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The arthropod community of Scots pine (Pinus sylvestris L.)
canopies in Norway
Karl H. Thunes*, John Skartveit, Ivar Gjerde, Josef Star�, Torstein Solhøy, Arne Fjellberg,
Sverre Kobro, Sueo Nakahara, Richard zur Strassen, Gijsbertus Vierbergen, Ryszard
Szadziewski, Daniel V. Hagan, William L. Grogan Jr., Terje Jonassen, Kjetil Aakra, Johannes
Alexandr F. Emeljanov, Per Douwes, Kai Berggren, Jutta Franzen, R. Henry L. Disney,
Sabine Prescher, Kjell A. Johanson, Boris Mamaev, Sigitas Podenas, Stig Andersen, Stephen
D. Gaimari, Emilia Nartshuk, Geir E. E. Søli, Laszlo Papp, Fred Midtgaard, Arild Andersen,
Michael von Tschirnhaus, Gerhard Bächli, Kjell M. Olsen, Hans Olsvik, Mihály Földvári, Jan
E. Raastad, Lars O. Hansen & Per Djursvoll
Thunes, K. H., Skartveit, J., Gjerde, I., Star�, J., Solhøy, T., Fjellberg, A., Kobro,S., Nakahara, S., zur Strassen, R., Vierbergen, G., Szadziewski, R., Hagan, D. V.,Grogan Jr., W. L., Jonassen, T., Aakra, K., Anonby, J., Greve, L., Aukema, B.,Heller, K., Michelsen, V., Haenni, J.-P., Emeljanov, A. F., Douwes, P., Berggren,K., Franzen, J., Disney, R. H. L., Prescher, S., Johanson, K. A., Mamaev, B.,Podenas, S., Andersen, S., Gaimari, S. D., Nartshuk, E., Søli, G. E. E., Papp, L.,Midtgaard, F., Andersen, A., von Tschirnhaus, M., Bächli, G., Olsen, K. M.,Olsvik, H., Földvári, M., Raastad, J. E., Hansen, L. O. & Djursvoll, P. 2004: Thearthropod community of Scots pine (Pinus sylvestris L.) canopies in Norway. —Entomol. Fennica 15: 65–90.
We summarise the findings of arthropods collected by fogging the canopy of 24pine trees in two sites in Eastern and Western Norway. From the samples, taken in1998 and in 1999, almost 30,000 specimens were determined to 512 species, withDiptera being most species rich (210 species), followed by Coleoptera (76 spe-cies) and Araneae (49 species). Of the 96 new species records, nine were new toscience (5 Diptera and 4 Oribatida), two were new to the European, three to theScandinavian and 82 to the Norwegian faunas. The paper demonstrates the needfor detailed faunistical inventories of European forests.
K. H. Thunes (correspondent author) and I. Gjerde, Norwegian Forest ResearchInstitute, Fanaflaten 4, N-5244 Fana, Norway; Email: [email protected]. Aakra, P. Djursvoll, L. Greve, K. A. Johanson and J. Skartveit, University ofBergen, Museum of Zoology, P.O. Box 7800, N-5020 Bergen, NorwayJ. Starý, Institute of Soil Biology, Academy of Sciences of the Czech Republic, Nasádkách 7, CZ-37005 �eské Bud�jovice, Czech RepublicT. Solhøy, University of Bergen, Department of Biology, P. O. Box 7800, N-5020Bergen, NorwayA. Fjellberg, Mågerøveien 168, N-3145 Tjøme, NorwayA. Andersen and S. Kobro, The Norwegian Crop Research Institute, Plant
Protecion Centre, Høgskolevn 7, N-1432 Ås, NorwayS. Nakahara, Systematic Entomology Laboratory, Agricultural Research Ser-vice, USDA, Beltsville, Maryland 20705-2350, U. S. A.R. zur Strassen, Entomologie 1, Forschungsinstitut Senckenberg, Senckenberg-Anlage 25, D-60325 Frankfurt am Main, GermanyB. Aukema and G. Vierbergen, Plant Protection Service, Entomology Section,P.O. Box 9102, 6700 HC Wageningen, The NetherlandsR. Szadziewski, Department of Invertebrate Zoology, University of Gdansk,Pilsudskiego 46, 81-378 Gdynia, PolandD. V. Hagan, Department of Biology, Institute of Arthropodology & Parasitol-ogy, Georgia Southern University, Statesboro, GA 30460-8042, U. S. A.W. L. Grogan Jr., Department of Biological Sciences, Salisbury State University,Salisbury, Maryland 21801, U. S. A.T. Jonassen, N-4170 Sjernarøy, NorwayJ. Anonby, N-6863 Leikanger, NorwayK. Heller, Norddeutsche Strasse 60, D-24143 Kiel, GermanyS. Andersen and V. Michelsen, Zoological Museum, Universitetsparken 15, DK-2100 Copenhagen, DenmarkJ.-P. Haenni, Museum d’Histoire Naturelle, Rue des Terreaux 14, CH-2000Neuchatel, SwitzerlandA. F. Emeljanov, Zoological Institute, Russian Academy of Sciences, St.Peters-burg 199034, RussiaP. Douwes, COB, Zoologen, Helgonavägen 3, S-223 62 Lund, SwedenK. Berggren, Bråvann terasse 21, N-4624 Kristansand S, NorwayJ. Franzen, Im Baumgarten 9, D-51105 Köln, GermanyR. H. L. Disney, University of Cambridge, Department of Zoology, Downing St.,Cambridge CB2 3EJ, U. K.S. Prescher, Hinter der Masch 26, 38114 Braunschweig, GermanyB. Mamaev, All Russian Continuous Educ. Forestry, Inst. Kaya Str. 17,Pushchino 141200, Moscow region, RussiaS. Podenas, University of Vilnius, Faculty of Natural Sciences, Ciurliono St.21/27, LT-2009 Vilnius, LithuaniaS. D. Gaimari, California State Collection of Arthropods, Plant Pest DiagnosticsBranch, California Department of Food and Agriculture, Sacramento, Califor-nia 95832-1448, U. S. A.E. Nartshuk, Zoological Institute, Russian Academy of Sciences, St. Petersburg199034, RussiaL. O. Hansen, J. E. Raastad and G. E. E. Søli, Zoological Museum, University ofOslo, Sarsgt. 1, N-0562 Oslo, NorwayM. Földvári and L. Papp, Hungarian Natural History Museum, Dept Zool,Baross Utca 13, H-1088 Budapest, HungaryF. Midtgaard, Norwegian Forest Research Institute, Høgskoleveien 12, N-1432Ås, NorwayM. von Tschirnhaus, Universität Bielefeld, Fakultät für Biologie, D-33501Bielefeld, GermanyG. Bächli, Zoological Museum, University of Zürich-Irchel, Winterthurerstrasse190, CH-8057 Zürich, Switzerland
66 Thunes et al. • ENTOMOL. FENNICA Vol. 15
K. M. Olsen, Biological Institute, University of Oslo, P. O. Box 1066 Blindern, N-0316 Oslo, NorwayH. Olsvik, N-6598 Foldfjorden, NorwayJ. Skartveit, Environmental Research Group, Scottish Agricultural College, AyrCampus, Auchincruive, Ayr KA6 5HW, Scotland
Received 3 February 2003, accepted 9 February 2004
1. Introduction
With the development of new methods in theearly 1970’s to access tree canopies, the study ofarboreal arthropod communities changed fromguesswork to highly accurate scientific stan-dards. Deforestation especially in tropical re-gions encouraged scientists concerned withbiodiversity loss, conservation issues, ecologyand systematics to document the species and eco-logical systems associated with the largest pro-portion (by volume) of the forests, viz. the forestcanopies. As a consequence, currently a large ar-ray of methods exist to gain access to the canopy,ranging from aerial trams and systems of ropes,pulleys and ladders to methods using insecticidefogging. While the arboreal arthropod forest-can-opy research still is in its infancy, it has neverthe-less documented a highly specialised fauna virtu-ally wherever carried out. The number of arthro-pod species that may exist on Earth is continu-ously being discussed; partly as a consequence ofrecent canopy studies, the most optimistic esti-mates suggest a number as high as 50–80 millionspecies (Erwin 1982, 1988, 1991, May 1988,Stork 1988). However, more modest global spe-cies richness estimates, also based upon canopystudies in the tropics, suggest a number of speciesas low as three million (e.g. Ødegaard 2000).
While the faunistics of several conifer specieshave been investigated to some extent, the associ-ated fauna of pine canopies, particularly in Eu-rope, is rather poorly known (Höregott 1960,Basset 1985, Borkowski 1986, Tenow & Larsson1987, Cmoluchowa & Lechowski 1993, Simandl1993, Bankowska 1994, Chobotow 1994, Chole-wicka-Wisniewska 1994a, b, Czechowska 1994,Kolodziejak 1994, Sterzynska & Slepowronski1994, Wasowska 1994, Docherty & Leather1997, Brändle & Rieger 1999, Gunnarsson et al.1999, Aakra 2000, Hagan et al. 2000, Ozanne et
al. 2000, Thunes et al. 2003). Moreover, most ofthese studies do not present a complete coverageof the fauna at a specific time, as only parts of thecanopy were sampled, sampling had been ex-tended over a very long period of time or sampleswere not identified to species for all groups.
This study is the first attempt to inventory thearboreal arthropod fauna associated with Scotspine (Pinus sylvestris L.) in Scandinavian forest.It was initiated in 1998 as part of a larger bio-diversity program, Miljøregistrering i Skog,funded by the Norwegian Ministry of Agri-culture. This paper will focus on the faunistics,whereas other papers investigate in more depthecological aspects of major arthropod groups (e.g. Hagan et al. 2000, Hauge & Nielsen 2001,Thunes et al. 2003). We present the complete listof identified taxa found in the investigated pinecanopies, with ecological discussion on the mostimportant species. Also, as many of the taxa iden-tified in this study rarely are treated in other sur-veys, the number of rarely recorded species is un-usually high. Thus, a general discussion of rarityand red lists is given.
2. Material and methods
2.1. Study sites
The study was carried out in two forest sites inNorway (Fig. 1). One site, Geitaknottane inKvam municipality (Hordaland County, 5°53’ E,60°05’ N, 180–200 m a.s.l.), was a Pinus syl-vestris dominated coastal forest with scatteredJuniperus communis, Sorbus aucuparia andBetula pubescens. The other site, Heimseteråsenin Sigdal municipality (Buskerud County, 9°25’E, 60°03’N, 400–450 m a.s.l.), was a P. sylvestrisdominated boreal forest where also B. pubescensand Picea abies were abundant. Additional site
ENTOMOL. FENNICA Vol. 15 • Arthropods of Scots pine canopies 67
details can be found in Ihlen et al. (2001) andThunes et al. (2003).
2.2. Data collection
In Kvam, we sampled six trees between 26 and 29May in 1998. In Sigdal, a total of 18 trees werefogged: six trees between 5 and 9 June in 1998and 12 additional trees between 19 June and 17July in 1999. To sample the arthropods, we used1% synthetic pyrethroid (PySekt), dissolved innon-aromatic white spirit. While standing on theground, we emitted the solution using a motorisedcanopy fogger (Swingfog 50) that heats up thegas that consequently rises into the canopy as avisible fog. It is, then, easy to observe if the entiretree has been treated. To avoid drift-away of thefog and to minimise disturbance, all trees weretreated before dawn after a windless and drynight.
Increment core samples were taken in order toage each tree. We then separated the samples to befrom either old (250+ years) or mature (70–110years) trees.
Clean plastic funnels (diameter 30 cm) wereexamined for unwanted taxa, and placed concen-trically on the ground to collect arthropods fallingfrom the fogged canopies. Circles of funnels wereplaced 0.5 m apart from each other. Within eachcircle, the funnels were 1.0 m apart at Kvam, and
0.5 m apart from each other at Sigdal. The funnelsremained on the ground for ca. one hour after fog-ging. Material collected from a given circle waspooled into one container, representing the sam-ple from that circle.
Almost all the arthropods were identified tospecies by the following authors who also pro-vided some faunistical information of the respec-tive groups. John Skartveit – Coleoptera andDiptera: Lonchaeidae, Bibionidae, Pseudopomy-zidae, Scatopsidae and Blattodea. Josef Star� andTorstein Solhøy – Oribatida. Arne Fjellberg –Collembola. Sverre Kobro, Sueo Nakahara,Richard zur Strassen and Gijsbertus Vierbergen –Thysanoptera. Ryszard Szadziewski, Daniel V.Hagan and William L. Grogan Jr. – Diptera:Ceratopogonidae. Terje Jonassen – Diptera: Hy-botidae, Empididae and Dolichopodidae. KjetilAakra – Araneae. Johannes Anonby –Psocoptera. Lita Greve – Diptera: Lonchaeidae,Lauxaniidae, Acroceridae and Pallopteridae,Raphidioptera and Planipennia. Berend Aukema– Hemiptera: Heteroptera. Kai Heller – Diptera:Sciaridae. Verner Michelsen – Diptera: Antho-myiidae, Muscidae, Fannidae, Calliphoridae andSarcophagidae. Jean-Paul Haenni – Diptera:Scatopsidae. Alexandr F. Emeljanov – He-miptera: Auchenorrhyncha. Per Douwes – Hy-menoptera: Formicidae. Kai Berggren – Lepi-doptera. Jutta Franzen, R. Henry L. Disney andSabine Prescher – Diptera: Phoridae andSphaeroceridae. Kjell A. Johanson – Epheme-roptera, Plecoptera and Trichoptera. Boris Ma-maev – Diptera: Cecidomyiidae. Sigitas Podenas– Diptera: Tipulidae, Limoniidae and Pediciidae.Stig Andersen – Diptera: Tachinidae. Stephen D.Gaimari – Diptera: Chamaemyiidae. Emilia Nart-shuk – Diptera: Chloropidae. Geir E. E. Søli –Diptera: Mycetophilidae. Laszlo Papp – Diptera:Acartophthalmidae, Borboropsidae and Mili-chiidae. Fred Midtgaard – Hymenoptera: Sym-phyta. Arild Andersen – Diptera: Agromyzidae.Michael von Tschirnhaus – Diptera: Agro-myzidae. Gerhard Bächli – Diptera: Droso-philidae. Kjell M. Olsen – Chilopoda. HansOlsvik – Odonata. Mihály Földvári – Diptera:Pipunculidae. Jan E. Raastad – Diptera: Simu-liidae. Lars O. Hansen – Hymenoptera: Vespidae.Per Djursvoll – Diplopoda.
The following taxa were not identified to spe-
68 Thunes et al. • ENTOMOL. FENNICA Vol. 15
Fig. 1. The study areas.
cies level due to the lack of taxonomical expertiseor time restrictions. Diptera: Chironomidae andsome minor families, Hymenoptera: Parasiticaand some Aculeata except ants, and Acari exceptOribatida. The majority of the material will be de-posited in the collections of the Norwegian ForestResearch Institute, Ås. Some collaborators re-tained voucher specimens for the collections oftheir own institutions. Type material of two spe-cies of Diptera: Ceratopogonidae that were de-scribed from this material (Szadziewski & Hagan2000) is deposited in the University of Gdansk,Poland. Six additional species (four Acari:Oribatida, two Diptera: Cecidomyiidae) awaitdescription and will subsequently be deposited inthe Academy of Sciences of the Czech Republicand the Russian Academy of Sciences, St. Peters-burg, Russia, respectively.
2.3. Assignment of new faunistical records
and central references for ecological
information
To assign Diptera species as new records ismostly based on the information by Papp andDarvas (1997, 1998), but also on considerationsand recommendations from the authors. For othergroups, a species is assigned a new record alsowhen it is represented in collections but is yet, toour knowledge, to be published.
We present here a list of articles used in thespecies record chapter below. Araneae – Roberts(1987, 1995), Aakra (2000) and Hauge & Nielsen(2001). Oribatida – Wunderle (1992) and Prin-zing & Wirtz (1997). Collembola – Prinzing(1997), Prinzing & Wirtz (1997) and Hågvar &Fjellberg (2002). Hemiptera – Wagner (1952,1966), Southwood & Leston (1959), LeQuesne(1960, 1965), Péricart (1972), Ossiannilsson(1978–1983) and LeQuesne & Payne (1981).Psocoptera – New (1974), Prinzing & Wirtz(1997) and Lienhard (1998). Thysanoptera –Lewis (1973) and Mound et al. (1976). Raphi-dioptera and Planipennia – Aspöck et al. (1980)and Plant (1997). Lepidoptera – Heath (1976),Emmet (1979), Skinner (1984), Skou (1984) andL. Aarvik (pers. comm). Diptera – Chvála (1975),Miller (1977), d’Assis Fonseca (1978),McAlpine (1987), Greve (1993), Chvála (1994),
The complete list of species is presented in theAppendix and in Figs. 2–3. Altogether 29,736specimens were identified to 512 species. Ninety-six species were new to the Norwegian fauna (78Diptera; 10 Oribatida, 3 Araneae, 2 Thysa-noptera, 2 Hymenoptera and 1 Psocoptera) (Table1). Of these, nine species were new to science;two ceratopogonid midges have recently been de-scribed by Szadziewski and Hagan (2000). In ad-dition, three of these species were new records forScandinavia and two were new European re-cords. One Diptera family, Borboropsidae, wasrecorded from Norway for the first time.
As conifer needles are a relatively poor nitro-gen source, compared to leaves, and the epiphyticcover is almost negligible in these forests, com-pared to old-growth conifer forests of westernUnited States and Canada, we did not expect avery high number of specimens (Schowalter et al.1988, Recher et al. 1996, Winchester & Ring1996b). Nevertheless, in the 24 trees, Oribatidawas the most abundant taxon with 8,532 speci-mens (29.0% of the total invertebrate catch), fol-lowed by Collembola (19.9%) and Diptera(19.8%) (Fig. 3a). When ranked, these numbersare very close to results from similar studies car-ried out in temperate and tropical regions (e. g.Ammer & Schubert 1999, Fagan & Winchester1999, Palacios-Vargas et al. 1999).
Diptera and Coleoptera were the two mostspecies rich groups in both study areas (Fig. 2).Altogether they comprised almost 50% of thenumber of species (alpha diversity) collected in1998. In 1999, the percentage represented by
ENTOMOL. FENNICA Vol. 15 • Arthropods of Scots pine canopies 69
these taxa was even higher (59%). Spiders, whichhave been shown to be very abundant in canopies,did not exceed 10% of the species in either Kvamor Sigdal (Fig. 2b–d), and the number of speci-mens was very low (Fig. 3b–d). While Dipteraconstituted one-third of the specimens collectedin Kvam (Fig. 3b), the thysanopterans constitutedmore than one-third (36%) of the Sigdal materialcollected in 1998, with the dipterans representedby less than one-fifth (17%).
It is particularly interesting to see the drasticchange from 1998 to 1999 in the material fromSigdal (Fig. 2c–d); the proportion of Thy-sanoptera was more than quartered while the pro-portion of Oribatida was doubled. The proportionof Diptera and Collembola in the samples wasstrikingly similar between the two years.Thysanoptera, Collembola, Oribatida andDiptera made up 94% of all specimens sampledfrom Sigdal in 1998, while the same groups con-stituted 84% in 1999. Thysanoptera dominatedthe 1998 samples (36%), while Oribatida playedthe most important role in 1999 (37%).
3.2. Species records
3.2.1. Araneae
Three species, viz. Entelecara flavipes (Black-wall), Theridion pinastri L. Koch and Dipoenatorva (Thorell), of totally 49 species were new re-cords for Norway. The faunistics of spiders is rel-atively well known in Norway (K. Aakra, pers.comm.), and even though the three species werefound in low numbers, both D. torva (an ant pred-ator) and T. pinastri are species known to be asso-ciated with pine forests. Aakra (2000) presentsdetails on the Araneae found in this study.
While Minyriolus pusillus (Wider), Poca-dicnemis pumila (Blackwall), Tenuiphantesalacris (Blackwall), Pardosa lugubris (Wal-ckenaer) and Neon reticulatus (Blackwall) mostlikely are visitors, most of the other species aretypical conifer forest species. Particular speciesrecords worth mentioning as pine associated spe-cies are Clubiona subsultans Thorell and Ro-bertus scoticus Jackson that are only known from
70 Thunes et al. • ENTOMOL. FENNICA Vol. 15
Fig. 2. Proportions of species. – a. Total, years combined. – b. Kvam. – c. Sigdal in 1998. – d. Sigdal in 1999.
pine forests, even though both species are pre-dominantly ground living.
Furthermore, Philodromus collinus C. L.Koch lives on lower branches of trees, especiallyconifers, while Atea sturmi (Hahn) is associatedwith evergreen trees and bushes. Walckenaeriadysderoides (Wider) is usually found in pine nee-dles and moss. Likewise, Dismodicus elevatus(C. L. Koch) is usually found on conifers.Philodromus margaritatus (Clerck) (on the barkof lichen-covered trees) and Moebelia penicillata(Westring) (in crevices on tree trunks) were com-monly found species that, we believe, do not usepines as a prime habitat. Two species, Entelecaracongenera (Cambridge) and Dendryphantesrudis (Sundevall) were found in Norway for thesecond time. The last time D. rudis was collectedwas in 1875.
3.2.2. Oribatida
The five most abundant oribatid species,Phauloppia lucorum (C. L. Koch), Cymbere-
maeus cymba (Nicolet), Camisia segnis (Her-mann), Hemileius initialis (Berlese) andCarabodes labyrinthicus (Michael), constituted96.1% of the total oribatid material. These spe-cies, except for H. initialis, are known arborealspecies. Further known arboreal species areCarabodes ornatus Storkan, C. willmanni Ber-nini, Paraleius leontonycha Travé, Phauloppiacoineaui Travé, P. saxicola Travé, Micreremusbrevipes (Michael), Diapterobates humeralis(Hermann) and possibly Steganacrus magnus(Nicolet). The remaining species are known tolive predominantly in other habitats than cano-pies.
3.2.3. Collembola
Thirty-four Collembola species were found, andnone of these was new to the Norwegian fauna;instead, all species are considered common.Lepidocyrtus lignorum (Fabr.) and Entomobryanivalis (L.) were the dominating species, consti-tuting over 90% of the total material. It is note-
ENTOMOL. FENNICA Vol. 15 • Arthropods of Scots pine canopies 71
Fig. 3. Proportions of specimens. – a. Total, years combined. – b. Kvam. – c. Sigdal in 1998. – d. Sigdal in 1999.
72 Thunes et al. • ENTOMOL. FENNICA Vol. 15
Table 1. List of new species records, with their preferred habitat association when known. Number of species in
each group is given in parentheses. “?” = habitat unknown,1= species described from the current material.
Higher taxon Species name Habitat
Species new to scienceAcari: Oribatida (4) Hypodamaeus sp. n. ?
Oribatula sp. n. ?Phthiacarus sp. n. (nr. 1) ?P. sp. n. (nr. 2) ?
Diptera: Cecidomyiidae (2) Lestodiplosis sp. n. ?Sitodiplosis sp. n. ?
worthy that 98% of the specimens of Hypo-gastrura socialis (Uzel) were sampled from onesingle tree in Sigdal in 1998. The species isknown for its aggregation behaviour and is oftenreported undertaking large mass migrations onthe forest floor.
3.2.4. Hemiptera
Of the 18 species found, none were new to theNorwegian fauna. Moreover, the following spe-cies are to varying extent associated with pine:Plesiodema pinetella (Zetterstedt) and Phoeni-
ENTOMOL. FENNICA Vol. 15 • Arthropods of Scots pine canopies 73
cocoris obscurellus (Fallén) commonly occur onboth pine and spruce, whereas both species ofAcompocoris, Elatophilus nigricornis (Zetter-stedt) and Gastrodes grossipes (DeGeer) are pineassociated. Aguriahana germari (Zetterstedt) isoliphagous on Pinus species. Oncopsis flavicollis(L.), Cixius similis (Kirschbaum) and Speudo-tettix subfusculus (Fallén) are associated withseveral habitats, and we suspect them to be occa-sional visitors.
3.2.5. Psocoptera
Valenzuela burmeisteri (Brauer), V. despaxi(Badonnel), Enderleinella obsoleta (Stephens),Cuneopalpus cyanops (Rostock) and Steno-psocus lachlani Kolbe are closely associated withconifers, as some of them are typical conifer-as-sociated species known to feed on fungal spores,algae and lichens growing on conifers. Interest-ingly, one female nymph of Valenzuela gy-napterus (Tetens) was collected; females of thisspecies are wingless and extremely rarely col-lected. Moreover, V. burmeisteri is known tooverwinter as egg. However, we sampled twoadult specimens as early as late May and earlyJune, possibly indicating that it also overwintersas nymph or imago. One species, Dorypteryxdomestica (Smithers), was recorded from Nor-way for the first time (J. Anonby in prep.).Liposcelis silvarum (Kolbe) is the only free-liv-ing Norwegian species of a genus otherwiseknown for its several domestic species (the“book-lice”). The flattened body may be an adap-tation to life under flakes of bark on tree trunks,habitat for several Central and Southern Euro-pean species. Rather few finds of L. silvarum areknown from Norway. Its abundance in our mate-rial, particularly in the inner parts of the canopy,suggests that the species prefers the tree trunk andinner parts of the branches, where it is not readilycollected by the “beating tray” most often usedfor Psocoptera sampling. It has not previouslybeen found in Western Norway; together with itsabsence on the British Isles, this supports an ideathat the species prefers dry climate.
3.2.6. Thysanoptera
Of fourteen species of thrips, two were new to the
Norwegian fauna, namely Aeolothrips vittatusHaliday and Acanthothrips nodicornis (Reuter).Twenty-nine A. vittatus individuals were found inSigdal, and it is likely to be a canopy specialist, asit is believed to be a predator in Pinus and Picea.In addition to A. vittatus, both Oxythrips speciesand Thrips pini (Uzel) are pine-living species.Hoplothrips ulmi (Fabricius), A. nodicornis andHoplandrothrips williamsianus Priesner are allassociated with saprophytic fungi. Many speciesof thrips are also known to use pine crevices asoverwintering habitats.
3.2.7. Raphidioptera and Planipennia
All but one species, viz. Coniopteryx pygmaeaEnderlein, were sparsely represented in this ma-terial. C. pygmaea is a conifer specialist, often ag-gregating in pine and spruce, where the larvaeprey upon mites. Other pine-associated speciesinclude Raphidia ophiopsis (L.), Conwentziapineticola Enderlein, Parasemidalis fuscipennis(Reuter), Sympherobius fuscescens (Wallen-gren), Hemerobius nitidulus Fabricius and H.stigma Stephens.
3.2.8. Lepidoptera
Almost the entire moth sample was collected aslarvae, and most of the species are also known tofeed directly on needle material. In the list of spe-cies (Appendix), the following species that in-clude all the common species are ubiquitous pinespecialists: Hylaea fasciaria (L.), Heterotherafirmata (Hübner), Thera obeliscata (Hübner),Panolis flammea (Denis and Schiffermueller),Exotelia dodecella (L.), Ocnerostoma piniarellaZeller, O. friesei Svensson, Sphinx pinastri L. andCedestis subfasciella (Stephens).
3.2.9. Diptera
Seventy-eight of the 210 dipterous species(37.1%) were new to the Norwegian fauna. Ofthese, five were new to Scandinavia, one new toEurope and five new to science. Among theDiptera, the lesser known families Cerato-pogonidae and Phoridae showed an extraordinaryhigh number of new faunistical records. Of the 78new records, 44 were ceratopogonids (56.4%),
74 Thunes et al. • ENTOMOL. FENNICA Vol. 15
including two species new to science, and tenspecies (12.8%) of Phoridae were new to the Nor-wegian fauna, with one new to science. In addi-tion, the following families had new records:Sciaridae (eight, including Cratyna as a new ge-nus), Cecidomyiidae (three, including two newspecies), Empididae (two), Anthomyiidae,Lonchaeidae, and Chloropidae with two specieseach, and Borboropsidae (new family record),Milichiidae, Drosophilidae, Acartophthalmidaeand Pediciidae with one species each (Appendix).Thus, by fogging 24 pine trees, our sampleshosted almost 2.2% new records to the Norwe-gian fauna [numbers based on Ottesen (1993)].
Because no Diptera larvae were identified, itis difficult to assign specific host associations.However, based on the limited information avail-able for many dipterous groups, the followingtaxa are probably associated with pine to someextent: all the species of Chamaemyiidae fromthis study are predators associated with pine liv-ing Adelgidae (Aphididae) in the genus Pineus.Although there are no relevant biological recordsfor the lauxaniid species Minettia lupulina (F.) inthe Palaearctic, several species of Minettia s. str.have been reared as saprophages from decayingcones and club tops of various gymnosperms, in-cluding species of Pinus. Moreover, the sciaridsCtenosciara hyalipennis (Meigen) and Epidapusgracilis (Walker) are very numerous in coniferforests. The hybotid species Tachypeza nubila(Meigen) and Medetera of the familyDolichopodidae are commonly found on treetrunks. Empis (Anacrostichus) lucidus (Empi-didae) is known to copulate on the branches onconiferous trees. Members of the genus Lon-chaea (Lonchaeidae) and Palloptera usta(Meigen) (Pallopteridae) and Medetera (Doli-chopodidae) are associated with bark beetles. Theceratopogonid midge Forcipomyia nigransRemm has been collected on rotting pine debris.The two species of Lasiomma (Anthomyiidae),Mydaena sootryeni Ringdahl (Muscidae) andFannia verrallii (Stein) (Fannidae) are extremelyrarely collected by conventional insect collectingmethods. Even though they are not abundant inour material, their presence indicates an associa-tion with canopies beyond accidental visits. Fi-nally, the phorid genus Menozziola is an antparasitoid and may parasitize arboreal ants.
3.2.10. Hymenoptera
Two species of Symphyta, Pristiphora conicepsLindquist and P. pallidiventris Fallén, were newto the Norwegian fauna. The former species is as-sociated with Salix, while the latter is associatedwith species in the family Rosaceae. The fewspecimens found, suggest no obligatory relation-ship with pines whatsoever. Xyela julii(Brebisson) is strictly associated with pine how-ever, as it feeds from pollen of male pine flowers.All the sampled species of Formica and Lasiusare common species in conifer forests.
3.2.11. Coleoptera
The majority of the beetle species recorded aresomehow linked to Scots pine, either inhabitingor feeding on dead or living trees, or on other in-sects associated with the trees. The five species ofDromius found are all arboreal. D. angustusBrullé is apparently confined to pine in Scandina-via, while D. fenestratus (Fabricius) and D.schneideri Crotch occur mainly on pine. D. agilisFabricius can be found on a wide range of trees.Other pine associates are Ernobius nigrinus(Sturm) which lives in pine shoots, Rhagonychaelongata (Fallén), Cryptophagus angustusGanglbauer, C. dorsalis Sahlberg, Brachonyxpineti (Paykull), Pissodes piniphilus (Herbst),Scymnus suturalis Thunberg, Exochomusquadripustulatus (L.) and Sphaeriestes casta-neus. The coccinellids found are all species of co-nifer woodlands. Myrrha octodecimguttata (L.)and Myzia oblongoguttata (L.) are particularlyfound in the crowns of mature Scots pines.
4. Discussion
A few species present may indicate some degreeof pollution of either the water used to dilute thealcohol, Calluna specialists entering the funnelsfrom the ground or specimens brought with thefunnels from the storage. The aquatic Limnozetesrugosus Sellnick (Oribatida) is probably presentdue to contaminated water. Hyledelphax ele-gantula (Boheman) (Auchenorrhyncha) mightalso be a contaminating species, because it is con-sidered as being associated with Calluna heaths
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and Vaccinium wood glades. Dorypteryx do-mestica (Psocoptera) was probably hidden in thefunnels prior to sampling, because this domesticspecies has previously been unknown fromnature.
4.1. Are the pine canopies that special?
Based on results from temperate and tropicalstudies, canopies represent a unique hotspot forinvertebrate biodiversity (e.g. Winchester & Ring1996a, b, Stork et al. 1997, Walter et al. 1998).Pine canopies seem to be no exception, but theirimportance is missed at the conventional sam-pling height of 1.5–2 m. However, broadleaf spe-cies such as Quercus, Fagus, Betula and Salixhave been shown to be comparably much richer(Overgaard Nielsen 1975, Overgaard Nielsen &Ejlertsen 1977, Gjelstrup 1979, Southwood et al.1982, Ammer & Schubert 1999). Nevertheless,510 species, almost 30,000 specimens and almost20% [(96 new spp. / 512 spp. altogether)*100]new species to the national fauna sampled withina total time span of roughly 24 hours is a veryhigh ’revenue’ compared to any conventionalmethod and sampling regime. It is, however, im-portant to take into consideration that many, if notmost of the taxa with new records are disregardedor assigned to morphospecies in most studies,usually because of the lack of taxonomic exper-tise or small budgets granted to species identifica-tion. Moreover, species richness per se does notnecessarily tell much about the uniqueness of thecanopy fauna for a given species of tree. Compli-mentary species, i.e. those that are not found else-where, may be more important to be consideredwhen comparing relatively species-poor pinetrees with e.g. oak.
Probably the most advantageous feature ofcanopy fogging is that one can be certain of theorigin of the material; even ’tourists’ are defi-nitely present in the canopy upon sampling. Onecannot ascertain, however, that the entire materialis obligatorily associated with canopies per se,and wood borers and several phytophagous spe-cies (e. g. miners) are underrepresented in thiskind of material. Even if they are killed by the in-secticide fog, they will remain inside their habitat.However, many dipterous species use overhang-
ing branches or the canopy as reference pointsduring swarming (Chvála 1983, 1990). Conse-quently, a number of species not directly associ-ated with canopies, such as Euthyneura myrtillii,will be over-represented in such material, ascorroborated by the high proportion of males inour material.
4.2. How valuable are faunistical lists?
This study demonstrates how little we knowabout the arthropod fauna in temperate forests.Huge efforts have been put into documenting thefauna and flora of tropical rain-forest canopies,but so much information awaiting to be revealedis hidden also within temperate forests. Many ofthe species we collected in the present study areclearly associated with pine trees, but most of thespecies are not. This raises a critical question tohow we set a price on natural values. The red listsof species are often used as an alibi for habitatconservation or perhaps more commonly the op-posite, habitat destruction: if only a few currentlyred-listed species are present in one area, its valueis lower than the value of another area with morered-listed species. In Norway, the only red-listedarthropod groups are spiders, beetles, Lepi-doptera and some minor groups, mainly aquaticinsects. Apart from these groups, none of the spe-cies-rich groups in forests are faunistically orecologically well known enough to be included inthe list. Counting both number of species andspecimens, these groups (with beetles as an ex-ception) are most abundant in the pine forest, atleast in canopies, the part of the forest making upthe largest proportion of its volume. Paradoxi-cally, because of the lack of taxonomists, thesegroups are rarely studied, and because of the lackof studies, their significance is neglected. How-ever, the present paper, representing the first stepof describing the canopy fauna of pine trees inNorway, substantiates the need for further basicfaunistical surveys and studies.
Acknowledgements. The project was financed by the Nor-wegian Ministry of Agriculture. We also acknowledge theEnvironmental Research Group of the Scottish Agricul-tural College, Scotland.
76 Thunes et al. • ENTOMOL. FENNICA Vol. 15
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Appendix. List of species. New records are marked with an asterisk. Species marked with asterisk(s) in paren-
theses are new records but have been published separately from this material. The numbers under Kvam, Sig-
dal 1998 and Sigdal 1999, respectively, are the actual numbers of specimens sampled of that particular species.