; citation_doi=https://doi.org/10.22073/pja.v12i2.80515 ; citation_title= ; citation_doi=https://doi.org/10.22073/pja.v12i2.80515 ; citation_publication_date= ; citation_doi=https://doi.org/10.22073/pja.v12i2.80515
1✉ Department of Biology, University of Montenegro, Cetinjski put b.b., 81000 Podgorica, Montenegro.
2Institute of Marine and Environmental Sciences, Center of Molecular Biology and Biotechnology, University of Szczecin, Wąska 13, 71–415 Szczecin, Poland.
3Bavarian State Collection of Zoology, Section Arthropoda varia, Münchhausenstraße 21, 81247 Munich, Germany.
2025 - Volume: 65 Issue: 4 pages: 1173-1187
https://doi.org/10.24349/n9hh-29w1The water mite genus Torrenticola Piersig, 1896, is one of the most diverse and abundant groups of water mites in running waters on all continents except Antarctica, with the highest diversity in the Northern Temperate and Tropical regions (Goldschmidt 2009). Over the last decade, the application of integrative taxonomical approaches has revealed a high degree of cryptic and pseudo-cryptic diversity among European torrenticolids, leading to the discovery of previously unrecognized species and the identification of several species complexes composed of genetically distinct lineages (e.g., Pešić et al. 2012; Pešić and Smit 2022; Pešić et al. 2021, 2023, 2024a, 2025a,d). Notable examples include the T. laskai complex (e.g., Pešić and Smit 2022; Pešić et al. 2020, 2023), the T. barsica complex (e.g., Pešić and Smit 2022), and the T. meridionalis complex (e.g., Pešić et al. 2021).
Torrenticola meridionalis Di Sabatino & Cicolani, 1990, was originally described from Calabria, southern Italy (Di Sabatino & Cicolani, 1990). In the original description, the species was compared with T. elliptica Maglio, 1909, a species widely distributed in Central Europe and typically associated with montane, low-order streams (Di Sabatino et al. 2009). Torrenticola meridionalis was distinguished from T. elliptica by its less slender idiosoma and, in males, by a relatively shorter medial suture of Cx-II+III and a stouter genital field. Subsequently, T. meridionalis was reported from the Balkans (Di Sabatino et al. 2003) and France (Di Sabatino et al. 2009). However, some of these populations exhibit a wide variability in the first two diagnostic characters, overlapping with the variation observed in T. elliptica, thereby blurring the morphological distinction between the two species.
For example, Di Sabatino et al. (2009) reported that specimens from France (Auvergne) possess a genital field consistent with T. elliptica (L/W ratio > 1.25), intermediate proportions of Cx-I/II+III (L Cx-I/Cx-II+III ratio 3.0-3.5), and a dorsal shield (L/W ratio < 1.5) resembling that of T. meridionalis. This suggests that the high morphometric variability observed across the distribution ranges of both morphospecies may indicate that they represent species complexes composed of genetically distinct lineages, often with geographically restricted distributions.
Recently, Pešić et al. (2021) demonstrated that populations previously identified as T. meridionalis include at least three divergent barcode clusters. One of these (BOLD:AEK9662) is restricted to populations from Italy, while the other two, i.e., BOLD:AED7519 and BOLD:AEI3402, represent widely distributed haplogroups comprising populations from the Balkans. A re-examination of the specimens assigned to BOLD:AEI3402, previously published by Pešić et al. (2021) under the name T. meridionalis Clade 3 (=TorrM-III Clade), revealed that these specimens, due to their elongated idiosoma and the excretory pore being distinctly embedded within the area of primary sclerotization, correspond morphologically to T. similis (see Pešić et al. 2025d for further discussion).
In the present study, we used morphological data and DNA barcoding to re-examine voucher material of T. meridionalis from Italy and the Balkans. As a result, we describe one species new to science.
Water mites were collected with kick nets and immediately preserved in 96% ethanol for the purpose of molecular analyses. Water mite specimens used for the molecular study are listed in Table 1. After non-destructive, whole-body DNA extraction, the specimen vouchers were stored in 96% ethanol and morphologically examined. Some of these vouchers were dissected and slide mounted in Faure's medium, while the rest was transferred to Koenike's fluid.
Morphological nomenclature follows Gerecke et al. (2016). The dorsal platelets of Torrenticola spp. were measured on both sides, therefore their dimensions are given as a range of values, rather than a single number. The holotype and paratypes of the new species are deposited in Naturalis Biodiversity Center in Leiden (RMNH).
All measurements are given in μm. The photographs of selected structures were made using a camera on a Samsung Galaxy smartphone. The following abbreviations are used: Al pl = antero-lateral platelets, Am pl = antero-medial platelets, Cx-I = first coxae, Cxgl-4 = coxoglandularia of first coxae, dL = dorsal length, dp = dorsal plate, ds = dorsal shield, expo = excretory pore, gf = genital field, H = height, ec = ejaculatory complex, I-L-4 = first leg, fourth segment, L = length, mL = medial length, P-1 = palp, first segment, RMNH = Naturalis Biodiversity Center in Leiden, Vgl = ventroglandularia, vL = ventral length, W = width.
The molecular analysis was conducted at the Institute of Biology, University of Szczecin (IoB-UoS), and at the University of Lodz (UniLodz), Lodz, Poland. DNA was extracted using a non-destructive protocol as described in Pešić et al. (2025b). At UniLodz amplification and DNA sequencing using Oxford Nanopore Technology was done according to the protocol in Pešić et al. (2025b). Raw reads were demultiplexed using the Pacific Biosciences SMRT Link software. Consensus sequences were generated with the PacBio Amplicon Analysis (pbaa) tool. Primer trimming, translation and stop codon checking were performed using Geneious Prime 2024.0.1. Consensus sequences were made available in the BOLD database (Ratnasingham & Hebert 2007). Relevant voucher information, photos, and DNA barcodes of the new species are publicly accessible through the Dataset ''DS-BALHYD DNA barcode reference library of Balkan water mites» (https://portal.boldsystems.org/recordset/DS-BALHYD
; doi.org/10.5883/DS-BALHYD).
Sequence alignments were performed using MUSCLE (Edgar 2004). Intra- and interspecific genetic distances were calculated based on the p-distance using MEGA11 (Tamura et al. 2021). The latter software was used to calculate Neighbor-Joining (NJ) trees based on K2P distances (standard for barcoding studies) using pairwise deletion for missing data. Branch support was calculated using nonparametric bootstrap (Felsenstein 1985) with 1000 replicates and shown next to the branches.
Figures 1, 5A
Material examined — Italy, Calabria, Fossiata, stream, 39.4011°N, 16.5884°E, 23 August 2018, leg. Goldschmidt, 2♂, 1♀ (sequenced; DCBDJ062-21, DCBDJ041-21, DCBDJ067-21), 1♂ (Voucher Id: CCDB 38392 F02) dissected and slide mounted (RMNH).
Remarks — Examination of specimens from Calabria, southern Italy, assigned to BOLD:AEI3403 showed that they morphologically match the original description of T. meridionalis, a species described from the River Alli at the locality Belladona in Calabria (Di Sabatino and Cicolani, 1990). In the original description, T. meridionalis was compared with T. elliptica, from which it differs by a less slender idiosoma (L/W ratio of dorsal shield < 1.5 vs. > 1.5 in T. elliptica), and in males, by a relatively shorter medial suture of Cx-II+III (length ratio Cx-I/Cx-II+III > 3.5 vs. < 3.0), and a stouter genital field (L/W ratio ~1.2 vs. ~1.3).
Additionally, Di Sabatino and Cicolani (1990) noted differences in the ecological preferences of the two species. Torrenticola elliptica is considered the most stenothermic species of the genus and, in the Mediterranean region, is confined to high-elevation habitats. In contrast, T. meridionalis is eurythermic and inhabits lowland streams (Figure 2) and rivers at lower elevations, often in watercourses affected by thermal fluctuations and seasonal changes in discharge.
Measurements of the examined male are provided in Table 1.
Download as
Torrenticola meridionalis
Torrenticola eurytopica n. sp.
Italy, Fossiata
North Macedonia, Prespa Lake
CCDB 38392 F02, ♂
15. CG2019_7 B12, ♂
♂
♀
Idiosoma L
825
806
791
938
Idiosoma W
602
606
575
700
Ds L
696
700
681
819
Ds W
500
473
453
561
Ds L/W ratio
1.39
1.48
1.5
1.46
Dp L
650
652
633
766
Al plate L
206-209
218-219
213-216
225
Al plate W
75-78
84-88
78-84
83-91
Al plate L/W
2.68-2.75
2.5-2.6
2.6-2.7
2.5-2.7
Am plate L
141
142-144
136-139
148-156
Am plate W
63
68-69
68
69-72
Am plate L/W ratio
2.24
2.06-2.12
2.0-2.04
2.1-2.3
Al pl L/Am pl L ratio
1.46-1.48
1.51-1.54
1.55-1.56
1.4-1.5
Gnathosomal bay L
166
147
156
178
Cx-I L
327
303
317
347
Cx-I mL
161
156
159
169
Cx-II+III mL
83
91
91
31
Cx-1 L/Cx-II+III mL
3.9
3.3
3.48
11.2
Cx-I mL/Cx-II+III mL ratio
1.94
1.71
1.75
5.45
Genital field L
163
170
166
200
Genital field W
141
130
131
165
Gf L/W ratio
1.16
1.3
1.26
1.21
Distance gf—expo
180
181
172
237
Distance gf—cauda
241
244
219
331
Ec L
250
-
259
-
Gnathosoma vL
316
312
305
348
Chelicera L
353
344
350
406
Palp, total L
331
332
323
366
P-1 dL/H
42/35
38/34
34/34
41/41
P-2 dL/H
103/57
106/56
105/53
119/69
P-3 dL/H
63/53
63/52
61/48
70/61
P-4 dL/H
103/31
105/33
103/31
114/38
P-5 dL/H
20/11
20/16
20/13
22/14
dL P-2/P-4 ratio
1
1.01
1.02
1.04
dL I-L-4
105
111
109
119
dL I-L-5
115
115
116
119
dL I-L-6
116
114
113
116
H I-L-6
44
42
40
44
dL/H I-L-6 ratio
2.64
2.7
2.9
2.6
Genetic data — All examined specimens belong to a unique BIN (BOLD:AEK9662).
Distribution — Southern Italy.
ZOOBANK: D4B72B56-529A-493B-98A1-40739C2398E2 ![]()
Figures 3-4, 5B-F
Torrenticola meridionalis Di Sabatino & Cicolani, 1990 [in part] – Di Sabatino et al. (2003), Pešić et al. (2018, 2021, 2024b, 2025c).
Holotype ♂ (sequenced; DNCBD049-20), Montenegro, Bar, Rikavac stream near Old Bar, 42.1001°N, 19.1432°E, 3 June 2020, leg. Pešić, dissected and slide mounted (voucher Id: CCDB_3867_E03; RMNH). Paratypes: 1♀ (sequenced; DNCBD049-20), same data as holotype, dissected and slide mounted (voucher Id: CCDB_3867_E01; RMNH); 2♂ (sequenced; DNCBD073-20, DNCBD074-20), Montenegro, Virpazar, Orahovštica river, 42.2476°N, 19.0798°E, 10 June 2020, leg. Pešić; 3♂, 1♀ (2♂ sequenced; DNAEC022-20, DNAEC023-20); North Macedonia, Prespa Lake near Oteševo, 40.979°N, 20.917°E, 15 September 2019 leg. Pešić, Jovanović & Manović, 2♂, 1♀ dissected and slide mounted (all RMNH).
Morphological — Colour pattern of dorsal shield as given in Figures. 5B-F; male medial suture Cx-II+III short (L 90-100); male genital field subrectangular in shape L/W ratio 1.3, posterior margins of genital flaps with a few short setae in both sexes; male ejaculatory complex with large proximal chamber, P-2 slightly longer than P-4.
Molecular — this lineage is represented by a unique BIN (BOLD:AED7519) which differs from T. meridionalis clade (BOLD:AEK9662) from South Italy by 7.18% p-distance for COI.
General features — Idiosoma longish in shape; dorsal shield with a colour pattern as given in Figures 5B-F; area of primary sclerotization of the dorsal plate with two dorsoglandularia (Figures 3A, 4A); gnathosomal bay U-shaped, proximally rounded; Cxgl–4 subapical; postgenital area extended, L > 200 μm; excretory pore and Vgl–2 near the line of primary sclerotization. Gnathosoma ventral margin strongly curved, gnathosomal rostrum well developed (Figure 3D); P-2 ventral margin nearly straight or slightly convex, P-2 and P-3 ventrodistal protrusions bluntly pointed, P-4 with a ventral tubercle bearing one long and three shorter setae (Figures 3C, 4C). Male — Medial suture Cx-II+III short, suture line of Cx-IV slightly evident; genital field large, subrectangular; ejaculatory complex with large proximal chamber (Figure 3E). Female — Genital field large (Figure 4B).
Measurements — Male (holotype [CCDB_3867_E03]) — Idiosoma L 859, W 663; dorsal shield L 718, W 514, L/W ratio 1.4; dorsal plate L 673; antero-lateral platelets L 213-220, W 78-79, L/W ratio 2.7-2.8; antero-medial platelet L 138, W 60-61, L/W ratio 2.25-2.3; antero-lateral/antero-medial platelets L 1.55-1.6. Gnathosomal bay L 158, Cx-I total L 330, Cx-I mL 172, Cx-II+III mL 97; ratio Cx-I L/Cx-II+III mL 3.4; Cx-I mL/Cx-II+III mL 1.77. Genital field L/W 178/141, ratio 1.27; distance genital field-excretory pore 172, genital field-caudal idiosoma margin 239. Ejaculatory complex L 312.
Capitulum vL 323, chelicera L 370; palp total L 326, dL/H: P-1, 36/36; P-2, 107/59; P-3, 61/52; P-4, 102/33; P-5, 20/11; L ratio P-2/P-4, 1.05. dL of I-L-4-6: 111, 116, 114; I-L-6 H 42; dL/H I-L-6 ratio 2.7.
Female (paratype, CCDB_3867_E01) — Idiosoma L 978, W 759; dorsal shield L 850, W 619, L/W ratio 1.37; dorsal plate L 789; antero-lateral platelets L 234-247, W 94-97, L/W ratio 2.5-2-55; antero-medial platelets L 169-170, W 80, L/W ratio 2.11-2.14; antero-lateral/antero-medial platelets L 1.37-1.46. Gnathosomal bay L 184, Cx-I total L 363, Cx-I mL 178, Cx-II+III mL 31; ratio Cx-I L/Cx-II+III mL 11.7; Cx-I mL/Cx-II+III mL 5.7. Genital field L/W 191/174, ratio 1.09; distance genital field-excretory pore 275, genital field-caudal idiosoma margin 369.
Capitulum vL 364, chelicera L 423; palp total L 387, dL/H: P-1, 41/45; P-2, 126/70; P-3, 75/61; P-4, 120/38; P-5, 25/14; L ratio P-2/P-4, 1.05. dL of I-L-4-6: 123, 129, 127; I-L-6 H 44; dL/H ratio I-L-6 2.9.
The name of new species refers to diversity of habitats where the new species was collected and combines two Greek words: eurys (''wide″) and topos (''place″).
The final alignment for species delimitation using COI sequence data comprised 669 nucleotide positions (nps) of the 134 Torrenticola specimens listed in Supplementary material and one outgroup, Monatractides madritensis (K. Viets, 1930) from Serbia to root the tree. Genetic data indicate that all examined specimens of the new species form a unique BIN (BOLD:AED7519). The closest neighboring BIN is that of the T. similis group (BOLD:AEI3402), comprising specimens from Montenegro, Austria, and Romania. The p-distance between these two BINs was estimated at 5.69%.
The NJ tree is presented in Figure 6. In the phylogenetic tree, T. meridionalis from southern Italy was recovered as a sister clade to the T. similis group (BOLD:AEI3402). The COI sequences obtained from specimens of T. eurytopica n. sp. form a strongly supported clade, which is placed as sister to the T. meridionalis (southern Italy) + T. similis group clade.
The genetic distance between the BIN of the new species (BOLD:AED7519) and the BIN grouping T. meridionalis sequences from southern Italy (BOLD:AEK9662) was estimated at 7.18% p-distance. The mean intraspecific p-distance within the cluster of the new species was 1.35%.
The new species morphologically closely resembles T. meridionalis, with which it was previously confused in the Balkans. However, T. meridionalis can be distinguished from the new species by the absence of a characteristic dorsal shield colour pattern (Figure 5A), nearly equal lengths of P-2 and P-4 (P-2 slightly longer than P-4 in T. eurytopica n. sp.), and in males, by a stouter genital field (L/W ratio ~1.2, vs. \textgreater1.25 in T. eurytopica n. sp.).
Phylogenetic analysis based on COI data supports the distinction between the two species, revealing a high genetic divergence (COI: 7.18% p-distance) between the new species and T. meridionalis from southern Italy. This suggests a long independent evolutionary history.
The new species appears to be eurytopic, inhabiting springs and running waters at low to medium elevations (Figures 7A-C). But it has also been found in a lacustrine environment (Prespa Lake in North Macedonia; Figure 7D).
The exact distribution of the new species remains unclear due to historical confusion with T. meridionalis. However, it is likely widespread across the Balkans. Previous records of T. meridionalis from this region (e.g., Di Sabatino et al. 2003; Pešić et al. 2018, 2021, 2024b, 2025c), belonging to BOLD:AED7519, likely refer to the new species. Recently, this lineage was reported from a stream in the Babia Góra Mountain in Poland (Szenejko et al. 2023).
This group is characterized by the relatively slender rostrum and palp, longish idiosoma, and in male a short median suture of Cx-II+III and extended postgenital area.
1. Excretory pore embedded in the area of primary sclerotization
...... Torrenticola similis
— Excretory pore not embedded in the area of primary sclerotization
...... 2
2. Idiosoma slender (dorsal shield L/W ratio > 1.5)
...... Torrenticola elliptica
— Idiosoma less slender (dorsal shield L/W ratio < 1.5).
...... 3
3. Male genital field enlarged, L/W ratio ~1.20; dorsal shield without a colour pattern
...... Torrenticola meridionalis
— Male genital field more slender, L/W ratio \textgreater1.25; dorsal shield with a colour pattern
...... Torrenticola eurytopica n. sp
Most species of the water mite genus Torrenticola Piersig, 1896 in the Palaearctic region inhabit lotic environments, although some have also been reported from interstitial waters (Di Sabatino et al. 2010). Exceptionally, certain Torrenticola species have been found to colonize lentic habitats, such as pools (e.g., T. anomala; see Di Sabatino et al. 2010) or even lakes. For example, Pešić et al. (2021) reported that Balkan populations of T. meridionalis Di Sabatino & Cicolani, 1990, herein described as T. eurytopica n. sp., inhabit streams and rivers at low to medium altitudes (see also Pešić et al. 2018, 2025c), but also colonize Prespa Lake (Figure 7D), one of the oldest permanent lake systems in Europe, situated on the North Macedonia–Albania–Greece border.
Based on our current knowledge, T. eurytopica n. sp. appears to be the only member of the genus Torrenticola in the Palaearctic known to occur in both standing (lakes) and running (streams and rivers) waters. This kind of bipolar habitat preference is much more commonly observed in other water mite genera, such as Hygrobates. For example, H. nigromaculatus Lebert, 1879 and H. longipalpis (Hermann, 1804) are both widely reported as common European species inhabiting both lakes and streams. However, the status of these Hygrobates species has recently been re-evaluated using DNA barcoding, which revealed that lake and stream populations represent morphologically and genetically distinct lineages (see Martin et al. 2010 for H. nigromaculatus; Pešić et al. 2019 for H. longipalpis). All these studies, as well as our study, emphasize the importance of using molecular methods in the ecological characterization of water mite species, improving their potential for ecological quality assessment.
We thank Joanna Mąkol (Wrocław), Harry Smit (Alkmaar) and Mirela Cîmpean (Cluj-Napoca), whose constructive comments greatly improved this work.
List of Torrenticola specimens used for building the Neighbour-Joining (NJ) tree (Fig. 6). BINs are based on the barcode analysis from 1 September 2025.
acarologia_4843_Supplementary_Material.docx

