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Syrphid flies in natural grass ecosystems of some areas of the Kraishte region (Bulgaria) (Insecta, Diptera, Syrphidae) PDF

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Preview Syrphid flies in natural grass ecosystems of some areas of the Kraishte region (Bulgaria) (Insecta, Diptera, Syrphidae)

SPIXIANA Fig.1. Schemeoftheinvestigatedregionandtheecosystemsfromwhichthematerialwasgathered. thatischaracterizedbylessrainfallduringthespringandsummermonthsincomparisonwiththatof autumnand winter. AcertaindifferencebetweentheKyustendilareandtheotherstudiedareasisnotedinaccordance withthespeciescompositionofthenaturalgrassecosystems.Thegrasscommunitiesintheecosystems studiedintheareasofTrun, Breznik, Divlya,Pernikand Dupnitsaarecomposedofxeromesophytic andxerothermicgrassformationsofAgrostiscapiUaris,Festucavalesiaca,Feshicastojanovü,Chrysopogon grylliandothers.ThegrassecosystemstudiedintheareaofKyustendilisamesophyticgrassformation ofPoasilvicola (Bondev 1991). Resultsand discussion Asaresultoftheinvestigation,22speciesofsyrphidflieswerenotedin 1990and 18speciesin1991. Thetotalnumberofrecorded speciesis26. 15ofthembelongtosubfamilySyrphinaeand 11 species tosubfamilyMilesiinae.Togetherwiththe6speciesfoundbyNedjalkov(1912),the6speciesrecorded byDrenski(1934),andthe24speciesrecordedbyMarkovathenumberofsyrphidflyspeciesreported forthispartofBulgariais36.Fourspeciesarenewforthesyrphidfaunainthisregion.Theyaremarked withanasterixinthelistbelow.Foreachspeciesthenumbersoftheindividualsper1 haaregivenin brackets behind the coUection date. The recorded species are arranged after the Classification of Vockeroth(forsubfamilySyrphinae)andofThompson&Hippa(forsubfamilyMilesiinae)afterPeck (1988): 74 1. Dasysyrphuslunulatus (Meigen, 1822)* Breznik(8/28/1990:67). 2. Episyrphus balteatus (DeGeer, 1776) Trun(5/25,8/28/1990:67,133and6/1,8/3/1991:100,100);Breznik(5/25/1990:67and6/1/1991: 133);Kyustendil (5/26/1990: 67and 6/2,8/4/1991: 133,33). 3. Metasyrphuscorolne(Fabricius,1794) Breznik(5/25,8/28,10/1/1990:67,133,67and6/1,8/3/1991:33,200);Divlya(8/27,10/2/1990: 133, 200 and 8/3, 10/5/1991: 200, 100); Pernik (8/26/1990: 67 and 8/4/1991: 67); Kyustendil (8/30/1990:267and6/2,8/4/1991: 100,100);Dupnitsa(8/25/1990:133and6/2,8/4,10/6/1991: 33,33,33). 4. Metasyrphuslatifasciattis(Macquart, 1829) Breznik(8/28/1990:67). 5. Metasyrphusluniger(Meigen, 1822) Kyustendil (9/27/1990: 67and8/4/1991: 33). 6. Sphaerophoriaphilauthus(Meigen, 1822) Dupnitsa (8/4/1991:33). 7. Sphaerophoriarueppelli(Wiedemann,1830) Breznik(5/25/1990: 67);Divlya (8/27/1990: 67);Kyustendil(8/30/1990: 67and8/4/1991: 33). 8. Sphaerophoriascripta(Linnaeus, 1758) Trun(5/25,8/25,10/1/1990:200,267,400and6/1,8/3,10/5/1991:233,100,200);Breznik(5/25, 8/28, 10/1/1990: 667, 200, 133 and 6/1, 8/3, 10/5/1991: 433, 233, 167); Divlya (5/28, 8127, 10/2/1990:200,33,133and6/1,8/3,10/5/1991:167,133,67);Pernik(5/25/1990:133and6/2,8/4, 10/6/1991:67,167,33);Kyustendil(8/30,9/27/1990:67,67and6/2,8/4,10/6/1991:100,100,33); Dupnitsa (5/27, 8/25/1990: 200,267and 6/2,8/4/1991: 167, 67). 9. SyrphusvitripennisMeigen, 1822 Kyustendil(8/4/1991: 33). 10. Melanostomamellinum (Linnaeus, 1758) Trun (5/25, 8/28/1990: 133, 67 and 6/1, 8/3, 10/5/1991: 100, 100, 33); Breznik (5/25, 8/28, 10/1/1990:200,200,67and6/1,8/3,10/5/1991:100,133,133);Divlya(5/28/1990:67and6/1,8/3, 10/5/1991: 67, 33, 67); Pernik (8/26, 9/30/1990: 67, 67 and 6/2, 8/4, 10/6/1991: 33, 67, 33); Kyustendil(9/27/1990: 67and6/2,8/4, 10/6/1991: 67, 100, 167);Dupnitsa (5/27/1990: 133and 6/2,8/4, 10/6/1991: 100,33,67). 11. Platycheirusangustatus(Zetterstedt, 1843)* Breznik(8/28/1990:67). 12. Platycheirusimmarginatus(Zetterstedt, 1849) Trun (8/28, 10/1/1990: 67, 67 and 10/5/1991: 67); Breznik (5/28/1990: 133 and 6/1, 8/3/1991: 100,67). 13. Platycheiruspodagratus (Zetterstedt, 1838) Kyustendil(8/30/1990: 67). 14. Paragustibialis (Fallen, 1817) Trun(10/1/1990:67and8/3/1991:33);Breznik(10/1/1990:267and6/1,8/3, 10/5/1991:33,67, 167); Divlya (8/27/1990: 67 and 6/4, 8/3/1991: 133, 67); Pernik (8/4/1991: 33); Kyustendil (5/26/1990:67). 15. Paragusbicolor(Fabricius, 1794) Breznik(5/25,8/28/1990:67,67and6/1,8/3/1991:100,33);Divlya(8/27/1990:67and8/3/1991: 33). 16. Pipizellavirens(Fabricius, 1805)* Breznik(5/25/1990:67). 75 10-13 11 9 3 4 3 4 1990 1991 Fig. 3. Syrphid flies density in theinvestigated ecosystems. Verticalbars indicate95%,confidenceintervals for arithmeticmeans. 1.Trun; 2.Breznik; 3.Divlya; 4.Pernik; 5.Kyustendil; 6.Dupnitsa. Inthedifferentecosystemsthespeciesnumbervariesfrom6to17in1990andfrom6to11 in1991.For thewholeinvestigationperiodthemaximumspeciesnumberisfoundintheecosystemofBreznik,i.e. 17. The smallest number is that of the species estabUshed in the ecosystem ofTrun and Pernik, i.e. 7speciesineachofthem.hitheecosystemofKyustendilthespeciesnumberis13,inthatofDupnitsa9, and intheecosystem ofDivlya 8. It becomes clear that the most frequent species in the region studied in 1990 are S. scripta and M.mellinum. Theyarefound inallecosystemsand ineachsamplingperiod. Thesamespeciesinthe regionplus S.pipienswereestablishedasconstantlypermanentonlyin 1991. Permanentspecies,i.e. specieswithfrequencyover50 % oftheecosystemsinbothyearsoftheinvestigationare M. corollae andP. tibialis.Therestofthespecieshasalowerdegreeoffrequency. In 19908speciesareaccessory and 9speciesaccidental; in 1991 6speciesareaccessoryand 7speciesaccidental. Thedifferencesamongthespeciesspectraofthesyrphidfliesintheexaminedecosystemsshould beconsideredasaresultofvariousfrequencyofthespecies.ThetaxonomicCommunityofthesyrphid complexesis,withinsimilarlimits,varyingfrom23to63%in1990andfrom29to70%in1991 (Fig.2). Thesimilarityismiddleinbothyearsinmostcomplexes.ThecomplexintheecosystemofKyustendil, howeverisoutstanding,becauseitstaxonomicsimilaritywiththeothercomplexesisverylow.In1990 thetaxonomicsimilarityofthiscomplexvaried from23 to42% and in 1991 from29to38 %. Theaveragedensityofthesyrphid fliesintheexaminedecosystemspresentedduringthetimeof studyisgiveninFig.3.In1990thedensityofthesyrphidfliesiswithinthelimitsof244±75ind./ha to 1.133±128ind./ha, and in 1991 from 253±60md./ha to 811 ±101 ind./ha. During the whole investigationperiodthedensityintheecosystemofBreznikisthehighestandreliablylarger(2-3xin 1990and1.6-3.2xin1991)thanthatoftherestoftheecosystems.ThedensityintheecosystemofTrun isthesecondin1990,butin1991 thesecondisthatintheecosystemofDvipnitsa.Thedensityinthese ecosystemsisreliablylargerwiththeexceptionofPernik.Thedifferencesinthedensityoftherestof theecosystemsarestatisticallynegligible.InbothyearsthedensityoftheecosystemofPernikisproved to be the lowest. The same is also established for most of the agroecosystems studied by Pernik (Markova 1995). A differenceamong thesyrphid complexes in the variousecosystems is observed in accordance with thedensityofthepopulationsofthespecies (Fig. 4). In 1990thesimilarityamongthedifferent complexesaccordingtopopulationdensityiswithinthelimitsof16 to41 % asin9ofthevariantsit ismiddleand in6ofthem low. In 1991 itvaries from26 to46% and ismiddleinall variants. Thenumberofthedominantspecies,i.e.thespecieswithrelativenumber>10% isfrom2to5in thedifferentecosystems.Generally9speciesappeartobedominant,namely: E. balteatus,M. corollae, S.scripta,M. mellinum,P. tibialis,E.strigatiis, E.arbustoriim,C. viduataand S.pipiens. However,onlya partofthemainspecieshasaconsiderablerelativepartfromthetotalnumberofallindividuals.In1990 theseare3species,i.e.54.1 %fromallindividuals.S.scriptahasthebiggestrelativesignificance:32.7%, 77 AnideaabouttheStatusofthesyrphidcenosesinthedifferentecosystemsisalsopresentedbythe IntegrationindexofVainshtein. Summarizingtheindexes forquantitativeandqualitativesimilarity amongthesyrphidcomplexesitcanbesaidthattheindexofVainshteinvariesfrom4to24%in1990 in1991 itisslightlyhigherandvariesfrom10to32%.TheextraordinaryStatusofthecomplexinthe ecosystematKyustendilisclearlyseenespeciallyconsideringthegraphicexpressionofthebiocenotic similarityshown inFig. 5 withthehelpofClusteranalysis. Thisdeterminationisdueto theclimatic characteristicsandthedifferencesofthespeciescompositionofthenaturalgrassecosysteminthearea ofKyustendilwhichaffectsdirectlyand indirectlythequalitativeindexesofthesyrphid cenoses. Consideringthetypeofnutrition,themostrecordedspeciesbelongtothegroupofthezoophages: 16species.Thesaprophagesarerepresentedbyeandthephytophagesbyonly2species.Thezoophag- es are 73% ofall individuals, the saprophages 26%, and the phytophages only 1 %. S. scripta and M.mellimimpredominateinthecomplexofzoophagesand S. pipiens in thecomplexofsaprophages mostlydistributed intheregionofinvestigation. References Bondev,1.1991.TheVegetationofBulgaria.Map1:600.000withexplanatorytext.-"St.Kl.Ohridski"University Press,Sofia,184pp. Dazho,r. 1975. Fundamentalsofecology.-Progress,Moscow,416pp. Drenski,P. 1934. Fliesofthefam. Syrphidae(Dipt.)fromBulgaria.-Announcem. Bulg. Ent.Soc. 8: 108-131 Georgiev,M. 1985. Phisicalgeodraphy.-Science&Art,Sofia,407pp. Hotko,E.I.,S.N.Vetrova,A.Matveenko,L.S.Chumakov1982.SoilinvertebratesandindustrialpoIlution.-Sei. &Techn.,Minsk.263pp. Markova, E. (1995). Syrphid flies (Syrphidae, Diptera) in theagroecosystems ofsomekettles ofthe Kraishte region.-Ann.Univ.Sofia,Book1 -Zoology86-87:5-16 Nedjalkov,N. 1912.SixthcontributiontoentomologicalfaunaofBulgaria.-Bull.Bulg.Acad.Sei. 2: 177-218 Peek,L.V. 1988.Syrphidae.In:CatalogueofPalaeareticDiptera.-Aead.Kado,Budapest8:8-230,327-363 Pesenko, Y. A. 1982. Prineiples and methods of the quantitative analysis in faunistical studies.-Seienee, Moseow,288pp. Tishkov, C. 1982. Climatic zones. In: Geography of Bulgaria, I. Physical geography.-Bulg. Aead. Sei. Sofia: 240-247 Zlotin,R.I.1975.MountainLife(studiesonecosystemsofthetyan-shanmountains).-Mysl,Moscow,225pp. 79

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