Vadonia soror Holzschuh, 1981
publication ID |
https://doi.org/ 10.11646/zootaxa.5541.2.3 |
publication LSID |
lsid:zoobank.org:pub:F891D73F-3DAE-452E-84D0-824CB3B05585 |
DOI |
https://doi.org/10.5281/zenodo.14284728 |
persistent identifier |
https://treatment.plazi.org/id/F50A87C1-1821-4B03-FF7B-FE16FB682E8C |
treatment provided by |
Plazi |
scientific name |
Vadonia soror Holzschuh, 1981 |
status |
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Vadonia soror Holzschuh, 1981 View in CoL
Specimens Examined: Denizli: Çivril , 9.VI.2021, 38°11'51"N, 29°34'37"E, 1093 m, 2♂, Leg. B. Şabanoğlu GoogleMaps ; UŞak: Karahallı , 9.VI.2021, 38°24'07"N, 29°30'21"E, 738 m, 21♀, 1♂, Leg. M. Kabalak GoogleMaps .
Distribution in Türkiye: Adana, Antalya, Burdur, Denizli, İçel, Karaman, Osmaniye ( Özdikmen, 2022)
Male genitalia ( Fig. 4 G View FIGURE 4 ): Total length of aedeagus 3.1 mm. Median lobe is strongly curved especially along the struts in lateral view, median struts separated up to medio-proximal. Median lobe slightly outward proximally, with wavy lateral edges. Median lobe with a triangular apex, an enlarged median orifice, and triangular edge of the median foramen. Tegmen with a vague roof part. Lateral lobes of tegmen converged at a slight angle inward, fingerlike shaped, 4.58 times longer than width; with orangeish hairs at apex. Ring part basally separated, parallel from base to distal, curved distally.
Spermatheca ( Fig. 3 c View FIGURE 3 ): Spermatheca 0.25 mm, moderately chitinized; body convex basally, curving inward apically.
Stenurella bifasciata ( Müller, 1776) was the most abundant species collected, with 175 individuals followed by Pseudovadonia livida Danilevsky, 2013 ) with 137 individuals. Other abundant species included Stictoleptura fulva with 75 individuals. The species with the fewest individuals were Anastrangalia sanguinolenta , Leptura aurulenta , and Stictoleptura rufa ( Table 2 View TABLE 2 ).
Ecological studies on habitat preferences and sampling methods ( Table 2 View TABLE 2 ), revealed that Rhv-In (Herbaceous vegetation near fields and roads-Insect net) had the greatest species diversity, followed by Shp-In (Herbaceous vegetation near streams-Insect net), F-Pt (Forest-Pheromone trap)and Fghv-In (Forest ground herbaceous vegetation-Insect net) ( Fig. 7 View FIGURE 7 ).
Field studies were conducted from April to October, with additional specimens collected by various researchers. When analyzed by month; 11 species were recorded in May, 14 in June, 16 in July, and two in August ( Fig. 8 View FIGURE 8 ). Lepturini species appear to be are most active in May, June, and July, with the fewest species collected in August, likely due to rising temperatures. One species was recorded only in May, three only in June, and four only in July ( Table 2 View TABLE 2 ).
Specimens were also divided by altitude (250-meter intervals) The most species were recorded between 751– 1000m (13 species), followed by 1251–1500m (12 species), 251-500m, 501–750m, and 1001–1250m (11 species each), 0–250m (6 species), 1501–1750m (3 species), and 1751–2000m (1 species) ( Fig. 9 View FIGURE 9 ).
Species | Vertical Distributions | Sampling Months | Specimens | Sampling Habitats-Methods | Distribution in Türkiye | Zoogeographical Distributions |
---|---|---|---|---|---|---|
Anastrangalia montana | B,C,D | M-J | 11 | Rhv-In | MtR, AR, CAR, MR | E, A |
Anastrangalia sanguinolenta | F | Jul | 1 | Rhv-In | MtR, EAR, CAR BR, MR | E, A, NTR |
Alosterna tabacicolor | C,D | M-J | 4 | Rhv-In; Shv-In | MtR AR BR, MR | E, A |
Anoplodera rufipes lucidipes | B | J | 2 | Rhv-In | AR, MR | ENDEMIC |
Etorofus pubescens | B,C,D | J-Jul | 17 | Rhv-In; Shv-In | MtR AR CAR BR | E, A |
Leptura quadrifasciata | D,E,F | Jul-A | 3 | Shv-In; F-Pt | MtR, EAR, CAR BR, MR | E, A |
Leptura aurulenta | C | Jul | 1 | F-Pt | MR, BR | E, A, N |
Pachytodes erraticus | C,D,E,F | M-Jul | 24 | Rhv-In; Shv-In | MtR EAR, AR, CAR, BR, MR | E, A |
Pedostrangalia emmipoda | A,B,C,D,E | M-J-Jul | 15 | Rhv-In; Shv-In | MtR EAR, AR, SAR, CAR | E, A |
Pedostrangalia verticenigra | A,F | M-Jul | 3 | Rhv-In; Shv-In | MtR, EAR, BR | E, A |
Pseudovadonia livida | A,B,D,E,F,G,H | M-J-Jul | 137 | Rhv-In; Shv-In | MtR, EAR, AR, SAR, CAR BR, MR | E, A |
Rutpela maculata | B,D,F | J-Jul | 7 | Rhv-In | MtR, EAR, CAR, BR, MR | E, A |
Stenurella bifasciata | A,B,C,D,E,F,G | M-J-Jul | 175 | Rhv-In | MtR, AR, CAR, BR, MR | E, A |
Stenurella septempunctata | B,C,D,E,F | M-J-Jul | 50 | Rhv-In | EAR, AR, CAR, BR, MR | E, A |
Stenurella afyoncayensis sp.n. | F | Jul | 8 | Rhv-In; Shv-In | AR | ENDEMIC |
Stictoleptura cordigera | B,C,D,E | J-Jul | 56 | Rhv-In | MtR, EAR, AR, SAR, CAR, BR, MR | E, A, N |
Paracorymbia fulva | A,B,C,E, F,G | M-J-Jul-A | 75 | Shv-In | MtR, EAR, AR, CAR, BR, MR | E, A |
Stictoleptura rufa | D | J | 1 | Rhv-In | MtR, EAR, AR, BR | E, A |
Paracorymbia excisipes | E | M | 2 | Rhv-In | MtR, AR | A |
Strangalia attenuata | F | Jul | 8 | Fghv-In | EAR, BR, MR | E, A |
Vadonia unipunctata | A,B,D,E,F | M-J-Jul | 36 | Rhv-In; Shv-In | MtR, EAR, AR, CAR, BR, MR | E, A |
Vadonia soror | C,E | J | 4 | Rhv-In | AR | ENDEMIC |
No known copyright restrictions apply. See Agosti, D., Egloff, W., 2009. Taxonomic information exchange and copyright: the Plazi approach. BMC Research Notes 2009, 2:53 for further explanation.
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