COMMUNITY AND ECOSYSTEM ECOLOGY Quantitative Association of Bark with Pitch Canker Fungus and Effects of Verbenone on Their Semiochemical Communication in Monterey Pine Forests in Northern Spain

PEDRO ROMO´ N,1 JUAN CARLOS ITURRONDOBEITIA,3 KEN GIBSON,4 5 1,2 B. STAFFAN LINDGREN, AND ARTURO GOLDARAZENA

Environ. Entomol. 36(4): 743Ð750 (2007) ABSTRACT The association between 11 of bark beetles (Coleoptera: Scolytinae) and one (Coleoptera: Entiminae) with the pitch canker fungus, Fusarium circinatum Nirenberg and OÕDonnell, was determined by crushing beetles on selective medium and histone H3 gene sequencing. Pityophthorus pubescens (Marsham) (25.00%), Hylurgops palliatus (Gyllenhal) (11.96%), sexden- tatus (Bo¨rner) (8.57%), Hypothenemus eruditus Westwood (7.89%), Hylastes attenuatus Erichson (7.40%), and erosus (Wollaston) (2.73%) were found to carry the inoculum. In addition, the root weevil Brachyderes incanus L. (14.28%) had the second highest frequency of occurrence of the fungus. The responses of the to a range of verbenone doses were tested in Þeld bioassays using funnel traps. Catches of P. pubescens, a species colonizing branch tips of live trees, were signiÞcantly reduced in a log-linear dose-dependent relationship. Catches of I. sexdentatus,anop- portunistic species normally attacking fresh dead host material, were also gradually reduced with increasing verbenone dose. Catches of piniperda L., O. erosus, autographus (Ratzeburg), H. eruditus, Xyleborus dryographus (Ratzeburg), Hylastes ater (Paykull), ligniperda (F.), H. attenuatus, and B. incanus were not signiÞcantly affected by verbenone. The effects of verbenone were consistent with differences in host-age preference. Semiochemical disruption by verbenone in P. pubescens and I. sexdentatus could represent an integrated pest management strategy for the prevention of the spread of pitch canker disease between different stands. However, several species associated with F. circinatum were unaffected by verbenone, not supporting this compound for prevention of the establishment of potential vectors in Northern Spain.

KEY WORDS Pinus radiata, bark beetles, verbenone, semiochemical communication, Fusarium circinatum epidemiology

Some species of bark beetles (Coleoptera: Scolytinae) 1982); from 1974 to 1980, outbreaks of are among the most destructive insects of coniferous frontalis Zimmerman in southeastern Texas covered forests representing a continuous threat (Ayres and 3,200,000 ha with heavy economic losses (Carter et al. Lombardero 2000). Economic losses caused by bark 1991); and during 1989, massive outbreaks of Tomicus infestations are difÞcult to quantify, and rough piniperda L. caused losses of 92 million euros in Pinus estimates exist for only a few species: during the 1970s, radiata (D. Don) in Basque Country region in Spain Ips typographus L. destroyed 2,000,000 m3 of wood in (Amezaga 1993). Scandinavia (Bakke 1983); since 1895, Dendroctonus In addition to direct damage, bark beetles inoculate ponderosae Hopkins has caused an average annual loss several economically important phytopathogenic and of Ϸ1.5 billion board feet particularly in Pinus contorta bluestaining fungi (Schowalter and Filip 1993). For Douglas ex Loudon in western North America (Wood example, pitch canker, caused by Fusarium circinatum Nirenberg and OÕDonnell, a fungus endemic to the 1 NEIKER-TECNALIA, Basque Institute of Agricultural Research southeastern United States (Dwinell et al. 1985), is and Development, Department of Plant Production and Protection, responsible for serious losses for the forest industry. Arkaute, 46 01080 Vitoria, Spain. More recently, pitch canker was identiÞed and re- 2 Corresponding author, e-mail: [email protected]. ported in California, predominantly in planted urban 3 Universidad del Paõ´s Vasco, Facultad de Ciencia y Tecnologõ´a, Departamento de Zoologõ´a y Dina´mica Celular , Sarriena s/n P. radiata and in native Monterey pine forest (Correll E-48940, Leioa, Spain. et al. 1991). Since being Þrst reported in the United 4 USDA Forest Service Forest Health Protection, PO Box 7669, States, it has been also found in Japan (Muramoto et Missoula, MT 59807. al. 1988), Mexico (Rodriquez 1989), South Africa (Vil- 5 Ecosystem Science and Management, University of Northern Brit- ish Columbia, 3333 University Way, Prince George, British Columbia, joen et al. 1994), and Spain (Landeras et al. 2005), Canada V2N 4Z9. probably because of softwood lumber, seedling, and

0046-225X/07/0743Ð0750$04.00/0 ᭧ 2007 Entomological Society of America 744 ENVIRONMENTAL ENTOMOLOGY Vol. 36, no. 4 seed exports. In California, wounding has not resulted that produced verbenone (as an allomone), and so in transmission of the pathogen to cones (Correll et al. avoid interspeciÞc competition. However, verbenone 1991) or branches (Fox et al. 1991), despite the pres- is also produced in aging logs (Flechtmann et al. 1999), ence of signiÞcant airborne inoculum. A complex of and it has been shown that verbenone increases with insects, however, seems to be capable of transmitting age of logs because of the activity of certain micro- F. circinatum (Fox et al. 1991, Hoover et al. 1995, Storer organisms (Leufve´n et al. 1988). et al. 2004). For example, Ips paraconfusus (Lanier), Our Þrst objective was to determine the association Ips mexicanus Hopkins, Ips plastographus (LeConte), between bark beetles and F. circinatum. The possible Pityophthorus carmeli Swaine, Pityophthorus nitidulus role of bark beetles as vectors of pitch canker fungus Mannerheim, Pityophthorus setosus Blackman, Con- has not been studied in Europe until now. Our second ophthorus radiatae Hopkins (Coleoptera: Scolytinae), objective was to determine the ecological effect of and Ernobius punctulatus (LeConte) (Coleoptera: verbenone on the aggregation of different Anobiidae) have been shown to be phoretically asso- species in Spain to evaluate the potential for using ciated with the fungus and are known to visit and infest verbenone in an integrated management strategy to nondiseased trees. This leads to the potential for de- reduce their indirect damages. There have also been velopment of integrated control strategies of pitch no previous studies of the function of verbenone in the canker by preventing the establishment of bark beetle chemical ecology of bark beetles in the Iberian Pen- vectors in high value pine stands. insula. Bark beetles use plant compounds, predominantly the monoterpenes ␣-pinene or myrcene, as kairomonal Materials and Methods precursors for their pheromonal components (Hendry et al. 1980). Many of the same pheromonal compounds Isolation and Identification of Fungi from Bark are used by species in the same , e.g., ipsenol, Beetles. Fungi were isolated from adult bark beetles ipsdienol, and cis-verbenol in the genus Ips (tribe collected from baiting logs in two stands of P. radiata Ipini) or exo-brevicomin, frontalin, trans-verbenol, localized in Morga and Muxika (Basque Country). In and verbenone in the genus Dendroctonus (tribe March 2004, 10 trap logs, 1.5 m long and 0.2 m in diameter Tomicini) (Borden 1982). Knowledge of the chemical (bark thickness Ϸ2 cm), were set out in each stand. One ecology of bark beetle species colonizing in half of the logs from each locality were partially buried southern Europe is very limited (Byers 1992, Schlyter at an angle of 90Њ, and the other Þve were placed on the et al. 2000). ground surface to capture bark beetles species with aerial Verbenone (4,6,6-trimethylbicyclo[3.1.1]-hept-3- and buried habitats. After 2 mo, all the logs at each site en-2-one) is a simple oxidation product of trans-ver- were inspected for the presence of beetle entrance holes. benol, which in turn is a biological oxidation product All beetles from a single gallery were removed using of ␣-pinene (Birgersson and Leufve´n 1988), one of the sterilized tweezers, placed individually in sterile bottles, most ubiquitous monoterpenes in the Pinaceae. and morphologically identiÞed by using a LEICA MZ95 ␣-Pinene is quite toxic to a number of coniferophagous dissectingmicroscope(LeicaMicrosystemsGmbH,Wetz- insects, whereas trans-verbenol and verbenone seem lar, Germany) to determine taxonomic characters located to be less toxic (Lindgren et al. 1996). Thus, insects in pronotum, scutellum, elytra, metapisternum, and an- inhabiting environments high in ␣-pinene could be tennal funiculum (Gil and Pajares 1986, Pfeffer 1995). expected to have either a high tolerance or an effec- Beetles were removed from storage bottles using ster- tive detoxiÞcation system. Verbenone has been found ilized tweezers and squashed onto the surface of a se- in relatively large amounts (mg) in hindguts of Den- lective medium for Fusarium species DCCP (15 g pep- droctonus ponderosae (Pierce et al. 1987), Dendrocto- tone,1gKH2PO4, 0.5 g MgSO4 0.7 H2O, 0.2 g nus frontalis (Renwick and Vite´ 1968), Dendroctonus chloramphenicol, 20 g agar, and 1,000 ml distilled water, brevicomis LeConte (Byers et al. 1984), and Dendroc- amended with 0.002 g 2Ð6-dichloro-4-nitroaniline in 10 tonus pseudotsugae Hopkins (Rudinsky et al. 1974), ml ethanol) (Burgess et al. 1988). After 2 wk of incuba- and in low amounts (ng) in T. piniperda (Lanne et al. tion at 25ЊC in the dark, fungal cultures were puriÞed by 1987), but it seems to be absent in I. paraconfusus, I. transferring hyphal tips from the edges of individual typographus, and chalcographus L. (Byers colonies to fresh potato dextrose agar (Panreac). Pure, 1983b, Birgersson et al. 1984, 1990). sporulating cultures were examined and classiÞed into Some bark beetle species of the formerly consid- putative types using a LEICA DM4500B microscope ac- ered subfamily Hylesininae (tribe Tomicini) produce cording to characteristics of the fruiting structures pro- verbenone in relatively signiÞcant amounts early in duced by the anamorphic stage (Nelson et al. 1983, Britz colonization, so it has been suggested that it plays a et al. 2002). F. circinatum putative isolates were properly role in reducing intraspeciÞc competition and inter- identiÞed by DNA sequences comparison. DNA extrac- speciÞc competition with other species (Byers et al. tions and polymerase chain reaction (PCR) ampliÞca- 1984). Therefore, some bark beetle species may have tions were performed as described by Steenkamp et al. evolved to use ␣-pinene and trans-verbenol as (1999). Sequence alignments were performed by Se- kairomonal precursors, producing verbenone as an quence Navigator 1.0 (Applied Biosystems, Lincoln, CA) anti-aggregation pheromone that reduces intraspe- and properly identiÞed by DNA sequences comparison ciÞc competition. Other sympatric bark beetle species using the services provided by the National Center for on the same host might then evolve to avoid species Biotechnology Information. August 2007 ROMON´ ET AL.: QUANTITATIVE ASSOCIATION OF BARK BEETLES WITH PITCH CANKER 745

Table 1. Parameters for verbenone dose experiments in Basque Country (Northern Spain), in 2004, with description of semio- chemical-releasing devices

Each experiment PheromonalÐ Other Targeted kairomonal Release rate No. collected Dates Description species attractant (mg/24 h)b insect species blenda 1 P. pubescens Ñ 1Ð30 May trans-Pityol Polyethylene bubble cap 0.14 2 H. palliatus H. attenuatus 1 JuneÐ Ethanol Polyethylene bottle (30 ml) 250.00 H. ater 30 July 3-Carene Polyethylene screw-cap bottle (15 ml) 250.00 O. erosus ␤-Pinene Polyethylene screw-cap bottle (15 ml) 250.00 H. eruditus cis-Verbenol Polyethylene bubble cap 2.10 X. dryographus trans-Verbenol Polyethylene bubble cap 2.10 B. incanus 3 T. piniperda Ñ 1 Aug.Ð Terpinolene Polyethylene screw-cap bottle (15 ml) 250.00 30 Sept. ␣-Pinene Polyethylene screw-cap bottle (15 ml) 250.00 ␣-Pineneoxide Polyvinyl bubble cap 0.20 trans-Verbenol Polyvinyl bubble cap 0.20 4 I. sexdentatus D. autographus 1 Oct.Ð Myrcene Polyethylene screw-cap bottle (15 ml) 250.00 H. ligniperda 30 Nov. Ipsdienol Polyvinyl bubble cap 0.20 Ipsenol Polyvinyl bubble cap 0.40

All experiments a Chemical Description Release rate (mg/24 h)b Verbenone (ϩ17/Ϫ83) Closed polyethylene centrifuge tube (250 ␮l) 0.01 Verbenone (ϩ17/Ϫ83) Closed polyethylene centrifuge tube (400 ␮l) 0.20 Verbenone (ϩ17/Ϫ83) Polyethylene bubble cap 1.80 Verbenone (ϩ17/Ϫ83) Polyethylene bubble cap 3.10

a All chemical purities Ͼ98%. b At 22Ð24ЊC.

All the beetles present in each gallery were treated as experiment 4, Orozketa) in which considerable pop- a single sample, recording only one isolate per gallery to ulation of the respective target insect species had been avoid the overestimation of frequency calculations. Fre- previously recorded (Goldarazena 2004), thus avoid- quencies of occurrence of fungi were computed using ing inßuencing subsequent experiments by the resid- the formula of Yamaoka et al. (1997) where F ϭ (NF/ ual compounds and the obtained catches during the NT)100 (%), and F represents the frequency of occur- previous experiments. rence (%) of the fungus, NT represents the total number In each experiment, treatments were assigned ran- of samples from which isolation attempts were made, and domly to traps within each block as follows: attractants NF represents the number of samples from which the alone or with devices resulting in one of four ver- fungus was isolated. benone release rates: 0.01, 0.2, 1.8, and 3.1 mg/24 h (at Semiochemical Experiments. Four separate exper- 22Ð24ЊC). The control trap in each experiment was a iments were conducted to evaluate dose effects of trap baited only with attractants. The optimal pheno- verbenone on the attraction of four targeted bark logical season was selected for each target species beetle species (Table 1). All release devices were (Goldarazena 2004), and known pheromonal and/or obtained from Pherotech International (Delta, British kairomonal blends (Vite´ et al. 1972, Volz 1988, Byers Columbia, Canada; Table 1). Ipsenol and ipsdienol 1992, Czokajlo 1998, Dallara et al. 2000) were used as were formulated in 1,3-butanediol at a concentration attractants (Table 1). Voucher specimens have been of 80 mg/ml. Release rates for devices representing deposited at the Entomology Collection at NEIKER- ipsenol and ipsdienol were determined by collection Basque Institute of Agricultural Research and Devel- of volatiles on Porapak-Q and analysis by capillary gas opment, Basque Country, Spain. chromatography. Release rates for all remaining de- Data were analyzed by regression using SPSS 13.0 vices were determined by weight loss. statistical software (SPSS 1999). All possible combi- In each experiment, Þve blocks (replicates) of Þve nation analysis between several transformations (ln, 12-unit Lindgren multiple funnel traps were set at log, square root) of both trap catches and the inde- least 100 m apart in stands of mature Monterey pine in pendent variable were tested, as needed from exam- Basque Country (Northern Spain). Traps were spaced inations of residuals and to correct for heteroscedas- 10Ð15 m apart in grids of 2 by 3 within each block. Each ticity and nonlinearity. trap was at least 2 m from any tree and suspended by rope such that the bottom of each trap was 0.2Ð0.5 m Results above ground level. Each experiment was conducted in different P. radiata plantations areas (experiment 1, A list of the results of the assays for the presence of F. Lezama; experiment 2, Muxika; experiment 3, Morga; circinatum (GenBank accession numbers DQ662828, 746 ENVIRONMENTAL ENTOMOLOGY Vol. 36, no. 4

Table 2. Variation about frequency of occurrence of F. circi- natum on several bark beetles (Coleoptera: Scolytinae) and (Coleoptera: Entiminae) species in Northern Spain

Total no. Insect species NF F (%)a samples Pityophthorus pubescens 32 8 25.00 Brachyderes incanus 42 6 14.28 Hylurgops palliatus 117 14 11.96 35 3 8.57 Hypothenemus eruditus 38 3 7.89 Hylastes attenuatus 54 4 7.40 Orthotomicus erosus 73 2 2.73 Dryocoetes autographus 45 Ñ Ñ Hylastes ater 32 Ñ Ñ Tomicus piniperda 18 Ñ Ñ Xyleborus dryographus 9ÑÑ Hylurgus ligniperda 5ÑÑ

a Frequency of occurrence F ϭ (NF/NT)100 (%), where NT rep- resents the total no. of samples from which isolations attempts were made, and NF represents the no. of samples from which F. circinatum was isolated.

DQ662829, DQ662830, DQ662831, DQ662832, and DQ352833) to determine potential transmission vectors is provided in Table 2. Six of the 11 species of bark beetles tested for fungal associates were identiÞed as carriers of F. circinatum. These included Pityophthorus pubescens (Marsham) (25.00%), Hylurgops palliatus (Gyllenhal) (11.96%), Ips sexdentatus (Bo¨rner) (8.57%), Hypothen- emus eruditus Westwood (7.89%), Hylastes attenuatus Erichson (7.40%), and Orthotomicus erosus (Wollaston) (2.73%). In addition, the root weevil Brachyderes incanus L. (14.28%) had the second highest frequency of occur- rence of the pitch canker fungus. Thus, of 391 galleries Fig. 1. Effect of verbenone, released at four rates, on the examined from the seven potential vector species, attraction of P. pubescens in experiment 1 (A) and I. sexden- 10.20% presented beetles carrying the fungus. tatus in experiment 4 (B). See Table 1 for experimental Verbenone signiÞcantly interrupted the attraction details. Slopes of regression lines are signiÞcantly different of P. pubescens to attractant-baited multiple-funnel from zero (t-test, P Ͻ 0.001). ConÞdence limits (95%; thin traps (F ϭ 10.704, df ϭ 4, P Ͻ 0.001) in a log-linear solid lines) are associated with each regression line (thick dose-dependent relationship (Fig. 1A). Verbenone solid line). Dashed lines represent conÞdence limits (95%) also reduced catches of I. sexdentatus signiÞcantly for catches in control traps. (F ϭ 9.299, df ϭ 4, P Ͻ 0.001). The relationship be- tween catches of beetles and dose of verbenone was of management efforts directed at these species may square root-linear for Ips sexdentatus (Fig. 1B). In therefore be justiÞable. contrast, verbenone did not signiÞcantly affect Lindgren (1994) proposed the hypothesis that ver- catches of O. erosus (F ϭ 0.917, df ϭ 4, P ϭ 0.473; Fig. benone quantity increases with the level of microbial 2A), Dryocoetes autographus (Ratzeburg) (F ϭ 0.674, degradation of phloem tissue. If this hypothesis is df ϭ 4, P ϭ 0.618), T. piniperda (F ϭ 0.479, df ϭ 4, P ϭ valid, one would expect verbenone to have a strong 0.751), B. incanus (F ϭ 0.703, df ϭ 4, P ϭ 0.599; Fig. 2B), inhibitory effect on species that need fresh host tissue, H. eruditus (F ϭ 0.240, df ϭ 4, P ϭ 0.912; Fig. 2C), even at low doses. Species that use aged tissue should Xyleborus dryographus (Ratzeburg) (F ϭ 0.331, df ϭ not respond to verbenone, respond only to high doses, 4, P ϭ 0.854), Hylastes ater (Paykull) (F ϭ 1.200, df ϭ 4, or even be attracted depending on where they occur P ϭ 0.341), Hylurgus ligniperda (F.) (F ϭ 0.558, df ϭ in the succession of insect colonization. Based on the 4, P ϭ 0.696), and H. attenuatus (F ϭ 0.851, df ϭ 4, P ϭ hypothesis proposed by Lindgren (1994), one would 0.510; Fig. 2D). expect the following ordering in verbenone dose sen- sitivity by the studied species: P. pubescens Ͼ T. pin- iperda Ͼ I. sexdentatus Ն O. erosus Ն D. autographus Ͼ Discussion B. incanus Ն H. eruditus Ն X. dryographus Ͼ H. ater Ն The presence of F. circinatum on Ͼ10% of the po- H. ligniperda Ն H. attenuatus. tential vector species shows that these species are Our data show partial agreement with LindgrenÕs associated with pitch cankerÐdiseased trees and that hypothesis. Pityophthorus pubescens exhibited a log- they may be vectors of the fungus. The consideration linear dose-dependent relationship that is in concor- August 2007 ROMON´ ET AL.: QUANTITATIVE ASSOCIATION OF BARK BEETLES WITH PITCH CANKER 747

Fig. 2. Effect of verbenone, released at four rates, on the attraction of O. erosus in experiment 2 (A), B. incanus in experiment 2 (B), H. eruditus in experiment 2 (C), and H. attenuatus in experiment 2 (D). See Table 1 for experimental details. Slopes of regression lines are signiÞcantly different from zero (t-test, P Ͻ 0.001). ConÞdence limits (95%; thin solid lines) are associated with each regression line (thick solid line). Dashed lines represent conÞdence limits (95%) for catches in control traps. dance with the primary characteristics of this bark sive outbreaks in recently wounded trees, and it also beetle species, because it usually colonizes apical can massively colonize stumps on the ground, so it may twigs of relatively large trees localized within wide be adapted to moderate natural amounts of verbenone forest areas. Ips sexdentatus, which still requires rela- (Lanne et al. 1987), which is consistent with our re- tively fresh phloem and may mass attack live trees sults. under favorable conditions, shows a square root-linear Orthotomicus erosus and D. autographus, which are dose response to verbenone, resulting in an almost pioneer competitors in wood colonization, did not complete shutdown of attractiveness of the aggrega- respond signiÞcantly to verbenone dose, possibly be- tion pheromonal blend. H. palliatus was not caught in cause these species are associated with I. sexdentatus high enough numbers to allow a representative eval- pioneer boring facilitating activity. As also expected, uation of verbenone. This could be linked to the dif- verbenone did not signiÞcantly affect catches of X. Þculty of monitoring populations of this bark beetle dryographus and H. eruditus, which are secondary spe- species with traps because of its main colonization of cies that seem adapted to mature stands and show buried niches (Romo´n et al. 2007). Further research strong feeding relationships with mutualistic fungi. is needed to bioassay how the mentioned bark beetle Similarly, catches of Hylastes species and H. ligniperda, responds to verbenone during the colonization of cut species often found in large numbers on stumps or logs logs deposited in the forest ßoor. Tomicus piniperda, in contact with the ground for relatively long periods, which feeds on pine shoots to complete sexual mat- were not signiÞcantly affected by verbenone. uration and needs fresh phloem for breeding, would The catches of all nontargeted species could be be expected to show relatively high sensitivity even to considered incidental, so their responses to verbenone low doses of verbenone. However, under favorable should be considered with caution because the knowl- environmental conditions, this species produces mas- edge about their semiochemical attractants is very 748 ENVIRONMENTAL ENTOMOLOGY Vol. 36, no. 4 limited, and further studies are needed to discern the association percentages with F. circinatum, but catches attractant ability of the tested compounds by exper- of these bark beetle species were not signiÞcantly imental designs with the inclusion of negative control affected by verbenone. traps. Considering, however, the results obtained dur- During the past two decades, verbenone has been ing this study, it is interesting to notice a trend of shown as a good natural repellent for the control of potential attractive effect of verbenone on Hylastes damages caused by several insect species such as Hy- attenuatus. Future assays are thus also needed with the lobius pales (Herbst) (Salom et al. 1994), Hylobius incorporation of higher verbenone release rates and abietis L. (Lindgren et al. 1996), D. ponderosae comparative mathematical analysis of the obtained (Lindgren et al. 1989), Ips pini (Say), and Ips latidens regression equations and signiÞcance values. In the (LeConte) (Lindgren and Miller 2002). However, re- case of conÞrmation of a signiÞcant attraction, studies sults in some subsequent experiments have been in- dealing with the determination of whether this bark consistent probably because of some inadequate re- beetle is able to produce verbenone, de novo and/or lease rate standardizations and/or differences in from host monoterpenes in the absence of effects on different conifer host subpopulations of the microorganisms, should be performed to discern the same insect species (Amman and Lindgren 1995). source of its potential natural adaptation to high levels Generally, verbenone has shown relatively good re- of verbenone. sults as an anti-aggregant only against pioneer bark In our experiments, both attractant compounds and beetle species probably because conifers have not verbenone release rates varied mostly only with tem- evolved the capacity of converting ␣-pinene to ver- perature as a function of the vapor pressures of the benone. Future studies should be directed to evaluate tested compounds and release membrane properties. the ability of several bark beetle species to directly Under natural conditions, however, beetles are ex- vector F. circinatum into plant material, determine the posed to various doses and ratios of attractant and efÞcacy of verbenone as potential inhibitor of I. sex- repellent compounds depending also on conifer spe- dentatus aggregation in wood yards with high risk of cies, tree genetics, bark-beetle associated microorgan- pitch canker fungus establishment, and study the ef- isms, free microorganisms, and direct autoxidations of fect and genetically based variation of P. radiata pri- semiochemicals by physical factors such as sunlight mary monoterpenes to assayed different potential (Hunt et al. 1989). The signiÞcant regressions ob- control compounds for other important primary bark tained for two bark beetle species, as well as medium beetle species such as T. piniperda. ßight temperature thresholds between 18 and 25ЊC (Bakke 1968, Kennedy and McCullough 2002), pro- vided a high level of conÞdence about the observed Acknowledgments verbenone dose-dependent effects for the targeted bark beetle species. We thank Forest Health Protection (USDA Forest Ser- To our knowledge, very few temperature-depen- vice) for providing test material needed for the development dent models for predicting release rates of volatile of this project and Pherotech International (Delta, BC, Can- compounds from Þeld dispensers have been devel- ada) for technical assistance with release rate determinations and formulation of compounds; the Spanish Ministry of Ed- oped (Bradley et al. 1995), and they cannot be applied ucation and Science (AGL2005Ð01711/FOR), partially to this study because they deal with other compounds funded by FEDER, and the Department of Agriculture and and release devices material and/or shape. Similarly, Fisheries of the Basque Country (DAP-VED2003016) for knowledge is extremely limited about the compounds Þnancial support; and the Department of Education, Uni- that are produced by direct oxidizing processes, as versities and Research of the Basque Country for a grant to well as their different vapor pressures (Capouet and P. Romo´n to support a PhD. We also thank the management Mu¨ ller 2005). Future laboratory studies are needed to and employees of NEIKER and Bizkaia Government for the determine the effect of the temperature and sunlight time and facilities to carry out this work, especially to P. Saint intensity on the release rates of the compounds from de Urturi, A. Isasmendi, and J. C. Pino. the release devices that were used during this study. This information would permit determining in the Þeld a broader range of effects of verbenone at release References Cited rate variations caused by temperature and sunlight Amman, G. D., and B. S. Lindgren. 1995. Semiochemicals intensity. This objective will also need the develop- for management of mountain pine beetle, Dendroctonus ment of an environmental sensor coupled to a digital ponderosae Hopkins: current status of research and ap- sample fractioning system (Byers 1983a). plication, pp. 14Ð22. In S. M. Salom and K. R. Hobson Based on the methodology used in this study, ver- (eds.), Application of semiochemicals for management of benone could be considered a component for an IPM bark beetle infestationsÑproceedings of an informal con- strategy for preventing P. pubescens and I. sexdentatus ference. Ogden, UT:USDA Forest Service. aggregation, two potential insect vectors of the pitch Amezaga, I. 1993. The ecology and pest status of Tomicus piniperda L. (Coleoptera: Scolytidae) on pines. PhD dis- canker pathogen. However, results in this study did sertation, University of London, London, UK. not support verbenone as a tool to completely avoid Ayres, M. P., and M. J. Lombardero. 2000. 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