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Numbers and types of arthropods overwintering on common mullein, Verbascum thapsus L. (Scrophulariaceae), in a central Washington fruit-growing region PDF

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Preview Numbers and types of arthropods overwintering on common mullein, Verbascum thapsus L. (Scrophulariaceae), in a central Washington fruit-growing region

J.ENTOMOL.SOC.BRIT.COLUMBIA100,DECEMBER2003 79 Numbers and types of arthropods overwintering on common mullein, Verbascum thapsus L. (Scrophulariaceae), in a central Washington fruit-growing region DAVID R. HORTON and TAMERA M. LEWIS USDA-ARS, 5230KONNOWAC PASSRd.,WAPATO,WA, UNITED STATES98951 ABSTRACT Densitiesandtypes ofarthropodsoverwinteringon common mullein, Verbascumthapsus L., in a fruit-growing region of Central Washington were determined. Over 45,000 arthropods were collected from 55 plants (5 plants from each of 11 sites), dominated numericallybyAcari andThysanoptera. Insectsrepresenting 8 orders and29 familieswere identified, distributedboth in thebasal leafrosettes and inthe stalkmaterial oftheplants. One specialist insect herbivore of mullein, the mullein thrips, Haplothrips verbasci (Osbom), was abundant at all sites. Several pest and predatorytaxathat commonlyoccur in orchards were also collected, suggestingthat mullein maybe a source ofoverwintered pests or predators moving into orchards in early spring. Pest taxa included primarily western flowerthrips {Frankliniella occidentalis (Pergande)), Lygus spp., andtetranychid spidermites. Common predators includedphytoseiidmites andminutepiratebugs {Orius tristicolor (White)). Sites that were geographically close to one another were not more similar (in taxonomic composition of overwintering arthropods) than more distantly separated sites. Key words: common mullein, overwintering, orchardpests, predatoryarthropods,mullein thrips, western flowerthrips, Orius tristicolor, mites INTRODUCTION Commonmullein, Verbascum thapsus L. (Scrophulariaceae), is abiennial herb native to Eurasia (Munz 1959) but now common throughout North America. The species occurs in open waste areas, along fence lines, in overgrazed pastures, and along river bottoms, often found growing in large single-species stands. Common mullein has a biennial life cycle, germinatingfromseedoftennearclunps ofthe deadparentalplants. Inthe firstyear, theplant develops as a rosette ofsoft, bluish-gray leaves which are densely covered with silky hairs. The followingyear, a stout, leafystalk is sentup fromthe centerofthe rosette, oftenreaching m a height ofmore than 2 inmid-summer. At the top ofthe stalk is a spike having 100-200 yellow flowers which are inbloomseveral at a time formuch ofthe summer. There is a great deal of interest in managing or conserving non-agricultural habitats adjacentto agriculturalhabitats to enhancebiological control orto reduce infestationofcrops by pest species (Pickett and Bugg 1998; Ekbom et al. 2000). In Pacific Northwest fruit growing regions, commonmullein often is abundant ontheperimeterofpome and stonefruit orchards. Theplantisknowntoharborimportantpests oftree fruits duringthe growing season (Thistlewood et al. 1990; Krupke et al. 2001), but it also is an important source ofcertain predators (e.g., Campylomma verbasci(Meyer), the mulleinbug) thatmayprovidebiological control of aphids and mites during the growing season. Less information is available concerninguse ofmulleinbypests andpredators as anoverwintering habitat(McAtee 1924). It is important to understand late winter and early spring population dynamics ofpests and predators in pear and apple orchards, as that time ofyear is often crucial for pest control. Thus, we need also to understand the overwintering biology ofarthropods both inside and outside ofthe orchard, including a determination ofwhere pests and predators overwinter 80 J.ENTOMOL.SOC.BRIT.COLUMBIA100,DECEMBER2003 (Hortonand Lewis 2000; Hortonetal 2002). McAtee (1924), inMaryland, conducteda cursorysurveyofthe insects associatingwith common mullein, and found that the dense basal rosette ofleaves provided overwintering habitat for several taxa ofarthropods, including both pest and predatory insects. Thus, in addition to being a source ofpest and beneficial arthropods during the summer and fall growing season, commonmulleinmayalsobe a source ofoverwintered arthropods moving into Central Washington orchards in late winter and early spring. Objectives ofthe present studywere to determine types anddensities ofarthropods overwinteringoncommonmullein ina fruit-growingregion ofCentral Washington. The studywas designedtoprovide amore thoroughlookatthe arthropodcommunities inmulleinthanprovidedbyMcAtee (1924), and toprovidedataforawestemUSpopulationofmullein. Wealsocomparedtypesandnumbers ofarthropods overwintering inthebasalrosette ofleaves to numbers andtypes occurring in the leaves, dried flowers, and seed capsules ofthe stalk. Lastly, we looked for geographic patterns in the taxonomic composition ofarthropod communities overwintering in mullein, testing the hypothesis that arthropod communities wouldbe more similarbetween sites that occurgeographicallynearone anotherthanbetween sites thatwere more widelyseparated. MATERIALS AND METHODS The study was done in and adjacent to Yakima, Washington, USA. Eleven sites, each having stands offullymature commonmullein, were selectedinNovember2000 forsampling. Plants that were sampled had bloomed the previous summer and were composed ofdead leaves andseed-ladenstalks atthe time ofcollection. Allofthe sites were alongroadsides that occurred immediatelyadjacentto orchardhabitatorwithin 1 kmoforchardhabitat. Straight- line distancesbetween sites rangedbetween0.5 to46.4 km. InDecember 2000 and January 2001, we collected five fully mature plants (1.5 to 1.8 m tall) from each site by cutting the plantsjustbeneath the soil surface. Plants wereplaced in large plastic bags for transportto the laboratory. Bags and plants were placed in a large walk-in cooler (2 ''C) until the arthropodswereextracted. To extractthe arthropods, theplantmaterialwasdistributedamong 25 Berlese-TuUgrenfunnels (Southwood 1980), keepingstalks and leafrosettes separate. We used 40 watt lightbulbs to force the arthropods into 75% ethanol. Arthropods were thenseparated fromtheplantdetritusbyfirstslowlypouringthe alcohol throughveryfine (0.2 x0.2 mm) organdymesh. Themeshappearedto capture allbutthevery smallest mites (mostly immature Tydeidae and Tenuipalpidae). These specimens were discarded withoutbeing identified, thus summaries providedbelow forAcari underestimate total numbers of certain small-bodied taxa. The arthropods remaining on the mesh were removed fromthe meshandplantdetritus withforceps, insectpins, orsmallpaintbrushes, and transferredto fresh 75% ethanol for later counting and identification. Insects other than Lepidoptera (all ofwhich were in the caterpillar stage) and parasitic Hymenoptera were identified at least to family. Known important predators and pests in orchards were identified to species. Most samples contained very large numbers of Thysanoptera, anditwasnotfeasibleto identifyeachspecimen. A subsampleof50thrips was removed fromeachsample foridentificationto genusbeneatha dissectionmicroscope, using the key ofMound and Kibby (1998). Immature thrips were not classified. Results for the subsample were thenextrapolatedbackto thefullsampletoprovideestimatesoftotalnumbers ofthrips for each genus. Representative examples ofeach genus were sent to an expert in thrips identification(Steve Nakahara; Beltsville, MD) to confirmour identifications. Mites were veryabundantinthe leafrosettes andmuchlessabundantinthe stalkmaterial, thus we limited acarine identificafions to those mites inhabiting the leaf rosettes. The identificationswere confinedto sixofthe 11 sites. We firstseparatedGamasida fromthe total sample, for laterexamination. Fromthe remaining sample, a subsampleofapproximately 50 , J.ENTOMOL.SOC.BRIT.COLUMBIA100,DECEMBER2003 81 to 500mites(dependingupontotalnumbers inthe sample) weremountedinHoyer's solution onmicroscope slides (Krantz 1978). The mites were then identified to genus (Tetranychus spp. only) orto familyunder a compoundmicroscope usingkeys inKrantz (1978). Counts for Tetranychus spp. were then extrapolated back to the total sample to obtain estimates of absolute densities for Tetranychus spp. Fromthe Gamasidawhole sample, subsamples of25 to 85 miteswerethentakenforthose siteshavinglargenumbers ofgamasidmites(>90mites). The mites were mounted on slides in Hoyer's solution and identified to family (all but Phytoseiidae) orto species(Phytoseiidae). Species identifications forthe Phytoseiidae were made using keys in Schuster and Pritchard (1963) and Chant et al (1974). We then extrapolatedresults forthe subsamplebacktothe full Gamasidasample toprovide estimates ofabsolutenumbers forphytoseiid species. Straight-line distances between sites were obtainedusing a Vista globalpositioning unit (Garmin; Olate, KS). Wetestedwhethersitesthatwere geographicallynearone anotherwere more similar than those more distantly separated by calculating taxonomic (family-level) similaritybetweenallpossible sitepairs, using the following formula: Relative absolute distance = ^Absolute value [(%/^Xy)- {xnJ^Xy^t)] wherej and k are two sites, is the abundance ofthe insect family at sitey, and xn^ is abundance ofthe insect family at site k (Ludwig and Reynolds 1988). The analysis was limitedto families ofInsecta. The indexvariesbetween0 and2, with0 indicatingmaximum similarityand 2 indicating complete dissimilaritybetweenthe two sites. RESULTS Atotalof46,712 arthropods wascountedfromthe 11 sites, ofwhich44.7%were collected fromthe leafrosettes and the remaining 55.3% were collected from the stalk material. The sampleswere dominatednumericallybytheThysanoptera andAcari(Table 1), accounting for over90% ofthe arthropods frombothleafand stalkmaterial. Forthe Insecta, 29 families in 8 orders were identified, withspeciesofThysanoptera, Coleoptera, andHeteropterabeingthe most abundant. There was considerable site-to-site variation in counts (Table 1, Range) for virtuallyall commontaxa. ' Miteswereveryabundantinthe leafrosettes(exceeding 500per5-plantsample) andmuch less abundantinthe stalkmaterial(Table 1). Specimens fromleafrosettes atsixofthe 11 sites were identified, andwere foundto include large numbers ofGamasida andActinedida (Table I 2). Gamasida were composedprimarilyofPhytoseiidae, including some importantpredatory I species (Amblyseius spp.; Typhlodromus caudiglans Schuster; western predatory mite, I Galendromusoccidentalis (Nesbitt)). Spidermites(Tetranychidae) were relativelyuncommon (Table 2), and includedprimarily Tetranychus spp. (47 of64 tetranychids in subsamples). Thysanoptera included two families, Thripidae and Phlaeothripidae (Table 1), the latter apparentlybeingrepresentedbya single species, Haplothrips verbasci(Osbom), the mullein thrips. This species was very abundant inboth stalks and leafrosettes, reaching densities of over800 adultsperstalkatone site. Thripidae included species ofThrips (apparentlymostly ThripstabaciLindemanbutincluding T.fallaciosusNakahara), Caliothrips, andFrankliniella (apparentlyall western flowerthrips, F. occidentalis (Pergande)). Homoptera were composed primarily ofaphids and psyllids (Table 1), including pear psylla, Cacopsylla pyricola (Foerster), a pest of pears. Heteroptera were dominated numericallybyAnthocoridae andMiridae (Table 1). The 75 Tingidae thatwere collected all occurred inthe leafrosettes ata single site. Anthocoridae were almost exclusively minute piratebug, Orius tristicolor(White) (164 total specimens), but includedalso five specimens ofXylocoris umbrinus VanDuzee. Overwintering Coleoptera were dominated numerically 1 H 1 82 J.ENTOMOL.SOC.BRIT.COLUMBIA100,DECEMBER2003 Table 1 Mean(averagedover 11 sites)numbers ofarthropodsper5 mulleinplantsinleafrosettes and stalkmaterial. Numbers inparentheses indicate percentage oftotal arthropods composedof that taxon [(tr) indicates less than 0.1%]. Range shows minima and maxima across the 1 sites. Familymeans maynotsumto ordermeans due topresence ofunidentifiedarthropods inthatorder (particularlytrue forThysanoptera, forwhich immatures were notidentified). Leaf rosettes Stalks ItIC^II IIUlllUvl9 i.TlC<tll llUlllUvi3 npr^nl$intc nprSnIfinfK ^^^^ 123-1455 34.0(1.4) 3-167 111^3(11IVJJJICIa 1i^2y6jy6j.Qy^y\6j\6j.7/^j 30-3936 2263 5C96 S^k 210-5516 11111L/lvJuV^ 515.6 0-2362 590.4 49-1655 1IlldCUUlIipiUdC 7106 2S 16^2 1i4to67/.SJ fxAui.1lA nUliHJ|JlCIa 1 2Q 4 Sf'O2^ /ApillUlUdC J.J 0yj-114 06 0\j-1j ("'prpf^niflap 0.1 0-1 0.0 0 l^lLaUCIllUaC yj.j n 1 00 AU rayiuuac t.J 0 14 J3.8O 0u-oR Het6roptera 30.5 (1.6) 4-87 8.9(0.4) 0-32 Anthocoridae 7.5 0-22 7.7 0-30 Delyuuac 0v.11 0 1 0\).\0J A\j Lygaeidae 1.6 0-16 0.0 0 IVl11IVJUV.' 10.6 0-64 0.8 0-6 0.1 0-1 0.0 0 1ClUalUIIllUaC 06 00 A\j RIvpHiLliVvi11iLiHdpep 0.1 0-1 0.0 0 RivlhInVrJ\L/^dlliIHv;J^up^ 2.3 0-12 0.1 0-1 T1i1n1ic^jiirlU^a^cp 6.8 0-75 0.0 0 Colcoptera JJ.OV 11-1107 jj.jyy.'^) 0-70 Anthicidae nu.nu AU n 1 n 1 07 0-1 0.0 0 r(\JrC*CrI*iHnCplllliIHUcajCp 0U.JS n 1 00 Au \^UnIr\y7i1uripniHll1Ur1cipC 57 0 37 0.6 0-6 27.5 1 130 32.5 6-98 Dermestidae 0.0 0 0.1 0-1 Staphylinidae 0.8 0-3 0.0 0 Neuroptera 0.5 (tr) 0-2 0.1 (tr) 0-1 Hemerobiidae 0.5 0-2 0.1 0-1 Lepidoptera 3.9(0.2) 0-17 0.3(tr) 0-2 Diptera 2.7(0.1) 0-16 0.4(tr) 0-2 Cecidomyiidae 1.5 0-11 0.2 0-2 Chironomidae 0.2 0-2 0.1 0-1 Mycetophilidae 0.1 0-1 0.0 0 Syrphidae 0.1 0-1 0.0 0 Hymenoptera 10.2(0.5) 0-73 0.5(tr) 0-2 Parasitoids 3.5 0-7 0.5 0-2 Formicidae 6.5 0-69 0.0 0 Vespidae 0.1 0-1 0.0 0 Araneae 7.4(0.4) 0-21 0.8(tr) 0-3 Opiliones 0.1 (tr) 0-1 0.0(tr) 0 Chilopoda 0.2(tr) 0-1 0.0(tr) 0 Isopoda 0.1 (tr) 0-1 0.0(tr) 0 1 J11 J.ENTOMOL.SOC.BRIT.COLUMBIA100,DECEMBER2003 83 Table 2 Taxonomic compositionofmite subsamples (Oribatida, Acaridida, Actinedida) andabsolute numbers ofGamasida inmullein leafrosettes ateachof6 sites. oiie 1 oiie z oiie J oiie 4 oiie J oiie o Oribatida 49 1 5 27 0 1 Acaridida 2 35 5 7 6 1 Actinedida /O 1i1z1i JJ 1 J/ z3/ Anystidae 3/ 1 3-> / '7 A A A Baelliaae z 14 0 Camerobiidae 10 4 4 0 4 17 Cunaxidae 0 1 7 0 0 Raphignathidae 3-> 21 1 0 1 0 Smarididae 2 1 0 0 0 0 1arsonemidae 0 0 0 128 0 0 A A A Tenuipalpidae 3 U u u 11 u Tetranychidae z J111 13 4/I A Tydeidae 11 J 1 11 ZUo Unidentified 0 0 0 0 34 0 Countedbutnot classified 0 235 90 841 92 364 Gamasida 238 94 58 29 52 379 Ameroseiidae 0* 0* 0 4 0 0* Ascidae 1* 1* 38 2 0 0* Laelapidae 0* 8* 7 0 0 0* Phytoseiidae 83* 17* 13 23 51 81* Unidentified 1* 1* 0 0 1 3* * Results for a subsample ofmites taken fromthe Gamasida total. byanunidentifiedweevil thatappearstobe associatedwiththe flowering andseedingmullein stalk also during the growing season. For the remaining taxa, spiders and ants were fairly abundant (both exceeding five specimens per 5-plant sample) inthe leafrosettes. Over90% ofthe ants were collected at a single site. Knowntree fruitpests overwintering inmulleinincludedpearpsylla, spidermites, westem flowerthrips, Lygus hesperus Knight, andLygus elisus VanDuzee (Table 3). Westem flower thrips was especiallyabundant inthe stalks, where densities reached 1000 thripsper 5- plant sample. Lygus spp. hada densityofover 10bugsper5-plantsample overwintering inthe leaf rosettes (Table 3). Beneficial arthropods knownto occurinorchards and foundoverwintering inmullein includedprimarilyphytoseiid mites and minute pirate bugs (Table 3), with much lower numbers ofa few other species. Ph3^oseiidae included species of Typhlodromus, G. occidentalism andunidentifiedAmblyseius. Minutepiratebugswere common, havingadensity ofalmost 15 bugs per 5-plant sample. Taxonomic similarity (basedupon insect families) between sites showed no relationship with distancebetween sites (Fig.l). DISCUSSION A large and diverse community ofarthropods usedboththe leaf rosettes and stalks of commonmulleinas overwinteringhabitat. The communities were dominatednumericallyby Thysanoptera (leaves and stalks) andAcari (leaves), butothertaxa including Heteroptera and Coleoptera were also relativelycommon. Atcertain sites, insects andmites overwintering in mulleineasilyexceeded a densityof1000 arthropods perplant, numbers considerablylarger 84 J.ENTOMOL.SOC.BRIT.COLUMBIA100,DECEMBER2003 Table3 Mean densities (averaged over 11 or 6 [Acari] sites) ofarthropods found overwintering in mulleinthatare alsoknownpestornaturalenemyinhabitantsoforchards. Densitiesexpressed as numbersper 5 mulleinplants. Mites not identifiedforstalksamples. Leaf rosettes Stalks ORCHARD PESTS Acari Tetranychidae 25.8 Tetranychus (urticaegroup^) 19.0 Thysanoptera Frankliniella occidentalis^ 280.0 733.4 Homoptera Cacopsyllapyricola 3.5 3.6 Heteroptera Lygus spp. 10.5 0.6 ORCHARD BENEFICIALS Acari Phytoseiidae 124.0 Galendromus occidentalis^ 106.5 Typhlodromus spp.^ 11.3 Amblyseius spp.^ 6.2 Heteroptera Orius tristicolor 7.2 7.7 Deraeocoris brevis (Uhler) 0.1 0.2 Geocoris spp. 0.6 0.0 Coleoptera Stethoruspicipes Casey 0.0 0^^2 ' Mean density estimated by extrapolating from subsamples (Table 2); spider mites were identifiedusing keys inBaker and Tuttle 1994. ^ Mean density estimatedby extrapolating fromsubsamples. ^ Mean densityestimatedby extrapolating fromsubsamples ofGamasida (Table 2). thanthose reportedbyMcAtee (1924) inMaryland (who appears to have ignoredAcari and Thysanoptera inhisbriefstudy). Itis ofinterestthataplantnative to Eurasiawouldhost such substantial numbers ofphytophagous arthropods inNorthAmerica. However, several ofthe most common species that we collected are cosmopolitan or Holarctic in distribution, including westem flower thrips and mullein thrips, and it is likely that these species have geographic ranges in Europe and Asia that overlap the native range ofcommon mullein. Indeed, themulleinthrips isknovmto specialize onspeciesofVerbascum inEurope andNorth America(Bailey 1939). Baileyrecordsthisthrips as overwinteringbothinthe leafrosette and in the seed capsules or stalkmaterial of V. thapsus, as shown alsohere. The westem flower thrips was very abundant overwintering in mullein (Table 3), suggesting that this plantmaybe an important source offlowerthrips moving into orchards during early spring. Westem flower thrips is a major source ofearly season damage on nectarines and certain apple varieties in the Pacific Northwest (Madsen and Jack 1966; Bradley and Mayer 1994; Pearsall and Myers 2000). Pearsall and Myers (2000, 2001) concluded that location ofnectarine orchards in relation to wild habitats strongly affected early-season densities ofthrips in orchards, with those orchards adjacent to other orchards (rather than adjacent to non-orchard habitats) having the lowest spring densities ofthjips. These authors suggestedthatcertainherbaceous and shmbbyplant species innative habitats of the Pacific Northwest are a source of flower thrips that colonize nectarine orchards. Pearsall and Myers (2000) did not include common mullein in their list ofimportant plant species, butresults reportedhere indicate thatcommonmullein should also be consideredto be an important source ofwestem flower thrips in tree fmit growing regions ofthe Pacific Northwest. Other potential pests oftree fmits, including pear psylla, Lygus spp., and spider mites, J.ENTOMOL.SOC.BRIT.COLUMBIA100,DECEMBER2003 85 werepresent inmulleinbutatconsiderably lowerdensities than flowerthrips. Pearpsylla is knownto overwinterinavarietyoflocations outside ofthepearorchard (Kaloostian 1970). Lygus spp. are sporadic pests in pear, apple, and stone fruit crops (Beers et al. 1993). Commonmulleinhasbeenreportedtobe ahostplantofLygus lineolaris (PalisotdeBeauvois) ineasternNorth-America (Young 1986), butitisnotclearwhetherthe two speciesrecovered inthepresentstudy{L. hesperus andL. elisus)usemulleinasmorethanoverwinteringhabitat. McAtee (1924) recorded that Lygus sp. overwintered on common mullein leafrosettes in Maryland. Spider mites are often abundant on broad-leaf plants within and adjacent to orchards, andtheseplants appeartobe sources ofpestmitesmoving into fruittreesduringthe summer(Flexneretal 1991; Alston 1994; Cohetal. 1994). Ourresults indicatethatcommon mullein growing near orchards in the Pacific Northwest may be a source ofoverwintered spidermites thatcould eventuallydisperse into fruittrees. Several importantpredator species also overwintered on commonmullein, including the highlyabundant O. tristicolorandpredatorymites. Orius tristicoloris animportantpredator ofthrips, mites, andothersmall soft-bodiedprey(Askari and Stem 1972; Salas-Aguilar and Ehler 1977). This and other species of Orius are known sources ofbiological control in orchards (Westigard etal. 1968; Niemczyk 1978; McCaffreyandHorsburgh 1986), and our results suggestthatmullein couldbe a source ofearly springpopulations ofO. tristicolorin orchards. McAtee (1924) collected Orius insidiosus (Say) overwintering oncommonmullein inMaryland. Predatory mites were abundant in mullein, and included three genera {Galendromus, Typhlodromus, Amblyseius) that are common in apple and pear orchards ofNorth America (McGroarty and Croft 1978; Croft et al. 1990; Horton et al. 2002), where they provide biologicalcontrolofpestmites (Hoyt 1969). As withspidermites inorchards, predatorymites maycolonize fruittrees fromherbaceous orshrubbyvegetationwithinoradjacentto orchards (McGroartyand Croft 1978; Johnson andCroft 1981; Alston 1994). Thus, the present study suggests that commonmullein could act as a fairly important source ofbeneficial mites that provide biological control ofpest mites inPacific Northwest orchards. There was substantial variation among sites in densities ofarthropods overwintering on mullein(range: 272 arthropodsperplantto 1986 arthropodsperplant). Anyofseveral factors could have contributed to this variation, including host quality, types and amounts of insecticides used innearbyorchards (e.g., Thistlewood etal. 1990), and local environmental ormicroenvironmental conditions. We hypothesized atthe beginning ofthis study that sites close to one another geographically would tend to have taxonomically similar communities comparedto sites geographicallyseparated. Therewasno supportforthis hypothesis (Fig. 1), possiblydue to the factthattwo taxa (Thripidae andPhlaeothripidae) were almost invariably the most numerically dominant taxa at all sites, and comprised more than 80% of all arthropods collected. CONCLUSIONS Boththe leafrosettes and stalks ofcommonmulleinprovided overwintering habitat to a large and taxonomically diverse collection of phytophagous and predatory arthropods. Because thisplant species commonly occurs in disturbed habitats adjacent to tree fruit orchards inthe Pacific Northwest, it maybe an important source ofbothpest and beneficial arthropods colonizing orchards. It is not possible to speculate on whether growers benefit fromhavinglarge stands ofmulleingrowingneartheirorchards, as thepotentialbenefitsmust bejudged relative to the possibleharmcausedbypests whichoverwinter onthe plant oruse itas ahostduring summer. The neteffectinanorchardofbeing adjacentto stands ofmullein woulddepend, ataminimum, onthe numbers ofpestandbeneficial arthropods overwintering inthe stand (which appears to be highlyvariable among stands), as well as each species' 86 J.ENTOMOL.SOC.BRIT.COLUMBIA100,DECEMBER2003 0 10 20 30 40 50 Distance between sites (km) Figure 1. Scatter plot showing relationship ofrelative absolute distance (i.e., taxonomic similarity) andgeographic distance forallpossiblepairings ofsites. Smallervalues ofrelative absolute distance indicate increasing taxonomic similaritybetweensites. Analysis limitedto Insecta at family level. tendencyto disperse into orchards. Untilwebetterunderstand factors affecting overwintering densities ofspecific pestandbeneficial arthropods, andtheirpost-overwintering movements, it is impossible to predict whethermullein is beneficial ordetrimental forgrowers. ACKNOWLEDGEMENTS WethankMerileeBayer, Deb Broers, IvanCampos, DanHallauer, andToniHinojosa for field and laboratoryassistance. We are also verygrateful to SteveNakahara for assistance in identifying our samples ofthrips. We thank GaryReed for loaning us his Berlese funnels. The comments ofRick Redak and Gene Miliczky on an earlier draft ofthis manuscript are appreciated. ThisresearchwaspartiallysupportedbytheInitiative forFutureAgriculture and Food Systems (USDA-CSREES-IFAFS; award number 00-52103-9657), and by funds obtained from the Washington State Tree Fruit Research Commission and the Winter Pear Control Committee. REFERENCES Alston, D.G. 1994. Effect ofapple orchard floor vegetation on density and dispersal ofphytophagous and predaceousmites inUtah. Agriculture, Ecosystems andEnvironment50: 73-84. Askari, A. andV.M. Stem. 1972. Biologyand feedinghabitsofOriustristicolor(Hemiptera: Anthocoridae). AnnalsoftheEntomological SocietyofAmerica65: 96-100. Bailey, S.F. 1939. 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