarlica 1 yes (stout, 14–20) anterior margin of III end of VIII yellow no (Fig. 8F) no (Fig. 8E) central & northern Europe
E. guttulata yes (≥ 16) anterior margin of III first third of VIII brownish-red yes (Fig. 8H) yes (Fig. 8G) central & southern Europe
E. madida yes (> 20) anterior margin of III first third of VIII black yes no (Fig. 8I) central–eastern Europe
E. asterix no last third of III first third of VIII brownish-black no no Karawanken/Soboth
E. malickyi no last third of III first third of VIII brownish-black no no Lessinian Alps
D. trifidus no anterior margin of III first third of VIII anterior: brown to brownish-black, posterior: beige no no central & western Europe

endemicity indicated by a cross

1

also present on British Islands.

3.5. Ecology, habitat and phenology of Ecclisopteryx keroveci

Larval habitat characteristics at the type locality of E. keroveci (mouth of the Jabučica River) indicate a preference for rhithral sections of streams. The collection site is approximately 9 km downstream from the spring, where the stream is about 4 m wide and has a mean current velocity of 0.1 ms−1 in July; water temperature in July 2012 was 12.7°C (10.00 am). However, strong discharge dynamics have been observed. Substrate was mainly composed of larger fractions, i.e., megalithal (30%), macrolithal (35%) and mesolithal (25%), and rocks were substantially covered with algae. Larvae of E. keroveci were collected on the surface of algae-covered stones, which, in agreement with larval mandibular morphology, indicates that E. keroveci is a grazer (Pauls et al. 2008; Waringer et al. 2010). Adults of E. keroveci were collected in early July 2012; however data on its flight period are still incomplete.

At the mouth of the Jabučica River, E. keroveci was sympatric with the trichopterans Rhyacophila armeniaca Guerin, 1834, Rhyacophila balcanica Radovanović, 1953, Rhyacophila moscaryi Klapálek, 1894, Rhyacophila nubila (Zetterstedt, 1840), Rhyacophila obliterata McLachlan, 1863, Rhyacophila trescavicensis Botosaneanu, 1960, Rhyacophila tristis Pictet, 1834, Glossosoma conformis Neboiss, 1963, Glossosoma discophorum Klapálek, 1902, Agapetus ochripes Curtis, 1834, Synagapetus slavorum Botosaneanu, 1960, Diplectrona atra McLachlan, 1878, Hydropsyche dinarica Marinković-Gospodnetić, 1979, Hydropsyche instabilis (Curtis, 1834), Hydropsyche mostarensis Klapálek, 1898, Hydropsyche tabacarui Botosaneanu, 1960, Polycentropus excisus Klapálek, 1894, Polycentropus flavomaculatus (Pictet, 1834), Polycentropus ierapetra dirfis Malicky, 1974, Lype reducta (Hagen, 1868), Brachycentrus montanus Klapálek, 1892, Micrasema minimum McLachlan, 1876, Drusus biguttatus (Pictet, 1834), Limnephilus hirsutus (Pictet, 1834), Potamophylax luctuosus (Piller & Mitterpacher, 1783), Lepidostoma basale (Kolenati, 1848), Odontocerum albicorne (Scopoli, 1763), Beraeamyia schmidi Botosaneanu, 1960, Oecismus monedula (Hagen, 1859), Sericostoma flavicorne Schneider, 1845 and the plecopterans Perla marginata (Panzer, 1799), Perla pallida Guerin, 1838, Dinocras megacephala (Klapálek, 1907), Isoperla tripartita Illies, 1954 and Chloroperla russevi Braasch, 1969 (Marinković-Gospodnetić 1970, our data). Hence, the caddisfly community at the mouth of the Jabučica River is quite species rich (e.g. Previšić et al. 2007). The finding of Polycentropus ierapetra dirfis is particularly noteworthy, since it was previously recorded only from the Hellenic Western Balkan ecoregion (ER6; Graf et al. 2008; Graf & Schmidt-Kloiber 2011; Malicky 2004). This collection site represents the north-westernmost distribution of the species and considerably extends its range to the Dinaric Western Balkan ecoregion (ER5 sensu Illies 1978).

3.6. Ecology, habitat and phenology of Ecclisopteryx ivkae

Larval habitat characteristics at the type locality of E. ivkae (Cetina River, Glavaš spring) indicate a preference for crenal sections of streams. Larvae were collected approximately 50 m downstream of the spring. Here the stream was about 5 m wide, with a mean current velocity of 0.21 ms−1 and water temperatures ranging from 8.4 to 12.9°C throughout the year (Popijač 2007). Substrate was mainly composed of smaller fractions (microlithal and mesolithal) with some larger stones and submersed vegetation. Larvae of E. ivkae were collected on the surface of algae-covered stones, which, in concordance with larval mandibular morphology, indicates that E. ivkae is also a grazer (Pauls et al. 2008; Waringer et al. 2010). Additionally, adults were collected at the site 2.4 km downstream, indicating a possible preference for rhithral sections as well. Adults were generally collected in late May and early June (in 2005, 2007 and 2012).

At Glavaš spring, E. ivkae was sympatric with the trichopterans Rhyacophila balcanica Radovanović, 1953, Rhyacophila fasciata Hagen, 1859, Glossosoma discophorum Klapálek, 1902, Hydropsyche sp., Tinodes dives (Pictet, 1834), Annitella apfelbecki Klapálek, 1899, Chaetopteryx fusca Brauer, 1857, Grammotaulius nigropunctatus (Retzius, 1783), Limnephilus flavicornis (Fabricius, 1787), Limnephilus lunatus Curtis, 1834, Limnephilus vittatus (Fabricius, 1798), Micropterna nycterobia McLachlan 1875, Micropterna testacea (Gmelin, 1789), Stenophylax permistus McLachlan, 1895, Allogamus uncatus (Brauer, 1857), Halesus digitatus (Schrank, 1781), Sericostoma flavicorne Scheider, 1845 and Odontocerum albicorne (Scopoli, 1763) and the plecopterans Leuctra mortoni Kempny, 1899, Nemoura cinerea (Retzius, 1783), Protonemura autumnalis Rauser, 1956, Protonemura hrabei Rauser, 1956, Isoperla illyrica Tabacaru, 1971, Isoperla inermis Kacanski & Zwick, 1970, Isoperla tripartita Illies, 1954, and Brachyptera tristis (Klapálek, 1901) (Popijač & Sivec 2010; Waringer et al. 2009; our data).

4. Discussion

4.1. Species delimitation and larval affiliation

Association of adults and larvae of the two new species collected at the mouth of the Jabučica River and the spring reach of the Cetina River, respectively, is supported by molecular genetic analyses at both intra- and interspecific levels. Additionally, larvae collected at both localities exhibit a unique combination of morphological characters and are clearly distinct from each other and the other Ecclisopteryx species (see 3.4. for details).

Despite the tremendous importance of species level identification of larvae in applied science (e.g., water quality monitoring, conservation biology) (e.g. Hering et al. 2004), ca. 60% of Drusinae larvae remain unknown (Waringer et al. 2013). In particular, species level identification offers enhanced resolution of trait-environment relationships, particularly in ecologically sensitive taxa. Thus, species-level resolution has the potential to improve the quality of ecological assessments that use caddisflies or other sensitive aquatic insects as quality indicators (e.g. Schmidt-Kloiber & Nijboer 2004). The morphological characteristics of the larva of E. keroveci and E. ivkae now allow clear identification of these species and will enable better ecological characterisation of Drusinae in the region. When this information is integrated in national and international databases it will be of great value for further use in ecological investigations.

The B/MCMCMC phylogenetic analysis presented here to discriminate the species is based on the combination of three gene fragments (mtCOI, mtLSU, nuWG) previously demonstrated to successfully resolve phylogenetic relationships among species of Drusinae (Pauls et al. 2008). The phylogeny suggests a highly supported sister clade relationship of (E. keroveci + E. ivkae) + (E. dalecarlica + E. guttulata) and monophyly of all putative Ecclisopteryx species except E. ivkae, which is recovered in a basal polytomy (Fig. 2). Interspecific p-distances of mt-COI sequence data between the two new species, E. keroveci and E. ivkae (1.6 – 2.7%), are similar to the observed intraspecific variability of the same mtCOI fragment in populations of some Drusinae species (e.g. Kučinić et al. 2008; Pauls et al. 2009; Previšić et al 2009, 2014). However, in several closely related Drusinae species, interspecific p-distances of the same mtCOI fragment are similar or even lower than observed between E. keroveci and E. ivkae in the current study (e.g., Waringer et al. 2007; Kučinić et al. 2011). Further, intraspecific p-distances of the mtCOI gene fragment in E. keroveci show relatively high divergence of easternmost and westernmost populations (e.g., 1.6% between haplotypes from eastern Montenegro (Brodavac) and western Croatia (Velika Belica), 1.8% between haplotypes from eastern Bosnia (Sutjeska NP) and the latter, Fig. 3). Nevertheless, the morphological and molecular data at hand suggests that these specimens all belong to a single species.

In contrast to the highly variable mtCOI gene, differences between closely related species in nuWG and particularly in mtLSU are much lower (Pauls et al. 2008), and thus provide less information. Probably for this reason the B/MCMCMC phylogeny does not fully support the delimitation of the two species, as E. ivkae forms a basal polytomy. Including additional (or more variable) loci would improve the present analysis. However, in our case, the striking differences in larval morphology of northern European populations of E. dalecarlica initially led us to think that two or more new species might occur, especially since larval characters in Drusinae are stable and vary little among species (e.g. Kučinić et al. 2011; Waringer & Graf 2011; Waringer et al. 2013). Furthermore, as indicated in our study, morphology of male and female genitalia of E. keroveci and E. ivkae differs distinctly between these species and E. dalecarlica (see 3.4 for details).

Thus, the integration of genetic and morphological differences, justifies the separation of E. ivkae and E. keroveci as two distinct species, as both taxa exhibit a unique combination of both genetic and morphological character states. Additional and equally comprehensive studies might uncover the existence of other localised allopatric lineages in Ecclisopteryx species in the Balkans, regardless of their current taxonomic status.

4.2. Distribution of E. keroveci and E. ivkae

With the addition of the 2 new Ecclisopteryx species, this genus currently comprises 7 species: 3 species relatively widespread in Europe, 1 regional endemic, and 3 microendemics (Table 2 & Fig. 1; Graf et al. 2008, 2011; Graf & Schmidt-Kloiber 2011). Unlike the 2 Ecclisopteryx range restricted endemics confined to different parts of the Alps (E. malicky is known exclusively from the southcentral Alps, and E. asterix from the south-eastern Alps; Graf et al. 2008, 2011; Graf & Schmidt-Kloiber 2011), E. keroveci and E. ivkae show rather unique distribution patterns in the Western Balkans (Fig. 1B). Although both are allopatric and endemic, E. keroveci seems to have a wider, disjunct distribution in the region.

Previous records of both E. dalecarlica (Urbanič 2004; Stanić-Koštroman 2009; Previšić & Popijač 2010; Ibrahimi 2011; Vučković 2011; Vučković et al. 2011) and E. guttulata (Radovanović 1935; Marinković-Gospodnetić 1970) in the region are misidentifications of these 2 new, formerly unknown cryptic endemics. This conclusion is further supported since specimens from most the localities where E. dalecarlica and/or E. guttulata were presumed to have been collected were available for the current study; these all proved to be either of the 2 new species. The only historical record we could examine is a single male from central Bosnia, collected at the end of the 19th century, from Klapálek’s collection (the National Museum, Prague, Czech Republic). It was originally listed as E. guttulata, but it proved to be E. keroveci. The findings of Radovanović (1935) and Marinković-Gospodnetić (1970) could not be checked because the material was not available for study.

4.3. The Western Balkans – a hotspot of freshwater biodiversity under threat

The description of E. keroveci and E. ivkae increases the number of endemic Western Balkan caddisflies: of 36 Drusinae species distributed in the region, 28 are endemics. Most of these are restricted to very small geographic areas (Graf et al. 2008; Oláh 2010, 2011; Graf & Schmidt-Kloiber 2011; Oláh & Kovács 2013). In the Dinaric Western Balkan ecoregion (ER5) 64% of Drusinae species are endemic (14 of 22 species); similarly, in the Hellenic Western Balkan ecoregion (ER6) 65% are endemic (13 of 20; Graf et al. 2008; Oláh 2010, 2011; Graf & Schmidt-Kloiber 2011; Oláh & Kovács 2013).

Hence, the Western Balkans is a diversity centre for highland caddisflies inhabiting isolated “island habitats” such as coldwater springs and streams (e.g. Drusinae, Chaetopteryx species; Kučinić et al. 2013). Such habitat preferences coupled with low dispersal abilities, specific life history traits, and historical processes causing further fragmentation and isolation of habitats (e.g., karstification; Previšić et al. 2009, 2014) most likely result in high diversification rates. A remarkable degree of cryptic diversity was recently observed in the Western Balkans not only in groundwater fauna (e.g. Zakšek et al. 2009), but also in widespread and commonly known surface aquatic species, such as the crayfish Austropotamobius torrentium (Klobučar et al. 2013) and the amphipod Gammarus fossarum (Weiss et al. 2014). Furthermore, a considerable fraction of the existing endemic diversity across various animal groups is considered cryptic in many parts of Europe, e.g., in isolated southern European mountain ranges (Essl et al. 2013). All this indicates that high degrees of cryptic diversity can be expected in many groups of aquatic organisms in the Balkans, and highlights the need for more comprehensive research of insufficiently investigated freshwater biodiversity and biogeography.

Near natural streams in all Western Balkan countries are increasingly threatened by human activities, especially the increase in construction of small power plants (Freyhof 2012; Schwarz 2012). According to Freyhof (2012), construction of dams and its inevitable side effects pose the most serious threat to freshwater diversity in the Balkans, the most important “hotspot” of European threatened biodiversity. Such adverse environmental impacts also threaten the existence of yet-to-be-discovered cryptic species.

Acknowledgements

We are grateful to the Sutjeska NP Authorities for granting sampling permission, our colleagues Marija Ivković, Zlatko Mihaljević and Marko Miliša (Zagreb, Croatia) for their help in the field, Svjetlana Stanić-Koštroman (Mostar, Bosnia and Hercegovina), Halil Ibrahimi (Prishtina, Kosovo), Peter Neu (Kasel, Germany), Hans Malicky (Lunz, Austria), Pavel Chvojka (Prague, Czech Republic) and Trond Andersen (Bergen, Norway) for providing Ecclisopteryx specimens. Peter Neu is also thanked for his help with distribution data of Ecclisopteryx species. Contributors to the Distribution Atlas of European Trichoptera (DAET; BioFresh) are thanked for permission to use their data on sampling localities of Ecclisopteryx species. This study was financially supported by the University in Zagreb (Project No. 202310), the Austrian Science Fund (FWF) (Project No. 23687-B17), the BioFresh EU project – Biodiversity of Freshwater Ecosystems: Status, Trends, Pressures and Conservation Priorities (contract No. 226874), the Romanian Ministry of National Education (CNCS-UEFISCDI-nr. PN-II-ID-PCE-2012-4-0595) and the research funding programme “LOEWE – Landes-Offensive zur Entwicklung wissenschaftlichökonomischer Exzellenz” of Hesse’s Ministry of Higher Education, Research, and the Arts.

References

  1. Avise JC. Molecular Markers, Natural History, and Evolution. 2nd edn Sinauer; Sunderland, MA: 2004. p. 684. [Google Scholar]
  2. Bickford D, Lohman DJ, Sodhi NS, Ng PKL, Meier R, Winker K, Ingram KK, Das I. Cryptic species as a window on diversity and conservation. Trends in Ecology and Evolution. 2007;22:148–155. doi: 10.1016/j.tree.2006.11.004. [DOI] [PubMed] [Google Scholar]
  3. Drummond AJ, Rambaut A. BEAST: Bayesian evolutionary analysis by sampling trees. BMC Evolutionary Biology. 2007;7:214. doi: 10.1186/1471-2148-7-214. [DOI] [PMC free article] [PubMed] [Google Scholar]
  4. Essl F, Rabitsch W, Dullinger S, Moser D, Milasowszky N. How well do we know species richness in a well-known continent? Temporal patterns of endemic and widespread species descriptions in the European fauna. Global Ecology and Biogeography. 2013;22:29–39. [Google Scholar]
  5. Francuski LJ, Ludoski J, Vujić A, Milankov V. Phenotypic evidence for hidden biodiversity in the Merodon aureus group (Diptera, Syrphidae) on the Balkan Peninsula: conservation implication. Journal of Insect Conservation. 2011;15:379–388. [Google Scholar]
  6. Freyhof J. Threatened freshwater fishes and molluscs of the Balkan, potential impact of hydropower projects. ECA Watch Austria&EuroNatur.; 2012. p. 81. Unpublished report. [Google Scholar]
  7. Geneious version R7 created by Biomatters. Available from http://www.geneious.com/
  8. Graf W, Murphy J, Dahl J, Zamora-Muñoz C, López-Rodríguez MJ. Volume 1 – Trichoptera. In: Schmidt-Kloiber A, Hering D, editors. Distribution and Ecological Preferences of European Freshwater Organisms. Pensoft Publishers; Sofia, Moscow: 2008. p. 388. [Google Scholar]
  9. Graf W, Schmidt-Kloiber A. [accessed on 20 July 2013];Additions to and update of the Trichoptera Indicator Database. 2011 www.freshwaterecology.info, version 5.0.
  10. Graf W, Kučinić M, Previšić A, Pauls SU, Waringer J. The larva of Ecclisopteryx malickyi Moretti, 1991 (Trichoptera: Limnephilidae; Drusinae) with comments on the genus. Zoosymposia. 2011;5:136–142. doi: 10.11646/zoosymposia.5.1.11. [DOI] [PMC free article] [PubMed] [Google Scholar]
  11. Hering D, Moog O, Sandin L, Verdonschot PFM. Overview and application of the AQEM assessment system. Hydrobiologia. 2004;516:1–20. [Google Scholar]
  12. Howard DJ, Berlocher SH. Endless Forms: Species and Speciation. Oxford University Press; New York: 1998. p. 470. [Google Scholar]
  13. Ibrahimi H. Faunistical, ecological and biogeographical characteristics of Kosovo caddisflies (Insecta: Trichoptera) University of Zagreb; Zagreb, Croatia: 2011. p. 183. PhD thesis. [Google Scholar]
  14. Illies J. Limnofauna Europaea. A Checklist of the Animals Inhabiting European Inland Waters, with an Account of their Distribution and Ecology. 2nd edn. Gustav Fischer Verlag; Stuttgart: 1978. p. 552. [Google Scholar]
  15. Jackson JK, Battle JM, White BP, Pilgrim EM, Stein ED, Miller PE, Sweeney BW. Cryptic biodiversity in streams: a comparison on macroinvertebrate communities based on morphological and DNA barcode identifications. Freshwater Science. 2014;33:312–324. [Google Scholar]
  16. Katoh K, Standley DM. MAFFT Multiple Sequence Alignment Software Version 7: Improvements in Performance and Usability. Molecular Biology and Evolution. 2013;30:772–780. doi: 10.1093/molbev/mst010. [DOI] [PMC free article] [PubMed] [Google Scholar]
  17. Klobučar GIV, Podnar M, Jelić M, Franjević D, Faller M, Štambuk A, Gottstein S, Simić V, Maguire I. Role of the Dinaric karst (western Balkans) in shaping the phylogeographic structure of the threatened crayfish Austropotamobius torrentium. Freshwater Biology. 2013;58:1089–1105. [Google Scholar]
  18. Kolenati FA. Genera et species Trichopterorum. Pars prior: Heteropalpoidea. Caes. Reg. Aulicae Typographiae Filiorum Amadei Haase; Prague: 1848. p. 123. [Google Scholar]
  19. Kučinić M, Previšić A, Stanić-Koštroman S, Franjević M, Šerić Jelaska L, Delić A, Posilović H. Description of the larvae of Drusus ramae Marinković-Gospodnetić, 1971 and Drusus medianus Marinković-Gospodnetić, 1976 (Trichoptera: Limnephilidae) with some genetic data, distribution, ecological, faunal and conservation notes. Zootaxa. 2010;2484:1–24. [Google Scholar]
  20. Kučinić M, Previšić A, Graf W, Šerić Jelaska L, Stanić-Koštroman S, Waringer J. Larval description, genetic and ecological features of Drusus radovanovici radovanovici Marinković-Gospodnetić, 1971 (Trichoptera: Limnephilidae: Drusinae) with some phylogenetic and taxonomic data on the bosnicus group in the Balkan Peninsula. Deutsche Entomologische Zeitschrift. 2011;58:135–153. [Google Scholar]
  21. Kučinić M, Szivák I, Pauls SU, Bálint M, Delić A, Vučković I. Chaetopteryx bucari sp. n., a new species from the Chaetopteryx rugulosa group from Croatia (Insecta, Trichoptera, Limnephilidae) with molecular, taxonomic and ecological notes on the group. ZooKeys. 2013;320:1–28. doi: 10.3897/zookeys.320.4565. [DOI] [PMC free article] [PubMed] [Google Scholar]
  22. Malicky H. Weiteres Neues über Köcherfliegen aus dem Mittelmeergebiet (Trichoptera) Zeitschrift für Entomologie. 1981;2:335–356. [Google Scholar]
  23. Malicky H. Ein kommentiertes Verzeichnis der Köcherfliegen (Trichoptera) Europas und des Mediterrangebietes. Linzer Biologische Beiträge. 2005;37:533–596. [Google Scholar]
  24. Malm T, Johanson KA. Revision of the New Caledonian endemic genus Gracilipsodes (Trichoptera: Leptoceridae: Grumichellini) Zoological Journal of the Linnean Society. 2008;153:425–452. [Google Scholar]
  25. Marinković-Gospodnetić M. Fauna Trichoptera područja Maglića, Volujka i Zelengore. Glasnik Zemaljskog Muzeja Bosne i Hercegovine u Sarajevu. 1970;9:107–119. [Google Scholar]
  26. Nielsen A. A comparative study of the genital segments and their appendages in male Trichoptera. Biologiske Skrifter udgivet af Det Kongelige Dankse Vedenskabernes Selskab. 1957;8:1–159. [Google Scholar]
  27. Nylander JAA. MrModeltest v2. – Program distributed by the author. Evolutionary Biology Centre, Uppsala University; Uppsala, Sweden: 2004. Available from: https://github.com/nylander/MrModeltest2. [Google Scholar]
  28. Oláh J. New species and new records of Palearctic Trichoptera in the material of the Hungarian Natural History Museum. Annales Historico-Naturales Musei Nationalis Hungarici. 2010;102:65–117. [Google Scholar]
  29. Oláh J. New species and records of Balkan Trichoptera. Folia Historico Naturalia Musei Matraensis. 2011;35:111–121. [Google Scholar]
  30. Oláh J, Kovács T, Sivec I, Szivák I, Urbanič G. Seven new species in the Chaetopteryx rugulosa species group: applying the phylogenetic species concept and the sexual selection theory (Trichoptera: Limnephilidae) Folia Historico Naturalia Musei Matraensis. 2012;36:51–79. [Google Scholar]
  31. Oláh J, Kovács T. New species and new records of Balkan Trichoptera II. Folia Historico Naturalia Musei Matraensis. 2013;37:109–121. [Google Scholar]
  32. Pauls SU, Lumbsch HT, Haase P. Phylogeography of the montane caddisfly Drusus discolor: Evidence for multiple refugia and periglacial survival. Molecular Ecology. 2006;15:2153–2169. doi: 10.1111/j.1365-294X.2006.02916.x. [DOI] [PubMed] [Google Scholar]
  33. Pauls SU, Graf W, Haase R, Lumbsch HT, Waringer J. Grazers, shredders and filtering carnivores – The evolution of feeding ecology in Drusinae (Trichoptera: Limnephilidae): Insights from a molecular phylogeny. Molecular Phylogenetics and Evolution. 2008;46:776–791. doi: 10.1016/j.ympev.2007.11.003. [DOI] [PMC free article] [PubMed] [Google Scholar]
  34. Pauls SU, Theissinger K, Ujvarosi L, Balint M, Haase P. Patterns of population structure in two closely related, partially sympatric caddisflies in Eastern Europe: historic introgression, limited dispersal, and cryptic diversity. Journal of the North American Benthological Society. 2009;28:517–536. [Google Scholar]
  35. Pauls SU, Blahnik RJ, Zhou X, Wardwell CT, Holzenthal RW. DNA barcode data confirm new species and reveal cryptic diversity in Chilean Smicridea (Smicridea) (Trichoptera: Hydropsychidae) Journal of the North American Benthological Society. 2010;29:1058–1074. [Google Scholar]
  36. Pfenninger M, Schwenk K. Cryptic animal species are homogeneously distributed among taxa and biogeographical regions. BMC Evolutionary Biology. 2007;7:121. doi: 10.1186/1471-2148-7-121. [DOI] [PMC free article] [PubMed] [Google Scholar]
  37. Popijač A. Diversity and ecology of stoneflies (Insecta: Plecoptera) in the area of Plitvice Lakes National Park and River Cetina. University of Zagreb; Zagreb, Croatia: 2007. p. 174. PhD thesis. [Google Scholar]
  38. Popijač A, Sivec I. The stonefly fauna (Insecta: Plecoptera) of the Mediterranean river Cetina, Croatia. Entomologia Croatica. 2010;14:103–120. [Google Scholar]
  39. Previšić A, Kerovec M, Kučinić M. Emergence and composition of Trichoptera from karst habitats, Plitvice Lakes region, Croatia. International Review of Hyrobiology. 2007;92:61–83. [Google Scholar]
  40. Previšić A, Popijač A. Caddisfly (Insecta: Trichoptera) fauna of Kupa and Čabranka rivers and their tributaries, Gorski kotar, W Croatia. Natura Croatica. 2010;19:357–368. [Google Scholar]
  41. Previšić A, Walton C, Kučinić M, Mitrikeski PT, Kerovec M. Pleistocene divergence of Dinaric Drusus endemics (Trichoptera, Limnephilidae) in multiple microrefugia within the Balkan Peninsula. Molecular Ecology. 2009;18:634–647. doi: 10.1111/j.1365-294X.2008.04046.x. [DOI] [PubMed] [Google Scholar]
  42. Previšić A, Schnitzler J, Kučinić M, Graf W, Ibrahimi H, Kerovec M, Pauls SU. Microscale vicariance and diversification of western Balkan caddisflies linked to karstification. Freshwater Science. 2014;33:250–262. doi: 10.1086/674430. [DOI] [PMC free article] [PubMed] [Google Scholar]
  43. R Core Team 2013 . R: A language and environment for statistical computing. R Foundation for Statistical Computing; Vienna, Austria: URL http://www.R-project.org/ [Google Scholar]
  44. Radovanović M. Trihoptere Jugoslavije. Glasnik Zemaljskog Muzeja u Bosni i Hercegovini. 1935;47:73–84. [Google Scholar]
  45. Ronquist F, Huelsenbeck JP. MrBayes 3: Bayesian phylogenetic inference under mixed models. Bioinformatics. 2003;19:1572–1574. doi: 10.1093/bioinformatics/btg180. [DOI] [PubMed] [Google Scholar]
  46. Ross HH. Biological Systematics. Addison-Wesley Publishing Company Inc.; Reading, Massachusetts: 1974. p. 345. [Google Scholar]
  47. Schmid F. La sous-famille des Drusinae (Trichoptera, Limnophilidae) Institut Royal des Sciences Naturelles de Belgique, Memoires 2. Ser. 1956;55:1–92. [Google Scholar]
  48. Schmidt-Kloiber A, Nijboer R. The effect of taxonomic resolution on the assessment of ecological water quality classes. Hydrobiologia. 2004;516:269–283. [Google Scholar]
  49. Schwarz U. Balkan Rivers – The Blue Heart of Europe. Hydromorphological Status and Dam Projects. Report. Vienna, Austria: 2012. p. 151. [Google Scholar]
  50. Simon C, Frati F, Beckenbach A. Evolution, weighting and phylogenetic utility of mitochondrial gene sequences and a compilation of conserved polymerase chain reaction primers. Annals of the Entomological Society of America. 1994;87:651701. [Google Scholar]
  51. Snodgrass RE. Principles of Insect Morphology. Cornell University Press; Ithaca, New York: 1935. p. 667. [Google Scholar]
  52. Stanić-Koštroman S. Faunistical, ecological and biogeographical charcteristics of caddisflies (Insecta: Trichoptera) of Bosnia and Herzegovina. University of Zagreb; Zagreb, Croatia: 2009. p. 151. PhD thesis. [Google Scholar]
  53. Tamura K, Dudley J, Nei M, Kumar S. MEGA4: Molecular Evolutionary Genetics Analysis (MEGA) software version 4.0. Molecular Biology and Evolution. 2007;24:1596–1599. doi: 10.1093/molbev/msm092. [DOI] [PubMed] [Google Scholar]
  54. Thomson RE, Holzenthal RW. New Neotropical species of the genus Austrotinoes Schmid (Trichoptera: Ecnomidae) Zootaxa. 2010;2437:38–50. [Google Scholar]
  55. Tsuomani M, Apostolidis AP, Leonardos ID. Biogeography of Rutilus species of the southern Balkan Peninsula as inferred by multivariate analysis of morphological data. Journal of Zoology. 2013;289:204–121. [Google Scholar]
  56. Urbanič G. Ecology and distribution of caddisflies (Insecta: Trichoptera) in some watercourses in Slovenia. Unversity of Ljubljana; Ljubljana, Slovenia: 2004. p. 188. PhD thesis. [Google Scholar]
  57. Vučković I. Faunistic, taxonomic and ecological characteristics of caddisfly (Insecta: Trichoptera) on the chatchment area of the river Cetina. University of Zagreb; Zagreb, Croatia: 2011. p. 176. PhD thesis. [Google Scholar]
  58. Vučković I, Previšić A, Graf W, Kučinić M. Description of the female and new data on distribution of Annitella apfelbecki Klapalek, 1899 (Insecta: Trichoptera) Aquatic Insects. 2011;33:312–321. [Google Scholar]
  59. Waringer J. The larva of Metanoea rhaetica Schmid 1955 (Trichoptera: Drusinae) from a small Austrian mountain brook. Aquatic Insects. 1985;7:243–248. [Google Scholar]
  60. Waringer J, Graf W, Pauls SU, Lubini V. The larva of Drusus nigrescens Meyer-Dür, 1875 (Trichoptera: Limnephilidae: Drusinae) with notes on its ecology, genetic differentiation and systematic position. Annales de Limnologie – International Journal of Limnology. 2007;43:161–166. doi: 10.1051/limn:2007010. [DOI] [PMC free article] [PubMed] [Google Scholar]
  61. Waringer J, Graf W, Kučinić M, Previšić A, Vučković I. The larva and life cycle of Annitella apfelbecki Klapalek, 1899, including a redescription of Melampophylax nepos McLachlan, 1880 (Trichoptera: Limnephilidae) Aquatic Insects. 2009;31:71–80. doi: 10.1080/01650420802616327. [DOI] [PMC free article] [PubMed] [Google Scholar]
  62. Waringer J, Graf W, Pauls SU, Previšić A, Kučinić M. A larval key to the Drusinae species (Trichoptera: Limnephilidae) of Austria, Germany, Switzerland and the dinaric western Balkan. Denisia. 2010;29:383–406. [PMC free article] [PubMed] [Google Scholar]
  63. Waringer J, Graf W. Atlas of Central European Trichoptera Larvae. Erik Mauch Verlag; Dinkelscherben: 2011. p. 468. [Google Scholar]
  64. Waringer J, Graf W, Bálint M, Kučinić M, Pauls SU, Previšić A, Keresztes L, Vitecek S. The larvae of Drusus franzressli Malicky 1974 and Drusus spelaeus (Ulmer 1920) (Trichoptera: Limnephilidae: Drusinae) with notes on ecology and zoogeography. Zootaxa. 2013;3637:1–16. doi: 10.11646/zootaxa.3637.1.1. [DOI] [PMC free article] [PubMed] [Google Scholar]
  65. Weiss M, Macher JN, Seefeldt MA, Leese F. Molecular evidence for further overlooked species within the Gammarus fossarum complex (Crustacea: Amphipoda) Hydrobiologia. 2014;721:165–184. [Google Scholar]
  66. Wiggins GB. Larvae of the North American Caddisfly Genera (Trichoptera) 2nd edn. University of Toronto Press; Toronto: 1998. p. 457. [Google Scholar]
  67. Zakšek V, Sket B, Gottstein S, Franjević D, Trontelj P. The limits of cryptic diversity in groundwater: phylogeography of the cave shrimp Troglocaris anophtalmus (Crustacea: Decapoda: Atyidae) Freshwater Biology. 2009;18:931–946. doi: 10.1111/j.1365-294X.2008.04061.x. [DOI] [PubMed] [Google Scholar]

RESOURCES