Figure 1.

Figure 2.

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Figure 5.

Figure 6.

Figure 7.

Taxonomy of Coleopterous predators in the sample plots of Gomilshanski Lisy NNP
| Family, Species | Family, Species |
|---|---|
| Family Histeridae | Family Cantharidae |
| 1. Acritus minutus (Herbst, 1792) | 22. Malthinus flaveolus (Herbst, 1786) |
| 2. Dendrophilus punctatus (Herbst, 1792) | Family Trogossitidae |
| 3. Paromalus flavicornis (Herbst, 1792) | 23. Nemozoma caucasicum Ménétriés, 1832 |
| 4. Paromalus parallelepipedus (Herbst, 1792) | 24. Nemozoma elongatum (Linnaeus, 1761) |
| 5. Platysoma compressum Herbst, 1783 | 25. Tenebroides fuscus (Goeze, 1777) |
| 6. Teretrius fabricii Mazur, 1972 | Family Cleridae |
| Family Staphylinidae | 26. Clerus mutillarius Fabricius, 1775 |
| 7. Thoracophorus corticinus Motschulsky, 1837 | 27. Thanasimus formicarius (Linnaeus, 1758) |
| 8. Bibloporus minutus Raffray, 1914 | 28. Korynetes caeruleus (De Geer, 1775) |
| 9. Bibloporus ultimus Guillebeau, 1892 | Family Rhadalidae |
| 10. Ctenistes palpalis (Reichenbach, 1816) | 29. Aplocnemus impressus (Marsham, 1802) |
| 11. Euplectus duponti Aubé, 1833 | Family Melyridae |
| 12. Euplectus karstenii (Reichenbach, 1816) | 30. Dasytes fusculus (Illiger, 1801) |
| 13. Euplectus mutator Fauvel, 1895 | 31. Dasytes niger (Linnaeus, 1761) |
| 14. Euplectus punctatus Mulsant et Rey, 1861 | 32. Dasytes plumbeus (Müller, 1776) |
| 15. Euplectus signatus (Reichenbach, 1816) | Family Salpingidae |
| 16. Lordithon lunulatus (Linnaeus, 1760) | 33. Salpingus planirostris (Fabricius, 1787) |
| 17. Sepedophilus bipustulatus (Gravenhorst, 1802) | 34. Salpingus ruficollis Linnaeus, 1761 |
| 18. Sepedophilus immaculatus (Stephens, 1832) | 35. Vincenzellus ruficollis (Panzer, 1794) |
| 19. Tachyporus corpulentus Sahlberg, 1876 | Family Tenebrionidae |
| 20. Tachyporus dispar (Paykull, 1789) | 36. Corticeus bicolor (Olivier, 1790) |
| Family Elateridae | |
| 21. Lacon lepidopterus (Panzer, 1800) |
Predatory beetle species in the top ten by synthetic index Q for groups of sample plots and zones of Gomilshanski lisy NNP
| Species | Q | Species | Q | Species | Q | Species | Q | Species | Q |
|---|---|---|---|---|---|---|---|---|---|
| Protected zone | Clear felling | Selective sanitary felling | Zone of stationary recreation | Zone of regulated recreation | |||||
| Sal. ruficollis | 23.4 | Cl. mutillarius | 38.3 | Cl. mutillarius | 14.6 | Cl. mutillarius | 10.5 | Sal. planirostris | 18.8 |
| Sal. planirostris | 20.3 | Th. formicarius | 11.4 | Das. niger | 14.6 | P. parallelepipedus | 9.6 | N. elongatum | 9.4 |
| Pl. compressum | 19.0 | Sal. ruficollis | 7.0 | Pl. compressum | 11.9 | N. caucasicum | 9.6 | Th. formicarius | 9.4 |
| P. parallelepipedus | 18.3 | P. parallelepipedus | 5.7 | Das. plumbeus | 10.7 | N. elongatum | 9.6 | N. caucasicum | 7.0 |
| V. ruficollis | 14.6 | P. flaviciornis | 5.7 | P. parallelepipedus | 6.5 | P. flavicornis | 8.6 | P. parallelepipedus | 6.3 |
| P. flavicornis | 14.0 | Das. plumbeus | 4.6 | P. flavicornis | 6.5 | Ten. fuscus | 4.3 | Pl. compressum | 6.3 |
| Th. formicarius | 11.4 | Sal. planirostris | 2.3 | Sal. planirostris | 5.3 | Das. niger | 3.0 | V. ruficollis | 6.3 |
| Sep. bipustulatus | 8.4 | Pl. compressum | 2.3 | V. ruficollis | 3.8 | Pl. compressum | 3.0 | Sal. ruficollis | 6.3 |
| E. mutator | 4.8 | C. bicolor | 2.3 | Sal. ruficollis | 2.7 | V. ruficollis | 3.0 | E. mutator | 6.3 |
| E. karstenii | 4.6 | Thor, corticinus | 2.3 | Sep. bipustulatus | 2.7 | C. bicolor | 3.0 | Cl. mutillarius | 3.1 |
The two-proportion Z-test for pairwise comparison of predator species proportion among trapped Coleoptera across sample plots and zones in Gomilshanski lisy NNP (Clear fell_ – clear felling in the managed zone; Sel_ fell_ – selective sanitary felling in the managed zone; Stat_ recr_ – zone of stationary recreation; Reg_ recr_ - zone of regulated recreation; Prot_ – protected zone; Z0_05 = 1_96; Z0_01 = 3_96; bold Z shows the significant differences between sample plots; proportions in the parentheses)
| Sample plots | Sel. fell. (17.2 %) | Stat. recr. (15.5 %) | Reg. recr. (15.4 %) | Prot. (18.5 %) |
|---|---|---|---|---|
| Clear fell. (13.4 %) | -0.69 | -2.23 | -2.48 | -0.94 |
| Sel. fell. (17.2 %) | – | 0.31 | 0.32 | -0.23 |
| Stat. recr. (15.5 %) | – | – | 0.02 | -0.55 |
| Reg. recr. (15.4 %) | – | – | – | -0.56 |
Predatory beetle species in the top ten most frequently occurring (F) in window traps in groups of sample plots and zones of Gomilshanski lisy NNP
| Species | F | Species | F | Species | F | Species | F | Species | F |
|---|---|---|---|---|---|---|---|---|---|
| Protected zone | Clear felling | Selective sanitary felling | Zone of stationary recreation | Zone of regulated recreation | |||||
| Sal. ruficollis | 40.6 | Cl. mutillarius | 25.0 | Cl. mutillarius | 15.6 | Cl. mutillarius | 9.4 | Sal. planirostris | 18.8 |
| Pl. compressum | 34.4 | Th. formicarius | 12.5 | Das. niger | 15.6 | P. parallelepipedus | 6.3 | N. elongatum | 9.4 |
| Sal. planirostris | 34.4 | Sal. ruficollis | 9.4 | Pl. compressum | 12.5 | P. flavicornis | 6.3 | Th. formicarius | 9.4 |
| P. parallelepipedus | 28.1 | P. parallelepipedus | 6.3 | Sal. planirostris | 6.3 | N. elongatum | 6.3 | P. parallelepipedus | 6.3 |
| Th. formicarius | 21.9 | P. flavicornis | 6.3 | P. parallelepipedus | 6.3 | N. caucasicum | 6.3 | Pl. compressum | 6.3 |
| V. ruficollis | 21.9 | Das. plumbeus | 6.3 | Das. plumbeus | 6.3 | Das. niger | 3.1 | V. ruficollis | 6.3 |
| Sep. bipustulatus | 15.6 | Pl. compressum | 3.1 | P. flavicornis | 6.3 | Pl. compressum | 3.1 | Sal. ruficollis | 6.3 |
| P. flavicornis | 12.5 | Sal. planirostris | 3.1 | V. ruficollis | 3.1 | V. ruficollis | 3.1 | E. mutator | 6.3 |
| E. karstenii | 9.4 | C. bicolor | 3.1 | Sal. ruficollis | 3.1 | C. bicolor | 3.1 | Cl. mutillarius | 3.1 |
| B. ultimus | 6.3 | Thor corticinus | 3.1 | E. mutator | 3.1 | Ten. fuscus | 3.1 | N. caucasicum | 3.1 |
Similarity indices of predator complexes in groups of sample plots and zones in Gomilshanski lisy NNP
| Zone A | Zone B | Common species | Csc |
|---|---|---|---|
| Clear fell. | Sel. fell. | 7 (Sal. planirostris, Sal. ruficollis, P. flavicornis, P. parallelepipedus, Pl. compressum, Cl. mutillarius, Das. plumbeus) | 0.47 |
| Clear fell. | Stat. recr. | 5 (P. flavicornis, P. parallelepipedus, Pl. compressum, Cl. mutillarius, C. bicolor) | 0.36 |
| Clear fell. | Reg. recr. | 8 (Sal. planirostris, Sal. ruficollis, Th. formicarius, P. parallelepipedus, Pl. compressum, Cl. mutillarius, Das. plumbeus, L. lepidopterus) | 0.59 |
| Clear fell. | Prot. | 9 (Sal. planirostris, Sal. ruficollis, Th. formicarius, P. flavicornis, P. parallele-pipedus, Pl. compressum, Cl. mutillarius, Das. plumbeus, C. bicolor) | 0.53 |
| Sel. fell. | Stat. recr. | 6 (P. flavicornis, P. parallelepipedus, Pl. compressum, V. ruficollis, Cl. mutillarius, Das. niger) | 0.38 |
| Sel. fell. | Reg. recr. | 10 (Sal. planirostris, Sal. ruficollis, P. parallelepipedus, Pl. compressum, V. ruficollis, E. mutator, Cl. mutillarius, Das. niger, Das. plumbeus, Sep. bipustulatus) | 0.65 |
| Sel. fell. | Prot. | 12 (Sal. planirostris, Sal. ruficollis, P. flavicornis, P. parallelepipedus, Pl. compressum, V. ruficollis, E. mutator, Cl. mutillarius, Das. plumbeus, Sep. bipustulatus, E. duponti, Lor. lunulatus) | 0.63 |
| Stat. recr. | Reg. recr. | 7 (N. caucasicum, N. elongatum, P. parallelepipedus, Pl. compressum, V. ruficollis, Cl. mutillarius, Das. niger) | 0.48 |
| Stat. recr. | Prot. | 8 (N. caucasicum, P. flavicornis, P. parallelepipedus, Pl. compressum, V. ruficollis, Cl. mutillarius, Ten. fuscus, C. bicolor) | 0.44 |
| Reg. recr. | Prot. | 11 (Sal. planirostris, Sal. ruficollis, N. caucasicum, Th. formicarius, P. parallele-pipedus, Pl. compressum, V. ruficollis, E. mutator, Cl. mutillarius, Das. plumbeus, Sep. bipustulatus) | 0.63 |
Dominance (D) and frequency of occurrence (F) of predatory beetle species in groups of sample plots and zones of Gomilshanski lisy NNP
| Predatory beetle species | Dominance, % (D) | Frequency of occurrence, % (F) | ||||||||
|---|---|---|---|---|---|---|---|---|---|---|
| Clear fell. | Sel. fell. | Stat. recr. | Reg. recr. | Prot. | Clear fell. | Sel. fell. | Stat. recr. | Reg. recr. | Prot. | |
| A. minutus | 0.00 | 0.00 | 2.94 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 |
| D. punctatus | 0.00 | 0.00 | 0.00 | 0.00 | 0.75 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 |
| P. flavicornis | 5.17 | 6.82 | 11.76 | 0.00 | 15.67 | 6.25 | 6.25 | 6.25 | 0.00 | 12.50 |
| P. parallelepipedus | 5.17 | 6.82 | 14.71 | 6.25 | 11.94 | 6.25 | 6.25 | 6.25 | 6.25 | 28.13 |
| Pl. compressum | 1.72 | 11.36 | 2.94 | 6.25 | 10.45 | 3.13 | 12.50 | 3.13 | 6.25 | 34.38 |
| Ter. fabricii | 0.00 | 0.00 | 2.94 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 |
| Thor. corticinus | 1.72 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 | 0.00 | 0.00 |
| B. minutus | 0.00 | 0.00 | 0.00 | 0.00 | 0.75 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 |
| B. ultimus | 0.00 | 0.00 | 0.00 | 0.00 | 1.49 | 0.00 | 0.00 | 0.00 | 0.00 | 6.25 |
| Ct. palpalis | 0.00 | 2.27 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 | 0.00 |
| E. duponti | 0.00 | 2.27 | 0.00 | 0.00 | 1.49 | 0.00 | 3.13 | 0.00 | 0.00 | 3.13 |
| E. karstenii | 0.00 | 0.00 | 0.00 | 0.00 | 2.24 | 0.00 | 0.00 | 0.00 | 0.00 | 9.38 |
| E. mutator | 0.00 | 2.27 | 0.00 | 6.25 | 3.73 | 0.00 | 3.13 | 0.00 | 6.25 | 6.25 |
| E. punctatus | 0.00 | 0.00 | 2.94 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 |
| E. signatus | 0.00 | 0.00 | 2.94 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 |
| Lor. lunulatus | 0.00 | 2.27 | 0.00 | 0.00 | 1.49 | 0.00 | 3.13 | 0.00 | 0.00 | 6.25 |
| Sep. bipustulatus | 0.00 | 2.27 | 0.00 | 3.13 | 4.48 | 0.00 | 3.13 | 0.00 | 3.13 | 15.63 |
| Sep. immaculatus | 0.00 | 0.00 | 0.00 | 0.00 | 0.75 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 |
| T. corpulentus | 0.00 | 2.27 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 | 0.00 |
| T. dispar | 0.00 | 2.27 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 | 0.00 |
| L. lepidopterus | 1.72 | 0.00 | 0.00 | 3.13 | 0.00 | 3.13 | 0.00 | 0.00 | 3.13 | 0.00 |
| M. flaveolus | 0.00 | 2.27 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 | 0.00 |
| N. caucasicum | 0.00 | 0.00 | 14.71 | 15.63 | 0.75 | 0.00 | 0.00 | 6.25 | 3.13 | 3.13 |
| N. elongatum | 0.00 | 0.00 | 14.71 | 9.38 | 0.00 | 0.00 | 0.00 | 6.25 | 9.38 | 0.00 |
| Ten. fuscus | 0.00 | 0.00 | 5.88 | 0.00 | 0.75 | 0.00 | 0.00 | 3.13 | 0.00 | 3.13 |
| Cl. mutillarius | 58.62 | 13.64 | 11.76 | 3.13 | 0.75 | 25.00 | 15.63 | 9.38 | 3.13 | 3.13 |
| Th. formicarius | 10.34 | 0.00 | 0.00 | 9.38 | 5.97 | 12.50 | 0.00 | 0.00 | 9.38 | 21.88 |
| K. caeruleus | 1.72 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 | 0.00 | 0.00 |
| Ap. impressus | 1.72 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 | 0.00 | 0.00 |
| Das. fusculus | 0.00 | 0.00 | 2.94 | 0.00 | 0.00 | 0.00 | 0.00 | 3.13 | 0.00 | 0.00 |
| Das. niger | 0.00 | 13.64 | 2.94 | 3.13 | 0.00 | 0.00 | 15.63 | 3.13 | 3.13 | 0.00 |
| Das. plumbeus | 3.45 | 18.18 | 0.00 | 3.13 | 0.75 | 6.25 | 6.25 | 0.00 | 3.13 | 3.13 |
| Sal. planirostris | 1.72 | 4.55 | 0.00 | 18.75 | 11.94 | 3.13 | 6.25 | 0.00 | 18.75 | 34.38 |
| Sal. ruficollis | 5.17 | 2.27 | 0.00 | 6.25 | 13.43 | 9.38 | 3.13 | 0.00 | 6.25 | 40.63 |
| V. ruficollis | 0.00 | 4.55 | 2.94 | 6.25 | 9.70 | 0.00 | 3.13 | 3.13 | 6.25 | 21.88 |
| C. bicolor | 1.72 | 0.00 | 2.94 | 0.00 | 0.75 | 3.13 | 0.00 | 3.13 | 0.00 | 3.13 |
The Hutcheson t-test for pairwise comparison of Shannon indices across sample plots and zones in Gomilshanski lisy NNP (Clear fell_ – clear felling in the managed zone; Sel_ fell_ – selective sanitary felling in the managed zone; Stat_ recr_ – zone of stationary recreation; Reg_ recr_ – zone of regulated recreation; Prot_ – protected zone; numerator – t, denominator – p; bold t shows the significant differences between sample plots; Shannon index H is in the parentheses)
| Sample plots | Sel. fell. (2.52) | Stat. recr. (2.45) | Reg. recr. (2.46) | Prot. (2.53) |
|---|---|---|---|---|
| Clear fell. (1.61) | -4.04 / 0.0001 | -3.63 / 0.0005 | -3.72 / 0.0003 | -4.61 / 1.56E-05 |
| Sel. fell. (2.52) | – | 0.38 / 0.71 | 0.35 / 0.72 | -0.03 / 0.98 |
| Stat. recr. (2.45) | – | – | -0.03 / 0.97 | -0.48 / 0.63 |
| Reg. recr. (2.46) | – | – | – | -0.46 / 0.65 |