Nálezy podle období
Gnaphosidae 0-19001901-19501951-20002001-2021
Gnaphosa badia Gnaphosa badia (L. Koch, 1866) Silně ohrožený 16x 16x
Gnaphosa bicolor Gnaphosa bicolor (Hahn, 1833) Ohrožený 1x 2x 111x 16x 130x
Gnaphosa inconspecta Gnaphosa inconspecta Simon, 1878 Kriticky ohrožený 1x 1x 2x
Gnaphosa lapponum Gnaphosa lapponum (L. Koch, 1866) Ohrožený 34x 34x
Gnaphosa lucifuga Gnaphosa lucifuga (Walckenaer, 1802) Téměř ohrožený 5x 13x 115x 57x 190x
Gnaphosa lugubris Gnaphosa lugubris (C. L. Koch, 1839) Téměř ohrožený 3x 5x 108x 32x 148x
Gnaphosa microps Gnaphosa microps Holm, 1939 Silně ohrožený 17x 1x 18x
Gnaphosa modestior Gnaphosa modestior Kulczyński, 1897 Kriticky ohrožený 2x 2x
Gnaphosa montana Gnaphosa montana (L. Koch, 1866) Ohrožený 1x 48x 8x 57x
Gnaphosa nigerrima Gnaphosa nigerrima L. Koch, 1877 Silně ohrožený 2x 29x 31x
Gnaphosa opaca Gnaphosa opaca Herman, 1879 Ohrožený 1x 3x 107x 38x 149x

Literatura

 © Oto Zimmermann
Tato práce se věnuje arachnofauně kaolinových oprámů, kde v minulosti probíhala těžba kaolinu. Po ukončení těžebních pracích byl ve zmíněných jámách ukládán odpad z nedaleké továrny. Tyto antropogenní činnosti samozřejmě výrazně ovlivnily dnešní podobu tohoto území. Navzdory chemickému zatížení nabízí tento biotop vhodné životní podmínky pro bezobratlé živočichy. Sběr pavouků se uskutečnil za použití zemních pastí a byl doplněn individuálním sběrem. Inventarizační výzkum probíhal ve dvou sezónách, od 26. 4 2019 do 19.10 2019 a od 19.3. 2020 do 16.10. 2020. Sledované území bylo rozděleno na těsné (12 stanovišť) a širší (12 stanovišť) okolí 4 oprámů. Druhů bylo zaznamenáno celkem 148 a to ve 25 čeledích. Mezi významné nálezy spadající do kategorie VU (ohrožený) patří pavučenka Silometopus elegans, skálovka Gnaphosa lugubris, slíďáci Pardosa paludicola, Piratula knorri a Hygrolycosa rubrofasciata. Do kategorie EN (silně ohrožené) je zařazena plachetnatka Bathyphantes setiger, slíďák Alopecosa schmidti a skálovka Micaria dives.

 © Oto Zimmermann
A total of 114 spider species from 25 families and one harvestmen species were found during the zoological research at several sites in the Podyjí National Park during 2019. Of them, forty-one species are listed in the Red List of spiders of the Czech Republic. Four new species for the Podyjí NP were recorded – Callilepis nocturna (Linnaeus, 1758), Euryopis laeta (Westring, 1861), Phrurolithus minimus C. L. Koch, 1839 and Trichoncus auritus (L. Koch, 1869). Among the most interesting species, four critically endangered spiders – Civizelotes caucasius (L. Koch, 1866), Phrurolithus szilyi Herman, 1879, Gnaphosa modestior Kulczyński, 1897 and Eresus moravicus Řezáč, 2008 should be mentioned. Other rare species include Acartauchenius scurrilis (O. Pickard-Cambridge, 1873), Agyneta fuscipalpa (C. L. Koch, 1836), Arctosa figurata (Simon, 1876), Atypus affinis Eichwald, 1830, Bassaniodes robustus (Hahn, 1832), Callilepis schuszteri (Herman, 1879), Centromerus incilium (L. Koch, 1881), Centromerus leruthi Fage, 1933, Cheiracanthium effossum Herman, 1879, Drassyllus villicus (Thorell, 1875), Euryopis quinqueguttata Thorell, 1875, Frontinellina frutetorum (C. L. Koch, 1835), Gibbaranea gibbosa (Walckenaer, 1802), Gnaphosa opaca Herman, 1879, Haplodrassus cognatus (Westring, 1861), Haplodrassus dalmatensis (L. Koch, 1866), Haplodrassus minor (O. Pickard-Cambridge, 1879), Heterotheridion nigrovariegatum (Simon, 1873), Kishidaia conspicua (L. Koch, 1866), Leptorchestes berolinensis (C. L. Koch, 1846), Minicia marginella (Wider, 1834), Phrurolithus pullatus Kulczyński, 1897, Trichopterna cito (O. Pickard-Cambridge, 1873), Walckenaeria simplex Chyzer, 1894, Zelotes erebeus (Thorell, 1871) and Zora manicata Simon, 1878.

 © Oto Zimmermann
A total of 114 spider species from 25 families and one harvestmen species were found during the zoological research at several sites in the Podyjí National Park during 2019. Of them, forty-one species are listed in the Red List of spiders of the Czech Republic. Four new species for the Podyjí NP were recorded – Callilepis nocturna (Linnaeus, 1758), Euryopis laeta (Westring, 1861), Phrurolithus minimus C. L. Koch, 1839 and Trichoncus auritus (L. Koch, 1869). Among the most interesting species, four critically endangered spiders – Civizelotes caucasius (L. Koch, 1866), Phrurolithus szilyi Herman, 1879, Gnaphosa modestior Kulczyński, 1897 and Eresus moravicus Řezáč, 2008 should be mentioned. Other rare species include Acartauchenius scurrilis (O. Pickard-Cambridge, 1873), Agyneta fuscipalpa (C. L. Koch, 1836), Arctosa figurata (Simon, 1876), Atypus affinis Eichwald, 1830, Bassaniodes robustus (Hahn, 1832), Callilepis schuszteri (Herman, 1879), Centromerus incilium (L. Koch, 1881), Centromerus leruthi Fage, 1933, Cheiracanthium effossum Herman, 1879, Drassyllus villicus (Thorell, 1875), Euryopis quinqueguttata Thorell, 1875, Frontinellina frutetorum (C. L. Koch, 1835), Gibbaranea gibbosa (Walckenaer, 1802), Gnaphosa opaca Herman, 1879, Haplodrassus cognatus (Westring, 1861), Haplodrassus dalmatensis (L. Koch, 1866), Haplodrassus minor (O. Pickard-Cambridge, 1879), Heterotheridion nigrovariegatum (Simon, 1873), Kishidaia conspicua (L. Koch, 1866), Leptorchestes berolinensis (C. L. Koch, 1846), Minicia marginella (Wider, 1834), Phrurolithus pullatus Kulczyński, 1897, Trichopterna cito (O. Pickard-Cambridge, 1873), Walckenaeria simplex Chyzer, 1894, Zelotes erebeus (Thorell, 1871) and Zora manicata Simon, 1878.

 © Oto Zimmermann
Data on the spider fauna from the forest ecosystems of the Děvín National Nature Reserve (South Moravia, Czech Republic) are presented. The research was carried out on 15 randomly chosen research plots in oak-hornbeam forest stands within different management regimes. Spider sampling was done by pitfall trapping from May to October 2016. Overall, 3683 adult spiders belonging to 22 families, 70 genera and 116 species were collected. The families Linyphiidae, Lycosidae, Gnaphosidae and Thomisidae exhibited high species richness. The most abundant species were Pardosa lugubris (Walckenaer, 1802) and Trochosa terricola Thorell, 1856. Faunistically remarkable species were Atypus piceus (Sulzer, 1776), Drassyllus villicus (Thorell, 1875), Gnaphosa montana (L. Koch, 1866), Panamomops affinis Miller & Kratochvíl, 1939 and Walckenaeria monoceros (Wider, 1834). The record of Gnaphosa montana is one of the first accounts of this psychrophilic spider from European lowlands. Of the identified species, 23 are listed in the Red List of Threatened Species in the Czech Republic (EN – 1 species, VU – 12 species, LC – 10 species).

 © Oto Zimmermann
A total of 151 spider species from 27 families and 4 harvestman species from 2 families were found during the zoological research of several sites in Podyjí National Park during 2018. Seventeen of the species found are listed in the Red List of Spiders of the Czech Republic. The most interesting species are Alopecosa sulzeri (Pavesi, 1873), Amaurobius jugorum L. Koch, 1868, Araniella inconspicua (Simon, 1874), Callilepis schuszteri (Herman, 1879), Clubiona marmorata L. Koch, 1866, Echemus angustifrons (Westring, 1861), Gnaphosa lugubris (C. L. Koch, 1839), Gnaphosa opaca Herman, 1879, Gongylidiellum murcidum Simon, 1884, Haplodrassus minor (O. P.-Cambridge, 1879), Kishidaia conspicua (L. Koch, 1866), Micaria formicaria (Sundevall, 1831), Pseudeuophrys obsoleta (Simon, 1868), Saaristoa abnormis (Blackwall, 1841), Tmarus piger
(Walckenaer, 1802), Xysticus luctator L. Koch, 1870, Zelotes erebeus (Thorell, 1871) and the harvestmen Egaenus convexus (C. L. Koch, 1835).


 © Oto Zimmermann
A total of 151 spider species from 27 families and 4 harvestman species from 2 families were found during the zoological research of several sites in Podyjí National Park during 2018. Seventeen of the species found are listed in the Red List of Spiders of the Czech Republic. The most interesting species are Alopecosa sulzeri (Pavesi, 1873), Amaurobius jugorum L. Koch, 1868, Araniella inconspicua (Simon, 1874), Callilepis schuszteri (Herman, 1879), Clubiona marmorata L. Koch, 1866, Echemus angustifrons (Westring, 1861), Gnaphosa lugubris (C. L. Koch, 1839), Gnaphosa opaca Herman, 1879, Gongylidiellum murcidum Simon, 1884, Haplodrassus minor (O. P.-Cambridge, 1879), Kishidaia conspicua (L. Koch, 1866), Micaria formicaria (Sundevall, 1831), Pseudeuophrys obsoleta (Simon, 1868), Saaristoa abnormis (Blackwall, 1841), Tmarus piger
(Walckenaer, 1802), Xysticus luctator L. Koch, 1870, Zelotes erebeus (Thorell, 1871) and the harvestmen Egaenus convexus (C. L. Koch, 1835).


 © Oto Zimmermann

Members of the genus Gnaphosa belong to the largest gnaphosid spiders. They are particularly interesting in nature conservation as their distribution is mainly restricted to disappearing natural non-forest habitats. In Europe, several Gnaphosa species groups occur. The exclusively Palaearctic group G. bicolor is characterised by a retrolaterally-shifted embolus, which occupies at least part of the middle one-third of the palpal bulb; females have laterally expanded epigyne and often have very elongated median epigynal ducts (Ovtsharenko et al. 1992). So far four species of this group have been identified in Europe, with a fifth species found in Central Asia (G. tarabaevi Ovtsharenko, Platnick & Song, 1992). Two of the European species, G. bicolor (Hahn, 1831) and G. badia (L. Koch, 1866), are well known and their taxonomy and nomenclature is stable, but the same does not hold true for the other two.

The taxonomy and nomenclature of the rare European gnaphosid spiders Gnaphosa alpica and Gnaphosa modestior have been confused. Simon (1878) first described females of G. alpica from southwestern Alps. Almost twenty years later, Władysław Kulczyński described two more species, Gnaphosa modestior (single male from northeastern Croatia, and females from central Hungary and southwestern Romania) and G. laeta (single female from northeastern Hungary) (Chyzer & Kulczyński 1897), however the author expressed doubts about the species status of G. laeta and suggested that it may be an abberant female Gnaphosa modestior. Ovtsharenko et al. (1992) later published a review of the north Asian Gnaphosa, including the species from Europe, in which they come to incorrect conclusions regarding the identities of the three aforementioned species/names due to a lack of available material. Recently, we were given the opportunity to review this group of species through the study of new material. We redescribe Gnaphosa modestior and G. alpica (including designation of the lectotype and first description of a male) and describe a new, closely related species G. dolanskyi sp. n. from the southeastern Europe and adjacent regions of Asia. Further, we remove G. laeta from synonymy of G. alpica and suggest it to be a synonym of Gnaphosa modestior.


 © Oto Zimmermann

Results of the exploration of the araneofauna and the entomofauna in West Bohemian heathlands are presented. Spiders and carabid beetles were collected during the vegetation seasons in 2011 and 2012 by the method of pitfall trapping. In total, 3188 specimens of 171 Araneae species and 2168 specimens of 93 Carabid species were determined. The most frequent spiders were Xerolycosa nemoralis (Westring, 1861), a common forest species. The following identified species are listed among the endangered spiders in the Czech Republic in the category „endangered“: Alopecosa schmidti (Hahn, 1835), Micaria dives (Lucas, 1846),  Peponocranium orbiculatum (O. P.-Cambridge, 1882), in the category „vulnerable“: Centromerus incilium (L. Koch, 1881), Evansia merens O. P.-Cambridge, 1900, Metopobactrus prominulus (O. P.-Cambridge, 1872), Arctosa figurata (Simon, 1876), Arctosa lutetiana (Simon, 1876), Pardosa nigriceps (Thorell, 1872), Gnaphosa bicolor (Hahn, 1833), Xysticus striatipes L. Koch, 1870, Evarcha laetabunda (C. L. Koch, 1846) and Trichopterna cito (Blackwall, 1841). The most remarkable species of the Carabids were the Amara equestris equestris (Duftschmid, 1812), Amara pulpani Kult, 1949, Bradycellus ruficollis (Stephens, 1828), Carabus arcensis arcensis Herbst, 1784, Carabus problematicus harcyniae Sturm, 1815, Cymindis axillaris axillaris (Fabricius, 1794), Cymindis vaporariorum (Linné, 1758), Masoreus wetterhallii wetterhallii (Gyllenhal, 1813), Olisthopus rotundatus rotundatus (Paykull, 1790). Studied material was reposited at the Department of Zoology of the West Bohemian Museum in Pilsen.



 © Oto Zimmermann
Méně známé druhy pavouků – Frontinellina frutetorum; Pirata von Noldenteich; Křižák Neoscona adianta za humny!; Ještě Porrhomma; Jak je to s původem křižáka Argiope bruennichi v Česku?; Rytířský souboj; Arachnologická exkurze – jižní Morava 2015; Ocenění arachnologové; Aktualizace rolí v České arachnologické společnosti; Konference; Česká bibliografie; Britská bibliografie; Inventarizace 2014

Fotografie

Statistiky

Dle měsíce v roce


Dle nadmořské výšky


Dle metody sběru (777 použitých nálezů)
Zemní pastSamciSamiceMláďataNálezy
Gnaphosa badia (L. Koch, 1866) 92 20 0 10
Gnaphosa bicolor (Hahn, 1833) 166 73 4 91
Gnaphosa lapponum (L. Koch, 1866) 159 7 3 34
Gnaphosa lucifuga (Walckenaer, 1802) 120 53 5 57
Gnaphosa lugubris (C. L. Koch, 1839) 131 91 13 89
Gnaphosa microps Holm, 1939 419 83 0 10
Gnaphosa modestior Kulczyński, 1897 1 0 0 1
Gnaphosa montana (L. Koch, 1866) 35 11 9 36
Gnaphosa nigerrima L. Koch, 1877 14 16 0 17
Gnaphosa opaca Herman, 1879 167 100 37 52
NeurčenoSamciSamiceMláďataNálezy
Gnaphosa badia (L. Koch, 1866) 2 2 0 3
Gnaphosa bicolor (Hahn, 1833) 6 1 2 22
Gnaphosa inconspecta Simon, 1878 0 0 0 2
Gnaphosa lucifuga (Walckenaer, 1802) 65 68 2 110
Gnaphosa lugubris (C. L. Koch, 1839) 20 18 5 43
Gnaphosa microps Holm, 1939 28 4 0 1
Gnaphosa montana (L. Koch, 1866) 1 2 0 10
Gnaphosa nigerrima L. Koch, 1877 1 4 0 5
Gnaphosa opaca Herman, 1879 139 144 9 81
Individuální sběrSamciSamiceMláďataNálezy
Gnaphosa badia (L. Koch, 1866) 1 3 0 3
Gnaphosa bicolor (Hahn, 1833) 4 7 1 10
Gnaphosa lucifuga (Walckenaer, 1802) 9 18 3 21
Gnaphosa lugubris (C. L. Koch, 1839) 7 11 0 14
Gnaphosa microps Holm, 1939 2 7 0 3
Gnaphosa modestior Kulczyński, 1897 0 1 0 1
Gnaphosa montana (L. Koch, 1866) 2 8 0 10
Gnaphosa nigerrima L. Koch, 1877 7 3 0 3
Gnaphosa opaca Herman, 1879 6 16 0 14
ProsevSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 3 0 3 3
Gnaphosa lucifuga (Walckenaer, 1802) 0 1 0 1
Gnaphosa microps Holm, 1939 0 1 0 1
Gnaphosa nigerrima L. Koch, 1877 14 5 0 6
Gnaphosa opaca Herman, 1879 1 0 0 1
SmykSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 8 2 0 4
Gnaphosa lucifuga (Walckenaer, 1802) 17 4 0 1
Gnaphosa lugubris (C. L. Koch, 1839) 1 1 0 2
Gnaphosa microps Holm, 1939 6 1 0 3
Gnaphosa montana (L. Koch, 1866) 0 1 0 1
Gnaphosa opaca Herman, 1879 1 2 0 1
 SamciSamiceMláďataNálezy

Dle biotopu (777 použitých nálezů)
NeurčenoSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 8 2 1 26
Gnaphosa inconspecta Simon, 1878 0 0 0 2
Gnaphosa lucifuga (Walckenaer, 1802) 156 111 2 133
Gnaphosa lugubris (C. L. Koch, 1839) 37 66 5 54
Gnaphosa montana (L. Koch, 1866) 8 5 0 18
Gnaphosa nigerrima L. Koch, 1877 3 7 0 7
Gnaphosa opaca Herman, 1879 146 145 9 84
Skalní stepi na vápenciSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 1 0 0 1
Gnaphosa lucifuga (Walckenaer, 1802) 13 5 1 17
Gnaphosa lugubris (C. L. Koch, 1839) 58 22 13 41
Gnaphosa opaca Herman, 1879 123 82 32 30
Suché loukySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 0 1 0 1
Gnaphosa lucifuga (Walckenaer, 1802) 26 15 6 24
Gnaphosa lugubris (C. L. Koch, 1839) 37 14 0 26
Gnaphosa opaca Herman, 1879 35 28 3 26
RašeliništěSamciSamiceMláďataNálezy
Gnaphosa badia (L. Koch, 1866) 92 19 0 9
Gnaphosa lapponum (L. Koch, 1866) 10 0 0 5
Gnaphosa microps Holm, 1939 455 95 0 17
Gnaphosa montana (L. Koch, 1866) 1 2 0 6
Gnaphosa nigerrima L. Koch, 1877 13 15 0 15
alpínské trávníkySamciSamiceMláďataNálezy
Gnaphosa lapponum (L. Koch, 1866) 149 7 3 29
Gnaphosa montana (L. Koch, 1866) 1 0 0 1
Lesostepní doubravySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 48 24 0 17
Gnaphosa lucifuga (Walckenaer, 1802) 2 0 0 2
Gnaphosa lugubris (C. L. Koch, 1839) 6 9 0 9
Suché doubravySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 28 13 0 19
Gnaphosa lucifuga (Walckenaer, 1802) 7 5 0 2
Gnaphosa lugubris (C. L. Koch, 1839) 3 2 0 2
Gnaphosa opaca Herman, 1879 0 1 0 1
PasekySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 6 6 0 6
Gnaphosa lucifuga (Walckenaer, 1802) 1 0 0 1
Gnaphosa lugubris (C. L. Koch, 1839) 2 2 0 2
Gnaphosa montana (L. Koch, 1866) 8 6 0 9
Acidofilní borySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 33 11 5 15
Gnaphosa lugubris (C. L. Koch, 1839) 3 2 0 2
Kamenité suti nižších polohSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 21 7 0 9
Gnaphosa lugubris (C. L. Koch, 1839) 2 1 0 2
Gnaphosa montana (L. Koch, 1866) 2 2 0 4
Výsadby jehličnanůSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 6 2 0 3
Gnaphosa montana (L. Koch, 1866) 13 4 9 12
Stinné skály nižších polohSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 10 2 1 6
Gnaphosa lucifuga (Walckenaer, 1802) 0 2 0 2
Gnaphosa lugubris (C. L. Koch, 1839) 2 0 0 1
Gnaphosa montana (L. Koch, 1866) 0 1 0 1
Gnaphosa opaca Herman, 1879 5 1 0 2
Přirozené lesySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 12 5 0 9
Xerotermní travinobylinná společenstvaSamciSamiceMláďataNálezy
Gnaphosa lucifuga (Walckenaer, 1802) 1 0 0 1
Gnaphosa lugubris (C. L. Koch, 1839) 1 2 0 2
Gnaphosa modestior Kulczyński, 1897 1 0 0 1
Gnaphosa opaca Herman, 1879 5 3 2 4
KamenolomySamciSamiceMláďataNálezy
Gnaphosa lucifuga (Walckenaer, 1802) 4 5 1 6
Gnaphosa opaca Herman, 1879 0 1 0 1
Mokré loukySamciSamiceMláďataNálezy
Gnaphosa nigerrima L. Koch, 1877 6 5 0 6
Suťové a roklinové lesySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 5 1 0 4
Gnaphosa lugubris (C. L. Koch, 1839) 3 0 0 1
Gnaphosa montana (L. Koch, 1866) 0 1 0 1
Reliktní bory na skaláchSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 1 2 0 3
Gnaphosa lugubris (C. L. Koch, 1839) 1 1 0 2
Lesní okrajeSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 0 1 3 3
Gnaphosa lugubris (C. L. Koch, 1839) 1 0 0 1
LesySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 1 1 0 2
Gnaphosa montana (L. Koch, 1866) 1 1 0 2
Louky a pastvinySamciSamiceMláďataNálezy
Gnaphosa lucifuga (Walckenaer, 1802) 1 0 0 1
Gnaphosa lugubris (C. L. Koch, 1839) 1 0 0 1
Břehy tekoucích vodSamciSamiceMláďataNálezy
Gnaphosa badia (L. Koch, 1866) 0 2 0 2
Luční ostřicové mokřadySamciSamiceMláďataNálezy
Gnaphosa microps Holm, 1939 0 1 0 1
Gnaphosa nigerrima L. Koch, 1877 2 0 0 1
Suché křovinySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 2 1 0 2
RuderálySamciSamiceMláďataNálezy
Gnaphosa lucifuga (Walckenaer, 1802) 0 1 0 1
Gnaphosa modestior Kulczyński, 1897 0 1 0 1
DubohabřinySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 2 0 0 1
Gnaphosa montana (L. Koch, 1866) 2 0 0 1
Skalní a suťové biotopySamciSamiceMláďataNálezy
Gnaphosa badia (L. Koch, 1866) 2 1 0 2
Kukuřičná poleSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 1 1 0 1
Lužní lesy nížinSamciSamiceMláďataNálezy
Gnaphosa nigerrima L. Koch, 1877 3 1 0 1
Porosty borůvekSamciSamiceMláďataNálezy
Gnaphosa nigerrima L. Koch, 1877 9 0 0 1
LoukySamciSamiceMláďataNálezy
Gnaphosa badia (L. Koch, 1866) 0 0 0 1
Bučiny nižších polohSamciSamiceMláďataNálezy
Gnaphosa montana (L. Koch, 1866) 1 0 0 1
Horské smrčinySamciSamiceMláďataNálezy
Gnaphosa badia (L. Koch, 1866) 1 1 0 1
Okraje silnicSamciSamiceMláďataNálezy
Gnaphosa lugubris (C. L. Koch, 1839) 1 0 0 1
Mezofilní loukySamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 1 1 0 1
Těžebny písku a jiných nezpevněných horninSamciSamiceMláďataNálezy
Gnaphosa bicolor (Hahn, 1833) 1 2 0 1
Suché lesní lemySamciSamiceMláďataNálezy
Gnaphosa lugubris (C. L. Koch, 1839) 1 0 0 1
Výsadby listnáčůSamciSamiceMláďataNálezy
Gnaphosa montana (L. Koch, 1866) 1 0 0 1
Skalní stepi na jiných hornináchSamciSamiceMláďataNálezy
Gnaphosa opaca Herman, 1879 0 1 0 1
Lesy vyšších poloh a strmých svahůSamciSamiceMláďataNálezy
Gnaphosa badia (L. Koch, 1866) 0 2 0 1
 SamciSamiceMláďataNálezy