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Influence of Host Tree Condition on the Performance of Tetropium

Influence of Host Tree Condition on the Performance of Tetropium fuscum (Coleoptera: Cerambycidae)

Author(s): Leah Flaherty, Jon D. Sweeney, Deepa Pureswaran, and Dan T. Quiring Source: Environmental Entomology, 40(5):1200-1209. 2011.

Published By: Entomological Society of America

DOI: https://www.doczj.com/doc/c114484221.html,/10.1603/EN11114

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P LANT-I NSECT I NTERACTIONS

In?uence of Host Tree Condition on the Performance of Tetropium fuscum(Coleoptera:Cerambycidae)

LEAH FLAHERTY,1,2,3JON D.SWEENEY,3DEEPA PURESWARAN,4AND DAN T.QUIRING1

Environ.Entomol.40(5):1200D1209(2011);DOI:https://www.doczj.com/doc/c114484221.html,/10.1603/EN11114 ABSTRACT Tetropium fuscum(F.)attacks weakened Norway spruce,Picea abies(L.)Karst.,in its native Europe and may colonize healthy spruce in Nova Scotia,Canada.We used manipulativeTeld experiments to evaluate:1)the development of T.fuscum on apparently healthy red spruce(Picea rubens Sarg.)in Nova Scotia;2)the in?uence of red spruce physiological condition(healthy,girdled or cut)on T.fuscum performance;and3)the impact of natural enemies and competitors on T.fuscum performance when developing on trees of varying condition.Tetropium fuscum successfully developed on healthy red spruce.Survival was higher on healthy than on girdled or cut trees when larvae were exposed to natural enemies and competitors.The beneTts of reduced competition and parasitism on healthy trees appeared to compensate for any reductions in nutritional quality,increase in host resistance,or both.In contrast,when T.fuscum were protected from natural enemies,apparent survival was highest on girdled trees.Tetropium fuscum development took longer on healthy than on cut or girdled trees,and emerged adults were largest on healthy trees.The disparities in adult sizes among the three treatments may mean that healthy trees are more nutritious.Alternatively,the differences may indicate that a greater amount of time was spent feeding in healthy than in girdled or cut trees. Tree condition appears to have a direct impact on the success of T.fuscum,in?uencing survival, development time,and adult size,and may mediate the impact of natural enemies and competitors, further affecting T.fuscum performance.

KEY WORDS Cerambycidae,development time,tree condition,tree moisture stress

The physiological condition of the host plant on which an insect herbivore develops can have a large impact on itsTtness(Koricheva and Larsson1998).For ex-ample,drought stress may promote outbreaks of her-bivorous insects(Mattson and Haack1987a),and her-bivore abundance and performance often vary with host plant growth rate(Quiring et al.2006).Variations in herbivore performance on host plants of varying condition may be caused directly by quantitative or qualitative variation in herbivore nutrition(Hodges and Lorio1969,White1984);by host plant resistance to attack,or both(Christiansen et al.1987);or indi-rectly because host plant condition may mediate the impact of natural enemies(Shibata2000,Paine et al. 2001)and competitors(Ohgushi2005).Thus,many insect herbivores are adapted to colonize hosts of a particular physiological condition,which is often as-sociated with their feeding guild(Larsson1989).Some species,most notably galling and chewing insects,of-ten attack vigorous host plants(Price1991),whereas others,like many bark and wood-boring beetles,more frequently attack stressed,dying,or dead hosts(Paine et al.1997,Hanks1999).

Tetropium fuscum(F.)(Coleoptera:Cerambyci-dae)is native to most of Europe,except the far west (Juutinen1955);it commonly attacks weakened or recently killed Norway spruce,Picea abies(L.)Karst., and is not considered an important pest species (Schimitschek1929,Juutinen1955).In Novia Scotia, Canada,where T.fuscum has been established since at least1990(Smith and Hurley2000),slow-growing red spruce,Picea rubens(Sarg.),appear to be more sus-ceptible to colonization by T.fuscum than faster grow-ing trees(O?Leary et al.2003).However,T.fuscum has been observed to colonize and kill apparently healthy spruce(Smith and Humble2000)and is consequently classiTed as a quarantine pest.

In its native range,T.fuscum typically has one gen-eration a year,and may take2yr to develop in cooler climates(Schimitschek1929,Juutinen1955).In Nova Scotia,sexually mature adult T.fuscum emerge from trees in late May to mid-August.They mate soon after emerging and have not been observed to feed.Mated females deposit eggs in bark crevices,and at20?C,eggs take?12d to hatch(Schimitschek1929,Juutinen 1955).Neonate larvae bore through the bark into the phloem,where they feed and create a network of

1Population Ecology Group,Faculty of Forestry and Environmen-

tal Management,University of New Brunswick,Fredericton,New Brunswick,E3B6C2,Canada.

2Corresponding author,e-mail:leahelizabeth?aherty@https://www.doczj.com/doc/c114484221.html,.

3Natural Resources Canada,Canadian Forest Service-Atlantic Forestry Centre,P.O.Box4000,Fredericton,New Brunswick,E3B

5P7,Canada.

4Natural Resources Canada,Canadian Forest Service-Lauren-

tian Forest Centre,1055du P.E.P.S.,Sainte-Foy Quebec,G1V4C7, Canada.

0046-225X/11/1200D1209$04.00/0?2011Entomological Society of America

galleries(Schimitschek1929,Juutinen1955).Prepu-pal larvae usually build pupal cells in fall,located at the phloemDsapwood interface or up to4-cm deep in the sapwood,and pupate in spring(Schimitschek1929). The apparent discrepancy in the condition of trees reported as susceptible to attack by T.fuscum in its native versus introduced range stimulated this re-search because the level of risk associated with this exotic beetle depends on its ability to attack and kill healthy trees.In this study,we used manipulativeTeld experiments to evaluate:1)the development of T. fuscum on apparently healthy red spruce trees in Nova Scotia;2)the in?uence of red spruce physiological condition(i.e.,growth rate and moisture stress)on T. fuscum performance;and3)the impact of natural enemies and competitors on T.fuscum performance when developing on red spruce of varying condition. We also tested the assumption that when adults are forced to oviposit on a particular host tree,a similar number of eggs will be laid regardless of tree condi-tion.

We hypothesized that moisture-stressed,slow-growing red spruce trees have reduced resistance to T. fuscum attack and contain higher or more balanced levels of nutrients for developing T.fuscum larvae than healthy trees(White1984,Mattson and Haack1987a). Conversely,we hypothesized that interspeciTc com-petition is greater in stressed than in healthy trees because the former are more commonly colonized by phloeophagous beetles,such as Tetropium cinnam-opterum Kirby and Dendroctonus ru?pennis(Kirby) (Coleoptera:Curculionidae)(Drooz1985).We also expected that natural enemies would forage more fre-quently on stressed than on healthy trees because of their greater likelihood ofTnding host insects and, therefore,predicted that when larvae are protected from natural enemies and native bark beetles,T.fus-cum performance would be greater on stressed than on healthy trees.However,when larvae are exposed to natural enemies and competitors,we predicted that mortality from natural enemies and competition would be greater on stressed than on healthy trees.

Materials and Methods

Description of Site and Tree Manipulation.In May 2008,we selected60apparently healthy,dominant or co-dominant red spruce trees(20D28cm diameter at breast height[DBH])with full green crowns near EnTeld,Nova Scotia,Canada(44?54.226?N,063?91.970?W)in a mature(?65-yr-old),red spruce-dominated mixed-wood stand.This stand was within the area currently infested by T.fuscum.We randomly assigned each tree to one of three host conditions: healthy,girdled,or cut(20trees per tree condition). On22May,the bark,phloem,and sapwood of girdled trees were cut to a depth of?2.5cm with a chainsaw, 30cm above the tree base.On27May,we felled20 trees,and took a2.4-m log from the base of each tree to serve as the“cut”treatment sample.Healthy trees were not manipulated.To evaluate whether the above-described treatments resulted in trees of vary-ing physiological condition,we measured moisture stress and current-year terminal shoot length of healthy and girdled trees.As the cut treatment was a log,detached from the roots and crown of the tree,we assumed it represented the least vigorous tree condi-tion.

Tree moisture stress was measured using a PMS Pressure Chamber Instrument(model610,PMS In-strument Company,Albany,OR)4wk after adult T. fuscum were caged on trees(see Effect of Tree Con-dition and Caging on T.fuscum Performance).As the oviposition period is?14d and eggs take10D14d to hatch(Juutinen1955),this represents the approxi-mate time of larval establishment.We used pole-prun-ers to cut an exposed midcrown branch and randomly selected two distal-lateral shoots.Shoots were cut so that only foliage from2007and2008remained.We removed the bark and phloem from the cut end of each shoot,extending1D2mm,and placed the shoot in a sealed pressure chamber with the cut end ex-posed.Pressure was applied to the shoot,and we noted the pressure required to force water up the water column,which was apparent by water appearing at the cut surface.Time of day was also recorded for each measurement.Tree condition treatment(F

1,37

?14.1;

P?0.001),but not time of day(F

1,37

?1.5;P?0.23), in?uenced tree moisture stress(analysis of covariance (ANCOVA)).Mean(?SE)moisture stress was sig-niTcantly higher on girdled(294?24psi)than on healthy(197?13psi)trees.

We measured current-year terminal shoot length on a subsample of10healthy and10girdled trees in November2008.Shoots on girdled trees(18?8mm), which experienced higher levels of moisture stress, grew signiTcantly less than shoots on healthy trees

(125?14mm)(two-tailed t-test,T

1,18

?6.9;P?0.001),supporting our assumption that trees in the three treatments represent a range of physiological conditions.

Effect of Tree Condition and Caging on T.fuscum Performance.Fine-mesh(opening?0.3mm2)cages (125-cm circumference by35cm high)were fastened around the bole of each tree,entirely enclosing a 30-cm-long section,40D70cm above the tree base. Cages were tied around the bole of each tree with drawstrings that were sewn into each125-cm edge, and Velcro fasteners(along the entire vertical35-cm edges)sealed cages together.We placed polyurethane foam between the drawstrings and tree bark to ensure a tightTt.Availability of adult T.fuscum prevented a single release date,so three mated T.fuscum pairs were placed in cages on10randomly selected trees per treatment(30trees)during theTrst week of June 2008,and on the remaining trees during the third week of June2008.Cages were fastened to trees just before T.fuscum manipulation.All T.fuscum used in this experiment were reared in the Atlantic Forestry Cen-tre?s containment laboratory(Natural Resources Can-ada,Fredericton,NB,Canada),from bolts cut from infested trees near Halifax,Nova Scotia.

To determine the effects of tree condition on T. fuscum mortality in the absence and presence of nat-

October2011F LAHERTY ET AL.:E FFECT OF H OST C ONDITION ON T.fuscum P ERFORMANCE1201

ural enemies,we removed the cages from half of the trees in each treatment after14d,the typicalTeld oviposition period(Juutinen1955),whereas all other cages remained on the tree for the duration of the experiment.

Tetropium fuscum larvae developed in trees through-out summer and we cut exploited portions of each tree into bolts in late October.We stored bolts at the stand boundary until15December to ensure that a sufTcient cold period had elapsed to satisfy larval diapause re-quirements(J.S.,unpublished data)and subsequently transported them to the containment laboratory in Fred-ericton.Trees that were caged throughout larval devel-opment were not caged from late October to15Decem-ber because parasitoids were not active during this period.However,substantial predation of T.fuscum lar-vae by woodpeckers occurred during this period. After transport to Fredericton,we placed each bolt in a Plexiglas cage and incubated bolts at20?C to facilitate T.fuscum adult emergence,which began3 wk after the start of the incubation period.Tetropium fuscum emergence ceased after11wk(except for one individual that emerged after15wk),but bolts were incubated for an additional5wk to ensure that all adults had emerged.After theTrst16wk of incubation, we peeled the bark from a subsample of two bolts per treatment,and found live T.fuscum larvae developing in bolts from both the healthy and girdled treatments. Tetropium fuscum and T.cinnamopterum larvae were distinguished based on the shape of their urogomphi (J.S.,unpublished data).Consequently,we placed the remaining18bolts per treatment in cold storage for16 wk(5?C for2wk followed by14wk at?2?C),to simulate a second winter,which may be required to satisfy diapause requirements of late instars that would have been early instars during the winter of2008D2009.After16wk of cold temperatures,bolts were incubated at20?C for an additional16wk.Throughout both incubation periods,we monitored insect emer-gence6d per week and collected any T.fuscum that emerged.Each emerged beetle was sexed and the length of adult elytra,a proxy for adult size,was mea-sured using an ocular micrometer on a dissecting scope at10?magniTcation.We also recorded devel-opment time(number of days incubated in the labo-ratory at20?C)for each adult that emerged.Voucher specimens are stored at the Atlantic Forestry Centre, Fredericton,NB.

We collected emerged parasitoids of T.fuscum throughout both incubation periods.In Canada,T.fus-cum is host to at least two native parasitoids,Wroughtonia occidentalis(Cresson)(Hymenoptera:Braconidae)and Rhimphoctona macrocephala(Provancher)(Hymenop-tera:Ichneumonidae)(Sweeney et al.2005).These are solitary koinobiont endoparasitoids of Tetropium spp. (Yu et al.2005).As larvae of T.cinnamopterum(Kirby), a native congener,were present in several study trees (see results),we do not know whether parasitoids emerged from T.fuscum or T.cinnamopterum and,there-fore,report percentage parasitism of Tetropium spp. After incubation was complete,we counted the number of woodpecker holes on each bolt to esti-mate predation of larvae by woodpeckers.Subse-quently,we peeled the bark and estimated larval density of Tetropium spp.at the time that predation occurred by counting the number of dead immature Tetropium https://www.doczj.com/doc/c114484221.html,rvae under the bark and the num-bers of pupal cells under the bark and in the sap-wood.This method may underestimate Tetropium https://www.doczj.com/doc/c114484221.html,rval density because woodpeckers also may have preyed on immature larvae.Therefore,we included the number of woodpecker holes per bolt in a second estimate of larval density,although this may overestimate density because each wood-pecker hole may not have resulted in the death of a Tetropium https://www.doczj.com/doc/c114484221.html,rva.

We visually estimated the percentage of phloem (surface area)consumed by all phloem feeders on six10-cm2sections on each bolt by using a2-cm grid. Sampling started with a randomly chosen point along the bottom of each bolt,followed by system-atic sampling of sections diagonal to the previously sampled area in a counter-clockwise fashion.This gave us two sections from each of the top,middle, and bottom sections of each bolt,which were av-eraged for each tree.We did not estimate the per-centage of phloem consumed for the six bolts(two per tree condition)that were peeled after theTrst incubation period.

Effect of Tree Condition on Oviposition.To test the assumption that a similar number of eggs were laid on trees from the three tree condition treatments, we conducted an independent study in2009.In early May,30apparently healthy red spruce trees (20-to24-cm DBH)with full green crowns were selected in a mature,mixed-wood,red spruce-dom-inated stand near Lower Sackville,Nova Scotia(44?51.892?N,063?39.462?W).This stand is also within the area currently infested by T.fuscum.On22May 2009,we fastened two drawstring cages around the bole of each tree at50D80and90D120cm above the tree base.We randomly assigned each tree to one of three host conditions:healthy,girdled,or cut(10 trees per tree condition)and treated trees on25 June2009,as described in Description of Site and Tree Manipulation.

On28July(24trees,eight per tree condition)or5 August(six trees,two per tree condition),we placed into each cage one male and one female T.fuscum that had been observed mating.Nine days after adults were placed in cages,we cut two30-cm-long bolts from the caged portions of each tree and immediately trans-ported bolts to the Atlantic Forestry Centre,where they were stored at?2?C.For each tree,we randomly selected one bolt and removed all of the bark and phloem in?70-cm2pieces.We dissected bark pieces under a dissecting microscope and counted the num-ber of eggs laid by T.fuscum females.Because of a longer than expected time required to process each bolt,we processed only one bolt per tree. Statistical Analysis.Standard errors accompany all means in the text or inTgures,and we present least square means for all percentage data.The date that T. fuscum were caged on trees was not a signiTcant factor

1202E NVIRONMENTAL E NTOMOLOGY Vol.40,no.5

in any preliminary analyses,so we pooled data across dates for subsequent analyses.When assumptions of parametric tests were not satisTed,as indicated by residual plots and Levene?s test,we analyzed data using either generalized linear modeling (GLM)or transformed data by log 10,log 10(x ?1),or arcsine square-root,before analysis of variance (ANOVA)(Zar 1999).We selected probability distributions for GLM by minimizing measures of goodness-of-Tt,in-cluding deviance,Pearson ?2,and log-likelihood.Gen-eralized linear models used logit links and binomial probability distributions unless otherwise speciTed.We conducted all analyses by using PASW Statistics 18,version 18.0.0(SPSS 2009,Chicago,IL).

Oviposition.We used a three-way ANOVA to eval-uate the effects of tree condition,position (50D80or 90D120cm from the tree base),and date on the num-ber of eggs laid per bolt in the 2009experiment.Colonization and Apparent Survival.We used a GLM to evaluate the effects of tree condition and caging on the number of trees from which at least one T.fuscum completed development.We used a two-way ANOVA to evaluate the effects of tree condition and caging on the mean number of T.fuscum adults that emerged per bolt.

Competition,Parasitism,and Predation.We used GLM to evaluate the effects of tree condition and caging on the number of T.cinnamopterum that emerged per bolt (logarithmic link and negative bi-nomial distribution)and the percentage of emerged Tetropium sp.that were T.cinnamopterum.We used a two-way ANOVA to evaluate the effects of tree con-dition and caging on the percentage of phloem con-sumed per bolt.To evaluate the effect of tree condi-tion on the percentage of Tetropium spp.that was parasitized by R.macrocephala,W.occidentalis,or either parasitoid in exposed trees,we used GLM.We did not observe any evidence of predation by woodpeckers from June to October 2008.The preda-tion by woodpeckers we report here occurred from late October to December 2008while the bolts were stored at the stand boundary.As we removed cages from trees just before they were cut in October,we did not include a caging factor in analyses of predation by woodpeckers.Although we had already cut trees in the healthy and girdled treatments before predation by woodpeckers,variation in the condition of the bolt because of tree treatments may have in?uenced pre-dation,and therefore,we included tree condition treatment as a factor in this analysis.We used GLM with logarithmic links and negative binomial distribu-tions to evaluate the effect of tree condition on the number of woodpecker holes per bolt and the effect of Tetropium https://www.doczj.com/doc/c114484221.html,rval density on the number of woodpecker holes per bolt.We also used a linear regression,Ttting a sigmoid curve,to evaluate the relationship between larval density and the number of woodpecker holes per bolt.These analyses were con-ducted with and without the number of woodpecker holes included in the estimate of larval density,as described above.

Size,Sex Ratio,and Development Time.We used GLM to evaluate the effects of tree condition and caging on the sex ratio of emerged T.fuscum adults.Tetropium fuscum adults emerged in two distinct co-horts (see results).Therefore,GLM was also used to evaluate the effects of treatment and caging on the percentage of T.fuscum that emerged in each cohort.We used a MANOVA to evaluate the effects of tree condition,caging,and sex on the mean elytra length and development time of emerged adult T.fuscum.Tree condition (Pillai?s Trace ?0.75;F 4,106?15.73;P ?0.001)and sex (Pillai?s Trace ?0.28;F 2,52?10.07;P ?0.001),but not caging (Pillai?s Trace ?0.05;F 2,52?1.29;P ?0.29)or any interaction,were signiTcant in the MANOVA and were,therefore,included as factors in separate two-way ANOVAs evaluating elytra length and development time independently.We added a cohort factor to subsequent ANOVAs,along with any factors that were signiTcant in the original ANOVA models.We included only trees where two or more T.fuscum emerged in these analyses.To graphically represent emergence phenology with respect to tree condition,we categorized daily adult T.fuscum emergence into 3-d intervals.

Results

Oviposition.Neither tree condition (F 2,19?0.59;P ?0.57),position (F 1,19?1.44;P ?0.25),date (F 1,19?0.092;P ?0.77),nor any two-or three-way interactions (P ?0.75)in?uenced the number of eggs laid on each bolt.This supports our assumption that a similar number of eggs were laid on trees in each tree condition treatment in the 2008experiment.

Colonization and Apparent Survival.Tree condi-tion,but not caging,in?uenced the number of trees on which at least one T.fuscum completed development (Table 1).Tetropium fuscum emerged from 17of 20healthy and girdled trees,and from only nine of 20cut trees.

Tree condition,caging,and their interaction in?u-enced the number of T.fuscum adults that emerged per bolt (Table 2).When trees were caged,emer-gence was much higher on bolts cut from girdled than from healthy or cut trees (Fig.1).In contrast,when trees were exposed,emergence was highest on healthy trees (Fig.1).As we assume that an equal number of eggs were laid on trees in each treatment,the number of T.fuscum adults that emerged estimates apparent survival from egg to adult.

Competition,Parasitism,and Predation.Two,seven,and 10species of bark and wood-boring insects (i.e.,potential competitors)emerged from healthy,girdled,and cut trees,respectively (Table 3).Te-tropium cinnamopterum emerged from only one of 20healthy trees,but from six of 20cut and 11of 20girdled trees.The number of T.cinnamopterum that emerged was in?uenced by tree condition,caging,and their interaction (Table 1).On both caged and exposed trees,T.cinnamopterum emergence was highest when the tree was girdled (Fig.2).The number of T.cin-namopterum that emerged from cut or healthy trees

October 2011F LAHERTY ET AL .:E FFECT OF H OST C ONDITION ON T .fuscum P ERFORMANCE 1203

was higher when trees were caged than when they were exposed,but a similar number emerged from exposed and caged girdled trees(Fig.2).Tetropium cinnamopterum likely colonized caged trees before the manipulation of T.fuscum,which coincided with cage placement on trees,but occurred several weeks after tree condition treatments.

Only the interaction between tree condition and caging had a signiTcant effect on the percentage of emerged Tetropium spp.that was T.cinnamopterum (Table1).On exposed girdled trees(60?5%),more T.cinnamopterum emerged than in all other groups (caged girdled18?2%,caged cut23?5%,and exposed cut11?10%).Tree condition,but not caging, in?uenced the percentage phloem consumed per tree (Table2).Phloem consumption was more than four times higher on cut and girdled trees than on healthy trees(Fig.3a).

Tetropium spp.developing on caged trees were oc-casionally parasitized,but parasitism rates were low

Table1.Summary of generalized linear models evaluating effects of tree condition and caging on several quanti?ed dependent

variables

Dependent variable Source of variation df Wald?2P

Number of trees on which at least one T.fuscum completed development Tree condition2 6.590.04

Caging10.380.44

Tree condition?caging2 1.620.45 Number of T.cinnamopterum that emerged per bolt Tree condition224.14?0.01

Caging17.07?0.01

Tree condition?caging1 3.94?0.05 Percentage of emerged Tetropium spp.that were T.cinnamopterum Tree condition2 4.770.09

Caging10.870.35

Tree condition?caging1 6.290.01 Percentage parasitized by W.occidentalis Tree condition115.91?0.01 Percentage parasitized by R.macrocephala Tree condition227.59?0.01 Percentage parasitized by either parasitoid Tree condition234.04?0.01 Number of woodpecker holes per bolt Tree condition240.07?0.01 T.fuscum adult sex ratio Tree condition20.430.81

Caging10.180.67

Tree condition?caging2 1.940.38 Percentage of T.fuscum that emerged in the second cohort Tree condition197.94?0.01

Caging1 2.000.16

Tree condition?caging1 1.780.18 Table2.Two-and three-way analyses of variance evaluating effects of tree condition,caging,and sex on several quanti?ed dependent

variables

Dependent variable Source of variation df MS F P Number of T.fuscum that emerged per bolt(log10(x?1))Tree condition2 1.9911.26?0.01

Caging1 1.8210.28?0.01

Tree condition?caging2 2.2312.62?0.01

Error540.18

Percentage phloem consumed(arcsine square-root)Tree condition2 2.16328.74?0.01

Caging10.0070.090.77

Tree condition?caging20.0740.980.38

Error470.075

Adult elytra length(log)Tree condition20.06233.67?0.01 Overall Sex10.03317.80?0.01

Tree condition?sex20.0020.910.41

Error580.002

Including cohort Tree condition20.0059 3.850.02

Sex10.038825.40?0.01

Cohort10.033121.68?0.01

Tree condition?sex20.00110.740.48

Tree condition?cohort10.00040.240.62

Sex?cohort10.00130.840.36

Tree condition?sex?cohort1--

Error650.0015

Development time(log)Tree condition2 1.69484.50?0.01 Overall Sex10.0010.070.79

Tree condition?sex20.0030.150.86

Error580.020

Including cohort Tree condition20.06513.56?0.01

Cohort1 1.516318.27?0.01

Tree condition?cohort10.018 3.700.06

Error650.005

Transformations of dependent variables are indicated in parentheses.SigniTcant factors in overall models evaluating elytra length and development time were re-analyzed with the added effect of cohort.

1204E NVIRONMENTAL E NTOMOLOGY Vol.40,no.5

(6.00?0.02%).Parasitoids emerging from caged trees likely parasitized naturally occurring Tetropium spp.before trees were caged,but it is possible that some oviposited through mesh cages.Tree condition in?u-enced the percentage of Tetropium spp.parasitized by R.macrocephala,W.occidentalis,or by either parasi-toid (total parasitism)on exposed trees (Table 1).Total parasitism was relatively high on cut and girdled trees,but signiTcantly reduced on healthy trees (Fig.3b).On cut trees,the percentage of larvae parasitized by W.occidentalis was double that parasitized by R.macrocephala,whereas W.occidentalis contributed lit-tle to the overall parasitism rate on girdled trees (Fig.3b).Only R.macrocephala parasitized Tetropium spp.developing in healthy trees (Fig.3b).

Tree condition in?uenced the number of woodpecker holes per bolt (Table 1).Bolts from girdled trees had twice as many woodpecker holes as cut trees and ten times more than healthy trees (Fig.3c).There was a positive relationship between the number of Tetropium https://www.doczj.com/doc/c114484221.html,rvae per bolt and the number of woodpecker holes per bolt,whether the estimate of larval density excluded (Wald ?2?45.39;P ?0.001)(Fig.4)or included (Wald

?2?72.57;P ?0.001)the number of woodpecker holes per bolt.

Size,Sex Ratio,and Development Time.Neither tree condition nor caging in?uenced T.fuscum adult sex ratio (Table 1),which was slightly male biased (1.2males per female).The elytra of adult T.fuscum females (7.6?0.2mm)were signiTcantly longer than those of males (6.7?0.1mm)(Table 2),and adults emerging from healthy trees (7.9?0.2mm)were signiTcantly larger than those emerging from cut (6.5?0.3mm)or girdled (6.7?0.1mm)trees (Table 2).

Tetropium fuscum emergence began 23d after the start of the Trst incubation period,and adults emerged continually until day 80(Fig.5).Only one adult emerged between days 80and 112(Fig.5).Between days 112and 113of incubation at 20?C,a second winter period was simulated (see methods).Eighteen days after the end of the simulated winter (day 130of incubation),T.fuscum emergence recommenced and continued until day 213(Fig.5).When the bark was removed from bolts at the end of the second incuba-tion period,19live T.fuscum larvae in total were found developing in bolts from three healthy trees (16,2,and one larvae per bolt).

Tree condition also in?uenced T.fuscum develop-ment time (Table 2).Adults that developed in cut trees emerged earliest (39?2d),followed by those from girdled trees (51?4d)(Fig.5).Tetropium fuscum developing in healthy trees took much longer to emerge (140?8d)(Fig.5).There was no signif-icant difference in the development time of male and female T.fuscum (Table 2).

Tetropium fuscum adults emerged in two distinct cohorts (Fig.5),perhaps representing 1-and 2-yr development times.There was a signiTcant effect of tree condition,but not caging,on the percentage of T.fuscum that emerged in the Trst versus the second cohort (Table 1).All adult T.fuscum that developed in cut trees,and most of those that developed on girdled trees (95?2%),emerged in the Trst cohort (Fig.5).In contrast,few T.fuscum that developed on healthy trees (29?4%)emerged in the Trst cohort (Fig.

5).

Fig.2.Mean (?SE)number of T .cinnamopterum adults that emerged from bolts cut from healthy,girdled,or cut red spruce trees.Bolts were either caged or exposed from June to October

2008.

Fig.1.Mean (?SE)number of T .fuscum adults that emerged from bolts cut from healthy,girdled,or cut red spruce trees,where developing T .fuscum were either caged or exposed during larval development (June to October 2008).

Table 3.List of bark-and wood-boring insects that emerged from bolts cut from healthy,girdled,or cut red spruce trees near En?eld,Nova Scotia,Canada

Species

Cut

Girdled

Healthy

Hymenoptera:Siricidae

Urocerus albicornis (Fabricius)a a Coleoptera:Cerambycida e

Tetropium cinnamopterum (Kirby)a a a Coleoptera:Curculionidae:Scolytinae Polygraphus ru?pennis (Kirby)a a a

Dendroctonus ru?pennis (Kirby)a a Dryocoetes affaber (Mannerheim)a a Dryocoetes autographus (Ratz.)a a Crypturgus borealis Swaine a a

Crypturgus pusillus (Gyllenhal)a Gnathotrichus materiarius (Fitch)a Trypodendron sp.

a

a

Indicates that a species emerged from a given treatment.Voucher specimens can be found at the Atlantic Forestry Centre,Fredericton,New Brunswick,Canada.

October 2011F LAHERTY ET AL .:E FFECT OF H OST C ONDITION ON T .fuscum P ERFORMANCE 1205

There was a signiTcant effect of emergence co-hort on mean elytra length and,predictably,on mean development time (Table 2).All factors sig-niTcant in the original models also were signiTcant in the reduced models,with the added effect of cohort,and exhibited the same trends (Table 2).Adults emerging in the second cohort were larger (8.3?0.2versus 6.6?0.1mm)and took longer to develop (166?3versus 46?2d)than those that emerged in the Trst cohort.Interactions between cohort and tree condition were not signiTcant in either model (Table 2),indicating that within each

cohort,T.fuscum were larger and took longer to develop on healthy trees.

Discussion

In contrast to reports from its native range,where it attacks stressed,moribund,or recently felled Nor-way spruce (Schimitschek 1929,Juutinen 1955),T.fuscum successfully developed when adults were forced to oviposit on apparently healthy red spruce in Nova Scotia.As predicted,the performance of T.fus-cum was in?uenced by the physiological condition of host trees both directly,presumably through varia-tions in nutritional quality and host resistance,and indirectly,through its in?uence on natural enemies and competitors.

Apparent survival of T.fuscum was higher on healthy than on experimentally stressed (cut and gir-dled)trees when developing larvae were exposed to natural enemies and competitors from June to Octo-ber.The beneTts of reduced competition and para-sitism on healthy,compared with stressed trees,ap-peared to compensate for any reductions in nutritional quality and/or increased host resistance.

When developing T.fuscum larvae were protected from natural enemies (but unfortunately not compet-itors)by caging,survival was higher on slow-growing,moisture-stressed,girdled trees than on apparently healthy or cut trees.Moisture or drought stress can reduce oleoresin exudation pressure (Mattson and Haack 1987b)and the production of induced oleo-resin in conifers (Croise ′and Lieutier 1993,Cobb et al.1997,Lombardero et al.2000)and also may cause qualitative changes in oleoresin composition (Hodges and Lorio 1975).Oleoresin is an important mechanism of resistance for conifers (Phillips and Croteau 1999),and reductions in its quantity or quality can increase the performance of phloeophagous insects and asso-ciated fungi (Berryman 1972,Mattson and Haack 1987b,Paine et al.1997,Shibata 2000,Tisdale et al.2003).This may explain the high rates of T.

fuscum

Fig.3.In?uence of tree condition on (a)the mean (?SE)percentage phloem consumed per bolt by all phloem feeders,(b)the mean (least square)percentage of Te-tropium spp.parasitized by W .occidentalis and R .macro-cephala on exposed (uncaged)bolts,and (c)the mean (?SE)number of woodpecker holes per bolt.Treatment means with different letters or numbers are signiTcantly different ([a]REGW multiple comparisons test,[b],and [c]pair-wise comparisons of least square means).In 3b,numbers,uppercase and lowercase letters indicate the signiTcance of pair-wise comparisons for total percentage parasitism,parasitism by R .macrocephala ,or parasitism by W .occidentalis ,

respectively.

Fig.4.Relationship between Tetropium https://www.doczj.com/doc/c114484221.html,rval den-sity and the number of woodpecker holes per https://www.doczj.com/doc/c114484221.html,rval density was estimated by counting the number of Tetropium spp.pupal cells and dead immature larvae when bark was peeled from bolts.

1206E NVIRONMENTAL E NTOMOLOGY Vol.40,no.5

apparent survival on caged,girdled trees in this study.Girdling may cause trees to be even less well defended than naturally drought-stressed trees as a result of severing carbohydrate transport to the roots and a reduction in the cross-sectional area of sapwood.In a similar study,fewer Semanotus japonicus Lacordaire (Coleoptera:Cerambycidae)larvae died as a result of resin produced in traumatic resin canals when they developed on experimentally stressed compared with untreated Japanese cedar (Cryptomeria japonica D.Don.)trees (Shibata 2000).

Higher survival,in the absence of natural enemies,on caged girdled than on caged healthy or cut trees may also have resulted from improved larval nutrition.Stressed trees often contain higher or more balanced levels of nutrients (Mattson and Haack 1987a),

including minerals,carbohydrates,and nitrogen (Hodges and Lorio 1969,White 1984,Mattson and Haack 1987b).

Although host resistance likely was negligible in cut trees,apparent survival was still low.Caging did not prevent colonization by competitors,and thus,low survival on caged cut trees may be because of high levels of interspeciTc competition,which may have reduced the amount of nutrition and space available for larval development.

The development of juvenile T.fuscum was pro-longed on healthy compared with cut and girdled trees.In Nova Scotia,most adults emerge in mid-June (Rhainds et al.2010),and adults that emerge later may experience reduced mate-Tnding success.When de-veloping on healthy trees,most T.fuscum adults emerged in the second cohort and would likely have taken 2yr to develop in the Teld.A second year of development inherently reduces Ttness by half and increases exposure time to natural enemies and to harsh winter weather.However,multiyear generation times appear to optimize Ttness for some cerambycids,especially when food quality and natural enemy pres-sure is low (Walczyn ′ska et al.2010),similar to healthy trees in this study.In an independent study,larvae

dissected from healthy trees were smaller (earlier instar)than larvae dissected from girdled trees after one summer of development in the Teld (L.F.,un-published data).The mechanism delaying larval de-velopment in healthy trees is unknown,and is likely related to reductions in larval nutrition (Mattson and Haack 1987a).

Contrary to our predictions,adult T.fuscum that emerged from healthy trees were larger than those that emerged from cut or girdled trees.This increase in size does not necessarily indicate that healthy trees are more nutritious than girdled or cut trees,as it may result from feeding for a longer period of time or because systemic tree defenses were weakened (or eliminated)once bolts were cut from living healthy trees.In the current study,all trees were cut in fall,and any larvae that had not matured continued to develop in cut bolts (see methods).Subsequent studies should evaluate the effect of host condition on T.fuscum adult size (and other measures of performance)when ju-veniles complete their entire development on living trees in the Teld.

In Europe,woodpeckers cause signiTcant (?20%)mortality of Tetropium https://www.doczj.com/doc/c114484221.html,rvae,and are regarded as their most important predator (Schimitschek 1929,Juutinen 1955,Kenis and Hilszczanski 2004).The high number of woodpecker holes (especially in the gir-dled treatment)observed on bolts in this study sug-gests that woodpeckers are also an important predator of Tetropium spp.in Nova Scotia.There was an effect of tree condition on the number of woodpecker holes per bolt (i.e.,more woodpecker holes were found on girdled than on healthy or cut trees),but this may be attributed to variations in the density of Tetropium spp.or other bark or wood borers,similar to emerald ash borer predation by woodpeckers (Lindell et al.2008).High rates of parasitism partially explain why T.fuscum apparent survival was higher on caged than on exposed cut and girdled trees.However,when

caged,

Fig.5.Emergence phenology for T .fuscum developing in red spruce trees that had been cut,girdled or were healthy (not manipulated)before being exposed to ovipositing T .fuscum .Bolts were collected from the Teld on 15December 2008and subsequently incubated at 20?C for 112d,followed by 112d of simulated winter and another 112d incubation at 20?C.The number of T .fuscum that emerged is categorized into 3-d intervals.

October 2011F LAHERTY ET AL .:E FFECT OF H OST C ONDITION ON T .fuscum P ERFORMANCE 1207

survival was much lower on cut than on girdled trees, indicating that parasitism alone cannot explain low rates of apparent survival on exposed cut https://www.doczj.com/doc/c114484221.html,rvae may have had less phloem and space available for successful development in cut than in girdled trees. Larval eclosion occurred between3and7wk after the treatment of cut trees,during which time cut trees were rapidly colonized by competitors,especially sco-lytids and associated fungi.The number of bark and wood-boring species that colonized cut trees and the percentage of phloem consumed by all phloem-feed-ers were highest on cut trees,despite the fact that few T.fuscum emerged.Thus,the reduced apparent sur-vival on exposed,as opposed to caged,girdled trees is probably due,at least in part,to interspeciTc compe-tition,as the percentage of Tetropium spp.that were T.cinnamopterum was low for all groups except for exposed girdled trees.

Parasitoids also cause signiTcant mortality of T.fus-cum in its native range(Schimitschek1929,Juutinen 1955,Kenis and Hilszczanski2004),and rates of par-asitism were similarly high in Nova Scotia.As pre-dicted,parasitoids foraged more often or more efT-ciently on cut and girdled than on apparently healthy trees.Parasitism of another longhorn beetle,S.japoni-cus,was also lower in untreated than in mechanically stressed trees(Shibata2000).An increase in parasit-ism on stressed trees may result from primary attrac-tion of parasitoids to stressed tree volatiles(Sullivan et al.1997,Pettersson2001,Rojas et al.2006),as foraging on stressed trees may increase their likelihood ofTnd-ing host insects that colonize these trees. Alternatively,larvae developing on healthy trees may be less susceptible to postalighted parasitoids because of phenological asynchrony between ovipos-iting parasitoids and susceptible host insects caused by changes in host development rates.This likely did not reduce parasitism of T.fuscum by W.occidentalis on healthy trees in our study,as this species parasitizes early instar T.fuscum(L.F.,unpublished data).As larval development was delayed on healthy trees,lar-vae developing therein should have been more sus-ceptible to this parasitoid.The life stage(s)parasitized by R.macrocephala are unknown.If they parasitize later instars,T.fuscum developing on healthy trees may initially be less susceptible to this parasitoid(i.e., in theTrst summer).However,R.macrocephala adults emerge at about the same time as W.occidentalis, shortly after T.fuscum adults(L.F.,unpublished data) and,therefore,likely also parasitize early instars. This research evaluates complex novel ecological interactions among an exotic herbivore,its host tree, competitors,and natural enemies.Tree condition ap-pears to have a large direct impact on T.fuscum per-formance,in?uencing apparent survival,development time,and adult size.It also appears to mediate the impact of natural enemies and competitors,further in?uencing T.fuscum performance.Understanding how the performance of this exotic herbivore is in-?uenced by factors from multiple trophic levels is essential to understanding its population dynamics (Price et al.1980,Moreau et al.2006)and the risk it poses to North American forests.Further research should examine the oviposition preference of T.fus-cum to evaluate more comprehensively the risk asso-ciated with this exotic beetle.

Acknowledgments

We thank R.Johns,S.Heard,C.Simpson,and three anon-ymous reviewers for comments on an earlier version of this manuscript,K.van Rooyen, A.Morrison,K.Pronk, C. Hughes,G.Fraser,D.MacFarlane,https://www.doczj.com/doc/c114484221.html,eau,T.McCarthy, H.Williams,A.Doane,T.Harrison,W.MacKay,J.Price,S. Palmer,W.McKinnon,and S.Carmichael for technical as-sistance,and J.Major and G.Goodine for the use of their pressure bomb.This research was supported by the Canadian Forest Service and the Natural Science and Engineering Research Council of Canada,and through SERG Interna-tional by Forest Protection Limited,Ontario Ministry of Natural Resources,Nova Scotia Department of Natural Re-sources,and Newfoundland Department of Natural Re-sources.

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Received30April2011;accepted27July2011.

October2011F LAHERTY ET AL.:E FFECT OF H OST C ONDITION ON T.fuscum P ERFORMANCE1209

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门禁控制器接线原理图

门禁系统操作手册门禁控制器接线--原理图

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comparison的用法解析大全

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comparative 比较级;对手 comparing 比较 comparability 相似性;可比较性 v. comparing 比较;对照(compare的ing形式) 双语例句 He liked the comparison. 他喜欢这个比喻。 There is no comparison between the two. 二者不能相比。 Your conclusion is wrong in comparison with their conclusion. 你们的结论与他们的相比是错误的。 comparison的用法解析大全相关文章: 1.by的用法总结大全

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金融行业 运维安全审计系统技术白皮书 东华软件股份公司 2011年4月

目录 1.........................................................................................................................................审计要求 1 2解决之道 (2) 2.1HAC简介 (2) 2.2应用环境 (2) 2.3认证资质 (3) 3产品介绍 (4) 3.1系统功能 (4) 3.1.1完整的身份管理和认证 (4) 3.1.2灵活、细粒度的授权 (4) 3.1.3后台资源自动登陆 (4) 3.1.4实时监控 (5) 3.1.5违规操作实时告警与阻断 (5) 3.1.6完整记录网络会话过程 (5) 3.1.7详尽的会话审计与回放 (6) 3.1.8完备的审计报表功能 (6) 3.1.9各类应用运维操作审计功能 (6) 3.1.10可结合ITSM(IT服务管理) (7) 3.1.11其他功能 (7) 3.2系统部署 (7) 3.3系统特点 (9) 3.3.1支持Unix和W indows平台下运维操作审计 (9) 3.3.2更严格的审计管理 (9) 3.3.3分权管理机制 (9) 3.3.4部署灵活、操作方便 (9) 3.3.5完善的系统安全设计 (9) 3.4与网络审计类产品比较 (9)

4技术指标 (11) 4.1型号说明 (11) 4.2HAC1000接口配置 (13) 4.3HAC1000兼容性 (13) 5典型案例 (14) 5.1现状描述 (14) 5.2部署方案 (15) 5.3方案特点 (15)

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余的共享存储和智能备份,物理服务器失败可在几分钟内自动恢复;服务环境采用高端服务器进行部署,同时采用集中的管理与监控,确保业务稳定可靠。更强的主机性能,总体性能远高于VPS,甚至强于部分低端的独立主机。 4. 与租用物理主机相比,云主机的主要优势是什么? 服务价格低于传统的物理主机租用,且无需支付押金。具有快速供应和部署能力,用户在提交云主机租用申请后可实时开通,立即获得服务。业务支持平滑扩展,当用户业务规模扩张时,可快速实现业务扩容。内置冗余的共享存储和智能备份,物理服务器失败可在几分钟内自动恢复;更方便的系统维护功能,重装系统最快只需要3~5分钟即可完成。 5. 用户能否申请多个IP? 云主机服务根据用户选择不同的线路会配备不同数量的IP地址。默认赠送一个独立ip,可以付费增加IP。 6. 云主机租用产品送产权吗? 不送产权。云主机是基于云计算平台的主机产品,用户实际付费使用的是云计算平台的计算、存储能力以及优质的网络带宽。用户只需要为实际使用的资源付费,这也是用户选用云主机可以显著降低成本的一个主要因素。 7. 用户可以选择安装操作系统么? 可以。云主机在产品使用形态上与传统的物理主机并没有明显的差别,用户可以根据自己的需求灵活选择或变更的操作系统。 8. 租用需要交押金吗? 与传统物理主机租用不同,云主机服务用户不需要支付押金即可享受服务。 9. 如何能查看租用的主机的配置? 因为云主机在使用上与物理主机相当,用户可以在操作系统中实时的查看主机的配置信息与当前

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