Brown Marmorated Stink Bug IPM Working Group Meeting

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Ernest S. Delfosse and Paul S. Botch Department of Entomology Michigan State University East Lansing, Michigan Identifying Potential Ecological Sieves That May Mediate Impacts from Trissolcus japonicus. Brown Marmorated Stink Bug IPM Working Group Meeting Alson H. Smith, Jr. Agriculture Research and Extension Center, Winchester, VA. 2 December 2015.

Transcript of Brown Marmorated Stink Bug IPM Working Group Meeting

Page 1: Brown Marmorated Stink Bug IPM Working Group Meeting

Ernest S. Delfosse and Paul S. BotchDepartment of EntomologyMichigan State UniversityEast Lansing, Michigan

Identifying Potential Ecological Sieves That May Mediate

Impacts from Trissolcus japonicus.

Brown Marmorated Stink Bug IPM Working Group Meeting

Alson H. Smith, Jr. Agriculture Research and Extension Center, Winchester, VA. 2 December 2015.

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Topics

Origin of the use of “sieves” to describe events that mediate field behavior of a biological control agent.

Risk as a matrix of probabilities.

Risk vs. host range.

Next steps.

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Confusion re. Definitions

Physiological host-specificity (innate, laboratory, artificial, predictive = hazard = “Can-Do”).

Ecological host range (field, realized; mediating hazard by ecological sieves = exposure = “Will-Do”).

Stability of host range.

Host shifts.

Risk.

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Exposure

Hazard

HighLow Medium

3 x 3 Idealized Risk Matrix ModelRelating -phagy to Hazard, and Numbers to Exposure

Low

High

Medium

Monophagous agentAttacks one species.

Polyphagous agent: Attacks genera outside of the family.

Oligophagous agent: Attacks genera in the same family.

Species in the same genus as the target species.

Species in other genera or families in the same

Superfamily.

Species in closely related genera in the same family as

the target species.

Low Risk N/A N/A

Probably Medium Risk

Medium Risk

N/A

Probably Medium Risk

MediumRisk

High Risk

Innate physiological characteristics of the agent

Factors that mediate potential hazard, and reduce risk to non-target species.

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Interpretation of Physiological Host-specificity Testing

Ecological Sieves

Hazard

Exposure

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The Concept of Sieves Comes from Biological Control of Weeds

The most difficult challenge to biological control is predicting the risk from a natural enemy that attacks, in physiological host-specificity tests:

a rare,threatened,endangered, native species, in the same subgenus as the target species.

Delfosse, E.S. 2005. Risk and ethics in biological control. Biological Control 35:319-29.Delfosse, E.S., R.C. Lewis and S. Hasan. 1995. Release of Uromyces heliotropii in Australia: A key agent in the integrated pest management

system for common heliotrope. Proceedings of the VIII International Symposium on Biological Control of Weeds, 2-7 February 1992, Christchurch, New Zealand. Delfosse, E.S. and R.R. Scott (Eds.). DSIR/CSIRO, Melbourne, 329-36.

Hasan, S. and E.S. Delfosse. 1995. Susceptibility of the Australian native, Heliotropium crispatum, to the rust fungus, Uromyces heliotropii, introduced to control common heliotrope, Heliotropium europaeum. Biocontrol Science and Technology 5:165-74.

Hasan, S., E.S. Delfosse, E. Aracil and R.C. Lewis. 1992. Host-specificity of Uromyces heliotropii, a fungal agent for the biological control of common heliotrope (Heliotropium europaeum) in Australia. Annals of Applied Biology 121:697-705.

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The Weed:

Heliotropium europaeum

(Common Heliotrope)

The Natural Enemy:

Uromyces heliotropii

(CH Rust Fungus)

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Exposure Analysis for H. europaeum:

Identified Mediating Ecological Sieves

+ Esfh

+ Esfh = H. crispatum is the only susceptible non-target field host.

– Ebsp = No bridging species.

– Edis = No overlap in distribution.

– Ephe = Minimal overlap in phenology of spores and young leaves; summer-vs. winter-growing annuals.

– Ecli = Prevailing wind in summer away from H. crispatum populations.

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Looking for Ecological Sieves

for T. japonicus.

Exposure acts upon hazard.What sieves (exposure) can we identify that could mediate the physiological host range (hazard)?

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Objective

Determine if host acceptance behavior and attack by T. japonicus differs between BMSB and non-target egg masses in multiple-species choice tests.

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Influence of time of exposure

Finishedo 1 ho 4 ho 6 ho 24 h

Behavioral observations

Arena

Egg mass Ongoingo Searching behavioro Oviposition behavioro Host choiceo …

Influence of arena size and complexity

Size (Completed)o 10 dramo 100 dramo 500 dramo 1000 dramo 2000 dram

Complexity (Started)o Choice tests on plants

Role of parasitoid physiology & experience

o Parental experienceo Parental physiologyo Effect of host choice on

offspring physiology & behavior

A Closer Look at Host Choice Behavior in T. japonicus

www.ars-fla.com

Olfactometer Studies(FL, MI) - ongoing

Slide from Hoelmer lab

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Thyanta custator accerra(Fabricius)

Podisus maculiventris(Say)

Euschistus variolarius (Palisot

de Beauvois)

Halyomorpha halys (Stål)

MethodsMultiple-Species Choice Experiments

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MethodsSelection Criteria for Native Stink Bugs

1. All species attacked in PHST: Thyanta custator accerra -- 100% of egg masses attacked. Podisus maculiventris -- 52% of egg masses attacked. Euschistus variolarius -- 20% of egg masses attacked.

2. Biological relevance: T.c. accerra – Most-often attacked native stink bug in

PHST. P. maculiventris – Beneficial predatory species. E. variolarius – Most common native stink bug in Michigan.

3. Must be able to rear and have eggs available daily for testing.

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Influence of Arena Size on Host Choice

• Arena sizes – 4 treatments total:

• 10 Dram• 100 Dram• 1000 Dram (2 treatments)

• Arena Setup:• Egg masses 1” apart &

placed in center of card stock (10 – 1000 Dram)

• PLUS egg masses 6.5” apart in 1000 Dram

Slide from Hoelmer lab

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MethodsArena Configuration

150 x 15 mm Petri dish arenas. 24-h-old egg clusters on filter paper.Randomized quadrants.Randomized directional bearing of BMSB cluster.

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MethodsBehavioral Scoring

24-h-old mated, naïve female T. japonicus reared from BMSB eggs placed in middle of arena.Scored behaviors (video): Encounter with eggs; Inspection of eggs by

circling and antennal drumming;

Egg rejection (abandoning); and

Egg acceptance (oviposition).

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Influence of Exposure Time on Host Choice

Observation of parasitoid behavior for 1 hourNaïve, 24h-old female T.

japonicus exposed to egg masses - 1 hour- 4 hours- 6 hours

- 24 hours

BMSB P. maculiventris

Slide from Hoelmer lab

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ResultsOviposition and Rejection of Eggs

No. replicates where eggs were accepted or rejected (n = 30)

BMSB accepted significantly more than native species (p < 0.00001; X2)

No.

Rep

licat

es

Ovipositions Rejections

H. halys T.c. accerra P. maculiventris E. variolarius

Presenter
Presentation Notes
Jumping into the results, here is the behavioral data that was recorded on camera. Each blue bar is the number of times an egg mass was accepted by T. japonicus. Each orange bar is the number of replicates that an egg mass was rejected by T. japonicus.
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ResultsOviposition and Rejection of Eggs

Native stink bugs rejected multiple times per replicate

0 3.5 3 3.250

0.5

1

1.5

2

2.5

3

3.5

4

4.5

5

H. halys T.c. accerra P. maculiventris E. variolarius

Aver

age

# Re

ject

ions

/Rep

licat

e

Test Species

Average number of rejections per replicate (n = 30)

H. halys T.c. accerra P. maculiventris E. variolarius

Presenter
Presentation Notes
Jumping into the results, here is the behavioral data that was recorded on camera. Each blue bar is the number of times an egg mass was accepted by T. japonicus. Each orange bar is the number of replicates that an egg mass was rejected by T. japonicus.
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ResultsT. japonicus Emergence

Wasps attacked only one egg mass 87% of the time (33 of 38 reps).

H. halys T.c. accerra P. maculiventris E. variolarius

Parasitized Egg Masses (n = 38)

Presenter
Presentation Notes
T. Japonicus also attacked significantly more egg masses
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28.4%

73.6%

47.6%

68.4%25.4%

21.8%

39.5%

29.5%46.2%

4.6%12.9%

2.1%

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

H. halys T.c. accerra P. maculiventris E. variolarius

Total Emergence (n = 38)

Wasp emergence

Failed eggs

Stink bug nymphs

ResultsT. japonicus Emergence

Ove

rall

Perc

ent

Total Emergence (n = 38)

H. halys T.c. accerra P. maculiventris E. variolarius

Presenter
Presentation Notes
T. Japonicus also attacked significantly more egg masses
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What About Wasps Emerged from Non-target Hosts?

• Does specificity differ?• Does fecundity differ?

Presenter
Presentation Notes
I was curious about how wasps that emerged from native hosts would behave. Would they show a preference for the species of egg masses that they emerged from?
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ResultsEmergence Proportions by T. japonicus Reared on

Native Stink Bugs

Ove

rall

Pe

rce

nt

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Influence of Environmental Cues on Host Choice

BMSB P. maculiventris

OR

BMSB P. maculiventris

OR

placed on the underside of top leaf

placed on the underside of bottom leaf

Slide from Hoelmer lab

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Conclusions

BMSB was strongly preferred in multiple-species choice tests using eggs of non-target species attacked in PHST.Native non-target pentatomid eggs that were attacked in no-choice tests were frequently rejected.BMSB was never rejected by wasps reared on BMSB.

Presenter
Presentation Notes
Tests in confined 2D space
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Conclusions

Wasps reared on non-target native hosts preferred BMSB, but also continued to attack the native hosts to a lesser degree.Possibly due to a combination of genetic inclination, training, and chemical cues.Wasps reared on T.c. accerra and P. maculiventris produce fewer offspring than those reared on BMSB.

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Future Research on Ecological Sieves

Effects of egg age on successful parasitization by T. japonicus and emergence in non-target hosts.Effects of habitat partitioning on host location and attack on non-target hosts.On-going olfactometry to determine chemical cues associated with host location.

Presenter
Presentation Notes
Temporal mediators of attack Spatial mediators of attack Chemical mediators of attack
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Acknowledgements

USDA-APHIS Farm Bill Grant: No. 11-13-8130-024 CA

Delfosse Classical Biological Control Lab

This material was made possible, in part, by Cooperative Agreement 8130-0024-CA 2016 from the United States Department of Agriculture's Animal and Plant Health Inspection Service (APHIS). It may not necessarily express APHIS' views.

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Questions and Group Discussion